Clean Air Act

July 1996 - TI#7988B
Introduction
Approaches For Clean Air
Regulatory Procedures
Federal Agency Responsibility Under the CAA
Air Force Guidance
Impact on Air Force Operations
Success Story: Edwards AFB
Success Story: Kelly AFB
Success Story: Andrews AFB
Acronyms
References


Introduction
We all must breathe to live and air pollution is one of the biggest environmental challenges we face as a Nation and as a species. The rapid industrial expansion the world has experienced in the last 100 years is globally affecting the air we breathe. In the United States, air pollution was first recognized in legislation with passage of the original Clean Air Act (CAA) of 1955. The CAA has been amended numerous times, the most recent being in 1990. The CAA amendments of 1990 are one of the largest, most complex and expensive pieces of environmental legislation ever passed. The 1990 amendments will have a profound impact on our daily lives from the products we buy to how we get to work. The Department of Defense (DoD) will also be significantly impacted in the way it does business.

Almost everything we do affects the air we breathe. We paint and solvents evaporate. We use air conditioners and freons (ozone depleting substances) are released. We drive our cars and combustion by-products (smog) are released into the environment. Power plants supplying our electricity and manufacturing plants making the products we enjoy release millions of tons of pollutants into the air each year.


Approaches For Clean Air
Geographical or Regional Approach to Air Pollution
One of the goals of the Clean Air Act (CAA) is to guarantee the concentration of certain pollutants in the air is at levels below which no adverse effects will be experienced by humans or the environment. To this end, the Environmental Protection Agency (EPA) promulgated six National Ambient Air Quality Standards (NAAQS) in 1970. The regulated pollutants (called criteria pollutants because the standards were developed from criteria documents) are carbon monoxide, lead, nitrogen dioxide, ozone, particulate matter and sulfur dioxide. The early legislation divided the country into Air Quality Regions (AQRs) and provided mechanisms for limiting the emission of these pollutants and bringing AQRs into compliance. Within these AQRs, there can be areas of attainment and nonattainment.

Attainment Areas - Any area in which one or more of the six NAAQS are being met is an attainment area for those standards and only those standards. For example, an area might be an attainment area for carbon monoxide and lead but nonattainment for the other NAAQS. Even though a NAAQS is being met, the EPA does not consider the NAAQS a ceiling to which the pollutant level can climb. In fact, the CAA contains provisions to prevent significant deterioration of the air quality in an attainment area. The CA A recognizes the effect on growth of an excessively stringent limit and allows for an incremental increase of a NAAQS pollutant in a given attainment area. Currently, there are increments for three pollutants: particulate matter, sulfur dioxide and nitrogen dioxide. Conversely, to ensure unlimited growth is not allowed to degrade the air quality in attainment areas and the allowable increments are not exceeded, attainment areas are subject to the EPA Prevention of Significant Deterioration (PSD) regulati ons. These regulations apply to new major stationary sources and major modifications to such sources. A major PSD source is defined as:
  • a stationary source belonging to a defined group with the potential to emit 100 tons per year (tpy), or more, of any pollutant subject to regulation under the CAA; or
  • any stationary source with the potential to emit 250 tpy, or more, of any pollutant subject to regulation under the CAA; or
  • any physical change occurring at a stationary source that would constitute a major stationary source by itself. For example, modifying a source so that its emissions exceed 250 tpy of a regulated pollutant.

Any source subject to the PSD regulations must obtain a preconstruction permit. Prior to obtaining the permit, the source must undergo a New Source Review (NSR). The NSR will evaluate the affect the emissions from the source will have on the levels of criteria pollutants.

As part of the NSR, a source must demonstrate to the regulators it is using Best Available Control Technology (BACT) to control all criteria pollutants it emits. BACT is an emission limitation based on the maximum degree of reduction a permitting authority believes is achievable for the new source or major modification to existing source taking into consideration energy, environmental and economic impacts and other costs. The BACT is determined on a case-by-case basis.

The source must also undergo an air quality analysis for criteria pollutants to ensure it's emissions after installing a BACT will not cause an allowable increment to be exceeded. If it does, the permit will not be issued, and the source will either have to be modified or planned for another area where it will not cause the increment to be exceeded.

