Attachment 6 - Eastern-Southern Europe-Israel Renewal - Final Governing Standard - Romania (Sep 2019) - 28 July 2020.pdf

Final

Environmental Final Governing Standards

ROMANIA

September 2019

CNREURAFSWA Environmental PSC 817 Box 108

FPO AE 09622‐0108

+39 081 568‐2886

Attachment 6

FGS – Romania Table of Contents i September 2019

1 OVERVIEW 1-1

2 AIR EMISSIONS 2-1

3 DRINKING WATER 3-1

4 WASTEWATER 4-1

5 HAZARDOUS MATERIAL 5-1

6 HAZARDOUS WASTE 6-1

7 SOLID WASTE 7-1

8 MEDICAL WASTE MANAGEMENT 8-1

9 PETROLEUM, OIL, AND LUBRICANTS 9-1

11 PESTICIDES 11-1

12 HISTORIC AND CULTURAL RESOURCES 12-1

13 NATURAL RESOURCES AND ENDANGERED SPECIES 13-1

14 POLYCHLORINATED BIPHENYLS 14-1

15 ASBESTOS 15-1

17 LEAD-BASED PAINT 17-1

18 SPILL PREVENTION & RESPONSE PLANNING 18-1

19 UNDERGROUND STORAGE TANKS 19-1

APPENDIXES

AP1 LIST OF HAZARDOUS WASTE/SUBSTANCES/MATERIALS

AP2 DETERMINATION OF WORST CASE DISCHARGE PLANNING VOLUME

FGS – Romania Chapter 1, Overview

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CHAPTER 1 − OVERVIEW

C1.1. PURPOSE

The primary purpose of this Final Governing Standards (FGS) document is to provide specific standards for environmental compliance criteria at United States (U.S.) Department of Defense (DoD) installations in Romania. This document implements DoD Instruction 4715.05, Environmental Compliance at Installations Outside the United States, dated 1 November 2013 (incorporating Changes 1 and 2, dated October 5, 2017 and August 31, 2018, respectively), and is based upon DOD 4715.05-G, Overseas Environmental Baseline Guidance Document (OEBGD), dated 1 May 2007 (Incorporating Change 1, August 31, 2018).

C1.2. APPLICABILITY

C1.2.1. This document provides specific standards for environmental compliance criteria applicable for actions by DoD Components at installations located in Romania.

C1.2.2. This document represents minimum criteria; DoD Components may impose additional criteria provided those policies and directives do not conflict with this document.

C1.2.3. Activities and installations shall notify the DoD Lead Environmental Component (LEC) for Romania of any conflicting DoD Component policies or directives they discover prior to imposing criteria more protective than provided in the FGS.

C1.2.4. DoD Components shall not enter into agreements with the Romanian authorities at any level that establishes a criterion for environmental compliance that contradicts those provided in this document without the prior written approval of the LEC.

C1.3. EXEMPTIONS. These standards do 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 the DoD does not control the instrumentality or operation that a criterion seeks to regulate.

C1.3.3. Operations of U.S. military vessels 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 U.S. 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 (DoDDs) and DoD Instructions (DoDIs), and environmental annexes incorporated into operation plans or operation orders. However, this document applies to support functions for U.S. military vessels and U.S. military aircraft provided by the DoD Components, including management or disposal of off-loaded waste or material.

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C1.3.4. Facilities and activities associated with the Naval Nuclear Propulsion Program, which are covered under Executive Order (E.O.) 12344, Naval Nuclear Propulsion Program, and conducted pursuant to 42 United States Code (U.S.C.) 7158. The determination or conduct of remediation to correct environmental problems caused by the Department of Defense's past activities, conducted in accordance with DoD Instruction (DoDI) 4715.08.

C1.3.5. The determination or conduct of remediation to correct environmental problems caused by the Department of Defense's past activities.

C1.3.6. Environmental analyses conducted under E.O. 12114, Environmental Effects Abroad of Major Federal Actions.

C1.4. DEFINITIONS. For purposes of this document, unless otherwise indicated, the following definitions apply:

C1.4.1. Criteria and Management Practices. Particular substantive provisions of the OEBGD that are used by the LEC to develop this document.

C1.4.2. Existing Facility. Any facility and/or building, source, or project in use or under construction before 1 October 1994, unless it is subsequently substantially modified.

C1.4.3. Final Governing Standards. A comprehensive set of country-specific substantive provisions, typically technical limitations on effluent, discharges, etc., or a specific management practice.

C1.4.4. New Facility. Any facility and/or building, source, or projects with a construction start date on or after 1 October 1994, or a pre-existing facility that has been substantially modified since 1 October 1994.

C1.4.5. Romanian Designated Authority. Romanian individual or organization designated by a Romanian authority to obtain a required authorization on behalf of the US.

