ASTM D5466-2015 Standard Test Method for Determination of Volatile Organic Compounds in Atmospheres (Canister Sampling Methodology)《测定大气中挥发性有机化合物的标准试验方法 (罐取样法)》.pdf
《ASTM D5466-2015 Standard Test Method for Determination of Volatile Organic Compounds in Atmospheres (Canister Sampling Methodology)《测定大气中挥发性有机化合物的标准试验方法 (罐取样法)》.pdf》由会员分享,可在线阅读,更多相关《ASTM D5466-2015 Standard Test Method for Determination of Volatile Organic Compounds in Atmospheres (Canister Sampling Methodology)《测定大气中挥发性有机化合物的标准试验方法 (罐取样法)》.pdf(32页珍藏版)》请在麦多课文档分享上搜索。
1、Designation: D5466 01 (Reapproved 2007)D5466 15Standard Test Method forDetermination of Volatile Organic ChemicalsCompounds inAtmospheres (Canister Sampling Methodology)1This standard is issued under the fixed designation D5466; the number immediately following the designation indicates the year ofo
2、riginal 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 standard describes a procedure for sampling
3、 and analysis of selected volatile organic compounds (VOCs)in ambient, indoor, orand workplace atmospheres. The test method is based on the collection of whole air samples in stainless steelcanisters with specially treated (passivated) interior surfaces. For sample analysis, a portion of the sample
4、is subsequently removedfrom the canister and the collected VOCs are selectively concentrated by adsorption or condensation onto a trap, subsequentlyreleased by thermal desorption, separated by gas chromatography, and measured by a mass spectrometric detector or otherdetector(s). This test method des
5、cribes procedures for sampling into canisters to final pressures both above and below atmosphericpressure (respectively referred to as pressurized and subatmospheric pressure sampling).21.2 This test method is applicable to specific VOCs that have been tested and determined to be stable when stored
6、in canisters.Numerous compounds, many of which are chlorinated VOCs, have been successfully tested for storage stability in pressurizedcanisters (1-4).3 Although not as extensive, documentation Documentation is also available demonstrating stability of VOCs insubatmospheric pressure canisters. While
7、 initial studies were concentrated on non-polar VOCs, information on storage stability hasbeen extended to Information on storage stability is available for many polar compounds as well (5-7).1.3 The procedure for collecting the sample involves the use of inlet lines and lines, air filters, flow rat
8、e regulators for obtainingtime-integrated samples, and in the case of pressurized samples, an air pump. Canister Typical long-term fixed location canistersamplers have been designed to automatically start and stop the sample collection process using electronically actuated valves andtimers (8-10). T
9、emporary or short-term canister samplers may require the user to manually start and stop sample collection. Aweatherproof shelter is may be required if the sampler is to be usedused outdoors. For the purposes of this test method, refer toPractice D1357 outside. for practices and planning ambient sam
10、pling events.1.4 The organic compounds that have been successfully measured at single-digit parts-per-billion by volume (ppbv) levels withthis test method are listed in Table 1. ThisThe test method is applicable to VOC concentrations ranging from the detection limitto approximately 300 ppbv. Above t
11、his concentration, samples require dilution smaller sample aliquots of sample gas may beanalyzed or samples can be diluted with dry ultra-high-purity nitrogen or air.1.5 The values stated in SI units are to be regarded as standard. No other units of measurement are included in this standard.1.6 This