Nonattainment Areas - Nonattainment areas are areas where one or more NAAQS are not met. In spite of the efforts to reduce the level of criteria pollutants, by 1990 there were still many Air Quality Regions where one or more NAAQS had not been met. These areas, called attainment areas, are addressed by the CAA amendments of 1990. These amendments contain provisions to bring all areas of the country into attainment for three of the criteria pollutants, ozone, carbon monoxide and particulate matter in a specified number of years.

Nonattainment areas are classified based on the extent to which they fail to meet the standard: the worse the classification, the more stringent the controls. The classifications are:

ozone (ppm=parts per million)
marginal (0.121 up to 0.138 ppm)
moderate (0.138 up to 0.160 ppm)
serious (0.160 up to 0.180 ppm)
severe (0.180 up to 0.280 ppm)
extreme (0.280 ppm and above)

carbon monoxide
moderate (9.1 - 16.4 ppm)
serious (16.5 ppm and above)

particulate matter
moderate (Initial classification for all nonattain-ment areas)
serious (Areas that cannot attain standard by attainment date)

Major new stationary sources and major modifications to existing sources in nonattainment areas must also obtain a preconstruction permit and undergo a NSR. However, a major source for a nonattainment area differs from that for PSD regulations and is defined as follows:

A major stationary source in an ozone nonattainment has the potential to emit the following quantities of volatile organic compounds (VOC) or oxides of nitrogen (NO, NO2):

  1. 100 tpy or more in marginal or moderate nonattainment areas.
  2. 50 tpy or more in serious nonattainment areas.
  3. 25 tpy or more in severe nonattainment areas.
  4. 10 tpy or more in extreme nonattainment areas.
  5. 50 tpy of more in ozone transport regions* (VOCs only).
A major stationary source in a carbon monoxide (CO) nonattainment area, classified as serious, has the potential to emit 50 tpy or more of CO. The area must be one in which stationary sources contribute significantly to CO levels.

A major source in a particulate matter (PM-10**) nonattainment area, classified as serious, has the potential to emit 70 tpy or more of PM-10.

As part of the NSR, a major new source must demonstrate to the regulators it has achieved the lowest achievable emission rate (LAER). The LAER is the most stringent emission limitation within any state implementation plan or the most stringent level of pollution control achievable in the related industry group. Economics is not a factor in implementing LAER An area which is classified as nonattainment for one pollutant can be an attainment area for the others. Therefore, the NSR for a nonattainment area also includes an air quality analysis for other criteria pollutants to ensure allowable increments are not exceeded. The CAA amendments of 1990 require states with ozone nonattainment areas classified as moderate or worse, impose emission controls on existing sources of VOCs and nitrogen oxides (NOx). These limitations include reasonably available control technology (RACT). The EPA has not clearly defined RACT. However, the Agency has specified it will issue control technique guidelines (CTGs) for various types of pollutant sources which will qualify as RACT. The States can also determine RACT on a case-by-case basis.

Applicants for new major sources in ozone nonattainment areas must also demonstrate they produce a "net air quality benefit." Thus, if a new major source releases any emissions, it must offset them at another source by an amount greater than the amount being released.

In severe and extreme ozone nonattainment areas and serious carbon monoxide nonattainment areas, the EPA requires development of an Employee Commute Options (ECO) program. This program is designed to reduce solo-driving and promote alternative transportation modes to reduce air pollution. It is aimed at large employers (100 or more employees at a single work site). Employers can select appropriate strategies to reduce commuting trips and increase vehicle occupancy. Currently, the following nine areas in the country require an ECO program:

  • Baltimore, MD;
  • Houston/Galveston/Brazoria,TX
  • Milwaukee WI
  • Philadelphia, PA/Wilmington, DE/Trenton, NJ
  • Ventura County, CA
  • Chicago, IL
  • Los Angeles, CA
  • NY/NJ/CT metro area
  • The Mohave Desert, CA.

