Standard Practice for Determining the Environmental Condition of Federal Property

SIGNIFICANCE AND USE
4.1 Uses—This practice is intended for use by federal agencies, and environmental professionals in order to facilitate ECP efforts. It is also intended for use by preparers and reviewers of environmental condition of property maps and ECP reports used to support CERFA uncontaminated property identifications and property suitable for transfer by lease or by deed. GSA regulations addressing the disposal of federal property (41 CFR §105-72), require the landholding agency to assert either that (a) there is no evidence of hazardous substance activity, or (b) there is evidence of hazardous substance activity that occurred on the property. If there is evidence that hazardous substance activity occurred on the property, the landholding agency has a “due diligence” obligation to provide detailed, accurate information on all “reportable quantities” of hazardous substances stored, released, or disposed of on property that it reports to GSA for disposal. The specific substances that must be reported under CERCLA and their reporting limits are described in 40 CFR §302.4 and 40 CFR §373. If the landholding agency discloses that hazardous substance activity took place on the property, then the landholding agency must assert whether or not all required remedial action necessary to protect human health and the environment has been taken with respect to those hazardous substances.  
4.1.1 The ECP reports prepared in accordance with this practice may be used to achieve compliance with the federal Management Regulations, Real Property Disposal rules codified in 41 CFR §102-75.  
4.2 Clarifications on Use:  
4.2.1 Use Not Limited to CERCLA—This practice is designed to assist the user in developing information about the environmental condition of a property and as such has utility for a wide range of persons, including those who may have no actual or potential CERCLA liability (see 40 CFR §373, 41 CFR §102-75 and Section 208 of the Federal Land Policy and Management Act, Public Law ...
SCOPE
1.1 Purpose—The purpose of this practice is to define good commercial and customary practice in the United States for assessing the environmental condition of property (ECP) of federal real property. This practice applies to property under consideration for lease, excess and surplus property at closing and realigning military installations, claims reverting to federal ownership such as abandoned mines, and other federally-owned property. The steps in this practice are conducted to fulfill certain requirements of the Comprehensive Environmental Response, Compensation and Liability Act of 1980 (CERCLA) section 120(h), as amended by the Community Environmental Response Facilitation Act of 1992 (CERFA) and the federal real property disposal regulations codified in 41 CFR Subpart C (41 CFR 102-75). As such, this practice is intended to help a user to gather and analyze data and information in order to classify property into the applicable environmental condition of property area types (in accordance with the ASTM D5746, Standard Classification of Environmental Condition of Property Area Types, (see Appendix X1). Once documented, the ECP report is used to support Findings of Suitability to Transfer (FOSTs), Findings of Suitability to Lease (FOSLs), or uncontaminated property determinations, or a combination thereof, pursuant to the requirements of CERFA and CERCLA § 120(h). Users of this practice should note that it does not address (except where explicitly noted) requirements for appropriate and timely regulatory consultation or concurrence, or both, during the conduct of the ECP or during the identification and use of the standard environmental condition of property area types.  
1.1.1 Environmental Condition of Property—In accordance with the federal landholding agency policies and General Services Administration’s (GSA) federal real property management regulations, an ECP will be prepared or evaluated for its usefulness (...

General Information

Status
Published
Publication Date
31-Aug-2022

Relations

Effective Date
01-Feb-2024
Effective Date
01-Nov-2023
Effective Date
01-Sep-2023
Effective Date
01-Dec-2016
Effective Date
01-Dec-2016
Effective Date
01-Apr-2010
Effective Date
01-Jun-2008
Effective Date
15-Oct-2006
Effective Date
01-Nov-2005
Effective Date
01-Oct-2005
Effective Date
10-Nov-2002
Effective Date
10-Oct-2000
Effective Date
10-May-2000
Effective Date
10-May-2000
Effective Date
10-Sep-1998

Overview

ASTM D6008-22: Standard Practice for Determining the Environmental Condition of Federal Property establishes a structured process for assessing the environmental condition of federally-owned properties in the United States. Developed by ASTM International, this standard is essential for federal agencies, environmental professionals, and real property managers who must evaluate federal property for lease, transfer, closure, or disposal. The practice supports compliance with complex federal regulations, including requirements from CERCLA (Comprehensive Environmental Response, Compensation and Liability Act), CERFA (Community Environmental Response Facilitation Act), and specific General Services Administration (GSA) real property disposal regulations.

Key Topics

  • Environmental Condition of Property (ECP): This standard defines best practices for evaluating environmental conditions on federal property, focusing on identifying hazardous substance activity, petroleum product storage, and contamination.
  • Regulatory Compliance: Satisfies due diligence and documentation requirements under CERCLA section 120(h), CERFA, and 41 CFR 102-75, which govern the transfer and disposal of federal real property.
  • Property Classification: Guides users in classifying property using the ASTM D5746 standard, which assists in determining if property can be reported as uncontaminated or requires further action.
  • ECP Reports: Outlines standardized development of ECP reports, which support Findings of Suitability to Transfer (FOST), Findings of Suitability to Lease (FOSL), and other property suitability determinations.
  • Hazardous Substances and Petroleum Products: Ensures all reportable quantities under 40 CFR §302.4 and 40 CFR §373 are documented, and clarifies eligibility for reporting uncontaminated property under CERFA.
  • Additional Considerations: Addresses the inclusion of emerging chemicals of environmental concern and the need for compliance with other applicable federal, state, and local environmental laws.

Applications

ASTM D6008-22 has broad applicability across the federal real estate management and environmental compliance sectors:

  • Federal Property Transfers: Used by agencies when transferring property via deed or lease to assert uncontaminated status or to disclose historical hazardous substance use.
  • Military Base Closures: Essential for documenting environmental baseline conditions in military installation realignments and closures.
  • GSA Property Disposal: Supports compliance with GSA regulations regarding the disposal of federal real property assets.
  • Environmental Due Diligence: Facilitates due diligence obligations related to hazardous substance identification, including areas with asbestos, lead-based paint, underground storage tanks, and contaminated wells.
  • Public Health and Environmental Protection: Ensures thorough identification of environmental hazards to protect human health and the environment during federal property reuse or redevelopment.
  • Support for Non-Federal Agencies: While created for federal properties, state and local agencies can also leverage this practice for environmental review and documentation of non-federal properties.

Related Standards

ASTM D6008-22 references several key standards, regulations, and guidance documents:

  • ASTM D5746: Standard Classification of Environmental Condition of Property Area Types.
  • ASTM E1527: Standard Practice for Environmental Site Assessments: Phase I Environmental Site Assessment Process.
  • ASTM E2247, E2107, E2365: Various standards for environmental due diligence and compliance audits.
  • 40 CFR §302.4, §373: EPA regulatory lists for hazardous substances and reporting activities in property transfers.
  • 41 CFR §102-75: GSA federal management regulations for real property disposal.
  • DODM 4165.66M: Department of Defense guidance on property redevelopment and realignment.
  • CERCLA and CERFA: Federal statutes governing environmental condition and property transfer obligations.
  • EPA Best Practices and Databases: Including the Superfund Enterprise Management System, Envirofacts, and federal facility cleanup guidance.

Keywords: ASTM D6008-22, environmental condition of federal property, ECP report, CERCLA, CERFA, federal property transfer, hazardous substances, GSA real property, environmental due diligence, property classification, environmental assessment standard.

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Frequently Asked Questions

ASTM D6008-22 is a standard published by ASTM International. Its full title is "Standard Practice for Determining the Environmental Condition of Federal Property". This standard covers: SIGNIFICANCE AND USE 4.1 Uses—This practice is intended for use by federal agencies, and environmental professionals in order to facilitate ECP efforts. It is also intended for use by preparers and reviewers of environmental condition of property maps and ECP reports used to support CERFA uncontaminated property identifications and property suitable for transfer by lease or by deed. GSA regulations addressing the disposal of federal property (41 CFR §105-72), require the landholding agency to assert either that (a) there is no evidence of hazardous substance activity, or (b) there is evidence of hazardous substance activity that occurred on the property. If there is evidence that hazardous substance activity occurred on the property, the landholding agency has a “due diligence” obligation to provide detailed, accurate information on all “reportable quantities” of hazardous substances stored, released, or disposed of on property that it reports to GSA for disposal. The specific substances that must be reported under CERCLA and their reporting limits are described in 40 CFR §302.4 and 40 CFR §373. If the landholding agency discloses that hazardous substance activity took place on the property, then the landholding agency must assert whether or not all required remedial action necessary to protect human health and the environment has been taken with respect to those hazardous substances. 4.1.1 The ECP reports prepared in accordance with this practice may be used to achieve compliance with the federal Management Regulations, Real Property Disposal rules codified in 41 CFR §102-75. 4.2 Clarifications on Use: 4.2.1 Use Not Limited to CERCLA—This practice is designed to assist the user in developing information about the environmental condition of a property and as such has utility for a wide range of persons, including those who may have no actual or potential CERCLA liability (see 40 CFR §373, 41 CFR §102-75 and Section 208 of the Federal Land Policy and Management Act, Public Law ... SCOPE 1.1 Purpose—The purpose of this practice is to define good commercial and customary practice in the United States for assessing the environmental condition of property (ECP) of federal real property. This practice applies to property under consideration for lease, excess and surplus property at closing and realigning military installations, claims reverting to federal ownership such as abandoned mines, and other federally-owned property. The steps in this practice are conducted to fulfill certain requirements of the Comprehensive Environmental Response, Compensation and Liability Act of 1980 (CERCLA) section 120(h), as amended by the Community Environmental Response Facilitation Act of 1992 (CERFA) and the federal real property disposal regulations codified in 41 CFR Subpart C (41 CFR 102-75). As such, this practice is intended to help a user to gather and analyze data and information in order to classify property into the applicable environmental condition of property area types (in accordance with the ASTM D5746, Standard Classification of Environmental Condition of Property Area Types, (see Appendix X1). Once documented, the ECP report is used to support Findings of Suitability to Transfer (FOSTs), Findings of Suitability to Lease (FOSLs), or uncontaminated property determinations, or a combination thereof, pursuant to the requirements of CERFA and CERCLA § 120(h). Users of this practice should note that it does not address (except where explicitly noted) requirements for appropriate and timely regulatory consultation or concurrence, or both, during the conduct of the ECP or during the identification and use of the standard environmental condition of property area types. 1.1.1 Environmental Condition of Property—In accordance with the federal landholding agency policies and General Services Administration’s (GSA) federal real property management regulations, an ECP will be prepared or evaluated for its usefulness (...

