AIR QUALITY MANAGEMENT THROUGH POLLUTION PREVENTION

front cover

AIR QUALITY MANAGEMENT

USING

POLLUTION PREVENTION:

A JOINT SERVICE APPROACH

 

Distribution authorized to Federal Agencies only; Administrative/Operational Use; March 1998.

 

TABLE OF CONTENTS

DISCLAIMER

ACKNOWLEDGEMENTS

FORWARD

POLLUTION PREVENTION AND AIR QUALITY MANAGEMENT

PURPOSE
WHAT IS POLLUTION PREVENTION?

REGULATORY FRAMEWORK

EPCRA
CAA
RCRA
WHY INCORPORATE P2 INTO AIR PROGRAMS?

CROSS REFERENCES

PROCESSES

1. CLEANING AND DEGREASING

1.1 Methylene Chloride Degreasing
1.2 1,1,1-Trichloroethane Degreasing
1.3 CFC-113
1.4 Parts Washing: Stoddard Solvent
1.5 General Cleaning
1.6 Weapons Cleaning: Wipe Cleaning
1.7 Weapons Cleaning: Dip Tanks
1.8 Electronics Cleaning

2. DEPAINTING

2.1 Paint Stripping: Methylene Chloride
2.2 Research and Development

3. SURFACE COATING

3.1 Paint Gun Washers
3.2 Primers
3.3 CARC Painting
3.4 Touch-Up Painting
3.5 General Painting
3.6 Architectural Coatings
3.7 Cadmium Plating
3.8 Chromic Acid Anodizing
3.9 Chromate Conversion Coating
3.10 Hard Chrome Plating
3.11 Coating Technology

4. COMBUSTION

4.1 Medical Waste Incinerators
4.2 Classified Waste Incinerators
4.3 Municipal Waste Combustors
4.4 Treatment, Storage, Disposal Facility
4.5 Boilers
4.6 Vehicles
4.7 Aerospace Ground Equipment
4.8 Generators
4.9 Jet Engine Testing

5. STORAGE

5.1 Listed Substance Storage

6. TRAINING

6.1 Fire Fighting Training
6.2 Field Training Exercises
6.3 Weapons Training at Firing Ranges

7. MISCELLANEOUS

7.1 Ethylene Oxide Sterilizing
7.2 Fuel Dispensing
7.3 Pesticides
7.4 Lubricants
7.5 Adhesives and Sealants
7.6 Potential to Emit

APPENDICES

Appendix A: ACRONYMS

Appendix B: APPROVAL AUTHORITY

Specifications and Standards: Obtaining Approval for Change
Specifications and Standards: Integrating P2 into Acquisition
How to Recommend an Air Force Tech Order (TO) Change
How to Recommend a Military Specification (MILSPEC) Change

Appendix C: WEB SITES

Appendix D: REGULATORY INFORMATION

Clean Air Act And Toxic Release Inventory Reporting Requirements
Governing Department Of Defense and Service
Regulations for Pollution Prevention
Initiatives to Reauthorize The PPA

Appendix E: EPA PROGRAMS & RESOURCES

Significant New Alternatives Policy Program (SNAP)
Design for the Environment
EPA Publications

Appendix F: DoD P2 SERVICES

Joint Service Pollution Prevention Technical Library
The HAP Status Binder
The Air Force Environment, Safety, and Occupational Health (ESOH)
Air Force Environmental Helpline
Navy Pollution Prevention Equipment Program
Navy Fleet Assistance Support and Technology Transfer (FASTT)
Army Pollution Prevention Investment Fund (P2IF)
Army Environmental Helpline
Joint Group on Acquistion Pollution Prevention (JG-APP)

Appendix G: HOW TO INCORPORATE P2


DISCLAIMER

This information resource is not a DoD Policy document. This document primarily contains ideas and information about what others in the DoD are doing. All decisions to implement any of the opportunities described herein should be authorized through normal channels.

The mention of product names in this document does not constitute endorsement by the Services, DoD, or other Federal agency, but is for clarification purposes only.

