Att 13 FGS Spain 2008.PDF

ENVIRONMENTAL

FINAL GOVERNING STANDARDS

SPAIN

JULY 2008

Commander, Navy Region Europe

PSC 817, Box 51

FPO AE 09622

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SP4520-10-R-0001, SPAIN

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ATTACHMENT 13

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SPAIN Table of Contents

Chapters Page

1 Overview (2002) 1-1

2 Air Emissions (2002) 2-1

3 Drinking Water (2008) 3-1

4 Wastewater (2002) 4-1

5 Hazardous Material (2002) 5-1

6 Waste Management (2008) 6-1

7 Solid Waste (2008)

8 Medical Waste (2002)

9 Petroleum, Oil, & Lubricants (2002) 9-1

10 [Reserved]*

11 Pesticides (2002) 11-1

12 Historic & Cultural Resources (2002) 12-1

13 Natural Resources & Endangered Species (2002) 13-1

14 Polychlorinated Biphenyls (2002) 14-1

15 Asbestos (2002) 15-1

16 [Reserved]*

17 Lead-Based Paint (2002) 17-1

18 Spill Prevention & Response Planning (2002) 18-1

19 Underground Storage Tanks (2002) 19-1

Appendices

A List of Hazardous Substances & Materials (2002) A-1

B.1 European Waste Catalog (2008) B.1-1

B.2 Waste Disposal Activities (2002) B.2-1

B.3 Waste Recovery Activities (2002) B.3-1

C Determination of Worst Case Discharge Planning Volume (2002) C-1

* Chapters 10 and 16 were reserved in DoD 4715.05-G (Overseas Environmental Baseline Guidance Document).

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SPAIN – 1 Overview

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1. CONCEPT & BACKGROUND

These standards were developed by comparing and adopting the more protective requirements of the U.S. DoD Overseas Environmental Baseline Guidance Document (OEBGD) and Spanish national, regional and local environmental laws and regulations, and applicable international agreements. These standards are the single definitive source of environmental compliance criteria applicable to DoD Components at installations in Spain. These are minimum requirements – component policy may impose additional requirements.

2. SCOPE

This document provides environmental standards for actions for DoD Components at installations in Spain. An installation is a base, camp, post, station, yard, center, or activity under the operational control of the Secretary of a Military Department or the Secretary of Defense.

Owned, leased, and joint use facilities that are operated or maintained by DoD Components must comply with these standards when, and to the extent that, the component controls the operation or maintenance activity (ies). At leased facilities operated and maintained by others, DoD Components may opt to require compliance with these standards by the lessor or contractor. In any case lessors and contractors must fully comply with Spanish legal requirements.

This document does not apply to:

1. 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 activities which DoD Components exercise control over only on a temporary or intermittent basis;

2. 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 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 document 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 off-loaded waste or material;

3. Facilities and activities associated with the Naval Nuclear Propulsion Program, which are covered under E.O. 12344 and conducted pursuant to 42 U.S.C. 7158;

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4. The determination or conduct of remediation to correct environmental problems caused by DoD's past activities, conducted in accordance with DoDI 4715.8 (Environmental Remediation Overseas); and,

5. Environmental analyses conducted under E.O. 12114.

This document does not create any rights or obligations enforceable against the United States, DoD, or any of its components, nor does it create any standard of care or practice for individuals.

Although the document references other DoD directives and instructions, it is intended only to coordinate the requirements of those directives as required. This document does not change other DoD or service directives or alter DoD or service policies.

3. RESPONSIBILITIES

It is DoD policy under the DoDI 4715.5 (Management of Environmental Compliance at Overseas Installations) that:

HQ USEUCOM will:

1. Coordinate and approve implementation of the FGS by the Environmental Executive Agent.

2. Resolve any disputes between other DoD Components and the Environmental Executive Agent regarding the FGS.

The DoD Environmental Executive Agent for Spain, CINCUSNAVEUR, will:

1. Develop and maintain the FGS in accordance with DoDI 4715.5.

2. Distribute the FGS and any subsequent amendments or guidance to the service components and DoD agencies with installations or facilities in Spain. Forward a copy of revised FGS via USEUCOM to the Military Departments and DUSD(ES) for information.

3. Revalidate and update the FGS at least every two years.

4. Consult with Host Nation authorities on environmental issues, as required, to maintain effective cooperation on environmental matters.

5. Resolve requests for waivers from the DoD Components.

6. Keep DoD Components informed of current environmental developments and trends.

DoD Components will:

1. Ensure that actions by DoD Components at installations in Spain, as well as planning, budgeting, programming, and execution, comply with these standards.

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2. Designate Component Commanders or other officials who are authorized to apply for waivers or initiate appeals.

3. Attain compliance with the FGS using pollution prevention as the preferred means where economically advantageous and consistent with mission requirements.

4. WAIVERS

If compliance with the FGS at particular installations or facilities would seriously impair operations, adversely affect relations with Spanish authorities, or require substantial expenditure of funds 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, a DoD Component may ask the Environmental Executive Agent to waive the particular standard. Waivers are not required if compliance projects have been programmed by the service components but remain unfunded.

See DoDI 4715.5 (Management of Environmental Compliance at Overseas Installations) and EUCOM Directive 80-1 (Environmental Security) for complete waiver procedures.