SIGNIFICANCE AND USE 4.1 Uses—This practice is intended for use by federal agencies, and environmental professionals in order to facilitate ECP efforts. It is also intended for use by preparers and reviewers of environmental condition of property maps and ECP reports used to support CERFA uncontaminated property identifications and property suitable for transfer by lease or by deed. GSA regulations addressing the disposal of federal property (41 CFR §105-72), require the landholding agency to assert either that (a) there is no evidence of hazardous substance activity, or (b) there is evidence of hazardous substance activity that occurred on the property. If there is evidence that hazardous substance activity occurred on the property, the landholding agency has a “due diligence” obligation to provide detailed, accurate information on all “reportable quantities” of hazardous substances stored, released, or disposed of on property that it reports to GSA for disposal. The specific substances that must be reported under CERCLA and their reporting limits are described in 40 CFR §302.4 and 40 CFR §373. If the landholding agency discloses that hazardous substance activity took place on the property, then the landholding agency must assert whether or not all required remedial action necessary to protect human health and the environment has been taken with respect to those hazardous substances. 4.1.1 The ECP reports prepared in accordance with this practice may be used to achieve compliance with the federal Management Regulations, Real Property Disposal rules codified in 41 CFR §102-75. 4.2 Clarifications on Use: 4.2.1 Use Not Limited to CERCLA—This practice is designed to assist the user in developing information about the environmental condition of a property and as such has utility for a wide range of persons, including those who may have no actual or potential CERCLA liability (see 40 CFR §373, 41 CFR §102-75 and Section 208 of the Federal Land Policy and Management Act, Public Law ... SCOPE 1.1 Purpose—The purpose of this practice is to define good commercial and customary practice in the United States for assessing the environmental condition of property (ECP) of federal real property. This practice applies to property under consideration for lease, excess and surplus property at closing and realigning military installations, claims reverting to federal ownership such as abandoned mines, and other federally-owned property. The steps in this practice are conducted to fulfill certain requirements of the Comprehensive Environmental Response, Compensation and Liability Act of 1980 (CERCLA) section 120(h), as amended by the Community Environmental Response Facilitation Act of 1992 (CERFA) and the federal real property disposal regulations codified in 41 CFR Subpart C (41 CFR 102-75). As such, this practice is intended to help a user to gather and analyze data and information in order to classify property into the applicable environmental condition of property area types (in accordance with the ASTM D5746, Standard Classification of Environmental Condition of Property Area Types, (see Appendix X1). Once documented, the ECP report is used to support Findings of Suitability to Transfer (FOSTs), Findings of Suitability to Lease (FOSLs), or uncontaminated property determinations, or a combination thereof, pursuant to the requirements of CERFA and CERCLA § 120(h). Users of this practice should note that it does not address (except where explicitly noted) requirements for appropriate and timely regulatory consultation or concurrence, or both, during the conduct of the ECP or during the identification and use of the standard environmental condition of property area types. 1.1.1 Environmental Condition of Property—In accordance with the federal landholding agency policies and General Services Administration’s (GSA) federal real property management regulations, an ECP will be prepared or evaluated for its usefulness (...

ASTM D6008-22 is classified under the following ICS (International Classification for Standards) categories: 13.020.40 - Pollution, pollution control and conservation. The ICS classification helps identify the subject area and facilitates finding related standards.

ASTM D6008-22 has the following relationships with other standards: It is inter standard links to ASTM D5746-24, ASTM E2247-23, ASTM D5746-23, ASTM D5746-98(2016), ASTM E2247-16, ASTM D5746-98(2010), ASTM E2247-08, ASTM E2107-06, ASTM E1527-05, ASTM E2365-05, ASTM E2247-02, ASTM E2107-00, ASTM E1527-00, ASTM E1527-97, ASTM D5746-98. Understanding these relationships helps ensure you are using the most current and applicable version of the standard.

ASTM D6008-22 is available in PDF format for immediate download after purchase. The document can be added to your cart and obtained through the secure checkout process. Digital delivery ensures instant access to the complete standard document.

Standards Content (Sample)