C1.4.6. Substantial Modification. Any modification to a facility and/or building the cost of which exceeds $1 million, regardless of funding source.

C1.5. ADDITIONAL INFORMATION

C1.5.1. The DoD Components shall establish and implement an environmental audit program to ensure that overseas installations assess compliance with this document at least once every 3 years at all major installations.

C1.5.2. DoDI 4715.23, Integrated Recycling and Solid Waste Management, implements policy, assigns responsibility, and prescribes procedures for implementation of pollution prevention programs throughout the DoD. As a matter of DoD policy, DoDI 4715.23 should be consulted for particular criteria. Pollution prevention should be considered in developing the criteria and management practices for FGS. Where economically advantageous and consistent with mission criteria, pollution prevention shall be the preferred means for attaining compliance

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C1.5.3. Laboratory analyses necessary to implement this document would normally be conducted in a laboratory that has been certified by a U.S. or Romanian regulatory authority for the applicable test method. In the absence of a certified laboratory, analyses may also be conducted at a laboratory that has an established reliable record of quality assurance/quality control compliance with standards for the applicable test method that are generally recognized by appropriate industry or scientific organizations, such as ISO 17025.

C1.5.4. This document 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 these FGS refer to other DoDDs and DoDIs, it is intended only to coordinate the criteria of those directives as required to implement the policies found in DoDI

4715.05. This document does not change other DoD or service directives or instructions, or alter DoD policies.

C1.6. EXCEPTIONS The DoD Component may request an exception to a particular standard in this document IAW DoDI 4715.05, Enclosure 3, paragraph 7.

C1.7. AUTHORIZATIONS

C1.7.1. Formal interaction or interaction of common interest between the US and Romania, on environmental activities, shall be conducted with the cognizance of the Romanian Installation Commander (RIC), Romania/US Joint Environmental Subcommittee (RUS JESC) and the LEC.

C.1.7.2. The DoD Components shall not directly obtain authorizations (including, but not limited to licenses and permits) from Romanian authorities. DoD Components shall contact the LEC to determine approval process and criteria for the authorization. If an authorization is required, DoD Components will assist the Romanian Designated Authority by providing reports, records, or other documentation needed to obtain the authorization.

C1.7.3. If the Romanian authorities obtain an authorization on behalf of the DoD Component and the authorization specifies a more protective standard than prescribed in the FGS, the standard in the approval shall be the compliance standard. However, if an approval allows a less protective standard, then the FGS will be the compliance standard unless an exception is obtained (see C1.6).

C1.7.4. Contractors performing work for DoD on DoD installations shall comply with all Romanian laws and regulations, including obtaining all necessary licenses and approvals.

Contracting services does not absolve DoD Components from compliance with this document unless exempted under section C1.3.

C1.8. WORKING WITH THE LEC

C1.8.1. DoD Components shall consult with the LEC when specified in this document and when:

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C1.8.1.1. Significant exceedances of FGS or approval criteria occur.

C1.8.1.2. Romanian enforcement action is initiated.

C1.8.1.3. An issue is raised that has the potential to affect multiple installations or military services.

C1.8.2. DoD Components shall notify the LEC when specified in this document and when:

C1.8.2.1. Information is provided to RIC or RUS JESC for activities requiring approval, as governed by this document.

C1.8.2.2. RIC, RUS JESC, or other Romanian official requests information.

C1.8.2.3. Any Romanian official requests access to an installation in order to conduct an environmental inspection.

C1.8.3. The LEC, working with the notifying DoD Component, may determine notification specified in this document is no longer required on a case-by-case basis.

C1.9. ACCESS TO INSTALLATIONS & INFORMATION BY ROMANIAN AUTHORITIES.

Inspections and non-routine requests for information by Romanian authorities shall be coordinated with the RIC, RUS JESC, and the LEC via the DoD Component chain-of-command.

To the maximum extent possible, U.S. military personnel, rather than civilian personnel, should lead the review of DoD Component activities by Romanian authorities during the inspection.

C1.10. LEAD ENVIRONMENTAL COMPONENT (LEC). The DoD LEC for Romania is the Commander, Navy Region Europe, Africa, Southwest Asia. However, the point of contact for the LEC is N40/CNREURAFSWA. Any questions or comments pertaining to this document shall be sent to:

CNREURAFSWA/N40

Commander, Navy Region Europe Africa Southwest Asia PSC 817 Box 108

FPO AE 09622

DSN Voice (314) 626-2886 Commercial +39 081-568-2886

FGS – Romania Chapter 2, Air Emissions

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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

Coal Refuse. Waste products from coal mining, cleaning, and coal preparation operations (e.g., culm and gob) containing coal, matrix material, clay, and other organic and inorganic material.

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

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.

