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ASTM D6008-22

(Practice)

Standard Practice for Determining the Environmental Condition of Federal Property

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
ICS
13.020.40 - Pollution, pollution control and conservation
Technical Committee
E50 - Environmental Assessment, Risk Management and Corrective Action
Drafting Committee
E50.02 - Real Estate Assessment and Management
Current Stage
Ref Project

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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
1
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-
1
This practice is under the jurisdiction of ASTM Committee E50 on Environ-
mation to partially fulfill the iden
...

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
1
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
1
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
...

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4.2 This guide is intended to identify the factors that should be considered in the selection and implementation of an appropriate remedial action to address COCs present in environmental media at the site at concentrations above the remedial action levels. The specific process used to select the remedial action will vary widely from site to site. However, in all cases, the selected remedial action should be both a protective remedial action (that is, achieves the risk-based remedial action objectives) and an acceptable remedial action (that is, satisfies the non-risk remedial action objectives).
SCOPE
1.1 This guide covers the selection of appropriate remedial actions at sites where a release of chemicals (for example, vapor-phase, dissolved-phase, or non-aqueous phase liquids (NAPL)) into the environment has occurred. This overall remedy selection process is illustrated in Fig. 1. The guide is intended to be applied within a risk-based corrective action (RBCA) framework.
FIG. 1 Remedy Selection Process  
1.2 The purpose of this guide is to facilitate the selection of acceptable remedial actions and to minimize bad decisions leading to the selection of remedial actions that do not satisfy both the risk-based remedial action objectives and the non-risk remedial action objectives.  
1.3 This guide is intended to be applied at sites that require a remedial action to address unacceptable human heath or ecological risks, other regulatory requirements, and/or other unacceptable site conditions. Prior to use of this guide, a site assessment should be completed resulting in: (1) the establishment of remedial action objectives, (2) a determination that a remedial action is required to achieve the remedial action objectives, (3) an identification of site areas requiring a remedial action, and (4) a conceptual site model that reflects the results of the site assessment. The risk-based remedial action objectives are assumed to have been established using RBCA or another risk-based assessment method that results in the identification of appropriate remedial action objectives based on an evaluation of sources, exposure pathways, and potential receptors. Remedial action objectives may be established using Guide E1739, Guide E2081, and/or Guide E2205. In addition, applicable federal, state, and local regulations, statutes, and policies should be followed and should form the basis for determining risk-based and non-risk remedial action objectives. The remedial action objectives may include resource protection standards and the prevention of aesthetic or nuisance impacts in addition to protection of human health and the environment.  
1.4 Each risk-based remedial action objective for an exposure pathway will typically include numeric remedial action levels for each chemical of concern (COC). Remedial action levels may also be developed for non-risk remedial action objectives such as resource protection standards. The non-risk remedial action levels may include thickness or mobility criteria for NAPL. The selected remedy must be effective and timely for each remedial action objective based on the consideration of the associated exposure pathway or resource protection standard.  
1.5 To facilitate the selection of acceptable remedial actions, this guide establishes a process for remedy selection (Fig. 2) that involves:
FIG. 2 Remedy Selection Flowchart  
FIG. 2 Remedy Selection Flowchart (continued)  
1.5.1 Development of risk-based remedial action objectives that includes identification of complete exposure pathways and numeric remedial action levels (Section 5).  
1.5.2 Development of non-risk remedial action objectives based on resource protection and other non-risk considerations...

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ASTM E2435-05(2020)(Guide)
Standard Guide for Application of Engineering Controls to Facilitate Use or Redevelopment of Chemical-Affected Properties