This international standard was developed in accordance with internationally recognized principles on standardization established in the Decision on Principles for the
Development of International Standards, Guides and Recommendations issued by the World Trade Organization Technical Barriers to Trade (TBT) Committee.
Designation: D6008 − 22
Standard Practice for
Determining the Environmental Condition of Federal
Property
This standard is issued under the fixed designation D6008; the number immediately following the designation indicates the year of
original adoption or, in the case of revision, the year of last revision. A number in parentheses indicates the year of last reapproval. A
superscript epsilon (´) indicates an editorial change since the last revision or reapproval.
1. Scope property to be transferred by deed or leased. The ECP will be
based on existing environmental information related to
1.1 Purpose—The purpose of this practice is to define good
storage, release, treatment, or disposal of hazardous
commercial and customary practice in the United States for
substances, munitions, or petroleum products on the property
assessing the environmental condition of property (ECP) of
to determine or discover the obviousness of the presence or
federal real property. This practice applies to property under
likely presence of a release or threatened release of any
consideration for lease, excess and surplus property at closing
hazardous substance or petroleum product. In certain cases,
and realigning military installations, claims reverting to federal
additional data, including sampling, if appropriate under the
ownership such as abandoned mines, and other federally-
circumstances, may be needed in the ECP to support the FOST
owned property. The steps in this practice are conducted to
or FOSL. A previously conducted ECP may be updated as
fulfillcertainrequirementsoftheComprehensiveEnvironmen-
necessary and used for making a FOSTor FOSL.An ECP also
tal Response, Compensation and Liability Act of 1980 (CER-
may help to satisfy other environmental requirements (for
CLA) section 120(h), as amended by the Community Environ-
example, to satisfy the requirements of CERFA or to facilitate
mental Response Facilitation Act of 1992 (CERFA) and the
the preparation of environmental condition reports). In
federal real property disposal regulations codified in 41 CFR
addition, the ECP provides a useful reference document and
Subpart C (41 CFR 102-75).As such, this practice is intended
assists in compliance with hazard abatement policies related to
to help a user to gather and analyze data and information in
asbestos and lead-based paint. The ECP process consists of
order to classify property into the applicable environmental
discrete steps. This practice principally addresses ECP-related
condition of property area types(inaccordancewiththeASTM
information gathering and analysis.
D5746, Standard Classification of Environmental Condition of
Property Area Types, (see Appendix X1). Once documented,
1.1.1.1 Discussion—Prior versions of this practice referred
the ECP report is used to support Findings of Suitability to
to environmental baseline surveys (EBS). The 2018 Depart-
Transfer (FOSTs), Findings of Suitability to Lease (FOSLs), or
ment of Defense 4165.66M Base Redevelopment and Realign-
uncontaminated property determinations, or a combination
mentManualchangedthefocusto ECP.Appendix3ofDODM
thereof, pursuant to the requirements of CERFAand CERCLA
4165.66M provides direction on the preparation of FOST and
§ 120(h). Users of this practice should note that it does not
FOSL documentation. Section C2.4.2.3 of DODM 4165.66M
address (except where explicitly noted) requirements for ap-
provides direction for Department of Defense property pro-
propriate and timely regulatory consultation or concurrence, or
posed for disposal and redevelopment.
both,duringtheconductofthe ECPorduringtheidentification
1.1.2 CERCLA Section 120(h) Requirements—This practice
and use of the standard environmental condition of property
is intended to assist with the identification of federal real
area types.
property and DoD installation areas subject to the notification
1.1.1 Environmental Condition of Property—In accordance
andcovenantrequirementsofCERCLA§120(h)relatingtothe
with the federal landholding agency policies and General
deed transfer of contaminated federal real property (42 USC
ServicesAdministration’s(GSA)federalreal propertymanage-
9601 et seq.), (see Appendix X2). Examples of other federal
ment regulations, an ECP will be prepared or evaluated for its
landholding agencies that must comply with CERCLA§120(h)
usefulness (and updated if necessary) for any federally-owned
requirements include the Bureau of Land Management, the
Federal Aviation Administration, and U.S. Forest Service.
1.1.3 CERFA Requirements—This practice provides infor-
This practice is under the jurisdiction of ASTM Committee E50 on Environ-
mation to partially fulfill the identification requirements of
mental Assessment, Risk Management and Corrective Action and is the direct
responsibility of Subcommittee E50.02 on Real Estate Assessment and Manage-
CERFA [Pub. L. 102-426, 106 Stat. 2174], which amended
ment.
CERCLA. Property classified as area Type 1, in accordance
Current edition approved Sept. 1, 2022. Published December 2022. Originally
with Classification D5746 is eligible for reporting as “uncon-
approved in 1937 as PS 37. Last previous edition approved in 2014 as D6008-
96(2014). DOI: 10.1520/D6008-22. taminated” under the provisions of CERFA and the Federal
Copyright © ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959. United States
D6008 − 22
Management Regulations, Real Property Disposal rules codi- 1.1.7 Non-Federal Property—This standard may also be
fied in 41 CFR 102-75.Additionally, certain property classified used by state and local agencies to assess the environmental
as area Type 2, where evidence indicates that storage occurred
condition of non-federal property.
for less than one year, may also be identified as uncontami-
1.2 Objectives—Objectives guiding the development of this
nated. At installations and federal property listed on the
practice are (1) to synthesize and put in writing a standard
National Priorities List, Environmental Protection Agency
practice for conducting a high quality ECP, (2) to facilitate the
(EPA) concurrence must be obtained for the property to be
development of high quality, standardized environmental con-
considered “uncontaminated” and therefore transferable under
dition of property maps to be included in an ECP that can be
CERCLA § 120(h)(4). The EPA has stated that there may be
used to support FOSTs, FOSLs, and other applicable environ-
instances in which it would be appropriate to concur with the
mental condition reports, (3) to facilitate the use of the
federal landholding agency that certain property can be iden-
standard classification of environmental condition of property
tified as uncontaminated under CERCLA§ 120(h)(4) although
area types (see Classification D5746), (4) to facilitate the
some limited quantity of hazardous substances or petroleum
development of a standard guide for preparing and updating
products have been stored, released,or disposed of on the
ECP reports, and (5) comply with the Federal Real Property
property (see EPA Office of Enforcement and Compliance
Disposal regulations codified in 41 CFR 102-75.
Assurance, May 2019). If the information available indicates
that the storage, release,or disposal was associated with
1.3 Limitations—Users of this practice should note that,
activities that would not be expected to pose a threat to human
while many of the elements of an ECP are performed in a
health or the environment (for example, housing areas,
manner consistent with other “due diligence” functions, an
petroleum-stainedpavementareas,andareashavingundergone
ECP is not prepared to satisfy a purchaser of real property’s
routine application of pesticides), such property should be
duty to conduct “all appropriate inquiries”, as defined in 40
eligible for expeditious reuse.
CFR 312, to establish an “innocent landowner defense”to
NOTE 1—Confirmed releases of emerging chemicals of environmental CERCLA § 107 liability. Any such use of any ECP by any
concern may require additional consideration (see Office of the Under-
party is outside the control of the federal agencies and beyond
secretary of Defense. Policy Memorandum for Clarifications and Upcom-
the scope of any ECP. No warranties or representations are
ingChangestoDepartmentofDefenseInstruction4715.18inResponseto
made by any federal agency, its employees, or contractors that
Department of Defense Office of Inspector General Findings,April 2022).
any ECP report satisfies any such requirement for any party.
1.1.4 Petroleum Products—Petroleum products and their
1.4 Organization of This Practice—This practice has 15
derivativesareincludedwithinthescopeofthispractice.Areas
sections. Section 1 is the scope. Section 2 identifies referenced
on which petroleum products or their derivatives were stored
documents. Section 3, Terminology, includes definitions of
for one year or more, known to have been released or disposed
terms not unique to this practice, descriptions of terms unique
of [CERCLA§ 120(h)(4)] are not eligible to be reported as
to this practice, and acronyms and abbreviations. Section 4 is
“uncontaminated property” under CERFA.
the significance and use of this practice. Section 5 describes
1.1.5 Other Federal, State, and Local Environmental
user’sresponsibilities.Sections6–13arethemainbodyofthe
Laws—This practice does not address requirements of any
data gathering analysis steps of the ECP process. Section 14
federal, state, or local laws other than the applicable provisions
briefly describes the ECP Step 3 classification of environmen-
of CERCLA identified in 1.1.2 and 1.1.3. These applicable or
tal condition of property area types. Section 15 contains a list
relevant and appropriate requirements (ARARs) may have a
of keywords. The seven appendices are non-binding and
bearing upon the ultimate disposition of the federal property.
non-mandatory; they provide background, guidance, and ex-
Users are cautioned that federal, state, and local laws may
amples.
impose additional ECP or other environmental assessment
obligations that are beyond the scope of this practice. Users
1.5 This standard does not purport to address all of the
should also be aware that there are likely to be other legal
safety concerns, if any, associated with its use. It is the
obligations with regard to hazardous substances or petroleum
responsibility of the user of this standard to establish appro-
products discovered on property that are not addressed in this
priate safety, health, and environmental practices and deter-
practice and that may pose risks of civil or criminal sanctions,
mine the applicability of regulatory limitations prior to use.
or both, for noncompliance.
1.6 This international standard was developed in accor-
1.1.6 Other Federal, State, and Local Real Property and
dance with internationally recognized principles on standard-
Natural and Cultural Resources Laws—This practice does not
ization established in the Decision on Principles for the
address requirements of any federal, state or local real property
Development of International Standards, Guides and Recom-
or natural and cultural resources laws. Users are cautioned that
mendations issued by the World Trade Organization Technical
numerous federal, state, and local laws may impose additional
Barriers to Trade (TBT) Committee.
environmental and other legal requirements that must be
satisfied prior to deed transfer of property that are beyond the
scope of this practice.
NOTE 2—The General Services Administration’s Excess Real Property
Due Diligence Checklist for Federal Landholding Agency Customers,
November 2017, provides additional detail on federal ARARs.
D6008 − 22
2. Referenced Documents Title 41, Code of Federal Regulations (CFR) Part 102-75
2 Federal Management Regulations, Subchapter C, Real
2.1 ASTM Standards:
Property Disposal
D5746 Classification of Environmental Condition of Prop-
2.4 US EPA References and Databases:
erty Area Types for Defense Base Closure and Realign-
RCRA40CFRPart264, SubpartXPermitWritersTechnical
ment Facilities
Resource Document. EPA, Office of Solid Waste,
E1527 Practice for Environmental SiteAssessments: Phase I
Washington, DC. June 1997
Environmental Site Assessment Process
OLEM Directive 9200.2-187, Best Practice Process for
E2107 Practice for Environmental Regulatory Compliance
Identifying and Determining StateApplicable or Relevant
Audits
andAppropriate Requirements Status Pilot, October 2017
E2247 Practice for Environmental SiteAssessments: Phase I
EPA Office of Enforcement and Compliance Assur-
Environmental Site Assessment Process for Forestland or
ance, Transmittal of Revised Policy Towards Landowners
Rural Property
and Transferees of Federal Facilities to Encourage
E2365 Guide for Environmental Compliance Performance
Cleanup and Reuse at Federal Facilities on the National
Assessment
Priorities List (NPL), May 2019
2.2 Federal Landholding Agency Documents:
Envirofacts A single point of access to select U.S. EPA
Department of the Navy Base Realignment and Closure
environmental data. This website provides access to sev-
Implementation Guidance, March 2007
eral EPA databases to provide the user with information
U.S. Army Regulation 200-1, Environmental Protection and
about environmental activities that may affect air, water,
Enhancement, December 2007
and land anywhere in the United States (https://
Department of Defense Manual 4715.20, Defense Environ-
enviro.epa.gov/)
mental Restoration Program (DERP) Management, Au-
FEDFacts Information about the Federal Electronic Docket
gust 2018
Facilities regarding contaminated federal facility sites in
DepartmentofDefense4165.66M, BaseRedevelopmentand
specific communities, technical fact sheets and tools and
Realignment Manual, August 2018
resources to help government agencies and their contrac-
Department of Defense Instruction 4715.18, Emerging
tors fulfill cleanup obligations (https://www.epa.gov/
Chemicals (ECs) of Environmental Concern, September
fedfac)
4, 2019
Superfund Enterprise Management System (https://ww-
Department of the Air Force Instruction 32-7020, Environ-
w.epa.gov/enviro/sems-search)
mental Restoration Program, December 2020
Office of the Undersecretary of Defense, Policy Memoran-
3. Terminology
dum for Clarifications and Upcoming Changes to Depart-
3.1 This section provides definitions (of terms not unique to
ment of Defense Instruction 4715.18 in Response to
thispractice),descriptionsoftermsspecifictothispractice,and
Department of Defense Office of Inspector General
