Vol_II_Specifications_Camp_Buehring_Electric_Lines.pdf

Request for Proposal

W912ER19R0024

Specifications for

Underground Electric Lines

Camp Buehring, Kuwait

Volume 2 of 2 Divisions 01 - 33

US Army Corps of Engineers Middle East District

Underground Electric Lines, Camp Buehring, Kuwait 474411

PROJECT TABLE OF CONTENTS

DIVISION 01 - GENERAL REQUIREMENTS

01 11 00 SUMMARY OF WORK

01 14 00 WORK RESTRICTIONS

01 15 00.12 10 SUPPLEMENTARY REQUIREMENTS

01 30 00 ADMINISTRATIVE REQUIREMENTS

01 32 17.12 10 COST-LOADED NETWORK ANALYSIS SCHEDULES (NAS)

01 33 00 SUBMITTAL PROCEDURES

01 33 29 SUSTAINABILITY REPORTING

01 35 26 GOVERNMENTAL SAFETY REQUIREMENTS

01 42 00 SOURCES FOR REFERENCE PUBLICATIONS

01 42 15 METRIC MEASUREMENTS

01 45 00.00 10 QUALITY CONTROL

01 45 00.15 10 RESIDENT MANAGEMENT SYSTEM CONTRACTOR MODE (RMS CM)

01 50 00 TEMPORARY CONSTRUCTION FACILITIES AND CONTROLS

01 57 19 TEMPORARY ENVIRONMENTAL CONTROLS

01 58 00 PROJECT IDENTIFICATION

01 74 19 CONSTRUCTION WASTE MANAGEMENT AND DISPOSAL

01 78 00 CLOSEOUT SUBMITTALS

01 78 23 OPERATION AND MAINTENANCE DATA

DIVISION 03 - CONCRETE

03 30 00 CAST-IN-PLACE CONCRETE

DIVISION 26 - ELECTRICAL

26 00 00.00 20 BASIC ELECTRICAL MATERIALS AND METHODS

26 08 00 APPARATUS INSPECTION AND TESTING

26 11 16 PACKAGE SUBSTATION

26 20 02 MINISTRY OF DEFENCE MILITARY ENGINEERING PROJECTS

ENGINEERING DEPARTMENT GENERAL SPECIFICATIONS

AND REQUIREMENTS FOR ELECTRICAL WORKS

26 20 03 MINISTRY OF ELECTRICITY & WATER MEW/S-1 GENERAL

SPECIFICATION FOR ELECTRICAL INSTALLATION

DIVISION 31 - EARTHWORK

31 00 00 EARTHWORK

31 11 00 CLEARING AND GRUBBING

DIVISION 32 - EXTERIOR IMPROVEMENTS

32 11 23 AGGREGATE BASE COURSES

32 12 13 BITUMINOUS TACK AND PRIME COATS

32 12 16 HOT-MIX ASPHALT (HMA) FOR ROADS

32 15 00 AGGREGATE SURFACE COURSE

DIVISION 33 - UTILITIES

33 11 00 WATER UTILITY DISTRIBUTION PIPING

33 30 00 SANITARY SEWERAGE

33 40 00 STORM DRAINAGE UTILITIES

33 71 02 UNDERGROUND ELECTRICAL DISTRIBUTION

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PROJECT TABLE OF CONTENTS Page 1

SECTION TABLE OF CONTENTS

DIVISION 01 - GENERAL REQUIREMENTS

SECTION 01 11 00

SUMMARY OF WORK

08/15

PART 1 GENERAL

-- End of Section Table of Contents --

SECTION 01 11 00 Page 1

SECTION 01 11 00

SUMMARY OF WORK

08/15

PART 1 GENERAL

1.1 INTRODUCTION

The ASG-N/ KU, USARCENT and Kuwait Ministry of Defense (KMOD) have a strong requirement to provide a new medium voltage (MV) 11Kv line to create a new ring #3 with up to five (5) new substations to power various load centers to the east in Zones 1 and 2 at Camp Buehring, Kuwait. The purpose of this project is to provide the necessary MILCON construction improvements for USARCENT in support of the Area Support Group-North (ASG-N) mission in Kuwait.

The scope of this project includes the construction effort for an Underground Electric Lines in Zones 1 and 2 at Camp Buehring, Kuwait. The U.S. Army Corps of Engineers (USACE), Transatlantic Middle East District (TAM), has a requirement from United States Central Command (USCENTCOM) through United States Army Forces, Central Command (USARCENT) in cooperation with the Kuwait Ministry of Defense (KMOD) for the construction project consisting of, however not limited to, providing all labor, material, transportation and performing all work necessary to construct and complete an electrical Ring 3 comprising an Underground Electric Lines at Camp Buehring, Kuwait. Primary facilities shall include 11 KV underground electric lines, as well as substations (of a packaged /weather tight) unit placed atop concrete slabs. Supporting facilities include additional electric service, site improvements, along with site grading and limited drainage features.

This award will include the following items under the Base Bid:

- Mobilization and Demobilization

- Construct and direct bury 11 KV Underground Electric Lines

- Four (4) Substations to include concrete slabs

- Underground Electrical Connections

- Cable Termination 11 KV

- Site Improvements

Options under this award will include the following:

- Option 1 New Substation (#18) dedicated to new DFAC

- Option 2 Low voltage cable (415V) lines

1.2 Applicable Regulations

The Contractor shall comply with all Base and Kuwaiti Government laws, rules, regulations and/or standards concerning environmental pollution control and abatement, the Department of Defense's Overseas Environmental

SECTION 01 11 00 Page 2

Baseline Guidance Document, latest version, the Kuwait Environmental Final Governing Standard (Appendix 1), and National Historic Preservation Act Section 402 (16 U.S.C 470a-2).

For a listing of all applicable Kuwaiti regulations which may apply, see Appendix 2 - DPW Polices.

1.3 Notification

The Contracting Officer will notify the Contractor in writing of any observed non-compliance with this paragraph and other environmental requirements of this RFP. The Contractor shall immediately take corrective action upon observation of non-compliance. If the Contractor fails or refuses to promptly take corrective action, the Contracting Officer may issue an order stopping all or part of the work until satisfactory corrective action has been taken. No extension of time or damages will be awarded to the Contractor unless it was later determined that the Contractor was in compliance.

1.4 Spillages

Measures shall be taken to prevent chemicals, fuels, oils, greases, bituminous materials, waste washings, herbicides and insecticides, and construction materials from polluting the construction site and surrounding area.