Fluorinated Gases. The family of man-made gases used in a range of industrial applications as substitutes for ozone-depleting substances (ODSs). F-gases are considered greenhouse gases. They include the following groups (including isomers and mixtures that may contain one of these compounds): chlorofluorocarbons (CFCs), halons, hydrobromofluorocarbons (HBFCs), hydrochlorofluorocarbons (HCFC), bromochloromethane (BCM), hydrofluorocarbons (HFCs), perfluorocarbons (PFCs), and sulfur hexafluoride (SF6).

Common F-gases are listed with ODS compounds in Table C2.T5.1 and with greenhouse gases in Table C2.T6.

C2.2.5. 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.

C2.2.6. 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.

C2.2.7. Hydrofluorocarbon (HFC). A compound consisting of hydrogen, fluorine, and carbon often used as a replacement for Ozone-Depleting Substances (ODS).

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C2.2.8. 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.

C2.2.9. Leak Detection System. A calibrated mechanical, electrical, or electronic device for detecting leaks of fluorinated greenhouse gases which, on detection, alerts the operator.

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. Ozone-Depleting Substances (ODS). Those substances listed in Table C2.T5.1.

C2.2.14. 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).

C2.2.15. Perfluorocarbon (PFC). A compound consisting solely of carbon and fluorine often used as a replacement for ODS.

C2.2.16. 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.

C2.2.17. Pyrolysis. The endothermic gasification of hospital waste and/or

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C2.2.18. Recovery. The collection and the storage of controlled substances or F-gases from for example, machinery, equipment, and containment vessels during service or before disposal.

C2.2.19. Recycling. The reuse of a recovered controlled substance or F-gases following a basic cleaning process, such as filtering and drying. For ODS refrigerants, recycling normally involves recharge back into equipment and is often carried out onsite.

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., or C2.3.6. 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. Any modification to a facility/building, the cost of which 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 which generates solvent vapor that is used as a part of the cleaning or drying cycle.

C2.2.24. Volatile Organic Compound (VOC). Any organic compound having a vapor pressure ≥ 0.01 kilopascal at a temperature of 293.15 °K (20 °C) or having a corresponding volatility under the particular conditions of use. The fraction of creosote which exceeds this value of vapor pressure at 293.15°K (20°C) shall also be considered a VOC.

C2.2.25. 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. All installations with steam/hot water-generating units of any size using standard or waste fuels, shall contact the DoD Lead Environmental Component (LEC) to determine compliance and permitting criteria. If a permit is received, the installations shall adhere to the conditions of the permit. However, if the permit conditions require a less protective standard than the emission standards prescribed in this section, this Final Governing Standards (FGS) shall be the compliance criteria. Additionally, if there are no permitting requirements, the following standards apply to units that commenced construction on or after 1 October 1994 or that were substantially modified since 1 October 1994.

C2.3.1.1. Air Emission Standards. The following criteria apply to units with a maximum design heat input capacity greater 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

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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 %) and higher heating value will be measured and recorded for each new shipment of fuel. Use these 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 nitrogen oxides (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 100 million Btu/hr: NOX and either O2 or CO2.

C2.3.2. Incinerators. All installations with incinerators of any size shall contact the LEC to determine compliance and permitting criteria. If a permit is received, the installations shall adhere to the conditions of the permit. However, if the permit conditions require a less protective standard than the emissions standards prescribed in this section, this FGS shall be the compliance criteria. Additionally, if there are no permitting requirements, this FGS shall be the compliance criteria. 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 units must comply with the applicable emission standards in Table C2.T2. and operating limits in Table C2.T3.

C2.3.2.2. Municipal Waste Combustion (MWC) Units. Each MWC unit must comply with the applicable emission standards in Table C2.T2. and operating limits in Table C2.T3.

C2.3.2.3. Sewage Sludge Incinerators. All sewage sludge incinerators that commenced construction on or after 1 October 1994 or that were substantially modified since 1 October 1994 and that burn > 1 ton per day (tpd) of sewage sludge or > 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

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C2.3.2.4.1. All MWI shall 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: 1400-1600oF (760 –

871°C).

C2.3.2.4.1.3. Minimum temperature in secondary chamber: 1800-2200°F (982 –

1,204.4°C)

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

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

C2.3.3. Dry Cleaning Using Volatile Organic Compounds. All installations with dry cleaning operations involving the use of VOCs must contact the LEC to determine permitting requirements. All dry-cleaning machines using VOCs to clean garments, furnishings, and similar consumer goods must meet the emission limit values of 20 g (0.7 oz) of solvent emitted per 1 kg (2.2 lb) of product (i.e., clothes, furniture, consumer goods) cleaned and dried within the machine.