ACKNOWLEDGEMENTS

The development of this document was sponsored by the U.S. Army Environmental Center. The Center supports implementation of the Army compliance program and encourages the use of pollution prevention techniques to minimize the impacts of regulatory requirements. More information about the Army Air Quality Compliance Program can be found by visiting the USAEC website at http://aec-www.apgea.army.mil or calling the Air Quality Media Manager at
(410) 671-1214/DSN 584.

The authors gratefully acknowledge the substantial contributions of the installations, as well as the National Aeronautics and Space Administration and the U.S. Coast Guard.

FORWARD

This Joint document was created through the efforts of the U.S. Army Center for Health Promotion and Preventive Medicine (USACHPPM), the U.S. Air Human Systems Center (HSC/OEBQ) and the Naval Facilities Engineering Service Center (NFESC). These three organizations have gathered information from installations within the Services, NASA, Coast Guard and from other resources to assemble within this document. This document highlights pollution prevention (P2) techniques that have either been successfully implemented at facilities or have potential to be implemented successfully. The current status of some relevant research efforts are included where appropriate. This document is not comprehensive. There was no data call, and many valuable ideas may have been missed. It is our intent to update this document as our readers bring new information to our attention. This document is a clearinghouse of potential solutions to Air Compliance Programs using P2, and will be posted on the Defense Environmental Network Information eXchange (DENIX) website.

Contact Information:

Army & others:
USACHPPM
Air Programs: (410) 671-3500/DSN 584
Linda Jekel
#CHPPM_Pgm42@chppm-ccmail.apgea.army.mil
Navy/Marine Corps:
NFESC
Compliance Branch: (805) 982-3567/DSN 551
Lisa Trembly
Ltrembl@nfesc.navy.mil
Air Force:
HSC/OEBQ
Human Systems Center: (210) 536-3305/DSN 240
Captain Kyle Blasch
Kyle.Blasch@guardian.brooks.af.mil

POLLUTION PREVENTION AND AIR QUALITY MANAGEMENT

PURPOSE

This document is for Air Quality Managers who would like to learn more about their options for using pollution prevention (P2) to manage air quality and achieve compliance. This is a forum for you to learn from each other about what works and what doesn't work. Success stories from throughout the Services are the core of this document. In addition, background information and summaries of current research are included for some processes. All of this information in the body of the document is organized according to the affected process, with references to associated regulations. The appendices also contain a variety of useful information.

This document differs from and compliments the Joint Service P2 Technical Library and the Hazardous Air Pollutant (HAP) Status Binder. The Joint Service P2 Technical Library was created to outline "off the shelf" technologies for use by DoD installations. The HAP Status Binder was developed to keep DoD Air Quality Managers apprised of the status of National Emission Standards for Hazardous Air Pollutants (NESHAPs). So while the former is oriented toward what technologies are available, and the latter is oriented toward what the regulations require, this document presents what is actually being done now in the Military and provides contact information to enhance networking. Web addresses are listed in Appendix C.

WHAT IS POLLUTION PREVENTION?

P2 means changing products used or manufacturing processes to reduce impact to the environment. This involves incorporating environmental considerations into product design and into the design, operation, and maintenance of production processes resulting in improved efficiency and performance. By operating more efficiently we protect human health, strengthen our economic well-being, and preserve the environment. P2 is a cost-effective and sound approach to environmental protection and is key to obtaining environmentally sustainable economic development.

Executive Order 12856, signed by President Clinton in August 1993, required Federal facilities to comply with the Emergency Planning and Community Right to Know Act (EPCRA), which was authorized in October 1986, and the Pollution Prevention Act (PPA) which was authorized in December 1990. The DoD required every facility that was not scheduled for operational closure by 31 December 1997 to develop and implement a P2 plan. This plan is supposed to address the actions required by the facility for reducing pollution from all sources and to all media, including the installation’s strategy for meeting the goal of a 50% reduction by 1999 in Toxic Release Inventory reportable releases and off-site transfers.

DoD Directive 4715.1 defined P2 as source reduction (as defined in the PPA of 1990, 42 U.S.C. Sections 13101-13109) and other practices that reduce or eliminate the creation of pollutants through: (a) increased efficiency in the use of raw materials, energy, water, or other resources; or (b) protection of natural resources by conservation.