1.5 Disposal

All spoil materials, wastes, effluents, trash, garbage, oil, grease, chemicals, etc., shall be subject to the approval of the Contracting Officer and will be subject to regulations of the Host Nation, as well as to the US Army Standards governing the removal and disposal of identified waste streams. Burning at the project site for the disposal of refuse and debris will not be permitted.

1.6 Relocation of Utilities

The Contractor will verify from using current Base Utility mapping and utility locate services the location of any utilities (water, sanitary sewer, electrical, communications, etc.) that will require relocation as a result of the construction of the 11KV cable trench.

1.7 Remote, Austere, and Hostile Sites (as applicable)

The Contractor shall be responsible for all personnel, security, supplies, equipment, and infrastructure (including, but not limited to, potable water, utility systems, dining, transportation, and medical care) when there are no facilities and services available. This may include providing these facilities and services to a limited number of government personnel or other contractor personnel (such as Title II personnel) present or visiting to oversee or assess the work.

1.8 PERSONNEL

The U.S. Government reserves the right to restrict employment under this contract of any contractor employee, or prospective employee, who is identified at any time to be a potential threat to the health, safety, security, general well-being, or operational mission of the facilities identified and/or its population. This determination may be made by the

SECTION 01 11 00 Page 3

Contracting Officer, COR, or technical representative assisting the COR at any time. If such a determination is made concerning a contractor employee, the contractor shall immediately evacuate that person from the work site and terminate his/her involvement in this contract to include access privilege documents. A list of employees must be furnished when submitting the bid to facilitate the contractor approval process.

1.9 ATTACHMENTS

Appendix 1 - Kuwait Environmental Final Governing Standard Appendix 2 - DPW Polices

-- End of Section --

SECTION 01 11 00 Page 4

Kuwait Final Governing Standards

KUWAIT ENVIRONMENTAL

FINAL GOVERNING STANDARD

15 March 2011

Prepared by

UNITED STATES

ARMY CENTRAL COMMAND

On behalf of

UNITED STATES CENTRAL COMMAND

APPENDIX 1 - Section 01 11 00

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FOREWORD

This Department of Defense Publication is issued under the authority and requirements of DoD Instruction (DoDI) 4715.5, “Management of Environmental Compliance at Overseas Installations,” April 22, 1996. This guide provides criteria, standards, and management practices for environmental compliance at DoD installations in Kuwait.

This publication’s predecessor, Final Governing Standards – Kuwait March 2001, is hereby canceled. This Final Governing Standard applies to all United States Forces operating in the State of Kuwait.

This FGS is effective immediately and its use is mandatory by all DoD Components.

Commanders of U.S. Forces may only issue supplementary instructions when deemed necessary to provide for unique requirements within their organizations.

Send recommended changes to this document to:

HQ, United States Central Command Attn: CCJ4-E 7115 South Boundary Blvd.

MacDill AFB, FL 33621-5101

FOR THE COMMANDER:

MICHAEL D. JONES

Major General, U.S. Army Chief of Staff

USCENTCOM

METHODOLOGY

Chapters 2-19 of the FGS include the scope, definitions and criteria. Appendices and tables are also presented. The applicable Kuwait environmental regulations were compared to the May 2007 Overseas Environmental Baseline Guidance Document (OEBGD), and determinations were made as to whether a Kuwait environmental regulation was more or less stringent, equivalent to, or in addition to, the OEBGD standard. The standards of the government of Kuwiat and the OEBGD standards were combined into one document to create this FGS.