C2.3.4. Perchloroethylene (PCE) Dry Cleaning Machines. The following requirements apply to all PCE dry cleaning machines. These requirements do not apply to coin-operated machines.

C2.3.4.1. Emissions from PCE dry cleaning machines installed before 1 October 1994 that use > 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. The temperature of the refrigerated condenser must be maintained at 45°F (7°C) or less. Dry cleaning machines and control devices must be operated according to manufacturer recommendations.

C2.3.4.2. 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 (7°C) or less. Dry cleaning machines and control devices must be operated according to manufacturer recommendations.

C2.3.5. 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 are most appropriate to suit local conditions:

C2.3.5.1. 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.

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C2.3.5.2. 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.

C2.3.5.3. 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 (ft2); K = a conversion factor, 425 dscm/(ft2-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.

C2.3.6. Halogenated Solvent Cleaning Machines. Facilities exceeding the solvent consumption thresholds of Table C2.T4 shall meet the emissions limits found in Table C2.T4 and contact the LEC to determine permitting requirements. If a permit is obtained and the emissions limits are more stringent than those found in Table C2.T4, the installation shall adhere to the conditions of the permit.

C2.3.6.1. Additionally and unless a more stringent permit condition exists, these requirements apply to all solvent cleaning machines that use solvent which contains > 5% 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.

C2.3.6.1.1. 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.

C2.3.6.2.2. All vapor cleaning machines (vapor degreasers) must incorporate design and work practices which minimize the direct release of halogenated solvent to the atmosphere.

C2.3.7. Units Containing ODS Listed in Table C2.T5.1 with Uses and Prohibitions. The following criteria apply to direct atmospheric emissions of ODS, HFCs, and perfluorocarbons (PFC) from refrigeration equipment and ODS from fire suppression equipment.

C2.3.7.1. Maintenance or servicing of products and equipment containing the ODSs listed in Table C2.T5.1 is prohibited, with the exception of those uses listed in paragraphs C2.3.7.1.1 and C2.3.7.1.2. Running an existing system (e.g., using a refrigerator) would not be classified as maintaining or servicing.

C2.3.7.1.1. Allowed Use of ODSs. ODSs listed in Table C2.T5.1 can be used as a feedstock, a process agent where emissions are insignificant, and for essential laboratory and analytical uses. Use of any of these ODSs other than HCFCs for laboratory use shall be reported to the LEC.

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C2.3.7.1.2. Allowed Use of Methyl Bromide. Methyl bromide may be used for quarantine and pre-shipment applications. Methyl bromide may also be used in an emergency where unexpected outbreaks of particular pests or diseases so require. Consult with the LEC prior to emergency use.

C2.3.7.2. Refrigerant Recovery/Recycling. All repairs, including leak repairs or services to equipment, 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. Operators shall be trained in proper recovery/recycling procedures, leak detection, safety, shipping, and disposal in accordance with recognized industry standards or Romanian equivalent.

C2.3.7.3. Refrigerant Venting Prohibition. Any class I or class II ODS, HFC, PFC and F-gas refrigerant, identified in Tables C2.T5.1. and C2.T6 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, PFC and F-gas refrigerants are not subject to this prohibition.

C2.3.7.4. General ODS Refrigerant (Table C2.T5.1.) and F-gas (Table C2.T6) Leak

Monitoring and Repair. Monitor and repair equipment in accordance with the following criteria and repair, if found to be leaking.

C2.3.7.4.1. Equipment containing 3 kg (6.6 lb) or more of ODS refrigerant or 5 tons of CO2 equivalent charge of F-gases shall be checked for leaks at least once every 12 months.

This shall not apply to equipment with Hermetically Sealed Systems, which are labeled as such and contain < 6 kg (13.2 lb) of ODS or 10 tonnes of CO2 equivalent charge of Fluorinated Greenhouse Gases (see the notes of Table C2.T6 to determine tonnes of CO2 equivalent).

C2.3.7.4.2. Equipment containing 30 kg (66 lb) or more of ODS refrigerant or 50 tonnes of CO2 equivalent charge of F-gases shall be checked for leaks at least once every 6 months (see the notes of Table C2.T6 to determine tonnes of CO2 equivalent).

C2.3.7.4.3. Equipment containing 300 kg (660 lb) or more of ODS refrigerant or F-gases shall be checked for leaks at least once every 3 months (see the notes of Table C2.T6 to determine tonnes of CO2 equivalent).

C2.3.7.4.4. Installations operating equipment containing 500 tonnes of CO2 equivalent charge or more of F-gases, shall install Leak Detection Systems. The Leak Detection Systems on equipment containing F-gases shall be checked at least once every 12 months to ensure proper functioning.

C2.3.7.4.5. Where a properly functioning appropriate Leak Detection System is in place on equipment containing Fluorinated Greenhouse Gases, the frequency of the checks required under C2.3.7.4.2 and C2.3.7.4.3 shall be halved.

