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本文(ASTM E697-1996(2011) 8125 Standard Practice for Use of Electron-Capture Detectors in Gas Chromatography 《气相色谱法中电子俘获检测器使用的标准操作规程》.pdf)为本站会员(ideacase155)主动上传,麦多课文库仅提供信息存储空间,仅对用户上传内容的表现方式做保护处理,对上载内容本身不做任何修改或编辑。 若此文所含内容侵犯了您的版权或隐私,请立即通知麦多课文库(发送邮件至master@mydoc123.com或直接QQ联系客服),我们立即给予删除!

ASTM E697-1996(2011) 8125 Standard Practice for Use of Electron-Capture Detectors in Gas Chromatography 《气相色谱法中电子俘获检测器使用的标准操作规程》.pdf

1、Designation: E697 96 (Reapproved 2011)Standard Practice forUse of Electron-Capture Detectors in Gas Chromatography1This standard is issued under the fixed designation E697; the number immediately following the designation indicates the year oforiginal adoption or, in the case of revision, the year o

2、f 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 the use of an electron-capturedetector (ECD) as the detection component of a gas chromato-graph

3、ic system.1.2 This practice is intended to describe the operation andperformance of the ECD as a guide for its use in a completechromatographic system.1.3 For general gas chromatographic procedures, PracticeE260 or Practice E1510 should be followed except wherespecific changes are recommended in thi

4、s practice for use of anECD. For a definition of gas chromatography and its variousterms, see Practice E355. These standards also describe theperformance of the detector in terms which the analyst can useto predict overall system performance when the detector iscoupled to the column and other chroma

5、tographic components.1.4 The values stated in SI units are to be regarded asstandard. No other units of measurement are included in thisstandard.1.5 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 stand

6、ard to establish appro-priate safety and health practices and determine the applica-bility of regulatory limitations prior to use. For specific safetyinformation, see Section 3.2. Referenced Documents2.1 ASTM Standards:2E260 Practice for Packed Column Gas ChromatographyE355 Practice for Gas Chromato

7、graphy Terms and Rela-tionshipsE1510 Practice for Installing Fused Silica Open TubularCapillary Columns in Gas Chromatographs2.2 CGA Standards:3CGA G-5.4 Standard for Hydrogen Piping Systems atConsumer LocationsCGA P-1 Safe Handling of Compressed Gases in Contain-ersCGA P-9 The Inert Gases: Argon, N

8、itrogen and HeliumCGA P-12 Safe Handling of Cryogenic LiquidsCGA V-7 Standard Method of Determining Cylinder ValveOutlet Connections for Industrial Gas MixturesHB-3 Handbook of Compressed Gases2.3 Federal Standard:4Title 10 Code of Federal Regulations, Part 203. Hazards3.1 Gas Handling SafetyThe saf

9、e handling of compressedgases and cryogenic liquids for use in chromatography is theresponsibility of every laboratory. The Compressed Gas Asso-ciation (CGA), a member group of specialty and bulk gassuppliers, publishes the following guidelines to assist thelaboratory chemist to establish a safe wor

10、k environment.Applicable CGA publications include: CGA P-1, CGA G-5.4,CGA P-9, CGA V-7, CGA P-12, and HB-3.3.2 The electron capture detector contains a radioactiveisotope that emits b-particles into the gas flowing through thedetector. The gas effluent of the detector must be vented to afume hood to

11、 prevent possible radioactive contamination in thelaboratory. Venting must conform to Title 10, Part 20 andAppendix B.4. Principles of Electron Capture Detection4.1 The ECD is an ionizating detector comprising a sourceof thermal electrons inside a reaction/detection chamber filledwith an appropriate

12、 reagent gas. In packed column GC thecarrier gas generally fullfills the requirements of the reagentgas. In capillary column GC the make-up gas acts as thereagent gas and also sweeps the detector volume in order topass column eluate efficiently through the detector. While the1This practice is under

13、the jurisdiction of ASTM Committee E13 on MolecularSpectroscopy and Separation Science and is the direct responsibility of Subcom-mittee E13.19 on Separation Science.Current edition approved Nov. 1, 2011. Published December 2011. Originallyapproved in 1979. Last previous edition approved in 2006 as

14、E697 96 (2006).DOI: 10.1520/E0697-96R11.2For 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 Summary page onthe ASTM website.3Available from Compr

15、essed Gas Association (CGA), 4221 Walney Rd., 5thFloor, Chantilly, VA 20151-2923, http:/.4Available from U.S. Government Printing Office Superintendent of Documents,732 N. Capitol St., NW, Mail Stop: SDE, Washington, DC 20401, http:/www.access.gpo.gov.1Copyright ASTM International, 100 Barr Harbor D

