TITLE 30.ENVIRONMENTAL QUALITY

Part 1. TEXAS NATURAL RESOURCE CONSERVATION COMMISSION

Chapter 101. GENERAL AIR QUALITY RULES

The Texas Natural Resource Conservation Commission (commission) proposes the repeal of §101.29, Emission Credit Banking and Trading. In addition, the commission proposes new §101.300, Definitions; §101.301, Purpose; §101.302, General Provisions; §101.303, Protocols; §101.304, Program Audits; §101.350, Definitions; §101.351, Applicability; §101.352, General Provisions; §101.353, Allocation of Allowances; §101.354, Allowance Deductions; §101.356, Allowance Banking and Trading; §101.358, Emission Monitoring and Compliance Demonstration; §101.359, Reporting; §101.360, Level of Activity Certification; §101.370, Definitions; §101.371, Purpose; §101.372, General Provisions; §101.373, Protocols; and §101.374, Program Audits. The repeal and new sections will be submitted to the United States Environmental Protection Agency (EPA) as a revision to the Texas state implementation plan (SIP).

BACKGROUND AND SUMMARY OF THE FACTUAL BASIS FOR THE PROPOSED RULES

The Houston/Galveston (HGA) ozone nonattainment area is classified as Severe-17 under the Federal Clean Air Act (FCAA) Amendments of 1990 (42 United States Code (USC), §§7401 et seq.), and therefore is required to attain the one-hour ozone standard of 0.12 parts per million (ppm) by November 15, 2007. The HGA area, defined by Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller Counties, has been working to develop a demonstration of attainment in accordance with 42 USC, §7410. On January 4, 1995, the state submitted the first of its Post-1996 SIP revisions for HGA.

The January 1995 SIP consisted of urban airshed model (UAM) modeling for 1988 and 1990 base-case episodes, adopted rules to achieve a 9% rate-of-progress (ROP) reduction in volatile organic compounds (VOC), and a commitment schedule for the remaining ROP and attainment demonstration elements. At the same time, but in a separate action, the State of Texas filed for the temporary nitrogen oxides (NO x ) waiver allowed by 42 USC, §7511a(f). The January 1995 SIP and the NO x waiver were based on early base-case episodes which marginally exhibited model performance in accordance with EPA modeling performance standards, but which had a limited data set as inputs to the model. In 1993 and 1994, the commission was engaged in an intensive data-gathering exercise known as the COAST study. The state believed that the enhanced emissions inventory, expanded ambient air quality and meteorological monitoring, and other elements would provide a more robust data set for modeling and other analysis, which would lead to modeling results that the commission could use to better understand the nature of the ozone air quality problem in the HGA area.

Around the same time as the 1995 submittal, EPA policy regarding SIP elements and timelines went through changes. Two national programs in particular resulted in changing deadlines and requirements. The first of these programs was the Ozone Transport Assessment Group. This group grew out of a March 2, 1995 memo from Mary Nichols, former EPA Assistant Administrator for Air and Radiation, that allowed states to postpone completion of their attainment demonstrations until an assessment of the role of transported ozone and precursors had been completed for the eastern half of the nation, including the eastern portion of Texas. Texas participated in this study, and it has been concluded that Texas does not significantly contribute to ozone exceedances in the Northeastern United States. The other major national initiative that has impacted the SIP planning process is the revisions to the national ozone standard. The EPA promulgated a final rule on July 18, 1997 changing the ozone standard to an eight-hour standard of 0.08 ppm. In November 1996, concurrent with the proposal of the standards, the EPA proposed an interim implementation plan (IIP) that it believed would help areas like HGA transition from the old to the new standard. In an attempt to avoid a significant delay in planning activities, Texas began to follow this guidance, and readjusted its modeling and SIP development timelines accordingly. When the new standard was published, the EPA decided not to publish the IIP, and instead stated that, for areas currently exceeding the one-hour ozone standard, that standard would continue to apply until it is attained. The FCAA requires that HGA attain the standard by November 15, 2007.

The EPA issued revised draft guidance for areas such as HGA that do not attain the one-hour ozone standard. The commission adopted on May 6, 1998 and submitted to the EPA on May 19, 1998 a revision to the HGA SIP which contained the following elements in response to EPA's guidance: UAM modeling based on emissions projected from a 1993 baseline out to the 2007 attainment date; an estimate of the level of VOC and NO x reductions necessary to achieve the one-hour ozone standard by 2007; a list of control strategies that the state could implement to attain the one-hour ozone standard; a schedule for completing the other required elements of the attainment demonstration; a revision to the Post-1996 9% ROP SIP that remedied a deficiency that EPA believed made the previous version of that SIP unapprovable; and evidence that all measures and regulations required by Subpart 2 of Title I of the FCAA to control ozone and its precursors have been adopted and implemented, or are on an expeditious schedule to be adopted and implemented.

In November 1998, the SIP revision submitted to EPA in May 1998 became complete by operation of law. However, EPA stated that it could not approve the SIP until specific control strategies were modeled in the attainment demonstration. The EPA specified a submittal date of November 15, 1999 for this modeling. In a letter to EPA dated January 5, 1999, the state committed to model two strategies showing attainment.

As the HGA modeling protocol evolved, the state eventually selected and modeled seven basic modeling scenarios. As part of this process, a group of HGA stakeholders worked closely with commission staff to identify local control strategies for the modeling. Some of the scenarios for which the stakeholders requested evaluation included options such as California-type fuel and vehicle programs as well as an acceleration simulation mode equivalent motor vehicle inspection and maintenance program. Other scenarios incorporated the estimated reductions in emissions that were expected to be achieved throughout the modeling domain as a result of the implementation of several voluntary and mandatory statewide programs adopted or planned independently of the SIP. It should be made clear that the commission did not propose that any of these strategies be included in the ultimate control strategy submitted to EPA in 2000. The need for and effectiveness of any controls which may be implemented outside the HGA eight-county area will be evaluated on a county-by-county basis.

The SIP revision was adopted by the commission on October 27, 1999, submitted to EPA by November 15, 1999, and contained the following elements: photochemical modeling of potential specific control strategies for attainment of the one-hour ozone standard in the HGA area by the attainment date of November 15, 2007; an analysis of seven specific modeling scenarios reflecting various combinations of federal, state, and local controls in HGA (additional scenarios H1 and H2 build upon Scenario VIf); identification of the level of reductions of VOC and NO x necessary to attain the one-hour ozone standard by 2007; a 2007 mobile source budget for transportation conformity; identification of specific source categories which, if controlled, could result in sufficient VOC and/or NO x reductions to attain the standard; a schedule committing to submit by April 2000 an enforceable commitment to conduct a mid-course review; and a schedule committing to submit modeling and adopted rules in support of the attainment demonstration by December 2000.

The April 2000 SIP revision for HGA contained the following enforceable commitments by the state: to quantify the shortfall of NO x reductions needed for attainment; to list and quantify potential control measures to meet the shortfall of NO x reductions needed for attainment; to adopt the majority of the necessary rules for the HGA attainment demonstration by December 31, 2000, and to adopt the rest of the shortfall rules as expeditiously as practical, but no later than July 31, 2001; to submit a Post-99 ROP plan by December 31, 2000; to perform a mid-course review by May 1, 2004; and to perform modeling of mobile source emissions using the EPA mobile source emissions model (MOBILE6), to revise the on-road mobile source budget as needed, and to submit the revised budget within 24 months of the model's release. In addition, if a conformity analysis is to be performed between 12 months and 24 months after the MOBILE6 release, the state will revise the motor vehicle emissions budget (MVEB) so that the conformity analysis and the SIP MVEB are calculated on the same basis.

In order for the state to have an approvable attainment demonstration, EPA has indicated that the state must adopt those strategies modeled in the November submittal and then adopt sufficient controls to close the remaining gap in NO x emissions. The modeling included in this proposal indicates that a gap of an additional 81 tons per day (tpd) of NO x reductions is necessary for an approvable attainment demonstration.

The emission reduction requirements included as part of this SIP revision represent substantial, intensive efforts on the part of stakeholder coalitions in the HGA area. These coalitions, involving local governmental entities, elected officials, environmental groups, industry, consultants, and the public, as well as the commission and EPA, have worked diligently to identify and quantify potential control strategy measures for the HGA attainment demonstration. Local officials from the HGA area have formally submitted a resolution to the commission, requesting the inclusion of many specific emission reduction strategies.

The current SIP revision contains rules, enforceable commitments, and photochemical modeling analyses in support of the HGA ozone attainment demonstration. In addition, this SIP contains post-1999 ROP plans for the milestone years 2002 and 2005, and for the attainment year 2007. The SIP also contains enforceable commitments to implement further measures, if needed, in support of the HGA attainment demonstration, as well as a commitment to perform and submit a mid-course review.

The Houston nonattainment area will need to ultimately reduce NO x more than 750 tons per day to reach attainment with the one-hour standard. In addition, a VOC reduction of about 25% will have to be achieved.

The proposed emissions banking and trading program has been designed to offer flexibility in generating and using emission reduction credits (ERCs), mobile emission reduction credits (MERCs), discrete emission reduction credits (DERCs), and mobile discrete emission reduction credits (MDERCs). Flexibility has been built into the proposed rules to create incentives for the early or permanent retirement of volatile organic compounds (VOC) and nitrogen oxides (NO x ) emissions. The intent of the proposed rules is to also streamline the emissions banking and trading program by combining the stationary credits with mobile credits to achieve continuity within the banking programs.

The proposed new §§101.300 - 101.304 are to be grouped into Subchapter H, Division 1, Emission Credit Banking and Trading. The proposed rules consolidate the requirements for generating, using, banking, and trading ERCs and MERCs. The proposed rules are intended to achieve consistency between the rules governing the use of ERCs/MERCs and DERCs and MDERCs. The proposed rules also address concerns raised by the EPA regarding current rules on how reductions are calculated as surplus and to ensure that emission reductions are not double-counted, that is, not banked as credits and relied upon as SIP reductions. These proposed sections would reduce the life of ERCs/MERCs generated after January 1, 2001 to five years to restrict the use of ERCs/MERCs to meet current environmental conditions. The rules would require the registration of emission reductions as ERCs/MERCs within 180 days of the actual reduction and add recordkeeping requirements to sources generating or using ERCs/MERCs.

The proposed new §§101.350 - 101.354, 101.356, 101.358 - 101.360 are to be grouped into Subchapter H, Division 3, Mass Emissions Cap and Trade Program. These proposed sections will implement a mandatory annual NOx emission cap on all existing stationary sources located in the Houston/Galveston (HGA) ozone nonattainment area that emit more than ten tons or more per year (tpy) of NO x and that have SIP emission requirements in 30 TAC §117.106, Emission Specifications for Attainment Demonstrations, §117.206, Emission Specifications for Attainment Demonstrations, and §117.475, Emission Specifications. The cap would be enforced by the allocation, trading, and banking of allowances. An allowance is the equivalent of one ton of NO x emissions. NO x is a precursor gas that reacts with VOCs in the presence of sunlight to form ground-level ozone. This NOx cap would be established at levels demonstrated as necessary to allow HGA to attain the national ambient air quality standard (NAAQS) for ozone. The proposed cap would initially be implemented on January 1, 2002 at historical emission levels, with three mandatory annual reductions until achieving the final cap by January 1, 2005. These proposed sections would also require all new or modified sources in HGA to obtain unused allowances from other sources already participating under the cap to offset any increased NO x emissions.

At this time, the commission proposes to cap only those sources located in the eight-county HGA area. The commission will continue to evaluate ozone control strategies and may extend the cap and trade program to include other regions of the state in future rulemaking.

The proposed new sections §§101.370 - 101.374 are to be grouped into Subchapter H, Division 4, Discrete Emission Credit Banking and Trading. The proposed rules consolidate the requirements for generating, using, banking, and trading DERCs and MDERCs. The proposed rules are intended to achieve consistency between the rules governing the use of ERCs/MERCs and DERCs/MDERCs. The proposed rules also address concerns raised by the EPA regarding current rules on how reductions are calculated as surplus and to ensure that emission reductions are not double-counted, that is, not banked as credits and relied upon as SIP reductions.

The commission solicits comment on additional flexibilities relating to rule content and implementation which have not been addressed in this or other concurrent rulemakings. These flexibilities may be available for both mobile and stationary sources. Additional flexibilities may also be achieved through innovative and/or emerging technology which may become available in the future. Additional sources of funds for incentive programs may become available to substitute for some of the measures considered here.

The commission solicits comment on additional flexibilities relating to rule content and implementation which have not been addressed in this or other concurrent rulemakings. These flexibilities may be available for both mobile and stationary sources. Additional flexibilities may also be achieved through innovative and/or emerging technology which may become available in the future. Additional sources of funds for incentive programs may become available to substitute for some of the measures considered here.

SECTION BY SECTION DISCUSSION

DIVISION 1

The proposed new §101.300 would contain the definitions to be used within Subchapter H, Emissions Credit Banking and Trading, Division 1, Emission Credit Banking and Trading. The definitions of "Activity", "Actual emissions", "Area Source", "Certified", "Emission Reduction Credit (ERC)", "Emission Reduction Strategy", "Generator", "Permanent", "Quantifiable", and "Shutdown" were defined in §101.29 and are proposed to be transferred unchanged to §101.300.

The following definitions are proposed to be moved from §101.29 to §101.300 and amended. "Applicable emission point" would be revised to refer to the emission point generating an emission reduction or using an emission credit. This revision will allow for consistency with the use of terms throughout the proposed rule language. The definition of "Baseline" would be amended to limit the emissions occurring prior to a reduction strategy to levels not to exceed the most recent level of emissions reported in the emission inventory used for SIP determinations. The definition of "Baseline activity" would be amended to describe a source's actual level of activity based on actual data averaged over any consecutive two calendar year periods during the most recent year of emissions inventory used for SIP determinations or subsequent year(s). For sources in existence less than 24 months or not having two complete calendar years of data, a shorter time period, not less than 12 months, may be considered by the executive director. The definition of "Baseline emission rate" would be amended to refer to the source's rate of emissions per unit of activity during the baseline activity period. The definition of "Curtailment" would be amended to mean a reduction in activity level at any stationary or mobile source. The definition of "Mobile emission reduction credit (MERC or mobile credit)" would be amended to be a credit representing the amount of emission reductions from a mobile source strategy. These emission reductions are voluntary and must be in addition to compliance with requirements of state and federal regulations. MERCs are any enforceable, permanent, and quantifiable emission reduction (exhaust and/or evaporative) generated by a mobile source, which has been banked in accordance with the rules of the commission. MERCs can be banked, purchased, traded, and sold to meet clean air mandates for specified air programs, which can be applied to the emission reduction obligations of another air quality source or to air quality attainment goals. "Most stringent allowable emissions level" would be amended to include a reference to state emission limits. The definition of "Ozone season" would be revised to be the portion of the year when ozone monitoring is required to occur in a specific geographic area. This amendment removes specific references to dates for a given nonattainment area. "Protocol" would be amended to refer to replicable and workable methods for mobile, stationary, or area sources. "Real reduction" would mean a reduction in which actual emissions are reduced as opposed to a reduction in allowable emissions. "Surplus" would be amended to refer to an emission reduction which is not otherwise required of a source by any state or federal law, regulation, or agreed order and is beyond the emissions level utilized for SIP determinations. "User" would be amended to refer to the owner or operator which acquires and uses emission credits to meet a regulatory requirement, demonstrate compliance, or offset an emission increase.

The following new definitions are proposed for addition to §101.300. "Baseline emissions" would be defined as the source's total actual emissions based on the baseline activity and baseline emission rate. An "Emission credit" would be newly defined as a credible emission reduction such as an "Emission reduction credit" or "Mobile emission reduction credit." A new definition of "Emission reduction" would be added as an actual reduction of emissions from a stationary or mobile source. "Mobile emission baseline" would be newly defined as a mobile source reduction that occurs prior to a mobile emission reduction strategy, considering all limitations required by applicable state and federal regulations. A valid mobile emission baseline could be calculated by either use of measured emissions of an appropriately sized sample of the participating mobile sources using an approved EPA test procedure or by using estimated emissions of the participating mobile sources using the most recent edition of EPA's mobile emissions factor model or other applicable model. The baseline cannot be higher than the emissions that are estimated in the SIP for that vehicle. "Mobile source" would be defined as on-road (highway) vehicles (e.g., automobiles, trucks, and motorcycles) and non-road vehicles (e.g., trains, airplanes, agricultural equipments, industrial equipment, construction vehicles, off-road motorcycles, and marine vessels). A "Mobile source baseline activity" would be newly defined as the mobile source's level of activity during the applicable mobile source baseline year. "Mobile source baseline emissions" would be newly defined as the mobile source's total emissions based on the product of mobile source baseline activity and mobile source baseline emission rate. "Source" would be a point of origin of air contaminants, whether privately or publicly owned or operated. Upon request of a source owner, the executive director shall determine whether multiple processes emitting air contaminants from a single point of emission will be treated as a single source or as multiple sources.

The proposed new §101.301 states that the purpose of Division 1 is to allow an operator of a source to generate and use emission credits. The wording of this section would be revised from the previous language in §101.29 to refer to both ERCs and MERCs as emission credits, unless the rule language refers to specifically only one of these emission credits. This new section would also state that participation in the program is voluntary.

The proposed new §101.302 would contain the general provisions for the Emission Credit and Trading Program (Division 1). The wording of this section would be revised from the previous language in §101.29 to refer to both ERCs and MERCs as emission credits, unless the rule language refers to only one of these emission credits. The certification requirements of an emission credit would be revised to only allow credits which have occurred after the most recent year of emissions inventory used for SIP determinations and to require the source's annual emissions to have been represented in the emissions inventory of the most recent year of emissions inventory used for SIP determinations prior to the submittal of the emission credit application. Rule language would be added to this division which would not allow emission credits which are certified as ERCs or MERCs to be recertified as emission credits under any other division within Subchapter H. The rules associated with eligible sources would be changed to be consistent with the previous language of §101.29 for discrete emission credits. The changes would allow for stationary sources (including area sources), mobile sources and stationary sources (including area sources), and mobile sources associated with agencies under §101.30 to be eligible to generate emission credits. Effective January 2, 2001, the life of an emission credit would be revised to be available for use for 60 months from the date of the reduction except to the extent regulatory changes reduce or invalidate the reduction. Administratively complete applications for ERCs which are received prior to January 2, 2001 would continue to be available for 120 months from the date of the reduction except to the extent regulatory changes reduce or invalidate the reduction. The geographic scope would remain the same as previously stated in §101.29 except the new rule language would allow for the trading of emission credits achieved in the county, state, or nation, provided the applicant can demonstrate an improvement to the air quality in the county of use and which is approved by the executive director. To be consistent with the previous language of §101.29, rule language would be added which allows for the possibility of the trading of emission credits to be discontinued by the executive director, with commission approval, as a remedy for problems caused by localized trading of emission credits. Recordkeeping requirements would be revised to require users to maintain a copy of all notices and information submitted to the registry for at least two years after the beginning of the use period along with the name, emission point number (EPN), and facility identification number (FIN) of each unit using emission credits, the amount of emission credits being used, and the specific identification number of the emission credits being used. The rule language concerning public information would be changed to be consistent with the discrete emission reduction requirements language previously located in §101.29(d)(1)(L). All information submitted with a notice or report regarding the nature and quantity of emissions associated with the use or generation of an emission credit is public information and will not be considered confidential. All non-confidential notices and information regarding generation, use, and availability of emission credits may be obtained from the Office of Permitting, Remediation, and Registration (OPRR). In addition, rule language is proposed which allows the executive director to prohibit a company from participating in the program if the company has violated or abused the program.

The proposed new §101.303 would outline the required protocols of generating, calculating, certifying and registering, using, and transferring emission credits. This section would require emission credits to be determined based on established EPA protocols or when available, actual monitoring results are calculated using good engineering practices. The existing procedures in §101.29 regarding the various means for generating emission credits would be transferred unchanged to this section. The rule addresses procedures for calculating MERCs although most mobile source strategies will likely only qualify for MDERCs, MERCs would be available for mobile source strategies that are ongoing, creating the same amount of mobile reduction each year. Language would be added which does not allow the generation of credits if the emissions have been transferred to another unit. This additional language would eliminate the potential of a company shutting down a unit to generate emission credits, but altering the operation of another piece of equipment to take the place of the shut down unit and thereby increasing the emissions at the altered unit. The new rules would require companies to apply for emission credits within 180 days of generation, except that those sources that have implemented strategies prior to the effective date of this rule will be given until June 1, 2001 to apply. When applying for credits, new language would be added to the rules specifying the information which must be submitted. The information, which is to be submitted on the EC-1 Form, includes the information necessary for the executive director to review the application in accordance with the proposed rules and to properly administer the program. As is currently stated in §101.29, applicants will be notified in writing if the executive director denies the application. Although it has been the commission's accepted practice, the proposed new rule language specifically states that emissions credits will be determined and certified to the nearest tenth of a ton per year. As is currently stated in §101.29, the proposed section would state that emission credits are determined and certified by using EPA methodologies, monitoring results, or otherwise good engineering practices, and all emission credits are deposited in the registry and reported as available credits until they are used, withdrawn, or expired. As is currently stated in §101.29, the proposed section would list the mechanisms which can be used to make emission credits enforceable. Rule language would be added which lists the OPCRE-1 form as an enforceable mechanism to establish new emission limits for grandfathered sources when applying for emission credits. Proposed rule language would also be added to make MERCs enforceable by registering them on a form approved by the executive director or by an agreed order that will set new maximum allowable mobile source emission limits which are not required to be implemented by a rule. The proposed language would limit the use of emission credits if there are permits under the same account number which contain a condition or conditions which preclude such use. As is currently stated in §101.29, the proposed section will allow ERCs to be used for offsets, mitigation offsets, and alternative compliance with reasonably available control technology (RACT) or SIP requirements. As has been the commission's practice, the proposed language would add the use of emission credits for netting only by the original applicant if the emission credits have not been previously sold or otherwise used and would also allow for emission credits to be used for other provisions as allowable within the guidelines of local, state, and federal laws. The proposed section would allow MERCs to be used as offsets, mitigation offsets, alternative compliance with RACT or SIP requirements, compliance with fleet requirements as allowed by the Texas Clean Fleet Program Requirements for Motor Vehicle Fleets, or other provisions as allowed within the guidelines of local, state, and federal laws. The requirements for compliance with §117.570, Trading, except for the equations for determining 30-day rolling average emission limits, would be changed to allow for emission reduction calculations in accordance with the methodology of this new division. These revisions would replace the former equations previously located in §117.570. The equations for calculating 30-day rolling average emission limits would be relocated from §117.570 to this section. The procedure for notifying the commission of the intent to use emission credits in accordance with 30 TAC Chapter 114, Control of Air Pollution from Motor Vehicles, §115.950, Emissions Trading, and §117.570 and any other commission rules would be revised to require the submittal of the EC-3 Form. The timelines for the review of this submittal would be removed from the rule language, revised, and included in the Emission Banking and Trading Program Technical Guidance Package. As previously required in §101.29, an additional 10% of emission credits would be retired as an environmental contribution. The proposed section would state that the user of credits shall submit an EC-3 Form along with the emission credit certificates when using the credits as offsets in accordance with 30 TAC Chapter 116, Division 7, Emission Reductions: Offsets, or for alternative compliance with 30 TAC Chapters 114, 115, or 117. The procedure for transfer would be revised to require emission credit certificate owners to submit an EC-4 Form, including the sale price, to the agency prior to the transfer. Transfers would only be considered final after the executive director has completed the transaction. This is a change to the existing language in §101.29, which requires notification within 30 days of the transfer. As currently stated in §101.29, the proposed section would state that the emission credits may be withdrawn from the registry at any time prior to the expiration date of the credit, and that emission reductions which have been certified as credits and have expired may still be used by the original owner for netting in accordance with §116.150. The proposed section would require applicants requiring offsets for a new source review permit to identify the credits at the time of permit issuance and to provide the original emission credit certificate prior to operation. It should be noted that emission credits will be evaluated to ensure that they are surplus at the time of use. The proposed section would require that any other uses of credits be approved by the executive director prior to commencement of the intended use. Rule language is proposed which would allow an applicant to file a motion of reconsideration with the executive director within 60 days of denying a use of emission credits.

The proposed new §101.304 would require the executive director to perform an audit of the emission reduction program within three years of the effective date of the new division and every three years thereafter. The audit would evaluate the timing of credit generation and use, the impact of the program on the SIP, availability and cost of credits, compliance by participants, and any other elements chosen by the executive director.

DIVISION 3

The proposed new §101.350 would contain the definitions to be used with Subchapter H, Emissions Credit Banking and Trading, Division 3, Mass Emission Cap and Trade Program. The definition of "Allowance" would be the authorization to emit one ton of NO x during a control period. The definition of "Authorized account representative" would be the responsible person who is authorized in writing, to transfer and otherwise manage allowances. The definition of "Banked allowance" would be an allowance which is not used to reconcile emissions in the designated year of allocation, but which is carried forward for up to one year and noted in the compliance or broker account as banked. The definition of "Broker" would be a person not required to participate in the requirements of this division who opens an account under this division for the purpose of banking and trading allowances. The definition of "Broker account" would be the account where allowances held by a broker are recorded. Allowances held in a broker account may not be used to satisfy compliance requirements for this division. The definition of "Compliance account" would be the account where allowances held by a source or multiple sources are recorded for the purposes of meeting the requirements of this division. Sources not under common ownership or control may have separate compliance accounts. The definition of "Control period" would be the 12-month period beginning January 1 and ending December 31 of each year. The initial control period would begin January 1, 2002. The definition of "Level of activity" would be the amount of activity at a source measured in terms of production, fuel use, raw materials input, or other similar units that have a direct correlation with the economic output and emission rate of the source (i.e., mass emitted per unit of activity). The definition of "Person" would be, for the purpose of issuance of allowances under this division, an individual, a partnership of two or more persons having a joint or common interest, a mutual or cooperative association, and a corporation.

The new section refers to the following predefined definitions: "Houston/Galveston (HGA) ozone nonattainment area" as defined in §101.1; and "Source" as defined in §101.1.

The proposed new §101.351 would state that the requirements of Division 3 apply to all stationary NO x sources in the HGA nonattainment area subject to the emission specifications under §§117.106, 117.206, and 117.475 and that have a designed capacity to emit ten tons or more per year of NO x .

The proposed new §101.352 would state that allowances may only be used to meet the requirements of Division 3 and cannot be used to meet or exceed the limitations of any annual emission limitation authorized under Chapter 116, Subchapter B, any applicable rule or law, or for netting purposes to avoid the applicability of federal and state new source review (NSR) requirements. The new section would require that each source subject to this division shall hold a quantity of allowances in its compliance account equal to or greater than its total emission of NO x emitted during the control period just ending. The cap and trade program would begin January 1, 2002. Beginning February 1, 2003, each source would be required to hold the amount of allowance it used in the previous year's control period. The new section would allow unused allowances to be banked as ERCs provided that an enforceable and permanent reduction of annual allowances is approved by the executive director, and all applicable requirements of Divisions 1 or 4 of Chapter 101, Subchapter H are met. The new section states that allowances may be simultaneously used to satisfy offset requirements for new or modified sources subject to federal nonattainment NSR requirements as provided in Chapter 116, Division 7 but not for netting requirements. The new section states that all allowances would be allocated, transferred, or used as whole allowances and that one compliance account shall be used for multiple sources located at the same property and under common ownership or control. The new section states that an allowance would not constitute a security or a property right. The commission would maintain a registry of the allowances in each compliance account. The registry would not contain proprietary information. Requests for information identified as proprietary when submitted to the agency would be subject to the procedures set out in the Texas Public Information Act.

The proposed new §101.353 describes how allowances will be allocated to individual sources. Initially, for any source operating prior to January 1, 1997, allowances will be based on its actual level of activity averaged over 1997, 1998, and 1999 multiplied by the higher of the source's actual emission factor averaged over 1997, 1998, and 1999 (not to exceed any applicable regulatory or permit limit) or the source's emission factor listed in Chapter 117. For a source not operating prior to January 1, 1997, but operating prior to January 1, 2000, allowances will be equal to the source's actual level of activity averaged over the most recent two consecutive calendar years (not to exceed any applicable regulatory or permit limit) multiplied by the higher of the source's actual emission factor averaged over the most recent two consecutive calendar years (not to exceed any applicable regulatory or permit limit) or the source's emission factor listed in Chapter 117. For a source authorized under Chapter 106 or 116 but not operating prior to January 1, 2000, allowances will be equal to the source's authorized level of activity multiplied by the higher of source's authorized emission factor or the source's emission factor listed in Chapter 117. The purpose for using a two- or three-year average, when available, is to limit the effect of a year in which the activity level was uncharacteristically low or high. The purpose for using the higher of the source's actual or allowable emission factor or its emission factor as listed in Chapter 117 is to prevent penalizing those sources already emitting or authorized to emit at levels equal to or lower than the requirements in Chapter 117. For the 2003 and 2004 control periods, a source's allowances will be reduced each year by one-third of the difference between its initial allocation in 2002 and calculated final allocation for 2005. For the 2005 and subsequent control periods, allowances will be allocated based on historical activity levels and emission factors as listed in Chapter 117 that are demonstrated necessary to reach attainment. The section states that any new source which has submitted an administratively complete application by January 2, 2001 will not be allocated any allowances. These new sources will be required to obtain allowances from other sources already participating in the cap and trade program or by obtaining DERC or MDERC. The section states that if a source emits more NO x than what was held in the compliance account on January 31 following the control period, that allocation of allowances for the next control period will be reduced by the amount equal to the emission exceeding the compliance account plus an additional 10%. The section states that allowances would be allocated by January 1 of each control period, beginning in 2002, and that the annual allocation of allowances may be adjusted for any new SIP requirement and that allowances may be added or subtracted from compliance accounts after reviewing the trading reports required in §101.356 and the annual reporting requirements in §101.359. Proposed language would allow the executive director to deviate from the allocation methodology in extenuating circumstances.

The proposed new §101.354 describes how allowances will be subtracted out of compliance accounts. The section states that allowances are deducted in whole tons based on the source's level of activity during a control period and multiplied by the source's emission factor during the control period. The section states that a source shall hold a quantity of allowances equal to or greater than its actual NO x emissions by February 1 for the preceding control period.

The proposed new §101.356 describes how allowances may be traded and banked. Allowances may generally be banked for future use or traded during the control period for which they are allocated or the following control period. Any allowance not used for compliance may be banked or traded for use in the following control period, with the exception of unused allowances allocated under proposed §101.353(a)(1)(C). The section states that allowances that aren't expired or used could be traded at any time after they have been allocated. Only authorized account representatives may trade allowances. Trade requests would be made through the submittal of a completed form ECT-2. As part of the application, the account representative shall report the price paid per allowance. Trades would be completed through the executive director and would be considered complete when the executive director issues a letter finalizing the trade. This section would allow for the use of discrete emission credits in accordance with Chapter 101, Subchapter H, Division 4 in place of allowances for compliance with Division 3. Currently, the proposed §101.356(d) only allows NO x credits to be used as an alternative to allowances under the mass cap and trade program. The commission is soliciting comments on how to address allowing certain VOC reductions which produce equal or better ozone results in lieu of NO x reductions for compliance with the cap.

The proposed new §101.358 states that if monitoring is required of a source under a federal or state program, that monitoring or other data shall be used to determine actual NO x emissions. Sources not required to monitor shall calculate actual NO x emissions using good engineering practices, including calculation methodologies in general use and accepted in NSR permitting.

The proposed new §101.359 states that sources shall submit by March 31 a completed ECT-1 detailing the amount of actual NO x emission for the preceding control period and shall include the methods used in determining the NO x emissions and a summary of all final trades.

The proposed new §101.360 states that all sources required to participate in the cap and trade program would be required to submit a completed ECT-3 certifying their historical level of activity by June 30, 2001. This information will be used to calculate each source's allocations.

DIVISION 4

The proposed new §101.370 would contain the definitions to be used within Subchapter H, Emissions Credit Banking and Trading, Division 4, Discrete Emission Credit Banking and Trading. The definitions of "Activity," "Actual emissions," "Area Source," "Certified," "Emission Reduction Strategy," "Generator," "Permanent," "Quantifiable," "Shutdown," and "Use period" were defined in §101.29 and are proposed to be transferred unchanged to §101.370.

The following definitions are proposed to be moved from §101.29 to this section and amended. "Applicable emission point" will be revised to refer to the emission point generating an emission reduction or using an emission credit. This revision would allow for consistency with the use of terms throughout the proposed rule language. The definition of "Baseline" would be amended to limit the emissions occurring prior to a reduction strategy to levels not to exceed the most recent level of emissions reported in the emission inventory used for SIP determinations. The definition of "Baseline activity" would be amended to describe a source's actual level of activity based on actual data averaged over any consecutive two calendar year period during the most recent year of emissions inventory used for SIP determinations or subsequent year(s). For sources in existence less than 24 months or not having two complete calendar years of data, a shorter time period, not less than 12 months, may be considered by the executive director. The definition of "Baseline emission rate" would be amended to refer to the source's rate of emissions per unit of activity during the baseline activity period. The definition of "Curtailment" would be amended to mean a reduction in activity level at any stationary or mobile source. The definition of "Discrete emission reduction credit" would be revised to be a credible emission reduction that is created during a generation period, quantified after the period in which emission reductions are made, and expressed in tons. This change provides consistency with the new terms and definitions of the proposed rules. The definition of "Ozone season" would be revised to the portion of the year when ozone monitoring is federally required to occur in a specific geographic area. "Protocol" would be amended to refer to replicable and workable methods for mobile and stationary sources. The definition of "Real reduction" would mean a reduction in which actual emissions are reduced as opposed to a reduction in allowable emissions. "Surplus" would be amended to refer to an emission reduction which is not otherwise required of a source by any state or federal law, regulation, or agreed order and is beyond the emissions level utilized for SIP determinations. "User" would be amended to refer to the owner or operator which acquires and uses emission credits to meet a regulatory requirement, demonstrate compliance, or offset an emission increase. "Use strategy" would be revised to refer to the use of "emission credits" which is more consistent with the terms in the proposed new rules.

The following new definitions are proposed for addition to §101.370. "Baseline emissions" would be defined as the source's total actual emissions based on the baseline activity and baseline emission rate. A "Discrete emission credit" would be newly defined as a credible emission reduction such as a "Discrete emission reduction credit" or "Mobile discrete emission reduction credit." A new definition of "Emission reduction" would be added as an actual reduction of emissions from a stationary or mobile area source. The "Generation period" would be defined as the discrete period of time, not exceeding 12 months, over which a discrete emission reduction credit is created. A "Mobile discrete emission reduction credit (MDERC or discrete mobile credit)" would be defined as a credit that is surplus, generated by a mobile source strategy. It is a creditable emission reduction that is created during a generation period, quantified after the period in which emissions reductions are made, and expressed in tons. AMobile emissions "baseline" is proposed to be mobile emissions which occur prior to a mobile emission reduction strategy, considering all limitations required by applicable state and federal regulations. A valid mobile emission baseline could be calculated by either using measured emissions of an appropriately-sized sample of the participating mobile sources using an approved EPA test procedure or by using estimated emissions of the participating mobile sources using the most recent edition of EPA's mobile emissions factor model or other applicable model. The baseline cannot be higher than the emissions which are estimated in the SIP for that vehicle. "Mobile source baseline activity" would be defined as the mobile source's level of activity during the applicable mobile source baseline year. A definition for "Mobile source baseline emissions" would be the source's total actual mobile source emissions based on the mobile source activity and the mobile source emissions rate. "Most stringent allowable emissions rate" would refer to the emission rate of a source, considering all limitations required by applicable local, state, and federal regulations. The term "Strategy activity" would be the source's level of activity during the discrete emission reduction generation period and "Strategy emission rate" would be the source's emission rate during the discrete emission reduction generation period. "Source" would be a point of origin of air contaminants, whether privately or publically owned or operated. Upon request of a source owner, the executive director shall determine whether multiple processes emitting air contaminants from a single point of emission will be treated as a single source or multiple sources.

The proposed new §101.371 states that the purpose of Division 4 is to allow an operator of a source to generate and use discrete emission credits. The wording of this section will be revised from the previous language in §101.29 to refer to both DERSs and MDERCs as discrete emission credits, unless the rule language refers to specifically only one of these discrete emission credits. This new section will also state that participation in the program is voluntary.

The proposed new §101.372 would contain the general provisions for the Discrete Emission Credit and Trading Program. The wording of this section will be revised from the previous language in §101.29 to refer to both DERCs and MDERCs as emission credits, unless the rule language refers to only one of these discrete emission credits. The section would specify to which pollutants the program will apply and is unchanged from those currently in §101.29. The section would state that DERCs and MDERCs must be real, quantifiable, and surplus. The certification requirements of a discrete emission credit would be revised to only allow credits which have occurred after the most recent year of emissions inventory used for SIP determinations and to require the source's annual emissions prior to the submittal of the emission credit application to have been represented in the emissions inventory of the most recent year of emissions inventory used for SIP determinations. Rule language would be added which prohibits emission credits certified as DERCs or MDERCs from being recertified as emission credits under any other division within Subchapter H. The proposed section would allow for stationary sources (including area sources), mobile sources, and stationary sources (including area sources) associated with agencies under §101.30 to be eligible to generate and use emission credits, if there are no permits under the same account number which contain a condition or conditions precluding the use of emission credits. The proposed rule language will allow DERCs and MDERCs to be available for use after the executive director has received a notice of generation and the discrete emission credits have been reviewed and deemed creditable. This is a change from previous procedures where emission credits were placed in the registry upon receipt of the notice and generation and were not reviewed for credibility until a notice of intent to use was received by the executive director. This change will allow for the emission reduction program and the discrete emission reduction program to operate on a more consistent basis. The proposed section states that DERCs and MDERCs may be used anytime after certification and do not expire. The geographic scope will remain the same as currently stated in §101.29, except the new rule language will allow for the trading and use of emission credits generated in other counties, states, or nations provided that a demonstration has been made and approved by the executive director showing that the reduction in the area where the credit was generated causes an improvement in air quality in the county where the credit is used. As currently stated in §101.29, the trading of discrete emission credits may be discontinued by the executive director, in whole or in part, with commission approval. As currently stated in §101.29 for areas having an ozone season less than 12 months, discrete emission credits generated outside the ozone season may not be used during the ozone season. The commission will maintain a registry that lists all discrete emission credits available or used. The proposed section would require the generator and user of discrete emission credits to maintain a copy of records for a minimum of five years regarding the generation and use of credits. The records shall include at a minimum the name, emission point, and facility identification number of each source using discrete reduction credits, the amount of discrete reduction credits being used, and the specific identification number of the credit being used. As currently stated in §101.29, all information submitted with any application to generate or use discrete emission credits may not be submitted as confidential and discrete emission credits do not constitute a property right. The proposed rules state that the executive director has the authority to prohibit either the generation or the use of discrete reduction credits if the executive director determines that the company has violated any of the requirements of the program or has abused the privileges provided by the program. Rule language concerning the start date for the discrete emission reduction program would be removed, since this program is currently ongoing.

The proposed new §101.373 outlines the required protocols of generating, calculating, certifying and registering, using, and transferring discrete emission credits. This section will require discrete emission credits, to be determined based on established EPA protocols or when available, actual monitoring results or calculated using good engineering practices. There are no changes from the existing §101.29 regarding the various means for generating discrete emission credits. The proposed section would revise the equation for calculating the amount of DERCs generated to use the lower of the baseline emission rate or the most stringent emission rate. This revision will allow for the correct calculation of DERCs if the baseline emission rate was exceeding the emission rate required by local, state, or federal requirements. As currently stated in §101.29, the proposed section would require DERCs to be rounded down to the nearest ton. The proposed section limits the generation period for DERCs to five years. The proposed section would not allow a source to generate discrete emission credits for any emissions exceeding its allowable emission limit. The proposed section deletes language from the existing §101.29 which restricted reductions used for netting from being generated as DERCs. The proposed section states what requirements and data must be documented to calculate MDERCs. The existing language located in §101.29 regarding registration and certification of emission credits would remain the same and would be relocated to this proposed section. The proposed section would add language detailing what information, at a minimum, would be required to generate mobile discrete emission credits. The information, which is to be submitted on DEC-1 Form, includes the information necessary for the executive director to review the application in accordance with the proposed rules and to properly administer the program. It should be noted that, for continuing credits, each application will be reviewed for creditability at the time of submittal in addition to the time of strategy implementation. Although it has always been the accepted practice, the proposed new rule language specifically states that discrete emissions credits will be determined and certified to the nearest ton. The proposed section would include new language regarding the review of discrete emission reduction registrations for credibility upon receipt and that applicants being denied registration of discrete emission credits would be notified of such denial in writing. The proposed section states that discrete emission credits will be reviewed and certified based on actual monitoring data, EPA methodology, or other commission approved protocols. In addition, rule language is added which states that discrete emission credits will be deposited in the registry and will be available for use until they are used, withdrawn, or expire. The proposed compliance and burden language is essentially the same as currently stated in §101.29. The user would be responsible for ensuring that the discrete emission credits are certified and certification, by the executive director, does not relieve the user on any other responsibilities. There are no proposed changes to the existing §101.29 language regarding what discrete emissions can or cannot be used for; however, the language would be reorganized into subparagraphs which state what the discrete emission credits can be used for and a subparagraph which states what they cannot be used for. The proposed language would relocate the equations which provide flexibility to the 30-day rolling average emission limits, and the new maximum daily emission limit for source caps as defined in Chapter 117. The commission proposes to change the equation used to calculate the amount of discrete emission credits needed to demonstrate compliance or meet a regulatory requirement to be consistent with the terms proposed for this division, and to add language which would be consistent with the procedures and methodologies proposed within this division. The equations for calculating 30-day rolling average emission limits would be relocated to this section unmodified. There are no changes proposed to the existing requirements for additional credits needed as compliance margins or for environmental contributions. As previously stated in §101.29, the calculated discrete emission credits will be rounded up to the nearest ton and the user must retire 10% more than are needed. The amount of discrete emission credits needed for NSR offsets would remain equal to the quantity of tons needed to achieve the maximum allowable emission level set in the user's NSR program. As previously stated in §101.29, discrete emission credits which are not used during the use period would remain surplus and available for use or transfer by the holder. As previously stated in §101.29, a notice of intent to use the DEC-2 Form would be submitted to inform the executive director of the intent to use discrete emission credits. The information required to be submitted on the DEC-2 Form would remain the same as previously stated in §101.29. The proposed section would include a list of the required information to be submitted when a mobile source user intends to use discrete emission credits. The proposed language listing the requirements for a user to notify the executive director of actual discrete emission credit use would remain the same as previously stated in §101.29 with the exception of added language requiring the user to submit the information on a DEC-3 Form. The proposed language regarding compliance burden and enforcement for discrete emission credit users would remain the same as previously stated in §101.29.

The proposed new §101.374 is a relocation, and there will be no wording changes to previously existing language in §101.29, concerning auditing of the DERC program.

FISCAL NOTE: COST TO STATE AND LOCAL GOVERNMENT

John Davis, Technical Specialist with Strategic Planning and Appropriations, has determined for each year of the first five-year period the proposed amendments are in effect, there will be fiscal implications which are not anticipated to be significant for any single unit of state or local government as a result of administration or enforcement of the proposed amendments.

The proposed amendments would consolidate existing requirements for generating, using, banking, and trading ERCs, MERCs, DERCs, and MDERCs into two separate programs. The section containing the original program would be repealed. The two programs would be grouped under two divisions. Division 1, Credit Banking and Trading, would handle ERC and MERC issues. Division 4, Discrete Emission Credit Banking and Trading, would handle DERC and MDERC issues. The creation of two separate programs would facilitate improved management and control of the programs. The proposed amendments would update definitions, make administrative changes to Divisions 1 and 4, and should provide flexibility and potential cost savings in planning and determining the most economical mix of the application of emission control technology with the use of emission credits to meet emission reduction requirements.

In addition to creating Divisions 1 and 4, the proposed amendments would create Division 3, The Mass Emission Cap and Trade Program. This program would implement and manage a mandatory annual NO x emission cap, phased-in between January 1, 2002 to January 1, 2005, on all existing and new stationary sources located in the HGA ozone nonattainment area consisting of: Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller Counties. The NO x emission cap only affects sources in the HGA that have the capacity to emit ten tons of NOx or more per year, and that have SIP emission requirements. Examples of equipment and processes at sources that would be affected by the proposed amendments include: electric utility boilers and stationary gas turbines; ICI boilers and stationary gas turbines; duct burners used in turbine exhaust ducts; process heaters and furnaces; stationary internal combustion engines; fluid catalytic cracking units (including catalyst regenerators and carbon monoxide (CO) boilers and furnaces); pulping liquor recovery furnaces; lime kilns; lightweight aggregate kilns; heat treating and reheat furnaces; magnesium chloride fluidized bed dryers; incinerators; and BIF units. The agency would allocate to a source a number of allowances (NO x emissions in tons) which a source would be allowed to emit during the calendar year. The source is not allowed to exceed this number of allowances granted unless they obtain additional allowances from another facility's surplus allowances. Allowance trading should provide flexibility and potential cost savings in planning and determining the most economical mix of the application of emission control technology with the purchase of other facility's surplus allowances to meet emission reduction requirements.

The commission is required to submit a new SIP revision by the end of 2000 which will bring the HGA into attainment by 2007. The plan sets forth a control strategy that provides emission reductions necessary for attainment and maintenance of the national standards.

There will be fiscal impacts to state and local government facilities if they elect to participate in the voluntary programs under Division 1 and 4 programs; however, the total number of state or local government sites affected by these provisions is unknown. Division 1 covers facilities in nonattainment counties and Division 4 covers facilities statewide. The costs associated with participation in Division 1 and 4 programs would result from the purchase of emission credits and would be dependent on the market value of the emission credits. The current cost of credits in the HGA ranges from $750 per ton for DERCs/MDERCs to $3,600 per ton per year for ERCs/MERCs. Actual costs will be dependent on availability and demand. Total costs to state and local government sites that elect to participate in Division 1 and 4 programs will depend on the amount of emission credits purchased.

Although the total number is unknown, some of the approximately 6,000 pieces of equipment at sources in the HGA that are affected by Division 3 provisions will be owned and operated by state or local governments. The cost of allowances in similar programs nationwide has ranged from approximately $500 to $5,000 per allowance (ton), depending on availability and demand. Actual costs for allowances will be dependent upon market demand and availability. The total cost to state and local government sites will depend on the total number of allowances purchased.

Most of the sources which will have to comply with the proposed rules are currently subject to air permits and are already being inspected for compliance. Consequently, only a limited number of additional facilities will need to be inspected for compliance with the proposed amendments; therefore, there are no significant fiscal implications for the agency as a result of implementation of the proposed amendments.

PUBLIC BENEFIT AND COSTS

Mr. Davis has also determined for each of the first five years the proposed amendments to Chapter 101 are in effect, the public benefit anticipated as a result on implementing the amendments will be the reduction of emissions of NO x in the HGA to a level that will allow the area to meet the NAAQS for ozone.

The proposed amendments would consolidate existing requirements for generating, using, banking, and trading ERCs, MERCs, DERCs, and MDERCs into two separate programs. The section containing the original program would be repealed. The two programs would be grouped under two divisions. Division 1, Credit Banking and Trading, would handle ERC and MERC issues. Division 4, Discrete Emission Credit Banking and Trading, would handle DERC and MDERC issues. The creation of two separate programs would facilitate improved management and control of the programs. The proposed amendments would update definitions, make administrative changes to Divisions 1 and 4, and should provide flexibility and potential cost savings in planning and determining the most economical mix of the application of emission control technology with the use of emission credits to meet emission reduction requirements.

In addition to creating Divisions 1 and 4, the proposed amendments would create Division 3, The Mass Emission Cap and Trade Program. This program would implement and manage a mandatory annual NO x emission cap, phased in between January 1, 2002 to January 1, 2005, on all existing and new stationary sources located in the HGA ozone nonattainment area consisting of: Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller Counties. The NO x emission cap only affects sources in the HGA that have the capacity to emit ten tons of NOx or more per year, and that have SIP emission requirements. Examples of equipment and processes at sources that would be affected by the proposed amendments include: electric utility boilers and stationary gas turbines; ICI boilers and stationary gas turbines; duct burners used in turbine exhaust ducts; process heaters and furnaces; stationary internal combustion engines; fluid catalytic cracking units (including catalyst regenerators and CO boilers and furnaces); pulping liquor recovery furnaces; lime kilns; lightweight aggregate kilns; heat treating and reheat furnaces; magnesium chloride fluidized bed dryers; incinerators; and BIF units. The agency would allocate to a source a number of allowances (NO x emissions in tons) which a source would be allowed to emit during the calendar year. The source is not allowed to exceed this number of allowances granted unless they obtain additional allowances from another facility's surplus allowances. Allowance trading should provide flexibility and potential cost savings in planning and determining the most economical mix of the application of emission control technology with the purchase of other facility's surplus allowances to meet emission reduction requirements.

There will be fiscal impacts to persons and businesses if they elect to participate in the voluntary programs under Division 1 and 4 programs; however, the total number private entities affected by these provisions is unknown. Division 1 covers facilities in nonattainment counties and Division 4 covers facilities statewide. The costs associated with participation in Division 1 and 4 programs would result from the purchase of emission credits and would be dependent on the market value of the emission credits. The current cost of credits in the HGA area ranges from $750 per ton for DERCs/MDERCs to $3,600 per ton per year for ERCs/MERCs. Actual costs will be dependent on availability and demand. Total costs to persons and businesses that elect to participate in Division 1 and 4 programs will depend on the amount of emission credits purchased.

There are approximately 6,000 pieces of equipment at sources in the HGA that are affected by Division 3 provisions, some of which will be owned and operated by persons and businesses. The cost of allowances in similar programs nationwide has ranged from approximately $500 to $5,000 per allowance (ton), depending on availability and demand. Actual costs for allowances will be dependent upon market demand and availability. The total cost to persons and businesses will depend on the total number of allowances purchased.

SMALL AND MICRO-BUSINESS ASSESSMENT

Adverse fiscal implications are not anticipated for small or micro-businesses as a result of administration or enforcement of the proposed amendments. Under the proposed amendments, small or micro-businesses electing to participate in the program established by Divisions 1 and 4 would pay the same unit cost for emission credits as other participants. There is no feasible way to reduce the unit costs for small businesses. However, participation in this portion of the program is voluntary. Under the Mass Emissions Cap and Trade Program as established by Division 3, small or micro-businesses located in the HGA would pay the same unit costs for the purchase of allowances as other businesses. Of the 6,000 identified pieces of equipment at sources in the HGA, some will be owned and operated by small or micro-businesses. Examples of likely equipment at sources operated by small or micro-businesses include boilers, process heaters, and internal combustion engines. The rules exempt sources which emit less than ten tons per year. There is no feasible way to further reduce the impact of the proposed amendments for small businesses.

DRAFT REGULATORY IMPACT ASSESSMENT

The commission has reviewed the proposed rulemaking in light of the regulatory analysis requirements of Texas Government Code, §2001.0225. Proposed Divisions 1 and 4 create a voluntary mechanism which provides regulatory flexibility for compliance with state and federal emission limitations and do not add mandatory regulatory requirements or required costs. The proposed Division 3 would affect owners and operators of new and existing stationary sources emitting NO x subject to §§117.106, 117.206, and 117.475 requirements in the HGA nonattainment area. The commission has determined the proposed rulemaking in Division 3 of Chapter 101 meets the definition of a "major environmental rule" as defined in Texas Government Code, §2001.0225, but proposed rulemaking in Divisions 1 and 4 is not. "Major environmental rule" means a rule, the specific intent of which, is to protect the environment or reduce risks to human health from environmental exposure, and that may adversely affect in a material way the economy, a sector of the economy, productivity, competition, jobs, the environment, or the public health and safety of the state or a sector of the state. Existing sources would be limited to NO x emission levels under an emissions cap based on historical operating data and source specific emission rates determined by Chapter 117. New stationary sources would be required to identify a source(s) of allowances equal to allowable emissions prior to commencing operation. All sources subject to this division would be required to hold a quantity of allowances in their compliance account by January 31 following the end of a control period, which is equal to or greater than the total emissions from the preceding control period. The cost of allowances in similar programs nationwide has ranged from approximately $500 to $5,000 per allowance (ton), depending on availability and demand. Actual costs in the HGA nonattainment area will be dependent upon market demand and availability. The commission is proposing these sections as part of a strategy to reduce and permanently cap emissions of NO x to a level which would allow the HGA nonattainment area to attain the NAAQS for ozone. In addition, Texas Government Code, §2001.0225, only applies to a major environmental rule, the result of which is to: 1.) exceed a standard set by federal law, unless the rule is specifically required by state law; 2.) exceed an express requirement of state law, unless the rule is specifically required by federal law; 3.) exceed a requirement of a delegation agreement or contract between the state and an agency or representative of the federal government to implement a state and federal program; or 4.) adopt a rule solely under the general powers of the agency instead of under a specific state law. This rulemaking is not subject to the regulatory analysis provisions of §2001.0225(b), because the proposed rule does not meet any of the four applicability requirements. Specifically, the emission banking and trading requirements within this proposal were developed in order to meet the ozone NAAQS set by the EPA under the Federal Clean Air Act (FCAA), §7409, and therefore meet a federal requirement. Provisions of 42 USC, §7410, require states to adopt a SIP which provides for "implementation, maintenance, and enforcement" of the primary NAAQS in each air quality control region of the state. While §7410 does not require specific programs, methods, or reductions in order to meet the standard, state SIPs must include "enforceable emission limitations and other control measures, means or techniques (including economic incentives such as fees, marketable permits, and auctions of emissions rights), as well as schedules and timetables for compliance as may be necessary or appropriate to meet the applicable requirements of this chapter," (meaning Chapter 85, Air Pollution Prevention and Control). It is true that 42 USC does require some specific measures for SIP purposes, like the inspection and maintenance program, but those programs are the exception, not the rule, in the SIP structure of 42 USC. The provisions of 42 USC recognize that states are in the best position to determine what programs and controls are necessary or appropriate in order to meet the NAAQS. This flexibility allows states, affected industry, and the public, to collaborate on the best methods for attaining the NAAQS for the specific regions in the state. Even though 42 USC allows states to develop their own programs, this flexibility does not relieve a state from developing a program that meets the requirements of §7410. Thus, while specific measures are not generally required, the emission reductions are required. States are not free to ignore the requirements of §7410 and must develop programs to assure that the nonattainment areas of the state will be brought into attainment on schedule.

The requirement to provide a fiscal analysis of proposed regulations in the Texas Government Code was amended by Senate Bill 633 (SB 633) during the 75th Legislative Session, 1999. The intent of SB 633 was to require agencies to conduct a regulatory impact analysis (RIA) of extraordinary rules. These are identified in the statutory language as major environmental rules that will have a material adverse impact and will exceed a requirement of state law, federal law, or a delegated federal program, or are adopted solely under the general powers of the agency. With the understanding that this requirement would seldom apply, the commission provided a cost estimate for SB 633 that concluded "based on an assessment of rules adopted by the agency in the past, it is not anticipated that the bill will have significant fiscal implications for the agency due to its limited application." The commission also noted that the number of rules that would require assessment under the provisions of the bill was not large. This conclusion was based, in part, on the criteria set forth in the bill that exempted proposed rules from the full analysis unless the rule was a major environmental rule that exceeds a federal law. As previously discussed, 42 USC does not require specific programs, methods, or reductions in order to meet the NAAQS; thus, states must develop programs for each nonattainment area to ensure that area will meet the attainment deadlines. Because of the ongoing need to address nonattainment issues, the commission routinely proposes and adopts SIP rules. The legislature is presumed to understand this federal scheme. If each rule proposed for inclusion in the SIP was considered to be a major environmental rule that exceeds federal law, then every SIP rule would require the full RIA contemplated by SB 633. This conclusion is inconsistent with the conclusions reached by the commission in its cost estimate and by the Legislative Budget Board (LBB) in its fiscal notes. Since the legislature is presumed to understand the fiscal impacts of the bills it passes, and that presumption is based on information provided by state agencies and the LBB, the commission believes that the intent of SB 633 was only to require the full RIA for rules that are extraordinary in nature. While the SIP rules will have a broad impact, that impact is no greater than is necessary or appropriate to meet the requirements of the FCAA. For these reasons, rules proposed for inclusion in the SIP fall under the exception in Texas Government Code, §2001.0225(a), because they are required by federal law. The commission performed photochemical grid modeling which predicts that NO x emission reductions, such as those required by these rules, will result in reductions in ozone formation in the HGA ozone nonattainment area. This rulemaking does not exceed an express requirement of state law. This rulemaking is intended to obtain NO x emission reductions which will result in reductions in ozone formation in the HGA ozone nonattainment area and help bring HGA into compliance with the air quality standards established under federal law as NAAQS for ozone. The rulemaking does not exceed a standard set by federal law, exceed an express requirement of state law (unless specifically required by federal law), or exceed a requirement of a delegation agreement. The rulemaking was not developed solely under the general powers of the agency, but was specifically developed to meet the NAAQS established under federal law and authorized under Texas Clean Air Act (TCAA), §§382.011, 382.012, and 382.017 as well as under 42 USC, §7410(a)(2)(A).

The commission invites public comment on the draft regulatory impact analysis.

TAKINGS IMPACT ASSESSMENT

The commission has completed a takings impact assessment for the proposed rules. The following is a summary of that assessment. These sections are proposed as part of a strategy to reduce and permanently cap emissions of NO x to a level which would allow the HGA nonattainment area to attain the NAAQS for ozone. Promulgation and enforcement of the rules will not burden private real property. The proposed new sections do not affect private property in a manner which restricts or limits an owner's right to the property that would otherwise exist in the absence of a governmental action. Additionally, the credits and allowances created under these rules are not property rights. Consequently, these proposed sections do not meet the definition of a takings under Texas Government Code, §2007.002(5). Although the proposed rule revisions do not directly prevent a nuisance or prevent an immediate threat to life or property, they do prevent a real and substantial threat to public health and safety, and partially fulfill a federal mandate under the FCAA, §7410. Specifically, the emission limitations and control requirements within this proposal were developed in order to meet the ozone NAAQS set by the EPA under the FCAA, §7409. States are primarily responsible for ensuring attainment and maintenance of the NAAQS once the EPA has established them. Under the FCAA, §7410 and related provisions, states must submit, for approval by the EPA, SIPs that provide for the attainment and maintenance of NAAQS through control programs directed to sources of the pollutants involved. Therefore, the purpose of the rule proposal is to implement a NO x strategy which is necessary for the HGA area to meet the air quality standards established under federal law as NAAQS. Consequently, the exemption which applies to these proposed rules is that of an action reasonably taken to fulfill an obligation mandated by federal law. Therefore, these proposed revisions will not constitute a takings under Texas Government Code, Chapter 2007.

COASTAL MANAGEMENT PROGRAM CONSISTENCY REVIEW

The commission has determined the proposed rulemaking relates to an action or actions subject to the Texas Coastal Management Program (CMP) in accordance with the Coastal Coordination Act of 1991, as amended (Texas Natural Resources Code, §§33.201 et seq.) , and the commission's rules in 30 TAC Chapter 281, Subchapter B, concerning Consistency with the Texas Coastal Management Program. As required by 30 TAC §281.45(a)(3) and 31 TAC §505.11(b)(2), relating to actions and rules subject to the CMP, commission rules governing air pollutant emissions must be consistent with the applicable goals and policies of the CMP. The commission has reviewed this action for consistency with the CMP goals and policies in accordance with the regulations of the Coastal Coordination Council and has determined that the proposed rules are consistent with the applicable CMP goal expressed in 31 TAC §501.12(1) of protecting and preserving the quality and values of coastal natural resource areas, and the policy in 31 TAC §501.14(q), which requires that the commission protect air quality in coastal areas. If adopted, the new sections will reduce and cap emissions of NO x in the HGA nonattainment area to a level that would allow attainment of the NAAQS for ozone. No new contaminants will be authorized by these rules, and a reduction of NOx emissions should occur. Interested persons may submit comments on the consistency of the proposed rule with the CMP during the public comment period.

EFFECT ON SITES SUBJECT TO THE FEDERAL OPERATING PERMIT PROGRAM

The proposed new sections under Divisions 1, 3, and 4, if adopted, would become part of the state's ozone attainment strategy; therefore, these amendments would be submitted as part of the SIP. As a result, the proposed sections and any allowances allocated under these sections would become applicable requirements under the federal operating permit program.

ANNOUNCEMENT OF HEARINGS

The commission will hold public hearings on this proposal at the following times and locations: September 18, 2000, 10:00 a.m., Lone Star Convention Center, 9055 Airport Road (FM 1484), Conroe; September 18, 2000, 7:00 p.m., Lake Jackson Civic Center, 333 Highway 332 East, Lake Jackson; September 19, 2000, 10:00 a.m. and 7:00 p.m., George Brown Convention Center, 1001 Avenida de Las Americas, Houston; September 20, 2000, 9:00 a.m., VFW Hall, 6202 George Bush Drive, Katy; September 20, 2000, 6:00 p.m., East Harris County Community Center, 7340 Spencer, Pasadena; September 21, 2000, 10:00 a.m., Southeast Texas Regional Airport Media Room, 6000 Airline Drive, Beaumont; September 21, 2000, 2:00 p.m., Amarillo City Commission Chambers, City Hall, 509 East 7th Avenue, Amarillo; September 21, 2000, 6:00 p.m., Charles T. Doyle Convention Center, 21st Street at Phoenix Lane, Texas City; September 22, 2000, 10:00 a.m., Dayton High School, 2nd Floor Lecture Room, 3200 North Cleveland Street, Dayton; El Paso City Council Chambers, 2 Civic Center Plaza, 2nd Floor, El Paso; September 22, 2000, 2:00 p.m., North Central Texas Council of Governments, 2nd Floor Board Room, 616 Six Flags Drive, Suite 200, Arlington; and September 25, 2000, 10:00 a.m., Texas Natural Resource Conservation Commission, 12100 North I-35, Building E, Room 201S, Austin. The hearings are structured for the receipt of oral or written comments by interested persons. Registration will begin one hour prior to each hearing. Individuals may present oral statements when called upon in order of registration. A four-minute time limit will be established at each hearing to assure that enough time is allowed for every interested person to speak. Open discussion will not occur during each hearing; however, agency staff members will be available to discuss the proposal one hour before each hearing, and will answer questions before and after each hearing.

Persons with disabilities who have special communication or other accommodation needs, who are planning to attend the hearings, should contact the Office of Environmental Policy, Analysis, and Assessment at (512) 239-4900. Requests should be made as far in advance as possible.

SUBMITTAL OF COMMENTS

Written comments may be submitted to Heather Evans, Office of Environmental Policy, Analysis, and Assessment, MC 206, P.O. Box 13087, Austin, Texas 78711-3087, faxed to (512) 239-4808, or emailed to siprules@tnrcc.state.tx.us. All comments should reference Rule Log Number 1998-089-101-AI. Comments must be received by 5:00 p.m., September 25, 2000. For further information, please contact Matthew R. Baker at (512) 239-1091 or Beecher Cameron at (512) 239-1495.

Subchapter A. GENERAL RULES

30 TAC §101.29

(Editor's note: The text of the following section proposed for repeal will not be published. The section may be examined in the offices of the Texas Natural Resource Conservation Commission or in the Texas Register office, Room 245, James Earl Rudder Building, 1019 Brazos Street, Austin.)

STATUTORY AUTHORITY

The repeal is proposed under the Texas Health and Safety Code, TCAA, §382.011, which authorizes the commission to control the quality of the state's air; §382.012, which authorizes the commission to develop a plan for control of the state's air; §382.017, which provides the commission the authority to adopt rules consistent with the policy and purposes of the TCAA, and 42 United States Code, §7410(a)(2)(A), which requires SIPs to include enforceable emission limitations and other control measures or techniques, including economic incentives such as fees, marketable permits, and auction of emission rights.

The proposed repeal implements TCAA, §382.011, General Powers and Duties; §382.012, State Air Control Plan; and §382.017, Rules.

§101.29.Emission Credit Banking and Trading.

This agency hereby certifies that the proposal has been reviewed by legal counsel and found to be within the agency's legal authority to adopt.

Filed with the Office of the Secretary of State, on August 11, 2000.

TRD-200005653

Margaret Hoffman

Director, Environmental Law Division

Texas Natural Resource Conservation Commission

Earliest possible date of adoption: September 24, 2000

For further information, please call: (512) 239-4808


Subchapter H. EMISSIONS BANKING AND TRADING

1. EMISSION CREDIT BANKING AND TRADING

30 TAC §§101.300-101.304

STATUTORY AUTHORITY

The new sections are proposed under the Texas Health and Safety Code, TCAA, §382.011, which authorizes the commission to control the quality of the state's air; §382.012, which authorizes the commission to develop a plan for control of the state's air; §382.017, which provides the commission the authority to adopt rules consistent with the policy and purposes of the TCAA, and United States Code, §7410(a)(2)(A), which requires SIPs to include enforceable emission limitations and other control measures or techniques, including economic incentives such as fees, marketable permits, and auction of emission rights.

The proposed new sections implement TCAA, §382.011, General Powers and Duties; §382.012, State Air Control Plan; and §382.017, Rules.

§101.300.Definitions.

The following words and terms, when used in this division, shall have the following meanings, unless the context clearly indicates otherwise.

(1)

Activity--The amount of activity at a source measured in terms of production, use, raw materials input, vehicle miles traveled (VMT), or other similar units that have a direct correlation with the economic output and emission rate of the source (i.e., mass emitted per unit of activity).

(2)

Actual emissions--Actual emissions as of a particular date shall equal the total emissions during the selected time period, using the unit's actual daily operating hours, production rates, types of materials processed, stored, or combusted during the selected time period.

(3)

Applicable emission point--The source which is either generating an emission reduction or using an emission credit.

(4)

Area source--Any source included in the agency emissions inventory under the area source category.

(5)

Baseline--Emissions that occur prior to an emission reduction strategy, considering all limitations required by applicable state and federal regulations. The baseline may not exceed the quantity of emissions reported in the most recent year of emissions inventory used for state implementation plan (SIP) determinations.

(6)

Baseline activity--The source's level of activity based on the unit's actual daily operating hours, production rates, or types of materials processed, stored, or combusted averaged over any consecutive two calendar year period following or including the most recent year of emissions inventory used for SIP determinations or subsequent year(s) which precede the emission reduction strategy or credit use period. For sources in existence less than 24 months or not having two complete calendar years of activity data, a shorter time period of not less than 12 months may be considered by the executive director.

(7)

Baseline emission rate (BER)--The source's rate of emissions per unit of activity during the baseline activity period.

(8)

Baseline emissions--The source's total actual emissions based on the product of baseline activity and BER.

(9)

Certified--Any emission reduction that is determined to be creditable upon review and approval by the executive director.

(10)

Curtailment--A reduction in activity level at any stationary or mobile source.

(11)

Emission Credit--An emission reduction credit (ERC) or mobile emission reduction credit (MERC).

(12)

Emission Reduction--An actual reduction of emissions from a stationary or mobile source.

(13)

Emission reduction credit (ERC)--A certified emission reduction that is created by eliminating future emissions, quantified during or before the period in which emission reductions are made, and expressed in tons per year.

(14)

Emission reduction strategy--The method implemented to reduce the source's emissions which are surplus.

(15)

Generator--The owner or operator of a source that creates an emission reduction.

(16)

Mobile emissions baseline--Mobile emissions that occur prior to a mobile emission reduction strategy, considering all limitations required by applicable state and federal regulations. A valid mobile emission baseline can be calculated by either using measured emissions of an appropriately sized sample of the participating mobile sources using an approved EPA test procedure or by using estimated emissions of the participating mobile sources using the most recent edition of EPA's on-road or non-road mobile emissions factor models, or other model as applicable. To ensure that mobile credits are surplus, mobile source baseline emissions estimates for each year of the proposed mobile source control program must be the same as, or lower than, those used, or proposed to be used, in the SIP in which the control program is proposed.

(17)

Mobile emission reduction credit (MERC or mobile credit)--A credit representing the amount of emission reductions from a mobile source strategy. These emission reductions are voluntary and must be in addition to compliance with requirements of state and federal regulations. MERCs are any enforceable, permanent, and quantifiable emission reduction (exhaust and/or evaporative) generated by a mobile source, which has been banked in accordance with the rules of the commission. MERCs can be banked, purchased, traded, and sold to meet clean air mandates for specified air programs, which can be applied to the emission reduction obligations of another air quality source or to air quality attainment goals.

(18)

Mobile source--On-road (highway) vehicles (e.g., automobiles, trucks and motorcycles) and non-road vehicles (e.g., trains, airplanes, agricultural equipment, industrial equipment, construction vehicles, off-road motorcycles, and marine vessels).

(19)

Mobile source baseline activity--Will be based on an estimate for each year for which the credits are to be generated. After the initial year, the annual estimates should reflect:

(A)

the change in the mobile source emissions to reflect any deterioration in the emission control performance of the participating source;

(B)

the change in the number of mobile sources resulting from normal retirement or attrition, and the replacement of retired mobile sources with newer and/or cleaner mobile sources;

(C)

the change in usage levels, hours of operation or VMT in the participating population; and

(D)

the change in the expected useful life of the participating population.

(20)

Mobile source baseline emission--The source's total actual mobile source emissions based on the product of mobile source action and the mobile source emissions rate.

(21)

Most stringent allowable emissions rate--The emission rate of a source, considering all limitations required by applicable local, state, and federal regulations.

(22)

Ozone season--The portion of the year when ozone monitoring is federally required to occur in a specific geographic area.

(23)

Permanent--An emission reduction that is long-lasting and unchanging for the remaining life of the source. Such a time period must be enforceable.

(24)

Protocol--A replicable and workable method of estimating emission rates or activity levels used to calculate the amount of emission reduction generated or credits required for stationary or mobile sources.

(25)

Quantifiable--An emission reduction that can be measured or estimated with confidence using replicable methodology.

(26)

Real reduction--A reduction in which actual emissions are reduced as opposed to a reduction in allowable emissions.

(27)

Shutdown--The permanent cessation of an activity producing emissions at a facility.

(28)

Source--As defined in §101.1(90) of this title (relating to Definitions).

(29)

Surplus--An emission reduction that is not otherwise required of a source by any local, state or federal law, regulation, or agreed order.

(30)

User--The owner or operator of a source that acquires and uses emission credits to meet a regulatory requirement, demonstrate compliance, or offset an emission increase.

§101.301.Purpose.

The purpose of this division is to allow the operator of a source to generate emission credits by reducing emissions beyond the level required by any local, state, and federal regulation and to allow the operator of another source to use these credits. Participation under this division is strictly voluntary.

§101.302.General Provisions.

(a)

Applicable pollutants. Reductions of volatile organic compounds (VOCs) and nitrogen oxides (NO x ) may qualify as emission credits. Reductions of other pollutants do not qualify as emission credits under this division. Reductions of one pollutant may not be used to meet the requirements of another pollutant, except at such time as urban airshed modeling demonstrates that one ozone precursor may be substituted for another.

(b)

Emission reduction requirements.

(1)

emission reduction credits (ERCs) are generated from reductions beyond those required. To be certified as an emission credit, an emission reduction must be enforceable, permanent, quantifiable, real, and surplus. The emission credit must be surplus at the time it is created, as well as when it is used. The certified reduction must have occurred after the most recent year of emissions inventory used for state implementation plan (SIP) determinations for VOC and NO x , and the source's annual emissions prior to the emission credit application must have been reported or represented in the emissions inventory used for SIP determinations.

(2)

mobile emission reduction credits (MERCs) are generated from reductions beyond those required, and derived from a calculation of the annual difference between the mobile source emissions baseline and the projected emissions level after the MERC strategy has been put in place. To be certified as a MERC, an emission reduction must be enforceable, permanent, quantifiable, real, and surplus. The emission credit must be surplus at the time it is created, as well as when it is used. The certified reduction must have occurred after the most recent year of emissions inventory used for SIP determinations for VOC and NO x , the mobile source's emissions must have been represented in the emissions inventory used for SIP determinations, and the applicable mobile sources must have been included in the attainment demonstration baseline.

(3)

Emission reductions from a source which are certified as emission credits under this division cannot be recertified in whole or in part as credits under another division within this subchapter.

(c)

Eligible sources. The following sources are eligible to generate emission credits:

(1)

stationary sources (including area sources);

(2)

any mobile source;

(3)

any stationary source (including area sources) or mobile source associated with actions by federal agencies under §101.30 of this title (relating to Conformity of General Federal Actions to State Implementation Plans).

(d)

Life of an emission credit.

(1)

If an ERC is used prior to its expiration date, the ERC is effective for the life of the applicable user source.

(2)

Effective January 2, 2001, an ERC is available for use for 60 months from the date of the emission reduction except to the extent regulatory changes occur after the date of reduction that reduce the certified amount or invalidate the entire reduction for affected emission points. ERCs certified or applied for prior to January 2, 2001 shall be available for use for 120 months from the date of the emission reduction except to the extent regulatory changes occur after the date of the emission reduction that reduce the certified amount or invalidate the entire reduction for affected emission points.

(e)

Geographic scope. Only emission reductions generated in ozone nonattainment areas can be certified. The trading of emission credits may be discontinued by the executive director in whole or in part and in any manner, with commission approval, as a remedy for problems resulting from trading in a localized area of concern. An emission credit must be used in the nonattainment area in which it is generated unless:

(1)

a demonstration has been made and approved by the executive director to show that the emission reductions achieved in another county, state, or nation provide an improvement to the air quality in the county of use; or

(2)

the emission credit was generated in an ozone nonattainment area which has an equal or higher nonattainment classification than the ozone nonattainment area of use, and a demonstration has been made and approved by the executive director to show that the emissions from the ozone nonattainment area where the emission credit is generated contribute to a violation of the national ambient air quality standard in the ozone nonattainment area of use; or

(3)

the user has obtained prior written approval of the executive director.

(f)

The registry. All emission credit generators and users must register with the executive director. A notice submitted by a generator or user will be posted to the registry. The registry will assign a unique number to each ton of emission reductions generated. The registry will maintain current listings of all credits available or used for each ozone nonattainment area.

(g)

Recordkeeping. The user must maintain a copy of all notices and backup information submitted to the registry during, and for at least two years after, the beginning of the use period. The user must also make such records available upon request to representatives of the executive director, EPA, and any local enforcement agency. The records shall include, but not necessarily be limited to:

(1)

the name, emission point number, and facility identification number of each unit using emission credits;

(2)

the amount of emission credits being used by each unit;

(3)

the specific number, name, or other identification of emission credits used for each unit.

(h)

Public information. All information submitted with a notice or report regarding the nature and quantity of emissions associated with the use or generation of an emission credit is public information and may not be submitted as confidential. Any claim of confidentiality for this type of information, or failure to submit all information, may result in the rejection of the emission reduction. All non-confidential notices and information regarding the generation, use, and availability of emission credits may be obtained from the Office of Permitting, Remediation, and Registration.

(i)

Authorization to emit. An emission credit created under this division is a limited authorization to emit VOC and/or NO x , unless otherwise defined, in accordance with the provisions of this section, the Federal Clean Air Act, and the Texas Clean Air Act, as well as regulations promulgated thereunder. An emission credit does not constitute a property right. Nothing in this division may be construed to limit the authority of the commission or the EPA to terminate or limit such authorization.

(j)

Program participation. The executive director has the authority to prohibit an organization from participating in emission credit trading either as a generator or user, if the executive director determines that the organization has violated the requirements of the program or abused the privileges provided by the program.

§101.303.Protocols.

(a)

All source categories must use an EPA approved protocol if one exists for the applicable source. If the source wants to deviate from an EPA approved protocol, EPA approval is required before the protocol can be used.

(b)

If an EPA approved protocol does not exist, the following applies.

(1)

Emission reduction credits (ERC)--The amount of emission credits in tons per year will be determined and certified based on actual monitoring results, when available, or otherwise calculated using good engineering practices including calculation methodologies in general use in new source review (NSR) permitting. The source must collect relevant data sufficient to characterize the process emissions of the affected pollutant and the process activity level for all representative phases of source operation during the period under which emission credits are created or used.

(2)

Mobile emission reduction credits (MERC)--The amount of emission credits in tons per year will be determined and certified based on actual monitoring results, when available, or otherwise calculated using good engineering practices. The generator must collect relevant data sufficient to characterize the process emissions of the affected pollutant, and the process activity level for all representative phases of mobile source operation during the period under which mobile credits are created.

(c)

Emission credit generation.

(1)

ERCs may be generated using one of the following methods or any other method that is approved by the executive director:

(A)

the permanent shutdown of a facility which causes a loss of capability to produce emissions;

(B)

the installation and operation of pollution control equipment which reduces emissions below the level required of the emission source;

(C)

a change in a manufacturing process which reduces emissions below the level required of the emission source;

(D)

the permanent curtailment in production, which reduces the source's capability to produce emissions;

(E)

pollution prevention projects that produce surplus emission reductions.

(2)

MERCs may be generated by any mobile source emission reduction strategy that creates actual mobile source emission reductions under this rule, and subject to the approval of the commission.

(d)

Emission credit calculation.

(1)

The quantity of ERCs is determined by subtracting the source's new allowable emission limit (tons per year) from the emission source's baseline emissions. The source's new allowable emission limit equals the enforceable emission limit for the applicable emission point after the emission reduction strategy has been implemented.

(2)

The quantity of MERCs must be calculated from the annual difference between the mobile source emissions baseline and the projected emissions level after the MERC strategy has been put in place. The projected emissions must be based on the best estimate of the actual in-use emissions of the replacement or substitute on-road or non-road vehicles or transportation system. Any estimate of a projected annual mobile source emissions level based on an assumption of reduced consumer service or transportation service would not be allowed without the support of a convincing analytical justification of the assumption. Emission baselines for quantifying MERCs should include the following information and data as appropriate, but not be limited to:

(A)

the emission standard to which the mobile source is subject or emission performance to which the mobile source is certified;

(B)

the estimated or measured in-use emissions levels per unit of use from all significant mobile source emissions sources;

(C)

the number of mobile sources in the participating group;

(D)

the type or types of mobile sources by model year;

(E)

the actual or projected activity level, hours of operation or miles traveled by type, and model year; and

(F)

the projected remaining useful life of the participating group of mobile sources.

(3)

Emission credits cannot be generated from a source if the emissions have been transferred from that source to another source.

(e)

Emission credit registration and certification.

(1)

Stationary sources with potential ERCs must submit an ERC application (EC-1 Form), within 180 days of the implementation of the emission reduction strategy to the Office of Permitting, Remediation, and Registration (OPRR). Sources that have implemented a strategy prior to the effective date of this rule, must submit an application by June 1, 2001. Applications will be subjected to a review to determine the credibility of the reductions. Reductions determined to be creditable will be certified by the executive director and an ERC certificate will be issued to the owner.

(2)

Mobile sources with potential MERCs must submit an emission credit application (EC-1 Form), within 180 days of implementation of the strategy to the OPRR if an obligation is exceeded, or if it is clearly demonstrated that actual mobile emission reductions are generated. Sources that have implemented a strategy prior to the effective date of this rule, must submit an application by June 1, 2001. The commission will then issue a MERC certificate(s) to the person, company, business, organization, or public entity generating the mobile emission reduction, upon approval of the application. A MERC certificate will be issued by the executive director which indicates the total amount of certified emission credits, the quantity available on an annual basis, and the date upon which the last annualized emission reduction expires.

(3)

The application for a stationary source generator must include the following information, where applicable for either an ERC or MERC, on the EC-1 Form for each pollutant reduced at each applicable emission point:

(A)

the name, address, county, telephone number, contact person, permit or permit by rule numbers, account number of the generator, and the unique facility identification number and emission point number of the applicable emission points;

(B)

the name of the owner and/or operator of the generator source;

(C)

the date of the reduction;

(D)

a complete description of the generation activity;

(E)

for shutdown or permanent curtailment emission reduction strategies, an explanation as to whether production shifted from the shut down facility to another facility in the same nonattainment area;

(F)

the amount of emission credits generated;

(G)

for volatile organic compound (VOC) reductions, a list of the specific compounds reduced;

(H)

the baseline emission activity, baseline emission rate, baseline total emissions, emissions inventory data from the most recent year of emissions inventory used for state implementation plan determinations and emissions inventory data for the two consecutive years used to determine baseline activity for each applicable pollutant and emission point;

(I)

the most stringent emission rate and the most stringent emission level for the applicable emission point, considering all the local, state, and federal applicable regulatory requirements,

(J)

a complete description of the protocol used to calculate the emission reduction generated;

(K)

the actual calculations performed by the generator to determine the amount of emission credits generated; and

(L)

a statement that the emission reductions on which the emission credits are based are real, surplus, and are based on an eligible emission reduction strategy listed in subsection (c)(1) of this section.

(4)

The application for a mobile source strategy must include the following information, where applicable for either an ERC or MERC, on the EC-1 Form for each pollutant reduced at each applicable mobile source strategy:

(A)

the name, address, county, telephone number, and contact person;

(B)

the name of the owner and/or operator of the generator source;

(C)

the date of the reduction;

(D)

a complete description of the generation activity;

(E)

the amount of emission credits generated;

(F)

the mobile source baseline emission activity, mobile source baseline emission rate, mobile source baseline total emissions, and the mobile source strategy;

(G)

a complete description of the protocol used to calculate the emission reduction generated;

(H)

the actual calculations performed by the generator to determine the amount of emission credits generated; and

(I)

a statement that the emission reductions on which the emission credits are based are real, surplus, and based on an eligible emission reduction strategy that is prohibited.

(5)

The applicant will be notified in writing if the executive director denies the emission credit application. The applicant may submit a revised application at any time.

(f)

Emission credit practices.

(1)

The amount of emission credits in tons per year will be determined and certified, to the nearest tenth of a ton per year.

(2)

ERCs are based on EPA methodologies, when available, actual monitoring results, when available, or otherwise calculated using good engineering practices including calculation methodologies in general use and accepted in NSR permitting. The executive director shall have the authority to inspect and request information to assure that the emissions reductions have actually been achieved.

(3)

MERCs will be determined and certified using:

(A)

EPA methodologies, when available;

(B)

actual monitoring results, when available;

(C)

otherwise calculated using the most current EPA MOBILE model or other model as applicable; or

(D)

otherwise calculated using creditable emission reduction measurement or estimation methodologies which satisfactorily address the analytical uncertainties of mobile source emissions reduction strategies.

(4)

All emission credits are deposited in the registry and reported as available credits by the Emissions Banking and Trading Program until they are used, withdrawn, or expire.

(5)

Compliance burden and enforcement.

(A)

ERCs will be made enforceable by one of the following methods:

(i)

amending or altering an NSR permit to reflect the emission reduction and set a new maximum allowable emission limit;

(ii)

voiding an NSR permit when an emission source has been shut down;

(iii)

registering on a PI-8 form the emission reduction and the new maximum allowable emission limit for any facility which is authorized by a standard exemption or permit by rule;

(iv)

registering on an OPCRE-1 Form the emission reduction and the new maximum allowable emission limit for any facility which is not required to have a permit or qualifies for a permit by rule; or

(v)

obtaining an agreed order which sets a new maximum allowable emission limit for a facility which is not required to have a permit or qualify for a permit by rule.

(B)

MERCs will be made enforceable by one of the following methods:

(i)

by registering, on a commission-provided form (MERC-1), that the MERCs are permanent, quantifiable, real, and surplus; or

(ii)

by obtaining an agreed order which sets a new maximum allowable mobile source emission limits, which is not required to be implemented by a rule.

(6)

Unless there are permits under the same commission account number which contain a condition or conditions precluding such use, ERCs may be used as the following:

(A)

offsets for a new source or major modification to an existing source;

(B)

mitigation offsets for action by federal agencies under §101.30 of this title (relating to Conformity of General Federal Actions to State Implementation Plans);

(C)

an alternative means of compliance with VOC and NOx reduction requirements as provided in Chapter 115 of this title (relating to the Control of Air Pollution from volatile organic compounds (VOCs)) and Chapter 117 of this title (relating to the Control of Air Pollution from Nitrogen Compounds);

(D)

netting by the original applicant, if not used, sold, or otherwise relied upon; or

(E)

other provisions as allowable within the guidelines of local, state, and federal laws.

(7)

MERCs may only be used for the following purposes:

(A)

an alternative means of compliance with VOC and NOx reduction requirements as provided in Chapters 115 and 117 of this title;

(B)

complying with fleet requirements to the extent allowed by the Texas Clean Fleet Program requirements for motor vehicle fleets;

(C)

providing offsets for a new major source or major modifications;

(D)

mitigation offsets for action by federal agencies under §101.30 of this title; or

(E)

other provisions as allowable within the guidelines of local, state, and federal laws.

(8)

The calculation of the number of ERCs of MERCs needed by the user for offsets or for compliance with Chapter 115 or Chapter 117 of this title are as follows:

(A)

for emission credits used as offsets, the method for determining the number of emission credits needed by the user for offsets is provided in §116.150 of this title (relating to New Major Source or Major Modification in Ozone Nonattainment Area); or

(B)

for emission credits used as compliance with Chapter 114, Chapter 115, or Chapter 117 of this title, the number of emission credits needed should be determined in accordance with the requirements of this section plus an additional 10% to be retired as an environmental contribution; or

(C)

for emission credits used to comply with §117.210 of this title (relating to Source Cap) and §117.223 of this title (relating to Source Cap), sources may reduce the amount of emission reductions otherwise required by complying with the following equations instead of the equations in §117.210(c)(1) and (2) and §117.223(b)(1) and (2) of this title.

Figure: 30 TAC §101.303(f)(8)(C)

(D)

emission reductions used as compliance with any other applicable program should be determined in accordance with the requirements of the appropriate chapter and section and must contain at least 10% extra to be retired as an environmental contribution.

(9)

Review schedule.

(A)

For emission credits which are to be used for compliance with the requirements of Chapter 114, Chapter 115, or Chapter 117 of this title, the user must submit a Notice of Intent to Use, (EC-3 Form) at least 90 days prior to the planned utilization of the emission credit. Emission credits may be utilized only after the executive director grants approval of the notice of intent to use.

(B)

For emission credits which are to be used as offsets in accordance with Chapter 116 of this title, the user must submit a Notice of Intent To Use Form (EC-3 Form), along with the emission credit certificate when providing the emission credits as offsets.

(10)

Emission credits are freely transferable in whole or in part, and may be traded or sold to a new owner any time before the expiration date of the emission credit. The Emissions Banking and Trading Program must be notified by means of an EC-4 Form prior to the transfer. The old certificate must be submitted to the registry. The executive director will issue a new certificate to the emission credit purchaser reflecting the emission credits purchased by the new owner, and a revised certificate to the emission credit seller showing any remaining emission credits available to the original owner. Emission credits may be transferrable only after the executive director grants approval of the transaction.

(11)

Emission credits may be withdrawn from the registry by the owner at any time prior to the expiration date of the credit and may be held by the owner. Emission credits may still be used by the original owner as an emission reduction for netting purposes after the emission credits have expired, as provided in §116.150 of this title.

(12)

Recording use of emission credits.

(A)

Emission credits to be used as offsets in an NSR permit must be identified prior to permit issuance. The original certificate must be submitted prior to operation.

(B)

Use of emission credits for purposes other than those specified in subparagraph (A) of this paragraph may not commence until the user has received approval from the executive director. The user must also keep a copy of the emission credit certificate, the notice, and all backup in accordance with §101.303(e) of this section.

(C)

If the executive director denies the stationary source's use of emission credits, any person affected by the executive director's decision may file a motion for reconsideration within 60 days of the denial. Notwithstanding the applicability provisions of §50.31(c)(7) of this title (relating to Purpose and Applicability), the requirements of §50.39 of this title (relating to Motion for Reconsideration) may apply. Only a person affected may file a motion for reconsideration.

§101.304.Program Audits.

(a)

No later than three years after the effective date of this division, and every three years thereafter, the executive director will audit this program.

(b)

The audit will evaluate the timing of credit generation and use, the impact of the program on the state's attainment demonstration and the emissions of hazardous air pollutants, the availability and cost of credits, compliance by the participants, and any other elements the executive director may choose to include.

(c)

The executive director will recommend measures to remedy any problems identified in the audit. The trading of emission credits may be discontinued by the executive director in part or in whole and in any manner, with commission approval, as a remedy for problems identified in the program audit.

(d)

The audit data and results will be completed and submitted to the EPA and made available for public inspection within six months of the date the audit begins.

This agency hereby certifies that the proposal has been reviewed by legal counsel and found to be within the agency's legal authority to adopt.

Filed with the Office of the Secretary of State, on August 11, 2000.

TRD-200005654

Margaret Hoffman

Director, Environmental Law Division

Texas Natural Resource Conservation Commission

Earliest possible date of adoption: September 24, 2000

For further information, please call: (512) 239-1966


3. MASS EMISSIONS CAP AND TRADE PROGRAM

30 TAC §§101.350-101.354, 101.356, 101.358-101.360

STATUTORY AUTHORITY

The new sections are proposed under the Texas Health and Safety Code, TCAA, §382.011, which authorizes the commission to control the quality of the state's air; §382.012, which authorizes the commission to develop a plan for control of the state's air; §382.017, which provides the commission the authority to adopt rules consistent with the policy and purposes of the TCAA, and United States Code, §7410(a)(2)(A), which requires SIPs to include enforceable emission limitations and other control measures or techniques, including economic incentives such as fees, marketable permits, and auction of emission rights.

The proposed new sections implement TCAA, §382.011, General Powers and Duties; §382.012, State Air Control Plan; and §382.017, Rules.

§101.350.Definitions.

The following words and terms, when used in this division, shall have the following meanings, unless the context clearly indicates otherwise.

(1)

Allowance - The authorization to emit one ton of nitrogen oxides (NO x ) during a control period.

(2)

Authorized account representative - The responsible person who is authorized, in writing, to transfer and otherwise manage allowances.

(3)

Banked allowance - An allowance which is not used to reconcile emissions in the designated year of allocation, but which is carried forward for up to one year and noted in the compliance or broker account as "banked."

(4)

Broker - A person not required to participate in the requirements of this division who opens an account under this division for the purpose of banking and trading allowances.

(5)

Broker account - The account where allowances held by a broker are recorded. Allowances held in a broker account may not be used to satisfy compliance requirements for this division.

(6)

Compliance account - The account where allowances held by a source or multiple sources are recorded for the purposes of meeting the requirements of this division. Sources not under common ownership or control may have separate compliance accounts.

(7)

Control period - The 12-month period beginning January 1 and ending December 31 of each year. The initial control period begins January 1, 2002.

(8)

Houston/Galveston (HGA) ozone nonattainment area - As defined in §101.1 of this title (relating to Definitions).

(9)

Level of activity - The amount of activity at a source measured in terms of production, fuel use, raw materials input, or other similar units that have a direct correlation with the economic output and emission rate of the source (i.e., mass emitted per unit of activity).

(10)

Person - For the purpose of issuance of allowances under this division, a person includes an individual, a partnership of two or more persons having a joint or common interest, a mutual or cooperative association, and a corporation.

(11)

Source - As defined in §101.1 of this title.

§101.351.Applicability.

This division applies to all stationary nitrogen oxides (NO x ) sources in the Houston/Galveston nonattainment area subject to the emission specifications under §§117.106, 117.206, and 117.475 of this title (relating to Emission Specifications for Attainment Demonstration; Emission Specifications for Attainment Demonstration; and Emission Specifications) and which have a design capacity to emit ten tons or more per year of NOx .

§101.352.General Provisions.

(a)

Allowances are valid only for the purposes described in this division and cannot be used to meet or exceed the limitations of any annual emission limitation authorized under Chapter 116, Subchapter B, of this title (relating to New Source Review Permits), or any other applicable rule or law.

(b)

Beginning February 1, 2003, and no later than February 1 following the end of every control period, each account, as defined in §101.1(1) of this title (relating to Definitions), shall hold a quantity of allowances in its compliance account that is equal to or greater than the total emissions of nitrogen oxides emitted during the control period just ending. Compliance with the allowance system will begin with the initial control period beginning January 1, 2002.

(c)

Unused allowances can be certified as emission reduction credits, provided that:

(1)

an enforceable and permanent reduction of annual allowances is approved by the executive director; and

(2)

all applicable requirements of Division 1 of this subchapter (relating to Emission Credit Banking and Trading) are met.

(d)

Allowances cannot be used for netting requirements to avoid the applicability of federal and state new source review (NSR) requirements.

(e)

Allowances may simultaneously be used to satisfy offset requirements for new or modified sources subject to federal nonattainment NSR requirements as provided in Chapter 116, Subchapter B, Division 7 of this title (relating to Emission Reductions Offsets).

(f)

An allowance does not constitute a security or a property right.

(g)

All allowances will be allocated, transferred, or used as whole allowances. To determine the number of whole allowances, the number of allowances will be rounded down when determining excess allowances and rounded up when determining allowances used.

(h)

One compliance account shall be used for multiple sources required to participate under this division and located at the same property and under common ownership or control.

(i)

The commission will maintain a registry of the allowances in each compliance account. The registry will not contain proprietary information.

§101.353.Allocation of Allowances.

(a)

Allowances will be allocated according to the requirements of this section.

(1)

For the 2002 control period in the Houston/Galveston (HGA) nonattainment area:

(A)

for sources operating prior to January 1, 1997, allowances will be equal to the source's actual level of activity averaged over 1997, 1998, and 1999 multiplied by the higher of the source's actual emission factor averaged over 1997, 1998, and 1999 (not to exceed any applicable regulatory or permit limit) or the source's emission factor listed in Chapter 117 of this title (relating to Control of Air Pollution from Nitrogen Compounds);

(B)

for sources not operating prior to January 1, 1997, but operating prior to January 1, 2000, allowances will be equal to the source's actual level of activity averaged over the most recent two consecutive calendar years multiplied by the higher of the source's actual emission factor averaged over the most recent two consecutive calendar years (not to exceed any applicable regulatory or permit limit) or the source's emission factor listed in Chapter 117 of this title.

(C)

for sources that have submitted an administratively complete application under Chapter 116 of this title (relating to Control of Air Pollution by Permits for New Construction or Modification) and for sources that qualify for a permit by rule under Chapter 106 of this title (relating to Permits by Rule), but not operating prior to January 1, 2000, allowances will be equal to the source's authorized level of activity multiplied by the source's authorized emission factor.

(2)

For the 2003 control period:

(A)

for sources with allowances allocated in accordance with paragraph (1)(A) and (B) of this subsection the number of allocations shall be two-thirds of the sum of the number of allocations derived in paragraphs (1) and (4) of this subsection;

(B)

for sources with allowances allocated in accordance with paragraph (1)(C) of this subsection, the number of allocations shall be determined according to the following:

(i)

for sources operating prior to January 1, 2001, allowances will be equal to the source's actual level of activity averaged over the most recent two consecutive calendar years multiplied by two-thirds of the sum of the higher of the source's actual emission factor averaged over the most recent two consecutive calendar years (not to exceed any applicable regulatory or permit limit) or the source's emission factor listed in Chapter 117 of this title and the source's emission factor listed in Chapter 117 of this title;

(ii)

for sources not operating prior to January 1, 2001, allowances will be equal to the source's authorized level of activity multiplied by two-thirds of the sum of the higher of the source's authorized emission factor or the source's emission factor listed in Chapter 117 and the source's authorized emission factor and the source's emission factor listed in Chapter 117.

(3)

For the 2004 control period:

(A)

for sources with allowances allocated in accordance with paragraph (1)(A) and (B) of this subsection, the number of allocations shall be one-third of the sum of the number of allocations derived in paragraphs (1) and (4) of this subsection.

(B)

for sources with allowances allocated in accordance with paragraph (1)(C) of this subsection, the number of allocations shall be determined according to the following:

(i)

for sources operating prior to January 1, 2002, allowances will be equal to the source's actual level of activity averaged over the most recent two consecutive calendar years multiplied by one-third of the sum of the higher of the source's actual emission factor averaged over the most recent two consecutive calendar years (not to exceed any applicable regulatory or permit limit) or the source's emission factor listed in Chapter 117 of this title and the source's emission factor listed in Chapter 117 of this title;

(ii)

for sources not operating prior to January 1, 2002, allowances will be equal to the source's authorized level of activity multiplied by one-third of the sum of the higher of the source's authorized emission factor or the source's emission factor listed in Chapter 117 of this title and the source's authorized emission factor and the source's emission factor listed in Chapter 117 of this title.

(4)

For the 2005 and subsequent control periods allowances will be calculated for each source using the following equation.

Figure: 30 TAC §101.353(a)(4)

(5)

For sources submitting applications for permits or qualifying for a permit by rule after January 2, 2001, allowances for each control period or the annual allocation rights shall be acquired from sources already participating under this division, or in accordance with §101.356(d) of this title (relating to Allowance Banking and Trading).

(6)

If actual emissions of NO x during a control period exceed the amount of allowances held in a compliance account no later than January 31 following the control period, allowances for the next control period will be reduced by an amount equal to the emissions exceeding the allowances in the compliance account plus an additional 10%.

(b)

Allowances will be allocated:

(1)

initially, by January 1, 2002;

(2)

subsequently, by January 1 of each following year by the executive director, who will deposit allowances into each compliance account.

(c)

The annual deposit for any control period may be adjusted to reflect new state implementation plan requirements.

(d)

Allowances may be added or deducted from compliance accounts following the review of trading reports required under §101.356 of this title.

(e)

In extenuating circumstances, the executive director may deviate from the requirements of this section to determine the amount of allowances to be allocated to a source.

§101.354.Allowance Deductions.

(a)

Allowances will be deducted in whole tons from a source's compliance account for a control period based upon the following equation.

Figure: 30 TAC §101.354(a)

(b)

On February 1 after every control period, a source shall hold a quantity of allowances in its compliance account that is equal to or greater than the total NO x emissions emitted during the prior control period.

§101.356.Allowance Banking and Trading.

(a)

Allowances not used for compliance during a control period may be banked for use in the following control period or traded except as provided in subsection (b) of this section.

(b)

Allowances not used for compliance during a control period which were allocated in accordance with §101.353(a)(1)(C) of this title (relating to Allocation of Allowances) may not be banked for future use or traded.

(c)

Allowances which have not expired may be traded at any time after they have been allocated.

(1)

Only authorized account representatives may trade allowances.

(2)

Trades shall be completed by the executive director following the submittal of a completed ECT-2 Form, Application for Transfer of Allowances. The completed ECT-2 shall include the price paid per allowance. The executive director will issue a letter to the purchaser and seller reflecting this trade. The trade will be considered finalized upon issuance of this letter.

(d)

Sources may use nitrogen oxides discrete emission credits (DERCs or MDERCs) which have been generated, acquired, and used in accordance with Division 4 of this subchapter (relating to Discrete Emission Credit Banking and Trading) in place of allowances for compliance with this division.

§101.358.Emission Monitoring and Compliance Demonstration.

(a)

Monitoring data or other emission quantifications for sources required to monitor or quantify emissions under any other federal or state program shall be used to show compliance with this division.

(b)

Sources not required to monitor or quantify nitrogen oxides emissions shall calculate emissions using good engineering practices, including calculation methodologies in general use and accepted in new source review permitting.

§101.359.Reporting.

Beginning March 31, 2003, for each control period, sources under each compliance account shall submit a completed ECT-1 Form, Annual Compliance Report, to the executive director by March 31 of each year detailing the following:

(1)

the amount of actual nitrogen oxides (NO x )emissions during the preceding control period;

(2)

the method of determining NO x emissions, including, but not limited to, any monitoring protocol and results, calculation methodology, level of activity, and emission factor; and

(3)

a summary of all final trades for the preceding control period.

§101.360.Level of Activity Certification.

No later than June 30, 2001, the owner or operator of any source subject to this division shall certify its historical level of activity by submitting to the executive director a completed ECT-3 Form, Level of Activity Certification, along with any supporting information such as usage records, testing or monitoring data, and production records.

This agency hereby certifies that the proposal has been reviewed by legal counsel and found to be within the agency's legal authority to adopt.

Filed with the Office of the Secretary of State, on August 11, 2000.

TRD-200005655

Margaret Hoffman

Director, Environmental Law Division

Texas Natural Resource Conservation Commission

Earliest possible date of adoption: September 24, 2000

For further information, please call: (512) 239-1966


4. DISCRETE EMISSION CREDIT BANKING AND TRADING

30 TAC §§101.370-101.374

STATUTORY AUTHORITY

The new sections are proposed under the Texas Health and Safety Code, TCAA, §382.011, which authorizes the commission to control the quality of the state's air; §382.012, which authorizes the commission to develop a plan for control of the state's air; §382.017, which provides the commission the authority to adopt rules consistent with the policy and purposes of the TCAA, and United States Code, §7410(a)(2)(A), which requires SIPs to include enforceable emission limitations and other control measures or techniques, including economic incentives such as fees, marketable permits, and auction of emission rights.

The proposed new sections implement TCAA, §382.011, General Powers and Duties; §382.012, State Air Control Plan; and §382.017, Rules.

§101.370.Definitions.

The following words and terms, when used in this division, shall have the following meanings, unless the context clearly indicates otherwise.

(1)

Activity--The amount of activity at a source measured in terms of production, use, raw materials input, vehicle miles traveled, or other similar units that have a direct correlation with the economic output and emission rate of the source (i.e., mass emitted per unit of activity).

(2)

Actual emissions--Shall equal the total emissions during the selected time period, using the unit's actual daily operating hours, production rates, and types of materials processed, stored, or combusted during the selected time period.

(3)

Applicable emission point--The emission point that is either generating an emission reduction or using a discrete emission credit.

(4)

Area source--Any source included in the agency emissions inventory under the area source category.

(5)

Baseline--Emissions that occur prior to an emission reduction strategy, considering all limitations required by applicable state and federal regulations. The baseline may not exceed the most recent level of emissions reported in the emissions inventory used for state implementation plan (SIP) determinations. For reduction strategies that exceed 12 months, the baseline is established after the first year of generation and is fixed for the life of the strategy. A new baseline is established for each emission reduction strategy.

(6)

Baseline activity--The source's actual level of activity based on the unit's actual daily operating hours, production rates, or types of materials processed, stored, or combusted averaged over any consecutive two calendar year period including and following the most recent year of emissions inventory used for SIP determinations or subsequent year(s) which precede the emission reduction strategy or credit use period. For sources in existence less than two years, a shorter time period not less than 12 months may be considered by the executive director.

(7)

Baseline emission rate--The source's rate of emissions per unit of activity during the baseline activity period.

(8)

Baseline emissions--The source's total actual emissions based on the baseline activity and baseline emission rate.

(9)

Certified--Any emission reduction that is determined to be creditable upon review and approval by the executive director.

(10)

Curtailment--A temporary or partial reduction in activity level at any facility or mobile source.

(11)

Discrete emission credit--An emission reduction generated over a discrete period of time, and measured in tons. A creditable emission credit such as a discrete emission reduction credit (DERC) or mobile discrete emission reduction credit (MDERC).

(12)

Discrete emission reduction credit (DERC)--A creditable emission reduction which is created during a generation period, quantified after the period in which emissions reductions are made, and expressed in tons.

(13)

Emission reduction--An actual reduction of emissions from a stationary or mobile source.

(14)

Emission reduction strategy--The method implemented to reduce the source's emissions beyond that required by state or federal law, regulation, or agreed order.

(15)

Generation period--The discrete period of time, not exceeding 12 months, over which a DERC is created.

(16)

Generator--The owner or operator of a source that creates an emission reduction.

(17)

Mobile discrete emission reduction credit (MDERC or discrete mobile credit)--A credit that is surplus, generated by a mobile source strategy. It is a creditable emission reduction that is created during a generation period, quantified after the period in which emissions reductions are made, and expressed in tons.

(18)

Mobile emissions baseline--Mobile emissions that occur prior to a mobile emission reduction strategy, considering all limitations required by applicable state and federal regulations. A valid mobile emission baseline can be calculated by either using measured emissions of an appropriately sized sample of the participating mobile sources using an approved EPA test procedure or by using estimated emissions of the participating mobile sources using the most recent edition of EPA's on-road or non-road mobile emissions factor models, or other model as applicable. To ensure that mobile credits are surplus, mobile source baseline emissions estimates for each year of the proposed mobile source control program must be the same as, or lower than, those used, or proposed to be used, in the SIP in which the control program is proposed.

(19)

Mobile source--On-road (highway) vehicles (e.g., automobiles, trucks, and motorcycles) and non-road vehicles (e.g., trains, airplanes, agricultural equipments, industrial equipment, construction vehicles, off-road motorcycles, and marine vessels).

(20)

Mobile source baseline activity--The mobile source's level of activity during the applicable mobile source baseline year.

(21)

Mobile source baseline emissions--The mobile source's total emissions based on the product of mobile source baseline activity and mobile source baseline emission rate.

(22)

Most stringent allowable emissions rate--The emissions rate of a source, considering all limitations required by applicable local, state, and federal regulations.

(23)

Ozone season--The portion of the year when ozone monitoring is federally required to occur in a specific geographic area.

(24)

Permanent--An emission reduction that is long-lasting and unchanging for the remaining life of the source.

(25)

Protocol--A replicable and workable method of estimating emission rates or activity levels used to calculate the amount of emission reduction generated or credits required for stationary or mobile sources.

(26)

Quantifiable--An emission reduction that can be measured or estimated with confidence using replicable techniques.

(27)

Real reduction--A reduction in which actual emissions are reduced.

(28)

Source--As defined in §101.1 of this title (relating to Definitions).

(29)

Shutdown--The permanent cessation of an activity producing emissions at a facility.

(30)

Strategy activity--The source's level of activity during the DERC generation period.

(31)

Strategy emission rate--The source's level of activity during the DERC generation period.

(32)

Surplus--An emission reduction that is not otherwise required of a source by a state or federal law, regulation, or agreed order.

(33)

Use period--The period of time over which the user source applies discrete emission credits to an applicable emission reduction requirement.

(34)

User--The owner or operator of a source that acquires and uses discrete emission credits to meet a regulatory requirement, demonstrate compliance, or offset an emission increase.

(35)

Use strategy--The compliance requirement for which discrete emission credits are being used.

§101.371.Purpose.

The purpose of this division is to allow the operator of a source to generate discrete emission credits by reducing emissions beyond the level required by any local, state, and federal regulation, and to allow the operator of another source to use these credits. Participation under this division is strictly voluntary.

§101.372.General Provisions.

(a)

Applicable pollutants. Reductions of volatile organic compounds (VOCs), nitrogen oxides (NO x ), carbon (CO), sulfur dioxide (SO 2 ), and particulates with an aerodynamic diameter of less than or equal to a nominal ten microns (PM 10 ) may qualify as discrete emission credits as appropriate. Reductions of other criteria pollutants are not creditable. Reductions of one pollutant may not be used to meet the reduction requirements for another pollutant, except at such time as modeling demonstrates that one may be substituted for another or as approved by the executive director.

(b)

Discrete emission credit requirements.

(1)

Discrete emission reduction credit (DERC)--To be creditable as a DERC, an emission reduction must be real, quantifiable, and surplus at the time the discrete emission credit is generated. The creditable reduction must have occurred after the most recent year of emissions inventory used for state implementation plan (SIP) determinations for all applicable pollutants and the source's annual emissions prior to the discrete emission credit application must have been reported or represented in the emissions inventory used for SIP determinations.

(2)

Mobile discrete emission reduction credit (MDERC)--To be creditable as an MDERC, an emission reduction must be quantifiable, real, and surplus. The discrete emission credit must be surplus at the time it is created, as well as when it is used. The creditable reduction must have occurred after the most recent year of emissions inventory used for SIP determinations for all applicable pollutants, the mobile source's emissions must have been represented in the emissions inventory used for SIP determinations, and the mobile sources are in the attainment demonstration baseline. If a mobile reduction is implemented that is not in the baseline for emissions, this would not constitute an emission reduction.

(3)

Emission reductions from a source which are certified as discrete emission credits under this division cannot be recertified in whole or in part as emission credits under another division within this subchapter.

(c)

Eligible sources include the following:

(1)

stationary sources (including area sources);

(2)

mobile sources; or

(3)

any stationary source (including area sources) associated with actions by federal agencies under §101.30 of this title (relating to Conformity of General Federal Actions to State Implementation Plans).

(d)

Life of a discrete emission credit. A discrete emission credit is available for use after the notice of generation, DC-1 Form, has been received and deemed creditable by the commission registry in accordance with subsection (h) of this section, and may be used anytime thereafter.

(e)

Geographic scope. Emission reductions generated in the State of Texas may be creditable and used in the state with the following limitations.

(1)

VOC and NO x discrete emission credits generated in an ozone attainment area may be used in any county or portion of a county designated as attainment or unclassified, but may not be used in an ozone nonattainment area.

(2)

VOC and NO x discrete emission credits generated in an ozone nonattainment area may be used either in the same ozone nonattainment area in which they were generated, or in any county or portion of a county designated as attainment or unclassified.

(3)

VOC and NO x discrete emission credits generated in an ozone nonattainment area may not be used in any other ozone nonattainment area, except as provided in this subsection.

(4)

CO, SO 2 , and PM 10 discrete emission credits must be used in the same metropolitan statistical area in which the reduction was generated.

(5)

VOC and NO x discrete emission credits generated in other counties, states, or nations can be used in any attainment or nonattainment county provided a demonstration has been made and approved by the executive director to show that the emission reductions achieved in the other county, state, or nation improves the air quality in the county where the credit is being used.

(f)

Trading discontinuation. The trading of discrete emission credits may be discontinued by the executive director in whole or in part and in any manner, with commission approval, as a remedy for problems resulting from trading in a localized area of concern.

(g)

Ozone season. In areas having an ozone season of less than 12 months, VOC and NO x discrete emission credits generated outside the ozone season may not be used during the ozone season.

(h)

The registry. All required notices of discrete emission credit generators and users must be submitted to the registry. A notice submitted by a generator or user will be reviewed for credibility and when deemed certified, posted to the registry. The registry will assign a unique number to each ton of emission reductions generated. The registry will maintain current listings of all credits available or used for each ozone nonattainment area. One combined listing for all the counties or portions of counties designated as attainment or unclassified will be provided by the registry.

(i)

Recordkeeping. The generator must maintain a copy of all notices and backup information submitted to the registry for a minimum of five years, following the completion of the generation period. The user must maintain a copy of all notices and backup information submitted to the registry for a minimum of five years, following the completion of the use period. Other relevant reference material or raw data must also be maintained on-site by the participating sources. The user must also maintain a copy of the generator's notice and backup information for a minimum of five years after the use is completed. The records shall include, but not necessarily be limited to:

(1)

the name, emission point number (EPN), and facility identification number (FIN) of each unit using discrete emission credits;

(2)

the amount of discrete emission credits being used by each unit;

(3)

the specific number, name, or other identification of discrete emission credits used for each unit.

(j)

Public information. All information submitted with a notice or report regarding the nature and quantity of emissions associated with the use or generation of discrete emission credits is public information and may not be submitted as confidential. Any claim of confidentiality for this type of material or failure to submit all information may result in the rejection of the emission reduction. All non-confidential notices and information regarding the generation, use, and availability of discrete emission credits may be obtained from the registry.

(k)

Authorization to emit. A discrete emission credit created under this division is a limited authorization to emit the specified pollutants in accordance with the provisions of this section, the Federal Clean Air Act, and the Texas Clean Air Act, as well as regulations promulgated thereunder. A discrete emission credit does not constitute a property right. Nothing in this division should be construed to limit the authority of the commission or the United States Environmental Protection Agency to terminate or limit such authorization.

(l)

Program participation. The executive director has the authority to prohibit a company from participating in discrete emission credit trading either as a generator or user, if the executive director determines that the company has violated the requirements of the program or abused the privileges provided by the program.

§101.373.Protocols.

(a)

All discrete emission credit source categories must use an EPA approved protocol if one exists for the applicable source. If the source wants to deviate from an EPA approved protocol, EPA approval is required before the protocol can be used.

(b)

If an EPA approved protocol does not exist, the amount of discrete emission credits in tons will be determined and certified based on actual monitoring results, when available, or otherwise calculated using good engineering practices, including calculation methodologies in general use in new source review (NSR) permitting. The source must collect relevant data sufficient to characterize the process emissions of the affected pollutant and the process activity level for all representative phases of source operation during the period under which discrete emission credits are created or used.

(c)

Discrete emission credit generation.

(1)

Discrete emission reduction credits (DERCs) may be generated by any strategy that reduces a source's emission rate below its baseline and is approved by the executive director, except for the following:

(A)

temporary curtailment of an activity at a source;

(B)

modification or discontinuation of any activity that is otherwise in violation of a federal, state, or local law;

(C)

emissions reductions required to comply with any provision under Title I of the Federal Clean Air Act (FCAA) regarding tropospheric ozone, or Title IV of the FCAA regarding acid rain;

(D)

emission reductions of hazardous air pollutants, as defined in the FCAA, §112, from application of a standard promulgated under FCAA, §112;

(E)

emission reductions which have occurred as a result of transferring the emissions to another source;

(F)

emission reductions credited or used under any other emissions trading program;

(G)

emission reductions occurring at a source which received an alternative emission limitation to meet a state reasonably available control technology requirement, except to the extent that the emissions are reduced below the level that would have been required had the alternative emission limitation not been issued; and

(H)

emission reductions at a facility with a flexible permit, unless the reductions are made permanent and enforceable or the generator can demonstrate that the emission reductions were not used to satisfy the conditions for the facilities under the flexible permit.

(2)

A mobile discrete emission reduction credit (MDERC) may be generated by any mobile source emission reduction strategy that creates actual mobile source emission reductions under this rule, and is subject to the approval of the commission.

(d)

Discrete emission credits generation calculation.

(1)

DERCs, except for shutdowns, are calculated as follows.

Figure: 30 TAC §101.373(d)(1)

(A)

The amount of DERCs generated must be rounded down to the nearest ton.

(B)

For shutdown emission reduction strategies, the quantity of emission reduction generated is equivalent to the baseline emissions.

(C)

The generation period for a shutdown is five years. Shutdown DERCs must be generated and noticed to the registry on an annual basis.

(D)

If a source's emissions exceed its allowable emission limit, the amount of emissions exceeding the limit may not be certified as DERCs.

(2)

An MDERC may be calculated from the annual difference between the mobile source emissions baseline and the actual emissions level after the MDERC strategy has been put in place. The MDERC must be based on actual in-use emissions of the replacement or substitute mobile source. Emission baselines for quantifying MDERCs should include the following information and data as appropriate, but not be limited to:

(A)

the emission standard to which the mobile source is subject or emission performance to which the mobile source is certified;

(B)

the measured in-use emissions levels per unit of use from all significant mobile source emissions sources;

(C)

the number of mobile sources in the participating group;

(D)

the type or types of mobile sources by model year; and

(E)

the actual activity level, hours of operation or miles traveled by type, and model year.

(e)

Registration and certification.

(1)

A notice of generation and generator certification (DEC-1 Form), must be submitted to the Office of Permitting, Remediation, and Registration (OPRR) no later than 90 days after the discrete emission reduction strategy activity has been completed, or no later than 90 days after the completion of the first 12 months of generation, if the generation period exceeds 12 months, whichever is sooner. Submission of the DEC-1 Form should continue every 12 months thereafter for each subsequent year of generation.

(2)

In the notice for a stationary source, including area source, the generator must include the following information for each pollutant reduced at each applicable emission point:

(A)

the name, address, county, telephone number, contact person, permit or standard exemption numbers, account number of the generator, and the unique facility identification number (FIN) and emission point number (EPN) of the applicable emission points;

(B)

the name of the owner and/or operator of the generator source;

(C)

the generation period;

(D)

a complete description of the generation activity;

(E)

for shutdown emission reduction strategies, an explanation as to whether production shifted from the shut down facility to another facility in the same nonattainment area;

(F)

the amount of emission credits generated;

(G)

for volatile organic compound (VOC) reductions, a list of the specific compounds reduced;

(H)

the baseline emission activity, baseline emission rate, emission reduction strategy emission rate, emission reduction strategy activity, emissions inventory data from the most recent year of emissions inventory used for state implementation plan determinations and emissions inventory data for the two consecutive years used to determine the baseline activity for each applicable pollutant and emission point;

(I)

the most stringent emission rate for the applicable emission point, considering all the local, state, and federal applicable regulatory requirements;

(J)

a complete description of the protocol used to calculate the emission reduction generated;

(K)

the actual calculations performed by the generator to determine the amount of discrete emission credits generated; and

(L)

a statement that the emission reductions on which the emission credits DERCs are based are real, surplus, and not based on an emission reduction strategy that is prohibited.

(3)

The notice for a mobile source generator must include the following information to verify the credit calculation, but is not limited to:

(A)

the name, address, county, telephone number, and contact person;

(B)

the name of the owner and/or operator of the generator source;

(C)

the date of the reduction;

(D)

a complete description of the generation activity;

(E)

the amount of discrete mobile source emission credits generated;

(F)

the mobile source baseline emission activity, mobile source baseline emission rate, mobile source baseline total emissions, and the mobile source strategy;

(G)

a complete description of the protocol used to calculate the discrete mobile source emission reduction generated;

(H)

the actual calculations performed by the generator to determine the amount of discrete mobile source emission credits generated; and

(I)

a statement that the discrete mobile source emission reductions on which the MDERCs are based are real, surplus, and not based on a mobile source emission reduction strategy that is prohibited.

(4)

Registrations will be reviewed in order to determine the credibility of the reductions. Reductions determined to be creditable will be certified by the executive director.

(5)

The applicant will be notified in writing if the executive director denies the notification. The applicant may submit a revised notification at any time.

(f)

Discrete emission credit practices.

(1)

The amount of DERCs, in tons, will be determined and certified based on actual monitoring results, when available, or otherwise calculated using good engineering practices, including calculation methodologies in general use in NSR permitting. The source must collect relevant data sufficient to characterize the process emissions of the affected pollutant and the process activity level for all representative phases of source operation during the period under which DERCs are created or used.

(2)

The amount of MDERCs will be quantified in tons. MDERCs will be determined and certified based on: EPA methodologies, when available; actual monitoring results, when available; otherwise calculated using the most current EPA MOBILE model; or otherwise calculated using creditable emission reduction measurement or estimation methodologies which satisfactorily address the analytical uncertainties of mobile source emissions reduction strategies. The generator must collect relevant data sufficient to characterize the process emissions of the affected pollutant and the process activity level for all representative phases of source operation during the period under which the MDERCs are created or used.

(3)

All discrete emission credits are deposited in the registry and reported as available credits until they are used, withdrawn, or expire.

(4)

Compliance burden and enforcement.

(A)

The generator is responsible for assuring that the discrete emission credits generated are certified.

(B)

The user is responsible for ensuring that discrete emission credits which currently reside in the registry and are not certified are certified prior to use.

(5)

Discrete emission credits may be used if the following requirements are met.

(A)

The user must have ownership of a sufficient amount of discrete emission credits before the use period for which the specific discrete emission credits are to be used.

(B)

The user must hold sufficient discrete emission credits to cover the user's compliance obligation at all times.

(C)

The user shall acquire additional discrete emission credits during the use period if the user determines that he does not possess enough discrete emission credits to cover the entire use period. The user must acquire additional credits as allowed under this section prior to the shortfall, or the user will be in violation of this section.

(D)

Source operators may acquire and use only discrete emission credits listed on the registry.

(6)

With the exception of uses prohibited in paragraph (7) of this subsection or strictly prohibited in other rules or regulatiuons, discrete emission credits may be used to meet or demonstrate compliance with any mobile or stationary regulatory requirement including the following:

(A)

to exceed any allowable emission level, if the following conditions are met:

(i)

in ozone nonattainment areas, permitted facilities may use discrete emission credits to exceed permit allowables by no more than 25 tons for nitrogen oxides (NO x ) or five tons for VOC in a 12-month period as approved by the executive director. This use is limited to one exceedance up to 12 months, within any 24-month period per use strategy. The use must extend beyond a 24-hour period; or

(ii)

at permitted facilities in counties or portions of counties designated as attainment or unclassified, discrete emission credits may be used to exceed permit allowables by values not to exceed the prevention of significant deterioration significance levels as provided in 40 Code of Federal Regulations, §52.21(b)(23), as approved by the executive director prior to use. This use is limited to one exceedance up to 12 months, within any 24-month period per use strategy. The user must demonstrate that there will be no adverse impacts from the use of discrete emission credits at the levels requested;

(B)

as NSR offsets if the following requirements are met:

(i)

the user must obtain the executive director's approval prior to the use of specific discrete emission credits to cover, at a minimum, one year of operation of the new or modified source in the NSR permit;

(ii)

the NSR permit must contain an enforceable requirement that the source obtain at least one additional year of offsets before continuing operation in each subsequent year;

(C)

compliance with NO x cap and trade requirements as provided in §101.356(d)of this title (relating to Allowance Banking and Trading).

(D)

compliance with §115.950 of this title (relating to Emissions Trading) and §117.570 of this title (relating to Use of Emission Credits for Compliance), as allowed.

(7)

A discrete emission credit, under this division, may not be used:

(A)

before it has been acquired by the user;

(B)

for netting to avoid the applicability of federal and state NSR requirements;

(C)

to meet FCAA requirements for:

(i)

new source performance standards under FCAA, §111;

(ii)

lowest achievable emission rate standards under FCAA, §173(a)(2);

(iii)

best available control technology standards under FCAA, §165(a)(4);

(iv)

hazardous air pollutants standards under FCAA, §112, including the requirements for maximum achievable control technology;

(v)

standards for solid waste combustion under FCAA, §129;

(vi)

requirements for a vehicle inspection and maintenance program under FCAA, §182(b)(4) or (c)(3);

(vii)

ozone control standards set under FCAA, §183(e) and (f);

(viii)

clean-fueled vehicle requirements under FCAA, §246;

(ix)

motor vehicle emissions standards under FCAA, §202;

(x)

standards for nonroad vehicles under FCAA, §213;

(xi)

requirements for reformulated gasoline under FCAA, §211(k); or

(xii)

requirements for Reid vapor pressure standards under FCAA, §211(h) and (i).

(D)

to allow an emissions increase of an air contaminant that exceeds the limitations of §106.261(3) or (4) or §106.262(3) of this title (relating to Facilities (Emission Limitations) and Facilities (Emission and Distance Limitations)) except as approved by the executive director;

(E)

to authorize a source whose emissions are enforceably limited to below applicable major source threshold levels, as defined in §122.10 of this title (relating to General Definitions), to operate with actual emissions above those levels without triggering applicable requirements that would otherwise be triggered by such major source status;

(F)

to exceed an allowable emission level where the exceedance would cause or contribute to a condition of air pollution as determined by the executive director.

(8)

Calculation of discrete emission credits.

(A)

A user may use the following equation to calculate the amount of discrete emission credits necessary to comply with §117.223 of this title (relating to Source Cap) instead of the equations in §117.223(b)(1) and (2) of this title.

Figure: 30 TAC §101.373(f)(8)(A)

(B)

Otherwise, the amount of discrete emission credits needed to demonstrate compliance or meet a regulatory requirement is calculated as follows.

Figure: 30 TAC §101.373(f)(8)(B)

(C)

The amount of discrete emission credits needed must be rounded up to the nearest ton.

(D)

The user must possess 10% more discrete emission credits than are needed, as calculated in subparagraph (B) of this paragraph, to ensure that the source's environmental contribution retirement obligation will be met.

(E)

If the amount of discrete emission credits needed to meet a regulatory requirement or to demonstrate compliance is greater than ten tons, an additional 5.0% of the discrete emission credits needed, as calculated in subparagraph (B) of this paragraph, must be acquired to ensure that sufficient discrete emission credits are available to the user with an adequate compliance margin.

(F)

The amount of discrete emission credits needed for NSR offsets equals the quantity of tons needed to achieve the maximum allowable emission level set in the user's NSR permit. The user must also purchase and retire enough discrete emission credits to meet the offset ratio requirement in the user's ozone nonattainment area. The user must purchase and retire either the environmental contribution of 10% or the offset ratio, whichever is higher.

(G)

Discrete emission credits that are not used during the use period are surplus and remain available for transfer or use by the holder. In addition, any portion of the calculated environmental contribution not attributed to actual use is also available.

(g)

Notice of intent to use. A notice of intent to use, DEC-2 Form, must be submitted to OPRR in accordance with the following requirements:

(1)

discrete emission credits may be used only after the user has submitted the notice to the registry;

(2)

the notice must be submitted at least 45 days prior to the first day of the use period if the generator is a stationary source, and 90 days if the generator is a mobile source, and every 12 months thereafter for each subsequent year if the use period exceeds 12 months;

(3)

a copy of the notice must also be sent to the federal land manager 30 days prior to use if the user is located within 100 kilometers of a Class I area;

(4)

the notice for a stationary or area source user must include the following information for each use:

(A)

the name, address, county, telephone number, contact person, permit or standard exemption numbers, and account number of the user, and the unique FIN and EPN identification numbers for each emission point;

(B)

the name of the owner and/or operator of the user source;

(C)

the applicable state and federal requirements that the discrete emission credits will be used to comply with and the intended use period;

(D)

the amount of discrete emission credits needed;

(E)

the baseline emission rate, activity level, and total emissions for the applicable emission points;

(F)

the actual emission rate, activity level, and total emissions for the applicable emission points;

(G)

the most stringent emission rate and the most stringent emission level for the applicable emission points, considering all applicable regulatory requirements;

(H)

a complete description of the protocol used to calculate the amount of discrete emission credits needed;

(I)

the actual calculations performed by the user to determine the amount discrete emission credits needed;

(J)

the date on which the discrete emission credits were acquired or will be acquired;

(K)

the discrete emission credit generator and the serial numbers of the discrete emission credits acquired or to be acquired;

(L)

the price of the discrete emission credits acquired or the expected price of the discrete emission credits to be acquired; and

(M)

a statement that due diligence was taken to verify that the discrete emission credits were not previously used, that the discrete emission credits were not generated as a result of actions prohibited under this regulation, and that the discrete emission credits will not be used in a manner prohibited under this regulation.

(5)

the notice for a mobile source user must include the following information:

(A)

the name, address, county, telephone number, and contact person;

(B)

the name of the owner and/or operator of the user source;

(C)

the applicable state and federal requirements that the discrete emission credits will be used to comply with and the intended use period;

(D)

the amount of discrete emission credits needed;

(E)

the mobile source baseline emission rate, mobile source activity level, and total mobile source emissions for the applicable mobile sources;

(F)

the actual mobile source emission rate, activity level, and total emissions for the applicable mobile source;

(G)

the most stringent mobile source emission rate and the most stringent mobile source emission level for the applicable emission points, considering all applicable regulatory requirements;

(H)

a complete description of the protocol used to calculate the amount of MDERCs needed;

(I)

the actual calculations performed by the user to determine the amount MDERCs needed;

(J)

the date on which the MDERCs were acquired or will be acquired;

(K)

the MDERC generator and the serial numbers of the MDERCs acquired or to be acquired;

(L)

the price of the MDERCs acquired or the expected price of the MDERCs to be acquired;

(M)

a statement that due diligence was taken to verify that the MDERCs DERCs were not previously used, that the MDERCs were not generated as a result of actions prohibited under this regulation, and that the MDERCs will not be used in a manner prohibited under this regulation; and

(N)

a certification of use, which must contain certification under penalty of law by a responsible official of the user source of truth, accuracy, and completeness. This certification must state that based on information and belief formed after reasonable inquiry, the statements and information in the document are true, accurate, and complete;

(6)

a user may submit a notice late in the case of an emergency, but the notice must be submitted before the discrete emission credits can be used. The user must include a complete description of the emergency situation in the notice of intent to use. All other notices submitted less than 45 days prior, or 90 days prior for a mobile source, to use will be considered late and in violation;

(7)

the user is responsible for determining the credits it will purchase and notifying the executive director of the selected generating source in the notice of intent to use. If the generator's credits are rejected or the notice of generation is incomplete, the use of discrete emission credits by the user may be delayed by the executive director. The user cannot use any discrete emission credits that have not been certified by the executive director. The executive director may reject the use of discrete emission credits by a source if the credit and use cannot be demonstrated to meet the requirements of this section.

(A)

Actual discrete emission credits use.

(i)

The user shall calculate:

(I)

the amount of discrete emission credits used, including the amount of discrete emission credits retired to cover the environmental contribution associated with actual use; and

(II)

the amount of discrete emission credits not used, including the amount of excess discrete emission credits that were purchased to cover the environmental contribution but not associated with the actual use, and available for future use.

(ii)

A report of use, DEC-3 Form, must be submitted to the registry in accordance with the following requirements:

(I)

a report of use must be submitted within 90 days after the end of the use period;

(II)

the report must be submitted within 90 days of the conclusion of each 12-month use period, if applicable;

(III)

the report is to be used as the mechanism to update or amend the notice of intent to use and must include any information different from that reported in the notice of intent to use, including, but not limited to, the following items:

(-a-)

purchase price of the discrete emission credits obtained prior to the current use period;

(-b-)

the actual amount of discrete emission credits possessed during the use period;

(-c-)

the actual emissions during the use period for VOC and NO x ;

(-d-)

the actual amount of discrete emission credits used;

(-e-)

the actual environmental contribution; and

(-f-)

the amount of discrete emission credits available for future use.

(iii)

The user is in violation of this section if the user submits the report of use later than the allowed 90 days following the conclusion of the use period.

(iv)

The registry shall not contain proprietary information.

(B)

Compliance burden and enforcement.

(i)

The user is responsible for assuring that a sufficient quantity of discrete emission credits is acquired to cover the applicable source's emissions for the entire use period. The user should ensure that the credits are real, surplus, and properly quantified discrete emission credits for purchase.

(ii)

The user is in violation of this section if the user does not possess enough discrete emission credits to cover the credit need for the use period. If the user possesses an insufficient quantity of discrete emission credits to cover its compliance need, the user will be out of compliance for the entire use period, unless the user can demonstrate otherwise. Each day the user is out of compliance may be considered a violation.

(iii)

Users may not transfer their compliance burden and legal responsibilities to a third party participant. Third party participants may only act in an advisory capacity to the user.

(C)

Discrete emission credits are freely transferable in whole or in part, and may be traded or sold to a new owner anytime before the expiration date of the discrete emission credit. The Emissions Banking and Trading Program must be notified by means of an DC-4 Form prior to the transfer. The executive director will issue a letter to the discrete emission credit purchaser reflecting the discrete emission credits purchased by the new owner, and a letter to the discrete emission credit seller showing any remaining discrete emission credits available to the original owner. Discrete emission credits may be transferrable only after the executive director grants approval of the transaction.

§101.374.Program Audits.

(a)

No later than three years after the effective date of this section, and every three years thereafter, the executive director will audit this program.

(b)

The audit will evaluate the timing of credit generation and use, the impact of the program on the state's attainment demonstration and the emissions of hazardous air pollutants, the availability and cost of credits, compliance by the participants, and any other elements the executive director may choose to include.

(c)

The executive director will recommend measures to remedy any problems identified in the audit. The trading of discrete emission credits may be discontinued by the executive director in part or in whole and in any manner, with commission approval, as a remedy for problems identified in the program audit.

(d)

The audit data and results will be completed and submitted to the EPA and made available for public inspection within six months after the audit begins.

This agency hereby certifies that the proposal has been reviewed by legal counsel and found to be within the agency's legal authority to adopt.

Filed with the Office of the Secretary of State, on August 11, 2000.