12、 standard does not purport to address all of the safety concerns, if any, associated with its use. It is the responsibilityof the user of this standard to establish appropriate safety and health practices and determine the applicability of regulatorylimitations prior to use. Safety practices should
13、be part of the users SOP manual.2. Referenced Documents2.1 ASTM Standards:4D1356 Terminology Relating to Sampling and Analysis of AtmospheresD1357 Practice for Planning the Sampling of the Ambient AtmosphereE260 Practice for Packed Column Gas ChromatographyE355 Practice for Gas Chromatography Terms
14、and Relationships1 This test method is under the jurisdiction of ASTM Committee D22 on Air Quality and is the direct responsibility of Subcommittee D22.05 on Indoor Air.Current edition approved April 1, 2007Dec. 1, 2015. Published June 2007June 2016. Originally approved in 1993. Last previous editio
15、n approved in 20012007 asD5466 01.D5466 01 (2007). DOI: 10.1520/D5466-01R07.10.1520/D5466-15.2 This test method is based on EPACompendium Method TO-14, “The Determination of Volatile Organic Compounds (VOCs) inAmbientAir Using SUMMAPassivatedCanister Sampling and Gas Chromatographic Analysis,” May 1
16、988.3 The boldface numbers in parentheses refer to the list of references at the end of the standard.4 For referencedASTM standards, visit theASTM website, www.astm.org, or contactASTM Customer Service at serviceastm.org. For Annual Book of ASTM Standardsvolume information, refer to the standards Do
17、cument Summary page on the ASTM website.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. Becauseit may not be technically possible to adequately depict all changes accurately, ASTM
18、 recommends that users consult prior editions as appropriate. In all cases only the current versionof the standard as published by ASTM is to be considered the official document.Copyright ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959. United States1TABLE 2
19、Ion/Abundance and Expected Retention Time for Selected VOCs Analyzed by GC-MS-SIMCompoundIon/Abundance(amu/%base peak)ExpectedRetentionTime (min)Freon 12 (Dichlorodifluoromethane) 85/100 5.0187/31Methyl chloride (Chloromethane) 50/100 5.6952/34Freon 114 (1,2-Dichloro-1,1,2,2-tetrafluoroethane) 85/10
20、0 6.55135/5687/33Vinyl chloride (Chloroethene) 62/100 6.7127/12564/32Methyl bromide (Bromomethane) 94/100 7.8396/85Ethyl chloride (Chloroethane) 64/100 8.4329/14027/140Freon 11 (Trichlorofluoromethane) 101/100 9.97103/67Vinylidene chloride (1,1-Dichloroethylene) 61/100 10.9396/5563/31Dichloromethane
21、 (Methylene chloride) 49/100 11.2184/6586/45Freon 113 (1,1,2-Trichloro-1,2,2-trifluoroethane) 151/100 11.60101/140103/901,1-Dichloroethane 63/100 12.5027/6465/33cis-1,2-Dichloroethylene 61/100 13.4096/6098/44Chloroform (Trichloromethane) 83/100 13.7585/6547/351,2-Dichloroethane (Ethylene dichloride)
22、 62/100 14.3927/7064/31Methyl chloroform (1,1,1-Trichloroethane) 97/100 14.6299/6461/61Benzene 78/100 15.0477/2550/35Carbon tetrachloride (Tetrachloromethane) 117/100 15.18119/971,2-Dichloropropane (Propylene dichloride) 63/100 15.8341/9062/70Trichloroethylene (Trichloroethene) 130/100 16.10132/9295
23、/87cis-1,3-Dichloropropene 75/100 16.9639/7077/30trans-1,3-Dichloropropene 75/100 17.4939/7077/301,1,2-Trichloroethane (Vinyl trichloride) 97/100 17.6183/9061/82Toluene (Methyl benzene) 91/100 17.8692/571,2-Dibromoethane (Ethylene dibromide) 107/100 18.48109/9627/115Tetrachloroethylene (Perchloroeth
24、ylene) 166/100 19.01164/74131/60Chlorobenzene 112/100 19.7377/62114/32D5466 152TABLE 2 ContinuedCompoundIon/Abundance(amu/%base peak)ExpectedRetentionTime (min)Ethylbenzene 91/100 20.20106/28m,p-Xylene (1,3/1,4-dimethylbenzene) 91/100 20.41106/40Styrene (Vinyl benzene) 104/100 20.8178/60103/491,1,2,
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