The installation commander will forward waiver requests to the Environmental Executive Agent via the Component chain of command. Waiver requests should specify, at a minimum:

1. The particular standard for which a waiver is requested;

2. The extent of the relief requested and the period that the waiver will be in effect;

3. The anticipated impact of the waiver, if any, on human health and the environment or relations with Spain authorities over the period of the waiver; and,

4. The justification for the waiver and if a complete waiver of the standard is requested, why a partial and/or temporary deviation would not be sufficient.

The Environmental Executive Agent will consult with the other DoD Components and USEUCOM and grant or deny the request for waiver in whole, in part, or conditionally. Waivers may require periodic reviews and reporting.

In the event that the Environmental Executive Agent denies a waiver, the DoD Component may appeal to HQ USEUCOM for reconsideration.

5. PERMITS & REPORTING

The Spanish Base Commander is the formal representative of the installation pursuant to bilateral agreement and serves as the liaison with national authorities and the contact with local authorities and local external military and civil entities. Therefore, any formal interaction or interaction of common (U.S. and Spanish) interest with Spanish authorities will be conducted under the cognizance, approval, or involvement of the Spanish Base Commander. DoD Components will assist the Spanish Base Commander with applying for permits and providing

FGS Spain 6 November 2002 1-4 reports and records or otherwise helping him with his liaison duties. DoD Components shall not obtain permits directly from the Host Nation. Matters for which the Spanish Base Commander may be expected to require assistance are listed in the Administrative Items at the end of each chapter.

If the Spanish Base Commander obtains a permit on behalf of a DoD Component and the permit requires a more protective standard than prescribed in the FGS, the standard in the permit shall be the compliance standard. However, if a permit allows a less protective standard, then the FGS will be the compliance standard unless a waiver is obtained.

If the installation at issue does not fall under the responsibility of a Spanish Base Commander, the DoD installation may request clarification from the Environmental Executive Agent via the chain of command. The Environmental Executive Agent may pursue having higher Spanish military headquarters resolve representational responsibility.

Contractors performing work for DoD must comply with all Spanish laws and regulations including obtaining all necessary licenses and permits.

6. ACCESS TO INSTALLATIONS & INFORMATION BY SPANISH AUTHORITIES

Inspections and non-routine requests for information by Spanish authorities shall be coordinated with the Spanish Base Commander and reported to the Environmental Executive Agent via the Component chain-of-command. To the maximum extent possible, U.S. military personnel shall lead the review of DoD Component activities by Spanish authorities during the inspection.

7. LEGAL PROTECTIONS FOR U.S. FORCES EMPLOYEES

Legal protections afforded DoD personnel investigated or charged by a Host Nation with alleged offenses arising out of any act or omission done in the performance of official duty vary depending upon the status of the individual under the NATO Status of Forces Agreement (SOFA) and other applicable international agreements. In general, there is a greater ability for the U.S. to assert a primary right to exercise criminal jurisdiction over a member of the force as opposed to a member of the civilian component. There is no such right with respect to local national employees. Accordingly, due consideration should be given to a military service member assuming responsibility, in coordination with the Spanish BaseCommander, for issues of alleged U.S. noncompliance raised by Host Nation authorities.

Installations, activities, and personnel should immediately contact their servicing legal office when faced with possible or actual Host Nation enforcement actions in order to maximize protections afforded to DoD personnel under the NATO SOFA, bilateral agreements, and U.S.

and DoD regulations, and to secure legal representation for the subjects of the enforcement action (including local national employees). Installations will report possible or actual Spanish enforcement actions to the Environmental Executive Agent via their chain-of-command.

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If the authorities seek to question a DoD employee regarding his or her official duties, a representative from installation legal should accompany the employee. The installation legal representative should clarify with the authorities whether the employee is questioned as a suspect or a witness, and the employee advised accordingly. It may not be readily apparent whether the Host Nation legal proceeding is criminal or administrative in nature. This point should be clarified as soon as possible since different procedures may apply depending on the answer.

Installations will report interview by Spanish authorities to the Environmental Executive Agent via their chain-of-command.

1.7.1 COUNSEL FEES & RELATED ASSISTANCE

AR 27-50/SECNAVINST 5820.4G (Status of Forces Policies, Procedures, and Information) establishes criteria and assigns responsibility for the provision of counsel and bail, the payment of court costs, and other necessary and reasonable expenses incident to representation in foreign criminal and civil proceedings. It includes appellate proceedings before foreign courts and foreign administrative agencies that involve military and civilian personnel (including local nationals). The payment of fines is not authorized by the reference. Approval authorities and additional procedures for requests for counsel fees and related assistance are listed in USAREUR Regulation 550-50/USAFE Instruction 51-706 (Exercise of Foreign Criminal Jurisdiction Over United States Personnel). Approval authority is assigned according to geographic area rather than chain of command.

1.7.2 CRIMINAL JURISDICTION

DoD policy is to maximize U.S. criminal jurisdiction to the extent permitted by applicable agreements. EUCOM Directive 45-3 and service instructions define policy, responsibilities, and procedures for the exercise of U.S. jurisdiction. Certain countries have tri-service regulations that address country specific policy, responsibilities and procedures. The primary right to exercise jurisdiction under the NATO SOFA may be more difficult for DoD to claim in official duty cases involving civilian employees because the extraterritorial application of U.S. law to civilians is limited. U.S. jurisdiction is not available for local national employees. In view of these limitations, a military member should be identified, where possible, as the responsible DoD party in an enforcement action. If an assertion of the primary right to exercise jurisdiction is not appropriate or is denied in a case, consideration should be given to requesting a waiver of Host Hation jurisdiction.