TRD-200005656

Margaret Hoffman

Director, Environmental Law Division

Earliest possible date of adoption:

For further information, please call:


Chapter 110. REDUCTION OF AIR POLLUTION FROM OZONE

30 TAC §§110.10, 110.12, 110.14, 110.15, 110.16, 110.17, 110.19

The Texas Natural Resource Conservation Commission (commission) proposes new §110.10, Definitions; §110.12, Performance Standards; §110.14, Technology Registration; §110.15, Testing Requirements; §110.16, Labeling Requirements; §110.17, Exemptions; and §110.19, Affected Counties and Compliance Schedules. The proposed new sections in new Chapter 110, Reduction of Air Pollution from Ozone, and corresponding revisions to the state implementation plan (SIP) are proposed in order to reduce ground-level ozone in the Houston/Galveston (HGA), Dallas/Fort Worth (DFW), and Beaumont/Port Arthur (BPA) ozone nonattainment areas, as well as in the 95-county central and eastern Texas region, and are one element of the strategy for the proposed HGA Post-1999 Rate-of-Progress (ROP)/Attainment Demonstration SIP. The purpose of these proposed rules is to incorporate a technology in the affected areas that will reduce ozone from ambient air that is drawn across the external heat exchanger units of air-cooled air conditioning units, including heat pumps.

BACKGROUND AND SUMMARY OF THE FACTUAL BASIS FOR THE PROPOSED RULES

The HGA ozone nonattainment area is classified as Severe-17 under the Federal Clean Air Act (FCAA) Amendments of 1990 (42 United States Code (USC), §§7401 et seq.), and therefore is required to attain the one-hour ozone standard of 0.12 parts per million (ppm) by November 15, 2007. The HGA area, defined by Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller Counties, has been working to develop a demonstration of attainment in accordance with 42 USC, §7410. On January 4, 1995, the state submitted the first of its Post- 1996 SIP revisions for HGA.

The January 1995 SIP consisted of urban airshed model (UAM) modeling for 1988 and 1990 base case episodes, adopted rules to achieve a 9% ROP reduction in volatile organic compounds (VOC), and a commitment schedule for the remaining ROP and attainment demonstration elements. At the same time, but in a separate action, the State of Texas filed for the temporary nitrogen oxides (NOx ) waiver allowed by 42 USC, §7511a(f). The January 1995 SIP and the NO x waiver were based on early base-case episodes which marginally exhibited model performance in accordance with the United States Environmental Protection Agency (EPA) modeling performance standards, but which had a limited data set as inputs to the model. In 1993 and 1994, the commission was engaged in an intensive data-gathering exercise known as the COAST study. The state believed that the enhanced emissions inventory, expanded ambient air quality and meteorological monitoring, and other elements would provide a more robust data set for modeling and other analysis, which would lead to modeling results that the commission could use to better understand the nature of the ozone air quality problem in the HGA area.

Around the same time as the 1995 submittal, the EPA policy regarding SIP elements and timelines went through changes. Two national programs in particular resulted in changing deadlines and requirements. The first of these programs was the Ozone Transport Assessment Group. This group grew out of a March 2, 1995 memo from Mary Nichols, former EPA Assistant Administrator for Air and Radiation, that allowed states to postpone completion of their attainment demonstrations until an assessment of the role of transported ozone and precursors had been completed for the eastern half of the nation, including the eastern portion of Texas. Texas participated in this study, and it has been concluded that Texas does not significantly contribute to ozone exceedances in the Northeastern United States. The other major national initiative that has impacted the SIP planning process is the revisions to the national ambient air quality standard (NAAQS) for ozone. The EPA promulgated a final rule on July 18, 1997 changing the ozone standard to an eight-hour standard of 0.08 ppm. In November 1996, concurrent with the proposal of the standards, the EPA proposed an interim implementation plan (IIP) that it believed would help areas like HGA transition from the old to the new standard. In an attempt to avoid a significant delay in planning activities, Texas began to follow this guidance and readjusted its modeling and SIP development timelines accordingly. When the new standard was published, the EPA decided not to publish the IIP, and instead stated that, for areas currently exceeding the one-hour ozone standard, that standard would continue to apply until it is attained. The FCAA requires that HGA attain the standard by November 15, 2007.

The EPA issued revised draft guidance for areas such as HGA that do not attain the one-hour ozone standard. The commission adopted on May 6, 1998, and submitted to EPA on May 19, 1998, a revision to the HGA SIP which contained the following elements in response to EPA's guidance: UAM modeling based on emissions projected from a 1993 baseline out to the 2007 attainment date; an estimate of the level of VOC and NO x reductions necessary to achieve the one-hour ozone standard by 2007; a list of control strategies that the state could implement to attain the one-hour ozone standard; a schedule for completing the other required elements of the attainment demonstration; a revision to the Post-1996 9% ROP SIP that remedied a deficiency that the EPA believed made the previous version of that SIP unapprovable; and evidence that all measures and regulations required by Subpart 2, of Title I of the FCAA to control ozone and its precursors have been adopted and implemented, or are on an expeditious schedule to be adopted and implemented.

In November 1998, the SIP revision submitted to the EPA in May 1998 became complete by operation of law. However, the EPA stated that it could not approve the SIP until specific control strategies were modeled in the attainment demonstration. The EPA specified a submittal date of November 15, 1999 for this modeling. In a letter to the EPA dated January 5, 1999, the state committed to model two strategies showing attainment.

As the HGA modeling protocol evolved, the state eventually selected and modeled seven basic modeling scenarios. As part of this process, a group of HGA stakeholders worked closely with commission staff to identify local control strategies for the modeling. Some of the scenarios for which the stakeholders requested evaluation included options such as California-type fuel and vehicle programs as well as an acceleration simulation mode equivalent motor vehicle inspection and maintenance program. Other scenarios incorporated the estimated reductions in emissions that were expected to be achieved throughout the modeling domain as a result of the implementation of several voluntary and mandatory statewide programs adopted or planned independently of the SIP. It should be made clear that the commission did not propose that any of these control strategies be included in the ultimate control strategy submitted to the EPA in 2000. The need for, and effectiveness of, any controls which may be implemented outside the covered area will be evaluated on a county-by-county basis.

The SIP revision was adopted by the commission on October 27, 1999, submitted to the EPA by November 15, 1999, and contained the following elements: photochemical modeling of potential specific control strategies for attainment of the one-hour ozone standard in the HGA area by the attainment date of November 15, 2007; an analysis of seven specific modeling scenarios reflecting various combinations of federal, state, and local controls in HGA (additional scenarios H1 and H2 build upon Scenario VIf); identification of the level of reductions of VOC and NO x necessary to attain the one-hour ozone standard by 2007; a 2007 mobile source budget for transportation conformity; identification of specific source categories which, if controlled, could result in sufficient VOC and/or NO x reductions to attain the standard; a schedule committing to submit by April 2000 an enforceable commitment to conduct a mid-course review; and a schedule committing to submit modeling and adopted rules in support of the attainment demonstration by December 2000.

The April 19, 2000 SIP revision for HGA contained the following enforceable commitments by the state: to quantify the shortfall of NO x reductions needed for attainment; to list and quantify potential control measures to meet the shortfall of NO x reductions needed for attainment; to adopt the majority of the necessary rules for the HGA attainment demonstration by December 31, 2000, and to adopt the rest of the shortfall rules as expeditiously as practical, but no later than July 31, 2001; to submit a Post-99 ROP plan by December 31, 2000; to perform a mid- course review by May 1, 2004; and to perform modeling of mobile source emissions using the EPA mobile source emissions model (MOBILE6), to revise the on-road mobile source budget as needed, and to submit the revised budget within 24 months of the model's release. In addition, if a conformity analysis is to be performed between 12 months and 24 months after the MOBILE6 release, the state will revise the motor vehicle emissions budget (MVEB) so that the conformity analysis and the SIP MVEB are calculated on the same basis.

In order for the state to have an approvable attainment demonstration, the EPA has indicated that the state must adopt those strategies modeled in the November submittal and then adopt sufficient controls to close the remaining gap in NO x emissions. The modeling included in this proposal indicates a gap of an additional 77.98 tons per day (tpd) of NO x reductions is necessary for an approvable attainment demonstration. The commission estimates that this measure will achieve a minimum of 13.0 tpd of NO x equivalent reductions and is therefore a necessary measure to consider for closing the gap and successfully demonstrating attainment.

The emission reduction requirements included as part of this SIP revision represent substantial, intensive efforts on the part of stakeholder coalitions in the HGA area. These coalitions, involving local governmental entities, elected officials, environmental groups, industry, consultants, and the public, as well as the commission and the EPA, have worked diligently to identify and quantify potential control strategy measures for the HGA attainment demonstration. Local officials from the HGA area have formally submitted a resolution to the commission, requesting the inclusion of many specific emission reduction strategies.

The current SIP revision contains rules, enforceable commitments, and photochemical modeling analyses in support of the HGA ozone attainment demonstration. In addition, this SIP contains post- 1999 ROP plans for the milestone years 2002 and 2005, and for the attainment year 2007. The SIP also contains enforceable commitments to implement further measures, if needed, in support of the HGA attainment demonstration, as well as a commitment to perform and submit a mid-course review.

The HGA ozone nonattainment area will need to ultimately reduce NOx more than 750 tpd to reach attainment with the one-hour standard. In addition, a VOC reduction of about 25% will have to be achieved. Adoption of the residential and commercial air conditioning rules will contribute to attainment and maintenance of the one-hour ozone standard in the HGA, DFW, BPA, and 95-county eastern and central Texas areas.

The commission solicits comment on additional flexibilities relating to rule content and implementation which have not been addressed in this or other concurrent rulemakings. These flexibilities may be available for both mobile and stationary sources. Additional flexibilities may also be achieved through innovative and/or emerging technology which may become available in the future. Additional sources of funds for incentive programs may become available to substitute for some of the measures considered here.

SECTION BY SECTION DISCUSSION

Chapter 110 is proposed as a new chapter which will contain rules to reduce ambient levels of ozone directly rather than through the reduction of ozone precursor chemicals.

Proposed new §110.10 includes new definitions for "covered air conditioning unit," "inlet ozone concentration," "ozone reduction technology," "ozone reduction efficiency," and "outlet ozone concentration."

Proposed new §110.12(a) sets performance standards for covered air conditioning units that may be supplied or installed in the HGA, DFW, and BPA ozone nonattainment areas after January 1, 2002. These requirements are for the ozone reduction technology to have an initial ozone reduction efficiency equal to or greater than 70%, and to retain an ozone reduction efficiency equal to or greater than 50% averaged over any one-hour period, for a period of 15 years. The requirements further mandate labeling of the covered air conditioning units. Proposed new §110.12(b) prohibits persons from tampering with, or knowingly disabling, ozone reduction technology on covered air conditioning units.

Proposed new §110.14(a) requires persons supplying or manufacturing ozone reduction technology to certify in a registration letter that each make and model of covered air conditioning unit will be compliant with the performance standards. Proposed new §110.14(b) clarifies that the ozone reduction technology is not registered until the executive director provides the persons supplying or manufacturing the ozone reduction technology with a written registration confirmation letter and a registration number for each covered air conditioner. Proposed new §110.14(c) provides the executive director the authority to revoke or deny any registration if he determines that the technology does not work.

Proposed new §110.15(a) establishes the testing requirements for determining the ozone reduction efficiency for covered air conditioning units. The requirements include the use of EPA reference methods for ozone concentration determination, sets the range of ambient air inlet conditions under which the technology must be able to show ozone reduction efficiency, and allows for testing in artificially-created atmospheres, as well as ambient air, under properly controlled conditions. Proposed new §110.15(b) allows the executive director to approve alternate air sampling test methods so long as those methods are equivalent to the methods listed in the section. Proposed new §110.15(c) clarifies that the executive director is authorized to require the ozone reduction technology manufacturer or supplier to conduct testing of any covered air conditioning unit then in use.

Proposed new §110.16(a) requires covered air conditioning units to be permanently labeled to identify that they are compliant with the rules. The label must identify the unit's ozone reduction technology registration number, the year and month of the unit's manufacture, and shall state whether the unit meets the performance standards of §110.12.

Proposed new §110.17(a) allows the executive director to exempt a manufacturer's covered air conditioning unit from specific rules in the chapter if the manufacturer can prove that the technology is not available for, or adaptable to, that unit.

Proposed new §110.19 lists the counties in which the rules apply, and specifies a compliance date for those rules.

FISCAL NOTE: COSTS TO STATE AND LOCAL GOVERNMENTS

Mr. John Davis, Technical Specialist with Strategic Planning and Appropriations determined for the first five-year period the proposed rules are in effect, the commission does not anticipate significant fiscal implications for any unit of state and local government as a result of administration or enforcement of the proposed new sections.

The proposed rulemaking action would require that all air conditioning units sold in the eight- county HGA, four-county DFW, and three-county BPA ozone nonattainment areas and 95 additional central and eastern Texas counties after January 1, 2002 have ozone reduction technology installed. The ozone reduction technology must achieve an initial ozone reduction efficiency equal to or greater than 70%, and an overall ozone reduction efficiency equal to or greater than 50% averaged over any one-hour period, for a period of 15 years. Each new unit will have to be permanently labeled to identify that it is compliant with the new requirements, and the manufacturers and suppliers of ozone reduction technology will have to provide a registration letter to the commission certifying that each make and model of covered air conditioning unit will be compliant with the performance standards.

Any unit of state or local government in the affected counties that purchases air conditioning units after January 1, 2002, will be affected by the proposed rulemaking action. The commission anticipates that it will cost manufacturers more to design and manufacture air conditioning units incorporating the ozone reduction technology. Based on estimates provided by air conditioning manufacturers and a potential ozone reduction technology manufacturer and supplier, affected air conditioning units are projected to cost between $42 and $116 more per ton of air conditioning capacity. Covered air conditioning units range in size from 1.0 ton and less window units; 1.5 to 5.0 ton residential and small commercial units; to 10 to 50 ton large air-cooled commercial units, such as rooftop units. The resulting price increase would be $42 to $116 for typical 1.0 ton window unit, $63 to $580 for a typical residential unit, and $420 to $5,800 for large commercial units. The overall fiscal impact to state and local governments is not anticipated to be significant unless a very large number of the new air conditioning units are purchased.

PUBLIC BENEFIT AND COSTS

Mr. Davis also determined for each of the first five years the proposed rules are in effect, the public benefit anticipated as a result on implementing the new sections will be the reduction of ambient ground-level ozone concentrations. The rules are expected to help the agency achieve the ozone NAAQS in the HGA, DFW, and BPA nonattainment areas, as well as maintain the ozone NAAQS in the central and eastern Texas region.

Under the proposed rulemaking, the commission will require that all air conditioning units supplied or installed in the affected counties after January 1, 2002 have some type of ozone reduction technology, unless otherwise exempted. The ozone reduction technology must achieve an initial ozone reduction efficiency equal to or greater than 70%, and an overall ozone reduction efficiency equal to or greater than 50% averaged over any one-hour period, for a period of 15 years. Each new unit will have to be permanently labeled to identify that it is compliant with the new requirements and the manufacturers and suppliers of ozone reduction technology will have to provide the agency a registration letter certifying that each make and model of covered air conditioning unit will be compliant with the performance standards.

Any individual or business in the affected counties that purchases covered air conditioning units after January 1, 2002, will be affected by the proposed rulemaking. The commission anticipates that it will cost manufacturers more to design and manufacture air conditioning units incorporating the ozone reduction technology. These increased costs will be offset by price increases to consumers. Based on estimates provided by air conditioning manufacturers and a potential ozone reduction technology manufacturer and supplier, affected air conditioning units are projected to cost between $42 and $116 more per ton of air conditioning capacity. Covered air conditioning units range in size from 1.0 ton and less window units; 1.5 to 5.0 ton residential and small commercial units; to 10 to 50 ton large air- cooled commercial units, such as rooftop units. The resulting price increase would be $42 to $116 for typical 1.0 ton window unit, $63 to $580 for a typical residential unit, and $420 to $5,800 for large commercial units. The overall fiscal impact to individuals and businesses will depend on the number and capacity of new air conditioning units purchased.

SMALL AND MICRO BUSINESS ASSESSMENT

The commission does not anticipate adverse fiscal implications for small or micro-businesses as a result of administration or enforcement of the proposed new sections. The total fiscal impact to small or micro-businesses in the affected counties will depend on how many air conditioning units they buy or produce after January 1, 2002.

Under the proposed rulemaking, the commission will require that all air conditioning units sold in the affected counties after January 1, 2002 have ozone reduction technology installed. Incorporation of the new technology will result in a price increase for air conditioners sold in the affected counties after January 1, 2002. Small and micro-businesses in the affected counties that purchase air conditioning units after January 1, 2002 can expect to pay approximately $42 to $116 more per ton of air conditioning capacity. Covered air conditioning units range in size from 1.0 ton and less window units; 1.5 to 5.0 ton residential and small commercial units; to 10 to 50 ton large air-cooled commercial units, such as rooftop units. The resulting price increase would be $42 to $116 for typical 1.0 ton window unit, $63 to $580 for a typical residential unit, and $420 to $5,800 for large commercial units.

DRAFT REGULATORY IMPACT ANALYSIS DETERMINATION

The commission reviewed the proposed rulemaking in light of the regulatory analysis requirements of Texas Government Code, §2001.0225, and determined that the rulemaking action meets the definition of a "major environmental rule" as defined in that statute. "Major environmental rule" means a rule, the specific intent of which is to protect the environment or reduce risks to human health from environmental exposure and that may adversely affect in a material way the economy, a sector of the economy, productivity, competition, jobs, the environment, or the public health and safety of the state or a sector of the state. Proposed new Chapter 110 is intended to protect the environment or reduce risks to human health from environmental exposure to ozone and may affect in an adverse material way, a sector of the economy, or competition.

However, the proposed rules do not meet any of the four criteria which would cause them to be subject to Texas Government Code, §2001.0225(b). Specifically, the ozone reduction technology required by the rules is part of a plan to help meet the ozone NAAQS in the HGA, DFW, and BPA ozone nonattainment areas. The rules are therefore being proposed to meet a federal requirement. States are primarily responsible for ensuring attainment and maintenance of NAAQS once the EPA has established those standards. Under 42 USC, §7410 and related provisions, states must submit, for EPA approval, SIPs that provide for the attainment and maintenance of NAAQS. The proposed rules do not exceed a requirement of a delegation agreement, and were not developed solely under the general powers of the agency, but were specifically developed to meet the air quality standards established under federal law as NAAQS and under TCAA, §§382.002, 382.011, 382.012, 382.017, and 382.019.

TAKINGS IMPACT ASSESSMENT

The staff prepared a takings impact assessment for these rules in accordance with Texas Government Code, §2007.043. The following is a summary of that assessment. The specific purpose of the rulemaking is to require ozone reduction technology on covered air conditioning units supplied or installed in the HGA, DFW, and BPA ozone nonattainment areas, and the 95-county eastern and central Texas region on or after January 1, 2002. This proposed rulemaking is part of an air pollution strategy to reduce the level of ozone in those areas. Promulgation and enforcement of the proposed rules will not burden private, real property. Although the proposed rules do not directly prevent a nuisance, do not prevent an immediate threat to life or property, and do not prevent a real and substantial threat to public health and safety, they do partially fulfill a federal mandate under 42 USC, §7410 requiring states to develop and submit to the EPA a SIP which details the state's plans for the attainment and maintenance of the NAAQS. Because the purpose of the rule proposal is to require certain ozone reduction technology in order to meet federal air quality standards for ozone it is exempted from the requirements of Texas Government Code, §2007.043 as an action reasonably taken to fulfill an obligation mandated by federal law. Consequently, this rulemaking action does not constitute a takings under the Texas Government Code, Chapter 2007.

CONSISTENCY WITH THE COASTAL MANAGEMENT PROGRAM

The commission determined that the proposed rulemaking relates to an action or actions subject to the Texas Coastal Management Program (CMP) in accordance with the Coastal Coordination Act of 1991, as amended (Texas Natural Resources Code, §§33.201 et seq.), and commission rules in 30 TAC Chapter 281, Subchapter B, concerning consistency with the CMP. As required by 30 TAC §281.45(a)(3) and 31 TAC §505.11(b)(2), commission rules governing air pollutant emissions must be consistent with the applicable goals and policies of the CMP. The commission has reviewed this action for consistency with the goals and policies of the Coastal Coordination Council, and has determined that they are consistent. The CMP goal applicable to this rule making action is to protect, preserve, and enhance the diversity, quality, quantity, functions, and values of coastal natural resource areas (31 TAC §501.12(1)). No new sources of air contaminants will be authorized and ambient ozone concentrations will be reduced as a result of these rules. The CMP policy applicable to this rulemaking action is that commission rules comply with regulations in 40 Code of Federal Regulations (CFR), to protect and enhance air quality in the coastal area (31 TAC §501.14(q)). This rulemaking action complies with 40 CFR Part 50, National Primary and Secondary Ambient Air Quality Standards, and 40 CFR Part 51, Requirements for Preparation, Adoption, and Submittal Of Implementation Plans. Accordingly, the commission finds this rule making action to be consistent with CMP goals and policies.

Interested persons may submit comments on the consistency of the proposed rules with the CMP during the public comment period.

ANNOUNCEMENT OF HEARINGS

The commission will hold public hearings on this proposal at the following times and locations: September 18, 2000, 10:00 a.m., Lone Star Convention Center, 9055 Airport Road (FM 1484), Conroe; September 18, 2000, 7:00 p.m., Lake Jackson Civic Center, 333 Highway 332 East, Lake Jackson; September 19, 2000, 10:00 a.m. and 7:00 p.m., George Brown Convention Center, 1001 Avenida de Las Americas, Houston; September 20, 2000, 9:00 a.m., VFW Hall, 6202 George Bush Drive, Katy; September 20, 2000, 6:00 p.m., East Harris County Community Center, 7340 Spencer, Pasadena; September 21, 2000, 10:00 a.m., Southeast Texas Regional Airport Media Room, 6000 Airline Drive, Beaumont; September 21, 2000, 2:00 p.m., Amarillo City Commission Chambers, City Hall, 509 East 7th Avenue, Amarillo; September 21, 2000, 6:00 p.m., Charles T. Doyle Convention Center, 21st Street at Phoenix Lane, Texas City; September 22, 2000, 10:00 a.m., Dayton High School, 2nd Floor Lecture Room, 3200 North Cleveland Street, Dayton; September 22, 2000, 11:00 a.m., El Paso City Council Chambers, 2 Civic Center Plaza, 2nd Floor, El Paso; September 22, 2000, 2:00 p.m., North Central Texas Council of Governments, 2nd Floor Board Room, 616 Six Flags Drive, Suite 200, Arlington; and September 25, 2000, 10:00 a.m., Texas Natural Resource Conservation Commission, 12100 North I-35, Building E, Room 201S, Austin. The hearings are being held to receive oral and written comments from interested persons. Registration will begin one hour prior to each hearing, and interested persons may provide oral comments when called upon, in order of registration. A four-minute time limit will be set at each hearing to assure that enough time is allowed for every interested person to speak. Open discussion will not occur during the hearings; however, agency staff members will be available to discuss the proposal one hour before each hearing, and will answer questions before and after each hearing.

Persons with disabilities who have special communication or other accommodation needs, who are planning to attend a hearing, should contact the Office of Environmental Policy, Analysis, and Assessment at (512) 239-4900. Requests should be made as far in advance as possible.

SUBMITTAL OF COMMENTS

Written comments may be submitted to Heather Evans, Office of Environmental Policy, Analysis, and Assessment, MC 206, P.O. Box 13087, Austin, Texas 78711-3087, faxed to (512) 239- 4808, or e-mailed to siprules@tnrcc.state.tx.us . All comments should reference Rule Log Number 2000-011J-110-AI. Comments must be received by 5:00 p.m., September 25, 2000. For further information, please contact Jeff Greif at (512) 239-1534 or Alan Henderson at (512) 239-1510.

STATUTORY AUTHORITY

The new sections are proposed under Texas Water Code (TWC or Code), §5.103, which authorizes the commission to adopt rules necessary to carry out its powers and duties under the Code, and under the Texas Health and Safety Code, TCAA, §382.017, which provides the commission the authority to adopt rules consistent with the policy and purposes of the TCAA. The new sections are also proposed under TCAA, §382.002, which states as the policy and purpose of the chapter the control or abatement of air pollution in the state; §382.011, which authorizes the commission to control the quality of the state's air; and §382.012, which authorizes the commission to prepare and develop a general, comprehensive plan for the control of the state's air.

The proposed new sections implement TCAA, §382.002, relating to Policy and Purpose; §382.011, relating to General Powers and Duties; and §382.012, relating to State Air Control Plan.

§110.10.Definitions.

Unless specifically defined in the TCAA or in the rules of the commission, the terms used by the commission have the meanings commonly ascribed to them in the field of air pollution regulation. In addition to the terms which are defined by the TCAA, the following words and terms, when used in this chapter, shall have the following meanings, unless the context clearly indicates otherwise.

(1)

Covered air conditioning unit - Any air-cooled air conditioning unit (including split or packaged units) or heat pump unit.

(2)

Inlet ozone concentration - The ozone concentration, measured in parts per billion, of the air entering a covered air conditioning unit prior to exposure to any ozone reduction technology.

(3)

Outlet ozone concentration - The ozone concentration, measured in parts per billion, of air exiting a covered air conditioning unit.

(4)

Ozone reduction efficiency - The difference between inlet ozone concentration and outlet ozone concentration, divided by the inlet ozone concentration, expressed in percent.

(5)

Ozone reduction technology - A technology that converts ozone into oxygen or removes ozone from the outdoor forced air flow through a covered air conditioning unit without adding harmful air pollutants to the ambient air.

§110.12.Performance Standards.

(a)

No person may supply or install a covered air conditioning unit for use unless it is equipped with a registered ozone reduction technology that has an initial ozone reduction efficiency equal to or greater than 70% averaged over any one-hour period, retains an efficiency equal to or greater than 50% averaged over any one-hour period for 15 years, and is properly labeled in accordance with §110.16 of this title (relating to Labeling Requirements).

(b)

No person may tamper with, or knowingly disable, an ozone reduction technology incorporated in a covered air conditioning unit in the counties specified in §110.19 of this title (relating to Affected Counties and Compliance Schedules).

§110.14.Technology Registration.

(a)

All persons supplying or manufacturing ozone reduction technology for use in the counties specified in §110.19 of this title (relating to Affected Counties and Compliance Schedules) must certify in writing to the executive director that their ozone reduction technology will meet the ozone reduction requirements of §110.12 of this title (relating to Performance Standards) for each make and model of covered air conditioning unit for which their technology is registered.

(b)

Each make and model of covered air conditioning unit is registered when the ozone reduction technology manufacturer or supplier receives a written registration confirmation from the executive director providing a registration number for each covered air conditioning unit make and model.

(c)

The executive director may revoke, in writing, any registration or part of a registration, if the executive director determines that the technology does not meet the performance standards of §110.12 of this title.

§110.15.Testing Requirements.

(a)

Ozone reduction efficiency for covered air conditioning units shall be determined in accordance with the following test methods and procedures.

(1)

Ozone concentrations shall be determined by selecting and using an appropriate EPA Reference Method from 40 Code of Federal Regulations Part 50, Appendix D.

(2)

Ozone reduction technology must be demonstrated to meet the ozone reduction efficiency performance standards in §110.12 of this title (relating to Performance Standards), under all of the following conditions;

(A)

inlet ozone concentration between 60 - 140 parts per billion;

(B)

inlet air temperature between 75 - 110 degrees Fahrenheit;

(C)

inlet dew points between 50 - 75 degrees Fahrenheit; and

(D)

maximum and minimum air flow rates if applicable (fan on).

(3)

Ozone reduction efficiency shall be measured using one or both of the following air sampling test methods:

(A)

simultaneous air sampling of the inlet and outlet ozone concentration of a covered air conditioning unit for an hour where conditions in the bulk air stream entering the unit are created by artificial means, provided that:

(i)

sampling locations are chosen so that sufficient mixing of the air enables sound ozone reduction measurements to be taken; and

(ii)

ozone is introduced and dispersed sufficiently upstream of the covered air conditioning unit sampling location to insure complete mixing in the air prior to the sampling point;

(B)

simultaneous air sampling of the inlet and outlet ozone concentration of a covered air conditioning unit where ambient conditions are within the ranges specified in paragraph (2) of this subsection for any one-hour test run, provided that:

(i)

the probe locations are chosen in a manner which accurately demonstrates the average ozone reduction efficiency of the ozone reduction technology; and

(ii)

the probe locations are sufficiently shrouded to insure the upstream and downstream measurements are taken from the same air mass and that no cross mixing has occurred.

(b)

Alternate air sampling test methods may be used if the executive director determines that the proposed methods are equivalent to the methods listed in this section, and he approves the proposed method in writing.

(c)

The ozone reduction technology manufacturer or supplier must test, at their expense, any covered air conditioner in use in the nonattainment area, within 90 days of being directed to conduct such testing by the executive director.

§110.16.Labeling Requirements.

Covered air conditioning units intended for use in the counties specified in §110.19 of this title (relating to Affected Counties and Compliance Schedules) shall be labeled with a permanent material that must be welded, riveted, or otherwise permanently attached to the unit. The label shall identify the unit's ozone reduction technology registration number (if applicable), the year and month of the unit's manufacture, and shall state whether the unit meets the performance standards of §110.12 of this title (relating to Performance Standards).

§110.17.Exemptions.

A covered air conditioning unit may be exempted from all or part of this chapter, by the executive director in writing, if the air conditioning unit manufacturer can demonstrate to the executive director's satisfaction that no ozone reduction technology compliant with §110.12 of this title (relating to Performance Standards) is available for, or adaptable to, any of the covered air conditioning manufacturer's units

§110.19.Affected Counties and Compliance Schedules.

Effective January 1, 2002, persons subject to this rule in the following counties shall be in compliance with §§110.12, 110.14 - 110.17 of this title (relating Performance Standards; Technology Registration; Testing Requirements; Labeling Requirements; and Exemptions):

(1)

Beaumont/Port Arthur counties including Hardin, Jefferson, and Orange;

(2)

Dallas/Fort Worth counties including Collin, Dallas, Denton, and Tarrant;

(3)

Houston/Galveston counties including Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller; and

(4)

East and Central Texas counties including Anderson, Angelina, Aransas, Atascosa, Austin, Bastrop, Bee, Bell, Bexar, Bosque, Bowie, Brazos, Burleson, Caldwell, Calhoun, Camp, Cass, Cherokee, Colorado, Comal, Cooke, Coryell, De Witt, Delta, Ellis, Falls, Fannin, Fayette, Franklin, Freestone, Goliad, Gonzales, Grayson, Gregg, Grimes, Guadalupe, Harrison, Hays, Henderson, Hill, Hood, Hopkins, Houston, Hunt, Jackson, Jasper, Johnson, Karnes, Kaufman, Lamar, Lavaca, Lee, Leon, Limestone, Live Oak, Madison, Marion, Matagorda, McLennan, Milam, Morris, Nacogdoches, Navarro, Newton, Nueces, Panola, Parker, Polk, Rains, Red River, Refugio, Robertson, Rockwall, Rusk, Sabine, San Jacinto, San Patricio, San Augustine, Shelby, Smith, Somervell, Titus, Travis, Trinity, Tyler, Upshur, Van Zandt, Victoria, Walker, Washington, Wharton, Williamson, Wilson, Wise, and Wood.

This agency hereby certifies that the proposal has been reviewed by legal counsel and found to be within the agency's legal authority to adopt.

Filed with the Office of the Secretary of State, on August 11, 2000.

TRD-200005631

Margaret Hoffman

Director, Environmental Law Division

Texas Natural Resource Conservation Commission

Earliest possible date of adoption: September 24, 2000

For further information, please call: (512) 239-0348


Chapter 114. CONTROL OF AIR POLLUTION FROM MOTOR VEHICLES

The Texas Natural Resource Conservation Commission (commission) proposes amendments to §114.6, Low Emission Fuel Definitions; §114.312, Low Emission Diesel Standards; §114.313, Designated Alternate Limits; §114.314, Registration of Diesel Producers and Importers; §114.315, Approved Test Methods; §114.316, Monitoring, Recordkeeping, and Reporting Requirements; §114.317, Exemptions to Low Emission Diesel Requirements; and §114.319, Affected Counties and Compliance Dates. The commission proposes these amendments to Chapter 114, Control of Air Pollution From Motor Vehicles, and corresponding revisions to the state implementation plan (SIP) in order to control ground-level ozone in the Houston/Galveston (HGA), Dallas/Fort Worth (DFW), and Beaumont/Port Arthur (BPA) ozone nonattainment areas.

BACKGROUND AND SUMMARY OF THE FACTUAL BASIS FOR THE PROPOSED RULES

The HGA ozone nonattainment area is classified as Severe-17 under the Federal Clean Air Act (FCAA) Amendments of 1990 (42 United States Code (USC), §§7401 et seq.), and therefore is required to attain the one-hour ozone standard of 0.12 parts per million (ppm) by November 15, 2007. The HGA area, defined by Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller Counties, has been working to develop a demonstration of attainment in accordance with 42 USC, §7410. On January 4, 1995, the state submitted the first of its Post- 1996 SIP revisions for HGA.

The January 1995 SIP consisted of urban airshed model (UAM) modeling for 1988 and 1990 base-case episodes, adopted rules to achieve a 9% rate-of-progress (ROP) reduction in volatile organic compounds (VOC), and a commitment schedule for the remaining ROP and attainment demonstration elements. At the same time, but in a separate action, the State of Texas filed for the temporary nitrogen oxide (NO x ) waiver allowed by 42 USC, §7511a(f). The January 1995 SIP and the NO x waiver were based on early base-case episodes which marginally exhibited model performance in accordance with the United States Environmental Protection Agency (EPA) modeling performance standards, but which had a limited data set as inputs to the model. In 1993 and 1994, the commission was engaged in an intensive data-gathering exercise known as the COAST study. The state believed that the enhanced emissions inventory, expanded ambient air quality and meteorological monitoring, and other elements would provide a more robust data set for modeling and other analysis, which would lead to modeling results that the commission could use to better understand the nature of the ozone air quality problem in the HGA area.

Around the same time as the 1995 submittal, the EPA policy regarding SIP elements and timelines went through changes. Two national programs in particular resulted in changing deadlines and requirements. The first of these programs was the Ozone Transport Assessment Group. This group grew out of a March 2, 1995 memo from Mary Nichols, former EPA Assistant Administrator for Air and Radiation, that allowed states to postpone completion of their attainment demonstrations until an assessment of the role of transported ozone and precursors had been completed for the eastern half of the nation, including the eastern portion of Texas. Texas participated in this study, and it has been concluded that Texas does not significantly contribute to ozone exceedances in the Northeastern United States. The other major national initiative that has impacted the SIP planning process is the revisions to the national ambient air quality standard (NAAQS) for ozone. The EPA promulgated a final rule on July 18, 1997 changing the ozone standard to an eight-hour standard of 0.08 ppm. In November 1996, concurrent with the proposal of the standards, the EPA proposed an interim implementation plan (IIP) that it believed would help areas like HGA transition from the old to the new standard. In an attempt to avoid a significant delay in planning activities, Texas began to follow this guidance, and readjusted its modeling and SIP development timelines accordingly. When the new standard was published, the EPA decided not to publish the IIP, and instead stated that, for areas currently exceeding the one-hour ozone standard, that standard would continue to apply until it is attained. The FCAA requires that HGA attain the standard by November 15, 2007.

The EPA issued revised draft guidance for areas such as HGA that do not attain the one-hour ozone standard. The commission adopted on May 6, 1998 and submitted to the EPA on May 19, 1998 a revision to the HGA SIP which contained the following elements in response to EPA's guidance: UAM modeling based on emissions projected from a 1993 baseline out to the 2007 attainment date; an estimate of the level of VOC and NO x reductions necessary to achieve the one-hour ozone standard by 2007; a list of control strategies that the state could implement to attain the one-hour ozone standard; a schedule for completing the other required elements of the attainment demonstration; a revision to the Post-1996 9% ROP SIP that remedied a deficiency that the EPA believed made the previous version of that SIP unapprovable; and evidence that all measures and regulations required by Subpart 2 of Title I of the FCAA to control ozone and its precursors have been adopted and implemented, or are on an expeditious schedule to be adopted and implemented.

In November 1998, the SIP revision submitted to the EPA in May 1998 became complete by operation of law. However, the EPA stated that it could not approve the SIP until specific control strategies were modeled in the attainment demonstration. The EPA specified a submittal date of November 15, 1999 for this modeling. In a letter to the EPA dated January 5, 1999, the state committed to model two strategies showing attainment.

As the HGA modeling protocol evolved, the state eventually selected and modeled seven basic modeling scenarios. As part of this process, a group of HGA stakeholders worked closely with commission staff to identify local control strategies for the modeling. Some of the scenarios for which the stakeholders requested evaluation included options such as California-type fuel and vehicle programs as well as an acceleration simulation mode equivalent motor vehicle inspection and maintenance program. Other scenarios incorporated the estimated reductions in emissions that were expected to be achieved throughout the modeling domain as a result of the implementation of several voluntary and mandatory statewide programs adopted or planned independently of the SIP. It should be made clear that the commission did not propose that any of these strategies be included in the ultimate control strategy submitted to the EPA in 2000. The need for and effectiveness of any controls which may be implemented outside the HGA eight-county area will be evaluated on a county-by-county basis.

The SIP revision was adopted by the commission on October 27, 1999, submitted to the EPA by November 15, 1999, and contained the following elements: photochemical modeling of potential specific control strategies for attainment of the one-hour ozone standard in the HGA area by the attainment date of November 15, 2007; an analysis of seven specific modeling scenarios reflecting various combinations of federal, state, and local controls in HGA (additional scenarios H1 and H2 build upon Scenario VIf); identification of the level of reductions of VOC and NO x necessary to attain the one-hour ozone standard by 2007; a 2007 mobile source budget for transportation conformity; identification of specific source categories which, if controlled, could result in sufficient VOC and/or NO x reductions to attain the standard; a schedule committing to submit by April 2000 an enforceable commitment to conduct a mid-course review; and a schedule committing to submit modeling and adopted rules in support of the attainment demonstration by December 2000.

The April 19, 2000 SIP revision for HGA contained the following enforceable commitments by the state: to quantify the shortfall of NO x reductions needed for attainment; to list and quantify potential control measures to meet the shortfall of NO x reductions needed for attainment; to adopt the majority of the necessary rules for the HGA attainment demonstration by December 31, 2000, and to adopt the rest of the shortfall rules as expeditiously as practical, but no later than July 31, 2001; to submit a Post-99 ROP plan by December 31, 2000; to perform a mid- course review by May 1, 2004; and to perform modeling of mobile source emissions using the EPA mobile source emissions model (MOBILE6), to revise the on-road mobile source budget as needed, and to submit the revised budget within 24 months of the model's release. In addition, if a conformity analysis is to be performed between 12 months and 24 months after the MOBILE6 release, the state will revise the motor vehicle emissions budget (MVEB) so that the conformity analysis and the SIP MVEB are calculated on the same basis.

In order for the state to have an approvable attainment demonstration, EPA has indicated that the state must adopt those strategies modeled in the November submittal and then adopt sufficient controls to close the remaining gap in NO x emissions. The modeling included in this proposal indicates a gap of an additional 77.98 tons per day (tpd) of NO x reductions is necessary for an approvable attainment demonstration.

The emission reduction requirements included as part of this SIP revision represent substantial, intensive efforts on the part of stakeholder coalitions in the HGA area. These coalitions, involving local governmental entities, elected officials, environmental groups, industry, consultants, and the public, as well as the commission and the EPA, have worked diligently to identify and quantify potential control strategy measures for the HGA attainment demonstration. Local officials from the HGA area have formally submitted a resolution to the commission, requesting the inclusion of many specific emission reduction strategies.

The current SIP revision contains rules, enforceable commitments, and photochemical modeling analyses in support of the HGA ozone attainment demonstration. In addition, this SIP contains Post- 1999 ROP plans for the milestone years 2002 and 2005, and for the attainment year 2007. The SIP also contains enforceable commitments to implement further measures, if needed, in support of the HGA attainment demonstration, as well as a commitment to perform and submit a mid-course review.

The HGA ozone nonattainment area will need to ultimately reduce NOx more than 750 tpd to reach attainment with the one-hour standard. In addition, a VOC reduction of about 25% will have to be achieved. Adoption of the Low Emission Diesel Fuel (LED) program will contribute to attainment and maintenance of the one-hour ozone standard in the HGA area. A LED program also should contribute to a successful demonstration of transportation conformity in the HGA area.

These proposed rules are one element of the control strategy for the HGA Attainment Demonstration SIP. The purpose of these proposed rules is to establish a LED air pollution control strategy that reduces NO x emissions necessary for the HGA nonattainment area to be able to demonstrate attainment with the ozone NAAQS. Additional benefits will be achieved in the BPA and DFW ozone nonattainment areas, and the 95-county central and eastern Texas region.

The proposed revisions to the LED rules will require LED fuel statewide for on-road use. In addition, the proposed revisions to the LED rules will require LED fuel for both on-road and non-road use in the eight counties in the HGA ozone nonattainment area which includes Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller Counties; the four counties of the DFW ozone nonattainment area which includes Collin, Dallas, Denton, and Tarrant Counties; the three counties of the BPA ozone nonattainment area which includes Hardin, Jefferson, and Orange Counties; and 95 additional central and eastern Texas counties including Anderson, Angelina, Aransas, Atascosa, Austin, Bastrop, Bee, Bell, Bexar, Bosque, Bowie, Brazos, Burleson, Caldwell, Calhoun, Camp, Cass, Cherokee, Colorado, Comal, Cooke, Coryell, De Witt, Delta, Ellis, Falls, Fannin, Fayette, Franklin, Freestone, Goliad, Gonzales, Grayson, Gregg, Grimes, Guadalupe, Harrison, Hays, Henderson, Hill, Hood, Hopkins, Houston, Hunt, Jackson, Jasper, Johnson, Karnes, Kaufman, Lamar, Lavaca, Lee, Leon, Limestone, Live Oak, Madison, Marion, Matagorda, McLennan, Milam, Morris, Nacogdoches, Navarro, Newton, Nueces, Panola, Parker, Polk, Rains, Red River, Refugio, Robertson, Rockwall, Rusk, Sabine, San Jacinto, San Patricio, San Augustine, Shelby, Smith, Somervell, Titus, Travis, Trinity, Tyler, Upshur, Van Zandt, Victoria, Walker, Washington, Wharton, Williamson, Wilson, Wise, and Wood Counties.

The LED fuel will lower the emissions of NO x and other pollutants from fuel combustion. Because NO x is a precursor to ground-level ozone formation, reduced emissions of NO x will result in ground-level ozone reductions. To comply with the state LED regulations, diesel fuel producers and importers must ensure that diesel fuel distributed to the LED fuel zone meets the specifications stated in these proposed rules. The proposed rules require that, beginning May 1, 2002, diesel fuel produced for delivery and ultimate sale to the consumer in the affected area does not exceed 500 ppm sulfur, must contain less than 10% by volume of aromatic hydrocarbons, and must have a cetane number of 48 or greater. In addition, the proposed rules will require the sulfur content in the diesel fuel supplied to the DFW, BPA, and HGA ozone nonattainment areas and 95 central and eastern Texas counties, be reduced to 30 ppm sulfur beginning May 1, 2004, and reduced again beginning May 1, 2006, to 15 ppm sulfur. Also, the proposed rules require diesel fuel producers and importers who provide fuel to the affected areas to register with the commission and provide quarterly status reports.

The proposed rules will also revise definitions that will impact who is affected by the proposed state LED fuel program as well as who is impacted by the current requirements of the regional low Reid vapor pressure (RVP) gasoline program, specified in §§114.301, 114.304 - 114.307, and 114.309. The proposed rules will restrict the registration, reporting, and testing requirements of these programs to those persons who have direct control over changes in fuel content, i.e., those persons who produce fuel or import fuel into the state.

The commission is aware that the EPA is currently proposing revised nationwide diesel fuel sulfur controls. If a new federal diesel fuel sulfur rule is adopted that covers the areas in Texas impacted by this rule, and the federal rule is at least as stringent as these rules, then the commission may consider compliance with the national rule equally effective and may repeal the state sulfur requirements for diesel fuel.

The commission is proposing to expand the LED fuel ozone control strategy which was developed for the DFW area and requires diesel fuel content limits more restrictive than federal diesel fuel regulations. The current federal regulations governing diesel fuel quality in Title 40 Code of Federal Regulations (40 CFR) Part 80, Regulation of Fuels and Fuel Additives, §80.29, Controls and Prohibitions on Diesel Fuel Quality, establish limits for fuel content for diesel fuel used in on-road motor vehicle applications. These federal regulations limit sulfur in on-road diesel fuel to 500 ppm and allow the producer to choose between meeting a minimum cetane number of 40 or a maximum aromatic hydrocarbon content of 35% by volume. The state's proposed LED regulations limit on-road diesel to 500 ppm sulfur, 10% aromatic hydrocarbons, and a 48 cetane minimum, and with a more restrictive limit on sulfur being implemented on-road and non-road in the HGA, DFW, BPA ozone nonattainment areas and 95 central and eastern Texas counties in 2004 and then again in 2006. However, although the EPA regulates diesel fuel content for on-road use, it does not regulate the fuel content for non-road diesel fuel. Therefore, since there is currently no federal limit on the content of non-road diesel, the state has the authority to place controls on the fuel content of non-road diesel fuel. As such, the commission is submitting, as part of the SIP, concurrent with this proposed rulemaking, a request for a waiver in accordance with the 42 USC, §7545(C)(4)(c), for the on-road portion of these rules. The commission does not believe that a waiver is needed for the non-road portion of these rules. This proposed SIP submittal is available to the public by contacting Heather Evans at (512) 239- 1970.

Modeling performed for the commission assessing the benefits of this NOx emission reduction strategy demonstrated that significant emission reductions could be achieved from using a low aromatic hydrocarbon/high cetane diesel fuel as specified by the commission's LED fuel requirements. By the year 2007, the proposed LED fuel program will reduce NO x emissions from on-road vehicles and non-road equipment statewide by 30 tpd, of which 6.84 tpd of reductions will be achieved in the HGA ozone nonattainment area. The commission anticipates production cost will increase from $.04 to $.08 per gallon of diesel fuel to comply with rules.

The commission developed this NO x emission control strategy to cover the eight counties contained in the HGA ozone nonattainment area. The coverage area also includes all counties in the state for on-road diesel fuel use and the four DFW ozone nonattainment counties, the three BPA ozone nonattainment counties, as well as 95 central and eastern Texas counties for both on- road and non-road diesel fuel use. The involvement of the statewide counties as part of the NO x emission control strategy is necessary for the HGA and DFW areas to demonstrate attainment of the ozone NAAQS. The proposed rules are intended to help bring the ozone nonattainment areas into compliance and to help keep attainment and near nonattainment areas from going into nonattainment. The proposed statewide coverage will also provide a greater market for diesel fuel producers and importers to provide the fuel required by these regulations and should help alleviate concerns regarding out of area refueling practices.

The commission solicits comment regarding the possible benefits of reducing sulfur content to 15 ppm prior to the 2006 federal deadline as a possible alternative to controls on aromatics and cetane as described in this proposal.

The commission solicits comment on additional flexibilities relating to rule content and implementation which have not been addressed in this or other concurrent rulemakings. These flexibilities may be available for both mobile and stationary sources. Additional flexibilities may also be achieved through innovative and/or emerging technology which may become available in the future. Additional sources of funds for incentive programs may become available to substitute for some of the measures considered here.

SECTION BY SECTION DISCUSSION

The proposed amendments to §114.6 contain revisions to the following definitions: bulk plant, imported, import facility, and importer. The proposed amendment to the definition of bulk plant is needed for clarification of the definition and will insert the word "fuel" that was inadvertently left out of the original rulemaking. The phrase "solely by truck" is also proposed to be amended to "by truck or pipeline" to account for those bulk plants that have pipeline delivery. The proposed amendments to the definitions of imported, import facility, and importer are necessary to clarify that only those persons who import fuel into the state are covered by these definitions. These proposed amendments will impact who is affected by the current requirements of the regional RVP gasoline program, specified in §§114.301, 114.304 - 114.307, and 114.309, as well as the proposed amendments to the LED fuel program and will restrict the registration, reporting, and testing requirements of these programs to those persons who have direct control over changes in fuel content, i.e., those persons who produce fuel or import fuel into the state. In addition, the proposed amendments to §114.6 contain new definitions for motor vehicle and non-road equipment. Also, as a result of the new definitions, the other existing definitions are to be renumbered accordingly.

The proposed amendments to §114.312 revise subsection (b) to modify the sulfur content standard for diesel fuel to provide for the phase down of sulfur content in certain affected areas from 500 ppm to 30 ppm and then again to 15 ppm. In addition, the proposed amendments to §114.312 revise subsection (g) to provide reference to the testing methods prescribed in the proposed amendments to §114.315.

The proposed amendments to §114.313 clarify the language of subsection (c) by adding commas in two locations.

The proposed amendments to §114.314 clarify language by adding the word "fuel" after the phrase "low emission diesel (LED)." The proposed amendments also change the word "chapter" to "division" to clarify that LED producers and importers shall comply with the requirements of the subchapter division regarding LED.

The proposed amendments to §114.315 revise subsection (a) to establish the American Society for Testing and Materials (ASTM) Test Method D287-92(1995) as the approved test method for determining the American Petroleum Institute (API) gravity, ASTM Test Method D445-97 as the approved test method for determining viscosity, ASTM Test Method D93-99c as the approved test method for determining the flash point, and ASTM Test Method D86-00 as the approved test method for determining the distillation temperatures of the diesel fuel. The proposed amendments to §114.315 also contain a new subsection (c) which establishes the test procedures and approval process for obtaining the executive director's approval of an alternative diesel fuel formulation.

The proposed amendments to §114.316 revise subsection (e) to require the California Air Resources Board (CARB) executive order number, or the approval notification number as issued by the executive director, to be included on the product transfer documents if the diesel fuel being transferred complies with one of those alternatives.

The proposed amendments to §114.319 contain a new subsection (a) which establishes the compliance date for statewide coverage of the LED program for on-road diesel fuel use, a new subsection (b) which establishes the compliance date and coverage area for the use of LED for both on- road and non-road use, a new subsection (c) which establishes the compliance date and coverage area for the sulfur content phase down to 30 ppm sulfur, and a new subsection (d) which establishes the compliance date and coverage area for the sulfur content phase down to 15 ppm sulfur.

FISCAL NOTE: COSTS TO STATE AND LOCAL GOVERNMENT

John Davis, Technical Specialist with Strategic Planning and Appropriations, determined that for the first five-year period the proposed amendments are in effect there will be fiscal implications which are not anticipated to be significant for any single unit of state and local government as a result of administration or enforcement of the proposed amendments. The total annual fiscal impact to statewide state and local government diesel vehicles is estimated to be approximately $177 per year per diesel vehicle following implementation of LED fuel standards on May 1, 2002 and an additional $177 per year per diesel vehicle in the DFW, BPA, and HGA ozone nonattainment areas and 95 additional central and eastern Texas counties, following the beginning of a desulfurization phase in period which requires the sulfur level per gallon of gasoline to be reduced from 30 ppm (May 1, 2004) to 15 ppm (May 1, 2006).

The proposed amendments to the current LED fuel rule will require LED fuel statewide for on- road use. In addition, the proposed amendments will require LED fuel for both on-road and non-road use in the eight-county HGA, four-county DFW, and three-county BPA nonattainment areas along with 95 additional counties in central and eastern Texas.

The HGA ozone nonattainment area consists of Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller Counties; the DFW ozone nonattainment area consists of Collin, Dallas, Denton, and Tarrant Counties; the BPA ozone nonattainment area consists of Hardin, Jefferson, and Orange Counties; and the 95 additional central and eastern Texas counties are Anderson, Angelina, Aransas, Atascosa, Austin, Bastrop, Bee, Bell, Bexar, Bosque, Bowie, Brazos, Burleson, Caldwell, Calhoun, Camp, Cass, Cherokee, Colorado, Comal, Cooke, Coryell, De Witt, Delta, Ellis, Falls, Fannin, Fayette, Franklin, Freestone, Goliad, Gonzales, Grayson, Gregg, Grimes, Guadalupe, Harrison, Hays, Henderson, Hill, Hood, Hopkins, Houston, Hunt, Jackson, Jasper, Johnson, Karnes, Kaufman, Lamar, Lavaca, Lee, Leon, Limestone, Live Oak, Madison, Marion, Matagorda, McLennan, Milam, Morris, Nacogdoches, Navarro, Newton, Nueces, Panola, Parker, Polk, Rains, Red River, Refugio, Robertson, Rockwall, Rusk, Sabine, San Jacinto, San Patricio, San Augustine, Shelby, Smith, Somervell, Titus, Travis, Trinity, Tyler, Upshur, Van Zandt, Victoria, Walker, Washington, Wharton, Williamson, Wilson, Wise, and Wood Counties.

In order to comply with the proposed amendments, beginning May 1, 2002, diesel fuel producers and importers must ensure diesel fuel distributed to affected areas shall not exceed 500 ppm sulfur, must contain less than 10% by volume of aromatic hydrocarbons, and must have a cetane number of 48 or greater. Additionally, the proposed amendments will require the sulfur content in the diesel fuel supplied to the DFW, BPA, and HGA nonattainment areas and 95 additional central and eastern Texas counties be reduced to 30 ppm sulfur beginning May 1, 2004, and reduced again beginning May 1, 2006, to 15 ppm.

It is anticipated that the cost of producing diesel fuel to the May 1, 2002 standard will result in an estimated increase, in the cost for this fuel at the pump, of $.04. Additionally, it is anticipated that owners and operators of diesel fueled vehicles in counties affected by the May 1, 2006 standard will have to pay an additional $.04 increase in diesel fuel prices, beginning May 1, 2004, when the phase in period to desulfurize diesel from 30 ppm to 15 ppm sulfur content per gallon of diesel begins. The increase in fuel cost for the May 1, 2002 standard was calculated in an analysis published by Northeast States for Coordinated Air Use Management (NESCAUM) comparing the cost of California diesel fuel to federal diesel. Federal diesel is the term used for diesel fuel which meets federal standards and is used to fuel diesel-powered, compression-ignition engines in on-road applications. The increase in fuel cost for the May 1, 2006 standard is based on the EPA's "Notice of Proposed Rulemaking on the Heavy-Duty Engine and Vehicle Standards and Highway Diesel Fuel Sulfur Control Requirements." In addition, the proposed amendments will require diesel fuel producers and importers who provide fuel to the affected areas to register with the commission, test their fuel for compliance, and provide quarterly status reports to the commission.

The following analysis in this fiscal note only considers on-road diesel vehicles. Vehicle counts for non-road diesel vehicles are not available.

Statewide units of state and local government will likely be required to pay an additional $.04 per gallon for diesel fuel that meets the proposed LED requirements following the May 1, 2002 deadline. Approximately 12,261 state and local government diesel vehicles statewide consumed approximately 54 million gallons of diesel fuel in 1999. Based on a 1.5% growth rate, an estimated 12,821 diesel vehicles would use approximately 57 million gallons of on-road diesel fuel in 2002. The total annual fiscal impact to units of state and local governments in 2002 would be approximately $1.5 million or approximately $117 per diesel vehicle for 2002 (May - December 2002) and then approximately $2.3 million or approximately $177 per year per diesel vehicle afterward.

Beginning May 1, 2004, a desulfurization phase in period will begin, which will eventually result in the reduction of sulfur content per gallon of diesel from 30 ppm (May 1, 2004) to 15 ppm (May 1, 2006). All diesel gas sold in the affected counties will have to meet the 15 ppm requirement by May 1, 2006. Units of state and local government in the affected counties will likely be required to pay an additional $.04 per gallon, for a total increase of $.08 beginning May 1, 2004, for diesel fuel that meets the stricter proposed LED requirements. It is anticipated there will be approximately 9,600 state and local government diesel vehicles operating in the affected areas by May 1, 2004. The additional fiscal impact for units of state and local government vehicles operating in the affected counties in 2004 will be approximately $1.1 million or approximately $117 per diesel vehicle for 2004 (May - December 2004) and then approximately $1.7 million or approximately $177 per diesel vehicle per year afterward. The combined annual cost increase to units of state and local governments which own or operate diesel vehicles in the affected areas, for the first full years following implementation of fuel standards associated with the May 1, 2002 and May 1, 2004 - 2006 phase-in period, is approximately $3.3 million or approximately $354 per diesel vehicle per year.

PUBLIC BENEFIT AND COSTS

Mr. Davis also determined that for the first five years the proposed amendments are in effect, the public benefit anticipated from enforcement of and compliance with the proposed amendments will be the potential reduction of on-road and non-road mobile source emissions, potentially improved air quality, and contribution toward demonstration of attainment with the NAAQS for the HGA ozone nonattainment areas. However, additional benefits will be achieved in the BPA and DFW ozone nonattainment areas, and the 95-county central and eastern Texas region.

There are fiscal implications which are not anticipated to be significant for any single owner or operator of diesel equipment as a result of administration or enforcement of the proposed amendments. It is anticipated that LED diesel fuel producers that supply fuel to the affected counties will incur additional costs to produce diesel fuel that meets the proposed May 1, 2002 LED standards. The cost of producing this LED fuel is estimated to be approximately $.04 per gallon more than for diesel fuel. Additionally, it is anticipated that owners and operators of diesel fueled vehicles in counties affected by the May 1, 2006 standard will be faced with an additional $.04 increase in diesel fuel prices, beginning May 1, 2004, when the phase in period to desulfurize diesel from 30 ppm to 15 ppm sulfur content per gallon of diesel begins.

The commission estimates that approximately 565,661 privately owned and operated diesel vehicles statewide consumed approximately 2.5 billion gallons of on-road diesel fuel in 1999. Based on a 1.5% growth rate, an estimated 591,499 privately owned and operated diesel vehicles would use approximately 2.6 billion gallons of on-road diesel fuel in 2002. The total fiscal impact to persons and businesses which own and operate diesel vehicles statewide in 2002 would be approximately $69 million or approximately $117 per diesel vehicle for 2002 (May - December 2002) and then approximately $105 million or approximately $177 per year per diesel vehicle afterward.

Beginning May 1, 2004, a desulfurization phase in period will begin, which will eventually result in the reduction of sulfur content per gallon of diesel from 30 ppm (May 1, 2004) to 15 ppm (May 1, 2006). All diesel gas sold in the affected counties will have to meet the 15 ppm requirement by May 1, 2006. Persons and businesses that own and operate diesel vehicles in the affected counties will likely be required to pay an additional $.04 per gallon, for a total increase of $.08 beginning May 1, 2004, for diesel fuel that meets the stricter proposed LED requirements. The commission anticipates there will be approximately 441,380 privately-owned diesel vehicles operating in the affected counties by May 1, 2004. The additional fiscal impact for persons and businesses that own and operate diesel vehicles operating in the affected counties in 2004 will be approximately $51 million or approximately $117 per diesel vehicle for 2004 (May - December 2004) and then approximately $78 million or approximately $177 per diesel vehicle per year afterward. The combined annual cost increase to persons and businesses which own or operate diesel vehicles in the affected counties, for the first full years following implementation of fuel standards associated with the May 1, 2002 and May 1, 2004 - 2006 phase in period, is approximately $153 million or approximately $354 per diesel vehicle per year.

There will be significant capital and operating costs to refineries to meet the proposed May 1, 2006 standard. According to EPA analysis found in the "Notice of Proposed Rulemaking on the Heavy-Duty Engine and Vehicle Standards and Highway Diesel Fuel Sulfur Control Requirements," the estimated capital costs for a typical refinery will be approximately $31 million and the average annual operating cost would be approximately $8 million. These increased costs will result in an anticipated $.04 per gallon increase in diesel fuel for consumers beginning May 1, 2004. There are no anticipated significant additional costs for diesel fuel producers and importers associated with registering with the commission or supplying monthly status reports. Likewise, there are no anticipated additional costs to producers for testing LED fuel because producers are already testing their fuel for compliance with federal regulations and industry standards.

SMALL AND MICRO-BUSINESS ASSESSMENT

There will be fiscal implications which are not anticipated to have an adverse impact on any small or micro-businesses as a result of administration or enforcement of the proposed amendments. There are no known diesel fuel producers or importers that would be considered small or micro- businesses. However, it is anticipated that many independent retailers of diesel fuel statewide are small or micro-businesses. Therefore, production costs of approximately $.04 per gallon for each standard (May 1, 2002 and May 1, 2004 - 2006) are not anticipated to affect small or micro-businesses except for passing increased costs of production through to consumers. The fiscal implications for small and micro-businesses would include additional costs of approximately $.04 per gallon for LED starting May 1, 2002 and then an additional $.04 per gallon for lower sulfur content diesel in counties affected by the May 1, 2004 - 2006 phase-in period standard. The additional costs would depend on the amount of fuel used by the business. On an average basis, the annual cost to businesses would be approximately $177 per diesel vehicle per year statewide and an additional $177 per diesel vehicle per year in the counties affected by the May 1, 2004 - 2006 phase-in period standard.

DRAFT REGULATORY IMPACT ANALYSIS DETERMINATION

The commission reviewed the proposed rulemaking in light of the regulatory analysis requirements of Texas Government Code, §2001.0225, and determined that the proposed rulemaking is subject to §2001.0225 because it could meet the definition of a "major environmental rule" as defined in that statute. "Major environmental rule" means a rule, the specific intent of which is to protect the environment or reduce risks to human health from environmental exposure and that may adversely affect in a material way the economy, a sector of the economy, productivity, competition, jobs, the environment, or the public health and safety of the state or a sector of the state. The amendments to Chapter 114 are intended to protect the environment or reduce risks to human health from environmental exposure to ozone and could affect in a material way, a sector of the economy, competition, and the environment due to its impact on the fuel manufacturing and distribution network of the state. The amendments are intended to implement an LED air pollution control program as part of the strategy to reduce emissions of NO x necessary for the counties included in the HGA ozone nonattainment area to be able to demonstrate attainment with the ozone NAAQS. Although the proposed amendments could meet the definition of a "major environmental rule" as defined in the Texas Government Code, §2001.0225 only applies to a major environmental rule, the result of which is to: 1.) exceed a standard set by federal law, unless the rule is specifically required by state law; 2.) exceed an express requirement of state law, unless the rule is specifically required by federal law; 3.) exceed a requirement of a delegation agreement or contract between the state and an agency or representative of the federal government to implement a state and federal program; or 4.) adopt a rule solely under the general powers of the agency instead of under a specific state law.

This proposed rulemaking action does not meet any of these four applicability requirements. Specifically, the LED fuel requirements within these proposed rules were developed in order to meet the ozone NAAQS set by the EPA under 42 USC, §7409, and therefore meet a federal requirement. Provisions of 42 USC, §7410, require states to adopt a SIP which provides for "implementation, maintenance, and enforcement" of the primary NAAQS in each air quality control region of the state. While §7410 does not require specific programs, methods, or reductions in order to meet the standard, state SIPs must include "enforceable emission limitations and other control measures, means or techniques (including economic incentives such as fees, marketable permits, and auctions of emissions rights), as well as schedules and timetables for compliance as may be necessary or appropriate to meet the applicable requirements of this chapter," (meaning Chapter 85, Air Pollution Prevention and Control). It is true that 42 USC does require some specific measures for SIP purposes, like the inspection and maintenance program, but those programs are the exception, not the rule, in the SIP structure of 42 USC. The provisions of 42 USC recognize that states are in the best position to determine what programs and controls are necessary or appropriate in order to meet the NAAQS. This flexibility allows states, affected industry, and the public, to collaborate on the best methods for attaining the NAAQS for the specific regions in the state. Even though 42 USC allows states to develop their own programs, this flexibility does not relieve a state from developing a program that meets the requirements of §7410. Thus, while specific measures are not generally required, the emission reductions are required. States are not free to ignore the requirements of §7410 and must develop programs to assure that the nonattainment areas of the state will be brought into attainment on schedule.

The requirement to provide a fiscal analysis of proposed regulations in the Texas Government Code was amended by Senate Bill 633 (SB 633) during the 75th Legislative Session, 1999. The intent of SB 633 was to require agencies to conduct a regulartory impact analysis (RIA) of extraordinary rules. These are identified in the statutory language as major environmental rules that will have a material adverse impact and will exceed a requirement of state law, federal law, or a delegated federal program, or are adopted solely under the general powers of the agency. With the understanding that this requirement would seldom apply, the commission provided a cost estimate for SB 633 that concluded "based on an assessment of rules adopted by the agency in the past, it is not anticipated that the bill will have significant fiscal implications for the agency due to its limited application." The commission also noted that the number of rules that would require assessment under the provisions of the bill was not large. This conclusion was based, in part, on the criteria set forth in the bill that exempted proposed rules from the full analysis unless the rule was a major environmental rule that exceeds a federal law. As previously discussed, 42 USC does not require specific programs, methods, or reductions in order to meet the NAAQS; thus, states must develop programs for each nonattainment area to ensure that area will meet the attainment deadlines. Because of the ongoing need to address nonattainment issues, the commission routinely proposes and adopts SIP rules. The legislature is presumed to understand this federal scheme. If each rule proposed for inclusion in the SIP was considered to be a major environmental rule that exceeds federal law, then every SIP rule would require the full RIA contemplated by SB 633. This conclusion is inconsistent with the conclusions reached by the commission in its cost estimate and by the Legislative Budget Board (LBB) in its fiscal notes. Since the legislature is presumed to understand the fiscal impacts of the bills it passes, and that presumption is based on information provided by state agencies and the LBB, the commission believes that the intent of SB 633 was only to require the full RIA for rules that are extraordinary in nature. While the SIP rules will have a broad impact, that impact is no greater than is necessary or appropriate to meet the requirements of the FCAA. For these reasons, rules proposed for inclusion in the SIP fall under the exception in Texas Government Code, §2001.0225(a), because they are required by federal law. The commission performed photochemical grid modeling which predicts that NO x emission reductions, such as those required by these rules, will result in reductions in ozone formation in the HGA ozone nonattainment area. This rulemaking does not exceed an express requirement of state law. This rulemaking is intended to obtain NO x emission reductions which will result in reductions in ozone formation in the HGA ozone nonattainment area and help bring HGA into compliance with the air quality standards established under federal law as NAAQS for ozone. The rulemaking does not exceed a standard set by federal law, exceed an express requirement of state law (unless specifically required by federal law), or exceed a requirement of a delegation agreement. The rulemaking was not developed solely under the general powers of the agency, but was specifically developed to meet the NAAQS established under federal law and authorized under Texas Clean Air Act (TCAA), §§382.011, 382.012, 382.017, 382.019, 382.037(g), and 382.039.

The commission invites public comment on the draft regulatory impact analysis.

TAKINGS IMPACT ASSESSMENT

The commission prepared a takings impact assessment for these proposed rules in accordance with Texas Government Code, §2007.043. The following is a summary of that assessment. The specific purpose of the proposed rulemaking is to establish an LED fuel program which will act as an air pollution control strategy to reduce NO x emissions necessary for the eight counties included in the HGA ozone nonattainment area to be able to demonstrate attainment with the ozone NAAQS. Promulgation and enforcement of the proposed rules may possibly burden private, real property because this proposed rulemaking action may result in investment in the permanent installation of new refinery processing equipment. Although the proposed rules do not directly prevent a nuisance or prevent an immediate threat to life or property, they do prevent a real and substantial threat to public health and safety, and partially fulfill a federal mandate under 42 USC, §7410. Specifically, the emission limitations and control requirements within this proposal have been developed in order to meet the ozone NAAQS set by the EPA under 42 USC, §7409. States are primarily responsible for ensuring attainment and maintenance of the NAAQS once the EPA has established them. Under 42 USC, §7410 and related provisions, states must submit, for approval by the EPA, SIPs that provide for the attainment and maintenance of NAAQS through control programs directed to sources of the pollutants involved. Therefore, the purpose of the proposed rules is to implement cleaner burning diesel fuel which is necessary for the HGA ozone nonattainment area to meet the air quality standards established under federal law as NAAQS. Consequently, the exemption which applies to these proposed rules is that of an action reasonably taken to fulfill an obligation mandated by federal law; therefore, these proposed rules do not constitute a takings under the Texas Government Code, Chapter 2007.

CONSISTENCY WITH THE COASTAL MANAGEMENT PROGRAM

The commission determined that the rulemaking action relates to an action or actions subject to the Texas Coastal Management Program (CMP) in accordance with the Coastal Coordination Act of 1991, as amended (Texas Natural Resources Code, §§33.201 et seq.), and the commission rules in 30 TAC Chapter 281, Subchapter B, concerning Consistency with the CMP. As required by 30 TAC §281.45(a)(3) and 31 TAC §505.11(b)(2), relating to actions and rules subject to the CMP, commission rules governing air pollutant emissions must be consistent with the applicable goals and policies of the CMP. The commission reviewed this action for consistency with the CMP goals and policies in accordance with the rules of the Coastal Coordination Council, and determined that the action is consistent with the applicable CMP goals and policies. The CMP goal applicable to this rulemaking action is the goal to protect, preserve, and enhance the diversity, quality, quantity, functions, and values of coastal natural resource areas (31 TAC §501.12(1)). No new sources of air contaminants will be authorized and NO x air emissions will be reduced as a result of these rules. The CMP policy applicable to this rulemaking action is the policy that commission rules comply with regulations in 40 CFR, to protect and enhance air quality in the coastal area (31 TAC §501.14(q)). This rulemaking action complies with 40 CFR 51. Therefore, in compliance with 31 TAC §505.22(e), the commission affirms that this rulemaking action is consistent with CMP goals and policies.

Interested persons may submit comments on the consistency of the proposed rules with the CMP during the public comment period.

ANNOUNCEMENT OF HEARINGS

The commission will hold public hearings on this proposal at the following times and locations: September 18, 2000, 10:00 a.m., Lone Star Convention Center, 9055 Airport Road (FM 1484), Conroe; September 18, 2000, 7:00 p.m., Lake Jackson Civic Center, 333 Highway 332 East, Lake Jackson; September 19, 2000, 10:00 a.m. and 7:00 p.m., George Brown Convention Center, 1001 Avenida de Las Americas, Houston; September 20, 2000, 9:00 a.m., VFW Hall, 6202 George Bush Drive, Katy; September 20, 2000, 6:00 p.m., East Harris County Community Center, 7340 Spencer, Pasadena; September 21, 2000, 10:00 a.m., Southeast Texas Regional Airport Media Room, 6000 Airline Drive, Beaumont; September 21, 2000, 2:00 p.m., Amarillo City Commission Chambers, City Hall, 509 East 7th Avenue, Amarillo; September 21, 2000, 6:00 p.m., Charles T. Doyle Convention Center, 21st Street at Phoenix Lane, Texas City; September 22, 2000, 10:00 a.m., Dayton High School, 2nd Floor Lecture Room, 3200 North Cleveland Street, Dayton; September 22, 2000, 11:00 a.m., El Paso City Council Chambers, 2 Civic Center Plaza, 2nd Floor, El Paso; September 22, 2000, 2:00 p.m., North Central Texas Council of Governments, 2nd Floor Board Room, 616 Six Flags Drive, Suite 200, Arlington; and September 25, 2000, 10:00 a.m., Texas Natural Resource Conservation Commission, 12100 North I-35, Building E, Room 201S, Austin. The hearings are structured for the receipt of oral or written comments by interested persons. Registration will begin one hour prior to each hearing. Individuals may present oral statements when called upon in order of registration. A four-minute time limit will be established at each hearing to assure that enough time is allowed for every interested person to speak. Open discussion will not occur during each hearing; however, agency staff members will be available to discuss the proposal one hour before each hearing, and will answer questions before and after each hearing.

Persons with disabilities who have special communication or other accommodation needs, who are planning to attend a hearing, should contact the Office of Environmental Policy, Analysis, and Assessment at (512) 239-4900. Requests should be made as far in advance as possible.

SUBMITTAL OF COMMENTS

Written comments may be submitted to Heather Evans, Office of Environmental Policy, Analysis, and Assessment, MC 206, P.O. Box 13087, Austin, Texas 78711-3087; faxed to (512) 239- 4808; or emailed to siprules@tnrcc.state.tx.us . All comments should reference Rule Log Number 2000-011D-114-AI. Comments must be received by 5:00 p.m., September 25, 2000. For further information, please contact Morris Brown at (512) 239-1438 or Alan Henderson at (512) 239- 1510.

Subchapter A. DEFINITIONS

30 TAC §114.6

STATUTORY AUTHORITY

The amendment is proposed under Texas Water Code (TWC), §5.103, which authorizes the commission to adopt rules necessary to carry out its powers and duties under the TWC; and under the Texas Health and Safety Code, TCAA, §382.017, which authorizes the commission to adopt rules consistent with the policy and purposes of the TCAA. The amendment is also proposed under TCAA, §382.011, which authorizes the commission to control the quality of the state's air; §382.012, which authorizes the commission to prepare and develop a general, comprehensive plan for the control of the state's air; §382.019, which authorizes the commission to adopt rules to control and reduce emissions from engines used to propel land vehicles; §382.037(g), which authorizes the commission to regulate fuel content if it is demonstrated to be necessary for attainment of the NAAQS; and §382.039, which authorizes the commission to develop and implement transportation programs and other measures necessary to demonstrate attainment and protect the public from exposure to hazardous air contaminants from motor vehicles.

The proposed amendment implements TCAA, §382.002, relating to Policy and Purpose; §382.011, relating to General Powers and Duties; §382.012, relating to State Air Control Plan; §382.019, relating to Methods Used to Control and Reduce Emissions from Land Vehicles; §382.037(g), relating to Vehicle Emissions Inspection and Maintenance Program; and §382.039, relating to Attainment Program.

§114.6.Low Emission Fuel Definitions.

Unless specifically defined in the TCAA or in the rules of the commission, the terms used in this subchapter [ by the commission ] have the meanings commonly ascribed to them in the field of air pollution control. In addition to the terms which are defined by the TCAA, §3.2 of this title (relating to Definitions), and §101.1 of this title (relating to Definitions), the following words and terms, when used in Subchapter H of this chapter (relating to Low Emission Fuels), shall have the following meanings, unless the context clearly indicates otherwise . [ : ]

(1)- (2)

(No change.)

(3)

Bulk plant - An intermediate motor vehicle fuel distribution facility where delivery of motor vehicle fuel to and from the facility is solely by truck or pipeline .

(4)- (9)

(No change.)

(10)

Import [ Imported ] - The process by which motor vehicle fuel is transported into the State of Texas [ counties listed in §114.319 of this title (relating to Affected Counties and Compliance Dates) ] via pipeline, tank ship, rail car, tank truck, or trailer.

(11)

Import facility - The stationary motor vehicle fuel transfer point wherein the importer takes delivery of imported motor vehicle fuel and from which imported motor vehicle fuel is transferred into the cargo tank truck, pipeline, or other delivery vessel from which the fuel will be delivered to a bulk plant or [ the ] retail fuel dispensing facility [ , at which the fuel will be dispensed into motor vehicles ].

(12)

Importer - Any person who imports motor vehicle fuel [ transports, stores, or causes the transportation or storage of motor vehicle fuel, produced by another person, at any point between any producer's facility and any retail fuel dispensing outlet or bulk purchaser/consumer's facility ].

(13)

(No change.)

(14)

Motor vehicle - Any self-propelled device powered by a gasoline fueled spark-ignition engine or a diesel fueled compression-ignition engine in or by which a person or property is or may be transported, and is required to be registered under Texas Transportation Code (TTC), §502.002, excluding vehicles registered under TTC, §502.006(c).

(15)

[ (14) ] Motor vehicle fuel - Any gasoline or diesel fuel used to power gasoline fueled spark-ignition or diesel fueled compression-ignition engines.

(16)

Non-road equipment - Any device powered by a gasoline fueled spark-ignition engine or a diesel fueled compression-ignition engine which is not required to be registered under TTC, §502.002.

(17)

[ (15) ] Produce - Perform the process to convert liquid compounds which are not motor vehicle fuel into motor vehicle fuel, except where a person supplies motor vehicle fuel to a refiner who agrees in writing to further process the motor vehicle fuel at the refiner's refinery and to be treated as a producer of the motor vehicle fuel, only the refiner shall be deemed for all purposes under Subchapter H of this chapter to be the producer of the motor vehicle fuel.

(18)

[ (16) ] Producer - Any person who owns, leases, operates, controls, or supervises a production facility and/or produces motor vehicle fuel.

(19)

[ (17) ] Production facility - A facility at which motor vehicle fuel is produced.

(20)

[ (18) ] Refiner - Any person who owns, leases, operates, controls, or supervises a refinery.

(21)

[ (19) ] Refinery - A facility that manufactures liquid fuels by distilling petroleum.

(22)

[ (20) ] Retail fuel dispensing outlet - Any establishment at which gasoline and/or diesel fuel is sold or offered for sale for use in motor vehicles, and the fuel is directly dispensed into the fuel tanks of the motor vehicles using the fuel.

(23)

[ (21) ] Supply - To provide or transfer fuel to a physically separate facility, vehicle, or transportation system.

This agency hereby certifies that the proposal has been reviewed by legal counsel and found to be within the agency's legal authority to adopt.

Filed with the Office of the Secretary of State, on August 11, 2000.

TRD-200005615

Margaret Hoffman

Director, Environmental Law Division

Texas Natural Resource Conservation Commission

Earliest possible date of adoption: September 24, 2000

For further information, please call: (512) 239-0348


Subchapter H. LOW EMISSION FUELS

2. LOW EMISSION DIESEL

30 TAC §§114.312 - 114.317, 114.319

STATUTORY AUTHORITY

The amendments are proposed under Texas Water Code (TWC), §5.103, which authorizes the commission to adopt rules necessary to carry out its powers and duties under the TWC; and under the Texas Health and Safety Code, Texas Clean Air Act (TCAA), §382.017, which authorizes the commission to adopt rules consistent with the policy and purposes of the TCAA. The amendments are also proposed under TCAA, §382.011, which authorizes the commission to control the quality of the state's air; §382.012, which authorizes the commission to prepare and develop a general, comprehensive plan for the control of the state's air; §382.019, which authorizes the commission to adopt rules to control and reduce emissions from engines used to propel land vehicles; §382.037(g), which authorizes the commission to regulate fuel content if it is demonstrated to be necessary for attainment of the NAAQS; and §382.039, which authorizes the commission to develop and implement transportation programs and other measures necessary to demonstrate attainment and protect the public from exposure to hazardous air contaminants from motor vehicles.

The proposed amendments implement TCAA, §382.002, relating to Policy and Purpose; §382.011, relating to General Powers and Duties; §382.012, relating to State Air Control Plan; §382.019, relating to Methods Used to Control and Reduce Emissions from Land Vehicles; §382.037(g), relating to Vehicle Emissions Inspection and Maintenance Program; and §382.039, relating to Attainment Program.

§114.312.Low Emission Diesel Standards.

(a)

(No change.)

(b)

Sulfur content. [ The maximum sulfur content of LED is 500 parts per million by weight per gallon. ]

(1)

The maximum sulfur content of LED shall not exceed 500 parts per million (ppm) by weight per gallon in the counties specified in §114.319(a) and (b) of this title.

(2)

The maximum sulfur content of LED shall not exceed 30 ppm by weight per gallon in the counties specified in §114.319(c) of this title.

(3)

The maximum sulfur content of LED shall not exceed 15 ppm by weight per gallon in the counties specified in §114.319(d) of this title.

(c)- (f)

(No change.)

(g)

Alternative diesel fuel formulations which the producer has demonstrated to the satisfaction of the executive director and the EPA, through emissions and performance testing methods prescribed in §114.315(c) of this title (relating to Approved Test Methods) [ programs with supporting data ], as achieving comparable or better reductions in emissions of oxides of nitrogen, volatile organic compounds, and particulate matter may be used to satisfy the requirements of subsection (a) of this section. For alternative diesel fuel formulations that incorporate additive systems, the estimated emissions benefits of the alternative diesel fuel formulation may be determined by comparing the [ in-use ] emissions and performance characteristics of the alternative diesel fuel with the additive system versus the emissions and performance characteristics of a diesel fuel without the additive system, as determined by the testing methods prescribed in §114.315(c) of this title [ approved by the executive director ]. The commission recognizes that fuel content specifications, additive formulation , and testing technology often include factors that can reasonably be considered proprietary or confidential. Therefore, proprietary or confidential information supplied by the producer for evaluation of an alternative diesel fuel formulation must be identified as such when submitted. Decisions regarding confidentiality will be made subject to the Texas Public Information Act, Texas Government Code, Chapter 552.

§114.313.Designated Alternate Limits.

(a)- (b)

(No change.)

(c)

Whenever the final blend of a producer or importer includes volumes of diesel fuel the producer or importer has produced or imported , and volumes it has not produced or imported, the producer's or importer's DAL shall apply only to the volume of diesel fuel the producer or importer has produced or imported. In such a case, the producer or importer shall report to the executive director in accordance with subsection (a)(2) of this section , both the volume of diesel fuel produced or imported and the total volume of the final blend.

§114.314.Registration of Diesel Producers and Importers.

Each producer and importer that sells, offers for sale, supplies, or offers for supply from its production facility or import facility low emission diesel fuel (LED) which may ultimately be used in [ to ] counties listed in §114.319 of this title (relating to Affected Counties and Compliance Dates) shall register with the executive director by December 1, 2001; or after May 31, 2002, within 30 days after the first date that such person will produce or import LED. Registration shall be on forms prescribed by the executive director and shall include a statement of acceptance of the standards and enforcement provisions of this division [ chapter ]; and shall include a statement of consent by the registrant that the executive director shall be permitted to collect samples and access documentation and records. The executive director shall maintain a listing of all registered suppliers.

§114.315.Approved Test Methods.

(a)

Compliance with the diesel fuel content requirements of §114.312 of this title (relating to Low Emission Diesel Standards) shall be determined by applying the following test methods and procedures, as appropriate.

(1)- (5)

(No change.)

(6)

The American Petroleum Institute (API) gravity index of LED shall be determined by ASTM Test Method D287-92 (Standard Test Method for API Gravity of Crude Petroleum and Petroleum Products (Hydrometer Method)), dated 1995.

(7)

The viscosity of LED shall be determined by ASTM Test Method D445-97 (Standard Test Method for Kinematic Viscosity of Transparent and Opaque Liquids (the Calculation of Dynamic Viscosity)), dated 1997.

(8)

The flashpoint of LED shall be determined by ASTM Test Method D93-99c (Standard Test Methods for Flash-Point by Pensky-Martens Closed Cup Tester), dated 1999.

(9)

The distillation temperatures of LED shall be determined by ASTM Test Method D86-00 (Standard Test Method for Distillation of Petroleum Products at Atmospheric Pressure), dated 2000.

(b)

Alternatives to the test methods prescribed in subsection (a) of this section may be used if validated by Title 40 Code of Federal Regulations (CFR) , Part 63, Appendix A (related to Test Methods), Method 301 (related to Field Validation of Pollutant Measurement Methods from Various Waste Media), dated December 29, 1992. For the purposes of this subsection, substitute "executive director" in each location that Test Method 301 references "administrator."

(c)

The executive director, upon application of any producer or importer, may approve alternative diesel fuel formulations in accordance with the following procedures.

(1)

The applicant shall initially submit a proposed test protocol to the executive director, which shall include:

(A)

the identity of the entity which will conduct the tests described in paragraph (4) of this subsection;

(B)

test procedures consistent with the requirements of paragraphs (2) and (4) of this subsection;

(C)

test data showing that the candidate fuel meets the specifications for Number 1-D or 2-D diesel fuel as specified in ASTM D975-98b (Standard Specification for Diesel Fuel Oils), dated 1998, and identifying the characteristics of the candidate fuel identified in paragraph (2) of this subsection;

(D)

test data showing that the fuel to be used as the reference fuel satisfies the specifications identified in paragraph (3) of this subsection;

(E)

reasonable quality assurance and quality control procedures; and

(F)

notification of any outlier identification and exclusion procedure that will be used, and a demonstration that any such procedure meets generally accepted statistical principles. The tests shall not be conducted until the protocol is approved by the executive director. Upon completion of the tests, the applicant may submit an application for certification to the executive director. The application shall include the approved test protocol, all of the test data, a copy of the complete test log prepared in accordance with paragraph (4)(D) of this subsection, a demonstration that the candidate fuel meets the requirements for certification specified in this subsection, and other information as the executive director may reasonably require. Upon review of the certification application, the executive director shall grant or deny the application. Any denial shall be accompanied by a written statement of the reasons for denial.

(2)

The applicant shall supply the candidate fuel to be used in the comparative testing in accordance with subsection paragraph (4) of this subsection.

(A)

The sulfur content, total aromatic hydrocarbon content, polycyclic aromatic hydrocarbon, nitrogen content, and cetane number of the candidate fuel shall be determined as the average of three tests conducted in accordance with the referenced test method specified in subsection (a) of this section.

(B)

The identity and concentration of each additive in the candidate fuel shall be determined by a test method specified by the applicant and approved by the executive director to adequately determine the presence and concentration of the additive.

(C)

The applicant may also specify any other parameters for the candidate fuel, along with the test method for determining the parameters. The applicant shall provide the chemical composition of each additive in the candidate fuel, except that if the chemical composition of an additive is not known to either the applicant or to the manufacturer of the additive (if other), the applicant may provide a full disclosure of the chemical process of manufacture of the additive in lieu of its chemical composition.

(3)

The reference fuel used in the comparative testing described in paragraph (4) of this subsection shall be produced from straight-run diesel fuel by a hydrodearomatization process and shall have the following characteristics determined in accordance with the referenced test method specified in subsection (a) of this section:

(A)

sulfur content - as specified in §114.312(b) of this title;

(B)

total aromatic hydrocarbon content - 10% maximum, volume percent;

(C)

polycyclic aromatic hydrocarbon content - 1.4%, maximum weight percent;

(D)

nitrogen content - ten parts per million, maximum;

(E)

cetane number - 48, minimum;

(F)

API gravity index - 33 to 39 degrees;

(G)

viscosity at 40 degrees Celsius - 2.0 to 4.1 centistokes;

(H)

flash point - 130 degrees Fahrenheit, minimum; and

(I)

distillation:

(i)

initial boiling point - 340 to 420 degrees Fahrenheit;

(ii)

10% point - 400 to 490 degrees Fahrenheit;

(iii)

50% point - 470 to 560 degrees Fahrenheit;

(iv)

90% point - 550 to 610 degrees Fahrenheit; and

(v)

end point - 580 to 660 degrees Fahrenheit.

(4)

Exhaust emission tests using the candidate fuel and the reference fuel specified in paragraph (3) of this subsection shall be conducted in accordance with the federal test procedures as specified in Title 40 CFR, Part 86 (Control of Emissions from New and in-Use Highway Vehicles and Engines), Subpart N (Emission Regulations for New Otto-Cycle and Diesel Heavy-Duty Engines - Gaseous and Particulate Exhaust Test Procedures), dated 1998.

(A)

The tests shall be performed using a Detroit Diesel Corporation Series-60 engine or an engine specified by the applicant and approved by the executive director to be equally representative of the post-1990 model year heavy-duty diesel engine fleet.

(B)

The comparative testing shall be conducted by a third-party or third-parties that are mutually agreed upon by the executive director and the applicant. The applicant shall be responsible for all costs of the comparative testing.

(C)

The applicant shall conduct a minimum of five exhaust emission tests on the engine with each fuel, using either of the following sequences, where "R" is the reference fuel and "C" is the candidate fuel:

(i)

RC, RC, RC, RC, RC (and continuing in the same order); or

(ii)

RC, CR, RC, CR, RC (and continuing in the same order).

(D)

The applicant shall submit a test schedule to the executive director at least one week prior to commencement of the tests. The test schedule shall identify the days on which the tests will be conducted, and shall provide for conducting the test consecutively without substantial interruptions other than those resulting from the normal hours of operations at the test facility. The executive director or his designee shall be permitted to observe any tests. The party conducting the testing shall maintain a test log which identifies all tests conducted, all engine mapping procedures, all physical modifications to or operational tests of the engine, all re-calibrations or other changes to the test instruments, and all interruptions between tests and the reason for each such interruption. The party conducting the tests or the applicant shall notify the executive director by telephone and in writing of any unscheduled interruption resulting in a test delay of 48 hours or more, and of the reason for such delay. Prior to restarting the test, the applicant or person conducting the tests shall provide the executive director with a revised schedule for the remaining tests. All tests conducted in accordance with the test schedule, other than any tests rejected in accordance with an outlier identification and exclusion procedure included in the approved test protocol, shall be included in the comparison of emissions in accordance with paragraph (5) of this subsection.

(E)

In each test of a fuel, exhaust emissions of oxides of nitrogen (NO x ), volatile organic compounds (VOC), and particulate matter (PM) shall be measured.

(5)

The average emissions during testing with the candidate fuel shall be compared to the average emissions during testing with the reference fuel specified in paragraph (3) of this subsection, applying one-sided Student's t statistics as set forth in Snedecar and Cochran, Statistical Methods (7th edition), page 91, Iowa State University Press, 1980. The executive director shall issue a certification in accordance with this paragraph only if he or she makes all of the following determinations:

(A)

the average individual emissions of NOx , VOC, and PM, respectively, during testing with the candidate fuel do not exceed the average individual emissions of NO x , VOC, and PM, respectively, during testing with the reference fuel; and

(B)

use of any additive identified in accordance with paragraph (2)(B) of this subsection in diesel powered engines will not increase emissions of noxious or toxic substances which would not be emitted by such engines operating without the additive.

(6)

If the executive director finds that a candidate fuel has been properly tested in accordance with this subsection, and makes the determinations specified in paragraph (5) of this subsection, then the executive director shall issue an approval notification certifying that the alternative diesel fuel formulation represented by the candidate fuel may be used to satisfy the requirements of §114.312(a) of this title. The approval notification shall identify all of the characteristics of the candidate fuel determined in accordance with paragraph (2) of this subsection.

(A)

The approval notification shall provide that the approved alternative diesel fuel formulation has the following specifications:

(i)

a sulfur content, total aromatic hydrocarbon content, polycyclic aromatic hydrocarbon content, and nitrogen content not exceeding that of the candidate fuel;

(ii)

a cetane number not less than that of the candidate fuel; and

(iii)

presence of all additives that were contained in the candidate fuel, in a concentration not less than in the candidate fuel.

(B)

All such characteristics shall be determined in accordance with the test methods identified in subsection (a) of this section. The approval notification shall assign an identification number to the specific approved alternative diesel fuel formulation.

§114.316.Monitoring, Recordkeeping, and Reporting Requirements.

(a)- (d)

(No change.)

(e)

All parties in the distribution chain (producer, importer, terminals, pipelines, truckers, rail carriers, and retail fuel dispensing outlets) subject to the provisions of §114.312 of this title must maintain copies or records of product transfer documents for a minimum of two years and shall upon request, make such copies or records available to representatives of the commission, EPA, or local air pollution agency having [ have ] jurisdiction in the area. The product transfer documents must contain, at a minimum, the following information:

(1)- (5)

(No change.)

(6)

the location of the diesel fuel at the time of transfer; [ and ]

(7)

the following certification statement: "This product complies with the requirements for low emission diesel fuel specified in Title 30 Texas Administrative Code, §114.312 and may be used in any Texas county requiring the use of low emission diesel fuel in compression-ignition engines." ; and

(8)

in the case of diesel fuel that was produced under the requirements of §114.312(f) or (g)of this title, the executive order number as issued by the CARB or the approval notification number as issued by the executive director in accordance with §114.315(c)(6) of this title.

(f)- (i)

(No change.)

§114.317.Exemptions to Low Emission Diesel Requirements.

(a)

(No change.)

(b)

Diesel fuel that does not meet the requirements of §114.312 of this title (relating to Low Emission Diesel Standards) is not prohibited from being transferred, placed, stored, and/or held within the affected counties so long as it is not ultimately used :

(1)

to power a diesel fueled compression-ignition engine in a motor vehicle in the counties listed in §114.319 of this title; or [ the affected counties. ]

(2)

to power a diesel fueled compression-ignition engine in non-road equipment in the counties listed in §114.319(b) of this title.

§114.319.Affected Counties and Compliance Dates.

(a)

Beginning May 1, 2002, affected persons in all [ the following ] counties of Texas shall be in compliance with §§114.312 - 114.317 of this title (relating to Low Emission Diesel Standards; Designated Alternate [ Alternative ] Limits; Registration of Diesel Producers and Importers; Approved Test Methods; Monitoring, Recordkeeping, and Reporting Requirements; and Exemptions to Low Emission Diesel Requirements) for that diesel fuel which may ultimately be used to power a diesel fueled compression-ignition engine in a motor vehicle [ : Collin, Dallas, Denton, Ellis, Johnson, Kaufman, Parker, Rockwall, and Tarrant ].

(b)

Beginning May 1, 2002, affected persons in the following counties shall be in compliance with §§114.312 - 114.317 of this title for that diesel fuel which may ultimately be used to power a diesel fueled compression-ignition engine in a motor vehicle or in non-road equipment:

(1)

Collin, Dallas, Denton, and Tarrant;

(2)

Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller;

(3)

Hardin, Jefferson, and Orange; and

(4)

Anderson, Angelina, Aransas, Atascosa, Austin, Bastrop, Bee, Bell, Bexar, Bosque, Bowie, Brazos, Burleson, Caldwell, Calhoun, Camp, Cass, Cherokee, Colorado, Comal, Cooke, Coryell, De Witt, Delta, Ellis, Falls, Fannin, Fayette, Franklin, Freestone, Goliad, Gonzales, Grayson, Gregg, Grimes, Guadalupe, Harrison, Hays, Henderson, Hill, Hood, Hopkins, Houston, Hunt, Jackson, Jasper, Johnson, Karnes, Kaufman, Lamar, Lavaca, Lee, Leon, Limestone, Live Oak, Madison, Marion, Matagorda, McLennan, Milam, Morris, Nacogdoches, Navarro, Newton, Nueces, Panola, Parker, Polk, Rains, Red River, Refugio, Robertson, Rockwall, Rusk, Sabine, San Jacinto, San Patricio, San Augustine, Shelby, Smith, Somervell, Titus, Travis, Trinity, Tyler, Upshur, Van Zandt, Victoria, Walker, Washington, Wharton, Williamson, Wilson, Wise, and Wood.

(c)

Beginning May 1, 2004, affected persons in the counties listed in subsection (b) of this section shall be in compliance with §114.312(b)(2) of this title for that diesel fuel which may ultimately be used to power a diesel fueled compression-ignition engine in a motor vehicle or in non- road equipment.

(d)

Beginning May 1, 2006, affected persons in the counties listed in subsection (b) of this section shall be in compliance with §114.312(b)(3) of this title for that diesel fuel which may ultimately be used to power a diesel fueled compression-ignition engine in a motor vehicle or in non- road equipment.

This agency hereby certifies that the proposal has been reviewed by legal counsel and found to be within the agency's legal authority to adopt.

Filed with the Office of the Secretary of State, on August 11, 2000.

TRD-200005614

Margaret Hoffman

Director, Environmental Law Division

Texas Natural Resource Conservation Commission

Earliest possible date of adoption: September 24, 2000

For further information, please call: (512) 239-0348


Chapter 114. CONTROL OF AIR POLLUTION FROM MOTOR VEHICLES

Subchapter C. VEHICLE INSPECTION AND MAINTENANCE

30 TAC §§114.50 - 114.53

The Texas Natural Resource Conservation Commission (commission) proposes amendments to §114.50, Vehicle Emissions Inspection Requirements; §114.51, Equipment Evaluation Procedures for Vehicle Exhaust Gas Analyzers; §114.52, Waivers and Extensions for Inspection Requirements; and §114.53, Inspection and Maintenance Fees. The commission proposes these amendments to Chapter 114 (Control of Air Pollution from Motor Vehicles), and to the state implementation plan (SIP) in order to control ground-level ozone in the Houston/Galveston (HGA) ozone nonattainment area. These amendments are one element of the control strategy for the proposed HGA Post-1999 Rate-of-Progress (ROP)/Attainment Demonstration SIP.

BACKGROUND AND SUMMARY OF THE FACTUAL BASIS FOR THE PROPOSED RULES

The HGA ozone nonattainment area is classified as Severe-17 under the Federal Clean Air Act (FCAA) Amendments of 1990 (42 United States Code (USC), §§7401 et seq.), and therefore is required to attain the one-hour ozone standard of 0.12 parts per million (ppm) by November 15, 2007. The HGA area, defined by Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller Counties, has been working to develop a demonstration of attainment in accordance with 42 USC, §7410. On January 4, 1995, the state submitted the first of its Post- 1996 SIP revisions for HGA.

The January 1995 SIP consisted of urban airshed model (UAM) modeling for 1988 and 1990 base-case episodes, adopted rules to achieve a 9% rate-of-progress (ROP) reduction in volatile organic compounds (VOC), and a commitment schedule for the remaining ROP and attainment demonstration elements. At the same time, but in a separate action, the State of Texas filed for the temporary nitrogen oxides (NO x ) waiver allowed by 42 USC, §7511a(f). The January 1995 SIP and the NO x waiver were based on early base-case episodes which marginally exhibited model performance in accordance with the United States Environmental Protection Agency (EPA) modeling performance standards, but which had a limited data set as inputs to the model. In 1993 and 1994, the commission was engaged in an intensive data-gathering exercise known as the COAST study. The state believed that the enhanced emissions inventory, expanded ambient air quality and meteorological monitoring, and other elements would provide a more robust data set for modeling and other analysis, which would lead to modeling results that the commission could use to better understand the nature of the ozone air quality problem in the HGA area.

Around the same time as the 1995 submittal, EPA policy regarding SIP elements and timelines went through changes. Two national programs in particular resulted in changing deadlines and requirements. The first of these programs was the Ozone Transport Assessment Group. This group grew out of a March 2, 1995 memo from Mary Nichols, former EPA Assistant Administrator for Air and Radiation, that allowed states to postpone completion of their attainment demonstrations until an assessment of the role of transported ozone and precursors had been completed for the eastern half of the nation, including the eastern portion of Texas. Texas participated in this study, and it has been concluded that Texas does not significantly contribute to ozone exceedances in the Northeastern United States. The other major national initiative that has impacted the SIP planning process is the revision to the national ambient air quality standard (NAAQS) for ozone. The EPA promulgated a final rule on July 18, 1997 changing the ozone standard to an eight-hour standard of 0.08 ppm. In November 1996, concurrent with the proposal of the standards, EPA proposed an interim implementation plan (IIP) that it believed would help areas like HGA transition from the old to the new standard. In an attempt to avoid a significant delay in planning activities, Texas began to follow this guidance, and readjusted its modeling and SIP development timelines accordingly. When the new standard was published, EPA decided not to publish the IIP, and instead stated that, for areas currently exceeding the one-hour ozone standard, that standard would continue to apply until it is attained. The FCAA requires that HGA attain the standard by November 15, 2007.

The EPA issued revised draft guidance for areas such as HGA that do not attain the one-hour ozone standard. The commission adopted on May 6, 1998 and submitted to EPA on May 19, 1998, a revision to the HGA SIP which contained the following elements in response to EPA's guidance: UAM modeling based on emissions projected from a 1993 baseline out to the 2007 attainment date; an estimate of the level of VOC and NO x reductions necessary to achieve the one-hour ozone standard by 2007; a list of control strategies that the state could implement to attain the one-hour ozone standard; a schedule for completing the other required elements of the attainment demonstration; a revision to the Post-1996 9% ROP SIP that remedied a deficiency that EPA believed made the previous version of that SIP unapprovable; and evidence that all measures and regulations required by Subpart 2 of Title I of the FCAA to control ozone and its precursors have been adopted and implemented, or are on an expeditious schedule to be adopted and implemented.

In November 1998, the SIP revision submitted to EPA in May 1998 became complete by operation of law. However, EPA stated that it could not approve the SIP until specific control strategies were modeled in the attainment demonstration. The EPA specified a submittal date of November 15, 1999 for this modeling. In a letter to EPA dated January 5, 1999, the state committed to model two strategies showing attainment.

As the HGA modeling protocol evolved, the state eventually selected and modeled seven basic modeling scenarios. As part of this process, a group of HGA stakeholders worked closely with commission staff to identify local control strategies for the modeling. Some of the scenarios for which the stakeholders requested evaluation included options such as California-type fuel and vehicle programs as well as an acceleration simulation mode (ASM-2) equivalent motor vehicle inspection and maintenance (I/M) program. Other scenarios incorporated the estimated reductions in emissions that were expected to be achieved throughout the modeling domain as a result of the implementation of several voluntary and mandatory statewide programs adopted or planned independently of the SIP. It should be made clear that the commission did not propose that any of these strategies be included in the ultimate control strategy submitted to EPA in 2000. The need for and effectiveness of any controls which may be implemented outside the HGA eight-county area will be evaluated on a county-by-county basis.

The SIP revision was adopted by the commission on October 27, 1999, submitted to EPA by November 15, 1999, and contained the following elements: photochemical modeling of potential specific control strategies for attainment of the one-hour ozone standard in the HGA area by the attainment date of November 15, 2007; an analysis of seven specific modeling scenarios reflecting various combinations of federal, state, and local controls in HGA (additional scenarios H1 and H2 build upon Scenario VIf); identification of the level of reductions of VOC and NO x necessary to attain the one-hour ozone standard by 2007; a 2007 mobile source budget for transportation conformity; identification of specific source categories which, if controlled, could result in sufficient VOC and/or NO x reductions to attain the standard; a schedule committing to submit by April 2000 an enforceable commitment to conduct a mid-course review; and a schedule committing to submit modeling and adopted rules in support of the attainment demonstration by December 2000.

The April 19, 2000 SIP revision for HGA contained the following enforceable commitments by the state: to quantify the shortfall of NO x reductions needed for attainment; to list and quantify potential control measures to meet the shortfall of NO x reductions needed for attainment; to adopt the majority of the necessary rules for the HGA attainment demonstration by December 31, 2000, and to adopt the rest of the shortfall rules as expeditiously as practical, but no later than July 31, 2001; to submit a Post-99 ROP plan by December 31, 2000; to perform a mid- course review by May 1, 2004; and to perform modeling of mobile source emissions using the EPA mobile source emissions model (MOBILE6), to revise the on-road mobile source budget as needed, and to submit the revised budget within 24 months of the model's release. In addition, if a conformity analysis is to be performed between 12 months and 24 months after the MOBILE6 release, the state will revise the motor vehicle emissions budget (MVEB) so that the conformity analysis and the SIP MVEB are calculated on the same basis.

In order for the state to have an approvable attainment demonstration, EPA has indicated that the state must adopt those strategies modeled in the November submittal and then adopt sufficient controls to close the remaining gap in NO x emissions. The modeling included in this proposal indicates a gap of an additional 77.98 tons per day (tpd) of NO x reductions is necessary for an approvable attainment demonstration.

The emission reduction requirements included as part of this SIP revision represent substantial, intensive efforts on the part of stakeholder coalitions in the HGA area. These coalitions, involving local governmental entities, elected officials, environmental groups, industry, consultants, and the public, as well as the commission and EPA, have worked diligently to identify and quantify potential control strategy measures for the HGA attainment demonstration. Local officials from the HGA area have formally submitted a resolution to the commission, requesting the inclusion of many specific emission reduction strategies.

The current SIP revision contains rules, enforceable commitments, and photochemical modeling analyses in support of the HGA ozone attainment demonstration. In addition, this SIP contains post- 1999 ROP plans for the milestone years 2002 and 2005, and for the attainment year 2007. The SIP also contains enforceable commitments to implement further measures, if needed, in support of the HGA attainment demonstration, as well as a commitment to perform and submit a mid-course review.

The HGA ozone nonattainment area will need to ultimately reduce NOx more than 750 tpd to reach attainment with the one-hour standard. In addition, a VOC reduction of about 25% will have to be achieved. Adoption of the I/M program will contribute to attainment and maintenance of the one-hour ozone standard in the HGA area. An I/M program should also contribute to a successful demonstration of transportation conformity in the HGA area.

The commission is proposing an air control strategy for NO x reductions which requires emissions testing of motor vehicles that are registered and primarily operated in the HGA ozone nonattainment area. The testing would utilize ASM-2 and on-board diagnostic (OBD) technologies. This proposed I/M program was modeled to cover the eight-county region comprising the HGA nonattainment area. The proposed I/M program will reduce NO x emissions from on-road vehicles in the HGA ozone nonattainment area by 42.03 tpd.

The proposed revisions will modify the vehicle emissions testing program by implementing ASM- 2 testing in the HGA ozone nonattainment area. Unlike the current two-speed idle (TSI) test, ASM-2 technology has the ability to detect NO x emissions. Because NO x is a precursor to ground-level ozone formation, reduced NO x and VOC emissions will result in ground-level ozone reduction.

The proposed amendments addressed in this rule change are: changing the testing technology in the HGA area to ASM-2 and OBD for Harris County beginning May 1, 2002; Brazoria, Fort Bend, Galveston, and Montgomery Counties beginning May 1, 2003; and Chambers, Liberty, and Waller Counties beginning May 1, 2004, and an increase to the emissions inspection fee. The commission is proposing a phase-in approach to make for a smoother implementation of the proposed I/M program while still providing significant air quality improvements. In addition, the proposed rules incorporate changes to the exhaust analyzer technical specifications which will apply in every I/M program area.

The commission will take comments on the option of Chambers, Liberty, and Waller Counties individually or collectively developing alternative air control strategies other than an I/M program to meet or exceed the NO x emission reductions that are anticipated from the proposed I/M program. The estimated I/M NO x emission reductions for Chambers County is .98 tpd, Liberty County .94 tpd, and Waller County is .77 tpd, for a combined estimated NO x emissions reduction of 2.69 tpd. The commission will consider proposed alternatives during the comment period and make a final determination. However, the remote sensing component implemented in Harris County will likely continue to cover vehicles registered in these counties even if an alternative control strategy is accepted by the commission.

It is expected that EPA will soon publish a notice of proposed rulemaking (NPRM) which will postpone the requirement to conduct OBD testing beginning January 1, 2001, in I/M program areas for one year or more. In addition, it is anticipated that EPA will propose dropping the tailpipe test for vehicles receiving an OBD test (model year 1996 and newer) with no credit loss. The commission may adjust OBD test requirements upon adoption of these rules, based on information contained in the NPRM.

The commission solicits comment on additional flexibilities relating to rule content and implementation which have not been addressed in this or other concurrent rulemakings. These flexibilities may be available for both mobile and stationary sources. Additional flexibilities may also be achieved through innovative and/or emerging technology which may become available in the future. Additional sources of funds for incentive programs may become available to substitute for some of the measures considered here.

SECTION BY SECTION DISCUSSION

Proposed amendments to §114.50 establish revised program requirements for the state I/M program for vehicle testing and inspection. The proposed amendments to the program concern the applicability and control requirements. The result of these amendments would be to incorporate the entire HGA nonattainment area into the full I/M program in a phased manner.

Section 114.50(a)(4) is proposed to be amended by deleting "Harris County of" the HGA program area. Subsection (a)(4)(A) and (B) is amended by adding vehicles which are "registered and primarily operated in Harris County." Subsection (a) is proposed to be amended by adding new paragraphs (4)(C) - (H) providing clarification of program areas, model years to be tested, types of equipment to be utilized, and implementation dates. New paragraph (4)(C) defines model year vehicles to be tested using OBD in conjunction with ASM-2 in Harris County beginning May 1, 2002. Paragraph (4)(D) defines model year vehicles to be tested in Harris County using ASM-2, or a vehicle emissions test that meets SIP emissions reduction requirements and is approved by EPA beginning May 1, 2002, and clarifies that testing stations must offer both an OBD and an ASM-2 test. Paragraph (4) (E) defines model year vehicles to be tested using OBD in conjunction with ASM-2 in Brazoria, Fort Bend, Galveston, and Montgomery Counties beginning May 1, 2003. Paragraph (4)(F) defines model year vehicles to be tested in Brazoria, Fort Bend, Galveston, and Montgomery Counties using ASM-2, or a vehicle emissions test that meets SIP emissions reduction requirements and is approved by EPA beginning May 1, 2003. Paragraph (4)(G) defines model year vehicles to be tested using OBD in conjunction with ASM-2 in Chambers, Liberty, and Waller Counties beginning May 1, 2004. Paragraph (4)(H) defines model year vehicles to be tested in Chamber, Liberty, and Waller Counties using ASM-2, or a vehicle emissions test that meets SIP emissions reductions requirements and is approved by EPA beginning May 1, 2004. Paragraph (4)(H) also clarifies that testing stations must offer both an OBD and an ASM-2 test.

Section 114.50(b)(3) is amended by adding "HGA" after EDFW to the program areas and deleting "or Harris County" concerning vehicle recall notification.

Section 114.51 is proposed to be amended to update the equipment evaluation procedures for vehicle emissions test equipment. This section currently specifies application, certification, maintenance, and service requirements for manufacturers or distributors of vehicle emissions testing equipment seeking approval of an exhaust gas analyzer or analyzer system for use in the Texas I/M program. Section 114.51(a) currently specifies a date of March 15, 2000, for the exhaust analyzer technical specifications known as "Specifications for Preconditioned Two Speed Idle Vehicle Exhaust Gas Analyzer Systems for use in the Texas Vehicle Emissions Testing Program." In order to incorporate new and updated specifications into the program, the proposed rule amendments specify a date of November 1, 2000, for both the TSI exhaust analyzer technical specifications, and the "Specifications for Acceleration Simulation Mode Vehicle Exhaust Gas Analyzer System for use in the Texas Vehicle Emissions Testing Program."

Proposed amendments to §114.52 establish the schedule for when motorists in specific counties become eligible for waivers and extensions. The schedule is consistent with the dates for the implementation of the emissions testing program in each county.

Proposed amendments to §114.53 establish fee schedules for the different counties which must be paid for the vehicle emissions inspection at an inspection station. Subsection (a)(3) and (4) is proposed to be amended by revising test methodology to ASM-2 and OBD and by adding counties to the I/M program beginning May 1, 2002, and May 1, 2003, respectively. New subsection (a)(5) is being proposed to provide for the collection of fees by those inspection stations conducting ASM-2 and OBD testing beginning May 1, 2004.

In addition to the proposed amendments, the proposed revisions to the SIP narrative clarify the new program elements such as applicability changes; new performance standards; emissions testing network type; emissions testing; affected vehicle populations; enforcement actions related to vehicles and service providers; on-road vehicle emissions testing; and the implementation schedule.

FISCAL NOTE: COSTS TO STATE AND LOCAL GOVERNMENT

John Davis, Technical Specialist with Strategic Planning and Appropriations, determined that for the first five-year period the proposed rules are in effect, the fiscal implication for affected units of state and local government, as a result vehicle emission tests, is estimated to be an additional annual cost of approximately $75,000 in the eight-county area consisting of Harris, Brazoria, Fort Bend, Galveston, Montgomery, Chambers, Liberty, and Waller Counties.

The proposed amendments to Chapter 114 revise the vehicle emission testing program as part of the control strategy to reduce NO x emissions necessary for the counties included in the HGA nonattainment area to be able to demonstrate attainment with the ozone NAAQS. The proposed amendments are one element of the proposed HGA Post-1999 ROP/Attainment Demonstration SIP. A SIP is a plan developed for any region where existing (measured and modeled) ambient levels of pollutant exceeds the levels specified in a national standard. The plan sets forth a control strategy that provides emission reductions necessary for attainment and maintenance of the national standard.

The proposed amendments revise the I/M program using ASM-2 vehicle emission testing equipment in the HGA ozone nonattainment area. Currently, only Harris County requires an Enhanced I/M program. Galveston, Brazoria, Fort Bend, Montgomery, Chambers, Liberty, and Waller Counties do not currently have an I/M program, but will be required to have an Enhanced I/M program similar to Harris County because they are in the HGA ozone nonattainment area. Harris County will use ASM-2 emissions testing technology beginning May 1, 2002; Brazoria, Fort Bend, Galveston, and Montgomery Counties will begin May 1, 2003; and Chambers, Liberty, and Waller Counties will begin May 1, 2004.

In accordance with EPA requirements, the proposed amendments will require an OBD check of all 1996 and newer model year vehicles subject to the I/M requirements starting January 1, 2001. It is anticipated that owners of over 2.8 million vehicles in the HGA ozone nonattainment area could be affected by vehicle emission inspections and other fee increases and the inspection requirements in the proposed amendments. In addition, owners of vehicle safety and emission inspection stations that choose to continue to perform emission testing will be required to upgrade existing equipment or purchase new equipment in order to comply with the proposed new emission test requirements incorporating ASM-2 and OBD technology. There are currently 1,058 emission inspection stations in Harris County. There are an additional 454 safety inspection stations in Galveston, Brazoria, Fort Bend, Montgomery, Chambers, Liberty, and Waller Counties where the Enhanced I/M program will now be mandatory that will have to purchase new analyzers. The cost to upgrade existing analyzers is $25,000 and the cost to purchase a new analyzer is $40,000.

A prior rulemaking increased the emission test fee in Harris County from $13 to $14, effective January 1, 2001. The proposed amendments increase the emission inspection fee in Harris County from $14 to $22.50 per inspection effective May 1, 2002. Motorists, state and local government agencies, and businesses owning registered vehicles in Harris County that are primarily operated in the HGA ozone nonattainment area will be required to pay an additional $8.50 for each emission inspection utilizing ASM-2 or OBD testing. Annual emission testing is not currently required in Galveston, Brazoria, Fort Bend, Montgomery, Chambers, Liberty, and Waller Counties. In the proposed amendments, motorists, state and local government agencies, and businesses in Galveston, Brazoria, Fort Bend, Montgomery, Chambers, Liberty, and Waller Counties owning registered vehicles that are primarily operated in the HGA ozone nonattainment area will be required to pay $22.50 for an emission inspection utilizing ASM-2 or OBD technology.

Units of state and local government that own or operate vehicles subject to I/M requirements in the HGA ozone nonattainment area will be required to have emission testing and will be required to pay the fees established in the proposed amendments. The fiscal impact on units of state and local government associated with emission inspection costs are similar to the impacts on business in general. Units of state and local government that own or operate vehicles subject to I/M requirements in the HGA ozone nonattainment area will be able to apply for a minimum expenditure waiver. The minimum expenditure to receive a waiver in counties under the proposed I/M program will be $450. This is no change in Harris County and a new $450 cost in Galveston, Brazoria, Fort Bend, Montgomery, Chambers, Liberty, and Waller Counties. Based on the inspection fee increase in Harris County and the inspection fee in the other counties, the commission estimates that 6,300 state and local government vehicles in HGA ozone nonattainment area will be affected with a total increased annual cost of approximately $75,000.

PUBLIC BENEFIT AND COSTS

Mr. Davis also determined that for each year of the first five years the proposed rules are in effect, the public benefit anticipated from enforcement of and compliance with the proposed amendments will be the potential reduction of on-road mobile source emissions, potential reduction in NO x emissions, potentially improved air quality, and contribution toward demonstration of attainment with the ozone NAAQS.

There are economic implications anticipated to individuals and businesses as a result of implementing the proposed amendments. Additional costs to affected persons and businesses associated with the proposed amendments include increased and additional costs associated with emission test fees, and additional costs for inspection stations that opt to perform emission testing associated with equipment upgrades or purchases. It is estimated that approximately 2.8 million vehicles in the HGA ozone nonattainment area could potentially be affected by the proposed amendments.

Individual motorists, state and local government agencies, and businesses with vehicles subject to I/M requirements that are registered and primarily operated in the HGA ozone nonattainment area will pay more to have their vehicle's emissions tested incorporating OBD testing on their 1996 and newer vehicles. Individual motorists, state and local government agencies, and businesses with pre-1996 vehicles subject to I/M requirements that are registered and primarily operated in the HGA ozone nonattainment area will pay more to have their vehicle's emissions tested incorporating ASM-2 testing.

In the proposed amendments, the annual emission inspection fee is increased from $14 to $22.50 in Harris County. Motorists, state and local government agencies, and businesses owning registered vehicles in Harris County that are primarily operated in the HGA ozone nonattainment area will pay $8.50 more for each emission inspection utilizing ASM-2 or OBD testing. Currently, emission inspections are not required in Galveston, Brazoria, Fort Bend, Montgomery, Chambers, Liberty, and Waller Counties. In the proposed amendments, motorists, state and local government agencies, and business owning registered vehicles in Galveston, Brazoria, Fort Bend, Montgomery, Chambers, Liberty, and Waller Counties that are primarily operated in the HGA ozone nonattainment area will pay $22.50 for an annual emission inspection utilizing ASM-2 or OBD.

The cost to any person or business to comply with an enhanced I/M program will vary depending upon the number of vehicles owned, the model year, and the condition of the vehicle.

Businesses or individuals that own or operate vehicles subject to I/M requirements in the HGA ozone nonattainment area will be able to apply for a minimum expenditure waiver. The minimum expenditure to receive a waiver in counties under the proposed I/M program will be $450. This is no change in Harris County and a new $450 cost in Galveston, Brazoria, Fort Bend, Montgomery, Chambers, Liberty, and Waller Counties.

Normally, the annual vehicle safety inspection and emission testing, where required, is accomplished at the same facility. The decision by each inspection facility to accomplish the proposed emission testing is voluntary and could have economic implications. Safety inspection stations in the HGA ozone nonattainment area that opt to perform emission testing for the I/M program would be required to upgrade existing equipment or may have to purchase new equipment in order to comply with the proposed new state emissions test requirements incorporating OBD and ASM-2 testing. Current emission inspection stations in Harris County that opt to continue to perform emission testing would be required to upgrade existing equipment or may have to purchase new equipment to comply with the proposed new state emissions test requirements incorporating ASM-2 and OBD testing technology. It is anticipated that the economic decision to upgrade or purchase the required equipment will include the economics of labor costs, potential alternative use of labor's time, the equipment capital costs, and volume of anticipated inspections, current equipment, and other anticipated costs associated with emission testing. It is anticipated that some inspection stations that must upgrade their equipment or purchase new equipment in order to comply with the proposed emission testing requirements in the proposed amendments will find it uneconomic to do so for various reasons and will be unable to accomplish emission inspections. It is anticipated that this business decision will be made by each inspection station.

According to Texas Department of Public Safety (DPS) records, there are currently 1,058 inspection stations in Harris County. If these inspection stations choose to perform emission testing, the commission staff estimated that 10% (approximately 106) of the current inspection stations in Harris County would have to purchase new ASM-2 equipment in order to conduct ASM-2 or OBD vehicle emission testing. Each new analyzer costs approximately $40,000. If this equipment cost is capitalized, the monthly cost for the new equipment is estimated to be approximately $900 per month for five years. The commission staff also estimated that the remaining 90% (approximately 952) of the inspection stations in Harris County could upgrade currently owned analyzers at a cost of approximately $25,000. If this equipment cost is capitalized, the monthly costs for the new equipment is estimated to be approximately $600 per month for five years.

According to DPS records, there are 454 safety inspection stations in Galveston, Brazoria, Fort Bend, Montgomery, Chambers, Liberty, and Waller Counties where the I/M program is proposed. All inspection stations in Galveston, Brazoria, Fort Bend, Montgomery, Chambers, Liberty, and Waller Counties will have to purchase new analyzers to comply with the Enhanced I/M program. Each new analyzer costs approximately $40,000. If this equipment cost is capitalized, the monthly costs for the new equipment is estimated to be approximately $900 per month for five years.

SMALL AND MICRO-BUSINESS ASSESSMENT

There are anticipated fiscal implications to small businesses and micro-businesses as a result of implementing the proposed amendments. The fiscal implications include increased minimum expenditure costs for waivers and increased costs for emission testing of business-owned vehicles.

In general, the costs indicated in the public benefit portion of this fiscal note for individuals, state and local government agencies, and businesses will apply to small and micro-businesses. The minimum expenditure to receive a waiver in counties under the proposed I/M program will be $450. This is no change in Harris County and a new $450 cost in Galveston, Brazoria, Fort Bend, Montgomery, Chambers, Liberty, and Waller Counties for the minimum expenditure waiver.

The annual emission inspection fee will be $22.50 for counties under the proposed I/M program in the HGA ozone nonattainment area. This is an increase of $8.50 Harris County and a new $22.50 fee for the emission test Galveston, Brazoria, Fort Bend, Montgomery, Chambers, Liberty, and Waller Counties.

The cost to small and micro-businesses will vary with the number of vehicles owned, model year, and condition of the vehicle(s).

In addition, it is anticipated that many of the inspection stations are small or micro-businesses that will be required to upgrade their current testing equipment or purchase new analyzers. New analyzer equipment required to conduct ASM-2 (with integrated OBD) vehicle emission testing costs approximately $40,000. The cost to upgrade currently owned analyzers to conduct ASM (with integrated OBD) testing costs approximately $25,000. It is anticipated that the economic decision to upgrade or purchase the required equipment will include the economics of labor costs, potential alternative use of labor's time, the equipment capital costs, and volume of anticipated inspections, current equipment, and other anticipated costs associated with emission testing. It is anticipated that some small or micro-business inspection stations that must upgrade their equipment or purchase new equipment in order to comply with the proposed emission testing requirements in the proposed amendments will find it uneconomic to do so for various reasons and will be unable to continue emission inspections. It is anticipated that this business decision will be made by each inspection station.

DRAFT REGULATORY IMPACT ANALYSIS DETERMINATION

The commission reviewed the proposed rulemaking in light of the regulatory analysis requirements of Texas Government Code, §2001.0225, and determined that the rulemaking action is not subject to §2001.0225 because it does not meet the definition of a "major environmental rule" as defined in that statute. "Major environmental rule" means a rule, the specific intent of which is to protect the environment or reduce risks to human health from environmental exposure and that may adversely affect in a material way the economy, a sector of the economy, productivity, competition, jobs, the environment, or the public health and safety of the state or a sector of the state. The proposed amendments to Chapter 114 are intended to protect the environment or reduce risks to human health from environmental exposure to ozone. However, the inspection stations in and around nonattainment areas would not normally be considered a sector of the economy. In addition, the commission structured the fees in this program to ensure that most additional equipment costs can be recovered. Therefore, the proposed rules do not affect in a material way, the economy, a sector of the economy, productivity, competition, jobs, the environment, or the public health and safety of the state or a sector of the state. The proposed amendments are intended to establish a vehicle emissions testing program as part of the control strategy to reduce NO x emissions necessary for the counties included in the HGA nonattainment area to be able to demonstrate attainment with the ozone NAAQS. The proposed amendments are one element of the proposed HGA Attainment Demonstration SIP. As defined in the Texas Government Code, §2001.0225 only applies to a major environmental rule, the result of which is to: exceed a standard set by federal law, unless the rule is specifically required by state law; exceed an express requirement of state law, unless the rule is specifically required by federal law; exceed a requirement of a delegation agreement or contract between the state and an agency or representative of the federal government to implement a state and federal program, or; adopt a rule solely under the general powers of the agency instead of under a specific state law. This rulemaking does not meet any of these four applicability requirements of a "major environmental rule." Specifically, the emission testing program within this proposal was developed in order to meet the ozone NAAQS set by the EPA under 42 USC, §7409, and therefore meets a federal requirement. Provisions of 42 USC, §7410, require states to adopt a SIP which provides for "implementation, maintenance, and enforcement" of the primary NAAQS in each air quality control region of the state. While §7410 does not require specific programs, methods, or reductions in order to meet the standard, state SIPs must include "enforceable emission limitations and other control measures, means or techniques (including economic incentives such as fees, marketable permits, and auctions of emissions rights), as well as schedules and timetables for compliance as may be necessary or appropriate to meet the applicable requirements of this chapter," (meaning Chapter 85, Air Pollution Prevention and Control). It is true that 42 USC does require some specific measures for SIP purposes, like the inspection and maintenance program, but those programs are the exception, not the rule, in the SIP structure of 42 USC. The provisions of 42 USC recognize that states are in the best position to determine what programs and controls are necessary or appropriate in order to meet the NAAQS. This flexibility allows states, affected industry, and the public, to collaborate on the best methods for attaining the NAAQS for the specific regions in the state. Even though 42 USC allows states to develop their own programs, this flexibility does not relieve a state from developing a program that meets the requirements of §7410. Thus, while specific measures are not generally required, the emission reductions are required. States are not free to ignore the requirements of §7410 and must develop programs to assure that the nonattainment areas of the state will be brought into attainment on schedule.

The requirement to provide a fiscal analysis of proposed regulations in the Texas Government Code was amended by Senate Bill 633 (SB 633) during the 75th Legislative Session, 1999. The intent of SB 633 was to require agencies to conduct a regulatory impact analysis (RIA) of extraordinary rules. These are identified in the statutory language as major environmental rules that will have a material adverse impact and will exceed a requirement of state law, federal law, or a delegated federal program, or are adopted solely under the general powers of the agency. With the understanding that this requirement would seldom apply, the commission provided a cost estimate for SB 633 that concluded "based on an assessment of rules adopted by the agency in the past, it is not anticipated that the bill will have significant fiscal implications for the agency due to its limited application." The commission also noted that the number of rules that would require assessment under the provisions of the bill was not large. This conclusion was based, in part, on the criteria set forth in the bill that exempted proposed rules from the full analysis unless the rule was a major environmental rule that exceeds a federal law. As previously discussed, 42 USC does not require specific programs, methods, or reductions in order to meet the NAAQS; thus, states must develop programs for each nonattainment area to ensure that area will meet the attainment deadlines. Because of the ongoing need to address nonattainment issues, the commission routinely proposes and adopts SIP rules. The legislature is presumed to understand this federal scheme. If each rule proposed for inclusion in the SIP was considered to be a major environmental rule that exceeds federal law, then every SIP rule would require the full RIA contemplated by SB 633. This conclusion is inconsistent with the conclusions reached by the commission in its cost estimate and by the Legislative Budget Board (LBB) in its fiscal notes. Since the legislature is presumed to understand the fiscal impacts of the bills it passes, and that presumption is based on information provided by state agencies and the LBB, the commission believes that the intent of SB 633 was only to require the full RIA for rules that are extraordinary in nature. While the SIP rules will have a broad impact, that impact is no greater than is necessary or appropriate to meet the requirements of the FCAA. For these reasons, rules proposed for inclusion in the SIP fall under the exception in Texas Government Code, §2001.0225(a), because they are required by federal law. The commission performed photochemical grid modeling which predicts that NO x emission reductions, such as those required by these rules, will result in reductions in ozone formation in the HGA ozone nonattainment area. This rulemaking does not exceed an express requirement of state law. This rulemaking is intended to obtain NO x emission reductions which will result in reductions in ozone formation in the HGA ozone nonattainment area and help bring HGA into compliance with the air quality standards established under federal law as NAAQS for ozone. The rulemaking does not exceed a standard set by federal law, exceed an express requirement of state law (unless specifically required by federal law), or exceed a requirement of a delegation agreement. The rulemaking was not developed solely under the general powers of the agency, but was specifically developed to meet the NAAQS established under federal law and authorized under Texas Clean Air Act (TCAA), §§382.011, 382.012, 382.017, 382.019, 382.037 through 382.038, and 382.039.

The commission invites public comment on the draft regulatory impact assessment.

TAKINGS IMPACT ASSESSMENT

The commission prepared a takings impact assessment for these rules in accordance with Texas Government Code, §2007.043. The following is a summary of that assessment. The specific purpose of the rulemaking is to implement a revised I/M program in the HGA ozone nonattainment area as part of the strategy to reduce emissions of ozone precursors necessary for the area to be able to demonstrate attainment with the ozone NAAQS.

Promulgation and enforcement of the rules will not burden private, real property because this rulemaking action does not require the installation of permanent equipment. Although the rule revisions do not directly prevent a nuisance or prevent an immediate threat to life or property, they do prevent a real and substantial threat to public health and safety and partially fulfill a federal mandate under 42 USC, §7410. Specifically, the emissions limitations and control requirements within this proposal were developed in order to meet the ozone NAAQS set by the EPA under 42 USC, §7409. States are primarily responsible for ensuring attainment and maintenance of the NAAQS once the EPA has established them. Under 42 USC, §7410 and related provisions, states must submit, for approval by the EPA, SIPs that provide for the attainment and maintenance of NAAQS through control programs directed to sources of the pollutants involved. Therefore, the purpose of the rulemaking action is to implement a revised I/M program which is necessary for the ozone nonattainment areas to meet the air quality standards established under federal law as NAAQS. Consequently, the exemption which applies to these rules is that of an action reasonably taken to fulfill an obligation mandated by federal law. Therefore, this rulemaking action will not constitute a takings under the Texas Government Code, Chapter 2007.

CONSISTENCY WITH THE COASTAL MANAGEMENT PROGRAM

The commission determined that this rulemaking action relates to an action or actions subject to the Texas Coastal Management Program (CMP) in accordance with the Coastal Coordination Act of 1991, as amended (Texas Natural Resources Code, §§33.201 et seq.), and the commission rules in 30 TAC Chapter 281, Subchapter B, Consistency with the CMP. As required by 31 TAC §505.11(b)(2) and 30 TAC §281.45(a)(3) relating to actions and rules subject to the CMP, commission rules governing air pollutant emissions must be consistent with the applicable goals and policies of the CMP. The commission reviewed this rulemaking action for consistency with the CMP goals and policies in accordance with the rules of the Coastal Coordination Council, and determined that the action is consistent with the applicable CMP goals and policies. The CMP policy applicable to this rulemaking action is the policy (31 TAC §501.14(q)) that commission rules comply with federal regulations in 40 Code of Federal Regulations to protect and enhance air quality in the coastal area (31 TAC §501.14(q)). This rulemaking action will have a beneficial effect on SIP emissions reduction obligations relating to reasonable further progress and attainment demonstrations by making additional emissions reductions over those made by the existing I/M program. Further, no new air contaminants will be authorized by the rule revisions. Therefore, in compliance with 31 TAC §505.22(e), this rulemaking is consistent with CMP goals and policies.

Interested persons may submit comments on the consistency of the proposed rules with the CMP during the public comment period.

ANNOUNCEMENT OF HEARINGS

The commission will hold public hearings on this proposal at the following times and locations: September 18, 2000, 10:00 a.m., Lone Star Convention Center, 9055 Airport Road (FM 1484), Conroe; September 18, 2000, 7:00 p.m., Lake Jackson Civic Center, 333 Highway 332 East, Lake Jackson; September 19, 2000, 10:00 a.m. and 7:00 p.m., George Brown Convention Center, 1001 Avenida de Las Americas, Houston; September 20, 2000, 9:00 a.m., VFW Hall, 6202 George Bush Drive, Katy; September 20, 2000, 6:00 p.m., East Harris County Community Center, 7340 Spencer, Pasadena; September 21, 2000, 10:00 a.m., Southeast Texas Regional Airport Media Room, 6000 Airline Drive, Beaumont; September 21, 2000, 2:00 p.m., Amarillo City Commission Chambers, City Hall, 509 East 7th Avenue, Amarillo; September 21, 2000, 6:00 p.m., Charles T. Doyle Convention Center, 21st Street at Phoenix Lane, Texas City; September 22, 2000, 10:00 a.m., Dayton High School, 2nd Floor Lecture Room, 3200 North Cleveland Street, Dayton; September 22, 2000, 11:00 a.m., El Paso City Council Chambers, 2 Civic Center Plaza, 2nd Floor, El Paso; September 22, 2000, 2:00 p.m., North Central Texas Council of Governments, 2nd Floor Board Room, 616 Six Flags Drive, Suite 200, Arlington; and September 25, 2000, 10:00 a.m., Texas Natural Resource Conservation Commission, 12100 North I-35, Building E, Room 201S, Austin. The hearings are structured for the receipt of oral or written comments by interested persons. Registration will begin one hour prior to each hearing. Individuals may present oral statements when called upon in order of registration. A four-minute time limit will be established at each hearing to assure that enough time is allowed for every interested person to speak. Open discussion will not occur during each hearing; however, agency staff members will be available to discuss the proposal one hour before each hearing, and will answer questions before and after each hearing.