C2.3.7.4.6. All equipment shall be checked for leaks within one month after a leak has been repaired to ensure that the repair has been effective.

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C2.3.7.5. Additional Leak Monitoring and Repair for F-gas (Table C2.T6) Fire

Protection Systems. Installations must monitor fire protection systems containing 3 kg (6.6 lb) or more of F-gases and repair any leaks according to the following criteria:

C2.3.7.5.1. Pressure gauges and weight-monitoring devices shall be checked once every 12 months to ensure proper functioning.

C2.3.7.5.2. A leak test shall be performed prior to recharging of equipment.

C2.3.7.5.3. Newly installed fire protection systems shall be checked for leaks immediately after they have been placed into service.

C2.3.7.6. Additional Leak Monitoring and Repair for F-gas (Table C2.T6) Heating and Cooling Systems. Leak monitoring and repair of working and temporarily out of operation stationary refrigeration, air conditioning, and heat pump equipment containing 3 kg (6.6 lb) or more of F-gases, shall meet the following criteria:

C2.3.7.6.1. Prior to any repair, a pump-down or recovery shall be carried out, where necessary.

C2.3.7.6.2. A leak test with Oxygen-Free Nitrogen (OFN) or another suitable pressure testing and drying gas shall be carried out where necessary, followed by evacuation, recharge and leak-test.

C2.3.7.6.3. Before pressure testing, F-gases shall be recovered from the appliance, where necessary.

C2.3.7.6.4. The cause of any leak shall be identified to the extent possible, to avoid recurrence.

C2.3.7.6.5. Newly installed refrigeration, air conditioning, and heat pump equipment shall be checked for leaks immediately after they have been placed into service.

C2.3.7.7. ODS Refrigerant (Table C2.T5.1.) and F-gas (Table C2.T6) Recovery.

C2.3.7.7.1. Technicians must ensure the proper recovery of ODS refrigerant or F-gases from refrigeration, air-conditioning, and heat pump equipment, equipment containing solvents, fire protection systems, fire extinguishers, and high-voltage switchgear prior to its disposal and, when appropriate, during its servicing and maintenance.

C2.3.7.7.2. ODS refrigerants and F-gases contained in other products and equipment not listed in C2.3.8.6.1 shall, to the extent that it is technically feasible and does not entail disproportionate cost, be recovered to ensure their recycling, reclamation, or destruction prior to its disposal and, when appropriate, during its servicing and maintenance.

C2.3.7.7.3. When a F-gas container used for transport or storage purposes reaches the end of its life, ensure the proper recovery of any residual gases it contains.

2-9 September 2019

C2.3.7.8. ODS Refrigerant (Table C2.T5.1.) and F-gas (Table C2.T6) Record

Keeping. Operators of stationary refrigeration, air conditioning, and heat pump equipment including circuitry, and fire protection systems containing 3 kg (6.6 lb) or more of ODS or 5 tonnes of CO2 equivalent charge of F-gases, shall maintain records on the quantity and type of ODS or F-gases installed, any quantities added, and the quantity recovered during servicing, maintenance, and final disposal.

C2.3.7.8.1. For all ODS and F-gas systems, installations shall maintain relevant information, including identification of the company and/or technician performing the service or maintenance and the dates and results of checks carried out to comply with C2.3.7.4.

C2.3.7.8.2. For F-gas systems containing 5 tonnes or more of CO2 equivalent charge of F-gases, installations shall also maintain the following information in the records:

C2.3.7.8.2.1. Information on whether the F-gases installed in a system were recovered or recycled, to include the source of these gases.

C2.3.7.8.2.2. If a system is being decommissioned, information on the measures taken to recover and dispose of the F-gases.

C2.3.7.8.2.3. The F-gas charge for a fire protection system, refrigeration, air conditioning or heat pump equipment.

C2.3.7.8.3. These records shall be retained for at least 5 years, and made available to the Romanian Installation Commander upon request.

C2.3.7.9. ODS Fire Suppression Agent (Halon) Venting Prohibition. Critical uses of halon, as indicated in Table C2.T7, are permitted until the date specified in Table C2.T7 for each category. The systems must be decommissioned by the listed end dates. All other uses of halon are banned. 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 permitted halon releases:

C2.3.7.9.1. 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 suppression systems).

C2.3.7.9.2. Emergency releases for the legitimate purpose of fire extinguishing, explosion, or other emergency applications for which the equipment or systems were designed.

C2.3.7.9.3. 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 simulant agent cannot be used.

2-10 September 2019

C2.3.7.10. Mobile Air Conditioners

C2.3.7.10.1. Prior to mobile air conditioner disposal, and when appropriate during servicing and maintenance, F-gases contained in air conditioners in mobile equipment shall be recovered to ensure their proper recycling, reclamation, or destruction where it is technically feasible and does not entail disproportionate costs.