Hazardous Air Pollutants Approach
The second approach is to identify pollutants which are a significant public health threat and are not regulated under NAAQS. In 1970 the CAA authorized the EPA to establish special emission standards for new and existing sources of these pollutants. Called National Emission Standards for Hazardous Air Pollutants (NESHAPS), the EPA, since 1970, issued standards for only seven substances: arsenic, asbestos, benzene, beryllium, mercury, radionuclides, and vinyl chloride.

The CAA amendments of 1990 significantly increased the number of pollutants considered to be a serious public health threat. In fact, the amendments require emission control for existing and new sources of 189 listed pollutants and categories with a new designation of hazardous air pollutants (HAPs). The EPA must develop technology-based emission standards for HAPs based on Maximum Achievable Control Technology (MACT). The standards, which are source-specific and are based on the best demonstrated contr ol technologies and practices are called National Emission Standards for Hazardous Air Pollutants for Source Categories (NESHAPSC).

MACT emission standards are slightly different for new and existing sources, but basically strive to achieve the lowest emission possible for a specific source category or subcategory. They take into consideration the cost of achieving such emission reduction, and health and environmental effects resulting from impacts on media other than air.

The HAP emission standards will apply only to major sources. For HAPs, a major source is defined as any stationary source or group of stationary sources located within a contiguous area that emits 10 tpy or more of a single HAP or 25 tpy or more of any combination of HAPs. However, the EPA administrator can establish a lesser quantity, or, for radionuclides, different criteria.

Air Pollutants Creating Significant Environmental Impacts
The third approach in the CAA is to address those air pollutants causing regional or global environmental damage such as acid air pollutants and stratospheric ozone depleting air pollutants.

Acid Air Pollutants - Acid rain which is part of a larger category of air pollutants known as acid pollutants has received a great deal of publicity in the northeast. A majority of the acid pollutants (acid rain, acid snow, acid fog, acid gas and acid dust) found in the northeast portion of the United States result from the release of sulfur dioxide (SOx) and NOx into the atmosphere by large coal burning power plants primarily in the midwest. In moist air, these compounds can eventually form sulfuric acid and nitric acid. When transported eastward, they eventually return to earth in the form of rain, snow, mist or solid particles possibly acidifying lakes and streams, damaging plant life and property, and causing health problems, especially among children and those with asthma.

To control sulfur dioxide emissions from the midwest power plants, the EPA has set up a market-based system of emission allowances. Every existing power plant covered by the Acid Air Pollutants program is issued a certain number of SO2 allowances, each worth one ton of sulfur dioxide. The system is market-based because the allowances can be bought and sold. However, new units coming on line after 12 December 1995 will not be given new allowances. They must obtain them from existing sources.

The NOx emission reduction program is not allowance-based. The EPA will control NOx emissions by establishing emission limits for existing units and new source performance standards (NSPSs) for new units.

Stratospheric Ozone Depletion - The other major air pollutants causing environmental concern are the chemicals possibly causing the hole in the stratospheric ozone layer. The ozone layer depletion is thought to be due mainly to man-made chemicals released into the atmosphere. These chemicals are divided into two classes depending on their ozone-depleting potential. Class I ozone depleting substances (ODSs) have a high potential, while the ODS depletion potential for class II substances is lower.

The EPA has banned the production of all but one of the class I substances effective 1 January 1996. The banned substances include all chlorofluorocarbons (CFCs), halons, carbon tetrachloride, methyl chloroform, and hydrobromofluorocarbons (HBFCs). The only class I substance that will continue to be produced is methyl bromide. It will be banned effective 1 January 2001.

Class II substances consist of hydrochlorofluoro-carbons (HCFCs). Currently they are used as substitutes for class I substances. However, they too have a phase-out schedule. HCFC-141b will be banned in 2003, HCFC-142b and HCFC-22 in 2020 and all other HCFCs in 2030.

The EPA has also established certification requirements for technicians who service, maintain, repair, and dispose of refrigeration and air conditioning systems containing CFCs and HCFCs. For all equipment, except motor vehicle air conditioners (MVACs), the technicians must pass a certification examination, but are not required to take a training course. Technicians working on MVACS must take both a training course and pass an examination.