Persons with disabilities who have special communication or other accommodation needs, who are planning to attend the hearings, should contact the Office of Environmental Policy, Analysis, and Assessment at (512) 239-4900. Requests should be made as far in advance as possible.

SUBMITTAL OF COMMENTS

Written comments may be submitted to Heather Evans, Office of Environmental Policy, Analysis, and Assessment, MC 206, P.O. Box 13087, Austin, Texas 78711-3087, faxed to (512) 239- 4808, or emailed to siprules@tnrcc.state.tx.us . All comments should reference Rule Log Number 2000-011A-114-AI. Comments must be received by 5:00 p.m., September 25, 2000. For further information, please contact Bob Wierzowiecki, Technical Analysis Division, (512) 239-1769 or Alan Henderson, Policy and Regulations Division, (512) 239-1510.

STATUTORY AUTHORITY

The amendments are proposed under Texas Water Code, §5.103, which provides the commission the authority to propose rules necessary to carry out its powers and duties under the TWC. The amendments are also proposed under the Texas Health and Safety Code, TCAA, §382.011, which provides the commission the authority to control the quality of the state's air; §382.012, which provides the commission the authority to prepare and develop a general, comprehensive plan for the control of the state's air; §382.017, which provides the commission the authority to adopt rules consistent with the policy and purposes of the TCAA; §382.019, which provides the commission the authority to adopt rules to control and reduce emissions from engines used to propel land vehicles; §382.037 through §382.038, which provide the commission the authority by rule to establish, implement, and administer a program requiring emissions-related inspections of motor vehicles to be performed at inspection facilities consistent with the requirements of the FCAA; and §382.039, which provides the commission the authority to coordinate with federal, state, and local transportation planning agencies to develop and implement transportation programs and other measures necessary to demonstrate and maintain attainment of NAAQS and to protect the public from exposure to hazardous air contaminants from motor vehicles.

The amendments implement TCAA, §382.002, relating to Policy and Purpose; §382.011, relating to General Powers and Duties; §382.012, relating to State Air Control Plan; §382.019, relating to Methods Used to Control and Reduce Emissions from Land Vehicles; §382.037 through §382.038, relating to Vehicle Emissions Inspection and Maintenance Program; and §382.039, relating to Attainment Program.

§114.50.Vehicle Emissions Inspection Requirements.

(a)

Applicability. The requirements of this section and those contained in the revised Texas Inspection and Maintenance (I/M) State Implementation Plan (SIP) shall be applied to all gasoline-powered motor vehicles 2-24 years old and subject to an annual emissions inspection, beginning with the first safety inspection. Currently, military tactical vehicles, motorcycles, diesel-powered vehicles, dual-fueled vehicles which cannot operate using gasoline, and antique vehicles registered with the Texas Department of Transportation are excluded from the program. Safety inspection facilities and inspectors certified by the Texas Department of Public Safety (DPS) shall inspect all subject vehicles, in the following program areas in accordance with the following schedule.

(1)- (3)

(No change.)

(4)

This paragraph applies to all vehicles registered and primarily operated in [ Harris County of ] the Houston/Galveston (HGA) program area.

(A)

Beginning January 1, 2001, all 1996 and newer model year vehicles registered and primarily operated in Harris County equipped with OBD systems shall be tested using EPA- approved OBD test procedures in conjunction with a TSI test.

(B)

Beginning January 1, 2001, all pre-1996 and older vehicles registered and primarily operated in Harris County shall be tested using a TSI test. All vehicle emissions test stations must offer both TSI and OBD tests to the public.

(C)

Beginning May 1, 2002, all 1996 and newer model year vehicles equipped with OBD systems and registered and primarily operated in Harris County shall be tested using EPA-approved OBD test procedures in conjunction with an ASM-2 test, or a vehicle emissions test that meets SIP emissions reduction requirements and is approved by the EPA.

(D)

Beginning May 1, 2002, all pre-1996 model year vehicles registered and primarily operated in Harris County shall be tested using the ASM-2 test, or a vehicle emissions test that meets SIP emissions reduction requirements and is approved by the EPA. All vehicle emissions test stations must offer both an OBD test and ASM-2 test, or a vehicle emissions test that meets SIP emissions reduction requirements and is approved by EPA, to the public.

(E)

Beginning May 1, 2003, all 1996 and newer model year vehicles equipped with OBD systems and registered and primarily operated in Brazoria, Fort Bend, Galveston, and Montgomery Counties shall be tested using EPA-approved OBD test procedures in conjunction with an ASM-2 test, or a vehicle emissions test that meets SIP emissions reduction requirements and is approved by the EPA.

(F)

Beginning May 1, 2003, all pre-1996 and newer model year vehicles registered and primarily operated in Brazoria, Fort Bend, Galveston, and Montgomery Counties shall be tested using the ASM-2 test procedures, or a vehicle emissions test that meets SIP emissions reduction requirements and is approved by the EPA. All vehicle emissions test stations must offer both an OBD test and an ASM-2 test or a vehicle emissions test that meets SIP emissions reduction requirements and is approved by the EPA, to the public.

(G)

Beginning May 1, 2004, all 1996 and newer model year vehicles equipped with OBD systems and registered and primarily operated in Chambers, Liberty, and Waller Counties shall be tested using EPA-approved OBD test procedures in conjunction with an ASM-2 test, or a vehicle emissions test that meets SIP emissions reduction requirements and is approved by the EPA.

(H)

Beginning May 1, 2004, all pre-1996 model year vehicles registered and primarily operated in Chambers, Liberty, and Waller Counties shall be tested using an ASM-2 test, or a vehicle emissions test that meets SIP emissions reduction requirements and is approved by the EPA. All vehicle emissions test stations must offer both an OBD test and ASM-2 test, or a vehicle emissions test that meets SIP emissions reduction requirements and is approved by EPA, to the public.

(5)

(No change.)

(b)

Control requirements.

(1)- (2)

(No change.)

(3)

Any motorist in the DFW, EDFW, HGA, or El Paso program areas [ or Harris County ] who has received a notice from an emissions inspection station that there are recall items unresolved on their motor vehicle, should furnish proof of compliance with the recall notice prior to the next vehicle emissions inspection. The motorist may present a written statement from the dealership or leasing agency indicating that emissions repairs have been completed as proof of compliance.

(4)- (7)

(No change.)

(c)- (d)

(No change.)

§114.51.Equipment Evaluation Procedures for Vehicle Exhaust Gas Analyzers.

(a)

Any manufacturer or distributor of vehicle testing equipment may apply to the executive director of the Texas Natural Resource Conservation Commission (commission) or his appointee, for approval of an exhaust gas analyzer or analyzer system for use in the Texas Inspection and Maintenance (I/M) program administered by the Texas Department of Public Safety. Each manufacturer shall submit a formal certificate to the commission stating that any analyzer model sold or leased by the manufacturer or its authorized representative and any model currently in use in the I/M program will satisfy all design and performance criteria set forth in "Specifications for Preconditioned Two Speed Idle Vehicle Exhaust Gas Analyzer Systems for Use in the Texas Vehicle Emissions Testing Program," dated November 1 [ March 15 ], 2000, or in "Specifications for Acceleration Simulation Mode (ASM-2) Vehicle Exhaust Gas Analyzer Systems for use in the Texas Vehicle Emissions Testing Program," dated November 1 [ March 15 ], 2000. Copies of these documents are available at the commission's Central Office, located at 12100 Park 35 Circle, Austin, Texas 78753. The manufacturer shall also provide sufficient documentation to demonstrate conformance with these criteria including a complete description of all hardware components, the results of appropriate performance testing, and a point-by-point response to each specific requirement.

(b)- (e)

(No change.)

§114.52.Waivers and Extensions for Inspection Requirements.

(a)

Applicability. The waivers and extensions apply to any motorist who can satisfy the conditions of a specific waiver or extension. Applications must be made to the Department of Public Safety (DPS). For the minimum expenditure waiver, individual vehicle waiver, and parts availability time extension, the motorist may apply only once during each testing cycle. For the low income time extension, the motorist may apply every other test cycle. Application for waivers and extensions may be made in the following inspection and maintenance program counties:

(1)

Motorists in Dallas, El Paso, Harris, and Tarrant Counties are eligible for waivers and extensions.

(2)

Beginning May 1, 2002, motorists in Collin and Denton Counties will be eligible for waivers and extensions.

(3)

Beginning May 1, 2003, motorists in Brazoria, Ellis, Fort Bend, Galveston, Johnson, Kaufman, Montgomery, Parker, and Rockwall Counties will be eligible for waivers and extensions.

(4)

Beginning May 1, 2004, motorists in Chambers, Liberty, and Waller Counties will be eligible for waivers and extensions.

(b)- (e)

(No change.)

§114.53.Inspection and Maintenance Fees.

(a)

The following fees must be paid for an emissions inspection of a vehicle at an inspection station. This fee shall include one free retest should the vehicle fail the emissions inspection, provided that the motorist has the retest performed at the same station where the vehicle originally failed and submits, prior to the retest, a properly completed Vehicle Repair Form showing that emissions-related repairs were performed and the retest is conducted within 15 days of the initial emissions test.

(1)- (2)

(No change.)

(3)

Beginning May 1, 2002, any emissions inspection station required to conduct an acceleration simulation mode (ASM-2) test and test in accordance with §114.50(a)(2)(C) and (D) and (4)(C) and (D) of this title shall collect a fee of $22.50 and shall remit $2.00 to the DPS.

(4)

Beginning May 1, 2003, any emissions inspection station required to conduct an ASM- 2 [ acceleration simulation mode ] test and OBD test in accordance with §114.50(a)(3) and (4)(E) and (F) of this title shall collect a fee of $22.50 and shall remit $2.00 to the DPS.

(5)

Beginning May 1, 2004, any emissions inspection station required to conduct an ASM-2 test and OBD test in accordance with §114.50(a)(4)(G) and (H) of this title shall collect a fee of $22.50 and shall remit $2.00 to the DPS.

(b)- (c)

(No change.)

This agency hereby certifies that the proposal has been reviewed by legal counsel and found to be within the agency's legal authority to adopt.

Filed with the Office of the Secretary of State, on August 11, 2000.

TRD-200005612

Margaret Hoffman

Director, Environmental Law Division

Texas Natural Resource Conservation Commission

Earliest possible date of adoption: September 24, 2000

For further information, please call: (512) 239-0348


Subchapter H. LOW EMISSION FUELS

3. LOW SULFUR GASOLINE

30 TAC §114.322, 114.325 - 114.327, 114.329

The Texas Natural Resource Conservation Commission (commission) proposes new §114.322, Control Requirements for Sulfur; §114.325, Approved Sulfur Test Methods; §114.326, Testing and Recordkeeping Requirements; §114.327, Exemptions; and §114.329, Affected Counties and Compliance Dates. The commission proposes these new sections in Chapter 114, Control of Air Pollution from Motor Vehicles; Subchapter H, Low Emission Fuels; new Division 3, Low Sulfur Gasoline; and revisions to the state implementation plan (SIP) in order to control ground-level ozone in the Houston/Galveston (HGA), Beaumont/Port Arthur (BPA), and Dallas/Fort Worth (DFW) ozone nonattainment areas; and the 95-county central and eastern Texas region.

BACKGROUND AND SUMMARY OF THE FACTUAL BASIS FOR THE PROPOSED RULES

The HGA ozone nonattainment area is classified as Severe-17 under the Federal Clean Air Act (FCAA) Amendments of 1990 (42 United States Code (USC), §§7401 et seq.), and therefore is required to attain the one-hour ozone standard of 0.12 parts per million (ppm) by November 15, 2007. The HGA area, defined by Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller Counties, has been working to develop a demonstration of attainment in accordance with 42 USC, §7410. On January 4, 1995, the state submitted the first of its Post-1996 SIP revisions for HGA.

The January 1995 SIP consisted of urban airshed model (UAM) modeling for 1988 and 1990 base-case episodes, adopted rules to achieve a 9% rate-of-progress (ROP) reduction in volatile organic compounds (VOC), and a commitment schedule for the remaining ROP and attainment demonstration elements. At the same time, but in a separate action, the State of Texas filed for the temporary nitrogen oxides (NO x ) waiver allowed by 42 USC, §7511a(f). The January 1995 SIP and the NO x waiver were based on early base-case episodes which marginally exhibited model performance in accordance with the United States Environmental Protection Agency (EPA) modeling performance standards, but which had a limited data set as inputs to the model. In 1993 and 1994, the commission was engaged in an intensive data-gathering exercise known as the COAST study. The state believed that the enhanced emissions inventory, expanded ambient air quality and meteorological monitoring, and other elements would provide a more robust data set for modeling and other analysis, which would lead to modeling results that the commission could use to better understand the nature of the ozone air quality problem in the HGA area.

Around the same time as the 1995 submittal, EPA policy regarding SIP elements and timelines went through changes. Two national programs in particular resulted in changing deadlines and requirements. The first of these programs was the Ozone Transport Assessment Group. This group grew out of a March 2, 1995 memo from Mary Nichols, former EPA Assistant Administrator for Air and Radiation, that allowed states to postpone completion of their attainment demonstrations until an assessment of the role of transported ozone and precursors had been completed for the eastern half of the nation, including the eastern portion of Texas. Texas participated in this study, and it has been concluded that Texas does not significantly contribute to ozone exceedances in the Northeastern United States. The other major national initiative that has impacted the SIP planning process is the revisions to the national ambient air quality standard (NAAQS) for ozone. The EPA promulgated a final rule on July 18, 1997 changing the ozone standard to an eight-hour standard of 0.08 ppm. In November 1996, concurrent with the proposal of the standards, the EPA proposed an interim implementation plan (IIP) that it believed would help areas like HGA transition from the old to the new standard. In an attempt to avoid a significant delay in planning activities, Texas began to follow this guidance, and readjusted its modeling and SIP development timelines accordingly. When the new standard was published, the EPA decided not to publish the IIP, and instead stated that, for areas currently exceeding the one-hour ozone standard, that standard would continue to apply until it is attained. The FCAA requires that HGA attain the standard by November 15, 2007.

The EPA issued revised draft guidance for areas such as HGA that do not attain the one-hour ozone standard. The commission adopted on May 6, 1998 and submitted to the EPA on May 19, 1998 a revision to the HGA SIP which contained the following elements in response to the EPA's guidance: UAM modeling based on emissions projected from a 1993 baseline out to the 2007 attainment date; an estimate of the level of VOC and NO x reductions necessary to achieve the one-hour ozone standard by 2007; a list of control strategies that the state could implement to attain the one-hour ozone standard; a schedule for completing the other required elements of the attainment demonstration; a revision to the Post-1996 9% ROP SIP that remedied a deficiency that the EPA believed made the previous version of that SIP unapprovable; and evidence that all measures and regulations required by Subpart 2 of Title I of the FCAA to control ozone and its precursors have been adopted and implemented, or are on an expeditious schedule to be adopted and implemented.

In November 1998, the SIP revision submitted to the EPA in May 1998 became complete by operation of law. However, the EPA stated that it could not approve the SIP until specific control strategies were modeled in the attainment demonstration. The EPA specified a submittal date of November 15, 1999 for this modeling. In a letter to the EPA dated January 5, 1999, the state committed to model two strategies showing attainment.

As the HGA modeling protocol evolved, the state eventually selected and modeled seven basic modeling scenarios. As part of this process, a group of HGA stakeholders worked closely with commission staff to identify local control strategies for the modeling. Some of the scenarios for which the stakeholders requested evaluation included options such as California-type fuel and vehicle programs as well as an acceleration simulation mode equivalent motor vehicle inspection and maintenance program. Other scenarios incorporated the estimated reductions in emissions that were expected to be achieved throughout the modeling domain as a result of the implementation of several voluntary and mandatory statewide programs adopted or planned independently of the SIP. It should be made clear that the commission did not propose that any of these strategies be included in the ultimate control strategy submitted to the EPA in 2000. The need for and effectiveness of any controls which may be implemented outside the HGA eight-county area will be evaluated on a county-by-county basis.

The SIP revision was adopted by the commission on October 27, 1999, submitted to the EPA by November 15, 1999, and contained the following elements: photochemical modeling of potential specific control strategies for attainment of the one-hour ozone standard in the HGA area by the attainment date of November 15, 2007; an analysis of seven specific modeling scenarios reflecting various combinations of federal, state, and local controls in HGA (additional scenarios H1 and H2 build upon Scenario VIf); identification of the level of reductions of VOC and NO x necessary to attain the one-hour ozone standard by 2007; a 2007 mobile source budget for transportation conformity; identification of specific source categories which, if controlled, could result in sufficient VOC and/or NO x reductions to attain the standard; a schedule committing to submit by April 2000 an enforceable commitment to conduct a mid-course review; and a schedule committing to submit modeling and adopted rules in support of the attainment demonstration by December 2000.

The April 19, 2000 SIP revision for HGA contained the following enforceable commitments by the state: to quantify the shortfall of NO x reductions needed for attainment; to list and quantify potential control measures to meet the shortfall of NO x reductions needed for attainment; to adopt the majority of the necessary rules for the HGA attainment demonstration by December 31, 2000, and to adopt the rest of the shortfall rules as expeditiously as practical, but no later than July 31, 2001; to submit a Post-99 ROP plan by December 31, 2000; to perform a mid-course review by May 1, 2004; and to perform modeling of mobile source emissions using the EPA mobile source emissions model (MOBILE6), to revise the on-road mobile source budget as needed, and to submit the revised budget within 24 months of the model's release. In addition, if a conformity analysis is to be performed between 12 months and 24 months after the MOBILE6 release, the state will revise the motor vehicle emissions budget (MVEB) so that the conformity analysis and the SIP MVEB are calculated on the same basis.

In order for the state to have an approvable attainment demonstration, EPA has indicated that the state must adopt those strategies modeled in the November submittal and then adopt sufficient controls to close the remaining gap in NO x emissions. The modeling included in this proposal indicates a gap of an additional 77.98 tons per day (tpd) of NO x reductions is necessary for an approvable attainment demonstration.

The emission reduction requirements included as part of this SIP revision represent substantial, intensive efforts on the part of stakeholder coalitions in the HGA area. These coalitions, involving local governmental entities, elected officials, environmental groups, industry, consultants, and the public, as well as the commission and the EPA, have worked diligently to identify and quantify potential control strategy measures for the HGA attainment demonstration. Local officials from the HGA area have formally submitted a resolution to the commission, requesting the inclusion of many specific emission reduction strategies.

The current SIP revision contains rules, enforceable commitments, and photochemical modeling analyses in support of the HGA ozone attainment demonstration. In addition, this SIP contains Post-1999 ROP plans for the milestone years 2002 and 2005, and for the attainment year 2007. The SIP also contains enforceable commitments to implement further measures, if needed, in support of the HGA attainment demonstration, as well as a commitment to perform and submit a mid-course review.

The HGA ozone nonattainment area will need to ultimately reduce NOx more than 750 tpd to reach attainment with the one-hour standard. In addition, a VOC reduction of about 25% will have to be achieved. Adoption of the Low Sulfur Gasoline (LSG) program will contribute to attainment and maintenance of the one-hour ozone standard in the HGA, BPA, and DFW ozone nonattainment areas, as well as the 95-county central and eastern Texas area. An LSG program also should contribute to a successful demonstration of transportation conformity in the HGA, BPA, and DFW nonattainment areas.

These proposed rules are one element of the control strategy for the HGA Post-1999 ROP/Attainment Demonstration SIP. The purpose of these proposed rules is to establish a regional LSG air pollution control strategy in the counties located within the DFW, BPA, and HGA ozone nonattainment areas, and in an additional 95 central and eastern Texas counties, to reduce NOx necessary for the counties included in the HGA ozone nonattainment area to be able to demonstrate attainment with the one-hour ozone NAAQS.

These proposed rules will implement a regional LSG program requiring gasoline used for both on-road and off-road applications in the DFW, BPA, and HGA ozone nonattainment areas and the 95-county central and eastern Texas region to meet the LSG standards. The use of LSG will lower the emissions of NOx and other pollutants from fuel combustion. Because NO x is a precursor to ground-level ozone formation, reduced NO x emissions will result in ground-level ozone reductions. To comply with the state LSG regulations, gasoline producers and importers must ensure that gasoline distributed to areas required to participate in the LSG program meets the specifications stated in these proposed rules. The proposed rules require that beginning May 1, 2004 all gasoline produced for delivery and ultimate sale to the consumer in the affected area does not exceed 15 ppm sulfur.

The proposed new LSG rules will require LSG for the eight HGA ozone nonattainment area counties, which include Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller Counties; the four DFW ozone nonattainment area counties, which include Collin, Dallas, Denton, and Tarrant Counties; the three BPA ozone nonattainment area counties, which include Hardin, Jefferson, and Hardin Counties; and the 95 central and eastern Texas region counties which include Anderson, Angelina, Aransas, Atascosa, Austin, Bastrop, Bee, Bell, Bexar, Bosque, Bowie, Brazos, Burleson, Caldwell, Calhoun, Camp, Cass, Cherokee, Colorado, Comal, Cooke, Coryell, De Witt, Delta, Ellis, Falls, Fannin, Fayette, Franklin, Freestone, Goliad, Gonzales, Grayson, Gregg, Grimes, Guadalupe, Harrison, Hays, Henderson, Hill, Hood, Hopkins, Houston, Hunt, Jackson, Jasper, Johnson, Karnes, Kaufman, Lamar, Lavaca, Lee, Leon, Limestone, Live Oak, Madison, Marion, Matagorda, McLennan, Milam, Morris, Nacogdoches, Navarro, Newton, Nueces, Panola, Parker, Polk, Rains, Red River, Refugio, Robertson, Rockwall, Rusk, Sabine, San Jacinto, San Patricio, San Augustine, Shelby, Smith, Somervell, Titus, Travis, Trinity, Tyler, Upshur, Van Zandt, Victoria, Walker, Washington, Wharton, Williamson, Wilson, Wise, and Wood Counties.

The commission developed an LSG ozone control strategy which requires gasoline content limits more restrictive than federal gasoline regulations. Currently, the HGA and DFW ozone nonattainment areas are required to use federal reformulated gasoline (RFG). In these areas, federal rules prohibit the sale of gasoline which is not certified by the EPA as federal RFG. Consequently, gasoline in these areas will have to continue to meet the federal RFG requirements in addition to the proposed LSG rules. In addition to the federal RFG regulations, the current federal regulations governing gasoline quality in Title 40 Code of Federal Regulations (40 CFR) Part 80, Regulation of Fuels and Fuel Additives; Subpart H, Gasoline Sulfur; §80.195, What Are the Gasoline Sulfur Standards for Refiners and Importers?; establish limits for sulfur content in gasoline used in motor vehicle applications. These federal regulations limit sulfur in gasoline, beginning January 1, 2006, to a 30 ppm average and an 80 ppm cap.

The commission is concurrently submitting, as part of the SIP and with this proposed rulemaking, a waiver request in accordance with the 42 USC, §7545(c)(4)(C), to implement this proposed LSG rule which is more stringent than the federal sulfur control rules. This proposed waiver and SIP submittal is available to the public by contacting Heather Evans at (512) 239-1970.

Modeling assessing the benefits of this NO x emission reduction strategy demonstrated that significant emission reductions could be achieved from using an LSG as specified by the commission requirements. By the year 2007, the LSG program will reduce NO x emissions in the HGA ozone nonattainment area by 1.15 tpd, and in all affected areas by 4.98 tpd. The commission anticipates that production costs will increase from $.03 to $.07 per gallon of gasoline to comply with the rules.

The commission solicits comment regarding the possible benefits of controlling components of gasoline other than sulfur by which equivalent emission reductions could be achieved as a possible alternative to the controls on sulfur as described in this proposal.

The commission solicits comment on additional flexibilities relating to rule content and implementation which have not been addressed in this or other concurrent rulemakings. These flexibilities may be available for both mobile and stationary sources. Additional flexibilities may also be achieved through innovative and/or emerging technology which may become available in the future. Additional sources of funds for incentive programs may become available to substitute for some of the measures considered here.

SECTION BY SECTION DISCUSSION

The proposed new §114.322 establishes the control requirement that the sulfur content in gasoline shall not exceed 15 ppm sulfur in the affected areas. This 15 ppm state sulfur cap is more stringent than the federal 30 ppm average and 80 ppm cap.

The proposed new §114.325 establishes the American Society for Testing and Materials (ASTM) Test Method D2622-98 (Standard Test Method for Sulfur in Petroleum Products by Wavelength Dispersive X-ray Fluorescence Spectrometry), dated 1998, or ASTM D5453-00 (Standard Test Method for Determination of Total Sulfur in Light Hydrocarbons, Motor Fuels and Oils by Ultraviolet Fluorescence), dated 2000, as the approved test methods to determine sulfur content in gasoline.

The proposed new §114.326 establishes the testing and recordkeeping requirements for the LSG program. These proposed requirements stipulate that producers and importers are required to test each batch of fuel for its sulfur content, maintain records of this testing for two years, and include a certification statement on the product transfer document that certifies that the fuel being transferred into the affected areas meets the 15 ppm sulfur standard.

The proposed new §114.327 provides exemptions to the LSG program regulations. These exemptions stipulate that gasoline solely intended for use as aviation gasoline is exempt from the proposed sulfur standard, the owner or operator of a retail fuel dispensing facility is exempt from the proposed testing requirements, and gasoline that does not meet the proposed sulfur standard is not prohibited from being transferred, placed, stored, and/or held within the affected counties so long as it is not ultimately used to power a gasoline-fueled spark-ignition engine in the affected counties.

The proposed new §114.329 establishes the compliance date and coverage area that is required to comply with the requirements of the LSG program. This section lists the affected counties for the DFW, BPA, and HGA ozone nonattainment areas, and the counties included in the 95-county region.

FISCAL NOTE: COSTS TO STATE AND LOCAL GOVERNMENT

John Davis, Technical Specialist with Strategic Planning and Appropriations, determined that for the first five-year period the proposed new sections are in effect, the commission anticipates no significant fiscal implications for any single unit of state and local government as a result of administration or enforcement of the proposed new sections. The commission estimates the total annual fuel related fiscal impact to state and local governments in the counties affected by the new sections to be approximately $20 to $47 per vehicle per year following implementation of LSG fuel standards on May 1, 2004.

The proposed new sections will require LSG fuel for on-road and non-road use within the eight-county HGA, the three-county BPA, and the four-county DFW ozone nonattainment areas, along with 95 additional counties in the central and eastern Texas region. The HGA ozone nonattainment area consists of Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller Counties; the BPA nonattainment area consists of Hardin, Jefferson, and Orange Counties; the DFW ozone nonattainment area consists of Collin, Dallas, Denton, and Tarrant Counties; and the 95 additional central and eastern Texas counties include Anderson, Angelina, Aransas, Atascosa, Austin, Bastrop, Bee, Bell, Bexar, Bosque, Bowie, Brazos, Burleson, Caldwell, Calhoun, Camp, Cass, Cherokee, Colorado, Comal, Cooke, Coryell, De Witt, Delta, Ellis, Falls, Fannin, Fayette, Franklin, Freestone, Goliad, Gonzales, Grayson, Gregg, Grimes, Guadelupe, Harrison, Hays, Henderson, Hill, Hood, Hopkins, Houston, Hunt, Jackson, Jasper, Johnson, Karnes, Kaufman, Lamar, Lavaca, Lee, Leon, Limestone, Live Oak, Madison, Marion, Matagorda, McLennan, Milam, Morris, Nacogdoches, Navarro, Newton, Nueces, Panola, Parker, Polk, Rains, Red River, Refugio, Robertson, Rockwall, Rusk, Sabine, San Jacinto, San Patricio, San Augustine, Shelby, Smith, Somerville, Titus, Travis, Trinity, Tyler, Upshur, Van Zandt, Victoria, Walker, Washington, Wharton, Williamson, Wilson, Wise, and Wood Counties.

The proposed new sections are one element of the proposed HGA Post-1999 ROP/Attainment Demonstration SIP. A SIP is a plan developed for any region where existing (measured and/or estimated) ambient pollutant levels exceed the level specified in a national standard. The plan establishes a control strategy that provides emission reductions necessary for attainment and maintenance of the national standards.

In order to comply with the proposed new sections, beginning May 1, 2004, gasoline fuel producers and importers must ensure that all gasoline distributed to affected areas shall not exceed 15 ppm sulfur.

The EPA analysis Regulatory Impact Analysis: Control of Air Pollution from Motor Vehicles: Tier 2 Vehicle Emissions Standards and Gas Sulfur Control Requirements and the responses to public comment from the California Air Resource Board (CARB) regarding adoption of federal Phase 3 gasoline standards, indicates that the anticipated cost of producing gasoline to the May 1, 2004 standard will range from $.03 to $.07 per gallon. The commission estimates that the increased production costs will raise the cost for this fuel at the pump by $.03 to $.07 per gallon. In addition, the proposed new sections will require gasoline producers and importers who provide fuel to the affected areas to test their fuel for compliance with the standard, maintain records for two years, and include certification statements regarding sulfur content compliance on product transfer documents.

The proposed rules contain several exemptions to the LSG program regulations, which are: gasoline solely intended for use as aviation gasoline is exempt from the proposed LSG standards; the owner or operator of a retail fuel dispensing facility is exempt from the proposed testing requirements; and gasoline that does not meet the proposed LSG standard is not prohibited from being transferred, placed, stored, or held within the affected counties as long as it is not ultimately used to power a gasoline fueled spark-ignition engine in the affected counties.

The following analysis in this fiscal note only considers on-road gasoline powered vehicles. Vehicle counts for non-road gasoline powered vehicles is not available.

Units of state and local government that own or operate gasoline powered vehicles within the affected counties will likely be required to pay an additional $.03 to $.07 per gallon for gasoline that meets the proposed LSG requirements following the May 1, 2004 deadline. Approximately 48,992 state and local government vehicles within the affected areas consumed approximately 33 million gallons of gasoline in 1999. Based on a 1.5% growth rate, an estimated 52,778 gasoline fueled vehicles would use approximately 36 million gallons of fuel in 2004. The total annual fuel related fiscal impact to units of state and local governments in 2004 would range from approximately $705,000 to $1.6 million or approximately $13 to $31 per vehicle for 2004 (May -December 2004) and then approximately $1 million to $2.5 million or approximately $20 to $47 per year per vehicle afterward.

PUBLIC BENEFIT AND COSTS

Mr. Davis also determined that for the first five years the proposed new sections are in effect, the public benefit anticipated from enforcement of and compliance with the proposed new sections will be the potential reduction of on-road and off-road mobile source emissions, contribution toward demonstration of attainment and maintenance with the ozone NAAQS for the HGA, BPA, and DFW ozone nonattainment areas, and potentially improved air quality for all counties affected by the new sections.

The commission does not anticipate significant fiscal implications for any single owner or operator of gasoline fueled vehicles as a result of administration or enforcement of the proposed new sections. The commission anticipates that gasoline producers that supply fuel to the affected counties will incur additional costs to produce fuel that meets the proposed LSG standards. The cost of producing this LSG fuel is estimated to be approximately $.03 to $.07 per gallon more than for current gasoline. The commission estimates that gasoline prices will increase by an additional $.03 to $.07 per gallon following implementation of the proposed LSG standards.

The commission estimates that approximately 11,357,736 privately owned and operated gasoline fueled vehicles in the affected counties consumed approximately 7.6 billion gallons of gasoline in 1999. Based on a 1.5% growth rate, an estimated 12,235,507 privately owned and operated gasoline fueled vehicles would use approximately eight billion gallons of gasoline in 2004. The total annual fuel related fiscal impact to units of individuals and businesses in the affected areas in 2004 would range from approximately $163 million to $380 million or approximately $13 to $31 per vehicle for 2004 (May -December 2004) and then approximately $247 million to $578 million or approximately $20 to $47 per year per vehicle afterward.

The commission anticipates significant increases to capital and operating costs in order for refineries to meet the proposed May 1, 2004 standard. An estimated cost to refineries to decrease sulfur content in gasoline to 15 ppm is not available; however, an EPA cost study that shows the costs to refine gasoline to 30 ppm provides an indication of the overall cost to refineries to meet the May 1, 2004 15 ppm standard. According to EPA analysis found in the Regulatory Impact Analysis: Control of Air Pollution from Motor Vehicles: Tier 2 Vehicle Emissions Standards and Gas Sulfur Control Requirements , the estimated capital costs for a typical refinery to decrease the sulfur content in gasoline to 30 ppm would be approximately $44 million and the average annual operating cost would be approximately $16 million. The commission anticipates no significant additional costs for gasoline producers and importers associated with required records retention and certification statements. Likewise, the commission anticipates no additional costs to producers for testing LSG gasoline, because producers are already testing their fuel for compliance with federal regulations and industry standards.

SMALL AND MICRO-BUSINESS ASSESSMENT

The commission does not anticipate fiscal implications which have an adverse fiscal impact on any small business or micro-business as a result of administration or enforcement of the proposed new sections. There are no known gasoline producers or importers that would be considered small or micro-businesses. However, the commission anticipates that many independent gasoline retailers within the affected counties are small or micro-businesses. Therefore, production costs of approximately $.03 to $.07 per gallon are not anticipated to affect small or micro-business except to pass the increased costs of production through to consumers. The fiscal implications for small or micro-businesses within the affected areas would include additional costs of approximately $.03 to $.07 per gallon for LSG beginning May 1, 2004. The total annual fuel-related costs would depend on the amount of fuel used by the business. On an average basis, the annual fuel-related cost to small or micro-businesses within the affected areas would be approximately $20 to $47 per vehicle per year.

DRAFT REGULATORY IMPACT ANALYSIS DETERMINATION

The commission reviewed the proposed rulemaking in light of the regulatory analysis requirements of Texas Government Code, §2001.0225, and determined that the proposed rulemaking is subject to §2001.0225 because it meets the definition of a "major environmental rule" as defined in that statute. "Major environmental rule" means a rule the specific intent of which is to protect the environment or reduce risks to human health from environmental exposure and that may adversely affect in a material way the economy, a sector of the economy, productivity, competition, jobs, the environment, or the public health and safety of the state or a sector of the state. The new sections to Chapter 114 are intended to protect the environment or reduce risks to human health from environmental exposure to ozone and could affect in a material way, a sector of the economy, competition, and the environment due to its impact on the fuel manufacturing and distribution network of the state. The new sections are intended to implement a LSG air pollution control program as part of the strategy to reduce NO x emissions necessary for the counties included in the eight-county HGA, three-county BPA, and four-county DFW ozone nonattainment areas to be able to demonstrate attainment and maintenance of the ozone NAAQS. The proposed new sections are one element of the proposed HGA Post-1999 ROP/Attainment Demonstration SIP. Although the proposed new sections meet the definition of a "major environmental rule" as defined in the Texas Government Code, §2001.0225 only applies to a major environmental rule, the result of which is to: (1) exceed a standard set by federal law, unless the rule is specifically required by state law; (2) exceed an express requirement of state law, unless the rule is specifically required by federal law; (3) exceed a requirement of a delegation agreement or contract between the state and an agency or representative of the federal government to implement a state and federal program; or (4) adopt a rule solely under the general powers of the agency instead of under a specific state law.

This proposed rulemaking action does not meet any of these four applicability requirements. Specifically, the LSG requirements within these proposed rules were developed in order to meet the ozone NAAQS set by the EPA under 42 USC, §7409, and therefore meet a federal requirement. Provisions of 42 USC, §7410, require states to adopt a SIP which provides for "implementation, maintenance, and enforcement" of the primary NAAQS in each air quality control region of the state. While §7410 does not require specific programs, methods, or reductions in order to meet the standard, state SIPs must include "enforceable emission limitations and other control measures, means or techniques (including economic incentives such as fees, marketable permits, and auctions of emissions rights), as well as schedules and timetables for compliance as may be necessary or appropriate to meet the applicable requirements of this chapter," (meaning Chapter 85, Air Pollution Prevention and Control). It is true that 42 USC does require some specific measures for SIP purposes, like the inspection and maintenance program, but those programs are the exception, not the rule, in the SIP structure of 42 USC. The provisions of 42 USC recognize that states are in the best position to determine what programs and controls are necessary or appropriate in order to meet the NAAQS. This flexibility allows states, affected industry, and the public, to collaborate on the best methods for attaining the NAAQS for the specific regions in the state. Even though 42 USC allows states to develop their own programs, this flexibility does not relieve a state from developing a program that meets the requirements of §7410. Thus, while specific measures are not generally required, the emission reductions are required. States are not free to ignore the requirements of §7410 and must develop programs to assure that the nonattainment areas of the state will be brought into attainment on schedule.

The requirement to provide a fiscal analysis of proposed regulations in the Texas Government Code was amended by Senate Bill 633 (SB 633) during the 75th Legislative Session, 1999. The intent of SB 633 was to require agencies to conduct a regulatory impact analysis (RIA) of extraordinary rules. These are identified in the statutory language as major environmental rules that will have a material adverse impact and will exceed a requirement of state law, federal law, or a delegated federal program, or are adopted solely under the general powers of the agency. With the understanding that this requirement would seldom apply, the commission provided a cost estimate for SB 633 that concluded "based on an assessment of rules adopted by the agency in the past, it is not anticipated that the bill will have significant fiscal implications for the agency due to its limited application." The commission also noted that the number of rules that would require assessment under the provisions of the bill was not large. This conclusion was based, in part, on the criteria set forth in the bill that exempted proposed rules from the full analysis unless the rule was a major environmental rule that exceeds a federal law. As previously discussed, 42 USC does not require specific programs, methods, or reductions in order to meet the NAAQS; thus, states must develop programs for each nonattainment area to ensure that area will meet the attainment deadlines. Because of the ongoing need to address nonattainment issues, the commission routinely proposes and adopts SIP rules. The legislature is presumed to understand this federal scheme. If each rule proposed for inclusion in the SIP was considered to be a major environmental rule that exceeds federal law, then every SIP rule would require the full RIA contemplated by SB 633. This conclusion is inconsistent with the conclusions reached by the commission in its cost estimate and by the Legislative Budget Board (LBB) in its fiscal notes. Since the legislature is presumed to understand the fiscal impacts of the bills it passes, and that presumption is based on information provided by state agencies and the LBB, the commission believes that the intent of SB 633 was only to require the full RIA for rules that are extraordinary in nature. While the SIP rules will have a broad impact, that impact is no greater than is necessary or appropriate to meet the requirements of the FCAA. For these reasons, rules proposed for inclusion in the SIP fall under the exception in Texas Government Code, §2001.0225(a), because they are required by federal law. The commission performed photochemical grid modeling which predicts that NO x emission reductions, such as those required by these rules, will result in reductions in ozone formation in the HGA ozone nonattainment area. This rulemaking does not exceed an express requirement of state law. This rulemaking is intended to obtain NO x emission reductions which will result in reductions in ozone formation in the HGA, BPA, and DFW ozone nonattainment areas and the 95-county central and eastern Texas region, and help bring HGA into compliance with the air quality standards established under federal law as NAAQS for ozone. The rulemaking does not exceed a standard set by federal law, exceed an express requirement of state law (unless specifically required by federal law), or exceed a requirement of a delegation agreement. The rulemaking was not developed solely under the general powers of the agency, but was specifically developed to meet the NAAQS established under federal law and authorized under Texas Clean Air Act (TCAA), §§382.011, 382.012, 382.017, 382.019, 382.037(g), and 382.039.

The commission invites public comment on the draft regulatory impact analysis.

TAKINGS IMPACT ASSESSMENT

The commission prepared a takings impact assessment for these proposed rules in accordance with Texas Government Code, §2007.043. The following is a summary of that assessment. The specific purpose of the proposed rulemaking is to establish an LSG program which will act as an air pollution control strategy to reduce NO x emissions necessary for the eight-county HGA and the four-county DFW ozone nonattainment areas, to be able to demonstrate attainment and maintenance of the ozone NAAQS. Promulgation and enforcement of the proposed rules may possibly burden private, real property because this proposed rulemaking action may result in investment in the permanent installation of new refinery processing equipment. Although the proposed rules do not directly prevent a nuisance or prevent an immediate threat to life or property, they do prevent a real and substantial threat to public health and safety, and partially fulfill a federal mandate under 42 USC, §7410. Specifically, the emission limitations and control requirements within this proposal have been developed in order to meet the ozone NAAQS set by the EPA under 42 USC, §7409. States are primarily responsible for ensuring attainment and maintenance of the NAAQS once the EPA has established them. Under 42 USC, §7410 and related provisions, states must submit, for approval by the EPA, SIPs that provide for the attainment and maintenance of NAAQS through control programs directed to sources of the pollutants involved. Therefore, the purpose of the proposed rules is to implement cleaner burning gasoline which is necessary for the HGA and DFW ozone nonattainment areas to meet the air quality standards established under federal law as NAAQS. Consequently, the exemption which applies to these proposed rules is that of an action reasonably taken to fulfill an obligation mandated by federal law; therefore, these proposed rules do not constitute a takings under Texas Government Code, Chapter 2007.

CONSISTENCY WITH THE COASTAL MANAGEMENT PROGRAM

The commission determined that the proposed rulemaking relates to an action or actions subject to the Texas Coastal Management Program (CMP) in accordance with the Coastal Coordination Act of 1991, as amended (Texas Natural Resources Code, §§33.201 et seq.), and the commission rules in 30 TAC Chapter 281, Subchapter B, concerning Consistency with the CMP. As required by 31 TAC §505.11(b)(2) and 30 TAC §281.45(a)(3), relating to actions and rules subject to the CMP, commission rules governing air pollutant emissions must be consistent with the applicable goals and policies of the CMP. The commission reviewed this action for consistency with the CMP goals and policies in accordance with the rules of the Coastal Coordination Council, and determined that the action is consistent with the applicable CMP goals and policies. The CMP goal applicable to this rulemaking action is the goal to protect, preserve, and enhance the diversity, quality, quantity, functions, and values of coastal natural resource areas (31 TAC §501.12(1)). No new sources of air contaminants will be authorized and NO x air emissions will be reduced as a result of these rules. The CMP policy applicable to this rulemaking action is the policy that commission rules comply with regulations in 40 CFR, to protect and enhance air quality in the coastal area (31 TAC §501.14(q)). This rulemaking action complies with 40 CFR 50, National Primary and Secondary Ambient Air Quality Standards, and 40 CFR 51, Requirements for Preparation, Adoption, and Submittal Of Implementation Plans. Therefore, in compliance with 31 TAC §505.22(e), this rulemaking action is consistent with CMP goals and policies.

ANNOUNCEMENT OF HEARINGS

The commission will hold public hearings on this proposal at the following times and locations: September 18, 2000, 10:00 a.m., Lone Star Convention Center, 9055 Airport Road (FM 1484), Conroe; September 18, 2000, 7:00 p.m., Lake Jackson Civic Center, 333 Highway 332 East, Lake Jackson; September 19, 2000, 10:00 a.m. and 7:00 p.m., George Brown Convention Center, 1001 Avenida de Las Americas, Houston; September 20, 2000, 9:00 a.m., VFW Hall, 6202 George Bush Drive, Katy; September 20, 2000, 6:00 p.m., East Harris County Community Center, 7340 Spencer, Pasadena; September 21, 2000, 10:00 a.m., Southeast Texas Regional Airport Media Room, 6000 Airline Drive, Beaumont; September 21, 2000, 2:00 p.m., Amarillo City Commission Chambers, City Hall, 509 East 7th Avenue, Amarillo; September 21, 2000, 6:00 p.m., Charles T. Doyle Convention Center, 21st Street at Phoenix Lane, Texas City; September 22, 2000, 10:00 a.m., Dayton High School, 2nd Floor Lecture Room, 3200 North Cleveland Street, Dayton; September 22, 2000, 11:00 a.m., El Paso City Council Chambers, 2 Civic Center Plaza, 2nd Floor, El Paso; September 22, 2000, 2:00 p.m., North Central Texas Council of Governments, 2nd Floor Board Room, 616 Six Flags Drive, Suite 200, Arlington; and September 25, 2000, 10:00 a.m., Texas Natural Resource Conservation Commission, 12100 North I-35, Building E, Room 201S, Austin. The hearings are structured for the receipt of oral or written comments by interested persons. Registration will begin one hour prior to each hearing. Individuals may present oral statements when called upon in order of registration. A four-minute time limit will be established at each hearing to assure that enough time is allowed for every interested person to speak. Open discussion will not occur during each hearing; however, agency staff members will be available to discuss the proposal one hour before each hearing, and will answer questions before and after each hearing.

Persons with disabilities who have special communication or other accommodation needs, who are planning to attend a hearing, should contact the Office of Environmental Policy, Analysis, and Assessment at (512) 239-4900. Requests should be made as far in advance as possible.

SUBMITTAL OF COMMENTS

Written comments may be submitted to Heather Evans, Office of Environmental Policy, Analysis, and Assessment, MC 206, P.O. Box 13087, faxed to (512) 239-4808, or emailed to siprules@tnrcc.state.tx.us . All comments should reference Rule Log Number 2000-011F-114-AI. Comments must be received by 5:00 p.m., September 25, 2000. For further information, please contact Morris Brown at (512) 239-1438 or Alan Henderson at (512) 219-1510.

STATUTORY AUTHORITY

The new sections are proposed under Texas Water Code (TWC), §5.103, which authorizes the commission to adopt rules necessary to carry out its powers and duties under the TWC, and under Texas Health and Safety Code, TCAA, §382.017, which provides the commission the authority to adopt rules consistent with the policy and purposes of the TCAA. The new sections are also proposed under TCAA, §382.011, which authorizes the commission to control the quality of the state's air; §382.012, which authorizes the commission to prepare and develop a general, comprehensive plan for the control of the state's air; §382.019, which authorizes the commission to adopt rules to control and reduce emissions from engines used to propel land vehicles; §382.037(g), which authorizes the commission to regulate fuel content if it is demonstrated to be necessary for attainment of the NAAQS; and §382.039, which authorizes the commission to develop and implement transportation programs and other measures necessary to demonstrate attainment and protect the public from exposure to hazardous air contaminants from motor vehicles.

The proposed new sections implement TCAA, §382.002, relating to Policy and Purpose; §382.011, relating to General Powers and Duties; §382.012, relating to State Air Control Plan; §382.019, relating to Methods Used to Control and Reduce Emissions from Land Vehicles; and §382.039, relating to Attainment Program.

§114.322.Control Requirements for Sulfur.

No person shall sell, offer for sale, supply, or offer for supply, dispense, transfer, allow the transfer, place, store, or hold in any stationary tank, reservoir, or other container any gasoline containing more than 15 parts per million sulfur, on a per gallon basis, which may ultimately be used to power a gasoline-fueled spark-ignition engine in the counties listed in §114.329 of this title (relating to Affected Counties and Compliance Dates).

§114.325.Approved Sulfur Test Methods.

(a)

Compliance with the sulfur content requirements under §114.322 of this title (relating to Control Requirements for Sulfur) shall be determined by applying American Society for Testing and Materials (ASTM) Test Method D2622-98 (Standard Test Method for Sulfur in Petroleum Products by Wavelength Dispersive X-ray Fluorescence Spectrometry), dated 1998, or ASTM D5453-00 (Standard Test Method for Determination of Total Sulfur in Light Hydrocarbons, Motor Fuels and Oils by Ultraviolet Fluorescence), dated 2000.

(b)

Alternatives to the test methods prescribed in subsection (a) of this section may be used if validated by 40 Code of Federal Regulations 63, Appendix A, Test Method 301 (effective December 29, 1992). For the purposes of this paragraph, substitute "executive director" each place that Test Method 301 references "administrator."

§114.326.Testing and Recordkeeping Requirements.

(a)

Every producer or importer that has elected to sell, offer for sale, supply, or offer for supply gasoline in counties listed in §114.329 of this title (relating to Affected Counties and Compliance Dates) is subject to the requirements of this section.

(1)

Each producer or importer shall sample and test for the sulfur content in each final blend of gasoline which the producer has produced or imported, by collecting and analyzing a representative sample of gasoline taken from the final blend, using the methodologies specified in §114.325 of this title (relating to Approved Sulfur Test Methods). If a producer or importer blends gasoline components directly to pipelines, tank ships, railway tank cars, or trucks and trailers, the loading(s) shall be sampled and tested for the sulfur content by the producer, importer, or authorized contractor. The producer or importer shall maintain, for two years from the date of each sampling, records showing the sample date, identity of blend sampled, container or other vessel sampled, final blend volume, and sulfur content. All gasoline produced or imported by the producer or importer and not tested for sulfur by the producer or importer as required by this section shall be deemed to have a sulfur content exceeding the requirements in §114.322 of this title (relating to Control Requirements for Sulfur), unless the producer or importer demonstrates that the gasoline meets those requirements.

(2)

A producer or importer shall provide to the executive director any records required to be maintained by the producer or importer in accordance with this section within five days of a written request from the executive director if the request is received before expiration of the period during which the records are required to be maintained. Whenever a producer or importer fails to provide records regarding a final blend of gasoline in accordance with the requirements of this section, the final blend of gasoline shall be presumed to have been sold or supplied by the producer or importer in violation of the sulfur content requirements specified in §114.322 of this title.

(b)

For each final blend which is sold or supplied by a producer or importer from their production or import facility, and which contains volumes of gasoline that they have produced or imported and volumes that they neither produced nor imported, the producer or importer shall establish, maintain, and retain adequately organized records containing the following information:

(1)

the volume of gasoline in the final blend that was not produced or imported by the producer or importer, the identity of the persons(s) from whom such gasoline was acquired, the date(s) on which it was acquired, and the invoice representing the acquisition(s);

(2)

the sulfur content of the volume of gasoline in the final blend that was not produced or imported by the producer or importer, determined either by:

(A)

sampling and testing, by the producer or importer, of the acquired gasoline represented in the final blend; or

(B)

written sampling results and gasoline testing supplied by the person(s) from whom the gasoline was acquired; and

(3)

a producer or importer subject to subsection (b) of this section shall establish such records by the time the final blend triggering the requirements is sold or supplied from the production or import facility, and shall retain such records for two years from such date. During the period of required retention, the producer or importer shall make any of the records available to the executive director upon request.

(c)

All parties in the distribution chain (producers, importers, terminals, pipelines, truckers, rail carriers, and retail fuel dispensing outlets) subject to the provisions of §114.322 of this title must maintain copies or records of product transfer documents for a minimum of two years, and shall upon request, make such copies or records available to representatives of the commission, the EPA, or local air pollution agency having jurisdiction in the area. The product transfer documents must contain, at a minimum, the following information:

(1)

the date of transfer;

(2)

the name and address of the transferor;

(3)

the name and address of the transferee;

(4)

the volume of gasoline being transferred;

(5)

the location of the gasoline at the time of transfer; and

(6)

the following certification statement: "This product complies with the control requirements for sulfur specified in Title 30 Texas Administrative Code §114.322, and may be used in any Texas county requiring gasoline with a maximum sulfur content of 15 parts per million."

§114.327.Exemptions.

(a)

The following exemptions apply in the counties listed in §114.329 of this title (relating to Affected Counties and Compliance Dates).

(1)

All gasoline solely intended for use as aviation gasoline is exempt from §114.322 and §114.326 of this title (relating to Control Requirements for Sulfur; and Testing and Recordkeeping Requirements).

(2)

The owner or operator of a retail fuel dispensing facility is exempt from all requirements of §114.326 of this title except §114.326(c) of this title.

(b)

Gasoline that does not meet the requirements of §114.322 of this title is not prohibited from being transferred, placed, stored, and/or held within the counties listed in §114.329 of this title so long as it is not ultimately used to power a gasoline-fueled spark-ignition engine in the affected counties.

§114.329.Affected Counties and Compliance Dates.

Beginning May 1, 2004, all affected persons in the counties listed in paragraphs (1) - (4) of this section shall be in compliance with §§114.322, 114.325 - 114.327 of this title (relating to Control Requirements for Sulfur; Approved Sulfur Test Methods; Testing and Recordkeeping Requirements; and Exemptions):

(1)

Collin, Dallas, Denton, and Tarrant;

(2)

Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller;

(3)

Hardin, Jefferson, and Orange; and

(4)

Anderson, Angelina, Aransas, Atascosa, Austin, Bastrop, Bee, Bell, Bexar, Bosque, Bowie, Brazos, Burleson, Caldwell, Calhoun, Camp, Cass, Cherokee, Colorado, Comal, Cooke, Coryell, De Witt, Delta, Ellis, Falls, Fannin, Fayette, Franklin, Freestone, Goliad, Gonzales, Grayson, Gregg, Grimes, Guadalupe, Harrison, Hays, Henderson, Hill, Hood, Hopkins, Houston, Hunt, Jackson, Jasper, Johnson, Karnes, Kaufman, Lamar, Lavaca, Lee, Leon, Limestone, Live Oak, Madison, Marion, Matagorda, McLennan, Milam, Morris, Nacogdoches, Navarro, Newton, Nueces, Panola, Parker, Polk, Rains, Red River, Refugio, Robertson, Rockwall, Rusk, Sabine, San Jacinto, San Patricio, San Augustine, Shelby, Smith, Somervell, Titus, Travis, Trinity, Tyler, Upshur, Van Zandt, Victoria, Walker, Washington, Wharton, Williamson, Wilson, Wise, and Wood.

This agency hereby certifies that the proposal has been reviewed by legal counsel and found to be within the agency's legal authority to adopt.

Filed with the Office of the Secretary of State, on August 11, 2000.

TRD-200005646

Margaret Hoffman

Director, Environmental Law Division

Texas Natural Resource Conservation Commission

Earliest possible date of adoption: September 24, 2000

For further information, please call: (512) 239-0348


4. DIESEL EMULSION FUEL

30 TAC §§114.330 - 114.332, 114.336, 114.338, 114.339

The Texas Natural Resource Conservation Commission (commission) proposes new §114.330, Definitions; §114.331, Applicability; §114.332, Diesel Emulsion Standards; §114.336, Recordkeeping and Labeling; §114.338, Registration; and §114.339, Affected Counties and Compliance Dates. The commission proposes these revisions to Chapter 114, Control of Air Pollution From Motor Vehicles; Subchapter H, Low Emission Fuels; new Division 4, Diesel Emulsion Fuel; and corresponding revisions to the state implementation plan (SIP) in order to control ground-level ozone in the Houston/Galveston (HGA) ozone nonattainment area. These rules are designed to require use of a low-emission diesel fuel formulation called diesel emulsion for both on- road and non-road vehicles.

BACKGROUND AND SUMMARY OF THE FACTUAL BASIS FOR THE PROPOSED RULES

The HGA ozone nonattainment area is classified as Severe-17 under the Federal Clean Air Act (FCAA) Amendments of 1990 (42 United States Code (USC), §§7401 et seq.), and therefore is required to attain the one-hour ozone standard of 0.12 parts per million (ppm) by November 15, 2007. The HGA area, defined by Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller Counties, has been working to develop a demonstration of attainment in accordance with 42 USC, §7410. On January 4, 1995, the state submitted the first of its Post- 1996 SIP revisions for HGA.

The January 1995 SIP consisted of urban airshed model (UAM) modeling for 1988 and 1990 base-case episodes, adopted rules to achieve a 9% rate-of-progress (ROP) reduction in volatile organic compounds (VOC), and a commitment schedule for the remaining ROP and attainment demonstration elements. At the same time, but in a separate action, the State of Texas filed for the temporary nitrogen oxides (NO x ) waiver allowed by 42 USC, §7511a(f). The January 1995 SIP and the NO x waiver were based on early base-case episodes which marginally exhibited model performance in accordance with the United States Environmental Protection Agency (EPA) modeling performance standards, but which had a limited data set as inputs to the model. In 1993 and 1994, the commission was engaged in an intensive data-gathering exercise known as the COAST study. The state believed that the enhanced emissions inventory, expanded ambient air quality and meteorological monitoring, and other elements would provide a more robust data set for modeling and other analysis, which would lead to modeling results that the commission could use to better understand the nature of the ozone air quality problem in the HGA area.

Around the same time as the 1995 submittal, EPA policy regarding SIP elements and timelines went through changes. Two national programs in particular resulted in changing deadlines and requirements. The first of these programs was the Ozone Transport Assessment Group. This group grew out of a March 2, 1995 memo from Mary Nichols, former EPA Assistant Administrator for Air and Radiation, that allowed states to postpone completion of their attainment demonstrations until an assessment of the role of transported ozone and precursors had been completed for the eastern half of the nation, including the eastern portion of Texas. Texas participated in this study, and it has been concluded that Texas does not significantly contribute to ozone exceedances in the Northeastern United States. The other major national initiative that has impacted the SIP planning process is the revisions to the national ambient air quality standard (NAAQS) for ozone. The EPA promulgated a final rule on July 18, 1997 changing the ozone standard to an eight-hour standard of 0.08 ppm. In November 1996, concurrent with the proposal of the standards, the EPA proposed an interim implementation plan (IIP) that it believed would help areas like HGA transition from the old to the new standard. In an attempt to avoid a significant delay in planning activities, Texas began to follow this guidance, and readjusted its modeling and SIP development timelines accordingly. When the new standard was published, the EPA decided not to publish the IIP, and instead stated that, for areas currently exceeding the one-hour ozone standard, that standard would continue to apply until it is attained. The FCAA requires that HGA area attain the standard by November 15, 2007.

The EPA issued revised draft guidance for areas such as HGA that do not attain the one-hour ozone standard. The commission adopted on May 6, 1998 and submitted to EPA on May 19, 1998 a revision to the HGA SIP which contained the following elements in response to EPA's guidance: UAM modeling based on emissions projected from a 1993 baseline out to the 2007 attainment date; an estimate of the level of VOC and NO x reductions necessary to achieve the one-hour ozone standard by 2007; a list of control strategies that the state could implement to attain the one-hour ozone standard; a schedule for completing the other required elements of the attainment demonstration; a revision to the Post-1996 9% ROP SIP that remedied a deficiency that the EPA believed made the previous version of that SIP unapprovable; and evidence that all measures and regulations required by Subpart 2 of Title I of the FCAA to control ozone and its precursors have been adopted and implemented, or are on an expeditious schedule to be adopted and implemented.

In November 1998, the SIP revision submitted to the EPA in May 1998 became complete by operation of law. However, the EPA stated that it could not approve the SIP until specific control strategies were modeled in the attainment demonstration. The EPA specified a submittal date of November 15, 1999 for this modeling. In a letter to the EPA dated January 5, 1999, the state committed to model two strategies showing attainment.

As the HGA modeling protocol evolved, the state eventually selected and modeled seven basic modeling scenarios. As part of this process, a group of HGA stakeholders worked closely with commission staff to identify local control strategies for the modeling. Some of the scenarios for which the stakeholders requested evaluation included options such as California-type fuel and vehicle programs as well as an acceleration simulation mode equivalent motor vehicle inspection and maintenance program. Other scenarios incorporated the estimated reductions in emissions that were expected to be achieved throughout the modeling domain as a result of the implementation of several voluntary and mandatory statewide programs adopted or planned independently of the SIP. It should be made clear that the commission did not propose that any of these strategies be included in the ultimate control strategy submitted to the EPA in 2000. The need for and effectiveness of any controls which may be implemented outside the HGA eight-county area will be evaluated on a county-by-county basis.

The SIP revision was adopted by the commission on October 27, 1999, submitted to the EPA by November 15, 1999, and contained the following elements: photochemical modeling of potential specific control strategies for attainment of the one-hour ozone standard in the HGA area by the attainment date of November 15, 2007; an analysis of seven specific modeling scenarios reflecting various combinations of federal, state, and local controls in HGA (additional scenarios H1 and H2 build upon Scenario VIf); identification of the level of reductions of VOC and NO x necessary to attain the one-hour ozone standard by 2007; a 2007 mobile source budget for transportation conformity; identification of specific source categories which, if controlled, could result in sufficient VOC and/or NO x reductions to attain the standard; a schedule committing to submit by April 2000 an enforceable commitment to conduct a mid-course review; and a schedule committing to submit modeling and adopted rules in support of the attainment demonstration by December 2000.

The April 19, 2000 SIP revision for HGA contained the following enforceable commitments by the state: to quantify the shortfall of NO x reductions needed for attainment; to list and quantify potential control measures to meet the shortfall of NO x reductions needed for attainment; to adopt the majority of the necessary rules for the HGA attainment demonstration by December 31, 2000, and to adopt the rest of the shortfall rules as expeditiously as practical, but no later than July 31, 2001; to submit a Post-99 ROP plan by December 31, 2000; to perform a mid- course review by May 1, 2004; and to perform modeling of mobile source emissions using the EPA mobile source emissions model (MOBILE6), to revise the on-road mobile source budget as needed, and to submit the revised budget within 24 months of the model's release. In addition, if a conformity analysis is to be performed between 12 months and 24 months after the MOBILE6 release, the state will revise the motor vehicle emissions budget (MVEB) so that the conformity analysis and the SIP MVEB are calculated on the same basis.

In order for the state to have an approvable attainment demonstration, EPA has indicated that the state must adopt those strategies modeled in the November submittal and then adopt sufficient controls to close the remaining gap in NO x emissions. The modeling included in this proposal indicates a gap of an additional 77.98 tons per day (tpd) of NO x reductions is necessary for an approvable attainment demonstration. The commission estimates that this measure will achieve a minimum of 10.70 tpd of NO x reductions and is therefore a necessary measure to consider for closing the gap and successfully demonstrating attainment.

The emission reduction requirements included as part of this SIP revision represent substantial, intensive efforts on the part of stakeholder coalitions in the HGA area. These coalitions, involving local governmental entities, elected officials, environmental groups, industry, consultants, and the public, as well as the commission and the EPA, have worked diligently to identify and quantify potential control strategy measures for the HGA attainment demonstration. Local officials from the HGA area have formally submitted a resolution to the commission, requesting the inclusion of many specific emission reduction strategies.

The current SIP revision contains rules, enforceable commitments, and photochemical modeling analyses in support of the HGA ozone attainment demonstration. In addition, this SIP contains Post- 1999 ROP plans for the milestone years 2002 and 2005, and for the attainment year 2007. The SIP also contains enforceable commitments to implement further measures, if needed, in support of the HGA attainment demonstration, as well as a commitment to perform and submit a mid-course review.

The HGA ozone nonattainment area will need to ultimately reduce NOx more than 750 tpd to reach attainment with the one-hour standard. In addition, a VOC reduction of about 25% will have to be achieved. Adoption of the proposed diesel emulsion fuel (DEF) program will contribute to attainment and maintenance of the one-hour ozone standard in the HGA ozone nonattainment area. These proposed rules are one element of the control strategy for the HGA Attainment Demonstration SIP. The purpose of these proposed rules is to establish a diesel emulsion fuel air pollution control strategy for the HGA area that will provide NO x reductions to assist in demonstrating attainment with the ozone NAAQS. The proposed rules would require on- road heavy-duty diesel engines which are registered in HGA and non-road heavy-duty diesel engines that are primarily operated in the HGA area and greater than 175 nominal horsepower (hp), to use diesel emulsions. Elsewhere in this edition of the Texas Register , the commission is proposing to amend 30 TAC Chapter 114, Control of Air Pollution from Motor Vehicles, Subchapter H, Low Emission Fuels, Division 2: Low Emission Diesel, to require the use of low emission diesel in the HGA nonattainment area. The proposed new Division 4: Diesel Emulsion Fuel, requires the addition of diesel emulsion additives to low emission diesel fuel for use in the HGA nonattainment area, thus, it should not conflict with the requirements of the low emission diesel fuel program.

Diesel emulsion fuel is an emergent fuel technology that relies on a water-in-fuel mixture to lower NO x emissions. The water content lowers flame temperature by absorbing latent heat in the combustion chamber, using the same principle of thermodynamics as injecting water into a turbine. There are three components to diesel emulsion fuels: 1.) diesel fuel; 2.) water, usually 10% to 20% by volume; and 3.) a diesel emulsion additive which suspends the fuel and water together. The diesel emulsion fuel can be blended by the diesel emulsion fuel distributor or blended on site using a fuel metering system. According to preliminary laboratory results, the diesel emulsion additive can lower exhaust NO x by 5.0% to 30%, irrespective of the baseline fuel, depending on the engine configuration and operating mode. At least one diesel emulsion additive has been approved for use by the EPA.

Since the EPA does not require the addition of diesel emulsion additives to diesel fuel, as is required by this proposal, the commission does not believe that a waiver under 42 USC, §7445(c)(4)(C) is required.

The commission solicits comment on additional flexibilities relating to rule content and implementation which have not been addressed in this or other concurrent rulemakings. These flexibilities may be available for both mobile and stationary sources. Additional flexibilities may also be achieved through innovative and/or emerging technology which may become available in the future. Additional sources of funds for incentive programs may become available to substitute for some of the measures considered here.

SECTION BY SECTION DISCUSSION

New §114.330 contains the following definitions. "Diesel Emulsion Additive" is defined as a type of diesel fuel additive which allows water and diesel to be blended so that it does not separate. The additive may also contain anti-freeze agents, cetane enhancers, and other ingredients as a water/fuel mixture containing a diesel fuel additive to emulsify the water with the fuel, usually in a mixture. "Diesel Emulsion Fuel" is defined as a water/fuel mixture containing a diesel fuel additive to emulsify the water with the low emission diesel fuel with the water. Typically, DEF contains 10% to 20% by volume water and achieves an emission reduction of 5.0% to 30% NO x relative to the baseline diesel fuel depending concentration of water in the fuel and engine design parameters. "Diesel Emulsion Fuel Distributor" is defined as any person, retailer, jobber, bulk fuel reseller, low emission diesel refiner who distributes diesel emulsion fuel to the ultimate user, diesel emulsion additive manufacturer, or other entity who distributes diesel fuel required to be mixed with a diesel emulsion additive. The proposed definition of "Non-Road Heavy-Duty Engine" includes any non-road engines which are rated over 175 nominal hp. This definition is intended to cover larger engines such as bulldozers, graders, and cranes as well as locomotives, tugs, tow-boats, and ferry boats. "On-road Heavy-duty Diesel Engine" is defined as a diesel engine in a on-road vehicle which is greater than 10,000 pounds gross vehicle weight rating (GVWR). The definition would exclude vehicles required to comply with the federal Tier 2 engine standards. "Primarily Operated" is defined as the use of a motor vehicle or engine more than 60 calendar days per year in an affected county; it is presumed that an on-road vehicle is primarily operated in the county in which it is registered.

Rule applicability is clarified in §114.331. The proposed new rule would apply to distributors of on-road diesel with a throughput of at least 25,000 gallons per month at a fuel dispensing facility, such as a truck stop, or vehicle fleet refueling station. It would apply to distributors of dyed and undyed, non-road diesel with a throughput of at least 500 gallons of diesel per month at one fuel dispensing facility, such as construction or agricultural refueling. The diesel emulsion fuel distributors would make the diesel emulsion fuel available to all on-road heavy-duty diesels, which are defined as being greater than 10,000 pounds GVWR and all non-road engines rated over 175 nominal hp. Any diesel fuel distributor who provides diesel fuel to owners or operators of affected engines and equipment without inclusion of the diesel emulsion fuel additive is considered in violation of this rule.

Diesel emulsion emission standards are specified in §114.332. The diesel component of the diesel emulsion fuel must first meet low emission diesel fuel requirements as required by §114.312, Low Emission Diesel Standards. The requirement to use low emission diesel fuel is being proposed elsewhere in this edition of the Texas Register for the HGA nonattainment area. Requiring use of low emission diesel fuel, consistent with proposed §114.312, will provide a common baseline for all users of the affected equipment and vehicles and will not require the production of an alternative low emission diesel fuel. The diesel emulsion additive must meet EPA requirements in 40 Code of Federal Regulations (CFR) Part 80, Registration of Fuels and Fuel Additives. The amount, concentration, or volume of water used in the diesel emulsion additive must be within the manufacturer specifications. The diesel emulsion must result in emissions that are 15% to 20% lower than the NO x emissions in the base line fuel, depending on the types and operating mode of the engine, and not result in a net increase in the other pollutant levels, as tested by the manufacturer and approved or recognized by the EPA. Typically, diesel emulsion fuel contains 10% to 20% by volume water and achieves an emission reduction of 5.0% to 30% NO x relative to the baseline diesel fuel, depending on the concentration of water in the fuel and engine design parameters. The 15% and 20% reduction are a reasonable requirement because significantly lower reductions would not be adequate to lower ozone production in the photochemical modeling.

Recordkeeping and labeling are addressed in §114.336. All diesel emulsion fuel distributors affected by this rule must retain some kind of proof of purchase such as a fuel contract, leased blending facility, or receipts which prove that the diesel emulsion fuel is actually being used. Also, any tanks which are used to blend and/or dispense diesel emulsion fuel must be labeled "DIESEL EMULSION FUEL ONLY," so as to differentiate between other fuel blends.

Registration is covered in §114.338. All diesel emulsion fuel distributors affected by this rule are required to register with the executive director. The registration must include a statement of acceptance of the requirements of this rule and consent to allow the collection of samples of diesel emulsion fuel and allow access to records. Registration will be on forms available from the executive director.

Affected counties are addressed in §114.339. The counties covered are in the HGA nonattainment area. The rules would be implemented on May 1, 2004.

FISCAL NOTE: COSTS TO STATE AND LOCAL GOVERNMENT

John Davis, Technical Specialist with Strategic Planning and Appropriations, has determined that for the first five-year period the proposed amendments are in effect, there will be fiscal implications which may be significant for units of state and local government located in the HGA area depending on the number of affected on-road heavy-duty diesel vehicles and non-road vehicles and equipment owned and operated as a result of administration or enforcement of the proposed amendments. There should be no fiscal implications to units of state and local government located outside of this nonattainment area as a result of this proposed rules.

The proposed amendments require diesel emulsion fuel use for engines installed in on-road heavy-duty diesel vehicles registered in HGA area with a GVWR greater than 10,000 pounds or engines that are rated more than 175 hp installed in non-road vehicles/equipment primarily operated in the HGA area. The proposed amendments are limited to distributors of on-road diesel that dispense 25,000 or more gallons of diesel fuel per month at one fuel dispensing facility. Additionally, the proposed amendments are limited to distributors of dyed and undyed, non-road diesel that dispense 500 or more gallons of diesel fuel per month at one fuel dispensing facility, such as construction or agricultural refueling sites. The proposed rules would affect approximately 1,900 state and local government and 53,000 privately owned and operated on-road heavy duty diesel vehicles. Additionally, the proposed amendments would also affect approximately 10,000 non-road vehicles/equipment.

Diesel emulsion fuel is an emergent technology for fuels which relies on a water-in-fuel mixture to lower NO x emissions. Diesel emulsion fuel is produced by blending diesel fuel, with water, and a diesel emulsion additive which suspends the fuel and water together.

In order to achieve certain reductions, low emission diesel (LED) fuel will be required to be blended with diesel emulsion fuel in the HGA area by May 1, 2004. Standards for and results of using LED fuel are being presented in a concurrent rulemaking. The commission requires that diesel emulsion fuel used in on-road heavy-duty diesel engines has to result in a 15% decrease in NO x compared to emission benefits from the use of LED fuel alone. Additionally, the diesel emulsion fuel used in non-road engines has to result in a 20% decrease in NO x compared to emission benefits from the use of LED fuel alone. Both uses should not result in a net increase in any other pollutant. The diesel emulsion fuel manufacturers have to provide the EPA with data that corroborates required emission reductions.

Based on comments from a nationwide producer, diesel emulsion fuel will cost the same per gallon as the diesel fuel component used to make the product, because the increased cost of the additive is offset by the displacement of fuel due to the inclusion of water in the overall mixture. By May 1, 2004, the use of LED fuel in the HGA area will increase diesel fuel costs in the HGA area by approximately $.08 more per gallon compared to today's current regular diesel prices. The increased cost for LED fuel is based on analysis published by Northeast States for Coordinated Air Use Management (NESCAUM) and EPA's Notice of Proposed Rulemaking on the Heavy-Duty Engine and Vehicle Standards and Highway Diesel Fuel Sulfur Control Requirements . In addition to the fuel-related cost, there may be an approximate 13% reduction in fuel economy as a result of using the fuel. Testing conducted by one nationwide producer shows that fuel economy can decrease by as much as 13%, but it can also stay the same depending on the vehicle and equipment use.

If a unit of state or local government wants to dispense diesel emulsion fuel, a special blending unit may be required. According to one nationwide diesel emulsion fuel producer, a typical unit, which is capable of processing over 5 million gallons a year, is used at major fuel distribution centers. The cost for this type of unit is approximately $400,000 installed ($350,000 for the unit and $50,000 for installation). Final costs would depend on the level of infrastructure at the proposed site (availability of water, electricity, diesel fuel, platform, piping, etc.). The commission does not anticipate additional costs to state and local government diesel emulsion fuel providers due to required records retention, diesel emulsion fuel tank labeling, and registration with the agency.

Units of state and local government will pay more to fuel affected vehicles due to the increased cost of diesel emulsion fuel compared with current diesel prices and the potential reduced gas mileage. Additionally, if a unit of state or local government decides to dispense the fuel, a special blending unit may have to be purchased or leased. The commission estimates that approximately 1,900 heavy-duty on-road diesel vehicles and a portion of the affected 10,000 non-road vehicles/equipment are owned and operated by state and local governments. These vehicles would be required to use diesel emulsion fuel beginning May 1, 2004. Based on a 25,000 vehicle miles traveled (VMT) per year the total annual cost for units of state and local government affected by the proposed amendments would increase by $775 per diesel vehicle per year. There will be a cost increase associated with using diesel emulsion fuel in non-road vehicles/equipment; however, the total amount cannot be determined at this time. Total costs to units of state and local government in affected counties, not including blending unit and related infrastructure costs and non-road vehicles/equipment, would be approximately $1.4 million.

PUBLIC BENEFIT AND COSTS

Mr. Davis also has determined that for the first five years the proposed amendments are in effect, the public benefit anticipated from enforcement of and compliance with the proposed amendments will be the potential reduction of on-road and non-road mobile source emissions, potentially improved air quality, and contribution toward demonstration of attainment with the NAAQS for the HGA area.

The commission estimates there may be significant fiscal impacts for owners and operators of on- road heavy-duty diesel vehicles and non-road diesel vehicles/equipment affected by the proposed amendments. The proposed rules require diesel emulsion fuel use in engines installed in on-road heavy-duty diesel vehicles registered in the HGA area with a GVWR greater than 10,000 pounds and in engines rated greater than 175 hp installed in non-road vehicles/equipment primarily operated in the HGA area. The proposed rules would affect approximately 53,000 privately owned and operated on- road heavy-duty diesel vehicles and a portion of the 10,000 affected non-road vehicles/equipment that are privately owned and operated.

Diesel emulsion fuel is an emergent technology for fuels which relies on a water-in-fuel mixture to lower NO x emissions. Diesel emulsion fuel is produced by blending diesel fuel, with water, and a diesel emulsion additive which suspends the fuel and water together.

In order to achieve certain reductions, LED fuel will be required to be blended with diesel emulsion fuel in the HGA area by May 1, 2004. Standards for and results of using LED fuel are being presented in a concurrent rulemaking. The commission requires that diesel emulsion fuel used in on- road heavy-duty diesel engines has to result in a 15% decrease in NO x compared to emission benefits from the use of LED fuel alone. Additionally, the diesel emulsion fuel used in non- road engines has to result in a 20% decrease in NO x compared to emission benefits from the use of LED fuel alone. Both uses should not result in a net increase in any other pollutant. The diesel emulsion fuel manufacturers must provide the EPA with data that corroborates required emission reductions.

Based on comments from potential producers, diesel emulsion fuel will cost the same per gallon as the diesel fuel component, because the increased cost of the additive is offset by the displacement of fuel due to the inclusion of water in the overall mixture. By May 1, 2004, the use of LED fuel in the HGA area will increase diesel fuel costs by approximately $.08 more per gallon compared to today's current regular diesel prices. Therefore, diesel emulsion fuel sold after May 1, 2004 should cost approximately $.08 more per gallon. In addition to the fuel-related cost increases, there may be an approximate 13% reduction in fuel economy as a result of using diesel emulsion fuel. Testing conducted by one producer shows that fuel economy can decrease by as much as 13%, but it can also stay the same. The overall fuel economy effect is dependent on vehicle/equipment use.

The proposed amendments will probably directly affect major fuel distribution centers that serve the affected counties and individuals and businesses that want to dispense diesel emulsion fuel to affected vehicles and equipment in the affected counties, because a special blending unit will probably have to be used in order to mix the diesel emulsion fuel. According to one nationwide diesel emulsion fuel producer, a typical unit, which is capable of processing over five million gallons a year, is used at major fuel distribution centers. The cost for this type of unit is approximately $400,000 installed ($350,000 for the unit and $50,000 for installation). Final costs would depend on the level of infrastructure at the proposed site (availability of water, electricity, diesel fuel, platform, piping, etc.). The commission does not anticipate additional costs to individuals and businesses that are diesel emulsion fuel providers due to required records retention, diesel emulsion fuel tank labeling, and registration with the agency.

Individuals and businesses will probably pay more to fuel affected vehicles due to the increased cost of diesel emulsion fuel compared with current diesel prices and the potential reduced gas mileage. Additionally, if an individual or business decides to dispense diesel emulsion fuel, a special blending unit will probably have to be purchased or leased. The commission estimates that approximately 53,000 heavy-duty diesel vehicles and a portion of the 10,000 affected non-road vehicles/equipment are owned and operated by individuals and businesses in the affected counties. These vehicles would be required to use diesel emulsion fuel beginning May 1, 2004. Based on a 25,000 to 50,000 VMT per year the total annual cost to individuals and businesses affected by the proposed amendments would increase by $775 to $1,550 per diesel vehicle per year. The higher VMT was used in order to reflect the increased miles that some privately-owned heavy-duty diesels (such as long haul semi-trucks) accrue compared with state and local government vehicles. There will be a cost increase associated with using diesel emulsion fuel in non-road vehicles/equipment; however the total amount cannot be determined at this time. Total annual costs to individuals and businesses in the affected counties, not including blending unit and related infrastructure costs and non-road vehicles/equipment, would be approximately $41 million to $82 million.

SMALL AND MICRO-BUSINESS ASSESSMENT

The commission determined that fiscal implications are possible as a result of administration or enforcement of the proposed amendments, for small and micro-businesses that own a fleet of vehicles or that dispense diesel fuel in the HGA area. There are no known diesel fuel producers or importers that would be considered small or micro-businesses. The commission estimates that many independent retailers of diesel fuel, which are potential diesel emulsion fuel retailers in the affected counties, are small or micro-businesses that will probably not choose to mix diesel emulsion fuel on-site. The commission anticipates that small or micro-businesses that choose to dispense diesel emulsion fuel will purchase the mixed fuel from larger fuel distributors and store the fuel on-site. However, if a small or micro-businesses chooses to mix and dispense diesel emulsion fuel, a special blending unit will have to be purchased or leased. A typical blending unit would cost approximately $400,000 installed ($350,000 for the unit and $50,000 for installation). Production costs to produce diesel emulsion fuel, which incorporates the estimated $.08 per gallon increase based on the use of LED fuel as the baseline, are not anticipated to affect small or micro-business except for passing increased costs of production through to consumers. Of the 53,000 heavy-duty on-road diesel vehicles and the 10,000 non-road vehicles/equipment affected by the proposed amendments, some will be owned and operated by small or micro-businesses. The total annual cost to small or micro-businesses, not including blending unit and related infrastructure costs and non-road vehicles/equipment, would increase by $775 to $1,550 per heavy-duty diesel vehicle per year. There will be a cost increase associated with using diesel emulsion fuel in non-road vehicles/equipment; however, the total amount cannot be determined at this time. Total fiscal impact to small or micro-businesses will depend on the total number of vehicles affected by the proposed amendments that are owned and operated by individual small and micro-businesses.

DRAFT REGULATORY IMPACT ANALYSIS DETERMINATION

The commission reviewed the rulemaking in light of the regulatory impact analysis (RIA) requirements of Texas Government Code, §2001.0225, and has determined that the rulemaking does not meet the definition of a "major environmental rule" as defined in that statute. "Major environmental rule" means a rule, the specific intent of which is to protect the environment or reduce risks to human health from environmental exposure and that may adversely affect in a material way the economy, a sector of the economy, productivity, competition, jobs, the environment, or the public health and safety of the state or a sector of the state. The new sections to Chapter 114 are one element of the HGA Attainment SIP and will require the use of diesel emulsions in the HGA nonattainment area. While the new rules are intended to protect the environment, based on the analysis provided in the preamble, including the discussion in the Public Benefit and Costs section, the commission does not believe the rules will adversely affect, in a material way, the operation of on-road or non-road heavy- duty diesel engines or diesel emulsion fuel distributors. The commission does not believe these entities comprise a sector of the economy, or that these rules will adversely affect in a material way the economy, productivity, competition, jobs, the environment, or the public health and safety of the state or a sector of the state.

Provisions of 42 USC, §7410, require states to adopt a SIP which provides for "implementation, maintenance, and enforcement" of the primary NAAQS in each air quality control region of the state. While §7410 does not require specific programs, methods, or reductions in order to meet the standard, state SIPs must include "enforceable emission limitations and other control measures, means or techniques (including economic incentives such as fees, marketable permits, and auctions of emissions rights), as well as schedules and timetables for compliance as may be necessary or appropriate to meet the applicable requirements of this chapter," (meaning Chapter 85, Air Pollution Prevention and Control). It is true that 42 USC does require some specific measures for SIP purposes, like the inspection and maintenance program, but those programs are the exception, not the rule, in the SIP structure of 42 USC. The provisions of 42 USC recognize that states are in the best position to determine what programs and controls are necessary or appropriate in order to meet the NAAQS. This flexibility allows states, affected industry, and the public, to collaborate on the best methods for attaining the NAAQS for the specific regions in the state. Even though 42 USC allows states to develop their own programs, this flexibility does not relieve a state from developing a program that meets the requirements of §7410. Thus, while specific measures are not generally required, the emission reductions are required. States are not free to ignore the requirements of §7410 and must develop programs to assure that the nonattainment areas of the state will be brought into attainment on schedule.

The requirement to provide a fiscal analysis of proposed regulations in the Texas Government Code was amended by Senate Bill 633 (SB 633) during the 75th Legislative Session, 1999. The intent of SB 633 was to require agencies to conduct a regulatory impact analysis (RIA) of extraordinary rules. These are identified in the statutory language as major environmental rules that will have a material adverse impact and will exceed a requirement of state law, federal law, or a delegated federal program, or are adopted solely under the general powers of the agency. With the understanding that this requirement would seldom apply, the commission provided a cost estimate for SB 633 that concluded "based on an assessment of rules adopted by the agency in the past, it is not anticipated that the bill will have significant fiscal implications for the agency due to its limited application." The commission also noted that the number of rules that would require assessment under the provisions of the bill was not large. This conclusion was based, in part, on the criteria set forth in the bill that exempted proposed rules from the full analysis unless the rule was a major environmental rule that exceeds a federal law. As previously discussed, 42 USC does not require specific programs, methods, or reductions in order to meet the NAAQS; thus, states must develop programs for each nonattainment area to ensure that area will meet the attainment deadlines. Because of the ongoing need to address nonattainment issues, the commission routinely proposes and adopts SIP rules. The legislature is presumed to understand this federal scheme. If each rule proposed for inclusion in the SIP was considered to be a major environmental rule that exceeds federal law, then every SIP rule would require the full RIA contemplated by SB 633. This conclusion is inconsistent with the conclusions reached by the commission in its cost estimate and by the Legislative Budget Board (LBB) in its fiscal notes. Since the legislature is presumed to understand the fiscal impacts of the bills it passes, and that presumption is based on information provided by state agencies and the LBB, the commission believes that the intent of SB 633 was only to require the full RIA for rules that are extraordinary in nature. While the SIP rules will have a broad impact, that impact is no greater than is necessary or appropriate to meet the requirements of the FCAA. For these reasons, rules proposed for inclusion in the SIP fall under the exception in Texas Government Code, §2001.0225(a), because they are required by federal law. The commission performed photochemical grid modeling which predicts that NO x emission reductions, such as those required by these rules, will result in reductions in ozone formation in the HGA ozone nonattainment area. This rulemaking does not exceed an express requirement of state law. This rulemaking is intended to obtain NO x emission reductions which will result in reductions in ozone formation in the HGA ozone nonattainment area and help bring HGA into compliance with the air quality standards established under federal law as NAAQS for ozone. The rulemaking does not exceed a standard set by federal law, exceed an express requirement of state law (unless specifically required by federal law), or exceed a requirement of a delegation agreement. The rulemaking was not developed solely under the general powers of the agency, but was specifically developed to meet the NAAQS established under federal law and authorized under Texas Clean Air Act (TCAA), §§382.011, 382.012, 382.017, 382.019, 382.037(g), and 382.039. The commission invites public comment on the draft regulatory impact analysis.

TAKINGS IMPACT ASSESSMENT

The commission prepared a takings impact assessment for these rules in accordance with Texas Government Code, §2007.043. The following is a summary of that assessment. These proposed new rules are one element of the control strategy for the HGA Post-1999 ROP/Attainment Demonstration SIP. The specific purpose of the rulemaking is to require on-road or non-road heavy- duty diesel engines which are registered or primarily operated in the HGA nonattainment area to use diesel emulsion fuel. Adoption of these requirements to reduce NO x can contribute to attainment and maintenance of the one-hour ozone standard in the HGA nonattainment area. Promulgation and enforcement of the rules may burden private real property because the requirement to use diesel emulsion fuel could require a diesel emulsion fuel distributor to install a blending station or other equipment, that could be attached to private real property. Although the rule revisions do not directly prevent a nuisance or prevent an immediate threat to life or property, they do prevent a real and substantial threat to public health and safety and fulfill federal mandates under the 42 USC, §7410. Specifically, control requirements have been developed to meet the ozone NAAQS set by the EPA under 42 USC, §7409. States are primarily responsible for ensuring attainment and maintenance of NAAQS once the EPA has established them. Under 42 USC, §7410 and related provisions, states must submit, for EPA approval, SIPs that provide for the attainment and maintenance of NAAQS through control programs directed to sources of the pollutants involved. Therefore, the purpose of this rulemaking is to implement restrictions on the use of heavy-duty on-road and non-road engines in the HGA ozone nonattainment area to meet the air quality standards established under federal law as NAAQS. Consequently, the exemption which applies to these rules is that of an action reasonably taken to fulfill an obligation mandated by federal law; therefore, these proposed rules do not constitute a takings under the Texas Government Code, Chapter 2007.

CONSISTENCY WITH THE COASTAL MANAGEMENT PROGRAM

The commission determined that the proposed rulemaking relates to an action or actions subject to the Texas Coastal Management Program (CMP) in accordance with the Coastal Coordination Act of 1991, as amended (Texas Natural Resources Code, §§33.201 et seq.), and the commission rules in 30 TAC Chapter 281, Subchapter B, concerning Consistency with the CMP. As required by 30 TAC §281.45(a)(3) and 31 TAC §505.11(b)(2), relating to actions and rules subject to the CMP, commission rules governing air pollutant emissions must be consistent with the applicable goals and policies of the CMP. The commission reviewed this action for consistency with the CMP goals and policies in accordance with the rules of the Coastal Coordination Council, and determined that the action is consistent with the applicable CMP goals and policies. The CMP goal applicable to this rulemaking action is the goal to protect, preserve, and enhance the diversity, quality, quantity, functions, and values of coastal natural resource areas (31 TAC §501.12(1)). No new sources of air contaminants will be authorized and NO x air emissions will be reduced as a result of these rules. The CMP policy applicable to this rulemaking action is the policy that commission rules comply with regulations in 40 CFR, to protect and enhance air quality in the coastal area (31 TAC §501.14(q)). This rulemaking action complies with 40 CFR 50, National Primary and Secondary Ambient Air Quality Standards, and 40 CFR 51, Requirements for Preparation, Adoption, and Submittal Of Implementation Plans. Therefore, in compliance with 31 TAC §505.22(e), this rulemaking action is consistent with CMP goals and policies.

Interested persons may submit comments on the consistency of the proposed rules with the CMP during the public comment period.

ANNOUNCEMENT OF HEARINGS

The commission will hold public hearings on this proposal at the following times and locations: September 18, 2000, 10:00 a.m., Lone Star Convention Center, 9055 Airport Road (FM 1484), Conroe; September 18, 2000, 7:00 p.m., Lake Jackson Civic Center, 333 Highway 332 East, Lake Jackson; September 19, 2000, 10:00 a.m. and 7:00 p.m., George Brown Convention Center, 1001 Avenida de Las Americas, Houston; September 20, 2000, 9:00 a.m., VFW Hall, 6202 George Bush Drive, Katy; September 20, 2000, 6:00 p.m., East Harris County Community Center, 7340 Spencer, Pasadena; September 21, 2000, 10:00 a.m., Southeast Texas Regional Airport Media Room, 6000 Airline Drive, Beaumont; September 21, 2000, 2:00 p.m., Amarillo City Commission Chambers, City Hall, 509 East 7th Avenue, Amarillo; September 21, 2000, 6:00 p.m., Charles T. Doyle Convention Center, 21st Street at Phoenix Lane, Texas City; September 22, 2000, 10:00 a.m., Dayton High School, 2nd Floor Lecture Room, 3200 North Cleveland Street, Dayton; September 22, 2000, 11:00 a.m., El Paso City Council Chambers, 2 Civic Center Plaza, 2nd Floor, El Paso; September 22, 2000, 2:00 p.m., North Central Texas Council of Governments, 2nd Floor Board Room, 616 Six Flags Drive, Suite 200, Arlington; and September 25, 2000, 10:00 a.m., Texas Natural Resource Conservation Commission, 12100 North I-35, Building E, Room 201S, Austin. The hearings are structured for the receipt of oral or written comments by interested persons. Registration will begin one hour prior to each hearing. Individuals may present oral statements when called upon in order of registration. A four-minute time limit will be established at each hearing to assure that enough time is allowed for every interested person to speak. Open discussion will not occur during each hearing; however, agency staff members will be available to discuss the proposal one hour before each hearing, and will answer questions before and after each hearing.

Persons with disabilities who have special communication or other accommodation needs, who are planning to attend a hearing, should contact the Office of Environmental Policy, Analysis, and Assessment at (512) 239-4900. Requests should be made as far in advance as possible.

SUBMITTAL OF COMMENTS

Comments may be mailed to Heather Evans, Office of Environmental Policy, Analysis, and Assessment, MC 206, P.O. Box 13087, Austin, Texas 78711-3087, faxed to (512) 239-4808, or emailed to siprules@tnrcc.state.tx.us . All comments should reference Rule Log Number 2000-011K-114-AI. Comments must be received by 5:00 p.m., September 25 2000. For further information, please contact Sam Wells at (512) 239-1441 or Alan Henderson at (512) 239-1510.

STATUTORY AUTHORITY

The new sections are proposed under Texas Water Code (TWC), §5.103, which authorizes the commission to adopt rules necessary to carry out its powers and duties under the TWC, and under the Texas Health and Safety Code, TCAA, §382.017, which provides the commission the authority to adopt rules consistent with the policy and purposes of the TCAA. The new sections are also proposed under TCAA, §382.011, which authorizes the commission to control the quality of the state's air; §382.012, which authorizes the commission to prepare and develop a general, comprehensive plan for the control of the state's air; §382.019, which authorizes the commission to adopt rules to control and reduce emissions from engines used to propel land vehicles; §382.037(g), which authorizes the commission to regulate fuel content if it is demonstrated to be necessary for attainment of the NAAQS; and §382.039, which authorizes the commission to develop and implement transportation programs and other measures necessary to demonstrate attainment and protect the public from exposure to hazardous air contaminants from motor vehicles.

The proposed new sections implement TCAA, §382.002, relating to Policy and Purpose; §382.011, relating to General Powers and Duties; §382.012, relating to State Air Control Plan; §382.019, relating to Methods Used to Control and Reduce Emissions from Land Vehicles; §382.037(g), relating to Vehicle Emissions Inspection and Maintenance Program, and §382.039, relating to Attainment Program.

§114.330.Definitions.

Unless specifically defined in the TCAA or in the rules of the commission, the terms used by the commission have the meanings commonly ascribed to them in the field of air pollution control. In addition to the terms which are defined by the TCAA, the following words and terms, when used in Subchapter H of this chapter (relating to Low Emission Fuels), shall have the following meanings, unless the context clearly indicates otherwise.

(1)

Diesel emulsion additive - A type of diesel fuel additive which allows water and diesel to be blended so that it does not separate. The additive may also contain, but is not limited to, anti-freeze agents, cetane enhancers, and other ingredients.

(2)

Diesel emulsion fuel - A water/fuel mixture containing a diesel fuel additive to emulsify the water with the fuel.

(3)

Diesel emulsion fuel distributor - Any person, retailer, jobber, bulk fuel reseller, low emission diesel refiner who distributes diesel emulsion fuel to the ultimate user, diesel emulsion additive manufacturer, or other entity who distributes diesel emulsion fuel required to be mixed with a diesel emulsion additive.

(4)

Non-road heavy-duty engine - A non-road engine that is greater than 175 nominal horsepower as rated by the manufacturer on the vehicle nameplate and is fueled by gasoline, diesel, diesel emulsion, or any alternate fuel, including, but not limited to, locomotives, tugs, tow-boats, construction equipment, and ferry boats.

(5)

On-road heavy-duty diesel engine - An engine installed in an on-road vehicle which is greater than 10,000 pounds gross vehicle weight rating.

(6)

Primarily operated - Use of a motor vehicle or engine more than 60 calendar days per year in an affected county. It is presumed that an on-road vehicle is primarily operated in the county in which it is registered.

§114.331.Applicability.

The requirements of this division apply to:

(1)

diesel emulsion fuel distributors that supply fuel for on-road heavy-duty diesel engines which are registered in the counties listed under §114.339 (relating to Affected Counties and Compliance Dates) with a total throughput of at least 25,000 gallons per month at one fuel dispensing facility; and

(2)

diesel emulsion fuel distributors who supply dyed and undyed diesel fuel for non-road heavy-duty engines primarily operated in the counties listed under §114.339 of this title with a total throughput of at least 500 gallons per month at one fuel dispensing facility.

§114.332.Diesel Emulsion Standards.

No diesel fuel shall be used in the counties listed in §114.329 of this title (relating to Affected Counties and Compliance Dates) unless it meets the following.

(1)

The low emission diesel fuel used to blend diesel emulsion fuel must meet all the performance standards contained in §114.312 of this title (regarding Low Emission Diesel Standards).

(2)

The diesel emulsion additive must be registered with the EPA in accordance with 40 Code of Federal Regulations (CFR), Subpart 80 (concerning Registration of Fuels and Fuel Additives, as amended on February 28, 2000).

(3)

The amount, concentration, or volume of water must be within the diesel emulsion additive manufacturer specifications.

(4)

The diesel emulsion must:

(A)

result in emissions that are lower than the emissions of oxides of nitrogen in the low emission diesel as follows:

(i)

on-road heavy-duty diesel engines - 15%; and

(ii)

non-road heavy-duty diesel engine - 20%; and

(B)

not result in a net increase in the other pollutant levels, as tested in accordance with 40 CFR, Subpart 80 as amended on February 28, 2000, or Title 13, California Code of Regulations, §2281 and §2282, as amended on June 4, 1997.

§114.336.Recordkeeping and Labeling.

(a)

All diesel emulsion fuel distributors affected by this division shall maintain complete and accurate records for at least two years and, upon request, shall make such records available to representatives of the commission, EPA, or local air pollution control agency having jurisdiction in the area. The information in the records shall include, but shall not be limited to, proof of purchase of diesel emulsion fuel such as by bulk fuel contract, bills of lading, purchase orders, fuel analysis, or other records sufficient to demonstrate compliance.

(b)

All tanks in service or blending units in which diesel emulsion fuel is stored must be clearly labeled with a sign which reads "DIESEL EMULSION FUEL ONLY" in at least four-inch letters, and each tank must have a visible, unique identification number which corresponds to a plot plan which shows the location of the tank or blending unit.

§114.338.Registration.

Diesel emulsion fuel distributors must register with the executive director. Registration will be on forms provided by the executive director and shall include a statement of acceptance of the requirements of this division and shall include a statement of consent by the registrant that the executive director shall be permitted to collect samples and have access to all documentation and records. The executive director shall maintain a listing of all registered diesel emulsion fuel distributors.

§114.339.Affected Counties and Compliance Dates.

Beginning on May 1, 2004, the requirements of this division shall be enforced in the counties of: Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller.

This agency hereby certifies that the proposal has been reviewed by legal counsel and found to be within the agency's legal authority to adopt.

Filed with the Office of the Secretary of State, on August 11, 2000.

TRD-200005630

Margaret Hoffman

Director, Environmental Law Division

Texas Natural Resource Conservation Commission

Earliest possible date of adoption: September 24, 2000

For further information, please call: (512) 239-0348


Subchapter I. NON-ROAD ENGINES

3. NON-ROAD LARGE SPARK-IGNITION ENGINES

30 TAC §114.421, §114.429

The commission proposes amendments to §114.421, Emission Specifications, and §114.429, Affected Counties and Compliance Schedules. These amendments to Chapter 114, Control of Air Pollution from Motor Vehicles; Subchapter I, Non-road Engines; Division 3: Non-road Large Spark-ignition Engines; and corresponding revisions to the associated state implementation plan (SIP) are being proposed in order to extend the existing requirements for non-road, large spark-ignition engines to all counties in the state thus controlling ground-level ozone in the state.

BACKGROUND AND SUMMARY OF THE FACTUAL BASIS FOR THE PROPOSED RULE

The Houston/Galveston (HGA) ozone nonattainment area is classified as Severe-17 under the Federal Clean Air Act (FCAA) Amendments of 1990 (42 United States Code (USC), §§7401 et seq.), and therefore is required to attain the one-hour ozone standard of 0.12 parts per million (ppm) by November 15, 2007. The HGA area, defined by Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller Counties, has been working to develop a demonstration of attainment in accordance with 42 USC, §7410. On January 4, 1995, the state submitted the first of its Post-1996 SIP revisions for HGA.

The January 1995 SIP consisted of urban airshed model (UAM) modeling for 1988 and 1990 base-case episodes, adopted rules to achieve a 9% rate-of-progress (ROP) reduction in volatile organic compounds (VOC), and a commitment schedule for the remaining ROP and attainment demonstration elements. At the same time, but in a separate action, the State of Texas filed for the temporary nitrogen oxides (NO x ) waiver allowed by 42 USC, §7511a(f). The January 1995 SIP and the NO x waiver were based on early base-case episodes which marginally exhibited model performance in accordance with the United States Environmental Protection Agency (EPA) modeling performance standards, but which had a limited data set as inputs to the model. In 1993 and 1994, the commission was engaged in an intensive data-gathering exercise known as the COAST study. The state believed that the enhanced emissions inventory, expanded ambient air quality and meteorological monitoring, and other elements would provide a more robust data set for modeling and other analysis, which would lead to modeling results that the commission could use to better understand the nature of the ozone air quality problem in the HGA area.

Around the same time as the 1995 submittal, EPA policy regarding SIP elements and timelines went through changes. Two national programs in particular resulted in changing deadlines and requirements. The first of these programs was the Ozone Transport Assessment Group. This group grew out of a March 2, 1995 memo from Mary Nichols, former EPA Assistant Administrator for Air and Radiation, that allowed states to postpone completion of their attainment demonstrations until an assessment of the role of transported ozone and precursors had been completed for the eastern half of the nation, including the eastern portion of Texas. Texas participated in this study, and it has been concluded that Texas does not significantly contribute to ozone exceedances in the Northeastern United States. The other major national initiative that has impacted the SIP planning process is the revisions to the national ambient air quality standard (NAAQS) for ozone. The EPA promulgated a final rule on July 18, 1997 changing the ozone standard to an eight-hour standard of 0.08 ppm. In November 1996, concurrent with the proposal of the standards, the EPA proposed an interim implementation plan (IIP) that it believed would help areas like HGA transition from the old to the new standard. In an attempt to avoid a significant delay in planning activities, Texas began to follow this guidance, and readjusted its modeling and SIP development timelines accordingly. When the new standard was published, the EPA decided not to publish the IIP, and instead stated that, for areas currently exceeding the one-hour ozone standard, that standard would continue to apply until it is attained. The FCAA requires that HGA attain the standard by November 15, 2007.

The EPA issued revised draft guidance for areas such as HGA that do not attain the one-hour ozone standard. The commission adopted on May 6, 1998 and submitted to the EPA on May 19, 1998 a revision to the HGA SIP which contained the following elements in response to EPA's guidance: UAM modeling based on emissions projected from a 1993 baseline out to the 2007 attainment date; an estimate of the level of VOC and NO x reductions necessary to achieve the one-hour ozone standard by 2007; a list of control strategies that the state could implement to attain the one-hour ozone standard; a schedule for completing the other required elements of the attainment demonstration; a revision to the Post-1996 9% ROP SIP that remedied a deficiency that the EPA believed made the previous version of that SIP unapprovable; and evidence that all measures and regulations required by the Subpart 2 of Title I of the FCAA to control ozone and its precursors have been adopted and implemented, or are on an expeditious schedule to be adopted and implemented.

In November 1998, the SIP revision submitted to the EPA in May 1998 became complete by operation of law. However, the EPA stated that it could not approve the SIP until specific control strategies were modeled in the attainment demonstration. The EPA specified a submittal date of November 15, 1999 for this modeling. In a letter to the EPA dated January 5, 1999, the state committed to model two strategies showing attainment.

As the HGA modeling protocol evolved, the state eventually selected and modeled seven basic modeling scenarios. As part of this process, a group of HGA stakeholders worked closely with commission staff to identify local control strategies for the modeling. Some of the scenarios for which the stakeholders requested evaluation included options such as California-type fuel and vehicle programs as well as an acceleration simulation mode equivalent motor vehicle inspection and maintenance program. Other scenarios incorporated the estimated reductions in emissions that were expected to be achieved throughout the modeling domain as a result of the implementation of several voluntary and mandatory statewide programs adopted or planned independently of the SIP. It should be made clear that the commission did not propose that any of these strategies be included in the ultimate control strategy submitted to the EPA in 2000. The need for and effectiveness of any controls which may be implemented outside the HGA eight-county area will be evaluated on a county-by-county basis.

The SIP revision was adopted by the commission on October 27, 1999, submitted to the EPA by November 15, 1999, and contained the following elements: photochemical modeling of potential specific control strategies for attainment of the one-hour ozone standard in the HGA area by the attainment date of November 15, 2007; an analysis of seven specific modeling scenarios reflecting various combinations of federal, state, and local controls in HGA (additional scenarios H1 and H2 build upon Scenario VIf); identification of the level of reductions of VOC and NO x necessary to attain the one-hour ozone standard by 2007; a 2007 mobile source budget for transportation conformity; identification of specific source categories which, if controlled, could result in sufficient VOC and/or NO x reductions to attain the standard; a schedule committing to submit by April 2000 an enforceable commitment to conduct a mid-course review; and a schedule committing to submit modeling and adopted rules in support of the attainment demonstration by December 2000.

The April 19, 2000 SIP revision for HGA contained the following enforceable commitments by the state: to quantify the shortfall of NO x reductions needed for attainment; to list and quantify potential control measures to meet the shortfall of NO x reductions needed for attainment; to adopt the majority of the necessary rules for the HGA attainment demonstration by December 31, 2000, and to adopt the rest of the shortfall rules as expeditiously as practical, but no later than July 31, 2001; to submit a Post-99 ROP plan by December 31, 2000; to perform a mid- course review by May 1, 2004; and to perform modeling of mobile source emissions using the EPA mobile source emissions model (MOBILE6), to revise the on-road mobile source budget as needed, and to submit the revised budget within 24 months of the model's release. In addition, if a conformity analysis is to be performed between 12 months and 24 months after the MOBILE6 release, the state will revise the motor vehicle emissions budget (MVEB) so that the conformity analysis and the SIP MVEB are calculated on the same basis.

In order for the state to have an approveable attainment demonstration, the EPA has indicated that the state must adopt those strategies modeled in the November submittal and then adopt sufficient controls to close the remaining gap in NO x emissions. The modeling included in this proposal indicates a gap of an additional 77.98 tons per day (tpd) of NO x reductions is necessary for an approveable attainment demonstration. The commission estimates that this measure will achieve a minimum of 2.8 tpd of NO x equivalent reductions and is therefore a necessary measure to consider for closing the gap and successfully demonstrating attainment.

The emission reduction requirements included as part of this SIP revision represent substantial, intensive efforts on the part of stakeholder coalitions in the HGA area. These coalitions, involving local governmental entities, elected officials, environmental groups, industry, consultants, and the public, as well as the commission and the EPA, have worked diligently to identify and quantify potential control strategy measures for the HGA attainment demonstration. Local officials from the HGA area have formally submitted a resolution to the commission, requesting the inclusion of many specific emission reduction strategies.

The current SIP revision contains rules, enforceable commitments, and photochemical modeling analyses in support of the HGA ozone attainment demonstration. In addition, this SIP contains Post- 1999 ROP plans for the milestone years 2002 and 2005, and for the attainment year 2007. The SIP also contains enforceable commitments to implement further measures, if needed, in support of the HGA attainment demonstration, as well as a commitment to perform and submit a mid-course review.

The HGA ozone nonattainment area will need to ultimately reduce NOx more than 750 tpd to reach attainment with the one-hour standard. In addition, a VOC reduction of about 25% will have to be achieved. Extension of the large spark-ignition non-road engine rules will contribute to attainment and maintenance of the one-hour ozone standard in the HGA area. The extension of these rules to all counties in the state should also contribute to maintenance of the one-hour ozone standard in the rest of the state.

The EPA has been regulating highway (on-road) cars and trucks since the early 1970s and continues to set increasingly stringent emissions standards for such vehicles. After considerable progress has been made in controlling emissions from on-road vehicles, the EPA has turned its attention to non-road (also called off-road) engines, which also contribute significantly to air pollution. Although emissions from non-road, large spark-ignition (LSI) engines have not yet been regulated by the EPA, the California Air Resources Board (CARB) has adopted exhaust emission standards for these engines. Non-road, LSI engines are primarily used to power industrial equipment such as forklifts, generators, pumps, compressors, aerial lifts, sweepers, and large lawn tractors. The engines are similar to automotive engines and can use similar automotive technology, such as closed-loop engine control and three-way catalysts, to reduce emissions.

The CARB has determined the exhaust emission standards for non-road, LSI engines to be technologically feasible and a cost effective strategy at $.25 per pound ($500 per ton) of NO x and hydrocarbons (HC) reduced, that will move the state toward reducing NO x and HC from non-road, LSI engines. HC, also called VOC, and NOx are precursor chemicals that contribute to the formation of ground-level ozone. The HGA area alone will contain 23% of the state's LSI engines by 2007, or approximately 88,374 engines. Statewide, there will be approximately 371,096 LSI engines by 2007. Adoption and implementation of California standards for non-road, LSI engines throughout the state should reduce the amount of VOC and NO x emissions from these sources and, therefore, help control ground-level ozone in nonattainment areas. For the HGA ozone nonattainment area, emission reductions by 2007 will be approximately 2.8 tpd. The program is estimated to cost about $500 per ton of NO x reduced, which compares very favorably with the cost per ton of other emission control strategies.

These amendments are proposed in order to control ground-level ozone in the state by restricting the sale and use of non-road, LSI engines 25 horsepower (hp) and larger produced in model year 2004, and all equipment and vehicles produced on or after January 1, 2004 that use such engines; to LSI engines that are certified under Title 13, California Code of Regulations, Chapter 9, concerning Off- Road Vehicles and Engines Pollution Control Devices (13 CCR 9), as adopted by the CARB on October 19, 1999 and effective November 18, 1999. The commission is incorporating the non-road, LSI engine rules by reference including all future revisions due to the need for the Texas program to remain identical to the program in California. For any state program that differs from the federal standards, the 42 USC, §7543(e)(2)(B), requires the state programs to be identical. The rules are proposed to be effective throughout the State of Texas. The proposed amendments are necessary in order to attain and maintain the ozone standard in nonattainment areas, and to establish a single equipment design standard for the state. A single equipment design standard will help to prevent incompatibility and expense which may arise from the distribution of equipment with different emission standards.

The commission solicits comment on additional flexibilities relating to rule content and implementation which have not been addressed in this or other concurrent rulemakings. These flexibilities may be available for both mobile and stationary sources. Additional flexibilities may also be achieved through innovative and/or emerging technology which may become available in the future. Additional sources of funds for incentive programs may become available to substitute for some of the measures considered here.

SECTION-BY-SECTION DISCUSSION

The intent of these proposed amendments is to extend to all counties in the State of Texas the existing non-road, LSI standards in the Dallas/Fort Worth (DFW) area. These existing standards are identical to the non-road, LSI standards in place in California.

The following sections of Division 3 were adopted during the DFW rule promulgation and cannot be reopened for public comment in this proposal because no changes are being proposed to these sections: §114.420, Definitions; §114.422, Control Requirements; and §114.427, Exemptions. The two sections of the rules being opened for comment will be §114.421 and 114.429. Section 114.421 is proposed to be amended to reflect the statewide applicability of the LSI rules, and §114.429 is proposed to be amended to reflect the compliance dates for the new portions of the state being affected by this rulemaking action.

Additionally, §§114.420, 114.422, and 114.427 may not be reopened because they incorporate by reference the California non-road, LSI rules and all future revisions as those rules are set out in 13 CCR 9, concerning Off-Road Vehicles and Engines Pollution Control Devices, as adopted by the CARB on October 19, 1999 and effective November 18, 1999. The Texas program must remain identical to the California program, so the sections already incorporated by reference in the DFW rulemaking may not be changed to be different from the California 13 CCR 9 rules.

Existing §114.421 (Emission Specifications) incorporated by reference the 42 definitions found in 13 CCR 9, §2431 (Definitions). This proposal makes no changes to these definitions.

Existing §114.429 applied the control requirements to nine counties in the DFW area which include Collin, Dallas, Denton, Ellis, Johnson, Kaufman, Parker, Rockwall, and Tarrant Counties. These proposed amendments extend the control requirements to all counties within the state. Proposed §114.429 also specifies the compliance schedule for engine manufacturers.

FISCAL NOTE: COSTS TO STATE AND LOCAL GOVERNMENT

John Davis, Technical Specialist with Strategic Planning and Appropriations, determined that for the first five-year period the proposed amendments to Chapter 114 are in effect there will be no significant fiscal implications for any single unit of state and local government as a result of administration or enforcement of the proposed amendments unless that unit of government replaces between 200 and 1,000 of these engines annually. The proposed amendments to Chapter 114 would require units of state and local government, businesses, and individuals statewide that own or operate non-road LSI engines of 25 hp and larger produced on or after January 1, 2004, and all equipment and vehicles produced on or after January 1, 2004 that use such engines, to use LSI engines certified under 13 CCR 9 as adopted by the CARB on October 19, 1999.

Non-road LSI engines are primarily used to power industrial equipment such as forklifts, generators, pumps, compressors, aerial lifts, sweepers, and large lawn tractors. The engines are similar to automotive engines and can use similar automotive technologies to reduce emissions. The CARB has determined the proposed standards are technologically feasible and has adopted exhaust emission standards for these engines designed to reduce NO x and VOC emissions. Oxides of nitrogen and VOC are precursor chemicals that contribute to the production of ground-level ozone.

The proposed amendments include exemptions for: 1.) Engines less than 175 hp used in construction and agriculture; 2.) Engines operated on or in any device used exclusively upon stationary rails or tracks; 3.) Engines used to propel marine vessels; 4.) Internal combustion engines attached to a foundation at a location for at least 12 consecutive months; 5.) Recreational vehicles and snowmobiles; and 6.) Stationary or transportable gas turbines for power generation.

The commission is required to submit a new SIP revision by the end of 2000 which will bring the HGA nonattainment area into attainment with the ozone NAAQS by 2007. The rule proposed for the HGA nonattainment area in this notice is one element of the HGA Post-1999 ROP/Attainment Demonstration SIP. A SIP is a plan developed for any region where existing (measured and/or modeled) ambient levels of pollutants exceed the levels specified in a national standard. The plan sets forth a control strategy that provides emission reductions necessary for attainment and maintenance of the national standards. The proposed set of rules are necessary for the HGA nonattainment area to be able to demonstrate attainment with the ozone NAAQS.

The cost of the technology needed to reduce emissions from these engines to comply with the standards is projected by an environmental consultant (Environ) to be approximately $100 to $500 per engine depending upon the engine size and typical engine type. Engines that currently apply closed- loop control would require less additional equipment reducing the overall cost of meeting the new standard. The commission estimated that the total cost impact of reducing emissions from the 176,522 engines to be purchased during calendar years 2004 through 2007 will be in the range of $18 million to $88 million or an average of approximately $4 million to $22 million per year from 2004 through 2007. A breakdown of the total number of engines bought by owner (i.e. state and local government, individuals or businesses) is not available at this time. However, the costs are not anticipated to be significant to any single unit of state or local government, unless that unit of government replaces between 200 and 1,000 of these engines annually.

PUBLIC BENEFIT AND COSTS

Mr. Davis also determined that for each year of the first five years the proposed amendments to Chapter 114 are in effect, the public benefit anticipated from enforcement of and compliance with the proposed amendments will be the potential reduction of NO x and VOC emissions, potentially improved air quality, and contribution toward demonstration of attainment with the ozone NAAQS.

There are no significant fiscal implications anticipated to individuals, state and local government agencies, and businesses statewide that own or operate affected equipment powered by LSI engines as a result of implementing the proposed amendments unless an entity replaces between 200 and 1,000 of these engines annually. The proposed amendments to Chapter 114 would require units of state and local government, businesses, and individuals statewide that own or operate non-road LSI engines of 25 hp and larger produced on or after January 1, 2004, and all equipment and vehicles produced on or after January 1, 2004 that use such engines to use LSI engines certified under 13 CCR 9 as adopted by the CARB on October 19, 1999. Affected owners and operators of this equipment will not be required to retrofit or purchase new engines for their existing inventory. However, if equipment is replaced with equipment produced after January 1, 2004, the new equipment must meet the proposed standards.

The proposed amendments allow manufacturers to continue to sell in-stock equipment that predates the proposed amendments in a phase-down manner. The phase-down requires that 25% of the equipment sold in year 2004 must have CARB-certified engines; 50% in year 2005; and 100% in year 2006 and thereafter. It is estimated that 25% of the engines sold in year 2004 will be CARB-certified engines that meet the proposed standards. The commission also estimated that 50% of the engines sold in year 2005 will be CARB-certified engines. In years 2006 and thereafter, the commission estimated that all engines sold will be CARB-certified engines. The commission estimated that 12,089 CARB- certified engines will be purchased statewide during year 2004; 27,098 certified engines in year 2005; 65,189 certified engines in 2006; and 72,146 certified engines in 2007, for a total of 176,522 CARB- certified engines during calendar years 2004 through 2007.

The cost of the technology needed to reduce emissions from these engines to comply with the standards is projected by an environmental consultant (Environ) to be approximately $100 to $500 per engine depending upon the engine size and typical engine type. Engines that currently apply closed- loop control would require less additional equipment reducing the overall cost of meeting the new standard. It is estimated that the total cost impact of reducing emissions from the 176,522 engines projected to be purchased during calendar years 2004 through 2007 will be in the range of $18 million to $88 million or an average of approximately $4 million to $22 million per year from 2004 through 2007.

These costs may be mitigated by improved performance of these types of engines. The following is quoted from an EPA Engine Programs and Compliance Division Memorandum dated January 29, 1999, titled California Requirements for Large SI Engines and Possible EPA Approaches : "Upgrading to modern engine technologies greatly improves the capability of these engines to control emissions and will generally improve engine performance. Electronically-controlled closed-loop operation also provides the potential for great improvement in engine operation. For example, improving control of combustion may allow a fuel economy improvement of 15% to 20%. Also, feedback control of air-fuel ratios eliminates much of the need to maintain and adjust a large number of fuel system calibrations, resulting in reduced product inventories and, more importantly, less downtime and maintenance for equipment in the field. Finally, improved control of the upgraded engines should lead to significantly longer engine lifetimes. The net present value of these benefits would likely be considerably greater than the incremental cost of improving the engines."

SMALL AND MICRO-BUSINESS ASSESSMENT

There are no significant fiscal implications anticipated to small and micro-businesses as a result of implementing the proposed amendments because there are no known small or micro-businesses that would need to replace from 200 to 1,000 of these engines annually. Estimates of the number of small and micro-businesses statewide that own and operate non-road equipment powered by LSI engines of 25 hp and larger are not available at this time; however, it is anticipated that costs would be similar to those for business in general as indicated in the Public Benefit and Costs Section of this preamble. The cost of the technology needed to reduce emissions from these engines to comply with the standards is projected by an environmental consultant (Environ) to be approximately $100 to $500 per engine depending upon the engine size and typical engine type. Engines that currently apply closed-loop control would require less additional equipment reducing the overall cost of meeting the new standard. The costs will depend less on the relative size of the company, and more on the size and number of non-road equipment powered by LSI engines that they own and operate.

DRAFT REGULATORY IMPACT ANALYSIS DETERMINATION

The commission reviewed the proposed rulemaking in light of the regulatory analysis requirements of Texas Government Code, §2001.0225, and determined that the rulemaking does not meet the definition of a "major environmental rule" as defined in that statute. "Major environmental rule" means a rule, the specific intent of which is to protect the environment or reduce risks to human health from environmental exposure and that may adversely affect in a material way the economy, a sector of the economy, productivity, competition, jobs, the environment, or the public health and safety of the state or a sector of the state. The new sections to Chapter 114 are one element of the HGA attainment SIP. While the new rules are intended to protect the environment, based on the analysis provided in the preamble, including the discussion in the Public Benefit and Costs section of this preamble, the commission does not believe the rules will adversely affect, in a material way, the sale or use of non-road large spark-ignition (LSI) engines. The commission does not believe these entities comprise a sector of the economy, or that these rules will adversely affect in a material way the economy, productivity, competition, jobs, the environment, or the public health and safety of the state or a sector of the state.

Provisions of 42 USC, §7410 require states to adopt a SIP which provides for "implementation, maintenance, and enforcement" of the primary NAAQS in each air quality control region of the state. While §7410 does not require specific programs, methods, or reductions in order to meet the standard, state SIPs must include "enforceable emission limitations and other control measures, means or techniques (including economic incentives such as fees, marketable permits, and auctions of emissions rights), as well as schedules and timetables for compliance as may be necessary or appropriate to meet the applicable requirements of this chapter," (meaning Chapter 85, Air Pollution Prevention and Control). It is true that 42 USC does require some specific measures for SIP purposes, like the inspection and maintenance program, but those programs are the exception, not the rule, in the SIP structure of 42 USC. The provisions of 42 USC recognize that states are in the best position to determine what programs and controls are necessary or appropriate in order to meet the NAAQS. This flexibility allows states, affected industry, and the public, to collaborate on the best methods for attaining the NAAQS for the specific regions in the state. Even though 42 USC allows states to develop their own programs, this flexibility does not relieve a state from developing a program that meets the requirements of §7410. Thus, while specific measures are not generally required, the emission reductions are required. States are not free to ignore the requirements of §7410 and must develop programs to assure that the nonattainment areas of the state will be brought into attainment on schedule.

The requirement to provide a fiscal analysis of proposed regulations in the Texas Government Code was amended by Senate Bill 633 (SB 633) during the 75th Legislative Session, 1999. The intent of SB 633 was to require agencies to conduct a regulatory impact analysis (RIA) of extraordinary rules. These are identified in the statutory language as major environmental rules that will have a material adverse impact and will exceed a requirement of state law, federal law, or a delegated federal program, or are adopted solely under the general powers of the agency. With the understanding that this requirement would seldom apply, the commission provided a cost estimate for SB 633 that concluded "based on an assessment of rules adopted by the agency in the past, it is not anticipated that the bill will have significant fiscal implications for the agency due to its limited application." The commission also noted that the number of rules that would require assessment under the provisions of the bill was not large. This conclusion was based, in part, on the criteria set forth in the bill that exempted proposed rules from the full analysis unless the rule was a major environmental rule that exceeds a federal law. As previously discussed, 42 USC does not require specific programs, methods, or reductions in order to meet the NAAQS; thus, states must develop programs for each nonattainment area to ensure that area will meet the attainment deadlines. Because of the ongoing need to address nonattainment issues, the commission routinely proposes and adopts SIP rules. The legislature is presumed to understand this federal scheme. If each rule proposed for inclusion in the SIP was considered to be a major environmental rule that exceeds federal law, then every SIP rule would require the full RIA contemplated by SB 633. This conclusion is inconsistent with the conclusions reached by the commission in its cost estimate and by the Legislative Budget Board (LBB) in its fiscal notes. Since the legislature is presumed to understand the fiscal impacts of the bills it passes, and that presumption is based on information provided by state agencies and the LBB, the commission believes that the intent of SB 633 was only to require the full RIA for rules that are extraordinary in nature. While the SIP rules will have a broad impact, that impact is no greater than is necessary or appropriate to meet the requirements of the FCAA. For these reasons, rules proposed for inclusion in the SIP fall under the exception in Texas Government Code, §2001.0225(a), because they are required by federal law.

The proposed amendments to Chapter 114 are intended to protect the environment or reduce risks to human health from environmental exposure to ozone but are not anticipated to affect in a material way, the economy, a sector of the economy, productivity, competition, jobs, the environment, or the public health and safety of the state or a sector of the state. The proposed amendments would require units of state and local government, businesses, and individuals statewide that own or operate model year 2004 and subsequent non-road LSI engines of 25 hp and larger, and all equipment and vehicles that use such engines to use LSI engines certified under 13 CCR 9 as adopted by the CARB on October 19, 1999. The increased cost of $100 to $500 per engine would not cause material impact given the high total cost of this type of equipment. This air pollution control program is part of the strategy to reduce emissions of NO x necessary for the counties included in the HGA nonattainment area to be able to demonstrate attainment with the ozone NAAQS. The commission is required to submit a new SIP revision by the end of 2000 which will bring the HGA nonattainment area into attainment by 2007. The rules proposed for HGA nonattainment area in this notice is one element of the ozone attainment demonstration SIP for HGA. The proposed set of rules are necessary for the HGA nonattainment area to be able to demonstrate attainment with the ozone NAAQS. In addition, §2001.0225 only applies to a major environmental rule, the result of which is to: exceed a standard set by federal law, unless the rule is specifically required by state law; exceed an express requirement of state law, unless the rule is specifically required by federal law; exceed a requirement of a delegation agreement or contract between the state and an agency or representative of the federal government to implement a state and federal program; or adopt a rule solely under the general powers of the agency instead of under a specific state law.

This proposal is not an express requirement of state law. This proposal is intended to help bring ozone nonattainment areas into compliance, and to help keep attainment and near nonattainment areas from becoming nonattainment areas. The proposed amendments do not exceed a standard set by federal law, exceed an express requirement of state law unless specifically required by federal law, nor exceed a requirement of a delegation agreement. The proposed amendments were not developed solely under the general powers of the agency but were specifically developed to meet the air quality standards established under federal law as NAAQS, as authorized under Texas Clean Air Act (TCAA), §§382.012, 382.017, 382.019, and 382.039.

The commission invites public comment on the draft regulatory impact analysis.

TAKINGS IMPACT ASSESSMENT

The commission has prepared a takings impact assessment for these rules in accordance with Texas Government Code, §2007.043. The following is a summary of that assessment. The specific purpose of the rulemaking is to establish emission requirements on model year 2004 and subsequent non-road, LSI engines 25 hp and larger and all equipment and vehicles that use such engines by requiring these engines to be certified under 13 CCR 9 throughout the state. This proposed rulemaking will act as an air pollution control strategy to reduce NO x emissions in the ozone nonattainment areas so that they may demonstrate attainment with the ozone NAAQS and maintain air quality in near nonattainment areas across the state. Promulgation and enforcement of the proposed rules will not burden private, real property. Although the proposed rules do not directly prevent a nuisance or prevent an immediate threat to life or property, they do prevent a real and substantial threat to public health and safety, and partially fulfill a federal mandate under 42 USC, §7410. Specifically, the emissions limitations and delays within this proposal were developed in order to meet the ozone NAAQS set by the EPA under 42 USC, §7409. States are primarily responsible for ensuring attainment and maintenance of the NAAQS once the EPA has established them. Under 42 USC, §7410 and related provisions, states must submit, for EPA approval, SIPs that provide for the attainment and maintenance of NAAQS through control programs directed to sources of the pollutants involved. Therefore, the purpose of the rule proposal is to implement a cleaner-burning, non-road, LSI engine program necessary for the entire state to meet air quality standards established under federal law as NAAQS. Consequently, the exemption which applies to these proposed rules is that of an action reasonably taken to fulfill an obligation mandated by federal law. Therefore, these proposed revisions will not constitute a taking under the Texas Government Code, Chapter 2007.

COASTAL MANAGEMENT PROGRAM CONSISTENCY REVIEW

The commission determined that the proposed rulemaking relates to an action or actions subject to the Texas Coastal Management Program (CMP) in accordance with the Coastal Coordination Act of 1991, as amended (Texas Natural Resources Code, §§33.201 et seq.), and the commission rules in 30 TAC Chapter 281, Subchapter B, concerning Consistency with the CMP. As required by 30 TAC §281.45(a)(3) and 31 TAC §505.11(b)(2), relating to actions and rules subject to the CMP, commission rules governing air pollutant emissions must be consistent with the applicable goals and policies of the CMP. The commission reviewed this action for consistency with the CMP goals and policies in accordance with the rules of the Coastal Coordination Council, and determined that the action is consistent with the applicable CMP goals and policies. The CMP goal applicable to this rulemaking action is the goal to protect, preserve, and enhance the diversity, quality, quantity, functions, and values of coastal natural resource areas (31 TAC §501.12(1)). No new sources of air contaminants will be authorized and NO x air emissions will be reduced as a result of these rules. The CMP policy applicable to this rulemaking action is the policy that commission rules comply with regulations in 40 Code of Federal Regulations (CFR), to protect and enhance air quality in the coastal area (31 TAC §501.14(q)). This rulemaking action complies with 40 CFR 50, National Primary and Secondary Ambient Air Quality Standards, and 40 CFR 51, Requirements for Preparation, Adoption, and Submittal Of Implementation Plans. Therefore, in compliance with 31 TAC §505.22(e), this rulemaking action is consistent with CMP goals and policies.

Interested persons may submit comments on the consistency of the proposed rules with the CMP during the public comment period.

ANNOUNCEMENT OF HEARINGS

The commission will hold public hearings on this proposal at the following times and locations: September 18, 2000, 10:00 a.m., Lone Star Convention Center, 9055 Airport Road (FM 1484), Conroe; September 18, 2000, 7:00 p.m., Lake Jackson Civic Center, 333 Highway 332 East, Lake Jackson; September 19, 2000, 10:00 a.m. and 7:00 p.m., George Brown Convention Center, 1001 Avenida de Las Americas, Houston; September 20, 2000, 9:00 a.m., VFW Hall, 6202 George Bush Drive, Katy; September 20, 2000, 6:00 p.m., East Harris County Community Center, 7340 Spencer, Pasadena; September 21, 2000, 10:00 a.m., Southeast Texas Regional Airport Media Room, 6000 Airline Drive, Beaumont; September 21, 2000, 2:00 p.m., Amarillo City Commission Chambers, City Hall, 509 East 7th Avenue, Amarillo; September 21, 2000, 6:00 p.m., Charles T. Doyle Convention Center, 21st Street at Phoenix Lane, Texas City; September 22, 2000, 10:00 a.m., Dayton High School, 2nd Floor Lecture Room, 3200 North Cleveland Street, Dayton; September 22, 2000, 11:00 a.m., El Paso City Council Chambers, 2 Civic Center Plaza, 2nd Floor, El Paso; September 22, 2000, 2:00 p.m., North Central Texas Council of Governments, 2nd Floor Board Room, 616 Six Flags Drive, Suite 200, Arlington; and September 25, 2000, 10:00 a.m., Texas Natural Resource Conservation Commission, 12100 North I-35, Building E, Room 201S, Austin. The hearings are structured for the receipt of oral or written comments by interested persons. Registration will begin one hour prior to each hearing. Individuals may present oral statements when called upon in order of registration. A four-minute time limit will be established at each hearing to assure that enough time is allowed for every interested person to speak. Open discussion will not occur during each hearing; however, agency staff members will be available to discuss the proposal one hour before each hearing, and will answer questions before and after each hearing.

Persons with disabilities who have special communication or other accommodation needs, who are planning to attend a hearing, should contact the Office of Environmental Policy, Analysis, and Assessment at (512) 239-4900. Requests should be made as far in advance as possible.

SUBMITTAL OF COMMENTS

Written comments may be submitted to Heather Evans, Office of Environmental Policy, Analysis, and Assessment, MC 206, P.O. Box 13087, Austin, Texas 78711-3087, faxed to (512) 239- 4808, or emailed to siprules@tnrcc.state.tx.us . All comments should reference Rule Log Number 2000-011G-114-AI. Comments must be received by 5:00 p.m., September 25, 2000. For further information, please contact Roland Castaneda, II at (512) 239-0774, or Alan Henderson at (512) 239-1510.

STATUTORY AUTHORITY

The amendments are proposed under Texas Water Code (TWC), §5.103, which authorizes the commission to adopt rules necessary to carry out its powers and duties under the TWC, and under the Texas Health and Safety Code, TCAA, §382.017, which provides the commission the authority to adopt rules consistent with the policy and purposes of the TCAA. The amendments are also proposed under TCAA, §382.011, which authorizes the commission to control the quality of the state's air; §382.012, which authorizes the commission to prepare and develop a general, comprehensive plan for the control of the state's air; §382.019, which authorizes the commission to adopt rules to control and reduce emissions from engines used to propel land vehicles; and §382.039, which authorizes the commission to develop and implement transportation programs and other measures necessary to demonstrate attainment and protect the public from exposure to hazardous air contaminants from motor vehicles.

The proposed amendments implement TCAA, §382.002, relating to Policy and Purpose; §382.011, relating to General Powers and Duties; §382.012, relating to State Air Control Plan; §382.019, relating to Methods Used to Control and Reduce Emissions from Land Vehicles; and §382.039, relating to Attainment Program.

§114.421.Emission Specifications.

(a)

(No change.)

(b)

Exhaust emissions from new non-road, LSI engines manufactured for sale, sold, or offered for sale, or that are introduced, delivered or imported for introduction into commerce in the State of Texas [ counties listed in §114.429 of this title (relating to Affected Counties and Compliance Schedules) ] shall not exceed the requirements of Title 13, California Code of Regulations, Chapter 9 (13 CCR 9), §2433(b), concerning Exhaust Emission Standards and Test Procedures -- Off-Road Large Spark-Ignition Engines, as effective on November 18, 1999.

(c)

New non-road, LSI engines operated in the State of Texas [ counties listed in §114.429 of this title ] shall not exceed the requirements of 13 CCR 9, §2433(b).

(d)

(No change.)

§114.429.Affected Counties and Compliance Schedules.

[ (a)

The provisions of this division shall apply in the following counties: Collin, Dallas, Denton, Ellis, Johnson, Kaufman, Parker, Rockwall, and Tarrant Counties.]