16、rive, PO Box C700, West Conshohocken, PA 19428-2959, United States.carrier/reagent gas flows through the chamber the devicedetects those compounds entering the chamber that are capableof reacting with the thermal electrons to form negative ions.These electron capturing reactions cause a decrease in

17、theconcentration of free electrons in the chamber. The detectorresponse is therefore a measure of the concentration and thechange in concentration of electrons (1-17).54.2 A radioactive source inside the detector provides asource of b-rays, which in turn ionize the carrier gas to producea source of

18、electrons (18). A constant or intermittent negativepotential, usually less than 100 V, is applied across the reactionchamber to collect these electrons at the anode. This flow of“secondary” electrons produces a background or “standing”current and is measured by a suitable electrometer-amplifierand r

19、ecording system.4.3 As sample components pass through the detector, theycombine with electrons. This causes a decrease in the standingcurrent or an increase in frequency of potential pulses depend-ing on the mode of ECD operation (see 5.3). The magnitude ofcurrent reduction or frequency increase is

20、a measure of theconcentration and electron capture rate of the compound. TheECD is unique among ionizing detectors because it is this lossin electron concentration that is measured rather than anincrease in signal.4.4 The two major classifications of electron-capture reac-tions in the ECD are the di

21、ssociative and nondissociativemechanisms.4.4.1 In the dissociative-capture mechanism, the samplemoleculeAB reacts with the electron and dissociates into a freeradical and a negative ion:AB + eA+B. This dissociativeelectron-capture reaction is favored at high detector tempera-tures. Thus, an increase

22、 in noncoulometric ECD response withincreasing detector temperature is evidence of the dissociativeelectron-capture reaction for a compound. Naturally, detect-ability is increased at higher detector temperatures for thosecompounds which undergo dissociative mechanisms.4.4.2 In the nondissociative re

23、action, the sample moleculeAB reacts with the electron and forms a molecular negativeion: AB + e AB. The cross section for electron absorptiondecreases with an increase in detector temperature in the caseof the nondissociative mechanism. Consequently, the nondis-sociative reaction is favored at lowe

24、r detector temperatures andthe noncoulometric ECD response will decrease if the detectortemperature is increased.4.4.3 Beside the two main types of electron capture reac-tions, resonance electron absorption processes are also possiblein the ECD (for example, AB+e=AB). These resonancereactions are ch

25、aracterized when an electron absorbing com-pound exhibits a large increase in absorption cross section overa narrow range of electron energies. This is an extremelytemperature sensitive reaction due to the reverse reactionwhich is a thermal electron deactivation reaction. For solutes inthis category

26、 a maximum detector temperature is reached atwhich higher temperatures diminish the response to the analyte(55).4.5 The ECD is very selective for those compounds thathave a high electron-capture rate and the principal use of thedetector is for the measurement of trace quantities of thesematerials, 1

27、09g or less. Often, compounds can be derivatizedby suitable reagents to provide detection of very low levels byECD (19, 20). For applications requiring less sensitivity, otherdetectors are recommended.4.6 A compound with a high electron-capture rate oftencontains an electrophoric group, that is, a h

28、ighly polar moietythat provides an electron-deficient center in the molecule. Thisgroup promotes the ability of the molecule to attach freeelectrons and also may stabilize the resultant negativemolecule-ion. Examples of a few electrophores are the halo-gens, sulfur, phosphorus, and nitro- and a-dica

29、rbonyl groups(21-25).4.7 A compound could also have a high electron-capturerate without containing an obvious electrophore in its structure,or its electron-capture rate could be much greater than that dueto the known electrophore that might be present. In these casescertain structural features, whic

30、h by themselves are onlyweakly electrophoric, are combined so as to give the moleculeits electrophoric character. A few examples of these are thequinones, cyclooctatetracene, 3,17-diketosteroids, o-phthalatesand conjugated diketones (26-32).4.8 Enhanced response toward certain compounds has beenrepo

31、rted after the addition of either oxygen or nitrous oxide tothe carrier gas. Oxygen doping can increase the responsetoward CO2, certain halogenated hydrocarbons, and polycyclicaromatic compounds (33). Small amounts of nitrous oxide canincrease the response toward methane, carbon dioxide, andhydrogen

32、.4.9 While it is true that the ECD is an extremely sensitivedetector capable of picogram and even femtogram levels ofdetection, its response characteristics vary tremendously fromone chemical class to another. Furthermore, the responsecharacteristic for a specific solute of interest can also beenhan

33、ced or diminished depending on the detectors operatingtemperature (56) (see 4.4 and 5.5). The detectors responsecharacteristic to a solute is also dependent on the choice ofreagent gas and since the ECD is a concentration dependentdetector, it is also dependent on the total gas flow rate throughthe