a list of acronyms and abbreviations used herein.The terms are
Findings, April 2022
an integral part of this practice and are critical to its under-
2.3 Federal Regulations:
standing and use.
Title 32, Code of Federal Regulations (CFR), Part 179,
3.2 Definitions:
Munitions Response Site Prioritization Protocol (MRSPP)
3.2.1 aqueous film forming foam (AFFF), n—a fire suppres-
Title 40, Code of Federal Regulations (CFR), Part 300,
santusedtoextinguishflammableliquidfiressuchasfuelfires.
National Oil and Hazardous Substances Pollution Contin-
3.2.1.1 Discussion—AFFF is often used in facility fire
gency Plan
suppression systems, fire fighting vehicles, and at fire training
Title 40, Code of Federal Regulations (CFR), Part 302,
facilities.
Designation Reportable Quantities and Notification
Title 40, Code of Federal Regulations (CFR) Part 312, 3.2.2 asbestos, n—six naturally occurring fibrous minerals
found in certain types of rock formations; of the six, the
Innocent Landowners, Standards for Conducting All Ap-
propriate Inquiries minerals chrysotile, amosite, and crocidolite have been most
commonly used in building products.
Title 40, Code of Federal Regulations (CFR), Part 355,
Emergency Planning and Notification 3.2.2.1 Discussion—Because asbestos is strong,
incombustible, and corrosion-resistant, asbestos was used in
Title 40, Code of Federal Regulations (CFR) Part 373,
Reporting Hazardous SubstanceActivity When Selling or many commercial products beginning early in the 20th century
and peaking in the period from World War II into the 1970s.
Transferring Federal Real Property
3.2.3 asbestos-containing material (ACM), n—any material
or product that contains more than 1 % asbestos.
For referenced ASTM standards, visit the ASTM website, www.astm.org, or
contact ASTM Customer Service at service@astm.org. For Annual Book of ASTM 3.2.4 contaminated public wells, n—public wells used for
Standards volume information, refer to the standard’s Document Summary page on
drinking water that have been designated by a government
the ASTM website.
Available from Department of Defense, Office of Environmental Security, 3400
Defense Pentagon, Washington, DC 20301-3400. AvailablefromUnitedStatesEnvironmentalProtectionAgency(EPA),William
Available from the Superintendent of Documents, U.S. Government Printing Jefferson Clinton Bldg., 1200 Pennsylvania Ave., NW, Washington, DC 20460,
Office, Washington, DC 20402. http://www.epa.gov.
D6008 − 22
entity as contaminated by toxic substances (for example, 3.2.11 hazardous waste, n—any hazardous waste having the
chlorinated solvents), or as having water unsafe to drink characteristics identified under or listed pursuant to section
without treatment. 3001 of the Solid Waste DisposalAct (42 USC § 6901 et seq.)
(but not including any waste the regulation of which under the
3.2.5 drum, n—as defined by the U.S. Department of
Solid Waste Disposal Act has been suspended by Act of
Transportation, a flat-ended or convex-ended cylindrical pack-
Congress).
aging made of metal, fiberboard, plastic, plywood, or other
3.2.11.1 Discussion—Some state waste management pro-
suitable materials; this definition does not include cylinders,
grams regulate additional solid wastes as hazardous waste.
jerricans, wooden barrels or bulk containers.
3.2.12 landfill, n—a place, location, tract of land, area, or
3.2.5.1 Discussion—A metal or plastic container (typically,
premises used for the disposal of solid wastes as defined by
but not necessarily, holding 55 gal [208 L] of liquid) that may
state solid waste regulations. The term is synonymous with the
have been used to store hazardous substances or petroleum
term solid waste disposal site and is also known as a garbage
products.
dump, trash dump, or similar term.
3.2.6 dwelling, n—structure or portion thereof used for
3.2.12.1 Discussion—The user is cautioned that not all
residential habitation.
garbage dumps and trash dumps have permits issued by either
3.2.7 environmental lien, n—a charge, security, or encum-
the state or local regulatory agency.
brance upon title to a property to secure the payment of a cost,
3.2.13 local street directories, n—directories published by
damage, debt, obligation, or duty arising out of response
private (or sometimes government) sources that list the occu-
actions, cleanup, or other remediation of hazardous substances
pant(s) of a specific address at the time the occupant data was
or petroleum products upon a property, including (but not
collected, typically within in a year of the publication date of
limited to) liens imposed pursuant to CERCLA 42 USC §
the directory.
9607(1) and similar state or local laws.
3.2.13.1 Discussion—Local street directories may not be
3.2.8 emerging chemicals of environmental concern, n—as
available for federally-owned property.
defined in DoDI 4715.18, chemicals relevant to the DoD that
3.2.14 munitions and explosives of concern,
are characterized by a perceived or real threat to human health
n—distinguishes specific categories of military munitions that
or the environment and that have new or changing toxicity
may pose unique explosives safety risks, such as unexploded
values or new or changing human health or environmental
ordnance, as defined in 10 U.S.C. §101(e)(5); discarded
regulatory standards.
military munitions, as defined in 10 U.S.C. §2710(e)(2); or
3.2.8.1 Discussion—These chemicals are defined as emerg-
munitions constituents (for example,TNT, RDX), as defined in
ing contaminants in Practice E1527. Per- and polyfluoroalkyl
10 U.S.C. §2710(e)(3), present in high enough concentrations
substances (PFAS) are examples of emerging chemicals of
to pose an explosive hazard.
environmental concern at federally-owned property. Although
3.2.15 National Contingency Plan (NCP), n—the National
PFAS are not currently regulated as hazardous substances
Oil and Hazardous Substances Pollution Contingency Plan
under CERCLA, some states have begun regulating the dis-
foundat40CFR§300,whichistheEPA’sregulationsforhow
posal or remediation of PFAS-impacted soil, sediment, surface
releases of hazardous substances are to be cleaned up pursuant
water,andgroundwater.Forfederal propertywherefirefighting
to CERCLA.
activities, including training, were conducted with aqueous
3.2.16 National Priorities List, n—list compiled by EPA
film-forming foam (AFFF) and properties where electroplating
pursuant to CERCLA 42 USC § 9605(a)(8)(B) of properties
operations were conducted, the user may refer to Appendix X4
with the highest priority for cleanup pursuant to EPA’s Hazard
for guidance addressing emerging chemicals of environmental
Ranking System. See 40 CFR Part 300.
concern. See also the Policy Memorandum for Clarifications
and Upcoming Changes to Department of Defense Instruction
3.2.17 occupants, n—those tenants, subtenants, or other
4715.18 in Response to Department of Defense Office of
persons or entities using the property or a portion of the
Inspector General Findings, April 2022.
property.
3.2.9 ERNS list, n—the Emergency Response Notification
3.2.18 per- and polyfluoroalkyl substances (PFAS), n—a
System (ERNS) is a database used to store information on
group of manufactured chemicals consisting of polymeric
notifications of oil discharges and hazardous substances re-
chains of carbon bonded to fluorine atoms, usually with a polar
leases.
functional group at the head.
3.2.9.1 Discussion—EPA’s Emergency Response Notifica-
3.2.18.1 Discussion—PFAS are fluorinated substances with
tion System is a list of reported CERCLA hazardous substance
acarbonchainstructure.Inperfluoroalkylsubstances(PFAAs),
releases or spills in quantities equal to or greater than the each carbon atom in the chain is fully saturated with fluorine
reportable quantity, as maintained by the National Response
(carbon-fluorine bonds only), whereas the carbon chain in
Center. Notification requirements for such releases or spills are polyfluoroalkyl substances is mostly saturated with fluorine
codified in 40 CFR Parts 302 and 355.
(carbon-fluorine bonds), but also contains carbon-hydrogen
bonds.
3.2.10 hazardous substance, n—means that group of sub-
stances defined as hazardous under CERCLA §101(14), and 3.2.19 Phase I Environmental Site Assessment, n—the pro-
that appear at 40 CFR §302.4. cess described in Practice E1527 and Practice E2247.
D6008 − 22
3.2.20 pits, ponds, or lagoons, n—man-made or natural term landfill and is also known as a garbage dump, trash dump,
depressions in a ground surface that are likely to hold liquids or similar term. Historic solid waste disposal sites at federally-
or sludge containing hazardous substances or petroleum prod- owned properties may not have operated under a permit.
ucts.
3.2.31 solvent, n—a chemical compound that is capable of
3.2.20.1 Discussion—The likelihood of such liquids or
dissolving another substance and a hazardous substance, used
sludge being present is determined by evidence of factors
in a number of manufacturing/industrial processes including
associated with the pit, pond, or lagoon, including, but not
but not limited to dry cleaning, the manufacture of paints and
limited to, discolored water, distressed vegetation, or the
coatings for industrial and household purposes, equipment
presence of an obvious wastewater discharge.
clean-up, and surface degreasing in industrial settings.
3.2.21 property, n—real property, including buildings,
3.2.31.1 Discussion—Solvents are routinely use for parts
fixtures, and other improvements located on and affixed to the
washing and the preparation of metal surfaces for plating.
land.
3.2.32 State registered USTs, n—State lists of underground
3.2.22 property tax files, n—the files kept for property tax
storagetanksrequiredtoberegisteredunderSubtitleI,Section
purposes by the local jurisdiction where the property is located
9002 of RCRA.
and includes records of past ownership, appraisals, maps,
3.2.33 sump, n—a pit, cesspool, or similar receptacle where
sketches, photos, or other information that is reasonably
liquids drain, collect, or are stored.
ascertainable and pertaining to the property.
3.2.34 Superfund Enterprise Management System (SEMS),
3.2.23 RCRA generators, n—those persons or entities that
n—the official repository for site and non site-specific Super-
generate hazardous wastes, as defined and regulated by RCRA
fund data in support of the Comprehensive Environmental
and have submitted EPA form 8700-12 to the EPA.
Response, Compensation, and Liability Act (CERCLA). It
3.2.24 RCRA generators list, n—list kept by EPA of those
contains information on hazardous waste site assessment and
persons or entities that have notified EPA that they generate
remediation.
hazardous wastes, as defined and regulated by RCRA.
3.2.34.1 Discussion—SEMS contains information on haz-
3.2.25 RCRA TSD facilities, n—those facilities on which ardous waste site assessment and remediation including PAs,
treatment, storage,or disposal, or a combination thereof, of remedial investigations and feasibility studies, chemicals of
hazardous wastes takes place, subject to regulation and per- concern, and 5-year review reports.
mitting under RCRA or a delegated state’s hazardous waste
3.2.35 underground storage tank (UST), n—any one or
management program; these facilities have submitted EPA
combination of tanks (including underground pipes connected
Form 8700-23 to the EPA.
thereto) that is used to contain an accumulation of regulated
3.2.26 RCRA TSD facilities list, n—listkeptbyEPAofthose
substances, and the volume of which (including the volume of
facilities that have submitted EPAForm 8700-23 to the agency. underground pipes connected thereto) is 10 percent or more
beneath the surface of the ground.
3.2.27 recorded land title records, n—records of fee
3.2.35.1 Discussion—for the purposes of this practice,regu-
ownership, leases, land contracts, easements, liens, and other
lated substances include hazardous substances, and petroleum
encumbrances on or of the property recorded in the place
and materials subject to regulation under 40 CFR Part 280.
where land title records are, by law or custom, recorded for the
local jurisdiction in which the property is located (see 3.2.32
3.2.36 USGS 7.5 Minute Topographic Map, n—the phrase
and 7.2.4, and 40 CFR §312.24(a)).
“USGS topographic map” refers to maps that cover a quad-
rangle that measures 7.5 minutes of longitude and latitude on
3.2.28 records of emergency release notifications (SARA§
all sides, so these are also referred to as 7.5-minute maps,
304),n—Section 304 of EPCRAor Title III of SARArequires
quadrangle maps, or “quad” maps with a wide range of scales,
operators of facilities to notify their local emergency planning
but the scale used for all modern USGS topographic maps is
committee (as defined in EPCRA) and state emergency re-
1:24,000.
sponse commission (as defined in EPCRA) of any release
beyond the facility’s boundary of any reportable quantity of
3.2.37 wastewater, n—water that (1) means any water
any extremely hazardous substance.
which, during manufacturing or processing, comes into direct
3.2.28.1 Discussion—Records of such notifications are “re-
contact with or results from the production or use of any raw
cords of emergency release notifications” (SARA § 304) and
material, intermediate product, finished product, byproduct, or
may be found in the ERNS database.
waste product or (2) conveys or has conveyed sewage.
3.2.37.1 Discussion—Wastewater does not include water
3.2.29 safety data sheet (SDS), n—written or printed mate-
rial concerning a hazardous substance which is prepared by originating on or passing through or adjacent to a site, such as
stormwater flows, that has not been used in industrial or
chemical manufacturers, importers, and employers for hazard-
ous chemicals pursuant to OSHA’s Hazard Communication manufacturing processes, has not been combined with sewage,
or is not directly related to manufacturing, processing, or raw
Standard, 29 CFR 1910.1200.
materials storage areas at an industrial plant. Wastewater
3.2.30 solid waste disposal site, n—aplace,location,tractof
includes washdown water that flows to a floor drain, sump,or
land, area, or premises used for the disposal of solid wastes as
drywell.
defined by state solid waste regulations.
3.2.30.1 Discussion—The term is synonymous with the 3.3 Definitions of Terms Specific to This Standard:
D6008 − 22
3.3.1 adjoining properties, n—any real property or proper- been transferred to federal control through Congressional
ties the border of which is (are) shared in part or in whole with action. The FOSL or FOST may be limited to an area in
thatofthefederally-owned property,orthatwouldbesharedin question as opposed to a larger federally-owned property.
part or in whole with that of the federally-owned property but
3.3.7 BRAC statutes, n—Title II of the Defense Authoriza-