The PPA defined source reduction as "any practice that (a) reduces the amount of any hazardous substance, pollutant, or contaminant entering any waste stream or otherwise released into the environment (including fugitive emissions) prior to recycling, treatment, and disposal; and (b) reduces the hazards to public health and the environment associated with the release of such substances, pollutants, or contaminants. The term includes equipment or technology modification, process or procedure modification, reformulation or redesign of products, substitution of raw materials, and improvements in housekeeping, maintenance, training, or inventory control." Source reduction does not entail any form of waste management (e.g., recycling and treatment).

Under Section 6602(b) of the PPA, Congress established a national policy that:

The primary focus of Air Quality Managers is to comply with regulations. Pollution prevention is a tool to meet or proactively surpass the regulatory requirements.

 

REGULATORY FRAMEWORK

EPCRA

The Emergency Planning and Community Right-to-Know Act (EPCRA) was promulgated as Title III of the Superfund Amendments and Reauthorization Act in 1986. The EPCRA requires covered facilities to:

  1. Follow certain procedures in the event of a dangerous accidental release.
  2. Conduct inventories of hazardous materials at the facility and make this information available to the local community.
  3. Conduct a Toxic Release Inventory (TRI) each year and report to the EPA and the State the quantities of toxic chemicals released to the environment.

Federal facilities were not covered by EPCRA, but Executive Order 12856 directed Federal agencies to comply with EPCRA and to reduce their reportable releases and off-site transfers of toxic chemicals by 50% by 31 December 1999 using the 1994 TRI reports as the baseline.

In the DoD’s 1994 TRI report, air emissions represented about two-thirds of all TRI reportable releases and off-site transfers (see Figure 1), and over 97% of all TRI reportable on-site releases (see Figure 2). The DoD did not realize the high percentage of toxic releases to the air until the release of the 1994 TRI report. These air emissions are primarily from maintenance activities associated with the painting and depainting of aircraft and cleaning and degreasing activities. The list of hazardous air pollutants (HAPs) included in the 1990 amendments of the Clean Air Act (CAA90) was based to a large extent on the TRI list. Title III of the CAA90 was one of the Environmental

Figure 1: TRI Reportable Releases And Off-Site Transfers for 1994 and 1995

Protection Agency's (EPA’s) tools to achieve a reduction of TRI pollutants. Table 1 compares the TRI top ten chemicals reported for the DoD for 1994 and 1995. Notice that all but one are HAPs.

Figure 2: 1994 DoD TRI On-Site Releases By Media

Table 1: Change in Top 10 Chemical Releases and Transfers Information

 Top 10 1994 Chemical

1994 (1,000 lbs)

1995 (1,000 lbs)

Change

*Dichloromethane (methylene chloride)

2,236

1,617

-28%

*Methyl ethyl ketone

1,505

1,097

-27%

*1,1,1-Trichloroethane (methyl chloroform)

1,232

751

-39%

*Ethylene glycol

537

329

-39%

*Toluene

445

235

-47%

*Phenol

412

267

-35%

Zinc compounds

409

45

-89%

*Tetrachloroethylene (perchloroethylene)

359

217

-39%

*Hexachloroethane

351

56

-84%

*Hydrochloric acid

298

Delisted

Not Applicable

Note: * indicates this TRI substance is also a HAP

CAA

The primary goal of the Clean Air Act (CAA) is to "protect the public" from air pollution with an "adequate margin of safety". End-of-pipe control technologies have been the primary method of reducing pollution emissions.

Under CAA Title I Section (§)112 and §129, Congress mandates that stationary sources be required to use Maximum Achievable Control Technology (MACT) or Generally Achievable Control Technology (GACT). Title I requires the EPA to set National Ambient Air Quality Standards (NAAQS) and State and Local agencies have the option to use either tools developed by the EPA or within their own agencies to control air emissions from stationary sources. New Source Performance Standards, Control Techniques Guidelines, Alternative Control Techniques, Best Available Control Technology, Best Available Control Measures, and Reasonably Available Control Technology are examples of some of the methods State and Local agencies typically use to control emissions. The strong emphasis on controlling emissions using control technologies under the CAA is easy to see. Facilities generally find it much easier to install a standard control technology called out under a specific regulation than to identify and implement a P2 option.

