ASTM D6044-1996(2003) Standard Guide for Representative Sampling for Management of Waste and Contaminated Media《废物和污染媒介管理用代表性取样的标准指南》.pdf
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1、Designation: D 6044 96 (Reapproved 2003)Standard Guide forRepresentative Sampling for Management of Waste andContaminated Media1This standard is issued under the fixed designation D 6044; the number immediately following the designation indicates the year oforiginal adoption or, in the case of revis
2、ion, the year of last revision. 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 This guide covers the definition of representativeness inenvironmental sampling, identifies sources
3、that can affectrepresentativeness (especially bias), and describes the at-tributes that a representative sample or a representative set ofsamples should possess. For convenience, the term“ represen-tative sample” is used in this guide to denote both a represen-tative sample and a representative set
4、of samples, unlessotherwise qualified in the text.1.2 This guide outlines a process by which a representativesample may be obtained from a population. The purpose of therepresentative sample is to provide information about a statis-tical parameter(s) (such as mean) of the population regardingsome ch
5、aracteristic(s) (such as concentration) of its constitu-ent(s) (such as lead). This process includes the followingstages: (1) minimization of sampling bias and optimization ofprecision while taking the physical samples, (2) minimizationof measurement bias and optimization of precision whenanalyzing
6、the physical samples to obtain data, and (3) minimi-zation of statistical bias when making inference from thesample data to the population. While both bias and precisionare covered in this guide, major emphasis is given to biasreduction.1.3 This guide describes the attributes of a representativesamp
7、le and presents a general methodology for obtainingrepresentative samples. It does not, however, provide specificor comprehensive sampling procedures. It is the users respon-sibility to ensure that proper and adequate procedures are used.1.4 The assessment of the representativeness of a sample isnot
8、 covered in this guide since it is not possible to ever knowthe true value of the population.1.5 Since the purpose of each sampling event is unique, thisguide does not attempt to give a step by step account of how todevelop a sampling design that results in the collection ofrepresentative samples.1.
9、6 Appendix X1 contains two case studies, which discussthe factors for obtaining representative samples.1.7 This standard does not purport to address all of thesafety concerns, if any, associated with its use. It is theresponsibility of the user of this standard to establish appro-priate safety and h
10、ealth practices and determine the applica-bility of regulatory limitations prior to use.2. Referenced Documents2.1 ASTM Standards:2D 3370 Practices for Sampling Water from Closed ConduitsD 4448 Guide for Sampling Groundwater Monitoring WellsD 4547 Practice for Sampling Waste and Soils for VolatileOr
11、ganic CompoundsD 4700 Guide for Soil Sampling from the Vadose ZoneD 4823 Guide for Core Sampling Submerged, Unconsoli-dated SedimentsD 5088 Practice for Decontamination of Field EquipmentUsed at Nonradioactive Waste SitesD 5792 Practice for Generation of Environmental DataRelated to Waste Management
12、 Activities: Development ofData Quality ObjectivesD 5956 Guide for Sampling Strategies for HeterogeneousWastesD 6051 Guide for Composite Sampling and Field Subsam-pling for Environmental Waste Management Activities3. Terminology3.1 analytical unit, nthe actual amount of the samplematerial analyzed i
13、n the laboratory.3.2 bias, na systematic positive or negative deviation ofthe sample or estimated value from the true population value.3.2.1 DiscussionThis guide discusses three sources ofbiassampling bias, measurement bias, and statistical bias.There is a sampling bias when the value inherent in th
14、ephysical samples is systematically different from what isinherent in the population.There is a measurement bias when the measurement processproduces a sample value systematically different from thatinherent in the sample itself, although the physical sample is1This guide is under the jurisdiction o
15、f ASTM Committee D34 on WasteManagement and is the direct responsibility of Subcommittee D34.01.01 onPlanning for Sampling.Current edition approved March 10, 2003. Published June 2003. Originallyapproved in 1996. Last previous edition approved in 1996 as D 6044 96.2For referenced ASTM standards, vis
16、it the ASTM website, www.astm.org, orcontact ASTM Customer Service at serviceastm.org. For Annual Book of ASTMStandards volume information, refer to the standards Document Summary page onthe ASTM website.1Copyright ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2
17、959, United States.itself unbiased. Measurement bias can also include any sys-tematic difference between the original sample and the sampleanalyzed, when the analyzed sample may have been altereddue to improper procedures such as improper sample preser-vation or preparation, or both.There is a stati
18、stical bias when, in the absence of samplingbias and measurement bias, the statistical procedure produces abiased estimate of the population value.Sampling bias is considered the most important factoraffecting inference from the samples to the population.3.3 biased sampling, nthe taking of a sample(
19、s) with priorknowledge that the sampling result will be biased relative tothe true value of the population.3.3.1 DiscussionThis is the taking of a sample(s) basedon available information or knowledge, especially in terms ofvisible signs or knowledge of contamination. This kind ofsampling is used to
20、detect the presence of localized contami-nation or to identify the source of a contamination. Thesampling results are not intended for generalization to theentire population. This is one form of authoritative sampling(see judgment sampling.)3.4 characteristic, na property of items in a sample orpopu
21、lation that can be measured, counted, or otherwise ob-served, such as viscosity, flash point, or concentration.3.5 composite sample, na combination of two or moresamples.3.6 constituent, n an element, component, or ingredient ofthe population.3.6.1 DiscussionIf a population contains several contami-
22、nants (such as acetone, lead, and chromium), these contami-nants are called the constituents of the population.3.7 Data Quality Objectives, DQOs, nqualitative andquantitative statements derived from a DQO process describingthe decision rules and the uncertainties of the decision(s)within the context
23、 of the problem(s) (see Practice D 5792).3.8 Data Quality Objective Processa quality managementtool based on the Scientific Method and developed by the U.S.Environmental Protection Agency to facilitate the planning ofenvironmental data collection activities. The DQO processenables planners to focus
24、their planning efforts by specifyingthe use of data (the decision), the decision criteria (actionlevel), and the decision makers acceptable decision error rates.The products of the DQO process are the DQOs (see PracticeD 5792).3.9 error, nthe random or systematic deviation of theobserved sample valu
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