Another program developed in accordance with the CAA to combat ozone depletion is the Significant New Alternatives Policy (SNAP) program established by the EPA. The EPA intends to publish quarterly updates to the SNAP list as new substitutes are developed and approved. The objectives of SNAP are:

  • To identify substitutes for ozone-depleting substances;
  • To evaluate the acceptability of these substitutes;
  • To promote the use of those substitutes believed to present lower overall risks to human health and the environment, relative to the class I and class II substances being replaced, as well as to other substitutes for the same end use; and
  • To prohibit the use of those substitutes found to increase overall risk.

The EPA has published a list, which it will update quarterly, of substitutes and potential substitutes evaluated under the SNAP program. Contact PRO-ACT for a copy of the SNAP list.

Motor Vehicle Air Pollution
Probably, the most serious air pollution is created from our constant use of motor vehicles. The 1970 amendments to the CAA established motor vehicle emission standards for criteria pollutants and hazardous pollutants. As a result, cars today produce 60 to 80 percent less pollution than cars in the 1960's, and the level of lead in the air has dropped dramatically. Still, motor vehicles:

  • Produce up to 50% of VOCs and NOx emitted into ambient air.
  • Produce more than 50% of the hazardous air pollutants generated.
  • Release up to 90% of the CO found in urban air.

Why? What went wrong?

  • More people are driving more cars, more miles, on more trips.
  • Commuting distances have increased and most people still drive to work alone.
  • Buses and trucks have not had to reduce emissions as much as cars.
  • To compensate for the removal of lead, refiners increased the amount of VOCs in the formulation, increasing the quantities of VOCs released to the atmosphere.

To deal with these problems, the CAA amendments of 1990 implemented a series of programs to provide cleaner fuels. Refiners must reformulate gasoline sold in the smoggiest areas so it contains less VOCs. Additionally, in areas where wintertime CO is a problem, refiners will have to sell gasoline with oxygen added (oxyfuel) to make the fuel burn more efficiently and reduce CO emissions. Finally, all gasolines must contain detergents to prevent build-up of engine deposits. This will keep engines working s moothly and burning fuel cleanly.

The CAA also encourages the development and sale of alternative clean fuels such as alcohols, compressed natural gas, liquified natural gas, and liquified petroleum gas. The amendments require the installation of vapor recovery nozzles in ozone nonattainment areas categorized as moderate or worse.

In addition to cleaning up fuels, the CAA requires the development of cleaner cars, trucks and buses. Pollution control devices must now work for 100,000 miles. Auto makers must build cars that use clean fuels and have reduced tailpipe emissions. They must also build electric cars. By 1996, all new cars will have to meet the emission limits specified in the CAA amendments of 1990. These cars will first be sold in southern California. Also, fleet operators (10 or more heavy-duty vehicles or light-duty p assenger cars or trucks) in 22 designated cities with smog problems will have to purchase the new cleaner cars. Finally, beginning in 1994, new large diesel trucks and new buses have been built to reduce particle emissions by at least 90 percent.

To ensure the use of clean gas and clean cars is effective, the CAA also requires the establishment of vehicle inspection and maintenance (I/M) programs in 40 metropolitan areas. This is in addition to the over 70 I/M programs already in place. These programs are expected to have a big payoff in reducing air pollution from cars.

Specific Source Emissions
Another approach to clean up is addressing site specific sources of air pollution. Therefore, in addition to establishing NAAQS, the EPA has also established uniform emission standards for over 60 specific source categories of new, modified, or reconstructed stationary sources such as fossil-fuel steam generators, incinerators, and petroleum dry cleaners. These standards, called New Source Performance Standards (NSPS) are nationwide and not dependent on location. Since the pollutants emitted by a majori ty of these sources are the same as those regulated by NAAQS and are not hazardous air pollutants which require MACT, the sources must install BACT during construction.

*A region where interstate transport of air pollutants from one or more states contributes significantly to a violation of a NAAQS in one or more other states.
**PM-10 - particulate matter less than 10 microns.


Regulatory Procedures
State Implementation Plans
Although the Clean Air Act is a Federal law applicable nationwide, the primary responsibility for implementing and enforcing its provisions rests with the states.