1.7.3 DEPARTMENT OF JUSTICE (DOJ) INVOLVEMENT

The 28 C.F.R. Section 50.15 provides procedures for representation of Federal employees by DOJ attorneys. A Federal employee may be provided representation in civil and criminal proceedings in which he or she is sued, subpoenaed, or charged in his individual capacity, where the actions of the employee reasonably appear to have been performed within the scope of the employee's employment and representation is in the interest of the U.S. In civil/administrative cases, DOJ may request substitution of the United States for the employee. The installation legal representative should coordinate requests for DOJ representation through Component command channels and the Environmental Executive Agent.

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SPAIN - 2 Air Emissions

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SCOPE & DEFINITIONS

This chapter contains standards for air emissions sources. Criteria addressing open burning of solid waste are contained in Chapter 7.

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, nonboiling solvent to clean the parts are classified as cold cleaning machines.

Combustion Unit – Any unit in which combustible products are oxidized so that the heat generated in this operation is used. Units include steam, heat, and energy/power production units.

Engler Degree – Unit of viscosity, symbolized as °E.

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.

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.

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.

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.

Ozone-Depleting Substances (ODS) – Those substances listed in Table 2.5.

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).

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.

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

Steam 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.

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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.

CRITERIA

C2.1 COMBUSTION UNITS

Installations that operate combustion units will provide the Spanish Base Commander with sufficient information to seek an operating permit for their units (see Chapter 1 for the process).

A technical report (with the facility’s design specifications) and an annex with the corresponding environmental information (including data on the projected air emissions) must be submitted with the permit request. The Spanish Base Commander may submit the permit request and technical report to the Technological Development and Employment Department of Andalusia (Consejería de Empleo y Desarrollo Tecnológico).

C2.1.1 Air Emissions Standards. The following criteria apply to combustion units as indicated below.

C2.1.1.1 Combustion units and associated emissions controls must be designed to meet the emission standards for specific sized units shown in Table 2.1, Table 2.2, and Table 2.3 (as applicable) at all times, except during periods of start up, shut down, or when emergency conditions exist.

C2.1.1.2 For combustion units with a maximum design heat input capacity of 2.93 MW

(10 MBtu/hr) or greater combusting liquid or solid fossil fuels, the fuel sulfur content (weight percent) and higher heating value will be measured and recorded for each new shipment of fuel. This data will be used to calculate sulfur dioxide (SO2) emissions and document compliance with the SO2 limits in Table 2.1 and Table 2.2. Alternatively, installations will install a properly calibrated and maintained continuous emissions monitoring system (CEMS) to measure the flue gas for SO2 and either oxygen (O2) or carbon dioxide (CO2).

C2.1.2 Air Emissions Monitoring Requirements. Combustion units with a maximum design heat input capacity of 2.93 MW (10 MBtu/hr) or greater that are subject to the opacity or NOX standards in Table 2.1 or Table 2.2 must have a properly calibrated and maintained CEMS to measure the flue gas as follows:

C2.1.2.1 For units with a maximum design heat input capacity greater than 8.79 MW

(30 MBtu/hr): Opacity, except that CEMS is not required where gaseous or distillate fuels are the only fuels combusted

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C2.1.2.2 For fossil-fuel fired units with a maximum design heat input capacity greater than 29.3 MW (100 MBtu/hr): nitrogen oxides (NOX) and either oxygen (O2) or carbon dioxide (CO2)

C2.1.2.3 For facilities operational after 1 January 1976 with a maximum design heat input capacity greater than 293 MW (1,000 MBtu/hr): SO2, NOx, O2, and particulate matter.

C2.2 INCINERATORS

Installations that operate an incinerator unit (for urban waste, sludge, or medical waste) will provide the Spanish Base Commander with sufficient information to seek an operating permit for their unit (see Chapter 1 for the process). A technical report (with the facility’s design specifications) and an annex with the corresponding environmental information (including data on the projected air emissions) must be submitted with the permit request.

The following requirements do not apply to incinerators combusting hazardous waste or munitions. Refer to Chapter 6 for information regarding hazardous waste disposal, including hazardous waste incineration (C6.10.7).

C2.2.1 Incinerators (Non-medical). All incinerators issued an operating permit on or after 1

December 1992 must meet the standards specified in Table 2.4.

Monitoring Requirements. Temperature, particulate matter (expressed in opacity units), CO, oxygen, and HCl must be continuously measured and recorded for incinerators with a capacity > 1 ton/hr.

C2.2.2 Sewage Sludge Incinerators. All non-hazardous sewage sludge incinerators must be designed to meet the emissions limits in Table 2.4. Incinerators for hazardous sewage sludge (i.e., waste codes 19 08 03, 19 08 06, and 19 08 07) must be designed to meet the emissions limits established in Chapter 6.

C2.2.3 Medical Waste Incinerators (MWI). The following standards apply to new and existing units. These requirements do not apply to any portable units (field deployable). Existing sources must comply within 5 years of the publication date of this document. Refer to Chapter 8 for other requirements pertaining to medical waste management.

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C2.2.3.1 All new and existing MWI must be designed and operated according to the following standards:

Flue gas temperature and internal combustion chamber

(for waste containing > 1% of halogenated organic substances expressed as chlorine)

850 °C (1,100 °C)

O2 content in wet flue gas 6% volume Contact time 2 seconds

The incinerator must be equipped with auxiliary burners that are automatically activated when the flue gas temperature drops below the minimum flue gas temperature (850 °C or 1,100 °C depending on the waste stream).