In recent years, EPA has been writing P2 opportunities along with control technologies into their standards. The EPA has tried to change their focus to performance based and cost effective standards.

Developing P2 strategies may require longer term investing than the three years usually allotted for compliance with a standard. Some processes may require large equipment changes thus making P2 cost prohibitive under the current funding system, which does not accommodate longer payback periods. This encourages the use of control technologies in those cases where the upfront cost is lower. The EPA has been trying to write into rules incentives for industry to develop P2 by giving longer time periods to comply if P2 initiatives are implemented (a one year extension is the typical length of the time period). The EPA also seeks to provide regulatory relief for the development of P2 through such cross media efforts as the Common Sense Initiative, Project XL, and ENVVEST. All of these programs have been very difficult to implement within both Industry and the DoD because consensus on solutions among industry, the EPA, and environmental groups has proved difficult to achieve.

The P2 initiatives that have been the most successful are those with a low up-front cost, such as coating and degreasing processes. Coating reformulations and application techniques have significantly contributed to HAP and volatile organic compound (VOC) reductions. Switching to aqueous degreasers has reduced both VOCs and operating costs.

RCRA

The Solid Waste Disposal Act (SWDA) of 1965 was the first Federal legislation that addressed the nation's waste management practices. This act, as amended by the Resource Conservation and Recovery Act (RCRA) of 1976 and the Hazardous and Solid Waste Amendments (HSWA) of 1984, is commonly referred to as RCRA.

Within the DoD, P2 seems to focus on the minimization of hazardous and solid wastes. There are four possible reasons for this. (1) The Resource Conservation and Recovery Act (RCRA) is the environmental law for which the DoD has paid the most fines. In addition, a number of DoD employees have been prosecuted for violation of RCRA regulations. Reducing the use of hazardous materials reduces liability. (2) There are hazardous waste minimization requirements within RCRA. Hazardous waste generators must submit a Biennial Report, to include a description of the efforts undertaken and progress made to reduce the volume and toxicity of waste generated [40 CFR 262.41(a)(6,7)]. In addition, RCRA requires the permit holder of a treatment, storage, and disposal facility to have, at a minimum, annual certification that there is a program in place to reduce the volume and toxicity of the hazardous waste generated, and to minimize the present and future threat to human health and the environment [40 CFR 264.73 (b)(9)]. (3) Hazardous waste disposal costs are high, so that P2 in this area yields a direct and immediate cost savings. (4) Solid and hazardous waste quantities and costs are more easily determined than air emission quantities and costs.

Many Military documents focus on solid and hazardous waste P2. The Joint Service P2 Technical Library’s introduction states that the purpose of the Library is "to identify available P2 technologies, management practices, and process changes that will reduce the amount of hazardous and solid waste being generated at joint service industrial facilities."

Some P2 initiated because of RCRA has benefited air quality, despite the apparent trend to pigeonhole P2 with hazardous/solid waste minimization efforts. Examples of common P2 applications which were initiated because of hazardous waste but have benefited air quality are: vapor degreasers replaced with aqueous parts washers, low VOC coatings formulated, and parts depainted using blasting techniques such as plastic, glass, wheat starch, or sodium bicarbonate where once solvents were used.

WHY INCORPORATE P2 INTO AIR PROGRAMS?

P2 is typically managed by the Hazardous Waste Manager or the P2 Program Manager. Consequently the installation’s Air Program is not usually involved with P2 and opportunities may be missed. Yet there are often substantial benefits from incorporating P2 into Air Programs:

1. Immediate Cost Savings

2. Regulatory Relief

3. Regulatory Policy Compliance

 

CROSS REFERENCES

The following tables cross-reference statutes, regulations, and executive orders to processes and sources. Success stories and potential alternatives gathered from Department of Defense installations are found under the Processes section. Points of contact and sources of the information are listed for further questions.