SIGNIFICANCE AND USE
4.1 Intended Application of Guide—This guide is intended for use at properties that are presently developed or proposed for development for residential, commercial, or industrial purposes but which contain chemical-affected soil, groundwater, air, or other environmental media, which may pose an unacceptable risk to human health. This guide can be used as a tool for planning and implementation of property reuse or redevelopment activities at former commercial/industrial facilities, “brownfield” properties, or properties containing naturally occurring, chemical-affected environmental media so as to effectively manage potential human exposures to COCs which might otherwise limit productive use of the property.  
4.2 Situations Where This Guide May Be Applied—An engineering control may be needed as part of the development plan when: (1) COCs are present in soil, groundwater, or other environmental media at concentrations posing unacceptable risk(s) to human health per applicable regulatory criteria or a risk-based evaluation; (2) a potentially complete exposure pathway for COCs is likely to exist in the absence of an engineering control or other response measure, and (3) installation and maintenance of the engineering control is determined to be an applicable and cost-effective response action relative to other options. A property should not be excluded from development or redevelopment solely on the basis of chemical-affected media, in general, and chemical-affected groundwater, in particular. If no affected environmental media are identified as having COC concentrations in excess of applicable regulatory standards or risk-based criteria, then engineering controls or other response measures are not required.  
4.3 Assumptions for Use of This Guide—For use of this guide, it is assumed that (1) an environmental site assessment has been completed to characterize chemical-affected environmental media, (2) exposures to COCs posing an unacceptable risk to the health of cur...
SCOPE
1.1 This guide presents general considerations for application of engineering controls to facilitate continued use or redevelopment of properties containing chemical-affected soil, groundwater, or other environmental media, due either to chemical releases or naturally-occurring conditions. This guide is not meant to be prescriptive but rather to present considerations for evaluating technologies capable of addressing potential human exposures associated with chemical-affected environmental media.  
1.2 Table 1 lists the considerations that should be taken into account when developing an engineering control in accordance with this guide.  
1.3 This guide is intended for use by real estate developers, civil/structural designers, environmental regulators, industrial parties, environmental consultants, and other persons concerned with residential, commercial, or industrial development of real properties where chemical-affected environmental media are present. The design process should involve the individuals and firms working on various aspects of the specifications for construction, operation, and maintenance. If the site is located on public property, then public participation should be considered during the design process.  
1.4 This guide is directed toward properties where chemical-affected environmental media, associated with either human-influenced activities or naturally-occurring conditions, will remain in place and where active or passive engineering controls will be used to reduce or eliminate exposures that may otherwise pose an unacceptable risk to property users.  
1.5 This guide identifies the exposure concerns associated with chemical-affected properties that may affect the property development plan, both in the construction phase and during the proposed use of the property; defines performance standards for control of applicable exposure pathways; and, for each exposure pathway, provides examples of eng...

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ASTM E1848-20(Guide)
Standard Guide for Selecting and Using Ecological Endpoints for Contaminated Sites

ABSTRACT
This guide deals with an approach to identification, selection, and use of ecological endpoints (both assessment and measurement endpoints) that are susceptible to the direct and indirect effects of both chemical and non-chemical stressors and agents associated with wastes and contaminated media at specific sites under current and future land uses. It does not address assessment and measurement endpoints for non-site specific studies (for example, chemical specific or regional risk assessments) or measurements in abiotic media (soil, water, or air). Conditions of the site and risk assessment that should be considered in identifying and selecting assessment and measurement endpoints include stressor characteristics, ecosystem types, spatial scale, temporal scale, ecological organization, and functionality/values. The following subsections present a partial listing of representative measurement endpoints: measurement endpoints representing ecosystem assessment endpoints, measurement endpoints representing community assessment endpoints, measurement endpoints representing population assessment endpoints, and measurement endpoints representing individual organism assessment endpoints. Other general considerations, desirable characteristics of assessment and measurement endpoints, candidate site-related ecological receptors, candidate assessment endpoints, specific steps in identifying, selecting and using assessment and measurement endpoints, addressing uncertainties in the identification and selection of assessment and measurement endpoints, documenting the selection of assessment and measurement endpoints.
SIGNIFICANCE AND USE
4.1 This guide assumes that a decision has been made that an ecological risk assessment is required for a contaminated site. In some cases, this decision could be made before any site data are collected. See Fig. 1.
FIG. 1 Conceptual Relationships between Assessment Endpoints, Measurement Endpoints and Lines of Evidence (Source: Federal Contaminated Sites Action Plan (FCSAP) Ecological Risk Assessment Guidance, Government of Canada, March 2012)  
4.2 The selection of assessment endpoints (defined as ecological values to be protected) and measurement endpoints (ecological characteristics related to the assessment endpoints) is a critical step in conducting an ecological risk assessment. Endpoint selection identifies those effects which are ecologically significant and not merely those that are adverse, thus providing a more rational and defensible basis for making risk and remedial decisions.  
4.3 This guide provides an approach for identifying, selecting and using assessment and measurement endpoints in an ecological risk assessment for a contaminated site. This guide has been developed because there is no universal, simple measure of ecological health analogous to measures used in human health risk assessment. Assessment and measurement endpoints have to be identified and selected from a variety of individual circumstances on a stressor-, ecosystem- and scale-specific basis. It is important to recognize that a diverse set of ecological endpoints could be required for a specific site. EPA/100/F15/005 Generic Ecological Assessment Endpoints (GEAEs) For Ecological Risk Assessment: Second Edition With Generic Ecosystem Services Endpoints Added. July 2016)  
4.4 This guide is intended to be used primarily by a biologist, ecologist, ecotoxicologist, or a team of environmental scientists during problem formulation and work plan development prior to initiating data collection activities at a contaminated site (3-8, 10).  
4.5 Ecological risk assessment is usually an...
SCOPE
1.1 This guide covers an approach to identification, selection, and use of ecological endpoints (both assessment and measurement endpoints) (1-8)2 that are susceptible to the direct and indirect effects of both chemical and non-chemical stressors or agents associated with wastes and contaminated media at spe...