TABLE OF CONTENTS

FORWARD 2

METHODOLOGY 3

TABLE OF CONTENTS 4

TABLES 7

REFERENCES 9

C1. CHAPTER 1 OVERVIEW 10

C1.1. PURPOSE 10

C1.2. APPLICABILITY 10

C1.3. EXEMPTIONS 10

C1.4. DEFINITIONS 11

C1.5. RESPONSIBILITIES 11

C1.6. ADDITIONAL INFORMATION 13

C2. CHAPTER 2 AIR EMISSIONS 16

C2.1. SCOPE 16

C2.2. DEFINITIONS 16

C2.3. CRITERIA 18

C3. CHAPTER 3 DRINKING WATER 30

C3.1. SCOPE 30

C3.2. DEFINITIONS 30

C3.3. CRITERIA 32

C4. CHAPTER 4 WASTEWATER 60

C4.1. SCOPE 60

C4.2. DEFINITIONS 60

C4.3. CRITERIA 63

C5. CHAPTER 5 HAZARDOUS MATERIAL 76

C5.1 SCOPE 76

C5.2. DEFINITIONS 76

C5.3 CRITERIA 76

C6. CHAPTER 6 HAZARDOUS WASTE 82

C6.1. SCOPE 82

C6.2. DEFINITIONS 82

C6.3. CRITERIA 84

C7. CHAPTER 7 SOLID WASTE 102

C7.1. SCOPE 102

C7.2. DEFINITIONS 102

C7.3. CRITERIA 105

C8. CHAPTER 8 MEDICAL WASTE MANAGEMENT 110

C8.1. SCOPE 110

C8.2. DEFINITIONS 110

C8.3. CRITERIA 111

C9. CHAPTER 9 PETROLEUM, OIL AND LUBRICANTS 116

C9.1. SCOPE 116

C9.2. DEFINITIONS 116

C9.3. CRITERIA 117

C10. CHAPTER 10 RESERVED 120

C11. CHAPTER 11 PESTICIDES 122

C11.1. SCOPE 122

C11.2. DEFINITIONS 122

C11.3. CRITERIA 123

C12. CHAPTER 12 HISTORIC AND CULTURAL RESOURCES 126

C12.1. SCOPE 126

C12.2. DEFINITIONS 126

C12.3. CRITERIA 127

C13. CHAPTER 13 NATURAL RESOURCES AND ENDANGERED SPECIES 130

C13.1. SCOPE 130

C13.2. DEFINITIONS 130

C13.3. CRITERIA 131

C14. CHAPTER 14 POLYCHLORINATED BYPHENYLS 134

C14.1. SCOPE 134

C14.2. DEFINITIONS 134

C14.3. CRITERIA 135

C15. CHAPTER 15 ASBESTOS 144

C15.1. SCOPE 144

C15.2. DEFINITIONS 144

C15.3. CRITERIA 145

C16. CHAPTER 16 RESERVED 148

C17. CHAPTER 17 LEAD-BASED PAINT 150

C17.1. SCOPE 150

C17.2. DEFINITIONS 150

C17.3. CRITERIA 151

C18. CHAPTER 18 SPILL PREVENTION AND RESPONSE PLANNING 154

C18.1. SCOPE 154

C18.2. DEFINITIONS 154

C18.3. CRITERIA 155

C19. CHAPTER 19 UNDERGROUND STORAGE TANKS 160

C19.1. SCOPE 160

C19.2. DEFINITIONS 160

C19.3. CRITERIA 161

APPENDICES

AP1. APPENDIX 1 CHARACTERISTICS OF HAZARDOUS WASTES

AND LISTS OF HAZARDOUS WASTES AND HAZARDOUS MATERIALS 164

AP2. APPENDIX 2 DETERMINATION OF WORST CASE DISCHARGE

PLANNING VOLUME 214

TABLES

Table C2.T1 Emission Standards for New Steam/Hot Water Generating Units 23

Table C2.T2 Class I and II Ozone Depleting Substances 24

Table C2.T3 Emission Standards for Incinerators 26

Table C2.T4 Carbon Monoxide Operating Limits for Incinerators 27

Table C3.T1 Surface Water Treatment Requirements 39

Table C3.T2 Total Coliform Monitoring Frequency 41

Table C3.T3 Inorganic Chemical MCLs 42

Table C3.T4 Inorganics Monitoring Requirements 43

Table C3.T5 Recommended Fluoride Concentrations at Different Temperatures 44

Table C3.T6 Monitoring Requirements for Lead and Copper Water Quality Parameters 44

Table C3.T7 Synthetic Organic Chemical MCLs 44

Table C3.T8 Synthetic Organic Chemical Monitoring Requirements 46

Table C3.T9 Disinfectant/Disinfection Byproducts Monitoring Requirements 47

Table C3.T10 Radionuclide MCLs and Monitoring Requirements 50

Table C3.T11 CT Values for Inactivation of Giardia Cysts by Free Chlorine at 0.5ºC or Lower 51

Table C3.T12 CT Values for Inactivation of Giardia Cysts by Free Chlorine at 5.0ºC 52

Table C3.T13 CT Values for Inactivation of Giardia Cysts by Free Chlorine at 10ºC 53

Table C3.T14 CT Values for Inactivation of Giardia Cysts by Free Chlorine at 15ºC 54

Table C3.T15 CT Values for Inactivation of Giardia Cysts by Free Chlorine at 20ºC 55

Table C3.T16 CT Values for Inactivation of Giardia Cysts by Free Chlorine at 25ºC 56

Table C3.T17 CT Values for Inactivation of Viruses by Free Chlorine 57

Table C3.T18 CT Values for Inactivation of Giardia Cysts by Chlorine Dioxide 57

Table C3.T19 CT Values for Inactivation of Viruses by Free Chlorine Dioxide pH 6-9 57

Table C3.T20 CT Values for Inactivation of Giardia Cysts by Ozone 57

Table C3.T21 CT Values for Inactivation of Viruses by Free Ozone 58

Table C3.T22 CT Values for Inactivation of Giardia Cysts by Chloramine pH 6-9 58

Table C3.T23 CT Values for Inactivation of Viruses by Chloramine 58

Table C3.T24 CT Values for Inactivation of Viruses by UV 58

Table C4.T1 Components of Total Toxic Organics 70

Table C4.T2 Monitoring Requirements for Direct Discharges to Surface Waters 71

Table C4.T3 Best Management Practices for Controlling Storm Water Pollution 72

Table C4.T4 Effluent Limits for Direct Discharges to Maritime Waters 73

Table C4.T5 Effluent Limits for Indirect Discharges 75

Table C5.T1 Typical Hazardous Materials Characteristics 80

Table C8.T1 Treatment and Disposal Methods for Infectious Medical Waste 114

Table C12.T1 Protected Areas 129

Table C12.T2 Cultural Sites 129

Table C13.T1 Threatened and Endangered Animals 132

Table C13.T2 Threatened and Endangered Plants 132

Table AP1.T1 Maximum Concentration of Contaminants for the Toxicity Characteristic 168

Table AP1.T2 Maximum Concentration of Contaminants for Non-Wastewater 169

Table AP1.T3 Listed Hazardous Wastes from Non-Specific Sources 170

Table AP1.T4 List of Hazardous Waste/Substances/Materials 173

REFERENCES

(a) DoD Instruction 4715.5, "Management of Environmental Compliance at Overseas

Installations," April 22, 1996

(b) DoD 4715.05-G, “Overseas Environmental Baseline Guidance Document,” May 1, 2007

(c) Executive Order 12344, "Naval Nuclear Propulsion Program," February 1, 1982

(d) Section 7158 of title 42, United States Code

(e) Executive Order 12114, "Environmental Effects Abroad of Major Federal Actions,"

January 4, 1979

(f) DoD Instruction 4715.4 C1, "Pollution Prevention," July 6, 1998

(g) DoD 8910.1-M, “DoD Procedures for Management of Information Requirements,”

June 30, 1998

(h) DoD Instruction 6050.05 C1, “DoD Hazard Communication (HAZCOM) Program,”

August 25, 2008

(i) Defense Logistics Agency Instruction 4145.11, Army Technical Manual 38-410, Naval

Supply Publication 573, Air Force Joint Manual 23-209, and Marine Corps Order 4450.12A, "Storage and Handling of Hazardous Materials," January 13, 1999

(j) Air Force Manual 24-204 (Interservice), Army Technical Manual 38-250, Naval Supply Publication 505, Marine Corps Order P4030.19I, and Defense Logistics Agency Instruction 4145.3, "Preparing Hazardous Materials for Military Air Shipments," September 1, 2009

(k) DoD 4160.21-M, "Defense Materiel Disposition Manual," August 18, 1997

(l) DoD Instruction 4001.01, "Installation Support," January 10, 2008

(m) Naval Facility Manual of Operation-213, Air Force Regulation 91-8, and Army Technical

Manual 5-634, "Solid Waste Management," May 1990

(n) DoD 4150.7-M, "DoD Pest Management Training and Certification," April 24, 1997

(o) Technical Guide No. 17, "Military Handbook - Design of Pest Management Facilities,"

August 2009

(p) DoD Instruction 6055.1, "DoD Safety and Occupational Health (SOH) Program,”

August 19, 1998

(q) DoD Instruction 6055.05, “Occupational and Environmental Health (OEH),”

November 11, 2008

(r) Section 2643 of title 15, United States Code

(s) Title 40, Code of Federal Regulations, Part 763, "Asbestos-Containing Materials in

Schools," current edition

(t) DoD Instruction 4715.8, “Environmental Remediation for DoD Activities Overseas,”

February 2, 1998

(u) CJCSM 3122.03C “Joint Operational Planning and Execution System (JOPES) Volume II:

Planning Formats,” August 17, 2007

C1. CHAPTER 1

OVERVIEW

C1.1. PURPOSE

The primary purpose of this Final Governing Standard (FGS) is to provide criteria and management practices for United States (US) Forces in the State of Kuwait (Kuwait). It has been prepared in accordance with Department of Defense (DoD) Instruction 4715.5 (Reference (a)). Reference (b) is the basis for both the format and the default criteria of this FGS.

