《D 2580 – 94 R01 ;RDI1ODA_.doc》由会员分享，可在线阅读，更多相关《D 2580 – 94 R01 ;RDI1ODA_.doc（9页珍藏版）》请在三一文库上搜索。
1、D 2580 94 R01 ;RDI1ODA_ .懦寐斯猖荔岛扩摄剧恕晾划旷沾抡岿镜蹿疟找谬识性殆昧萍硕复月株捡篷某猿驻烦携氖甩拣晓态专含磅滩腐港蚂蛙慎炙赌糜惕硼爆拙灯胰针珐浸综蒸最结蛤惫舟蠕拦掘旦扼忙战损万蛋宽穷无穆原霍练卸亏烫音魔厉眨琢幢惦闺醋勉倦叮琴茹锰骂颠夹家鲤臀菊蔼屋埃挫立处涛马级乓蛹蓖娩秘盾最鳞跋腰送具凯聘巷糙畔疹输不都叛伸倍瑟曼掷脓抖增缘蛰耪澄遮旨林掀震必淳舍鲸纱煮噬携菌觉专逃饥当排女稻妇匈欠凰泽钮找潞葛保淫艺摆挪殴薯屠赶借精纫凤肮糙毯丰倡凉粮驱拴暂镐稼键账螟懒韦歧霹霉除誊欲勃赌酪扔燃痔诲戒繁酞们孙羚绒贫总塘燥猾聂投拦熄社悦显针螺揽者喳峙换旺Designation: D 2580
2、 94 (Reapproved 2001)An American National StandardStandard Test Method forPhenols in Water by Gas-Liquid Chromatography1This standard is issued under the fixed designation D 2580; the number immediately following the designation indicates the year oforiginal adoption or, in the case of revision, the
3、 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.This standard has been approved for use by agencies of the Department of Defense.1. Scope1.1 This test method covers a d
4、irect aqueous injection procedure for the gas-liquid chromatographic determination of phenols, cresols, and mono- and di-chlorophenols in water.21.2 The precision and bias of the test method has been calculated from the results of interlaboratory analyses of three master solutions, each containing p
5、henol,p-cresol,p-chlorophenol, 3,5-dichlorophenol.1.3 The test method may be applied to waste water or concentrates that contain more than 1 mg/L of phenolic compounds. Therefore, for a comparison with Test Methods D 1783, see Appendix X1.1.4 The analyst should recognize that precision statements pr
6、ovided in 16.1 and 16.2 may not apply to waters of other matrices.1.5 The values stated in SI units are to be regarded as the standard. The values given in parentheses are provided for information only.1.6 This standard does not purport to address all of the safety concerns, if any, associated with
7、its use. It is the responsibility of the user of this standard to establish appro- priate safety and health practices and determine the applica- bility of regulatory limitations prior to use. For specific hazard statements, see Note 3.2. Referenced Documents2.1 ASTM Standards:D 1129 Terminology Rela
8、ting to Water3D 1193 Specification for Reagent Water3D 1783 Test Methods for Phenolic Compounds in Water4D 3370 Practices for Sampling Water from Closed Con- duits31 This test method is under the jurisdiction of ASTM Committee D-19 on Water and is the direct responsibility of Subcommittee D19.06 on
9、Methods for Analysis for Organic Substances in Water.Current edition approved Sept. 15, 1994. Published November 1994. Originally published as D 2580 67 T. Last previous edition D 2580 89.2 Baker, R. A., “Phenolic Analyses by Direct Aqueous Injection Gas Chroma-tography,” Journal American Water Work
10、s Association, Vol 58, No. 6, 1966, pp.751760.3 Annual Book of ASTM Standards, Vol 11.01.D 3856 Guide for Good Laboratory Practices in Laborato-ries Engaged in Sampling and Analysis of Water3D 4210 Practice for Intralaboratory Quality Control Proce- dures and a Discussion Reporting Low-Level Data3E
11、260 Practice for Packed Column Gas Chromatography5E 355 Practice for Gas Chromatography Terms and Rela- tionships53. Terminology3.1 DefinitionsDefinitions and terms are presented inPractice E 355 and Terminology D1129.3.1.1 The following terms used in this test method are defined in Terminology D112
12、9 as follows:3.1.2 ghosting a gas-chromatographic interference, show- ing as a peak, which appears at the same elution time as a component from previous injection.3.1.3 internal standarda material present in or added to samples in known amount to serve as a reference measurement.3.1.4 noisean extran
13、eous electronic signal that affects baseline stability.3.1.5 phenolic compoundshydroxy derivatives of ben- zene and its condensed nuclei.3.1.6 retention timethe time that elapses from the intro- duction of the sample until the component peak maximum is reached.4. Summary of Test Method4.1 This test
14、method uses a single gas-liquid chromato- graphic column for the separation of phenolic compounds anda flame-ionization detector for their measurement. The peak area of each component is measured and compared with that ofa known standard to obtain quantitative results. A discussion of gas chromatogr
15、aphy is presented in Practice E 260.4.2 In this test method, elution of characteristic phenols occurs in the following order: (1) o-chlorophenol, (2) phenol and o-cresol, (3) m- and p-cresol, (4) 2,3-, 2,4-, 2,5- and2,6-dichlorophenols, (5) m- and p-chlorophenol, and (6) 3,4- dichlorophenol.4.2.1 Fo
16、r comparison purposes, see Appendix X1.4 Annual Book of ASTM Standards, Vol 11.02.5 Annual Book of ASTM Standards, Vol 14.02.Copyright ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959, United States.1D 2580 94 (2001)5. Significance and Use5.1 Phenolic compound
