ASTM D5175-1991(2011) Standard Test Method for Organohalide Pesticides and Polychlorinated Biphenyls in Water by Microextraction and Gas Chromatography《用微量萃取和气相色谱法测试水中有机卤化农药和多氯联苯含量.pdf

《ASTM D5175-1991(2011) Standard Test Method for Organohalide Pesticides and Polychlorinated Biphenyls in Water by Microextraction and Gas Chromatography《用微量萃取和气相色谱法测试水中有机卤化农药和多氯联苯含量.pdf》由会员分享，可在线阅读，更多相关《ASTM D5175-1991(2011) Standard Test Method for Organohalide Pesticides and Polychlorinated Biphenyls in Water by Microextraction and Gas Chromatography《用微量萃取和气相色谱法测试水中有机卤化农药和多氯联苯含量.pdf（12页珍藏版）》请在麦多课文档分享上搜索。

1、Designation: D5175 91 (Reapproved 2011)Standard Test Method forOrganohalide Pesticides and Polychlorinated Biphenyls inWater by Microextraction and Gas Chromatography1This standard is issued under the fixed designation D5175; the number immediately following the designation indicates the year oforig

2、inal adoption or, in the case of revision, the year of last revision. A number in parentheses indicates the year of last reapproval. Asuperscript epsilon () indicates an editorial change since the last revision or reapproval.1. Scope1.1 This test method ( 1, 2, 3 )2is applicable to thedetermination

3、of the following analytes in finished drinkingwater, drinking water during intermediate stages of treatment,and the raw source water:AnalyteChemical Abstract ServiceRegistry NumberAAlachlor 5972-60-8Aldrin 309-00-2Chlordane 57-74-9Dieldrin 60-57-1Endrin 72-20-8Heptachlor 76-44-8Heptachlor Epoxide 10

4、24-57-3Hexachlorobenzene 118-74-1Lindane 58-89-9Methoxychlor 72-43-5Toxaphene 8001-35-2AroclorB1016 12674-11-2AroclorB1221 11104-28-2AroclorB1232 11141-16-5AroclorB1242 53469-21-9AroclorB1248 12672-29-6AroclorB1254 11097-69-1AroclorB1260 11096-82-5ANumbering system of CAS Registry Services, P.O. Box

5、 3343, Columbus, OH43210-0334.BAroclor is a registered trademark of Monsanto Co.1.2 Detection limits for most test method analytes are lessthan 1 g/L. Actual detection limits are highly dependent onthe characteristics of the sample matrix and the gas chroma-tography system. Table 1 contains the appl

6、icable concentrationrange for the precision and bias statements. Only Aroclor 1016and 1254 were included in the interlaboratory test used toderive the precision and bias statements. Data for other PCBproducts are likely to be similar.1.3 Chlordane, toxaphene, and Aroclor products (polychlo-rinated b

7、iphenyls) are multicomponent materials. Precision andbias statements reflect recovery of these materials dosed intowater samples. The precision and bias statements may notapply to environmentally altered materials or to samplescontaining complex mixtures of polychlorinated biphenyls(PCBs) and organo

8、chlorine pesticides.1.4 For compounds other than those listed in 1.1 or for othersample sources, the analyst must demonstrate the applicabilityof this test method by collecting precision and bias data onspiked samples (groundwater, tap water) (4) and providequalitative confirmation of results by gas

9、 chromatography/mass spectrometry (GC/MS) (5) or by GC analysis usingdissimilar columns.1.5 This test method is restricted to use by or under thesupervision of analysts experienced in the use of GC and in theinterpretation of gas chromatograms. Each analyst must dem-onstrate the ability to generate

10、acceptable results using theprocedure described in Section 13.1.6 Analytes that are not separated chromatographically,(analytes that have very similar retention times) cannot beindividually identified and measured in the same calibrationmixture or water sample unless an alternative technique foriden