for a street, road, or other public thoroughfare separating the
tion Amendments and Base Closure and Realignment Act of
properties.
1988 (Pub. L. 100-526, 10 USC 2687, note.) and the Defense
Base Closure and Realignment Act of 1990 (Part A of Title
3.3.2 aerial photographs, n—photographs, taken from an
XXIX of Pub. L. 101-510, 10 USC 2687, note.), collectively.
aerial platform, having sufficient resolution to allow identifi-
3.3.7.1 Discussion—The 2005 Round (P.L. 107-107);
cation of development and activities of areas encompassing the
amended the Defense Base Closure and Realignment Act of
property.
1990 (P.L. 101- 510). No new BRAC activities have been
3.3.2.1 Discussion—Aerial photographs are commonly
authorized by Congress since 2016.
available from government agencies or private collections
unique to a local area.
3.3.8 DoD component, n—collectively, the Office of the
Secretary of Defense, the Military Departments, the Chairman
3.3.3 all required remedial action, n—for the purposes of
of the Joint Chiefs of Staff, the Inspector General of the
this practice, all remedial action, as described in CERCLA§
Department of Defense, the Defense Agencies and the DoD
120(h)(3)(B)(i), has been taken if “the construction and instal-
Field Activities.
lation of an approved remedial design has been completed, and
the remedy has been demonstrated to the administrator [of 3.3.9 disposal, v—the discharge, deposit, injection,
EPA] to be operating properly and successfully; the carrying dumping, spilling, leaking, or placing of any hazardous
out of long-term pumping and treating, or operation and substances, or petroleum products or their derivatives into or
maintenance, after the remedy has been demonstrated to the on any land or water so that such hazardous substances,or
administrator to be operating properly and successfully does petroleum products or their derivatives or any constituent
not preclude the transfer of the property.” [42 USC § thereof may enter the environment or be emitted into the air or
9620(h)(3)]. discharged into any waters including ground water.
3.3.3.1 Discussion—Alternatively,incircumstanceswherea
3.3.10 due diligence, n—the process, in accordance with 41
remedy has been constructed, but no ongoing treatment or
CFR §102.75-115 through §102-75.130, of inquiring into the
operation and maintenance is required, for example, “clean
environmental characteristics of a federal property scheduled
closure” or excavation of soil with off-site treatment, all
for transfer, sale, or disposal.
remedial action means that all action required to meet appli-
3.3.11 environmental compliance audit, n—theinvestigative
cable state or federal regulatory standards, including, as
process to determine if the operations of an existing facility are
required, state or federal regulatory approval, has been taken
in compliance with applicable environmental laws and regula-
(see section 12.2). Land use restrictions may be components of
tions (see E2107 and E2365).
required remedial action.
3.3.12 environmental condition of property (ECP), n—a
3.3.4 applicable or relevant and appropriate requirements
survey of federal real property based on all existing environ-
(ARARs), n—those cleanup standards, standards of control, and
mental information related to storage, release, treatment, or
other substantive requirements, criteria, or limitations promul-
disposal of hazardous substances or petroleum products or
gated under federal environmental or State environmental or
derivatives on the property to determine or discover the
facility siting laws that, while not “applicable” to a hazardous
obviousness of the presence or likely presence of a release or
substance, pollutant, contaminant, remedial action, location, or
threatened release of any hazardous substance or petroleum
other circumstance at a CERCLA site, address problems or
product.
situations sufficiently similar to those encountered at the
3.3.12.1 Discussion—In certain cases, additional data, in-
CERCLA site that their use is well suited to the particular site
cluding sampling and analysis, may be needed in the ECP to
(see EPA OLEM 9200.1-187).
support the classification of the property into one of the
3.3.4.1 Discussion—Only those state standards that are
standard environmental condition of property area types.
identified in a timely manner and are more stringent than
Additionally, an ECP may also satisfy the uncontaminated
federal requirements may be relevant and appropriate.
property identification requirements of CERFA. An ECP will
3.3.5 approximate minimum search distance, n—theareafor consider all sources of available information concerning envi-
which agency records must be obtained and reviewed pursuant ronmentally significant current and past uses of the real
to Section 7 subject to the limitations provided in that section. propertyandshall,ataminimum,consistofthestepsidentified
3.3.5.1 Discussion—This may include areas outside the in Section 6.
federally-owned property and shall be measured from the
3.3.13 environmental condition of property (ECP) report,
nearest property boundary. This term is used instead of radius
n—the written record of an ECP; see Appendix X5 for a
to include irregularly shaped properties.
recommended report format.
3.3.13.1 Discussion—The ECP report is the documentation
3.3.6 area in question, n—that portion of federal real
for the Standard Classification in accordance with D5746.
property that is the subject of the ECP.
3.3.6.1 Discussion—The area in questionmaybeasubsetof 3.3.14 environmental condition of property area type,
a larger piece of federal property or may be property that has n—any of the seven standard environmental condition of
D6008 − 22
property area types defined in D5746, Standard Classification kilogram if the substances are listed under 40 CFR § 261.30 as
of Environmental Condition of Property Area Types (see acutely hazardous substances.
Appendix X1).
3.3.20 innocent landowner defense, n—that defense to
CERCLAliabilityprovidedin42USC§9601(35)and42USC
3.3.15 environmental condition of property map, n—a map,
prepared on the basis of all environmental investigation infor- § 9607(b)(3) (see also 40 CFR Part 312).
mation conducted to date, that shows the environmental
3.3.20.1 Discussion—One of the requirements to qualify for
condition of a DoD installation’s or federal agency’s real
this defense is that the party make “all appropriate inquiry into
property in terms of the seven standard environmental condi-
the previous ownership and uses of the property consistent
tion of property area types as defined in the standard classifi-
with good commercial or customary practice.” (see 40 CFR
cation D5746.
§312).
3.3.16 environmental investigation, n—any investigation in-
3.3.21 installation restoration program (IRP), n—the DoD
tended to determine the nature and extent of environmental
program, mandated by 10 USC § 2701-2710 to assess and
contamination or to determine the environmental condition of
respond to releases of hazardous substances on military
property at a DoD installation or other federally-owned prop-
property under the control of the military services.
erty.
3.3.21.1 Discussion—Tthe IRP is one of two programs
3.3.16.1 Discussion—Environmental investigations may
established under the Defense Environmental Restoration Pro-
include, but are not limited to, environmental site assessments, gram (DERP) to identify, investigate and clean up hazardous
preliminary assessments (PAs), site inspections, remedial
substances, pollutants, and contaminants that pose environ-
investigations, ECPs, RCRA facility assessments, and RCRA mental health and safety risks at active military installations
facility investigations. The results of some environmental
and formerly used defense sites (FUDS). In 2001, DoD
investigations can be found in SEMS. established the Military Munitions Response Program
(MMRP) to address sites, referred to munitions response sites
3.3.17 environmental professional, n—a person possessing
or (MRSs) known or suspected to contain unexploded
sufficient training and experience necessary to conduct an ECP
ordnance, discarded military munitions, or munitions constitu-
including all activities related to this practice, and from the
ents. Through the IRP and MMRP, DoD complies with
information and data gathered by such activities, having the
environmental cleanup laws, such as CERCLA (see 32 CFR
ability to develop conclusions regarding environmental condi-
179,MunitionsResponseSitePrioritizationProtocol).The IRP
tion of property and recognized environmental conditions in
serves as an umbrella program for environmental response in
connection with the property being evaluated.
all media, including RCRAcorrective action, LUST corrective
3.3.17.1 Discussion—This individual may be an employee
action, as well as CERCLA removals and remedial actions.
or independent contractor of the user.An individual’s status as
Generally, where field sampling or intrusive environmental
an environmental professional may be limited to the type of
testing is required, the IRP will serve as a vehicle for such
ECP to be performed or to specific steps of the ECP for which
testing (see DoDM 4715.20).
the professional is responsible. The person may be an indepen-
3.3.22 interviews, n—sessions with current or former em-
dentcontractororanemployeeofthefederalgovernment.This
ployees involved in operations on the real property, conducted
definition is different than the definition of an environmental
to ascertain if storage, release, treatment, or disposal of
professional in the EPA’s All Appropriate Inquiries Rule (40
hazardous substances, petroleum products or their derivatives
CFR §312.10).
occurred or is occurring on the real property.
3.3.18 fill dirt, n—dirt, soil, sand, or other earth taken from
3.3.23 local government agencies, n—those agencies of
a different location, that is used to fill holes or depressions,
municipal or county government having jurisdiction over the
create mounds, or otherwise artificially change the grade or
property.
elevation of real property. It does not include material that is
used in limited quantities for normal landscaping activities. 3.3.23.1 Discussion—Municipal and county government
agencies include, but are not limited to, cities, parishes,
3.3.18.1 Discussion—The potential for fill dirt to be con-
townships, and similar entities. Local government agencies
taminated with hazardous substances should be considered,
may also include, where appropriate, state agencies with local
and if appropriate, the material should be tested and analyzed
jurisdiction which perform functions commonly performed in
for chemicals of concern.
other locations by local government agencies.
3.3.19 hazardous substance activity, v—defined as (1) the
3.3.24 migration, v—the movement of contaminant(s) away
known release of hazardous substances in quantities equal to
fromasourcethroughpermeablesubsurfacemedia(suchasthe
or greater than the reportable quantity found in 40 CFR §
movement of a ground water plume of contamination), or
302.4; (2) the disposal of a hazardous substance at the subject
movement of contaminant(s) by a combination of surficial and
facility; or (3) the storage for one year or more of a hazardous
subsurface processes; vapor intrusion is an example of migra-
substance in quantities of 1000 kilograms or more, or the
tion.
reportable quantity found in 40 CFR § 302.4, whichever is
greater.
3.3.25 obviousness, n—the condition of being plain or
3.3.19.1 Discussion—Hazardous substance activity in- evident. A condition or fact which could not be ignored or
cludes storage in quantities greater than or equal to one overlooked by a reasonable observer while conducting a
D6008 − 22
records search or while physically or visually observing the pliance with laws. The term is not intended to include de
property in conjunction with an ECP. minimis conditions that generally do not present a material risk
of harm to public health or the environment and that generally
3.3.26 open burning/open detonation, n—open detonation
would not be the subject of an enforcement action if these
and open burn operations are used to destroy excess, obsolete,
conditions were brought to the attention of appropriate gov-
or unserviceable munitions, explosives, propellants, and pyro-
ernmental agencies. This term is introduced in Practice E1527,
technics.
and is used herein only in conjunction with ECP Steps 1 and 2
3.3.26.1 Discussion—In open burning, materials such as
(see 6.2), as an intermediate outcome prior to the Step 3
rocket fuel are destroyed by self-sustained combustion after
classification of environmental condition of property area
being ignited. In general, electric initiation systems are pref-
types.A Phase I Environmental Site Assessment results in
erable because they provide better control. In open detonation,
recognized environmental conditions, but not environmental
explosives and munitions are destroyed by a detonation of
condition of property area types.
added explosive charges. Historically, these operations oc-
curred at land surface or in pits, (see EPA 1997).
3.3.33 recorded chain of title documents, n—this term has
the same meaning as recorded land title records.
3.3.27 physical setting sources, n—sources that provide
information about the geologic, hydrogeologic, hydrologic, or
3.3.34 records search and/or review, v—detailed search and
topographic characteristics of a property.
review of available information and records in the possession
of the DoD components, the federal landholding agency and
3.3.28 practically reviewable, adj—informationthatis prac-
records made available by the regulatory agencies or other
tically reviewable is information provided by the source in a
involved federal agencies, including, but not limited to IRP
manner and in a form that, upon examination, yields informa-
studies and analyses, surveys for radioactive materials,
tion relevant to the property without the need for extraordinary
asbestos, asbestos-containing materials, radon, lead-based
analysis of irrelevant data.
paint, electrical devices (that is, transformers) containing PCB,
3.3.28.1 Discussion—The form of the information shall be
RCRA Facility Assessments and Investigations to determine
such that the user can review the records for a limited
what, if any, hazardous substances or petroleum products may
geographic area. Records that cannot be feasibly retrieved by
be present on the property.
reference to the location of the property or a geographic area in
which the property is located are not generally practically 3.3.34.1 Discussion—For the purposes of adjoining
reviewable. Most data bases of public records are practically properties, a records search includes the review of reasonably
reviewable if they can be obtained from the source agency by obtainable
...