Table 2

The Clean Air Act & Amendments Referenced to Regulations

Title Name CAA Section Regulation
I New Source Performance Standard (NSPS) Program 111 40 CFR 60
I National Ambient Air Quality Standards (NAAQS) Program 105-110, 160-193 40 CFR 50-53, 55, 58, 81, 93
II Mobile Sources Program 202-250 40 CFR 80, 85-88
III National Emission Standards for Hazardous Air Pollutants (NESHAP) Program 112 40 CFR 61, 63, 68
IV Acid Rain Program 401-416 40 CFR 72-78
V Operating Permit Program 501-507 40 CFR 70-71
VI Stratospheric Ozone Protection Program 601-618 40 CFR 82

Table 3

Laws Referenced to Processes
Laws and Regulations Affected Processes and their Section Numbers in This Document
Accidental Release Prevention Program 5.1 Listed Substance Storage
Aerospace NESHAP 1.1 Methylene Chloride Cleaning
2.1 Paint Stripping: Methylene Chloride
3.1 Paint Gun Washers
3.2 Primers
3.3 CARC Painting
3.4 Touch Up Painting
3.5 General Painting
Architectural Coating NSPS 3.6 Architectural Coatings
Cadmium Compounds HAP 3.7 Cadmium Plating
Carbon Monoxide NAAQS 4.5 Boilers
4.7 Aerospace Ground Equipment
Chromium Compounds HAP 3.2 Primers
3.8 Chromic Acid Anodizing
3.9 Chromate Chemical Conversion Coating
3.10 Hard Chrome Plating
Engine Test Facilities NESHAP 4.9 Jet engine testing
Executive Order 12902, Section 305 4.5 Boilers
Existing Source Emission Guideline 4.1 Medical Waste Incinerators
4.3 Municipal Waste Combustors
Halogenated Solvent Cleaners NESHAP 1.1 Methylene Chloride Cleaning
1.2 1,1,1-Trichloroethane
Hazardous Waste Combustor NESHAP 4.4 Treatment, Storage, Disposal Facility
Industrial Combustion Coordinated Rulemaking 4.2 Classified Waste Incinerators
Lead NAAQS 6.3 Weapons Training at Firing Ranges
New Source Performance Standard (NSPS) 4.1 Medical Waste Incinerators
4.3 Municipal Waste Combustors
Nitrogen Dioxide (NO2) NAAQS 4.5 Boilers
4.7 Aerospace Ground Equipment
4.9 Jet Engine Testing
Ozone Depleting Substances 1.2 1,1,1-Trichloroethane
1.3 CFC-113
1.5 General Cleaning
1.6 Weapons Cleaning: Wipe Cleaning
1.7 Weapons Cleaning: Dip Tanks
1.8 Electronics Cleaning
Ozone NAAQS (measured in VOCs and NOx) 4.5 Boilers
4.7 Aerospace Ground Equipment
4.9 Jet Engine Testing
Particulate Matter NAAQS 4.5 Boilers
4.7 Aerospace Ground Equipment
4.8 Generators
6.1 Fire Fighting Training
6.2 Field Training Exercises
Sulfur Dioxide (SO2) NAAQS 4.5 Boilers
Ozone NAAQS
(measured in VOCs and NOx)
1.1 Methylene Chloride
1.2 1,1,1-Trichloroethane
1.4 Parts Washing: Stoddard Solvent
1.5 General Cleaning
1.6 Weapons Cleaning: Wipe Cleaning
1.7 Weapons Cleaning: Dip Tanks
2.1 Paint Stripping: Methylene Chloride
3.1 Paint Gun Washers
3.2 Primers
3.3 CARC Painting
3.4 Touch Up Painting
3.5 General Painting
3.6 Architectural Coatings
7.2 Fuel Dispensing
7.3 Pesticides
7.4 Lubricants
7.5 Adhesives and Sealants