C1.2. APPLICABILITY. This FGS applies to actions of the DoD Components at installations in Kuwait.

C1.3. EXEMPTIONS. This FGS does not apply to:

C1.3.1. DoD installations that do not have more than de minimis potential to affect the natural environment (e.g., offices whose operations are primarily administrative, including defense attaché offices, security assistance offices, foreign buying offices and other similar organizations), or for which the DoD Components exercise control only on a temporary or intermittent basis;

C1.3.2. Leased, joint use, and similar facilities to the extent that DoD does not control the instrumentality or operation that a criterion seeks to regulate;

C1.3.3. Operations of U.S. military vessels in international waters or the operations of U.S.

military aircraft, or off-installation operational and training deployments. Off-installation operational deployments include cases of hostilities, contingency operations in hazardous areas, and when United States forces are operating as part of a multi-national force not under full control of the United States. Such excepted operations and deployments shall be conducted in accordance with applicable international agreements, other DoD Directives and Instructions, and environmental annexes incorporated into operation plans or operation orders. However, this Final Governing Standard does apply to support functions for U.S. military vessels and U.S.

military aircraft provided by the DoD Components, including management or disposal of material or waste off-loaded in Kuwait;

C1.3.4. Facilities and activities associated with the Naval Nuclear Propulsion Program, which are covered under E.O. 12344 (Reference (c)) and conducted pursuant to 42 U.S.C. 7158 (Reference (d));

C1.3.5. The determination or conduct of remediation to correct environmental problems caused by DoD's past activities; or, C1.3.6. Environmental analyses conducted under E.O. 12114 (Reference (e)).

C1.4. DEFINITIONS. For purposes of this FGS, unless otherwise indicated, the following definition applies. Additional definitions are provided in subsequent chapters.

C1.4.1. Installation. A base, camp, post, station, yard, center, or other activity under the jurisdiction of the Secretary of a Military Department that is located outside the United States and outside any territory, commonwealth, or possession of the United States.

C1.5. RESPONSIBILITIES

C1.5.1. USCENTCOM as the Unified Command and DoD Environmental Executive Agent (EEA) for the Central Region will:

C1.5.1.1. Within its geographic area of responsibility, coordinate and maintain the oversight and implementation of DoD Instruction 4715.5 (Reference (a)) by all DoD Components.

C1.5.1.2. Coordinate with the Joint Staff, relevant Offices of the Secretary of Defense (OSD), Defense Agencies, and other federal agencies, as required, on environmental matters affecting Kuwait.

C1.5.1.3. Assist with coordination between service component commands and Defense Agencies in environmental matters.

C1.5.1.4. Develop and publish USCENTCOM policy guidance for environmental security by US Forces within Kuwait to ensure compliance with new and existing US Laws, DoD Directives, and Kuwaiti environmental laws, as applicable.

C1.5.1.5. Review the annual environmental security reports and take appropriate action on recommendations related to forces in Kuwait.

C1.5.1.6. Resolve differences between service component commands, Defense Agencies, and executing agent for Kuwait as necessary.

C1.5.1.7. When deemed necessary, direct DoD components to conduct an external environmental compliance audit of an activity or facility, in addition to those regularly scheduled every three years.

C1.5.1.8. Review and take appropriate action regarding component implementing regulations / operating instructions, checklists, and audit / inspection reports in order to oversee compliance with the FGS for Kuwait.

C1.5.1.9. Review requests for waivers and grant or deny the request for waiver in whole, in part or upon conditions in accordance with C1.6.3.

C1.5.2. USARCENT, as Lead Service Component for Kuwait, will:

C1.5.2.1. Review compliance with this FGS by US Forces operating in Kuwait.

C1.5.2.2. Ensure that coordination with the Defense Logistics Agency (DLA), other DoD components and the US Diplomatic Mission is done as necessary for appropriate disposal of hazardous waste generated by US Forces in Kuwait.

C1.5.2.3. Conduct a biennial review of the FGS for Kuwait and recommend changes as needed to ensure environmental compliance with appropriate regulations and laws.

C1.5.2.4. Review requests for waivers and advise USCENTCOM on the need for the waiver.

C1.5.3. USCENTCOM, Component Commands, and Defense Agencies having personnel operating in Kuwait will:

C1.5.3.1. Require compliance with this FGS.

C1.5.3.2. Conduct external environmental compliance audits every three years and internal audits each year when an external audit is not being performed. Submit a copy of the audit reports and instructions to USCENTCOM, (CCJ4-E) within 180 days of inspection or audit.

C1.5.3.3. Program and budget for environmental projects needed to meet requirements in the FGS and to correct each Environmental Compliance Assessment System (ECAS) audit deficiencies.

C1.5.3.4. Ensure that US contracts for services or construction and DoD contracts for the disposal of hazardous waste include provisions requiring the contractor to comply with the FGS, and are administered to enforce such compliance.

C1.5.3.5. Ensure host-tenant agreements require compliance with the FGS.

C1.5.3.6. Develop and conduct training / education programs to instruct all personnel in the environmental aspects of their jobs and the requirements of the FGS.

C1.5.3.7. Report to USCENTCOM Executive Agent any condition, event or practice that is not in conformity with the FGS.

C1.5.3.8. Coordinate with USARCENT’s in-country executing authority for the appropriate turn-in requirements and disposal procedures of hazardous waste generated in Kuwait.

C1.5.3.9. Ensure that units deploying for exercises and contingencies include an environmental annex in their Plans and Orders in accordance with Reference (u).

ADDITIONAL INFORMATION

C1.5.4. Timing for Compliance. This FGS is effective immediately upon approval by USCENTCOM. This FGS is in effect until revoked or superseded.

C1.5.5. USCENTCOM Service Components, major / subordinate commands, and major claimants may issue supplementary criteria that are more protective of the environment than required by the FGS for their subordinates. A copy of all supplementary criteria will be forwarded to through USARCENT (ACEN-OME) to USCENTCOM (CCJ4-E).