(a)

[ (b) ] Beginning with model year 2004 , but no later than January 1, 2004 , all sales of new non-road, large spark-ignition (LSI) engines in the State of Texas [ affected counties ] shall comply with §114.421(b) of this title (relating to Emissions Specifications) and §114.422 of this title (relating to Control Requirements).

(b)

[ (c) ] Beginning January 1, 2004, new non-road, LSI engines as defined in §114.420 of this title (relating to Definitions) which are used in the State of Texas [ affected counties ] shall comply with §114.421(c) of this title.

This agency hereby certifies that the proposal has been reviewed by legal counsel and found to be within the agency's legal authority to adopt.

Filed with the Office of the Secretary of State, on August 11, 2000.

TRD-200005645

Margaret Hoffman

Director, Environmental Law Division

Texas Natural Resource Conservation Commission

Earliest possible date of adoption: September 24, 2000

For further information, please call: (512) 239-0348


5. NITROGEN OXIDES REDUCTION SYSTEMS

30 TAC §§114.440 - 114.442, 114.445, 114.446, 114.448, 114.449

The Texas Natural Resource Conservation Commission (commission) proposes new §114.440, Definitions; §114.441, Applicability; §114.442, Control Requirements; §114.445, Emission Reduction Credits; §114.446, Recordkeeping and Labeling; §114.448; Registration; and §114.449; Affected Counties and Compliance Dates. The commission proposes these amendments to Chapter 114, Control of Air Pollution From Motor Vehicles; Subchapter I, Non-road Engines; new Division 5, Nitrogen Oxides Reduction Systems; and corresponding revisions to the state implementation plan (SIP) in order to control ground-level ozone in the Houston/Galveston (HGA) ozone nonattainment area.

BACKGROUND AND SUMMARY OF THE FACTUAL BASIS FOR THE PROPOSED RULES

The HGA ozone nonattainment area is classified as Severe-17 under the Federal Clean Air Act (FCAA) Amendments of 1990 (42 United States Code (USC), §§7401 et seq.), and therefore is required to attain the one-hour ozone standard of 0.12 parts per million (ppm) by November 15, 2007. The HGA area, defined by Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller Counties, has been working to develop a demonstration of attainment in accordance with 42 USC, §7410. On January 4, 1995, the state submitted the first of its Post- 1996 SIP revisions for HGA.

The January 1995 SIP consisted of urban airshed model (UAM) modeling for 1988 and 1990 base-case episodes, adopted rules to achieve a 9% rate-of-progress (ROP) reduction in volatile organic compounds (VOC), and a commitment schedule for the remaining ROP and attainment demonstration elements. At the same time, but in a separate action, the State of Texas filed for the temporary nitrogen oxides (NO x ) waiver allowed by 42 USC, §7511a(f). The January 1995 SIP and the NO x waiver were based on early base-case episodes which marginally exhibited model performance in accordance with the United States Environmental Protection Agency (EPA) modeling performance standards, but which had a limited data set as inputs to the model. In 1993 and 1994, the commission was engaged in an intensive data-gathering exercise known as the COAST study. The state believed that the enhanced emissions inventory, expanded ambient air quality and meteorological monitoring, and other elements would provide a more robust data set for modeling and other analysis, which would lead to modeling results that the commission could use to better understand the nature of the ozone air quality problem in the HGA area.

Around the same time as the 1995 submittal, EPA policy regarding SIP elements and timelines went through changes. Two national programs in particular resulted in changing deadlines and requirements. The first of these programs was the Ozone Transport Assessment Group. This group grew out of a March 2, 1995 memo from Mary Nichols, former EPA Assistant Administrator for Air and Radiation, that allowed states to postpone completion of their attainment demonstrations until an assessment of the role of transported ozone and precursors had been completed for the eastern half of the nation, including the eastern portion of Texas. Texas participated in this study, and it has been concluded that Texas does not significantly contribute to ozone exceedances in the Northeastern United States. The other major national initiative that has impacted the SIP planning process is the revisions to the national ambient air quality standard (NAAQS) for ozone. The EPA promulgated a final rule on July 18, 1997 changing the ozone standard to an eight-hour standard of 0.08 ppm. In November 1996, concurrent with the proposal of the standards, the EPA proposed an interim implementation plan (IIP) that it believed would help areas like HGA transition from the old to the new standard. In an attempt to avoid a significant delay in planning activities, Texas began to follow this guidance, and readjusted its modeling and SIP development timelines accordingly. When the new standard was published, the EPA decided not to publish the IIP, and instead stated that, for areas currently exceeding the one-hour ozone standard, that standard would continue to apply until it is attained. The FCAA requires that HGA attain the standard by November 15, 2007.

The EPA issued revised draft guidance for areas such as HGA that do not attain the one-hour ozone standard. The commission adopted on May 6, 1998 and submitted to the EPA on May 19, 1998 a revision to the HGA SIP which contained the following elements in response to EPA's guidance: UAM modeling based on emissions projected from a 1993 baseline out to the 2007 attainment date; an estimate of the level of VOC and NO x reductions necessary to achieve the one-hour ozone standard by 2007; a list of control strategies that the state could implement to attain the one-hour ozone standard; a schedule for completing the other required elements of the attainment demonstration; a revision to the Post-1996 9% ROP SIP that remedied a deficiency that the EPA believed made the previous version of that SIP unapprovable; and evidence that all measures and regulations required by Subpart 2 of Title I of the FCAA to control ozone and its precursors have been adopted and implemented, or are on an expeditious schedule to be adopted and implemented.

In November 1998, the SIP revision submitted to the EPA in May 1998 became complete by operation of law. However, the EPA stated that it could not approve the SIP until specific control strategies were modeled in the attainment demonstration. The EPA specified a submittal date of November 15, 1999 for this modeling. In a letter to the EPA dated January 5, 1999, the state committed to model two strategies showing attainment.

As the HGA modeling protocol evolved, the state eventually selected and modeled seven basic modeling scenarios. As part of this process, a group of HGA stakeholders worked closely with commission staff to identify local control strategies for the modeling. Some of the scenarios for which the stakeholders requested evaluation included options such as California-type fuel and vehicle programs as well as an acceleration simulation mode equivalent motor vehicle inspection and maintenance program. Other scenarios incorporated the estimated reductions in emissions that were expected to be achieved throughout the modeling domain as a result of the implementation of several voluntary and mandatory statewide programs adopted or planned independently of the SIP. It should be made clear that the commission did not propose that any of these strategies be included in the ultimate control strategy submitted to the EPA in 2000. The need for and effectiveness of any controls which may be implemented outside the HGA eight-county area will be evaluated on a county-by-county basis.

The SIP revision was adopted by the commission on October 27, 1999, submitted to the EPA by November 15, 1999, and contained the following elements: photochemical modeling of potential specific control strategies for attainment of the one-hour ozone standard in the HGA area by the attainment date of November 15, 2007; an analysis of seven specific modeling scenarios reflecting various combinations of federal, state, and local controls in HGA (additional scenarios H1 and H2 build upon Scenario VIf); identification of the level of reductions of VOC and NO x necessary to attain the one-hour ozone standard by 2007; a 2007 mobile source budget for transportation conformity; identification of specific source categories which, if controlled, could result in sufficient VOC and/or NO x reductions to attain the standard; a schedule committing to submit by April 2000 an enforceable commitment to conduct a mid-course review; and a schedule committing to submit modeling and adopted rules in support of the attainment demonstration by December 2000.

The April 19, 2000 SIP revision for HGA contained the following enforceable commitments by the state: to quantify the shortfall of NO x reductions needed for attainment; to list and quantify potential control measures to meet the shortfall of NO x reductions needed for attainment; to adopt the majority of the necessary rules for the HGA attainment demonstration by December 31, 2000, and to adopt the rest of the shortfall rules as expeditiously as practical, but no later than July 31, 2001; to submit a Post-99 ROP plan by December 31, 2000; to perform a mid- course review by May 1, 2004; and to perform modeling of mobile source emissions using the EPA mobile source emissions model (MOBILE6), to revise the on-road mobile source budget as needed, and to submit the revised budget within 24 months of the model's release. In addition, if a conformity analysis is to be performed between 12 months and 24 months after the MOBILE6 release, the state will revise the motor vehicle emissions budget (MVEB) so that the conformity analysis and the SIP MVEB are calculated on the same basis.

In order for the state to have an approvable attainment demonstration, the EPA has indicated that the state must adopt those strategies modeled in the November submittal and then adopt sufficient controls to close the remaining gap in NO x emissions. The modeling included in this proposal indicates a gap of an additional 77.98 tons per day (tpd) of NO x reductions is necessary for an approvable attainment demonstration. The commission estimates that this measure will achieve a minimum of 16.25 tpd of NO x reductions and is therefore a necessary measure to consider for closing the gap and successfully demonstrating attainment.

The emission reduction requirements included as part of this SIP revision represent substantial, intensive efforts on the part of stakeholder coalitions in the HGA area. These coalitions, involving local governmental entities, elected officials, environmental groups, industry, consultants, and the public, as well as the commission and the EPA, have worked diligently to identify and quantify potential control strategy measures for the HGA attainment demonstration. Local officials from the HGA area have formally submitted a resolution to the commission, requesting the inclusion of many specific emission reduction strategies.

The current SIP revision contains rules, enforceable commitments, and photochemical modeling analyses in support of the HGA ozone attainment demonstration. In addition, this SIP contains Post- 1999 ROP plans for the milestone years 2002, 2005, and for the attainment year 2007. The SIP also contains enforceable commitments to implement further measures, if needed, in support of the HGA attainment demonstration, as well as a commitment to perform and submit a mid-course review.

The HGA ozone nonattainment area will need to ultimately reduce NOx more than 750 tpd to reach attainment with the one-hour standard. In addition, a VOC reduction of about 25% will have to be achieved. Adoption of the NO x reduction systems program will contribute to attainment and maintenance of the one-hour ozone standard in the HGA area.

These proposed amendments are one element of the control strategy for the HGA Post-1999 ROP/Attainment Demonstration SIP. The proposed amendments would require owners or operators of on-road or non-road vehicles or equipment manufactured prior to model year 1997 having a heavy-duty on-road or non-road engine and fueled by gasoline, diesel, diesel emulsion fuel or any alternate fuel located in Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller Counties to use exhaust systems that will achieve a 80% reduction in NO x emissions from what the engine would emit without the exhaust system. Examples of exhaust systems that could be used to meet the proposed rule are NO x adsorbers, methane catalysts, diesel oxidation catalysts, selective catalyst reduction, lean NO x catalysts, and other exhaust after-treatment systems. Adoption of these requirements to reduce NO x can contribute to attainment and maintenance of the one-hour ozone standard in the HGA area.

The commission solicits comment on additional flexibilities relating to rule content and implementation which have not been addressed in this or other concurrent rulemakings. These flexibilities may be available for both mobile and stationary sources. Additional flexibilities may also be achieved through innovative and/or emerging systems which may become available in the future. Additional sources of funds for incentive programs may become available to substitute for some of the measures considered here.

SECTION BY SECTION DISCUSSION

The proposed §114.440 has the following definitions: "NO x Reduction System" is defined as an exhaust or engine-related control device designed for gasoline or diesel engine exhaust systems to achieve NOx emissions reductions. For example, a NO x Reduction System could include exhaust systems which use catalysts such as NO x adsorbers, methane catalysts, diesel oxidation catalysts, selective catalyst reduction, lean NO x catalysts, and other exhaust after-treatment systems. A "Heavy- Duty On-Road Engine" is defined as an on-road engine installed in an on-road vehicle that is greater than 10,000 pounds gross vehicle weight rating (GVWR) and is fueled by gasoline, diesel, diesel emulsion fuel, or any alternate fuel. This would exclude vehicles regulated under the federal Tier 2 engine standards. A "Heavy-Duty Non-Road Engine" is defined as a non-road engine used in locomotives, tugs, tow-boats, and ferry boats, that is greater than 175 nominal horsepower (hp) as rated by the manufacturer on the vehicle nameplate and is fueled by gasoline, diesel, diesel emulsion fuel, or any alternate fuel. The proposal focuses on the use of both heavy-duty on-road and non-road engines; because, as seen in the EPA MOBILE and NONROAD models, heavy-duty engines have NOx emissions which are six to 12 times higher than their light-duty counterparts. "Primarily Operated" is defined as the use of a motor vehicle or engine more than 60 calendar days per year in an affected county; it is presumed that an on-road vehicle is primarily operated in the county in which it is registered.

Proposed §114.441 provides that owners or operators of on-road or non-road vehicles or equipment manufactured prior to model year 1997 having a heavy-duty on-road or non-road engine and fueled by gasoline, diesel, diesel emulsion fuel, or any alternate fuel primarily operated in Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller Counties must comply with the requirements of Subchapter I, Division 5. The commission believes these model years are appropriate because newer vehicles and engines have generally much lower NO x emissions. Thus, the commission believes the regulatory focus should be on the older heavy-duty engines with higher emissions.

Proposed §114.442 provide the criteria for use of heavy-duty on-road and non-road engines in the affected counties. NO x reduction systems used by any heavy-duty on-road and non-road engines in the affected counties must, at a minimum, comply with the emissions testing and emission standards required by applicable EPA or California Air Resources Board (CARB) regulations. The NO x reduction system installed on the vehicle or engine must be able to reduce NO x emissions by at least 80%. Initial laboratory tests show that the use of NO x reduction systems can reduce NOx emissions from 65% to in excess of 99%. Based on the emissions modeling for HGA, the commission believes the 80% reduction is necessary to achieve attainment. Further, the NO x reduction system must not result in a net increase in other primary pollutants.

The commission anticipates that NO x reduction systems currently under development will be available by May 1, 2004, the proposed compliance date for the proposed rules. The commission believes this is true because NO x reduction systems are being developed. However, the commission acknowledges that no NO x reduction systems have been certified for use by the EPA in on-road and non-road applications. This is because most of these systems are used in large, stationary, industrial diesels which have steady-state loads. Nevertheless, the commission believes that these systems will be developed and that they are critical towards obtaining necessary reductions in NO x emissions in the HGA nonattainment area. Further, to provide consistency in the development process and for implementation, it is important that these systems be able to meet applicable EPA and CARB standards. However, heavy- duty on-road and non-road engines are often subjected to harsh, transient loads which cause variation in catalyst performance. For these reasons, the commission is specifically soliciting comments about alternatives to the use of NO x reduction systems as means of control which could achieve the same emission reductions.

Proposed §114.445 provides the incentive for owners or operators of affected heavy-duty on-road and non-road engines to install NO x reduction systems that result in reductions in excess of the required 80% NO x emissions reduction. If a NO x reduction system is used that will achieve greater than 80% NOx reductions, the owner or operator may obtain mobile emissions reduction credits in accordance with §101.29 of this title (relating to Emission Credit Banking and Trading.) In addition to demonstrating that the NO x reduction system will achieve NOx emission reductions of greater than 80%, the owner or operator must demonstrate that all applicable sections of Chapter 114 are met, including Subchapter B, §114.20 and §114.21, relating to Motor Vehicle Anti-Tampering Requirements; Subchapter E, §§114.150 - 114.157, relating to Low Emission Vehicle Fleet Requirements; and Subchapter I, §§114.400 - 114.439, relating to Non-Road Engines. This will ensure that the emissions from NO x reduction systems comply with Chapter 114 and that additional reductions are surplus to reductions required by other rule requirements.

Recordkeeping and labeling requirements are addressed in proposed §114.446. The owner or operator of heavy-duty on-road and non-road engines in the affected counties must follow manufacturer installation, maintenance, and labeling requirements as required for the NO x reduction system and by the EPA in 40 Code of Federal Regulations (CFR) Part 86, Control of Emissions from New and In-Use Highway Vehicles and Engines as amended on February 28, 2000; or 40 CFR Part 89, Control of Emissions from New and In-Use Nonroad Compression-Ignition Engines; or by CARB in Title 13, California Code of Regulations, §1976, as amended on February 26, 1999.

Registration of on-road and non-road engines is specified in §114.448. Owners and operators of affected engines must register using a form available from the executive director which proves that a NO x reduction system that meets the requirements of Chapter 114 was properly installed.

Affected counties are addressed in §114.449. The affected counties in the HGA ozone nonattainment area are Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller. If adopted, compliance with the rules would be required on May 1, 2004.

FISCAL NOTE: COSTS TO STATE AND LOCAL GOVERNMENT

John Davis, Technical Specialist with Strategic Planning and Appropriations, has determined that for the first five-year period the proposed amendments are in effect, there will be fiscal implications which may be significant for units of state and local government located in the HGA ozone nonattainment area as a result of administration or enforcement of the proposed amendments.

The proposed amendments require the use of NO x reduction systems, that will achieve a 80% reduction in NO x , from all engines manufactured prior to model year 1997 installed in on-road vehicles with a GVWR greater than 10,000 pounds and on engines rated at 175 nominal hp or greater used in non-road locomotives and commercial marine vessels primarily operated in the HGA ozone nonattainment area by May 1, 2004. The NO x reductions must be accomplished without increasing other pollutants. The HGA area consists of Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller counties. The proposed rules would affect approximately 340 state and local government and 64,000 privately owned and operated on-road heavy-duty vehicles and an unknown number of locomotives and commercial marine vessels.

Examples of NO x reduction systems that could be used to meet the proposed rules are NO x absorbers, methane catalysts, diesel oxidation catalyst, selective catalyst reduction, lean NO x catalysts, and other exhaust after-treatment systems.

The commission anticipates that approximately 340 heavy-duty on-road vehicles are owned and operated by state and local governments. Based on a report from the Manufacturers of Emission Controls Association (MECA) titled Emission Control Retrofit of Diesel-Fueled Vehicles , the cost to state and local governments to purchase emission control devices that would meet the emission requirements of the proposed amendments would range from $500 to $2,000 per heavy-duty on-road and non-road vehicles/equipment.

The total costs to state and local governments within the HGA area would be approximately $170,000 to $680,000 for heavy-duty on-road vehicles/equipment as a result of implementing the proposed amendments. The total costs do not factor in non-road locomotives and commercial marine vessels because the total number owned and operated by state and local governments in the HGA area is unknown. The commission anticipates the operating costs associated with the proposed amendments will not be significant unless 50 - 200 or more affected vehicles/equipment are owned and operated by a single unit of state or local government.

PUBLIC BENEFIT AND COSTS

Mr. Davis also has determined that for the first five years the proposed amendments are in effect, the public benefit anticipated from enforcement of and compliance with the proposed amendments will be the potential reduction of on-road and non-road mobile source emissions, potentially improved air quality, and contribution toward demonstration of attainment with the NAAQS for the HGA ozone nonattainment areas.

The proposed amendments require the use of NO x reduction systems that will achieve an 80% reduction in NO x , from all engines manufactured prior to model year 1997 installed in on-road vehicles with a GVWR greater than 10,000 pounds and engines rated at 175 nominal hp or greater installed in non-road locomotives and commercial marine vessels primarily operated in the HGA area by May 1, 2004. The NOx reductions must be accomplished without increasing other pollutants.

The commission estimates that approximately 64,000 heavy-duty on-road vehicles affected by the proposed amendments are owned and operated by individuals and businesses. Based on a report from the MECA titled Emission Control Retrofit of Diesel-Fueled Vehicles , the cost to state and local governments to purchase emission control devices that would meet the emission requirements of the proposed amendments would range from $500 to $2,000.

The total costs to individuals and businesses within the HGA area as a result of the proposed amendments would be approximately $32 million to $128 million as a result of implementing the proposed amendments. The total costs does not factor in non-road locomotives or commercial marine vessels because the total number owned and operated by individuals and businesses in the HGA area is unknown. The total fiscal impact to individuals and businesses would depend on the number of vehicles that would be required to have the NOx reducing systems installed.

SMALL AND MICRO-BUSINESS ASSESSMENT

There may be adverse fiscal implications for small or micro-businesses located in the HGA area as a result of administration or enforcement of the proposed amendments. The proposed amendments require the use of NO x reduction systems that will achieve a 80% reduction in NO x , on all engines manufactured prior to model year 1997 installed in on-road heavy-duty vehicles with a GVWR greater than 10,000 pounds or higher, and engines with a hp rating greater than 175 installed in non-road locomotives and commercial marine vessels primarily operated in the HGA area by May 1, 2004. The NO x reductions must be accomplished without increasing other pollutants. Of the approximately 64,000 privately owned and operated on-road heavy- duty vehicles and the unknown number of non-road locomotives and commercial marine vessels affected by the proposed amendments, some are anticipated to be owned and operated by small and/or micro-businesses in an amount that cannot be determined. The cost to small or micro-businesses to purchase emission control devices that would meet the emission requirements of the proposed amendments would range from $500 to $2,000 per vehicle affected by the proposed amendment. The total fiscal impact to small or micro-businesses would depend on the number of vehicles that would be required to have the NO x reduction systems installed.

DRAFT REGULATORY IMPACT ANALYSIS DETERMINATION

The commission reviewed the rulemaking in light of the regulatory analysis requirements of Texas Government Code, §2001.0225, and has determined that the rulemaking action does not meet the definition of a "major environmental rule" as defined in that statute. "Major environmental rule" means a rule the specific intent of which is to protect the environment or reduce risks to human health from environmental exposure and that may adversely affect in a material way the economy, a sector of the economy, productivity, competition, jobs, the environment, or the public health and safety of the state or a sector of the state. The amendments to Chapter 114 are one element of the HGA Post- 1999 ROP/Attainment Demonstration SIP and will require NO x emission reductions from owners or operators of heavy-duty on-road and non-road engines in the HGA ozone nonattainment area. The commission does not believe the rules will have an adverse, material affect or will impact a sector of the economy. While the new rules are intended to protect the environment, based on the analysis provided in the preamble including the discussion in the Public Benefit and Costs section, the commission does not believe the rules will adversely affect, in a material way, the use of heavy-duty engines greater than 10,000 pounds GVWR or heavy-duty non-road engines that are greater than 175 nominal hp as rated by the manufacturer on the nameplate, both of which are fueled by gasoline, diesel, diesel emulsion fuel, or any alternative fuel. The commission does not believe that the owners or operators of these entities comprise a sector of the economy, or that these rules will adversely affect, in a material way, the economy, productivity, competition, jobs, the environment, or the public health and safety of the state or a sector of the state.

Title 42 USC, §7410, requires states to adopt a SIP which provides for "implementation, maintenance, and enforcement" of the primary NAAQS in each air quality control region of the state. While §7410 does not require specific programs, methods, or reductions in order to meet the standard, state SIPs must include "enforceable emission limitations and other control measures, means, or techniques (including economic incentives such as fees, marketable permits, and auctions of emissions rights), as well as schedules and timetables for compliance as may be necessary or appropriate to meet the applicable requirements of this chapter," (meaning Chapter 85, Air Pollution Prevention and Control). It is true that 42 USC does require some specific measures for SIP purposes, like the inspection and maintenance program, but those programs are the exception, not the rule, in the 42 USC SIP structure. The provisions of 42 USC recognize that states are in the best position to determine what programs and controls are necessary or appropriate in order to meet the NAAQS. This flexibility allows states, affected industry, and the public, to collaborate on the best methods for attaining the NAAQS for the specific regions in the state. Even though 42 USC allows states to develop their own programs, this flexibility does not relieve a state from developing a program that meets the requirements of §7410. Thus, while specific measures are not generally required, the emission reductions are required. States are not free to ignore the requirements of §7410 and must develop programs to assure that the nonattainment areas of the state will be brought into attainment on schedule.

The requirement to provide a fiscal analysis of proposed regulations in the Texas Government Code was amended by Senate Bill (SB) 633 during the 75th Legislative Session. The intent of SB 633 was to require agencies to conduct a regulatory impact analysis (RIA) of extraordinary rules. These are identified in the statutory language as major environmental rules that will have a material adverse impact and will exceed a requirement of state law, federal law, or a delegated federal program, or are adopted solely under the general powers of the agency. With the understanding that this requirement would seldom apply, the commission provided a cost estimate for SB 633 that concluded "based on an assessment of rules adopted by the agency in the past, it is not anticipated that the bill will have significant fiscal implications for the agency due to its limited application." The commission also noted that the number of rules that would require assessment under the provisions of the bill was not large. This conclusion was based, in part, on the criteria set forth in the bill that exempted proposed rules from the full analysis unless the rule was a major environmental rule that exceeds a federal law. As previously discussed, 42 USC does not require specific programs, methods, or reductions in order to meet the NAAQS; thus, states must develop programs for each nonattainment area to ensure that area will meet the attainment deadlines. Because of the ongoing need to address nonattainment issues, the commission routinely proposes and adopts SIP rules. The legislature is presumed to understand this federal scheme. If each rule proposed for inclusion in the SIP was considered to be a major environmental rule that exceeds federal law, then every SIP rule would require the full RIA contemplated by SB 633. This conclusion is inconsistent with the conclusions reached by the commission in its cost estimate and by the Legislative Budget Board (LBB) in its fiscal notes. Since the legislature is presumed to understand the fiscal impacts of the bills it passes, and that presumption is based on information provided by state agencies and the LBB, the commission believes that the intent of SB 633 was only to require the full RIA for rules that are extraordinary in nature. While the SIP rules will have a broad impact, that impact is no greater than is necessary or appropriate to meet the requirements of 42 USC. For these reasons, rules proposed for inclusion in the SIP fall under the exception in Texas Government Code, §2001.0225(a), because they are required by federal law. The commission has performed photochemical grid modeling which predicts that NO x emission reductions, such as those required by these rules, will result in reductions in ozone formation in the HGA ozone nonattainment area. This rulemaking action does not exceed an express requirement of state law. This rulemaking action is intended to obtain NO x emission reductions which will result in reductions in ozone formation in the HGA ozone nonattainment area and help bring HGA into compliance with the air quality standards established under federal law as NAAQS for ozone. The rulemaking does not exceed a standard set by federal law, exceed an express requirement of state law (unless specifically required by federal law), or exceed a requirement of a delegation agreement. The rulemaking was not developed solely under the general powers of the agency, but was specifically developed to meet the NAAQS established under federal law and authorized under Texas Clean Air Act (TCAA) §§382.002, 382.011, 382.012, 382.019, and 382.039.

The commission invites public comment on the draft regulatory impact analysis determination.

TAKINGS IMPACT ASSESSMENT

The commission prepared a takings impact assessment for these rules in accordance with Texas Government Code, §2007.043. The following is a summary of that assessment. These proposed new sections are one element of the control strategy for the HGA Post-1999 ROP/Attainment Demonstration SIP. The specific purpose of the rulemaking is to require owners or operators of on- road or non-road vehicles or equipment manufactured prior to model year 1997 having a heavy-duty on-road or non-road engine and fueled by gasoline, diesel, diesel emulsion fuel, or any alternate fuel located in the HGA nonattainment area to use exhaust systems that will achieve a 80% reduction in NO x emissions from what the engine would emit without the exhaust technology. Adoption of these requirements to reduce NO x can contribute to attainment and maintenance of the one-hour ozone standard in the HGA area.

Promulgation and enforcement of the rule amendments will not burden private real property because the NO x reduction system requirement applies to heavy-duty on-road and non-road engines, which are not attached to, or considered to be, private real property. Although the rule revisions do not directly prevent a nuisance or prevent an immediate threat to life or property, they do prevent a real and substantial threat to public health and safety and fulfill federal mandates under the 42 USC, §7410. Specifically, control requirements have been developed to meet the ozone NAAQS set by the EPA under 42 USC, §7409. States are primarily responsible for ensuring attainment and maintenance of NAAQS once the EPA has established them. Under 42 USC, §7410 and related provisions, states must submit, for EPA approval, SIPs that provide for the attainment and maintenance of NAAQS through control programs directed to sources of the pollutants involved. Therefore, the purpose of this rulemaking action is to implement restrictions on the use of heavy-duty on-road and non-road engines in the HGA ozone nonattainment area to meet the air quality standards established under federal law as NAAQS. Consequently, the exemption which applies to these rules is that of an action reasonably taken to fulfill an obligation mandated by federal law; therefore, these proposed rules do not constitute a takings under the Texas Government Code, Chapter 2007.

CONSISTENCY WITH THE COASTAL MANAGEMENT PROGRAM

The commission determined that this rulemaking relates to an action or actions subject to the Texas Coastal Management Program (CMP) in accordance with the Coastal Coordination Act of 1991, as amended (Texas Natural Resources Code, §§33.201 et seq.), and the commission rules in 30 TAC Chapter 281, Subchapter B, concerning Consistency with Texas Coastal Management Program. As required by 31 TAC §505.11(b)(2) and 30 TAC §281.45(a)(3), relating to actions and rules subject to the CMP, commission rules governing air pollutant emissions must be consistent with the applicable goals and policies of the CMP. The commission reviewed this action for consistency with the CMP goals and policies in accordance with the regulations of the Coastal Coordination Council. For this rulemaking, the commission determined that the rules are consistent with the applicable CMP goal expressed in 31 TAC §501.12(1) of protecting and preserving the quality and values of coastal natural resource areas and the policy in 31 TAC §501.14(q), which requires that the commission protect air quality in coastal areas. This rulemaking will require owners or operators of on-road or non-road vehicles or equipment manufactured prior to model year 1997 having a heavy-duty on-road or non-road engine and fueled by gasoline, diesel, diesel emulsion fuel, or any alternate fuel located in the HGA nonattainment area to use exhaust systems that will achieve a 80% reduction in NO x emissions from what the engine would emit without the exhaust system. Adoption of these requirements to reduce NO x can contribute to attainment and maintenance of the one-hour ozone standard in the HGA area. This action is consistent with the CMP because it does not authorize any new emissions and will reduce existing emissions of NO x .

Interested persons may submit comments on the consistency of the proposed rules with the CMP during the public comment period.

ANNOUNCEMENT OF HEARINGS

The commission will hold public hearings on this proposal at the following times and locations: September 18, 2000, 10:00 a.m., Lone Star Convention Center, 9055 Airport Road (FM 1484), Conroe; September 18, 2000, 7:00 p.m., Lake Jackson Civic Center, 333 Highway 332 East, Lake Jackson; September 19, 2000, 10:00 a.m. and 7:00 p.m., George Brown Convention Center, 1001 Avenida de Las Americas, Houston; September 20, 2000, 9:00 a.m., VFW Hall, 6202 George Bush Drive, Katy; September 20, 2000, 6:00 p.m., East Harris County Community Center, 7340 Spencer, Pasadena; September 21, 2000, 10:00 a.m., Southeast Texas Regional Airport Media Room, 6000 Airline Drive, Beaumont; September 21, 2000, 2:00 p.m., Amarillo City Commission Chambers, City Hall, 509 East 7th Avenue, Amarillo; September 21, 2000, 6:00 p.m., Charles T. Doyle Convention Center, 21st Street at Phoenix Lane, Texas City; September 22, 2000, 10:00 a.m., Dayton High School, 2nd Floor Lecture Room, 3200 North Cleveland Street, Dayton; September 22, 2000, 11:00 a.m., El Paso City Council Chambers, 2 Civic Center Plaza, 2nd Floor, El Paso; September 22, 2000, 2:00 p.m., North Central Texas Council of Governments, 2nd Floor Board Room, 616 Six Flags Drive, Suite 200, Arlington; and September 25, 2000, 10:00 a.m., Texas Natural Resource Conservation Commission, 12100 North I-35, Building E, Room 201S, Austin. The hearings are structured for the receipt of oral or written comments by interested persons. Registration will begin one hour prior to each hearing. Individuals may present oral statements when called upon in order of registration. A four-minute time limit will be established at each hearing to assure that enough time is allowed for every interested person to speak. Open discussion will not occur during each hearing; however, agency staff members will be available to discuss the proposal one hour before each hearing, and will answer questions before and after each hearing.

Persons with disabilities who have special communication or other accommodation needs who are planning to attend the hearing should contact the Office of Environmental Policy, Analysis, and Assessment at (512) 239-4900. Requests should be made as far in advance as possible.

SUBMITTAL OF COMMENTS

Written comments may be submitted to Heather Evans, Office of Environmental Policy, Analysis, and Assessment, MC 206, P.O. Box 13087, faxed to (512) 239-4808, or emailed to siprules@tnrcc.state.tx.us . All comments should reference Rule Log Number 2000- 011M-114-AI. Comments must be received by 5:00 p.m., September 25, 2000. For further information, please contact Sam Wells at (512) 239-1441 or Alan Henderson at (512) 239-1510.

STATUTORY AUTHORITY

The new sections are proposed under the Texas Water Code (TWC), §5.103, which authorizes the commission to adopt rules necessary to carry out its powers and duties under the TWC; and under the Texas Health and Safety Code, TCAA, §382.017, which authorizes the commission to adopt rules consistent with the policy and purposes of the TCAA. The new sections are also proposed under TCAA, §382.011, which authorizes the commission to control the quality of the state's air; §382.012, which authorizes the commission to prepare and develop a general, comprehensive plan for the control of the state's air; §382.019, which authorizes the commission to adopt rules to control and reduce emissions from engines used to propel land vehicles; and §382.039, which authorizes the commission to develop and implement transportation programs and other measures necessary to demonstrate attainment and protect the public from exposure to hazardous air contaminants from motor vehicles.

The proposed new sections implement TCAA, §382.002, relating to Policy and Purpose; §382.011, relating to General Powers and Duties; §382.012, relating to State Air Control Plan; §382.019, relating to Methods Used to Control and Reduce Emissions from Land Vehicles; and §382.039, relating to Attainment Program.

§114.440.Definitions.

Unless specifically defined in the TCAA or in the rules of the commission, the terms used by the commission have the meanings commonly ascribed to them in the field of air pollution control. In addition to the terms which are defined by the TCAA, the following words and terms, when used in this chapter, shall have the following meanings, unless the context clearly indicates otherwise.

(1)

Heavy-duty on-road engine - An on-road engine installed in an on-road vehicle that is greater than 10,000 pounds gross vehicle weight rating, and is fueled by gasoline, diesel, diesel emulsion fuel, or any alternate fuel.

(2)

Heavy-duty non-road engine - A non-road engine used in locomotives, tugs, tow-boats, and ferry boats that is greater than 175 nominal horsepower as rated by the manufacturer on the vehicle nameplate and is fueled by gasoline, diesel, diesel emulsion, or any alternate fuel.

(3)

Nitrogen oxides (NO x ) reduction system - An exhaust or engine-related control device designed for gasoline or diesel engine exhaust systems to achieve NO x emissions reductions;

(4)

Primarily operated - Use of a motor vehicle or engine more than 60 calendar days per year in an affected county. It is presumed that an on-road vehicle is primarily operated in the county in which it is registered.

§114.441.Applicability.

(a)

Owners or operators of non-road vehicles or equipment manufactured prior to model year 1997 having a heavy-duty non-road engine primarily operated in the counties listed in §114.449 of this title (relating to Affected Counties and Compliance Dates) must comply with the requirements of this division.

(b)

Owners or operators of on-road vehicles or equipment manufactured prior to model year 1997 having a heavy-duty on-road engine primarily operated in the counties listed in §114.449 of this title must comply with the requirements of this division.

§114.442.Control Requirements.

(a)

Non-road vehicles or equipment manufactured prior to model year 1997 using heavy-duty on-road and non-road engines primarily operated in the counties listed in §114.449 of this title (relating to Affected Counties and Compliance Dates) must use nitrogen oxides (NO x ) emission reduction systems that are approved:

(1)

by the EPA as to their emissions as tested by the applicable Federal Test Procedure in 40 Code of Federal Regulations (CFR) Part 86, Control of Emissions from New and In-Use Highway Vehicles and Engines as amended on February 28, 2000; or 40 CFR Part 89, Control of Emissions from New and In-Use Nonroad Compression-Ignition Engines as amended on October 23, 1998; or

(2)

by the California Air Resources Board as tested by the applicable emissions test in Title 13, California Code of Regulations, §1976, as amended on February 26, 1999.

(b)

Owners or operators of heavy-duty engines subject to §114.441 of this title (relating to Applicability) shall ensure that the NO x reduction system has a minimum control efficiency of 80% for NOx emissions.

(c)

The installation of the NO x reduction system cannot result in an increase in any pollutant.

§114.445.Emission Reduction Credits.

(a)

Owners or operators of heavy-duty engines subject to §114.441 of this title (relating to Applicability) that install nitrogen oxides (NOx ) reduction systems that achieve greater than 80% reductions as required by §114.442 of this title (relating to Control Requirements) may obtain mobile emissions reduction credits in accordance with §101.29 of this title (relating to Emission Credit Banking and Trading.)

(b)

In order to demonstrate that the NO x reduction system will achieve emission reductions of greater than 80%, the owner or operator of the on-road heavy-duty engine or non-road heavy-duty engine must demonstrate that all applicable sections of this chapter are met, including the following provisions:

(1)

§114.20 of this title (relating to Maintenance and Operation of Air Pollution Control Systems or Devices Used to Control Emissions from Motor Vehicles);

(2)

§§114.150-157 of this title (relating to Requirements for Mass Transit Authorities, Requirements for Local Governments and Private Entities, Exceptions, Exceptions for Certain Mass Transit Authorities, Reporting, Record Keeping, and Low Emission Vehicle Fleet Program Compliance Credits); and

(3)

the requirements of Chapter 114, Control of Air Pollution from Motor Vehicles, Subchapter I, Non-Road Engines, Division 5: Airport Ground Support Equipment; Division 2: Heavy Equipment Fleets - Compression-Ignition Engines; Division 3: Non-Road Large Spark-Ignition Engines; and Division 4: Construction Equipment Operating Restrictions.

§114.446.Recordkeeping and Labeling.

Owners or operators of heavy-duty on-road and non-road engines subject to §114.441 of this title (relating to Applicability) that install nitrogen oxides (NO x ) reduction systems must follow all:

(1)

written procedures by the manufacturer of the NO x reduction systems, as to engine maintenance and recordkeeping; and

(2)

written labeling requirements set by the EPA in 40 Code of Federal Regulations (CFR), Part 86, as amended on February 28, 2000 or the California Air Resources Board in Title 13, California Code of Regulations, §1976, as amended on February 26, 1999.

§114.448.Registration.

Owners or operators of heavy-duty on-road and non-road engines subject to §114.441 of this title (relating to Applicability) that install nitrogen oxides (NO x ) reduction systems must submit registration on an appropriate form available from the executive director which will require information that demonstrates compliance with the requirements of this division.

§114.449.Affected Counties and Compliance Dates.

Beginning on May 1, 2004, the requirements of this division shall be enforced in the following counties: Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller.

This agency hereby certifies that the proposal has been reviewed by legal counsel and found to be within the agency's legal authority to adopt.

Filed with the Office of the Secretary of State, on August 11, 2000.

TRD-200005629

Margaret Hoffman

Director, Environmental Law Division

Texas Natural Resource Conservation Commission

Earliest possible date of adoption: September 24, 2000

For further information, please call: (512) 239-0348


6. LAWN SERVICE EQUIPMENT OPERATING RESTRICTIONS

30 TAC §114.452, §114.459

The Texas Natural Resource Conservation Commission (commission) proposes new §114.452, Control Requirements, and §114.459, Affected Counties and Compliance Dates. The commission proposes these revisions to add new Division 6, Lawn Service Equipment Operating Restrictions, to Subchapter I, Non-road Engines; Chapter 114, Control of Air Pollution from Motor Vehicles; and to the associated state implementation plan (SIP). The commission proposes these amendments to Chapter 114 and corresponding revisions to the SIP in order to control ground-level ozone in the Houston/Galveston (HGA) ozone nonattainment area. The proposed revisions are one element of the control strategy for the proposed HGA Post-1996 Rate-of-Progress (ROP)/Attainment Demonstration SIP.

BACKGROUND AND SUMMARY OF THE FACTUAL BASIS FOR THE PROPOSED RULES

The HGA ozone nonattainment area is classified as Severe-17 under the Federal Clean Air Act (FCAA) Amendments of 1990 (42 United States Code (USC), §§7401 et seq.), and therefore is required to attain the one-hour ozone standard of 0.12 parts per million (ppm) by November 15, 2007. The HGA area, defined by Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller Counties, has been working to develop a demonstration of attainment in accordance with 42 USC, §7410. On January 4, 1995, the state submitted the first of its Post-1996 SIP revisions for HGA.

The January 1995 SIP consisted of urban airshed model (UAM) modeling for 1988 and 1990 base-case episodes, adopted rules to achieve a 9% ROP reduction in volatile organic compounds (VOC), and a commitment schedule for the remaining ROP and attainment demonstration elements. At the same time, but in a separate action, the State of Texas filed for the temporary nitrogen oxides (NOx ) waiver allowed by 42 USC, §7511a(f). The January 1995 SIP and the NO x waiver were based on early base-case episodes which marginally exhibited model performance in accordance with the United States Environmental Protection Agency (EPA) modeling performance standards, but which had a limited data set as inputs to the model. In 1993 and 1994, the commission was engaged in an intensive data-gathering exercise known as the COAST study. The state believed that the enhanced emissions inventory, expanded ambient air quality and meteorological monitoring, and other elements would provide a more robust data set for modeling and other analysis, which would lead to modeling results that the commission could use to better understand the nature of the ozone air quality problem in the HGA area.

Around the same time as the 1995 submittal, EPA policy regarding SIP elements and timelines went through changes. Two national programs in particular resulted in changing deadlines and requirements. The first of these programs was the Ozone Transport Assessment Group. This group grew out of a March 2, 1995, memo from Mary Nichols, former EPA Assistant Administrator for Air and Radiation, that allowed states to postpone completion of their attainment demonstrations until an assessment of the role of transported ozone and precursors had been completed for the eastern half of the nation, including the eastern portion of Texas. Texas participated in this study, and it has been concluded that Texas does not significantly contribute to ozone exceedances in the Northeastern United States. The other major national initiative that has impacted the SIP planning process is the revisions to the national ambient air quality standard (NAAQS) for ozone. The EPA promulgated a final rule on July 18, 1997, changing the ozone standard to an eight-hour standard of 0.08 ppm. In November 1996, concurrent with the proposal of the standards, the EPA proposed an interim implementation plan (IIP) that it believed would help areas like HGA transition from the old to the new standard. In an attempt to avoid a significant delay in planning activities, Texas began to follow this guidance, and readjusted its modeling and SIP development timelines accordingly. When the new standard was published, the EPA decided not to publish the IIP, and instead stated that, for areas currently exceeding the one-hour ozone standard, that standard would continue to apply until it is attained. The FCAA requires that HGA attain the standard by November 15, 2007.

The EPA issued revised draft guidance for areas such as HGA that do not attain the one-hour ozone standard. The commission adopted on May 6, 1998, and submitted to the EPA on May 19, 1998, a revision to the HGA SIP which contained the following elements in response to EPA's guidance: UAM modeling based on emissions projected from a 1993 baseline out to the 2007 attainment date; an estimate of the level of VOC and NO x reductions necessary to achieve the one-hour ozone standard by 2007; a list of control strategies that the state could implement to attain the one-hour ozone standard; a schedule for completing the other required elements of the attainment demonstration; a revision to the Post-1996 9% ROP SIP that remedied a deficiency that the EPA believed made the previous version of that SIP unapprovable; and evidence that all measures and regulations required the Subpart 2 of Title I of the FCAA to control ozone and its precursors have been adopted and implemented, or are on an expeditious schedule to be adopted and implemented.

In November 1998, the SIP revision submitted to the EPA in May 1998 became complete by operation of law. However, the EPA stated that it could not approve the SIP until specific control strategies were modeled in the attainment demonstration. The EPA specified a submittal date of November 15, 1999, for this modeling. In a letter to the EPA dated January 5, 1999, the state committed to model two strategies showing attainment.

As the HGA modeling protocol evolved, the state eventually selected and modeled seven basic modeling scenarios. As part of this process, a group of HGA stakeholders worked closely with commission staff to identify local control strategies for the modeling. Some of the scenarios for which the stakeholders requested evaluation included options such as California-type fuel and vehicle programs as well as an acceleration simulation mode equivalent motor vehicle inspection and maintenance program. Other scenarios incorporated the estimated reductions in emissions that were expected to be achieved throughout the modeling domain as a result of the implementation of several voluntary and mandatory statewide programs adopted or planned independently of the SIP. It should be made clear that the commission did not propose that any of these strategies be included in the ultimate control strategy submitted to the EPA in 2000. The need for and effectiveness of any controls which may be implemented outside the HGA eight-county area will be evaluated on a county-by-county basis.

The SIP revision was adopted by the commission on October 27, 1999, submitted to the EPA by November 15, 1999, and contained the following elements: photochemical modeling of potential specific control strategies for attainment of the one-hour ozone standard in the HGA area by the attainment date of November 15, 2007; an analysis of seven specific modeling scenarios reflecting various combinations of federal, state, and local controls in HGA (additional scenarios H1 and H2 build upon Scenario VIf); identification of the level of reductions of VOC and NO x necessary to attain the one-hour ozone standard by 2007; a 2007 mobile source budget for transportation conformity; identification of specific source categories which, if controlled, could result in sufficient VOC and/or NO x reductions to attain the standard; a schedule committing to submit by April 2000 an enforceable commitment to conduct a mid-course review; and a schedule committing to submit modeling and adopted rules in support of the attainment demonstration by December 2000.

The April 19, 2000, SIP revision for HGA contained the following enforceable commitments by the state: to quantify the shortfall of NO x reductions needed for attainment; to list and quantify potential control measures to meet the shortfall of NO x reductions needed for attainment; to adopt the majority of the necessary rules for the HGA attainment demonstration by December 31, 2000, and to adopt the rest of the shortfall rules as expeditiously as practical, but no later than July 31, 2001; to submit a Post-99 ROP plan by December 31, 2000; to perform a mid-course review by May 1, 2004; and to perform modeling of mobile source emissions using the EPA mobile source emissions model (MOBILE6), to revise the on-road mobile source budget as needed, and to submit the revised budget within 24 months of the model's release. In addition, if a conformity analysis is to be performed between 12 months and 24 months after the MOBILE6 release, the state will revise the motor vehicle emissions budget (MVEB) so that the conformity analysis and the SIP MVEB are calculated on the same basis.

In order for the state to have an approvable attainment demonstration, EPA has indicated that the state must adopt those strategies modeled in the November submittal and then adopt sufficient controls to close the remaining gap in NO x emissions. The modeling included in this proposal indicates a gap of an additional 77.98 tons per day (tpd) of NO x reductions is necessary for an approvable attainment demonstration. The commission estimates that this measure will achieve a minimum of 0.58 tpd delay of NO x until after noon. There will also be a 20.6 tpd delay in VOC emissions until after noon. Because the emission of NO x and VOC, both precursors to the formation of ozone, will be delayed until after noon, this delay will lead to a reduction in ozone that is equal to 7.7 tpd NO x reduced. These reductions are a necessary measure to consider for closing the gap and successfully demonstrating attainment.

The emission reduction requirements included as part of this SIP revision represent substantial, intensive efforts on the part of stakeholder coalitions in the HGA area. These coalitions, involving local governmental entities, elected officials, environmental groups, industry, consultants, and the public, as well as the commission and the EPA, have worked diligently to identify and quantify potential control strategy measures for the HGA attainment demonstration. Local officials from the HGA area have formally submitted a resolution to the commission, requesting the inclusion of many specific emission reduction strategies.

The current SIP revision contains rules, enforceable commitments, and photochemical modeling analyses in support of the HGA ozone attainment demonstration. In addition, this SIP contains Post-1999 ROP plans for the milestone years 2002 and 2005, and for the attainment year 2007. The SIP also contains enforceable commitments to implement further measures, if needed, in support of the HGA attainment demonstration, as well as a commitment to perform and submit a mid-course review.

The HGA ozone nonattainment area will need to ultimately reduce NOx more than 750 tpd to reach attainment with the one-hour standard. In addition, a VOC reduction of about 25% will have to be achieved. Adoption of the lawn and garden service equipment operating restriction program will contribute to attainment and maintenance of the one-hour ozone standard in the HGA area.

The purpose of these proposed rules is to establish a restriction on the use of handheld and non-handheld spark-ignition lawn and garden service equipment that operate at or below 25 horsepower (hp), 19 kilowatts. This air pollution control strategy would delay the emissions of NO x from these engines until later in the day, thus limiting ozone production. This control strategy is necessary for the counties included in the HGA nonattainment area to be able to demonstrate attainment with the NAAQS for ozone.

The proposed revisions would implement an operating-use restriction program requiring that the handheld and non-handheld spark-ignition lawn and garden service equipment, rated at 25-hp and below, be restricted from use between the hours of 6:00 a.m. and noon, April 1 through October 31. The affected handheld equipment includes, but is not limited to, trimmers, edgers, chainsaws, leaf blowers/vacuums, and shredders. Non-handheld lawn and garden equipment includes such devices as walk-behind lawnmowers, lawn tractors, tillers, and small generators. The affected area would include the eight-county HGA nonattainment area of Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller Counties. The effective date would be April 1, 2005.

The intent of these proposed rules is to limit the use of handheld and non-handheld spark-ignition lawn and garden service equipment that operate at or below 25 hp between the hours of 6:00 a.m. and noon. Between these hours this equipment is restricted from operating. Other lawn and garden service work not requiring the use of handheld and non-handheld spark-ignition lawn and garden service equipment remains unrestricted under these proposed rules. That is, electric or man-powered lawn equipment may be utilized. It should be noted however that the regulated types of lawn and garden service equipment are banned from use during the hours specified regardless of how they are being used.

The amount of NO x shifted will total 0.58 tpd. The non-road mobile source category is one of the few sources of ozone-causing emissions that are not currently regulated. Federal controls on handheld lawn and garden service equipment such as cleaner-burning engines have been adopted, and will be phased in beginning with the 2002 model year.

The California Air Resources Board (CARB) has stated that "using a commercial chain saw-powered by a two-stroke engine-for two hours produces the same amount of smog-forming hydrocarbon emissions as driving ten 1996 cars about 250 miles each." By shifting the hours of use for handheld and non-handheld spark-ignition lawn and garden service equipment until after noon, NO x emissions from such lawn and garden equipment will not mix in the atmosphere with other ozone-causing compounds until later in the day. Ozone is formed through chemical reactions between natural and man-made emissions of VOC and NO x in the presence of sunlight. Higher ozone levels occur most frequently on hot summer afternoons. The critical time for the mixing of NO x and VOC is early in the day. By delaying the release of NO x emissions from lawn and garden service equipment until later in the day, production of ozone will be stalled until optimum conditions no longer exist, thus avoiding the production of higher levels of ozone.

The commission solicits comment on additional flexibilities relating to rule content and implementation which have not been addressed in this or other concurrent rulemakings. These flexibilities may be available for both mobile and stationary sources. Additional flexibilities may also be achieved through innovative and/or emerging technology which may become available in the future. Additional sources of funds for incentive programs may become available to substitute for some of the measures considered here.

The commission is soliciting comments on alternative applications of this rule including: innovative uses of technology, such as incentives to use ultra low emission engines; alternative use restrictions, such as restricting use to every 10th day; and alternative restrictions on commercial use versus residential use, such as limiting the application of the rule to commercial services (which could be at residential property) or activities at commercial (versus residential) properties.

SECTION BY SECTION DISCUSSION

The new Division 6 is proposed regarding lawn and garden service equipment operating restrictions.

The proposed new §114.452 establishes control requirements for lawn and garden service equipment operating-use limitations. The proposal restricts the operation by all persons of all handheld or non-handheld lawn and garden service spark-ignition equipment 25 hp and below, between the hours of 6:00 a.m. and noon, during the time period between April 1 and October 31.

The proposed new §114.459 specifies the counties which are subject to the new requirements. The affected counties include all counties in the HGA nonattainment area, including Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller Counties.

FISCAL NOTE AND COSTS TO STATE AND LOCAL GOVERNMENTS

John Davis, Technical Specialist with Strategic Planning and Appropriations, has determined that for the first five-year period the proposed rules are in effect, there will be fiscal implications which are not anticipated to be significant for units of state and local government as a result of administration or enforcement of the proposed rules.

The proposed rules would restrict the use of handheld and non-handheld spark-ignition lawn and garden equipment, rated at 25 hp or less, from use between the hours of 6:00 a.m. and noon, from April 1 through October 31. The restriction would apply to lawn and garden equipment in the eight-county HGA ozone nonattainment area. The proposed rules would become effective April 1, 2005. The proposed rules do not require additional control equipment or new emission control technologies to be applied to the affected lawn and garden equipment.

The commission is required to submit a new SIP revision by the end of 2000 which will bring the HGA into attainment by 2007. The rules proposed for HGA in this notice comprise one element of the ozone Attainment Demonstration SIP for HGA. The purpose of the proposed rules is for the HGA nonattainment area to demonstrate attainment with the ozone NAAQS. The plan sets forth a control strategy that provides emission reductions necessary for attainment and maintenance of the national standards.

The commission estimates that units of state and local government within the HGA ozone nonattainment area may have to pay more to contract for landscape services if landscape businesses charge more for their services due to the proposed time restrictions. Although the extent of the fiscal implications are not known at this time, the commission anticipates that the potential increased costs to units of state and local government as a result of the proposed rules will not be significant.

PUBLIC BENEFIT AND COSTS

Mr. Davis also determined that for each year of the first five years the proposed rules are in effect, the public benefit anticipated from enforcement of and compliance with the proposed rules will be a potential reduction in the formation of ozone by delaying NO x emissions from lawn and garden equipment until later in the day when optimum conditions for the formation of ozone no longer exist, potentially improved air quality, and contribution toward demonstration of attainment with the NAAQS for ozone.

The proposed rules would restrict the use of handheld and non-handheld spark-ignition lawn and garden equipment, rated at 25 hp or less, from use between the hours of 6:00 a.m. and noon, from April 1 through October 31. The restriction would apply to lawn and garden equipment in the HGA ozone nonattainment area. The proposed rules would become effective April 1, 2005. The proposed rules do not require additional control equipment or new emission control technologies to be applied to the affected lawn and garden equipment.

Persons within the HGA ozone nonattainment area that utilize equipment affected by the proposed rules may experience adverse fiscal implications in an amount that cannot be determined at this time. Because the proposed rules do not require additional control equipment or new technology, the commission does not anticipate significant economic impacts to commercial operators beyond the shift in work schedule and possible implications caused by potential work delays attributable to the proposed rules. Delaying use of lawn and garden equipment until after noon may require commercial operators to adjust their work schedules and could cause extensions of projects or the need to hire more employees and procure additional equipment to meet business requirements. Private operators that utilize commercial operators to perform lawn and garden related work may have to pay more for the services.

SMALL BUSINESS AND MICRO-BUSINESS ASSESSMENT

There will be fiscal implications, in an amount which cannot be determined, which may have an adverse fiscal impact on small or micro-businesses as a result of administration or enforcement of the proposed rules.

The proposed rules would restrict the use of handheld and non-handheld spark-ignition lawn and garden equipment, rated at 25 hp or less, from use between the hours of 6:00 a.m. and noon, from April 1 through October 31. The restriction would apply to lawn and garden equipment in the HGA ozone nonattainment area. The proposed rules would become effective April 1, 2005. The proposed rules do not require additional control equipment or new emission control technologies to be applied to the affected lawn and garden equipment.

Small or micro-businesses within the HGA ozone nonattainment area that utilize equipment affected by the proposed rules may experience adverse fiscal implications in an amount that cannot be determined at this time. Because the proposed rules do not require additional control equipment or new technology, the commission does not anticipate significant economic impacts to affected individuals and businesses beyond the shift in work schedule and possible implications caused by potential work delays attributable to the proposed amendments. Delaying use of lawn and garden equipment until after noon may require affected small or micro-businesses to adjust their work schedules and could cause extensions of projects or the need to hire more employees and procure additional equipment to meet business requirements. Small or micro-businesses that utilize businesses to perform lawn and garden related work may have to pay more for the services.

DRAFT REGULATORY IMPACT ANALYSIS DETERMINATION

The commission reviewed the proposed rulemaking in light of the regulatory analysis requirements of Texas Government Code, §2001.0225, and determined that the rulemaking does not meet the definition of a "major environmental rule" as defined in that statute. "Major environmental rule" means a rule the specific intent of which is to protect the environment or reduce risks to human health from environmental exposure and that may adversely affect in a material way the economy, a sector of the economy, productivity, competition, jobs, the environment, or the public health and safety of the state or a sector of the state. The proposed rules to Chapter 114 are intended to protect the environment or reduce risks to human health from environmental exposure to ozone and, although no estimates of cost are available at this time, the commission does not believe work delays could affect a sector of the economy in a material way. The proposed rules are intended to implement an operating-use restriction program requiring that certain lawn and garden equipment be restricted from use between the hours of 6:00 a.m. and noon, April 1 through October 31. This program is part of the strategy to reduce the formation of ozone by delaying NO x emissions from lawn and garden equipment until later in the day when optimum conditions for the formation of ozone no longer exist. The program was developed for the HGA ozone nonattainment area to be able to demonstrate attainment with the ozone NAAQS. The commission does not believe that the businesses that provide lawn and garden services comprise a sector of the economy, nor does the commission believe that the rules will adversely affect in a material way, the economy, productivity, competition, jobs, the environment, or the public health and safety of the state or a sector of the state.

Provisions of 42 USC, §7410, require states to adopt a SIP which provides for "implementation, maintenance, and enforcement" of the primary NAAQS in each air quality control region of the state. While §7410 does not require specific programs, methods, or reductions in order to meet the standard, state SIPs must include "enforceable emission limitations and other control measures, means or techniques (including economic incentives such as fees, marketable permits, and auctions of emissions rights), as well as schedules and timetables for compliance as may be necessary or appropriate to meet the applicable requirements of this chapter," (meaning Chapter 85, Air Pollution Prevention and Control). It is true that 42 USC does require some specific measures for SIP purposes, like the inspection and maintenance program, but those programs are the exception, not the rule, in the SIP structure of 42 USC. The provisions of 42 USC recognize that states are in the best position to determine what programs and controls are necessary or appropriate in order to meet the NAAQS. This flexibility allows states, affected industry, and the public, to collaborate on the best methods for attaining the NAAQS for the specific regions in the state. Even though 42 USC allows states to develop their own programs, this flexibility does not relieve a state from developing a program that meets the requirements of §7410. Thus, while specific measures are not generally required, the emission reductions are required. States are not free to ignore the requirements of §7410 and must develop programs to assure that the nonattainment areas of the state will be brought into attainment on schedule.

The requirement to provide a fiscal analysis of proposed regulations in the Texas Government Code was amended by Senate Bill 633 (SB 633) during the 75th Legislative Session, 1999. The intent of SB 633 was to require agencies to conduct a regulatory impact analysis (RIA) of extraordinary rules. These are identified in the statutory language as major environmental rules that will have a material adverse impact and will exceed a requirement of state law, federal law, or a delegated federal program, or are adopted solely under the general powers of the agency. With the understanding that this requirement would seldom apply, the commission provided a cost estimate for SB 633 that concluded "based on an assessment of rules adopted by the agency in the past, it is not anticipated that the bill will have significant fiscal implications for the agency due to its limited application." The commission also noted that the number of rules that would require assessment under the provisions of the bill was not large. This conclusion was based, in part, on the criteria set forth in the bill that exempted proposed rules from the full analysis unless the rule was a major environmental rule that exceeds a federal law. As previously discussed, 42 USC does not require specific programs, methods, or reductions in order to meet the NAAQS; thus, states must develop programs for each nonattainment area to ensure that area will meet the attainment deadlines. Because of the ongoing need to address nonattainment issues, the commission routinely proposes and adopts SIP rules. The legislature is presumed to understand this federal scheme. If each rule proposed for inclusion in the SIP was considered to be a major environmental rule that exceeds federal law, then every SIP rule would require the full RIA contemplated by SB 633. This conclusion is inconsistent with the conclusions reached by the commission in its cost estimate and by the Legislative Budget Board (LBB) in its fiscal notes. Since the legislature is presumed to understand the fiscal impacts of the bills it passes, and that presumption is based on information provided by state agencies and the LBB, the commission believes that the intent of SB 633 was only to require the full RIA for rules that are extraordinary in nature. While the SIP rules will have a broad impact, that impact is no greater than is necessary or appropriate to meet the requirements of the FCAA. For these reasons, rules proposed for inclusion in the SIP fall under the exception in Texas Government Code, §2001.0225(a), because they are required by federal law. The commission performed photochemical grid modeling which predicts that NO x emission reductions, such as those required by these rules, will result in reductions in ozone formation in the HGA ozone nonattainment area. This rulemaking does not exceed an express requirement of state law. This rulemaking is intended to obtain NO x emission reductions which will result in reductions in ozone formation in the HGA ozone nonattainment area and help bring HGA into compliance with the air quality standards established under federal law as NAAQS for ozone. The rulemaking does not exceed a standard set by federal law, exceed an express requirement of state law (unless specifically required by federal law), or exceed a requirement of a delegation agreement. The rulemaking was not developed solely under the general powers of the agency, but was specifically developed to meet the NAAQS established under federal law and authorized under Texas Clean Air Act (TCAA), §§382.011, 382.012, 382.017, 382.019, and 382.039.

The commission invites public comment on the draft regulatory impact analysis.

TAKINGS IMPACT ASSESSMENT

The commission prepared a takings impact assessment for these rules in accordance with Texas Government Code, §2007.043. The following is a summary of that assessment. The specific purpose of the rulemaking action is to establish a lawn and garden service equipment operating-use limitation to delay NO x emissions that lead to high levels of ground-level ozone production. This proposed rulemaking will act as an air pollution control strategy to reduce NO x emissions necessary for the eight counties included in the HGA ozone nonattainment area to be able to demonstrate attainment with the ozone NAAQS. The proposed affected area consists of the eight counties contained in the HGA CMSA. Promulgation and enforcement of the proposed rules will not burden private, real property as it only regulates handheld and non-handheld spark-ignition lawn and garden equipment rated at 25 hp or less. Although the proposed rules do not directly prevent a nuisance, prevent an immediate threat to life or property, or prevent a real and substantial threat to public health and safety, the proposed rules partially fulfill a federal mandate under 42 USC, §7410. Specifically, the emissions limitations and delays within this proposal were developed in order to meet the ozone NAAQS set by the EPA under 42 USC, §7409. States are primarily responsible for ensuring attainment and maintenance of the NAAQS, once the EPA has established them. Under 42 USC, §7410 and related provisions, states must submit, for EPA approval, SIPs that provide for the attainment and maintenance of NAAQS through control programs directed to sources of the pollutants involved. Therefore, the purpose of the rule proposal is to implement a lawn and garden service equipment operating-use limitation necessary for the HGA nonattainment area to meet the air quality standards established under federal law as NAAQS. Consequently, the exemption which also applies to these proposed rules is that of an action reasonably taken to fulfill an obligation mandated by federal law. For the reasons stated, these proposed rules will not constitute a takings under the Texas Government Code, Chapter 2007.

CONSISTENCY WITH THE COASTAL MANAGEMENT PROGRAM

The commission determined that the proposed rulemaking relates to an action or actions subject to the Texas Coastal Management Program (CMP) in accordance with the Coastal Coordination Act of 1991, as amended (Texas Natural Resources Code, §§33.201 et seq.), and the commission rules in 30 TAC Chapter 281, Subchapter B, concerning Consistency with the CMP. As required by 30 TAC §281.45(a)(3) and 31 TAC §505.11(b)(2), relating to actions and rules subject to the CMP, commission rules governing air pollutant emissions must be consistent with the applicable goals and policies of the CMP. The commission reviewed this action for consistency with the CMP goals and policies in accordance with the rules of the Coastal Coordination Council, and determined that the action is consistent with the applicable CMP goals and policies. The CMP goal applicable to this rulemaking action is the goal to protect, preserve, and enhance the diversity, quality, quantity, functions, and values of coastal natural resource areas (31 TAC §501.12(1)). No new sources of air contaminants will be authorized and NO x air emissions will be reduced as a result of these rules. The CMP policy applicable to this rulemaking action is the policy that commission rules comply with regulations in 40 Code of Federal Regulations (CFR), to protect and enhance air quality in the coastal area (31 TAC §501.14(q)). This rulemaking action complies with 40 CFR 50, National Primary and Secondary Ambient Air Quality Standards, and 40 CFR 51, Requirements for Preparation, Adoption, and Submittal Of Implementation Plans. Therefore, in compliance with 31 TAC §505.22(e), this rulemaking action is consistent with CMP goals and policies.

Interested persons may submit comments on the consistency of the proposed rules with the CMP during the public comment period.

ANNOUNCEMENT OF HEARINGS

The commission will hold public hearings on this proposal at the following times and locations: September 18, 2000, 10:00 a.m., Lone Star Convention Center, 9055 Airport Road (FM 1484), Conroe; September 18, 2000, 7:00 p.m., Lake Jackson Civic Center, 333 Highway 332 East, Lake Jackson; September 19, 2000, 10:00 a.m. and 7:00 p.m., George Brown Convention Center, 1001 Avenida de Las Americas, Houston; September 20, 2000, 9:00 a.m., VFW Hall, 6202 George Bush Drive, Katy; September 20, 2000, 6:00 p.m., East Harris County Community Center, 7340 Spencer, Pasadena; September 21, 2000, 10:00 a.m., Southeast Texas Regional Airport Media Room, 6000 Airline Drive, Beaumont; September 21, 2000, 2:00 p.m., Amarillo City Commission Chambers, City Hall, 509 East 7th Avenue, Amarillo; September 21, 2000, 6:00 p.m., Charles T. Doyle Convention Center, 21st Street at Phoenix Lane, Texas City; September 22, 2000, 10:00 a.m., Dayton High School, 2nd Floor Lecture Room, 3200 North Cleveland Street, Dayton; September 22, 2000, 11:00 a.m., El Paso City Council Chambers, 2 Civic Center Plaza, 2nd Floor, El Paso; September 22, 2000, 2:00 p.m., North Central Texas Council of Governments, 2nd Floor Board Room, 616 Six Flags Drive, Suite 200, Arlington; and September 25, 2000, 10:00 a.m., Texas Natural Resource Conservation Commission, 12100 North I-35, Building E, Room 201S, Austin. The hearings are structured for the receipt of oral or written comments by interested persons. Registration will begin one hour prior to each hearing. Individuals may present oral statements when called upon in order of registration. A four-minute time limit will be established at each hearing to assure that enough time is allowed for every interested person to speak. Open discussion will not occur during each hearing; however, agency staff members will be available to discuss the proposal one hour before each hearing, and will answer questions before and after each hearing.

Persons with disabilities who have special communication or other accommodation needs, who are planning to attend a hearing, should contact the Office of Environmental Policy, Analysis, and Assessment at (512) 239-4900. Requests should be made as far in advance as possible.

SUBMITTAL OF COMMENTS

Written comments may be submitted to Heather Evans, Office of Environmental Policy, Analysis, and Assessment, MC 206, P.O. Box 13087, Austin, Texas 78711-3087, faxed to (512) 239-4808, or emailed to siprules@tnrcc.state.tx.us . All comments should reference Rule Log Number 2000-011O-114-AI. Comments must be received by 5:00 p.m., September 25, 2000. For further information, please contact Roland Castaneda at (512) 239-0774, or Alan Henderson at (512) 239-1510.

STATUTORY AUTHORITY

The new sections are proposed under the Texas Water Code (TWC), §5.103, which authorizes the commission to adopt rules necessary to carry out its powers and duties under the TWC, and under the Texas Health and Safety Code, TCAA, §382.017, which provides the commission the authority to adopt rules consistent with the policy and purposes of the TCAA. The new sections are also proposed under TCAA, §382.011, which authorizes the commission to control the quality of the state's air;§382.012, which authorizes the commission to prepare and develop a general, comprehensive plan for the control of the state's air; §382.019, which authorizes the commission to adopt rules to control and reduce emissions from engines used to propel land vehicles; and §382.039, which authorizes the commission to develop and implement programs and other measures necessary to demonstrate attainment and protect the public from exposure to hazardous air contaminants from motor vehicles.

The proposed new sections implement TCAA, §382.002, relating to Policy and Purpose; §382.011, relating to General Powers and Duties; §382.012, relating to State Air Control Plan; §382.019, relating to Methods Used to Control and Reduce Emissions from Land Vehicles; and §382.039, relating to Attainment Program.

§114.452.Control Requirements.

No person shall start or operate any handheld or non-handheld, spark-ignition lawn and garden service equipment, of 25 horsepower and below, between the hours of 6:00 a.m. and noon, during the time period between April 1 through October 31, in the counties listed in §114.459 of this title (relating to Affected Counties and Compliance Dates).

§114.459.Affected Counties and Compliance Dates.

Effective April 1, 2005, persons in the following counties shall be in compliance with §114.452 of this title (relating to Control Requirements). These include Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller Counties in the Houston/Galveston ozone nonattainment area.

This agency hereby certifies that the proposal has been reviewed by legal counsel and found to be within the agency's legal authority to adopt.

Filed with the Office of the Secretary of State, on August 11, 2000.

TRD-200005627

Margaret Hoffman

Director, Environmental Law Division

Texas Natural Resource Conservation Commission

Earliest possible date of adoption: September 24, 2000

For further information, please call: (512) 239-0348


7. HOUSTON/GALVESTON AIRPORT GROUND SUPPORT EQUIPMENT

30 TAC §§114.460, 114.462, 114.466, 114.469

The Texas Natural Resource Conservation Commission (commission) proposes new §114.460, Definitions; §114.462, Control Requirements; §114.466, Reporting and Recordkeeping Requirements; and §114.469, Affected Counties and Compliance Schedules. The commission proposes these new sections in Chapter 114, Control of Air Pollution from Motor Vehicles; Subchapter I, Non-Road Engines; new Division 7, Houston/Galveston Airport Ground Support Equipment; and corresponding revisions to the state implementation plan (SIP) in order to control ground-level ozone in the Houston/Galveston (HGA) ozone nonattainment area through the reduction of nitrogen oxide (NO x ) emissions from airport ground support equipment (GSE).

BACKGROUND AND SUMMARY OF THE FACTUAL BASIS FOR THE PROPOSED RULES

The HGA ozone nonattainment area is classified as Severe-17 under the Federal Clean Air Act (FCAA) Amendments of 1990 (42 United States Code (USC), §§7401 et seq.), and therefore is required to attain the one-hour ozone standard of 0.12 parts per million (ppm) by November 15, 2007. The HGA area, defined by Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller Counties, has been working to develop a demonstration of attainment in accordance with 42 USC, §7410. On January 4, 1995, the state submitted the first of its Post-1996 SIP revisions for HGA.

The January 1995 SIP consisted of urban airshed model (UAM) modeling for 1988 and 1990 base-case episodes, adopted rules to achieve a 9% rate-of-progress (ROP) reduction in volatile organic compounds (VOC), and a commitment schedule for the remaining ROP and attainment demonstration elements. At the same time, but in a separate action, the State of Texas filed for the temporary NOx waiver allowed by 42 USC, §7511a(f). The January 1995 SIP and the NO x waiver were based on early base-case episodes which marginally exhibited model performance in accordance with the United States Environmental Protection Agency (EPA) modeling performance standards, but which had a limited data set as inputs to the model. In 1993 and 1994, the commission was engaged in an intensive data-gathering exercise known as the COAST study. The state believed that the enhanced emissions inventory, expanded ambient air quality and meteorological monitoring, and other elements would provide a more robust data set for modeling and other analysis, which would lead to modeling results that the commission could use to better understand the nature of the ozone air quality problem in the HGA area.

Around the same time as the 1995 submittal, EPA policy regarding SIP elements and timelines went through changes. Two national programs in particular resulted in changing deadlines and requirements. The first of these programs was the Ozone Transport Assessment Group. This group grew out of a March 2, 1995, memo from Mary Nichols, former EPA Assistant Administrator for Air and Radiation, that allowed states to postpone completion of their attainment demonstrations until an assessment of the role of transported ozone and precursors had been completed for the eastern half of the nation, including the eastern portion of Texas. Texas participated in this study, and it has been concluded that Texas does not significantly contribute to ozone exceedances in the Northeastern United States. The other major national initiative that has impacted the SIP planning process is the revisions to the national ambient air quality standard (NAAQS) for ozone. The EPA promulgated a final rule on July 18, 1997, changing the ozone standard to an eight-hour standard of 0.08 ppm. In November 1996, concurrent with the proposal of the standards, the EPA proposed an interim implementation plan (IIP) that it believed would help areas like HGA transition from the old to the new standard. In an attempt to avoid a significant delay in planning activities, Texas began to follow this guidance, and readjusted its modeling and SIP development timelines accordingly. When the new standard was published, the EPA decided not to publish the IIP, and instead stated that, for areas currently exceeding the one-hour ozone standard, that standard would continue to apply until it is attained. The FCAA requires that HGA attain the standard by November 15, 2007.

The EPA issued revised draft guidance for areas such as HGA that do not attain the one-hour ozone standard. The commission adopted on May 6, 1998, and submitted to the EPA on May 19, 1998, a revision to the HGA SIP which contained the following elements in response to the EPA's guidance: UAM modeling based on emissions projected from a 1993 baseline out to the 2007 attainment date; an estimate of the level of VOC and NO x reductions necessary to achieve the one-hour ozone standard by 2007; a list of control strategies that the state could implement to attain the one-hour ozone standard; a schedule for completing the other required elements of the attainment demonstration; a revision to the Post-1996 9% ROP SIP that remedied a deficiency that the EPA believed made the previous version of that SIP unapprovable; and evidence that all measures and regulations required by Subpart 2 of Title I of the FCAA to control ozone and its precursors have been adopted and implemented, or are on an expeditious schedule to be adopted and implemented.

In November 1998, the SIP revision submitted to the EPA in May 1998 became complete by operation of law. However, the EPA stated that it could not approve the SIP until specific control strategies were modeled in the attainment demonstration. The EPA specified a submittal date of November 15, 1999, for this modeling. In a letter to the EPA dated January 5, 1999, the state committed to model two strategies showing attainment.

As the HGA modeling protocol evolved, the state eventually selected and modeled seven basic modeling scenarios. As part of this process, a group of HGA stakeholders worked closely with commission staff to identify local control strategies for the modeling. Some of the scenarios for which the stakeholders requested evaluation included options such as California-type fuel and vehicle programs as well as an acceleration simulation mode equivalent motor vehicle inspection and maintenance program. Other scenarios incorporated the estimated reductions in emissions that were expected to be achieved throughout the modeling domain as a result of the implementation of several voluntary and mandatory statewide programs adopted or planned independently of the SIP. It should be made clear that the commission did not propose that any of these strategies be included in the ultimate control strategy submitted to the EPA in 2000. The need for and effectiveness of any controls which may be implemented outside the HGA eight-county area will be evaluated on a county-by-county basis.

The SIP revision was adopted by the commission on October 27, 1999, submitted to the EPA by November 15, 1999, and contained the following elements: photochemical modeling of potential specific control strategies for attainment of the one-hour ozone standard in the HGA area by the attainment date of November 15, 2007; an analysis of seven specific modeling scenarios reflecting various combinations of federal, state, and local controls in HGA (additional scenarios H1 and H2 build upon Scenario VIf); identification of the level of reductions of VOC and NO x necessary to attain the one-hour ozone standard by 2007; a 2007 mobile source budget for transportation conformity; identification of specific source categories which, if controlled, could result in sufficient VOC and/or NO x reductions to attain the standard; a schedule committing to submit by April 2000 an enforceable commitment to conduct a mid-course review; and a schedule committing to submit modeling and adopted rules in support of the attainment demonstration by December 2000.

The April 19, 2000, SIP revision for HGA contained the following enforceable commitments by the state: to quantify the shortfall of NO x reductions needed for attainment; to list and quantify potential control measures to meet the shortfall of NO x reductions needed for attainment; to adopt the majority of the necessary rules for the HGA attainment demonstration by December 31, 2000, and to adopt the rest of the shortfall rules as expeditiously as practical, but no later than July 31, 2001; to submit a Post-99 ROP plan by December 31, 2000; to perform a mid-course review by May 1, 2004; and to perform modeling of mobile source emissions using the EPA mobile source emissions model (MOBILE6), to revise the on-road mobile source budget as needed, and to submit the revised budget within 24 months of the model's release. In addition, if a conformity analysis is to be performed between 12 months and 24 months after the MOBILE6 release, the state will revise the motor vehicle emissions budget (MVEB) so that the conformity analysis and the SIP MVEB are calculated on the same basis.

In order for the state to have an approvable attainment demonstration, EPA has indicated that the state must adopt those strategies modeled in the November submittal and then adopt sufficient controls to close the remaining gap in NO x emissions. The modeling included in this proposal indicates a gap of an additional 77.98 tons per day (tpd) of NO x reductions is necessary for an approvable attainment demonstration. The commission estimates that this measure will achieve a minimum of 5.09 tpd of NO x equivalent reductions and is therefore a necessary measure to consider for closing the gap and successfully demonstrating attainment.

The emission reduction requirements included as part of this SIP revision represent substantial, intensive efforts on the part of stakeholder coalitions in the HGA area. These coalitions, involving local governmental entities, elected officials, environmental groups, industry, consultants, and the public, as well as the commission and the EPA, have worked diligently to identify and quantify potential control strategy measures for the HGA attainment demonstration. Local officials from the HGA area have formally submitted a resolution to the commission, requesting the inclusion of many specific emission reduction strategies.

The current SIP revision contains rules, enforceable commitments, and photochemical modeling analyses in support of the HGA ozone attainment demonstration. In addition, this SIP contains Post-1999 ROP plans for the milestone years 2002 and 2005, and for the attainment year 2007. The SIP also contains enforceable commitments to implement further measures, if needed, in support of the HGA attainment demonstration, as well as a commitment to perform and submit a mid-course review.

The HGA ozone nonattainment area will need to ultimately reduce NOx more than 750 tpd to reach attainment with the one-hour standard. In addition, a VOC reduction of about 25% will have to be achieved. Adoption of these airport GSE rules will contribute to the attainment and maintenance of the one-hour ozone standard in the HGA area. An airport GSE program should also contribute to a successful demonstration of transportation conformity in the HGA area.

Airport GSE rules were adopted by the commission for the Dallas/Fort Worth (DFW) nonattainment area on April 19, 2000. This rulemaking action proposes identical requirements applied to the eight-county HGA ozone nonattainment area and are necessary for the area to be able to demonstrate attainment with the ozone NAAQS.

Airport GSE is used from the moment an aircraft lands, until the aircraft takes off. Airport GSE is comprised of a variety of vehicles and equipment necessary to service aircraft during ground-based operations, including cargo loading and unloading, passenger loading and unloading, potable water storage, lavatory waste tank drainage, aircraft refueling, engine and fuselage examination and maintenance, and food and beverage catering. Airlines employ specially designed GSE to support all these operations. Moreover, electrical power and conditioned air are generally required during aircraft operations at the terminal gate to provide comfort and safety for the passengers and crew. These services are often provided by the terminal facility, however many times these services are provided by GSE. Airport GSE includes, but is not limited to, aircraft pushback tugs, baggage and cargo tugs, carts, forklifts, lifts, ground power units, air conditioning units, air start units, and belt loaders. Electric-powered versions of baggage tugs and belt loaders, which represent about a third of all GSE, are available and in use. Electric-powered versions of aircraft pushback tugs, air start units, air conditioning units, forklifts, lifts, ground power units, and other specialty GSE are also available in the marketplace.

The initial purchase cost of electric-powered GSE is typically higher than diesel-powered and gasoline-powered GSE. A recent report by the EPA, Technical Support for Development of Airport Ground Support Equipment Emission Reductions (EPA 420-R-99-007, May 1999), estimated that the cost of an electric baggage tractor would be $30,000, while the gasoline-powered version would be $17,000, and the diesel-powered version would be $22,000. However, electricity is such a less expensive power source than fossil fuels, that the savings in the cost of fuel will offset the increased electric GSE purchase price in two to three years. Additionally, the existing rules allow the GSE owner or operator to reduce emissions from the GSE fleet or in the nonattainment area by any means available. The owners and operators may also use the commission emission banking program to meet their emission reduction requirements. That is, an owner or operator may meet emission control requirements of this chapter, in whole or in part, by obtaining emission reduction credits (ERCs), mobile emission reduction credits (MERCs), discrete emission reduction credit (DERCs), or mobile discrete emission reduction credit (MDERCs) in accordance with this section and 30 TAC Chapter 101 (General Air Rules), §101.29 (Emission Credit Banking and Trading). In a concurrent rulemaking (rule log number 1998-089-101-AI), the emission credit banking and trading rules are being moved to Chapter 101, Subchapter H (Emissions Banking and Trading), Division 1 (Emission Credit Banking and Trading) and Division 4 (Discrete Emission Credit Banking and Trading).

The majority of GSE engines are "uncontrolled" from an emission perspective, because they have not been designed for low emissions. Therefore, GSE emits significant amounts of VOC and NO x . The EPA report (420-R-99-007) states that GSE is responsible for 15%-20% of airport-related NO x and 10%-15% of airport-related VOC. The replacement of internal combustion engine-powered GSE with low-or zero-emission GSE at the airports where this equipment is used will reduce the VOC and NOx emissions from this source category. These NOx emissions will be reduced by at least 90%, thus leading to 5.09 tpd of NO x emission reductions.

The commission solicits comment on additional flexibilities relating to rule content and implementation which have not been addressed in this or other concurrent rulemakings. These flexibilities may be available for both mobile and stationary sources. Additional flexibilities may also be achieved through innovative and/or emerging technology which may become available in the future. Additional sources of funds for incentive programs may become available to substitute for some of the measures considered here.

SECTION-BY-SECTION DISCUSSION

Rules regarding airport GSE were adopted for the DFW ozone nonattainment area on April 19, 2000. These rules were adopted in Chapter 114, Subchapter I, Division 1, §114.400, Definitions; §114.402, Control Requirements; §114.406, Reporting and Recordkeeping Requirements; and §114.409, Affected Counties. This rulemaking action proposes identical requirements in Subchapter I, Division 7 which would apply to the eight-county HGA ozone nonattainment area.

The proposed new §114.460 includes definitions for air carrier, air carrier operations, ground support equipment, ground support equipment fleet, GSE average emission factor, and subject airport.

The proposed new §114.462(a), explains that affected owners and operators of GSE must demonstrate a NO x emissions reduction which is equal to or greater than the percentages of NO x emissions attributable to the GSE fleet during the 1996 calender year. These reductions must be made in accordance with the following schedule: 20% reduction by December 31, 2003; 50% reduction by December 31 2004; and 90% reduction by December 31, 2005. Subsection (b) pertains to those fleets which were not in operation in 1996. Using the emission factors from §114.460(6), the owner and/or operator of the fleet must demonstrate the following NOx emission reductions: 20% reduction by December 31, 2003, or December 31 of the first year of operation, whichever is later; 50% reduction by December 31, 2004, or December 31 of the third year of operation, whichever is later; and 90% reduction by December 31, 2005, or December 31 of the third year of operation, whichever is later instead of electrifying the fleet. This demonstration will be accomplished by multiplying the appropriate emission factor by the number of non-electric GSE units on hand at the end of one year of operation. The new §114.462(c) applies to airports which become subject to the rule after the effective date. Owners or operators of GSE at these airports must comply with the emission reduction requirements of §114.462(a) or (b), whichever is applicable. However, the owner or operator of GSE may comply with the 20% reduction on December 31, 2003, or December 31 of the year an airport becomes a subject airport; with the 50% reduction on December 31, 2004, or the year after the airport becomes a subject airport; and with the 90% reduction on 2005, or the second year after the airport becomes a subject airport. Because it takes a three-year average to become a subject airport, these fleet operators will have at least a three-year lead time before reductions are required. The commission required 90% instead of 100% reduction for these alternative compliance measures, because availability of electric equipment cannot be considered as it can in subsection (g) of this section. The commission anticipates that fleets complying with subsection (g) will be able to demonstrate that some of their equipment is not available in electric power and so they would not actually achieve a 100% reduction in emissions. The 90% is intended to approximate this difference.

The proposed new §114.462(d) allows the commission to better enforce the rule by providing that each entity that chooses not to fully electrify its fleet shall submit a plan to the commission by May 1, 2003, or the first May 1st following operation at a subject airport. This plan shall list each GSE unit, its horsepower rating, its emission factor, the total actual annual emissions for each unit in existence in 1996, and provide for the implementation of emission reduction measures to achieve NO x emissions in the amount required by §114.462(a), (b), (c), and (e). To provide alternate means of compliance while still achieving emission reductions, the plan may include emission reductions measures which are applied to the GSE fleet itself, and measures which have been achieved elsewhere in the nonattainment area if those measures would be creditable under the commission emissions banking program as defined in 30 TAC §101.29. This plan must be approved by the executive director and the EPA, and should be revised as needed to accurately reflect the compliance plan. New subsection (e) ensures emission reductions for growth after 1996, specifying that beginning December 31, 2004, owners and operators of GSE subject to §114.462(a), (b), or (c) must demonstrate that their non-electric GSE units added to the fleet after December 31, 1996, or after the first year of being subject to the rule, are offset by 90%. Subsection (f) states that the requirements of any enforceable agreement between the EPA, the United States Department of Transportation, and the GSE owners/operators may be included in a plan submitted under §114.462(d).

The proposed new §114.462(g) states that in lieu of compliance with §114.462(a)-(e) an owner or operator of GSE at a subject airport may ensure that the fleet is 100% electric powered by May 1, 2005, or three years after the airport becomes a subject airport. Additionally, §114.462(g) states that for any GSE unit not available for purchase or conversion to electric power, an owner or operator of GSE may meet the requirements of this subsection if it can be shown that the lowest emitting equipment is being used, subject to approval by the executive director and the EPA.

The proposed new §114.466(a) requires that owners or operators subject to §114.462 submit annual GSE fleet reports to be submitted to the executive director. Subsection (b) requires them to maintain copies of the submitted reports for a minimum of three years. For convenience, the commission will permit these reports to be kept in hard-copy or electronic form.

The proposed new §114.469 identifies the counties subject to these rules as being Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller Counties. These counties make up the HGA ozone nonattainment area.

FISCAL NOTE: COSTS TO STATE AND LOCAL GOVERNMENT

John Davis, Technical Specialist with Strategic Planning and Appropriations, determined that for the first five-year period these proposed rules are in effect there will be no significant fiscal implications for units of state and local government as a result of administration or enforcement of the rules. The airlines and businesses that serve the George Bush Intercontinental, William P. Hobby, and Ellington Airports in Harris County will probably incur relatively high costs for the first five-year period of the proposed rules due to the purchase/lease of cleaner operating GSE needed to meet reduced emission requirements at subject airports; however, those initial costs will be offset by reduced maintenance and fuel costs over time (especially in the case of electric-powered GSE).

The proposed rules will require airports in the eight-county HGA nonattainment area to comply with requirements identical to the existing GSE emission reduction requirements operated at airports in the DFW area. Affected airports are those with 100 or greater air carrier operations per year (excluding general aviation operations, non-fixed wing operations, and military operations), averaged over a three-year period. Owners or operators of GSE subject to this section at the time of the effective date must demonstrate the following emission reductions based on 1996 NO x emissions levels: 20% reduction by December 31, 2003; 50% reduction by December 31, 2004; and 90% reduction by December 31, 2005. Owners or operators of GSE not in operation in 1996 at an airport which is a subject airport by the effective date of this rule must demonstrate a reduction of NO x emissions which is equal to or greater than the following percentages: 20% reduction by December 31, 2003, or December 31 of the first year of operation, whichever is later; 50% reduction by December 31, 2004, or December 31 of the second year of operation, whichever is later; and 90% reduction by December 31, 2005, or December 31 of the third year of operation, whichever is later. Owners and operators of affected GSE will also be required to submit annual GSE fleet reports to the commission. The reporting is designed to demonstrate compliance with the implementation schedule. This air pollution control program is part of the strategy to reduce NO x emissions necessary for the counties included in the HGA nonattainment area to be able to demonstrate attainment with the ozone NAAQS.

The City of Houston, which owns and operates the three affected airports, will be affected if they own or operate GSE. Additionally, there may be costs to the city related to the possible addition or retrofitting of infrastructure which accommodate alternative-fueled GSE at the affected airports. Infrastructure costs for full electrification of GSE at the four affected airports in the DFW area have been estimated by the Air Transport Association to be approximately $70 million. Presumably estimates for Houston could be similar. Actual infrastructure costs are expected to be lower depending upon the compliance options chosen. The City of Houston could pass some or all of these costs on to its tenants at the airports. The local air pollution control agency having jurisdiction in the area may request reports relating to §114.406 as well. There are no significant fiscal implications anticipated for the City of Houston or other units of state and local government as a result of administration of the proposed rules, except as mentioned in the previous paragraphs.

PUBLIC BENEFIT AND COSTS

Mr. Davis also determined that for each year of the first five years the proposed rules are in effect, the public benefit anticipated from enforcement of and compliance with the proposed rules will be the potential reduction in NO x emissions from affected airports, potentially improved air quality, and contribution toward demonstration of attainment with the ozone NAAQS within the HGA nonattainment area.

Although GSE owners and operators have a number of options to reduce NOx emission levels, because 100% electrification of the GSE fleets provides the greatest degree of emissions reductions and long-term cost effectiveness, this portion of the preamble analyzes the potential cost of GSE electrification at the George Bush Intercontinental, William P. Hobby, and Ellington Airports. The commission anticipates that GSE owners or operators subject to the proposed rules will incur relatively significant costs in the short term to purchase or lease electric-powered GSE due to the fact that electric-powered GSE is more expensive to purchase relative to fossil-fueled GSE. However, with electric-powered GSE the avoided cost of purchasing fossil fuels and lower maintenance costs are expected to offset the additional purchase/lease costs over time. The commission estimates that the savings achieved from the avoided cost for fossil fuels over the life cycle of the equipment will offset the incremental purchase cost of the electric-powered GSE.

At George Bush Intercontinental Airport, the following airlines will be affected: AeroMexico, American, America West, British Airways, Canadian Airlines, Continental, Delta, Northwest, TWA, United, US Airways, Atlantic Southeast, Lufthansa, Sun Country, KLM Royal Dutch, Comair, Air France, Air Canada, TACA, Federal Express, BAX Global, Aeromexpress, American International, and Trans World Airlines. At William P. Hobby Airport, AirTran, American, Atlantic Southeast, Continental, Delta, Northwest, and Comair will be affected. At Ellington Airport, United Postal Service will be affected. Other businesses at the three affected airports that support airline operations and use GSE will also be required to adhere to the GSE NO x emission reduction requirements found in these rules. Tenant entities at the affected airports could be affected by infrastructure costs detailed in the Fiscal Note: Cost to State and Local Government section of this preamble.

The EPA report (420-R-99-007), indicates the cost savings for electric-powered GSE, initial purchase costs for electric GSE are high relative to their fossil-fueled counterparts. The cost premium is almost entirely associated with the required battery pack and recharger. Table I, Life Cycle Costs for Baggage Tractors, presents a comparison of electric baggage tractor initial costs relative to those of fossil-fueled GSE. As indicated, the cost premium ranges from about $8,000 relative to a diesel-powered tractor, to about $13,000 relative to a gasoline-powered tractor. These purchase price premiums are augmented by periodic battery replacement requirements (at about $4,500 every five to six years) that are two to four times higher on a life cycle basis than corresponding fossil fuel engine rebuild or replacement costs. However, these cost premiums are counterbalanced by a substantial reduction in fuel costs. Electric GSE use no fuel during idle periods and such periods can comprise as much as 50% of typical GSE operation. Using an estimated electricity cost of $.045 per kilowatt-hour, the overall fuel savings associated with high-use GSE operations, such as baggage tractors, can range from $2,500 per year relative to diesel equipment to over $6,000 per year relative to gasoline and compressed natural gas equipment. While lower-use GSE fuel cost savings will be smaller, it is clear that fuel savings alone can offset the entire electric GSE purchase price premium in two to three years. Moreover, electric GSE fuel cost savings will increase as more efficient electric motors and motor controllers continue to evolve.

In addition to reduced fuel costs, the latest generation of electric GSE have demonstrated significantly reduced maintenance requirements. Costs have been estimated to be reduced by as much as two-thirds relative to gasoline-and diesel-powered GSE. The table presents the results of a life cycle cost comparison for a baggage tractor under a high-use operating scenario (i.e., generally used to service aircraft continuously throughout an operating day such as occurs at high traffic airports). The tabulated costs represent the net present value of the various expenditures required over the 16-year useful life of the tractor. Regardless of whether maintenance costs are assumed to be reduced, the electric-powered tractor consistently exhibits the lowest life cycle costs. Life cycle costs for the electric baggage tractor are estimated to be over 40% lower than the next lowest cost diesel option under a reduced maintenance scenario, and still 10% lower even if maintenance costs are assumed to be identical to conventional gasoline-and diesel-powered GSE maintenance costs.

Precise cost effectiveness estimates for electric GSE are difficult to quantify because the impact of such equipment varies across the pollutants examined and relative to the fossil fuel equipment being replaced, and the emissions performance of local utilities. However, it is clear from the data presented in the table that electric GSE represent the lowest cost option relative to all fossil fuel GSE. Therefore, if an appropriate battery recharging schedule and infrastructure can be established, all derived emission reductions accrue for free. Assuming local utility emissions performance is not too different from average United States utility emission levels, electric GSE are cost effective from an economic standpoint alone.

Figure: 30 TAC Chapter 114E-Preamble

The EPA report also stated that " . . . generally, there are no technical limitations to the size or type of GSE that can be converted to or replaced with electrically powered equipment. Electrically powered versions of baggage tugs and belt loaders, which together account for over a third of all GSE, are available and in use (although current usage constitutes only a minor fraction of total activity). Additionally, electric powered versions of aircraft pushback tractors, air start units, conditioned air units, forklifts, ground power units, lifts, general purpose vehicles (cars, trucks, and vans), and other specialty GSE are currently available in the marketplace. Electric carts are already fulfilling about half of overall GSE cart demand."

The following is an excerpt from a study titled Assessment of Airport Ground Support Equipment Using Electric Power or Low-Emitting Fuels (Arcadis, Geraghty and Miller, July 20, 1999) that indicates the costs for electric-powered GSE. The study estimated the purchase cost for an electric baggage tractor to be $24,250; an electric belt loader to be $30,000; and an electric aircraft tug to be $85,000. Their gasoline-powered equivalents are $16,000, $27,000, and $72,000, respectively. The diesel-powered equivalents are $19,000, $29,000, and $72,000, respectively. The study also estimated the GSE population in California. If airport GSE population within the HGA area is similar, then the baggage tractors make up 44%; belt loaders make up 20%; and aircraft tugs make up 6% of the total GSE. If the estimated 3,154 pieces of GSE at the affected airports are equally proportioned and assuming none of the current GSE is electric-powered, the commission estimates that there are 1,388 baggage tractors, 631 belt loaders, and 189 aircraft tugs. Applying the cost from the Geraghty and Miller study, the estimated total cost for 70% of the equipment at the affected airports is $68.6 million. Assuming that the remaining 30% of the equipment, or 946 units, are lower cost equipment in the $10,000 to $20,000 range, the total cost should not be in excess of $87.5 million less trade-in, transfer, or sale of current equipment. As stated previously, the commission also anticipates that additional costs associated with replacing current GSE with electric-powered GSE will be offset with fuel and maintenance savings over time. The commission estimates that the cost of the reporting requirements in the proposed rules will not be significant.

SMALL BUSINESS AND MICRO-BUSINESS IMPACT ANALYSES

The commission anticipates no adverse fiscal implications to small businesses and micro-businesses as a result of implementing the proposed rules, because there are no known small or micro-businesses that own and operate GSE at the George Bush Intercontinental, William P. Hobby, or Ellington Airports. If there are small or micro-businesses that own GSE for the purpose of delivering their products to the aircraft; providing maintenance support for aircraft at affected airports; or renting/leasing GSE to airlines or related companies which provide services to the airlines; their costs will be similar to those specified for businesses in general in the PUBLIC BENEFITS AND COSTS section of this preamble.

The Geraghty and Miller study estimated the costs for electric-powered GSE. The study estimated the purchase cost for an electric baggage tractor to be $24,250; an electric belt loader to be $30,000; and an electric aircraft tug to be $85,000. The commission anticipates that some of the equipment used by affected small or micro-businesses may be lower cost units in the $10,000 to $30,000 range. Actual total costs would be dependent on the amount and types of GSE used by the business. The commission also anticipates that costs will be mitigated by the trade-in, transfer, or sale of current equipment. As stated previously, the commission anticipates that additional costs associated with replacing current GSE with electric-powered GSE will be offset with fuel and maintenance savings over time, and that the cost of the reporting requirements in the proposed rules will not be significant.

DRAFT REGULATORY IMPACT ANALYSIS DETERMINATION

The commission reviewed the proposed rulemaking in light of the regulatory analysis requirements of Texas Government Code, §2001.0225, and determined that the rulemaking meets the definition of a "major environmental rule" as defined in that statute. "Major environmental rule" means a rule the specific intent of which is to protect the environment or reduce risks to human health from environmental exposure and that may adversely affect in a material way the economy, a sector of the economy, productivity, competition, jobs, the environment, or the public health and safety of the state or a sector of the state. The proposed rules are intended to protect the environment or reduce risks to human health from environmental exposure to ozone and could affect in a material way, a sector of the economy, competition, and the environment. The proposed rules regarding airports operating in the HGA ozone nonattainment area, impose requirements to reduce the NO x emission levels at the airports through the conversion of fossil-fueled GSE to electric-powered GSE, or equivalent conversion measures which meet the required emission reduction levels, over a three-to four-year period. This air pollution control program is part of the strategy to reduce NO x emissions necessary for the counties included in the HGA ozone nonattainment area to be able to demonstrate attainment with the ozone NAAQS. Although the proposed rulemaking meets the definition of a "major environmental rule" as defined in the Texas Government Code, and is considered a major environmental rule, §2001.0225 only applies to a major environmental rule, the result of which is to: 1. exceed a standard set by federal law, unless the rule is specifically required by state law; 2. exceed an express requirement of state law, unless the rule is specifically required by federal law; 3. exceed a requirement of a delegation agreement or contract between the state and an agency or representative of the federal government to implement a state and federal program; or 4. adopt a rule solely under the general powers of the agency instead of under a specific state law.

This rulemaking does not meet any of these four applicability requirements of a "major environmental rule." Specifically, the proposed rules regarding airports operating in the HGA ozone nonattainment area, impose requirements to reduce the NO x emission levels at the airports through the conversion of fossil-fueled GSE to electric-powered GSE, or equivalent conversion measures which meet the required emission reduction levels. These requirements are necessary to meet the ozone NAAQS set by the EPA under 42 USC, §7409, and therefore meet a federal requirement. Provisions of 42 USC, §7410, require states to adopt a SIP which provides for "implementation, maintenance, and enforcement" of the primary NAAQS in each air quality control region of the state. While §7410 does not require specific programs, methods, or reductions in order to meet the standard, state SIPs must include "enforceable emission limitations and other control measures, means or techniques (including economic incentives such as fees, marketable permits, and auctions of emissions rights), as well as schedules and timetables for compliance as may be necessary or appropriate to meet the applicable requirements of this chapter," (meaning Chapter 85, Air Pollution Prevention and Control). It is true that 42 USC does require some specific measures for SIP purposes, like the inspection and maintenance program, but those programs are the exception, not the rule, in the SIP structure of 42 USC. The provisions of 42 USC recognize that states are in the best position to determine what programs and controls are necessary or appropriate in order to meet the NAAQS. This flexibility allows states, affected industry, and the public, to collaborate on the best methods for attaining the NAAQS for the specific regions in the state. Even though 42 USC allows states to develop their own programs, this flexibility does not relieve a state from developing a program that meets the requirements of §7410. Thus, while specific measures are not generally required, the emission reductions are required. States are not free to ignore the requirements of §7410 and must develop programs to assure that the nonattainment areas of the state will be brought into attainment on schedule.

The requirement to provide a fiscal analysis of proposed regulations in the Texas Government Code was amended by Senate Bill 633 (SB 633) during the 75th Legislative Session, 1999. The intent of SB 633 was to require agencies to conduct a regulatory impact analysis (RIA) of extraordinary rules. These are identified in the statutory language as major environmental rules that will have a material adverse impact and will exceed a requirement of state law, federal law, or a delegated federal program, or are adopted solely under the general powers of the agency. With the understanding that this requirement would seldom apply, the commission provided a cost estimate for SB 633 that concluded "based on an assessment of rules adopted by the agency in the past, it is not anticipated that the bill will have significant fiscal implications for the agency due to its limited application." The commission also noted that the number of rules that would require assessment under the provisions of the bill was not large. This conclusion was based, in part, on the criteria set forth in the bill that exempted proposed rules from the full analysis unless the rule was a major environmental rule that exceeds a federal law. As previously discussed, 42 USC does not require specific programs, methods, or reductions in order to meet the NAAQS; thus, states must develop programs for each nonattainment area to ensure that area will meet the attainment deadlines. Because of the ongoing need to address nonattainment issues, the commission routinely proposes and adopts SIP rules. The legislature is presumed to understand this federal scheme. If each rule proposed for inclusion in the SIP was considered to be a major environmental rule that exceeds federal law, then every SIP rule would require the full RIA contemplated by SB 633. This conclusion is inconsistent with the conclusions reached by the commission in its cost estimate and by the Legislative Budget Board (LBB) in its fiscal notes. Since the legislature is presumed to understand the fiscal impacts of the bills it passes, and that presumption is based on information provided by state agencies and the LBB, the commission believes that the intent of SB 633 was only to require the full RIA for rules that are extraordinary in nature. While the SIP rules will have a broad impact, that impact is no greater than is necessary or appropriate to meet the requirements of the FCAA. For these reasons, rules proposed for inclusion in the SIP fall under the exception in Texas Government Code, §2001.0225(a), because they are required by federal law. The commission performed photochemical grid modeling which predicts that NO x emission reductions, such as those required by these rules, will result in reductions in ozone formation in the HGA ozone nonattainment area. This rulemaking does not exceed an express requirement of state law. This rulemaking is intended to obtain NO x emission reductions which will result in reductions in ozone formation in the HGA ozone nonattainment area and help bring HGA into compliance with the air quality standards established under federal law as NAAQS for ozone. The rulemaking does not exceed a standard set by federal law, exceed an express requirement of state law (unless specifically required by federal law), or exceed a requirement of a delegation agreement. The rulemaking was not developed solely under the general powers of the agency, but was specifically developed to meet the NAAQS established under federal law and authorized under Texas Clean Air Act (TCAA), §§382.011, 382.012, 382.017, 382.019, and 382.039.

The commission invites public comment on the draft regulatory impact analysis determination.

TAKINGS IMPACT ASSESSMENT

The commission prepared a takings impact assessment for this rulemaking action in accordance with Texas Government Code, §2007.043. The following is a summary of that assessment. The specific purpose of the rulemaking is to require airport GSE to be electric-powered or to lower emissions by any means available which will act as an air pollution control strategy to reduce NO x emissions necessary for the eight counties included in the HGA ozone nonattainment area to be able to demonstrate attainment with the ozone NAAQS. The proposed affected area consists of the eight-county HGA ozone nonattainment area, which includes Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller Counties. Promulgation and enforcement of the rules may burden private real property, because this proposed rulemaking action may result in investment in the permanent installation of supplied utilities at the major airports in the HGA area. Although the proposed rules do not directly prevent a nuisance or prevent an immediate threat to life or property, they do prevent a real and substantial threat to public health and safety and partially fulfill a federal mandate under 42 USC, §7410. Specifically, the emission limitations and control requirements within this proposal were developed in order to meet the ozone NAAQS set by the EPA under 42 USC, §7409. States are primarily responsible for ensuring attainment and maintenance of the NAAQS once the EPA has established them. Under 42 USC, §7410 and related provisions, states must submit, for approval by the EPA, SIPs that provide for the attainment and maintenance of NAAQS through control programs directed to sources of the pollutants involved. Therefore, the purpose of the rule proposal is to implement a GSE emissions reduction program in the HGA ozone nonattainment area which is necessary for the area to meet the air quality standards established under federal law as NAAQS. Consequently, the exemption which applies to this rulemaking action is that of an action reasonably taken to fulfill an obligation mandated by federal law; therefore, these proposed rules will not constitute a takings under the Texas Government Code, Chapter 2007.

CONSISTENCY WITH THE COASTAL MANAGEMENT PROGRAM

The commission determined that the proposed rulemaking relates to an action or actions subject to the Texas Coastal Management Program (CMP) in accordance with the Coastal Coordination Act of 1991, as amended (Texas Natural Resource Code, §§33.201 et seq.), and the commission rules in 30 TAC Chapter 281, Subchapter B, concerning Consistency with the Texas Coastal Management Program. As required by 31 TAC §505.11(b)(2) and 30 TAC §281.45(a)(3), relating to actions and rules subject to the CMP, commission rules governing air pollutant emissions must be consistent with the applicable goals and policies of the CMP. The commission reviewed this action for consistency with the CMP goals and policies in accordance with the rules of the Coastal Coordination Council, and determined that the action is consistent with the applicable CMP goals and policies. The CMP goal applicable to this rulemaking action is the goal to protect, preserve, and enhance the diversity, quality, quantity, functions, and values of coastal natural resource areas (31 TAC §501.12(1)). No new sources of air contaminants will be authorized and NO x air emissions will be reduced as a result of these rules. The CMP policy applicable to this rulemaking action is the policy that commission rules comply with regulations in 40 Code of Federal Regulations (CFR), to protect and enhance air quality in the coastal area (31 TAC §501.14(q)). This rulemaking action complies with 40 CFR 50, National Primary and Secondary Ambient Air Quality Standards, and 40 CFR 51, Requirements for Preparation, Adoption, and Submittal Of Implementation Plans. Therefore, in compliance with 31 TAC §505.22(e), this rulemaking action is consistent with CMP goals and policies.

Interested persons may submit comments on the consistency of the proposed rules with the CMP during the public comment period.

ANNOUNCEMENT OF HEARINGS

The commission will hold public hearings on this proposal at the following times and locations: September 18, 2000, 10:00 a.m., Lone Star Convention Center, 9055 Airport Road (FM 1484), Conroe; September 18, 2000, 7:00 p.m., Lake Jackson Civic Center, 333 Highway 332 East, Lake Jackson; September 19, 2000, 10:00 a.m. and 7:00 p.m., George Brown Convention Center, 1001 Avenida de Las Americas, Houston; September 20, 2000, 9:00 a.m., VFW Hall, 6202 George Bush Drive, Katy; September 20, 2000, 6:00 p.m., East Harris County Community Center, 7340 Spencer, Pasadena; September 21, 2000, 10:00 a.m., Southeast Texas Regional Airport Media Room, 6000 Airline Drive, Beaumont; September 21, 2000, 2:00 p.m., Amarillo City Commission Chambers, City Hall, 509 East 7th Avenue, Amarillo; September 21, 2000, 6:00 p.m., Charles T. Doyle Convention Center, 21st Street at Phoenix Lane, Texas City; September 22, 2000, 10:00 a.m., Dayton High School, 2nd Floor Lecture Room, 3200 North Cleveland Street, Dayton; El Paso City Council Chambers, 2 Civic Center Plaza, 2nd Floor, El Paso; September 22, 2000, 2:00 p.m., North Central Texas Council of Governments, 2nd Floor Board Room, 616 Six Flags Drive, Suite 200, Arlington; and September 25, 2000, 10:00 a.m., Texas Natural Resource Conservation Commission, 12100 North I-35, Building E, Room 201S, Austin. The hearings are structured for the receipt of oral or written comments by interested persons. Registration will begin one hour prior to each hearing. Individuals may present oral statements when called upon in order of registration. A four-minute time limit will be established at each hearing to assure that enough time is allowed for every interested person to speak. Open discussion will not occur during each hearing; however, agency staff members will be available to discuss the proposal one hour before each hearing, and will answer questions before and after each hearing.

Persons with disabilities who have special communication or other accommodation needs, who are planning to attend a hearing, should contact the Office of Environmental Policy, Analysis, and Assessment at (512) 239-4900. Requests should be made as far in advance as possible.

SUBMITTAL OF COMMENTS

Written comments may be submitted to Heather Evans, Office of Environmental Policy, Analysis, and Assessment, MC 206, P.O. Box 13087, Austin, Texas 78711-3087, faxed to (512) 239-4808, or emailed to siprules@tnrcc.state.tx.us . All comments should reference Rule Log Number 2000-011E-114-AI. Comments must be received by 5:00 p.m., September 25, 2000. For further information, please contact Roland Castaneda at (512) 239-0774, or Alan Henderson at (512) 239-1510.

STATUTORY AUTHORITY

The new sections are proposed under the Texas Water Code (TWC), §5.103, which authorizes the commission to adopt rules necessary to carry out its powers and duties under the TWC, and under the Texas Health and Safety Code, TCAA, §382.017, which provides the commission the authority to adopt rules consistent with the policy and purposes of the TCAA. The new sections are also proposed under TCAA, §382.011, which authorizes the commission to control the quality of the state's air; §382.012, which authorizes the commission to prepare and develop a general, comprehensive plan for the control of the state's air; §382.019, which authorizes the commission to adopt rules to control and reduce emissions from engines used to propel land vehicles; and §382.039, which authorizes the commission to develop and implement transportation programs and other measures necessary to demonstrate attainment and protect the public from exposure to hazardous air contaminants from motor vehicles.

The proposed new sections implement TCAA, §382.002, relating to Policy and Purpose; §382.011, relating to General Powers and Duties; §382.012, relating to State Air Control Plan; §382.019, relating to Methods Used to Control and Reduce Emissions from Land Vehicles; and §382.039, relating to Attainment Program.

§114.460.Definitions.

Unless specifically defined in the TCAA or in the rules of the commission, the terms used by the commission have the meanings commonly ascribed to them in the field of air pollution control. In addition to the terms which are defined by the TCAA, the following words and terms, when used in this division, shall have the following meanings, unless the context clearly indicates otherwise.

(1)

Air carrier--An entity providing air transportation of persons or goods for remuneration.

(2)

Air carrier operation--Landings and takeoffs of air carriers (excluding general aviation, non-fixed wing aircraft operations, and military operations) at airports for the purpose of transportation of persons and/or goods, or for the purpose of maintenance.

(3)

Ground support equipment (GSE)--Equipment that is used to service aircraft during passenger and/or cargo loading and unloading, maintenance, and other ground-based operations (excluding the servicing of general aviation aircraft, non-fixed wing aircraft, and military aircraft). This includes, but is not limited to, aircraft pushback tugs, baggage and cargo tugs, carts, forklifts, lifts, ground power units, air conditioning units, air start units, and belt loaders. Equipment that is used during freezing weather only is excluded from this definition (including, but not limited to, ground heaters and deicing vehicles).

(4)

Ground support equipment fleet--A group of ground support equipment controlled by the owner or operator at the same location. For purposes of compliance with the requirements of this division, a unit of GSE which is leased on a long-term basis (12 months or more) shall be considered part of the fleet of the lessee while a unit of GSE which is leased on a short-term basis (less than 12 months) shall be considered part of the fleet of the lessor.

(5)

GSE average emission factor--For purposes of calculating emission reductions needed for compliance with §114.462(b) of this title (relating to Control Requirements), the following factor should be used depending on engine size.

Figure: 30 TAC §114.460(5)

(6)

Subject airport--For purposes of compliance with this division, airports which have more than or equal to 100 air carrier operations per year, averaged over a three-year period. For airports which do not meet this average operating level on the effective date of this rule, the date which the airport becomes a subject airport is the January 1st following three years at or above that average operating level.

§114.462.Control Requirements.

(a)

In the counties listed in §114.469 of this title (relating to Affected Counties and Compliance Schedules), owners or operators of a ground support equipment (GSE) fleet at an airport which was a subject airport by the effective date of this rule must demonstrate a reduction of oxides of nitrogen (NO x ) emissions which is equal to or greater than the following percentage of NO x emissions attributable to the GSE fleet during the 1996 calendar year in accordance with the following schedule:

(1)

20% reduction by December 31, 2003;

(2)

50% reduction by December 31, 2004; and

(3)

90% reduction by December 31, 2005.

(b)

For a GSE fleet which was not in operation in 1996, owners or operators of the GSE fleet at an airport which was a subject airport by the effective date of this rule must demonstrate a reduction of NO x emissions which is equal to or greater than the following percentages of the amount obtained by multiplying the number of non-electric GSE units at the end of one year of operation by the GSE average emission factor as defined in §114.460 of this title (relating to Definitions) in accordance with the following schedule:

(1)

20% reduction by December 31, 2003 or December 31 of the first year of operation, whichever is later;

(2)

50% reduction by December 31, 2004 or December 31 of the second year of operation, whichever is later; and

(3)

90% reduction by December 31, 2005 or December 31 of the third year of operation, whichever is later.

(c)

At an airport which becomes a subject airport after the effective date of this rule, owners or operators of a GSE fleet shall meet the emission reduction requirements of subsection (a) or (b) of this section in accordance with the following schedule:

(1)

20% reduction by December 31, 2003 or December 31 of the year the airport becomes a subject airport, whichever is later;

(2)

50% reduction by December 31, 2004 or December 31 of the year after the airport becomes a subject airport, whichever is later; and

(3)

90% reduction by December 31, 2005 or December 31 of the second year after the airport becomes a subject airport, whichever is later.

(d)

Each GSE fleet subject to this subsection shall submit a plan to the executive director by May 1, 2003, or the first May 1st following operation at a subject airport, which lists each GSE unit, an emission factor for each unit, and the total actual annual emissions for each unit in existence in calendar year 1996. The plan shall provide for the implementation of emission reduction measures to achieve NO x emissions in the amount required by subsections (a), (b), or (c) of this section. The plan may include emission reductions measures which are applied to the GSE fleet itself and measures which have been achieved elsewhere within the nonattainment area as long as those measures would be creditable in accordance with the commission's emissions banking program as defined in §101.29 of this title (relating to Emission Credit Banking and Trading). The plan shall be revised as necessary and is subject to the approval of the executive director and the EPA.

(e)

Beginning in December 31, 2004, all owners or operators of GSE fleets subject to subsections (a), (b), or (c) of this section must demonstrate that emissions from any non-electric GSE added to the GSE fleet after December 31, 1996, or after the first year of operation at a subject airport, is offset by 90%. This subsection does not apply to GSE which is added to the fleet to replace existing GSE.

(f)

In the event that the EPA, the United States Department of Transportation, and the GSE owners/operators adopt an enforceable agreement, the measures defined within that agreement may be used in a plan submitted in accordance with subsection (d) of this section.

(g)

In lieu of compliance with subsections (a)-(e) of this section, an owner or operator of a GSE fleet at a subject airport may ensure that the fleet is 100% electric powered by May 1, 2005, or three years after the airport became a subject airport, whichever is later. For any GSE unit which is not available for purchase or conversion to electric power, an owner or operator may meet the requirement of this subsection if the owner or operator demonstrates that the lowest emitting equipment is used, subject to the approval of the executive director and the EPA.

§114.466.Reporting and Recordkeeping Requirements.

(a)

Owners or operators affected by §114.462 of this title (relating to Control Requirements) must submit annual ground support equipment (GSE) fleet reports for the previous year starting on February 1, 2004, and every February 1 thereafter. The report shall be submitted to the executive director and must contain, at a minimum:

(1)

the GSE fleet identification number when assigned by the commission;

(2)

area in which the affected GSE primarily operate;

(3)

the purchase date, make, model, model year, horsepower rating, and fuel type for each unit of GSE;

(4)

a demonstration of compliance with the applicable control requirements under §114.462 of this title; and

(5)

any other information requested in writing by the executive director necessary to demonstrate compliance with this division.

(b)

The owner or operator of GSE shall maintain copies of submitted reports required by subsection (a) of this section on-site either in hard copy or electronically at the reported fleet address for a minimum of three years, and upon request shall make such reports immediately available to the executive director or local air pollution control agencies having jurisdiction in the area.

§114.469.Affected Counties and Compliance Schedules.

Owners or operators of ground equipment at subject airports in Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller Counties shall be in compliance with §114.462 of this title (relating to Control Requirements) and §114.466 of this title (relating to Reporting and Recordkeeping Requirements) no later than the dates specified therein.

This agency hereby certifies that the proposal has been reviewed by legal counsel and found to be within the agency's legal authority to adopt.

Filed with the Office of the Secretary of State, on August 11, 2000.

TRD-200005647

Margaret Hoffman

Director, Environmental Law Division

Texas Natural Resource Conservation Commission

Earliest possible date of adoption: September 24, 2000

For further information, please call: (512) 239-0348


8. HOUSTON/GALVESTON HEAVY EQUIPMENT FLEETS--COMPRESSION--IGNITION ENGINES

30 TAC §§114.470, 114.472, 114.476, 114.477, 114.479

The Texas Natural Resource Conservation Commission (commission) proposes new §114.470, Definitions; §114.472, Control Requirements; §114.476, Reporting and Recordkeeping Requirements; §114.477, Exemptions; and §114.479, Affected Counties. The commission proposes these revisions to new Division 8, Houston/Galveston Heavy Equipment Fleets--Compression-Ignition Engines; Subchapter I, Non-road Engines; Chapter 114, Control of Air Pollution from Motor Vehicles, and to the state implementation plan (SIP) in order to reduce ambient concentrations of ground-level ozone in the Houston/Galveston (HGA) ozone nonattainment area through the accelerated purchase of United States Environmental Protection Agency (EPA) certified Tier 2 and Tier 3 non-road equipment 50 horsepower (hp) and larger.

BACKGROUND AND SUMMARY OF THE FACTUAL BASIS FOR THE PROPOSED RULES

The HGA ozone nonattainment area is classified as Severe-17 under the Federal Clean Air Act (FCAA) Amendments of 1990 (42 United States Code (USC), §§7401 et seq.), and therefore is required to attain the one-hour ozone standard of 0.12 parts per million (ppm) by November 15, 2007. The HGA area, defined by Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller Counties, has been working to develop a demonstration of attainment in accordance with 42 USC, §7410. On January 4, 1995, the state submitted the first of its Post-1996 SIP revisions for HGA.

The January 1995, SIP consisted of urban airshed model (UAM) modeling for 1988 and 1990 base-case episodes, adopted rules to achieve a 9% rate-of-progress (ROP) reduction in volatile organic compounds (VOC), and a commitment schedule for the remaining ROP and attainment demonstration elements. At the same time, but in a separate action, the State of Texas filed for the temporary nitrogen oxides (NO x ) waiver allowed by 42 USC, §7511a(f). The January 1995, SIP and the NO x waiver were based on early base-case episodes which marginally exhibited model performance in accordance with EPA modeling performance standards, but which had a limited data set as inputs to the model. In 1993 and 1994, the commission was engaged in an intensive data-gathering exercise known as the COAST study. The state believed that the enhanced emissions inventory, expanded ambient air quality and meteorological monitoring, and other elements would provide a more robust data set for modeling and other analysis, which would lead to modeling results that the commission could use to better understand the nature of the ozone air quality problem in the HGA area.

Around the same time as the 1995 submittal, EPA policy regarding SIP elements and timelines went through changes. Two national programs in particular resulted in changing deadlines and requirements. The first of these programs was the Ozone Transport Assessment Group. This group grew out of a March 2, 1995, memo from Mary Nichols, former EPA Assistant Administrator for Air and Radiation, that allowed states to postpone completion of their attainment demonstrations until an assessment of the role of transported ozone and precursors had been completed for the eastern half of the nation, including the eastern portion of Texas. Texas participated in this study, and it has been concluded that Texas does not significantly contribute to ozone exceedances in the Northeastern United States. The other major national initiative that has impacted the SIP planning process is the revisions to the national ambient air quality standard (NAAQS) for ozone. The EPA promulgated a final rule on July 18, 1997, changing the ozone standard to an eight-hour standard of 0.08 ppm. In November 1996, concurrent with the proposal of the standards, the EPA proposed an interim implementation plan (IIP) that it believed would help areas like HGA transition from the old to the new standard. In an attempt to avoid a significant delay in planning activities, Texas began to follow this guidance, and readjusted its modeling and SIP development timelines accordingly. When the new standard was published, the EPA decided not to publish the IIP, and instead stated that, for areas currently exceeding the one-hour ozone standard, that standard would continue to apply until it is attained. The FCAA requires that HGA attain the standard by November 15, 2007.

The EPA issued revised draft guidance for areas such as HGA that do not attain the one-hour ozone standard. The commission adopted on May 6, 1998, and submitted to the EPA on May 19, 1998, a revision to the HGA SIP which contained the following elements in response to the EPA guidance: UAM modeling based on emissions projected from a 1993 baseline out to the 2007 attainment date; an estimate of the level of VOC and NO x reductions necessary to achieve the one-hour ozone standard by 2007; a list of control strategies that the state could implement to attain the one-hour ozone standard; a schedule for completing the other required elements of the attainment demonstration; a revision to the Post-1996 9% ROP SIP that remedied a deficiency that the EPA believed made the previous version of that SIP unapprovable; and evidence that all measures and regulations required by Subpart 2 of Title I of the FCAA to control ozone and its precursors have been adopted and implemented, or are on an expeditious schedule to be adopted and implemented.

In November 1998, the SIP revision submitted to the EPA in May 1998 became complete by operation of law. However, the EPA stated that it could not approve the SIP until specific control strategies were modeled in the attainment demonstration. The EPA specified a submittal date of November 15, 1999, for this modeling. In a letter to the EPA dated January 5, 1999, the state committed to model two strategies showing attainment.

As the HGA modeling protocol evolved, the state eventually selected and modeled seven basic modeling scenarios. As part of this process, a group of HGA stakeholders worked closely with commission staff to identify local control strategies for the modeling. Some of the scenarios for which the stakeholders requested evaluation included options such as California-type fuel and vehicle programs, as well as an acceleration simulation mode equivalent motor vehicle inspection and maintenance program. Other scenarios incorporated the estimated reductions in emissions that were expected to be achieved throughout the modeling domain as a result of the implementation of several voluntary and mandatory statewide programs adopted or planned independently of the SIP. It should be made clear that the commission did not propose that any of these strategies be included in the ultimate control strategy submitted to the EPA in 2000. The need for and effectiveness of any controls which may be implemented outside the HGA eight-county area will be evaluated on a county-by-county basis.

The SIP revision was adopted by the commission on October 27, 1999, submitted to the EPA by November 15, 1999, and contained the following elements: photochemical modeling of potential specific control strategies for attainment of the one-hour ozone standard in the HGA area by the attainment date of November 15, 2007; an analysis of seven specific modeling scenarios reflecting various combinations of federal, state, and local controls in HGA (additional scenarios H1 and H2 build upon Scenario VIf); identification of the level of reductions of VOC and NO x necessary to attain the one-hour ozone standard by 2007; a 2007 mobile source budget for transportation conformity; identification of specific source categories which, if controlled, could result in sufficient VOC and/or NO x reductions to attain the standard; a schedule committing to submit by April 2000 an enforceable commitment to conduct a mid-course review; and a schedule committing to submit modeling and adopted rules in support of the attainment demonstration by December 2000.

The April 19, 2000, SIP revision for HGA contained the following enforceable commitments by the state: to quantify the shortfall of NO x reductions needed for attainment; to list and quantify potential control measures to meet the shortfall of NO x reductions needed for attainment; to adopt the majority of the necessary rules for the HGA attainment demonstration by December 31, 2000, and to adopt the rest of the shortfall rules as expeditiously as practical, but no later than July 31, 2001; to submit a Post-99 ROP plan by December 31, 2000; to perform a mid-course review by May 1, 2004; and to perform modeling of mobile source emissions using the EPA mobile source emissions model (MOBILE6), to revise the on-road mobile source budget as needed, and to submit the revised budget within 24 months of the model's release. In addition, if a conformity analysis is to be performed between 12 months and 24 months after the MOBILE6 release, the state will revise the motor vehicle emissions budget (MVEB) so that the conformity analysis and the SIP MVEB are calculated on the same basis.

In order for the state to have an approvable attainment demonstration, EPA has indicated that the state must adopt those strategies modeled in the November submittal and then adopt sufficient controls to close the remaining gap in NO x emissions. The modeling included in this proposal indicates a gap of an additional 77.98 tons per day (tpd) of NO x reductions is necessary for an approvable attainment demonstration. The commission estimates that this measure will achieve a minimum of 12.2 tpd of NO x equivalent reductions and is therefore a necessary measure to consider for closing the gap and successfully demonstrating attainment.

The emission reduction requirements included as part of this SIP revision represent substantial, intensive efforts on the part of stakeholder coalitions in the HGA area. These coalitions, involving local governmental entities, elected officials, environmental groups, industry, consultants, and the public, as well as the commission and the EPA, have worked diligently to identify and quantify potential control strategy measures for the HGA attainment demonstration. Local officials from the HGA area have formally submitted a resolution to the commission, requesting the inclusion of many specific emission reduction strategies.

The current SIP revision contains rules, enforceable commitments, and photochemical modeling analyses in support of the HGA ozone attainment demonstration. In addition, this SIP contains post-1999 ROP plans for the milestone years 2002 and 2005, and for the attainment year 2007. The SIP also contains enforceable commitments to implement further measures, if needed, in support of the HGA attainment demonstration, as well as a commitment to perform and submit a mid-course review.

The HGA ozone nonattainment area will need to ultimately reduce NOx more than 750 tpd to reach attainment with the one-hour standard. In addition, a VOC reduction of about 25% will have to be achieved. Adoption of the accelerated purchase of federal Tier 2/Tier 3 non-road diesel equipment program will contribute to attainment and maintenance of the one-hour ozone standard in the HGA area. This program also should contribute to a successful demonstration of transportation conformity in the HGA area.

The commission proposes these amendments to Chapter 114 and revisions to the SIP in order to control ground-level ozone in the HGA ozone nonattainment area, and the proposed rules are one element of the control strategy for the HGA Post-1999 ROP/Attainment Demonstration SIP. The purpose of these proposed rules is to establish the accelerated purchase and operation of non-road, compression-ignition fleet equipment within the HGA nonattainment area which will reduce NO x and VOC emissions that are necessary for the counties included in the HGA nonattainment area to be able to demonstrate attainment with NAAQS.

The EPA has been regulating highway (on-road) cars and trucks since the early 1970s and continues to set increasingly stringent emissions standards for such vehicles. After making considerable progress in controlling the emissions from on-road vehicles, the EPA turned its attention to non-road engines, which also contribute significantly to air pollution.

Diesel engines, also referred to as compression-ignition engines, dominate the large non-road engine market. Examples of non-road equipment that use diesel engines include: agricultural equipment such as tractors, balers, and combines; construction equipment such as backhoes, graders, and bulldozers; general industrial equipment such as concrete/industrial saws, crushing equipment, and scrubber/sweepers; lawn and garden equipment such as garden tractors, rear engine mowers, and chipper/grinders; material handling equipment such as heavy forklifts; and utility equipment such as generators, compressors, and pumps.

The EPA adopted regulations in 40 Code of Federal Regulations Part 89 (40 CFR 89), Control of Emissions from New and In-use Nonroad Engines, as effective June 17, 1994. Under 40 CFR 89, compression-ignition engines greater than 50 hp must comply with Tier 1 emissions standards that are being phased in between calendar years 1996 and 2000, depending on the size of the engine. Under the Tier 1 standards, the EPA projects that NO x emissions from new non-road, compression-ignition equipment will be reduced by over 30% from uncontrolled levels of unregulated engines. The Tier 1 standards do not apply to engines used in underground mining equipment, locomotives, and marine vessels. The Mine Safety and Health Administration is responsible for setting requirements for underground mining equipment. Locomotives and marine vessels are covered by separate EPA programs.

On October 23, 1998, the EPA revised 40 CFR 89 and adopted more stringent emission standards for NO x , hydrocarbons (HC, which are also called VOC), and particulate matter (PM) for new non-road, compression-ignition engines, to be phased in over several years beginning in model year 1999. Engines used in underground mining equipment, locomotives, and marine vessels over 50 hp are not included. This comprehensive new program phases in more stringent Tier 2 standards for all engine sizes from the model years 2001 to 2006, and yet more stringent Tier 3 standards from the model years 2006 to 2008. The following figure, which was extracted from the Table 1-1 of the "Final Regulatory Impact Analysis: Control of Emissions from Non-road Diesel Engines," (EPA 420-R-98-016, dated August 1998) shows the emission standards adopted by EPA in 40 CFR, §89.112. Also, the new program includes a voluntary program called the "Blue Sky Series" engine program to encourage the production of advanced, very low-emitting engines. Under these new standards, the EPA projects that emissions from new non-road, compression-ignition equipment will be further reduced by 60% for NO x and 40% for PM compared to the emission levels of engines meeting the Tier 1 standards.

Figure 1: 30 TAC Chapter 114C-Preamble

As part of the attainment demonstration SIP for the Dallas/Fort Worth (DFW) ozone nonattainment area, the commission adopted accelerated non-road, compression-ignition fleet rules (§§114.410, 114.412, 114.416, 114.417, and 114.419). The proposed new rules would apply requirements identical to the existing DFW rules in the eight-county HGA ozone nonattainment counties.

Non-road equipment covered by these rules only includes equipment that is used exclusively for non-road purposes. In other words, non-road equipment does not have a license plate and cannot be used on roads. Dump trucks and other equipment that are used both on-road and off-road are not subject to the requirements of these rules.

The proposed rules will require persons in the HGA nonattainment area which own or operate non-road equipment powered by compression-ignition engines 50 hp and up to meet the following requirements. For the portion of the fleet that is 50 hp up to 100 hp, the owner or operator must ensure that such equipment will consist of 100% Tier 2 non-road equipment by the end of the calendar year 2007. For the portion of the fleet that is 100 hp up to 750 hp, the owner or operator must ensure that such equipment consist of a minimum of 50% Tier 3 non-road equipment and the remainder Tier 2 non-road equipment by the end of the calendar year 2007. Finally, for the portion of the fleet that is greater than 750 hp, the owner or operator must ensure that such equipment consist of 100% Tier 2 engines by the end of calendar year 2007. This will accelerate the turnover rate of compression-ignition, engine-powered, non-road equipment that would occur as a result of the federal Tier 2/Tier 3 program. Alternatively, an affected person may be exempted from these requirements if an emission reduction plan is developed that will achieve emissions reductions equivalent to the full implementation of these rules. As part of this plan an owner or operator may achieve these reductions, in whole or in part, by obtaining emission reduction credits (ERC), mobile emission reduction credits (MERC), discrete emission reduction credit (DERC), or mobile discrete emission reduction credit (MDERC) in accordance with proposed new §114.477 and 30 TAC Chapter 101, General Air Rules, §101.29, Emission Credit Banking and Trading. In concurrent rulemaking (rule log number 1998-089-101-AI), the emission credit banking and trading rules are being moved to Chapter 101, Subchapter H, Emissions Banking and Trading, Division 1, Emission Credit Banking and Trading and Division 4, Discrete Emission Credit Banking and Trading.

The HGA area needs emissions reductions earlier than what the natural turnover would allow; therefore, these proposed rules will require that Tier 2 and Tier 3 equipment be purchased at an accelerated rate once they become available under the EPA schedule outlined in 40 CFR 89. The proposed rules exempt non-road engines used in locomotives, underground mining equipment, marine application, aircraft, airport ground support equipment (GSE), equipment used solely for agricultural purposes, emergency equipment, and freezing weather equipment.