11、tification and quantitation exists (see section 13.4).1.7 When this test method is used to analyze unfamiliarsamples for any or all of the analytes listed in 1.1, analyteidentifications and concentrations should be confirmed by atleast one additional technique.1.8 The values stated in SI units are t

12、o be regarded as thestandard. The inch-pound units given in parentheses are forinformation only.1.9 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 health p

13、ractices and determine the applica-bility of regulatory limitations prior to use. For specific hazardstatements, see Section 9.2. Referenced Documents2.1 ASTM Standards:3D1129 Terminology Relating to WaterD1193 Specification for Reagent Water1This test method is under the jurisdiction of ASTM Commit

14、tee D19 on Waterand is the direct responsibility of Subcommittee D19.06 on Methods forAnalysis forOrganic Substances in Water.Current edition approved May 1, 2011. Published June 2011. Originallyapproved in 1991. Last previous edition approved in 2003 as D5175 91 (2003).DOI: 10.1520/D5175-91R11.2The

15、 boldface numbers in parentheses refer to a list of references at the end ofthis test method.3For referenced ASTM standards, visit 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

16、Summary page onthe ASTM website.1Copyright ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959, United States.D3534 Test Method for Polychlorinated Biphenyls (PCBs)in Water4D3856 Guide for Good Laboratory Practices in Laborato-ries Engaged in Sampling and Analysi

17、s of WaterD4128 Guide for Identification and Quantitation of OrganicCompounds in Water by Combined Gas Chromatographyand Electron Impact Mass SpectrometryD4210 Practice for Intralaboratory Quality Control Proce-dures and a Discussion on Reporting Low-Level Data4E355 Practice for Gas Chromatography T

18、erms and Rela-tionships2.2 EPA Standards:4Withdrawn. The last approved version of this historical standard is referencedon www.astm.org.TABLE 1 Test Method Precision and BiasAas Functions of ConcentrationCompound Applicable Concentration Range, g/LWater TypeBCDEReagent water Ground waterAlachlor 0.5

19、0 to 37.50 So= 0.077X + 0.09 So= 0.075X + 0.05St= 0.107X + 0.15 St= 0.086X + 0.29X = 1.004C 0.08 X = 1.059C + 0.03Aldrin 0.04 to 1.42 So= 0.030X + 0.02 So=0.115X + 0.00St= 0.251X + 0.00 St= 0.189X + 0.01X = 1.066C + 0.00 X = 0.945C 0.00Chlordane 0.51 to 50.90 So= 0.083X + 0.06St= 0.125X + 0.19X = 1.

20、037C + 0.06So= 0.062X + 0.09St= 0.147X + 0.24X = 0.941C + 0.09Dieldrin 0.10 to 7.53 So= 0.091X + 0.01St= 0.199X + 0.02X = 1.027C + 0.00So= 0.089X + 0.04St= 0.221X + 0.04X = 0.961C + 0.01Endrin 0.10 to 7.50 So=0.116X + 0.01St= 0.134X + 0.02X = 0.958C + 0.01So= 0.045X + 0.15St= 0.196X + 0.07X = 0.958C

21、 + 0.05Heptachlor 0.04 to 1.41 So= 0.104X + 0.01St= 0.206X + 0.02X = 1.002C + 0.02So= 0.058X + 0.02St= 0.153X + 0.02X = 0.964C + 0.02Heptachlor Epoxide 0.04 to 1.42 So= 0.031X + 0.02St= 0.127X + 0.02X = 0.952C + 0.00So= 0.032X + 0.00St= 0.103X + 0.02X = 0.932C + 0.01Hexachlorobenzene 0.01 to 0.37 So

22、= 0.104X + 0.00St= 0.231X + 0.00X = 1.028C 0.00So= 0.148X + 0.00St= 0.301X + 0.00X = 0.901C 0.00Lindane 0.04 to 1.39 So= 0.056X + 0.01St= 0.141X + 0.00X = 1.009C 0.00So= 0.095X + 0.00St= 0.134X 0.00X = 0.909C + 0.00Methoxychlor 0.20 to 15.00 So=0.115X + 0.12St= 0.122X + 0.21X = 0.950C + 0.15So= 0.17