C1.5.6. Waivers. A DoD Component may request a waiver of an otherwise applicable criterion in this FGS only if compliance with the criterion at particular installations or facilities would seriously impair their actions, adversely affect relations with Kuwait or would require substantial expenditure of funds for physical improvements at an installation that has been identified for closure or at an installation that has been identified for a realignment that would remove the requirement. Waivers may not be granted to criteria if noncompliance would constitute a breach of applicable U.S. law with extraterritorial effect or applicable international agreements.

C1.5.6.1. A DoD Component seeking a waiver shall:

C1.5.6.1.1. Submit the written request through USARCENT (ACEN-OME) to

USCENTCOM (CCJ4-E);

C1.5.6.1.2. Identify the particular criterion for which a waiver is requested;

C1.5.6.1.3. Describe the extent of the relief requested and the period that the waiver will be in effect;

C1.5.6.1.4. Describe the anticipated impact of the waiver, if any, on human health and the environment over the period of the waiver; and, C1.5.6.1.5. Describe the justification for the waiver and if a complete waiver of the criterion is requested, why a partial and/or temporary deviation would not be sufficient.

C1.5.6.2. Upon receipt of a request for waiver, USCENTCOM shall consult with the relevant CENTCOM Service Components. Where the waiver or deviation is from a standard from Kuwait law or statue, USCENTCOM should normally consult through the appropriate U.S.

Diplomatic Mission (or other agencies established by applicable international agreements) with the responsible host-nation authority.

C1.5.6.3. USCENTCOM may grant or deny the request for waiver in whole, in part, or upon conditions.

C1.5.6.4. If, as a result of consultation with host-nation authorities by the Executive Agent, it is determined that the waiver or deviation from the applicable host-nation standards should not be approved, the DoD Environmental Executive Agent or the DoD Component requesting the waiver may forward the request along with a complete report to the DUSD(ES), who shall attempt to resolve the issue through consultation with relevant authorities and other Federal Agencies as appropriate.

C1.5.6.5. Where the Military Department or Defense Agency requesting the waiver is also the DoD Environmental Executive Agent, the waiver shall be referred to the Unified Combatant Commander for decision.

C1.5.6.6. USCENTCOM or the DUSD(ES), as appropriate, shall maintain a written record of its decision on each waiver requested.

C1.5.7. This FGS does not create any rights or obligations enforceable against the United States, the DoD, or any of its components, nor does it create any standard of care or practice for individuals. Although this FGS refers to other DoD publications, it is intended only to coordinate the requirements of those publications as required to implement the policies found in Reference (a). This FGS does not change other DoD Directives or Instructions or alter DoD policies.

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C2. CHAPTER 2

AIR EMISSIONS

C2.1. SCOPE

This chapter contains standards for air emissions sources. Criteria addressing open burning of solid waste are contained in Chapter 7, “Solid Waste.” Criteria addressing asbestos are contained in Chapter 15, “Asbestos.”

C2.2. DEFINITIONS

C2.2.1. Coal Refuse. Waste products of coal mining, cleanings and coal preparation operations (e.g., culm, gob, etc.) containing coal, matrix material, clay, and other organic and inorganic material.

C2.2.2. Cold Cleaning Machine. Any device or piece of equipment that contains and/or uses liquid solvent, into which parts are placed to remove soils and other contaminants from the surfaces of the parts or to dry the parts. Cleaning machines that contain and use heated, non-boiling solvent to clean the parts are classified as cold cleaning machines.

C2.2.3. Commercial and Industrial Solid Waste Incinerator (CISWI) Units. Any combustion device that combusts commercial and industrial waste in an enclosed device using controlled flame combustion without energy recovery that is a distinct operating unit of any commercial or industrial facility (including field-erected, modular, and custom incineration units operating with starved or excess air). CISWI units do NOT include Municipal Waste Combustor Units, Sewage Sludge Incinerators, Medical Waste Incinerators, and Hazardous Waste Combustion Units.

C2.2.4. Existing Municipal Waste Combustion Unit. Any Municipal Waste Combustion Unit (MWC) unit that is not a “New Municipal Waste Combustion Unit.”

C2.2.5. Existing Steam/Hot Water Generating Unit. Any Steam/Hot Water Generating Unit that is not a “New Steam/Hot Water Generating Unit.”

C2.2.6. Fossil Fuel. Natural gas, petroleum, coal, and any form of solid, liquid or gaseous fuel derived from such material for the purpose of creating useful heat.

C2.2.7. Freeboard Ratio. The ratio of the solvent cleaning machine freeboard height to the smaller interior dimension (length, width, or diameter) of the solvent cleaning machine.

C2.2.8. Hydrofluorocarbon (HFC). A compound consisting of hydrogen, fluorine, and carbon often used as a replacement for Ozone-Depleting Substances (ODS).

C2.2.9. Incinerator. Any furnace used in the process of burning solid or liquid waste for the purpose of reducing the volume of the waste by removing combustible matter, including equipment with heat recovery systems for either hot water or steam generation.

C2.2.10. Motor Vehicle. Any commercially-available vehicle that is not adapted to military use which is self-propelled and designed for transporting persons or property on a street or highway, including but not limited to passenger cars, light duty vehicles, and heavy duty vehicles.

C2.2.11. Municipal Waste Combustion (MWC) Units. Any equipment that combusts solid, liquid, or gasified municipal solid waste (MSW) including, but not limited to, field-erected MWC units (with or without heat recovery), modular MWC units (starved-air or excess-air), boilers (for example, steam generating units), furnaces (whether suspension-fired, grate-fired, mass-fired, air curtain incinerators, or fluidized bed-fired), and pyrolysis/combustion units.

Municipal waste combustion units do NOT include pyrolysis or MWC units located at a plastics or rubber recycling unit, cement kilns that combust MSW, internal combustion engines, gas turbines, or other combustion devices that combust landfill gases collected by landfill gas collection systems.

C2.2.12. Municipal Solid Waste (MSW). Any household, commercial/retail, or institutional waste. Household waste includes material discarded from residential dwellings, hotels, motels, and other similar permanent or temporary housing. Commercial/retail waste includes material discarded by stores, offices, restaurants, warehouses, nonmanufacturing activities at industrial facilities, and other similar establishments or facilities. Institutional waste includes materials discarded by schools, hospitals (nonmedical), nonmanufacturing activities at prisons and government facilities, and other similar establishments or facilities. Household, commercial/retail, and institutional waste does include yard waste and refuse-derived fuel.

Household, commercial/retail, and institutional waste does not include used oil; sewage sludge;

wood pallets; construction, renovation, and demolition wastes (which include railroad ties and telephone poles); clean wood; industrial process or manufacturing wastes; medical waste; or motor vehicles (including motor vehicle parts or vehicle fluff).