Under the law, the EPA establishes the minimum requirements for achieving acceptable air quality. This ensures all individuals will have the same basic health and environmental protection. The actual implementation of the program, however, lies with the states.

To implement the CAA, each state must develop a state implementation plan (SIP). The SIP is a collection of the regulations a state will use to clean up polluted areas. The implementation of the CAA was given to the states because controlling air pollution problems often requires knowledge of local industries, geography, housing patterns, etc.

Since each SIP is tailored for a particular state, they will differ from state to state, and in some states, from region to region. In many cases, the regulations developed by the state will be more stringent than the corresponding Federal ones. A well-known example is California. The State is divided into Air Quality Management Districts, each with it own set of regulations. For example, the South Coast Air Quality Management District (SCAQMD), which includes Los Angeles, has some of the strictest air pollution regulations in the nation, far exceeding Federal standards.

Under no circumstances, however, can SIPs have weaker pollution controls than those established by the EPA. Also, each plan must be approved by the EPA. If a SIP is not acceptable, the EPA can take over enforcing the Clean Air Act in that state.

Operating Permits
To ensure compliance with the provisions of the SIP, the CAA contains provisions for a comprehensive nationwide air emissions operating permit program for new, modified and existing major stationary sources. The permits are designed to enhance the ability of the EPA, State and local regulatory agencies and private citizens to monitor and enforce CAA requirements. The permits will identify the pollutants emitted by a source, specify enforceable emission limits and standards, contain compliance schedules, emission monitoring requirements and reporting requirements, as well as any other conditions necessary to assure compliance.

The permits will be administered by the states or air quality management districts (AQMDs) and will reflect the particular provisions of the SIP. The states will charge each source an annual emission fee to cover the costs of administering the program. The recommended minimum is $25.00 per ton for each pollutant emitted.


Federal Agency Responsibility Under the CAA
Federal facilities are not exempt from the provisions of the CAA. The following sections of the Act apply specifically to Federal agencies:
  • Section 118 waives Federal immunity from complying with the CAA. It states all Federal agencies will comply with all Federal, State, interstate, and local requirements in the same manner and to the same extent as any nongovernmental entity.
  • Section 176 prohibits any Federal department, agency, or instrumentality of the Federal Government from engaging in any activity which does not conform to an implementation plan after it has been approved or promulgated.
The President has also issued several Executive Orders (EOs) which stem from the CAA and impact Federal facilities:
  • EO 12759 "Federal Energy Management" prescribes energy efficiency goals which all Federal agencies must meet. These goals include minimization of petroleum use in Federal facilities; vehicle fuel efficiency outreach programs; and Federal vehicle fuel efficiency. Note: Only sections 3, 9, 10 of the EO remain in effect. The other sections of this EO were revoked by EO 12902 (see below).
  • EO 12844 "Federal Use of Alternative Fueled Vehicles" requires Federal agencies to purchase 33,750 alternative fuel vehicles by 1995.
  • EO 12843 "Procurement Requirements and Policies for Federal Agencies for Ozone-Depleting Substances" requires Federal agencies to implement cost-effective programs to minimize the procurement of materials that deplete ozone, and to give preference to the procurement of alternate products.
  • EO 12902 "Energy Efficiency and Water Conservation at Federal Facilities" prescribes energy efficiency goals for all Federal Facilities and includes water conservation initiatives. Each agency must develop and implement a program to reduce energy consumption by 30 percent by the year 2005 relative to the agencies 1985 energy use.

Air Force Guidance
Air Force Instruction (AFI) 32-7040, "Air Quality Compliance," 9 May 1994, outlines Air Force responsibilities for complying with the CAA. This instruction requires Air Force activities to comply with all applicable Federal, State, and local standards for air quality compliance. The AFI does not duplicate these standards, but is designed to provide a framework on the way to do business to comply with them. It defines responsibilities for Air Force components and details the basic actions which must be done to comply with the CAA.