23、9X + 0.02St= 0.210X + 0.08X = 1.014C + 0.07Toxaphene 5.63 to 70.40 So= 0.132X 0.32St= 0.273X 0.72X = 1.087C + 0.24So= 0.067X + 0.28St= 0.181X + 1.52X = 0.903C + 0.50PCB-1016 0.50 to 49.80 So= 0.106X + 0.31St= 0.144X + 0.46X = 0.856C + 0.31So= 0.141X + 0.13St= 0.218X + 0.06X = 0.958C + 0.07PCB-1254 0

24、.50 to 50.40 So= 0.122X + 0.12St= 0.282X + 0.05X = 0.872C 0.01So= 0.126X + 0.17St= 0.396X + 0.02X = 0.938C 0.02ABias = CX.BX = Mean recovery.CC = True concentration value.DSt= Overall standard deviation.ESo= Single analyst standard deviation.D5175 91 (2011)2Method 505, Analysis of Organohalide Pesti

25、cides and Aro-clors in Water by Microextraction and Gas Chromatogra-phy5Method 680, Determination of Pesticides and PCBs inWater and Soil/Sediment by Gas Chromatography/MassSpectrometry53. Terminology3.1 DefinitionsFor definitions of terms used in this testmethod, refer to Terminology D1129 and Prac

26、tice E355.3.2 Definitions of Terms Specific to This Standard:3.2.1 field duplicates (FD 1 and FD 2), ntwo separatesamples collected at the same time and placed under identicalcircumstances and treated exactly the same throughout fieldand laboratory procedures. Analyses of FD 1 and FD 2 give ameasure

27、 of the precision associated with sample collection,preservation and storage, as well as with laboratory procedures.3.2.2 field reagent blank (FRB), nreagent water placed ina sample container in the laboratory and treated as a sample inall respects, including exposure to sampling site conditions,sto

28、rage, preservation, and all analytical procedures. The re-agent water must be transferred to an empty, clean samplecontainer in the field. The purpose of the FRB is to determineif analytes or other interferences are present in the fieldenvironment.3.2.3 instrument performance check solution (IPC), n

29、asolution of analytes used to evaluate the performance of theinstrument system with respect to test method criteria.3.2.4 laboratory duplicates (LD 1 and LD 2), ntwosample aliquots taken in the analytical laboratory and analyzedseparately with identical procedures. Analyses of LD 1 and LD2 give a me

30、asure of the precision associated with laboratoryprocedures but not with sample collection, preservation, orstorage procedures.3.2.5 laboratory fortified blank (LFB), nan aliquot ofreagent water to which known quantities of the analytes areadded in the laboratory. The LFB is analyzed exactly like as

31、ample, and its purpose is to determine whether the method-ology is in control, and whether the laboratory is capable ofmaking accurate and precise measurements.3.2.6 laboratory fortified sample matrix (LFM), nanaliquot of an environmental sample to which known quantitiesof the analytes are added in

32、the laboratory. The LFM isanalyzed as a sample, and its purpose is to determine whetherthe sample matrix contributes bias to the analytical results. Thebackground concentrations of the analytes in the sample matrixmust be determined in a separate aliquot and the measuredvalues in the LFM corrected f

33、or background concentrations.3.2.7 laboratory reagent blank (LRB), nan aliquot ofreagent water that is treated as a sample including exposure toall glassware, equipment, solvents, and reagents used withother samples. The LRB is used to determine if methodanalytes or other interferences are present i

34、n the laboratoryenvironment, the reagents, or the apparatus.3.2.8 standard solution, secondary dilution, na solutionof several analytes prepared in the laboratory from stockstandard solutions and diluted as needed to prepare calibrationsolutions and other needed analyte solutions.3.2.9 standard solu

35、tion, stock, na concentrated solutioncontaining a single certified standard that is an analyte or aconcentrated solution of a single analyte prepared in thelaboratory with an assayed reference compound. Stock stan-dard solutions are used to prepare secondary dilution standards.3.2.10 quality control