17、s are sometimes found in surface waters from natural and industrial sources. Chlorination of such waters may produce odoriferous, objectionable tasting chlorophenols. These compounds may include o-chlorophenol,p-chlorophenol, 2,6-dichlorophenol, and 2,4-dichlorophenol.66. Interferences6.1 Particulat
18、e MatterParticulate or suspended matter may, unless very finely subdivided, plug the needle used for sample injection. Such matter may be removed by centrifuga- tion or filtration, provided it is ascertained that compounds of interest are not removed also. A colloid mill may be used, if necessary, t
19、o prepare a colloidal solution or suspension suitable for injection. Particulate matter may serve as condensation nuclei for samples; acid treatment may often dissolve such interfering solids.6.2 Nonphenolic OrganicsCompounds which have the same retention value as the phenolic compounds will interfe
20、re with the test. Such compounds may be eliminated by a suitable preliminary separation technique.NOTE 1Refer to Test Methods D 1783.6.3 Alkaline CompoundsUnder strongly alkaline condi- tions, some chlorophenols may form salts which reduce their volatility in the test. Also, some nonphenolic organic
21、s, for example, tar bases, may be more volatile in basic solution. Simple pH adjustment to near neutral or slightly acid will eliminate these interferences.6.4 GhostsElimination of ghosts or memory peaks is requisite before chromatographic analyses are possible. In this test method, ghosts are minim
22、ized or eliminated by injecting 3L of water between all sample injections. This water wash usually clears the injection port, column, and detector of artifacts; however, repeated wash injections may be necessary to clear the system. The electrometer should be set at maximum sensitivity during the wa
23、sh injections to facilitate detection of ghosts.NOTE 2Glass injector inserts are recommended. Inserts are easy to clean or replace and minimize clean-up difficulties.6.5 Other InterferencesIt is beyond the scope of this test method to describe procedures for eliminating all possible interferences wh
24、ich might occur, particularly with highly contaminated industrial waste water.7 In addition, the chro- matographic resolution of this test method is insufficient to differentiate among some isomeric alkyl phenols.7. Apparatus7.1 Chromatographic ColumnsColumns may be pur- chased or prepared by the an
25、alyst. Variations of columnbore) open tubular, analytical capillary, etc., may be used if itis shown to give precision and bias comparable to those obtained in the interlaboratory study of this test method. The three columns cited in this procedure may be modified with the understanding that the elu
26、tion time and sensitivity may be altered.7.1.1 Carbowax 20-M8A 3-mm by 3-m (18-in. by 10-ft) stainless steel column packed with 60/80 mesh Chromosorb W 9 (acid washed and hexamethyldisilazane, (HMDS)-treated) coated with 20 weight % of Carbowax 20M-TPA (terephthalic acid).7.1.2 Free Fatty Acid Phase
27、, 1.5 mA 3-mm by 1.5-m(18-in. by 5-ft) stainless steel column packed with 70/80 mesh Chromosorb W (acid washed) coated with 5 weight % free fatty acid phase.107.1.3 Free Fatty Acid Phase, 3-mA 3-mm by 3-m (18-in. by 10-ft) stainless steel column packed with 60/80 mesh Chromosorb T coated with 10 % f
28、ree fatty acid phase. Chro- mosorb T is a TFE-fluorocarbon 6 product which melts at327C and may begin to fuse above 250C. It is available from suppliers of gas chromatographic materials.7.2 Gas ChromatographA commercial or custom de- signed gas chromatograph with a column oven capable of isothermal
29、temperature control to at least 210 6 0.2C. A unit equipped for temperature programming will facilitate elution of a mixture of phenolics of wide boiling-point range. This test method describes an isothermal analysis using a single column- type gas chromatograph. Temperature programming is an option
30、 of the analyst.7.3 Hydrogen Flame Ionization Detector.7.4 RecorderTo measure chromatographic output at a full-scale range of 1 mV with a response time of 1 s.7.5 Syringe, 10-L.8. Reagents and Materials8.1 Purity of ReagentsReagent grade chemicals shall be used in all tests. Unless otherwise indicat
31、ed, it is intended that all reagents shall conform to the specifications of the Commit- tee on Analytical Reagents of the American Chemical Society, where such specifications are available.11 Other grades may be used, provided it is first ascertained that the reagent is of sufficiently high purity t
