ASTM D2908-91(2017) Standard Practice for Measuring Volatile Organic Matter in Water by Aqueous-Injection Gas Chromatography.pdf
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1、Designation: D2908 91 (Reapproved 2017)Standard Practice forMeasuring Volatile Organic Matter in Water by Aqueous-Injection Gas Chromatography1This standard is issued under the fixed designation D2908; the number immediately following the designation indicates the year oforiginal adoption or, in the
2、 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 practice covers general guidance applicable tocertain test methods for the qualita
3、tive and quantitative deter-mination of specific organic compounds, or classes ofcompounds, in water by direct aqueous injection gas chroma-tography (1, 2, 3, 4).21.2 Volatile organic compounds at aqueous concentrationsgreater than about 1 mg/L can generally be determined bydirect aqueous injection
4、gas chromatography.1.3 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, health, and environmental practices and deter-mine the applicability of regulatory limit
5、ations prior to use.1.4 This international standard was developed in accor-dance with internationally recognized principles on standard-ization established in the Decision on Principles for theDevelopment of International Standards, Guides and Recom-mendations issued by the World Trade Organization
6、TechnicalBarriers to Trade (TBT) Committee.2. Referenced Documents2.1 ASTM Standards:3D1129 Terminology Relating to WaterD1192 Guide for Equipment for Sampling Water and Steamin Closed Conduits (Withdrawn 2003)4D1193 Specification for Reagent WaterD3370 Practices for Sampling Water from Closed Condu
7、itsE260 Practice for Packed Column Gas ChromatographyE355 Practice for Gas Chromatography Terms and Relation-ships3. Terminology3.1 DefinitionsThe following terms in this standard aredefined in accordance with Terminology D1129. For defini-tions of other chromatographic terms used in this standard,r
8、efer to Practice E355.3.1.1 “ghosting” or memory peaks, nan interference,showing as a peak, which appears at the same elution time asthe organic component of previous analysis.3.1.2 internal standard, na material present in or added tosamples in known amount to serve as a reference measurement.3.1.3
9、 noise, nan extraneous electronic signal which affectsbaseline stability.3.1.4 relative retention ratio, nthe retention time of theunknown component divided by the retention time of theinternal standard.3.1.5 retention time, nthe time that elapses from theintroduction of the sample until the peak ma
10、ximum is reached.4. Summary of Practice4.1 This practice defines the applicability of various col-umns and conditions for the separation of naturally occurringor synthetic organics or both, in an aqueous medium forsubsequent detection with a flame ionization detector. Aftervaporization, the aqueous
11、sample is carried through the columnby an inert carrier gas. The sample components are partitionedbetween the carrier gas and a stationary liquid phase on an inertsolid support. The column effluent is burned in an air-hydrogenflame. The ions released from combustion of the organiccomponents induce a
12、n increase in standing current which ismeasured. Although this method is written for hydrogen flamedetection, the basic technology is applicable to other detectorsif water does not interfere.4.2 The elution times are characteristic of the variousorganic components present in the sample, while the pe
13、ak areasare proportional to the quantities of the components. A discus-sion of gas chromatography is presented in Practice E260.1This practice is under the jurisdiction of ASTM Committee D19 on Water andis the direct responsibility of Subcommittee D19.06 on Methods for Analysis forOrganic Substances
14、 in Water.Current edition approved Dec. 15, 2017. Published December 2017. Originallyapproved in 1970. Last previous edition approved in 2011 as D2908 91 (2011).DOI: 10.1520/D2908-91R17.2The boldface numbers in parentheses refer to the list of references at the end ofthis standard.3For referenced AS
15、TM 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 Summary page onthe ASTM website.4The last approved version of this historical standard is referenced onwww.astm
16、.org.Copyright ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959. United StatesThis international standard was developed in accordance with internationally recognized principles on standardization established in the Decision on Principles for theDevelopment of
17、International Standards, Guides and Recommendations issued by the World Trade Organization Technical Barriers to Trade (TBT) Committee.15. Significance and Use5.1 This practice is useful in identifying the major organicconstituents in wastewater for support of effective in-plant orpollution control
18、programs. Currently, the most practical meansfor tentatively identifying and measuring a range of volatileorganic compounds is gas-liquid chromatography. Positiveidentification requires supplemental testing (for example, mul-tiple columns, speciality detectors, spectroscopy, or a combi-nation of the
19、se techniques).6. Interferences6.1 Particulate MatterParticulate or suspended mattershould be removed by centrifugation or membrane filtration ifcomponents of interest are not altered. This pretreatment willprevent both plugging of syringes and formation of condensa-tion nuclei. Acidification will o
20、ften facilitate the dissolving ofparticulate matter, but the operator must determine that pHadjustment does not alter the components to be determined.6.2 Identical Retention TimesWith any given column andoperating conditions, one or more components may elute atidentical retention times. Thus a chrom
21、atographic peak is onlypresumptive evidence of a single component. Confirmationrequires analyses with other columns with varying physical andchemical properties, or spectrometric confirmation of theisolated peak, or both.6.3 AcidificationDetection of certain groups of compo-nents will be enhanced if
22、 the sample is made neutral or slightlyacidic. This may minimize the formation of nonvolatile salts incases such as the analysis of volatile organic acids and basesand certain chlorophenols.6.4 GhostingGhosting is evidenced by an interferencepeak that occurs at the same time as that for a component
23、froma previous analysis but usually with less intensity. Ghostingoccurs because of organic holdup in the injection port. Re-peated Type I water washing with 5-L injections betweensample runs will usually eliminate ghosting problems. Thebaseline is checked at maximum sensitivity to assure that theint
24、erference has been eliminated. In addition to waterinjections, increasing the injection port temperature for aperiod of time will often facilitate the elimination of ghostingproblems.6.4.1 Delayed ElutionHighly polar or high boiling com-ponents may unpredictably elute several chromatograms laterand
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