C2.3 PERCHLOROETHYLENE (PCE) DRY CLEANING MACHINES

The following requirements apply to new and existing dry cleaning machines. These requirements do not apply to coin-operated machines. Existing sources must comply within 3 years of the publication date of this document.

C2.3.1 Emissions from existing PCE dry cleaning machines, at installations that use more than

2,000 gallons/year of PCE (installation wide) in their dry cleaning operations, must be controlled with a refrigerated condenser, or, if already installed, a carbon absorber.

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.

C2.3.2 All new PCE dry cleaning systems 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.

C2.4 CHROMIUM ELECTROPLATING AND CHROMIUM ANODIZING TANKS

The following standards apply to new and existing tanks. Existing sources must comply within 3 years of the publication date of this document.

C2.4.1 Ventilation exhaust from new and existing tanks must be controlled by a wet scrubber, composite mesh-pad eliminator, fiber bed filter, or equivalent control device capable of limiting emissions to 0.015 milligrams per dry standard cubic meter (mg/dscm).

Control devices must be operated according to manufacturer recommendations.

C2.4.2 Alternatively, in lieu of control devices, decorative chromium and chromium anodize tanks may use chemical tank additives to prevent the surface tension from exceeding 45 dynes per centimeter provided that the surface tension is monitored prior to the first initiation of electric current on a given day and every 4 hours thereafter.

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C2.5 HALOGENATED SOLVENT CLEANING MACHINES

These requirements apply to new and existing 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. Existing sources must comply within 3 years of the publication date of this document. (Note: 1,1,1-trichloroethane is an ozone depleting substance that must be phased out of existence by 31 December 2008.)

C2.5.1 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.

C2.5.2 All vapor cleaning machines (vapor degreasers) must incorporate design and work practices which minimize the direct release of halogenated solvent to the atmosphere.

C2.6 OZONE DEPLETING SUBSTANCES (ODS)

The following criteria apply to direct atmospheric emissions of ODS:

C2.6.1 Except as allowed in C2.6.2, use (i.e., utilization in maintenance or servicing of products and equipment) of the following ODSs is prohibited. Running an existing system without maintenance (e.g., using a refrigerator) would not be classified as use.

• Chlorofluorocarbons (CFCs)

• Other fully halogenated chlorofluorocarbons

• Halons

• Carbon tetrachloride

• 1,1,1-Trichloroethane

• Hydrobromofluorocarbons

C2.6.2 Halons may still be used under the following conditions:

• Halons that have been recovered, recycled, or reclaimed may be used in existing fire protection systems and fire extinguishers until 31 December 2002.

• Fire protection systems and fire extinguishers containing halons may be operated without maintenance or servicing of the halons, but must be decommissioned and the halons recovered before 31 December 2003.

• Halons for critical uses as specified in Table 2.6.

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C2.6.3 Except as allowed in C2.6.4, use (i.e., utilization in maintenance or servicing of products and equipment) of hydrochlorofluorocarbons (HCFCs) is prohibited in the following applications. Running an existing system without maintenance (e.g., using a refrigerator) would not be classified as use.

C2.6.3.1 In aerosols

C2.6.3.2 As solvents:

• In non-contained solvent uses (including open-top cleaners and open-top dewatering systems without refrigerated areas, in adhesives and mould-release agents when not employed in closed equipment, and for drain cleaning where HCFCs are not recovered)

• From 1 January 2002, in all solvent uses except precision cleaning of electrical and other components in aerospace and aeronautics applications, where use is prohibited beginning on 31 December 2008

C2.6.3.3 As refrigerants:

C2.6.3.3.1 In equipment produced after 31 December 1995 for the following uses:

• In non-confined direct-evaporation systems

• In household refrigerators and freezers

• In motor vehicle, tractor, and off-road vehicle or trailer air-conditioning systems operating on any energy source. However, for military applications, the use is prohibited on 31 December 2008

• In road public-transport air-conditioning

C2.6.3.3.2 In equipment produced after 31 December 1997 for use in rail transport air-conditioning

C2.6.3.3.3 In equipment produced after 31 December 1999 for the following uses:

• In public and distribution cold stores and warehouses

• For equipment of 150 kW and over, shaft input

C2.6.3.3.4 In all other refrigeration and air-conditioning equipment produced after

31 December 2000 with two exceptions:

• HCFCs can be used in fixed air-conditioning equipment with a cooling capacity of less than 100 kW until 1 July 2002

• HCFCs can be used in reversible air-conditioning/heat pumps until 1 January 2004

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C2.6.3.3.5 The use of virgin HCFCs in the maintenance and servicing of refrigeration and air-conditioning equipment shall be prohibited on 1 January 2010. The use of all HCFCs in the maintenance and servicing of refrigeration and air-conditioning equipment shall be prohibited on 1 January 2015.

C2.6.3.4 For the production of foams except integral skin foams for use in safety applications and rigid insulating foams

C2.6.3.5 As carrier gas for sterilization substances in closed systems, in equipment produced after 31 December 1997

C2.6.3.6 In all other applications

C2.6.4 The use of HCFCs shall be permitted:

C2.6.4.1 In laboratory uses, including research and development

C2.6.4.2 As feedstock (i.e., undergoes chemical transformation in a process in which it is entirely converted from its original composition and its emissions are insignificant)

C2.6.4.3 As halon substitutes in existing fire protection systems specified in Table 2.6 under the following conditions:

• Original halons contained in such fire protection systems shall be replaced completely

• Halons withdrawn shall be disposed in accordance with DoD 4160.21-M, Defense Materiel Disposition Manual, Chapter 10.