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ASTM E2790-20(Guide)
Standard Guide for Identifying and Complying With Continuing Obligations

SIGNIFICANCE AND USE
4.1 Uses—This guide is intended for use on a voluntary basis primarily by parties who desire to satisfy  continuing obligations at commercial real estate or at forestland or rural properties. As such, this guide provides information and suggested procedures that could be useful to persons who wish to establish one of the CERCLA LLPs or similar liability protections offered under state law. This guide may apply where response actions have already occurred, where response actions remain ongoing, or where response actions may be necessary in the future. As noted in 1.1.2, the use of this guide need not be necessarily limited to CERCLA LLPs.  
4.2 Clarifications on Use:  
4.2.1 Use is Property-Specific—Continuing obligations, and the process to identify and implement continuing obligations, is necessarily property-specific. Therefore, this guide includes information to consider when performing a property-specific, fact-based evaluation to determine appropriate continuing obligations.  
4.2.2 Partially Addresses Eligibility for CERCLA LLPs—Users wishing to establish CERCLA LLPs should be aware that the continuing obligations covered by this guide comprise only part of CERCLA's statutory eligibility requirements for LLPs. For example, users seeking to qualify for LLPs  must perform AAI before property acquisition. Users  seeking the BFPP or CPO LLP must also demonstrate that they are not liable or potentially liable or affiliated with any person who is liable or potentially liable for releases of  hazardous substances under CERCLA. 42 U.S.C. §9607(q)(1)(A)(ii); 42 U.S.C. §9601(40)(B)(viii). Further, users seeking the BFPP  or ILO  LLP must establish that disposal of hazardous substances occurred on the property prior to its acquisition. 42 U.S.C. §9601(40)(B)(i); 42 U.S.C. §9601(35)(A). Users seeking the CPO LLP must establish that they did not cause, contribute or consent to the release of hazardous substances. 42 U.S.C. §9607(q)(A)(i). Finally, users seeking to qual...
SCOPE
1.1 Purpose—The purpose of this guide is to provide information and guidance2 related to the process of identifying and fulfilling continuing obligations3 at commercial real estate, and forestland and rural property that is contaminated by hazardous substances within the scope of the Comprehensive Environmental Response, Compensation and Liability Act (CERCLA) (42 U.S.C. § 9601 et seq.), petroleum products, or other contaminants that require cleanup under federal or state law (collectively hereafter chemicals of concern). Because of the importance of federal law, this guide largely focuses on continuing obligations applicable to the innocent landowner (ILO), the contiguous property owner (CPO), and the bona fide prospective purchaser (BFPP) protections from CERCLA liability (hereinafter, collectively referred to as the “CERCLA Landowner Liability Protections,” or “CERCLA LLPs”) (see Legal Appendix X1 to Appendix X3 for an outline of CERCLA's liability and defense provisions). However, the continuing obligations arising from CERCLA LLPs are often very similar to the types of continuing obligations that state laws set as conditions for state liability protections. And, therefore, the purpose of this guide seeks to help users who wish to perform continuing obligations because of concerns over CERCLA liability and also extends to help users who wish to perform continuing obligations because of concerns over state law liability. Similarly, where sound risk management rather than a desire for liability protection is the goal, the procedures recommended in this guide can also prove useful  
1.1.1 Intended Scope of Standard Guide—As a standard guide, this document provides a compendium of information and options but does not recommend a specific course of action. As a guide, the purpose of this standard is to simply increase the awareness of possible techniques or procedures related to continuing obligations and to offer guida...

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ASTM F3634-23(Guide)
Standard Guide for Preparing Weathered Samples of Oil Using a Rotary Evaporator

SIGNIFICANCE AND USE
4.1 A standard procedure is necessary to prepare samples of oils or petroleum products at different oil weathering stages with compositional distribution that is representative of weathered spilled oil.  
4.2 This procedure uses standardized equipment and test procedures.  
4.3 This procedure should be performed at the stages of weathering corresponding to the spill conditions of interest.
SCOPE
1.1 This guide summarizes methods to produce representative residual oil following evaporative weathering using a rotary evaporator.  
1.1.1 The results of this guide can provide weathered oil samples for further study and characterization.  
1.2 This guide covers general procedures for artificial weathering of oil by using rotary evaporation devices and does not cover all possible procedures that may be applicable to this topic.  
1.3 The accuracy of this guide depends very much on the representative nature of the oil sample used. Certain oils can have different properties depending on their chemical contents at the time a sample is taken.  
1.4 Units—The values stated in SI units are to be regarded as the standard. No other units of measurement are included in this standard.  
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, health, and environmental 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.

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