This document is not an ASTM standard and is intended only to provide the user of an ASTM standard an indication of what changes have been made to the previous version. Because
it may not be technically possible to adequately depict all changes accurately, ASTM recommends that users consult prior editions as appropriate. In all cases only the current version
of the standard as published by ASTM is to be considered the official document.
Designation: D6008 − 96 (Reapproved 2014) D6008 − 22
Standard Practice for
Conducting Environmental Baseline SurveysDetermining
the Environmental Condition of Federal Property
This standard is issued under the fixed designation D6008; the number immediately following the designation indicates the year of
original adoption or, in the case of revision, the year of last revision. A number in parentheses indicates the year of last reapproval. A
superscript epsilon (´) indicates an editorial change since the last revision or reapproval.
1. Scope
1.1 Purpose—The purpose of this practice is to define good commercial and customary practice in the United States for conducting
anassessing the environmental baseline survey (EBS) incondition of property (ECP) order to determineof federal real
certainproperty. elements of the environmentalThis practice applies to conditionproperty of federal real property, including under
consideration for lease, excess and surplus property at closing and realigning military installations. This effort is installations,
claims reverting to federal ownership such as abandoned mines, and other federally-owned property. The steps in this practice are
conducted to fulfill certain requirements of the Comprehensive Environmental Response, Compensation and Liability Act of 1980
(CERCLA) section 120(h), as amended by the Community Environmental Response Facilitation Act of 1992 (CERFA). (CERFA)
and the federal real property disposal regulations codified in 41 CFR Subpart C (41 CFR 102-75). As such, this practice is intended
to help a user to gather and analyze data and information in order to classify property into seven the applicable environmental
condition of property area types (in accordance with the ASTM D5746, Standard Classification of Environmental Condition of
Property Area Types). Types, (see Appendix X1). Once documented, the EBS ECP report is used to support Findings of Suitability
to Transfer (FOSTs), Findings of Suitability to Lease (FOSLs), or uncontaminated property determinations, or a combination
thereof, pursuant to the requirements of CERFA. CERFA and CERCLA § 120(h). Users of this practice should note that it does
not address (except where explicitly noted) requirements for appropriate and timely regulatory consultation or concurrence, or
both, during the conduct of the EBSECP or during the identification and use of the standard environmental condition of property
area types.
1.1.1 Environmental Baseline Survey—Condition of Property—In accordance with the Department of Defense (DoD) policy,
federal landholding agency policies and General Services Administration’s (GSA) federal real property management regulations,
an EBSECP will be prepared or evaluated for its usefulness (and updated if necessary) for any federally-owned property to be
transferred by deed or leased. The EBSECP will be based on existing environmental information related to storage,release,
treatment, or disposal of hazardous substances, munitions, or petroleum products on the property to determine or discover the
obviousness of the presence or likely presence of a release or threatened release of any hazardous substance or petroleum product.
In certain cases, additional data, including sampling, if appropriate under the circumstances, may be needed in the EBSECP to
support the FOST or FOSL. A previously conducted EBSECP may be updated as necessary and used for making a FOST or FOSL.
An EBSECP also may help to satisfy other environmental requirements (for example, to satisfy the requirements of CERFA or to
facilitate the preparation of environmental condition reports). In addition, the EBSECP provides a useful reference document and
assists in compliance with hazard abatement policies related to asbestos and lead-based paint. The EBSECP process consists of
discrete steps. This practice principally addresses EBS-relatedECP-related information gathering and analysis.
1.1.1.1 Discussion—Prior versions of this practice referred to environmental baseline surveys (EBS). The 2018 Department of
Defense 4165.66M Base Redevelopment and Realignment Manual changed the focus to ECP. Appendix 3 of DODM 4165.66M
This practice is under the jurisdiction of ASTM Committee E50 on Environmental Assessment, Risk Management and Corrective Action and is the direct responsibility
of Subcommittee E50.02 on Real Estate Assessment and Management.
Current edition approved Feb. 1, 2014Sept. 1, 2022. Published March 2014December 2022. Originally approved in 1937 as PS 37. Last previous edition approved in
20052014 as D6008-96(2005).D6008-96(2014). DOI: 10.1520/D6008-96R14.10.1520/D6008-22.
Copyright © ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959. United States
D6008 − 22
provides direction on the preparation of FOST and FOSL documentation. Section C2.4.2.3 of DODM 4165.66M provides direction
for Department of Defense property proposed for disposal and redevelopment.
1.1.2 CERCLA Section 120(h) Requirements—This practice is intended to assist with the identification of federal real property and
DoD installation areas subject to the notification and covenant requirements of CERCLA § 120(h) relating to the deed transfer of
contaminated Federalfederal real property (42 USC 9601 et seq.seq.), (see Appendix X2). Examples of other federal landholding
agencies that must comply with CERCLA §120(h) requirements include the Bureau of Land Management, the Federal Aviation
Administration, and U.S. Forest Service.
1.1.3 CERFA Requirements—This practice can be used to provide information that can be used provides information to partially
fulfill the identification requirements of CERFA [Pub. L. 102-426, 106 Stat. 2174], which amended CERCLA. Property classified
as area Type 1, in accordance with Classification D5746 is eligible for reporting as “uncontaminated” under the provisions of
CERFA. CERFA and the Federal Management Regulations, Real Property Disposal rules codified in 41 CFR 102-75. Additionally,
certain property classified as area Type 2, where evidence indicates that storage occurred for less than one year, may also be
identified as uncontaminated. At installations and federal property listed on the National Priorities List, Environmental Protection
Agency (EPA) concurrence must be obtained for the property to be considered “uncontaminated” and therefore transferable under
CERCLA § 120(h)(4). The EPA has stated that there may be instances in which it would be appropriate to concur with the DoD
Component federal landholding agency that certain property can be identified as uncontaminated under CERCLA § 120(h)(4)
although some limited quantity of hazardous substances or petroleum products have been stored, released, or disposed of on the
property.property (see EPA Office of Enforcement and Compliance Assurance, May 2019). If the information available indicates
that the storage,release, or disposal was associated with activities that would not be expected to pose a threat to human health or
the environment (for example, housing areas, petroleum-stained pavement areas, and areas having undergone routine application
of pesticides), such property should be eligible for expeditious reuse.
NOTE 1—Confirmed releases of emerging chemicals of environmental concern may require additional consideration (see Office of the Undersecretary of
Defense. Policy Memorandum for Clarifications and Upcoming Changes to Department of Defense Instruction 4715.18 in Response to Department of
Defense Office of Inspector General Findings, April 2022).
1.1.4 Petroleum Products—Petroleum products and their derivatives are included within the scope of this practice. Areas on which
petroleum products or their derivatives were stored for one year or more, known to have been released or disposed of [CERCLA§
120(h)(4)] are not eligible to be reported as “uncontaminated property”property” under CERFA.
1.1.5 Other Federal, State, and Local Environmental Laws—This practice does not address requirements of any federal, state, or
local laws other than the applicable provisions of CERCLA identified in 1.1.2 and 1.1.3. These applicable or relevant and
appropriate requirements (ARARs) may have a bearing upon the ultimate disposition of the federal property.Users are cautioned
that federal, state, and local laws may impose additional EBSECP or other environmental assessment obligations that are beyond
the scope of this practice. Users should also be aware that there are likely to be other legal obligations with regard to hazardous
substances or petroleum products discovered on property that are not addressed in this practice and that may pose risks of civil
or criminal sanctions, or both, for noncompliance.
1.1.6 Other Federal, State, and Local Real Property and Natural and Cultural Resources Laws—This practice does not address
requirements of any federal, state or local real property or natural and cultural resources laws. Users are cautioned that numerous
federal, state, and local laws may impose additional environmental and other legal requirements that must be satisfied prior to deed
transfer of property that are beyond the scope of this practice.
NOTE 2—The General Services Administration’s Excess Real Property Due Diligence Checklist for Federal Landholding Agency Customers, November
2017, provides additional detail on federal ARARs.
1.1.7 Non-Federal Property—This standard may also be used by state and local agencies to assess the environmental condition
of non-federal property.
1.2 Objectives—Objectives guiding the development of this practice are (1(1)) to synthesize and put in writing a standard practice
for conducting a high quality EBS, (2ECP,)(2) to facilitate the development of high quality, standardized environmental condition
of property maps to be included in an EBSECP that can be used to support FOSTs, FOSLs, and other applicable environmental
condition reports, (3(3)) to facilitate the use of the standard classification of environmental condition of property area types,types
and ((see Classification D5746), 4(4)) to facilitate the development of a standard guide for preparing and updating EBS
reports.ECP reports, and (5) comply with the Federal Real Property Disposal regulations codified in 41 CFR 102-75.
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1.3 Limitations—Users of this practice should note that, while many of the elements of an EBSECP are performed in a manner
consistent with other “due“ diligence”due diligence” functions, an EBSECP is not prepared to satisfy a purchaser of real
property’sproperty’s duty to conduct an “appropriate inquiry” in order “all appropriate inquiries”, as defined in 40 CFR 312, to
establish an “innocent“innocent landowner defense”defense” to CERCLA § 107 liability. Any such use of any EBSECP by any
party is outside the control of the United States Department of Defense and its components and federal agencies and beyond the
scope of any EBS.ECP. No warranties or representations are made by the United States Department of Defense, its components,
its officers, any federal agency, its employees, or contractors that any EBS ReportECP report satisfies any such requirement for
any party.
1.4 Organization of This Practice—This practice has 15 sections. Section 1 is the scope. Section 2 identifies referenced documents.
Section 3, Terminology, includes definitions of terms not unique to this practice, descriptions of terms unique to this practice, and
acronyms and abbreviations. Section 4 is the significance and use of this practice. Section 5 describes user’s responsibilities.
Sections 6 – 13 are the main body of the data gathering analysis steps of the EBSECP process. Section 14 briefly describes the
EBSECP Step 3 classification of environmental condition of property area types. Section 15 contains a list of keywords. The seven
appendices are non-binding and non-mandatory; they provide background, guidance, and examples.
1.5 This standard does not purport to address all of the safety concerns, if any, associated with its use. It is the responsibility
of the user of this standard to establish appropriate safety safety, health, and healthenvironmental practices and determine the
applicability of regulatory limitations prior to use.
1.6 This international standard was developed in accordance with internationally recognized principles on standardization
established in the Decision on Principles for the Development of International Standards, Guides and Recommendations issued
by the World Trade Organization Technical Barriers to Trade (TBT) Committee.
2. Referenced Documents
2.1 ASTM Standards:
D5746 Classification of Environmental Condition of Property Area Types for Defense Base Closure and Realignment Facilities
E1527 Practice for Environmental Site Assessments: Phase I Environmental Site Assessment Process
E1528E2107 Practice for Limited Environmental Due Diligence: Transaction Screen ProcessEnvironmental Regulatory
Compliance Audits
D5746E2247 Classification of Environmental Condition of Property Area Types for Defense Base Closure and Realignment
FacilitiesPractice for Environmental Site Assessments: Phase I Environmental Site Assessment Process for Forestland or Rural
Property
E2365 Guide for Environmental Compliance Performance Assessment
2.2 Department of Defense Policies:Federal Landholding Agency Documents:
DoD PolicyDepartment of the Navy on the Environmental Review Process to Reach a Finding of Suitability to Lease (FOSL),
September 1993Base Realignment and Closure Implementation Guidance, March 2007
DoD Policy U.S. Army Regulation 200-1, on the Environmental Review Process to Reach a Finding of Suitability to Transfer
(FOST) for Property Where No Release or Disposal Has Occurred, June 1994Environmental Protection and Enhancement,
December 2007
DoD Policy Department of Defense Manual 4715.20, on the Environmental Review Process to Reach a Finding of Suitability
to Transfer (FOST) for Property Where Release or Disposal Has Occurred, June 1994Defense Environmental Restoration
Program (DERP) Management, August 2018
Department of Defense 4165.66M, Base Redevelopment and Realignment Manual, August 2018
Department of Defense Instruction 4715.18, Emerging Chemicals (ECs) of Environmental Concern, September 4, 2019
Department of the Air Force Instruction 32-7020, Environmental Restoration Program, December 2020
DoD Policy Office of the Undersecretary of Defense, on the Implementation of the Community Environmental Response