36、 sample (QCS), na sample contain-ing analytes or a solution of analytes in a water-misciblesolvent used to fortify reagent water or environmental samples.The QCS must be independent of solutions used to preparestandards and should be obtained from a source external to thelaboratory. The QCS is used

37、to check laboratory performancewith externally prepared test materials.4. Summary of Test Method4.1 This is a microextraction method in which 35 mL ofsample are extracted with 2 mL of hexane. Two L of theextract are injected into a gas chromatograph equipped with alinearized electron capture detecto

38、r for separation and analysis.Aqueous calibration standards are extracted and analyzed in anidentical manner to compensate for possible extraction losses.4.2 The extraction and analysis time is 30 to 50 min persample depending upon the analytes and the analytical condi-tions chosen.4.3 This test met

39、hod is based largely on EPA Method 505.5. Significance and Use5.1 The extensive and widespread use of organochlorinepesticides and PCBs has resulted in their presence in all partsof the environment. These compounds are persistent and mayhave adverse effects on the environment. Thus, there is a needt

40、o identify and quantitate these compounds in water samples.6. Interferences6.1 Interferences may be caused by contaminants in sol-vents, reagents, glassware, and other sample processing appa-ratus that lead to discrete artifacts or elevated baselines in gaschromatograms. All reagents and apparatus m

41、ust be routinelydemonstrated to be free from interferences under the conditionsof the analysis by running laboratory reagent blanks asdescribed in 12.2.6.1.1 Glassware must be scrupulously cleaned (2). Clean allglassware as soon as possible after use by thoroughly rinsingwith the last solvent used i

42、n it. Follow by washing with hot tapwater and detergent and thoroughly rinsing with tap andreagent water. Drain dry and heat in an oven or muffle furnaceat 400C for 1 h. Do not heat volumetric ware. Thermallystable materials might not be eliminated by this treatment.Thorough rinsing with acetone may

43、 be substituted for theheating. After drying and cooling, seal and store glassware ina clean environment to prevent any accumulation of dust orother contaminants. Store inverted or capped with aluminumfoil.6.1.2 The use of high purity reagents and solvents helps tominimize interference problems. Pur

44、ification of solvents bydistillation in all-glass systems may be required.6.2 Phthalate esters, frequently found in plastics, paints, andother common laboratory items, produce a positive response on5Available from US EPA, Environmental Monitoring Systems Laboratory,Cincinnati, OH 45268.D5175 91 (201

45、1)3an electron capture detector. Therefore, samples and solventsshould come in contact only with those materials specified inthis test method.6.3 Interfering contamination may occur when a samplecontaining low concentrations of analytes is analyzed imme-diately following a sample containing relative

46、ly high concen-trations of analytes. Between-sample rinsing of the samplesyringe and associated equipment with hexane can minimizesample cross contamination. After analysis of a sample con-taining high concentrations of analytes, one or more injectionsof hexane should be made to ensure that accurate

47、 values areobtained for the next sample.6.4 Matrix interferences may be caused by contaminantsthat are coextracted from the sample. Also, note that all theanalytes listed in the scope are not resolved from each other onany one column; one analyte of interest may be an interferentfor another analyte

48、of interest. The extent of matrix interfer-ences will vary considerably from source to source dependingupon the water sampled. Cleanup of sample extracts may benecessary. Positive identifications should be confirmed (seesection 13.4).6.5 It is important that samples and working standards becontained

49、 in the same solvent. The solvent for workingstandards must be the same as the final solvent used in samplepreparation. If this is not the case, chromatographic compara-bility of standards to sample may be affected.6.6 Caution must be taken in the determination of endrinsince it has been reported that the splitless injector may causeendrin degradation (6). The analyst should be alerted to thispossible interference resulting in an erratic response for endrin.6.7 Variable amounts of pesticides and PCBs from aqueoussolutions adhere to gla