C2.3.7.10.2. When servicing and repairing air conditioning systems on vehicles, technicians shall not fill equipment with F-gases if an abnormal amount of the refrigerant has leaked from the system, until the necessary repairs have been completed.

C2.3.7.11. New Substances listed in Table C2.T5.2. Maintenance or servicing of products and equipment containing the new substances listed in Table C2.T5.2 is prohibited other than use as a feedstock or for laboratory and analytical purposes. Running an existing system (e.g., using a refrigerator) would not be classified as maintenance or servicing.

C2.3.7.12. Pending F-gas Restrictions. Unrestricted use of fluorinated greenhouse gases as refrigerants may continue until 2020. Beginning 1 January 2020, use of virgin gases with a Global Warming Potential (GWP) (Table C2.T6) over 2,500 is prohibited in refrigeration units containing a charge size of 40 tonnes of CO2 equivalent, or more. Use of reclaimed or recycled F-gases with a GWP over 2,500 may continue until 2030, provided the refrigerant is recovered or recycled from similar equipment.

C2.3.8. Motor Vehicles. This criterion applies to DoD-owned motor vehicles as defined in criteria C2.2.10.

C2.3.8.1. All vehicles shall be inspected every two years to ensure that no tampering with factory-installed emission control equipment has occurred.

C2.3.8.2. If available on the local economy, use only unleaded gasoline in vehicles that are designed for this fuel.

C2.3.9. Stack Heights. Hg is the good engineering practice stack height necessary to minimize downwash of stack emissions due to aerodynamic influences from nearby structures.

C2.3.9.1. Stacks shall be designed and constructed to heights at least equal to the largest

Hg calculated from either of the following two criteria:

C2.3.9.1.1. 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.

C2.3.9.1.2. 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% in excess of the maximum

2-11 September 2019 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 >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 3.2 km (2 miles) if such feature achieves a height (Ht) 0.8 km (0.5 mile) from the stack that is at least 40% of the good engineering practice stack height determined by the formulae provided in

2.3.8.1.1. of this part or 26 meters (85 feet), 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.

Table C2.T1. Emission Standards for Steam Generating Unitsa

Fuel Type

Maximum Design for Steam Input Capacity

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

PM Opacity b SO2 c PM Opacity b SO2 c NOX d Gaseous N/A N/A N/A N/A N/A N/A 0.2 Gaseous—coal derived N/A N/A N/A N/A N/A N/A 0.5

Liquid fossil fuel N/A 20% 0.50e 0.1 20% 0.8 0.3 Solid fossil fuel 0.1 20% 1.2 0.1 20% 1.2 0.7 Other solid fuel (f) 0.3 20% N/A 0.2 20% N/A N/A

N/A = Not applicable.

a. Standards apply to units constructed or substantially modified after 1 October 1994. 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.

b. 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. A 30% opacity value is allowed for one six-minute period per hour.

c. 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.]

d. 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.

e. 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 %) which is statistically equivalent to 0.5 lb/million BTU.

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

2-12 September 2019

Table C2.T2. Emission Standards for Incinerators

Pollutant OEBGD Emission Standards1

Incinerator type Existing MWC units2

MWC units that begin new construction or undergo substantial modification2

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 % 10 % 10 % NOx N/A See Note 3 500 ppmv 150 ppmv 388 ppmv

SO2

50% reduction or

77 ppmv 75% reduction or

29 ppmv 80% reduction or 30 ppmv 20 ppmv

Dioxins/fur ans 125 ng/dscm See Note 4 13 ng/dscm 0.41 mg/dscm

Cadmium 0.10 mg/dscm 0.040 mg/dscm 0.020 mg/dscm 0.004 mg/dscm

Lead 1.6 mg/dscm 0.44 mg/dscm 0.20 mg/dscm 0.04 mg/dscm

Mercury 85% reduction or 0.080 mg/dscm 85% reduction or 0.080 mg/dscm 0.47 mg/dscm

HCl 50% reduction or 250 ppmv

95% reduction or 29 ppmv

80% reduction or 30 ppmv

95% reduction or 25 ppmv 62 ppmv

Fugitive Ash 5% of hourly observation period 5% of hourly observation period N/A

Notes:

1 Emission standard concentrations (mg/dscm, ppmv) are corrected to 7% oxygen, dry basis at standard conditions.

mg/dscm = milligram per dry standard cubic meter, ng = nanogram, ppm = parts per million.

2 Construction or modifications that were undertaken pursuant to existing (or previous) FGS are not subject to these requirements. These criteria are not intended to require retrofitting of MWC units.