Table 4

Processes Referenced to Laws, Order of Appearance
Processes Covered in this Document
In Numerical Order By Section Number
Laws and Regulations
Affected by Change
1.1 Methylene Chloride Ozone NAAQS (measured in VOCs and NOx)
Halogenated Solvent Cleaners NESHAP
Aerospace NESHAP
1.2 1,1,1-Trichloroethane Ozone Depleting Substance
Ozone NAAQS (measured in VOCs and NOx)
Halogenated Solvent Cleaners NESHAP
1.3 CFC-113 Ozone Depleting Substances
1.4 Parts Washing: Stoddard Solvent Ozone NAAQS (measured in VOCs and NOx)
1.5 General Cleaning Ozone NAAQS (measured in VOCs and NOx)
Ozone Depleting Substances
1.6 Weapons Cleaning: Wipe Cleaning Ozone NAAQS (measured in VOCs and NOx)
Ozone Depleting Substances
1.7 Weapons Cleaning: Dip Tanks Ozone NAAQS (measured in VOCs and NOx)
Ozone Depleting Substances
1.8 Electronics Cleaning Ozone Depleting Substances
2.1 Paint Stripping: Methylene Chloride Ozone NAAQS (measured in VOCs and NOx)
Aerospace NESHAP
3.1 Paint Gun Washers Ozone NAAQS (measured in VOCs and NOx)
Aerospace NESHAP
3.2 Primers Ozone NAAQS (measured in VOCs and NOx)
Chromium compounds (HAP)
Aerospace NESHAP
3.3 CARC Painting Ozone NAAQS (measured in VOCs and NOx)
Aerospace NESHAP
3.4 Touch Up Painting Ozone NAAQS (measured in VOCs and NOx)
Aerospace NESHAP
3.5 General Painting Ozone NAAQS (measured in VOCs and NOx)
Aerospace NESHAP
3.6 Architectural Coatings Architectural Coating NSPS
Ozone NAAQS (measured in VOCs and NOx)
3.7 Cadmium Plating Cadmium Compounds HAP
3.8 Chromic Acid Anodizing Chromium Compounds HAP
3.9 Chromate Chemical Conversion Coating Chromium Compounds HAP
3.10 Hard Chrome Plating Chromium Compounds HAP
4.1 Medical Waste Incinerators Hospital/Medical/Infectious Waste Incinerator (HMIWI)
New Source Performance Standard (NSPS)
Existing Source Emission Guideline (EG)
4.2 Classified Waste Incinerators Industrial Combustion Coordinated Rulemaking
4.3 Municipal Waste Combustors Municipal Waste Combustor NSPS/EG
4.4 Treatment, Storage, Disposal Facility Hazardous Waste Combustor NESHAP
4.5 Boilers Carbon Monoxide (CO) NAAQS
Executive Order 12902 Section 305
Nitrogen Dioxide (NO2) NAAQS
Ozone (measured in VOCs and NOx) NAAQS
Particulate Matter (PM) NAAQS
Sulfur Dioxide (SO2) NAAQS
4.6 Vehicles PM and Ozone NAAQS
Executive Order 13031
4.7 Aerospace Ground Equipment Carbon Monoxide (CO) NAAQS
Nitrogen Dioxide (NO2) NAAQS
Ozone (measured in VOCs and NOx) NAAQS
Particulate Matter (PM) NAAQS
4.8 Generators Carbon Monoxide (CO) NAAQS
Nitrogen Dioxide (NO2) NAAQS
4.9 Jet engine testing Engine Test Facilities NESHAP
CO, NO2, Ozone, PM NAAQS
5.1 Listed Substance Storage Accidental Release Prevention Program
(Risk Management Programs and Plans)
6.1 Fire Fighting Training Particulate Matter (PM) NAAQS - Fugitive Emissions
6.2 Field Training Exercises Particulate Matter (PM) NAAQS – Fugitive Emissions
6.3 Weapons Training at Firing Ranges Lead NAAQS
7.1 Ethylene Oxide Sterilizing State-Specific Regulations
7.2 Fuel Dispensing VOC and HAP Emissions
7.3 Pesticides VOC and HAP Emissions
7.4 Lubricants VOC and HAP Emissions
7.5 Adhesives and Sealants VOC and HAP Emissions
7.6 Potential to Emit Criteria and HAP Emissions