Generally, the rules will affect equipment 50 hp and larger used in construction, general industrial, lawn and garden, utility, and material handling applications. Examples of equipment used in construction applications include backhoes, bore/drill rigs, cement mixers, crawler tractors, excavators, graders, off-highway trucks, pavers, paving equipment, plate compactors, rollers, rubber-tire dozers, rubber-tire loaders, scrapers, signal boards, skid-steer loaders, trenchers, and feller/bunchers. Examples of equipment used in general industrial applications include concrete/industrial saws, crushing equipment, oil field equipment, refrigeration/air conditioning units, scrubber/sweepers, and rail maintenance equipment. Examples of equipment used in lawn and garden applications include garden tractors, rear engine mowers, and chipper/grinders. Examples of equipment used in utility applications include air compressors, hydro-power units, pressure washers, pumps, generator sets, irrigation sets, and welders. Examples of equipment used in material handling applications include aerial lifts, cranes, forklifts, and rough-terrain forklifts.

The costs of meeting the new federal emission standards are expected to add about 1.0% to the purchase price of typical new non-road, compression-ignition equipment, although for some equipment the standards may cause price increases on the order of 2.0% to 3.0%. However, the cost of this program is the cost of having to replace the non-road, compression-ignition fleet on an accelerated schedule, not the cost of Tier 2 and Tier 3 engines. The cost of Tier 2 and Tier 3 engines is already accounted for in the EPA regulations, not as a result of these rules. The program is expected to cost between $30 million to $42 million average annual cost.

The commission solicits comment on additional flexibilities relating to rule content and implementation which have not been addressed in this or other concurrent rulemakings. These flexibilities may be available for both mobile and stationary sources. Additional flexibilities may also be achieved through innovative and/or emerging technology which may become available in the future. Additional sources of funds for incentive programs may become available to substitute for some of the measures considered here.

SECTION-BY-SECTION DISCUSSION

Rules regarding an accelerated purchase of federal Tier 2 and Tier 3 non-road diesel equipment were adopted for the DFW ozone nonattainment area on April 19, 2000. These rules were adopted in Chapter 114, Subchapter I, Division 2, §114.410, Definitions; §114.412, Control Requirements; §114.416, Reporting and Recordkeeping Requirements; §114.417, Exemptions; and §114.419, Affected Counties. This rulemaking action proposes identical requirements which would apply to the eight-county HGA ozone nonattainment area.

The proposed new §114.470 adds definitions for Blue Sky Series engine, compression-ignition engine, fleet, non-road engine, non-road equipment, Tier 2 engine, and Tier 3 engine.

The proposed new §114.472 would require persons in the affected counties listed in §114.479, which own or operate non-road equipment powered by compression-ignition engines to use non-road equipment powered by Tier 2 and Tier 3 compression engines. The phase-in schedule specified in these rules accelerates the natural turnover of non-road equipment. To ensure the equipment is available, the phase-in schedule specified in these rules is set up so that compliance dates come after the implementation dates of the new federal standard as specified in the schedule specified in the federal rules in 40 CFR 89.112, as amended on October 23, 1998. For the portion of the non-road fleets powered by compression-ignition engines greater than or equal to 100 hp, but less than or equal to 750 hp, the rule proposes a gradually increased percentage of Tier 2 and Tier 3 equipment required, so that by the end of calendar year 2007, at least 50% of the affected portion of the fleet shall meet Tier 3 standards and the remainder of the affected fleet shall meet Tier 2 standards. For the portion of the fleet greater than or equal to 50 hp, but less than 100 hp, the proposed rule requires that 100% of the equipment meet Tier 2 standards by the end of calendar year 2007. For engines greater than 750 hp, the proposed rule requires that 100% of the affected fleet be Tier 2 engines by the end of calendar year 2007. The rule also allows the non-road engines designated as "Blue Sky Series" engines be counted toward the percentage requirements as either Tier 2 or Tier 3 engines. The "Blue Sky Series" engine program is a voluntary EPA program that allows for earlier introduction of cleaner engines. The emission standards for the Blue Sky Series program are the same as Tier 3 emission standards. Finally, the proposed rule will allow that an EPA-certified retrofit of newly purchased engines, in order to meet the Tier 2 or Tier 3 emission standards, be allowed to meet the percentage requirements. This retrofit allowance is proposed because some newly purchased engines may be able to meet the Tier 2 and Tier 3 emission standards by being retrofitted. Therefore, for an affected entity to meet the percentage requirements, they may purchase new equipment or retrofit existing engines if there is an EPA-certified retrofit available.

The proposed new §114.476 requires persons subject to §114.472 to submit annual fleet reports. The proposed rule also requires them to maintain copies of the submitted reports for a minimum of three years.

The proposed new §114.477 exempts locomotives, underground mining equipment, marine engines, aircraft engines, airport GSE, and agricultural equipment. Locomotives, underground mining equipment, marine engines, and aircraft engines are exempt from this proposed rule because they are not regulated by the EPA non-road rule. Airport GSE is exempt from this rule because it is being regulated by another strategy being proposed concurrently. Agricultural equipment is exempt from the proposed rule because of its small contribution (less than 1.0%) to non-road emissions, and it is operated primarily in rural areas. Also, the commission proposes an exemption for equipment used exclusively for emergency operations and for equipment used exclusively for freezing weather operations due to their low impact on air quality during the ozone season.

In the rulemaking for the DFW area construction equipment operating restrictions rules, the commission specifically requested comment on allowing the use of added controls such as catalytic converters or other after-market devices, or the use of EPA-certified cleaner equipment, to exempt such equipment from the operating restrictions of these rules. In response to the DFW construction equipment operating restrictions exemption comments and other comments to those rules concerning the difficulty in complying with these rules, the commission proposes §114.477(b). This subsection allows owners or operators to be exempt from the requirements of these rules if they submit an emissions reduction plan by May 31, 2002, that is approved by the executive director and the EPA by May 31, 2003. The commission anticipates that by offering this exemption, the entities affected by these rules, the trade associations representing these entities, and the manufacturers will be encouraged to accelerate the research and development of emissions-reducing technology for equipment that will enable affected entities to meet the exemption. Each plan must describe in detail how the owner or operator will modify the equipment fleet to reduce NO x emissions by June 1, 2005 by a target amount equivalent to the total reductions achieved by implementation of these rules. If equipment subject to these rules is also subject to the HGA construction equipment operating restrictions rules, and the owner or operator would like to be exempt from both sets of rules, then the plan must reduce NO x emissions by a target amount equivalent to the total reductions achieved by both sets of rules. If the plan demonstrates that these reductions will occur by June 1, 2005, the reductions will be considered equivalent for purposes of timing. The commission will apply emissions inventory factors for equipment used in the modeling to develop these rules to quantify the emissions reductions resulting from the fleet modifications. The commission will develop a guidance document to assist operators in developing their plans. The guidance document will contain both the target emissions amount operators must meet, as well as emission factors for each type of equipment affected by the rules, and will offer guidance on how to calculate total emissions reductions for an equipment fleet.

The commission is requiring submission of the emission reduction plans by May 31, 2002, to allow sufficient time to review and quantify the collective emissions reductions the plans propose. The commission will complete the reviews by May 31, 2003, which coincides with the planned mid-course review of all control measures included in the SIP. After reviewing the plans, the commission will determine whether the collective emissions reductions proposed by the plans are equivalent to the reductions achieved from implementing both these rules.

The proposed new §114.479 specifies the counties that are subject to the new requirements. The counties included in the eight-county HGA nonattainment area are Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller.

FISCAL NOTE: COSTS TO STATE AND LOCAL GOVERNMENT

John Davis, Technical Specialist with Strategic Planning and Appropriations, determined that for the first five-year period the proposed new sections are in effect, there will be significant fiscal implications for units of state and local government located within the HGA ozone nonattainment area that own or operate non-road diesel vehicles and engines of 50 hp and larger.

For the portion of the fleet that is 50 hp up to 100 hp, owners and operators must ensure that such equipment will consist of 100% Tier 2 non-road equipment by the end of the calendar year 2007. For the portion of the fleet that is 100 hp up to 750 hp, owners and operators must ensure that such equipment consist of a minimum of 50% Tier 3 non-road equipment and the remainder Tier 2 non-road equipment by the end of the calendar year 2007. Finally, for the portion of the fleet that is greater than 750 hp, owners and operators must ensure that such equipment consist of 100% Tier 2 engines by the end of calendar year 2007.

Tier 2 and 3 standards are EPA standards whose goals are to reduce NOx , HC (or VOC), and PM emissions for new non-road, compression-ignition engines. The primary differences between the current Tier 1 and Tier 2 standards is that in Tier 2 for the combined emissions of NO x and non-methane hydrocarbons (NMHC) has replaced a separate standard for NO x and HC in Tier 1; in Tier 2, standards for carbon monoxide (CO) and PM were added in engines of 50 to 175 hp; and in all other engine sizes, the CO and PM standards are more stringent for Tier 2 than Tier 1. The primary difference between Tier 3 and Tier 2 standards is that NMHC and NO x emission standards are approximately 39% more stringent in Tier 3 than Tier 2. The EPA has a voluntary program called the "Blue Sky Series" engine program to encourage the production of advanced, very-low emitting engines. These proposed rules gradually increase the percentage of Tier 2 and 3 engines needed in the fleet. "Blue Sky Series" engines will be allowed to meet either percentage requirement because the Blue Sky standards are the same as Tier 3 standards. These rules will also allow EPA-certified retrofit of newly purchased engines that meet the Tier 2 or Tier 3 emission standards to be used to meet the percentage requirements for each tier.

The proposed rules will affect the owners and operators of diesel equipment of 50 hp and larger used in the construction, general industrial, lawn and garden, utility, and material handling categories in the HGA ozone nonattainment area. Examples of equipment in the construction category include backhoes, bore/drill rigs, cement mixers, crawler tractors, excavators, graders, off-highway trucks, pavers, paving equipment, plate compactors, rollers, rubber-tire dozers, rubber-tire loaders, scrapers, signal boards, skid-steer loaders, trenchers, and feller/bunchers. Examples of equipment in the general industrial category include concrete/industrial saws, crushing equipment, oil field equipment, refrigeration/air conditioning units, scrubber/sweepers, and rail maintenance equipment. Examples of equipment used in the lawn and garden category include garden tractors, rear engine mowers, and chipper/grinders. Examples of equipment in the utility category include air compressors, hydro-power units, pressure washers, pumps, generator units, irrigation units, and welders. Examples of equipment in the material handling category include aerial lifts, cranes, forklifts, and rough-terrain forklifts.

The proposed new rules will also require affected individuals, state and local units of government, and businesses in the HGA area to submit to the commission, annual reports that demonstrate compliance with the proposed new sections. The proposed rules exempt non-road engines used in locomotives, underground mining equipment, marine applications, aircraft, airport ground support equipment, equipment used solely for agricultural purposes, emergency equipment, and freezing weather equipment.

The total number of existing diesel equipment covered by the proposed new sections and owned by units of state and local government is unknown; therefore, the total cost to units of state and local government cannot be quantified. As a sample of the potential equipment involved, the Texas Department of Transportation has 137 pieces of equipment affected by these rules. The total cost to units of state and local government will be similar to the costs discussed in the PUBLIC BENEFITS AND COSTS section of this preamble and will vary with the number of units owned that will need to be retrofitted, re-engined, or replaced to comply with the proposed new sections.

PUBLIC BENEFIT AND COSTS

Mr. Davis also determined that for each year of the first five years the proposed new sections are in effect, the public benefit anticipated from enforcement of and compliance with the proposed new sections will be the potential reduction of NO x , VOC, CO, and PM emissions, potentially improved air quality, and contribution toward demonstration of attainment with the ozone NAAQS.

The commission anticipates significant fiscal implications anticipated to affected individuals, state and local government agencies, and businesses as a result of implementing the proposed new sections.

The EPA's NONROAD computer model estimated a population, in calendar year 2007, of approximately 44,525 pieces of compression-ignition, non-road equipment in the eight-county HGA ozone nonattainment area affected by the proposed new sections. Based on the 1999 population of 34,609 pieces of compression-ignition, non-road equipment in the eight-county HGA ozone nonattainment area, this is a growth factor of approximately 3.2% per year. The commission estimates that by the end of calendar year 1997, the population of compression-ignition, non-road equipment in the eight-county HGA ozone nonattainment area was approximately 32,496 units. Using the ten year life-cycle for medium to large engines in the EPA final regulatory impact analysis, approximately 12,969 units with these types of engines will be purchased as a result of aging or growth from the beginning of year 1998 through year 2000. This equipment will have to be either retrofitted or re-engined with compliant engines or replaced during years 2001 through 2007 in order to comply with the proposed new sections. The commission estimates that approximately 9,264 units will be either retrofitted, re-engined, or replaced from year 2001 through year 2005, the period covered by this fiscal note. The commission assumes that retrofit, re-engine, or replacement will begin in the year 2001. In the years following calendar year 2000, the commission expects the population of compression-ignition, non-road units to grow by 8,809 units through the end of calendar year 2007 to a total of 44,525 units. In addition, the commission estimates that another 22,747 aging units will be replaced due to the normal life-cycle of this equipment. The total of new units purchased due to growth and normal replacement is 31,556 units through year 2007. The commission estimates that approximately 22,340 of these units will be purchased during years 2001 through 2005 due to growth and normal replacement.

The EPA's regulatory impact analysis contains estimated purchase prices for new non-road diesel equipment. Two of these price estimates include new portable and motive equipment in the 250 to 450 hp range and are applicable to the proposed rule. The EPA estimated costs of $24,000 to $40,000 is for new portable equipment in the 250 hp to 450 hp range. The EPA report does not specify the types of the portable equipment, but the types could include equipment like pumps, oil field equipment, refrigeration, and air conditioning units. These types of equipment may be classified for the most part as industrial equipment. In the EPA NONROAD model, the closest equivalent hp range is 175 hp to 300 hp. In that range, approximately 78 units must be retrofitted, re-engined, or replaced through calendar year 2005 to comply with the proposed standards. The estimated total replacement cost for these 78 units is an average of approximately $373,502 to $622,503 per year from 2001 through the end of calendar year 2005. The second EPA estimated cost is $130,000 for new motive equipment in the 250 hp to 450 hp range. The EPA does not specify the types of the motive equipment; however, the motive equipment types in the NONROAD model are probably classified as tractors and other related construction equipment. In the EPA NONROAD model, there are 4,321 pieces of construction (motive) equipment in the 175 hp to 300 hp range by the end of calendar year 2007. In that size engine, approximately 899 units will be retrofitted, re-engined, or replaced from calendar year 2001 through 2005. The estimated replacement cost for these 899 units is an average of approximately $23 million per year from 2001 through the end of calendar year 2005.

Since the EPA study addressed the larger engines, the commission assumes that approximately 7,971 of the remaining 8,286 units existing at the end of calendar year 2000 in the HGA ozone nonattainment area that must be retrofitted, or replaced are smaller units of equipment with replacement costs in the range of $15,000 to $30,000. If the 7,971 smaller units of diesel non-road equipment in the HGA ozone nonattainment area have replacement costs in the range of $15,000 to $30,000, the estimated replacement cost for these units is an average of approximately $24 million to $48 million per year from 2001 through the end of calendar year 2005. The commission also assumes that 316 of the remaining population of equipment with diesel engines in the HGA ozone nonattainment area that must be retrofitted or replaced are larger units of equipment in the $130,000 to $150,000 range. If the remaining 316 units of very large diesel, non-road equipment in the HGA ozone nonattainment area have replacement costs in the range of $130,000 to $150,000, the estimated replacement cost for these units is an average of approximately $8 million to $9 million per year from 2001 through the end of calendar year 2005.

The commission estimates the cost impact to replace the 9,264 units of non-road diesel equipment due to growth and replacement to meet standards in the HGA ozone nonattainment area at the end of calendar year 2005 to be an average of approximately $56 million to $81 million per year through the end of calendar year 2005. This cost impact is based on the assumption that all 9,264 units which will require modification or replacement through the end of calendar year 2005 will be replaced with new equipment. It is probable that some of this equipment will be retrofitted to meet either Tier 2 or Tier 3 standards, or re-engined with Tier 2 or Tier 3 compliant engines at costs much lower than the replacement cost indicated here. It is also probable that many equipment operators will choose to obtain equivalent emission reductions without making any changes to their equipment. In addition, the commission anticipates the total cost impact to be mitigated by the trade-in or the sale of existing equipment if new equipment is purchased. However, over 96% of this cost is based on the assumption that all of the 9,264 units that must be retrofitted, re-engined, or replaced by the end of the calendar year 2005 will be replaced with all new equipment. The commission estimates that used equipment in good condition is sold for from 40% to 60% of its original cost. If a 50% factor is applied to replacement costs to offset the reduced cost for retrofit, re-engine, and trade-in, the final cost impact to replace or retrofit the 9,264 units is approximately $140 million to $203 million. The decision to either purchase new equipment, retrofit, or re-engine will likely be based on the economics for each unit of equipment.

Between the years 2001 and 2007, the EPA NONROAD computer model estimates the population of diesel non-road equipment in the HGA ozone nonattainment area to grow by 8,809 units. In addition, another 22,747 units will be purchased to replace aging units for a total of 31,556 units. Approximately 22,340 of the total 31,556 units purchased for growth and aging replacement will be purchased during the years 2001 through 2005. The EPA analysis contains estimates of domestic sales of various sizes of equipment. If the sales within the HGA ozone nonattainment area are similar, the commission estimates that the additional cost of the engines for this equipment would be an average of approximately $2.1 million per year through the end of calendar year 2005. The EPA document states that the costs of meeting the new emission standards are expected to add about 1.0% to the purchase price of typical new non-road, compression-ignition equipment, although for some equipment the standards may cause price increases on the order of 2.0% to 3.0%.

The commission estimates the total fiscal impact to replace the estimated 31,604 units of equipment which will be either purchased new, retrofitted, re-engined, or replaced through 2005 to be an average of approximately $58 million to $83 million per year through calendar year 2005. Over 96% of this cost is based on the assumption that all of the 31,604 units that must be retrofitted, re-engined, or replaced by the end of calendar year 2005 will be replaced with all new equipment. It is probable that some of this equipment will be retrofitted to meet either Tier 2 or Tier 3 standards or re-engined with Tier 2 or Tier 3 compliant engines at a much lower cost than replacement cost. It is also probable that many equipment operators will choose to obtain equivalent emission reductions without making any changes to their equipment. In addition, the commission anticipates the total cost impact to be mitigated by the trade-in or the sale of existing equipment if new equipment is purchased. If trade-in allowances are considered, the commission anticipates the total annual cost between the years 2001 to 2005 to be approximately $30 million to $42 million. The decision to either purchase new equipment, retrofit, or re-engine will likely be based on the economics for each unit of equipment. The following table summarizes the costs through year 2005:

Figure 2: 30 TAC Chapter 114C-Preamble

SMALL BUSINESS AND MICRO-BUSINESS ASSESSMENT

The commission anticipates significant fiscal implications to small businesses and micro-businesses located in the HGA ozone nonattainment area as a result of implementing the proposed new sections. The commission anticipates that there are many small and micro-businesses in the affected area that own and operate non-road diesel equipment affected by the proposed rule. Depending on the relative age of current equipment and the economics to retrofit or re-engine the equipment versus new purchase for such equipment, affected small and micro-businesses in the HGA ozone nonattainment area may have to retrofit, re-engine, or replace some or most of their current diesel equipment in the years 2001 through the end of calendar year 2007 in order to comply with the proposed new sections. The commission anticipates that costs will be similar to those for businesses at large as indicated in the PUBLIC BENEFIT AND COSTS section of this preamble. The EPA estimated the costs of new portable equipment in the 250 hp to 450 hp category at $24,000 to $40,000 and motive equipment in the 250 hp to 450 hp range at approximately $130,000. The commission anticipates that most effected small businesses or micro-businesses will own and operate engines in the lower hp ranges, portable equipment, and other types of equipment in the lower cost ranges of approximately $15,000 to $30,000 per unit. The EPA estimated that the additional cost for diesel engines which comply with the proposed standards are in the range of $240 to $1,900 each. The total cost impact will be more dependent on the relative size of the fleet and on the size and number of the non-road diesel equipment they own and operate. The commission also anticipates that the total fiscal impact may be mitigated by the trade-in or sale of existing equipment. The total number of existing diesel equipment covered by the proposed new rules and owned by small and micro-businesses is unknown; therefore, the total cost to small and micro-businesses is undetermined.

DRAFT REGULATORY IMPACT ANALYSIS DETERMINATION

The commission reviewed the proposed rulemaking in light of the regulatory analysis requirements of Texas Government Code, §2001.0225, and determined that the rulemaking is subject to §2001.0225 because it meets the definition of a "major environmental rule" as defined in that statute. "Major environmental rule" means a rule of which the specific intent is to protect the environment or reduce risks to human health from environmental exposure and that may adversely affect in a material way the economy, a sector of the economy, productivity, competition, jobs, the environment, or the public health and safety of the state or a sector of the state. The proposed new rules are intended to protect the environment or reduce risks to human health from environmental exposure to ozone and will affect in a material way, the economy, a sector of the economy, productivity, competition, jobs, the environment, or the public health and safety of the state or a sector of the state. The proposed new rules would require units of state and local government, businesses, and persons in the eight-county HGA ozone nonattainment area which own or operate non-road equipment powered by compression-ignition equipment to meet the following requirements. For the portion of the fleet that is 50 hp up to 100 hp, owners and operators must ensure that such equipment will consist of 100% Tier 2 non-road equipment by the end of the calendar year 2007. For the portion of the fleet that is 100 hp up to 750 hp, owners and operators must ensure that such equipment consist of a minimum of 50% Tier 3 non-road equipment and the remainder Tier 2 non-road equipment by the end of the calendar year 2007. Finally, for the portion of the fleet that is greater than 750 hp, owners and operators must ensure that such equipment consist of 100% Tier 2 engines by the end of calendar year 2007. This air pollution control program is part of the strategy to reduce NO x emissions necessary for the counties included in the HGA ozone nonattainment area to be able to demonstrate attainment with the ozone NAAQS. The commission proposes an air pollution control program, including the use of Tier 2 and Tier 3 non-road, compression-ignition engine standards, be established to reduce NO x emissions necessary for the counties included in the HGA nonattainment area to be able to demonstrate attainment with the ozone NAAQS. Although the proposed rules meet the definition of a "major environmental rule" as defined in Texas Government Code, §2001.0225 only applies to a major environmental rule, the result of which is to: exceed a standard set by federal law, unless the rule is specifically required by state law; exceed an express requirement of state law, unless the rule is specifically required by federal law; exceed a requirement of a delegation agreement or contract between the state and an agency or representative of the federal government to implement a state and federal program; or adopt a rule solely under the general powers of the agency instead of under a specific state law. This rulemaking action does not meet any of these four applicability requirements of a "major environmental rule." Specifically, the use of Tier 2 and Tier 3 non-road, compression-ignition engine standards within this proposal were developed in order to meet the ozone NAAQS set by the EPA under 42 USC, §7409, and therefore meet a federal requirement. Provisions of 42 USC, §7410, require states to adopt a SIP which provides for "implementation, maintenance, and enforcement" of the primary NAAQS in each air quality control region of the state. While §7410 does not require specific programs, methods, or reductions in order to meet the standard, state SIPs must include "enforceable emission limitations and other control measures, means or techniques (including economic incentives such as fees, marketable permits, and auctions of emissions rights), as well as schedules and timetables for compliance as may be necessary or appropriate to meet the applicable requirements of this chapter," (meaning Chapter 85, Air Pollution Prevention and Control). It is true that 42 USC does require some specific measures for SIP purposes, like the inspection and maintenance program, but those programs are the exception, not the rule, in the SIP structure of 42 USC. The provisions of 42 USC recognize that states are in the best position to determine what programs and controls are necessary or appropriate in order to meet the NAAQS. This flexibility allows states, affected industry, and the public, to collaborate on the best methods for attaining the NAAQS for the specific regions in the state. Even though 42 USC allows states to develop their own programs, this flexibility does not relieve a state from developing a program that meets the requirements of §7410. Thus, while specific measures are not generally required, the emission reductions are required. States are not free to ignore the requirements of §7410 and must develop programs to assure that the nonattainment areas of the state will be brought into attainment on schedule.

The requirement to provide a fiscal analysis of proposed regulations in the Texas Government Code was amended by Senate Bill 633 (SB 633) during the 75th Legislative Session, 1999. The intent of SB 633 was to require agencies to conduct a regulatory impact analysis (RIA) of extraordinary rules. These are identified in the statutory language as major environmental rules that will have a material adverse impact and will exceed a requirement of state law, federal law, or a delegated federal program, or are adopted solely under the general powers of the agency. With the understanding that this requirement would seldom apply, the commission provided a cost estimate for SB 633 that concluded "based on an assessment of rules adopted by the agency in the past, it is not anticipated that the bill will have significant fiscal implications for the agency due to its limited application." The commission also noted that the number of rules that would require assessment under the provisions of the bill was not large. This conclusion was based, in part, on the criteria set forth in the bill that exempted proposed rules from the full analysis unless the rule was a major environmental rule that exceeds a federal law. As previously discussed, 42 USC does not require specific programs, methods, or reductions in order to meet the NAAQS; thus, states must develop programs for each nonattainment area to ensure that area will meet the attainment deadlines. Because of the ongoing need to address nonattainment issues, the commission routinely proposes and adopts SIP rules. The legislature is presumed to understand this federal scheme. If each rule proposed for inclusion in the SIP was considered to be a major environmental rule that exceeds federal law, then every SIP rule would require the full RIA contemplated by SB 633. This conclusion is inconsistent with the conclusions reached by the commission in its cost estimate and by the Legislative Budget Board (LBB) in its fiscal notes. Since the legislature is presumed to understand the fiscal impacts of the bills it passes, and that presumption is based on information provided by state agencies and the LBB, the commission believes that the intent of SB 633 was only to require the full RIA for rules that are extraordinary in nature. While the SIP rules will have a broad impact, that impact is no greater than is necessary or appropriate to meet the requirements of the FCAA. For these reasons, rules proposed for inclusion in the SIP fall under the exception in Texas Government Code, §2001.0225(a), because they are required by federal law. The commission performed photochemical grid modeling which predicts that NO x emission reductions, such as those required by these rules, will result in reductions in ozone formation in the HGA ozone nonattainment area. This rulemaking does not exceed an express requirement of state law. This rulemaking is intended to obtain NO x emission reductions which will result in reductions in ozone formation in the HGA ozone nonattainment area and help bring HGA into compliance with the air quality standards established under federal law as NAAQS for ozone. The rulemaking does not exceed a standard set by federal law, exceed an express requirement of state law (unless specifically required by federal law), or exceed a requirement of a delegation agreement. The rulemaking was not developed solely under the general powers of the agency, but was specifically developed to meet the NAAQS established under federal law and authorized under Texas Clean Air Act (TCAA), §§382.011, 382.012, 382.017, 382.019, and 382.039.

The commission invites public comment on the draft regulatory impact analysis.

TAKINGS IMPACT ASSESSMENT

The commission prepared a takings impact assessment for this rulemaking action in accordance with Texas Government Code, §2007.043. The following is a summary of that assessment. The specific purpose of the proposed rulemaking action would require persons in the eight-county HGA nonattainment area which own or operate non-road, compression-ignition equipment to meet the following requirements. For the portion of the fleet that is 50 hp up to 100 hp, the owner or operator must ensure that such equipment will consist of 100% Tier 2 non-road equipment by the end of the calendar year 2007. For the portion of the fleet that is 100 hp up to 750 hp, the owner or operator must ensure that such equipment consist of a minimum of 50% Tier 3 non-road equipment and the remainder Tier 2 non-road equipment by the end of the calendar year 2007. Finally, for the portion of the fleet that is greater than 750 hp, the owner or operator must ensure that such equipment consist of 100% Tier 2 engines by the end of calendar year 2007. This proposed rulemaking action will act as an air pollution control strategy to reduce NO x emissions necessary for the eight counties included in the HGA ozone nonattainment area to be able to demonstrate attainment with the ozone NAAQS. Promulgation and enforcement of this rule will not burden private, real property. Although the proposed rule does not directly prevent a nuisance, or prevent an immediate threat to life or property, it does prevent a real and substantial threat to public health and safety, and partially fulfill a federal mandate under 42 USC, §7410. Specifically, the emissions limitations and delays within the proposed rule were developed in order to meet the ozone NAAQS set by the EPA under 42 USC, §7409. States are primarily responsible for ensuring attainment and maintenance of the NAAQS, once the EPA has established them. Under 42 USC, §7410, and related provisions, states must submit, for EPA approval, SIPs that provide for the attainment and maintenance of NAAQS through control programs directed to sources of the pollutants involved. Therefore, the purpose of this rule is to implement a cleaner-burning, non-road, compression-ignition fleet program necessary for the HGA nonattainment area to meet the air quality standards established under federal law as NAAQS. Consequently, the exemption which applies to this rulemaking action is that of an action reasonably taken to fulfill an obligation mandated by federal law. Therefore, these proposed rules will not constitute a takings under Texas Government Code, Chapter 2007.

CONSISTENCY WITH THE COASTAL MANAGEMENT PROGRAM

The commission determined that the proposed rulemaking relates to an action or actions subject to the Texas Coastal Management Program (CMP) in accordance with the Coastal Coordination Act of 1991, as amended (Texas Natural Resources Code, §§33.201 et seq.), and the commission rules in 30 TAC Chapter 281, Subchapter B, concerning Consistency with the CMP. As required by 30 TAC §281.45(a)(3) and 31 TAC §505.11(b)(2), relating to actions and rules subject to the CMP, commission rules governing air pollutant emissions must be consistent with the applicable goals and policies of the CMP. The commission reviewed this action for consistency with the CMP goals and policies in accordance with the rules of the Coastal Coordination Council, and determined that the action is consistent with the applicable CMP goals and policies. The CMP goal applicable to this rulemaking action is the goal to protect, preserve, and enhance the diversity, quality, quantity, functions, and values of coastal natural resource areas (31 TAC §501.12(1)). No new sources of air contaminants will be authorized and NO x air emissions will be reduced as a result of these rules. The CMP policy applicable to this rulemaking action is the policy that commission rules comply with regulations in 40 CFR, to protect and enhance air quality in the coastal area (31 TAC §501.14(q)). This rulemaking action complies with 40 CFR 50, National Primary and Secondary Ambient Air Quality Standards, and 40 CFR 51, Requirements for Preparation, Adoption, and Submittal Of Implementation Plans. Therefore, in compliance with 31 TAC §505.22(e), this rulemaking action is consistent with CMP goals and policies.

ANNOUNCEMENT OF HEARINGS

The commission will hold public hearings on this proposal at the following times and locations: September 18, 2000, 10:00 a.m., Lone Star Convention Center, 9055 Airport Road (FM 1484), Conroe; September 18, 2000, 7:00 p.m., Lake Jackson Civic Center, 333 Highway 332 East, Lake Jackson; September 19, 2000, 10:00 a.m. and 7:00 p.m., George Brown Convention Center, 1001 Avenida de Las Americas, Houston; September 20, 2000, 9:00 a.m., VFW Hall, 6202 George Bush Drive, Katy; September 20, 2000, 6:00 p.m., East Harris County Community Center, 7340 Spencer, Pasadena; September 21, 2000, 10:00 a.m., Southeast Texas Regional Airport Media Room, 6000 Airline Drive, Beaumont; September 21, 2000, 2:00 p.m., Amarillo City Commission Chambers, City Hall, 509 East 7th Avenue, Amarillo; September 21, 2000, 6:00 p.m., Charles T. Doyle Convention Center, 21st Street at Phoenix Lane, Texas City; September 22, 2000, 10:00 a.m., Dayton High School, 2nd Floor Lecture Room, 3200 North Cleveland Street, Dayton; September 22, 2000, 11:00 a.m., El Paso City Council Chambers, 2 Civic Center Plaza, 2nd Floor, El Paso; September 22, 2000, 2:00 p.m., North Central Texas Council of Governments, 2nd Floor Board Room, 616 Six Flags Drive, Suite 200, Arlington; and September 25, 2000, 10:00 a.m., Texas Natural Resource Conservation Commission, 12100 North I-35, Building E, Room 201S, Austin. The hearings are structured for the receipt of oral or written comments by interested persons. Registration will begin one hour prior to each hearing. Individuals may present oral statements when called upon in order of registration. A four-minute time limit will be established at each hearing to assure that enough time is allowed for every interested person to speak. Open discussion will not occur during each hearing; however, agency staff members will be available to discuss the proposal one hour before each hearing, and will answer questions before and after each hearing.

Persons with disabilities who have special communication or other accommodation needs, who are planning to attend a hearing, should contact the Office of Environmental Policy, Analysis, and Assessment at (512) 239-4900. Requests should be made as far in advance as possible.

SUBMITTAL OF COMMENTS

Written comments may be submitted to Heather Evans, Office of Environmental Policy, Analysis, and Assessment, MC 206, P.O. Box 13087, Austin, Texas 78711-3087; faxed to (512) 239-4808; or emailed to siprules@tnrcc.state.tx.us . All comments should reference Rule Log Number 2000-011C-114-AI. Comments must be received by 5:00 p.m., September 25, 2000. For further information, please contact Ken Gathright at (512) 239-0599 or Alan Henderson at (512) 239-1510.

STATUTORY AUTHORITY

The new sections are proposed under Texas Water Code (TWC), §5.103, which authorizes the commission to adopt rules necessary to carry out its powers and duties under the TWC, and under Texas Health and Safety Code, TCAA, §382.017, which authorizes the commission to adopt rules consistent with the policy and purposes of the TCAA. The new sections are also proposed under TCAA, §382.011, which authorizes the commission to control the quality of the state's air; §382.012, which authorizes the commission to prepare and develop a general, comprehensive plan for the control of the state's air; §382.019, which authorizes the commission to adopt rules to control and reduce emissions from engines used to propel land vehicles; and §382.039, which authorizes the commission to develop and implement transportation programs and other measures necessary to demonstrate attainment and protect the public from exposure to hazardous air contaminants from motor vehicles.

The proposed new sections implement TCAA, §382.002, relating to Policy and Purpose; §382.011, relating to General Powers and Duties; §382.012, relating to State Air Control Plan; §382.019, relating to Methods Used to Control and Reduce Emissions from Land Vehicles; and §382.039, relating to Attainment Program.

§114.470.Definitions.

Unless specifically defined in the TCAA or in the rules of the commission, the terms used by the commission have the meanings commonly ascribed to them in the field of air pollution control. In addition to the terms which are defined by the TCAA, the following words and terms, when used in this division, shall have the following meanings, unless the context clearly indicates otherwise.

(1)

Blue Sky Series engine--A non-road engine meeting the requirements of Title 40 Code of Federal Regulations (CFR) §89.112(f), as amended on October 23, 1998.

(2)

Compression-ignition engine--A type of engine with operating characteristics significantly similar to the theoretical diesel combustion cycle. The non-use of a throttle to regulate intake air flow for controlling power during normal operation is indicative of a compression-ignition engine.

(3)

Fleet--The aggregate of non-road equipment powered by compression-ignition engines that operate within the counties specified in §114.479 of this title (relating to Affected Counties) under the authority of the same person. Regarding fleet equipment leased for one year or longer, the authority is considered to reside with the lessee. For fleet equipment leased for less than one year, the authority is considered to reside with the lessor.

(4)

Non-road engine--An engine as defined in Title 40 CFR §89.2, as amended on December 29, 1999.

(5)

Non-road equipment--Equipment which is powered by a non-road engine and which is not licensed for on-road use.

(6)

Tier 2 engine--An engine subject to the Tier 2 emission standards listed in Title 40 CFR §89.112(a), Table 1, as amended on October 23, 1998.

(7)

Tier 3 engine--An engine subject to the Tier 3 emission standards listed in Title 40 CFR §89.112(a), Table 1, as amended on October 23, 1998.

§114.472.Control Requirements.

(a)

Persons who own or operate non-road equipment powered by compression-ignition engines 50 horsepower (hp) and larger, in the counties listed in §114.479 of this title (relating to Affected Counties), are subject to the compliance requirements specified in subsection (b) of this section.

(b)

Owners or operators shall ensure that their fleet is certified to meet or exceed the Tier 2 and Tier 3 standards in accordance with the following schedule.

(1)

For the part of the fleet greater than or equal to 50 and less than 100 hp:

(A)

at least 25% of the affected portion of the fleet shall meet Tier 2 certification standards by December 31, 2004;

(B)

at least 50% of the affected portion of the fleet shall meet Tier 2 certification standards by December 31, 2005;

(C)

at least 75% of the affected portion of the fleet shall meet Tier 2 certification standards by December 31, 2006; and

(D)

100% of the affected portion of the fleet shall meet Tier 2 certification standards by December 31, 2007.

(2)

For the part of the fleet greater than or equal to 100 and less than or equal to 750 hp:

(A)

at least 10% of the affected portion of the fleet shall meet Tier 2 certification standards by December 31, 2004;

(B)

at least 20% of the affected portion of the fleet shall meet Tier 2 certification standards by December 31, 2005;

(C)

at least 30% of the affected portion of the fleet shall meet Tier 2 certification standards by December 31, 2006; and

(D)

at least 50% of the affected portion of the fleet shall meet Tier 3 certification standards, and the remainder of the affected portion of the fleet shall meet Tier 2 certification standards by December 31, 2007.

(3)

For that part of the fleet with an hp rating greater than 750 hp:

(A)

at least 50% of the affected portion of the fleet must meet Tier 2 certification standards by December 31, 2006; and

(B)

100% of the affected portion of the fleet must meet Tier 2 certification standards by December 31, 2007.

(c)

Non-road equipment that uses a "Blue Sky Series" engine, as defined in §114.470 of this title (relating to Definitions) may be considered a Tier 2 or Tier 3 engine for compliance with the percentage requirements of subsection (b) of this section.

(d)

The percentage requirements of subsection (b) of this section may also be met by a retrofit of currently owned or newly purchased non-road, compression-ignition engines certified by the EPA to meet or exceed the Tier 2 or Tier 3 emission standards.

§114.476.Reporting and Recordkeeping Requirements.

(a)

Persons affected by §114.472 of this title (relating to Control Requirements) must submit annual reports for the previous year beginning February 1, 2005, and every February 1 thereafter. The report shall be submitted to the executive director and shall contain, at a minimum:

(1)

the fleet identification number (when assigned by the Texas Natural Resource Conservation Commission);

(2)

the person's name, mailing address, telephone and fax numbers;

(3)

the name, title, mailing address, and telephone number of the specified person responsible for the fleet;

(4)

a list of all non-road equipment with compression-ignition engines 50 horsepower and larger; and

(5)

a demonstration of compliance with the applicable implementation schedule under §114.472 of this title.

(b)

The affected person shall maintain copies of reports required by subsection (a) of this section on-site at the reported fleet address for a minimum of three years, and upon request shall make such reports available to the executive director or local air pollution control agencies with jurisdiction.

§114.477.Exemptions.

(a)

The following non-road equipment powered by compression-ignition engines are exempt from §114.472 and §114.476 of this title (relating to Control Requirements; and Reporting and Recordkeeping Requirements):

(1)

locomotives;

(2)

underground mining equipment;

(3)

marine engines;

(4)

aircraft engines;

(5)

airport ground support equipment;

(6)

equipment used solely for agricultural purposes which includes, but is not limited to, tractors, balers, combines, sprayers, swathers, and skidders;

(7)

equipment used exclusively for emergency operations to protect public health and safety or the environment; and

(8)

equipment used exclusively for freezing weather operations.

(b)

Owners or operators who submit an emission reduction plan by May 31, 2002, that is approved by the executive director and the EPA by May 31, 2003, will be exempt from §114.472 and §114.476 of this title in the counties listed in §114.479 of this title (relating to Affected Counties) upon implementation of the rules of this division on December 31, 2004. In order to be approved, the plan must demonstrate reductions of oxides of nitrogen emissions equivalent to those required by §114.472 of this title and must contain adequate enforcement provisions.

§114.479.Affected Counties.

Persons in the following counties shall be in compliance with §114.472 and §114.476 of this title (relating to Control Requirements; and Reporting and Recordkeeping Requirements) no later than the dates specified in §114.472(b) of this title: Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller.

This agency hereby certifies that the proposal has been reviewed by legal counsel and found to be within the agency's legal authority to adopt.

Filed with the Office of the Secretary of State, on August 11, 2000.

TRD-200005613

Margaret Hoffman

Director, Environmental Law Division

Texas Natural Resource Conservation Commission

Earliest possible date of adoption: September 24, 2000

For further information, please call: (512) 239-0348


9. HOUSTON/GALVESTON CONSTRUCTION EQUIPMENT OPERATING RESTRICTIONS

30 TAC §§114.482, 114.486, 114.487, 114.489

The Texas Natural Resource Conservation Commission (commission) proposes new §114.482, Control Requirements; §114.486, Recordkeeping Requirements; §114.487, Exemptions; and §114.489, Affected Counties and Compliance Dates. The commission proposes these revisions to add new Division 9, Houston/Galveston Construction Equipment Operating Restrictions; to Subchapter I, Non-road Engines; Chapter 114, Control of Air Pollution from Motor Vehicles; and corresponding revisions to the state implementation plan (SIP). The commission proposes these new sections in Chapter 114 and revisions to the SIP in order to control ground-level ozone in the Houston/Galveston (HGA) ozone nonattainment area. The proposed sections are one element of the control strategy for the proposed HGA Post-1999 Rate-of-Progress (ROP)/Attainment Demonstration SIP.

BACKGROUND AND SUMMARY OF THE FACTUAL BASIS FOR THE PROPOSED RULES

The HGA ozone nonattainment area is classified as Severe-17 under the Federal Clean Air Act (FCAA) Amendments of 1990 (42 United States Code (USC), §§7401 et seq.), and therefore is required to attain the one-hour ozone standard of 0.12 parts per million (ppm) by November 15, 2007. The HGA area, defined by Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller Counties, has been working to develop a demonstration of attainment in accordance with 42 USC, §7410. On January 4, 1995, the state submitted the first of its Post-1996 SIP revisions for HGA.

The January 1995 SIP consisted of urban airshed model (UAM) modeling for 1988 and 1990 base-case episodes, adopted rules to achieve a 9% ROP reduction in volatile organic compounds (VOC), and a commitment schedule for the remaining ROP and attainment demonstration elements. At the same time, but in a separate action, the State of Texas filed for the temporary nitrogen oxides (NOx ) waiver allowed by 42 USC, §7511a(f). The January 1995 SIP and the NO x waiver were based on early base-case episodes which marginally exhibited model performance in accordance with the United States Environmental Protection Agency (EPA) modeling performance standards, but which had a limited data set as inputs to the model. In 1993 and 1994, the commission was engaged in an intensive data-gathering exercise known as the COAST study. The state believed that the enhanced emissions inventory, expanded ambient air quality and meteorological monitoring, and other elements would provide a more robust data set for modeling and other analysis, which would lead to modeling results that the commission could use to better understand the nature of the ozone air quality problem in the HGA area.

Around the same time as the 1995 submittal, the EPA policy regarding SIP elements and timelines went through changes. Two national programs in particular resulted in changing deadlines and requirements. The first of these programs was the Ozone Transport Assessment Group. This group grew out of a March 2, 1995, memo from Mary Nichols, former EPA Assistant Administrator for Air and Radiation, that allowed states to postpone completion of their attainment demonstrations until an assessment of the role of transported ozone and precursors had been completed for the eastern half of the nation, including the eastern portion of Texas. Texas participated in this study, and it has been concluded that Texas does not significantly contribute to ozone exceedances in the Northeastern United States. The other major national initiative that has impacted the SIP planning process is the revisions to the national ambient air quality standard (NAAQS) for ozone. The EPA promulgated a final rule on July 18, 1997 changing the ozone standard to an eight-hour standard of 0.08 ppm. In November 1996, concurrent with the proposal of the standards, the EPA proposed an interim implementation plan (IIP) that it believed would help areas like HGA transition from the old to the new standard. In an attempt to avoid a significant delay in planning activities, Texas began to follow this guidance, and readjusted its modeling and SIP development timelines accordingly. When the new standard was published, the EPA decided not to publish the IIP, and instead stated that, for areas currently exceeding the one-hour ozone standard, that standard would continue to apply until it is attained. The FCAA requires that HGA attain the standard by November 15, 2007.

The EPA issued revised draft guidance for areas such as HGA that do not attain the one-hour ozone standard. The commission adopted on May 6, 1998 and submitted to the EPA on May 19, 1998, a revision to the HGA SIP which contained the following elements in response to the EPA guidance: The UAM modeling based on emissions projected from a 1993 baseline out to the 2007 attainment date; an estimate of the level of VOC and NO x reductions necessary to achieve the one-hour ozone standard by 2007; a list of control strategies that the state could implement to attain the one-hour ozone standard; a schedule for completing the other required elements of the attainment demonstration; a revision to the Post-1996 9% ROP SIP that remedied a deficiency that the EPA believed made the previous version of that SIP unapprovable; and evidence that all measures and regulations required by Subpart 2 of Title I of the FCAA to control ozone and its precursors have been adopted and implemented, or are on an expeditious schedule to be adopted and implemented.

In November 1998, the SIP revision submitted to the EPA in May 1998 became complete by operation of law. However, the EPA stated that it could not approve the SIP until specific control strategies were modeled in the attainment demonstration. The EPA specified a submittal date of November 15, 1999, for this modeling. In a letter to the EPA dated January 5, 1999, the state committed to model two strategies showing attainment.

As the HGA modeling protocol evolved, the state eventually selected and modeled seven basic modeling scenarios. As part of this process, a group of HGA stakeholders worked closely with commission staff to identify local control strategies for the modeling. Some of the scenarios for which the stakeholders requested evaluation included options such as California-type fuel and vehicle programs as well as an acceleration simulation mode equivalent motor vehicle inspection and maintenance program. Other scenarios incorporated the estimated reductions in emissions that were expected to be achieved throughout the modeling domain as a result of the implementation of several voluntary and mandatory statewide programs adopted or planned independently of the SIP. It should be made clear that the commission did not propose that any of these strategies be included in the ultimate control strategy submitted to the EPA in 2000. The need for and effectiveness of any controls which may be implemented outside the HGA eight-county area will be evaluated on a county-by-county basis.

The SIP revision was adopted by the commission on October 27, 1999, submitted to the EPA by November 15, 1999, and contained the following elements: photochemical modeling of potential specific control strategies for attainment of the one-hour ozone standard in the HGA area by the attainment date of November 15, 2007; an analysis of seven specific modeling scenarios reflecting various combinations of federal, state, and local controls in HGA (additional scenarios H1 and H2 build upon Scenario VIf); identification of the level of reductions of VOC and NO x necessary to attain the one-hour ozone standard by 2007; a 2007 mobile source budget for transportation conformity; identification of specific source categories which, if controlled, could result in sufficient VOC and/or NO x reductions to attain the standard; a schedule committing to submit by April 2000 an enforceable commitment to conduct a mid-course review; and a schedule committing to submit modeling and adopted rules in support of the attainment demonstration by December 2000.

The April 19, 2000, SIP revision for HGA contained the following enforceable commitments by the state: to quantify the shortfall of NO x reductions needed for attainment; to list and quantify potential control measures to meet the shortfall of NO x reductions needed for attainment; to adopt the majority of the necessary rules for the HGA attainment demonstration by December 31, 2000, and to adopt the rest of the shortfall rules as expeditiously as practical, but no later than July 31, 2001; to submit a Post-99 ROP plan by December 31, 2000; to perform a mid-course review by May 1, 2004; and to perform modeling of mobile source emissions using the EPA mobile source emissions model (MOBILE6), to revise the on-road mobile source budget as needed, and to submit the revised budget within 24 months of the model's release. In addition, if a conformity analysis is to be performed between 12 months and 24 months after the MOBILE6 release, the state will revise the motor vehicle emissions budget (MVEB) so that the conformity analysis and the SIP MVEB are calculated on the same basis.

In order for the state to have an approvable attainment demonstration, the EPA has indicated that the state must adopt those strategies modeled in the November submittal and then adopt sufficient controls to close the remaining gap in NO x emissions. The modeling included in this proposal indicates a gap of an additional 77.98 tons per day (tpd) of NO x reductions is necessary for an approvable attainment demonstration.

The emission reduction requirements included as part of this SIP revision represent substantial, intensive efforts on the part of stakeholder coalitions in the HGA area. These coalitions, involving local governmental entities, elected officials, environmental groups, industry, consultants, and the public, as well as the commission and the EPA, have worked diligently to identify and quantify potential control strategy measures for the HGA attainment demonstration. Local officials from the HGA area have formally submitted a resolution to the commission, requesting the inclusion of many specific emission reduction strategies.

The current SIP revision contains rules, enforceable commitments, and photochemical modeling analyses in support of the HGA ozone attainment demonstration. In addition, this SIP contains post-1999 ROP plans for the milestone years 2002 and 2005, and for the attainment year 2007. The SIP also contains enforceable commitments to implement further measures, if needed, in support of the HGA attainment demonstration, as well as a commitment to perform and submit a mid-course review.

The HGA ozone nonattainment area will need to ultimately reduce NOx more than 750 tpd to reach attainment with the one-hour standard. In addition, a VOC reduction of about 25% will have to be achieved. Adoption of the HGA Construction Equipment Operating Restrictions program will contribute to attainment and maintenance of the one-hour ozone standard in the HGA area. An HGA construction equipment operating restriction program should also contribute to a successful demonstration of transportation conformity in the HGA area.

The purpose of these rules is to establish a restriction on the use of construction equipment (non-road, heavy-duty diesel equipment rated at 50 horsepower (hp) and greater) as an air pollution control strategy to delay the emissions of NO x , a key ozone precursor, until later in the day, thus limiting ozone formation. The non-road mobile source category is one of the few sources of ozone-forming emissions that is not currently regulated by state or federal rules. Federal controls such as cleaner-burning engines and cleaner-diesel fuel have been proposed, but are not scheduled to be implemented until the 2004 time frame.

The proposed revisions provide a similar restriction on the use of construction equipment previously adopted by the commission for the Dallas/Fort Worth (DFW) ozone nonattainment area, except for the effective period, which is between the hours of 6:00 a.m. and noon, during Daylight Savings Time, which begins on the first Sunday in April and ends on the last Sunday in October, for the HGA ozone nonattainment area. The affected area includes the eight-county HGA nonattainment area of Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller Counties. The contribution towards the reduction in ozone levels from restricting the hours of operation of construction equipment is an essential component of the control strategy and is necessary for the eight-county HGA ozone nonattainment area to demonstrate attainment with the ozone NAAQS.

The effective date of the amended rules for HGA will be April 3, 2005. The commission established an effective date in 2005 to allow manufacturers time to produce and release new cleaner-burning equipment and retrofit technology, which would enable equipment operators to plan for and implement purchases of this equipment before rules concerning restrictions on the operation of construction equipment become effective.

The equipment to which the rules concerning restrictions on the operation of construction equipment apply includes all non-road, heavy-duty diesel equipment classified as "construction equipment," rated at 50 hp and greater, regardless of how it is being used. For example, equipment such as bulldozers used in sanitary landfills, non-road cranes used in demolition, and rubber tire loaders used in manufacturing operations are covered by these rules concerning restrictions on the operation of construction equipment. It is not the commission's intent to restrict the use of agriculture equipment, which does not meet the definition of construction equipment.

The commission understands that a literal interpretation of the term "construction equipment" could lead the reader to believe that the rules concerning restrictions on the operation of construction equipment only applied to non-road, heavy-duty diesel equipment used only for purposes of construction and mining, when in fact, the rules apply to all construction equipment greater than 50 hp, regardless of how it is being used.

Construction equipment is considered to be, but is not limited to, pavers, paving equipment, plate compactors, rollers, scrapers, surfacing equipment, signal boards/light plants, trenchers, bore/drill rigs, excavators, concrete/industrial saws, cement and mortar mixers, cranes, graders, off-highway trucks, crushing/processing equipment, rough terrain forklifts, rubber tire loaders, rubber tire tractors/dozers, tractors/loaders/backhoes, crawler tractors/dozers, skid steer loaders, off-highway tractors, and dumpsters/tenders.

Ozone is formed through chemical reactions between natural and man-made emissions of VOC and NO x in the presence of sunlight. Higher ozone levels occur most frequently on hot summer afternoons. The critical time for the mixing of NO x and VOC is early in the day. By delaying the hours of operation for construction equipment and delaying the release of NO x emissions until after noon during Daylight Savings Time in the HGA nonattainment area, the NOx emissions will not mix in the atmosphere with other ozone-forming compounds until after the critical mixing time has passed. Therefore, production of ozone will be stalled until later in the day when optimum ozone formation conditions no longer exist, ultimately reducing the peak level of ozone produced.

This strategy is not dependent on atmospheric conditions to reduce ozone formation, as such strategies are disfavored by 42 USC, §7423. Instead, the strategy creates reductions in the amount of NO x added to the atmosphere by construction equipment during the time of day when those emissions have been shown to contribute to exceedances of the ozone NAAQS. Use of "time of day" restrictions such as this for NAAQS compliance strategies was anticipated and discussed by the EPA in their off-road mobile source rules.

As established in the previously adopted DFW rules concerning restrictions on the operation of construction equipment, the proposed rules contain exemptions from control and recordkeeping requirements. These exemptions include construction equipment used exclusively for emergency operations to protect public health and the environment, and for mixing, transporting, pouring, or processing wet concrete. Also, the proposed rules contain an exemption that allows operators that submit an emissions reduction plan (plan) by May 31, 2002, which is approved by the executive director and the EPA by May 31, 2003, to operate during the restricted hours. The commission anticipates that by offering this exemption, equipment manufacturers or regulated businesses will invest in research and development of emissions-reducing technology for construction equipment to enable affected businesses to meet the exemption.

The emission reduction plan must describe in detail how the operator will modify his behavior or fleet of equipment to reduce NO x emissions by the implementation date in 2005 by a target amount equivalent to the total NO x reductions achieved by implementation of the rule from which the operator is applying for exemption. Owners or operators may submit plans to apply for exemption from either the construction equipment operating restriction rule or the accelerated purchase of non-road heavy-duty diesel equipment rule, or from both rules. The plans must contain emission reductions equivalent to the total NO x reductions achieved by the rule from which they are applying for exemption and must contain adequate enforcement provisions. Examples of modifications that may result in emission reductions include using new, cleaner-burning equipment, replacing existing equipment with cleaner-burning engines, retrofitting existing equipment with emissions-reducing technology, using emissions-reducing fuel, changing hours of operation, restricting equipment idling, and participating in an emissions banking and trading program. For example, an owner or operator may obtain emission reduction credits (ERCs), mobile emission reduction credits (MERCs), discrete emission reduction credit (DERCs), or mobile discrete emission reduction credit (MDERCs) in accordance with this section and 30 TAC Chapter 101 (General Air Rules), §101.29 (Emission Credit Banking and Trading). In a concurrent rulemaking (rule log number 1998-089-101-AI), the emission credit banking and trading rules are being moved to Chapter 101, Subchapter H (Emissions Banking and Trading), Division 1 (Emission Credit Banking and Trading) and Division 4 (Discrete Emission Credit Banking and Trading).

The commission will apply emission inventory factors for construction equipment used in the modeling utilized in the development of the rules concerning restrictions on the operation of construction equipment to quantify the NO x and VOC emission reductions and equivalent ozone reductions resulting from the fleet modifications. The commission will develop a guidance document to assist operators in developing their plans. The guidance document will contain both the target emissions amount operators must meet, as well as emission factors for each type of equipment affected by the rules concerning restrictions on the operation of construction equipment, and will offer guidance on how to calculate total emissions reductions for a fleet of equipment. The commission estimates that this measure results in an approximate 8.0 tpd shift of NOx emissions from morning to afternoon which is equivalent to a 6.7 tpd NO x reduction.

The commission is requiring submission of the plans by May 31, 2002 to allow sufficient time to review and quantify the collective emissions reductions the plans propose. The executive director and the EPA will complete the reviews by May 31, 2003, which coincides with the planned mid-course review of all control measures included in the SIP. After reviewing the plans, the executive director will determine whether the collective emission reductions proposed by the plans are equivalent to the NO x reductions achieved from implementing the underlying exempted rule. The commission will implement the construction equipment operating restrictions rules on April 3, 2005 and the accelerated purchase rules on December 31, 2004, as proposed, for operators who did not submit plans or whose plans were not approved.

Because this proposed strategy does not create an actual reduction in emissions nor require the use of additional control equipment or any new technology, the commission estimated that the fiscal implications may be significant due to the shift in work hours. The restriction in the hours of operation may require that companies adjust their work schedules to coincide with the hours of operation allowed under the regulation.

The commission solicits comment on additional flexibilities relating to rule content and implementation which have not been addressed in this or other concurrent rulemakings. These flexibilities may be available for both mobile and stationary sources. Additional flexibilities may also be achieved through innovative and/or emerging technology which may become available in the future. Additional sources of funds for incentive programs may become available to substitute for some of the measures considered here.

SECTION BY SECTION DISCUSSION

The new Division 9 is proposed regarding HGA construction equipment operating restrictions in order to provide an opportunity for comment on the complete control strategy.

The proposed new §114.482 establishes control requirements for construction equipment operating restrictions. The proposal restricts the operation of any non-road diesel construction equipment of 50 hp and above, between the hours of 6:00 a.m. and noon, during Daylight Savings Time, which begins on the first Sunday in April and ends on the last Sunday in October.

The proposed new §114.486 requires all persons subject to the provisions of §114.482 to maintain daily records of equipment operation in the affected counties.

The proposed new §114.487 establishes exemptions from the control requirements of §114.482 and the recordkeeping requirements of §114.486. These exemptions include diesel equipment used exclusively for situations involving emergency operations and diesel equipment while being used for mixing, transporting, pouring, or processing of wet concrete. The commission understands the definition of emergency equipment includes equipment which may have to be used to repair facilities or devices which have failed in order to prevent greater immediate environmental harm. Also, the proposed rules contain an exemption that allows operators that submit an emissions reduction plan by May 31, 2002, which is approved by the executive director and the EPA by May 31, 2003, to operate during the restricted hours.

The proposed new §114.489 specifies the counties which are subject to the new requirements and the dates and times these counties are subject to these requirements. The affected counties include all eight counties in the HGA ozone nonattainment area, which include Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller Counties. The compliance date for the HGA area is April 3, 2005.

FISCAL NOTE: COSTS TO STATE AND LOCAL GOVERNMENT

John Davis, Technical Specialist with Strategic Planning and Appropriations, has determined that for the first five-year period that the proposed rules are in effect, significant fiscal implications are anticipated for units of state and local government as a result of administration or enforcement of the proposed rules. The proposed rules would restrict the use of heavy-duty diesel construction equipment, rated at 50 hp and greater, from use between the hours of 6:00 a.m. and noon, during Daylight Savings Time, which begins on the first Sunday in April and ends the last Sunday in October. The restriction would apply to construction equipment in the eight-county HGA ozone nonattainment area of Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller Counties. The proposed rules would become effective April 3, 2005. Units of state and local government within the HGA ozone nonattainment area that have ongoing construction projects will be affected. Based on comments received from units of state and local government affected by the DFW rules, including the North Central Texas Council of Government (NCTCOG) and the Texas Department of Transportation (TxDOT), costs associated with delays and extended construction schedules may increase overall construction costs by 15% to 20%. State and local agencies engaged in road construction and repair are anticipated to bear the heaviest burden among state and local agencies. The proposed rules do not require additional control equipment or new emission control technologies to be applied to the affected diesel equipment.

The proposed rules would establish a limitation on the use of heavy-duty diesel construction equipment as an air pollution control strategy to delay the emission of NO x until later in the day, thus limiting ozone production. The commission is required to submit a SIP revision by the end of 2000 which will bring the HGA into attainment by 2007. The rules proposed for HGA in this notice are one element of the ozone attainment demonstration SIP for HGA. The purpose of the proposed rules is for the HGA nonattainment area to demonstrate attainment with the ozone NAAQS. The SIP sets forth a control strategy that provides part of the emission reductions necessary for attainment and maintenance of the ozone NAAQS.

As established in the DFW rules concerning restrictions on the operation of construction equipment, the existing rules contain exemptions from control and recordkeeping requirements. These exemptions include construction equipment used exclusively for emergency operations to protect public health and the environment, and for mixing, transporting, pouring, or processing wet concrete. Also, the existing rules contain an exemption that allows operators that submit a plan by May 31, 2002, which is approved by the executive director and the EPA by May 31, 2003, to operate during the restricted hours.

Units of state and local government within the HGA ozone nonattainment area that have ongoing construction projects may have significant fiscal implications. According to TxDOT, the TxDOT's Houston and Beaumont districts (which cover Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller Counties) spent over $464 million during calendar year 1999 for road and bridge construction projects in the HGA area. Based on the TxDOT expenditures, an estimated 15% to 20% cost increase due to delays and extended construction schedules would add $70 million to $93 million annually to TxDOT-related construction costs in the HGA area. Note, these figures only apply to TxDOT-related road and bridge construction costs. Because the proposed rules do not require additional control equipment or new technology, the commission does not anticipate significant economic impacts to affected agencies and businesses beyond the shift in work schedule and possible implications caused by potential construction delays attributable to the proposed rules. Delaying use of diesel construction equipment until after noon may require affected state and local agencies and associated businesses to adjust their work schedules and could cause extensions of construction timelines. The fiscal impact of potential delays would depend on the scope, magnitude, and time-critical nature of the construction projects.

PUBLIC BENEFIT AND COSTS

Mr. Davis also determined that for each year of the first five years the proposed rules are in effect, the public benefit anticipated from enforcement of and compliance with the proposed rules will be a potential reduction in the formation of ozone by delaying NO x emissions from construction equipment until later in the day when optimum conditions for the formation of ozone no longer exist, potentially improved air quality, and contribution toward demonstration of attainment with the ozone NAAQS.

The proposed rules would restrict the use of heavy-duty diesel construction equipment, rated at 50 hp and greater, from use between the hours of 6:00 a.m. and noon, during Daylight Savings Time, which begins on the first Sunday in April and ends the last Sunday in October. The restriction would apply to construction equipment in the eight-county HGA ozone nonattainment area. The proposed rules would become effective April 3, 2005.

Businesses within the HGA ozone nonattainment area that have ongoing construction projects may have significant fiscal implications in an amount that cannot be determined at this time; however, based on comments received from units of state and local government affected by the DFW rules, including the NCTCOG and TxDOT, costs associated with delays and extended construction schedules may increase overall construction costs by 15% to 20%. Because the proposed rules do not require additional control equipment or new technology, the commission does not anticipate significant economic impacts to affected agencies and businesses beyond the shift in work schedule and possible implications caused by potential construction delays attributable to the proposed rules. Delaying use of diesel construction equipment until after noon may require affected state and local agencies and businesses to adjust their work schedules and could cause extensions of construction timelines. The fiscal impact of potential delays would depend on the scope, magnitude, the slack time available in the schedule, and the time-critical nature of certain parts of the construction project.

As established in the DFW rules concerning restrictions on the operation of construction equipment, the existing rules contain exemptions from control and recordkeeping requirements. These exemptions include construction equipment used exclusively for emergency operations to protect public health and the environment, and for mixing, transporting, pouring, or processing wet concrete. Also, the existing rules contain an exemption that allows operators that submit a plan by May 31, 2002, which is approved by the executive director and EPA by May 31, 2003, to operate during the restricted hours.

SMALL BUSINESS AND MICRO-BUSINESS ASSESSMENT

Small and micro-businesses within the HGA ozone nonattainment area that have ongoing construction projects may have significant fiscal implications as a result of enforcement and administration of the proposed rules in an amount which cannot be determined.

The proposed rules would restrict the use of heavy-duty diesel construction equipment, rated at 50 hp and greater, from use between the hours of 6:00 a.m. and noon, during Daylight Savings Time, which begins on the first Sunday in April and ends the last Sunday in October. The restriction would apply to construction equipment in the eight-county HGA ozone nonattainment area. The proposed rules would become effective April 3, 2005.

Small and micro-businesses within the HGA ozone nonattainment area that have ongoing construction projects may have significant fiscal implications in an amount that cannot be determined at this time; however, based on comments received from units of state and local government affected by the DFW rules, including the NCTCOG and TxDOT, costs associated with delays and extended construction schedules may increase overall construction costs by 15% to 20%. Because the proposed rules do not require additional control equipment or new technology, the commission does not anticipate significant economic impacts to affected small and micro-businesses beyond the shift in work schedule and possible implications caused by potential construction delays attributable to the proposed rules. Delaying use of diesel construction equipment until after noon may require affected small and micro-businesses to adjust their work schedules and could cause extensions of construction timelines. The fiscal impact of potential delays would depend on the scope, magnitude, the slack time available in the schedule, and the time-critical nature of certain parts of the construction project.

As established in the DFW rule concerning restrictions on the operation of construction equipment, the existing rules contain exemptions from control and recordkeeping requirements. These exemptions include construction equipment used exclusively for emergency operations to protect public health and the environment, and for mixing, transporting, pouring, or processing wet concrete. Also, the existing rules contain an exemption that allows operators that submit an emissions reduction plan (plan) by May 31, 2002, which is approved by the executive director and the EPA by May 31, 2003, to operate during the restricted hours.

DRAFT REGULATORY IMPACT ANALYSIS DETERMINATION

The commission reviewed the proposed rulemaking in light of the regulatory analysis requirements of Texas Government Code, §2001.0225, and determined that the rulemaking is subject to §2001.0225 because it meets the definition of a "major environmental rule" as defined in that statute. "Major environmental rule" means a rule the specific intent of which is to protect the environment or reduce risks to human health from environmental exposure and that may adversely affect in a material way the economy, a sector of the economy, productivity, competition, jobs, the environment, or the public health and safety of the state or a sector of the state. The proposed rules are intended to protect the environment or reduce risks to human health from environmental exposure to ozone and, although we do not have definitive cost estimates at this time, construction delays could affect a sector of the economy in a material way. The proposed rules are intended to implement an operating-use restriction program requiring that heavy-duty diesel construction equipment be restricted from use between the hours of 6:00 a.m. and noon, during Daylight Savings Time, which begins on the first Sunday in April and ends the last Sunday in October. This program is part of the strategy to reduce the formation of ozone by delaying NO x emissions from construction equipment until later in the day when optimum conditions for the formation of ozone no longer exist. The program was developed for the HGA ozone nonattainment area to be able to demonstrate attainment with the ozone NAAQS. The proposed rules are one element of the HGA Post-1999 ROP/Attainment Demonstration SIP. Provisions of 42 USC, §7410, require states to adopt a SIP which provides for "implementation, maintenance, and enforcement" of the primary NAAQS in each air quality control region of the state. While §7410 does not require specific programs, methods, or reductions in order to meet the standard, state SIPs must include "enforceable emission limitations and other control measures, means or techniques (including economic incentives such as fees, marketable permits, and auctions of emissions rights), as well as schedules and timetables for compliance as may be necessary or appropriate to meet the applicable requirements of this chapter," (meaning Chapter 85, Air Pollution Prevention and Control). It is true that 42 USC does require some specific measures for SIP purposes, like the inspection and maintenance program, but those programs are the exception, not the rule, in the SIP structure of 42 USC. The provisions of 42 USC recognize that states are in the best position to determine what programs and controls are necessary or appropriate in order to meet the NAAQS. This flexibility allows states, affected industry, and the public, to collaborate on the best methods for attaining the NAAQS for the specific regions in the state. Even though 42 USC allows states to develop their own programs, this flexibility does not relieve a state from developing a program that meets the requirements of §7410. Thus, while specific measures are not generally required, the emission reductions are required. States are not free to ignore the requirements of §7410 and must develop programs to assure that the nonattainment areas of the state will be brought into attainment on schedule.

The requirement to provide a fiscal analysis of proposed regulations in the Texas Government Code was amended by Senate Bill 633 (SB 633) during the 75th Legislative Session, 1999. The intent of SB 633 was to require agencies to conduct a regulatory impact analysis (RIA) of extraordinary rules. These are identified in the statutory language as major environmental rules that will have a material adverse impact and will exceed a requirement of state law, federal law, or a delegated federal program, or are adopted solely under the general powers of the agency. With the understanding that this requirement would seldom apply, the commission provided a cost estimate for SB 633 that concluded "based on an assessment of rules adopted by the agency in the past, it is not anticipated that the bill will have significant fiscal implications for the agency due to its limited application." The commission also noted that the number of rules that would require assessment under the provisions of the bill was not large. This conclusion was based, in part, on the criteria set forth in the bill that exempted proposed rules from the full analysis unless the rule was a major environmental rule that exceeds a federal law. As previously discussed, 42 USC does not require specific programs, methods, or reductions in order to meet the NAAQS; thus, states must develop programs for each nonattainment area to ensure that area will meet the attainment deadlines. Because of the ongoing need to address nonattainment issues, the commission routinely proposes and adopts SIP rules. The legislature is presumed to understand this federal scheme. If each rule proposed for inclusion in the SIP was considered to be a major environmental rule that exceeds federal law, then every SIP rule would require the full RIA contemplated by SB 633. This conclusion is inconsistent with the conclusions reached by the commission in its cost estimate and by the Legislative Budget Board (LBB) in its fiscal notes. Since the legislature is presumed to understand the fiscal impacts of the bills it passes, and that presumption is based on information provided by state agencies and the LBB, the commission believes that the intent of SB 633 was only to require the full RIA for rules that are extraordinary in nature. While the SIP rules will have a broad impact, that impact is no greater than is necessary or appropriate to meet the requirements of the FCAA. For these reasons, rules proposed for inclusion in the SIP fall under the exception in Texas Government Code, §2001.0225(a), because they are required by federal law. The commission performed photochemical grid modeling which predicts that NO x emission reductions, such as those required by these rules, will result in reductions in ozone formation in the HGA ozone nonattainment area. This rulemaking does not exceed an express requirement of state law. This rulemaking is intended to obtain NO x emission reductions which will result in reductions in ozone formation in the HGA ozone nonattainment area and help bring HGA into compliance with the air quality standards established under federal law as NAAQS for ozone. The rulemaking does not exceed a standard set by federal law, exceed an express requirement of state law (unless specifically required by federal law), or exceed a requirement of a delegation agreement. The rulemaking was not developed solely under the general powers of the agency, but was specifically developed to meet the NAAQS established under federal law and authorized under Texas Clean Air Act (TCAA), §§382.011, 382.012, 382.017, 382.019, and 382.039.

The commission invites public comment on the draft regulatory impact analysis.

TAKINGS IMPACT ASSESSMENT

The commission prepared a takings impact assessment for these rules in accordance with Texas Government Code, §2007.043. The following is a summary of that assessment. The specific purpose of the rulemaking action is to establish a construction equipment operating restriction to delay NOx emissions that lead to high levels of ground-level ozone production. This rulemaking action will act as an air pollution control strategy to reduce NO x emissions necessary for the HGA ozone nonattainment area to be able to demonstrate attainment with the ozone NAAQS. The affected area consists of the eight counties included in the HGA ozone nonattainment area. Promulgation and enforcement of the rules will not burden private, real property as it only regulates mobile sources, and will not cause a takings to occur. Although the rules do not directly prevent a nuisance, prevent an immediate threat to life or property, or prevent a real and substantial threat to public health and safety, the rules partially fulfill a federal mandate under the 42 USC, §7410. Specifically, the emissions limitations and delays within these rules were developed in order to meet the ozone NAAQS set by the EPA under the 42 USC, §7409. States are primarily responsible for ensuring attainment and maintenance of the NAAQS, once the EPA has established them. Under 42 USC, §7410 and related provisions, states must submit, for EPA approval, SIPs that provide for the attainment and maintenance of NAAQS through control programs directed to sources of the pollutants involved. Therefore, the purpose of the rules is to implement a construction equipment operating restriction necessary for the HGA nonattainment area to meet the air quality standards established under federal law as NAAQS. Consequently, the exemption which also applies to these rules is that of an action reasonably taken to fulfill an obligation mandated by federal law. For the reasons stated, these proposed rules will not constitute a takings under Texas Government Code, Chapter 2007.

CONSISTENCY WITH THE COASTAL MANAGEMENT PROGRAM

The commission determined that the proposed rulemaking relates to an action or actions subject to the Texas Coastal Management Program (CMP) in accordance with the Coastal Coordination Act of 1991, as amended (Texas Natural Resources Code, §§33.201 et seq.), and the commission rules in 30 TAC Chapter 281, Subchapter B, concerning Consistency with the CMP. As required by 31 TAC §505.11(b)(2) and 30 TAC §281.45(a)(3), relating to actions and rules subject to the CMP, commission rules governing air pollutant emissions must be consistent with the applicable goals and policies of the CMP. The commission reviewed this action for consistency with the CMP goals and policies in accordance with the rules of the Coastal Coordination Council, and determined that the action is consistent with the applicable CMP goals and policies. The CMP goal applicable to this rulemaking action is the goal to protect, preserve, and enhance the diversity, quality, quantity, functions, and values of coastal natural resource areas (31 TAC §501.12(1)). No new sources of air contaminants will be authorized and NO x air emissions will be reduced as a result of these rules. The CMP policy applicable to this rulemaking action is the policy that commission rules comply with regulations in 40 Code of Federal Regulations (CFR), to protect and enhance air quality in the coastal area (31 TAC §501.14(q)). This rulemaking action complies with 40 CFR 50, National Primary and Secondary Ambient Air Quality Standards, and 40 CFR 51, Requirements for Preparation, Adoption, and Submittal Of Implementation Plans. Therefore, in compliance with 31 TAC §505.22(e), this rulemaking action is consistent with CMP goals and policies.

Interested persons may submit comments on the consistency of the proposed rules with the CMP during the public comment period.

ANNOUNCEMENT OF HEARINGS

The commission will hold public hearings on this proposal at the following times and locations: September 18, 2000, 10:00 a.m., Lone Star Convention Center, 9055 Airport Road (FM 1484), Conroe; September 18, 2000, 7:00 p.m., Lake Jackson Civic Center, 333 Highway 332 East, Lake Jackson; September 19, 2000, 10:00 a.m. and 7:00 p.m., George Brown Convention Center, 1001 Avenida de Las Americas, Houston; September 20, 2000, 9:00 a.m., VFW Hall, 6202 George Bush Drive, Katy; September 20, 2000, 6:00 p.m., East Harris County Community Center, 7340 Spencer, Pasadena; September 21, 2000, 10:00 a.m., Southeast Texas Regional Airport Media Room, 6000 Airline Drive, Beaumont; September 21, 2000, 2:00 p.m., Amarillo City Commission Chambers, City Hall, 509 East 7th Avenue, Amarillo; September 21, 2000, 6:00 p.m., Charles T. Doyle Convention Center, 21st Street at Phoenix Lane, Texas City; September 22, 2000, 10:00 a.m., Dayton High School, 2nd Floor Lecture Room, 3200 North Cleveland Street, Dayton; September 22, 2000, 11:00 a.m., El Paso City Council Chambers, 2 Civic Center Plaza, 2nd Floor, El Paso; September 22, 2000, 2:00 p.m., North Central Texas Council of Governments, 2nd Floor Board Room, 616 Six Flags Drive, Suite 200, Arlington; and September 25, 2000, 10:00 a.m., Texas Natural Resource Conservation Commission, 12100 North I-35, Building E, Room 201S, Austin. The hearings are structured for the receipt of oral or written comments by interested persons. Registration will begin one hour prior to each hearing. Individuals may present oral statements when called upon in order of registration. A four-minute time limit will be established at each hearing to assure that enough time is allowed for every interested person to speak. Open discussion will not occur during each hearing; however, agency staff members will be available to discuss the proposal one hour before each hearing, and will answer questions before and after each hearing.

Persons with disabilities who have special communication or other accommodation needs, who are planning to attend a hearing, should contact the Office of Environmental Policy, Analysis, and Assessment at (512) 239-4900. Requests should be made as far in advance as possible.

SUBMITTAL OF COMMENTS

Written comments may be submitted to Heather Evans, Office of Environmental Policy, Analysis, and Assessment, MC 206, P.O. Box 13087, faxed to (512) 239-4808, or emailed to siprules@tnrcc.state.tx.us . All comments should reference Rule Log Number 2000-011B-114-A1. Comments must be received by 5:00 p.m., September 25, 2000. For further information, please contact Gayla McCarty at (512) 239-4631 or Alan Henderson at (512) 239-1510.

STATUTORY AUTHORITY

The new sections are proposed under Texas Water Code (TWC), §5.103, which authorizes the commission to adopt rules necessary to carry out its powers and duties under the TWC, and under Texas Health and Safety Code, TCAA, §382.017, which provides the commission the authority to adopt rules consistent with the policy and purposes of the TCAA. The new sections are also proposed under TCAA, §382.011, which authorizes the commission to control the quality of the state's air; §382.012, which authorizes the commission to prepare and develop a general, comprehensive plan for the control of the state's air; §382.019, which authorizes the commission to adopt rules to control and reduce emissions from engines used to propel land vehicles; and §382.039, which authorizes the commission to develop and implement transportation programs and other measures necessary to demonstrate attainment and protect the public from exposure to hazardous air contaminants from motor vehicles.

The proposed new sections implement TCAA, §382.002, relating to Policy and Purpose; §382.011, relating to General Powers and Duties; §382.012, relating to State Air Control Plan; §382.019, relating to Methods Used to Control and Reduce Emissions from Land Vehicles; and §382.039, relating to Attainment Program.

§114.482.Control Requirements.

No person shall start or operate any non-road diesel construction equipment, of 50 horsepower and above, between the hours of 6:00 a.m. and noon, during Daylight Savings Time, which begins on the first Sunday in April and ends on the last Sunday in October, in the counties listed in §114.489 of this title (relating to Affected Counties and Compliance Dates.)

§114.486.Recordkeeping Requirements.

(a)

Any person that operates construction equipment described in §114.482 of this title (relating to Control Requirements) in those counties listed in §114.489 of this title (relating to Affected Counties and Compliance Dates) is subject to requirements of this section.

(b)

Such person described in subsection (a) of this section shall provide to the executive director, or other air pollution program with jurisdiction, any records required to be maintained in accordance with this section within five days of a written request from the executive director, or other air pollution program with jurisdiction.

(c)

Such person described in subsection (a) of this section shall maintain daily operating records on the job site. These records must be maintained for a minimum of two years. The records at a minimum must contain:

(1)

date(s) of operation;

(2)

start and end times of daily operation;

(3)

types of equipment being used; and

(4)

name(s) of the equipment operator(s).

§114.487.Exemptions.

(a)

The following uses of construction equipment are exempt from §114.482 and §114.486 of this title (relating to Control Requirements; and Recordkeeping Requirements) in the counties listed in §114.489 of this title (relating to Affected Counties and Compliance Dates):

(1)

equipment used exclusively for emergency operations to protect public health and safety or the environment; and

(2)

equipment used for mixing, transporting, pouring, or processing of wet concrete provided such equipment is actually processing wet concrete.

(b)

Operators that submit an emissions reduction plan by May 31, 2002 (that is approved by the executive director and the EPA by May 31, 2003) will be exempt upon implementation of the rule in 2005, and will be permitted to operate during the restricted hours. In order to be approved, the plan must demonstrate reductions of oxides of nitrogen equivalent to those required by both §114.472 of this title (relating to Control Requirements) and §114.482 of this title, and must contain adequate enforcement provisions.

§114.489.Affected Counties and Compliance Dates.

Effective April 3, 2005, affected persons in the following counties shall be in compliance with §§114.482, 114.486, and 114.487 of this title (relating to Control Requirements; Recordkeeping Requirements; and Exemptions). These include Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller Counties.

This agency hereby certifies that the proposal has been reviewed by legal counsel and found to be within the agency's legal authority to adopt.

Filed with the Office of the Secretary of State, on August 11, 2000.

TRD-200005616

Margaret Hoffman

Director, Environmental Law Division

Texas Natural Resource Conservation Commission

Earliest possible date of adoption: September 24, 2000

For further information, please call: (512) 239-0348


Subchapter J. OPERATIONAL CONTROLS FOR MOTOR VEHICLES

1. MOTOR VEHICLE IDLING LIMITATIONS

30 TAC §§114.500, 114.502, 114.507, 114.509

The Texas Natural Resource Conservation Commission (commission) proposes new §114.500, Definitions; §114.502, Control Requirements for Motor Vehicle Idling; §114.507, Exemptions; and §114.509, Affected Counties and Compliance Dates. The commission proposes these new sections to Chapter 114, Control of Air Pollution From Motor Vehicles; new Subchapter J, Operational Controls for Motor Vehicles; new Division 1, Motor Vehicle Idling Restrictions; and corresponding revisions to the state implementation plan (SIP) in order to control ground-level ozone in the Houston/Galveston (HGA) ozone nonattainment area.

BACKGROUND AND SUMMARY OF THE FACTUAL BASIS FOR THE PROPOSED RULES

The HGA ozone nonattainment area is classified as Severe-17 under the Federal Clean Air Act (FCAA) Amendments of 1990 (42 United States Code (USC), §§7401 et seq.), and therefore is required to attain the one-hour ozone standard of 0.12 parts per million (ppm) by November 15, 2007. The HGA area, defined by Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller Counties, has been working to develop a demonstration of attainment in accordance with 42 USC, §7410. On January 4, 1995, the state submitted the first of its Post- 1996 SIP revisions for HGA.

The January 1995 SIP consisted of urban airshed model (UAM) modeling for 1988 and 1990 base-case episodes, adopted rules to achieve a 9% rate-of-progress (ROP) reduction in volatile organic compounds (VOC), and a commitment schedule for the remaining ROP and attainment demonstration elements. At the same time, but in a separate action, the State of Texas filed for the temporary nitrogen oxide (NO x ) waiver allowed by 42 USC, §7511a(f). The January 1995 SIP and the NO x waiver were based on early base-case episodes which marginally exhibited model performance in accordance with the United States Environmental Protection Agency (EPA) modeling performance standards, but which had a limited data set as inputs to the model. In 1993 and 1994, the commission was engaged in an intensive data-gathering exercise known as the COAST study. The state believed that the enhanced emissions inventory, expanded ambient air quality and meteorological monitoring, and other elements would provide a more robust data set for modeling and other analysis, which would lead to modeling results that the commission could use to better understand the nature of the ozone air quality problem in the HGA area.

Around the same time as the 1995 submittal, EPA policy regarding SIP elements and timelines went through changes. Two national programs in particular resulted in changing deadlines and requirements. The first of these programs was the Ozone Transport Assessment Group. This group grew out of a March 2, 1995 memo from Mary Nichols, former EPA Assistant Administrator for Air and Radiation, that allowed states to postpone completion of their attainment demonstrations until an assessment of the role of transported ozone and precursors had been completed for the eastern half of the nation, including the eastern portion of Texas. Texas participated in this study, and it has been concluded that Texas does not significantly contribute to ozone exceedances in the Northeastern United States. The other major national initiative that has impacted the SIP planning process is the revisions to the national ambient air quality standard (NAAQS) for ozone. The EPA promulgated a final rule on July 18, 1997 changing the ozone standard to an eight-hour standard of 0.08 ppm. In November 1996, concurrent with the proposal of the standards, the EPA proposed an interim implementation plan (IIP) that it believed would help areas like HGA transition from the old to the new standard. In an attempt to avoid a significant delay in planning activities, Texas began to follow this guidance, and readjusted its modeling and SIP development timelines accordingly. When the new standard was published, the EPA decided not to publish the IIP, and instead stated that, for areas currently exceeding the one-hour ozone standard, that standard would continue to apply until it is attained. The FCAA requires that HGA attain the standard by November 15, 2007.

The EPA issued revised draft guidance for areas such as HGA that do not attain the one-hour ozone standard. The commission adopted on May 6, 1998 and submitted to the EPA on May 19, 1998 a revision to the HGA SIP which contained the following elements in response to EPA's guidance: UAM modeling based on emissions projected from a 1993 baseline out to the 2007 attainment date; an estimate of the level of VOC and NO x reductions necessary to achieve the one-hour ozone standard by 2007; a list of control strategies that the state could implement to attain the one-hour ozone standard; a schedule for completing the other required elements of the attainment demonstration; a revision to the Post-1996 9% ROP SIP that remedied a deficiency that the EPA believed made the previous version of that SIP unapprovable; and evidence that all measures and regulations required by Subpart 2 of Title I of the FCAA to control ozone and its precursors have been adopted and implemented, or are on an expeditious schedule to be adopted and implemented.

In November 1998, the SIP revision submitted to the EPA in May 1998 became complete by operation of law. However, the EPA stated that it could not approve the SIP until specific control strategies were modeled in the attainment demonstration. The EPA specified a submittal date of November 15, 1999 for this modeling. In a letter to the EPA dated January 5, 1999, the state committed to model two strategies showing attainment.

As the HGA modeling protocol evolved, the state eventually selected and modeled seven basic modeling scenarios. As part of this process, a group of HGA stakeholders worked closely with commission staff to identify local control strategies for the modeling. Some of the scenarios for which the stakeholders requested evaluation included options such as California-type fuel and vehicle programs as well as an acceleration simulation mode equivalent motor vehicle inspection and maintenance program. Other scenarios incorporated the estimated reductions in emissions that were expected to be achieved throughout the modeling domain as a result of the implementation of several voluntary and mandatory statewide programs adopted or planned independently of the SIP. It should be made clear that the commission did not propose that any of these strategies be included in the ultimate control strategy submitted to the EPA in 2000. The need for and effectiveness of any controls which may be implemented outside the HGA eight-county area will be evaluated on a county-by-county basis.

The SIP revision was adopted by the commission on October 27, 1999, submitted to the EPA by November 15, 1999, and contained the following elements: photochemical modeling of potential specific control strategies for attainment of the one-hour ozone standard in the HGA area by the attainment date of November 15, 2007; an analysis of seven specific modeling scenarios reflecting various combinations of federal, state, and local controls in HGA (additional scenarios H1 and H2 build upon Scenario VIf); identification of the level of reductions of VOC and NO x necessary to attain the one-hour ozone standard by 2007; a 2007 mobile source budget for transportation conformity; identification of specific source categories which, if controlled, could result in sufficient VOC and/or NO x reductions to attain the standard; a schedule committing to submit by April 2000 an enforceable commitment to conduct a mid-course review; and a schedule committing to submit modeling and adopted rules in support of the attainment demonstration by December 2000.

The April 19, 2000 SIP revision for HGA contained the following enforceable commitments by the state: to quantify the shortfall of NO x reductions needed for attainment; to list and quantify potential control measures to meet the shortfall of NO x reductions needed for attainment; to adopt the majority of the necessary rules for the HGA attainment demonstration by December 31, 2000, and to adopt the rest of the shortfall rules as expeditiously as practical, but no later than July 31, 2001; to submit a Post-99 ROP plan by December 31, 2000; to perform a mid- course review by May 1, 2004; and to perform modeling of mobile source emissions using the EPA mobile source emissions model (MOBILE6), to revise the on-road mobile source budget as needed, and to submit the revised budget within 24 months of the model's release. In addition, if a conformity analysis is to be performed between 12 months and 24 months after the MOBILE6 release, the state will revise the motor vehicle emissions budget (MVEB) so that the conformity analysis and the SIP MVEB are calculated on the same basis.

In order for the state to have an approvable attainment demonstration, the EPA has indicated that the state must adopt those strategies modeled in the November submittal and then adopt sufficient controls to close the remaining gap in NO x emissions. The modeling included in this proposal indicates a gap of an additional 77.98 tons per day (tpd) of NO x reductions is necessary for an approvable attainment demonstration. The commission estimates that this measure will achieve a minimum of 0.92 tpd of NO x equivalent reductions and is therefore a necessary measure to consider for closing the gap and successfully demonstrating attainment.

The emission reduction requirements included as part of this SIP revision represent substantial, intensive efforts on the part of stakeholder coalitions in the HGA area. These coalitions, involving local governmental entities, elected officials, environmental groups, industry, consultants, and the public, as well as the commission and the EPA, have worked diligently to identify and quantify potential control strategy measures for the HGA attainment demonstration. Local officials from the HGA area have formally submitted a resolution to the commission, requesting the inclusion of many specific emission reduction strategies.

The current SIP revision contains rules, enforceable commitments, and photochemical modeling analyses in support of the HGA ozone attainment demonstration. In addition, this SIP contains post- 1999 ROP plans for the milestone years 2002 and 2005, and for the attainment year 2007. The SIP also contains enforceable commitments to implement further measures, if needed, in support of the HGA attainment demonstration, as well as a commitment to perform and submit a mid-course review.

The HGA ozone nonattainment area will need to ultimately reduce NOx more than 750 tpd to reach attainment with the one-hour standard. In addition, a VOC reduction of about 25% will have to be achieved. Adoption of the proposed rules limiting idling of heavy-duty motor vehicles can contribute to attainment of the one-hour ozone standard in the HGA area. The proposed rules limiting idling of heavy-duty motor vehicles also may contribute to a successful demonstration of transportation conformity in the HGA area.

These proposed rules are one element of the control strategy for the HGA Attainment Demonstration SIP. The purpose of these proposed rules is to establish heavy-duty motor vehicle idling restrictions as one element of an air pollution control strategy in the eight counties of the HGA ozone nonattainment area to reduce NO x necessary for the counties to be able to demonstrate attainment with the ozone NAAQS.

These proposed rules will implement idling limits for gasoline and diesel powered engines in heavy-duty motor vehicles in the HGA area. The proposed idling limits will lower NO x emissions and other pollutants from fuel combustion. Because NO x is a precursor to ground-level ozone formation, reduced emissions of NOx will result in ground-level ozone reductions. To comply with the motor vehicle idling regulations, no person in the affected counties may cause, suffer, allow, or permit the primary propulsion engine of a heavy-duty motor vehicle to idle for more than five consecutive minutes when the vehicle is not in motion during the time from April 1 through October 31.

The commission developed an ozone control strategy which limits the time allowed for the engines of heavy-duty motor vehicles to idle when not in motion. Currently, there are no federal regulations governing idle time for heavy-duty motor vehicles. Therefore, the state has the authority to control motor vehicle idling and the proposed idling requirements developed by the commission for this NO x emission reduction strategy will result in restrictions on the time allowed for motor vehicle idling.

Modeling assessing the benefits of this NO x emission reduction strategy demonstrated that emission reductions could be achieved by limiting the idling time of heavy-duty motor vehicles. By the year 2007, the idling limits will reduce NO x emissions in the affected area by 0.92 tpd. The commission estimates the daily cost savings benefit of this strategy to be approximately $126,150 per ton of NO x reduced. This figure was calculated from the estimated NO x reductions from this strategy of 0.92 tpd, the estimated reduction in fuel consumption per hour, and the current price per gallon of fuel sold in the affected area.

The commission solicits comment on additional flexibilities relating to rule content and implementation which have not been addressed in this or other concurrent rulemakings. These flexibilities may be available for both mobile and stationary sources. Additional flexibilities may also be achieved through innovative and/or emerging technology which may become available in the future. Additional sources of funds for incentive programs may become available to substitute for some of the measures considered here.

SECTION BY SECTION DISCUSSION

The proposed new §114.500 contains the definitions of idle, motor vehicle, and primary propulsion engine.

The proposed new §114.502 establishes the control requirements that limit motor vehicle idling to five consecutive minutes when the vehicle is not in motion during the time from April 1 through October 31.

The proposed new §114.507 provides exemptions to the control requirements of §114.502 for motor vehicles that have a gross vehicle weight rating of 14,000 pounds or less, that are forced to remain motionless because of traffic conditions over which the operator has no control; are being used as an emergency or law enforcement motor vehicle; or when the engine of a motor vehicle is providing power takeoff for refrigeration, lift gate pumps or other auxiliary uses; or when the engine of a motor vehicle is being operated for maintenance or diagnostic purposes; or when the engine of a motor vehicle is being operated solely to defrost a windshield.

The proposed new §114.509 establishes a compliance date of April 1, 2001, and identifies the eight HGA counties covered by the motor vehicle idle control requirements of §114.502.

FISCAL NOTE: COSTS TO STATE AND LOCAL GOVERNMENT

John Davis, Technical Specialist with Strategic Planning and Appropriations, determined that for the first five-year period the proposed rules are in effect there will be no significant fiscal implications for any single unit of state and local government as a result of administration or enforcement of these proposed rules.

The proposed rules will implement idling limits for state and local government owned and operated gasoline and diesel powered engines in heavy-duty motor vehicles with a gross vehicle weight rating (GVWR) greater than 14,000 pounds in the HGA ozone nonattainment area. The proposed rules would affect approximately 3,200 state and local government and 92,718 privately-owned or operated gas and diesel powered heavy-duty vehicles registered in the HGA ozone nonattainment area. To comply with the motor vehicle idling regulations, the primary propulsion engine for any state and local government owned and operated heavy-duty vehicle operating in the HGA nonattainment area must not be allowed to idle for more than five consecutive minutes when the vehicle is not in motion during the period of April 1 through October 31 of each calendar year.

The proposed rules will implement idling limits for gasoline and diesel powered engines in heavy-duty motor vehicles with a GVWR greater than 14,000 pounds in the HGA ozone nonattainment area. Exemptions to these proposed rules include the following: vehicles with a GVWR of 14,000 pounds or less; vehicles that are forced to remain motionless because of traffic conditions over which the operator has no control; vehicles that are being used as an emergency or law enforcement motor vehicle; when the primary propulsion engine is providing power takeoff for refrigeration, lift gate pumps or other auxiliary uses; when the primary propulsion engine is being operated for maintenance or diagnostic purposes; or when the primary propulsion engine is being operated solely to defrost a windshield.

There will be no significant fiscal impacts to units of state and local government as a result of administration or enforcement of the proposed rules; however, adhering to the proposed idling restrictions could provide cost savings by reducing fuel consumption. Heavy-duty diesel and gasoline powered vehicles can consume up to one gallon of fuel per hour while idling. The Eastern Research Group (ERG) conducted a study titled Determination of NO x Benefits from Proposed Idle Shut-Off Rule , July 2000, to determine the benefits of idle restrictions. Assuming two five-minute idle periods per day, approximately 88 hours of idle time could be saved per diesel and gasoline vehicle per year, resulting in a cost savings of approximately $132 per vehicle per year. There are approximately 3,200 state and local government gas and diesel powered heavy-duty vehicles registered in the HGA ozone nonattainment area. The commission anticipates that the total annual savings to units of state and local government in the HGA ozone nonattainment area will be approximately $422,400.

PUBLIC BENEFIT AND COSTS

Mr. Davis also determined that for the first five years the proposed rules are in effect, the public benefit anticipated from enforcement of and compliance with the proposed rules will be the potential reduction of NO x , which contributes to the formation of ground-level ozone, potentially improved air quality, and contribution toward demonstration of attainment with the NAAQS for the HGA ozone nonattainment area. There are no significant fiscal implications as a result of administration or enforcement of the proposed rules for any single person or business which owns and operates heavy-duty gasoline and diesel vehicles within the HGA ozone nonattainment area.

The proposed rules will implement idling limits for privately-owned and operated gasoline and diesel powered engines in heavy-duty motor vehicles with a gross vehicle weight rating greater than 14,000 pounds in the HGA nonattainment area. To comply with the motor vehicle idling regulations, the primary propulsion engine for any person or business-owned and operated heavy-duty vehicle operating in the HGA nonattainment area must not be allowed to idle for more than five consecutive minutes when the vehicle is not in motion during the period of April 1 through October 31 of each calendar year. Exemptions to this rule affecting persons and businesses are the same as those described in the Cost to State and Local Government section of this fiscal note.

There will be no significant fiscal impacts to any person or business as a result of administration or enforcement of the proposed rules; however, adhering to the proposed idling restrictions could provide cost savings by reducing fuel consumption. Heavy-duty diesel and gasoline powered vehicles can consume up to one gallon of fuel per hour while idling. The ERG conducted a study titled Determination of NO x Benefits from Proposed Idle Shut-Off Rule , in July 2000 to determine the benefits of idle restrictions. Assuming two five-minute idle periods per day, approximately 88 hours of idle time could be saved per vehicle per year, resulting in a cost savings of approximately $132 per vehicle per year. There are approximately 92,718 privately-owned and operated gas and diesel powered heavy-duty vehicles registered in the HGA ozone nonattainment area. It is anticipated that the total annual savings to persons and businesses in the HGA ozone nonattainment area will be approximately $12 million.

SMALL AND MICRO-BUSINESS ASSESSMENT

No significant adverse effects are anticipated to small or micro-businesses as a result of implementing the proposed rules. The proposed rules will implement idling limits for small and micro- business owned and operated gasoline and diesel powered engines in heavy-duty motor vehicles with a gross vehicle weight rating greater than 14,000 pounds in the HGA nonattainment area. To comply with the motor vehicle idling regulations, the primary propulsion engine for any persons or business- owned and operated heavy-duty vehicle operating in the HGA nonattainment area must not be allowed to idle for more than five consecutive minutes when the vehicle is not in motion during the period of April 1 through October 31 of each calendar year.

There will be no significant fiscal impacts to any small or micro-business as a result of administration or enforcement of the proposed rules; however, adhering to the proposed idling restrictions could provide cost savings by reducing fuel consumption. Heavy-duty diesel and gasoline powered vehicles can consume up to one gallon of fuel per hour while idling. The ERG conducted a study titled Determination of NO x Benefits from Proposed Idle Shut-Off Rule , in July 2000 to determine the benefits of idle restrictions. Assuming two five-minute idle periods per day, approximately 88 hours of idle time could be saved per vehicle per year, resulting in a cost savings of approximately $132 per vehicle per year. Of the 92,718 privately-owned and operated gas and diesel powered heavy-duty vehicles registered in the HGA ozone nonattainment area, some of these vehicles are owned by small or micro-businesses. The total savings to small and micro-businesses would depend on the number of heavy-duty vehicles owned and operated.

DRAFT REGULATORY IMPACT ANALYSIS DETERMINATION

The commission reviewed the proposed rulemaking in light of the regulatory analysis requirements of Texas Government Code, §2001.0225, and determined that the proposed rulemaking is not subject to §2001.0225 because it does not meet the definition of a "major environmental rule" as defined in that statute. "Major environmental rule" means a rule of which the specific intent is to protect the environment or reduce risks to human health from environmental exposure and that may adversely affect in a material way the economy, a sector of the economy, productivity, competition, jobs, the environment, or the public health and safety of the state or a sector of the state. The proposed new sections to Chapter 114 are intended to protect the environment or reduce risks to human health from environmental exposure to ozone but the proposed control requirements within this proposal should not adversely affect in any material way the economy, a sector of the economy, productivity, competition, jobs, the environment, or the public health and safety of the state or a sector of the state. The proposed rules are intended to implement heavy-duty motor vehicle idle limitations as part of the strategy to reduce emissions of NOx necessary for the counties included in the HGA ozone nonattainment area to be able to demonstrate attainment with the ozone NAAQS. The proposed rules are part of the commission response to the request and one element of the proposed Attainment Demonstration SIP. Provisions of 42 USC, §7410, require states to adopt a SIP which provides for "implementation, maintenance, and enforcement" of the primary NAAQS in each air quality control region of the state. While §7410 does not require specific programs, methods, or reductions in order to meet the standard, state SIPs must include "enforceable emission limitations and other control measures, means or techniques (including economic incentives such as fees, marketable permits, and auctions of emissions rights), as well as schedules and timetables for compliance as may be necessary or appropriate to meet the applicable requirements of this chapter," (meaning Chapter 85, Air Pollution Prevention and Control). It is true that 42 USC does require some specific measures for SIP purposes, like the inspection and maintenance program, but those programs are the exception, not the rule, in the SIP structure of 42 USC. The provisions of 42 USC recognize that states are in the best position to determine what programs and controls are necessary or appropriate in order to meet the NAAQS. This flexibility allows states, affected industry, and the public, to collaborate on the best methods for attaining the NAAQS for the specific regions in the state. Even though 42 USC allows states to develop their own programs, this flexibility does not relieve a state from developing a program that meets the requirements of §7410. Thus, while specific measures are not generally required, the emission reductions are required. States are not free to ignore the requirements of §7410 and must develop programs to assure that the nonattainment areas of the state will be brought into attainment on schedule.

The requirement to provide a fiscal analysis of proposed regulations in the Texas Government Code was amended by Senate Bill 633 (SB 633) during the 75th Legislative Session, 1999. The intent of SB 633 was to require agencies to conduct a regulatory impact analysis (RIA) of extraordinary rules. These are identified in the statutory language as major environmental rules that will have a material adverse impact and will exceed a requirement of state law, federal law, or a delegated federal program, or are adopted solely under the general powers of the agency. With the understanding that this requirement would seldom apply, the commission provided a cost estimate for SB 633 that concluded "based on an assessment of rules adopted by the agency in the past, it is not anticipated that the bill will have significant fiscal implications for the agency due to its limited application." The commission also noted that the number of rules that would require assessment under the provisions of the bill was not large. This conclusion was based, in part, on the criteria set forth in the bill that exempted proposed rules from the full analysis unless the rule was a major environmental rule that exceeds a federal law. As previously discussed, 42 USC does not require specific programs, methods, or reductions in order to meet the NAAQS; thus, states must develop programs for each nonattainment area to ensure that area will meet the attainment deadlines. Because of the ongoing need to address nonattainment issues, the commission routinely proposes and adopts SIP rules. The legislature is presumed to understand this federal scheme. If each rule proposed for inclusion in the SIP was considered to be a major environmental rule that exceeds federal law, then every SIP rule would require the full RIA contemplated by SB 633. This conclusion is inconsistent with the conclusions reached by the commission in its cost estimate and by the Legislative Budget Board (LBB) in its fiscal notes. Since the legislature is presumed to understand the fiscal impacts of the bills it passes, and that presumption is based on information provided by state agencies and the LBB, the commission believes that the intent of SB 633 was only to require the full RIA for rules that are extraordinary in nature. While the SIP rules will have a broad impact, that impact is no greater than is necessary or appropriate to meet the requirements of the FCAA. For these reasons, rules proposed for inclusion in the SIP fall under the exception in Texas Government Code, §2001.0225(a), because they are required by federal law.

Specifically, the motor vehicle idle requirements within these proposed rules were developed in order to meet the ozone NAAQS set by the EPA under 42 USC, §7409, and therefore meet a federal requirement. States are primarily responsible for ensuring attainment and maintenance of NAAQS once the EPA has established those standards. Under 42 USC, §7410 and related provisions, states must submit, for EPA approval, SIPs that provide for the attainment and maintenance of NAAQS through a control program directed to sources of the pollutants involved. These proposed rules are not an express requirement of state law, but were developed specifically in order to meet the air quality standards established under federal law as NAAQS. These proposed rules are intended to help bring ozone nonattainment areas into compliance and to help keep attainment and near nonattainment areas from reaching nonattainment. The proposed rules do not exceed a standard set by federal law, exceed an express requirement of state law unless specifically required by federal law, nor exceed a requirement of a delegation agreement. The proposed rules were not developed solely under the general powers of the agency, but were specifically developed to meet the air quality standards established under federal law as NAAQS.

The commission invites public comment on the draft regulatory impact analysis.

TAKINGS IMPACT ASSESSMENT

The commission prepared a takings impact assessment for these proposed rules in accordance with Texas Government Code, §2007.043. The following is a summary of that assessment. The specific purpose of the proposed rulemaking is to establish motor vehicle idle limits which will act as an air pollution control strategy to reduce NO x emissions necessary for the eight- county HGA ozone nonattainment area to be able to demonstrate attainment with the ozone NAAQS. Promulgation and enforcement of the proposed rules should not burden private, real property because this proposed rulemaking action should not result in any increased costs. Although the proposed rules do not directly prevent a nuisance or prevent an immediate threat to life or property, they do prevent a real and substantial threat to public health and safety, and partially fulfill a federal mandate under 42 USC, §7410. Specifically, the emission limitations and control requirements within this proposal have been developed in order to meet the ozone NAAQS set by the EPA under 42 USC, §7409. States are primarily responsible for ensuring attainment and maintenance of the NAAQS once the EPA has established them. Under 42 USC, §7410 and related provisions, states must submit, for EPA approval, SIPs that provide for the attainment and maintenance of NAAQS through control programs directed to sources of the pollutants involved. Therefore, the purpose of the proposed rules is to implement motor vehicle idle limits which are necessary for the HGA ozone nonattainment areas to meet the air quality standards established under federal law as NAAQS. Consequently, the exemption which applies to these proposed rules is that of an action reasonably taken to fulfill an obligation mandated by federal law; therefore, these proposed rules do not constitute a takings under the Texas Government Code, Chapter 2007.

CONSISTENCY WITH THE COASTAL MANAGEMENT PROGRAM

The commission determined that the proposed rulemaking relates to an action or actions subject to the Texas Coastal Management Program (CMP) in accordance with the Coastal Coordination Act of 1991, as amended (Texas Natural Resources Code, §§33.201 et seq.), and the commission rules in 30 TAC Chapter 281, Subchapter B, concerning Consistency with the CMP. As required by 31 TAC §505.11(b)(2) and 30 TAC §281.45(a)(3), relating to actions and rules subject to the CMP, commission rules governing air pollutant emissions must be consistent with the applicable goals and policies of the CMP. The commission reviewed this action for consistency with the CMP goals and policies in accordance with the rules of the Coastal Coordination Council, and determined that the action is consistent with the applicable CMP goals and policies. The CMP goal applicable to this rulemaking action is to protect, preserve, and enhance the diversity, quality, quantity, functions, and values of coastal natural resource areas (31 TAC §501.12(1)). No new sources of air contaminants will be authorized and NO x air emissions will be reduced as a result of these rules. The CMP policy applicable to this rulemaking action is the policy that commission rules comply with regulations in 40 Code of Federal Regulations (CFR), to protect and enhance air quality in the coastal area (31 TAC §501.14(q)). This rulemaking action complies with 40 CFR 50, National Primary and Secondary Ambient Air Quality Standards, and 40 CFR 51, Requirements for Preparation, Adoption, and Submittal Of Implementation Plans. Therefore, in compliance with 31 TAC §505.22(e), this rulemaking action is consistent with CMP goals and policies.

Interested persons may submit comments on the consistency of the proposed rules with the CMP during the public comment period.

ANNOUNCEMENT OF HEARINGS

The commission will hold public hearings on this proposal at the following times and locations: September 18, 2000, 10:00 a.m., Lone Star Convention Center, 9055 Airport Road (FM 1484), Conroe; September 18, 2000, 7:00 p.m., Lake Jackson Civic Center, 333 Highway 332 East, Lake Jackson; September 19, 2000, 10:00 a.m. and 7:00 p.m., George Brown Convention Center, 1001 Avenida de Las Americas, Houston; September 20, 2000, 9:00 a.m., VFW Hall, 6202 George Bush Drive, Katy; September 20, 2000, 6:00 p.m., East Harris County Community Center, 7340 Spencer, Pasadena; September 21, 2000, 10:00 a.m., Southeast Texas Regional Airport Media Room, 6000 Airline Drive, Beaumont; September 21, 2000, 2:00 p.m., Amarillo City Commission Chambers, City Hall, 509 East 7th Avenue, Amarillo; September 21, 2000, 6:00 p.m., Charles T. Doyle Convention Center, 21st Street at Phoenix Lane, Texas City; September 22, 2000, 10:00 a.m., Dayton High School, 2nd Floor Lecture Room, 3200 North Cleveland Street, Dayton; September 22, 2000, 11:00 a.m., El Paso City Council Chambers, 2 Civic Center Plaza, 2nd Floor, El Paso; September 22, 2000, 2:00 p.m., North Central Texas Council of Governments, 2nd Floor Board Room, 616 Six Flags Drive, Suite 200, Arlington; and September 25, 2000, 10:00 a.m., TNRCC, 12100 North I-35, Building E, Room 201S, Austin. The hearings are structured for the receipt of oral or written comments by interested persons. Registration will begin one hour prior to each hearing. Individuals may present oral statements when called upon in order of registration. A four-minute time limit will be established at each hearing to assure that enough time is allowed for every interested person to speak. Open discussion will not occur during each hearing; however, agency staff members will be available to discuss the proposal one hour before each hearing, and will answer questions before and after each hearing.

Persons with disabilities who have special communication or other accommodation needs, who are planning to attend a hearing, should contact the Office of Environmental Policy, Analysis, and Assessment at (512) 239-4900. Requests should be made as far in advance as possible.

SUBMITTAL OF COMMENTS

Written comments may be submitted to Heather Evans, Office of Environmental Policy, Analysis, and Assessment, MC 206, P.O. Box 13087, Austin, Texas 78711-3087, faxed to (512) 239- 4808, or emailed to siprules@tnrcc.state.tx.us . All comments should reference Rule Log Number 2000-011N-114-AI. Comments must be received by 5:00 p.m., September 25, 2000. For further information, please contact Scott Carpenter at (512) 239-1757 or Alan Henderson at (512) 239- 1510.

STATUTORY AUTHORITY

The new sections are proposed under Texas Water Code (TWC), §5.103, which authorizes the commission to adopt rules necessary to carry out its powers and duties under the TWC, and under the Texas Health and Safety Code, TCAA, §382.017, which provides the commission authority to adopt rules consistent with the policy and purposes of the TCAA. The new sections are also proposed under TCAA, §382.011, which authorizes the commission to control the quality of the state's air; §382.012, which authorizes the commission to prepare and develop a general, comprehensive plan for the control of the state's air; §382.019, which authorizes the commission to adopt rules to control and reduce emissions from engines used to propel land vehicles; and §382.039, which authorizes the commission to develop and implement transportation programs and other measures necessary to demonstrate attainment and protect the public from exposure to hazardous air contaminants from motor vehicles.

The proposed new sections implement TCAA, §382.002, relating to Policy and Purpose; §382.011, relating to General Powers and Duties; §382.012, relating to State Air Control Plan; §382.019, relating to Methods Used to Control and Reduce Emissions from Land Vehicles; and §382.039, relating to Attainment Program.

§114.500.Definitions.

Unless specifically defined in the TCAA or in the rules of the commission, the terms used in this subchapter have the meanings commonly ascribed to them in the field of air pollution control. In addition to the terms which are defined by the TCAA, §3.2 of this title (relating to Definitions); §101.1 of this title (relating to Definitions); and §114.1 of this title (relating to Definitions), the following words and terms, when used in this subchapter shall have the following meanings, unless the context clearly indicates otherwise.

(1)

Idle - The operation of an engine in the operating mode where the engine is not engaged in gear, where the engine operates at a speed at the revolutions per minute specified by the engine or vehicle manufacturer for when the accelerator is fully released, and there is no load on the engine.

(2)

Motor vehicle - Any self-propelled device powered by an internal combustion engine and designed to operate with four or more wheels in contact with the ground, in or by which a person or property is or may be transported, and is required to be registered under Texas Transportation Code (TTC), §502.002, excluding vehicles registered under TTC, §502.006(c).

(3)

Primary propulsion engine - The internal combustion engine attached to a motor vehicle that provides the power to propel the motor vehicle into and maintain motion.

§114.502.Control Requirements for Motor Vehicle Idling.

No person shall cause, suffer, allow, or permit the primary propulsion engine of a motor vehicle to idle for more than five consecutive minutes in the counties listed in §114.509 of this title (relating to Affected Counties and Compliance Dates) when the vehicle is not in motion during the period of April 1 through October 31 of each calendar year.

§114.507.Exemptions.

The provisions of §114.502 of this title (relating to Control Requirements for Motor Vehicle Idling) shall not apply to:

(1)

a motor vehicle that has a gross vehicle weight rating of 14,000 pounds or less;

(2)

a motor vehicle forced to remain motionless because of traffic conditions over which the operator has no control;

(3)

a motor vehicle being used as an emergency or law enforcement motor vehicle;

(4)

the primary propulsion engine of a motor vehicle providing power takeoff for refrigeration, lift gate pumps or other auxiliary uses;

(5)

the primary propulsion engine of a motor vehicle being operated for maintenance or diagnostic purposes; or

(6)

the primary propulsion engine of a motor vehicle being operated solely to defrost a windshield.

§114.509.Affected Counties and Compliance Dates.

Beginning April 1, 2001, all affected persons in the following counties shall comply with §114.502 of this title (relating to Control Requirements): Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller.

This agency hereby certifies that the proposal has been reviewed by legal counsel and found to be within the agency's legal authority to adopt.

Filed with the Office of the Secretary of State, on August 11, 2000.

TRD-200005628

Margaret Hoffman

Director, Environmental Law Division

Texas Natural Resource Conservation Commission

Earliest possible date of adoption: September 24, 2000

For further information, please call: (512) 239-0348


Chapter 115. CONTROL OF AIR POLLUTION FROM VOLATILE ORGANIC COMPOUNDS

The Texas Natural Resource Conservation Commission (TNRCC or commission) proposes amendments to §§115.161, 115.162, 115.164 - 115.167, and 115.169, concerning Batch Processes; §§115.122, 115.125 - 115.127, and 115.129, concerning Vent Gas Control; and §115.449, concerning Offset Lithographic Printing. The commission proposes these revisions to Chapter 115, concerning Control of Air Pollution from Volatile Organic Compounds, and to the state implementation plan (SIP) in order to conform with the United States Environmental Protection Agency's (EPA) reasonably available control technology (RACT) requirements in the Houston/ Galveston (HGA) ozone nonattainment area and to obtain volatile organic compound (VOC) emission reductions which will result in reductions in ozone formation in HGA. In an effort to improve implementation of the existing Chapter 115, the commission also proposes amendments to §115.10, concerning Definitions; and §§115.211, 115.212, and 115.216, concerning Loading and Unloading of Volatile Organic Compounds; new §115.120, concerning Vent Gas Definitions; §115.240, concerning Stage II Vapor Recovery Definitions; and §115.430, concerning Flexographic and Rotogravure Printing Definitions; and revisions to the SIP.

BACKGROUND AND SUMMARY OF THE FACTUAL BASIS FOR THE PROPOSED RULES

The HGA ozone nonattainment area is classified as Severe-17 under the 1990 Amendments to the Federal Clean Air Act (FCAA), and therefore is required to attain the one-hour ozone standard of 0.12 parts per million (ppm) by November 15, 2007. The HGA area, defined by Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller Counties, has been working to develop a demonstration of attainment in accordance with the FCAA. On January 4, 1995, the state submitted the first of its Post-1996 SIP revisions for HGA.

The January 1995 SIP consisted of urban airshed model (UAM) modeling for 1988 and 1990 base case episodes, adopted rules to achieve a 9% rate-of-progress (ROP) reduction in VOC, and a commitment schedule for the remaining ROP and attainment demonstration elements. At the same time, but in a separate action, the State of Texas filed for the temporary nitrogen oxide (NO x ) waiver allowed by the FCAA (42 United States Code (USC)), §7511a(f). The January 1995 SIP and the NO x waiver were based on early base case episodes which marginally exhibited model performance in accordance with EPA modeling performance standards, but which had a limited data set as inputs to the model. In 1993 and 1994, the commission was engaged in an intensive data-gathering exercise known as the Coastal Oxidant Assessment for Southeast Texas (COAST) study. The commission believed that the enhanced emissions inventory, expanded ambient air quality and meteorological monitoring, and other elements would provide a more robust data set for modeling and other analysis, which would lead to modeling results that the commission could use to better understand the nature of the ozone air quality problem in the HGA area. This modeling has been ongoing since that time.

Around the same time as the 1995 submittal, EPA policy regarding SIP elements and timelines went through changes. Two national programs in particular resulted in changing deadlines and requirements. The first of these programs was the Ozone Transport Assessment Group. This group grew out of a March 2, 1995 memo from Mary Nichols, former EPA Assistant Administrator for Air and Radiation, that allowed states to postpone completion of their attainment demonstrations until an assessment of the role of transported ozone and precursors had been completed for the eastern half of the nation, including the eastern portion of Texas. Texas participated in this study, and it has been concluded that Texas does not significantly contribute to ozone exceedances in the Northeastern United States. The other major national initiative that has impacted the SIP planning process is the revision to the national ambient air quality standard (NAAQS) for ozone. The EPA promulgated a final rule on July 18, 1997 changing the ozone standard to an eight-hour standard of 0.08 ppm. In November 1996, concurrent with the proposal of the standards, the EPA proposed an interim implementation plan (IIP) that it believed would help areas like HGA transition from the old to the new standard. In an attempt to avoid a significant delay in planning activities, Texas began to follow this guidance, and readjusted its modeling and SIP development timelines accordingly. When the new standard was published, the EPA decided not to publish the IIP, and instead stated that, for areas currently exceeding the one-hour ozone standard, that standard would continue to apply until it is attained. The FCAA requires that HGA attain the one-hour standard by November 15, 2007.

The EPA issued revised draft guidance for areas such as HGA that do not attain the one-hour ozone standard. The commission adopted on May 6, 1998 and submitted to the EPA on May 19, 1998 a revision to the HGA SIP which contained the following elements in response to the EPA's guidance: UAM modeling based on emissions projected from a 1993 baseline out to the 2007 attainment date; an estimate of the level of VOC and NO x reductions necessary to achieve the one-hour ozone standard by 2007; a list of control strategies that the state could implement to attain the one-hour ozone standard; a schedule for completing the other required elements of the attainment demonstration; a revision to the Post-1996 9% ROP SIP that remedied a deficiency that the EPA believed made the previous version of that SIP unapprovable; and evidence that all measures and regulations required by Subpart 2 of Title I of the FCAA to control ozone and its precursors have been adopted and implemented, or are on an expeditious schedule to be adopted and implemented.

In November 1998, the SIP revision submitted to the EPA in May 1998 became complete by operation of law. However, the EPA stated that it could not approve the SIP until specific control strategies were modeled in the attainment demonstration. The EPA specified a submittal date of November 15, 1999 for this modeling. In a letter to the EPA dated January 5, 1999, the state committed to model two strategies showing attainment.

As the HGA modeling protocol evolved, the commission eventually selected and modeled seven basic modeling scenarios. As part of this process, a group of HGA stakeholders worked closely with commission staff to identify local control strategies for the modeling. Some of the scenarios for which the stakeholders requested evaluation include options such as California-type fuel and vehicle programs as well as an acceleration simulation mode equivalent motor vehicle inspection and maintenance program. Other scenarios incorporate the estimated reductions in emissions that are expected to be achieved throughout the modeling domain as a result of the implementation of several voluntary and mandatory statewide programs adopted or planned independently of this SIP. It should be made clear that the commission did not propose that any of these strategies be included in the ultimate control strategy submitted to the EPA in 2000. Decisions regarding the actual control strategy to be submitted to the EPA will be the next step in an iterative process of evaluating potential control strategies, an effort which will continue through 2000. The need for and effectiveness of any controls which may be implemented outside the HGA eight-county area will be evaluated on a county-by-county basis.

The SIP revision was adopted by the commission on October 27, 1999, submitted to the EPA by November 15, 1999, and contained the following elements: photochemical modeling of potential specific control strategies for attainment of the one-hour ozone standard in the HGA area by the attainment date of November 15, 2007; an analysis of seven specific modeling scenarios reflecting various combinations of federal, state, and local controls in HGA (additional scenarios H1 and H2 build upon Scenario VIf); identification of the level of reductions of VOC and NO x necessary to attain the one-hour ozone standard by 2007; a 2007 mobile source budget for transportation conformity; identification of specific source categories which, if controlled, could result in sufficient VOC and/or NO x reductions to attain the standard; a schedule committing to submit by April 2000 an enforceable commitment to conduct a mid-course review; and a schedule committing to submit modeling and adopted rules in support of the attainment demonstration by December 2000.

The HGA Attainment Demonstration SIP revision which was adopted April 19, 2000, contained the following enforceable commitments by the state: to quantify the shortfall of NO x reductions needed for attainment; to list and quantify potential control measures to meet the shortfall of NOx reductions needed for attainment; to adopt the majority of the necessary rules for the HGA attainment demonstration by December 31, 2000, and to adopt the rest of the shortfall rules as expeditiously as practical, but no later than July 31, 2001; to submit a Post-1999 ROP plan by December 31, 2000; to perform a mid-course review by May 1, 2004; and to perform modeling of mobile source emissions using the EPA mobile source emissions model (MOBILE6), to revise the on- road mobile source budget as needed, and to submit the revised budget within 24 months of the model's release. In addition, if a conformity analysis is to be performed between 12 months and 24 months after the MOBILE6 release, the state will revise the motor vehicle emissions budget (MVEB) so that the conformity analysis and the SIP MVEB are calculated on the same basis.

The Houston nonattainment area will need to ultimately reduce NO x more than 750 tons per day (tpd) to reach attainment with the one-hour standard. In addition, a VOC reduction of about 25% will have to be achieved. Adoption of VOC RACT rules can contribute to attainment and maintenance of the one-hour ozone standard in the HGA area. The VOC RACT rules also may contribute to a successful demonstration of transportation conformity in the HGA area.

Under 42 USC, §7511b of the 1990 Amendments to the FCAA, the EPA is required to issue Control Techniques Guideline (CTG) guidance documents for the purpose of assisting states in developing RACT controls for sources of VOC emissions. In turn, each state is required to submit a revision to its SIP which implements RACT regulations for VOC sources in moderate or above ozone nonattainment areas. Specifically, FCAA, 42 USC, §7511a(b)(2)(A), requires states to submit RACT regulations for VOC sources that are covered by a CTG issued after November 15, 1990 (the enactment date of the 1990 FCAA), but prior to the time of attainment. Similarly, FCAA, 42 USC, §7511a(b)(2)(C), requires that RACT be applied to major VOC sources located in moderate or above ozone nonattainment areas which are not the subject of a CTG; such sources are known as "non-CTG" sources. Limits in state rules must be at least as stringent as the CTG limits or otherwise must be determined to meet RACT.

Each CTG contains a "presumptive norm" for RACT for a specific source category, based on the EPA's evaluation of the capabilities and problems general to that category. Where applicable, the EPA recommends that states adopt requirements consistent with the presumptive norm. However, the presumptive norm is only a recommendation. States may choose to develop their own RACT requirements on a case-by-case basis, considering the emission reductions needed to obtain achievement of the NAAQS and the economic and technical circumstances of the individual source.

Source categories for which the EPA was to issue CTGs under FCAA, 42 USC, §7511a(b)(2)(A), include batch processes and offset lithographic printing. Instead of issuing CTGs for these source categories, the EPA issued guidance documents known as Alternative Control Techniques (ACT) documents. An ACT does not establish the presumptive norm for RACT but merely contains information on emissions, controls, control options, and costs. The EPA itself has consistently noted in the ACT documents that each ACT "...presents options only, and does not contain a recommendation on RACT." Although the EPA has not issued the required CTGs for batch processes and offset lithographic printing, 42 USC, §7511a(b)(2)(C) of the 1990 FCAA Amendments still requires states to ensure that RACT is in place for all major VOC sources in moderate and above ozone nonattainment areas.

Historically, the commission's position has been that the existing general vent gas rule in Chapter 115, Subchapter B: Division 2 is adequate to ensure RACT for batch processes; however, this is difficult to demonstrate because the necessary information for such a demonstration is not in the emissions inventory (EI). Staff attempted to develop a demonstration of equivalency between the existing general vent gas rule and the batch processes ACT using the EPA's 5% rule. The EPA's "5% rule" provides a mechanism for states to justify exemptions or cutpoints which are more lenient than the EPA's RACT baseline. It is applied by determining the total emissions allowed by the EPA's RACT baseline (including exemptions) and comparing this to the emissions allowed (including exemptions) by a state regulation. If the difference is less than 5.0%, the EPA considers that there is no substantive difference between the EPA and state requirements. The staff was unable to assemble the information necessary to demonstrate to the EPA's satisfaction that existing rules represent RACT for batch processes in HGA. Consequently, it is necessary to adopt and implement Chapter 115 rules for batch processes in HGA.

Bakeries are a non-CTG source category. The EPA published an ACT guidance document detailing appropriate control technology for bakeries. Based on this document, as well as on input from the bakery industry, the commission developed the applicable portion of the Chapter 115 vent gas rule pertaining to bakeries.

The EPA has stated that this rule is deficient in implementing RACT for bakeries and therefore is unapprovable. The EPA has made it clear that failure to correct the deficiencies will result in undesirable consequences for the affected ozone nonattainment areas, as specified in the FCAA. The commission adopted revisions on February 24, 1999 which address deficiencies in the bakery rule as it applies in the Dallas/Fort Worth (DFW) ozone nonattainment area. (See the March 12, 1999 issue of the Texas Register (24 TexReg 1777)). However, there are still deficiencies in the bakery rule as it applies in HGA which must be corrected for the HGA Attainment Demonstration SIP to be approvable. Specifically, the EPA has specified that RACT for bakery ovens is 80-90% control efficiency, while the commission rule as negotiated in 1994 requires only a 30% emission reduction.

The Chapter 115 offset lithographic printing rule (§§115.440, 115.442, 115.443, 115.445, 115.446, and 115.449) is currently a contingency rule for HGA. Because HGA is a severe ozone nonattainment area, a source in HGA is major if it has the potential to emit 25 tons per year (tpy) or more of VOC emissions. FCAA, 42 USC, §7511a(b)(2), requires that RACT be applied to major sources, and consequently it is necessary to implement this rule in HGA for sources with VOC emissions equal to or greater than 25 tpy. The rule will remain a contingency rule for offset lithographic printers in HGA with VOC emissions below 25 tpy. The offset lithographic printers in HGA with VOC emissions below 25 tpy must still comply with the general vent gas rules in Chapter 115.

SECTION BY SECTION DISCUSSION

The proposed amendments to §115.10, concerning Definitions, delete the definitions of bakery oven, synthetic organic chemical manufacturing industry batch distillation operation, synthetic organic chemical manufacturing industry batch process, synthetic organic chemical manufacturing industry distillation operation, synthetic organic chemical manufacturing industry distillation unit, and synthetic organic chemical manufacturing industry reactor process. These terms are used solely within the Chapter 115 vent gas rules (§§115.121 - 115.123, 115.125 - 115.127, and 115.129) and are proposed to be relocated to a new §115.120, concerning Vent Gas Definitions.

The proposed amendments to §115.10 also delete the definitions of independent small business marketer of gasoline, and owner or operator of a motor vehicle fuel dispensing facility. These terms are used solely within the Chapter 115 Stage II vapor recovery rules (§§115.241 - 115.249) and are proposed to be relocated to a new §115.240, concerning Stage II Vapor Recovery Definitions.

In addition, the proposed amendments to §115.10 delete the definitions of flexographic printing process, packaging rotogravure printing, publication rotogravure printing, and rotogravure printing. These terms are used solely within the Chapter 115 flexographic and rotogravure printing rules (§§115.432, 115.433, 115.435 - 115.437, and 115.439) and are proposed to be relocated to a new §115.430, concerning Flexographic and Rotogravure Printing Definitions.

The proposed amendments to §115.10 also delete the definitions of flare and vapor combustor. The definitions of these terms in §115.10 have been superceded by the corresponding definitions of these terms in 30 TAC §101.1, concerning Definitions. (See the December 17, 1999 issue of the Texas Register (24 TexReg 11494)). The commission added the definitions of flare and vapor combustor to §115.10 on June 30, 1999 as placeholders until definitions of these terms could be added to §101.1. (See the July 16, 1999 issue of the Texas Register (24 TexReg 5488)).

In addition, the proposed amendments to §115.10 delete the definition of vapor recovery system and combine it with the definition of vapor control system. The existing definitions of vapor recovery system and vapor control system are identical, and the commission is in the process of a transition in the Chapter 115 rules to the term "vapor control system" from the misleading term "vapor recovery system," which is defined to include both recovery and combustion control devices. Combining both terms under the definition of vapor control system will facilitate this transition.

The proposed amendments to §115.10 also revise the definitions of external floating roof and internal floating cover to more clearly specify that an external floating roof storage tank which is equipped with a self-supporting fixed roof (typically a bolted aluminum geodesic dome) is considered to be an internal floating roof storage tank for the purposes of Chapter 115 only.

In addition, the proposed amendments to §115.10 add a definition of liquefied petroleum gas in order to clarify the exemptions in §115.217(a)(3) and (b)(4) for loading and unloading of liquefied petroleum gas. Before the commission adopted revisions on June 30, 1999 (effective date: July 21, 1999), the previous versions of these exemptions referred to the safety rules of the Liquefied Petroleum Gas Division of the Texas Railroad Commission (RRC), which regulates many aspects of the handling and transport of liquefied petroleum gas. Because these exemptions historically referred to the RRC rules, it follows logically that the term "liquified petroleum gas" was intended to have the same meaning as defined in those RRC rules (specifically, 16 TAC §9.2(32), effective March 2, 1998). The National Fire Protection Association, which develops and publishes fire codes and safety standards, has a definition of liquefied petroleum gas in Standard 58 - Standard for the Storage and Handling of Liquefied Petroleum Gases which is functionally identical to the RRC's definition. Furthermore, Section 3-1 of the Petroleum Products Handbook , First Edition (Virgil B. Guthrie, editor), states that this is the most commonly used definition of liquefied petroleum gas. Therefore, the proposed definition of liquefied petroleum gas is consistent with other Texas state rules and industrial reference materials.

The proposed amendments to §115.10 also revise the definition of polymer and resin manufacturing process by replacing the "and" with "or" to make it clear that a manufacturing process only has to manufacture a listed polymer or a listed resin, but not both, in order to meet the definition. This proposed amendment will make the definition consistent with the usage of this definition in the fugitive monitoring rules for ozone nonattainment areas (§§115.352 - 115.357 and 115.359).

In addition, the proposed amendments to §115.10 revise the definition of synthetic organic chemical manufacturing process by replacing the reference to Table I (Synthetic Organic Chemicals) with a reference to 40 Code of Federal Regulations (CFR) 60.489 (effective October 18, 1983). Concurrently, Table I is being deleted. The list of affected chemicals is unchanged because Table I was derived from the corresponding table in 40 CFR 60.489.

Finally, the proposed amendments to §115.10 revise the definition of transport vessel to delete the ambiguous term "primarily." The revision will clearly specify that a transport vessel includes any land-based mode of transportation (truck or rail) of oil, gasoline, or other volatile organic liquid bulk cargo in a storage tank which has a capacity greater than 1,000 gallons. This has always been the interpretation of the term "transport vessel," so this revision simply makes that interpretation more clear.

The proposed new §115.120, concerning Vent Gas Definitions, adds definitions of bakery oven, synthetic organic chemical manufacturing industry batch distillation operation, synthetic organic chemical manufacturing industry batch process, synthetic organic chemical manufacturing industry distillation operation, synthetic organic chemical manufacturing industry distillation unit, and synthetic organic chemical manufacturing industry reactor process. These definitions are proposed to be relocated from the §115.10, concerning Definitions, because they are used solely within the Chapter 115 vent gas rules (§§115.121 - 115.123, 115.125 - 115.127, and 115.129).

The proposed amendments to §115.122, concerning Control Requirements, change the 30% emission reduction requirement from the 1990 baseline emissions inventory for major source bakeries in HGA to an 80% emission reduction requirement from the uncontrolled VOC emission rate of the oven(s) and establish a December 31, 2001 compliance date. The proposed amendments to §115.122 also change the baseline for major source bakeries in the DFW ozone nonattainment area from the 1990 baseline emissions inventory to the uncontrolled VOC emission rate of the oven(s). In addition, the proposed amendments to §115.122 update rule cross-references; update references from "standard exemption" to "permit by rule;" and change references from "vapor recovery system" to "vapor control system" for clarification.