C2.6.5 ODS Refrigerant Venting Prohibition. Do not intentionally release any ODS refrigerant (identified in Table 2.5) 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 refrigerants are not subject to this prohibition.

C2.6.6 ODS Fire Suppression Agent (Halon) Venting Prohibition. Do not intentionally release halons into the environment while testing, maintaining, servicing, repairing, or disposing of halon-containing equipment or using such equipment for technician training. Halon uses authorized in C2.6.2 are exempt from the venting prohibition in the following situations:

• 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)

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

• 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 (i.e., substitute product that can perform the same function) cannot be used

C2.6.7 Recovery Requirements for ODSs. ODSs identified in Table 2.5 shall be recovered as follows using equipment operated by trained personnel:

• ODSs contained in commercial and industrial refrigeration/air-conditioning equipment, equipment containing solvents, fire protection systems, and fire extinguishers shall be recovered for disposition in accordance with DoD 4160.21- M, Defense Materiel Disposition Manual, Chapter 10

• After 31 December 2001, ODSs contained in domestic refrigerators and freezers shall be recovered per DoD 4160.21-M, Defense Materiel Disposition Manual, Chapter 10

• ODSs contained in products, installations, and equipment other than those mentioned above shall be recovered, if practicable, per DoD 4160.21-M, Defense Materiel Disposition Manual, Chapter 10

C2.6.8 Leakage of ODSs. The following precautionary measures must be taken to prevent leakage of ODSs in Table 2.5:

• All precautionary measures practicable shall be taken to prevent leakage of ODSs.

In particular, fixed equipment with a refrigerating fluid charge of more than 3 kg shall be checked annually for leakages

• All precautionary measures practicable shall be taken to prevent and minimize leakage of methyl bromide from fumigation installations and operations in which methyl bromide are used

• All precautionary measures practicable shall be taken to prevent and minimize any leakage of ODSs inadvertently produced in the course of the manufacture of other chemicals

C2.7 MOTOR VEHICLES

This criterion applies to DoD-owned motor vehicles (as defined in the definitions section).

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C2.7.1 Inspect all vehicles as follows to ensure that no one has tampered with the factory-installed emission control equipment:

Vehicle Age Inspection Frequency

0-4 years every 2 years after 4 years annually

CO emission limits for gasoline vehicles manufactured in Europe when at idle will not exceed 5% by volume (at 15-20º C and 750-760 mm Hg). Motor vehicles manufactured in Europe and equipped with diesel engines will not exceed the following opacity limits:

Engine Power (Horsepower) Absolute Units > 200 2.1

>100 and <200 2.4 < 100 2.8

Notes:

1. The opacity limits are based on measures made at a minimum motor temperature of 60°C.

C2.7.2 Use only unleaded gasoline in vehicles that are designed for this fuel.

C2.8 FUEL COMPOSITION

The composition of fuels permitted for use in Spain is specified in the following table.

Parameter Units Diesel Fuel #1 Fuel Oil #2 Fuel Oil Density at 15°C kg/L 0.9 - - - - - - Viscosity at 100°C mm2/S - - - 27 37 Total sulfur content % by weight 0.2 1, 2 2.5 3.5 Water and sediments % by volume 0.1 1 1 Water % by volume - - - 0.5 0.5

Notes:

1. 0.05% effective 1 Oct 1996 for Class A automotive diesel.

2. 350 mg/kg (0.035%) effective 1 Jan 2000 for Class A automotive diesel.

ADMINISTRATIVE ITEMS

The following items shall be provided to the Spanish Base Commander for further transmittal as appropriate:

1. Installations that operate thermal units (steam generating unit, or thermal heating units) will provide the Spanish Base Commander with sufficient information to seek an operating permit for their units (see Chapter 1 for the process). A technical report (with the facility’s design specifications) and an annex with the corresponding environmental information (including data on the projected air emissions) must be submitted with the permit request. The Spanish Base Commander may submit the permit request and technical report to the Technological

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Development and Employment Department of Andalusia (Consejería de Empleo y Desarrollo Tecnológico).

2. Installations that operate an incinerator unit (for urban waste, sludge, or medical waste) will provide the Spanish Base Commander with sufficient information to seek an operating permit for their unit (see Chapter 1 for the process). A technical report (with the facility’s design specifications) and an annex with the corresponding environmental information (including data on the projected air emissions) must be submitted with the permit request.

Table 2.1 – Maximum Emission Limits for Combustion Units for Energy Production ≥ 50 MW (170.6 MBtu/Hr)

Thermal Capacity of Facility 1 Emission Limit 2

Fuel

(MW)

(MBTU/hr)

SO2 Particulate Matter

NOx 4 Opacity 3

(mg/Nm3) (mg/Nm3) (mg/Nm3) (%) Solid fuel 50 - 100 170.6 – 341.3 2,000 100 6505 20%

100 - 500 341.3 – 1,706.5 400 – 2,000 100 6505 20% > 500 > 1,706.5 400 50 6505 20%

Liquid fuel 50 - 300 170.6 - 1,023.9 1,700 506 450 20% 300 - 500 1,023.9 - 1,706.5 400 - 1,700 506 450 20% > 500 > 1,706.5 400 506 450 20%

Gas fuel Combustible gaseous materials in general

NA NA 35 5

350 20%

Liquified gas NA NA 5 350 20% Notes:

1. Maximum design heat input capacity

2. Standards do not apply during periods of start up, shut down, or when emergency conditions exist.

3. The 20% opacity standard applies to the average opacity over a 6-minute period per hour.

4. The emission limit for NOX is based on a 30-day rolling average.

5. The limit is 650 mg/Nm3 for solid fuel in general, and 1,300 mg/Nm3 for solid fuel with <10% volatile materials.

6. For units with <100 MW thermal capacity that use combustibles with an ash content >0.06%, the particulate matter emission limit is 100 mg/Nm3.