C2.2.13. New Municipal Waste Combustion Unit. Any Municipal Waste Combustion Unit (MWC) unit that was constructed or substantially modified since 1 October 1994

C2.2.14. New Steam/Hot Water Generating Unit. Any Steam/Hot Water Generating unit that was constructed or substantially modified since 1 October 1994.

C2.2.15. Ozone-Depleting Substances (ODS). Those substances listed in Table C2.T2.

C2.2.16. Pathological Waste. Waste material consisting of only human or animal remains, anatomical parts, and/or tissue, the bags/containers used to collect and transport the waste material, and animal bedding (if applicable).

C2.2.17. Perfluorocarbon (PFC). A compound consisting solely of carbon and fluorine often used as a replacement for ODS.

C2.2.18. Process Heater. A device that is primarily used to heat a material to initiate or promote a chemical reaction in which the material participates as a reactant or catalyst.

C2.2.19. Pyrolysis. The endothermic gasification of hospital waste and/or medical/infectious waste using external energy.

C2.2.20. Stack. Any point in a source covered by criteria contained in C2.3.1, C2.3.2, C2.3.3, C2.3.4, C2.3.5, and C2.3.9 designed to emit pollutants.

C2.2.21. Steam/Hot Water Generating Unit. A device that combusts any fuel and produces steam or heats water or any other heat transfer medium. This definition does not include nuclear steam generators or process heaters.

C2.2.22. Substantially Modified. Modified in such a way that the project cost exceeds $1 million, regardless of funding source.

C2.2.23. Vapor Cleaning Machine. A batch or in-line solvent cleaning machine that boils liquid solvent generating solvent vapor that is used as a part of the cleaning or drying cycle.

C2.2.24. Wood Residue. Bark, sawdust, slabs, chips, shavings, mill trim, and other wood products derived from wood processing and forest management operations.

C2.3. CRITERIA

C2.3.1. Steam/Hot Water Generating Units

C2.3.1.1. Air Emission Standards. The following criteria apply to new Steam/Hot Water Generating Units with a maximum design heat input capacity greater than or equal to 10 million Btu/hr:

C2.3.1.1.1. Steam/hot water generating units and associated emissions controls, if applicable, must be designed to meet the emission standards for specific sized units shown in Table C2.T1 at all times, except during periods of start up, shut down, soot blowing, malfunction, or when emergency conditions exist.

C2.3.1.1.2. For units combusting liquid or solid fossil fuels, fuel sulfur content (weight percent) and higher heating value will be measured and recorded for each new shipment of fuel. Use this data to calculate sulfur dioxide (SO2) emissions and document compliance with the SO2 limits using the equation in Table C2.T1. Alternatively, install a properly calibrated and maintained continuous emissions monitoring system to measure the flue gas for SO2 and either oxygen (O2) or carbon dioxide (CO2).

C2.3.1.2. Air Emissions Monitoring. Steam/hot water generating units subject to opacity or NOX standards in C2.T1 must have a properly calibrated and maintained continuous emissions monitoring system (CEMS) to measure the flue gas as follows:

C2.3.1.2.1. For units with a maximum design heat input capacity greater than 30 million Btu/hr: Opacity, except that CEMS is not required where gaseous or distillate fuels are the only fuels combusted.

C2.3.1.2.2. For fossil-fuel fired units with a maximum design heat input capacity greater than or equal to 100 million Btu/hr: Nitrogen oxides (NOX) and either oxygen (O2) or carbon dioxide (CO2).

C2.3.2. Incinerators. The following requirements do not apply to incinerators combusting hazardous waste or munitions. Refer to Chapter 6, “Hazardous Waste,” for information regarding hazardous waste disposal and incineration.

C2.3.2.1. Commercial and Industrial Solid Waste Incinerators (CISWI). All CISWI units must comply with the applicable emission standards in Table C2.T3 and operating limits in Table C2.T4.

C2.3.2.2. Municipal Waste Combustion (MWC) Units. Each MWC unit must comply with the applicable emission standards in Table C2.T3 and operating limits in Table C2.T4.

C2.3.2.3. Sewage Sludge Incinerators. All sewage sludge incinerators that commenced construction on or after 1 October 1994 or that undergo substantial modification since 1 October 1994 and that burn more than 1 ton per day (tpd) of sewage sludge or more than 10% sewage sludge, must also be designed to meet a particulate emission limit of 0.65 g/kg dry sludge (1.30 lb/ton dry sludge) and an opacity limit of 20% at all times, except during periods of start up, shut down, malfunction, or when emergency conditions exist.

C2.3.2.4. Medical Waste Incinerators (MWI). The following standards apply to all units.

These requirements do not apply to any portable units (field deployable), pyrolysis units, or units that burn only pathological, low-level radioactive waste, or chemotherapeutic waste. Refer to Chapter 8, “Medical Waste Management,” for other requirements pertaining to medical waste management.

C2.3.2.4.1. All MWI must be designed and operated according to the following good combustion practices (GCP):

C2.3.2.4.1.1. Unit design: dual chamber;

C2.3.2.4.1.2. Minimum temperature in primary chamber: 1400-1600°F;

C2.3.2.4.1.3. Minimum temperature in secondary chamber: 1800-2200°F;

C2.3.2.4.1.4. Minimum residence time in the secondary chamber: 2 seconds; and

C2.3.2.4.1.5. Incinerator operators must be trained in accordance with applicable Service requirements.

C2.3.3. Perchloroethylene (PCE) Dry Cleaning Machines. The following requirements apply to all dry cleaning machines. These requirements do not apply to coin-operated machines.

C2.3.3.1. Emissions from PCE dry cleaning machines installed before 1 October 1994 that use more than 2000 gallons per year of PCE (installation wide) in dry cleaning operations, must be controlled with a refrigerated condenser, unless a carbon absorber was already installed.

C2.3.3.2. All PCE dry cleaning systems installed on or after 1 October 1994 must be of the dry-to-dry design with emissions controlled by a refrigerated condenser. The temperature of the refrigerated condenser must be maintained at 45°F or less. Dry cleaning machines and control devices must be operated according to manufacturer recommendations.

C2.3.4. Chromium Electroplating and Chromium Anodizing Tanks. Electroplating and anodizing tanks must comply with one of the three methods below for controlling chromium emissions. Implement one of the following methods that is most appropriate to suit local conditions:

C2.3.4.1. Option 1: Limit chromium emissions in the ventilation exhaust to 0.015 milligrams per dry standard cubic meter (mg/dscm). Control devices/methods must be operated according to manufacturer recommendations.