3 NOx limits for units rated > 250 tons/day (tpd) capacity: mass burn refractory-no limit; mass burn waterwall-205 ppmv; mass burn rotary waterwall: 250 ppmv; refuse-derived fuel combustor-250 ppmv; fluidized bed combustor- 180 ppmv.

4 Dioxins/furans limits for units rated >250 tpd capacity: MWC with electrostatic precipitator (ESP)-60 ng/dscm;

MWC with non-ESP-30 ng/dscm.

2-13 September 2019

Table C2.T3. Carbon Monoxide Operating Limits for Incinerators1

Incinerator Type Existing MWC units2 MWC units that begin new construction or undergo substantial modification2

CISWI

units All units

Rated Capacity 35-250 tpd 35-250 tpd 35-252 tpd >250 tpd All Fluidized bed 100 ppmv (4-hr avg) 100 ppmv (4-hr avg) ppmv

Fluidized bed, mixed fuel, (wood/refuse-derived fuel) 200 ppmv (24-hour average) 200 ppmv (24-hr avg) 100 ppmv (4-hr avg)

Mass burn rotary refractory 100 ppmv (4-hr avg)

100 ppmv (24-hr avg) 100 ppmv (24-hr avg)

Mass burn rotary waterwall 250 ppmv (24-hr avg) 100 ppmv (24-hr avg) Mass burn waterwall and refractory 100 ppmv (4-hr avg) 100 ppmv (4-hr avg)

Mixed fuel-fired, (pulverized coal/rerfuse-derived fuel) 150 ppmv (4-hr avg) 150 ppmv (4-hr avg)

Modular starved-air and excess air 50 ppmv (4-hr avg) 50 ppmv (4-hr avg)

Spreader stoker, mixed fuel-fired (coal/refuse-derived fuel

200 ppmv (24-hr avg) 150 ppmv (24-hr avg)

Stoker, refuse-derived fuel 200 ppmv (24-hr avg) 150 ppmv (24-hr avg) Notes:

1 Emission standard concentrations (mg/dscm, ppmv) are corrected to 7% oxygen, dry basis at standard conditions.

mg/dscm = milligram per dry standard cubic meter, ng = nanogram, ppm = parts per million.

2 Construction or modifications that were undertaken pursuant to existing (or previous) FGS are not subject to these requirements. These criteria are not intended to require retrofitting of MWC units.

3 NOx limits for units rated > 250 tons/day (tpd) capacity: mass burn refractory-no limit; mass burn waterwall-205 ppmv; mass burn rotary waterwall: 250 ppmv; refuse-derived fuel combustor-250 ppmv; fluidized bed combustor- 180 ppmv.

4 Dioxins/furans limits for units rated >250 tpd capacity: MWC with electrostatic precipitator (ESP)-60 ng/dscm;

MWC with non-ESP-30 ng/dscm.

2-14 September 2019

Table C2.T4. Air Emission Limits for Specific Operations Using VOCs 1

Activity Solvent consumption threshold (metric tonnes/year) 2

Emission limit values in waste gases (mg C/Nm3)

Fugitive emission values (% of solvent input)

Total Emission Limit Values

(g/kg)6

Surface cleaning 1-5 20 4 15 4 - > 5 10 4 -

Other surface cleaning 2-10 75 3 20 4 - > 10 15 4 -

Vehicle refinishing > 0.5 50 25 - Dry cleaning - - - 20 5

Coating 5-15 100 7 25 7 -

>15 50 (drying) 7 75 (coating) 7 20 7 -

Notes:

1 These limits apply to stationary technical units with exhaust stacks to remove waste gases. They do not apply to operations that are mobile.

2 One metric ton is equal to 2,205 pounds.

3 Using substances or preparations that are classified as: Carcinogenic, mutagenic or toxic to reproduction (R45, R46, R49, R60, R6) because of their VOC contents;

4 R40 for halogenated substances (R40 - Possible risks of irreversible effects.).

5 Limit refers to mass of compounds in milligrams per normal cubic meter (mg C/Nm3), and not total carbon.

6 Facilities that demonstrate their average organic solvent content of all cleaning material used does not exceed 30% by weight are exempt from these values.

7 Mass of solvent (measured in g) emitted per kg of product cleaned and dried.

g/kg = grams per kilogram Coating activities that cannot be applied under contained conditions (e.g. shipbuilding, aircraft painting) may be exempted from these values.