The proposed amendments to §115.125, concerning Testing Requirements, extend the existing test methods to Aransas, Bexar, Calhoun, Matagorda, San Patricio, and Travis Counties; consolidate the existing §115.125(a) and (b) into a single subsection; and reorganize the section by grouping related test methods together. Because it is not reasonably possible to measure the mass emission rate from an elevated flare (an elevated flare's flame is open to the atmosphere, such that the emissions cannot be routed through a stack), the test methods for flow rate and VOC concentration in the existing §115.125(a)(3) - (6) and (b)(3) - (6), which are proposed to be renumbered as §115.125(1) and (2), do not apply to flares. In order to specify performance requirements for flares, the proposed revisions to new §115.125(3) establish the test requirements of 40 CFR 60.18(b) for flares in the Beaumont/Port Arthur (BPA), DFW, and HGA ozone nonattainment areas. Because flares cannot be stack-tested, the proposed amendments to §115.125(3) also specify that compliance with the requirements of 40 CFR 60.18(b) represents compliance with the emission specifications of §115.121 and the control efficiency requirements of §115.122. In addition, the proposed amendments to §115.125 include an option that the owner or operator of a vapor combustor may consider it to be a flare and meet the flare requirements specified in 40 CFR 60.18(b) instead of the test methods and procedures appropriate for a thermal or catalytic oxidizer. The proposed amendments to §115.125 also add a new paragraph (5), which authorizes the use of test methods other than those specifically listed in §115.125, provided that any new test method is validated using the procedures in 40 CFR 63, Appendix A, Test Method 301, with the executive director acting as the administrator. This revision is necessary because in some specific unique situations, the listed test methods may be inappropriate. The new paragraph (5) increases flexibility by allowing the use of additional test methods which may be more cost-effective and more appropriate in certain unique situations.

The proposed amendments to §115.126, concerning Monitoring and Recordkeeping Requirements, extend the existing test methods to Aransas, Bexar, Calhoun, Matagorda, San Patricio, and Travis Counties; consolidate the existing §115.126(a) and (b) into a single subsection; update references to other sections; and replace "true partial pressure" with the more understandable term "concentration." The proposed amendments to §115.126 also change the 30% emission reduction requirement from the 1990 baseline emissions inventory for major source bakeries in HGA to an 80% emission reduction requirement from the uncontrolled VOC emission rate of the oven(s), establish a December 31, 2001 compliance date, and require submittal of a control plan by March 31, 2001 which shows how the owner or operator will meet the emission reduction requirements. In addition, the proposed amendments to §115.126 change the baseline for major source bakeries in DFW from the 1990 emissions inventory to the uncontrolled VOC emission rate of the oven(s), and delete the annual reporting requirements for major source bakeries in DFW and HGA. Because the major source bakeries in DFW and HGA have installed (or are in the process of installing) catalytic oxidizers which can readily meet the control requirements and the monitoring and recordkeeping requirements will ensure that these control devices are functioning properly, there is no need for these bakeries to submit an annual report.

Finally, the proposed amendments to §115.126 also specify that flares in BPA, DFW, and HGA must meet the requirements of 40 CFR 60.18(b) and Chapter 111; and state that records of appropriate operating parameters must be kept for types of vapor control systems not specifically listed in §115.126(1)(A) and (B). The proposed §115.126(1)(A)(iv) and (1)(B) specify exhaust gas temperature monitoring of vapor combustors, with an option that the owner or operator of a vapor combustor may consider it to be a flare and monitor the unit under the flare requirements specified in 40 CFR 60.18(b) and 30 TAC Chapter 111. These amendments are necessary to ensure that control devices are functioning properly and to clarify how vapor combustors are to be monitored. Based upon information from the Air Permits Division, most existing flares meet the design and operating criteria of 40 CFR 60.18(b). The commission solicits information regarding vents in BPA, DFW, and HGA which are controlled by flares that do not meet the requirements of 40 CFR 60.18(b).

Sources which are addressed by a Chapter 115 contingency rule (i.e., one in which Chapter 115 requirements are triggered for that source by the commission publishing notification in the Texas Register that implementation of the contingency rule is necessary) are subject to the requirements of Division 2, concerning Vent Gas Control, until the compliance date of that contingency rule. The purpose is to ensure that a Chapter 115 rule (either the general vent gas rule or the more specific contingency rule, but not both) applies at all times to sources addressed by a contingency rule. The proposed amendments to §115.127(a) add a new paragraph (8) which specifies that for a source that is addressed by a Chapter 115 contingency rule, the owner or operator of that source may choose to comply with the requirements of the contingency rule as though the contingency rule already had been implemented for that source, rather than complying with Division 2. In the case of bakeries, this option would be an alternative to complying with the general vent gas control requirements of §115.121(a)(1) and §115.122(a)(1) because these currently applicable requirements are in the same division (Division 2, concerning Vent Gas Control), as the bakery contingency measure requirements.

For example, under §115.449(c) the offset printing rules of §§115.442 - 115.446 are a contingency rule for each printing operation in DFW for which all offset lithographic printing presses on a property, when uncontrolled, emit a combined weight of VOC less than 50 tons per calendar year. Such sources are currently subject to the requirements of Division 2, concerning Vent Gas Control. Under the proposed new §115.127(a)(8), the owner or operator of such a printing operation instead would have the option of complying with the offset printing rules of §§115.442 - 115.446 as though that offset printing contingency rule had been implemented in DFW and the compliance date had already passed.

In addition, the proposed amendments to §115.127 delete the concentration thresholds in true partial pressure and retain the more understandable concentration thresholds in parts per million by volume.

The proposed amendments to §115.129, concerning Counties and Compliance Schedules, specify the compliance schedule for the new requirements described earlier in this preamble; delete language which is obsolete due to the passing of the May 31, 1996 and November 15, 1996 compliance dates; and update references to other sections.

The proposed rule amendments add the Chapter 115 batch process requirements (§§115.160 - 115.167 and 115.169) to the eight-county HGA ozone nonattainment area. The rule language is based upon the EPA's Control of Volatile Organic Compound Emissions from Batch Processes - Alternative Control Techniques Information Document (EPA-453/R-94-020, February 1994).

The proposed amendments to §115.161, concerning Applicability, specify that the batch process requirements of §§115.162 - 115.167 apply to vent gas streams at batch process operations in the HGA area under the Standard Industrial Classification (SIC) codes 2821 (plastic resins and materials), 2833 (medicinals and botanicals), 2834 (pharmaceutical preparations), 2861 (gum and wood chemicals), 2865 (cyclic crudes and intermediates), 2869 (industrial organic chemicals, not elsewhere classified), and 2879 (agricultural chemicals, not elsewhere classified).

The proposed amendments to §115.161 also specify that the existing requirements of Subchapter B, Division 2, concerning Vent Gas Control, will continue to apply to batch process operations in HGA which are exempt from §§115.162 - 115.166 because they are located at an account which has total VOC emissions (determined before control but after the last recovery device) of less than 25 tpy from all stationary emission sources at the account.

The proposed amendments to §115.162, concerning Control Requirements, make batch process operations in HGA subject to: the applicable RACT equations for low, moderate, and high volatility materials; a successive ranking scheme which determines which sources must be controlled and which are exempt; and the EPA's "once-in, always-in" (OIAI) requirement. OIAI is an EPA concept which means that once emissions from a source exceed the applicability cutoff for a particular VOC regulation in the SIP, that source is always subject to the control requirements of the regulation.

Although no amendments are proposed to §115.163, concerning Alternate Control Requirements, an alternate means of control will be available under this section for batch process operations in HGA.

The proposed amendments to §115.164, concerning Determination of Emissions and Flow Rates, make batch process operations in HGA subject to the procedures for determining the uncontrolled annual emission total and the average flow rate for process vents.

The proposed amendments to §115.165, concerning Approved Test Methods and Testing Requirements, make batch process operations in HGA subject to specified test methods and testing requirements for determining compliance with the control requirements. Minor modifications to the test methods may be used if approved by the executive director.

Because it is not reasonably possible to measure the mass emission rate from an elevated flare (an elevated flare's flame is open to the atmosphere, such that the emissions cannot be routed through a stack), the test methods for flow rate and VOC concentration do not apply to flares. In order to specify performance requirements for flares, §115.165 includes the test requirements of 40 CFR 60.18(b). Because flares cannot be stack-tested, the §115.165 also specifies that compliance with the requirements of 40 CFR 60.18(b) represents a 98% control efficiency. Based upon information from the Air Permits Division, most existing flares meet the design and operating criteria of 40 CFR 60.18(b). The commission solicits information regarding flares which are used to control emissions from batch process operations in HGA, but do not meet the requirements of 40 CFR 60.18(b).

Section 115.165 also includes authorization for the use of test methods other than those specifically listed in §115.165, provided that any new test method is validated using the procedures in 40 CFR 63, Appendix A, Test Method 301, with the executive director acting as the administrator. This option is included in §115.165 because in some specific unique situations the listed test methods may be inappropriate. The availability of this option increases flexibility by allowing the use of additional test methods which may be more cost-effective and more appropriate in certain unique situations.

The proposed amendments to §115.166, concerning Recordkeeping Requirements, make batch process operations in HGA subject to requirements for: continuous monitoring and recording of control device operating parameters; recordkeeping of the annual mass emission total, average flow rate, and associated documentation for each process vent; and the control device operating parameters to be measured and recorded during performance testing. The proposed amendments also change an incorrect reference in §115.166(1) from "VOC transfer operations" to "batch process operations." As a result of this correction, the term "VOC" is being spelled out in §115.166(1)(A)(iii)(II).

The proposed amendments to §115.167, concerning Exemptions, make the following exemptions available in HGA: batch process operations which are located at an account in HGA which has total VOC emissions (determined before control but after the last recovery device) of less than 25 tpy; single unit operations that have a mass annual emissions of 500 pounds per year or less; and combined vents from a batch process train which have a mass annual emissions total below specified levels which vary depending on the volatility of the VOCs. In addition, the proposed amendments revise the existing exemption in §115.167(2) to clarify that §115.164, concerning Determination of Emissions and Flow Rates, is to be used for determining if the exemptions available under §115.167(2) are met. The proposed amendments to §115.167 also specify that the existing requirements of Subchapter B, Division 2, concerning Vent Gas Control, will continue to apply to batch process operations which qualify for exemption because they are located at an account in HGA which has total VOC emissions (determined before control but after the last recovery device) of less than 25 tpy.

The proposed amendments to §115.169, concerning Counties and Compliance Schedules, specify the newly affected counties in HGA (Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller) and a December 31, 2002 compliance date for the new requirements. The proposed amendments to §115.169 also specify that batch process operations which are subject to the requirements of §§115.162 - 115.166 must continue to comply with the existing requirements of Subchapter B, Division 2, concerning Vent Gas Control, until these batch process operations are in compliance with the new requirements.

The proposed amendments to §115.211, concerning Emission Specifications, delete a reference to gasoline bulk plants which is no longer necessary due to the deletion of the gasoline bulk plant emission specification adopted by the commission on November 10, 1999. (See the November 26, 1999 issue of the Texas Register (24 TexReg 10559)).

The proposed amendments to §115.212, concerning Control Requirements, revise §115.212(a)(3) and (b)(3) to state that the requirements regarding vapor and liquid leaks during land-based VOC transfer apply specifically to transport vessels. This revision is necessary in order to clarify that the requirements are not intended to apply to vessels which do not meet the definition of "transport vessel" in §115.10 (for example, drums).

The proposed amendments to §115.216, concerning Monitoring and Recordkeeping Requirements, revise §115.216(3)(A)(i) to only require records of the identification number of tank-truck tanks for which annual leak testing is required under §115.214(a)(1)(C) or (b)(1)(C), rather than all tank-truck tanks as is currently required. This amendment is being proposed because it is unnecessary to track the identification number of tank-truck tanks which are excluded from the annual leak testing requirements.

The proposed new §115.240, concerning Stage II Vapor Recovery Definitions, adds definitions of independent small business marketer of gasoline, and owner or operator of a motor vehicle fuel dispensing facility. These definitions are proposed to be relocated from the §115.10, concerning Definitions, because they are used solely within the Chapter 115 Stage II vapor recovery rules (§§115.241 - 115.249).

The proposed new §115.430, concerning Flexographic and Rotogravure Printing Definitions, adds definitions of flexographic printing process, packaging rotogravure printing, publication rotogravure printing, and rotogravure printing. These definitions are proposed to be relocated from the §115.10, concerning Definitions, because they are used solely within the Chapter 115 flexographic and rotogravure printing rules (§§115.432, 115.433, 115.435 - 115.437, and 115.439). In addition, the commission proposes to change the title of Subchapter E, Division 3 from "Graphic Arts (Printing) by Rotogravure and Flexographic Processes" to "Flexographic and Rotogravure Printing" in order to more clearly specify the operations addressed by to this division.

HGA is classified as a severe ozone nonattainment area and the major source definition includes VOC sources with emissions of 25 tpy and higher. Because FCAA, 42 USC, §7511a(b)(2), requires that RACT be applied to major sources, the proposed amendments to §115.449, concerning Counties and Compliance Schedules, implement the offset lithographic printing rule in HGA for sources with VOC emissions equal to or greater than 25 tpy and establishes a compliance date of December 31, 2002. The offset lithographic printing rule is currently a contingency rule for HGA; after the proposed change, the rule will be a contingency rule for offset lithographic printers in HGA with VOC emissions below 25 tpy.

EFFECT ON SITES SUBJECT TO THE FEDERAL OPERATING PERMITS PROGRAM

Since 30 TAC Chapter 115 is an applicable requirement under 30 TAC Chapter 122, owners or operators subject to the Federal Operating Permit Program must, consistent with the revision process in Chapter 122, revise their operating permit to include the revised Chapter 115 requirements for each emission unit affected by the revisions to Chapter 115 at their site.

FISCAL NOTE: COSTS TO STATE AND LOCAL GOVERNMENT

John Davis, Technical Specialist in the Strategic Planning and Appropriations Section, has reviewed these proposed amendments to Chapter 115, Control of Air Pollution from Volatile Organic Compounds, under the requirements of Texas Government Code, §2001.024, and has made the following determination concerning the fiscal effects of the proposed amendments for each year of the first five years the amendments are in effect.

Mr. Davis has determined that for the first five-year period the proposed amendments to Chapter 115 are in effect, there will be no significant fiscal implications for units of state and local government as a result of administration or enforcement of the proposed amendments, except those that may operate sources subject to the proposed revisions to Chapter 115. For these units of state and local government, the fiscal implications of these revisions to Chapter 115 will be equivalent to those for any affected public or private entity.

Most of the sources which will have to comply with the proposed rules are currently subject to air permits and are already being inspected for compliance. Consequently, only a limited number of additional facilities will need to be inspected for compliance with the proposed Chapter 115 rule amendments. The commission anticipates that the Field Operations Division inspectors will inspect for compliance with the proposed requirements when conducting their routine inspections. The commission also anticipates that enforcement of these rules will not significantly increase the number of facilities currently inspected by the state and local governments. However, these rules will cause a minor increase in workload when inspecting the affected facilities.

PUBLIC BENEFIT AND COSTS

Mr. Davis has also determined that for each year of the first five years the proposed amendments to Chapter 115 are in effect, the public benefit anticipated from enforcement of and compliance with the proposed amendments will be: a reduction of public exposure to VOC emitted from affected batch processes, offset lithographic printers, and bakeries; the concomitant reduced risks to human health and safety from ozone; a reduction of ground-level ozone in the HGA ozone nonattainment area; and conformance with the requirements of the FCAA.

The proposed amendments to Chapter 115 will ensure that the batch process, offset lithographic printing, and bakery rules represent RACT in HGA, which will satisfy FCAA requirements and enable these rules to be federally approvable. The amendments would require these sources in the HGA ozone nonattainment area to meet new emission specifications and other requirements in order to reduce VOC emissions and ozone air pollution. These standards and specifications are part of the strategy to reduce emissions of VOC necessary for the counties in the HGA ozone nonattainment area to be able to demonstrate attainment with the NAAQS for ozone. The proposed amendments are one element of the proposed HGA attainment demonstration SIP. A SIP is a plan developed for any region where existing (measured and estimated) ambient levels of pollutant exceeds the levels specified in a national standard. The plan sets forth a control strategy that provides emission reductions necessary for attainment and maintenance of the national standards.

For batch processes, the commission estimates the cost-effectiveness (the cost per ton of VOC emissions reduced), annualized total cost of control, annual operating costs, and total capital cost for flow rates of 500 and 5,000 standard cubic feet per minute (scfm) as follows, based on the cost- effectiveness data of Appendix F of EPA's Control of Volatile Organic Compound Emissions from Batch Processes - Alternative Control Techniques Information Document (EPA-453/R-94- 020, February 1994).

Figure: 30 TAC Chapter 115 - Preamble

For sources which route vent gas emissions (including batch process emissions) to flares that do not already meet the requirements of 40 CFR 60.18(b), the commission estimates the cost of testing to determine the exit velocity and the net heating value of the vapors being combusted to be approximately $6,000, based upon vendor estimates. The commission estimates that installing a heat-sensing device, such as an ultraviolet beam sensor or thermocouple, at the pilot light to indicate the continuous presence of a flame would cost approximately $19,300 to $22,300, based upon vendor estimates.

For bakeries, an analysis of the emissions inventory revealed that there are four bakeries in HGA with VOC emissions at or above 25 tpy and four bakeries in DFW with VOC emissions at or above 50 tpy that will become subject to the vent gas rule's revised control requirements. These bakeries have already installed (or are installing) catalytic oxidizers in response to previous rulemaking. Each of these catalytic oxidizers can meet the revised control requirements, and therefore there will be no cost to install add-on control devices. Elimination of the annual reporting requirement will result in a minor cost savings due to the associated reduction in manpower needed to assemble the reports.

For offset lithographic printers, the commission estimates that there are approximately 20 sources in HGA with VOC emissions at or above 25 tpy that will become subject to the offset printing requirements. The printers with offset heatset printing presses have already installed add-on controls due to Chapter 111 opacity limitations and/or Chapter 116 new source review permitting requirements. Because these add-on controls can already meet the control requirements, there will be no cost for installation of add-on control devices. Regarding the fountain solution limitations which would apply to both heatset and nonheatset offset printing, EPA's draft Control Techniques Guideline for Offset Lithographic Printing (December 14, 1992) estimates that reducing alcohol in the fountain solution results in a savings of $920 per ton of alcohol not used. This document states that nonalcohol fountain solutions save money because they are used in lower quantities, even though they cost more than alcohol. Regarding the cleaning solution limitations which would apply to both heatset and nonheatset offset printing, the draft CTG states that lower VOC cleaning solutions are slightly more expensive than traditional cleaning solutions. This document estimates that the incremental costs of using lower VOC cleaning solutions range from approximately $550 to $24,000 per year, depending on the size and type of the printing plant.

SMALL BUSINESS AND MICRO-BUSINESS ASSESSMENT

The agency has been unable to identify any small businesses or micro-businesses as defined in the Texas Government Code which would be affected by these proposed amendments to Chapter 115. If there are affected small businesses or micro-businesses, the estimated annualized cost for installing and operating the control technology in dollars per ton of VOC reduced that was used for the various types of units in this fiscal note would appear to be a reasonable cost estimate for small businesses or micro- businesses. The proposed amendments do not specify a particular control technology to achieve the emission limits and there may be other control technologies or combinations of control technologies which may be used to comply.

DRAFT REGULATORY IMPACT ANALYSIS DETERMINATION

The commission has reviewed the rulemaking in light of the regulatory analysis requirements of Texas Government Code, §2001.0225, and has determined that the rulemaking does not meet the definition of a "major environmental rule" as defined in that statute. "Major environmental rule" means a rule the specific intent of which is to protect the environment or reduce risks to human health from environmental exposure and that may adversely affect in a material way the economy, a sector of the economy, productivity, competition, jobs, the environment, or the public health and safety of the state or a sector of the state. The amendments to Chapter 115 are one element of the HGA Attainment Demonstration SIP and will require VOC emission reductions from batch processes, offset lithographic printers, and bakeries in the HGA ozone nonattainment area. While the rules are intended to protect the environment, based on the analysis provided earlier in this preamble and in particular, the discussion in the Public Benefit and Costs section, the commission does not believe that the rules will adversely affect, in a material way, the operation of certain batch processes, offset lithographic printers, and bakeries. The commission does not believe these entities comprise a sector of the economy, or that these rules will adversely affect in a material way the economy, productivity, competition, jobs, the environment, or the public health and safety of the state or a sector of the state.

The amendments do not meet the definition of a "major environmental rule" as defined in the Texas Government Code, and they do not meet any of the four applicability requirements listed in §2001.0225(a). FCAA, 42 USC, §7410, requires states to adopt a SIP which provides for "implementation, maintenance, and enforcement" of the primary NAAQS in each air quality control region of the state. While FCAA, 42 USC, §7410, does not require specific programs, methods, or reductions in order to meet the standard, state SIPs must include "enforceable emission limitations and other control measures, means or techniques (including economic incentives such as fees, marketable permits, and auctions of emissions rights), as well as schedules and timetables for compliance as may be necessary or appropriate to meet the applicable requirements of this chapter," (meaning Chapter 85, Air Pollution Prevention and Control). It is true that the FCAA does require some specific measures for SIP purposes, such as the inspection and maintenance program, but those programs are the exception, not the rule, in the SIP structure of the FCAA. The provisions of the FCAA recognize that states are in the best position to determine what programs and controls are necessary or appropriate in order to meet the NAAQS. This flexibility allows states, affected industry, and the public, to collaborate on the best methods for attaining the NAAQS for the specific regions in the state. Even though the FCAA allows states to develop their own programs, this flexibility does not relieve a state from developing a program that meets the requirements of FCAA, 42 USC, §7410. Thus, while specific measures are not generally required, the emission reductions are required. States are not free to ignore the requirements of FCAA, 42 USC, §7410, and must develop programs to assure that the nonattainment areas of the state will be brought into attainment on schedule.

The requirement to provide a fiscal analysis of proposed regulations in the Texas Government Code was amended by Senate Bill 633 (SB 633) during the 75th Legislative Session. The intent of SB 633 was to require agencies to conduct a regulatory impact analysis (RIA) of extraordinary rules. These are identified in the statutory language as major environmental rules that will have a material adverse impact and will exceed a requirement of state law, federal law, or a delegated federal program, or are adopted solely under the general powers of the agency. With the understanding that this requirement would seldom apply, the commission provided a cost estimate for SB 633 that concluded "based on an assessment of rules adopted by the agency in the past, it is not anticipated that the bill will have significant fiscal implications for the agency due to its limited application." The commission also noted that the number of rules that would require assessment under the provisions of the bill was not large. This conclusion was based, in part, on the criteria set forth in the bill that exempted proposed rules from the full analysis unless the rule was a major environmental rule that exceeds a federal law. As previously discussed, the FCAA does not require specific programs, methods, or reductions in order to meet the NAAQS; thus, states must develop programs for each nonattainment area to ensure that area will meet the attainment deadlines. Because of the ongoing need to address nonattainment issues, the commission routinely proposes and adopts SIP rules. The legislature is presumed to understand this federal scheme. If each rule proposed for inclusion in the SIP was considered to be a major environmental rule that exceeds federal law, then every SIP rule would require the full RIA contemplated by SB 633. This conclusion is inconsistent with the conclusions reached by the commission in its cost estimate and by the Legislative Budget Board (LBB) in its fiscal notes. Since the legislature is presumed to understand the fiscal impacts of the bills it passes, and that presumption is based on information provided by state agencies and the LBB, the commission believes that the intent of SB 633 was only to require the full RIA for rules that are extraordinary in nature. While the SIP rules will have a broad impact, that impact is no greater than is necessary or appropriate to meet the requirements of the FCAA. For these reasons, rules adopted for inclusion in the SIP fall under the exception in Texas Government Code, §2001.0225(a), because they are specifically required by federal law. FCAA, 42 USC, §7511a(b)(2)(C), requires states to ensure that RACT is in place for all major VOC sources in moderate and above ozone nonattainment areas. The commission has performed photochemical grid modeling which predicts that VOC emission reductions, such as those required by these rules, will result in reductions in ozone formation in the HGA ozone nonattainment area. This rulemaking is not an express requirement of state law, but was developed specifically in order to ensure that RACT is in place for all major VOC sources in the HGA ozone nonattainment area as required under federal law. This will enable the Chapter 115 batch process, offset lithographic printing, and bakery rules for HGA to be federally approvable. This rulemaking is also intended to obtain VOC emission reductions which will result in reductions in ozone formation in the HGA ozone nonattainment area and help bring HGA into compliance with the air quality standards established under federal law as NAAQS for ozone. The rulemaking does not exceed a standard set by federal law, exceed an express requirement of state law (unless specifically required by federal law), or exceed a requirement of a delegation agreement. The rulemaking was not developed solely under the general powers of the agency, but was specifically developed to meet the RACT requirements and NAAQS established under federal law and authorized under Texas Clean Air Act (TCAA), §§382.011, 382.012, and 382.017.

The commission invites public comment on the draft regulatory impact analysis.

TAKINGS IMPACT ASSESSMENT

The commission has prepared a takings impact assessment for these rules pursuant to Texas Government Code, §2007.043. The following is a summary of that assessment. The specific purpose of the rulemaking is twofold: to ensure that RACT is in place for all major VOC sources in the HGA ozone nonattainment area in order to conform with the EPA's RACT requirements, thus enabling the Chapter 115 batch process, offset lithographic printing, and bakery rules for HGA to be federally approvable; and to obtain VOC emission reductions which will result in reductions in ozone formation in the HGA ozone nonattainment area and help bring HGA into compliance with the air quality standards established under federal law as NAAQS for ozone. This rulemaking action may require the installation of control systems at batch process operations, offset lithographic printers, and bakeries in HGA in some cases. Promulgation and enforcement of the rule amendments may possibly burden private property because in some cases the permanent installation of control systems and associated piping is necessary in order to comply with the rules. Although the rule revisions do not directly prevent a nuisance or prevent an immediate threat to life or property, they do prevent a real and substantial threat to public health and safety and fulfill federal mandates under the 1990 Amendments to the FCAA, 42 USC, §7410 and §7511a(b)(2). Specifically, FCAA, 42 USC, §7511a(b)(2)(C), requires states to ensure that RACT is in place for all major VOC sources in moderate and above ozone nonattainment areas. In addition, the emission limitations and control requirements within this rulemaking were developed in order to meet the NAAQS for ozone set by the EPA under FCAA, 42 USC, §7409. States are primarily responsible for ensuring attainment and maintenance of NAAQS once the EPA has established them. Under the FCAA, 42 USC, §7410, and related provisions, states must submit, for approval by the EPA, SIPs that provide for the attainment and maintenance of NAAQS through control programs directed to sources of the pollutants involved. Therefore, the purpose of this rulemaking is to ensure that RACT is in place for all major VOC sources in the HGA ozone nonattainment area as required under federal law and to meet the air quality standards established under federal law as NAAQS. Consequently, the following exemption applies to these rules: an action reasonably taken to fulfill an obligation mandated by federal law.

COASTAL MANAGEMENT PROGRAM CONSISTENCY REVIEW

The commission has determined that this rulemaking relates to an action or actions subject to the Texas Coastal Management Program (CMP) in accordance with the Coastal Coordination Act of 1991, as amended (Texas Natural Resources Code, §§33.201 et seq.), and the commission's rules in 30 TAC Chapter 281, Subchapter B, concerning Consistency with Texas Coastal Management Program. As required by 31 TAC §505.11(b)(2) and 30 TAC §281.45(a)(3), relating to actions and rules subject to the CMP, commission rules governing air pollutant emissions must be consistent with the applicable goals and policies of the CMP. The commission has reviewed this action for consistency with the CMP goals and policies in accordance with the regulations of the Coastal Coordination Council. For this rulemaking, the commission has determined that the rules are consistent with the applicable CMP goal expressed in 31 TAC §501.12(1) of protecting and preserving the quality and values of coastal natural resource areas and the policy in 31 TAC §501.14(q), which requires that the commission protect air quality in coastal areas. This rulemaking is intended to reduce overall emissions of VOC from batch process vent gas streams, bakeries, and offset lithographic printers. This action is consistent with the CMP because it does not authorize any new emissions and will reduce existing emissions of VOC. Interested persons may submit comments on the consistency of the proposed rules with the CMP during the public comment period.

ANNOUNCEMENT OF HEARINGS

The commission will hold public hearings on this proposal at the following times and locations: September 18, 2000, 10:00 a.m., Lone Star Convention Center, 9055 Airport Road (FM 1484), Conroe; September 18, 2000, 7:00 p.m., Lake Jackson Civic Center, 333 Highway 332 East, Lake Jackson; September 19, 2000, 10:00 a.m. and 7:00 p.m., George Brown Convention Center, 1001 Avenida de Las Americas, Houston; September 20, 2000, 9:00 a.m., VFW Hall, 6202 George Bush Drive, Katy; September 20, 2000, 6:00 p.m., East Harris County Community Center, 7340 Spencer, Pasadena; September 21, 2000, 10:00 a.m., Southeast Texas Regional Airport Media Room, 6000 Airline Drive, Beaumont; September 21, 2000, 2:00 p.m., Amarillo City Commission Chambers, City Hall, 509 East 7th Avenue, Amarillo; September 21, 2000, 6:00 p.m., Charles T. Doyle Convention Center, 21st Street at Phoenix Lane, Texas City; September 22, 2000, 10:00 a.m., Dayton High School, 2nd Floor Lecture Room, 3200 North Cleveland Street, Dayton; September 22, 2000, 11:00 a.m., El Paso City Council Chambers, 2 Civic Center Plaza, 2nd Floor, El Paso; September 22, 2000, 2:00 p.m., North Central Texas Council of Governments, 2nd Floor Board Room, 616 Six Flags Drive, Suite 200, Arlington; and September 25, 2000, 10:00 a.m., Texas Natural Resource Conservation Commission, 12100 North I-35, Building E, Room 201S, Austin. The hearings are structured for the receipt of oral or written comments by interested persons. Registration will begin one hour prior to each hearing. Individuals may present oral statements when called upon in order of registration. A four-minute time limit will be established at each hearing to assure that enough time is allowed for every interested person to speak. Open discussion will not occur during each hearing; however, agency staff members will be available to discuss the proposal one hour before each hearing, and will answer questions before and after each hearing.

Persons with disabilities who have special communication or other accommodation needs, who are planning to attend a hearing, should contact the Office of Environmental Policy, Analysis, and Assessment at (512) 239-4900. Requests should be made as far in advance as possible.

SUBMITTAL OF COMMENTS

Written comments may be submitted to Heather Evans, Office of Environmental Policy, Analysis, and Assessment, MC 206, P.O. Box 13087, Austin, Texas 78711-3087; faxed to (512) 239- 4808; or emailed to siprules@tnrcc.state.tx.us . All comments should reference Rule Log Number 2000-011i-115-AI. Comments must be received by 5:00 p.m., September 25, 2000. For further information, please contact Eddie Mack of the Strategic Assessment Division at (512) 239-1488.

Subchapter A. DEFINITIONS

30 TAC §115.10

STATUTORY AUTHORITY

The amendment is proposed under the Texas Health and Safety Code, TCAA, §382.011, concerning General Powers and Duties, which provides the commission with the authority to establish the level of quality to be maintained in the state's air and the authority to control the quality of the state's air; §382.017, concerning Rules, which provides the commission with the authority to adopt rules consistent with the policy and purposes of the TCAA; and §382.012, concerning State Air Control Plan, which requires the commission to develop plans for protection of the state's air.

The proposed amendment implements the Texas Health and Safety Code, TCAA, §§382.011, 382.012, and 382.017.

§115.10.Definitions.

Unless specifically defined in the Texas Clean Air Act (TCAA) or in the rules of the Texas Natural Resource Conservation Commission (commission), the terms used by the commission have the meanings commonly ascribed to them in the field of air pollution control. In addition to the terms which are defined by the TCAA, the following terms, when used in this chapter, shall have the following meanings, unless the context clearly indicates otherwise. Additional definitions for terms used in this chapter are found in §101.1 of this title (relating to Definitions) and §3.2 of this title (relating to Definitions).

[ (1)

Bakery oven - An oven for baking bread or any other yeast-leavened products.]

(1)

[ (2) ] Beaumont/Port Arthur area - Hardin, Jefferson, and Orange Counties.

(2)

[ (3) ] Capture efficiency - The amount of volatile organic compounds (VOC) collected by a capture system which is expressed as a percentage derived from the weight per unit time of VOC entering a capture system and delivered to a control device divided by the weight per unit time of total VOC generated by a source of VOC.

(3)

[ (4) ] Carbon adsorption system - A carbon adsorber with an inlet and outlet for exhaust gases and a system to regenerate the saturated adsorbent.

(4)

[ (5) ] Component - A piece of equipment, including, but not limited to pumps, valves, compressors, and pressure relief valves, which has the potential to leak VOC.

(5)

[ (6) ] Continuous monitoring - Any monitoring device used to comply with a continuous monitoring requirement of this chapter will be considered continuous if it can be demonstrated that at least 95% of the required data is captured.

(6)

[ (7) ] Covered attainment counties - Anderson, Angelina, Aransas, Atascosa, Austin, Bastrop, Bee, Bell, Bexar, Bosque, Bowie, Brazos, Burleson, Caldwell, Calhoun, Camp, Cass, Cherokee, Colorado, Comal, Cooke, Coryell, De Witt, Delta, Ellis, Falls, Fannin, Fayette, Franklin, Freestone, Goliad, Gonzales, Grayson, Gregg, Grimes, Guadalupe, Harrison, Hays, Henderson, Hill, Hood, Hopkins, Houston, Hunt, Jackson, Jasper, Johnson, Karnes, Kaufman, Lamar, Lavaca, Lee, Leon, Limestone, Live Oak, Madison, Marion, Matagorda, McLennan, Milam, Morris, Nacogdoches, Navarro, Newton, Nueces, Panola, Parker, Polk, Rains, Red River, Refugio, Robertson, Rockwall, Rusk, Sabine, San Jacinto, San Patricio, San Augustine, Shelby, Smith, Somervell, Titus, Travis, Trinity, Tyler, Upshur, Van Zandt, Victoria, Walker, Washington, Wharton, Williamson, Wilson, Wise, and Wood Counties.

(7)

[ (8) ] Dallas/Fort Worth area - Collin, Dallas, Denton, and Tarrant Counties.

(8)

[ (9) ] El Paso area - El Paso County.

(9)

[ (10) ] External floating roof - A cover or roof in an open-top tank which rests upon or is floated upon the liquid being contained and is equipped with a single or double seal to close the space between the roof edge and tank shell. A double seal consists of two complete and separate closure seals, one above the other, containing an enclosed space between them. For the purposes of this chapter (relating to Control of Air Pollution from Volatile Organic Compounds), an [ An ] external floating roof storage tank which is equipped with a self-supporting fixed roof (typically a bolted aluminum geodesic dome) shall be considered to be an internal floating roof storage tank.

[ (11)

Flare - An open combustor without enclosure or shroud which is used as a control device.]

[ (12)

Flexographic printing process - A method of printing in which the image areas are raised above the non-image areas, and the image carrier is made of an elastomeric material.]

(10)

[ (13) ] Fugitive emission - Any VOC entering the atmosphere which could not reasonably pass through a stack, chimney, vent, or other functionally equivalent opening designed to direct or control its flow.

(11)

[ (14) ] Gasoline bulk plant - A gasoline loading and/or unloading facility, excluding marine terminals, having a gasoline throughput less than 20,000 gallons (75,708 liters) per day, averaged over each consecutive 30-day period. A motor vehicle fuel dispensing facility is not a gasoline bulk plant.

(12)

[ (15) ] Gasoline terminal - A gasoline loading and/or unloading facility, excluding marine terminals, having a gasoline throughput equal to or greater than 20,000 gallons (75,708 liters) per day, averaged over each consecutive 30-day period.

(13)

[ (16) ] Houston/Galveston area - Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller Counties.

[ (17)

Independent small business marketer of gasoline - A person engaged in the marketing of gasoline who owns the dispensing equipment at a motor vehicle fuel dispensing facility and receives at least 50% of his annual income from the marketing of gasoline. A person is not an independent small business marketer of gasoline if such person:]

[ (A)

is a refiner; or]

[ (B)

controls (i.e., owns more than 50% of a business or corporation's stock), is controlled by, or is under common control with, a refiner; or]

[ (C)

is otherwise directly or indirectly affiliated with a refiner or with a person who controls, is controlled by, or is under common control with a refiner (unless the sole affiliation is by means of a supply contract or an agreement or contract to use a trademark, trade name, service mark, or other identifying symbol or name owned by such refiner or any such person).]

(14)

[ (18) ] Internal floating cover - A cover or floating roof in a fixed roof tank which rests upon or is floated upon the liquid being contained, and is equipped with a closure seal or seals to close the space between the cover edge and tank shell. For the purposes of this chapter (relating to Control of Air Pollution from Volatile Organic Compounds), an [ An ] external floating roof storage tank which is equipped with a self-supporting fixed roof (typically a bolted aluminum geodesic dome) shall be considered to be an internal floating roof storage tank.

(15)

Liquefied petroleum gas - Any material that is composed predominantly of any of the following hydrocarbons or mixtures of hydrocarbons: propane, propylene, normal butane, isobutane, and butylenes.

(16)

[ (19) ] Leak-free marine vessel - A marine vessel whose cargo tank closures (hatch covers, expansion domes, ullage openings, butterworth covers , and gauging covers) were inspected prior to cargo transfer operations and all such closures were properly secured such that no leaks of liquid or vapors can be detected by sight, sound, or smell. Cargo tank closures shall meet the applicable rules or regulations of the marine vessel's classification society or flag state. Cargo tank pressure/vacuum valves shall be operating within the range specified by the marine vessel's classification society or flag state and seated when tank pressure is less than 80% of set point pressure such that no vapor leaks can be detected by sight, sound, or smell. As an alternative, a marine vessel operated at negative pressure is assumed to be leak-free for the purpose of this standard.

(17)

[ (20) ] Marine loading facility - The loading arm(s), pumps, meters, shutoff valves, relief valves, and other piping and valves that are part of a single system used to fill a marine vessel at a single geographic site. Loading equipment that is physically separate (i.e., does not share common piping, valves, and other loading equipment) is considered to be a separate marine loading facility.

(18)

[ (21) ] Marine loading operation - The transfer of oil, gasoline, or other volatile organic liquids at any affected marine terminal, beginning with the connections made to a marine vessel and ending with the disconnection from the marine vessel.

(19)

[ (22) ] Marine terminal - Any marine facility or structure constructed to load oil, gasoline, or other volatile organic liquid bulk cargo into a marine vessel. A marine terminal consists of one or more marine loading facilities.

(20)

[ (23) ] Natural gas/gasoline processing - A process that extracts condensate from gases obtained from natural gas production and/or fractionates natural gas liquids into component products, such as ethane, propane, butane, and natural gasoline. The following facilities shall be included in this definition if, and only if, located on the same property as a natural gas/gasoline processing operation previously defined: compressor stations, dehydration units, sweetening units, field treatment, underground storage, liquified natural gas units, and field gas gathering systems.

[ (24)

Owner or operator of a motor vehicle fuel dispensing facility (as used in §§115.241 - 115.249 of this title (relating to Control of Vehicle Refueling Emissions (Stage II) at Motor Vehicle Fuel Dispensing Facilities)) - Any person who owns, leases, operates, or controls the motor vehicle fuel dispensing facility.]

[ (25)

Packaging rotogravure printing - Any rotogravure printing upon paper, paper board, metal foil, plastic film, or any other substrate which is, in subsequent operations, formed into packaging products or labels.]

(21)

[ (26) ] Petroleum refinery - Any facility engaged in producing gasoline, kerosene, distillate fuel oils, residual fuel oils, lubricants, or other products through distillation of crude oil, or through the redistillation, cracking, extraction, reforming, or other processing of unfinished petroleum derivatives.

(22)

[ (27) ] Polymer or [ and ] resin manufacturing process - A process that produces any of the following polymers or resins: polyethylene, polypropylene, polystyrene, and styrenebutadiene latex.

(23)

[ (28) ] Printing line - An operation consisting of a series of one or more printing processes and including associated drying areas.

[ (29)

Publication rotogravure printing - Any rotogravure printing upon paper which is subsequently formed into books, magazines, catalogues, brochures, directories, newspaper supplements, or other types of printed materials.]

[ (30)

Rotogravure printing - The application of words, designs, and/or pictures to any substrate by means of a roll printing technique which involves a recessed image area. The recessed area is loaded with ink and pressed directly to the substrate for image transfer.]

[ (31)

Synthetic Organic Chemical Manufacturing Industry (SOCMI) batch distillation operation - A SOCMI noncontinuous distillation operation in which a discrete quantity or batch of liquid feed is charged into a distillation unit and distilled at one time. After the initial charging of the liquid feed, no additional liquid is added during the distillation operation.]

[ (32)

Synthetic Organic Chemical Manufacturing Industry (SOCMI) batch process - Any SOCMI noncontinuous reactor process which is not characterized by steady-state conditions, and in which reactants are not added and products are not removed simultaneously.]

[ (33)

Synthetic Organic Chemical Manufacturing Industry (SOCMI) distillation operation - A SOCMI operation separating one or more feed stream(s) into two or more exit streams, each exit stream having component concentrations different from those in the feed stream(s). The separation is achieved by the redistribution of the components between the liquid and vapor-phase as they approach equilibrium within the distillation unit.]

[ (34)

Synthetic Organic Chemical Manufacturing Industry (SOCMI) distillation unit - A SOCMI device or vessel in which distillation operations occur, including all associated internals (including, but not limited to, trays and packing), accessories (including, but not limited to, reboilers, condensers, vacuum pumps, and steam jets), and recovery devices (such as absorbers, carbon adsorbers, and condensers) which are capable of, and used for, recovering chemicals for use, reuse, or sale.]

[ (35)

Synthetic Organic Chemical Manufacturing Industry (SOCMI) reactor process - A SOCMI unit operation in which one or more chemicals, or reactants other than air, are combined or decomposed in such a way, that their molecular structures are altered and one or more new organic compounds are formed.]

(24)

[ (36) ] Synthetic organic chemical manufacturing process - A process that produces, as intermediates or final products, one or more of the chemicals listed in 40 Code of Federal Regulations 60.489 (effective October 18, 1983) [ Table I of this section ].

(25)

[ (37) ] Tank-truck tank - Any storage tank having a capacity greater than 1,000 gallons, mounted on a tank-truck or trailer. Vacuum trucks used exclusively for maintenance and spill response are not considered to be tank-truck tanks.

(26)

[ (38) ] Transport vessel - Any land-based mode of transportation (truck or rail) that is equipped with a storage tank having a capacity greater than 1,000 gallons which is used [ primarily ] to transport oil, gasoline, or other volatile organic liquid bulk cargo. Vacuum trucks used exclusively for maintenance and spill response are not considered to be transport vessels.

(27)

[ (39) ] True partial pressure - The absolute aggregate partial pressure (psia) of all VOC in a gas stream.

(28)

[ (40) ] Vapor balance system - A system which provides for containment of hydrocarbon vapors by returning displaced vapors from the receiving vessel back to the originating vessel.

[ (41)

Vapor combustor - A partially enclosed combustion device, where the combustion flame may be partially visible, but at no time does the device operate with a fully visible flame. A vapor combustor is used to destroy VOCs to the destruction requirements defined in the applicable emission specifications and control requirements sections of this chapter by smokeless combustion without extracting energy in the form of process heat or steam. Auxiliary fuel and/or a flame air control damping system, which can operate at all times to control the air/fuel mixture to the combustor's flame zone, may be required to ensure smokeless combustion during operation.]

(29)

[ (42) ] Vapor control system or vapor recovery system - Any control system which utilizes vapor collection equipment to route VOC to a control device that reduces VOC emissions.

[ (43)

Vapor recovery system - Any control system which utilizes vapor collection equipment to route VOC to a control device that reduces VOC emissions.]

(30)

[ (44) ] Vapor-tight - Not capable of allowing the passage of gases at the pressures encountered except where other acceptable leak-tight conditions are prescribed in this chapter [ the Regulations ].

(31)

[ (45) ] Waxy, high pour point crude oil - A crude oil with a pour point of 50 degrees Fahrenheit (10 degrees Celsius) or higher as determined by the American Society for Testing and Materials Standard D97-66, "Test for Pour Point of Petroleum Oils."

[ Figure: 30 TAC §115.10(45) ]

This agency hereby certifies that the proposal has been reviewed by legal counsel and found to be within the agency's legal authority to adopt.

Filed with the Office of the Secretary of State, on August 11, 2000.

TRD-200005638

Margaret Hoffman

Director, Environmental Law Division

Texas Natural Resource Conservation Commission

Earliest possible date of adoption: September 24, 2000

For further information, please call: (512) 239-0348


Subchapter B. GENERAL VOLATILE ORGANIC COMPOUND SOURCES

2. VENT GAS CONTROL

30 TAC §§115.120, 115.122, 115.125 - 115.127, 115.129

STATUTORY AUTHORITY

The new section and amendments are proposed under the Texas Health and Safety Code, Texas Clean Air Act (TCAA), §382.011, concerning General Powers and Duties, which provides the commission with the authority to establish the level of quality to be maintained in the state's air and the authority to control the quality of the state's air; §382.017, concerning Rules, which provides the commission with the authority to adopt rules consistent with the policy and purposes of the TCAA; and §382.012, concerning State Air Control Plan, which requires the commission to develop plans for protection of the state's air.

The proposed new section and amendments implement the Texas Health and Safety Code, TCAA, §§382.011, 382.012, and 382.017.

§115.120.Vent Gas Definitions.

The following words and terms, when used in this division, shall have the following meanings, unless the context clearly indicates otherwise. Additional definitions for terms used in this division are found in §115.10 of this title (relating to Definitions), §101.1 of this title (relating to Definitions), and §3.2 of this title (relating to Definitions).

(1)

Bakery oven - An oven for baking bread or any other yeast-leavened products.

(2)

Synthetic Organic Chemical Manufacturing Industry (SOCMI) batch distillation operation - A SOCMI noncontinuous distillation operation in which a discrete quantity or batch of liquid feed is charged into a distillation unit and distilled at one time. After the initial charging of the liquid feed, no additional liquid is added during the distillation operation.

(3)

Synthetic Organic Chemical Manufacturing Industry (SOCMI) batch process - Any SOCMI noncontinuous reactor process which is not characterized by steady-state conditions, and in which reactants are not added and products are not removed simultaneously.

(4)

Synthetic Organic Chemical Manufacturing Industry (SOCMI) distillation operation - A SOCMI operation separating one or more feed stream(s) into two or more exit streams, each exit stream having component concentrations different from those in the feed stream(s). The separation is achieved by the redistribution of the components between the liquid and vapor-phase as they approach equilibrium within the distillation unit.

(5)

Synthetic Organic Chemical Manufacturing Industry (SOCMI) distillation unit - A SOCMI device or vessel in which distillation operations occur, including all associated internals (including, but not limited to, trays and packing), accessories (including, but not limited to, reboilers, condensers, vacuum pumps, and steam jets), and recovery devices (such as absorbers, carbon adsorbers, and condensers) which are capable of, and used for, recovering chemicals for use, reuse, or sale.

(6)

Synthetic Organic Chemical Manufacturing Industry (SOCMI) reactor process - A SOCMI unit operation in which one or more chemicals, or reactants other than air, are combined or decomposed in such a way that their molecular structures are altered and one or more new organic compounds are formed.

§115.122.Control Requirements.

(a)

For all persons in the Beaumont/Port Arthur, Dallas/Fort Worth, El Paso, and Houston/Galveston areas, the following control requirements shall apply . [ : ]

(1)

Any vent gas streams affected by §115.121(a)(1) of this title (relating to Emission Specifications) must be controlled properly with a control efficiency of at least 90% or to a volatile organic compound (VOC) concentration of no more than 20 parts per million by volume (ppmv) (on a dry basis corrected to 3.0% oxygen for combustion devices):

(A) - (B)

(No change.)

(C)

by any other vapor control [ recovery ] system, as defined in §115.10 of this title (relating to Definitions).

(2)

Any vent gas streams affected by §115.121(a)(2) of this title must be controlled properly with a control efficiency of at least 98% or to a VOC concentration of no more than 20 ppmv (on a dry basis corrected to 3.0% oxygen for combustion devices):

(A)

(No change.)

(B)

by any other vapor control [ recovery ] system, as defined in §115.10 of this title.

(3)

For the Dallas/Fort Worth, El Paso, and Houston/Galveston areas, VOC emissions from each bakery with a bakery oven vent gas stream(s) affected by §115.121(a)(3) of this title shall be reduced as follows.

(A)

Each bakery in the Houston/Galveston area with a total weight of VOC emitted from all bakery ovens on the property, when uncontrolled, equal to or greater than 25 tons per calendar year shall ensure that the overall emission reduction from the uncontrolled VOC emission rate of the oven(s) will be [ reduce total VOC emissions by ] at least 80% [ 30% from the bakery's 1990 baseline emissions inventory ] by December 31, 2001 [ May 31, 1996 ].

(B)

Each bakery in the Dallas/Fort Worth area with a total weight of VOC emitted from all bakery ovens on the property, when uncontrolled, equal to or greater than 50 tons per calendar year, shall ensure that the overall emission reduction from the uncontrolled VOC emission rate of the oven(s) will be [ reduce total VOC emissions by ] at least 80% [ from the bakery's 1990 baseline emissions inventory ] by December 31, 2000.

(C)

Each bakery in the Dallas/Fort Worth area with a total weight of VOC emitted from all bakery ovens on the property, when uncontrolled, equal to or greater than 25 tons per calendar year, but less than 50 tons per calendar year, shall reduce total VOC emissions by at least 30% from the bakery's 1990 [ baseline ] emissions inventory in accordance with the schedule specified in §115.129(d) [ §115.129(a)(4) ] of this title (relating to Counties and Compliance Schedules).

(D)

Each bakery in the El Paso area with a total weight of VOC emitted from all bakery ovens on the property, when uncontrolled, equal to or greater than 25 tons per calendar year shall reduce total VOC emissions by at least 30% from the bakery's 1990 [ baseline ] emissions inventory in accordance with the schedule specified in §115.129(e) [ §115.129(a)(5) ] of this title.

(E)

(No change.)

(4)

Any vent gas stream that becomes subject to the provisions of paragraphs (1), (2), or (3) of this subsection by exceeding provisions of §115.127(a) of this title (relating to Exemptions) shall remain subject to the provisions of this subsection, even if throughput or emissions later fall below the exemption limits unless and until emissions are reduced to no more than the controlled emissions level existing before implementation of the project by which throughput or emission rate was reduced to less than the applicable exemption limits in §115.127(a) of this title ; and:

(A)

the project by which throughput or emission rate was reduced is authorized by any permit or permit amendment or standard permit or permit by rule [ standard exemption ] required by Chapter 116 or Chapter 106 of this title (relating to Control of Air Pollution by Permits for New Construction or Modification; and Permits by Rule [ Exemptions from Permitting ]). If a permit by rule [ a standard exemption ] is available for the project, compliance with this subsection must be maintained for 30 days after the filing of documentation of compliance with that permit by rule [ standard exemption ]; or

(B)

if authorization by permit, permit amendment, standard permit, or permit by rule [ standard exemption ] is not required for the project, the owner or [ / ] operator has given the executive director 30 days' notice of the project in writing.

(b)

For all persons in Nueces and Victoria Counties, any vent gas streams affected by §115.121(b) of this title must be controlled properly with a control efficiency of at least 90% or to a VOC concentration of no more than 20 ppmv (on a dry basis corrected to 3.0% oxygen for combustion devices):

(1) - (2)

(No change.)

(3)

by any other vapor control [ recovery ] system, as defined in §115.10 of this title.

(c)

For all persons in Aransas, Bexar, Calhoun, Matagorda, San Patricio, and Travis Counties, the following control requirements shall apply . [ : ]

(1)

Any vent gas streams affected by §115.121(c)(1) of this title must be controlled properly:

(A) - (B)

(No change.)

(C)

by any other vapor control [ recovery ] system, as defined in §115.10 of this title, with a control efficiency of at least 90% or to a VOC concentration of no more than 20 ppmv (on a dry basis corrected to 3.0% oxygen for combustion devices).

(2)

Any vent gas streams affected by §115.121(c)(2) of this title must be controlled properly:

(A)

(No change.)

(B)

by any other vapor control [ recovery ] system, as defined in §115.10 of this title, with a control efficiency of at least 90% or to a VOC concentration of no more than 20 ppmv (on a dry basis corrected to 3.0% oxygen for combustion devices).

(3)

Any vent gas streams affected by §115.121(c)(3) of this title must be controlled properly:

(A)

(No change.)

(B)

by any other vapor control [ recovery ] system, as defined in §115.10 of this title, with a control efficiency of at least 90% or to a VOC concentration of no more than 20 ppmv (on a dry basis corrected to 3.0% oxygen for combustion devices).

(4)

Any vent gas streams affected by §115.121(c)(4) of this title must be controlled properly:

(A)

(No change.)

(B)

by any other vapor control [ recovery ] system, as defined in §115.10 of this title, with a control efficiency of at least 90% or to a VOC concentration of no more than 20 ppmv (on a dry basis corrected to 3.0% oxygen for combustion devices).

§115.125.Testing Requirements.

[ (a) ]

Compliance with the emission specifications, vapor control system efficiency, and certain control requirements and exemption criteria of §§115.121 - 115.123 and 115.127 of this title (relating to Emission Specifications; Control Requirements; Alternate Control Requirements; and Exemptions) [ For the Beaumont/Port Arthur, Dallas/Fort Worth, El Paso, and Houston/Galveston areas, compliance with §115.121(a) of this title (relating to Emission Specifications) ] shall be determined by applying one or more of the following test methods and procedures , as appropriate . [ : ]

(1)

Flow rate. Test Methods 1-4 (40 Code of Federal Regulations (CFR) 60, Appendix A) are used for determining flow rates, as necessary.

(2)

Concentration of volatile organic compounds (VOC).

(A)

Test Method 18 (40 CFR 60, Appendix A) is used for determining gaseous organic compound emissions by gas chromatography.

(B)

Test Method 25 (40 CFR 60, Appendix A) is used for determining total gaseous nonmethane organic emissions as carbon.

(C)

Test Methods 25A or 25B (40 CFR 60, Appendix A) are used for determining total gaseous organic concentrations using flame ionization or nondispersive infrared analysis.

(3)

Performance requirements for flares and vapor combustors.

(A)

[ (1) ] For flares, Test Method 22 (40 CFR [ Code of Federal Regulations ] 60, Appendix A) is used for visual determination of fugitive emissions from material sources and smoke emissions . [ from flares; ]

(B)

[ (2) ] For flares, additional test method requirements are [ for flares ] described in 40 CFR [ Code of Federal Regulations ] 60.18(f) . [ ; ]

(C)

For flares in the Beaumont/Port Arthur, Dallas/Fort Worth, and Houston/Galveston areas, the performance test requirements of 40 CFR 60.18(b) shall apply.

(D)

For vapor combustors, the owner or operator may consider the unit to be a flare and meet the performance test requirements of 40 CFR 60.18(b) rather than the procedures of paragraphs (1) and (2) of this section.

(E)

Compliance with the requirements of 40 CFR 60.18(b) will be considered to demonstrate compliance with the emission specifications and control efficiency requirements of §115.121 and §115.122 of this title.

[ (3)

Test Methods 1-4 (40 Code of Federal Regulations 60, Appendix A) for determining flow rate, as necessary;]

[ (4)

Test Method 18 (40 Code of Federal Regulations 60, Appendix A) for determining gaseous organic compound emissions by gas chromatography;]

[ (5)

Test Method 25 (40 Code of Federal Regulations 60, Appendix A) for determining total gaseous nonmethane organic emissions as carbon;]

[ (6)

Test Methods 25A or 25B (40 Code of Federal Regulations 60, Appendix A) for determining total gaseous organic concentrations using flame ionization or nondispersive infrared analysis; or]

(4)

[ (7) ] Minor modifications. Minor [ minor ] modifications to these test methods may be used, if approved by the executive director.

(5)

Alternate test methods. Test methods other than those specified in paragraphs (1) - (3) of this section may be used if validated by 40 CFR 63, Appendix A, Test Method 301 (effective December 29, 1992). For the purposes of this paragraph, substitute "executive director" each place that Test Method 301 references "administrator."

[ (b)

For Nueces and Victoria Counties, compliance with §115.121(b) of this title shall be determined by applying the following test methods, as appropriate:]

[ (1)

Test Method 22 (40 Code of Federal Regulations 60, Appendix A) for visual determination of fugitive emissions from material sources and smoke emissions from flares;]

[ (2)

additional test method requirements for flares described in 40 Code of Federal Regulations 60.18(f);]

[ (3)

Test Methods 1-4 (40 Code of Federal Regulations 60, Appendix A) for determining flow rate, as necessary;]

[ (4)

Test Method 18 (40 Code of Federal Regulations 60, Appendix A) for determining gaseous organic compound emissions by gas chromatography;]

[ (5)

Test Method 25 (40 Code of Federal Regulations 60, Appendix A) for determining total gaseous nonmethane organic emissions as carbon;]

[ (6)

Test Methods 25A or 25B (40 Code of Federal Regulations 60, Appendix A) for determining total gaseous organic concentrations using flame ionization or nondispersive infrared analysis; or]

[ (7)

minor modifications to these test methods approved by the executive director.]

§115.126.Monitoring and Recordkeeping Requirements.

[ (a) ]

The [ For the Beaumont/Port Arthur, Dallas/Fort Worth, El Paso, and Houston/ Galveston areas, the ] owner or operator of any facility which emits volatile organic compounds (VOC) through a stationary vent in Aransas, Bexar, Calhoun, Matagorda, Nueces, San Patricio, Travis, and Victoria Counties or in the Beaumont/Port Arthur, Dallas/Fort Worth, El Paso, and Houston/Galveston areas shall maintain the following information [ records ] at the facility for at least two years . The owner or operator [ and ] shall make the information [ such records ] available upon request to representatives of the executive director, EPA, or any local air pollution control agency having jurisdiction in the area [ upon request ]. [ These records shall include, but not be limited to, the following. ]

(1)

Vapor control systems. For vapor control systems used to control emissions in Victoria County and in the Beaumont/Port Arthur, Dallas/Fort Worth, El Paso, and Houston/Galveston areas from vents subject to [ Records for each vent required to satisfy ] the provisions of §115.121 [ §115.121(a)(1)-(3) ] of this title (relating to Emission Specifications) , records of appropriate parameters to demonstrate compliance, [ shall be sufficient to demonstrate the proper functioning of applicable control equipment to design specifications, ] including:

(A)

continuous monitoring and recording of :

(i)

the exhaust gas temperature immediately downstream of a direct-flame incinerator;

(ii)

[ (B) ] [ continuous monitoring of ] the inlet and outlet gas temperatures [ upstream and downstream ] of a catalytic incinerator or chiller;

(iii)

[ (C) ] [ continuous monitoring of ] the exhaust gas VOC concentration of any carbon adsorption system, as defined in §101.1 of this title (relating to Definitions); and

(iv)

the exhaust gas temperature immediately downstream of a vapor combustor. Alternatively, the owner or operator of a vapor combustor may consider the unit to be a flare and meet the requirements specified in 40 Code of Federal Regulations (CFR) 60.18(b) and Chapter 111 of this title (relating to Control of Air Pollution from Visible Emissions and Particulate Matter) for flares;

(B)

in the Beaumont/Port Arthur, Dallas/Fort Worth, and Houston/Galveston areas, the requirements specified in 40 CFR 60.18(b) and Chapter 111 of this title for flares; and

(C)

for vapor control systems other than those specified in subparagraphs (A) and (B) of this paragraph, records of appropriate operating parameters .

(2) [ (D) ]

Test results. A record of the results of any testing [ of any vent ] conducted [ at an affected facility ] in accordance with [ the provisions specified in ] §115.125 [ §115.125(a) ] of this title (relating to Testing Requirements).

(3)

[ (2) ] Records for exempted vents. Records for each vent exempted from control requirements in accordance with §115.127 [ §115.127(a) ] of this title (relating to Exemptions) shall be sufficient to demonstrate compliance with applicable exemption limits, including:

(A)

the pounds of ethylene emitted per 1,000 pounds of low-density polyethylene produced;

(B)

the combined weight of VOC of each vent gas stream on a daily basis; and

(C)

the concentration [ true partial pressure ] of VOC in each vent gas stream on a daily basis . [ ; and ]

[ (D)

the results of any testing of any vent conducted at an affected facility in accordance with the provisions specified in this section.]

(4)

[ (3) ] Alternative records for exempted vents. As an alternative to the requirements of paragraph (3) [ (2) ] of this section [ subsection ], records for each vent exempted from control requirements in accordance with §115.127 [ §115.127(a) ] of this title and having a VOC emission rate or concentration less than 50% of the applicable exemption limits at maximum actual operating conditions shall be sufficient to demonstrate continuous compliance with the applicable exemption limit. These records shall include complete information from either test results or appropriate calculations which clearly documents that the emission characteristics at maximum actual operating conditions are less than 50% of the applicable exemption limits. This documentation shall include the operating parameter levels that occurred during any testing, and the maximum levels feasible for the process.

(5)

[ (4) ] Bakeries. For bakeries subject to [ affected by ] §115.122(a)(3)(A) - (B) of this title (relating to Control Requirements), the following additional requirements apply.

(A)

The owner or operator of each bakery in the Houston/Galveston area with a total weight of VOC emitted from all bakery ovens on the property, when uncontrolled, equal to or greater than 25 tons per calendar year, shall submit a control plan no later than March 31, 2001, to the executive director, the appropriate regional office, and any local air pollution control program with jurisdiction. The plan shall demonstrate that the overall emission reduction from the uncontrolled VOC emission rate of the oven(s) will be at least 80% by December 31, 2001. At a minimum, the control plan shall include the emission point number (EPN) and the facility identification number (FIN) of each bakery oven and any associated control device, a plot plan showing the location, EPN, and FIN of each bakery oven and any associated control device, and the 2000 VOC emission rates (consistent with the bakery's 2000 emissions inventory). The projected 2002 VOC emission rates shall be calculated in a manner consistent with the 2000 emissions inventory.

[ (A)

The owner or operator of each bakery in the Dallas/Fort Worth area with a total weight of VOC emitted from all bakery ovens on the property, when uncontrolled, equal to or greater than 50 tons per calendar year, shall submit an initial control plan no later than March 31, 2000, to the executive director, the appropriate regional office, and any local air pollution control program with jurisdiction which demonstrates that the overall reduction of VOC emissions from the bakery's 1990 baseline emissions inventory will be at least 80% by December 31, 2000. At a minimum, the control plan shall include the emission point number (EPN) and the facility identification number (FIN) of each bakery oven and any associated control device, a plot plan showing the location, EPN, and FIN of each bakery oven and any associated control device, and the 1990 VOC emission rates (consistent with the bakery's 1990 emissions inventory). The projected 2000 VOC emission rates shall be calculated in a manner consistent with the 1990 emissions inventory.]

[ (B)

In order to document continued compliance with §115.122(a)(3) of this title, the owner or operator of each bakery specified in clauses (i) and (ii) of this subparagraph shall submit an annual report no later than March 31 of each year to the executive director, the appropriate regional office, and any local air pollution control program with jurisdiction which demonstrates the overall reduction of VOC emissions from the bakery's 1990 baseline emissions inventory during the preceding calendar year. At a minimum, the report shall include the EPN and FIN of each bakery oven and any associated control device, a plot plan showing the location, EPN, and FIN of each bakery oven and any associated control device, and the VOC emission rates. The emission rates for the proceeding calendar year shall be calculated in a manner consistent with the 1990 emissions inventory.]

[ (i)

The owner or operator of each bakery in the Houston/Galveston area with VOC emissions, when uncontrolled, equal to or greater than 25 tons per calendar year, shall submit an annual report which demonstrates that the overall reduction of VOC emissions from the bakery's 1990 baseline emissions inventory during the preceding calendar year is at least 30% after May 31, 1996.]

[ (ii)

Beginning in 2002, the owner or operator of each bakery in the Dallas/Fort Worth area with VOC emissions, when uncontrolled, equal to or greater than 50 tons per calendar year, shall submit an annual report which demonstrates that the overall reduction of VOC emissions from the bakery's 1990 baseline emissions inventory during the preceding calendar year is at least 80% after December 31, 2000.]

(B)

[ (C) ] All representations in [ initial ] control plans [ and annual reports ] become enforceable conditions. It shall be unlawful for any person to vary from such representations if the variation will cause a change in the identity of the specific emission sources being controlled or the method of control of emissions unless the owner or operator of the bakery submits a revised control plan to the executive director, the appropriate regional office, and any local air pollution control program with jurisdiction within 30 days of the change. All control plans [ and reports ] shall include documentation that the overall emission reduction from the uncontrolled VOC emission rate of the bakery's oven(s) [ of VOC emissions from the bakery's 1990 baseline emissions inventory ] continues to be at least the specified percentage reduction [ 30% ]. The emission rates shall be calculated in a manner consistent with the most recent [ 1990 ] emissions inventory.

(6)

[ (5) ] Bakeries (contingency measures). For bakeries subject to [ affected by ] §115.122(a)(3)(C) and (D) of this title, the following additional requirements apply.

(A)

No later than six months after the commission publishes notification in the Texas Register as specified in §115.129(d) or (e) [ §115.129(a)(4) ] of this title (relating to Counties and Compliance Schedules), the owner or operator of each bakery shall submit an initial control plan to the executive director, the appropriate regional office, and any local air pollution control program with jurisdiction which demonstrates that the overall reduction of VOC emissions from the bakery's 1990 [ baseline ] emissions inventory will be at least 30%. At a minimum, the control plan shall include the EPN and the FIN of each bakery oven and any associated control device, a plot plan showing the location, EPN, and FIN of each bakery oven and any associated control device, and the 1990 VOC emission rates (consistent with the bakery's 1990 emissions inventory). The projected VOC emission rates shall be calculated in a manner consistent with the 1990 emissions inventory.

(B)

In order to document continued compliance with §115.122(a)(3) of this title, the owner or operator of each bakery shall submit an annual report no later than March 31 of each year to the executive director, the appropriate regional office, and any local air pollution control program with jurisdiction which demonstrates that the overall reduction of VOC emissions from the bakery's 1990 [ baseline ] emissions inventory during the preceding calendar year is at least 30%. At a minimum, the report shall include the EPN and FIN of each bakery oven and any associated control device, a plot plan showing the location, EPN, and FIN of each bakery oven and any associated control device, and the VOC emission rates. The emission rates for the proceeding calendar year shall be calculated in a manner consistent with the 1990 emissions inventory.

(C)

All representations in [ initial ] control plans and annual reports become enforceable conditions. It shall be unlawful for any person to vary from such representations if the variation will cause a change in the identity of the specific emission sources being controlled or the method of control of emissions unless the owner or operator of the bakery submits a revised control plan to the executive director, the appropriate regional office, and any local air pollution control program with jurisdiction within 30 days of the change. All control plans and reports shall include documentation that the overall reduction of VOC emissions from the bakery's 1990 [ baseline ] emissions inventory continues to be at least 30%. The emission rates shall be calculated in a manner consistent with the 1990 emissions inventory.

(7)

[ (6) ] Additional flare requirements. The owner or operator of a facility that uses a flare to meet the requirements of §115.122(a)(2) of this title shall install, calibrate, maintain, and operate according to the manufacturer's specifications, a heat-sensing device, such as an ultraviolet beam sensor or thermocouple, at the pilot light to indicate continuous presence of a flame.

[ (b)

For Victoria County, the owner or operator of any facility which emits VOC through a stationary vent shall maintain records at the facility for at least two years and shall make such records available to representatives of the executive director, EPA, or any local air pollution control agency having jurisdiction in the area upon request. These records shall include, but not be limited to, the following. ]

[ (1)

Records for each vent required to satisfy the provisions of §115.121(b) of this title shall be sufficient to demonstrate the proper functioning of applicable control equipment to design specifications, including:]

[ (A)

continuous monitoring of the exhaust gas temperature immediately downstream of a direct-flame incinerator;]

[ (B)

continuous monitoring of temperatures upstream and downstream of a catalytic incinerator or chiller;]

[ (C)

continuous monitoring of the exhaust gas VOC concentration of any carbon adsorption system, as defined in §101.1 of this title;]

[ (D)

the results of any testing of any vent conducted at an affected facility in accordance with the provisions specified in §115.125(b) of this title.]

[ (2)

Records for each vent exempted from control requirements in accordance with §115.127(b) of this title shall be sufficient to demonstrate compliance with applicable exemption limits, including:]

[ (A)

the pounds of ethylene emitted per 1,000 pounds of low-density polyethylene produced;]

[ (B)

the combined weight of VOC of each vent gas stream on a daily basis;]

[ (C)

the true partial pressure of VOC in each vent gas stream on a daily basis; and]

[ (D)

the results of any testing of any vent conducted at an affected facility in accordance with the provisions specified in this section.]

[ (3)

As an alternative to the requirements of paragraph (2) of this subsection, records for each vent exempted from control requirements in accordance with §115.127(b) of this title and having a VOC emission rate or concentration less than 50% of the applicable exemption limits at maximum actual operating conditions shall be sufficient to demonstrate continuous compliance with the applicable exemption limit. These records shall include complete information from either test results or appropriate calculations which clearly documents that the emission characteristics at maximum actual operating conditions are less than 50% of the applicable exemption limits. This documentation shall include the operating parameter levels that occurred during any testing, and the maximum levels feasible for the process.]

§115.127.Exemptions.

(a)

For all persons in the Beaumont/Port Arthur, Dallas/Fort Worth, El Paso, and Houston/Galveston areas, the following exemptions apply.

(1)

(No change.)

(2)

The following vent gas streams are exempt from the requirements of §115.121(a)(1) of this title:

(A)

(No change.)

(B)

a vent gas stream specified in §115.121(a)(1) of this title with a concentration of VOC less than 612 parts per million by volume (ppmv) [ 0.009 pounds per square inch absolute (psia) true partial pressure (612 parts per million (ppm)) ];

(C)

until April 15, 2001, for facilities which have been assigned the code number 26 as described in the document Standard Industrial Classification (SIC) Manual, 1972, as amended by the 1977 Supplement, a vent gas stream specified in §115.121(a)(1) of this title with a concentration of VOC less than 30,000 ppmv [ 0.44 psia true partial pressure (30,000 ppm) ];

(D) - (E)

(No change.)

(3)

The following vent gas streams are exempt from the requirements of §115.121(a)(2)(B) - (E) of this title:

(A)

(No change.)

(B)

a vent gas stream from any air oxidation synthetic organic chemical manufacturing process with a concentration of VOC less than 612 ppmv [ 0.009 pounds psia true partial pressure (612 ppm)) ]; and

(C)

a vent gas stream from any liquid phase polypropylene manufacturing process, any liquid phase slurry high-density polyethylene manufacturing process, and any continuous polystyrene manufacturing process with a concentration of VOC less than 408 ppmv [ 0.006 psia true partial pressure (408 ppm) ].

(4)

For synthetic organic chemical manufacturing industry (SOCMI) reactor processes and distillation operations:

(A) - (B)

(No change.)

(C)

Any reactor process or distillation operation vent gas stream with a flow rate less than 0.011 standard cubic meters per minute or a VOC concentration less than 500 ppmv [ parts per million by volume ] is exempt from the requirements of §115.121(a)(2)(A) of this title.

(D) - (E)

(No change.)

(5) - (7)

(No change.)

(8)

As an alternative to complying with the requirements of this division (relating to Vent Gas Control) (or, in the case of bakeries, as an alternative to complying with the requirements of §115.121(a)(1) and §115.122(a)(1) of this title) for a source that is addressed by a Chapter 115 contingency rule (i.e., one in which Chapter 115 requirements are triggered for that source by the commission publishing notification in the Texas Register that implementation of the contingency rule is necessary), the owner or operator of that source may instead choose to comply with the requirements of the contingency rule as though the contingency rule already had been implemented for that source. The owner or operator of each source choosing this option shall submit written notification to the executive director and any local air pollution control program with jurisdiction. When the executive director and the local program (if any) receive such notification, the source will then be considered subject to the contingency rule as though the contingency rule already had been implemented for that source.

(b)

For all persons in Nueces and Victoria Counties, the following exemptions apply.

(1)

(No change.)

(2)

The following vent gas streams are exempt from the requirements of §115.121(b) of this title:

(A)

(No change.)

(B)

a vent gas stream with a concentration of the VOC or classes of compounds specified in §115.121(b)(2) and (3) of this title less than 30,000 ppmv [ 0.44 psia true partial pressure (30,000 ppm) ].

(3) - (4)

(No change.)

(c)

For all persons in Aransas, Bexar, Calhoun, Matagorda, San Patricio, and Travis Counties, the following exemptions apply.

(1)

The following vent gas streams are exempt from the requirements of §115.121(c)(1) of this title:

(A) - (B)

(No change.)

(C)

a vent gas stream having a concentration of the VOC specified in §115.121(c)(1)(B) and (C) of this title less than 30,000 ppmv [ 0.44 psia true partial pressure (30,000 ppm) ].

(2) - (4)

(No change.)

§115.129.Counties and Compliance Schedules.

(a)

The owner or operator of each vent gas stream in Aransas, Bexar, Brazoria, Calhoun, Chambers, Collin, Dallas, Denton, El Paso, Fort Bend, Galveston, Hardin, Harris, Jefferson, Liberty, Matagorda, Montgomery, Nueces, Orange, San Patricio, Tarrant, Travis, Victoria, and Waller Counties shall continue to comply with this division (relating to Vent Gas Control) as required by §115.930 of this title (relating to Compliance Dates). [ All affected persons in the Beaumont/Port Arthur, Dallas/Fort Worth, El Paso, and Houston/Galveston areas shall be in compliance with this undesignated head (relating to Vent Gas Control) in accordance with the following schedules: ]

[ (1)

All affected synthetic organic chemical manufacturing industry reactor process or distillation operations in Brazoria, Chambers, Collin, Dallas, Denton, El Paso, Fort Bend, Galveston, Hardin, Harris, Jefferson, Liberty, Montgomery, Orange, Tarrant, and Waller Counties shall be in compliance with §115.121(a)(2)(A) of this title (relating to Emission Specifications) as soon as practicable, but no later than November 15, 1996.]

(b)

[ (2) ] The owner or operator of each bakery [ All affected bakeries ] in Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller Counties shall comply [ be in compliance ] with §§115.121(a)(3), 115.122(a)(3), and 115.126(5) [ 115.126(a)(4), and 115.127(a)(5) ] of this title (relating to Emission Specifications; Control Requirements; and Monitoring and Recordkeeping Requirements [ ; and Exemptions ]) as soon as practicable, but no later than December 31, 2001 [ May 31, 1996 ].

(c)

[ (3) ] The owner or operator of each bakery [ All bakeries ] in Collin, Dallas, Denton, and Tarrant Counties subject to [ affected by ] §115.122(a)(3)(B) of this title shall comply [ be in compliance ] with §§115.121(a)(3), 115.122(a)(3), and 115.126(5) [ 115.126(a)(4), and 115.127(a)(5) ] of this title as soon as practicable, but no later than December 31, 2000 [ May 31, 1996 ].

(d)

[ (4) ] The owner or operator of each bakery [ All bakeries ] in Collin, Dallas, Denton, and Tarrant Counties subject to [ affected by ] §115.122(a)(3)(C) of this title shall comply [ be in compliance ] with §§115.121(a)(3), 115.122(a)(3)(C), and 115.126(6) [ 115.126(a)(5), and 115.127(a)(5) ] of this title as soon as practicable, but no later than one year, after the commission publishes notification in the Texas Register of its determination that this contingency rule is necessary as a result of failure to attain the national ambient air quality standard (NAAQS) for ozone by the attainment deadline or failure to demonstrate reasonable further progress as set forth in the FCAA [ 1990 Amendments to the Federal Clean Air Act (FCAA) ], §172(c)(9).

(e)

[ (5) ] The owner or operator of each bakery [ All bakeries ] in El Paso County subject to [ affected by ] §115.122(a)(3)(D) of this title shall comply [ be in compliance ] with §§115.121(a)(3), 115.122(a)(3)(D), and 115.126(6) [ 115.126(a)(5), and 115.127(a)(5) ] of this title as soon as practicable, but no later than one year, after the commission publishes notification in the Texas Register of its determination that this contingency rule is necessary as a result of failure to attain the NAAQS for ozone by the attainment deadline or failure to demonstrate reasonable further progress as set forth in [ the 1990 Amendments to ] the FCAA, §172(c)(9).

(f)

The owner or operator of each flare in Brazoria, Chambers, Collin, Dallas, Denton, Fort Bend, Galveston, Hardin, Harris, Jefferson, Liberty, Montgomery, Orange, Tarrant, and Waller Counties which is used to comply with the requirements of §115.121 and/or §115.122 of this title shall comply with §115.125(3)(C) and §115.126(1)(B) of this title (relating to Testing Requirements; and Monitoring and Recordkeeping Requirements) as soon as practicable, but no later than December 31, 2001.

This agency hereby certifies that the proposal has been reviewed by legal counsel and found to be within the agency's legal authority to adopt.

Filed with the Office of the Secretary of State, on August 11, 2000.

TRD-200005637

Margaret Hoffman

Director, Environmental Law Division

Texas Natural Resource Conservation Commission

Earliest possible date of adoption: September 24, 2000

For further information, please call: (512) 239-0348


6. BATCH PROCESSES

30 TAC §§115.161, 115.162, 115.164 - 115.167, 115.169

STATUTORY AUTHORITY

The amendments are proposed under the Texas Health and Safety Code, Texas Clean Air Act, (TCAA), §382.011, concerning General Powers and Duties, which provides the commission with the authority to establish the level of quality to be maintained in the state's air and the authority to control the quality of the state's air; §382.017, concerning Rules, which provides the commission with the authority to adopt rules consistent with the policy and purposes of the TCAA; and §382.012, concerning State Air Control Plan, which requires the commission to develop plans for protection of the state's air.

The amendments implement the Texas Health and Safety Code, TCAA, §§382.011, 382.012, and 382.017.

§115.161.Applicability.

(a)

The provisions of §§115.162 - 115.167 of this title (relating to Control Requirements; Alternate Control Requirements; Determination of Emissions and Flow Rates; Approved Test Methods and Testing Requirements; Monitoring and Recordkeeping Requirements; and Exemptions) apply to vent gas streams at batch process operations in the Beaumont/Port Arthur and Houston/Galveston areas [ area ], as defined in §115.10 of this title (relating to Definitions), under the following Standard Industrial Classification (SIC) codes:

(1) - (7)

(No change.)

(b)

(No change.)

§115.162.Control Requirements.

The owner or operator of each batch process operation in the Beaumont/Port Arthur and Houston/Galveston areas [ area ] shall comply with the following control requirements.

(1) - (3)

(No change.)

§115.164.Determination of Emissions and Flow Rates.

The owner or operator of each batch process operation in the Beaumont/Port Arthur and Houston/Galveston areas [ area ] shall determine the mass emissions and flow rates as follows.

(1) - (2)

(No change.)

§115.165.Approved Test Methods and Testing Requirements.

The owner or operator of each batch process operation in the Beaumont/Port Arthur and Houston/Galveston areas [ area ] shall comply with the following.

(1) - (2)

(No change.)

§115.166.Monitoring and Recordkeeping Requirements.

The owner or operator of each batch process operation in the Beaumont/Port Arthur and Houston/Galveston areas [ area ] shall maintain the following information for at least two years at the plant, as defined by its air quality account number. The owner or operator shall make the information available upon request to representatives of the executive director, EPA, or any local air pollution control agency having jurisdiction in the area:

(1)

Vapor control systems. For vapor control systems used to control emissions from batch process [ volatile organic compounds (VOC) transfer ] operations, records of appropriate parameters to demonstrate compliance, including:

(A)

continuous monitoring and recording of:

(i) - (ii)

(No change.)

(iii)

for an absorber, either:

(I)

(No change.)

(II)

the concentration level of volatile organic compounds (VOC) [ VOC ] exiting the recovery device based on a detection principle such as infrared, photoionization, or thermal conductivity;

(iv) - (vii)

(No change.)

(B) - (C)

(No change.)

(2) - (3)

(No change.)

§115.167.Exemptions.

The following exemptions apply [ in the Beaumont/Port Arthur area ].

(1)

Batch process operations at an account which has total volatile organic compound (VOC) emissions (determined before control but after the last recovery device) of less than the following rates [ 100 tons per year ] from all stationary emission sources included in the account are exempt from the requirements of this division (relating to Batch Processes), except for §115.161(b) of this title (relating to Applicability) : [ . ]

(A)

100 tons per year (tpy) in the Beaumont/Port Arthur area; and

(B)

25 tpy in the Houston/Galveston area.

(2)

The following are exempt from the requirements of this division, except for §115.164 and §115.166(2) and (3) of this title (relating to Determination of Emissions and Flow Rates; and Monitoring and Recordkeeping Requirements):

(A) - (B)

(No change.)

§115.169.Counties and Compliance Schedules.

(a)

The owner or operator of each batch process operation in Hardin, Jefferson, and Orange Counties shall be in compliance with this division (relating to Batch Processes) as soon as practicable, but no later than December 31, 2001. All batch process operations subject to this division in Hardin, Jefferson, and Orange Counties shall continue to comply with the requirements of Division 2 of this subchapter (relating to Vent Gas Control) until these batch process operations are in compliance with the requirements of this division.

(b)

The owner or operator of each batch process operation in Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller Counties shall be in compliance with this division (relating to Batch Processes) as soon as practicable, but no later than December 31, 2002. All batch process operations subject to this division in Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller Counties shall continue to comply with the requirements of Division 2 of this subchapter (relating to Vent Gas Control) until these batch process operations are in compliance with the requirements of this division.

This agency hereby certifies that the proposal has been reviewed by legal counsel and found to be within the agency's legal authority to adopt.

Filed with the Office of the Secretary of State, on August 11, 2000.

TRD-200005636

Margaret Hoffman

Director, Environmental Law Division

Texas Natural Resource Conservation Commission

Earliest possible date of adoption: September 24, 2000

For further information, please call: (512) 239-0348


Subchapter C. VOLATILE ORGANIC COMPOUND TRANSFER OPERATIONS

1. LOADING AND UNLOADING OF VOLATILE ORGANIC COMPOUNDS

30 TAC §§115.211, 115.212, 115.216

STATUTORY AUTHORITY

The amendments are proposed under the Texas Health and Safety Code, Texas Clean Air Act (TCAA), §382.011, concerning General Powers and Duties, which provides the commission with the authority to establish the level of quality to be maintained in the state's air and the authority to control the quality of the state's air; §382.017, concerning Rules, which provides the commission with the authority to adopt rules consistent with the policy and purposes of the TCAA; and §382.012, concerning State Air Control Plan, which requires the commission to develop plans for protection of the state's air.

The proposed amendments implement the Texas Health and Safety Code, TCAA, §§382.011, 382.012, and 382.017.

§115.211.Emission Specifications.

The owner or operator of each gasoline terminal [ and gasoline bulk plant ] in the covered attainment counties and in the Beaumont/Port Arthur, Dallas/Fort Worth, El Paso, and Houston/Galveston areas, as defined in §115.10 of this title (relating to Definitions), shall ensure that volatile organic compound (VOC) emissions from the vapor control system vent at gasoline terminals do not exceed the following rates:

(1) - (2)

(No change.)

§115.212.Control Requirements.

(a)

The owner or operator of each volatile organic compound (VOC) transfer operation, transport vessel, and marine vessel in the Beaumont/Port Arthur, Dallas/Fort Worth, El Paso, and Houston/Galveston areas shall comply with the following control requirements.

(1) - (2)

(No change.)

(3)

Leak-free requirements. All land-based [ loading and unloading of ] VOC transfer to or from transport vessels shall be conducted such that:

(A) - (E)

(No change.)

(4) - (7)

(No change.)

(b)

The owner or operator of each land-based VOC transfer operation and transport vessel in the covered attainment counties shall comply with the following control requirements.

(1) - (2)

(No change.)

(3)

Leak-free requirements. All land-based [ loading and unloading of ] VOC transfer to or from transport vessels shall be conducted such that:

(A) - (E)

(No change.)

(4) - (5)

(No change.)

§115.216.Monitoring and Recordkeeping Requirements.

The owner or operator of each volatile organic compound (VOC) loading or unloading operation in the covered attainment counties or in the Beaumont/Port Arthur, Dallas/Fort Worth, El Paso, and Houston/Galveston areas shall maintain the following information for at least two years at the plant, as defined by its air quality account number. The owner or operator shall make the information available upon request to representatives of the executive director, EPA, or any local air pollution control agency having jurisdiction in the area.

(1) - (2)

(No change.)

(3)

Land-based VOC transfer to or from transport vessels.

(A)

A daily record of:

(i)

the identification number of each tank-truck tank for which annual leak testing is required under §115.214(a)(1)(C) or (b)(1)(C) of this title (relating to Inspection Requirements) ;

(ii)

(No change.)

(iii)

the date of the last leak testing of each tank-truck tank as required by §115.214(a)(1)(C) or (b)(1)(C) of this title [ (relating to Inspection Requirements) ].

(B) - (E)

(No change.)

(4)

(No change.)

This agency hereby certifies that the proposal has been reviewed by legal counsel and found to be within the agency's legal authority to adopt.

Filed with the Office of the Secretary of State, on August 11, 2000.

TRD-200005635

Margaret Hoffman

Director, Environmental Law Division

Texas Natural Resource Conservation Commission

Earliest possible date of adoption: September 24, 2000

For further information, please call: (512) 239-0348


4. CONTROL OF VEHICLE REFUELING EMISSIONS (STAGE II) AT MOTOR VEHICLE FUEL DISPENSING FACILITIES

30 TAC §115.240

STATUTORY AUTHORITY

The new section is proposed under the Texas Health and Safety Code, Texas Clean Air Act (TCAA), §382.011, concerning General Powers and Duties, which provides the commission with the authority to establish the level of quality to be maintained in the state's air and the authority to control the quality of the state's air; §382.017, concerning Rules, which provides the commission with the authority to adopt rules consistent with the policy and purposes of the TCAA; and §382.012, concerning State Air Control Plan, which requires the commission to develop plans for protection of the state's air.

The proposed new section implements the Texas Health and Safety Code, TCAA, §§382.011, 382.012, and 382.017.

§115.240.Stage II Vapor Recovery Definitions.

The following words and terms, when used in this division, shall have the following meanings, unless the context clearly indicates otherwise. Additional definitions for terms used in this division are found in §115.10 of this title (relating to Definitions), §101.1 of this title (relating to Definitions), and §3.2 of this title (relating to Definitions).

(1)

Independent small business marketer of gasoline - A person engaged in the marketing of gasoline who owns the dispensing equipment at a motor vehicle fuel dispensing facility and receives at least 50% of his annual income from the marketing of gasoline. A person is not an independent small business marketer of gasoline if such person:

(A)

is a refiner; or

(B)

controls (i.e., owns more than 50% of a business or corporation's stock), is controlled by, or is under common control with, a refiner; or

(C)

is otherwise directly or indirectly affiliated with a refiner or with a person who controls, is controlled by, or is under common control with a refiner (unless the sole affiliation is by means of a supply contract or an agreement or contract to use a trademark, trade name, service mark, or other identifying symbol or name owned by such refiner or any such person).

(2)

Owner or operator of a motor vehicle fuel dispensing facility - Any person who owns, leases, operates, or controls the motor vehicle fuel dispensing facility.

This agency hereby certifies that the proposal has been reviewed by legal counsel and found to be within the agency's legal authority to adopt.

Filed with the Office of the Secretary of State, on August 11, 2000.

TRD-200005634

Margaret Hoffman

Director, Environmental Law Division

Texas Natural Resource Conservation Commission

Earliest possible date of adoption: September 24, 2000

For further information, please call: (512) 239-0348


Subchapter E. SOLVENT-USING PROCESS

3. FLEXOGRAPHIC AND ROTOGRAVURE PRINTING

30 TAC §115.430

STATUTORY AUTHORITY

The new section is proposed under the Texas Health and Safety Code, Texas Clean Air Act (TCAA), §382.011, concerning General Powers and Duties, which provides the commission with the authority to establish the level of quality to be maintained in the state's air and the authority to control the quality of the state's air; §382.017, concerning Rules, which provides the commission with the authority to adopt rules consistent with the policy and purposes of the TCAA; and §382.012, concerning State Air Control Plan, which requires the commission to develop plans for protection of the state's air.

The proposed new section implements the Texas Health and Safety Code, TCAA, §§382.011, 382.012, and 382.017.

§115.430.Flexographic and Rotogravure Printing Definitions.

The following words and terms, when used in this division, shall have the following meanings, unless the context clearly indicates otherwise. Additional definitions for terms used in this division are found in §115.10 of this title (relating to Definitions), §101.1 of this title (relating to Definitions), and §3.2 of this title (relating to Definitions).

(1)

Flexographic printing process - A method of printing in which the image areas are raised above the non-image areas, and the image carrier is made of an elastomeric material.

(2)

Packaging rotogravure printing - Any rotogravure printing upon paper, paper board, metal foil, plastic film, or any other substrate which is, in subsequent operations, formed into packaging products or labels.

(3)

Publication rotogravure printing - Any rotogravure printing upon paper which is subsequently formed into books, magazines, catalogues, brochures, directories, newspaper supplements, or other types of printed materials.

(4)

Rotogravure printing - The application of words, designs, and/or pictures to any substrate by means of a roll printing technique which involves a recessed image area. The recessed area is loaded with ink and pressed directly to the substrate for image transfer.

This agency hereby certifies that the proposal has been reviewed by legal counsel and found to be within the agency's legal authority to adopt.

Filed with the Office of the Secretary of State, on August 11, 2000.

TRD-200005633

Margaret Hoffman

Director, Environmental Law Division

Texas Natural Resource Conservation Commission

Earliest possible date of adoption: September 24, 2000

For further information, please call: (512) 239-0348


4. OFFSET LITHOGRAPHIC PRINTING

30 TAC §115.449

STATUTORY AUTHORITY

The amendment is proposed under the Texas Health and Safety Code, Texas Clean Air Act (TCAA), §382.011, concerning General Powers and Duties, which provides the commission with the authority to establish the level of quality to be maintained in the state's air and the authority to control the quality of the state's air; §382.017, concerning Rules, which provides the commission with the authority to adopt rules consistent with the policy and purposes of the TCAA; and §382.012, concerning State Air Control Plan, which requires the commission to develop plans for protection of the state's air.

The proposed amendment implements the Texas Health and Safety Code, TCAA, §§382.011, 382.012, and 382.017.

§115.449.Counties and Compliance Schedules.

(a) - (c)

(No change.)

(d)

In Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller Counties, all offset lithographic printing presses on a property which, when uncontrolled, emit a combined weight of VOC equal to or greater than 25 tons per calendar year, shall be in compliance with §§115.442, 115.443, 115.445, and 115.446 of this title as soon as practicable, but no later than December 31, 2002.

(e)

[ (d) ] In Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller Counties, all offset lithographic printing presses on a property which, when uncontrolled, emit a combined weight of VOC less than 25 tons per calendar year, shall be in compliance with §§115.442, 115.443, 115.445, and 115.446 of this title as soon as practicable, but no later than one year, after the commission publishes notification in the Texas Register of its determination that this contingency rule is necessary as a result of failure to attain the NAAQS for ozone by the attainment deadline or failure to demonstrate reasonable further progress as set forth in [ the 1990 Amendments to ] the FCAA, §172(c)(9).

This agency hereby certifies that the proposal has been reviewed by legal counsel and found to be within the agency's legal authority to adopt.

Filed with the Office of the Secretary of State, on August 11, 2000.

TRD-200005632

Margaret Hoffman

Director, Environmental Law Division

Texas Natural Resource Conservation Commission

Earliest possible date of adoption: September 24, 2000

For further information, please call: (512) 239-0348


Subchapter J. ADMINISTRATIVE PROVISIONS

4. EMISSIONS TRADING

30 TAC §115.950

The Texas Natural Resource Conservation Commission (commission) proposes an amendment to §115.950, Emissions Trading. This amendment is also proposed as a revision to the Texas state implementation plan (SIP).

BACKGROUND AND SUMMARY OF THE FACTUAL BASIS FOR THE PROPOSED RULES

Section 115.950 currently refers to 30 TAC §101.29, Emissions Credit Banking and Trading, as a method of meeting emission requirements of Chapter 115. In concurrent rulemaking, §101.29 would be repealed and its requirements transferred and amended in new Chapter 101, Subchapter H, Divisions 1 and 4. This rulemaking would amend §115.950 to cite the correct cross-reference. The amended section would require the user of credits to obtain additional emission reduction credits or achieve lower actual emissions if new lower volatile organic compound (VOC) emission specifications are established by future amendments to this chapter.

The commission solicits comment on additional flexibilities relating to rule content and implementation which have not been addressed in this or other concurrent rulemakings. These flexibilities may be available for both mobile and stationary sources. Additional flexibilities may also be achieved through innovative and/or emerging technology which may become available in the future. Additional sources of funds for incentive programs may become available to substitute for some of the measures considered here.

SECTION BY SECTION DISCUSSION

Section 115.950 would be amended to change the title to "Use of Emissions Credits for Compliance" from "Emissions Trading" to more clearly reflect the language in §115.950, which discusses how to use emission reduction credits for alternative compliance, not how to trade emission reduction credits.

The proposed §115.950(a) removes the reference to §101.29 and corrects the reference to Chapter 101, Subchapter H, Division 1, Emission Reduction Credit Banking and Trading, or Division 4, Discrete Emission Reduction Banking and Trading. In addition, the amendment clarifies that emission reduction credits (ERCs), mobile emission reduction credits (MERCs), discrete emission reduction credit (DERCs), or mobile discrete emission reduction credit (MDERCs) may be used to meet any of the requirements of Chapter 115. The term "RC" refers to an ERC, MERC, DERC, or MDERC.

The proposed §115.950(b) adds language requiring that owners or operators using Chapter 101, Subchapter H, Division 1 or Division 4 to meet the emission control requirements of Chapter 115 must obtain additional RCs or reduce actual emissions if any lower VOC emission specification is established by future amendments to Chapter 115.

FISCAL NOTE: COST TO STATE AND LOCAL GOVERNMENT

John Davis, Technical Specialist with Strategic Planning and Appropriations, has determined that for each year of the first five-year period the proposed amendment is in effect, there will be no fiscal implications for any unit of state and local government as a result of administration or enforcement of the proposed amendment.

The proposed amendment will achieve administrative consistency with amendments to Chapter 101 proposed in concurrent rulemaking by correcting a cross-reference, and repealing and transferring requirements relating to Emission Credit Banking and Trading.

The proposed amendment does not add regulatory requirements, but is being proposed to allow compliance flexibility in meeting current or future VOC emission limitations. The proposed amendment clarifies that ERCs, MERCs, DERCs, or MDERCs may be used to meet any of the requirements for meeting emission requirements. Additionally, the proposed amendment adds language to describe how owners or operators using emission credit banking and trading to meet the emission control requirements must obtain additional emission credits or reduce actual emissions if any lower VOC emission specification is established by future amendments.

PUBLIC BENEFIT AND COSTS

Mr. Davis also has determined that for each year of the first five years the proposed amendment is in effect, the public benefit anticipated as a result of implementing the amendment will be the increased compliance with VOC emissions limitations through increased rule flexibility.

There are no anticipated fiscal impacts to persons and businesses as a result of implementation of the proposed amendment, because the proposed action is administrative in nature. The proposed amendment will correct a cross-reference with Chapter 101, clarify the use of ERCs, MERCs, DERCs, and MERCs, and will add language specifying that owners must obtain additional emission credits or lower actual emissions if stricter VOC requirements are implemented through future amendments.

SMALL AND MICRO-BUSINESS ASSESSMENT

There will be no adverse fiscal implications for small or micro-businesses as a result of administration or enforcement of the proposed amendment. The proposed action is administrative in nature. The proposed amendment will correct a cross reference with Chapter 101, clarify the use of ERCs, MERCs, DERCs, and MERCs, and will add language specifying that owners must obtain additional emission credits or lower actual emissions if stricter VOC requirements are implemented through future amendments to Chapter 115.

DRAFT REGULATORY IMPACT ANALYSIS

The commission has reviewed the proposed rulemaking in light of the regulatory analysis requirements of Texas Government Code §2001.0225. The commission has determined that the proposed amendment to Chapter 115 does not meet the definition of a "major environmental rule" as defined in Texas Government Code, §2001.0225. "Major environmental rule" means a rule, the specific intent of which, is to protect the environment or reduce risks to human health from environmental exposure, and that may adversely affect in a material way the economy, a sector of the economy, productivity, competition, jobs, the environment, or the public health and safety of the state or a sector of the state. The commission is proposing the amendment to achieve administrative consistency with amendments to Chapter 101 proposed in concurrent rulemaking. The proposed amendment to Chapter 115 does not add regulatory requirements, but is proposed to allow compliance flexibility in meeting current or future VOC emission limitations in Chapter 115. In addition, Texas Government Code, §2001.0225, only applies to a major environmental rule, the result of which is to: 1.) exceed a standard set by federal law, unless the rule is specifically required by state law; 2.) exceed an express requirement of state law, unless the rule is specifically required by federal law; 3.) exceed a requirement of a delegation agreement or contract between the state and an agency or representative of the federal government to implement a state and federal program; or 4.) adopt a rule solely under the general powers of the agency instead of under a specific state law. This rulemaking is not subject to the regulatory analysis provisions of §2001.0225(b), because the proposed rule does not meet any of the four applicability requirements. Specifically, the emission banking and trading requirements within this proposal were developed in order to meet the ozone NAAQS set by the EPA under the Federal Clean Air Act (FCAA), §7409, and therefore meet a federal requirement. States are primarily responsible for ensuring attainment and maintenance of NAAQS once EPA has established those standards. Under the FCAA, §7410 and related provisions, states must submit, for EPA approval, SIPs that provide for the attainment and maintenance of NAAQS through a control program directed to sources of the pollutants involved. This proposal is not an express requirement of state law, but was developed specifically in order to meet the air quality standards established under federal law as NAAQS, as authorized under the TCAA, §382.012 (concerning State Air Control Plan). This proposal is intended to help bring the HGA ozone nonattainment area into compliance. The proposed amendments do not exceed a standard set by federal law, exceed an express requirement of state law unless specifically required by federal law, nor exceed a requirement of a delegation agreement. The proposed amendments were not developed solely under the general powers of the agency, but were specifically developed to meet the air quality standards established under federal law as NAAQS. The commission invites public comment on the draft regulatory impact analysis.

TAKINGS IMPACT ASSESSMENT

The commission has completed a takings impact assessment for the proposed rule. The following is a summary of that assessment. The commission is proposing the amendment to achieve administrative consistency with amendments to Chapter 101 proposed in concurrent rulemaking. The proposed amendment to Chapter 115 does not add regulatory requirements, but is proposed to allow compliance flexibility in meeting current or future VOC emission limitations in Chapter 115. The proposed amendment does not affect private real property in a manner which restricts or limits an owner's right to the property that would otherwise exist in the absence of a governmental action. Consequently, the proposed section does not meet the definition of a takings under Texas Government Code, §2007.002(5).

COASTAL MANAGEMENT PROGRAM CONSISTENCY REVIEW

The commission has determined the proposed rulemaking relates to an action or actions subject to the Texas Coastal Management Program (CMP) in accordance with the Coastal Coordination Act of 1991, as amended (Texas Natural Resources Code, §§33.201 et seq.), and the commission's rules in 30 TAC Chapter 281, Subchapter B, concerning Consistency with the Texas Coastal Management Program. As required by 30 TAC §281.45(a)(3) and 31 TAC §505.11(b)(2) relating to actions and rules subject to the CMP, commission rules governing air pollutant emissions must be consistent with the applicable goals and policies of the CMP. The commission has reviewed this action for consistency with the CMP goals and policies in accordance with the regulations of the Coastal Coordination Council, and has determined that the proposed rule is consistent with the applicable CMP goal expressed in 31 TAC §501.12(1) of protecting and preserving the quality and values of coastal natural resource areas, and the policy in 31 TAC §501.14(q), which requires that the commission protect air quality in coastal areas. The proposed amendment to Chapter 115 does not add regulatory requirements, but is proposed to allow compliance flexibility in meeting current or future VOC emission limitations in Chapter 115. Interested persons may submit comments on the consistency of the proposed rule with the CMP during the public comment period.

EFFECT ON SITES SUBJECT TO THE FEDERAL OPERATING PERMIT PROGRAM

Sources that currently have §115.590 listed in their federal operating permit would not be required to amend the permit in response to this amendment. However those sources that wish to use RCs to comply with this chapter must revise their operating permit, consistent with the process in 30 TAC Chapter 122, to include the revised §115.590 requirements for each emission unit affected by §115.590 at their site.

ANNOUNCEMENT OF HEARINGS

The commission will hold public hearings on this proposal at the following times and locations: September 18, 2000, 10:00 a.m., Lone Star Convention Center, 9055 Airport Road (FM 1484), Conroe; September 18, 2000, 7:00 p.m., Lake Jackson Civic Center, 333 Highway 332 East, Lake Jackson; September 19, 2000, 10:00 a.m. and 7:00 p.m., George Brown Convention Center, 1001 Avenida de Las Americas, Houston; September 20, 2000, 9:00 a.m., VFW Hall, 6202 George Bush Drive, Katy; September 20, 2000, 6:00 p.m., East Harris County Community Center, 7340 Spencer, Pasadena; September 21, 2000, 10:00 a.m., Southeast Texas Regional Airport Media Room, 6000 Airline Drive, Beaumont; September 21, 2000, 2:00 p.m., Amarillo City Commission Chambers, City Hall, 509 East 7th Avenue, Amarillo; September 21, 2000, 6:00 p.m., Charles T. Doyle Convention Center, 21st Street at Phoenix Lane, Texas City; September 22, 2000, 10:00 a.m., Dayton High School, 2nd Floor Lecture Room, 3200 North Cleveland Street, Dayton; September 22, 2000, 11:00 a.m., El Paso City Council Chambers, 2 Civic Center Plaza, 2nd Floor, El Paso; September 22, 2000, 2:00 p.m., North Central Texas Council of Governments, 2nd Floor Board Room, 616 Six Flags Drive, Suite 200, Arlington; and September 25, 2000, 10:00 a.m., Texas Natural Resource Conservation Commission, 12100 North I-35, Building E, Room 201S, Austin. The hearings are structured for the receipt of oral or written comments by interested persons. Registration will begin one hour prior to each hearing. Individuals may present oral statements when called upon in order of registration. A four-minute time limit will be established at each hearing to assure that enough time is allowed for every interested person to speak. Open discussion will not occur during each hearing; however, agency staff members will be available to discuss the proposal one hour before each hearing, and will answer questions before and after each hearing.

Persons with disabilities who have special communication or other accommodation needs, who are planning to attend the hearings, should contact the Office of Environmental Policy, Analysis, and Assessment at (512) 239-4900. Requests should be made as far in advance as possible.

SUBMITTAL OF COMMENTS

Written comments may be submitted to Heather Evans, Office of Environmental Policy, Analysis, and Assessment, MC 206, P.O. Box 13087, Austin, Texas 78711-3087, faxed to (512) 239-4808, or emailed to siprules@tnrcc.state.tx.us. All comments should reference Rule Log Number 1998-089-101-AI. Comments must be received by 5:00 p.m., September 25, 2000. For further information, please contact Matthew R. Baker at (512) 239-1091 or Beecher Cameron at (512) 239-1495.

STATUTORY AUTHORITY

The amendment is proposed under the Texas Health and Safety Code, TCAA, §382.011, which authorizes the commission to control the quality of the state's air; §382.012, which authorizes the commission to develop a plan for control of the state's air; §382.017, which provides the commission the authority to adopt rules consistent with the policy and purposes of the TCAA, and 42 United States Code, §7410(a)(2)(A), which requires SIPs to include enforceable emission limitations and other control measures or techniques, including economic incentives such as fees, marketable permits, and auction of emission rights.

The proposed amendment implements TCAA, §382.002, relating to Policy and Purpose; §382.011, relating to General Powers and Duties; and §382.012, relating to State Air Control Plan.

Use of Emissions Credits for Compliance [ Emissions Trading ]. (a)

An owner or operator may meet the emission control requirements of this chapter, in whole or in part, by obtaining emission reduction credits (ERCs), mobile emission reduction credits (MERCs), [ or ] discrete emission reduction credits (DERCs), or mobile discrete emission reduction credits (MDERCs) in accordance with this section and Chapter 101, Subchapter H, Division 1 of this title (relating to Emission Credit Banking and Trading) or Chapter 101, Subchapter H, Division 4 of this title (relating to Discrete Emission Reduction Banking and Trading). For the purposes of this section, the term "RC" refers to an ERC, MERC, DERC, or MDERC, whichever is applicable. [ §101.29 of this title (relating to Emission Credit Banking and Trading) ].

(b)

Any lower volatile organic compound (VOC) emission specification established under this chapter for the unit or units using RCs shall require the user of the RCs to obtain additional RCs in accordance with Chapter 101, Subchapter H, Division 1 of this title or Chapter 101, Subchapter H, Division 4 of this title and/or otherwise reduce emissions prior to the effective date of such rule change. The owner or operator of the unit(s) currently using RCs shall calculate the necessary emission reductions per unit as follows.

Figure: 30 TAC §115.950(b)

This agency hereby certifies that the proposal has been reviewed by legal counsel and found to be within the agency's legal authority to adopt.

Filed with the Office of the Secretary of State, on August 11, 2000.

TRD-200005657

Margaret Hoffman

Director, Environmental Law Division

Texas Natural Resource Conservation Commission

Earliest possible date of adoption: September 24, 2000

For further information, please call: (512) 239-1966


Chapter 117. CONTROL OF AIR POLLUTION FROM NITROGEN COMPOUNDS

The Texas Natural Resource Conservation Commission (TNRCC or commission) proposes amendments to §117.10, concerning Definitions; §§117.101, 117.103, 117.105, 117.106, 117.108, 117.111, 117.113, 117.116, 117.119, and 117.121, concerning Utility Electric Generation in Ozone Nonattainment Areas; §117.138, concerning System Cap; §§117.201, 117.203, 117.205 - 117.208, 117.211, 117.213, 117.216, 117.219, and 117.221, concerning Industrial, Commercial, and Institutional Sources in Ozone Nonattainment Areas; and §117.510 and §117.520, concerning Administrative Provisions. The commission also proposes new §117.114 and §117.214, concerning Emission Testing and Monitoring for the Houston/Galveston Attainment Demonstration; §117.210, concerning System Cap; and §117.534, concerning Compliance Schedule for Boilers, Process Heaters, and Stationary Engines at Minor Sources. The commission also proposes new §§117.471, 117.473, 117.475, 117.478, and 117.479 in Subchapter D, to be added as a new Division 2, concerning Boilers, Process Heaters, and Stationary Engines at Minor Sources. The proposed revisions to Chapter 117 and to the state implementation plan (SIP) would require a wide variety of stationary sources of nitrogen oxides (NO x ) emissions in the Houston/Galveston (HGA) ozone nonattainment area to meet new emission specifications and other requirements in order to reduce NO x emissions and ozone air pollution.

The affected equipment types and processes include electric utility boilers and stationary gas turbines; industrial, commercial, and institutional (ICI) boilers and stationary gas turbines; duct burners used in turbine exhaust ducts; process heaters and furnaces; stationary internal combustion engines; fluid catalytic cracking units (including catalyst regenerators and associated carbon monoxide (CO) boilers and furnaces); pulping liquor recovery furnaces, lime kilns, lightweight aggregate kilns, heat treating furnaces, reheat furnaces, magnesium chloride fluidized bed dryers, incinerators, and hazardous waste-fired boilers and industrial furnaces (BIF units). The commission proposes these amendments to Chapter 117, concerning Control of Air Pollution from Nitrogen Compounds, and to the SIP as essential components of and consistent with the SIP that Texas is required to develop under the Federal Clean Air Act (FCAA) Amendments of 1990 (42 United States Code (USC)), §7410, to demonstrate attainment of the National Ambient Air Quality Standard (NAAQS) for ozone. In addition, 42 USC, §7502(a)(2), requires attainment as expeditiously as practicable, and 42 USC, §7511a(d), requires states to submit ozone attainment demonstration SIPs for severe ozone nonattainment areas such as HGA. Another purpose of these proposed revisions is to ensure that reasonably available control technology (RACT) requirements, as required by 42 USC, §7511a(f), are applied to major NO x sources in HGA which are not subject to the previous NO x RACT rules.

BACKGROUND AND SUMMARY OF THE FACTUAL BASIS FOR THE PROPOSED RULES

The HGA ozone nonattainment area is classified as Severe-17 under the 1990 Amendments to the FCAA (42 USC), and therefore is required to attain the one-hour ozone standard of 0.12 parts per million (ppm) by November 15, 2007. The HGA area, defined by Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller Counties, has been working to develop a demonstration of attainment in accordance with 42 USC §7410. On January 4, 1995, the state submitted the first of its Post-1996 SIP revisions for HGA.

The January 1995 SIP consisted of urban airshed model (UAM) modeling for 1988 and 1990 base case episodes, adopted rules to achieve a 9% rate-of-progress (ROP) reduction in volatile organic compounds (VOC), and a commitment schedule for the remaining ROP and attainment demonstration elements. At the same time, but in a separate action, the State of Texas filed for the temporary NOx waiver allowed by 42 USC, §7511a(f). The January 1995 SIP and the NO x waiver were based on early base case episodes which marginally exhibited model performance in accordance with the United States Environmental Protection Agency (EPA) modeling performance standards, but which had a limited data set as inputs to the model. In 1993 and 1994, the commission was engaged in an intensive data-gathering exercise known as the Coastal Oxidant Assessment for Southeast Texas (COAST) study. The commission believed that the enhanced emissions inventory, expanded ambient air quality and meteorological monitoring, and other elements would provide a more robust data set for modeling and other analysis, which would lead to modeling results that the commission could use to better understand the nature of the ozone air quality problem in the HGA area.

Around the same time as the 1995 submittal, EPA policy regarding SIP elements and timelines went through changes. Two national programs in particular resulted in changing deadlines and requirements. The first of these programs was the Ozone Transport Assessment Group. This group grew out of a March 2, 1995 memo from Mary Nichols, former EPA Assistant Administrator for Air and Radiation, that allowed states to postpone completion of their attainment demonstrations until an assessment of the role of transported ozone and precursors had been completed for the eastern half of the nation, including the eastern portion of Texas. Texas participated in this study, and it has been concluded that Texas does not significantly contribute to ozone exceedances in the Northeastern United States. The other major national initiative that has impacted the SIP planning process is the revision to the national ozone standard. The EPA promulgated a final rule on July 18, 1997 changing the ozone standard to an eight-hour standard of 0.08 ppm. In November 1996, concurrent with the proposal of the standards, the EPA proposed an interim implementation plan (IIP) that it believed would help areas like HGA transition from the old to the new standard. In an attempt to avoid a significant delay in planning activities, Texas began to follow this guidance, and readjusted its modeling and SIP development timelines accordingly. When the new standard was published, the EPA decided not to publish the IIP, and instead stated that, for areas currently exceeding the one-hour ozone standard, that standard would continue to apply until it is attained. The FCAA requires that HGA attain the one-hour standard by November 15, 2007.

The EPA issued revised draft guidance for areas such as HGA that do not attain the one-hour ozone standard. The commission adopted on May 6, 1998 and submitted to the EPA on May 19, 1998 a revision to the HGA SIP which contained the following elements in response to EPA's guidance: UAM modeling based on emissions projected from a 1993 baseline out to the 2007 attainment date; an estimate of the level of VOC and NO x reductions necessary to achieve the one-hour ozone standard by 2007; a list of control strategies that the state could implement to attain the one-hour ozone standard; a schedule for completing the other required elements of the attainment demonstration; a revision to the Post-1996 9% ROP SIP that remedied a deficiency that the EPA believed made the previous version of that SIP unapprovable; and evidence that all measures and regulations required by Subpart 2 of Title I of the FCAA to control ozone and its precursors have been adopted and implemented, or are on an expeditious schedule to be adopted and implemented.

In November 1998, the SIP revision submitted to the EPA in May 1998 became complete by operation of law. However, the EPA stated that it could not approve the SIP until specific control strategies were modeled in the attainment demonstration. The EPA specified a submittal date of November 15, 1999 for this modeling. In a letter to the EPA dated January 5, 1999, the state committed to model two strategies showing attainment.

As the HGA modeling protocol evolved, the commission eventually selected and modeled seven basic modeling scenarios. As part of this process, a group of HGA stakeholders worked closely with commission staff to identify local control strategies for the modeling. Some of the scenarios for which the stakeholders requested evaluation included options such as California-type fuel and vehicle programs as well as an acceleration simulation mode equivalent motor vehicle inspection and maintenance program. Other scenarios incorporated the estimated reductions in emissions that were expected to be achieved throughout the modeling domain as a result of the implementation of several voluntary and mandatory statewide programs adopted or planned independently of the SIP. It should be made clear that the commission did not propose that any of these strategies be included in the ultimate control strategy submitted to the EPA in 2000. The need for and effectiveness of any controls which may be implemented outside the HGA eight-county area will be evaluated on a county-by-county basis.

The SIP revision was adopted by the commission on October 27, 1999, submitted to the EPA by November 15, 1999, and contained the following elements: photochemical modeling of potential specific control strategies for attainment of the one-hour ozone standard in the HGA area by the attainment date of November 15, 2007; an analysis of seven specific modeling scenarios reflecting various combinations of federal, state, and local controls in HGA (additional scenarios H1 and H2 build upon Scenario VIf); identification of the level of reductions of VOC and NO x necessary to attain the one-hour ozone standard by 2007; a 2007 mobile source budget for transportation conformity; identification of specific source categories which, if controlled, could result in sufficient VOC and/or NO x reductions to attain the standard; a schedule committing to submit by April 2000 an enforceable commitment to conduct a mid-course review; and a schedule committing to submit modeling and adopted rules in support of the attainment demonstration by December 2000.

The April 2000 SIP revision for HGA contained the following enforceable commitments by the state: to quantify the shortfall of NO x reductions needed for attainment; to list and quantify potential control measures to meet the shortfall of NO x reductions needed for attainment; to adopt the majority of the necessary rules for the HGA attainment demonstration by December 31, 2000, and to adopt the rest of the shortfall rules as expeditiously as practical, but no later than July 31, 2001; to submit a Post-99 ROP plan by December 31, 2000; to perform a mid- course review by May 1, 2004; and to perform modeling of mobile source emissions using the EPA mobile source emissions model (MOBILE6), to revise the on-road mobile source budget as needed, and to submit the revised budget within 24 months of the model's release. In addition, if a conformity analysis is to be performed between 12 months and 24 months after the MOBILE6 release, the state will revise the motor vehicle emissions budget (MVEB) so that the conformity analysis and the SIP MVEB are calculated on the same basis.

The emission reduction requirements included as part of this SIP revision represent substantial, intensive efforts on the part of stakeholder coalitions in the HGA area. These coalitions, involving local governmental entities, elected officials, environmental groups, industry, consultants, and the public, as well as the commission and the EPA, have worked diligently to identify and quantify potential control strategy measures for the HGA attainment demonstration. Local officials from the HGA area have formally submitted a resolution to the commission, requesting the inclusion of many specific emission reduction strategies.

The current SIP revision contains rules, enforceable commitments, and photochemical modeling analyses in support of the HGA ozone attainment demonstration. In addition, this SIP contains post- 1999 ROP plans for the milestone years 2002 and 2005, and for the attainment year 2007. The SIP also contains enforceable commitments to implement further measures, if needed, in support of the HGA attainment demonstration, as well as a commitment to perform and submit a mid-course review.

In order for the state to have an approvable attainment demonstration, EPA has indicated that the state must adopt those strategies modeled in the November 15, 1999 submittal and then adopt sufficient controls to close the remaining gap in NO x emissions.

The Houston nonattainment area will need to ultimately reduce NO x more than 750 tons per day (tpd) to reach attainment with the one-hour standard. In addition, a VOC reduction of about 25% will have to be achieved. Adoption of point source NO x rules will contribute to attainment and maintenance of the one-hour ozone standard in the HGA area. Point source NO x rules also should contribute to a successful demonstration of transportation conformity in the HGA area.

The commission solicits comment on additional flexibilities relating to rule content and implementation which have not been addressed in this or other concurrent rulemakings. These flexibilities may be available for both mobile and stationary sources. Additional flexibilities may also be achieved through innovative and/or emerging technology which may become available in the future. Additional sources of funds for incentive programs may become available to substitute for some of the measures considered here.

The attainment demonstration modeling produces a target emission rate of about 66.7 tons of NO x per day in 2007 from industrial point sources. The staff analyzed the most recent available point source NOx emissions inventory, from 1997, categorizing the emitting sources by equipment type to identify how to reasonably obtain the necessary reductions. In the Tables and Graphics section of this issue of the Texas Register , the table titled "Potential NO x Emission Reductions by Point Source Category for Houston/Galveston Nonattainment Area Counties" indicates the relative proportion of emissions according to equipment category.

Figure 1: 30 TAC Chapter 117 - Preamble

Another table in the Tables and Graphics section of this issue of the Texas Register , titled "Subcategories - Point Source Potential NO x Emission Reductions by Subcategory for Houston/Galveston Nonattainment Area Counties," further breaks down the equipment categories and indicates the estimated NO x emission reductions which would result from implementation of the proposed Chapter 117 rules.

Figure 2: 30 TAC Chapter 117 - Preamble

The tables show that emission reductions approaching the tpd rate required by the attainment demonstration necessitate further reductions from essentially all categories, including electric utility boilers and stationary gas turbines; ICI boilers and stationary gas turbines; duct burners used in turbine exhaust ducts; process heaters and furnaces; stationary internal combustion engines; fluid catalytic cracking units (including catalyst regenerators and CO boilers and furnaces); pulping liquor recovery furnaces; lime kilns; lightweight aggregate kilns; heat treating furnaces; reheat furnaces; magnesium chloride fluidized bed dryers; incinerators; and BIF units.

To develop the information in this table and analyze the reductions obtainable by potential NO x emission rate limits (in pound per million British thermal units (lb/MMBtu) heat input, gram per horsepower-hour (g/hp-hr), etc.), commission staff gathered the emission rate factors used to calculate 1997 ozone season emissions for the major NO x sources in HGA. In January 2000, commission staff sent out a rate data survey to major NO x sources in HGA and made follow-up requests in an attempt to fill in missing rate data. In situations where the major NO x sources did not or could not provide rate data, commission staff estimated the missing rate data from available data for similar equipment. Commission staff also conducted a quality assurance analysis of the 1997 emissions inventory in order to correctly classify equipment into the various categories shown in the table. The information was compiled in a spreadsheet, allowing reductions from a rate limit applied to an equipment category to be calculated either as a number of tons of NOx per day reduced or as a percentage reduction from the category.

The commission staff then evaluated the emission reductions that would be achieved by applying various attainment demonstration emission rate limits to the equipment categories. Because some NO x emission sources simply can not be reasonably controlled (for example, flares), it is necessary that the larger emission categories, especially electric utility boilers, stationary gas turbines, heaters, engines, and ICI boilers, achieve more than a 90% reduction in order for the overall emission reductions from NO x point sources to meet the 90% goal that modeling has shown is necessary for HGA to be able to demonstrate attainment of the ozone NAAQS. Through an iterative process, the commission staff developed emission rate limits for the major NO x point source categories which approach the maximum practicable emission reductions for these sources and, while technically challenging to meet, are a necessary and essential component of the HGA Attainment Demonstration SIP, being noticed for public hearings and comment concurrently in a separate section of this issue of the Texas Register .

SECTION BY SECTION DISCUSSION

The primary purpose of the proposed revisions to Chapter 117 and to the SIP is to establish new emission limits for the ozone attainment demonstrations. However, another purpose of these proposed revisions is to ensure that RACT requirements are applied to major NO x sources in HGA, as required by 42 USC, §7511a(f). The current NO x RACT limits in §117.105, concerning Emission Specifications for Reasonably Available Control Technology (RACT), and §117.205, concerning Emission Specifications for Reasonably Available Control Technology (RACT), apply to certain boilers, process heaters, and stationary internal combustion engines and stationary gas turbines. The proposed revisions will establish emission limits for boilers; process heaters and furnaces; stationary internal combustion engines and stationary gas turbines; duct burners used in turbine exhaust ducts; fluid catalytic cracking units (including catalyst regenerators and associated CO boilers and furnaces); pulping liquor recovery furnaces; lime kilns; lightweight aggregate kilns; heat treating furnaces; reheat furnaces; magnesium chloride fluidized bed dryers; incinerators; and BIF units which are currently exempt from the NO x RACT limits in §117.105 and §117.205. While the proposed attainment demonstration emission limits are more stringent than RACT, these limits will nevertheless also fulfill the NO x RACT requirements of 42 USC, §7511a(f), for major sources in HGA which are not subject to the previous NO x RACT rules.

The proposed changes to §117.10, concerning Definitions, revise the definition of "low annual capacity factor boiler, process heater, or gas turbine supplemental waste heat recovery unit" by changing the order of "commercial, institutional, or industrial" to "industrial, commercial, or institutional" for consistency with the title of this division. The proposed changes to §117.10 also add a definition of "electric generating facility (EGF)" which is consistent with the corresponding definition in §117.330(12), concerning Definitions. Subsequent definitions in §117.10 are renumbered to accommodate the proposed new definition of "electric generating facility (EGF)."

In addition, the proposed changes to §117.10 revise the definitions of "boiler or steam generator," "electric power generating system," "industrial boiler or steam generator," "large DFW system," "process heater," "small DFW system," "unit," and "utility boiler or steam generator" by deleting the superfluous term "steam generator" since a steam generator is simply a boiler and is already addressed by this term in the Chapter 117 rules.

The proposed changes to §117.10 also revise the definition of "unit" to broaden its applicability. Currently, this definition includes boilers, process heaters, stationary gas turbines, and stationary internal combustion engines. Because the emission reductions approaching the tpd emission rate required by the attainment demonstration necessitate further reductions from essentially all categories, the proposed revisions broaden the applicability of the definition of unit to include any other stationary source of NOx at a major source. Finally, the proposed changes to §117.10 revise the renumbered §117.10(34) to define "predictive emissions monitoring system (PEMS)" rather than "predictive emission monitoring system (PEMS)" for consistency with the definition of "continuous emissions monitoring system (CEMS)" in the renumbered §117.10(10) and the usage of these terms in the rules.

The proposed changes to §117.101, concerning Applicability, delete the superfluous term "steam generator" since a steam generator is simply a boiler and is already addressed by this term in the Chapter 117 rules, and renumber the paragraphs accordingly. The proposed changes to §117.101 also revise a reference in the renumbered §117.101(3) from "gas turbines" to "stationary gas turbines" for consistency with the definition of this term in the renumbered §117.10(38), and update a reference to the renumbered §117.10(12).

The proposed changes to §117.103, concerning Exemptions, revise §117.103(a) to specify the exemptions from the RACT requirements. The units which are exempt from RACT are those currently exempt under this subsection from the entire division. However, the revised language states that these units are exempt from the specific sections for which these units would otherwise be subject, rather than from the entire division. Although this would appear to narrow the scope of the exemptions, it is not expected to add any additional requirements because other sections in this division generally do not apply to these units (except as specified in §117.113, concerning Continuous Demonstration of Compliance). In addition, the proposed changes to §117.103 revise §117.103(a)(2) to delete the superfluous term "steam generator" since a steam generator is simply a boiler and is already addressed by this term in the Chapter 117 rules.

A proposed new §117.103(b) specifies that stationary gas turbines and engines which are used solely to power other engines or gas turbines during start-ups are exempt from the attainment demonstration requirements of §§117.106, concerning Emission Specifications for Attainment Demonstrations; 117.108, concerning System Cap; and 117.113, except as may be specified in §117.113(i). The attainment demonstration exemptions do not include the RACT exemptions for new units placed into service after November 15, 1992; utility boilers, and auxiliary steam boilers with an annual heat input less than or equal to 2.2(10 11 ) Btu per year; and stationary gas turbines and engines which operate less than 850 hours per year, because emission reductions from essentially all categories are necessary to approach the tpd emission rate required by the attainment demonstration. Finally, subsections are given titles (catchlines) to identify the topics covered.

Because the attainment demonstration exemptions do not include the RACT exemptions for new units placed into service after November 15, 1992, the title of Subchapter B, concerning Combustion at Existing Major Sources, is proposed to be changed to Combustion at Major Sources.

The existing §117.103(b) includes an exemption from the oil-fired RACT emission limits during emergency conditions which necessitate oil firing. The proposed changes to §117.103 renumber this exemption as §117.103(c), break it into paragraphs to make the text more readable, and revise it to include exemption from the emission limits of §117.106, concerning Emission Specifications for Attainment Demonstrations, and §117.108. This revision is proposed in order to address concerns regarding times of natural gas curtailments, which are typically a cold weather issue. Although the system cap is less likely to be exceeded under natural gas curtailment conditions because the 30-day average winter peak electric demand is not as great as the summer 30-day peak demand, extensive oil firing due to an emergency condition could cause exceedances of the cap. The proposed broadening of the exemption in the renumbered §117.103(c) will address this concern.

The proposed new §117.103(d) exempts from the requirements of Chapter 117 all combustion units which would meet the requirements of a standard permit currently being developed for electricity-generating combustion units rated at less than ten megawatts (MW) in capacity and which emit no more than 0.015 lb NO x /MMBtu heat input. The commission is proposing this exemption to facilitate the distributed generation of electricity through authorization of relatively small electricity-producing units.

The proposed changes to §117.105 revise §117.105(a) - (d) and (h) to delete the superfluous term "steam generator" since a steam generator is simply a boiler and is already addressed by this term in the Chapter 117 rules. In addition, the proposed changes to §117.105 correct the title of §117.510 in §117.105(k)(2). The proposed changes to §117.105 also add a new §117.105(l) which specifies that after the applicable attainment demonstration SIP compliance date(s), the RACT emission specifications will no longer apply to equipment for which §117.106, concerning Emission Specifications for Attainment Demonstrations, has established more stringent emission limits. This will avoid any potential conflicts of RACT limits and the new more stringent attainment demonstration limits.

The proposed changes to §117.106 specify new NO x limits for electric utility boilers located in HGA. The proposed limits are essential components of and consistent with the HGA Attainment Demonstration SIP, being noticed for public hearings and comment concurrently in a separate section of this issue of the Texas Register . The proposed emission limits and ozone attainment demonstration SIP are required by 42 USC, §7410 and §7511a, which require states to submit SIPs to the EPA which contain enforceable measures to achieve the NAAQS. The process by which the emission limits were developed is described in the Background and Summary of the Factual Basis for the Proposed Rules section of this preamble.

The proposed revisions to §117.106(a) and (b) abbreviate the term "pound per million Btu," correct a typographical error in "Beaumont/Port Arthur," and reorganize the syntax of these sentences for consistency with the proposed new §117.106(c).

The proposed NO x emission limits for electric utility boilers located in HGA are being added as a new §117.106(c) and are based on a daily rate for electric utility boilers. The 24-hour emission limit in both NO x RACT and these rules is designed to limit the amount of NO x allowed in a 24-hour period, in order to control peak ozone, which forms on a daily cycle. The emission limits of §117.106(c) also apply as specified in §117.108 and in the emissions banking and trading program of Chapter 101, Subchapter H, Division 3, concerning Mass Emissions Cap and Trade Program, being noticed for public hearings and comment concurrently in this issue of the Texas Register .

The proposed limits of §117.106(c) for electric utility boilers in HGA are part of a larger set of emission reduction measures for the HGA Attainment Demonstration SIP. The larger context of development of the proposed NOx emission limit for electric utility boilers in HGA is discussed in the Background and Summary of the Factual Basis for the Proposed Rules section of this preamble. The proposed emission limits of 0.010 lb NOx /MMBtu heat input for gas- fired boilers, 0.030 lb NO x /MMBtu heat input for oil- or coal-fired, tangential-fired boilers, 0.030 lb NO x /MMBtu heat input for oil- or coal-fired, wall-fired boilers, 0.010 lb NO x /MMBtu heat input for auxiliary boilers with a maximum rated capacity equal to or greater than 100 MMBtu/hr, 0.015 lb NO x /MMBtu heat input for auxiliary boilers with a maximum rated capacity equal to or greater than 40 MMBtu/hr but less than 100 MMBtu/hr, and 0.036 lb NO x per MMBtu heat input (or alternatively, 30 parts per million by volume (ppmv) NO x , at 3.0% oxygen (O 2 ), dry basis) for auxiliary boilers with a maximum rated capacity less 40 MMBtu/hr will achieve a 93% emission reduction and generate an estimated 184.26 tpd NO x reductions from HGA electric utility boiler emissions. The proposed 93% NOx reduction is expected to necessitate combustion controls and flue gas cleanup on many of the boilers at electric utilities in the HGA area.

The proposed emission limits of 0.015 lb NO x /MMBtu heat input for stationary gas turbines will achieve a 91% emission reduction in conjunction with the proposed emission limit of 0.015 lb NO x per MMBtu heat input for stationary gas turbines and duct burners in §117.206(c)(11) and (12), respectively, concerning Emission Specifications for Attainment Demonstrations, and generate an estimated total of 141.00 tpd NO x reductions from these units in HGA, based on the 1997 emissions inventory. The proposed 91% NO x reduction is expected to necessitate combustion controls and flue gas cleanup on many of the stationary gas turbines in the HGA area.

The existing §117.106(c) and (d) are proposed to be renumbered as §117.106(d) and (e). The proposed revisions to the renumbered §117.106(d) make applicable in HGA the ammonia and CO emission limits in order to address pollutants which may increase as an incidental result of compliance with the proposed NOx limits. The CO and ammonia limits are the limits which are applicable in Beaumont/Port Arthur (BPA) and Dallas/Fort Worth (DFW). This ammonia limit of ten ppmv is lower than the existing RACT limit of §117.105(j). The lower ammonia limit is supported by information from selective catalytic reduction (SCR) vendors and ammonia test data for gas-fired boilers using SCR, not available when the original NO x RACT rules were adopted in 1993. The test data are reported in Table 2-5 of Status Report on NO x Control Technologies and Cost Effectiveness for Utility Boilers , issued by the Northeast States for Coordinated Air Use Management (NESCAUM) and the Mid-Atlantic Regional Air Management Association (MARAMA) (June 1998) (will be referred to as NESCAUM). It is desirable to minimize ammonia emissions because ammonia emissions create fine particulate matter, another form of air pollution. The commission proposes to exclude these related pollutant limits from the attainment demonstration SIP, in order to simplify the approval process for alternative emission specification under §107.121. This step will eliminate the need for case-specific SIP revisions by the EPA to complete the approval of an alternate CO or ammonia limit.

The revisions to the renumbered §117.106(e) specify that in HGA, the utility owner or operator may not use the trading option in §117.570. This is necessary to ensure that any trading that occurs is done under the emissions banking and trading program of Chapter 101, Subchapter H, Division 3, being noticed for public hearings and comment concurrently in this issue of the Texas Register . The owners and operators of the equipment addressed by these proposed Chapter 117 revisions will be required to use the compliance flexibility provided by the proposed Chapter 101 mass emissions cap and trade program, which will allow compliance to be established through the use of surplus reductions created from other sources. Units which meet the definition of EGF are required to use both the system cap specified in §117 and the mass emissions cap and trade program in Chapter 101, Subchapter H, Division 3 to comply with the NO x emission specifications of §117.106(c).