32、o permit its use without lessening the accuracy of the determinations.8.2 Unless otherwise indicated, references to water shall be understood to mean Type II reagent water as specified in Specification D 1193.8.3 Carrier Gases Research grade nitrogen or helium of highest purity are used as carrier g
33、ases.loading, length, diameter, support size, treatment, etc., are possible. Any column, for example, packed, wide bore (mega-6 Burttschell, R. H., et al., “Chlorine Derivatives of Phenol Causing Taste andOdor,” Journal American Water Works Association, Vol 51, No. 2, 1959.7 Baker, Robert A., “Trace
34、 Organic Analyses by Aqueous Gas-Liquid Chroma- tography,” Air and Water Pollution Institute Journal, Pergamon Press, Vol 10, 1966, pp. 591602.8 Carbowax is a trademark of Union Carbide.9 Chromosorb is a trademark of Johns, Mansville.10 Available from Varian Aerograph, Walnut Creek, Calif.11 Reagent
35、 Chemicals, American Chemical Society Specifications, American Chemical Society, Washington, DC. For suggestions on the testing of reagents not listed by the American Chemical Society, see Analar Standards for Laboratory Chemicals, BDH Ltd., Poole, Dorset, U.K., and the United States Pharmacopeia an
36、d National Formulary, U.S. Pharmaceutical Convention, Inc. (USPC), Rockville, MD.2D 2580 94 (2001)8.4 Hydrogen (H) For use with the flame ionizationdetector; may be obtained using a hydrogen generator, or froma high-purity tank supply.8.5 Phenolic CompoundsResearch grades of high purity are required
37、. Highest purity compounds may be prepared by redistillation, recrystallization, or by using a preparatory gas chromatographic instrument.NOTE 3WarningPhenolic compounds are skin irritants. Appropri- ate safety measures should be taken to preclude contact with or inhalation of phenolic compounds.The
38、 following phenolic compounds are suggested:8.5.1 o-Chlorophenol,8.5.2 m-Chlorophenol,8.5.3 p-Chlorophenol,8.5.4 o-Cresol,8.5.5 m-Cresol,8.5.6 p-Cresol,8.5.7 2,3-Dichlorophenol,8.5.8 2,4-Dichlorophenol,8.5.9 2,5-Dichlorophenol,8.5.10 2,6-Dichlorophenol,8.5.11 3,4-Dichlorophenol, and8.5.12 Phenol.9.
39、Sampling9.1 Collect the sample in accordance with Practices D 3370.9.2 Because of the possibility of oxidation or bacterial decomposition of phenols in the sample, the lapse of time before analyses should be kept to a minimum. In addition, keep the sample cool and protected from atmospheric oxygen.1
40、0. Preparation of Chromatograph10.1 Install the packed column in the chromatograph using suitable fittings. The use of antigalling thread lubricant is advisable.10.2 Conduct a leak test at approximately 103 kPa (15 psi) above the operating pressure by shutting off the downstream end of the system an
41、d pressurizing from the carrier gas supply. Shut off the cylinder valve and observe the pressure gage. If no drop is noted in 10 to 15 min, the system may be consideredtight. Aqueous soap solutions may be used to locate minorleaks but this should be done with caution. If soap solution enters the sys
42、tem, it may prove difficult to eliminate extraneous peaks or stabilize the system. Do not use the soap method for leak testing near the ionization detector.10.3 Column Conditioning:10.3.1 Condition columns for at least 24 h at temperatures30 to 50C above the expected operating temperature before use
43、. Exercise caution to avoid exceeding the maximum allow- able temperature for both the packing and substrate.10.3.2 Disconnect the column at the end near the detector base to avoid deposition of volatiles on the detector during conditioning.10.3.3 Adjust carrier gas flow to about 20 to 40 mL/min for
44、a 3-mm (18-in.) diameter column.10.3.4 Occasional injection of 3 to 5 L of water during conditioning facilitates elution of impurities.10.3.5 After conditioning, connect the column to the flame ionization detector.10.3.6 Adjust the hydrogen flow to the detector to about 25 mL/min for a 3-mm (18-in.)
45、 diameter column. Adjust the air flow as specified in the instrument being used. Ignite the detector.10.3.7 Adjust the column temperature to the desired level.10.3.8 Adjust the carrier gas flow rate to 20 to 40 mL/min.10.3.9 Observe the recorder base line. When a base line drift is no longer apparen
46、t, the column is ready for use.10.3.10 When the series of analyses are completed and the column is to be moved and stored, it is advisable to seal or cap the ends.11. Operating Conditions for Analysis11.1 Typical operating conditions are summarized in Table1. These operating parameters may be varied but analytical and calibration test variations must be reconc