7. For blast-furnace gas.

8. For gas produced by the iron and steel industry to be used in other types of plants.

FGS Spain 6 November 2002 2-11

Table 2.2 – Emission Limits for Combustion Units for Energy Production < 50 MW (170.6 MBtu/hr)

Emission Limits

Fuel Source Opacity (1)

SO2

(mg/Nm3)

Particulate Matter (mg/Nm3)

Liquid fuels 20 5,500 200 Solid fuel (anthracite coal) 20 2,400 400 Solid fuel (lignite coal) 20 9,000 400

Notes:

1. The limits should not exceed 40% opacity or more than one 2-minute period per hour.

2. The units of mg/Nm3 are at normal physical conditions of 0ºC and 0.1013 Mpa.

Table 2.3 – Emission Limits for Industrial Combustion Facilities (Steam/Heat Generating Units, Excluding Thermal Plants)

Emission Limits

Fuel Source Opacity (1)

SO2

(mg/Nm3)

CO

(ppm)

Gas oil or domestic fuel oil 20 1,700 1.445 Heavy #1 fuel oil 40 4,200 1.445 Heavy #2 fuel oil 50 6,800 1.445

Notes:

1. The limits should not be exceeded more than three times per day, with each period lasting < 10 minutes.

2. The units of mg/Nm3 are at normal physical conditions of 0ºC and 0.1013 Mpa.

Table 2.4 – Emission Limits for Municipal Solid Waste Incinerators

Pollutant < 1 ton/hr ≥ 1 ton/hr but ≤ 3 tons/hr

≥ 3 tons/hr

(mg/Nm³) (mg/Nm³) (mg/Nm³) Total dust (PM) 200 100 30 Heavy metals:

Pb + Cr + Cu + Mn - 5 5 Ni + As - 1 1 Cd + Hg - 0.2 0.2

Hydrochloric acid (HCl) 250 100 50 Hydrofluoric acid (HF) - 4 2 Organic Substances (TOC) - 20 20

CO - 100 100

Sulfur dioxide (SOx) - 300 300

Notes:

1. The emissions are considered in compliance with the limits if the 7-day average does not exceed the corresponding emission limit and the 1-day average does not exceed 30% of the corresponding emission limit. The average values are calculated including measurements collected during start-up and shut-down operations.

2. For plants with a capacity < 1 ton/hr, the emission limits may refer to an oxygen level of 17%. In this case, the emissions should not exceed the above limits divided by 2.5.

FGS Spain 6 November 2002 2-12

Table 2.5 – Ozone Depleting Substances

Molecular Formula Common Name CAS Number1 Chemical Name

Chlorofluorocarbons (CFCs) CFCl3 CFC – 11 75-69-4 Trichlorofluoromethane CF2Cl2 CFC – 12 75-71-8 Dichlorodifluoromethane C2F3Cl3 CFC – 113 76-13-1 Trichlorotrifluoroethane C2F4Cl2 CFC – 114 76-14-2 Dichlorotetrafluoroethane C2F5Cl CFC – 115 76-15-3 Chloropentafluoroethane

Other Fully Halogenated Chlorofluorocarbons CF3Cl CFC – 13 75-72-9 Chlorotrifluoromethane C2FCl5 CFC – 111 354-56-3 Pentachlorofluoroethane C2F2Cl4 CFC – 112 76-12-0 Tetrachlorodifluoroethane C3FCl7 CFC – 211 422-78-6 Heptachlorofluoropropane C3F2Cl6 CFC – 212 3182-26-1 Hexachlorodifluoropropane C3F3Cl5 CFC – 213 2354-06-5 Pentachlorotrifluoropropane C3F4Cl4 CFC – 214 29255-31-0 Tetrachlorotetrafluoropropane C3F5Cl3 CFC – 215 4259-43-2 Trichloropentafluoropropane C3F6Cl2 CFC – 216 661-97-2 Dichlorohexafluoropropane C3F7Cl CFC – 217 422-86-6 Chloroheptafluoropropane CF2Cl2 • C2F2H4 CFC – 500 56275-41-3 Dichlorodifluoromethane •

Difluoroethane CHF2Cl • C2F5Cl CFC – 502 74-45-6 and

76-15-3 Chlorodifluoromethane • Chloropentafluoroethane

CF3Cl • CHF3 CFC – 503 75-72-9 and 75-46-7

Chlorotrifluoromethane • Trifluoromethane

Halons CF2BrCl Halon – 1211 353-59-3 Bromochlorodifluoromethane CF3Br Halon – 1301 75-63-8 Bromotrifluoromethane C2F4Br2 Halon – 2402 124-73-2 Dibromotetrafluoroethane