Facilitation Act (CERFA), September 1993Policy Memorandum for Clarifications and Upcoming Changes to Department of
Defense Instruction 4715.18 in Response to Department of Defense Office of Inspector General Findings, April 2022
2.3 Department of Defense Guidance Document:
BRAC Cleanup Plan Guidebook, Fall 1993
For referenced ASTM standards, visit the ASTM website, www.astm.org, or contact ASTM Customer Service at service@astm.org. For Annual Book of ASTM Standards
volume information, refer to the standard’s Document Summary page on the ASTM website.
Available from Department of Defense, Office of Environmental Security, 3400 Defense Pentagon, Washington, DC 20301-3400.
D6008 − 22
2.3 Federal Standards:Regulations:
Title 32, Code of Federal Regulations (CFR), Part 179, Munitions Response Site Prioritization Protocol (MRSPP)
Title 40, Code of Federal Regulations (CFR), Part 300, National Oil and Hazardous Substances Pollution Contingency Plan
Title 40, Code of Federal Regulations (CFR), Part 302, Designation Reportable Quantities and Notification
Title 40, Code of Federal Regulations (CFR) Part 312, Innocent Landowners, Standards for Conducting All Appropriate
Inquiries
Title 40, Code of Federal Regulations (CFR), Part 355, Emergency Planning and Notification
Title 40, Code of Federal Regulations (CFR) Part 373, Reporting Hazardous Substance Activity When Selling or Transferring
Federal Real Property
Title 41, Code of Federal Regulations (CFR) Part 102-75 Federal Management Regulations, Subchapter C, Real Property
Disposal
2.4 US EPA References and Databases:
RCRA 40 CFR Part 264, Subpart X Permit Writers Technical Resource Document. EPA, Office of Solid Waste, Washington, DC.
June 1997
OLEM Directive 9200.2-187, Best Practice Process for Identifying and Determining State Applicable or Relevant and
Appropriate Requirements Status Pilot, October 2017
EPA Office of Enforcement and Compliance Assurance, Transmittal of Revised Policy Towards Landowners and Transferees of
Federal Facilities to Encourage Cleanup and Reuse at Federal Facilities on the National Priorities List (NPL), May 2019
Envirofacts A single point of access to select U.S. EPA environmental data. This website provides access to several EPA
databases to provide the user with information about environmental activities that may affect air, water, and land anywhere
in the United States (https://enviro.epa.gov/)
FEDFacts Information about the Federal Electronic Docket Facilities regarding contaminated federal facility sites in specific
communities, technical fact sheets and tools and resources to help government agencies and their contractors fulfill cleanup
obligations (https://www.epa.gov/fedfac)
Superfund Enterprise Management System (https://www.epa.gov/enviro/sems-search)
3. Terminology
3.1 This section provides definitions (of terms not unique to this practice), descriptions of terms specific to this practice, and a list
of acronyms and abbreviations used herein. The terms are an integral part of this practice and are critical to its understanding and
use. Many of these terms are also found in Practice E1527.
3.2 Definitions:
3.2.1 aqueous film forming foam (AFFF), n—a fire suppressant used to extinguish flammable liquid fires such as fuel fires.
3.2.1.1 Discussion—
AFFF is often used in facility fire suppression systems, fire fighting vehicles, and at fire training facilities.
3.2.2 asbestos—asbestos, n—six naturally occurring fibrous minerals found in certain types of rock formations. Offormations; of
the six, the minerals chrysotile, amosite, and crocidolite have been most commonly used in building products. When mined and
processed, asbestos is typically separated into very thin fibers. Because asbestos is strong, incombustible, and corrosion-resistant,
asbestos was used in many commercial products beginning early in this century and peaking in the period from World War II into
the 1970s. When inhaled in sufficient quantities, asbestos fibers can cause serious health problems.
3.2.2.1 Discussion—
Because asbestos is strong, incombustible, and corrosion-resistant, asbestos was used in many commercial products beginning
early in the 20th century and peaking in the period from World War II into the 1970s.
3.2.3 asbestos-containing material (ACM)—(ACM), n—any material or product that contains more than 1 % asbestos.
3.2.3 Comprehensive Environmental Response, Compensation, and Liability Information System (CERCLIS)—the list of sites
compiled by EPA that EPA has investigated or is currently investigating for potential hazardous substance contamination for
possible inclusion on the National Priorities List.
Available from the Superintendent of Documents, U.S. Government Printing Office, Washington, DC 20402.
Available from United States Environmental Protection Agency (EPA), William Jefferson Clinton Bldg., 1200 Pennsylvania Ave., NW, Washington, DC 20460,
http://www.epa.gov.
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3.2.4 contaminated public wells—wells, n—public wells used for drinking water that have been designated by a government entity
as contaminated by toxic substances (for example, chlorinated solvents),solvents), or as having water unsafe to drink without
treatment.
3.2.5 drum—drum, n—as defined by the U.S. Department of Transportation, a container (typically, but not necessarily, holding 55
gal [208 L] of liquid) that may have been used to store hazardous substances or petroleum products.flat-ended or convex-ended
cylindrical packaging made of metal, fiberboard, plastic, plywood, or other suitable materials; this definition does not include
cylinders, jerricans, wooden barrels or bulk containers.
3.2.5.1 Discussion—
A metal or plastic container (typically, but not necessarily, holding 55 gal [208 L] of liquid) that may have been used to store
hazardous substances or petroleum products.
3.2.6 dwelling—dwelling, n—structure or portion thereof used for residential habitation.
3.2.7 environmental lien—lien, n—a charge, security, or encumbrance upon title to a property to secure the payment of a cost,
damage, debt, obligation, or duty arising out of response actions, cleanup, or other remediation of hazardous substances or
petroleum products upon a property, including (but not limited to) liens imposed pursuant to CERCLA 42 USC § 9607(1) and
similar state or local laws.
3.2.8 emerging chemicals of environmental concern, n—as defined in DoDI 4715.18, chemicals relevant to the DoD that are
characterized by a perceived or real threat to human health or the environment and that have new or changing toxicity values or
new or changing human health or environmental regulatory standards.
3.2.8.1 Discussion—
These chemicals are defined as emerging contaminants in Practice E1527. Per- and polyfluoroalkyl substances (PFAS) are
examples of emerging chemicals of environmental concern at federally-owned property. Although PFAS are not currently regulated
as hazardous substances under CERCLA, some states have begun regulating the disposal or remediation of PFAS-impacted soil,
sediment, surface water, and groundwater. For federal property where firefighting activities, including training, were conducted
with aqueous film-forming foam (AFFF) and properties where electroplating operations were conducted, the user may refer to
Appendix X4 for guidance addressing emerging chemicals of environmental concern. See also the Policy Memorandum for
Clarifications and Upcoming Changes to Department of Defense Instruction 4715.18 in Response to Department of Defense Office
of Inspector General Findings, April 2022.
3.2.9 ERNS list—list, n—EPA’sthe Emergency Response Notification System list of reported CERCLA hazardous substance
releases or spills in quantities equal to or greater than the reportable quantity, as maintained by the National Response Center.
Notification requirements for such releases or spills are codified in 40 CFR Parts 302 (ERNS) is a database used to store
information on notifications of oil discharges and 355hazardous. substances releases.
3.2.9.1 Discussion—
EPA’s Emergency Response Notification System is a list of reported CERCLA hazardous substance releases or spills in quantities
equal to or greater than the reportable quantity, as maintained by the National Response Center. Notification requirements for such
releases or spills are codified in 40 CFR Parts 302 and 355.
3.2.9 Federal Register (FR)—publication of the United States government published daily (except for Federal holidays and
weekends) containing all proposed and final regulations and some other activities of the Federal government. When regulations
become final, they are included in the Code of Federal Regulations (CFR) as well as published in the Federal Register.
3.2.10 hazardous substance—substance, n—a substance means that group of substances defined as a hazardous substance pursuant
to CERCLA 42 USC § 9601(14), as interpreted by EPA regulations and the courts: “(hazardous A) any substance designated
pursuant to section 1321(b)(2)(A) of Title 33, (B) any element, compound, mixture, solution, or substance designated pursuant to
Section 9602 of this title, (C) any hazardous waste having the characteristics identified under or listed pursuant to Section 3001
of the Solid Waste Disposal Act (42 USC § 6921) (but not including any waste the regulation of which under the Solid Waste
Disposal Act (42 USC§ 6921 under CERCLA §101(14), et seq.) has been suspended by Act of Congress), (D) any toxic pollutant
listed under Section 1317(a) of Title 33, (E) any hazardous air pollutant listed under Section 112 of the Clean Air Act (42 USC
§ 7412), and (and F) any imminently hazardous chemical substance or mixture with respect to which the Administrator (of EPA)
has taken action pursuant to Section 2606 of Title 15. The term does not include petroleum, including crude oil or any fraction
thereof which is not otherwise specifically listed or designated as a hazardous substance under subparagraphs (A) through (F) of
D6008 − 22
this paragraph, and the term does not include natural gas, natural gas liquids, liquefied natural gas, or synthetic gas usable for fuel
(or mixtures of natural gas and such synthetic gas).” Users of this practice should note that certain states may expand this definition
to include other substances not meeting the above definition. The user or environmental professional should consider whether the
state in which the installation is located has identified such identified substances.that appear at 40 CFR §302.4.
3.2.11 hazardous waste—waste, n—any hazardous waste having the characteristics identified under or listed pursuant to section
3001 of the Solid Waste Disposal Act (42 USC § 6901 et seq.) (but not including any waste the regulation of which under the Solid
Waste Disposal Act has been suspended by Act of Congress) and so forth.Congress).
3.2.11.1 Discussion—
Some state waste management programs regulate additional solid wastes as hazardous waste.
3.2.12 landfill—landfill, n—a place, location, tract of land, area, or premises used for the disposal of solid wastes as defined by
state solid waste regulations. The term is synonymous with the term solid waste disposal site and is also known as a garbage dump,
trash dump, or similar term.
3.2.12.1 Discussion—
The user is cautioned that not all garbage dumps and trash dumps have permits issued by either the state or local regulatory agency.
3.2.13 local street directories—directories, n—directories published by private (or sometimes government) sources that show
ownership, occupancy, or use of sites, or combination thereof, by reference to street addresses. Often local street directories are
available at libraries of local governments, colleges or universities, or historical societies.list the occupant(s) of a specific address
at the time the occupant data was collected, typically within in a year of the publication date of the directory.
3.2.13.1 Discussion—
Local street directories may not be available for federally-owned property.
3.2.14 material safety data sheet (MSDS)—munitions and explosives of concern, n—written or printed material concerning a
hazardous substance which is prepared by chemical manufacturers, importers, and employers for hazardous chemicals pursuant to
OSHA’s Hazard Communication Standard, 29 CFR 1910.1200.distinguishes specific categories of military munitions that may
pose unique explosives safety risks, such as unexploded ordnance, as defined in 10 U.S.C. §101(e)(5); discarded military
munitions, as defined in 10 U.S.C. §2710(e)(2); or munitions constituents (for example, TNT, RDX), as defined in 10 U.S.C.
§2710(e)(3), present in high enough concentrations to pose an explosive hazard.
3.2.15 National Contingency Plan (NCP)—(NCP), n—the National Oil and Hazardous substancesSubstances Pollution Contin-
gency Plan found at 40 CFR § 300, which is the EPA’s regulations for how releases of hazardous substances are to be cleaned
up pursuant to CERCLA.
3.2.16 National Priorities List—List, n—list compiled by EPA pursuant to CERCLA 42 USC § 9605(a)(8)(B) of properties with
the highest priority for cleanup pursuant to EPA’s Hazard Ranking System. See 40 CFR Part 300.
3.2.17 occupants—occupants, n—those tenants, subtenants, or other persons or entities using the property or a portion of the
property.
3.2.18 owner—generally the fee owner of record of the property.
3.2.19 petroleum exclusion—the exclusion from CERCLA liability provided in 42 USC § 9601(14), as interpreted by the courts
and EPA: “The term (hazardous substance) does not include petroleum, including crude oil or any fraction thereof which is not
otherwise specifically listed or designated as a hazardous substance under subparagraphs (A) through (F) of this paragraph, and
the term does not include natural gas, natural gas liquids, liquefied natural gas, or synthetic gas usable for fuel (or mixtures of
natural gas and such synthetic gas).”
3.2.18 petroleum products—per- and polyfluoroalkyl substances (PFAS), n—those substances included within the meaning of the
petroleum exclusion to CERCLA, 42 USC § 9601(14) as interpreted by the courts and EPA, that is: “petroleum, including crude
oil or any fraction thereof which is not otherwise specifically listed or designated as a hazardous substance under subparagraphs
(a group A) through (F) of this paragraph, and the term does not include natural gas, natural gas liquids, liquefied natural gas, or
synthetic gas usable for fuel (or mixtures of natural gas and such synthetic gas).”of manufactured chemicals consisting of
polymeric chains of carbon bonded to fluorine atoms, usually with a polar functional group at the head.
3.2.18.1 Discussion—
D6008 − 22
PFAS are fluorinated substances with a carbon chain structure. In perfluoroalkyl substances (PFAAs), each carbon atom in the chain
is fully saturated with fluorine (carbon-fluorine bonds only), whereas the carbon chain in polyfluoroalkyl substances is mostly