Section §117.106(e) also does not allow the use of §117.107 as an alternative for complying with the §117.106 emission specifications for attainment demonstrations. Section 117.107 emission averaging does not address the effects of activity level, and may not produce the intended reductions that would be achieved with direct compliance by all units or flexible compliance with an emission cap. Under §117.107, higher emissions will result if units selected for less control are subsequently operated more, or if units selected for more control are subsequently operated less. The proposed §117.106 emission limits will necessitate installation of flue gas cleanup emission controls on a number of units. As a result, these units are likely to have higher operating costs than units operating with only combustion controls, creating an economic incentive to operate the best-controlled units less and to produce greater emissions.

The proposed changes to §117.108 require the owner or operator of each EGF in HGA to comply with the daily and 30-day system cap emission limitations of the existing system cap. The proposed changes to §117.108 also revise §117.108(a) - (i) and (k) by replacing references to "utility boiler" with the term "EGF." In addition, the proposed changes to §117.108 revise §117.108(b) by updating the reference to the definition of "electric power generating system" in the renumbered §117.10(12).

The proposed changes to §117.108 also revise §117.108(e)(4) to replace a reference to testing in a non-existent rule with a reference to the maximum block one-hour emission rate as measured by the 30-day test. In addition, the proposed changes to §117.108 revise §117.108(f) by correcting the title in the reference to §117.119, concerning Notification, Recordkeeping, and Reporting Requirements.

Finally, the proposed changes to §117.108 revise §117.108(i), which specifies that an EGF which is permanently retired or decommissioned and rendered inoperable may be included in the source cap emission limit, to state that in HGA the permanent shutdown must have occurred after January 1, 2000. Because §117.108(c)(1) specifies 1997, 1998, and 1999 for calculating the emissions cap, it is necessary for the shutdown to occur after this period.

Currently, EGFs in DFW may comply with §117.106 through compliance with the daily and 30-day system cap available under §117.108. The commission solicits comments concerning the possibility of adding flexibility for these EGFs by allowing trading between different electric power generating systems in DFW in order to meet the system cap of §117.108. Any such flexibility would necessitate separate rulemaking to establish the mechanism for trading between different electric power generating systems in DFW.

The proposed changes to §117.111, concerning Initial Demonstration of Compliance, correct the sentence structure of §117.111(a) by changing "be tested" to "test the units." The proposed changes to §117.111 also correct the title of §117.510 in §117.111(a)(3), and revise §117.111(d)(3) by replacing the term "utility boilers" with "EGFs" for consistency with the corresponding changes to §117.108.

The proposed changes to §117.113, concerning Continuous Demonstration of Compliance, revise a reference in §117.113(f)(2)(A)(ii) from "United States Environmental Protection Agency" to "EPA" because this abbreviation is defined in Chapter 3, concerning Definitions.

The proposed changes to §117.113 also revise the catchline in §117.113(g) to clarify that these subsections apply to the NO x RACT emission specifications of §117.105, and revise references in §117.113(g)(1) and (2) from "gas turbine" to "stationary gas turbine" for consistency with the definition of this term in §117.10(37).

In addition, the proposed changes to §117.113 add a new §117.113(h)(2) which specifies the totalizing fuel flow meter requirements for units at major NO x sources in HGA which are subject to §117.106. All units which are listed in §117.101 will be subject to the totalizing fuel flow meter requirements because knowledge of the fuel usage is critical in determining the emission allocations for the proposed Chapter 101 mass emissions cap and trade program. The existing §117.113(h)(1) - (3) is being renumbered as §117.113(h)(1)(A) - (C) to accommodate the new §117.113(h)(2).

The proposed changes to §117.113 also revise §117.113(i) to reflect the addition of the new §117.103(b). This revision will ensure that stationary gas turbines and engines which were required to install run time meters under the existing RACT requirements will continue to utilize those existing run time meters.

In addition, the proposed changes to §117.113 also revise §117.113(k) (being renumbered as §117.113(k)(1)) to specify that this subparagraph only applies to units in BPA or DFW, or to units in HGA which are subject to the NO x RACT emission specifications of §117.105. A new §117.113(k)(2) specifies that for units in HGA which are subject to the attainment demonstration emission specifications of §117.106(c), the methods required in §117.113 and §117.114 shall be used in conjunction with the requirements of Chapter 101, Subchapter H, Division 3 to determine compliance. The new §117.113(k)(2) further specifies that for enforcement purposes, the executive director may also use other commission compliance methods to determine whether the source is in compliance with applicable emission specifications.

Finally, the proposed revisions to the catchlines in §117.113(l) clarify that this subsection applies to the NO x RACT emission specifications of §117.105.

The proposed new §117.114 applies to units in HGA which are subject to the attainment demonstration limits of §117.106(c) and specifies monitoring and testing requirements. The proposed new §117.114(a) requires monitoring for NO x , CO, and fuel flow as specified in §117.113(a) - (f) and (g). The proposed new §117.114(b) requires testing of each unit which is subject to the emission limits of §117.106(c). The testing requirements are consistent with the testing previously required of these units for NO x RACT under §117.111.

Regarding emission allowances for the proposed Chapter 101 mass emissions cap and trade program, the proposed §117.114(c) specifies that the NOx testing and monitoring data specified in §117.114(a) and (b), together with the level of activity, as defined in §101.350, concerning Definitions, are used to establish the emission factor for the mass emissions cap and trade program. For units without CEMS or PEMS, retesting is required after any modifications which could increase the NO x emission rate, but is optional after any modifications which could decrease the NO x emission rate, including, but not limited to, installation of post-combustion controls, low-NO x burners, low excess air operation, staged combustion (for example, overfire air), flue gas recirculation (FGR), and fuel-lean and conventional (fuel-rich) reburn. The NO x emission rate determined by the retesting establishes a new emission factor which must be used instead of the previously determined emission factor for the proposed Chapter 101 mass emissions cap and trade program.

The proposed changes to §117.116, concerning Final Control Plan Procedures for Attainment Demonstration Emission Specifications, revise the requirements in §117.116(a)(1), (2), and (5) to apply to auxiliary boilers and stationary gas turbines in HGA and, in conjunction with these changes, revise §117.116(a) to refer to units listed in §117.101, rather than to utility boilers listed in §117.101. While this change broadens the scope of the final control plan procedures, it will not add any requirements to auxiliary boilers and stationary gas turbines in BPA and DFW because the proposed changes to §117.116(a)(1), (2), and (5) specify that these paragraphs only apply to utility boilers in BPA and DFW. In addition, the remaining paragraphs in §117.116 do not apply to auxiliary boilers and stationary gas turbines in BPA and DFW.

The proposed changes to §117.116 also revise §117.116(a)(1) to reference the Chapter 101 mass emissions cap and trade program being proposed concurrently in this issue of the Texas Register . This revision is necessary because the owners and operators of the equipment addressed by these proposed Chapter 117 revisions will be required to use the compliance flexibility provided by the proposed Chapter 101 mass emissions cap and trade program, which will allow compliance to be established through the use of surplus reductions created from other sources.

In addition, the proposed changes to §117.116 also revise §117.116(a)(3) and (4) to add a reference to the requirements of §117.114.

The proposed changes to §117.119 revise a reference in §117.119(a) from "Unites States Environmental Protection Agency" (which should have been "United States Environmental Protection Agency") to "EPA" because this abbreviation is defined in Chapter 3, concerning Definitions; and correct the reference in §117.119(a) to §101.11 to reflect the recent title change of this section from "Exemptions from Rules and Regulations" to "Demonstrations." (See the July 14, 2000 issue of the Texas Register (25 TexReg 6727)). The proposed changes to §117.110 also revise a reference in §117.119(d)(1)(A) from "gas turbines" to "stationary gas turbines" for consistency with the definition of this term in §117.10(37).

The proposed changes to §117.121, concerning Alternative Case Specific Specifications, update a reference to the existing §117.106(c) which is being renumbered as §117.106(d) and revise a reference from "United States Environmental Protection Agency" to "EPA" because this abbreviation is defined in Chapter 3, concerning Definitions.

The proposed changes to §117.138, concerning System Cap, revise §117.138(b) to update a reference to the renumbered §117.10(12).

The proposed changes to §117.201, concerning Applicability, generalize the applicability by deleting the references to size cutoffs and adding the following to the list of units which are subject to this division: fluid catalytic cracking units (including CO boilers, CO furnaces, and catalyst regenerator vents); pulping liquor recovery furnaces; lime kilns; lightweight aggregate kilns; heat treating furnaces; reheat furnaces; magnesium chloride fluidized bed dryers; incinerators; BIF units which were regulated as existing facilities by the EPA at 40 Code of Federal Regulations (CFR) Part 266, Subpart H (as was in effect on June 9, 1993); and duct burners used in turbine exhaust ducts. It is necessary to generalize the applicability since the HGA Attainment Demonstration SIP rules include units which are presently excluded from §117.201. These changes do not broaden the scope of the existing rules in BPA or HGA due to corresponding exemptions already in, or being added to, §117.203, concerning Exemptions, and §117.205(h) which are described later in this preamble. Finally, the proposed changes to §117.201 revise §117.201(1) by changing the order of "commercial, institutional, or industrial" to "industrial, commercial, or institutional" for consistency with the title of this division. Units used to produce steam for the purpose of generating electricity, but which are not owned or operated by a municipality or Public Utility Commission of Texas regulated utility, are included in the applicability of §117.201, rather than §117.101.

The proposed changes to §117.203 move the existing exemptions into a new subsection (a) and add a new exemption for heat treating furnaces and reheat furnaces as new §117.203(a)(3), with an expiration of this exemption in HGA for units rated at 20 MMBtu/hr or greater after the appropriate compliance date(s) for §117.206(c) specified in §117.520, concerning Compliance Schedule for Commercial, Institutional, and Industrial Combustion Sources in Ozone Nonattainment Areas. The expiration of this exemption in HGA for certain units is necessary for consistency with the proposed §117.206(c)(14), which establishes emission limits for these units in HGA.

In addition, the exemption in the existing §117.203(3) for electric utility power generating boilers is proposed for deletion. Although this change would appear to narrow the scope of the exemptions, it is not expected to add any additional requirements to these units in BPA and DFW because other sections in this division do not apply to these units. The requirements for units in HGA which are not subject to §117.106 will parallel the requirements of §117.206.

Further, the proposed changes to the renumbered §117.203(a)(4) and (5) specify that the exemptions for incinerators, fume abaters, pulping liquor recovery furnaces, dryers, kilns, and ovens in HGA no longer apply after the appropriate compliance date(s) for §117.206 specified in §117.520.The revisions to the renumbered §117.203(a)(4) and (5) are necessary for consistency with the proposed §117.206(c)(12) - (16), which establish emission limits for certain units in these categories in HGA.

The proposed changes to §117.203 also add a new §117.203(a)(9) which exempts boilers and process heaters with a maximum rated capacity of 2.0 MMBtu/hr or less. This exemption level is proposed because units with a maximum rated capacity of 2.0 MMBtu/hr or less are already regulated under Subchapter D, Division 1, concerning Water Heaters, Small Boilers, and Process Heaters.

In addition, the proposed changes to §117.203 add a new §117.203(b) which specifies that the exemptions in §117.203(a)(1), (2), (6)(B), (7), and (8)(A) no longer apply in HGA after the appropriate compliance date(s) for emission specifications for attainment demonstrations specified in §117.520.The expiration of these exemptions in HGA for certain units is necessary for consistency with the proposed §117.206(c), which establishes emission limits for these units in HGA.

The proposed new §117.203(c) exempts from the requirements of Chapter 117 all combustion units which would meet the requirements of a standard permit currently being developed for electricity-generating combustion units rated at less than ten MW in capacity and which emit no more than 0.015 lb NOx /MMBtu heat input. The commission is proposing this exemption to facilitate the distributed generation of electricity through authorization of relatively small electricity-producing units.

The proposed changes to §117.205 revise §117.205(b)(6) to include an equation for calculating an emission limitation for each rolling 30-day period for cases when gas fired boilers or process heaters at times also fire gaseous fuel which contain more than 50% hydrogen by volume. The equation uses a time weighted average to incorporate the two emission limits, from combusting two types of gaseous fuels, into one emission limitation for each rolling 30-day average. This proposed change is based on a rule interpretation (Code Number R7-205.001) made by the agency's Air Rule Interpretation Team.

The proposed changes to §117.205 also revise §117.205(b)(7) by changing references from "continuous emission monitors" to "continuous emissions monitoring system" and from "predictive emission monitors" to "predictive emissions monitoring system" for consistency with the definitions of these terms in §117.10(9) and (33), respectively.

In addition, the proposed changes to §117.205 revise §117.205(c) to allow stationary gas turbines equipped with CEMS or PEMS for CO to meet the CO limit on a rolling 24-hour average, rather than on a one-hour average. This revision is consistent with the corresponding CO limit for boilers and process heaters in §117.205(f).

The proposed changes to §117.205 also revise §117.205(h)(1) by changing the order of "commercial, institutional, or industrial" to "industrial, commercial, or institutional" for consistency with the title of this division.

Additionally, the proposed changes to §117.205 revise the language for fluid catalytic cracking units and duct burners in §117.205(h)(4) and (5) for consistency with the corresponding language in §117.201(4) and (6). The proposed changes to §117.205 also add new paragraphs (8) - (11) for new units placed into service after November 15, 1992; ICI boilers and process heaters with a maximum rated capacity of less than 40 MMBtu per hour; stationary gas turbines and engines which are demonstrated to operate less than 850 hours per year (based on a rolling 12-month average); and stationary internal combustion engines with a horsepower (hp) rating of less than 150 hp and 300 hp in HGA and BPA, respectively.

Finally, the proposed changes to §117.205, add a new §117.205(i) which specifies that after the applicable attainment demonstration SIP compliance date, the RACT emission specifications will no longer apply to equipment for which §117.206 has established a more stringent emission limit. This will avoid any potential conflicts of RACT limits and the new more stringent attainment demonstration limits.

The proposed changes to §117.206(a) and (b) revise references to subsections (d) and (e), which should have been (e) and (f), to subsections (f) and (g) to accommodate the new §117.206(c) described in the following paragraph. In addition, the proposed changes to §117.206(b)(2) abbreviate the terms "horsepower" and "carbon monoxide."

The proposed changes to §117.206, add a new §117.206(c) which specifies NO x limits for boilers, process heaters, stationary internal combustion engines, stationary gas turbines, fluid catalytic cracking units (including CO boilers, CO furnaces, and catalyst regenerator vents), BIF units, duct burners used in turbine exhaust ducts, pulping liquor recovery furnaces, lime kilns, lightweight aggregate kilns, heat treating furnaces, reheat furnaces, magnesium chloride fluidized bed dryers, and incinerators at major sources of NO x in HGA. For units in HGA, the emission limits in the new §117.206(c) will be used in the proposed Chapter 101, Subchapter H, Division 3, to establish emission allocations and shall be the lower of any applicable permit limit or the emission limits described in the following paragraphs.

The proposed limits are essential components of and consistent with the HGA Attainment Demonstration SIP, being noticed for public hearings and comment concurrently in a separate section of this issue of the Texas Register . The proposed emission limits and ozone attainment demonstration SIP are required by 42 USC, §7410 and §7511a, which require states to submit SIPs to the EPA which contain enforceable measures to achieve the NAAQS. The proposed revisions to §117.206 also update cross-references and renumber subsequent subsections to accommodate the new emission specifications within the section. The process by which the emission limits were developed is described in the Background and Summary of the Factual Basis for the Proposed Rules section of this preamble.

The proposed emission limits in §117.206(c)(1) of 0.010 lb NOx per MMBtu heat input for gas-fired boilers with a maximum rated capacity equal to or greater than 100 MMBtu/hr; 0.015 lb NOx per MMBtu heat input for gas-fired boilers with a maximum rated capacity equal to or greater than 40 MMBtu/hr, but less than 100 MMBtu/hr; and 0.036 lb NO x per MMBtu heat input (or alternatively, 30 ppmv NO x , at 3.0% O 2 , dry basis) for gas-fired boilers with a maximum rated capacity less 40 MMBtu/hr will achieve a 92% NO x emission reduction from ICI boilers and generate an estimated 57.26 tpd NO x reductions in HGA, based on the 1997 emissions inventory.

The proposed emission limit in §117.206(c)(2) of ten ppmv NOx (at 0.0% O 2 , dry basis) for fluid catalytic cracking units (including CO boilers, CO furnaces, and catalyst regenerator vents) will achieve a 90% NO x emission reduction and generate an estimated 13.44 tpd NO x reductions in HGA, based on the 1997 emissions inventory.

The proposed emission limit in §117.206(c)(3) of 0.015 lb NOx per MMBtu heat input for BIF units will achieve an 81% NO x emission reduction and generate an estimated 9.95 tpd NO x reductions in HGA, based on the 1997 emissions inventory.

The proposed emission limit in §117.206(c)(4) of 0.057 lb NOx per MMBtu heat input for coke-fired boilers will achieve a 90% NO x emission reduction and generate an estimated 10.44 tpd NO x reductions in HGA, based on the 1997 emissions inventory.

The proposed emission limit in §117.206(c)(5) of 0.020 lb NOx per MMBtu heat input for wood fuel-fired boilers will achieve a 90% NO x emission reduction and generate an estimated 0.91 tpd NO x reductions in HGA, based on the 1997 emissions inventory.

The proposed emission limit in §117.206(c)(6) of 0.089 lb NOx per MMBtu heat input for rice hull-fired boilers will achieve a 90% NO x emission reduction and generate an estimated 0.46 tpd NO x reductions in HGA, based on the 1997 emissions inventory.

The proposed emission limit in §117.206(c)(7) of 2.0 lb NO x per 1,000 gallons of oil burned for oil-fired boilers will achieve a 90% NO x emission reduction and generate an estimated 0.13 tpd NO x reductions in HGA, based on the 1997 emissions inventory.

The proposed emission limits in §117.206(c)(8) of 0.010 lb NOx per MMBtu heat input for process heaters with a maximum rated capacity equal to or greater than 100 MMBtu/hr; 0.015 lb NO x per MMBtu heat input for process heaters with a maximum rated capacity equal to or greater than 40 MMBtu/hr, but less than 100 MMBtu/hr; and 0.036 lb NO x per MMBtu heat input (or alternatively, 30 ppmv NO x , at 3.0% O 2 , dry basis) for process heaters with a maximum rated capacity less 40 MMBtu/hr will achieve an 88% NO x emission reduction from process heaters and generate an estimated 96.56 tpd NOx reductions in HGA, based on the 1997 emissions inventory.

The proposed emission limits for stationary reciprocating internal combustion engines in §117.206(c)(9) are: 0.17 g NO x /hp-hr for gas-fired engines at sites with a total hp rating of 3,000 hp or more in 1997 or later; 0.50 g NO x /hp-hr for gas-fired engines at sites with a total hp rating of less than 3,000 hp in 1997 or later; 0.50 g NO x /hp-hr for existing dual-fuel, stationary reciprocating internal combustion engines; and 0.17 g NO x /hp-hr for dual-fuel, stationary reciprocating internal combustion engines initially placed into service after December 31, 2000. These emission limits will achieve a 94% NO x emission reduction and generate an estimated 78.50 tpd NO x reductions in HGA, based on the 1997 emissions inventory.

The proposed emission limits for stationary gas turbines in §117.206(c)(10) and duct burners used in turbine exhaust ducts in §117.206(c)(11) of 0.015 lb NO x per MMBtu heat input will achieve a 91% NO x emission reduction in conjunction with the proposed emission limit of 0.015 lb NO x per MMBtu heat input for stationary gas turbines in §117.106(c)(3) and generate an estimated total of 141.00 tpd NO x reductions in HGA, based on the 1997 emissions inventory.

The proposed emission limit for pulping liquor recovery furnaces in §117.206(c)(12) of 0.050 lb NO x per MMBtu heat input will achieve a 64% NO x emission reduction and generate an estimated 1.09 tpd NO x reductions in HGA, based on the 1997 emissions inventory.

The proposed emission limits for kilns in §117.206(c)(13) of 0.66 lb NO x per ton of calcium oxide (CaO) for lime kilns and 0.76 lb NO x per ton of product for lightweight aggregate kilns will achieve a 39% NO x emission reduction from the kiln category and generate an estimated 0.30 tpd NO x reductions in HGA, based on the 1997 emissions inventory.

The proposed emission limits for heat treating furnaces and reheat furnaces in §117.206(c)(14) of 0.087 lb NO x per MMBtu heat input for heat treating furnaces and 0.062 lb NO x per MMBtu heat input for reheat furnaces will achieve a 35% NOx emission reduction from the steel furnace category and generate an estimated 0.39 tpd NO x reductions in HGA, based on the 1997 emissions inventory.

The proposed emission limit for magnesium chloride fluidized bed dryers in §117.206(c)(15) of a 90% reduction from the emission factor used to calculate the 1997 ozone season daily NO x emissions will achieve a 41% NO x emission reduction from the dryer category and generate an estimated 0.95 tpd NO x reductions in HGA, based on the 1997 emissions inventory.

The proposed emission limit for incinerators in §117.206(c)(16) of a 90% reduction from the emission factor used to calculate the 1997 ozone season daily NO x emissions will achieve a 61% NO x emission reduction and generate an estimated 3.62 tpd NO x reductions in HGA, based on the 1997 emissions inventory.

The NO x emission limit averaging times for BPA and DFW in the renumbered §117.206(d)(1) are consistent with the averaging times for NO x RACT compliance, in §117.205(b)(7). Units with NO x emission monitors are capable of tracking emissions over time, and are allowed to demonstrate compliance on a 30-day average in BPA and DFW under this subsection. The proposed changes to §117.206 also revise §117.206(d)(1)(A) by changing references from "continuous emission monitors" to "continuous emissions monitoring system" and from "predictive emission monitors" to "predictive emissions monitoring system" for consistency with the definitions of these terms in §117.10(9) and (33), respectively. For HGA, a new §117.206(d)(2) specifies that the averaging time for the attainment demonstration emission limits shall be as specified in the mass emissions cap and trade program of Chapter 101, Subchapter H, Division 3, except that EGFs shall also comply with the daily and 30-day system cap emission limitations of §117.210, concerning System Cap.

The emission limits of the renumbered §117.206(e) address pollutants which may increase as an incidental result of compliance with the proposed NO x limits. The CO limit is consistent with the existing CO limit of §117.205(f) for RACT because nothing in these rules necessitates changing the existing limit. In rulemaking adopted on April 19, 2000, the commission intended to change the proposed ammonia limit of five ppm to ten ppm in the renumbered §117.205(e)(2) but inadvertently did not change the rule language. (See the May 5, 2000 issue of the Texas Register (25 TexReg 4146).) The proposed change to the renumbered §117.206(e)(2) makes this correction. The ammonia limit of ten ppm is lower than the existing limit of §117.205(g) and is supported by information from SCR vendors and ammonia test data for gas-fired boilers using SCR, not available when the original NO x RACT rules were adopted in 1993. The test data are reported in Table 2-5 of NESCAUM. It is desirable to minimize ammonia emissions because ammonia emissions create fine particulate matter, another form of air pollution. The commission is not including these related pollutant limits in the attainment demonstration SIP, in order to simplify the approval process for alternative emission specification under §107.221. This step will eliminate the need for case-specific SIP revisions to complete the approval of an alternate CO or ammonia limit.

With the exception of the availability of alternative CO and ammonia limits through §117.221, the revisions to the renumbered §117.206(f) specify that an owner or operator in HGA may not use the alternative plant-wide emission specifications in §117.207, the alternative case-specific specifications of §117.221, the source cap in §117.223, or the trading option in §117.570, except that EGFs shall also comply with the daily and 30-day system cap emission limitations of §117.210 of this title. This is necessary to ensure that any trading that occurs is done under the Chapter 101 mass emissions cap and trade program being noticed for public hearings and comment concurrently in this issue of the Texas Register . The owners and operators of the equipment addressed by these proposed Chapter 117 revisions will be required to use the compliance flexibility provided by the proposed Chapter 101 mass emissions cap and trade program, which will allow compliance to be established through the use of surplus reductions created from other sources.

In addition, the proposed changes to §117.206 also revise the renumbered §117.206(g) to make the exemptions of §117.206(g)(1) and (2) unavailable in HGA for consistency with the applicability of §117.206(c). The proposed changes to the renumbered §117.206(g)(1) also change the order of "commercial, institutional, or industrial" to "industrial, commercial, or institutional" for consistency with the title of this division.

The proposed changes to §117.207, concerning Alternative Plant-wide Emission Specifications, update cross-references to renumbered rules. The proposed changes to §117.207 also revise §117.207(b)(1) by changing references from "continuous emission monitors" to "continuous emissions monitoring system" and from "predictive emission monitors" to "predictive emissions monitoring system" for consistency with the definitions of these terms in §117.10(9) and (33), respectively. In addition, the proposed changes to §117.207(f) change references to §117.206(e), which should have been §117.206(f), to §117.206(g) to account for the subsection renumbering in §117.206. The proposed changes to §117.207 also revise references in §117.207(f)(1) from "gas turbines" and "engines" to "stationary gas turbines" and "stationary internal combustion engines" for consistency with the definition of these terms in §117.10(37) and (38), respectively.

Finally, the proposed changes to §117.207(f)(4) delete the superfluous term "steam generator" since a steam generator is simply a boiler and is already addressed by this term in the Chapter 117 rules, and revise a reference from "United States Environmental Protection Agency" to "EPA" because this abbreviation is defined in Chapter 3, concerning Definitions.

The proposed changes to §117.208, concerning Operating Requirements, correct the format of references to §§117.205 - 117.207 and 117.223 for consistency with Texas Register formatting requirements, and revise a reference in §117.208(d)(4) from "gas turbines" to "stationary gas turbines" for consistency with the definition of this term in §117.10(37).

The proposed new §117.210 establishes a system cap for units which generate electricity, but which will be subject to §117.206 rather than §117.106. The proposed new §117.210, would create a flexible method of complying with the NO x emission specifications proposed in §117.206 for units which meet the definition of EGF. The proposed section is patterned on the existing source cap compliance option in §117.108 for electric utilities. The proposed system cap sets limits on total pounds of NO x allowed to be emitted by EGFs which will not be subject to §117.106. A cap has the advantage over rate-based standards of allowing the source owner to control the activity levels of the regulated equipment as a means of compliance. This means that a company's compliance measures may include installing less extensive emission controls on a piece of equipment and choosing to operate it less, or upgrading its efficiency to require less fuel firing.

The proposed changes to §117.211, concerning Initial Demonstration of Compliance, revise §117.211(e)(5) by revising a reference from "United States Environmental Protection Agency" to "EPA" because this abbreviation is defined in Chapter 3, concerning Definitions.

The proposed changes to §117.213, concerning Continuous Demonstration of Compliance, add a new §117.213(a)(1)(B) which specifies the totalizing fuel flow meter requirements for units at major NO x sources in HGA which are subject to §117.206. All units which are listed in §117.201 will be subject to the totalizing fuel flow meter requirements because knowledge of the fuel usage is critical in determining the emission allocations for the proposed Chapter 101 mass emissions cap and trade program. The existing §117.213(a)(1)(A) - (D) is being renumbered as §117.213(a)(1)(A)(i) - (iv) to accommodate the new §117.213(a)(1)(B).

The proposed changes to §117.213 also revise the renumbered §117.213(a)(1)(A)(ii) (currently §117.213(a)(1)(B)) to reflect the renumbering of §117.203(6) and (8) as §117.203(a)(6) and (8) and the addition of the new §117.205(h)(10) - (11), and revise §117.213(b)(2)(A) and §117.213(c)(2)(A) to reflect the addition of the new §117.205(h)(8) - (11). The existing requirement in §117.213(b) for O 2 monitors on certain boilers and process heaters will continue to apply to these sources in HGA after the emission specifications of §117.206(c) supersede those of §117.205.

In addition, the proposed changes to §117.213 also add new §117.213(c)(G) - (I) to specify that the requirement to install a CEMS or PEMS NO x monitor applies to the following units in HGA: lime kilns, lightweight aggregate kilns, and units with a rated heat input greater than or equal to 100 MMBtu/hr which are subject to §117.206(c). The existing requirement in §117.213(c) for NO x monitors on certain boilers, process heaters, stationary gas turbines, and units which use a chemical reagent for reduction of NO x will continue to apply to these sources in HGA after the emission specifications of §117.206(c) supersede those of §117.205. Similarly, the existing requirement in §117.213(d) - (f) for CO monitoring, CEMS, and PEMS will continue to apply to these sources in HGA after the emission specifications of §117.206(c) supersede those of §117.205.

The proposed changes to §117.213 also revise §117.213(c)(1)(F) and (2)(A), and (k) (being renumbered as §117.213(k)(1)) to specify that these rules only apply to units in BPA or DFW, or to units in HGA which are subject to the NO x RACT emission specifications of §117.205. A new §117.213(k)(2) specifies that for units in HGA which are subject to the attainment demonstration emission specifications of §117.206(c), the methods required in §117.213 and §117.214 shall be used in conjunction with the requirements of Chapter 101, Subchapter H, Division 3 to determine compliance. The new §117.213(k)(2) further specifies that for enforcement purposes, the executive director may also use other commission compliance methods to determine whether the source is in compliance with applicable emission specifications.

In addition, the proposed changes to §117.213 revise a reference in §117.213(h) from "gas turbines" to "stationary gas turbines" for consistency with the definition of this term in §117.10(37); and revise §117.213(i) to reflect the renumbering of §117.203(6)(B) as §117.203(a)(6)(B).

Finally, the proposed revisions to the catchlines in §117.213(l) and (m) clarify that these subsections apply to the NO x RACT emission specifications of §117.205.

The proposed new §117.214 applies to units in HGA which are subject to the attainment demonstration limits of §117.206(c) and specifies monitoring and testing requirements. The proposed new §117.214(a) requires monitoring for NO x , CO, and fuel flow as specified in §117.213(a) and (c) - (f). The proposed new §117.214(b) requires testing of each unit which is subject to the emission limits of §117.106(c). The testing requirements are consistent with the testing previously required of these units for NO x RACT under §117.211.

Regarding emission allowances for the proposed Chapter 101 mass emissions cap and trade program, the proposed §117.214(c) specifies that the NOx testing and monitoring data specified in §117.214(a) and (b), together with the level of activity, as defined in §101.350, are used to establish the emission factor for the mass emissions cap and trade program. For units without CEMS or PEMS, retesting is required after any modifications which could increase the NO x emission rate, but is optional after any modifications which could decrease the NO x emission rate, including, but not limited to, installation of post-combustion controls, low-NO x burners, low excess air operation, staged combustion (for example, overfire air), FGR, and fuel-lean and conventional (fuel-rich) reburn. The NO x emission rate determined by the retesting establishes a new emission factor which must be used instead of the previously determined emission factor for the proposed Chapter 101 mass emissions cap and trade program.

The proposed changes to §117.216, concerning Final Control Plan Procedures for Attainment Demonstration Emission Specifications, revise §117.216(a)(1) to reference the proposed system cap of 117.210 and the Chapter 101 mass emissions cap and trade program being proposed concurrently in this issue of the Texas Register . This revision is necessary because the owners and operators of the equipment addressed by these proposed Chapter 117 revisions will be required to use the compliance flexibility provided by the proposed Chapter 101 mass emissions cap and trade program, which will allow compliance to be established through the use of surplus reductions created from other sources.

The proposed changes to §117.219, concerning Notification, Recordkeeping, and Reporting Requirements, amend §117.219(a) by correcting the reference to §101.11 to reflect the recent title change of this section from "Exemptions from Rules and Regulations" to "Demonstrations." (See the July 14, 2000 issue of the Texas Register (25 TexReg 6727)).

The proposed changes to §117.219 also replace the term "performance evaluation" with "relative accuracy test audit" in §117.219(b)(2) to more accurately describe the CEMS or PEMS performance evaluation; and replace the term "executive director" with "appropriate regional office" in §117.219(c) to more precisely specify where at the agency the test results are to be sent.

In addition, the proposed changes to §117.219 revise references in §117.219(d)(1)(A) and the renumbered §117.219(f)(4) from "gas turbine" to "stationary gas turbine" for consistency with the definition of this term in §117.10(37).

The proposed changes to §117.219 also revise a reference in the renumbered §117.219(f)(3) from "internal combustion engine" to "stationary internal combustion engine" for consistency with the definition of this term in §117.10(38), and revise a reference in the renumbered §117.219(f)(4) from "gas turbine" to "stationary gas turbine" for consistency with the definition of this term in §117.10(37).

In addition, the proposed revisions to §117.219(f) also renumber paragraphs (1 ) - (8) as (2) - (9) to accommodate the new §117.219(f)(1), and add a new §117.219(f)(1) in order to specify that records of annual fuel usage shall be kept for each unit subject to the totalizing fuel flow meter requirements of §117.213(a). Finally, the proposed changes to the renumbered §117.219(f)(3)(A)(i) correct a typographical error in a reference to §117.208(d)(7).

The proposed changes to §117.221, concerning Alternative Case Specific Specifications, revise §117.221(a) to reflect the renumbering of §117.206(d) as §117.206(e), and revise a reference in §117.211(b) from "United States Environmental Protection Agency" to "EPA" because this abbreviation is defined in Chapter 3, concerning Definitions.

The proposed requirements of §117.471, concerning Applicability; §117.473, concerning Exemptions; §117.475, concerning Emission Specifications; §117.478, concerning Operating Requirements; and §117.479, concerning Monitoring, Recordkeeping, and Reporting Requirements, apply to stationary reciprocating internal combustion engines, boilers, and process heaters located in HGA at stationary sources of NO x which are not major sources of NO x . Therefore, a new Division 2, concerning Boilers, Process Heaters, and Stationary Engines at Minor Sources, is being added to Subchapter D, concerning Small Combustion Sources.

The proposed limits are essential components of and consistent with the HGA Attainment Demonstration SIP, being noticed for public hearings and comment concurrently in a separate section of this issue of the Texas Register . The proposed emission limits and ozone attainment demonstration SIP are required by 42 USC, §7410 and §7511a, which require states to submit SIPs to the EPA which contain enforceable measures to achieve the NAAQS. The process by which the emission limits were developed is described in the Background and Summary of the Factual Basis for the Proposed Rules section of this preamble.

The proposed new §117.471 specifies that the new Division 2, concerning Boilers, Process Heaters, and Stationary Engines at Minor Sources, which is being added to Subchapter D, concerning Small Combustion Sources, applies to stationary reciprocating internal combustion engines, boilers, and process heaters located in HGA at a stationary source of NO x which is not a major source of NO x .

The proposed new §117.473 exempts boilers and process heaters with a maximum rated capacity of 2.0 MMBtu/hr or less. This exemption level is proposed because units with a maximum rated capacity of 2.0 MMBtu/hr or less are already regulated under Subchapter D, Division 1, concerning Water Heaters, Small Boilers, and Process Heaters.

In addition, the following engines are exempt in the proposed new §117.473: engines used in research and testing; engines used for purposes of performance verification and testing; engines used solely to power other engines or gas turbines during start-ups; engines operated exclusively for firefighting and/or flood control; engines used in response to and during the existence of any officially declared disaster or state of emergency; and engines used directly and exclusively by the owner or operator for agricultural operations necessary for the growing of crops or raising of fowl or animals. This exemption is consistent with the exemption in the renumbered §117.203(3) which is available for stationary sources of NO x which are major sources of NO x . The proposed new §117.473 also exempts stationary reciprocating internal combustion engines with a hp rating of 50 hp or less.

In addition, the proposed new §117.473 establishes an exemption for certain boilers and process heaters located at any stationary source of NOx which is not subject to Chapter 101, Subchapter H, Division 3. The boilers and process heaters qualify for this exemption if the maximum rated capacity is greater than 2.0 MMBtu/hr and less than 5.0 MMBtu/hr and the annual heat input is less than or equal to 1.8 (10 9 ) Btu per calendar year; or if the maximum rated capacity is equal to or greater than 5.0 MMBtu/hr and the annual heat input is less than or equal to 9.0 (10 9 ) Btu per calendar year. However, the totalizing fuel flow requirements of §117.479(a), (d), and (g)(1) will apply to these exempted units in order to document that the annual heat input conditions of the exemption are met.

The proposed new §117.473(c) exempts from the requirements of Chapter 117 all combustion units which would meet the requirements of a standard permit currently being developed for electricity-generating combustion units rated at less than ten MW in capacity and which emit no more than 0.015 lb NOx /MMBtu heat input. The commission is proposing this exemption to facilitate the distributed generation of electricity through authorization of relatively small electricity-producing units.

The proposed new §117.475 establishes a proposed emission limit of 0.036 lb NO x per MMBtu heat input (or alternatively, 30 ppmv NO x , at 3.0% O 2 , dry basis) for boilers and process heaters in HGA at non-major stationary sources of NO x . The proposed new §117.475 also establishes a proposed emission limit of 0.50 g NO x /hp-hr for gas-fired stationary reciprocating internal combustion engines in HGA at non-major stationary sources of NO x .

The proposed new §117.478 specifies techniques to be used to minimize NO x emissions. The proposed §117.478(b)(1) requires boilers to be operated with O 2 , CO, or fuel trim. Such systems can pay for themselves with fuel savings while reducing NO x due to low excess air operation and reduced firing. Fuel trim has been demonstrated as an effective control technique for natural gas fired boilers operating with FGR to achieve compliance with a 30 ppmv NO x limit.

The proposed new §117.478(b)(2) requires operation of boilers and process heaters equipped with forced FGR such that the proportional design rate of FGR is maintained over the operating range.

The proposed new §117.478(b)(3) requires operation of any post combustion controls such that the injection rate of the reducing agent (i.e., ammonia or urea) is maintained to limit NO x concentrations to no more than the NO x concentrations achieved at maximum rated capacity.

The proposed new §117.478(b)(4) requires engines controlled with nonselective catalytic reduction (NSCR) to be operated with an air-fuel ratio (AFR) controller which operates on exhaust O 2 or CO.

The proposed new §117.478(b)(5) requires engines to be checked for proper operation measuring and recording NO x and CO emissions at least quarterly and as soon as practicable after each occurrence of engine maintenance which may reasonably be expected to increase emissions, O 2 sensor replacement, or catalyst cleaning or catalyst replacement. The proposed new §117.478(b)(5) allows the use of stain tube indicators specifically designed to measure NOx concentrations, provided a hot air probe or equivalent device is used to prevent error due to high stack temperature, and three sets of concentration measurements are made and averaged. The proposed new §117.478(b)(5) allows the use of portable NO x analyzers.

The proposed new §117.479 specifies the monitoring, recordkeeping, and reporting requirements for boilers, process heaters, and engines which are subject to the emission specifications of §117.475.

The proposed new §117.479(a) requires installation of totalizing fuel flow meters because knowledge of the fuel usage is critical in determining the NO x emission rate as well as the emission allocations for the proposed Chapter 101 mass emissions cap and trade program.

The proposed new §117.479(b) does not require O 2 monitors, but instead specifies that if an owner or operator installs an O 2 monitor, then the criteria in §117.213(e) is the appropriate guidance for the location and calibration of the monitor.

The proposed new §117.479(c) does not require NO x monitors, but instead specifies that if an owner or operator installs a NO x monitor, then it must meet the CEMS or PEMS requirements of §117.213(e) or (f).

The proposed new §117.479(d) specifies that monitors must be installed on the schedule specified in §117.534.

The proposed new §117.479(e) specifies the testing requirements for boilers, process heaters, and engines which are subject to the emission limits of §117.475. These requirements are based upon the existing requirements of §117.211. The proposed §117.479 also specifies that for units without CEMS or PEMS, retesting is required after any modifications which could increase the NO x emission rate, but is optional after any modifications which could decrease the NO x emission rate, including, but not limited to, installation of post-combustion controls, low-NO x burners, low excess air operation, staged combustion (for example, overfire air), FGR, and fuel-lean and conventional (fuel-rich) reburn. The NO x emission rate determined by the retesting establishes a new emission factor which must be used instead of the previously determined emission factor for the proposed Chapter 101 mass emissions cap and trade program.

The proposed new §117.479(f) specifies that the NO x testing and monitoring data specified in §117.479(a) - (e), together with the level of activity, as defined in §101.350, are used to establish the emission factor for the proposed Chapter 101 mass emissions cap and trade program.

The proposed new §117.479(g) specifies the records to be used to demonstrate compliance with the emission limits of §117.475.

The proposed changes to §117.510, concerning Compliance Schedule for Utility Electric Generation, revise §117.510(c) to create separate paragraphs in this subsection addressing compliance schedules for the NO x RACT rules and the proposed emission specifications for attainment demonstrations. The commission is proposing a staged four-year implementation schedule for compliance with the new HGA emission specifications. First, one-third of the total reductions required to comply with the attainment demonstration emission specifications is required by December 31, 2002. The second one-third of the reductions is required by December 31, 2003. The final one-third of the reductions is required by December 31, 2004. A combination of combustion controls and flue gas cleanup controls will be necessary on many units.

The proposed revisions to §117.510(b)(2) modify the compliance schedule for utility boilers in DFW by allowing exclusion of boilers which are to be retired and decommissioned before May 1, 2005 from the calculation of the emission reductions to be made by May 1, 2003. This two-year compliance schedule extension will avoid the costs associated with installation of controls which would be used for a relatively short period of time, yet still achieve the necessary emission reductions before the critical 2005 ozone season. To qualify for this compliance date extension, a boiler must be designated by the Public Utility Commission of Texas to be necessary to operate for reliability of the electric system, and the owner must provide the executive director an enforceable written commitment by May 1, 2003 to retire and permanently decommission the boiler by May 1, 2005.

In addition, the proposed changes to §117.510 add the missing word "in" to §117.510(a)(2)(E)(iii) and (F) and the renumbered §117.510(b)(2)(A)(v)(III) and (vi). The proposed changes to §117.510 also make a variety of minor punctuation corrections throughout the section. Finally, the proposed changes to §117.510 revise §117.510(a)(2)(A)(i) and the renumbered §117.510(b)(2)(A)(i)(I) by replacing a reference to the effective date of these rules with the actual effective date, May 11, 2000.

The proposed changes to §117.520, concerning Compliance Schedule for Industrial, Commercial, and Institutional Combustion Sources in Ozone Nonattainment Areas, revise §117.520(c) to create separate paragraphs in this subsection addressing compliance schedules for the NO x RACT rules and the proposed emission specifications for attainment demonstrations. The commission is proposing a staged four-year implementation schedule for compliance with the new HGA emission specifications. First, one-third of the total reductions required to comply with the attainment demonstration emission specifications is required by December 31, 2002. The second one-third of the reductions is required by December 31, 2003. The final one-third of the reductions is required by December 31, 2004. A combination of combustion controls and flue gas cleanup controls will be necessary on many units.

In addition, the proposed changes to §117.520 add the missing word "in" to §117.520(a)(3)(B)(v) and (E)(iii) and the renumbered §117.510(b)(2)(A)(v)(III) and (vi). The proposed changes to §117.520 also revise §117.520(a), (b), and (c) by changing the order of "commercial, institutional, or industrial" to "industrial, commercial, or institutional" for consistency with the title of this division. Finally, the proposed changes to §117.520 revise §117.520(a)(3)(A)(i) by replacing a reference to the effective date of this rule with the actual effective date, May 11, 2000.

The proposed new §117.534 specifies the compliance schedule for boilers, process heaters, and stationary engines at minor sources in HGA.

PUBLIC UTILITY REGULATORY ACT DETERMINATION

As described earlier in this preamble, the commission proposes these revisions to Chapter 117 and the SIP in order to reduce NO x emissions and demonstrate attainment in the HGA ozone nonattainment area. Accordingly, the commission makes the following determination, as required by the Public Utility Regulatory Act (PURA), Texas Utilities Code (TUC), §39.263(c)(1)(A) and §39.263(c)(3): reductions of NO x made in compliance with this rulemaking are hereby determined to be an essential component in achieving compliance with the NAAQS for ground-level ozone; and the amount and location of reductions of NO x emissions resulting from this rulemaking are hereby determined to be consistent with the air quality goals and policies of the commission.

EFFECT ON SITES SUBJECT TO THE FEDERAL OPERATING PERMIT PROGRAM

Since Chapter 117 is an applicable requirement under 30 TAC Chapter 122, owners or operators subject to the Federal Operating Permit Program must, consistent with the revision process in Chapter 122, revise their operating permit to include the revised Chapter 117 requirements for each emission unit affected by the revisions to Chapter 117 at their site.

FISCAL NOTE: COSTS TO STATE AND LOCAL GOVERNMENTS

John Davis, Technical Specialist in the Strategic Planning and Appropriations Section, has determined that for the first five-year period the proposed amendments are in effect, there will be no significant fiscal implications for most units of state government and most units of local government as a result of administration or enforcement of the proposed amendments. However, there will be significant fiscal implications to the University of Houston and Baylor College of Medicine because they will be required to install emission controls on stationary sources of NO x emissions as a result of the proposed rules.

The proposed amendments would require a wide variety of stationary sources of NO x emissions in HGA to meet new emission specifications and other requirements in order to reduce NO x emissions and ozone air pollution. The affected equipment types and processes include electric utility boilers and stationary gas turbines; ICI boilers; duct burners used in turbine exhaust ducts; process heaters and furnaces; stationary internal combustion engines; fluid catalytic cracking units (including catalyst regenerators and associated CO boilers and furnaces); pulping liquor recovery furnaces; lime kilns; lightweight aggregate kilns; heat treating and reheat furnaces; magnesium chloride fluidized bed dryers; incinerators; and BIF units.

These standards and specifications are part of the strategy to reduce emissions of NO x necessary for the counties in the HGA ozone nonattainment area to be able to demonstrate attainment with the NAAQS for ozone. The proposed amendments are a necessary and essential component of the proposed HGA Attainment Demonstration SIP. A SIP is a plan developed for any region where existing (measured and estimated) ambient levels of pollutant exceeds the levels specified in a national standard. The plan sets forth a control strategy that provides emission reductions necessary for attainment and maintenance of the national standards.

For sources with a design capacity to emit NO x in amounts greater than or equal to ten tons per year (tpy), the commission is proposing a staged four-year implementation schedule for compliance with the new HGA emission specifications. First, one-third of the total reductions required to comply with the attainment demonstration emission specifications are required by December 31, 2002. The second one-third of the reductions are required by December 31, 2003. The final one-third of the reductions are required by December 31, 2004. For sources with a design capacity to emit NO x in amounts less than ten tpy, the final compliance date is December 31, 2002.

Most of the sources which will have to comply with the proposed rules are currently subject to air permits and are already being inspected for compliance. Consequently, only a limited number of additional facilities will need to be inspected for compliance with the proposed amendments. The commission anticipates that enforcement of these rules will not significantly increase the number of facilities currently inspected by the state and local governments.

The commission estimates that there may be other state and local government facilities affected by the proposed amendments that have not been identified in this fiscal note. State and local government facilities with equipment affected by the proposed amendments would be required to adhere to the proposed standards. Costs to those units would be similar as presented in this fiscal note.

Based upon an analysis of the 1997 emission inventory database, it is anticipated that four ICI boilers at the Baylor College of Medicine and three ICI boilers at the University of Houston and will be affected by the proposed amendments. The ICI boilers at the Baylor College of Medicine have a maximum capacity less than 40 MMBtu/hr. The new NO x emission standard for this type of boiler is 0.036 lb/MMBtu. It is estimated that the these boilers will have to reduce emissions by 0.01 tpd through the use of combustion modifications, such as low-NO x burners (LNB) or FGR. Total capital costs for the combustion modifications are estimated at $3,100 per MMBtu/hr, and the annual costs are estimated at $600 per MMBtu/hr. These cost estimates were derived from cost models on page E-23 of EPA's alternative control techniques (ACT) document, Alternative Control Techniques Document -- NO x Emissions from Industrial/Commercial/Institutional (ICI) Boilers . Total capital costs for the Baylor College of Medicine ICI gas-fired boilers are approximately $257,000 with an annual cost of $52,200. The average capital cost for each affected boiler is approximately $65,000 with an average annual cost of $13,000. Cost effectiveness for the proposed emission reductions is approximately $15,000 per ton of NO x reduced.

The three ICI boilers at the University of Houston are larger units, with capacities greater than 40 MMBtu/hr but less than 100 MMBtu/hr. The new NOx emission standard for this type of boiler is 0.015 lb/MMBtu. It is estimated that these ICI boilers will have to reduce emissions by 0.04 tpd through the use of SCR. In order to determine costs related to these ICI boilers, a spreadsheet provided by NESCAUM was used. This spreadsheet determines SCR costs based on the capacity of the affected unit. Capital costs for SCR on these boilers ranges from $70/kilowatt (kW) to $76/kW. Total capital costs for the University of Houston as a result of the proposed amendments are approximately $1.4 million with an annual cost of $384,000. The average capital cost for each affected boiler is approximately $467,000 with an average annual cost of $128,000. Cost effectiveness for the proposed emission reductions is approximately $27,000 per ton of NO x reduced.

PUBLIC BENEFIT AND COSTS

Mr. Davis has also determined that for each year of the first five years the proposed amendments to Chapter 117 are in effect, the public benefit anticipated from enforcement of and compliance with the proposed amendments will be a reduction of public exposure to NO x emitted from affected stationary sources, a reduction of ground-level ozone in ozone nonattainment areas, and conformance with the requirements of the FCAA, 42 USC, §§7410, 7502(a)(2), and 7511a(d) and (f).

The proposed amendments would require a wide variety of stationary sources of NO x emissions in HGA to meet new emission specifications and other requirements in order to reduce NO x emissions and ozone air pollution. The affected equipment types and processes include electric utility boilers and stationary gas turbines; ICI boilers; duct burners used in turbine exhaust ducts; process heaters and furnaces; stationary internal combustion engines; fluid catalytic cracking units (including catalyst regenerators and associated CO boilers and furnaces); pulping liquor recovery furnaces; lime kilns; lightweight aggregate kilns; heat treating furnaces; reheat furnaces; magnesium chloride fluidized bed dryers; incinerators; and BIF units.

The proposed amendments do not specify a particular control technology to achieve the emission limits and there are a variety of control technologies or combinations of control technologies which may be used to comply, depending on the specific circumstances of each affected source. In addition, the Chapter 101 mass emissions cap and trade program being proposed concurrently in this issue of the Texas Register establishes compliance flexibility through a mass emissions cap and trade program, which allows compliance to be established through the use of surplus reductions created from other sources.

There may be individual sources for which the equipment actual control costs are higher than those identified in this cost note. The numbers of sources affected by these rules are approximations which do not include all new sources which have been placed into service after 1997. Because these new sources have been permitted under rules which require the new emissions to be offset from existing sources, the counted number of sources will not vary significantly because of offsetting source shutdowns from obsolete equipment. The commission anticipates costs for units not addressed in this fiscal note would be similar to the overall findings of this analysis. Additionally, the commission has included cost for units affected by the proposed amendments that did not report any emission rate data for 1997. No rate data could indicate the unit has been shut down; however, for the purpose of this note, costs were estimated for these units and included in the overall total.

The proposed emission limit for electric utility boilers is 0.010 lb NOx /MMBtu heat input for gas-fired boilers and auxiliary steam boilers, 0.030 lb NO x /MMBtu heat input for oil- or coal-fired, tangential-fired boilers, and 0.030 lb NO x /MMBtu heat input for oil- or coal-fired, wall-fired boilers. The proposed 93% emission reduction, calculated from the average emissions of the electric utility boilers in the area during the baseline period, is expected to necessitate combustion modifications and SCR on the affected electric utility boilers.

Based upon an analysis of the 1997 emission inventory database, it is anticipated that 25 utility boilers and seven auxiliary boilers in HGA will be affected by the proposed amendments. It is estimated that these boilers will be required to reduce NO x emissions by 184.26 tpd (67,255 tpy). Capital cost of the utility boiler combustion modifications is estimated at $10/kW for the gas-fired combustion modifications, and $5/kW for the coal-fired modifications. The costs of SCR for the coal and gas-fired utility boilers are estimated from the cost models contained in Appendix D of Status Report on NO x Control Technologies and Cost Effectiveness for Utility Boilers , issued by NESCAUM (June 1998). In addition, the catalyst cost for the coal fired boilers was estimated from discussions with engineers familiar with SCR application, and the catalyst cost for gas-fired boilers was estimated based on more specific cost information from gas-fired installation in the Los Angeles area, as identified in the May 5, 2000 issue of the Texas Register (25 TexReg 4157). It is estimated that the cost of NO x reduction for the electric utility power boilers will range between approximately $1,000 to $8,000 per ton of NO x reduced. There are two utility systems affected by the proposed amendments. Total capital cost for the first utility system with 10,069 MW of electric generating capacity is $528 million with an increased annual cost of $88 million. This utility system has a mixture of gas- and coal-fired boilers. The average capital cost to gas-fired boilers in this utility system is $16 million with an average increased annual cost of $2.6 million. The average capital cost for coal-fired boilers in this system is $54 million with an average increased annual cost of $9.2 million. Total capital costs for the second utility system with 532 MW of capacity are $24 million with an increased annual cost of $5 million. The average capital cost for boilers in the smaller utility system is $12 million with an average increased annual cost of $2.3 million.

The proposed emission limits for gas-fired ICI boilers are 0.010 lb NOx per MMBtu heat input for boilers with a maximum rated capacity equal to or greater than 100 MMBtu/hr; 0.015 lb NO x per MMBtu heat input for boilers with a maximum rated capacity equal to or greater than 40 MMBtu/hr, but less than 100 MMBtu/hr; and 0.036 lb NOx per MMBtu heat input (or alternatively, 30 ppmv NOx , at 3.0% O 2 , dry basis) for boilers with a maximum rated capacity less 40 MMBtu/hr. The proposed 92% NO x emission reduction from ICI boilers is expected to necessitate SCR and combustion modifications.

Based upon an analysis of the 1997 emission inventory database, it is anticipated that 235 gas- fired ICI boilers with a maximum rated capacity less 40 MMBtu/hr in HGA will be affected by the proposed amendments. The commission estimates that these boilers will be required to reduce NO x emissions by 0.99 tpd (361 tpy) through the use of combustion modifications. Total capital costs for the combustion modifications are estimated at $3,100 per MMBtu/hr and the annual costs are estimated at $600 per MMBtu/hr. These cost estimates were derived from cost models on page E-23 of EPA's Alternative Control Techniques Document -- NO x Emissions from Industrial/Commercial/Institutional (ICI) Boilers . Total capital costs for ICI gas- fired boilers rated at 40 MMBtu/hr or less in HGA are approximately $8.1 million with an increased annual cost of $1.6 million. The average capital costs for boilers in this category are approximately $41,000 with an average increased annual cost of $8,300. Cost effectiveness for the proposed emission reductions from the affected boilers in this category is approximately $4,500 per ton of NO x reduced.

Based upon an analysis of the 1997 emission inventory database, it is anticipated that 90 gas-fired ICI boilers with a maximum rated capacity equal to or greater than 40 MMBtu/hr, but less than 100 MMBtu/hr in HGA will be affected by the proposed amendments. The commission estimates that these boilers will be required to reduce NO x emissions by 3.03 tpd (1,106 tpy) through the use of SCR. The costs of SCR for these ICI boilers were estimated from a spreadsheet provided by NESCAUM. Capital costs for SCR on the affected boilers range from $68/kW to $80/kW. Total capital costs for ICI boilers with a maximum rated capacity equal to or greater than 40 MMBtu/hr, but less than 100 MMBtu/hr in HGA are approximately $38 million with an increased annual cost of approximately $11 million. The average capital costs for boilers in this category are approximately $467,000 with an average increased annual cost of $135,000. Cost effectiveness for the proposed emission reductions from the affected boilers in this category is approximately $10,000 per ton of NO x reduced.

Based upon an analysis of the 1997 emission inventory database, it is anticipated that 180 gas- fired ICI boilers with a maximum rated capacity equal to or greater than 100 MMBtu/hr in HGA will be affected by the proposed amendments. The commission estimates that these boilers will be required to reduce NOx emissions by 53.24 tpd (19,433 tpy) through the use of SCR and combustion modifications. The costs of SCR for these ICI boilers were estimated from the NESCAUM spreadsheet, and combustion modification costs were estimated to be $10/kW. Capital costs for SCR on the affected boilers range from $49/kW to $80/kW. Total capital costs for ICI boilers with a maximum rated capacity equal to or greater than 100 MMBtu/hr in HGA are approximately $354 million with an increased annual cost of approximately $76 million. The average capital cost for boilers in this category is approximately $1.9 million with an average increased annual cost of $421,000. Cost effectiveness for the proposed emission reductions from the affected boilers in this category is approximately $4,000 per ton of NO x reduced.

The proposed emission limit for coke-fired boilers is 0.057 lb NOx per MMBtu heat input. The proposed 90% emission reduction is expected to necessitate SCR on the affected coke- fired boilers. Based upon an analysis of the 1997 emission inventory database, it is anticipated that one coke-fired ICI boiler in HGA will be affected by the proposed amendments. The commission estimates that this boiler will be required to reduce NOx emissions by 10.44 tpd (3,811 tpy) through the use of SCR. The costs of SCR for this ICI boiler were estimated from a spreadsheet provided by NESCAUM. Capital costs for SCR on the affected boiler are estimated to be $85/kW. Total capital costs for this coke-fired boiler are approximately $15 million with an increased annual cost of approximately $2.8 million. Cost effectiveness for the proposed emission reductions from this boiler is approximately $728 per ton of NO x reduced.

The proposed emission limit for wood fuel-fired boilers is 0.020 lb NOx per MMBtu heat input. The proposed 90% emission reduction is expected to necessitate SCR on the affected wood-fired boilers. Based upon an analysis of the 1997 emission inventory database, it is anticipated that three wood-fired ICI boilers in HGA will be affected by the proposed amendments. The commission estimates that these boilers will be required to reduce NOx emissions by 0.91 tpd (332 tpy) through the use of SCR and combustion modifications. The smallest of the three wood-fired boilers is a four MMBtu/hr unit. There are no cost estimates available for SCR installed on units of this size. Based on the NESCAUM spreadsheet, the overall capital costs would exceed $100/kW to install SCR on this unit; therefore, the owner or operator of this unit may decide to install combustion modifications and purchase allowances in order to meet required emission limits. The commission estimates the combustion modifications would cost approximately $31/kW. This estimate was derived from costs associated with a 17 MMBtu/hr watertube gas-fired boiler equipped with LNB and FGR which is listed in EPA's Alternative Control Techniques Document -- NO x Emissions from Industrial/Commercial/Institutional (ICI) Boilers . The costs of SCR for the two remaining wood-fired ICI boilers were estimated from a spreadsheet provided by NESCAUM. Capital costs for SCR on the two remaining boilers are approximately $55/kW and $71/kW. Total capital costs for the three wood-fired ICI boilers are approximately $3.5 million with an increased annual cost of approximately $825,000. The average capital cost for the larger two boilers is approximately $1.7 million with an average increased annual cost of $411,000. Cost effectiveness for the proposed emission reductions from the affected boilers in this category is approximately $2,525 per ton of NOx reduced.

The proposed emission limit for rice hull-fired boilers is 0.089 lb NOx per MMBtu heat input. The proposed 90% emission reduction is expected to necessitate SCR on the one rice hull-fired boiler contained in the inventory; however, according to agency records this boiler is currently shut down and there are no plans to reactivate this boiler. Consequently, the total annual fiscal impact for rice hull- fired boilers in HGA is assumed to be zero.

The proposed emission limit for oil-fired boilers is 2.0 lb NO x per 1,000 gallons of oil burned. The proposed 90% emission reduction is expected to necessitate SCR on the affected oil-fired boilers. Based upon an analysis of the 1997 emission inventory database, it is anticipated that three oil-fired ICI boilers will be affected by the proposed amendments. The commission estimates that these boilers will be required to reduce NOx emissions by 0.13 tpd (47 tpy) through the use of SCR and combustion modifications. Two of the units are low capacity three MMBtu/hr and eight MMBtu/hr boilers. There are no cost estimates available for SCR installed on units of this size. Based on the NESCAUM spreadsheet, the overall capital costs would exceed $90/kW to install SCR on these units; therefore, the owner or operator of these units may decide to install combustion modifications and purchase allowances in order to meet required emission limits. The commission estimates the combustion modifications would cost approximately $31/kW. This estimate was derived from costs associated with a 17 MMBtu/hr watertube gas-fired boiler equipped with LNB and FGR which is listed in EPA's Alternative Control Techniques Document -- NO x Emissions from Industrial/Commercial/Institutional (ICI) Boilers . The costs of SCR on the remaining boilers were estimated from spreadsheets provided by NESCAUM. Capital costs for SCR on the third oil-fired boiler are approximately $72/kW. Total capital costs for affected oil-fired ICI boilers in HGA is approximately $472,000 with an increased annual cost of approximately $135,000. Cost effectiveness for the proposed emission reductions from the affected boilers in this category is approximately $2,900 per ton of NOx reduced.

The commission estimates the total capital costs for the 513 identified ICI boilers affected by the proposed amendments are approximately $419 million with an annualized cost of $95 million. The overall estimated cost effectiveness for the proposed emission reductions for ICI boilers is approximately $3,800 per ton of NO x reduced.

The proposed emission limit for fluid catalytic cracking units (including CO boilers, CO furnaces, and catalyst regenerator vents) is ten ppmv NOx (at 0.0% O 2 , dry basis). The proposed 90% emission reduction is expected to necessitate SCR on the affected fluid catalytic cracking units (FCCUs).

Based upon an analysis of the 1997 emission inventory database, it is anticipated that 14 FCCUs at nine refineries in HGA will be affected by the proposed amendments. The commission estimates that these units will be required to reduce NOx emissions by 13.44 tpd (4,906 tpy) through the use of SCR. The costs of SCR for these FCCUs were estimated from a spreadsheet provided by NESCAUM. Capital costs for SCR on the affected FCCUs range from $46/kW to $60/kW. Total capital costs for affected FCCUs in HGA are approximately $38.5 million with an increased annual cost of approximately $8.6 million. The average capital costs for units in this category are approximately $2.7 million with an average increased annual cost of $616,000. Cost effectiveness for the proposed emission reductions from the affected FCCUs is approximately $1,800 per ton of NO x reduced.

The proposed emission limit for pulping liquor recovery furnaces is 0.050 lb NO x per MMBtu heat input. The proposed 64% NO x emission reduction is expected to necessitate SNCR on the affected pulping liquor recovery furnaces.

Based upon an analysis of the 1997 emission inventory database, it is anticipated that three pulping liquor recovery furnaces at two pulp mills in HGA will be affected by the proposed amendments. It is estimated that these units will be required to reduce NO x emissions by 1.09 tpd (398 tpy). Using the total annual cost estimates for SNCR for several types of wood-fired boilers in EPA's Alternative Control Techniques Document -- NO x Emissions from Industrial/Commercial/Institutional (ICI) Boilers , it is estimated that the cost effectiveness will range from approximately $2,000 to $4,500 per ton of NO x reduced. The total annual fiscal impact for pulping liquor recovery furnaces in HGA is approximately $850,000 to $1.7 million per year.

The proposed emission limits for kilns are 0.66 lb NO x per ton of CaO for lime kilns and 0.76 lb NO x per ton of product for lightweight aggregate kilns. The proposed 39% NO x emission reduction from the kiln category is expected to necessitate combustion controls (such as LNB, or mid-kiln firing and staged combustion) on the affected kilns.

Based upon an analysis of the 1997 emission inventory database, it is anticipated that two lime kilns at two pulp mills and three lightweight aggregate kilns at one lightweight aggregate plant in HGA will be affected by the proposed amendments. It is estimated that these units will be required to reduce NOx emissions by 0.30 tpd (110 tpy). Based on vendor quotes, installations of staged combustion technology would cost approximately $225,000 per kiln, with estimated annual operating costs of $10,000. Total capital costs for affected kilns in HGA are approximately $1.1 million with an increased annual cost of $125,000. Cost effectiveness for the proposed emission reductions from affected kilns is approximately $1,141 per ton of NO x reduced.

The proposed emission limits for heat treating and reheat furnaces are 0.087 lb NO x per MMBtu heat input for heat treating furnaces and 0.062 lb NO x per MMBtu heat input for reheat furnaces. The proposed 35% NO x emission reduction from the steel furnace category is expected to necessitate combustion controls (such as LNB) on the affected furnaces.

Based upon an analysis of the 1997 emission inventory database, it is anticipated that two heat treating furnaces and seven reheat furnaces at one steel processing plant in HGA will be affected by the proposed amendments. It is estimated that these units will be required to reduce NO x emissions by 0.39 tpd (142 tpy). Annual costs for combustion controls on these units was derived from Tables 7 and 8 on page 85 of the State and Territorial Air Pollution Program Administrators (STAPPA)/Association of Local Air Pollution Control Officials (ALAPCO) document titled Controlling Nitrogen Oxides Under the Clean Air Act: A Menu of Options . Based on the source, annualized costs for the installation of LNB on the affected heat treat furnaces would be approximately $70,000 and $35,000 for the reheat furnaces. The estimated total increased annual costs for affected furnaces are $385,000. Cost effectiveness for the proposed emission reductions from affected furnaces is approximately $2,705 per ton of NO x reduction.

The proposed emission limit for magnesium chloride fluidized bed dryers is a 90% reduction from 1997 ozone season daily NO x emissions. The proposed 41% NO x emission reduction from the dryer category would be expected to necessitate SCR on the one affected dryer; however, this dryer is currently shut down. According to the company, there are no plans to reactivate this dryer. Consequently, the total annual fiscal impact for dryers in HGA is assumed to be zero.

The proposed emission limit for incinerators is a 90% reduction from 1997 ozone season daily NO x emissions. The proposed 61% NO x emission reduction from this emission category is expected to necessitate SCR on the affected incinerators.

Based upon an analysis of the 1997 emission inventory database, it is anticipated that 23 incinerators at 16 refineries, chemical plants, and hazardous waste disposal operations in HGA will be affected by the proposed amendments. It is estimated that these units will be required to reduce NO x emissions by 3.62 tpd (1,321 tpy). The costs of SCR for these incinerators were estimated from a spreadsheet provided by NESCAUM. Capital costs for SCR on the affected incinerators are estimated to range from $49/kW to $72/kW. Total capital costs for these incinerators are approximately $28 million with an increased annual cost of approximately $6.3 million. The average capital cost for units in this category is approximately $1.2 million with an average increased annual cost of $272,000. Cost effectiveness for the proposed emission reductions from affected incinerators is approximately $4,800 per ton of NOx reduced.

The proposed emission limit for BIF units is 0.015 lb NO x per MMBtu heat input. The proposed 81% emission reduction is expected to necessitate SCR on the affected BIF units. The proposed emission limit reflects the installation of post-combustion controls, but not combustion controls, because combustion controls potentially could affect the VOC destruction efficiency when these units are burning waste-derived fuel. At the very least, installation of combustion controls potentially could trigger the requirements for a relatively costly trial burn.

Based upon an analysis of the 1997 emission inventory database, it is anticipated that 41 BIF units at 15 refineries and chemical plants in HGA will be affected by the proposed amendments. It is estimated that these units will be required to reduce NO x emissions by 9.95 tpd (3,632 tpy). The costs of SCR for these units was estimated from the NESCAUM spreadsheet for units with a capacity greater than 40 MMBtu/hr. The cost for SCR on a 50 MMBtu/hr gas-fired boiler, as documented in the STAPPA/ALAPCO document titled Controlling Nitrogen Oxides Under the Clean Air Act: A Menu of Options , was used for units with a capacity less than 40 MMBtu/hr. Capital costs for SCR installed on BIF units less than 40 MMBtu/hr are estimated to be $6,420 per MMBtu/hr with an annual cost of $1,510 per MMBtu/hr. Capital costs for the larger units would range from $49/kW to $65/kW. Total capital costs affected BIF units in HGA are approximately $45 million with an increased annual cost of approximately $10.7 million. The average capital costs for units in this category are approximately $1.1 million with an average increased annual cost of $256,000. Cost effectiveness for the proposed emission reductions from affected BIF units is approximately $3,000 per ton of NO x reduced.

The proposed emission limits for gas-fired process heaters are 0.010 lb NO x per MMBtu heat input for units with a maximum rated capacity equal to or greater than 100 MMBtu/hr; 0.015 lb NO x per MMBtu heat input for units with a maximum rated capacity equal to or greater than 40 MMBtu/hr, but less than 100 MMBtu/hr; and 0.036 lb NOx per MMBtu heat input (or alternatively, 30 ppmv NOx , at 3.0% O 2 , dry basis) for units with a maximum rated capacity less 40 MMBtu/hr. The proposed 88% NO x emission reduction is expected to necessitate SCR on many affected process heaters and combustion controls on smaller affected process heaters.

Based upon an analysis of the 1997 emission inventory database, it is anticipated that 726 process heaters with a maximum rated capacity less 40 MMBtu/hr in HGA will be affected by the proposed amendments. The commission estimates that these process heaters will be required to reduce NO x emissions by 4.33 tpd (1,580 tpy) through the use of combustion modifications such as LNB. Based on cost estimates found on page 49, Table 4 in the STAPPA/ALAPCO document titled Controlling Nitrogen Oxides Under the Clean Air Act: A Menu of Options , the commission estimates that the capital costs to install LNB on these process heaters are approximately $3,280 per MMBtu/hr with an annualized cost of approximately $560 per MMBtu/hr. The total capital costs for process heaters with a maximum rated capacity less than 40 MMBtu/hr are approximately $22.3 million with an increased annual cost of approximately $4 million. The average capital cost for units in this category is approximately $32,000 with an average increased annual cost of $5,700. The cost effectiveness for the proposed emission reductions from affected process heaters in this category is approximately $2,510 per ton of NOx reduced.

Based upon an analysis of the 1997 emission inventory database, it is anticipated that 216 process heaters with a maximum rated capacity greater than 40 MMBtu/hr, but less than 100 MMBtu/hr, in HGA will be affected by the proposed amendments. The commission estimates that these process heaters will be required to reduce NO x emissions by 12.84 tpd (4,686 tpy) through the use of SCR and combustion modifications. The costs of SCR for these incinerators were estimated from a spreadsheet provided by NESCAUM. Capital costs for SCR on the affected incinerators are estimated to range from $68/kW to $80/kW. Combustion modifications are estimated to cost $28/kW based on cost estimates found on page 49, Table 4 in the STAPPA/ALAPCO document titled Controlling Nitrogen Oxides Under the Clean Air Act: A Menu of Options . The total capital costs for process heaters with a maximum rated capacity greater than 40 MMBtu/hr, but less than 100 MMBtu/hr, are approximately $95 million with an increased annual cost of approximately $27 million. The average capital cost for units in this category is approximately $429,000 with an average increased annual cost of $120,000. The cost effectiveness for the proposed emission reductions from affected process heaters in this category is approximately $5,700 per ton of NO x reduced.

Based upon an analysis of the 1997 emission inventory database, it is anticipated that 424 process heaters with a maximum rated capacity greater than or equal to 100 MMBtu/hr in HGA will be affected by the proposed amendments. The commission estimates that these process heaters will be required to reduce NO x emissions by 79.35 tpd (28,963 tpy) through the use of SCR and combustion modifications. The costs of SCR for these process heaters were estimated from a spreadsheet provided by NESCAUM. Capital costs for SCR on the affected process heaters are estimated to range from $68/kW to $80/kW. Combustion modifications are estimated to cost $17/kW based on cost estimates found on page 49, Table 4 in the STAPPA/ALAPCO document titled Controlling Nitrogen Oxides Under the Clean Air Act: A Menu of Options . The total capital costs for process heaters with a maximum rated capacity greater than or equal to 100 MMBtu/hr are approximately $596 million with an increased annual cost of approximately $137 million. The average capital cost for units in this category is approximately $1.4 million with an average increased annual cost of $330,000. The cost effectiveness for the proposed emission reductions from affected process heaters in this category is approximately $4,700 per ton of NO x reduced.

Based upon an analysis of the 1997 emission inventory database, it is anticipated that one oil-fired process heater in HGA will be affected by the proposed amendments. The commission estimates that this process heater will be required to reduce NO x emissions by 0.04 tpd (15 tpy) through the use of SCR and combustion modifications . Based on cost estimates found on page 50, Table 5 in the STAPPA/ALAPCO document titled Controlling Nitrogen Oxides Under the Clean Air Act: A Menu of Options , the commission estimates SCR cost effectiveness will be approximately $2,300 per ton. The cost effectiveness for LNB is approximately $1,300 per ton. The total increased annual cost for this process heater is approximately $54,000.

The commission estimates that the total capital costs for the 1,367 process heaters affected by the proposed amendments are approximately $713 million with an increased annual cost of $168 million. The overall estimated cost effectiveness for the proposed emission reductions from affected process heaters is approximately $4,800 per ton of NO x reduced.

The proposed emission limits for gas-fired stationary reciprocating internal combustion engines are: 0.17 g NO x /hp-hr at sites with reciprocating gas-fired engine compressors totaling 3,000 hp or more in 1997 or later; 0.50 g NO x /hp-hr at sites with gas-fired compressors totaling less than 3,000 hp in 1997 or later; and 0.50 g NO x /hp-hr for dual-fuel, reciprocating engines.

The emission inventory indicates 38 sites in 1997 had gas-fired compressor engines totaling more than 3,000 hp. These locations include sixteen upstream gas plants or compressor stations, nine gas transmission or gas storage stations, seven chemical plants, four oil refineries, and two oil terminals.

The proposed limit of 0.17 g NO x /hp-hr at large compressor sites is expected to necessitate replacement with electric motors. The limit is approximately equal to the projected emission rate from electric generating facilities after the addition of Attainment Demonstration SIP NO x controls. Therefore, either adding emission controls to the engines to meet the limit or converting the site to electric drive would produce similar NO x reductions. The 3,000 hp or greater site compression threshold is intended to: maximize emission reductions by reducing 90% of the gas compressor engine NO x according to the more stringent emission limit; include sites with reasonable access to existing transmission lines; exclude smaller sites which are more likely to be located at greater distances from transmission lines; and avoid new transmission line costs to sites with small electric loads.

Since 1997, two of the 38 sites have been converted to electric drive compressors. The estimated costs of conversion to electric drive for the remaining sites are based on cost for one of these sites, documented in an application for property tax abatement for the pollution control project, filed with the commission in April, 2000. The total capital cost of $32.5 million for 42,500 hp of new electric compressors equates to $714/hp. This does not include the cost of upgraded electric transmission lines to the site, which cost approximately $700,000 per mile. The distance of new transmission lines necessary to deliver the appropriate electrical power to gas plants and compressor stations is estimated to average three miles. Operating cost savings for the project with cost information were estimated to include a reduction of eight full time positions to maintain 24,000 hp of existing gas-fired compressor engines and the value of emission credits from the shutdown of the engines. Energy costs were estimated to remain in balance, in part based on the ability to obtain wholesale electric rates. For this analysis, the annual operating costs will be assumed to remain in balance between energy costs and maintenance and emission credit savings.

An analysis of the inventory indicates about 118 gas-fired engines located at sites with less than 3,000 hp of compressor engines would be subject to the 0.5 g NO x /hp-hr limit. Of these, 12 engines reported emissions less than 0.5 g NO x /hp-hr in 1997. Of the remainder, there appear to be 87 rich-burn engines and 31 lean burn engines.

The proposed limit of 0.50 g NO x /hp-hr for gas-fired engines at sites with gas- fired compressors totaling less than 3,000 hp in 1997 or later is expected to be achieved with a combination of technologies. For rich-burn engines, the existing RACT limit of 2.0 g NOx /hp-hr has been met through application of non-selective catalytic reduction (NSCR) to many engines rated more than 150 hp. Many of these rich-burn engines are currently achieving 0.50 g NO x /hp-hr with NSCR. An additional catalyst module will be necessary for some of the rich burn engines to ensure compliance with the proposed limit. The total annualized cost of an additional catalyst module is estimated at $15/hp, based on vendor information. For lean-burn engines, the anticipated controls necessary to comply are a combination of combustion modifications to limit emissions to 5.0 g NO x /hp-hr or less, and then SCR to achieve the 0.50 g NO x /hp-hr emission limit. Combustion modifications to reduce emissions to 5.0 g NOx /hp-hr or less include low emission retrofits, high energy ignition, and high pressure fuel injection. Low emission combustion costs for this cost note were based on total capital ($315,000 + ($350*HP) and annualized ($71,300 + ($74.8*HP) cost equations on pages 6-33 and 6-38 of EPA's ACT document, Alternative Control Techniques Document NO x Emissions from Stationary Reciprocating Internal Combustion Engines . (EPA-453/R-93-032). Based on an analysis of the emission inventory data, the SCR reductions necessary range from 50% for engines with a current baseline of 1.0 g NO x /hp-hr, to 90% for engines which must initially reduce to 5.0 g NO x /hp-hr with combustion modification. The cost of SCR for gas-fired engines is estimated from the total capital ($310,000 + ($72.7*HP) and annualized ($140,000 + ($40*HP) cost equations on page 6-56 of the ACT document.

An analysis of the inventory indicates one dual-fuel electric generator engine would be subject to the 0.5 g NO x /hp-hr limit. This engine appears to currently operate at approximately 5.0 g NOx /hp-hr, such that a 92% efficient SCR would enable it to comply with the proposed limit without additional combustion modifications. The higher removal efficiency appears feasible because the literature contains examples of SCR operating at 92% removal efficiency on stationary diesel and gas-fired engines. The cost of SCR for the dual-fuel engine is estimated from the total capital ($187,000 + ($98*HP) and annualized ($37,300 + $16.3*HP) cost equations on page 6- 60 of the ACT document.

Based upon an analysis of the 1997 emission inventory database, it is anticipated that approximately 450 stationary gas-fired reciprocating internal combustion engines in HGA will be affected by the proposed amendments. It is estimated that these engines will be required to reduce NO x emissions by 78.50 tpd. Based on the referenced sources, it is estimated that the cost will range from approximately $50 to $25,000 per ton of NO x reduced. The total capital cost for gas-fired reciprocating internal combustion engines in HGA is approximately $441 million with an increased annual cost of approximately $63 million per year.

The proposed emission limits for stationary gas turbines and duct burners used in turbine exhaust ducts is 0.015 lb NO x per MMBtu heat input (about four ppmv, dry at 15% O 2 ). The proposed 92% NO x emission reduction is expected to necessitate SCR on affected stationary gas turbines and duct burners. In addition, for those gas turbines which are currently not achieving the RACT limit of 42 ppmv, it is anticipated that combustion modifications such as water or steam injection will also be necessary to achieve the proposed emission limits.

Based upon an analysis of the 1997 emission inventory database, it is anticipated that approximately 189 stationary gas turbines and any associated duct burners in HGA will be affected by the proposed amendments. Total annualized costs are estimated from cost tables 6-6, 6-9, 6-10, and 6- 12 of EPA's ACT document, Alternative Control Techniques Document NO x Emissions from Stationary Gas Turbines , (EPA-453/R-93-007). It is estimated that these units will be required to reduce NO x emissions by 141 tpd (51,465 tpy). It is estimated that the cost effective will range from approximately $1,000 to $25,000 per ton of NOx reduced, except for peaking gas turbines. For peaking gas turbines, it is estimated that the cost effectiveness will range from approximately $13,000 to $75,000 per ton of NO x reduced. Using the ACT document, the total capital costs for turbines in this category are approximately $403 million with an increased annual cost of $130 million per year.

Based on an analysis of the 1997 emission inventory database, the proposed continuous monitoring of boilers and heaters with heat input rated greater than or equal to 100 MMBtu/hr will require approximately an additional 300 boilers, heaters, and furnaces to install and operate NO x CEMS or PEMS. The commission estimates the initial cost of a CEMS which monitors NO x , oxygen, and flow to be approximately $137,400 to $179,600, with total annual costs of $64,800 to $66,000, based upon U.S. EPA's Continuous Emission Monitoring System Cost Model, Version 3.0 . Based on these figures, the total cost for the additional NO x CEMS or PEMS would be $54 million with an increased annual cost of approximately $20 million. It should be noted that this cost model provides the initial costs (including capital and installation costs) and annual costs (operating costs) for a single CEMS installed to monitor emissions from one source at a plant. In the cost model's user manual, the EPA notes that the cost model is not intended for use in estimating the costs for multiple CEMS to monitor multiple sources at a plant. Simply multiplying the number of CEMS by the model's result will overestimate the total cost since some of the costs are not repeated with the addition of a second CEMS or more.

Based on vendor quotes, it appears that the cost of CEMS has been dropping, such that the EPA cost model overestimates both the initial and annual costs. In addition, the proposed rules allow multiple stacks to share one CEMS, as well as allowing PEMS as an alternative to CEMS, which should further reduce the costs of complying with the proposed rules. It is generally recognized that a PEMS, which consists of equipment necessary for the continuous determination and recordkeeping of process gas concentrations and emission rates using process or control device operating parameters measurements and a conversion equation, graph, or computer program to produce results in units of the applicable emission limitation, are generally less expensive than a CEMS. Therefore, the costs estimated by the EPA's cost model could be expected to represent an upper bound of the monitoring costs.

Based on an analysis of the emissions inventory, there are approximately 600 industrial boilers, process heaters and furnaces with rated heat input between two MMBtu/hr and 40 MMBtu/hr, which would require fuel use meters to track annual emissions. Installed costs for fuel flow meters are estimated to range from $3,500 to $10,000 per meter. The total increased annual cost for additional fuel meters in HGA is approximately $0.5 million.

In addition to the direct emission control costs identified in this note, there are additional costs associated with lost production for those sources which will not be able to accommodate the installation of the control equipment during normal equipment outage periods. In some cases, there may be costs of lost production due to additional process outages related to emission control equipment start up.

The total capital cost for all known affected sources in HGA is approximately $2.7 billion with an increased annual cost of approximately $597 million.

SMALL BUSINESS AND MICRO-BUSINESS ASSESSMENT

The commission has been unable to identify any small or micro-businesses which would be affected by the proposed amendments. The majority of sites affected by the proposed amendments are large petrochemical and industrial businesses. If there are affected small or micro-businesses, the estimated capital and annualized cost for installing and operating the control technology used for the various types of units in this fiscal note would appear to be a reasonable cost estimate for small or micro-businesses. The proposed amendments would require a wide variety of stationary sources of NO x emissions in HGA to meet new emission specifications and other requirements in order to reduce NO x emissions and ozone air pollution. The affected equipment types and processes include electric utility boilers and stationary gas turbines; ICI boilers; duct burners used in turbine exhaust ducts; process heaters and furnaces; stationary internal combustion engines; FCCUs (including catalyst regenerators and associated CO boilers and furnaces); pulping liquor recovery furnaces; lime kilns; lightweight aggregate kilns; heat treating furnaces; reheat furnaces; magnesium chloride fluidized bed dryers; incinerators; and BIF units. The proposed amendments do not specify a particular control technology to achieve the emission limits and there may be other control technologies or combinations of control technologies which may be used to comply. In addition, the Chapter 101 mass emissions cap and trade program being proposed concurrently in this issue of the Texas Register establishes compliance flexibility through a mass emissions cap and trade program, which allows compliance to be established through the use of surplus reductions created from other sources.

DRAFT REGULATORY IMPACT ANALYSIS DETERMINATION

The commission has reviewed the proposed rulemaking in light of the regulatory analysis requirements of Texas Government Code, §2001.0225, and has determined that the rulemaking meets the definition of a "major environmental rule" as defined in that statute. "Major environmental rule" means a rule the specific intent of which is to protect the environment or reduce risks to human health from environmental exposure and that may adversely affect in a material way the economy, productivity, competition, jobs, the environment, or the public health and safety of the state or a sector of the state. The amendments to Chapter 117 will require emission reductions from electric utility boilers and stationary gas turbines; ICI boilers and stationary gas turbines; duct burners used in turbine exhaust ducts; process heaters and furnaces; stationary internal combustion engines; fluid catalytic cracking units (including catalyst regenerators and CO boilers and furnaces); pulping liquor recovery furnaces; lime kilns; lightweight aggregate kilns; heat treating furnaces; reheat furnaces; magnesium chloride fluidized bed dryers; incinerators; and BIF units in the HGA ozone nonattainment area. The rules are intended to protect the environment and reduce risks to human health and safety from environmental exposure and may have adverse effects on certain utilities, petrochemical plants, refineries, and other industrial, commercial, or institutional groups, and each group could be considered a sector of the economy. While the proposed amendments are intended to protect the environment, the commission believes they may adversely affect in a material way all sources in the HGA ozone nonattainment area with a potential to emit NO x in amounts greater than or equal to ten tpy, as well as boilers, heaters, and stationary engines with a potential to emit NO x in amounts less than ten tpy. These sources comprise sectors of the economy (including petroleum refineries, petrochemical plants, and electric generating plants) in a sector of the state. This is based on the analysis provided elsewhere in this preamble, including the discussion in the Public Benefit and Costs section.

The amendments implement requirements of the FCAA. Under 42 USC, §7410, states are required to adopt a SIP which provides for "implementation, maintenance, and enforcement" of the primary NAAQS in each air quality control region of the state. While 42 USC, §7410, does not require specific programs, methods, or reductions in order to meet the standard, state SIPs must include "enforceable emission limitations and other control measures, means or techniques (including economic incentives such as fees, marketable permits, and auctions of emissions rights), as well as schedules and timetables for compliance as may be necessary or appropriate to meet the applicable requirements of this chapter," (meaning Chapter 85, Air Pollution Prevention and Control). It is true that the FCAA does require some specific measures for SIP purposes, such as the inspection and maintenance program, but those programs are the exception, not the rule, in the SIP structure of the FCAA. The provisions of the FCAA recognize that states are in the best position to determine what programs and controls are necessary or appropriate in order to meet the NAAQS. This flexibility allows states, affected industry, and the public, to collaborate on the best methods for attaining the NAAQS for the specific regions in the state. Even though the FCAA allows states to develop their own programs, this flexibility does not relieve a state from developing a program that meets the requirements of 42 USC, §7410. Thus, while specific measures are not generally required, the emission reductions are required. States are not free to ignore the requirements of 42 USC, §7410, and must develop programs to assure that the nonattainment areas of the state will be brought into attainment on schedule.

The requirement to provide a fiscal analysis of proposed regulations in the Texas Government Code was amended by Senate Bill (SB) 633 during the 75th Legislative Session. The intent of SB 633 was to require agencies to conduct a regulatory impact analysis (RIA) of extraordinary rules. These are identified in the statutory language as major environmental rules that will have a material adverse impact and will exceed a requirement of state law, federal law, or a delegated federal program, or are adopted solely under the general powers of the agency. With the understanding that this requirement would seldom apply, the commission provided a cost estimate for SB 633 that concluded "based on an assessment of rules adopted by the agency in the past, it is not anticipated that the bill will have significant fiscal implications for the agency due to its limited application." The commission also noted that the number of rules that would require assessment under the provisions of the bill was not large. This conclusion was based, in part, on the criteria set forth in the bill that exempted proposed rules from the full analysis unless the rule was a major environmental rule that exceeds a federal law. As discussed earlier in this preamble, the FCAA does not require specific programs, methods, or reductions in order to meet the NAAQS; thus, states must develop programs for each nonattainment area to ensure that area will meet the attainment deadlines. Because of the ongoing need to address nonattainment issues, the commission routinely proposes and adopts SIP rules. The legislature is presumed to understand this federal scheme. If each rule proposed for inclusion in the SIP was considered to be a major environmental rule that exceeds federal law, then every SIP rule would require the full RIA contemplated by SB 633. This conclusion is inconsistent with the conclusions reached by the commission in its cost estimate and by the Legislative Budget Board (LBB) in its fiscal notes. Since the legislature is presumed to understand the fiscal impacts of the bills it passes, and that presumption is based on information provided by state agencies and the LBB, the commission believes that the intent of SB 633 was only to require the full RIA for rules that are extraordinary in nature. While the SIP rules will have a broad impact, that impact is no greater than is necessary or appropriate to meet the requirements of the FCAA. For these reasons, rules adopted for inclusion in the SIP fall under the exception in Texas Government Code, §2001.0225(a), because they are required by federal law.

In addition, 42 USC, §7502(a)(2), requires attainment as expeditiously as practicable, and 42 USC, §7511a(d), requires states to submit ozone attainment demonstration SIPs for severe ozone nonattainment areas such as HGA. The proposed rules, which reduce ambient NO x and ozone in HGA, will be submitted to the EPA as one of several measures of the required new attainment demonstrations. These rules will also implement NO x RACT for major sources in HGA which are not subject to the previous NO x RACT rules. The FCAA, 42 USC, §7511a(f), requires any moderate, serious, severe, or extreme ozone nonattainment area to implement NO x RACT, unless a demonstration is made that NO x reductions would not contribute to or would not be necessary for attainment of the ozone standard. By policy, the EPA requires photochemical grid modeling to demonstrate whether the 42 USC, §7511a(f), NO x measures would contribute to ozone attainment. The commission has performed photochemical grid modeling which predicts that NO x emission reductions, such as those required by these rules, will result in reductions in ozone formation in the HGA ozone nonattainment area and help bring HGA into compliance with the air quality standards established under federal law as NAAQS for ozone. The 42 USC, §7511a(f), exemption from NO x measures for HGA expired on December 31, 1997. The expiration of the exemption under 42 USC, §7511a(f), was based on the finding that NO x reductions in HGA are necessary for attainment of the ozone standard. Therefore, the proposed amendments are necessary components of and consistent with the ozone attainment demonstration SIP for HGA, required by 42 USC, §7410.

The proposed amendments do not meet any of the four applicability criteria of a "major environmental rule" as defined in the Texas Government Code. Section 2001.0225 applies only to a major environmental rule the result of which is to: (1) exceed a standard set by federal law, unless the rule is specifically required by state law; (2) exceed an express requirement of state law, unless the rule is specifically required by federal law; (3) exceed a requirement of a delegation agreement or contract between the state and an agency or representative of the federal government to implement a state and federal program; or (4) adopt a rule solely under the general powers of the agency instead of under a specific state law.

As discussed earlier, the proposed amendments implement requirements of the FCAA. There is no contract or delegation agreement that covers the topic that is the subject of this rulemaking. In addition, the proposed changes comply with the requirements of the Texas Health and Safety Code, Texas Clean Air Act (TCAA), §§382.011, 382.012, 382.016, 382.017, 382.018, and 382.051(d). Therefore, these proposed amendments do not exceed a standard set by federal law, exceed an express requirement of state law, exceed a requirement of a delegation agreement, nor are adopted solely under the general powers of the agency.

The commission invites public comment on the draft regulatory impact analysis.

TAKINGS IMPACT ASSESSMENT

The commission has prepared a takings impact assessment for these sections under Texas Government Code, §2007.043. The following is a summary of that assessment. The specific purposes of these amendments are: to develop a new attainment demonstration SIP for the ozone NAAQS for HGA; and to implement NO x RACT required by 42 USC, §7511a(f), for certain source categories. If adopted, certain sources located in HGA will be required to install new emission control equipment, and implement new operating, reporting, and recordkeeping requirements. Installation of the necessary control equipment could conceivably place a burden on private, real property. Also, Texas Government Code, §2007.003(b)(13), states that Chapter 2007 does not apply to an action that: (1) is taken in response to a real and substantial threat to public health and safety; (2) is designed to significantly advance the health and safety purpose; and (3)does not impose a greater burden than is necessary to achieve the health and safety purpose. Although the rule revisions do not directly prevent a nuisance or prevent an immediate threat to life or property, they do prevent a real and substantial threat to public health and safety and significantly advance the health and safety purpose. In addition, these amendments to fulfill an obligation mandated by federal law. The proposed amendments will implement requirements of 42 USC, §7410 and §7511a(f). This action is taken in response to the HGA area exceeding the federal ambient air quality standard for ground-level ozone, which adversely affects public health, primarily through irritation of the lungs. The action significantly advances the health and safety purpose by reducing ambient NO x and ozone levels in HGA. Attainment of the ozone standard will eventually require substantial NOx reductions. Any NO x reductions resulting from the current rulemaking are no greater than what the best scientific research indicates is necessary to achieve the desired ozone levels. However, this rulemaking is only one step among many necessary for attaining the ozone standard.

COASTAL MANAGEMENT PROGRAM CONSISTENCY REVIEW

The commission has determined that this rulemaking action relates to an action or actions subject to the Texas Coastal Management Program (CMP) in accordance with the Coastal Coordination Act of 1991, as amended (Texas Natural Resources Code, §§33.201 et seq.), and the commission's rules in 30 TAC Chapter 281, Subchapter B, concerning Consistency with the Texas Coastal Management Program. As required by 31 TAC §505.11(b)(2) and 30 TAC §281.45(a)(3), relating to actions and rules subject to the CMP, commission rules governing air pollutant emissions must be consistent with the applicable goals and policies of the CMP. The commission has reviewed this rulemaking action for consistency with the CMP goals and policies in accordance with the rules of the Coastal Coordination Council, and has determined that this rulemaking action is consistent with the applicable CMP goals and policies. The primary CMP policy applicable to this rulemaking action is the policy that commission rules comply with regulations at 40 CFR to protect and enhance air quality in the coastal area. The rules, which require additional reductions of air emissions in HGA, will result in reductions of ambient NO x and ozone concentrations. The proposed rules are consistent with the applicable CMP policy because they are consistent with Title 40. Title 40, Part 51, sets out requirements for states to prepare, adopt, and submit implementation plans for the attainment of the NAAQS. The adopted rules would be submitted to the EPA under these requirements. Interested persons may submit comments on the consistency of the proposed rules with the CMP during the public comment period.

ANNOUNCEMENT OF HEARINGS

The commission will hold public hearings on this proposal at the following times and locations: September 18, 2000, 10:00 a.m., Lone Star Convention Center, 9055 Airport Road (FM 1484), Conroe; September 18, 2000, 7:00 p.m., Lake Jackson Civic Center, 333 Highway 332 East, Lake Jackson; September 19, 2000, 10:00 a.m. and 7:00 p.m., George Brown Convention Center, 1001 Avenida de Las Americas, Houston; September 20, 2000, 9:00 a.m., VFW Hall, 6202 George Bush Drive, Katy; September 20, 2000, 6:00 p.m., East Harris County Community Center, 7340 Spencer, Pasadena; September 21, 2000, 10:00 a.m., Southeast Texas Regional Airport Media Room, 6000 Airline Drive, Beaumont; September 21, 2000, 2:00 p.m., Amarillo City Commission Chambers, City Hall, 509 East 7th Avenue, Amarillo; September 21, 2000, 6:00 p.m., Charles T. Doyle Convention Center, 21st Street at Phoenix Lane, Texas City; September 22, 2000, 10:00 a.m., Dayton High School, 2nd Floor Lecture Room, 3200 North Cleveland Street, Dayton; September 22, 2000, 11:00 a.m., El Paso City Council Chambers, 2 Civic Center Plaza, 2nd Floor, El Paso; September 22, 2000, 2:00 p.m., North Central Texas Council of Governments, 2nd Floor Board Room, 616 Six Flags Drive, Suite 200, Arlington; and September 25, 2000, 10:00 a.m., Texas Natural Resource Conservation Commission, 12100 North I-35, Building E, Room 201S, Austin. The hearings are structured for the receipt of oral or written comments by interested persons. Registration will begin one hour prior to each hearing. Individuals may present oral statements when called upon in order of registration. A four-minute time limit will be established at each hearing to assure that enough time is allowed for every interested person to speak. Open discussion will not occur during each hearing; however, agency staff members will be available to discuss the proposal one hour before each hearing, and will answer questions before and after each hearing.

Persons with disabilities who have special communication or other accommodation needs, who are planning to attend a hearing, should contact the Office of Environmental Policy, Analysis, and Assessment at (512) 239-4900. Requests should be made as far in advance as possible.

SUBMITTAL OF COMMENTS

Written comments may be submitted to Heather Evans, Office of Environmental Policy, Analysis, and Assessment, MC 206, P.O. Box 13087, Austin, Texas 78711-3087; faxed to (512) 239-4808; or emailed to siprules@tnrcc.state.tx.us . All comments should reference Rule Log Number 2000-011H-117-AI. Comments must be received by 5:00 p.m., September 25, 2000. For further information or questions concerning this proposal, please contact Randy Hamilton at (512) 239-1512 or Eddie Mack at (512) 239-1488.

Subchapter A. DEFINITIONS

30 TAC §117.10

STATUTORY AUTHORITY

The amendment is proposed under the Texas Health and Safety Code, TCAA, §382.011, concerning General Powers and Duties, which provides the commission with the authority to establish the level of quality to be maintained in the state's air and the authority to control the quality of the state's air; §382.012, concerning State Air Control Plan, which requires the commission to develop plans for protection of the state's air, such as the SIP; §382.016, concerning Monitoring Requirements; Examination of Records, which authorizes the commission to prescribe requirements for owners or operators of sources to make and maintain records of emissions measurements; §382.017, concerning Rules, which provides the commission with the authority to adopt rules consistent with the policy and purposes of the TCAA; and §382.051(d), concerning Permitting Authority of Board; Rules, which authorizes the commission to adopt rules as necessary to comply with changes in federal law or regulations applicable to permits under Chapter 382.

The proposed amendment implements the Texas Health and Safety Code, TCAA, §§382.011, 382.012, 382.016, 382.017, and 382.051(d).

§117.10.Definitions.

Unless specifically defined in the Texas Clean Air Act or Chapter 101 of this title (relating to General Air Quality Rules), the terms in this chapter shall have the meanings commonly used in the field of air pollution control. Additionally, the following meanings apply, unless the context clearly indicates otherwise.

(1) - (5)

(No change.)

(6)

Boiler [ or steam generator ] - Any combustion equipment fired with solid, liquid, and/or gaseous fuel used to produce steam.

(7) - (10)

(No change.)

(11)

Electric generating facility (EGF) - A facility that generates electric energy for compensation and is owned or operated by a person in this state, including a municipal corporation, electric cooperative, or river authority.

(12)

[ (11) ] Electric power generating system - One electric power generating system consists of either:

(A)

All boilers, [ steam generators, ] auxiliary steam boilers, and stationary gas turbines that generate electric energy for compensation; are owned or operated by a municipality or a Public Utility Commission of Texas regulated utility, or any of its successors; and are entirely located in one of the following ozone nonattainment areas:

(i)

Beaumont/Port Arthur;

(ii)

Dallas/Fort Worth;

(iii)

Houston/Galveston; or

(B)

All boilers, [ steam generators, ] auxiliary steam boilers, and stationary gas turbines that generate electric energy for compensation; are owned or operated by an electric cooperative, independent power producer, municipality, river authority, or public utility, or any of its successors; and are located in Atascosa, Bastrop, Bexar, Brazos, Calhoun, Cherokee, Fannin, Fayette, Freestone, Goliad, Gregg, Grimes, Harrison, Henderson, Hood, Hunt, Lamar, Limestone, Marion, McLennan, Milam, Morris, Nueces, Parker, Red River, Robertson, Rusk, Titus, Travis, Victoria, or Wharton County.

(13)

[ (12) ] Functionally identical replacement - A unit that performs the same function as the existing unit which it replaces, with the condition that the unit replaced must be physically removed or rendered permanently inoperable before the unit replacing it is placed into service.

(14)

[ (13) ] Heat input - The chemical heat released due to fuel combustion in a unit, using the higher heating value of the fuel. This does not include the sensible heat of the incoming combustion air. In the case of carbon monoxide (CO) boilers, the heat input includes the enthalpy of all regenerator off-gases and the heat of combustion of the incoming carbon monoxide and of the auxiliary fuel. The enthalpy change of the fluid catalytic cracking unit regenerator off-gases refers to the total heat content of the gas at the temperature it enters the CO boiler, referring to the heat content at 60 degrees Fahrenheit, as being zero.

(15)

[ (14) ] High heat release rate - A ratio of boiler design heat input to firebox volume (as bounded by the front firebox wall where the burner is located, the firebox side waterwall, and extending to the level just below or in front of the first row of convection pass tubes) greater than or equal to 70,000 British thermal units (Btu) per hour per cubic foot.

(16)

[ (15) ] Horsepower rating - The engine manufacturer's maximum continuous load rating at the lesser of the engine or driven equipment's maximum published continuous speed.

(17)

[ (16) ] Industrial boiler [ or steam generator ] - Any combustion equipment, not including utility or auxiliary steam boilers as defined in this section, fired with liquid, solid, or gaseous fuel, that is used to produce steam.

(18)

[ (17) ] International Standards Organization (ISO) conditions - ISO standard conditions of 59 degrees Fahrenheit, 1.0 atmosphere, and 60% relative humidity.

(19)

[ (18) ] Large DFW system - All boilers, [ steam generators, ] auxiliary steam boilers, and stationary gas turbines that are located in the Dallas/Fort Worth ozone nonattainment area, are part of one electric power generating system, and, on January 1, 2000, had a combined electric generating capacity equal to or greater than 500 megawatts.

(20)

[ (19) ] Lean-burn engine - A spark-ignited or compression-ignited, Otto cycle, diesel cycle, or two-stroke engine that is not capable of being operated with an exhaust stream oxygen concentration equal to or less than 0.5% by volume, as originally designed by the manufacturer.

(21)

[ (20) ] Low annual capacity factor boiler, process heater, or gas turbine supplemental waste heat recovery unit - An industrial, [ A ] commercial, or institutional [ , or industrial ] boiler; process heater; or gas turbine supplemental waste heat recovery unit with maximum rated capacity:

(A)

greater than or equal to 40 million Btu per hour (MMBtu/hr), but less than 100 MMBtu/hr and an annual heat input less than or equal to 2.8(10 11 ) Btu per year (Btu/yr), based on a rolling 12-month average; or

(B)

greater than or equal to 100 MMBtu/hr and an annual heat input less than or equal to 2.2(10 11 ) Btu/yr, based on a rolling 12-month average.

(22)

[ (21) ] Low annual capacity factor stationary gas turbine or stationary internal combustion engine - A stationary gas turbine or stationary internal combustion engine which is demonstrated to operate less than 850 hours per year, based on a rolling 12-month average.

(23)

[ (22) ] Low heat release rate - A ratio of boiler design heat input to firebox volume less than 70,000 Btu per hour per cubic foot.

(24)

[ (23) ] Major source - Any stationary source or group of sources located within a contiguous area and under common control that emits or has the potential to emit:

(A)

at least 50 tons per year (tpy) of nitrogen oxides (NOx ) and is located in the Beaumont/Port Arthur ozone nonattainment area;

(B)

at least 50 tpy of NO x and is located in the Dallas/Fort Worth ozone nonattainment area;

(C)

at least 25 tpy of NO x and is located in the Houston/Galveston ozone nonattainment area; or

(D)

the amount specified in the major source definition contained in the Prevention of Significant Deterioration of Air Quality regulations promulgated by EPA in Title 40 Code of Federal Regulations (CFR) §52.21 as amended June 3, 1993 (effective June 3, 1994) and is located in Atascosa, Bastrop, Bexar, Brazos, Calhoun, Cherokee, Comal, Ellis, Fannin, Fayette, Freestone, Goliad, Gregg, Grimes, Harrison, Hays, Henderson, Hood, Hunt, Lamar, Limestone, Marion, McLennan, Milam, Morris, Nueces, Parker, Red River, Robertson, Rusk, Titus, Travis, Victoria, or Wharton County.

(25)

[ (24) ] Maximum rated capacity - The maximum design heat input, expressed in MMBtu/hr, unless:

(A)

the unit is a boiler, utility boiler, or process heater operated above the maximum design heat input (as averaged over any one-hour period), in which case the maximum operated hourly rate shall be used as the maximum rated capacity; or

(B)

the unit is limited by operating restriction or permit condition to a lesser heat input, in which case the limiting condition shall be used as the maximum rated capacity; or

(C)

the unit is a stationary gas turbine, in which case the manufacturer's rated heat consumption at the International Standards Organization (ISO) conditions shall be used as the maximum rated capacity, unless limited by permit condition to a lesser heat input, in which case the limiting condition shall be used as the maximum rated capacity; or

(D)

the unit is a stationary, internal combustion engine, in which case the manufacturer's rated heat consumption at Diesel Equipment Manufacturer's Association or ISO conditions shall be used as the maximum rated capacity, unless limited by permit condition to a lesser heat input, in which case the limiting condition shall be used as the maximum rated capacity.

(26)

[ (25) ] Megawatt (MW) rating - The continuous MW rating or mechanical equivalent by a gas turbine manufacturer at ISO conditions, without consideration to the increase in gas turbine shaft output and/or the decrease in gas turbine fuel consumption by the addition of energy recovered from exhaust heat.

(27)

[ (26) ] Nitric acid - Nitric acid which is 30% to 100% in strength.

(28)

[ (27) ] Nitric acid production unit - Any source producing nitric acid by either the pressure or atmospheric pressure process.

(29)

[ (28) ] Nitrogen oxides (NOx ) - The sum of the nitric oxide and nitrogen dioxide in the flue gas or emission point, collectively expressed as nitrogen dioxide.

(30)

[ (29) ] Parts per million by volume (ppmv) - All ppmv emission limits specified in this chapter are referenced on a dry basis.

(31)

[ (30) ] Peaking gas turbine or engine - A stationary gas turbine or engine used intermittently to produce energy on a demand basis.

(32)

[ (31) ] Plant-wide emission limit - The ratio of the total allowable nitrogen oxides mass emissions rate dischargeable into the atmosphere from affected units at a major source when firing at their maximum rated capacity to the total maximum rated capacities for those units.

(33)

[ (32) ] Plant-wide emission rate - The ratio of the total actual nitrogen oxides mass emissions rate discharged into the atmosphere from affected units at a major source when firing at their maximum rated capacity to the total maximum rated capacities for those units.

(34)

[ (33) ] Predictive emissions [ emission ] monitoring system (PEMS) - The total equipment necessary for the continuous determination and recordkeeping of process gas concentrations and emission rates using process or control device operating parameter measurements and a conversion equation, graph, or computer program to produce results in units of the applicable emission limitation.

(35)

[ (34) ] Process heater - Any combustion equipment fired with liquid and/or gaseous fuel which is used to transfer heat from combustion gases to a process fluid, superheated steam, or water for the purpose of heating the process fluid or causing a chemical reaction. The term "process heater" does not apply to any unfired waste heat recovery heater that is used to recover sensible heat from the exhaust of any combustion equipment, or to boilers [ or steam generators ] as defined in this section.

(36)

[ (35) ] Rich-burn engine - A spark-ignited, Otto cycle, four-stroke, naturally aspirated or turbocharged engine that is capable of being operated with an exhaust stream oxygen concentration equal to or less than 0.5% by volume, as originally designed by the manufacturer.

(37)

[ (36) ] Small DFW system - All boilers, [ steam generators, ] auxiliary steam boilers, and stationary gas turbines that are located in the Dallas/Fort Worth ozone nonattainment area, are part of one electric power generating system, and, on January 1, 2000, had a combined electric generating capacity less than 500 megawatts.

(38)

[ (37) ] Stationary gas turbine - Any gas turbine system that is gas and/or liquid fuel fired with or without power augmentation. This unit is either attached to a foundation at a major source or is portable equipment operated at a specific major source for more than 90 days in any 12- month period. Two or more gas turbines powering one shaft shall be treated as one unit.

(39)

[ (38) ] Stationary internal combustion engine - A reciprocating engine that remains or will remain at a location (a single site at a building, structure, facility, or installation) for more than 12 consecutive months. Included in this definition is any engine that, by itself or in or on a piece of equipment, is portable, meaning designed to be and capable of being carried or moved from one location to another. Indicia of portability include, but are not limited to, wheels, skids, carrying handles, dolly, trailer, or platform. Any engine (or engines) that replaces an engine at a location and that is intended to perform the same or similar function as the engine being replaced is included in calculating the consecutive residence time period. An engine is considered stationary if it is removed from one location for a period and then returned to the same location in an attempt to circumvent the consecutive residence time requirement.

(40)

[ (39) ] System-wide emission limit - The ratio of the total allowable nitrogen oxides mass emissions rate dischargeable into the atmosphere from affected units in an electric power generating system or portion thereof located within a single ozone nonattainment area when firing at their maximum rated capacity to the total maximum rated capacities for those units. For fuel oil firing, average activity levels shall be used in lieu of maximum rated capacities for the purpose of calculating the system-wide emission limit.

(41)

[ (40) ] System-wide emission rate - The ratio of the total actual nitrogen oxides mass emissions rate discharged into the atmosphere from affected units in an electric power generating system or portion thereof located within a single ozone nonattainment area when firing at their maximum rated capacity to the total maximum rated capacities for those units. For fuel oil firing, average activity levels shall be used in lieu of maximum rated capacities for the purpose of calculating the system-wide emission rate.

(42)

[ (41) ] Thirty-day rolling average - An average, calculated for each day that fuel is combusted in a unit, of all the hourly emissions data for the preceding 30 days that fuel was combusted in the unit.

(43)

[ (42) ] Twenty-four hour rolling average - An average, calculated for each hour that fuel is combusted (or acid is produced, for a nitric or adipic acid production unit), of all the hourly emissions data for the preceding 24 hours that fuel was combusted in the unit.

(44)

[ (43) ] Unit - A unit consists of either:

(A)

for the purposes of §117.105 and §117.205 of this title (relating to Emission Specifications for Reasonably Available Control Technology) and each requirement of this chapter associated with §117.105 and §117.205 of this title, any [ Any ] boiler, [ steam generator, ] process heater, stationary gas turbine, or stationary internal combustion engine, as defined in this section ; or [ . ]

(B)

for the purposes of §117.106 and §117.206 of this title (relating to Emission Specifications for Attainment Demonstrations) and each requirement of this chapter associated with §117.106 and §117.206 of this title, any boiler, process heater, stationary gas turbine, or stationary internal combustion engine, as defined in this section, or any other stationary source of nitrogen oxides (NO x ) at a major source, as defined in this section.

(45)

[ (44) ] Utility boiler [ or steam generator ] - Any combustion equipment owned or operated by a municipality or Public Utility Commission of Texas regulated utility, fired with solid, liquid, and/or gaseous fuel, used to produce steam for the purpose of generating electricity.

(46)

[ (45) ] Wood - Wood, wood residue, bark, or any derivative fuel or residue thereof in any form, including, but not limited to, sawdust, sander dust, wood chips, scraps, slabs, millings, shavings, and processed pellets made from wood or other forest residues.

This agency hereby certifies that the proposal has been reviewed by legal counsel and found to be within the agency's legal authority to adopt.

Filed with the Office of the Secretary of State, on August 11, 2000.

TRD-200005644

Margaret Hoffman

Director, Environmental Law Division

Texas Natural Resource Conservation Commission

Earliest possible date of adoption: September 24, 2000

For further information, please call: (512) 239-0348


Subchapter B. COMBUSTION AT MAJOR SOURCES

1. UTILITY ELECTRIC GENERATION IN OZONE NONATTAINMENT AREAS

30 TAC §§117.101, 117.103, 117.105, 117.106, 117.108, 117.111, 117.113, 117.114, 117.116, 117.119, 117.121

STATUTORY AUTHORITY

The amendments and new sections are proposed under the Texas Health and Safety Code, TCAA, §382.011, concerning General Powers and Duties, which provides the commission with the authority to establish the level of quality to be maintained in the state's air and the authority to control the quality of the state's air; §382.012, concerning State Air Control Plan, which requires the commission to develop plans for protection of the state's air, such as the SIP; §382.016, concerning Monitoring Requirements; Examination of Records, which authorizes the commission to prescribe requirements for owners or operators of sources to make and maintain records of emissions measurements; §382.017, concerning Rules, which provides the commission with the authority to adopt rules consistent with the policy and purposes of the TCAA; and §382.051(d), concerning Permitting Authority of Board; Rules, which authorizes the commission to adopt rules as necessary to comply with changes in federal law or regulations applicable to permits under Chapter 382.

The proposed amendments and new sections implement the Texas Health and Safety Code, TCAA, §§382.011, 382.012, 382.016, 382.017, and 382.051(d).

§117.101.Applicability.

(a)

The provisions of this division (relating to Utility Electric Generation in Ozone Nonattainment Areas) shall apply to the following units used in an electric power generating system, as defined in §117.10(12)(A) [ §117.10(11)(A) ] of this title (relating to Definitions) , owned or operated by a municipality or a Public Utility Commission of Texas (PUC) regulated utility, or any of their successors, regardless of whether the successor is a municipality or is regulated by the PUC, located within the Beaumont/Port Arthur, Houston/Galveston, or Dallas/Fort Worth ozone nonattainment areas:

(1)

(No change.)

[ (2)

steam generators;]

(2)

[ (3) ] auxiliary steam boilers; and

(3)

[ (4) ] stationary gas turbines.

(b)

(No change.)

§117.103.Exemptions.

(a)

Reasonably available control technology. Units exempted from the provisions of §§117.105, 117.107, and 117.113 of this title (relating to Emission Specifications for Reasonably Available Control Technology (RACT); Alternative System-wide Emission Specifications; and Continuous Demonstration of Compliance) [ this division (relating to Utility Electric Generation in Ozone Nonattainment Areas) ], except as may be specified in §117.113(h),(i), and (j) [ §117.113(i) ] of this title [ (relating to Continuous Demonstration of Compliance) ], include the following:

(1)

(No change.)

(2)

any utility boiler, [ steam generator, ] or auxiliary steam boiler with an annual heat input less than or equal to 2.2(10 11 ) Btu per year; or

(3)

(No change.)

(b)

Emission specifications for attainment demonstrations. Stationary gas turbines and engines which are used solely to power other engines or gas turbines during start-ups are exempt from the provisions of §§117.106, 117.108, and 117.113 of this title (relating to Emission Specifications for Attainment Demonstrations; System Cap; and Continuous Demonstration of Compliance), except as may be specified in §117.113(i) of this title.

(c)

[ (b) ] Emergency fuel oil firing.

(1)

The fuel oil firing emission limitations [ limitation ] of §§117.105(c), 117.106(a), (b), and (c)(1)(B), 117.107(b), and 117.108 [ §117.105(c) or §117.107(b) ] of this title [ (relating to Emissions Specifications in Ozone Nonattainment Areas and Alternative System-wide Emission Specifications) ] shall not apply during an emergency operating condition declared by the Electric Reliability Council of Texas or the Southwest Power Pool, or any other emergency operating condition which necessitates oil firing. All findings that emergency operating conditions exist are subject to the approval of the executive director.

(2)

The owner or operator of an affected unit shall give the executive director and any local air pollution control agency having jurisdiction verbal notification as soon as possible but no later than 48 hours after declaration of the emergency. Verbal notification shall identify the anticipated date and time oil firing will begin, duration of the emergency period, affected oil-fired equipment, and quantity of oil to be fired in each unit, and shall be followed by written notification containing this information no later than five days after declaration of the emergency.

(3)

The owner or operator of an affected unit shall give the executive director and any local air pollution control agency having jurisdiction final written notification as soon as possible but no later than two weeks after the termination of emergency fuel oil firing. Final written notification shall identify the actual dates and times that oil firing began and ended, duration of the emergency period, affected oil-fired equipment, and quantity of oil fired in each unit.

(d)

Distributed generation. Upon issuance of a standard permit by the commission for the distributed generation of electricity, combustion sources registered under that permit are exempt from this chapter.

§117.105.Emission Specifications for Reasonably Available Control Technology (RACT).

(a)

No person shall allow the discharge into the atmosphere from any utility boiler [ ,steam generator, ] or auxiliary steam boiler, emissions of nitrogen oxides (NO x ) in excess of 0.26 pound per million (MM) Btu heat input on a rolling 24-hour average and 0.20 pound per MMBtu heat input on a 30-day rolling average while firing natural gas or a combination of natural gas and waste oil.

(b)

No person shall allow the discharge into the atmosphere from any utility boiler [ or steam generator ], NO x emissions in excess of 0.38 pound per MMBtu heat input for tangentially-fired units on a rolling 24-hour averaging period or 0.43 pound per MMBtu heat input for wall-fired units on a rolling 24-hour averaging period while firing coal.

(c)

No person shall allow the discharge into the atmosphere from any utility boiler [ , steam generator, ] or auxiliary steam boiler, NO x emissions in excess of 0.30 pound per MMBtu heat input on a rolling 24-hour averaging period while firing fuel oil only.

(d)

No person shall allow the discharge into the atmosphere from any utility boiler [ , steam generator, ] or auxiliary steam boiler, NO x emissions in excess of the heat input weighted average of the applicable emission limits specified in subsections (a) - (c) of this section on a rolling 24-hour averaging period while firing a mixture of natural gas and fuel oil, as follows:

Figure: 30 TAC §117.105(d) (No change.)

(e) - (g)

(No change.)

(h)

No person shall allow the discharge into the atmosphere from any utility boiler [ , steam generator, ] or auxiliary steam boiler subject to the NO x emission limits specified in subsections (a) - (e)of this section, carbon monoxide (CO) emissions in excess of 400 ppmv at 3.0% O 2 , dry (or alternatively, 0.30 pound per MMBtu heat input), based on :

(1) - (2)

(No change.)

(i) - (j)

(No change.)

(k)

For purposes of this subchapter, the following shall apply:

(1)

(No change.)

(2)

For any unit placed into service after June 9, 1993 and prior to the final compliance date as specified in §117.510 of this title (relating to Compliance Schedule for Utility Electric Generation in Ozone Nonattainment Areas ) or approved under the provisions of §117.540 of this title (relating to Phased Reasonably Available Control Technology (RACT)), as functionally identical replacement for an existing unit or group of units subject to the provisions of this chapter, the higher of any permit NO x emission limit under a permit issued after June 9, 1993 pursuant to Chapter 116 of this title and the emission limits of subsections (a) - (g) of this section shall apply. Any emission credits resulting from the operation of such replacement units shall be limited to the cumulative maximum rated capacity of the units replaced. The inclusion of such new units is an optional method for complying with the emission limitations of §117.107 of this title. Compliance with this paragraph does not eliminate the requirement for new units to comply with Chapter 116 of this title.

(l)

This section shall no longer apply:

(1)

to any utility boiler in the Beaumont/Port Arthur ozone nonattainment area after the appropriate compliance date(s) for emission specifications for attainment demonstrations given in §117.510(a)(2) of this title;

(2)

to any utility boiler in the Dallas/Fort Worth ozone nonattainment area after the appropriate compliance date(s) for emission specifications for attainment demonstrations given in §117.510(b)(2) of this title; and

(3)

in the Houston/Galveston ozone nonattainment area after the appropriate compliance date(s) for emission specifications for attainment demonstrations given in §117.510(c)(2) of this title.

§117.106.Emission Specifications for Attainment Demonstrations.

(a)

Beaumont/Port Arthur [ Beaumont Port/Arthur ]. The owner or operator of each [ No person shall allow the discharge into the atmosphere from any ] utility boiler located in the Beaumont/Port Arthur ozone nonattainment area [ , ] shall ensure that emissions of nitrogen oxides (NO x ) do not exceed [ in excess of ] 0.10 pound per million Btu (lb/MMBtu) heat input, on a daily average, except as provided in §117.108 of this title (relating to System Cap), or §117.570 of this title (relating to Trading).

(b)

Dallas/Fort Worth. The owner or operator of each [ No person shall allow the discharge into the atmosphere from any ] utility boiler located in the Dallas/Fort Worth (DFW) ozone nonattainment area [ , ] shall ensure that emissions of NO x do not exceed [ in excess of ]: 0.033 lb/MMBtu [ pound per million Btu ] heat input from boilers which are part of a large DFW system, and [ emissions of NO x in excess of ] 0.06 lb/MMBtu [ pound per million Btu ] heat input from boilers which are part of a small DFW system, on a daily average, except as provided in §117.108 of this title or §117.570 of this title. The annual heat input exemption of §117.103(2) of this title (relating to Exemptions) is not applicable to a small DFW system.

(c)

Houston/Galveston. The owner or operator of each utility boiler, auxiliary steam boiler, or stationary gas turbine located in the Houston/Galveston ozone nonattainment area shall ensure that emissions of NO x do not exceed the lower of any applicable permit limit or the following rates, in lb/MMBtu heat input, on the basis of daily and 30-day averaging periods as specified in §117.108 of this title, and as specified in the emissions banking and trading program of Chapter 101, Subchapter H, Division 3 of this title (relating to Mass Emissions Cap and Trade Program):

(1)

utility boilers:

(A)

gas-fired, 0.010; and

(B)

coal-fired or oil-fired:

(i)

wall-fired, 0.030; and

(ii)

tangential-fired, 0.030;

(2)

auxiliary steam boilers:

(A)

with a maximum rated capacity equal to or greater than 100 MMBtu/hr, 0.010;

(B)

with a maximum rated capacity equal to or greater than 40 MMBtu/hr, but less than 100 MMBtu/hr, 0.015; and

(C)

with a maximum rated capacity less 40 MMBtu/hr, 0.036 (or alternatively, 30 parts per million by volume (ppmv) NO x , at 3.0% oxygen (O 2 ), dry basis); and

(3)

stationary gas turbines, 0.015.

(d)

[ (c) ] Related emissions. No person shall allow the discharge into the atmosphere from any utility boiler subject to the NO x emission limits specified in subsections (a) , (b), and (c) [ (b) ] of this section:

(1)

carbon monoxide (CO) emissions in excess of 400 ppmv [ parts per million by volume (ppmv) ] at 3.0% O2 [ oxygen ], dry (or alternatively, 0.30 lb/MMBtu [ pound per MMBtu ] heat input), based on:

(A)

a one-hour average for units not equipped with continuous emissions monitoring systems (CEMS) or predictive emissions monitoring systems (PEMS) for CO; or

(B)

a rolling 24-hour averaging period for units equipped with CEMS or PEMS for CO; and

(2)

ammonia emissions in excess of 10 ppmv, based on a block one-hour averaging period.

(e)

[ (d) ] Compliance flexibility.

(1)

In the Beaumont/Port Arthur and Dallas/Fort Worth ozone nonattainment areas, an [ An ] owner or operator may use either of the following alternative methods of compliance with the NOx emission specifications of this section:

(A)

§117.108 of this title [ (relating to System Cap) ]; or

(B)

§117.570 of this title (relating to Trading).

(2)

An owner or operator may petition the executive director for an alternative to the CO or ammonia limits of this section in accordance with §117.121 of this title (relating to Alternative Case Specific Specifications).

(3)

Section 117.107 of this title (relating to Alternative System-wide Emission Specifications) and §117.121 of this title are not alternative methods of compliance with the NO x emission specifications of this section.

(4)

In the Houston/Galveston ozone nonattainment area, an owner or operator may not use the alternative methods specified in §117.570 of this title to comply with the NO x emission specifications of this section. In addition, the following requirements apply.

(A)

For units which meet the definition of electric generating facility (EGF), the owner or operator must use both the alternative methods specified in §117.108 of this title and the mass emissions cap and trade program in Chapter 101, Subchapter H, Division 3 of this title (relating to Mass Emissions Cap and Trade Program) to comply with the NO x emission specifications of this section.

(B)

For units which do not meet the definition of EGF, the owner or operator must use the mass emissions cap and trade program in Chapter 101, Subchapter H, Division 3 of this title to comply with the NO x emission specifications of this section.

§117.108.System Cap.

(a)

An owner or operator of an electric generating facility (EGF) in the Beaumont/Port Arthur or Dallas/Fort Worth ozone nonattainment areas may achieve compliance with the nitrogen oxides (NO x ) emission limits of §117.106 of this title (relating to Emission Specifications for Attainment Demonstrations) by achieving equivalent NOx emission reductions obtained by compliance with a daily and 30-day system cap emission limitation in accordance with the requirements of this section. An owner or operator of an electric generating facility in the Houston/Galveston ozone nonattainment area must comply with a daily and 30-day system cap emission limitation in accordance with the requirements of this section.

(b)

Each EGF [ utility boiler ] within an electric power generating system, as defined in §117.10 (12)(A) [ §117.10 (11)(A) ] of this title (relating to Definitions), that would otherwise be subject to the NO x emission rates of §117.106 of this title must be included in the system cap.

(c)

The system cap shall be calculated as follows.

(1)

A rolling 30-day average emission cap shall be calculated using the following equation . [ : ]

Figure: 30 TAC §117.108(c)(1)

(2)

A maximum daily cap shall be calculated using the following equation . [ : ]

Figure: 30 TAC §117.108(c)(2) (No change.)

(3)

Each EGF [ utility boiler ] in the system cap shall be subject to the emission limits of both paragraphs (1) and (2) of this subsection at all times.

(d)

The NO x emissions monitoring required by §117.113 of this title (relating to Continuous Demonstration of Compliance) for each EGF [ utility boiler ] in the system cap shall be used to demonstrate continuous compliance with the system cap.

(e)

For each operating EGF [ utility boiler ], the owner or operator shall use one of the following methods to provide substitute emissions compliance data during periods when the NO x monitor is off-line:

(1)

if the NO x monitor is a continuous emissions monitoring system (CEMS):

(A)

subject to 40 Code of Federal Regulations (CFR) 75, use the missing data procedures specified in 40 CFR 75, Subpart D (Missing Data Substitution Procedures); or

(B)

(No change.)

(2)

(No change.)

(3)

if the NO x monitor is a predictive emissions monitoring system (PEMS):

(A)

use the methods specified in 40 CFR 75, Subpart D; or

(B)

(No change.)

(4)

if the methods specified in paragraphs (1) - (3) of this subsection are not used, the owner or operator must use the maximum block one-hour emission rate as measured by the 30-day testing [ conducted in accordance with §117.111(e) of this title (relating to Initial Demonstration of Compliance) ].

(f)

The owner or operator of any EGF [ utility boiler ] subject to a system cap shall maintain daily records indicating the NO x emissions and fuel usage from each EGF [ utility boiler ] and summations of total NO x emissions and fuel usage for all EGFs [ utility boilers ] under the system cap on a daily basis. Records shall also be retained in accordance with §117.119 of this title (relating to Notification, Recordkeeping [ Record keeping ], and Reporting Requirements).

(g)

The owner or operator of any EGF [ utility boiler ] subject to a system cap shall report any exceedance of the system cap emission limit within 48 hours to the appropriate regional office. The owner or operator shall then follow up within 21 days of the exceedance with a written report to the regional office which includes an analysis of the cause for the exceedance with appropriate data to demonstrate the amount of emissions in excess of the applicable limit and the necessary corrective actions taken by the company to assure future compliance. Additionally, the owner or operator shall submit semiannual reports for the monitoring systems in accordance with §117.119 of this title.

(h)

The owner or operator of any EGF [ utility boiler ] subject to a system cap shall demonstrate initial compliance with the system cap in accordance with the schedule specified in §117.510 of this title (relating to Compliance Schedule for Utility Electric Generation in Ozone Nonattainment Areas).

(i)

For the Beaumont/Port Arthur and Dallas/Fort Worth ozone nonattainment areas, an EGF [ A utility boiler ] which is permanently retired or decommissioned and rendered inoperable may be included in the source cap emission limit, provided that the permanent shutdown occurred after January 1, 1999. For the Houston/Galveston ozone nonattainment area, an EGF which is permanently retired or decommissioned and rendered inoperable may be included in the source cap emission limit, provided that the permanent shutdown occurred after January 1, 2000. The source cap emission limit is calculated in accordance with subsection (b) of this section.

(j)

(No change.)

(k)

For the purposes of determining compliance with the source cap emission limit, the contribution of each affected EGF [ utility boiler ] that is operating during a startup, shutdown, or upset period shall be calculated from the NO x emission rate measured by the NO x monitor, if operating properly. If the NO x monitor is not operating properly, the substitute data procedures identified in subsection (e) of this section must be used. If neither the NO x monitor nor the substitute data procedure are operating properly, the owner or operator must use the maximum daily rate measured during the initial demonstration of compliance, unless the owner or operator provides data demonstrating to the satisfaction of the executive director and the EPA that actual emissions were less than maximum emissions during such periods.

§117.111.Initial Demonstration of Compliance.

(a)

The owner or operator of all units which are subject to the emission limitations of this division (relating to Utility Electric Generation in Ozone Nonattainment Areas) must test the units [ be tested ] as follows.

(1) - (2)

(No change.)

(3)

Testing shall be performed in accordance with the schedules specified in §117.510 of this title (relating to Compliance Schedule for [ For ] Utility Electric Generation in Ozone Nonattainment Areas).

(b) - (c)

(No change.)

(d)

Initial compliance with the emission specifications of this division for units operating with CEMS or PEMS in accordance with §117.113 of this title shall be demonstrated after monitor certification testing using the NO x CEMS or PEMS as follows:

(1) - (2)

(No change.)

(3)

For EGFs [ utility boilers ] complying with §117.108 of this title (relating to System Cap), a rolling 30-day average of total daily pounds of NO x emissions from the EGFs [ utility boilers ] are monitored (or calculated in accordance with §117.108(e) of this title) for 30 successive system operating days and the 30-day average emission rate is used to determine compliance with the NO x emission limit. The 30-day average emission rate is calculated as the average of all daily emissions data recorded by the monitoring and recording system during the 30-day test period. There must be no exceedances of the maximum daily cap during the 30-day test period.

(4) - (5)

(No change.)

§117.113.Continuous Demonstration of Compliance.

(a) - (e)

(No change.)

(f)

PEMS requirements. The owner or operator of any PEMS used to meet a pollutant monitoring requirement of this section must comply with the following. The required PEMS and fuel flow meters shall be used to demonstrate continuous compliance with the emission limitations of this division.

(1)

(No change.)

(2)

Monitor diluent, either oxygen or carbon dioxide:

(A)

using a CEMS

(i)

(No change.)

(ii)

with a similar alternative method approved by the executive director and EPA [ the United States Environmental Protection Agency ]; or

(B)

(No change.)

(3) - (4)

(No change.)

(g)

Stationary gas [ Gas ] turbine monitoring for NO x RACT. The owner or operator of each stationary gas turbine subject to the emission specifications of §117.105 of this title (relating to Emission Specifications for Reasonably Available Control Technology (RACT)), instead of monitoring emissions in accordance with the monitoring requirements of 40 CFR 75, may comply with the following monitoring requirements:

(1)

for stationary gas turbines rated less than 30 megawatt (MW) or peaking gas turbines (as defined in §117.10 of this title) which use steam or water injection to comply with the emission specifications of §117.105(g) of this title:

(A) - (B)

(No change.)

(2)

for stationary gas turbines subject to the emission specifications of §117.105(f) of this title, install, calibrate, maintain and operate a CEMS or PEMS in compliance with this section.

(h)

Totalizing fuel flow meters. The owner or operator of units listed in this subsection shall install, calibrate, maintain, and operate totalizing fuel flow meters to individually and continuously measure the gas and liquid fuel usage. A computer which collects, sums, and stores electronic data from continuous fuel flow meters is an acceptable totalizer. The units are:

(1)

for units which are subject to §117.105 of this title (relating to Emission Specifications for Reasonably Available Control Technology (RACT)), and for units in the Beaumont/Port Arthur (BPA) and Dallas/Fort Worth (DFW) ozone nonattainment areas which are subject to §117.106 of this title (relating to Emission Specifications for Attainment Demonstrations):

(A)

[ (1) ] any unit subject to the emission specifications of this division;

(B)

[ (2) ] any stationary gas turbine with an MW rating greater than or equal to 1.0 MW operated more than 850 hours per year (hr/yr); and

(C)

[ (3) ] any unit claimed exempt from the emission specifications of this division using the low annual capacity factor exemption of §117.103(a)(2) of this title (relating to Exemptions) ; and [ . ]

(2)

for units in the Houston/Galveston ozone nonattainment area ozone nonattainment area which are subject to §117.106 of this title:

(A)

utility boilers;

(B)

auxiliary steam boilers; and

(C)

stationary gas turbines.

(i)

Run time meters. The owner or operator of any stationary gas turbine using the exemption of §117.103(a)(3) or (b) of this title shall record the operating time with an elapsed run time meter approved by the executive director.

(j)

(No change.)