2-15 September 2019

Table C2.T5.1. Class I and II Ozone-Depleting Substances

Class I (EU Groups I to VII and IX)

CFC - 11 CFC - 114 CFC - 215 Halon – 1011 (Chlorobromomethane)

CFC - 12 CFC - 115 CFC - 216 Halon - 1211 CFC - 13 CFC - 211 CFC - 217 Halon - 1301

CFC - 111 CFC - 212 Halon - 2402 CFC - 112 CFC - 213 Carbon Tetrachloride CFC - 113 CFC - 214 Methyl Chloroform CHFBr2 C2H2F3Br C3HF6Br Methyl Bromide

HBFC-2201 (CHF2Br) C2H3FBr2 C3H2FBr5 C3H3F4Br

CH2FBr C2H3F2Br C3H2F2Br4 C3H4FBr3

C2HFBr4 C2H4FBr C3H2F3Br3 C3H4F2Br2

C2HF2Br3 C3HFBr6 C3H2F4Br2 C3H4F3Br

C2HF3Br2 C3HF2Br5 C3H2F5Br C3H5FBr2

C2HF4Br C3HF3Br4 C3H3FBr4 C3H5F2Br

C2H2FBr3 C3HF4Br3 C3H3F2Br3 C3H6FBr

C2H2F2Br2 C3HF5Br2 C3H3F3Br2

Class II (EU Group VIII)

HCFC - 21 HCFC - 133 HCFC - 224 HCFC - 241

HCFC - 22 HCFC - 133a HCFC - 225 HCFC - 242 HCFC - 31 HCFC - 141 HCFC - 225ca HCFC - 243

HCFC - 121 HCFC - 141b HCFC - 225cb HCFC - 244

HCFC - 122 HCFC - 142 HCFC - 226 HCFC - 251

HCFC - 123 HCFC - 142b HCFC - 231 HCFC - 252

HCFC - 124 HCFC - 151 HCFC - 232 HCFC - 253

HCFC - 131 HCFC - 221 HCFC - 233 HCFC - 261

HCFC - 132 HCFC - 222 HCFC - 234 HCFC - 262

HCFC - 132b HCFC - 223 HCFC - 235 HCFC - 271

Table C2.T5.2. New Controlled Substances

Halon 1202

Notes:

All isomers of the listed chemicals are considered as controlled substances, except isomers of 1,1,1-trichloroethane (also known as methyl chloroform) (such as 1,1,2-trichloroethane), and isomers of carbontetrachloride, methyl bromide and bromochloromethane.

2-16 September 2019

Table C2.T6. Fluorinated Greenhouse Gases Substance

GWP1,2

Industrial

Designation Chemical Name (common name) Chemical Formula Section 1: Hydrofluorocarbons HFC-23 trifluoromethane (fluoroform) CHF3 14,800 HFC-32 difluoromethane CH2F2 675 HFC-41 fluoromethane (methyl fluoride) CH3F 92 HFC-125 pentafluoroethane CHF2CF3 3,500 HFC-134 1,1,2,2-tetrafluoroethane CHF2CHF2 1,100 HFC-134a 1,1,1,2-tetrafluoroethane CH2FCF3 1,430 HFC-143 1,1,2-trifluoroethane CH2FCHF2 353 HFC-143a 1,1,1-trifluoroethane CH3CF3 4,470 HFC-152 1,2-difluoroethane CH2FCH2F 53 HFC-152a 1,1-difluoroethane CH3CHF2 124 HFC-161 fluoroethane (ethyl fluoride) CH3CH2F 12 HFC-227ea 1,1,1,2,3,3,3-heptafluoropropane CF3CHFCF3 3,220 HFC-236cb 1,1,1,2,2,3-hexafluoropropane CH2FCF2CF3 1,340 HFC-236ea 1,1,1,2,3,3-hexafluoropropane CHF2CHFCF3 1,370 HFC-236fa 1,1,1,3,3,3-hexafluoropropane CF3CH2CF3 9,810 HFC-245ca 1,1,2,2,3-pentafluoropropane CH2FCF2CHF2 693 HFC-245fa 1,1,1,3,3-pentafluoropropane CHF2CH2CF3 1,030 HFC-365 mfc 1,1,1,3,3-pentafluorobutane CF3CH2CF2CH3 794 HFC-43-10 mee 1,1,1,2,2,3,4,5,5,5-decafluoropentane CF3CHFCHFCF2CF3 1,640 Section 2: Perfluorocarbons PFC-14 tetrafluoromethane (perfluoromethane, carbon tetrafluoride)

CF4 7,390

PFC-116 hexafluoroethane (perfluoroethane) C2F6 12,200 PFC-218 octafluoropropane (perfluoropropane) C3F8 8,830 PFC-3-1-10 (R-31-10) decafluorobutane (perfluorobutane) C4F10 8,860 PFC-4-1-12 (R-41-12) dodecafluoropentane (perfluoropentane) C5F12 9,160 PFC-5-1-14 (R-51-14) tetradecafluorohexane (perfluorohexane) C6F14 9,300 PFC-c-318 octafluorocyclobutane (perfluorocyclobutane) c-C4F8 10,300…