Carbon Tetrachloride CCl4 Carbon Tetrachloride 56-23-5 Carbon Tetrachloride

1,1,1-trichloroethane C2H3Cl3 Methyl Chloroform 71-55-6 1,1,1-trichloroethane

Methyl Bromide CH3Br Methyl Bromide 74-83-9 Methyl Bromide

Hydrobromofluorocarbons CHFBr2 N/A Dibromofluoromethane CHF2Br HBFC-22B1 Bromodifluoromethane CH2FBr N/A Bromofluoromethane C2HFBr4 N/A Tetrabromofluoroethane C2HF2Br3 N/A Tribromodifluoroethane C2HF3Br2 N/A Dibromotrifluoroethane C2HF4Br N/A Bromotetrafluoroethane C2H2FBr3 N/A Tribromofluoroethane C2H2F2Br2 N/A Dibromodifluoroethane C2H2F3Br N/A Bromotrifluoroethane C2H3FBr2 N/A Dibromofluoroethane C2H3F2Br N/A Bromodifluoroethane C2H4FBr N/A Bromofluoroethane C3HFBr6 N/A Hexabromofluoropropane

FGS Spain 6 November 2002 2-13

Molecular Formula Common Name CAS Number1 Chemical Name

C3HF2Br5 N/A Pentabromodifluoropropane C3HF3Br4 N/A Tetrabromotrifluoropropane C3HF4Br3 N/A Tribromotetrafluoropropane C3HF5Br2 N/A Dibromopentafluoropropane C3HF6Br N/A Bromohexafluoropropane C3H2FBr5 N/A Pentabromofluoropropane C3H2F2Br4 N/A Tetrabromodifluoropropane C3H2F3Br3 N/A Tribromotrifluoropropane C3H2F4Br2 N/A Dibromotetrafluoropropane C3H2F5Br N/A Bromopentafluoropropane C3H3FBr4 N/A Tetrabromofluoropropane C3H3F2Br3 N/A Tribromodifluoropropane C3H3F3Br2 N/A Dibromotrifluoropropane C3H3F4Br N/A Bromotetrafluoropropane C3H4FBr3 N/A Tribromofluoropropane C3H4F2Br2 N/A Dibromodifluoropropane C3H4F3Br N/A Bromotrifluoropropane C3H5FBr2 N/A Dibromofluoropropane C3H5F2Br N/A Bromodifluoropropane C3H6FBr N/A Bromofluoropropane

Hydrochlorofluorocarbons (HCFCs) CHFCl2 HCFC – 21 Dichlorofluoromethane CHF2Cl HCFC – 22 Chlorodifluoromethane CH2FCl HCFC – 31 Chlorofluoromethane C2HFCl4 HCFC – 121 Tetrachlorofluoroethane C2HF2Cl3 HCFC – 122 Trichlorodifluoroethane C2HF3Cl2 HCFC – 123 Dichlorotrifluoroethane C2HF4Cl HCFC – 124 Chlorotetrafluoroethane C2H2FCl3 HCFC – 131 Trichlorofluoroethane C2H2F2Cl2 HCFC – 132 Dichlorodifluoroethane C2H2F3Cl HCFC – 133 Chlorotrifluoroethane C2H3FCl2 HCFC – 141 Dichlorofluoroethane CH3CFCl2 HCFC – 141b 1,1-dichloro-1-fluoroethane C2H3F2Cl HCFC – 142 Chlorodifluoroethane CH3CF2Cl HCFC – 142b 1-chloro-1,1-difluoroethane C2H4FCl HCFC – 151 Chlorofluoroethane C3HFCl6 HCFC – 221 Hexachlorofluoropropane C3HF2Cl5 HCFC – 222 Pentachlorodifluoropropane C3HF3Cl4 HCFC – 223 Tetrachlorotrifluoropropane C3HF4Cl3 HCFC – 224 Trichlorotetrafluoropropane C3HF5Cl2 HCFC – 225 Dichloropentafluoropropane CF3CF2CHCl2 HCFC – 225ca 1,1-dichloro-2,2,3,3,3-pentafluoropropane CF2ClCF2CHClF HCFC – 225cb 1,3-dichloro-1,2,2,3,3-pentafluoropropane C3HF6Cl HCFC – 226 Chlorohexafluoropropane C3H2FCl5 HCFC – 231 Pentachlorofluoropropane C3H2F2Cl4 HCFC – 232 Tetrachlorodifluoropropane C3H2F3Cl3 HCFC – 233 Trichlorotrifluoropropane C3H2F4Cl2 HCFC – 234 Dichlorotetrafluoropropane

FGS Spain 6 November 2002 2-14

Molecular Formula Common Name CAS Number1 Chemical Name

C3H2F5Cl HCFC – 235 Chloropentafluoropropane C3H3FCl4 HCFC – 241 Tetrachlorofluoropropane C3H3F2Cl3 HCFC – 242 Trichlorodifluoropropane C3H3F3Cl2 HCFC – 243 Dichlorotrifluoropropane C3H3F4Cl HCFC – 244 Chlorotetrafluoropropane C3H4FCl3 HCFC – 251 Trichlorofluoropropane C3H4F2Cl2 HCFC – 252 Dichlorodifluoropropane C3H4F3Cl HCFC – 253 Chlorotrifluoropropane C3H5FCl2 HCFC – 261 Dichlorofluoropropane C3H5F2Cl HCFC – 262 Chlorodifluoropropane C3H6FCl HCFC – 271 Chlorofluoropropane

Note:

1. The American Chemical Society’s Chemical Abstracts Service number.

Table 2.6 – Critical Uses of Halon

Use of Halon 1301:

1. In aircraft for the protection of crew compartments, engine nacelles, cargo bays, and dry bays

2. In military land vehicles and naval vessels for the protection of spaces occupied by personnel and engine compartments