The Air Force has also issued the following policy letters which deal with ozone-depleting substances and reduction of air pollution:

  • "ACTION MEMORANDUM-Air Force Ban on Purchase of Ozone Depleting Chemicals (ODCs)," 7 January 1993.
  • "ACTION MEMORANDUM-Air Force Pollution Prevention Program," 7 January 1993.
  • "Interim Air Force Contracting Policy for Elimination of Class I Ozone Depleting Substances," 26 May 1993.
  • "Air Force Ozone Depleting Chemical (ODC) Interim Waiver Application, Approval Procedures, and Reporting Requirements," 14 July 1993.

Impact on Air Force Operations
The extent to which the CAA impacts the operation of an Air Force facility will depend on the location of the base. If the base is located in a nonattainment area, it will have to comply with strict regulations governing emissions from stationary sources, the use of alternative fuels and restrictions on the use of vehicles.

Bases located in areas affected by the Acid Rain provisions of the CAA may have higher utility costs due to the increased emission control requirements placed on utility plants in the region.

All bases, regardless of their location, will be required to obtain pre-construction and operating permits for new or modified major stationary sources.

One fact is certain. No Air Force facility is beyond the reach of the Clean Air Act.


Success Story: Edwards AFB
Edwards AFB has a new paint booth that is considered a "quantum leap" in best available control technology (BACT). The facility, which is capable of holding a Boeing 707, has a unique carbon adsorption/de-adsorption system; the first ever this large to destroy over 98% of VOCs and 99% of particulate emissions generated from the paint application area. The system is so effective the Kern County Air Pollution Control District has recommended it to the EPA as a model for facilities of this kind all over the United States.

Air from the facility flows through a two-stage poly filter, a 1-micron high-efficiency particulate filter, and an 18 bank carbon bed. The system removes 98% of all pollutants generated. The exhaust air is actually cleaner than the outside ambient air. Once the carbon bank is saturated, one bank at a time is transported to a de-sorption unit. The carbon is heated to 450 degrees F to remove VOCs and clean the carbon. It is estimated 93% of the carbon may be recovered.

The solvent-laden vapors pass through a thermal oxidizer which destroys the VOCs at temperatures ranging from 1200 to 1500 degrees F.

Because of this facility, Edwards AFB is receiving contract work from the Army, Navy, and NASA, as well as out-of-state facilities. Within five years, Edwards plans to become the primary regional painting facility. It expects to recover its building costs by attracting outside business. (Hazardous Technical Information Services Bulletin, Nov-Dec 95.)


Success Story: Kelly AFB
Kelly AFB has developed a multi-pronged approach to complying with the Clean Air Act. The base is an active member of the Air Quality Task Force in San Antonio. This group has actively pursued maintaining the area's attainment status for all six criteria pollutants. As part of this effort, the base distributed over 1,000 copies of its Ozone Action Day Plan brochure to increase base awareness and knowledge of the problem.

Kelly has reduced yearly VOC emissions from 1,135 tons to 250 tons over a four year period (1990-1994). Much of this reduction has resulted from switching to alternative cleaning processes and compliant vapor degreasers which will ultimately lead to complete phaseout of perchloroethylene.

To comply with the Chromium Electroplating NESHAPSC, the base is installing a state of the art chrome electroplating line. The new line will incorporate multiple control technologies including fume suppressants, mist eliminators, and moisture extractors.

The base also has the largest bead blasting facility in the world. Its use has nearly eliminated the need for chemical stripping processes to depaint aircraft. Kelly expects to meet the 50% reduction of hazardous air pollutants four years ahead of schedule.

For more information on these programs, contact Captain Michael Blank, DSN 945-3100, Ext. 213. Air Program Desk


Success Story: Andrews AFB
To make a significant contribution to reducing local air pollution levels, Andrews AFB has embarked on an ambitious program to reduce the use of gasoline and reduce the emission of VOCs from base vehicles. Using a National Renewable Energy Laboratory (NREL) contract, the base has already converted 40 fleet vehicles from gasoline to a bi-fuel compressed natural gas (CNG) system.