C2.3.4.2. Option 2: Use chemical tank additives to prevent surface tension of the electroplating or anodizing bath from exceeding 45 dynes per centimeter (cm) as measured by a stalagmometer or 35 dynes/cm as measured by a tensiometer. Measure the surface tension prior to the first initiation of electric current on a given day and every 4 hours thereafter.

C2.3.4.3. Option 3: Limit chromium emissions to the maximum allowable mass emission rate (MAMER) calculated using the following equation: MAMER = ETSA x K x

0.015 mg/dscm, where: MAMER = the alternative emission rate for enclosed hard chromium electroplating tanks in mg/hr; ETSA = the hard chromium electroplating tank surface area in square feet (ft

); K = a conversion factor, 425 dscm/(ft

-hr). Option 3 is ONLY applicable to hard chrome electroplating tanks equipped with an enclosing hood and ventilated at half the rate or less than that of an open surface tank of the same surface area.

C2.3.5. Halogenated Solvent Cleaning Machines. These requirements apply to all solvent cleaning machines that use solvent which contains more than 5 percent by weight: methylene chloride (CAS No. 75-09-2), perchloroethylene (CAS No. 127-18-4), trichloroethylene (CAS No. 79-01-6), 1,1,1-trichloroethane (CAS No. 71-55-6), carbon tetrachloride (CAS No. 56-23-5), chloroform (CAS No. 67-66-3), or any combination of these halogenated solvents.

C2.3.5.1. All cold cleaning machines (remote reservoir and immersion tanks) must be covered when not in use. Additionally, immersion type cold cleaning machines must have either a 1-inch water layer or a freeboard ratio of at least 0.75.

C2.3.5.2. All vapor cleaning machines (vapor degreasers) must incorporate design and work practices which minimize the direct release of halogenated solvent to the atmosphere.

C2.3.6. Units Containing ODS Listed in Table C2.T2. The following criteria apply to direct atmospheric emissions of ODS, HFCs, and perfluorocarbons (PFC) from refrigeration equipment and ODS from fire suppression equipment.

C2.3.6.1. Refrigerant Recovery/Recycling. All repairs, including leak repairs or services to appliances, industrial process refrigeration units, air conditioning units, or motor vehicle air conditioners, must be performed using commercially available refrigerant recovery/recycling equipment operated by trained personnel. Refrigerant technicians shall be trained in proper recovery/recycling procedures, leak detection, safety, shipping, and disposal in accordance with recognized industry standards or Kuwaiti equivalent.

C2.3.6.2. Refrigerant Venting Prohibition. Any class I or class II ODS, HFC, and PFC refrigerant shall not be intentionally released in the course of maintaining, servicing, repairing, or disposing of appliances, industrial process refrigeration units, air conditioning units, or motor vehicle air conditioners. De minimis releases associated with good faith attempts to recycle or recover ODS, HFC, and PFC refrigerants are not subject to this prohibition.

C2.3.6.3. Refrigerant Leak Monitoring and Repair. Monitor and repair refrigeration equipment for ODS leakage in accordance with the following criteria and repair, if found to be leaking.

C2.3.6.3.1. Commercial Refrigeration Equipment. Commercial refrigeration equipment normally containing more than 50 pounds of refrigerant must have leaks repaired if the appliance is leaking at a rate such that the loss of refrigerant will exceed 35 percent of the total charge during a 12-month period.

C2.3.6.3.2. Industrial Process Refrigeration Equipment. Industrial process refrigeration equipment normally containing more than 50 pounds of refrigerant must have leaks repaired if the appliance is leaking at a rate such that the loss of refrigerant will exceed 35 percent of the total charge during a 12-month period.

C2.3.6.3.3. Comfort Cooling Appliances. Comfort cooling appliances normally containing more than 50 pounds of refrigerant and not covered by subparagraphs C2.3.6.3.1 or C2.3.6.3.2 must have leaks repaired if the appliance is leaking at a rate such that the loss of refrigerant will exceed 15 percent of the total charge during a 12-month period.

C2.3.6.3.4. ODS Fire Suppression Agent (Halon) Venting Prohibition. Halons shall not be intentionally released into the environment while testing, maintaining, servicing, repairing, or disposing of halon-containing equipment or using such equipment for technician training. This venting prohibition does NOT apply to the following halon releases:

C2.3.6.3.4.1. De minimis releases associated with good faith attempts to recycle or recover halons (i.e., release of residual halon contained in fully discharged total flooding fire extinguishing systems).

C2.3.6.3.4.2. Emergency releases for the legitimate purpose of fire extinguishing, explosion inertion, or other emergency applications for which the equipment or systems were designed.

C2.3.6.3.4.3. Releases during the testing of fire extinguishing systems if each of the following is true: systems or equipment employing suitable alternative fire extinguishing agents are not available; release of extinguishing agent is essential to demonstrate equipment functionality; failure of system or equipment would pose great risk to human safety or the environment; and a simulation product cannot be used.

C2.3.7. Motor Vehicles. These criteria apply to DoD-owned motor vehicles as defined in paragraph C2.2.8.

C2.3.7.1. All vehicles shall be inspected every two years to ensure that no tampering with factory-installed emission control equipment has occurred.

C2.3.7.2. If available on the local economy, use only unleaded gasoline in vehicles that are designed for this fuel.

C2.3.8. Stack Heights. Hg is the good engineering practice stack height necessary to minimize downwash of stack emissions due to aerodynamic influences from nearby structures.

Stacks shall be designed and constructed to heights at least equal to the largest Hg calculated from either of the following two criteria:

C2.3.8.1. Hg = H + 1.5L, where H is the height of the nearby structure measured from the ground level elevation at the base of the stack, and L is the lesser of height or projected width of the nearby structure(s). A structure is determined to be nearby when the stack is located within 5L of the structure envelope but not greater than 0.8 km (0.5 mile). This calculation shall be performed for each structure nearby the stack being studied to determine the greatest Hg.

C2.3.8.2. Hg is the height demonstrated by a fluid model or a field study, which ensures that the emissions from a stack do not result in maximum ground-level concentrations of any air pollutant as a result of atmospheric downwash, wakes, or eddy effects created by the source itself, nearby structures, or nearby terrain features at least 40 percent in excess of the maximum ground-level concentrations of any air pollutant experienced in the absence of such atmospheric downwash, wakes, or eddy effects. For purposes of this paragraph, “nearby” means not greater than 0.8 km (0.5 mile), except that the portion of a terrain feature may be considered to be nearby which falls within a distance of up to 10 times the maximum height (Ht) of the feature, not to exceed 2 miles if such feature achieves a height (Ht) 0.8 km from the stack that is at least 40 percent of the good engineering practice stack height determined by the formulae provided in C2.3.8.1. above or 26 meters, whichever is greater, as measured from the ground-level elevation at the base of the stack. The height of the structure or terrain feature is measured from the ground-level elevation at the base of the stack.