3. For the making inert of occupied spaces where flammable liquid and/or gas release could occur in the military and oil, gas and petrochemical sector, and in existing cargo ships

4. For the making inert of existing manned communication and command centers of the armed forces or others, essential for national security

5. For the making inert of spaces where there may be a risk of dispersion of radioactive matter

6. In the Channel Tunnel and associated installations and rolling stock

Use of Halon 1211:

1. In hand-held fire extinguishers and fixed extinguisher equipment for engines for use on board aircraft

2. In aircraft for the protection of crew compartments, engine nacelles, cargo bays and dry bays

3. In fire extinguishers essential to personal safety used for initial extinguishing by fire brigades

4. In military and police fire extinguishers for use on persons

SPAIN - 3 Drinking Water

FGS Spain July 2008 3-1

SCOPE & DEFINITIONS

This chapter contains criteria for providing potable water.

Action Level – The concentration of a substance in water that establishes appropriate treatment for a water system.

Appropriate DoD Medical Authority – The medical professional designated by the in-theater component commander to be responsible for resolving medical issues necessary to provide safe drinking water at the Component’s installations.

Community Water System (CWS) – A public water system having at least 15 service connections used by year-round residents, or which regularly serves at least 25 year-round residents.

Competent Sanitary Authority –The competent regional sanitary administration or other competent regional bodies.

Concentration/Time (CT) – The product of residual disinfectant concentration, C, in mg/L determined before or at the first customer, and the corresponding disinfectant contact time, T, in minutes. CT values appear in Tables 3.11 through 3.24.

Conventional Treatment – Water treatment including chemical coagulation, flocculation, sedimentation, and filtration.

Diatomaceous Earth Filtration – A water treatment process of passing water through a precoat of diatomaceous earth deposited on a support membrane while additional diatomaceous earth is continuously added to the feed water to maintain the permeability of the precoat, resulting in substantial particulate removal from the water.

Direct Filtration – Water treatment including chemical coagulation, possibly flocculation, and filtration, but not sedimentation.

Disinfectant – Any oxidant (including, but not limited to, chlorine, chlorine dioxide, chloramines, and ozone) intended to kill or inactivate pathogenic microorganisms in water.

DoD-Produced Water – Any water used for drinking water where the raw water is extracted by DoD. If DoD blends raw water with purchased water, the drinking water is considered DoD-produced water. Any drinking water that does not meet the definition of purchased water must be considered DoD-produced water.

DoD Water System – A public water system or non-public water system.

Emergency Assessment – An evaluation of the susceptibility of the water source, treatment, storage, and distribution system(s) to disruption of service from natural disasters, accidents, and sabotage.

FGS Spain July 2008 3-2

First Draw Sample – A 1-liter sample of tap water that has been standing in plumbing at least 6 hours and is collected without flushing the tap.

Groundwater Under the Direct Influence of Surface Water (GWUDISW) – Any water below the surface of the ground with significant occurrence of insects or other microorganisms, algae, or large diameter pathogens such as Giardia lamblia; or significant and relatively rapid shifts in water characteristics (such as turbidity, temperature, conductivity, or pH) which closely correlate to climatological or surface water conditions.

Lead-Free – A maximum lead content of 0.2% for solder and flux, and 8.0% for pipes and fittings.

Lead Service Line – A service line made of lead that connects the water main to the building inlet, and any lead pigtail, gooseneck, or other fitting which is connected to such line.

Local National – An employee hired under Spanish employment conditions.

Maximum Contaminant Level (MCL) – The maximum permissible level of a contaminant in water that is delivered to the free-flowing outlet of the ultimate user of a public water system except for turbidity for which the maximum permissible level is measured after filtration.

Contaminants added to the water under circumstances controlled by the user (except those resulting from the corrosion of piping and plumbing caused by water quality) are excluded.

Non-Public Water System (NPWS) – A system that does not meet the definition of a public water system (for example, a well serving a building with less than 25 people).

Point-of-Entry (POE) Treatment Device – A treatment device applied to the drinking water entering a facility to reduce contaminants in drinking water throughout the facility.

Point-of-Use (POU) Treatment Device – A treatment device applied to a tap to reduce contaminants in drinking water at that tap.

Potable Water – Water that has been examined and treated to meet the standards in this chapter, and has been approved as potable by the appropriate DoD medical authority. It includes water used for drinking, cooking, food preparation, and other domestic uses, regardless of its origin or the manner in which it is distributed to the consumer.

Public Water System (PWS) – A system for providing piped water to the public for human consumption, if such system has at least 15 service connections or regularly serves at least 25 year round residents. This term includes both "community water systems" which serve year-round residents and "non-community systems" along with any collection, treatment, storage, and distribution facilities under control of the operator of such systems, and any collection or pretreatment storage facilities not under such control that are used primarily in connection with such systems. A non-community system is used by intermittent users or travelers and is sub-classified into a non-transient, non-community or NTNC system and a transient, non-community

FGS Spain July 2008 3-3 or TNC system. A NTNC system could be a school or factory with its own water supply where the same people drink the water throughout the year, but not 24-hours a day. A TNC system example is a motel with its own well.

Purchased Water – Any drinking water acquired from an entity authorized by the competent local authorities to produce and distribute drinking water. Note: All facilities (including leased facilities) should ensure that their water supplier is authorized by the competent local authorities.

River Basin Authority – The institution in charge of the management of a river and its…