saturated with fluorine (carbon-fluorine bonds), but also contains carbon-hydrogen bonds.
3.2.19 Phase I Environmental Site Assessment—Assessment, n—the process described in Practice E1527 and Practice E2247.
3.2.20 pits, ponds, or lagoons—lagoons, n—man-made or natural depressions in a ground surface that are likely to hold liquids
or sludge containing hazardous substances or petroleum products. The likelihood of such liquids or sludge being present is
determined by evidence of factors associated with the pit, pond, or lagoon, including, but not limited to, discolored water,
distressed vegetation, or the presence of an obvious wastewater discharge.
3.2.20.1 Discussion—
The likelihood of such liquids or sludge being present is determined by evidence of factors associated with the pit, pond, or lagoon,
including, but not limited to, discolored water, distressed vegetation, or the presence of an obvious wastewater discharge.
3.2.21 property—property, n—the real property, that is the subject of the EBS described in this practice as well as the real property
adjacent to the subject property (which may be privately owned). Real property includes buildings and other fixtures and including
buildings, fixtures, and other improvements located on the property and affixed to the land.
3.2.22 property tax files—files, n—the files kept for property tax purposes by the local jurisdiction where the property is located
and includes records of past ownership, appraisals, maps, sketches, photos, or other information that is reasonably ascertainable
and pertaining to the property.
3.2.23 RCRA generators—generators, n—those persons or entities that generate hazardous wastes, as defined and regulated by
RCRA.RCRA and have submitted EPA form 8700-12 to the EPA.
3.2.24 RCRA generators list—list, n—list kept by EPA of those persons or entities that have notified EPA that they generate
hazardous wastes, as defined and regulated by RCRA.
3.2.25 RCRA TSD facilities—facilities, n—those facilities on which treatment, storage, or disposal, or a combination thereof, of
hazardous wastes takes place, as defined and regulated by RCRA.subject to regulation and permitting under RCRA or a delegated
state’s hazardous waste management program; these facilities have submitted EPA Form 8700-23 to the EPA.
3.2.26 RCRA TSD facilities list—list, n—list kept by EPA of those facilities on which treatment, storage, or disposal, or a
combination thereof, of hazardous wastes takes place, as defined and regulated by RCRA. that have submitted EPA Form 8700-23
to the agency.
3.2.27 recorded land title records—records, n—records of fee ownership, leases, land contracts, easements, liens, and other
encumbrances on or of the property recorded in the place where land title records are, by law or custom, recorded for the local
jurisdiction in which the property is located. (Commonly, such records are kept by a municipal or county recorder or clerk.) Such
records may be obtained from title companies or directly from the local government agency. Information about the title to the
property that is recorded in a U.S. district court or any place other than where land title records are, by law or custom, recorded
for the local jurisdiction in which the property is located, are not considered part of recorded land title records. See located (see
3.3.333.2.32 and 7.2.4., and 40 CFR §312.24(a)).
3.2.28 records of emergency release notifications (SARA§ 304)304),—n—Section 304 of EPCRA or Title III of SARA requires
operators of facilities to notify their local emergency planning committee (as defined in EPCRA) and Statestate emergency
response commission (as defined in EPCRA) of any release beyond the facility’s boundary of any reportable quantity of any
extremely hazardous substance.Often the local fire department is the local emergency planning committee. Records of such
notifications are “records of emergency release notifications” (SARA § 304).
3.2.28.1 Discussion—
Records of such notifications are “records of emergency release notifications” (SARA § 304) and may be found in the ERNS
database.
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3.2.29 safety data sheet (SDS), n—written or printed material concerning a hazardous substance which is prepared by chemical
manufacturers, importers, and employers for hazardous chemicals pursuant to OSHA’s Hazard Communication Standard, 29 CFR
1910.1200.
3.2.30 solid waste disposal site—site, n—a place, location, tract of land, area, or premises used for the disposal of solid wastes
as defined by state solid waste regulations. The term is synonymous with the term landfill and is also known as a garbage dump,
trash dump, or similar term.
3.2.30.1 Discussion—
The term is synonymous with the term landfill and is also known as a garbage dump, trash dump, or similar term. Historic solid
waste disposal sites at federally-owned properties may not have operated under a permit.
3.2.31 solvent—solvent, n—a chemical compound that is capable of dissolving another substance and a hazardous substance, used
in a number of manufacturing/industrial processes including but not limited to dry cleaning, the manufacture of paints and coatings
for industrial and household purposes, equipment clean-up, and surface degreasing in metal fabricating industries.industrial
settings.
3.2.31.1 Discussion—
Solvents are routinely use for parts washing and the preparation of metal surfaces for plating.
3.2.32 State registered USTs—USTs, n—State lists of underground storage tanks required to be registered under Subtitle I, Section
9002 of RCRA.
3.2.33 sump—sump, n—a pit, cistern, cesspool, or similar receptacle where liquids drain, collect, or are stored.
3.2.34 Superfund Enterprise Management System (SEMS), n—the official repository for site and non site-specific Superfund data
in support of the Comprehensive Environmental Response, Compensation, and Liability Act (CERCLA). It contains information
on hazardous waste site assessment and remediation.
3.2.34.1 Discussion—
SEMS contains information on hazardous waste site assessment and remediation including PAs, remedial investigations and
feasibility studies, chemicals of concern, and 5-year review reports.
3.2.35 underground storage tank (UST)—(UST), n—any tank, including underground piping connected to the tank that is or has
been one or combination of tanks (including underground pipes connected thereto) that is used to contain hazardous substances
or petroleum productsan accumulation of regulated substances, and the volume of which is 10 % (including the volume of
underground pipes connected thereto) is 10 percent or more beneath the surface of the ground.
3.2.35.1 Discussion—
for the purposes of this practice, regulated substances include hazardous substances, and petroleum and materials subject to
regulation under 40 CFR Part 280.
3.2.36 USGS 7.5 Minute Topographic Map—Map, n—the map (if any) available from or produced by the United States Geological
Survey, entitled “USGS 7.5 Minute Topographic Map” and showing the property. phrase “USGS topographic map” refers to maps
that cover a quadrangle that measures 7.5 minutes of longitude and latitude on all sides, so these are also referred to as 7.5-minute
maps, quadrangle maps, or “quad” maps with a wide range of scales, but the scale used for all modern USGS topographic maps
is 1:24,000.
3.2.37 wastewater—wastewater, n—water that (1) is or has been used in an industrial or manufacturing process, (means any water
which, during manufacturing or processing, comes into direct contact with or results from the2) conveys or has conveyed sewage,
or ( production or use of any raw material,3) is directly related to manufacturing, processing, or raw materials storage intermediate
product, finished product, byproduct, or waste product or (2 areas at an industrial plant. Wastewater does not include water
originating on or passing through or adjacent to a site, such as stormwater flows, that has not been used in industrial or
manufacturing processes, has not been combined with sewage, or is not directly related to manufacturing, processing, or raw
materials storage areas at an industrial plant.) conveys or has conveyed sewage.
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3.2.37.1 Discussion—
Wastewater does not include water originating on or passing through or adjacent to a site, such as stormwater flows, that has not
been used in industrial or manufacturing processes, has not been combined with sewage, or is not directly related to manufacturing,
processing, or raw materials storage areas at an industrial plant. Wastewater includes washdown water that flows to a floor drain,
sump, or drywell.
3.3 Definitions of Terms Specific to This Standard:
3.3.1 adjacent properties—adjoining properties, n—those any real property or properties contiguous or partially contiguous to the
boundariesthe border of which is (are) shared in part or in whole with that of the federally-owned ofproperty, the property being
surveyed during an EBS or other activity intended to classify the propertyor that would be shared in part or in whole with that of
the federally-owned intoproperty a standard environmental condition of property area type, or other properties relatively nearbut
for a street, road, or other public thoroughfare separating the installation properties.that could pose significant environmental
concern and/or have a significant impact on the results of an EBS or on the classification of installation property into standard
environmental condition of property area types.
3.3.2 aerial photographs—photographs, n—photographs, taken from an aerial platform, having sufficient resolution to allow
identification of development and activities of areas encompassing the property.Aerial photographs are commonly available from
government agencies or private collections unique to a local area.
3.3.2.1 Discussion—
Aerial photographs are commonly available from government agencies or private collections unique to a local area.
3.3.3 all required remedial action, taken—n—for the purposes of this practice,all remedial action, as described in CERCLA§
120(h)(3)(B)(i), has been taken if “the construction and installation of an approved remedial design has been completed, and the
remedy has been demonstrated to the administrator [of EPA] to be operating properly and successfully. Thesuccessfully; the
carrying out of long-term pumping and treating, or operation and maintenance, after the remedy has been demonstrated to the
administrator to be operating properly and successfully does not preclude the transfer of the property.”property.” [42 USC §
9620(h)(3)]. Alternatively, in circumstances where a remedy has been constructed, but no ongoing treatment or operation and
maintenance is required, for example, “clean closure” or excavation of soil with off-site treatment, all remedial action means that
all action required to meet applicable state or federal regulatory standards, including, as required, state or federal regulatory
approval, has been taken.
3.3.3.1 Discussion—
Alternatively, in circumstances where a remedy has been constructed, but no ongoing treatment or operation and maintenance is
required, for example, “clean closure” or excavation of soil with off-site treatment, all remedial action means that all action
required to meet applicable state or federal regulatory standards, including, as required, state or federal regulatory approval, has
been taken (see section 12.2). Land use restrictions may be components of required remedial action.
3.3.4 applicable requirements—or relevant and appropriate requirements (ARARs), n—those cleanup standards, standards of
control, and other substantive requirements, criteria, or limitations promulgated under federal environmental or State environ-
mental or facility siting laws that specifically address that, while not “applicable” to a hazardous substance, pollutant, contaminant,
remedial action, location, or other circumstances found circumstance at a CERCLA site. Only those state standards that are
identified by a state in a timely manner and that are more stringent than federal requirements may be applicable. site, address
problems or situations sufficiently similar to those encountered at the CERCLA site that their use is well suited to the particular
site (see EPA OLEM 9200.1-187).
3.3.4.1 Discussion—
Only those state standards that are identified in a timely manner and are more stringent than federal requirements may be relevant
and appropriate.
3.3.5 approximate minimum search distance—distance, n—the area for which agency records must be obtained and reviewed
pursuant to Section 7 subject to the limitations provided in that section. This may include areas outside the property and shall be
measured from the nearest property boundary. This term is used instead of radius to include irregularly shaped properties.
3.3.5.1 Discussion—
This may include areas outside the federally-owned property and shall be measured from the nearest property boundary. This term
is used instead of radius to include irregularly shaped properties.
3.3.6 area in question, n—that portion of federal real property that is the subject of the ECP.
3.3.6.1 Discussion—
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The area in question may be a subset of a larger piece of federal property or may be property that has been transferred to federal
control through Congressional action. The FOSL or FOST may be limited to an area in question as opposed to a larger
federally-owned property.
3.3.7 BRAC statutes—statutes, n—Title II of the Defense Authorization Amendments and Base Closure and Realignment Act of
1988 (Pub. L. 100-526, 10 USC 2687, note.) and the Defense Base Closure and Realignment Act of 1990 (Part A of Title XXIX
of Pub. L. 101-510, 10 USC 2687, note.), collectively.
3.3.7.1 Discussion—
The 2005 Round (P.L. 107-107); amended the Defense Base Closure and Realignment Act of 1990 (P.L. 101- 510). No new BRAC
activities have been authorized by Congress since 2016.
3.3.7 closing military installation—installations identified for closure pursuant to BRAC statutes, or installations previously closed
under the authority of 10 USC 2687.
3.3.8 DoD Component—component, n—collectively, the Office of the Secretary of Defense, the Military Departments, the
Chairman of the Joint Chiefs of Staff, the Inspector General of the Department of Defense, the Defense Agencies and the DoD Field
Activities.
3.3.9 disposal—disposal, v—the discharge, deposit, injection, dumping, spilling, leaking, or placing of any hazardous substances,
or petroleum products or their derivatives into or on any land or water so that such hazardous substances, or petroleum products
or their derivatives or any constituent thereof may enter the
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