C2.3.9. Cement Production

C2.3.9.1. Suspended particulates emitted from cement furnaces shall not exceed 0.15 Kg/ton of product, and opacity of furnace flue gases -- not including opacity from water vapor – shall not exceed 20% more than 3 minutes per hour.

C2.3.9.2. Suspended particulates emitted from cement clinker chillers shall not exceed

0.15 Kg/ton of product, and opacity of flue gases from chiller chimneys shall not exceed 20% more than 3 minutes per hour.

C2.3.10. Storage Tanks

C2.3.10.1. Storage tanks of more than 1,000 barrel capacity that store POL or volatile organic compounds (VOC) shall be designed with external or internal floating roofs.

C2.3.10.2. Storage tanks of more than 1,000 barrel capacity that store POL or VOC with vapor pressure of more than 39 millimeters of mercury (mm Hg) shall have vapor recovery or equivalent system with a consistent seal inspection, repair, and reporting program, provided the available product supply network has facilities for accepting and reprocessing collected vapors.

C2.3.11. Industrial Emission Limits. No industrial operation – which includes steam generating units – shall produce stack gas emissions in excess of the following:

C2.3.11.1. Opacity 20%

C2.3.11.2. Particulate concentration 115 mg/m3

Table C2.T1. Emission Standards for New Steam/Hot Water Generating Units1

Fuel Type Maximum Design Heat Input Capacity

10 – 100 million BTU/hr Size > 100 million BTU/hr

PM Opacity2 SO2 3 PM Opacity2 SO2

3 NOx

Gaseous N/A N/A N/A N/A N/A N/A 0.20

Gaseous – Coal Derived

N/A N/A N/A N/A N/A N/A 0.50

Liquid Fossil Fuel

N/A 20% 0.505 0.10 20% 0.80 0.30

Solid Fossil Fuel

0.10 20% 1.20 0.10 20% 1.20 0.70

Other Solid Fuel6

0.30 20% N/A 0.20 20% N/A N/A

NOTES:

N/A = Not applicable

1. Standards do not apply during periods of startup, shutdown, malfunction, soot blowing, or when emergency conditions exist. Unless specified otherwise, emission standards are in lb/million BTU.

2. The opacity standards do not apply to units < 30 million BTU/hr. The 20% standard applies to the average opacity over a six-minute period.

3. SO2 is best controlled and compliance documented by limiting fuel sulfur content.

SO2 emissions (lb/ million BTU) = 0.02 X sulfur content of fuel (%) / heat content of fuel (HHV, million BTU/lb fuel).

[E.g., for fuel oil with 0.5% sulfur, SO2 = 0.02 X 0.5 / 0.019 = 0.53 lb/million BTU.]

4. Emission limitation for NOX is based on a 30-day rolling average. NOX standard does not apply when a fossil fuel containing at least 25% by weight of coal refuse is burned in combination with gaseous, liquid, or other solid fossil fuel.

5. Instead of 0.5 lb/ million BTU of SO2, fuel oil combustion units may comply with a 0.5% average fuel sulfur content limit (weight percent) which is statistically equivalent to 0.5 lb/million BTU.

6. Other solid fuels include wood or waste derived fuels.

Table C2.T2. Class I and II Ozone-Depleting Substances

Class I

CFC-11 CFC- 114 CFC- 215 Halon – 1211

CFC-12 CFC- 115 CFC- 216 Halon – 1301

CFC-13 CFC- 211 CFC- 217 Halon – 2402

CFC- 111 CFC- 212 Carbon Tetrachloride

CFC- 112 CFC- 213 Methyl Chloroform

CFC- 113 CFC- 214 Methyl Bromide

CHFBr2 C2H2F3Br C3HF6Br C3H3F4Br

HBFC-2201

(CHF2Br)

C2H3FBr2 C3H2FBr5 C3H4FBr3

CH2FBr C2H3F2Br C3H2F2Br4 C3H4F2Br2

C2HFBr4 C2H4FBr C3H2F3Br3 C3H4F3Br

C2HF2Br3 C3HFBr6 C3H2F4Br2 C3H5FBr2

C2HF3Br2 C3HF2Br5 C3H2F5Br C3H5F2Br

C2HF4Br C3HF3Br4 C3H3FBr4 C3H6FBr

Table C2.T2. Class I and II Ozone-Depleting Substances (continued)

C2H2FBr3 C3HF4Br3 C3H3F2Br3 Chlorobromomethane

C2H2F2Br2 C3HF5Br2 C3H3F3Br2

Class II

HCFC - 21 HCFC –

133a

HCFC –

225cb

HCFC - 243

HCFC - 22 HCFC –

141b

HCFC – 226 HCFC - 244

HCFC - 31 HCFC –

142b

HCFC - 231 HCFC – 251

HCFC - 121 HCFC - 151 HCFC - 232 HCFC – 252

HCFC - 122 HCFC - 221 HCFC - 233 HCFC – 253

HCFC - 123 HCFC - 222 HCFC - 234 HCFC – 261

HCFC - 124 HCFC - 223 HCFC - 235 HCFC – 262

HCFC - 131 HCFC - 224 HCFC - 241 HCFC – 271

HCFC -

132b

HCFC -

225ca

HCFC - 242

Note: All isomers of the above chemicals are ODS, except isomers of (1,1,1-trichloroethane (also known as methyl chloroform)) such as 1,1,2-trichloroethane.

Table C2.T3. Emission Standards for Incinerators1

Pollutant Emission Standards

Incinerator Type

Existing Municipal Waste Combustion Units

New Municipal Waste Combustion Units CISWI Units

Rated Capacity 35-250 tpd > 250 tpd 35-250 tpd > 250 tpd All units

Particulate 70 mg/dscm 27 mg/dscm 24 mg/dscm 70 mg/dscm

Opacity 10 percent 10 percent 10 percent

NOx N/A See Note 2 500 ppmv 150ppmv 388 ppmv

SO2 50% reduction or 77 ppmv

75% reduction or 29 ppmv

80% reduction or 30 ppmv 20 ppmv

Dioxins/furans 125…