34、detector (see 5.5). These two parameters affect both theabsolute sensitivity and the linear range an ECD has to a givensolute. It is prudent of the operator of the ECD to understandthe influence that each of the aforementioned parameters hason the detection of a solute of interest and, to optimize t

35、heparameters prior to final testing.5. Detector Construction5.1 Geometry of the Detector Cell:5.1.1 Three basic types of b-ray ionization-detector geom-etries can be considered applicable as electron-capture detectorcells: the parallel-plate design, the concentric-tube or coaxial-tube design, and re

36、cessed electrode or asymmetric type (34-37). The latter could be considered a variation of theconcentric-tube design. Both the plane-plate geometry andconcentric geometry are used almost exclusively for pulsedoperation. Although the asymmetric configuration is primarilyemployed in the d-c operation

37、of electron-capture detectors, a5The boldface numbers in parentheses refer to a list of references at the end ofthis practice.E697 96 (2011)2unique version of the asymmetric design (referred to as adisplaced-coaxial-cylinder geometry) has been developed forpulse-modulated operation. The optimum mode

38、 of operation isusually different for each detector geometry and this must beconsidered, where necessary, in choosing certain operatingparameters.5.1.2 In general, more efficient operation is achieved if thedetector is polarized such that the gas flow is counter to theflow of electrons toward the an

39、ode. In this regard, the radio-active source should be placed at the cathode or as near to it aspossible.5.1.3 Other geometric factors that affect cell response andoperation are cell volume and electrode spacing, which may ormay not be altered concurrently depending upon the construc-tion of the det

40、ector. Of course, both these variables can besignificant at the extremes, and optimum values will alsodepend upon other parameters of operation. In the pulsedoperational mode, the electrons within the cell must be able toreach the anode or collector electrode during the 0.1 to 1.0-svoltage pulse. Ge

41、nerally, electrode distances of 0.5 to 1.0 cmare acceptable and can be used optimally by the proper choiceof operating conditions. Cell volume should be small enough tomaintain effective electron capture without encountering othertypes of electron reactions and also small enough so as not tolose any

42、 resolution that may have been achieved by high-resolution chromatographic systems. Typical ECD cell vol-umes range from approximately 2 to 0.3 cm3. A detector cellwith a relatively low internal volume is particularly importantwhen the ECD is used with open tubular columns. In additionto the precedi

43、ng electrical and chromatographic requirements,the electrode dimensions of the detector are also determined bythe range of the particular b-rays.5.2 Radioactive Source:5.2.1 Many b-ray-emitting isotopes can be used as theprimary ionization source. The two most suitable are3H(tritium) (38, 39). and63

44、Ni (40).5.2.1.1 TritiumThis isotope is usually coated on 302stainless steel or Hastelloy C, which is a nickel-base alloy. Thetritium attached to the former foil material is in the form of Ti3H2; however, there is uncertainty concerning the exact meansof tritium attachment to the scandium (Sc) substr

45、ate of theHastelloy C foil. The proposed methods of attachment includeSc3H3and3H2as the occluded gas.The nominal source activityfor tritium is 250 mCi in titanium sources and 1000 mCi inscandium sources. Department of Energy regulations permit amaximum operating temperature of 225C for the Ti3H2sour

46、ceand 325C for the Sc3H3source. Naturally, detector tempera-tures that are less than the maximum values will lengthen thelifetimes of the tritiated sources by reducing the tritiumemanation rates. The newer scandium sources are more effec-tive at minimizing the contamination problems associated withe

47、lectron-capture detectors because of their capability for op-eration at 325C. Furthermore, the tritiated-scandium sourcedisplays a factor-of-three detectability increase for dissociativeelectron-capturing species, that is, halogenated molecules.Another advantage of scandium tritide sources is their

48、avail-ability at much higher specific activities than nickel-63sources; therefore, Sc3H3sources are smaller and permit theconstruction of detector cells with smaller internal volumes.The maximum energy of the b-rays emitted by tritium is 0.018MeV.5.2.1.2 Nickel-63 (63Ni)This radioactive isotope is u

49、su-ally either electroplated directly on a gold foil in the detectorcell or is plated directly onto the interior of the cell block.Since the maximum energy of the b-rays from the63Ni is 0.067MeV and63Ni is a more effective radiation source than tritium,the normal63Ni activity is typically 10 to 15 mCi. Anadvantage of63Ni is its ability to be heated to 350C and theconcomitant decrease in detector contamination during chro-matographic operation. Another advantage of the high detectortemperatures available with63Ni is an enhanced sensitivity forcompounds

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