(k)

Data used for compliance.

(1)

After the initial demonstration of compliance required by §117.111 of this title (relating to Initial Demonstration of Compliance) the methods required in this section shall be used to determine compliance with the emission specifications of §117.105 or §117.106(a) or (b) of this title [ this division ]. Compliance with the emission limitations may also be determined at the discretion of the executive director using any commission compliance method.

(2)

For units subject to the emission specifications of §117.106(c) of this title, the methods required in this section and §117.114 of this title (relating to Emission Testing and Monitoring for the Houston/Galveston Attainment Demonstration) shall be used in conjunction with the requirements of Chapter 101, Subchapter H, Division 3 of this title (relating to Mass Emissions Cap and Trade Program) to determine compliance. For enforcement purposes, the executive director may also use other commission compliance methods to determine whether the source is in compliance with applicable emission limitations.

(l)

Enforcement of NO x RACT limits. If compliance with §117.105 of this title is selected, no unit subject to §117.105 of this title shall be operated at an emission rate higher than that allowed by the emission specifications of §117.105 of this title. If compliance with §117.107 of this title is selected, no unit subject to §117.107 of this title shall be operated at an emission rate higher than that approved by the executive director pursuant to §117.115(b) of this title (relating to Final Control Plan Procedures).

§117.114.Emission Testing and Monitoring for the Houston/Galveston Attainment Demonstration.

(a)

Monitoring requirements. The owner or operator of units which are subject to the emission limits of §117.106(c) of this title (relating to Emission Specifications for Attainment Demonstrations) must comply with the following monitoring requirements.

(1)

The nitrogen oxides (NO x ) monitoring requirements of §117.113(a), (c), and (d)- (f) of this title (relating to Continuous Demonstration of Compliance) apply.

(2)

The carbon monoxide (CO) monitoring requirements of §117.113(b) of this title apply.

(3)

The totalizing fuel flow meter requirements of §117.113(h) of this title apply.

(4)

Installation of monitors shall be performed in accordance with the schedule specified in §117.510(c)(2) of this title (relating to Compliance Schedule for Utility Electric Generation in Ozone Nonattainment Areas).

(b)

Testing requirements. The owner or operator of units which are subject to the emission limits of §117.106(c) of this title must test the units as specified in §117.111 of this title (relating to Initial Demonstration of Compliance).

(c)

Emission allowances.

(1)

The NO x testing and monitoring data of subsections (a) and (b) of this section, together with the level of activity, as defined in §101.350 of this title (relating to Definitions), shall be used to establish the emission factor for calculating actual emissions for compliance with Chapter 101, Subchapter H, Division 3 of this title (relating to Mass Emissions Cap and Trade Program).

(2)

For units not operating with continuous emissions monitoring system (CEMS) or predictive emissions monitoring system (PEMS), the following apply.

(A)

Retesting as specified in subsection (b) of this section is required within 60 days after any modification which could reasonably be expected to increase the NO x emission rate.

(B)

Retesting as specified in subsection (b) of this section may be conducted at the discretion of the owner or operator after any modification which could reasonably be expected to decrease the NO x emission rate, including, but not limited to, installation of post-combustion controls, low-NO x burners, low excess air operation, staged combustion (for example, overfire air), flue gas recirculation (FGR), and fuel-lean and conventional (fuel-rich) reburn.

(C)

The NO x emission rate determined by the retesting shall establish a new emission factor to be used to calculate actual emissions instead of the previously determined emission factor used to calculate actual emissions for compliance with Chapter 101, Subchapter H, Division 3 of this title.

(3)

The emission factor in paragraph (1) or (2) of this subsection is multiplied by the unit's level of activity to determine the unit's actual emissions for compliance with Chapter 101, Subchapter H, Division 3 of this title.

§117.116.Final Control Plan Procedures for Attainment Demonstration Emission Specifications.

(a)

The owner or operator of units [ utility boilers ] listed in §117.101 of this title (relating to Applicability) at a major source of nitrogen oxides (NO x ) shall submit to the executive director a final control report to show compliance with the requirements of §117.106 of this title (relating to Emission Specifications for Attainment Demonstrations). The report must include:

(1)

the section under which NO x compliance is being established for the utility boilers (and, in the Houston/Galveston ozone nonattainment area, auxiliary boilers and stationary gas turbines) within the electric generating system, either:

(A) - (B)

(No change.)

(C)

§117.570 of this title (relating to Trading); or

(D)

Chapter 101, Subchapter H, Division 3 of this title (relating to Mass Emissions Cap and Trade Program);

(2)

the methods of control of NO x emissions for each utility boiler (and, in the Houston/Galveston ozone nonattainment area, auxiliary boilers and stationary gas turbines) [ unit ];

(3)

the emissions measured by testing required in §117.111 or §117.114 of this title (relating to Initial Demonstration of Compliance ; and Emission Testing and Monitoring for the Houston/Galveston Attainment Demonstration) ;

(4)

the submittal date, and whether sent to the Austin or the regional office (or both), of any compliance stack test report or relative accuracy test audit report required by §117.111 or §117.114 of this title which is not being submitted concurrently with the final compliance report; and

(5)

the specific rule citation for any utility boiler (and, in the Houston/Galveston ozone nonattainment area, auxiliary boilers and stationary gas turbines) with a claimed exemption from the emission specification of §117.106 of this title.

(b)

(No change.)

(c)

The report must be submitted by the applicable date specified for final control plans in §117.510 of this title (relating to Compliance Schedule for [ For ] Utility Electric Generation in Ozone Nonattainment Areas). The plan must be updated with any emission compliance measurements submitted for units using continuous emissions monitoring system or predictive emissions monitoring system and complying with the system cap rolling 30-day average emission limit, according to the applicable schedule given in §117.510 of this title.

§117.119.Notification, Recordkeeping, and Reporting Requirements.

(a)

Start-up and shutdown records. For units subject to the start-up and/or shutdown exemptions allowed under §101.11 of this title (relating to Demonstrations [ Exemptions from Rules and Regulations ]), hourly records shall be made of start-up and/or shutdown events and maintained for a period of at least two years. Records shall be available for inspection by the executive director, EPA [ the Unites States Environmental Protection Agency (EPA) ], and any local air pollution control agency having jurisdiction upon request. These records shall include, but are not limited to: type of fuel burned; quantity of each type fuel burned; gross and net energy production in megawatt-hours (MW-hr); and the date, time, and duration of the event.

(b) - (c)

(No change.)

(d)

Semiannual reports. The owner or operator of a unit required to install a CEMS, PEMS, or steam- to-fuel or water-to-fuel ratio monitoring system under §117.113 of this title shall report in writing to the executive director on a semiannual basis any exceedance of the applicable emission limitations in this division and the monitoring system performance. All reports shall be postmarked or received by the 30th day following the end of each calendar semiannual period. Written reports shall include the following information:

(1)

the magnitude of excess emissions computed in accordance with 40 Code of Federal Regulations (CFR), Part 60, §60.13(h), any conversion factors used, the date and time of commencement and completion of each time period of excess emissions, and the unit operating time during the reporting period.

(A)

For stationary gas turbines using steam-to-fuel or water-to-fuel ratio monitoring to demonstrate compliance in accordance with §117.113 of this title, excess emissions are computed as each one-hour period during which the hourly steam-to-fuel or water-to-fuel ratio is less than the ratio determined to result in compliance during the initial demonstration of compliance test required by §117.111 of this title.

(B)

(No change.)

(2) - (5)

(No change.)

(e)

(No change.)

§117.121.Alternative Case Specific Specifications.

(a)

Where a person can demonstrate that an affected unit cannot attain the applicable requirements of §117.105 of this title (relating to Emission Specifications for Reasonably Available Control Technology (RACT)), or the carbon monoxide or ammonia limits of §117.106(d) [ §117.106(c) ] of this title (relating to Emission Specifications for Attainment Demonstrations), the executive director may approve emission specifications different from §117.105 of this title for that unit. The executive director:

(1) - (3)

(No change.)

(b)

Any person affected by the executive director's decision to deny an alternative case specific emission specification may file a motion for reconsideration. The requirements of §50.39 of this title (relating to Motion for Reconsideration) or §50.139 of this title (relating to Overturn Executive Director's Decision) apply. However, only a person affected may file a motion for reconsideration. Executive director approval does not necessarily constitute satisfaction of all federal requirements nor eliminate the need for approval by the EPA [ United States Environmental Protection Agency ] in cases where specified criteria for determining equivalency have not been clearly identified in applicable sections of this division (relating to Utility Electric Generation in Ozone Nonattainment Areas).

This agency hereby certifies that the proposal has been reviewed by legal counsel and found to be within the agency's legal authority to adopt.

Filed with the Office of the Secretary of State, on August 11, 2000.

TRD-200005643

Margaret Hoffman

Director, Environmental Law Division

Texas Natural Resource Conservation Commission

Earliest possible date of adoption: September 24, 2000

For further information, please call: (512) 239-0348


2. UTILITY ELECTRIC GENERATION IN EAST AND CENTRAL TEXAS

30 TAC §117.138

STATUTORY AUTHORITY

The amendment is proposed under the Texas Health and Safety Code, TCAA, §382.011, concerning General Powers and Duties, which provides the commission with the authority to establish the level of quality to be maintained in the state's air and the authority to control the quality of the state's air; §382.012, concerning State Air Control Plan, which requires the commission to develop plans for protection of the state's air, such as the SIP; §382.016, concerning Monitoring Requirements; Examination of Records, which authorizes the commission to prescribe requirements for owners or operators of sources to make and maintain records of emissions measurements; §382.017, concerning Rules, which provides the commission with the authority to adopt rules consistent with the policy and purposes of the TCAA; and §382.051(d), concerning Permitting Authority of Board; Rules, which authorizes the commission to adopt rules as necessary to comply with changes in federal law or regulations applicable to permits under Chapter 382.

The proposed amendment implements the Texas Health and Safety Code, TCAA, §§382.011, 382.012, 382.016, 382.017, and 382.051(d).

§117.138.System Cap.

(a)

(No change.)

(b)

Each unit within an electric power generating system, as defined in §117.10(12)(B) [ §117.10(11)(B) ] of this title (relating to Definitions), that would otherwise be subject to the NO x emission limits of §117.135 of this title must be included in the system cap.

(c) - (k)

(No change.)

This agency hereby certifies that the proposal has been reviewed by legal counsel and found to be within the agency's legal authority to adopt.

Filed with the Office of the Secretary of State, on August 11, 2000.

TRD-200005642

Margaret Hoffman

Director, Environmental Law Division

Texas Natural Resource Conservation Commission

Earliest possible date of adoption: September 24, 2000

For further information, please call: (512) 239-0348


3. INDUSTRIAL, COMMERCIAL, AND INSTITUTIONAL COMBUSTION SOURCES IN OZONE NONATTAINMENT AREAS

30 TAC §§117.201, 117.203, 117.205 - 117.208, 117.210, 117.211, 117.213, 117.214, 117.216, 117.219, 117.221

STATUTORY AUTHORITY

The amendments and new sections are proposed under the Texas Health and Safety Code, TCAA, §382.011, concerning General Powers and Duties, which provides the commission with the authority to establish the level of quality to be maintained in the state's air and the authority to control the quality of the state's air; §382.012, concerning State Air Control Plan, which requires the commission to develop plans for protection of the state's air, such as the SIP; §382.016, concerning Monitoring Requirements; Examination of Records, which authorizes the commission to prescribe requirements for owners or operators of sources to make and maintain records of emissions measurements; §382.017, concerning Rules, which provides the commission with the authority to adopt rules consistent with the policy and purposes of the TCAA; and §382.051(d), concerning Permitting Authority of Board; Rules, which authorizes the commission to adopt rules as necessary to comply with changes in federal law or regulations applicable to permits under Chapter 382.

The proposed amendments and new sections implement the Texas Health and Safety Code, TCAA, §§382.011, 382.012, 382.016, 382.017, and 382.051(d).

§117.201.Applicability.

The provisions of this division (relating to Industrial, Commercial, and Institutional Combustion Sources in Ozone Nonattainment Areas), shall apply to the following units located at any major stationary source of nitrogen oxides located within the Beaumont/Port Arthur, Dallas/Fort Worth, or Houston/Galveston ozone nonattainment areas:

(1)

industrial, commercial, or institutional [ , or industrial ] boilers and process heaters [ with a maximum rated capacity of 40 million Btu per hour or greater ];

(2)

stationary gas turbines ; [ with a megawatt (MW) rating of 1.0 MW or greater; and ]

(3)

stationary internal combustion engines ; [ which are: ]

[ (A)

located in the Houston/Galveston ozone nonattainment area with a horsepower (hp) rating of 150 hp or greater; or]

[ (B)

located in the Beaumont/Port Arthur or Dallas/Fort Worth ozone nonattainment area with a horsepower rating of 300 hp or greater.]

(4)

fluid catalytic cracking units (including carbon monoxide (CO) boilers, CO furnaces, and catalyst regenerator vents);

(5)

boilers and industrial furnaces which were regulated as existing facilities by the EPA at 40 Code of Federal Regulations Part 266, Subpart H (as was in effect on June 9, 1993);

(6)

duct burners used in turbine exhaust ducts;

(7)

pulping liquor recovery furnaces;

(8)

lime kilns;

(9)

lightweight aggregate kilns;

(10)

heat treating furnaces and reheat furnaces;

(11)

magnesium chloride fluidized bed dryers; and

(12)

incinerators (including fume abaters).

§117.203.Exemptions.

(a)

Units exempted from the provisions of this division (relating to Industrial, Commercial, and Institutional Combustion Sources in Ozone Nonattainment Areas), except as may be specified in §117.209(c)(1) of this title (relating to Initial Control Plan Procedures) [ and §117.213(a) and (i) of this title (relating to Continuous Demonstration of Compliance) ], include the following:

(1)

any new units placed into service after November 15, 1992, except for new units which were placed into service as functionally identical replacement for existing units subject to the provisions of this division as of June 9, 1993. Any emission credits resulting from the operation of such replacement units shall be limited to the cumulative maximum rated capacity of the units replaced;

(2)

any commercial, institutional, or industrial boiler or process heater with a maximum rated capacity of less than 40 million Btu per hour (MMBtu/hr);

(3)

heat treating furnaces and reheat furnaces. This exemption shall no longer apply to any heat treating furnace or reheat furnace with a maximum rated capacity of 20 MMBtu/hr or greater in the Houston/Galveston ozone nonattainment area after the appropriate compliance date(s) for emission specifications for attainment demonstrations specified in §117.520 of this title (relating to Compliance Schedule for Industrial, Commercial, and Institutional Combustion Sources in Ozone Nonattainment Areas);

[ (3)

any electric utility power generating boiler;]

(4)

flares, incinerators, fume abaters, pulping liquor recovery furnaces, sulfur recovery units, sulfuric acid regeneration units, and sulfur plant reaction boilers . This exemption shall no longer apply to the following units in the Houston/Galveston ozone nonattainment area after the appropriate compliance date(s) for emission specifications for attainment demonstrations specified in §117.520 of this title:

(A)

incinerators (including fume abaters) with a maximum rated capacity of 40 MMBtu/hr or greater; and

(B)

pulping liquor recovery furnaces;

(5)

dryers, kilns, or ovens used for drying, baking, cooking, calcining, and vitrifying . This exemption shall no longer apply to the following units in the Houston/Galveston ozone nonattainment area after the appropriate compliance date(s) for emission specifications for attainment demonstrations specified in §117.520 of this title:

(A)

magnesium chloride fluidized bed dryers; and

(B)

lime kilns and lightweight aggregate kilns;

(6)

stationary gas turbines and engines, which are:

(A)

used in research and testing, or used for purposes of performance verification and testing, or used solely to power other engines or gas turbines during start-ups, or operated exclusively for firefighting and/or flood control, or used in response to and during the existence of any officially declared disaster or state of emergency, or used directly and exclusively by the owner or operator for agricultural operations necessary for the growing of crops or raising of fowl or animals, or used as chemical processing gas turbines; or

(B)

demonstrated to operate less than 850 hours per year, based on a rolling 12-month average ; [ . ]

(7)

stationary gas turbines with a megawatt (MW) rating of less than 1.0 MW; [ and ]

(8)

stationary internal combustion engines which are:

(A)

located in the Houston/Galveston ozone nonattainment area with a horsepower (hp) rating of less than 150 hp; or

(B)

located in the Beaumont/Port Arthur or Dallas/Fort Worth ozone nonattainment area with a hp rating of less than 300 hp ; and [ . ]

(9)

any boiler or process heater with a maximum rated capacity of 2.0 MMBtu/hr or less.

(b)

The exemptions in paragraphs (1), (2), (6)(B), (7), and (8)(A) of subsection (a) shall no longer apply in the Houston/Galveston ozone nonattainment area after the appropriate compliance date(s) for emission specifications for attainment demonstrations specified in §117.520 of this title.

(c)

Upon issuance of a standard permit by the commission for the distributed generation of electricity, combustion sources registered under that permit are exempt from this chapter.

§117.205.Emission Specifications for Reasonably Available Control Technology (RACT).

(a)

(No change.)

(b)

For each boiler and process heater with a maximum rated capacity greater than or equal to 100.0 MMBtu/hr of heat input, the applicable emission limit is as follows:

(1) - (5)

(No change.)

(6)

for any gas-fired boiler or process heater firing gaseous fuel which contains more than 50% hydrogen by volume, over an eight-hour period, in which the fuel gas composition is sampled and analyzed every three hours, a multiplier of up to 1.25 times the appropriate emission limit in this subsection may be used for that eight-hour period. The total hydrogen volume in all gaseous fuel streams will be divided by the total gaseous fuel flow volume to determine the volume percent of hydrogen in the fuel supply. The multiplier may not be used to increase limits set by permit . [ ; ] The following equation shall be used by an owner or operator using a gas-fired boiler or process heater which is subject to this paragraph and one of the rolling 30-day averaging period emission limitations contained in paragraph (1) or (2) of this subsection to calculate an emission limitation for each rolling 30-day period:

Figure: 30 TAC §117.205(b)(6)

(7)

for units which operate with a NO x continuous emissions monitoring system [ emission monitors ] (CEMS) or predictive emissions monitoring system [ emission monitors ] (PEMS) under §117.213 of this title (relating to Continuous Demonstration of Compliance), the emission limits shall apply as:

(A) - (B)

(No change.)

(8)

(No change.)

(c)

No person shall allow the discharge into the atmosphere from any stationary gas turbine with a MW rating greater than or equal to 10.0 MW, emissions in excess of a block one-hour average concentration of 42 parts per million by volume (ppmv) NO x and 132 ppmv carbon monoxide (CO) at 15% oxygen (O 2 ), dry basis. For stationary gas turbines equipped with CEMS or PEMS for CO, the owner or operator may elect to comply with the CO limit of this subsection using a 24-hour rolling average.

(d) - (g)

(No change.)

(h)

Units exempted from the emissions specifications of this section include the following:

(1)

any industrial, commercial, or institutional [ , or industrial ] boiler or process heater with a maximum rated capacity less than 100 MMBtu/hr;

(2)

(No change.)

(3)

boilers and industrial furnaces which were regulated as existing facilities by the EPA [ United States Environmental Protection Agency ] at 40 Code of Federal Regulations Part 266, Subpart H, as was in effect on June 9, 1993;

(4)

fluid catalytic cracking units (including CO boilers , CO furnaces, and catalyst regenerator vents) ;

(5)

duct burners [ supplemental waste heat recovery units ] used in turbine exhaust ducts;

(6)

any lean-burn, stationary, reciprocating internal combustion engine located in the Houston/Galveston or Dallas/Fort Worth ozone nonattainment area; [ and ]

(7)

any stationary gas turbine with an MW rating less than 10.0 MW ; [ . ]

(8)

any new units placed into service after November 15, 1992, except for new units which were placed into service as functionally identical replacement for existing units subject to the provisions of this division as of June 9, 1993. Any emission credits resulting from the operation of such replacement units shall be limited to the cumulative maximum rated capacity of the units replaced;

(9)

any industrial, commercial, or institutional, boiler or process heater with a maximum rated capacity of less than 40 MMBtu/hr;

(10)

stationary gas turbines and engines, which are demonstrated to operate less than 850 hours per year, based on a rolling 12-month average; and

(11)

stationary internal combustion engines which are:

(A)

located in the Houston/Galveston ozone nonattainment area with a horsepower (hp) rating of less than 150 hp; or

(B)

located in the Beaumont/Port Arthur or Dallas/Fort Worth ozone nonattainment area with a hp rating of less than 300 hp.

(i)

This section shall no longer apply:

(1)

to any gas-fired boiler or process heater in the Beaumont/Port Arthur ozone nonattainment area after the appropriate compliance date(s) for emission specifications for attainment demonstrations given in §117.520(a)(3) of this title; and

(2)

in the Houston/Galveston ozone nonattainment area after the appropriate compliance date(s) for emission specifications for attainment demonstrations given in §117.520(c)(2) of this title.

§117.206.Emission Specifications for Attainment Demonstrations.

(a)

Beaumont/Port Arthur. No person shall allow the discharge into the atmosphere from any gas-fired boiler or process heater with a maximum rated capacity equal to or greater than 40 million (MM) Btu/hr in the Beaumont/Port Arthur ozone nonattainment area, emissions of nitrogen oxides (NO x ) in excess of the following, except as provided in subsections (f) [ (d) ] and (g) [ (e) ] of this section:

(1) - (2)

(No change.)

(b)

Dallas/Fort Worth. No person shall allow the discharge into the atmosphere in the Dallas/Fort Worth ozone nonattainment area, emissions in excess of the following, except as provided in subsections (f) [ (d) ] and (g) [ (e) ] of this section:

(1)

(No change.)

(2)

gas-fired and gas/liquid-fired, lean-burn, stationary reciprocating internal combustion engines rated 300 horsepower (hp) or greater, 2.0 grams NO x per horsepower hour (g NOx /hp-hr) and 3.0 g carbon monoxide (CO)/hp-hr [ g CO/hp-hr ].

(c)

Houston/Galveston. In the Houston/Galveston ozone nonattainment area, the emission rate values used to determine allocations for Chapter 101, Subchapter H, Division 3 of this title (relating to Mass Emissions Cap and Trade Program) shall be the lower of any applicable permit limit or the following:

(1)

gas-fired boilers:

(A)

with a maximum rated capacity equal to or greater than 100 MMBtu/hr, 0.010 lb NO x per MMBtu;

(B)

with a maximum rated capacity equal to or greater than 40 MMBtu/hr, but less than 100 MMBtu/hr, 0.015 lb NO x per MMBtu; and

(C)

with a maximum rated capacity less 40 MMBtu/hr, 0.036 lb NO x per MMBtu (or alternatively, 30 ppmv NO x , at 3.0% O 2 , dry basis);

(2)

fluid catalytic cracking units (including CO boilers, CO furnaces, and catalyst regenerator vents), 10 ppmv NO x at 0.0% O 2 , dry basis;

(3)

boilers and industrial furnaces which were regulated as existing facilities by the EPA at 40 Code of Federal Regulations Part 266, Subpart H (as was in effect on June 9, 1993), 0.015 lb NO x per MMBtu;

(4)

coke-fired boilers, 0.057 lb NO x per MMBtu;

(5)

wood fuel-fired boilers, 0.020 lb NO x per MMBtu;

(6)

rice hull-fired boilers, 0.089 lb NO x per MMBtu;

(7)

oil-fired boilers, 2.0 lb NO x per 1,000 gallons of oil burned;

(8)

process heaters:

(A)

with a maximum rated capacity equal to or greater than 100 MMBtu/hr, 0.010 lb NO x per MMBtu;

(B)

with a maximum rated capacity equal to or greater than 40 MMBtu/hr, but less than 100 MMBtu/hr, 0.015 lb NO x per MMBtu; and

(C)

with a maximum rated capacity less 40 MMBtu/hr, 0.036 lb NO x per MMBtu (or alternatively, 30 ppmv NO x , at 3.0% O 2 , dry basis);

(9)

stationary, reciprocating internal combustion engines:

(A)

gas-fired engines at sites with a total hp rating of 3,000 hp or more in 1997 or later, 0.17 g NO x /hp-hr, except as specified in subparagraph (C) of this paragraph;

(B)

gas-fired engines at sites with a total hp rating of less than 3,000 hp in 1997 or later, 0.50 g NO x /hp-hr; and

(C)

dual-fuel engines:

(i)

with initial start of operation on or before December 31, 2000, 0.50 g NO x /hp-hr; and;

(ii)

with initial start of operation after December 31, 2000, 0.17 g NO x /hp- hr;

(10)

stationary gas turbines, 0.015 lb NO x per MMBtu;

(11)

duct burners used in turbine exhaust ducts, 0.015 lb NO x per MMBtu;

(12)

pulping liquor recovery furnaces, 0.050 lb NO x per MMBtu;

(13)

kilns:

(A)

lime kilns, 0.66 lb NO x per ton of calcium oxide (CaO); and

(B)

lightweight aggregate kilns, 0.76 lb NOx per ton of product;

(14)

furnaces:

(A)

heat treating furnaces, 0.087 lb NO x per MMBtu; and

(B)

reheat furnaces, 0.062 lb NO x per MMBtu;

(15)

magnesium chloride fluidized bed dryers, a 90% reduction from the emission factor used to calculate the 1997 ozone season daily NO x emissions; and

(16)

incinerators (including fume abaters), a 90% reduction from the emission factor used to calculate the 1997 ozone season daily NO x emissions.

(d)

[ (c) ] NO x averaging time.

(1)

In the Beaumont/Port Arthur and Dallas/Fort Worth ozone nonattainment areas, the [ The ] emission limits of subsections (a) and (b) of this section shall apply:

(A)

[ (1) ] if the unit is operated with a NO x continuous emissions monitoring system [ emission monitors ] (CEMS) or predictive emissions monitoring system [ emission monitors ] (PEMS) under §117.213 of this title (relating to Continuous Demonstration of Compliance), either as:

(i)

[ (A) ] a rolling 30-day average period, in the units of the applicable standard;

(ii)

[ (B) ] a block one-hour average, in the units of the applicable standard, or alternatively;

(iii)

[ (C) ] a block one-hour average, in pounds per hour, for boilers and process heaters, calculated as the product of the boiler's or process heater's maximum rated capacity and its applicable limit in lb NO x per MMBtu; and

(B)

[ (2) ] if the unit is not operated with a NO x CEMS or PEMS under §117.213 of this title, a block one-hour average, in the units of the applicable standard. Alternatively for boilers and process heaters, the emission limits may be applied in lbs per hour, as specified in subparagraph (A)(iii) of this paragraph [ paragraph (1)(C) of this subsection ].

(2)

In the Houston/Galveston ozone nonattainment area, the averaging time for the emission limits of subsection (c) of this section shall be as specified in Chapter 101, Subchapter H, Division 3 of this title, except that electric generating facilities (EGFs) shall also comply with the daily and 30-day system cap emission limitations of §117.210 of this title (relating to System Cap).

(e)

[ (d) ] Related emissions. No person shall allow the discharge into the atmosphere from any boiler or process heater subject to NO x emission specifications in subsection (a) , (b), or (c) [ (b) ] of this section, emissions in excess of the following, except as provided in §117.221 of this title (relating to Alternative Case Specific Specifications):

(1)

carbon monoxide (CO), 400 ppmv at 3.0% O 2 , dry basis;

(A)

on a rolling 24-hour averaging period, for units equipped with CEMS or PEMS for CO; and

(B)

on a one-hour average, for units not equipped with CEMS or PEMS for CO; and

(2)

ammonia emissions, 10 [ 5 ] ppmv on a block one-hour averaging period.

(f)

[ (e) ] Compliance flexibility.

(1)

In the Beaumont/Port Arthur and Dallas/Fort Worth ozone nonattainment areas, an [ An ] owner or operator may use any of the following alternative methods to comply with the NO x emission specifications of this section:

(A)

§117.207 of this title (relating to Alternative Plant-Wide Emission Specifications);

(B)

§117.223 of this title (relating to Source Cap); or

(C)

§117.570 (relating to Trading).

(2)

Section 117.221 of this title (relating to Alternative Case Specific Specifications) is not an applicable method of compliance with the NO x emission specifications of this section.

(3)

An owner or operator may petition the executive director for an alternative to the CO or ammonia limits of this section in accordance with §117.221 of this title.

(4)

In the Houston/Galveston ozone nonattainment area, an owner or operator may not use the alternative methods specified in §§117.207, 117.223, and 117.570 of this title to comply with the NO x emission specifications of this section. The owner or operator shall use the mass emissions cap and trade program in Chapter 101, Subchapter H, Division 3 of this title to comply with the NO x emission specifications of this section, except that EGFs shall also comply with the daily and 30-day system cap emission limitations of §117.210 of this title.

(g)

[ (f) ] Exemptions. Units exempted from the emissions specifications of this section include the following in the Beaumont/Port Arthur and Dallas/Fort Worth ozone nonattainment areas:

(1)

any industrial, commercial, or institutional [ , or industrial ] boiler or process heater with a maximum rated capacity less than 40 MMBtu/hr; and

(2)

units exempted from emission specifications in §117.205(h)(2) - (5) of this title.

§117.207.Alternative Plant-wide Emission Specifications.

(a)

(No change.)

(b)

The owner or operator shall establish an enforceable (NOx ) emission limit for each affected unit at the source as follows.

(1)

For boilers and process heaters which operate with continuous emissions monitoring system [ emission monitors ] (CEMS) or predictive emissions monitoring system [ emission monitors ] (PEMS) in accordance with §117.213 of this title (relating to Continuous Demonstration of Compliance), the emission limits shall apply in:

(A) - (B)

(No change.)

(2) - (4)

(No change.)

(c) - (e)

(No change.)

(f)

Units exempted from emission specifications in accordance with §117.205(h) and §117.206(g) [ §117.206(e) ] of this title are also exempt under this section and shall not be included in the plant-wide emission limit, except as follows. The owner or operator of exempted units as defined in §117.205(h) and §117.206(g) [ §117.206(e) ] of this title may opt to include one or more of an entire equipment class of exempted units into the alternative plant-wide emission specifications.

(1)

Low annual capacity factor boilers, process heaters, stationary gas turbines, or stationary internal combustion engines as defined in §117.10 of this title are not to be considered as part of the opt-in class of equipment.

(2) - (3)

(No change.)

(4)

The equipment classes which may be included in the alternative plant-wide emission specifications and the NO x emission rates that are to be used in calculating the alternative plant-wide emission specifications are listed in the [ following ] table titled [ , ] §117.207(f) OPT- IN UNITS . [ : ]

Figure: 30 TAC §117.207(f)(4)

(g) - (i)

(No change.)

§117.208.Operating Requirements.

(a) - (c)

(No change.)

(d)

All units subject to the emission limitations of §§117.205, 117.206 [ (relating to Emission Specifications for Attainment Demonstrations ], 117.207, or 117.223 of this title (relating to Emission Specifications for Reasonably Available Control Technology (RACT); Emission Specifications for Attainment Demonstrations; Alternative Plant-wide Emission Specifications; and Source Cap) shall be operated so as to minimize NO x emissions, consistent with the emission control techniques selected, over the unit's operating or load range during normal operations. Such operational requirements include the following.

(1) - (3)

(No change.)

(4)

Each unit controlled with steam or water injection shall be operated such that injection rates are maintained to limit NO x concentrations to less than or equal to the NO x concentrations achieved at maximum rated capacity (corrected to 15% O 2 on a dry basis for stationary gas turbines).

(5) - (7)

(No change.)

§117.210.System Cap.

(a)

The owner or operator of each electric generating facility (EGF) in the Houston/Galveston ozone nonattainment area must comply with a daily and 30-day system cap emission limitation for nitrogen oxides (NOx ) in accordance with the requirements of this section.

(b)

Each EGF that would otherwise be subject to the NOx emission rates of §117.206 of this title (relating to Emission Specifications for Attainment Demonstrations) must be included in the system cap.

(c)

The system cap shall be calculated as follows.

(1)

A rolling 30-day average emission cap shall be calculated using the following equation.

Figure: 30 TAC §117.210(c)(1)

(2)

A maximum daily cap shall be calculated using the following equation.

Figure: 30 TAC §117.210(c)(2)

(3)

Each EGF in the system cap shall be subject to the emission limits of both paragraphs (1) and (2) of this subsection at all times.

(d)

The NO x emissions monitoring required by §117.213 of this title (relating to Continuous Demonstration of Compliance) for each EGF in the system cap shall be used to demonstrate continuous compliance with the system cap.

(e)

For each operating EGF, the owner or operator shall use one of the following methods to provide substitute emissions compliance data during periods when the NO x monitor is off-line:

(1)

if the NO x monitor is a continuous emissions monitoring system (CEMS):

(A)

subject to 40 CFR 75, use the missing data procedures specified in 40 CFR 75, Subpart D (Missing Data Substitution Procedures); or

(B)

subject to 40 CFR 75, Appendix E, use the missing data procedures specified in 40 CFR 75, Appendix E, §2.5 (Missing Data Procedures);

(2)

use Appendix E monitoring in accordance with §117.113(d) of this title (relating to Continuous Demonstration of Compliance);

(3)

if the NO x monitor is a predictive emissions monitoring system (PEMS):

(A)

use the methods specified in 40 CFR 75, Subpart D; or

(B)

use calculations in accordance with §117.113(f) of this title; or

(4)

if the methods specified in paragraphs (1) - (3) of this subsection are not used, the owner or operator must use the maximum block one-hour emission rate as measured by the 30-day testing.

(f)

The owner or operator of any EGF subject to a system cap shall maintain daily records indicating the NO x emissions and fuel usage from each EGF and summations of total NO x emissions and fuel usage for all EGFs under the system cap on a daily basis. Records shall also be retained in accordance with §117.219 of this title (relating to Notification, Recordkeeping, and Reporting Requirements).

(g)

The owner or operator of any EGF subject to a system cap shall report any exceedance of the system cap emission limit within 48 hours to the appropriate regional office. The owner or operator shall then follow up within 21 days of the exceedance with a written report to the regional office which includes an analysis of the cause for the exceedance with appropriate data to demonstrate the amount of emissions in excess of the applicable limit and the necessary corrective actions taken by the company to assure future compliance. Additionally, the owner or operator shall submit semiannual reports for the monitoring systems in accordance with §117.219 of this title.

(h)

The owner or operator of any EGF subject to a system cap shall demonstrate initial compliance with the system cap in accordance with the schedule specified in §117.520 of this title (relating to Compliance Schedule for Industrial, Commercial, and Institutional Combustion Sources in Ozone Nonattainment Areas).

(i)

An EGF which is permanently retired or decommissioned and rendered inoperable may be included in the source cap emission limit, provided that the permanent shutdown occurred after January 1, 2000. The source cap emission limit is calculated in accordance with subsection (b) of this section.

(j)

Emission reductions from shutdowns or curtailments which have been used for netting or offset purposes under the requirements of Chapter 116 of this title (relating to Control of Air Pollution by Permits for New Construction or Modification) may not be included in the baseline for establishing the cap.

(k)

For the purposes of determining compliance with the source cap emission limit, the contribution of each affected EGF that is operating during a startup, shutdown, or upset period shall be calculated from the NOx emission rate measured by the NO x monitor, if operating properly. If the NO x monitor is not operating properly, the substitute data procedures identified in subsection (e) of this section must be used. If neither the NO x monitor nor the substitute data procedure are operating properly, the owner or operator must use the maximum daily rate measured during the initial demonstration of compliance, unless the owner or operator provides data demonstrating to the satisfaction of the executive director and the EPA that actual emissions were less than maximum emissions during such periods.

§117.211.Initial Demonstration of Compliance.

(a)

The owner or operator of all units which are subject to the emission limitations of this division (relating to Industrial, Commercial, and Institutional Combustion Sources in Ozone Nonattainment Areas) must test the units as follows .

(1) - (4)

(No change.)

(b) - (d)

(No change.)

(e)

Compliance with the emission specifications of this division for units operating without CEMS or PEMS shall be demonstrated while operating at the maximum rated capacity, or as near thereto as practicable. Compliance shall be determined by the average of three one-hour emission test runs, using the following test methods:

(1) - (4)

(No change.)

(5)

American Society of Testing and Materials (ASTM) Method D1945-91 or ASTM Method D3588- 93 for fuel composition; ASTM Method D1826-88 or ASTM Method D3588-91 for calorific value; or alternate methods as approved by the executive director and EPA [ the United States Environmental Protection Agency (EPA) ]; or

(6)

(No change.)

(f) - (g)

(No change.)

§117.213.Continuous Demonstration of Compliance.

(a)

Totalizing fuel flow meters. The owner or operator of units listed in this subsection shall install, calibrate, maintain, and operate a totalizing fuel flow meter to individually and continuously measure the gas and liquid fuel usage. A computer which collects, sums, and stores electronic data from continuous fuel flow meters is an acceptable totalizer.

(1)

The units are the following:

(A)

for units which are subject to §117.205 of this title (relating to Emission Specifications for Reasonably Available Control Technology (RACT)), and for units in the Beaumont/Port Arthur (BPA) and Dallas/Fort Worth (DFW) ozone nonattainment areas which are subject to §117.206 of this title (relating to Emission Specifications for Attainment Demonstrations):

(i)

[ (A) ] if individually rated more than 40 million British thermal units (Btu) per hour (MMBtu/hr):

(I)

[ (i) ] boilers;

(II)

[ (ii) ] process heaters;

(III)

[ (iii) ] boilers and industrial furnaces which were regulated as existing facilities by EPA at 40 Code of Federal Regulations (CFR) Part 266, Subpart H, as was in effect on June 9, 1993; and

(IV)

[ (iv) ] gas turbine supplemental-fired waste heat recovery units;

(ii)

[ (B) ] stationary, reciprocating internal combustion engines not exempt by §117.203(a)(6) or (8) [ §117.203(6) or (8) ] of this title (relating to Exemptions) , or §117.205(h)(10) or (11) of this title;

(iii)

[ (C) ] stationary gas turbines with a megawatt (MW) rating greater than or equal to 1.0 MW operated more than 850 hours per year; and

(iv)

[ (D) ] fluid catalytic cracking unit boilers using supplemental fuel ; and [ . ]

(B)

for units in the Houston/Galveston (HGA) ozone nonattainment area which are subject to §117.206 of this title:

(i)

boilers;

(ii)

process heaters;

(iii)

boilers and industrial furnaces which were regulated as existing facilities by EPA at 40 CFR Part 266, Subpart H, as was in effect on June 9, 1993;

(iv)

duct burners used in turbine exhaust ducts;

(v)

stationary, reciprocating internal combustion engines;

(vi)

stationary gas turbines;

(vii)

fluid catalytic cracking unit boilers and furnaces using supplemental fuel;

(viii)

pulping liquor recovery furnaces;

(ix)

lime kilns;

(x)

lightweight aggregate kilns;

(xi)

heat treating furnaces;

(xii)

reheat furnaces;

(xiii)

magnesium chloride fluidized bed dryers; and

(xiv)

incinerators.

(2)

As an alternative to the fuel flow monitoring requirements of this subsection, units operating with a nitrogen oxides (NO x ) and diluent continuous emissions [ emission ] monitoring system (CEMS) under subsection (e) of this section may monitor stack exhaust flow using the flow monitoring specifications of 40 CFR 60, Appendix B, Performance Specification 6 or 40 CFR 75, Appendix A.

(b)

Oxygen (O 2 ) monitors.

(1)

(No change.)

(2)

The following are not subject to this subsection:

(A)

units listed in §117.205(h)(3) - (5) and (8) - (11) of this title [ (relating to Emission Specifications ];

(B) - (C)

(No change.)

(3)

(No change.)

(c)

NO x monitors.

(1)

The owner or operator of units listed in this paragraph shall install, calibrate, maintain, and operate a CEMS or predictive emissions monitoring system (PEMS) to monitor exhaust NO x . The units are:

(A) - (D)

(No change.)

(E)

units which use a chemical reagent for reduction of NOx ; [ and ]

(F)

units for which the owner or operator elects to comply with the NO x emission specifications of §117.205 or §117.206(a) or (b) of this title [ this division ] using a pound per MMBtu limit on a 30-day rolling average ; [ . ]

(G)

lime kilns and lightweight aggregate kilns in HGA; and

(H)

units with a rated heat input greater than or equal to 100 MMBtu/hr which are subject to §117.206(c) of this title.

(2)

The following are not required to install CEMS or PEMS under this subsection:

(A)

for purposes of §117.205 or §117.206(a) or (b) of this title, units listed in §117.205(h)(3) - (5) and (8) - (11) of this title [ (relating to Emission Specifications for Reasonably Available Control Technology) ]; and

(B)

(No change.)

(d) - (g)

(No change.)

(h)

Monitoring for stationary gas turbines less than 30 MW. The owner or operator of any stationary gas turbine rated less than 30 MW using steam or water injection to comply with the emission specifications of §117.205 or §117.207 of this title (relating to Alternative Plant- wide Emission Specifications) shall either:

(1) - (2)

(No change.)

(i)

Run time meters. The owner or operator of any stationary gas turbine or stationary internal combustion engine claimed exempt using the 850 hours per year exemption of §117.203(a)(6)(B) [ §117.203(6)(B) ] of this title shall record the operating time with an elapsed run time meter.

(j)

(No change.)

(k)

Data used for compliance.

(1)

After the initial demonstration of compliance required by §117.211 of this title, the methods required in this section shall be used to determine compliance with the emission specifications of §117.205 or §117.206(a) or (b) of this title [ this division ]. For enforcement purposes, the executive director may also use other commission compliance methods to determine whether the source is in compliance with applicable emission limitations.

(2)

For units subject to the emission specifications of §117.206(c) of this title, the methods required in this section and §117.214 of this title (relating to Emission Testing and Monitoring for the Houston/Galveston Attainment Demonstration) shall be used in conjunction with the requirements of Chapter 101, Subchapter H, Division 3 of this title (relating to Mass Emissions Cap and Trade Program) to determine compliance. For enforcement purposes, the executive director may also use other commission compliance methods to determine whether the source is in compliance with applicable emission limitations.

(l)

Enforcement of NO x RACT limits. If compliance with §117.205 of this title is selected, no unit subject to §117.205 of this title shall be operated at an emission rate higher than that allowed by the emission specifications of §117.205 of this title. If compliance with §117.207 of this title is selected, no unit subject to §117.207 of this title shall be operated at an emission rate higher than that approved by the executive director pursuant to §117.215(b) of this title (relating to Final Control Plan Procedures for Reasonably Available Control Technology).

(m)

Loss of NO x RACT exemption. The owner or operator of any unit claimed exempt from the emission specifications of this division using the low annual capacity factor exemption of §117.205(h)(2) of this title (relating to Definitions), shall notify the executive director within seven days if the Btu/yr or hour-per-year limit specified in §117.10 of this title, as appropriate, is exceeded.

(1) - (3)

(No change.)

§117.214.Emission Testing and Monitoring for the Houston/Galveston Attainment Demonstration.

(a)

Monitoring requirements. The owner or operator of units which are subject to the emission limits of §117.206(c) of this title (relating to Emission Specifications for Attainment Demonstrations) must comply with the following monitoring requirements.

(1)

The nitrogen oxides (NO x ) monitoring requirements of §117.213(c), and (e) - (f) of this title (relating to Continuous Demonstration of Compliance) apply.

(2)

The carbon monoxide (CO) monitoring requirements of §117.213(d) of this title apply.

(3)

The totalizing fuel flow meter requirements of §117.213(a) of this title apply.

(4)

Installation of monitors shall be performed in accordance with the schedule specified in §117.520(c)(2) of this title (relating to Compliance Schedule for Industrial, Commercial, and Institutional Combustion Sources in Ozone Nonattainment Areas).

(b)

Testing requirements. The owner or operator of units which are subject to the emission limits of §117.206(c) of this title must test the units as specified in §117.211 of this title (relating to Initial Demonstration of Compliance).

(c)

Emission allowances.

(1)

The NO x testing and monitoring data of subsections (a) and (b) of this section, together with the level of activity, as defined in §101.350 of this title (relating to Definitions), shall be used to establish the emission factor for calculating actual emissions for compliance with Chapter 101, Subchapter H, Division 3 of this title (relating to Mass Emissions Cap and Trade Program).

(2)

For units not operating with continuous emissions monitoring system (CEMS) or predictive emissions monitoring system (PEMS), the following apply.

(A)

Retesting as specified in subsection (b) of this section is required within 60 days after any modification which could reasonably be expected to increase the NO x emission rate.

(B)

Retesting as specified in subsection (b) of this section may be conducted at the discretion of the owner or operator after any modification which could reasonably be expected to decrease the NO x emission rate, including, but not limited to, installation of post-combustion controls, low-NO x burners, low excess air operation, staged combustion (for example, overfire air), flue gas recirculation (FGR), and fuel-lean and conventional (fuel-rich) reburn.

(C)

The NO x emission rate determined by the retesting shall establish a new emission factor to be used to calculate actual emissions instead of the previously determined emission factor used to calculate actual emissions for compliance with Chapter 101, Subchapter H, Division 3 of this title.

(3)

The emission factor in paragraph (1) or (2) of this subsection is multiplied by the unit's level of activity to determine the unit's actual emissions for compliance with Chapter 101, Subchapter H, Division 3 of this title.

§117.216.Final Control Plan Procedures for Attainment Demonstration Emission Specifications.

(a)

The owner or operator of units listed in §117.206 of this title (relating to Emission Specifications for Attainment Demonstrations) at a major source of nitrogen oxides (NO x ) shall submit a final control report to show compliance with the requirements of §117.206 of this title. The report must include:

(1)

the section under which NO x compliance is being established, either:

(A)

(No change.)

(B)

Section 117.210 of this title (relating to System Cap);

(C)

[ (B) ] Section 117.223 of this title (relating to Source Cap); and as applicable, [ or ]

(D)

[ (C) ] Section 117.570 of this title (relating to Trading); or

(E)

Chapter 101, Subchapter H, Division 3 of this title (relating to Mass Emissions Cap and Trade Program);

(2) - (5)

(No change.)

(b)

(No change.)

(c)

The report must be submitted to the executive director by the applicable date specified for final control plans in §117.520(a) or (b) of this title (relating to Compliance Schedule for [ For ] Industrial, Commercial, and Institutional Combustion Sources in Ozone Nonattainment Areas). The plan must be updated with any emission compliance measurements submitted for units using continuous emissions monitoring system or predictive emissions monitoring system and complying with the source cap rolling 30-day average emission limit, according to the applicable schedule given in §117.520 of this title.

§117.219.Notification, Recordkeeping, and Reporting Requirements.

(a)

Start-up and shutdown records. For units subject to the start-up and/or shutdown exemptions allowed under §101.11 of this title (relating to Demonstrations [ Exemptions from Rules and Regulations ]), hourly records shall be made of start-up and/or shutdown events and maintained for a period of at least two years. Records shall be available for inspection by the executive director, EPA, and any local air pollution control agency having jurisdiction upon request. These records shall include, but are not limited to: type of fuel burned; quantity of each type of fuel burned; and the date, time, and duration of the procedure.

(b)

Notification. The owner or operator of an affected source shall submit notification to the executive director, as follows:

(1)

(No change.)

(2)

verbal notification of the date of any continuous emissions monitoring system (CEMS) or predictive emissions monitoring system (PEMS) relative accuracy test audit (RATA) [ performance evaluation ] conducted under §117.213 of this title (relating to Continuous Demonstration of Compliance) at least 15 days prior to such date followed by written notification within 15 days after testing is completed.

(c)

Reporting of test results. The owner or operator of an affected unit shall furnish the appropriate regional office [ executive director ] and any local air pollution control agency having jurisdiction a copy of any initial demonstration of compliance testing conducted under §117.211 of this title and any CEMS or PEMS RATA [ relative accuracy test audit (RATA) ] conducted under §117.213 of this title:

(1)

(No change.)

(2)

not later than the compliance schedule specified in §117.520 of this title (relating to Compliance Schedule for [ For ] Industrial, Commercial, and Institutional Combustion Sources in Ozone Nonattainment Areas).

(d)

Semiannual reports. The owner or operator of a unit required to install a CEMS, PEMS, or water- to-fuel or steam-to-fuel ratio monitoring system under §117.213 of this title shall report in writing to the executive director on a semiannual basis any exceedance of the applicable emission limitations of this division (relating to Industrial, Commercial, and Institutional Combustion Sources in Ozone Nonattainment Areas) and the monitoring system performance. All reports shall be postmarked or received by the 30th day following the end of each calendar semiannual period. Written reports shall include the following information:

(1)

the magnitude of excess emissions computed in accordance with 40 Code of Federal Regulations, Part 60, §60.13(h), any conversion factors used, the date and time of commencement and completion of each time period of excess emissions, and the unit operating time during the reporting period.

(A)

For stationary gas turbines using steam-to-fuel or water-to-fuel ratio monitoring to demonstrate compliance in accordance with §117.213(h)(2) of this title, excess emissions are computed as each one-hour period during which the average steam or water injection rate is below the level defined by the control algorithm as necessary to achieve compliance with the applicable emission limitations in §117.205 of this title (relating to Emission Specifications for Reasonably Available Control Technology (RACT)).

(B)

(No change.)

(2) - (5)

(No change.)

(e)

(No change.)

(f)

Recordkeeping. The owner or operator of a unit subject to the requirements of this division shall maintain written or electronic records of the data specified in this subsection. Such records shall be kept for a period of at least five years and shall be made available upon request by authorized representatives of the executive director, EPA, or local air pollution control agencies having jurisdiction. The records shall include:

(1)

for each unit subject to §117.213(a) of this title, records of annual fuel usage;

(2)

[ (1) ] for [ For ] each unit using a CEMS or PEMS in accordance with §117.213 of this title, monitoring records of:

(A)

hourly emissions and fuel usage (or stack exhaust flow) for units complying with an emission limit enforced on a block one-hour average; and

(B)

daily emissions and fuel usage (or stack exhaust flow) for units complying with an emission limit enforced on a rolling 30-day average. Emissions must be recorded in units of:

(i)

pound per million British thermal units (Btu) heat input; and

(ii)

pounds or tons per day ; [ . ]

(3)

[ (2) ] for each stationary internal combustion engine subject to the emission specifications of this division, records of:

(A)

emissions measurements required by:

(i)

§117.208(d)(7) [ §117.208(7) ] of this title; and

(ii)

§117.213(g) of this title; and

(B)

catalytic converter, air-fuel ratio controller, or other emissions-related control system maintenance, including the date and nature of corrective actions taken ; [ . ]

(4)

[ (3) ] for each stationary gas turbine monitored by steam-to-fuel or water-to-fuel ratio in accordance with §117.213(h) of this title, records of hourly:

(A)

pounds of steam or water injected;

(B)

pounds of fuel consumed; and

(C)

the steam-to-fuel or water-to-fuel ratio ; [ . ]

(5)

[ (4) ] for hydrogen (H 2 ) fuel monitoring in accordance with §117.213(j) of this title, records of the volume percent H 2 every three hours ; [ . ]

(6)

[ (5) ] for units claimed exempt from the emission specifications of this division using the low annual capacity factor exemption of §117.205(h)(2), either records of monthly:

(A)

fuel usage, for exemptions based on heat input; or

(B)

hours of operation, for exemptions based on hours per year of operation ; [ . ]

(7)

[ (6) ] Records of carbon monoxide measurements specified in §117.213(d)(2) of this title ; [ . ]

(8)

[ (7) ] records of the results of initial certification testing, evaluations, calibrations, checks, adjustments, and maintenance of CEMS, PEMS, or steam-to-fuel or water-to-fuel ratio monitoring systems ; and [ . ]

(9)

[ (8) ] records of the results of performance testing, including initial demonstration of compliance testing conducted in accordance with §117.211 of this title.

§117.221.Alternative Case Specific Specifications.

(a)

Where a person can demonstrate that an affected unit cannot attain the applicable requirements of §117.205 of this title (relating to Emission Specifications for Reasonably Available Control Technology (RACT)) or the carbon monoxide or ammonia limits of §117.206(e) [ §117.206(d) ] of this title (relating [ Relating ] to Emission Specifications for Attainment Demonstrations), the executive director may approve emission specifications different from §117.205 of this title for that unit. The executive director:

(1) - (3)

(No change.)

(b)

Any person affected by the executive director's decision to deny an alternative case specific emission specification may file a motion for reconsideration. The requirements of §50.39 of this title (relating to Motion for Reconsideration) or §50.139 of this title (relating to Motion to Overturn Executive Director's Decision) apply. However, only a person affected may file a motion for reconsideration. Executive director approval does not necessarily constitute satisfaction of all federal requirements nor eliminate the need for approval by EPA [ the United States Environmental Protection Agency ] in cases where specified criteria for determining equivalency have not been clearly identified in applicable sections of this division (relating to Industrial, Commercial, and Institutional Combustion Sources in Ozone Nonattainment Areas).

This agency hereby certifies that the proposal has been reviewed by legal counsel and found to be within the agency's legal authority to adopt.

Filed with the Office of the Secretary of State, on August 11, 2000.

TRD-200005641

Margaret Hoffman

Director, Environmental Law Division

Texas Natural Resource Conservation Commission

Earliest possible date of adoption: September 24, 2000

For further information, please call: (512) 239-0348


Subchapter D. SMALL COMBUSTION SOURCES

2. BOILERS, PROCESS HEATERS, AND STATIONARY ENGINES AT MINOR SOURCES

30 TAC §§117.471, 117.473, 117.475, 117.478, 117.479

STATUTORY AUTHORITY

The new sections are proposed under the Texas Health and Safety Code, TCAA, §382.011, concerning General Powers and Duties, which provides the commission with the authority to establish the level of quality to be maintained in the state's air and the authority to control the quality of the state's air; §382.012, concerning State Air Control Plan, which requires the commission to develop plans for protection of the state's air, such as the SIP; §382.016, concerning Monitoring Requirements; Examination of Records, which authorizes the commission to prescribe requirements for owners or operators of sources to make and maintain records of emissions measurements; §382.017, concerning Rules, which provides the commission with the authority to adopt rules consistent with the policy and purposes of the TCAA; and §382.051(d), concerning Permitting Authority of Board; Rules, which authorizes the commission to adopt rules as necessary to comply with changes in federal law or regulations applicable to permits under Chapter 382.

The proposed new sections implement the Texas Health and Safety Code, TCAA, §§382.011, 382.012, 382.016, 382.017, and 382.051(d).

§117.471.Applicability.

This division (relating to Boilers, Process Heaters, and Stationary Engines at Minor Sources) applies in the Houston/Galveston ozone nonattainment area to the following equipment at any stationary source of nitrogen oxides (NO x ) which is not a major source of NOx :

(1)

boilers and process heaters; and

(2)

stationary, reciprocating internal combustion engines.

§117.473.Exemptions.

(a)

This division (relating to Boilers, Process Heaters, and Stationary Engines at Minor Sources) does not apply to the following:

(1)

boilers and process heaters with a maximum rated capacity of 2.0 million British thermal units per hour (MMBtu/hr) or less; and

(2)

the following engines:

(A)

engines with a horsepower (hp) rating of 50 hp or less;

(B)

engines used in research and testing;

(C)

engines used for purposes of performance verification and testing;

(D)

engines used solely to power other engines or gas turbines during start-ups;

(E)

engines operated exclusively for firefighting and/or flood control;

(F)

engines used in response to and during the existence of any officially declared disaster or state of emergency; and

(G)

engines used directly and exclusively by the owner or operator for agricultural operations necessary for the growing of crops or raising of fowl or animals.

(b)

At any stationary source of nitrogen oxides (NO x ) which is not subject to Chapter 101, Subchapter H, Division 3 of this title (relating to Mass Emissions Cap and Trade Program), the following are exempt from the requirements of this division, except for the totalizing fuel flow requirements of §117.479(a), (d), and (g)(1) of this title (relating to Monitoring, Recordkeeping, and Reporting Requirements):

(1)

any boiler or process heater with a maximum rated capacity greater than 2.0 MMBtu/hr and less than 5.0 MMBtu/hr that has an annual heat input less than or equal to 1.8 (10 9 ) Btu per calendar year; and

(2)

any boiler or process heater with a maximum rated capacity equal to or greater than 5.0 MMBtu/hr that has an annual heat input less than or equal to 9.0 (10 9 ) Btu per calendar year.

(c)

Upon issuance of a standard permit by the commission for the distributed generation of electricity, combustion sources registered under that permit are exempt from this chapter.

§117.475.Emission Specifications.

(a)

For sources which are subject to Chapter 101, Subchapter H, Division 3 of this title (relating to Mass Emissions Cap and Trade Program), the nitrogen oxides (NO x ) emission rate values used to determine allocations for Chapter 101, Subchapter H, Division 3 of this title shall be the lower of any applicable permit limit or the limits in subsection (c) of this section. The averaging time shall be as specified in Chapter 101, Subchapter H, Division 3 of this title.

(b)

For sources which are not subject to Chapter 101, Subchapter H, Division 3 of this title, NO x emissions are limited to the lower of any applicable permit limit or the limits in subsection (c) of this section. The averaging time shall be as follows:

(1)

if the boiler, process heater, or engine is operated with a NO x continuous emissions monitoring system (CEMS) or predictive emissions monitoring system (PEMS) under §117.479(c) of this title (relating to Monitoring, Recordkeeping, and Reporting Requirements), either as:

(A)

a rolling 30-day average period, in the units of the applicable standard;

(B)

a block one-hour average, in the units of the applicable standard, or alternatively;

(C)

a block one-hour average, in pounds per hour, for boilers and process heaters, calculated as the product of the boiler's or process heater's maximum rated capacity and its applicable limit in pound NOx per million British thermal units (lb/MMBtu); or

(2)

if the unit is not operated with a NO x CEMS or PEMS under §117.479(c) of this title, a block one-hour average, in the units of the applicable standard.

(c)

No person shall allow the discharge of NO x emissions into the atmosphere in excess of the following rates:

(1)

from boilers and process heaters, 0.036 lb/MMBtu heat input (or alternatively, 30 parts per million by volume (ppmv), at 3.0% oxygen (O2 ), dry basis); and

(2)

from stationary, reciprocating internal combustion engines, 0.50 gram per horsepower-hour (g/hp- hr).

§117.478.Operating Requirements.

(a)

The owner or operator shall operate any boiler, process heater, or engine subject to the emission limitations of §117.475 of this title (relating to Emission Specifications) in compliance with those limitations.

(b)

All boilers, process heaters, and engines subject to the emission limitations of §117.475 of this title shall be operated so as to minimize nitrogen oxides (NO x ) emissions, consistent with the emission control techniques selected, over the unit's operating or load range during normal operations. Such operational requirements include the following.

(1)

Each boiler, except for wood-fired boilers, shall be operated with oxygen (O 2 ), carbon monoxide (CO), or fuel trim.

(2)

Each boiler and process heater controlled with forced flue gas recirculation (FGR) to reduce NO x emissions shall be operated such that the proportional design rate of FGR is maintained, consistent with combustion stability, over the operating range.

(3)

Each boiler, process heater, or engine controlled with post combustion control techniques shall be operated such that the reducing agent injection rate is maintained to limit NO x concentrations to less than or equal to the NO x concentrations achieved at maximum rated capacity.

(4)

Each stationary internal combustion engine controlled with nonselective catalytic reduction shall be equipped with an automatic air-fuel ratio (AFR) controller which operates on exhaust O 2 or CO control and maintains AFR in the range required to meet the engine's applicable emission limits.

(5)

Each stationary internal combustion engine shall be checked for proper operation of the engine by recorded measurements of NO x and CO emissions at least quarterly and as soon as practicable after each occurrence of engine maintenance which may reasonably be expected to increase emissions, O 2 sensor replacement, catalyst cleaning, or catalyst replacement. Stain tube indicators specifically designed to measure NO x concentrations shall be acceptable for this documentation, provided a hot air probe or equivalent device is used to prevent error due to high stack temperature, and three sets of concentration measurements are made and averaged. Portable NO x analyzers shall also be acceptable for this documentation.

§117.479.Monitoring, Recordkeeping, and Reporting Requirements.

(a)

Totalizing fuel flow meters.

(1)

The owner or operator of each boiler, process heater, or engine subject to the emission limitations of §117.475 of this title (relating to Emission Specifications) shall install, calibrate, maintain, and operate totalizing fuel flow meters to individually and continuously measure the gas and liquid fuel usage. A computer which collects, sums, and stores electronic data from continuous fuel flow meters is an acceptable totalizer.

(2)

As an alternative to the fuel flow monitoring requirements of this subsection, units operating with a nitrogen oxides (NO x ) and diluent continuous emissions monitoring system (CEMS) under subsection (c) of this section may monitor stack exhaust flow using the flow monitoring specifications of 40 Code of Federal Regulations (CFR) 60, Appendix B, Performance Specification 6 or 40 CFR 75, Appendix A.

(b)

Oxygen (O 2 ) monitors. If the owner or operator installs an O 2 monitor, the criteria in §117.213(e) of this title (relating to Continuous Demonstration of Compliance) should be considered the appropriate guidance for the location and calibration of the monitor.

(c)

NO x monitors. If the owner or operator installs a CEMS or predictive emissions monitoring system (PEMS), it shall meet the requirements of §117.213(e) or (f) of this title.

(d)

Monitor installation schedule. Installation of monitors shall be performed in accordance with the schedule specified in §117.534 of this title (relating to Compliance Schedule for Boilers, Process Heaters, and Stationary Engines at Minor Sources).

(e)

Testing requirements. The owner or operator of any boiler, process heater, or engine subject to the emission limitations of §117.475 of this title shall comply with the following testing requirements.

(1)

Each boiler, process heater, or engine shall be tested for NO x , carbon monoxide (CO), and O 2 emissions.

(2)

Boilers, process heaters, and engines which inject urea or ammonia into the exhaust stream for NO x control shall be tested for ammonia emissions.

(3)

All testing shall be conducted while operating at the maximum rated capacity, or as near thereto as practicable. Compliance shall be determined by the average of three one-hour emission test runs, using the following test methods:

(A)

Test Method 7E or 20 (40 CFR 60, Appendix A) for NOx ;

(B)

Test Method 10, 10A, or 10B (40 CFR 60, Appendix A) for CO;

(C)

Test Method 3A or 20 (40 CFR 60, Appendix A) for O2 ;

(D)

Test Method 2 (40 CFR 60, Appendix A) for exhaust gas flow and following the measurement site criteria of Test Method 1, Section 2.1 (40 CFR 60, Appendix A), or Test Method 19 (40 CFR 60, Appendix A) for exhaust gas flow in conjunction with the measurement site criteria of Performance Specification 2, Section 3.2 (40 CFR 60, Appendix B);

(E)

American Society of Testing and Materials (ASTM) Method D1945-91 or ASTM Method D3588- 93 for fuel composition; ASTM Method D1826-88 or ASTM Method D3588-91 for calorific value; or

(F)

EPA-approved alternate test methods or minor modifications to these test methods as approved by the executive director, as long as the minor modifications meet the following conditions:

(i)

the change does not affect the stringency of the applicable emission limitation; and

(ii)

the change affects only a single source or facility application.

(4)

Test results shall be reported in the units of the applicable emission limits and averaging periods. If compliance testing is based on 40 CFR, Part 60, Appendix A reference methods, the report must contain the information specified in §117.211(g) of this title (relating to Initial Demonstration of Compliance).

(5)

For boilers, process heaters, or engines equipped with CEMS or PEMS, the CEMS or PEMS shall be installed and operational before testing under this subsection. Verification of operational status shall, as a minimum, include completion of the initial monitor certification and the manufacturer's written requirements or recommendations for installation, operation, and calibration of the device.

(6)

Initial compliance with the emission specifications of §117.475 of this title for boilers, process heaters, or engines operating with CEMS or PEMS shall be demonstrated after monitor certification testing using the NO x CEMS or PEMS.

(7)

For units not operating with CEMS or PEMS, the following apply.

(A)

Retesting as specified in paragraphs (1) - (4) of this subsection is required within 60 days after any modification which could reasonably be expected to increase the NO x emission rate.

(B)

Retesting as specified in paragraphs (1) - (4) of this subsection may be conducted at the discretion of the owner or operator after any modification which could reasonably be expected to decrease the NOx emission rate, including, but not limited to, installation of post-combustion controls, low-NO x burners, low excess air operation, staged combustion (for example, overfire air), flue gas recirculation (FGR), and fuel-lean and conventional (fuel-rich) reburn.

(C)

The NO x emission rate determined by the retesting shall establish a new emission factor to be used to calculate actual emissions instead of the previously determined emission factor used to calculate actual emissions for compliance with Chapter 101, Subchapter H, Division 3 of this title (relating to Mass Emissions Cap and Trade Program).

(8)

Testing shall be performed in accordance with the schedule specified in §117.534 of this title.

(f)

Emission allowances.

(1)

For sources which are subject to Chapter 101, Subchapter H, Division 3 of this title, the NO x testing and monitoring data of subsections (a) - (e) of this section, together with the level of activity, as defined in §101.350 of this title (relating to Definitions), shall be used to establish the emission factor calculating actual emissions for compliance with Chapter 101, Subchapter H, Division 3 of this title.

(2)

The emission factor in paragraph (e)(7) of this section or paragraph (1) of this subsection is multiplied by the unit's level of activity to determine the unit's actual emissions for compliance with Chapter 101, Subchapter H, Division 3 of this title.

(g)

Recordkeeping. The owner or operator of a unit subject to the emission limitations of §117.475 of this title shall maintain written or electronic records of the data specified in this subsection. Such records shall be kept for a period of at least five years and shall be made available upon request by authorized representatives of the executive director, EPA, or local air pollution control agencies having jurisdiction. The records shall include:

(1)

records of annual fuel usage;

(2)

for each unit using a CEMS or PEMS in accordance with subsection (c) of this section, monitoring records of:

(A)

hourly emissions and fuel usage (or stack exhaust flow) for units complying with an emission limit enforced on a block one-hour average; and

(B)

daily emissions and fuel usage (or stack exhaust flow) for units complying with an emission limit enforced on a rolling 30-day average. Emissions must be recorded in units of:

(i)

pound per million British thermal units (Btu) heat input; and

(ii)

pounds or tons per day;

(3)

for each stationary internal combustion engine subject to the emission limitations of §117.475 of this title, records of:

(A)

emissions measurements required by §117.478(b)(5) of this title (relating to Operating Requirements); and

(B)

catalytic converter, air-fuel ratio controller, or other emissions-related control system maintenance, including the date and nature of corrective actions taken;

(4)

records of carbon monoxide measurements specified in §117.478(b)(5) of this title;

(5)

records of the results of initial certification testing, evaluations, calibrations, checks, adjustments, and maintenance of CEMS, PEMS, or steam-to-fuel or water-to-fuel ratio monitoring systems; and

(6)

records of the results of performance testing, including the testing conducted in accordance with subsection (e) of this section.

This agency hereby certifies that the proposal has been reviewed by legal counsel and found to be within the agency's legal authority to adopt.

Filed with the Office of the Secretary of State, on August 11, 2000.

TRD-200005640

Margaret Hoffman

Director, Environmental Law Division

Texas Natural Resource Conservation Commission

Earliest possible date of adoption: September 24, 2000

For further information, please call: (512) 239-0348


Subchapter E. ADMINISTRATIVE PROVISIONS

30 TAC §§117.510, 117.520, 117.534

STATUTORY AUTHORITY

The amendments and new section are proposed under the Texas Health and Safety Code, TCAA, §382.011, concerning General Powers and Duties, which provides the commission with the authority to establish the level of quality to be maintained in the state's air and the authority to control the quality of the state's air; §382.012, concerning State Air Control Plan, which requires the commission to develop plans for protection of the state's air, such as the SIP; §382.016, concerning Monitoring Requirements; Examination of Records, which authorizes the commission to prescribe requirements for owners or operators of sources to make and maintain records of emissions measurements; §382.017, concerning Rules, which provides the commission with the authority to adopt rules consistent with the policy and purposes of the TCAA; and §382.051(d), concerning Permitting Authority of Board; Rules, which authorizes the commission to adopt rules as necessary to comply with changes in federal law or regulations applicable to permits under Chapter 382.

The proposed amendments and new section implement the Texas Health and Safety Code, TCAA, §§382.011, 382.012, 382.016, 382.017, and 382.051(d).

§117.510.Compliance Schedule for [ For ] Utility Electric Generation in Ozone Nonattainment Areas.

(a)

The owner or operator of each electric utility in the Beaumont/Port Arthur ozone nonattainment area shall comply with the requirements of Subchapter B, Division 1 of this chapter (relating to Utility Electric Generation in Ozone Nonattainment Areas) as soon as practicable, but no later than the dates specified in this subsection.

(1)

(No change.)

(2)

Emission specifications for attainment demonstration. The owner or operator shall comply with the requirements of §117.106(a) of this title (relating to Emission Specifications for Attainment Demonstrations) as soon as practicable, but no later than:

(A)

May 1, 2003, demonstrate that at least two-thirds of the NO x emission reductions required by §117.106(a) of this title have been accomplished, as measured either by

(i)

the total number of units required to reduce emissions in order to comply with §117.106(a) of this title using direct compliance with the emission specifications, counting only units still required to reduce after May 11, 2000 [ the effective date of §117.106(a) of this title ]; or

(ii)

the total amount of emissions reductions required to comply with §117.106(a) of this title using the alternative methods to comply, either:

(I)

Section 117.108 of this title (relating to System Cap) ; [ , ] or

(II)

(No change.)

(B) - (D)

(No change.)

(E)

May 1, 2005, submit a revised final control plan which contains:

(i) - (ii)

(No change.)

(iii)

any other revisions to the source's final control plan as a result of complying with the emission specifications in §117.106(a) of this title; and

(F)

July 31, 2005, submit to the executive director the applicable tests for the initial demonstration of compliance as specified in §117.111 of this title, if using the 30-day average system cap NO x emission limit to comply with the emission specifications in §117.106(a) of this title.

(b)

The owner or operator of each electric utility in the Dallas/Fort Worth ozone nonattainment area shall comply with the requirements of Subchapter B, Division 1 of this chapter as soon as practicable, but no later than the dates specified in this subsection.

(1)

Reasonably available control technology (RACT). The owner or operator shall comply with the requirements of Subchapter B, Division 1 of this chapter as soon as practicable, but no later than March 31, 2001 (final compliance date), except as provided in subparagraph (D) of this paragraph, relating to oil firing, and paragraph (2) of this subsection, relating to emission specifications for attainment demonstration.

(A) - (B)

(No change.)

(C)

Submit to the executive director:

(i)

(No change.)

(ii)

for units operating with CEMS or PEMS in accordance with §117.113 of this title, the results of:

(I) - (II)

(No change.)

(III)

no later than:

(-a-)

March 31, 2001 for units complying with the NO x emission limit in pounds per hour on a block one-hour average ; [ . ]

(-b-)

May 31, 2001 for units complying with the NO x emission limit on a rolling 30-day average; [ and ]

(D) - (E)

(No change.)

(2)

Emission specifications for attainment demonstration.

(A)

The owner or operator shall comply with the requirements of §117.106(b) of this title [ (relating to Emission Specifications for Attainment Demonstrations) ] as soon as practicable, but no later than:

(i)

[ (A) ] May 1, 2003, demonstrate that at least two-thirds of the NO x emission reductions required by §117.106(b) of this title have been accomplished, as measured either by

(I)

[ (i) ] the total number of units required to reduce emissions in order to comply with §117.106(b) of this title using direct compliance with the emission specifications, counting only units still required to reduce after May 11, 2000 [ the effective date of §117.106(b) of this title ]; or

(II)

[ (ii) ] the total amount of emissions reductions required to comply with §117.106(b) of this title using the alternative methods to comply, either:

(-a-)

[ (I) ] Section 117.108 of this title (relating to System Cap) ; [ , ] or

(-b-)

[ (II) ] Section 117.570 (relating to Trading);

(ii)

[ (B) ] May 1, 2003, submit to the executive director:

(I)

[ (i) ] identification of enforceable emission limits which satisfy clause (i) [ subparagraph (A) ] of this subparagraph [ paragraph ];

(II)

[ (ii) ] the information specified in §117.116 of this title [ (relating to Final Control Plans Procedures for Attainment Demonstration Emission Specifications) ] to comply with clause (i) [ subparagraph (A) ] of this subparagraph [ paragraph ]; and

(III)

[ (iii) ] any other revisions to the source's final control plan as a result of complying with clause (i) [ subparagraph (A) ] of this subparagraph [ paragraph ];

(iii)

[ (C) ] July 31, 2003, submit to the executive director the applicable tests for the initial demonstration of compliance as specified in §117.111 of this title, if using the 30-day average system cap to comply with clause (i) [ subparagraph (A) ] of this subparagraph [ paragraph ];

(iv)

[ (D) ] May 1, 2005, comply with §117.106(b) of this title;

(v)

[ (E) ] May 1, 2005, submit a revised final control plan which contains:

(I)

[ (i) ] a demonstration of compliance with §117.106(b) of this title;

(II)

[ (ii) ] the information specified in §117.116 of this title; and

(III)

[ (iii) ] any other revisions to the source's final control plan as a result of complying with the emission specifications in §117.106(b) of this title; and

(vi)

[ (F) ] July 31, 2005, submit to the executive director the applicable tests for the initial demonstration of compliance as specified in §117.111 of this title, if using the 30-day average system cap NO x emission limit to comply with the emission specifications in §117.106(b) of this title.

(B)

The requirements of 117.510(b)(2)(A)(i) of this title may be modified as follows. Boilers which are to be retired and decommissioned before May 1, 2005 are not required to install controls by May 1, 2003 if the following conditions are met:

(i)

the boiler is designated by the Public Utility Commission of Texas to be necessary to operate for reliability of the electric system;

(ii)

the owner provides the executive director an enforceable written commitment by May 1, 2003 to retire and permanently decommission the boiler by May 1, 2005;

(iii)

the utility boiler is retired and permanently decommissioned by May 1, 2005; and

(iv)

by May 1, 2003, all remaining boilers (those not designated for retirement and decommissioning as specified in clauses (i) - (iii) of this subparagraph) within the electric utility system are controlled to achieve at least two-thirds of the NO x emission reductions from units not being retired and decommissioned.

(c)

The owner or operator of each electric utility in the Houston/Galveston ozone nonattainment area shall comply with the requirements of Subchapter B, Division 1 of this chapter as soon as practicable, but no later than the dates specified in this subsection. [ November 15, 1999 (final compliance date). The owner or operator shall: ]

(1)

Reasonably Available Control Technology. The owner or operator shall, for all units, comply with the requirements of Subchapter B, Division 1 of this chapter as soon as practicable, but no later than November 15, 1999 (final compliance date), except as specified in subparagraph (D) of this paragraph, relating to oil firing, and paragraph (2) of this subsection, relating to emission specifications for attainment demonstration.

(A)

[ (1) ] conduct applicable CEMS or PEMS evaluations and quality assurance procedures as specified in §117.113 of this title according to the following schedules:

(i)

[ (A) ] for equipment and software required pursuant to 40 CFR 75, no later than January 1, 1995 for units firing coal, and no later than July 1, 1995 for units firing natural gas or oil; and

(ii)

[ (B) ] for equipment and software not required under 40 CFR 75, no later than November 15, 1999;

(B)

[ (2) ] install all NO x abatement equipment and implement all NO x control techniques no later than November 15, 1999;

(C)

[ (3) ] submit to the executive director:

(i)

[ (A) ] for units operating without CEMS or PEMS, the results of applicable tests for initial demonstration of compliance as specified in §117.111 of this title; by April 1, 1994, or as early as practicable, but in no case later than November 15, 1999;

(ii)

[ (B) ] for units operating with CEMS or PEMS in accordance with §117.113 of this title, the results of:

(I)

[ (i) ] the applicable CEMS or PEMS performance evaluation and quality assurance procedures as specified in §117.113 of this title; and

(II)

[ (ii) ] the applicable tests for the initial demonstration of compliance as specified in §117.111 of this title;

(III)

[ (iii) ] no later than:

(-a-)

[ (I) ] November 15, 1999, for units complying with the NO x emission limit on an hourly average; and

(-b-)

[ (II) ] January 15, 2000, for units complying with the NO x emission limit on a rolling 30-day average;

(D)

[ (4) ] conduct applicable tests for initial demonstration of compliance with the NO x emission limit for fuel oil firing, in accordance with §117.111(d)(2) of this title, and submit test results within 60 days after completion of such testing; and

(E)

[ (5) ] submit a final control plan for compliance in accordance with §117.115 of this title, no later than November 15, 1999.

(2)

Emission specifications for attainment demonstration. The owner or operator shall comply with the requirements of §117.106(c) of this title as soon as practicable, but no later than:

(A)

December 31, 2001, install all totalizing fuel flow meters, NO x monitors, and carbon monoxide (CO) monitors required by §117.113 of this title;

(B)

December 31, 2002, demonstrate that at least one-third of the NO x emission reductions required by §117.106(c) of this title have been accomplished, as measured by the total amount of emissions reductions required to comply with §117.106(c) of this title using §117.108 of this title;

(C)

December 31, 2003, demonstrate that at least two-thirds of the NO x emission reductions required by §117.106(c) of this title have been accomplished, as measured by the total amount of emissions reductions required to comply with §117.106(c) of this title using §117.108 of this title;

(D)

December 31, 2002, submit to the executive director:

(i)

identification of enforceable emission limits which satisfy subparagraph (B) of this paragraph;

(ii)

the information specified in §117.116 of this title to comply with subparagraph (B) of this paragraph; and

(iii)

any other revisions to the source's final control plan as a result of complying with subparagraph (B) of this paragraph;

(E)

February 28, 2003, submit to the executive director the applicable tests for the initial demonstration of compliance as specified in §117.111 of this title;

(F)

December 31, 2004, demonstrate that all NOx emission reductions required by §117.106(c) of this title have been accomplished, as measured by the total amount of emissions reductions required to comply with §117.106(c) of this title using §117.108 of this title;

(G)

February 28, 2005, submit a revised final control plan which contains:

(i)

a demonstration of compliance with §117.106(c) of this title;

(ii)

the information specified in §117.116 of this title; and

(iii)

any other revisions to the source's final control plan as a result of complying with the emission specifications in §117.106(c) of this title; and

(H)

the appropriate dates specified in Chapter 101, Subchapter H, Division 3 of this title (relating to Mass Emissions Cap and Trade Program) for the requirements of that program.

§117.520.Compliance Schedule for [ For ] Industrial, Commercial, and Institutional Combustion Sources in Ozone Nonattainment Areas.

(a)

The owner or operator of each industrial, commercial, and institutional [ , and industrial ] source in the Beaumont/Port Arthur ozone nonattainment area shall comply with the requirements of Subchapter B, Division 3 of this chapter (relating to Industrial, Commercial, and Institutional Combustion Sources in Ozone Nonattainment Areas) as soon as practicable, but no later than the dates specified in this subsection.

(1) - (2)

(No change.)

(3)

Emission specifications for attainment demonstration. The owner or operator shall comply with the requirements of §117.206(a) of this title (relating to Emission Specifications for Attainment Demonstrations) as soon as practicable, but no later than

(A)

May 1, 2003, demonstrate that at least two-thirds of the NO x emission reductions required by §117.206(a) of this title have been accomplished, as measured either by

(i)

the total number of units required to reduce emissions in order to comply with §117.206(a) of this title using direct compliance with the emission specifications, counting only units still required to reduce after May 11, 2000 [ the effective date of §117.206(a) of this title ]; or

(ii)

(No change.)

(B)

May 1, 2003, submit to the executive director:

(i) - (iv)

(No change.)

(v)

any other revisions to the source's final control plan as a result of complying with the emission specifications in §117.206(a) of this title;

(C) - (D)

(No change.)

(E)

May 1, 2005, submit a revised final control plan which contains:

(i) - (ii)

(No change.)

(iii)

any other revisions to the source's final control plan as a result of complying with the emission specifications in §117.206(a) of this title; and

(F)

July 31, 2005, submit to the executive director the applicable tests for the initial demonstration of compliance as specified in §117.211 of this title, if using the 30-day average source cap NO x emission limit to comply with the emission specifications in §117.206(a) of this title.

(b)

The owner or operator of each industrial, commercial, and institutional [ , and industrial ] source in the Dallas/Fort Worth ozone nonattainment area shall comply with the requirements of Subchapter B, Division 3 of this chapter as soon as practicable, but no later than March 31, 2002 (final compliance date). The owner or operator shall:

(1) - (2)

(No change.)

(c)

The owner or operator of each industrial, commercial, and institutional [ , and industrial ] source in the Houston/Galveston ozone nonattainment area shall comply with the requirements of Subchapter B, Division 3 of this chapter as soon as practicable, but no later than the dates specified in this subsection. [ November 15, 1999 (final compliance date). The owner or operator shall: ]

(1)

Reasonably available control technology (RACT). The owner or operator shall, for all units, comply with the requirements of Subchapter B, Division 3 of this chapter, except as specified in paragraph (2) (relating to emission specifications for attainment demonstration), by November 15, 1999 (final compliance date) and:

(A)

[ (1) ] submit a plan for compliance in accordance with §117.209 of this title (relating to Initial Control Plan Procedures) according to the following schedule:

(i)

[ (A) ] for major sources of NOx which have units subject to emission specifications under this chapter, submit an initial control plan for all such units no later than April 1, 1994;

(ii)

[ (B) ] for major sources of NOx which have no units subject to emission specifications under this chapter, submit an initial control plan for all such units no later than September 1, 1994; and

(iii)

[ (C) ] for major sources of NOx subject to either subparagraphs (A) or (B) of this paragraph, submit the information required by §117.209(c)(6), (7), and (9) of this title no later than September 1, 1994;

(B)

[ (2) ] install all NO x abatement equipment and implement all NO x control techniques no later than November 15, 1999;

(C)

[ (3) ] submit to the executive director:

(i)

[ (A) ] for units operating without CEMS or PEMS, the results of applicable tests for initial demonstration of compliance as specified in §117.211 of this title; by April 1, 1994, or as early as practicable, but in no case later than November 15, 1999;

(ii)

[ (B) ] for units operating with CEMS or PEMS in accordance with §117.213 of this title, submit the results of:

(I)

[ (i) ] the applicable CEMS or PEMS performance evaluation and quality assurance procedures as specified in §117.213(e)(1)(A) and (B) and (f)(3) - (5)(A) of this title; and

(II)

[ (ii) ] the applicable tests for the initial demonstration of compliance as specified in §117.211 of this title;

(III)

[ (iii) ] no later than:

(-a-)

[ (I) ] November 15, 1999, for units complying with the NO x emission limit on an hourly average; and

(-b-)

[ (II) ] January 15, 2000, for units complying with the NO x emission limit on a rolling 30-day average;

(iii)

[ (C) ] a final control plan for compliance in accordance with §117.215 of this title, no later than November 15, 1999; and

(iv)

[ (D) ] the first semiannual report required by §117.219(d) or (e) of this title, covering the period November 15, 1999, through December 31, 1999, no later than January 31, 2000.

(2)

Emission specifications for attainment demonstration. The owner or operator shall comply with the requirements of §117.206(c) of this title as soon as practicable, but no later than:

(A)

December 31, 2001, install all totalizing fuel flow meters, NO x monitors, and carbon monoxide (CO) monitors required by §117.213 of this title;

(B)

December 31, 2002, demonstrate that at least one-third of the NO x emission reductions required by §117.206(c) of this title have been accomplished, as measured by:

(i)

for electric generating facilities (EGFs), the total amount of emissions reductions required to comply with §117.206(c) of this title using §117.210 of this title (relating to System Cap); and

(ii)

for non-EGFs, the total amount of emissions reductions required to comply with §117.206(c) of this title using Chapter 101, Subchapter H, Division 3 of this title (relating to Mass Emissions Cap and Trade Program);

(C)

December 31, 2003, demonstrate that at least two-thirds of the NO x emission reductions required by §117.206(c) of this title have been accomplished, as measured by:

(i)

for EGFs, the total amount of emissions reductions required to comply with §117.206(c) of this title using §117.210 of this title; and

(ii)

for non-EGFs, the total amount of emissions reductions required to comply with §117.206(c) of this title using Chapter 101, Subchapter H, Division 3 of this title;

(D)

December 31, 2002, submit to the executive director:

(i)

identification of enforceable emission limits which satisfy subparagraph (B) of this paragraph;

(ii)

for units operating without CEMS or PEMS, the results of applicable tests for initial demonstration of compliance as specified in §117.211 of this title;

(iii)

for units newly operating with CEMS or PEMS to comply with the monitoring requirements of §117.213(c) of this title, the applicable CEMS or PEMS performance evaluation and quality assurance procedures as specified in §117.213(e)(1)(A) and (B) and (f)(3) - (5)(A) of this title;

(iv)

the information specified in §117.216 of this title to comply with subparagraph (B) of this paragraph; and

(v)

any other revisions to the source's final control plan as a result of complying with subparagraph (B) of this paragraph;

(E)

February 28, 2003, submit to the executive director the applicable tests for the initial demonstration of compliance as specified in §117.211 of this title;

(F)

December 31, 2004, demonstrate that all NOx emission reductions required by §117.206(c) of this title have been accomplished, as measured by:

(i)

for EGFs, the total amount of emissions reductions required to comply with §117.206(c) of this title using §117.210 of this title; and

(ii)

for non-EGFs, the total amount of emissions reductions required to comply with §117.206(c) of this title using Chapter 101, Subchapter H, Division 3 of this title;

(G)

February 28, 2005, submit a revised final control plan which contains:

(i)

a demonstration of compliance with §117.206(c) of this title;

(ii)

the information specified in §117.216 of this title; and

(iii)

any other revisions to the source's final control plan as a result of complying with the emission specifications in §117.206(c) of this title; and

(H)

the appropriate dates specified in Chapter 101, Subchapter H, Division 3 of this title (relating to Mass Emissions Cap and Trade Program) for the requirements of that program.

§117.534.Compliance Schedule for Boilers, Process Heaters, and Stationary Engines at Minor Sources.

The owner or operator of each stationary source of nitrogen oxides (NO x ) in the Houston/Galveston ozone nonattainment area which is not a major source of NO x shall comply with the requirements of Subchapter D, Division 2 of this chapter (relating to Boilers, Process Heaters, and Stationary Engines at Minor Sources) as follows.

(1)

For sources which are subject to Chapter 101, Subchapter H, Division 3 of this title (relating to Mass Emissions Cap and Trade Program), the owner or operator shall:

(A)

install all totalizing fuel flow meters and begin keeping records of fuel usage no later than December 31, 2001; and

(B)

comply with all other requirements of Subchapter D, Division 2 of this chapter in accordance with the schedule specified in Chapter 101, Subchapter H, Division 3 of this title.

(2)

For sources which are not subject to Chapter 101, Subchapter H, Division 3 of this title, the owner or operator shall:

(A)

install all totalizing fuel flow meters and begin keeping records of fuel usage no later than December 31, 2001; and

(B)

comply with all other requirements of Subchapter D, Division 2 of this chapter as soon as practicable, but no later than December 31, 2002.

This agency hereby certifies that the proposal has been reviewed by legal counsel and found to be within the agency's legal authority to adopt.

Filed with the Office of the Secretary of State, on August 11, 2000.

TRD-200005639

Margaret Hoffman

Director, Environmental Law Division

Texas Natural Resource Conservation Commission

Earliest possible date of adoption: September 24, 2000

For further information, please call: (512) 239-0348


30 TAC §117.570

The Texas Natural Resource Conservation Commission (commission) proposes an amendment to §117.570, Trading. This amendment is also proposed as a revision to the Texas state implementation plan (SIP).

BACKGROUND AND SUMMARY OF THE FACTUAL BASIS FOR THE PROPOSED RULE

Section 117.570 currently refers to 30 TAC §101.29, Emissions Credit Banking and Trading, as a method of meeting emission requirements in Chapter 117. In concurrent rulemaking, §101.29 would be repealed and its requirements transferred and amended to new Chapter 101, Subchapter H, Divisions 1 and 4. This rulemaking would amend §117.570 to cite the correct cross-references and relocate equations and methodologies for calculating emission requirements to comply with Chapter 117 nitrogen oxides (NO x ) emission specifications to Chapter 101, Subchapter H, Divisions 1 and 4. In addition, the amended section would require the user of credits to obtain additional emission credits or achieve lower actual emissions if new lower NO x emission specifications are established by future amendments to Chapter 117.

The commission solicits comment on additional flexibilities relating to rule content and implementation which have not been addressed in this or other concurrent rulemakings. These flexibilities may be available for both mobile and stationary sources. Additional flexibilities may also be achieved through innovative and/or emerging technology which may become available in the future. Additional sources of funds for incentive programs may become available to substitute for some of the measures considered here.

SECTION BY SECTION DISCUSSION

The revised §117.570 changes the title of the section to "Use of Emissions Credits for Compliance" from "Trading" to more clearly reflect the language in §117.570, which discusses how to use emission reduction credits for alternative compliance, not how to trade emission reduction credits.

The proposed amendment to §117.570(a) removes the reference to §101.29 and replace it with a reference to Chapter 101, Subchapter H, Division 1, Emission Reduction Credit Banking and Trading, or Chapter 101, Subchapter H, Division 4, Discrete Emission Reduction Banking and Trading. In addition, this proposal clarifies that emission reduction credits (ERCs), mobile emission reduction credits (MERCs), discrete emission reduction credits (DERCs), or mobile discrete emission reduction credits (MDERCs) may be used to meet certain control requirements of Chapter 117. This option would be limited to those units not subject to the mass cap and trade requirements of Chapter 101, Subchapter H, Division 3. The term "RC" refers to an ERC, MERC, DERC, or MDERC.

The existing §117.570(b), and the equations located there, would be deleted because the methodology for computing emission credits for compliance with Chapter 117 would be revised to be consistent with existing methodology in §101.29. In concurrent rulemaking, §101.29 would be repealed and its requirements transferred to Chapter 101, Subchapter H, new Divisions 1 and 4.

The existing §117.570(c), and the equations located there, would be deleted. The equations currently in §117.570(c)(1) would be transferred to Chapter 101, Subchapter H, new Divisions 1 and 4 in concurrent rulemaking. The equations in §117.570(c)(2) would be deleted because the methodology for computing emission credits for compliance with Chapter 117 would be revised to be consistent with existing methodology in §101.29. In concurrent rulemaking, §101.29 would be repealed and its requirements transferred to Chapter 101, Subchapter H, new Divisions 1 and 4.

The amendments to §117.570(d) would redesignate the subsection to §117.570(b) and would remove the requirement to reevaluate used RCs and add language detailing how owners or operators using Chapter 101, Subchapter H, Division 1 or Division 4 to meet the emission control requirements of Chapter 117 must obtain additional RCs or reduce actual emissions if any lower volatile organic compound emission specification is established by Chapter 117 for the unit or units using RCs.

FISCAL NOTE: COST TO STATE AND LOCAL GOVERNMENT

John Davis, Technical Specialist with Strategic Planning and Appropriations, has determined for the first five-year period the proposed amendment is in effect, there will be no fiscal implications for any unit of state and local government as a result of administration or enforcement of the proposed amendment.

The proposed amendment will achieve administrative consistency with amendments proposed in concurrent rulemaking by correcting a cross-reference made to sections relating to emission credit banking and trading. The concurrent rulemaking would repeal and transfer requirements, and move equations related to the calculation of emission credits for compliance with emission reduction requirements.

The proposed amendment does not add regulatory requirements, but is proposed to allow compliance flexibility in meeting current or future NO x emission limitations. The proposed amendment clarifies that ERCs, MERCs, DERCs, or MDERCs may be used to meet any of the requirements for meeting emission requirements. Additionally, the proposed amendment adds language describing how owners or operators using emission credit banking and trading to meet emission control requirements must obtain additional emission credits or reduce actual emissions if any lower NO x emission specification is established by future amendments.

PUBLIC BENEFIT AND COSTS

Mr. Davis has also determined for each of the first five years the proposed amendment is in effect, the public benefit anticipated as a result of implementing the amendment will be the increased compliance with NO x emissions limitations through increased rule flexibility.

There are no anticipated fiscal impacts to persons and businesses as a result of implementation of the proposed amendment because the proposed actions are administrative in nature. The proposed amendment will correct a cross-reference with Chapter 101, clarify the use of ERCs, MERCs, DERCs, and MERCs, and will add language specifying that owners must obtain additional emission credits or lower actual emissions if stricter NO x requirements are implemented through future amendments.

SMALL AND MICRO-BUSINESS ASSESSMENT

There will be no adverse fiscal implications for small or micro-businesses as a result of administration or enforcement of the proposed amendment. The proposed actions are administrative in nature. The proposed amendment will correct a cross-reference with Chapter 101, clarify the use of ERCs, MERCs, DERCs, and MERCs, and will add language specifying that owners must obtain additional emission credits or lower actual emissions if stricter NOx requirements are implemented through future amendments to Chapter 117.

DRAFT REGULATORY ANALYSIS

The commission has reviewed the proposed rulemaking in light of the regulatory analysis requirements of Texas Government Code, §2001.0225. The commission has determined that these proposed amendment to Chapter 117 does not meet the definition of a "major environmental rule" as defined in Texas Government Code, §2001.0225. "Major environmental rule" means a rule, the specific intent of which, is to protect the environment or reduce risks to human health from environmental exposure, and that may adversely affect in a material way the economy, a sector of the economy, productivity, competition, jobs, the environment, or the public health and safety of the state or a sector of the state. The commission is proposing the amendment to achieve administrative consistency with amendments to Chapter 101 proposed in concurrent rulemaking. The proposed amendment to Chapter 117 does not add regulatory requirements, but is proposed to allow compliance flexibility in meeting current or future NO x emission limitations in Chapter 117. In addition, Texas Government Code, §2001.0225, only applies to a major environmental rule, the result of which is to: 1.) exceed a standard set by federal law, unless the rule is specifically required by state law; 2.) exceed an express requirement of state law, unless the rule is specifically required by federal law; 3.) exceed a requirement of a delegation agreement or contract between the state and an agency or representative of the federal government to implement a state and federal program; or 4.) adopt a rule solely under the general powers of the agency instead of under a specific state law. This rulemaking is not subject to the regulatory analysis provisions of §2001.0225(b), because the proposed rule does not meet any of the four applicability requirements. Specifically, the emission banking and trading requirements within this proposal were developed in order to meet the ozone NAAQS set by the EPA under the Federal Clean Air Act (FCAA), §7409, and therefore meet a federal requirement. States are primarily responsible for ensuring attainment and maintenance of NAAQS once EPA has established those standards. Under the FCAA, §7410 and related provisions, states must submit, for EPA approval, SIPs that provide for the attainment and maintenance of NAAQS through a control program directed to sources of the pollutants involved. This proposal is not an express requirement of state law, but was developed specifically in order to meet the air quality standards established under federal law as NAAQS, as authorized under the TCAA, §382.012 (concerning State Air Control Plan). This proposal is intended to help bring the HGA ozone nonattainment area into compliance. The proposed amendments do not exceed a standard set by federal law, exceed an express requirement of state law unless specifically required by federal law, nor exceed a requirement of a delegation agreement. The proposed amendments were not developed solely under the general powers of the agency, but were specifically developed to meet the air quality standards established under federal law as NAAQS. The commission invites public comment on the draft regulatory impact analysis.

TAKINGS IMPACT ASSESSMENT

The commission has completed a takings impact assessment for the proposed rule. The following is a summary of that assessment. The commission is proposing the amendment to achieve administrative consistency with amendments to Chapter 101 proposed in concurrent rulemaking. The proposed amendment to Chapter 117 does not add regulatory requirements, but is proposed to allow compliance flexibility in meeting current or future NO x emission limitations in Chapter 117. The proposed amendment does not affect private real property in a manner which restricts or limits an owner's right to the property that would otherwise exist in the absence of a governmental action. Consequently, the proposed section does not meet the definition of a takings under Texas Government Code, §2007.002(5).

COASTAL MANAGEMENT PROGRAM CONSISTENCY REVIEW

The commission has determined the proposed rulemaking relates to an action or actions subject to the Texas Coastal Management Program (CMP) in accordance with the Coastal Coordination Act of 1991, as amended (Texas Natural Resources Code, §§33.201 et seq.), and the commission's rules in 30 TAC Chapter 281, Subchapter B, concerning Consistency with the Texas Coastal Management Program. As required by 30 TAC §281.45(a)(3) and 31 TAC §505.11(b)(2) relating to actions and rules subject to the CMP, commission rules governing air pollutant emissions must be consistent with the applicable goals and policies of the CMP. The commission has reviewed this action for consistency with the CMP goals and policies in accordance with the regulations of the Coastal Coordination Council, and has determined that the proposed rules are consistent with the applicable CMP goal expressed in 31 TAC §501.12(1) of protecting and preserving the quality and values of coastal natural resource areas, and the policy in 31 TAC §501.14(q), which requires that the commission protect air quality in coastal areas. The proposed amendment to Chapter 117 does not add regulatory requirements, but is proposed to allow compliance flexibility in meeting current or future NO x emission limitations in Chapter 117. Interested persons may submit comments on the consistency of the proposed rule with the CMP during the public comment period.

EFFECT ON SITES SUBJECT TO THE FEDERAL OPERATING PERMIT PROGRAM

Sources which currently have §117.570 listed in their federal operating permit would not be required to amend the permit in response to this amendment. However, those sources that do not have a reference to §117.570 in their operating permit and wish to use RCs must revise their operating permit consistent with the process in 30 TAC Chapter 122, to include the revised §117.570 requirements for each emission unit affected by §117.570 at their site.

ANNOUNCEMENT OF HEARINGS

The commission will hold public hearings on this proposal at the following times and locations: September 18, 2000, 10:00 a.m., Lone Star Convention Center, 9055 Airport Road (FM 1484), Conroe; September 18, 2000, 7:00 p.m., Lake Jackson Civic Center, 333 Highway 332 East, Lake Jackson; September 19, 2000, 10:00 a.m. and 7:00 p.m., George Brown Convention Center, 1001 Avenida de Las Americas, Houston; September 20, 2000, 9:00 a.m., VFW Hall, 6202 George Bush Drive, Katy; September 20, 2000, 6:00 p.m., East Harris County Community Center, 7340 Spencer, Pasadena; September 21, 2000, 10:00 a.m., Southeast Texas Regional Airport Media Room, 6000 Airline Drive, Beaumont; September 21, 2000, 2:00 p.m., Amarillo City Commission Chambers, City Hall, 509 East 7th Avenue, Amarillo; September 21, 2000, 6:00 p.m., Charles T. Doyle Convention Center, 21st Street at Phoenix Lane, Texas City; September 22, 2000, 10:00 a.m., Dayton High School, 2nd Floor Lecture Room, 3200 North Cleveland Street, Dayton; September 22, 2000, 11:00 a.m., El Paso City Council Chambers, 2 Civic Center Plaza, 2nd Floor, El Paso; September 22, 2000, 2:00 p.m., North Central Texas Council of Governments, 2nd Floor Board Room, 616 Six Flags Drive, Suite 200, Arlington; and September 25, 2000, 10:00 a.m., Texas Natural Resource Conservation Commission, 12100 North I-35, Building E, Room 201S, Austin. The hearings are structured for the receipt of oral or written comments by interested persons. Registration will begin one hour prior to each hearing. Individuals may present oral statements when called upon in order of registration. A four-minute time limit will be established at each hearing to assure that enough time is allowed for every interested person to speak. Open discussion will not occur during each hearing; however, agency staff members will be available to discuss the proposal one hour before each hearing, and will answer questions before and after each hearing.

Persons with disabilities who have special communication or other accommodation needs, who are planning to attend the hearing, should contact the Office of Environmental Policy, Analysis, and Assessment at (512) 239-4900. Requests should be made as far in advance as possible.

SUBMITTAL OF COMMENTS

Written comments may be submitted to Heather Evans, Office of Environmental Policy, Analysis, and Assessment, MC 206, P.O. Box 13087, Austin, Texas 78711-3087, faxed to (512) 239-4808, or emailed to siprules@tnrcc.state.tx.us . All comments should reference Rule Log Number 1998-089-101-AI. Comments must be received by 5:00 p.m., September 25, 2000. For further information, please contact Matthew R. Baker at (512) 239-1091 or Beecher Cameron at (512) 239-1495.

STATUTORY AUTHORITY

The amendment is proposed under the Texas Health and Safety Code, TCAA, §382.011, which authorizes the commission to control the quality of the state's air; §382.012, which authorizes the commission to develop a plan for control of the state's air; §382.017, which provides the commission the authority to adopt rules consistent with the policy and purposes of the TCAA, and 42 United States Code, §7410(a)(2)(A), which requires SIPs to include enforceable emission limitations and other control measures or techniques, including economic incentives such as fees, marketable permits, and auction of emission rights.

The proposed amendment implements TCAA, §382.002, relating to Policy and Purpose; §382.011, relating to General Powers and Duties; and §382.012, relating to State Air Control Plan.

Use of Emissions Credits for Compliance [ Trading ].

(a)

An owner or operator of a unit not subject to Chapter 101, Subchapter H, Division 3 of this title (relating to Mass Emission Cap and Trade Program) may meet emission control requirements of [ may reduce the amount of emission reductions required by ] §117.105 or §117.205 of this title (relating to Emission Specifications for Reasonably Available Control Technology (RACT)), §117.106 or §117.206 of this title (relating to Emission Specifications for Attainment Demonstrations), §117.107 of this title (relating to Alternative System-Wide Emission Specifications), §117.207 of this title (relating to Alternative Plant-Wide Emission Specifications), §117.108 of this title (relating to System Cap), §117.223 of this title (relating to Source Cap), or §117.475 of this title (relating to Emission Specifications) in whole or in part , by obtaining an emission reduction credit (ERC), mobile emission reduction credit (MERC), discrete emission reduction credit (DERC), or mobile discrete emission reduction credit (MDERC) [ established ] in accordance with [ this section and §101.29 of this title (relating to Emission Credit Banking and Trading) ] Chapter 101, Subchapter H, Division 1 of this title (relating to Emission Credit Banking and Trading) or Chapter 101, Subchapter H, Division 4 of this title (relating to Discrete Emission Reduction Banking and Trading), unless there are federal or state regulations or permits under the same commission account number which contain a condition or conditions precluding such use . [ Any ERCs or DERCs for nitrogen oxides (NO x ) generated under the provisions of §101.29 of this title used for the purposes of this chapter become subject to the limitations and provisions of this section. ] For the purposes of this section, the term " reduction credit (RC) [ ARC ]" refers to an ERC, MERC, DERC, or MDERC , whichever is applicable.

[(b)

Reduction credits (RCs) shall be generated as follows.]

[(1)

For sources not subject to the emission specifications of §§117.105, 117.205, or 117.206 of this title, creditable RCs used to meet compliance with those sections shall be established in accordance with the following requirements:]

[(A)

The source shall use emissions test data to establish the actual emissions baseline in accordance with the testing requirements of §117.209(b) of this title (relating to Initial Control Plan Procedures), or §117.111 or §117.211 of this title (relating to Initial Demonstration of Compliance), as applicable. The actual emissions baseline is defined as the actual annual emissions, in tons per year, from a source determined by use of data representative of actual operations:]

[(i)

in 1990 or later, for compliance with emission specifications required for reasonably available control technology under §117.105 or §117.205(a) - (d) of this title;]

[(ii)

after September 10, 1993 for compliance with emission specifications required for the Beaumont/Port Arthur ozone attainment demonstration under §§117.106, 117.205(e), or 117.206 of this title;]

[(iii)

after 1997 for compliance with emission specifications required for the Dallas/Fort Worth ozone attainment demonstration under §117.106 or §117.206 of this title;]

[(iv)

assuming full compliance with all applicable state and federal rules and regulations;]

[(B)

If the source creating the RC has been shut down or irreversibly changed, the source shall use the best available data and good engineering practice to establish the actual emissions baseline.]

[(2)

For sources subject to the emission specifications of §§117.105, 117.106, 117.205, or 117.206 of this title, creditable RCs shall be calculated using the following equations:]

[Figure: 30 TAC §117.570(b)(2)]

[(3)

RCs from shutdown units may be generated only by units participating in a source cap in accordance with §117.223 of this title.]

[(4)

For units participating in a source cap in accordance with §117.223 of this title, creditable RCs may be generated only under the following conditions:]

[(A)

The source cap allowable must be reduced by the amount of any creditable ERCs claimed for the unit or units, and]

[(B)

the actual historical average of the daily heat input for the unit or units may not include one standard deviation of the actual average daily heat input for the period for which creditable reductions are claimed.]

[(c)

Reduction credits shall be used as follows.]

[(1)

An owner or operator complying with §117.223 of this title may reduce the amount of emission reductions otherwise required by complying with the following equations instead of the equations in §117.223(b)(1) and (2) of this title.]

[Figure: 30 TAC §117.570(c)(1)]

[(2)

An owner or operator complying with §§117.105, 117.106, 117.107, 117.205, 117.206, §117.207 of this title may reduce the amount of emission reduction otherwise required by those sections for a unit or units at a major source by complying with individual unit emission limits calculated from the following equation:]

[Figure: 30 TAC §117.570(c)(2)]

[(3)

RCs from shutdown units may be used only by units participating in a source cap in accordance with §117.223 of this title]

(b)

[ (d) ] Any lower NO x emission specification established under this chapter [ by rule or permit ] for the unit or units using Rcs [ generating an ERC ] shall require the user of the RCs [ ERC ] to obtain additional RCs in accordance with Chapter 101 Subchapter H, Division 1 of this title or Chapter 101, Subchapter H, Division 4 of this title and/or [ an approved new reduction credit or ] otherwise reduce emissions prior to the effective date of such rule [ or permit ] change. For units using RCs [ an ERC ] in accordance with this section which are subject to new, more stringent rule [ or permit ] limitations, the owner or operator using the RCs [ ERC ] shall submit a revised final control plan to the executive director in accordance with §117.117 or §117.217 of this title (relating to Revision of Final Control Plan) to revise the basis for compliance with the emission specifications of this chapter. The owner or operator using the RCs [ ERC ] shall submit the revised final control plan as soon as practicable, but no later than 90 days prior to the effective date of the new, more stringent rule [ or permit limitations ]. The owner or operator of the unit(s) currently using RCs shall calculate the necessary emission reductions per unit as follows. [ In addition, the owner or operator of a unit generating the ERC shall submit a revised registration application to the executive director, in accordance with subsection (e)(1) of this section, within 90 days prior to the effective date of any new, more stringent rule or permit limitations affecting that unit. If a more stringent NO x emission specification is established by rule or permit for the unit or units generating the ERC, the value of the ERC shall be recalculated as follows: ]

Figure: 30 TAC §117.570(b)

[ Figure: 30 TAC §117.570(d) ]

[(e)

The RC program established by this section shall be administered as follows:]

[(1)

For emission units subject to the emission specifications of this chapter, which generate ERCs, MERCs, DERCs, or MDERCs and for which the owner or operator elects to comply with the individual emission specifications of §§117.105, 117.106, 117.107, 117.205, 117.206, or 117.207 of this title, the enforceable emission limit RBj shall be calculated using the maximum rated capacity.]

[(2)

For emission units subject to the emission specifications of this chapter, which generate ERCs, MERCs, DERCs, or MDERCs, and for which the owner or operator elects to achieve compliance using §117.223 of this title, the enforceable emission limit RBj shall be substituted for Rj in the source cap allowable mass emission rate equations of §117.223(b)(1) and (2) of this title, and those allowable rates shall be the enforceable limits for those sources.]

This agency hereby certifies that the proposal has been reviewed by legal counsel and found to be within the agency's legal authority to adopt.

Filed with the Office of the Secretary of State, on August 11, 2000.

TRD-200005658

Margaret Hoffman

Director, Envronmental Law Division

Texas Natural Resorce Conservatin Commission

Earliest possible date of adoption: September 24, 2000

For further information, please call: (512) 239-1966


Chapter 311. WATERSHED PROTECTION

The Texas Natural Resource Conservation Commission (TNRCC or commission) proposes new §311.6, Storm Water Runoff and Certain Non-Storm Water Discharges; §311.16, Storm Water Runoff and Certain Non-Storm Water Discharges; and §311.56, Storm Water Runoff and Certain Non-Storm Water Discharges.

BACKGROUND AND SUMMARY OF THE FACTUAL BASIS FOR THE PROPOSED RULES

Chapter 311 provides that the disposal of wastewater within defined watersheds, or water quality areas, is either prohibited or is allowed only under certain conditions. Subchapters A and B prohibit all discharges within the Lakes Travis and Austin Water Quality Areas and Lakes Inks and Buchanan Water Quality Areas, respectively, except for discharges from sewage treatment facilities that meet a defined level of effluent quality. Subchapter F prohibits discharges into or adjacent to water in the state within the Lakes Lyndon B. Johnson and Marble Falls Water Quality Areas except for discharges from treatment facilities that meet a defined level of effluent quality.

The commission received authority from the United States Environmental Protection Agency (EPA) to issue storm water and certain non-storm water discharge permits on September 14, 1998. In a September 14, 1998 memorandum of agreement (MOA) between the EPA and the commission, the EPA agreed to continue to administer storm water and certain non-storm water discharge permits that were issued prior to September 14, 1998 until they expire. Following the expiration of these permits, the commission would reissue and administer these permits as Texas pollutant discharge elimination system (TPDES) permits.

Although the TNRCC has not operated a separate state storm water permitting program, the current requirements in Subchapters A, B, and F could be interpreted to restrict the development and issuance of TPDES storm water permits within these watersheds. The commission is proposing to revise these subchapters to allow the discharge of storm water runoff and certain other non-storm water runoff if authorized by a TPDES permit. TPDES discharge permits are currently being developed to authorize storm water and certain non-storm water discharges throughout the state. The proposed new sections would allow the issuance of these permits within the specified watersheds.

SECTION BY SECTION DISCUSSION

Proposed new §§311.6, 311.16, and 311.56 (Storm Water Runoff and Certain Non-Storm Water Discharges) would allow the commission to issue TPDES permits to regulate the discharge of storm water runoff from industrial facilities, municipal separate storm sewer systems, and construction activities into the Lakes Travis, Austin, Inks, Buchanan, Lyndon B. Johnson, and Marble Falls Water Quality Areas. The proposal would also allow the commission to issue TPDES permits to regulate the discharge of the following 11 non-storm water discharges into these water quality areas: fire-fighting activities; fire hydrant flushings; potable water sources, including drinking fountain water and water line flushings; uncontaminated air conditioning or compressor condensate; lawn watering and similar irrigation drainage; pavement washdown without the use of detergents or other chemicals and where spills or leaks of toxic or hazardous materials have not occurred (unless all spilled material has been removed); routine external building wash down that does not use detergents or other compounds; uncontaminated ground water or spring water; foundation or footing drains where flows are not contaminated with process materials such as solvents; spray down of lumber and wood product storage yards where no chemical additives are used in the spray down waters and no chemicals are applied to the wood during storage; and storm water and ground water seepage from mine dewatering activities at construction sand and gravel, industrial sand, or crushed stone mining facilities.

These discharges are currently authorized in the federal national pollutant discharge elimination system (NPDES) storm water permit program. The TNRCC could choose to be more stringent in the TPDES program than the EPA is in the NPDES program, by imposing a blanket prohibition on all such discharges. However, the TNRCC's opinion is that it is probably environmentally appropriate and economically sound to allow the discharges to continue. These point source storm water and other discharges have been authorized under the NPDES program for several years, and they existed before they were regulated. Continuing the discharges under a regulatory program of individual and general permits is appropriate to ensure that the discharges do not cause an environmental problem. The commission will carefully consider the necessary terms and conditions of each proposed permit before it is issued.

Conversely, to now entirely prohibit these discharges would cause serious economic disruption. Businesses that rely on being able to discharge their storm water and other discharges would have to either find another means of disposing of the water, or shut down their business. Because of the volume of storm water, methods other than discharge would likely be prohibitively expensive. The EPA has issued permits for these discharges based on EPA's finding that the permit conditions maintain water quality. The TPDES program will continue to regulate these discharges to ensure that they do not have an adverse environmental impact. Therefore, amending this rule to enable the commission to continue the NPDES policy authorizing these discharges is appropriate.

COSTS TO STATE AND LOCAL GOVERNMENT

John Davis, Technical Specialist with Strategic Planning and Appropriations, has determined that for the first five-year period the proposed new sections are in effect, there will be fiscal implications which are not anticipated to be significant for any single unit of state and local government as a result of administration or enforcement of the proposed new sections.

The proposed new sections would provide the authority for the commission to issue TPDES storm water and certain non-storm water discharge permits, covering industrial facilities, municipal separate storm sewer systems, and construction sites located within the Lakes Travis, Austin, Inks, Buchanan, Lyndon B. Johnson, and Marble Falls Water Quality Areas (located in Travis, Burnet, and Llano Counties). The EPA currently grants permits covering storm water and certain non-storm water discharges into the areas covered by the proposed new sections. State law currently allows the issuance of permits for storm water and certain non-storm water discharges statewide; however, current commission rules prohibit storm water and certain non-storm water discharges in the areas covered by the proposed new sections.

The commission received authority from the EPA to issue storm water and certain non-storm water discharge permits on September 14, 1998. In a September 14, 1998 memorandum of agreement (MOA) between the EPA and the commission, the EPA agreed to continue to administer storm water and certain non-storm discharge permits that were issued prior to September 14, 1998 until they expire. Following expiration of these permits, the commission would reissue and administer these storm water and certain non-storm water permits as TPDES permits. The MOA also stipulated that any new storm water and certain non-storm water permits would be issued by the commission as TPDES storm water and certain non-storm water discharge permits. If the rules are not amended, facilities located within the Lakes Travis, Austin, Inks, Buchanan, Lyndon B. Johnson, and Marble Falls Water Quality Areas currently permitted by the EPA will have to capture and dispose of, in a manner that would not discharge to water in the state, all storm water and certain non-storm water that falls on their facilities. TPDES storm water and certain non-storm water discharge permits are currently being developed to authorize storm water and certain non-storm water discharges throughout the state. The proposed new sections would allow the issuance of these permits within the specified watersheds.

Examples of facilities that would be allowed to discharge as a result of these proposed new sections include: dairy product processing sites; textile mills; feedlots; cement, fertilizer, soap, glass, and rubber manufacturing facilities; metal and coal mining facilities; oil and gas extraction facilities; hazardous waste treatment, storage and disposal facilities; landfills; metal scrap yards; battery reclaimers; salvage yards; automobile junkyards; steam electric power generating facilities; transportation facilities; wastewater facilities; municipal separate storm sewer systems; and construction sites (including clearing, grading, excavation) that disturb one acre or larger tracts of land.

Units of state and local government that operate a facility, subject to these rules, that want to discharge storm water and certain non-storm water into the water quality areas covered under this rulemaking will be required to pay application and annual fees. These will be new fees for the affected facilities. According to the EPA and based on the 1990 census, there are approximately 189 industrial sites and 822 construction sites that have obtained permits under the federal storm water discharge program that are located within Blanco, Llano and Travis Counties. There is also one municipal separate storm sewer system (Austin) within the aforementioned counties. Not all of these federally permitted industrial and construction sites are located within the covered water quality areas. Therefore, the total number of sites located within the specific water quality areas covered by this rulemaking should be less than the total number of facilities cited. Any new storm water and certain non-storm water discharge permits issued by the commission will be at least as stringent as those permits administered by the EPA. Currently, the cost to comply for units of state and local government only includes the payment of application and annual fees. The commission anticipates that all facilities, except for municipal separate storm sewer systems, seeking permits as a result of this rulemaking will be required to pay an approximate $100 application fee. The operator of a municipal separate storm sewer system will be required to pay an approximate $2,000 application fee. Additionally, all facilities seeking permits authorized by this rulemaking, except for construction sites, will be required to pay an approximate $100-$600 annual fee. Construction sites will not be required to pay an annual fee for the duration of the permit.

PUBLIC BENEFIT AND COSTS

Mr. Davis also has determined that for each year of the first five years the proposed new sections are in effect, the public benefit anticipated from enforcement of and compliance with the proposed new sections will be standardization and clarification of storm water permit requirements within the water quality areas covered by this rulemaking and the continued granting of storm water and certain non-storm water discharge permits currently authorized by the EPA.

The proposed new sections would provide the authority for the commission to issue TPDES storm water and certain non-storm water discharge permits, covering industrial facilities, municipal separate storm sewer systems, and construction sites located within the Lakes Travis, Austin, Inks, Buchanan, Lyndon B. Johnson, and Marble Falls Water Quality Areas (located in Travis, Burnet, and Llano Counties). The EPA currently grants permits covering storm water and certain non-storm water discharges into the areas covered by the proposed new sections. State law currently allows the issuance of permits for storm water and certain non-storm water discharge statewide; however, current commission rules prohibit storm water and certain non-storm water discharges in the areas covered by the proposed new sections.

There will be fiscal implications which are not anticipated to be significant to persons and businesses as a result of administration and enforcement of the proposed new sections. Owners and operators of facilities, subject to these rules, that want to discharge storm water and certain non-storm water into the covered water quality areas of this rulemaking will be required to pay application and annual fees. These will be new fees for the affected facilities. According to the EPA there are approximately 189 industrial sites and 822 construction sites that have obtained permits under the federal storm water discharge program that are located within Blanco, Llano and Travis Counties. Not all of these federally permitted industrial and construction sites are located within the covered water quality areas. Therefore, the total number of sites located within the specific water quality areas covered by this rulemaking should be less than the total number of facilities cited. Any new storm water and certain non-storm water discharge permits issued by the commission will be at least as stringent as those permits administered by the EPA. Currently, the cost to comply for persons and businesses only includes the payment of application and annual fees. The commission anticipates that all facilities seeking permits as a result of this rulemaking will be required to pay an approximate $100 application fee. Additionally, all facilities seeking permits under this rulemaking, except for construction sites, will be required to pay an approximate $100-$600 annual fee. Construction sites will not be required to pay an annual fee for the duration of the permit.

SMALL BUSINESS AND MICRO-BUSINESS ASSESSMENT

There will be fiscal implications which are not anticipated to be adverse to any affected small business and micro-business as a result of implementing the proposed new sections.

Small and micro-businesses that own and operate facilities, subject to these rules, that want to discharge storm water and certain non-storm water into the water quality areas covered under this rulemaking, will be required to pay application and annual fees. These will be new fees for the affected facilities. According to the EPA there are approximately 189 industrial sites and 822 construction sites that have obtained permits under the federal storm water discharge program that are located within Blanco, Llano and Travis Counties. Not all of these federally permitted industrial and construction sites are located within the covered water quality areas. Therefore, the total number of sites located within the specific water quality areas covered by this rulemaking, some of which are small and micro-businesses, should be less than the total number of facilities cited. Any new storm water and certain non-storm water discharge permits issued by the commission will be at least as stringent as those permits administered by the EPA. Currently, the cost to comply for small and micro-businesses only includes the payment of application and annual fees. The commission anticipates that all facilities seeking permits under this rulemaking will be required to pay an approximate $100 application fee. Additionally, all facilities seeking permits under this rulemaking, except for construction sites, will be required to pay an approximate $100-$600 annual fee. Construction sites will not be required to pay an annual fee for the duration of the permit.

DRAFT REGULATORY IMPACT ANALYSIS DETERMINATION

The commission has reviewed the proposed rulemaking in light of the regulatory analysis requirements of Texas Government Code, §2001.0225, and has determined that the rulemaking is not subject to §2001.0225 because it does not meet the definition of a "major environmental rule" as defined in the Government Code.

The specific intent of the proposed new sections is to protect the environment by authorizing, and thus controlling, storm water and certain non-storm water discharges into the Lakes Travis, Austin, Inks, Buchanan, Lyndon B. Johnson, and Marble Falls Water Quality Areas. The proposed new sections, however, will not adversely affect the economy, a sector of the economy, productivity, competition, jobs, the environment, or the public health and safety of the state or a sector of the state; therefore, the new sections do not constitute a major environmental rule.

The proposed rules will not adversely affect the economy, or a sector of the economy. In actuality, the rules will result in an overall economic savings because, without these proposed new sections, all covered discharges would have to be collected and disposed of in some other manner. Any alternative discharge method would be very expensive, and would thus result in an adverse economic impact.

The proposed new sections will not adversely affect productivity, because the proposed changes will authorize the discharge of storm water directly into the lakes in the affected water quality areas. If the rules are not amended, however, there will be an adverse affect on productivity, competition, and jobs, because the affected industries would be required to contain and dispose of storm water in some other manner than discharging to water in the state.

The proposed new sections will not aversely affect jobs, because the affected industries will be able to discharge storm water in a way that is both economically practical and environmentally safe. If the rules are not amended there could be a negative impact on jobs, because the impacted industries would be required to spend resources on collecting and disposing of storm water. If the affected industries are required to collect and treat storm water, there will necessarily be less money to spend on other areas of the business; thus, jobs could be affected.

Additionally, the proposed new sections will not adversely affect competition; in fact, if the rule is not amended, there will be a significant adverse impact on competition. Industries that do not discharge into the affected water quality areas will have a definite competitive advantage over those that do discharge into the water quality areas. Because industries that do not discharge into one of the affected water quality areas will not be required to collect storm water, but the same industries that do discharge into affected water quality areas will be required to collect the storm water; those industries that do not discharge into the affected water quality areas will have a definite competitive advantage.

Furthermore, the proposed rules will not adversely affect the environment for two reasons. First, discharges authorized under the rules will not add significant concentrations of pollutants to the lakes because the quality of storm water and the certain other non-storm water discharges will be maintained through the TPDES permit. Second, storm water is currently being discharged into the affected lakes, under the terms existing authorization from the EPA. Under federal law, Texas permits must be at least as stringent as the expiring NPDES permit; thus, these proposed new sections will not degrade the affected water bodies.

The public health and safety of the state will not be adversely affected by the proposed new sections because the proposed new sections only give the agency the authority to authorize storm water discharges. The proposed new sections do not authorize any specific discharge; thus, the new sections will not have an impact on public health and safety.

TAKINGS IMPACT ASSESSMENT

The commission's preliminary assessment is that Texas Government Code, Chapter 2007 does not apply to these proposed rules because the proposed new sections are not a taking as defined in Chapter 2007, nor are they a constitutional taking of private real property. The specific purpose of the proposed new sections is to authorize the discharge of storm water and certain types of non-storm water into the water quality areas of Lakes Travis, Austin, Inks, Buchanan, Lyndon B. Johnson, and Marble Falls.

Promulgation and enforcement of these proposed rules will not affect private real property which is the subject of the rules because the proposed new sections will neither restrict or limit the owner's right to the property, nor cause a reduction of 25% or more in the market value of the property. First, the new sections will enable the commission to authorize discharges of storm water, and certain other kinds of non-storm water, which would otherwise not be authorized. Thus, property owner's use of their property will not be restricted.

Secondly, property values will not be decreased because the new sections will not limit the use of the property. Conversely, if the rules are not amended, property values will be decreased because industries that would discharge into the affected water quality areas would be forced to collect and dispose of storm water, and the other authorized non-storm water discharges. The collection and treatment cost would render the property less valuable, thus reducing the property value. Thus, these rules will not constitute a takings under Texas Government Code, Chapter 2007.

CONSISTENCY WITH THE COASTAL MANAGEMENT PROGRAM

The commission has reviewed the proposed rulemaking and found that the rules are neither identified in the Coastal Coordination Act Implementation Rules, 31 TAC §505.11(b)(2), relating to Actions and Rules Subject to the Coastal Management Program, nor will they affect any action or authorization identified in the Coastal Coordination Act Implementation Rules, 31 TAC §505.11(a)(6). Therefore, the proposed rules are not subject to the Texas Coastal Management Program.

ANNOUNCEMENT OF HEARING

A public hearing on this proposal will be held in Austin on September 11, 2000 at 2:00 p.m. at the TNRCC Complex in Building F, Room 2210, located at 12015 Park 35 Circle. The hearing will be structured for the receipt of oral or written comments by interested persons. Individuals may present oral statements when called upon in order of registration. There will be no open discussion during the hearing; however, an agency staff member will be available to discuss the proposal 30 minutes prior to the hearing and will answer questions before and after the hearing.

Persons with disabilities who have special communication or other accommodation needs who are planning to attend the hearing should contact the Office of Environmental Policy, Analysis, and Assessment at (512) 239-4900. Requests should be made as far in advance as possible.

SUBMITTAL OF COMMENTS

Comments may be submitted to Joyce Spencer, Office of Environmental Policy, Analysis, and Assessment, MC 205, Texas Natural Resource Conservation Commission, P.O. Box 13087, Austin, Texas, 78711-3087, or faxed to (512) 239-4808. All comments must reference Rule Log Number 2000-010-311-WT. Comments must be received by 5:00 p.m., September 25, 2000. For further information, please contact Mary Ambrose, Policy and Regulations Division, at (512) 239-4813.

Subchapter A. LAKES TRAVIS AND AUSTIN WATER QUALITY

30 TAC §311.6

STATUTORY AUTHORITY

The new section is proposed under Texas Water Code, §5.103 and §26.011, which provide the commission with the authority to adopt any rules necessary to carry out its powers and duties under the Texas Water Code or other laws of this state. Section 26.011 gives the commission the duty to administer the provisions of Texas Water Code, Chapter 26, to establish the level of quality to be maintained in water in the state, and to control the quality of water in the state.

No other codes or statutes will be affected by this proposal.

§311.6.Allowable Storm Water Runoff and Certain Non-Storm Water Discharges.

(a)

The following discharges of storm water runoff may be authorized by a Texas pollutant discharge elimination system (TPDES) permit:

(1)

storm water runoff from industrial facilities;

(2)

storm water runoff from municipal separate storm sewer systems; and

(3)

storm water runoff from construction activities.

(b)

The following non-storm water discharges may be authorized by a TPDES permit:

(1)

discharges from fire fighting activities;

(2)

discharges from fire hydrant flushings;

(3)

discharges from potable water sources, including drinking fountain water and water line flushings;

(4)

discharges from uncontaminated air conditioning or compressor condensate;

(5)

discharges from lawn watering and similar irrigation drainage;

(6)

discharges from pavement washdown without the use of detergents or other chemicals and where spills or leaks of toxic or hazardous materials have not occurred (unless all spilled material has been removed);

(7)

discharges from routine external building wash down that does not use detergents or other compounds;

(8)

discharges from uncontaminated groundwater or spring water;

(9)

discharges from foundation or footing drains where flows are not contaminated with process materials such as solvents;

(10)

discharges from the spray down of lumber and wood product storage yards where no chemical additives are used in the spray down waters and no chemicals are applied to the wood during storage; and

(11)

discharges of storm water and groundwater seepage from mine dewatering activities at construction sand and gravel, industrial sand, or crushed stone mining facilities.

This agency hereby certifies that the proposal has been reviewed by legal counsel and found to be within the agency's legal authority to adopt.

Filed with the Office of the Secretary of State, on August 10, 2000.

TRD-200005568

Margaret Hoffman

Director, Environmental Law Division

Texas Natural Resource Conservation Commission

Earliest possible date of adoption: September 24, 2000

For further information, please call: (512) 239-5017


Subchapter B. LAKES INKS AND BUCHANAN WATER QUALITY

30 TAC §311.16

STATUTORY AUTHORITY

The new section is proposed under Texas Water Code, §5.103 and §26.011, which provide the commission with the authority to adopt any rules necessary to carry out its powers and duties the Texas Water Code or other laws of this state. Section 26.011 gives the commission the duty to administer the provisions of Texas Water Code, Chapter 26, to establish the level of quality to be maintained in water in the state, and to control the quality of water in the state.

No other codes or statutes will be affected by this proposal.

§311.16.Allowable Storm Water Runoff and Certain Non-Storm Water Discharges.

(a)

The following discharges of storm water runoff may be authorized by a Texas pollutant discharge elimination system (TPDES) permit:

(1)

storm water runoff from industrial facilities;

(2)

storm water runoff from municipal separate storm sewer systems; and

(3)

storm water runoff from construction activities.

(b)

The following non-storm water discharges may be authorized by a TPDES permit:

(1)

discharges from fire fighting activities;

(2)

discharges from fire hydrant flushings;

(3)

discharges from potable water sources, including drinking fountain water and water line flushings;

(4)

discharges from uncontaminated air conditioning or compressor condensate;

(5)

discharges from lawn watering and similar irrigation drainage;

(6)

discharges from pavement washdown without the use of detergents or other chemicals and where spills or leaks of toxic or hazardous materials have not occurred (unless all spilled material has been removed);

(7)

discharges from routine external building wash down that does not use detergents or other compounds;

(8)

discharges from uncontaminated groundwater or spring water;

(9)

discharges from foundation or footing drains where flows are not contaminated with process materials such as solvents;

(10)

discharges from the spray down of lumber and wood product storage yards where no chemical additives are used in the spray down waters and no chemicals are applied to the wood during storage; and

(11)

discharges of storm water and groundwater seepage from mine dewatering activities at construction sand and gravel, industrial sand, or crushed stone mining facilities.

This agency hereby certifies that the proposal has been reviewed by legal counsel and found to be within the agency's legal authority to adopt.

Filed with the Office of the Secretary of State, on August 10, 2000.

TRD-200005567

Margaret Hoffman

Director, Environmental Law Division

Texas Natural Resource Conservation Commission

Earliest possible date of adoption: September 24, 2000

For further information, please call: (512) 239-5017


Subchapter F. LAKES LYNDON B. JOHNSON AND MARBLE FALLS WATER QUALITY

30 TAC §311.56

STATUTORY AUTHORITY

The new section is proposed under Texas Water Code, §5.103 and §26.011, which provides the commission with the authority to adopt any rules necessary to carry out its powers and duties under the Texas Water Code or other laws of this state. Section 26.011 gives the commission the duty to administer the provisions of Texas Water Code, Chapter 26, to establish the level of quality to be maintained in water in the state, and to control the quality of water in the state.

No other codes or statutes will be affected by this proposal.

§311.56.Allowable Storm Water Runoff and Certain Non-Storm Water Discharges.

(a)

The following discharges of storm water runoff into or adjacent to water in the state may be authorized by a Texas pollutant discharge elimination system (TPDES) permit:

(1)

storm water runoff from industrial facilities;

(2)

storm water runoff from municipal separate storm sewer systems; and

(3)

storm water runoff from construction activities.

(b)

The following non-storm water discharges into or adjacent to water in the state may be authorized by a TPDES permit:

(1)

discharges from fire fighting activities;

(2)

discharges from fire hydrant flushings;

(3)

discharges from potable water sources, including drinking fountain water and water line flushings;

(4)

discharges from uncontaminated air conditioning or compressor condensate;

(5)

discharges from lawn watering and similar irrigation drainage;

(6)

discharges from pavement washdown without the use of detergents or other chemicals and where spills or leaks of toxic or hazardous materials have not occurred (unless all spilled material has been removed);

(7)

discharges from routine external building wash down that does not use detergents or other compounds;

(8)

discharges from uncontaminated groundwater or spring water;

(9)

discharges from foundation or footing drains where flows are not contaminated with process materials such as solvents;

(10)

discharges from the spray down of lumber and wood product storage yards where no chemical additives are used in the spray down waters and no chemicals are applied to the wood during storage; and

(11)

discharges of storm water and groundwater seepage from mine dewatering activities at construction sand and gravel, industrial sand, or crushed stone mining facilities.

This agency hereby certifies that the proposal has been reviewed by legal counsel and found to be within the agency's legal authority to adopt.

Filed with the Office of the Secretary of State, on August 10, 2000.

TRD-200005566

Margaret Hoffman

Director, Environmental Law Division

Texas Natural Resource Conservation Commission

Earliest possible date of adoption: September 24, 2000

For further information, please call: (512) 239-5017