ASTM D6008-1996(2005) Standard Practice for Conducting Environmental Baseline Surveys《进行环境基线调查的标准实施规程》.pdf
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1、Designation: D 6008 96 (Reapproved 2005)Standard Practice forConducting Environmental Baseline Surveys1This standard is issued under the fixed designation D 6008; the number immediately following the designation indicates the year oforiginal adoption or, in the case of revision, the year of last rev
2、ision. A number in parentheses indicates the year of last reapproval. Asuperscript epsilon (e) indicates an editorial change since the last revision or reapproval.1. Scope1.1 PurposeThe purpose of this practice is to define goodcommercial and customary practice in the United States forconducting an
3、environmental baseline survey (EBS) in order todetermine certain elements of the environmental condition offederal real property, including excess and surplus property atclosing and realigning military installations. This effort isconducted to fulfill certain requirements of the ComprehensiveEnviron
4、mental Response, Compensation and Liability Act of1980 (CERCLA) section 120(h), as amended by the Commu-nity Environmental Response Facilitation Act of 1992(CERFA). As such, this practice is intended to help a user togather and analyze data and information in order to classifyproperty into seven env
5、ironmental condition of property areatypes (in accordance with the Standard Classification ofEnvironmental Condition of Property Area Types). Once docu-mented, the EBS is used to support Findings of Suitability toTransfer (FOSTs), Findings of Suitability to Lease (FOSLs), oruncontaminated property d
6、eterminations, or a combinationthereof, pursuant to the requirements of CERFA. Users of thispractice should note that it does not address (except whereexplicitly noted) requirements for appropriate and timelyregulatory consultation or concurrence, or both, during theconduct of the EBS or during the
7、identification and use of thestandard environmental condition of property area types.1.1.1 Environmental Baseline SurveyIn accordance withthe Department of Defense (DoD) policy, an EBS will beprepared or evaluated for its usefulness (and updated ifnecessary) for any property to be transferred by dee
8、d or leased.The EBS will be based on existing environmental informationrelated to storage, release, treatment, or disposal of hazardoussubstances or petroleum products on the property to determineor discover the obviousness of the presence or likely presenceof a release or threatened release of any
9、hazardous substance orpetroleum product. In certain cases, additional data, includingsampling, if appropriate under the circumstances, may beneeded in the EBS to support the FOST or FOSL. A previouslyconducted EBS may be updated as necessary and used formaking a FOST or FOSL. An EBS also may help to
10、 satisfyother environmental requirements (for example, to satisfy therequirements of CERFA or to facilitate the preparation ofenvironmental condition reports). In addition, the EBS pro-vides a useful reference document and assists in compliancewith hazard abatement policies related to asbestos and l
11、ead-based paint. The EBS process consists of discrete steps. Thispractice principally addresses EBS-related information gather-ing and analysis.1.1.2 CERCLA Section 120(h) RequirementsThis practiceis intended to assist with the identification of installation areassubject to the notification and cove
12、nant requirements of CER-CLA 120(h) relating to the deed transfer of contaminatedFederal real property (42 USC 9601 et seq.).1.1.3 CERFA RequirementsThis practice can be used toprovide information that can be used to partially fulfill theidentification requirements of CERFA Pub. L. 102-426, 106Stat.
13、 2174, which amended CERCLA. Property classified asarea Type 1, in accordance with Classification D 5746 iseligible for reporting as “uncontaminated” under the provisionsof CERFA. Additionally, certain property classified as areaType 2, where evidence indicates that storage occurred for lessthan one
14、 year, may also be identified as uncontaminated. Atinstallations listed on the National Priorities List, Environmen-tal Protection Agency (EPA) concurrence must be obtained forthe property to be considered “uncontaminated” and thereforetransferable under CERCLA 120(h)(4). The EPA has statedthat ther
15、e may be instances in which it would be appropriate toconcur with the DoD Component that certain property can beidentified as uncontaminated under CERCLA 120(h)(4)although some limited quantity of hazardous substances orpetroleum products have been stored, released, or disposed ofon the property. If
16、 the information available indicates that thestorage, release, or disposal was associated with activities thatwould not be expected to pose a threat to human health or theenvironment (for example, housing areas, petroleum-stainedpavement areas, and areas having undergone routine applica-tion of pest
17、icides), such property should be eligible forexpeditious reuse.1.1.4 Petroleum ProductsPetroleum products and theirderivatives are included within the scope of this practice.Areason which petroleum products or their derivatives were stored1This practice is under the jurisdiction of ASTM Committee E5
18、0 on Environ-mental Assessment and is the direct responsibility of Subcommittee E50.02 onCommercial Real Estate Transactions.Current edition approved April 1, 2005. Published May 2005. Originallyapproved in 1937 as PS 37. Last previous edition approved in 2005 as D 6008-96.1Copyright ASTM Internatio
19、nal, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959, United States.for one year or more, known to have been released or disposedof CERCLA 120(h)(4) are not eligible to be reported as“uncontaminated property” under CERFA.1.1.5 Other Federal, State, and Local EnvironmentalLawsThi
20、s practice does not address requirements of anyfederal, state, or local laws other than the applicable provisionsof CERCLA identified in 1.1.2 and 1.1.3. Users are cautionedthat federal, state, and local laws may impose additional EBSor other environmental assessment obligations that are beyondthe s
21、cope of this practice. Users should also be aware that thereare likely to be other legal obligations with regard to hazardoussubstances or petroleum products discovered on property thatare not addressed in this practice and that may pose risks ofcivil or criminal sanctions, or both, for noncomplianc
22、e.1.1.6 Other Federal, State, and Local Real Property andNatural and Cultural Resources LawsThis practice does notaddress requirements of any federal, state or local real propertyor natural and cultural resources laws. Users are cautioned thatnumerous federal, state, and local laws may impose additi
23、onalenvironmental and other legal requirements that must besatisfied prior to deed transfer of property that are beyond thescope of this practice.1.2 ObjectivesObjectives guiding the development of thispractice are (1) to synthesize and put in writing a standardpractice for conducting a high quality
24、 EBS, (2) to facilitate thedevelopment of high quality, standardized environmental con-dition of property maps to be included in an EBS that can beused to support FOSTs, FOSLs, and other applicable environ-mental condition reports, (3) to facilitate the use of the standardclassification of environme
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