The base has recently obtained a $200K contract from the Advanced Research Project Agency (ARPA), through the Robins Alternative Fueled Vehicle Systems Program Office (AFVSPO) to assist in converting 27 diesel powered vehicles to dual fuel use. This will enable the vehicles to use 80% CNG and 20% diesel fuel. The contract for the conversion was awarded with an estimated completion date of May 1996. Finally, Andrews AFB is currently working with NREL and AFVSPO to convert an additional 76 vehicles to use CNG.

For more information on this program contact Mr. Allan Holtzman, DSN 858-2337.


Acronyms
AQMDAir Quality Management District NESHAP National Emission Standards for Hazardous Air Pollutants
AQRAir Quality RegionNOxNitrogen Oxides
BACT Best Available Control TechnologyNSPS New Source Performance Standards
CAAClean Air Act
NSRNew Source Review
CFCChlorofluorocarbonODCOzone Depleting Chemical
COCarbon MonoxideODSOzone Depleting Substance
CTGControl Techniques GuidelinePM-10Particulate matter less than 10 microns
DoDDepartment of DefenseppmParts per million
ECOEmployee Commute OptionsPSD Prevention of Significant Deterioration
EOExecutive OrderRACTReasonably Available Control Technology
EPAU.S. Environmental Protection AgencySO2Sulfur Dioxide
HAPHazardous Air PollutantSCAQMDSouth Coast Air Quality Management District
HBFCHydrobromofluorocarbonSIP State Implementation Plans
HCFCdHydrochlorofluorocarbonSNAP Significant New Alternative Policy
LAERLowest Achievable Emission Ratestpy Tons per year
MACT Maximum Available Control TechnologyVOC Volatile Organic Compound
MVACs Motor Vehicle Air ConditionersNAAQS National Ambient Air Quality Standards

References
  1. 40 CFR 50 "National Primary and Secondary Ambient Air Quality Standards."

  2. 40 CFR 51 "Requirements for Preparation, Adoption, and Submittal of Implementation Plans."

  3. 40 CFR 52 "Approval and Promulgation of Implementation Plans."

  4. 40 CFR 60 "Standards of Performance for New Stationary Sources."

  5. 40 CFR 61 "National Emission Standards for Hazardous Air Pollutants."

  6. 40 CFR 63 "National Emission Standards for Hazardous Air Pollutants for Source Categories."

  7. 40 CFR 70 "State Operating Permit Programs."

  8. 40 CFR 82 "Protection of Stratospheric Ozone."

  9. "Air Force Hazardous Technical Information Services Bulletin, November/December 1995.

  10. Air Force Instruction 32-7040, "Air Quality Compliance," 9 May 1994.

  11. "Air Quality Management," Army Environmental Manager's Handbook (draft), August 1994.

  12. "An Abstract of Title I of the Federal Clean Air Act, as amended in 1990: Attaining and Maintaining National Ambient Air Quality Standards (NAAQS)," National Defense Center for Environmental Excellence, July 1994.

  13. "Clean Air Act Amendments of 1990, Title III-Air Toxics," ENSR Consulting and Engineering, April 1991.

  14. "Clean Air Act Amendments of 1990, Detailed Summary of Titles," United States Environmental Protection Agency, November 30, 1990.

  15. "Employee Commute Options (ECO), Questions and Answers," June 15, 1995.

  16. "Energy Conservation," PRO-ACT Fact Sheet, October 1995.

  17. "Obtaining Information on RACT, BACT, and LAER Determinations_Seek and You Shall Find," The Air Pollution Consultant, November/December 1994.

  18. "Ozone Depleter Compliance Guide," Thompson Publishing Group, November 1995.

  19. Public Law 90-148, as Amended.

  20. "The Employee Commute Options (ECO) Program in Practice," May 9, 1995.

  21. "The Federal Clean Air Act, as Amended in 1990," National Defense Center for Environmental Excellence, July 1994.

  22. "The Plain English Guide To The Clean Air Act," United States Environmental Protection Agency, EPA 400-K-93-001, April 1993.

  23. "Title I of the Clean Air Act, as Amended in 1990 (CAA): Emission Source and Volatile Organic Compounds (VOCs) Offset Requirements in Ozone Nonattainment Areas," National Defense Center for Environmental Excellence, May 1995.