Table 5

Processes Referenced to Laws, Alphabetical Order
Processes Covered in this Document in Alphabetical Order
(Section Number in Parentheses)
Laws and Regulations
Affected by Change
1,1,1-Trichloroethane (1.2) Ozone Depleting Substance
Ozone NAAQS (measured in VOCs and NOx)
Halogenated Solvent Cleaners NESHAP
Adhesives and Sealants (7.5) VOC and HAP Emissions
Aerospace Ground Equipment (4.7) Nitrogen Dioxide (NO2) NAAQS
Particulate Matter (PM) NAAQS
Architectural Coatings (3.6) Architectural Coating NSPS
Ozone NAAQS (measured in VOCs and NOx)
Boilers (4.5) Executive Order 12902 Section 305
Sulfur Dioxide (SO2) NAAQS
Nitrogen Dioxide (NO2) NAAQS
Ozone NAAQS (measured in VOCs and NOx)
Particulate Matter (PM) NAAQS
Cadmium Plating (3.7) Fugitive Emissions - Cadmium
CARC Painting (3.3) Ozone NAAQS (measured in VOCs and NOx)
Aerospace NESHAP
CFC-113 (1.3) Ozone Depleting Substances
Chromate Chemical Conversion Coating (3.9) Chromium Compounds HAP
Chromic Acid Anodizing (3.8) Chromium Compounds HAP
Classified Waste Incinerators (4.2) Industrial Combustion Coordinated Rulemaking
Electronics Cleaning (1.8) Ozone Depleting Substances
Ethylene Oxide Sterilizing (7.1) State-Specific Regulations
Field Training Exercises (6.2) Particulate Matter (PM) NAAQS – Fugitive Emissions
Fire Fighting Training (6.1) Particulate Matter (PM) NAAQS - Fugitive Emissions
Fuel Dispensing (7.2) VOC and HAP Emissions
General Cleaning (1.5) Ozone NAAQS (measured in VOCs and NOx)
Ozone Depleting Substances
General Painting (3.5) Ozone NAAQS (measured in VOCs and NOx)
Aerospace NESHAP
Generators (4.8) Carbon Monoxide (CO) NAAQS
Nitrogen Dioxide (NO2) NAAQS
Ozone NAAQS (measured in VOCs and NOx)
Hard Chrome Plating (3.10) Chromium Compounds HAP
Jet engine testing (4.9) Engine Test Facilities NESHAP
CO, NO2, Ozone, PM NAAQS
Listed Substance Storage (5.1) Accidental Release Prevention Program
(Risk Management Programs and Plans)
Lubricants (7.4) VOC and HAP Emissions
Medical Waste Incinerators (4.1) Hospital/Medical/Infectious Waste Incinerator (HMIWI)
New Source Performance Standard (NSPS)
Existing Source Emission Guideline (EG)
Methylene Chloride (1.1) Ozone NAAQS (measured in VOCs and NOx)
Halogenated Solvent Cleaners NESHAP
Aerospace NESHAP
Municipal Waste Combustors (4.3) Municipal Waste Combustor NSPS/EG
Paint Gun Washers (3.1) Ozone NAAQS (measured in VOCs and NOx)
Aerospace NESHAP
Paint Stripping: Methylene Chloride (2.1) Ozone NAAQS (measured in VOCs and NOx)
Aerospace NESHAP
Parts Washing - Stoddard Solvent (1.4) Ozone NAAQS (measured in VOCs and NOx)
Pesticides (7.3) VOC and HAP Emissions
Potential to Emit (7.6) Criteria and HAP Emissions
Primers (3.2) Ozone NAAQS (measured in VOCs and NOx)
Chromium compounds (HAP)
Aerospace NESHAP
Touch Up Painting (3.4) Ozone NAAQS (measured in VOCs and NOx)
Aerospace NESHAP
Treatment, Storage, Disposal Facility (4.4) Hazardous Waste Combustor NESHAP
Vehicles (4.6) PM and Ozone NAAQS
Executive Order 13031
Weapons Cleaning: Dip Tanks (1.7) Ozone NAAQS (measured in VOCs and NOx)
Ozone Depleting Substances
Weapons Cleaning: Wipe Cleaning (1.6) Ozone NAAQS (measured in VOCs and NOx)
Ozone Depleting Substances
Weapons Training at Firing Ranges (6.3) Lead NAAQS

 

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