ASTM D5085-2002(2008) Standard Test Method for Determination of Chloride Nitrate and Sulfate in Atmospheric Wet Deposition by Chemically Suppressed Ion Chromatography《用化学抑制型离子色谱法测定.pdf

1、Designation: D 5085 02 (Reapproved 2008)Standard Test Method forDetermination of Chloride, Nitrate, and Sulfate inAtmospheric Wet Deposition by Chemically Suppressed IonChromatography1This standard is issued under the fixed designation D 5085; the number immediately following the designation indicat

2、es the year oforiginal 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 is applicable to the determi

3、nation ofchloride, nitrate, and sulfate in atmospheric wet deposition(rain, snow, sleet, and hail) by chemically suppressed ionchromatography (1)2. For additional applications refer to TestMethod D 4327.1.2 The concentration ranges for this test method are listedbelow. The range tested was confirmed

4、 using the interlabora-tory collaborative test (see Table 1 for statistical summary ofthe collaborative test).MDL (mg/L) (2)Range ofMethod(mg/L)RangeTested(mg/L)Chloride 0.03 0.092.0 0.151.36Nitrate 0.03 0.095.0 0.154.92Sulfate 0.03 0.098.0 0.156.521.3 The method detection limit (MDL) is based on si

5、ngleoperator precision (2) and may be higher or lower for otheroperators and laboratories. The precision and bias data pre-sented are insufficient to justify use at this low level, however,many workers have found that this test method is reliable atlower levels than those that were tested.1.4 This s

6、tandard 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 practices and determine the applica-bility of regulatory limitations prior to use. Specific precau-tionary

7、statements are given in Section 9.2. Referenced Documents2.1 ASTM Standards:3D 883 Terminology Relating to PlasticsD 1129 Terminology Relating to WaterD 1193 Specification for Reagent WaterD 1356 Terminology Relating to Sampling and Analysis ofAtmospheresD 2777 Practice for Determination of Precisio

8、n and Bias ofApplicable Test Methods of Committee D19 on WaterD 3670 Guide for Determination of Precision and Bias ofMethods of Committee D22D 4210 Practice for Intralaboratory Quality Control Proce-dures and a Discussion on Reporting Low-Level Data4D 4327 Test Method for Anions in Water by Chemical

9、lySuppressed Ion ChromatographyD 5012 Guide for Preparation of Materials Used for theCollection and Preservation of Atmospheric Wet Deposi-tionIEEE/ASTM SI-10 Standard for Use of the InternationalSystem of Units (SI): The Modern Metric SystemE 694 Specification for Laboratory Glass Volumetric Appa-r

10、atus3. Terminology3.1 DefinitionsFor definitions of terms used in this testmethod, refer toTerminologies D 883, D 1129, and D 1356 andTest Method D 4327 and Practice E 380.4. Summary of Test Method4.1 Ion chromatography combines conductometric detectionwith the separation capabilities of ion exchang

11、e resins. (1) Afiltered aliquot of the sample, ranging in size from 50 to 250L, is pumped through an ion exchange column where theanions of interest are separated. Each ions affinity for theexchange sites, known as its selectivity quotient, is largelydetermined by its radius and valence. Because dif

12、ferent ionshave different selectivity quotients, the sample ions elute fromthe column as discrete bands. Each ion is identified by itsretention time within the exchange column. The sample ionsare selectively eluted off the separator column and onto asuppressor column, where the conductivity of the e

13、luent ions isreduced and the sample ions are converted to their correspond-ing strong acids. The separated anions are detected by a1This test method is under the jurisdiction of ASTM Committee D22 on AirQuality and is the direct responsibility of Subcommittee D22.03 on AmbientAtmospheres and Source

14、Emissions.Current edition approved Aug. 1, 2008. Published September 2008. Originallyapproved in 1990. Last previous edition approved in 2002 as D 5085 02.2The boldface numbers in parentheses refer to references at the end of this testmethod.3For referenced ASTM standards, visit the ASTM website, ww

15、w.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.4Withdrawn.1Copyright ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959, United

16、States.conductance cell. The chromatograms produced are displayedon a strip chart recorder or other data acquisition device.Measurement of peak height or area is used for quantitation.The ion chromatograph is calibrated with standard solutionscontaining known concentrations of the anion(s) of intere

17、st.Calibration curves are constructed from which the concentra-tion of each analyte in the unknown sample is determined. Foradditional information on ion chromatography refer to TestMethod D 4327.5. Significance and Use5.1 This test method is useful for the determination of theanions: chloride, nitr

18、ate, and sulfate in atmospheric wet depo-sition.5.2 Fig. X1.1 in the appendix represents cumulative fre-quency percentile concentration plots of chloride, nitrate, andsulfate obtained from analyses of over 5000 wet depositionsamples. These data may be used as an aid in the selection ofappropriate ca

19、libration solutions. (3)6. Interferences6.1 Unresolved peaks will result when the concentration ofone of the sample components is 10 to 20 times higher thananother component that appears in the chromatogram as anadjacent peak. Decreasing the eluent concentration or flow rate,increasing column length

20、, or decreasing sample size maycorrect this problem.6.2 Interferences may be caused by ions with retentiontimes that are similar to the anion of interest.The retention timeof sulfite may be similar to nitrate or sulfate. Other possibleinterfering ions are bromide and phosphate. Before analyzingpreci

21、pitation samples, measure the retention times of thesepossible interfering ions. Interference is common in some typesof wet deposition samples. If this interference is anticipated,decreasing the eluent concentration or flow rate, increasingcolumn length, or decreasing sample size will result in im-p

22、roved peak resolution.6.3 Water from the sample injection will cause a negativepeak (water dip) in the chromatogram when it elutes becauseits conductance is less than that of the suppressed eluent.Chloride may elute near the water dip and must be sufficientlyresolved from the dip to be accurately qu

23、antified. This can beachieved by changing the eluent concentration or decreasingthe flow rate. The potential interference of the negative peakcan be eliminated by adding an equivalent of 100 l of aprepared eluent concentrate (solution that is 100 times moreconcentrated than the eluent used for analy

24、sis) per 10.0 mL ofsample. Identical eluent additions must also be included incalibration and quality control solutions.6.4 Decreases in retention times and resolution are symp-toms of column deterioration which may be caused by thebuildup of contaminants on the exchange resin. Refer to themanufactu

25、rers guidelines for instructions on cleaning thecolumn resin and column filter beds. Excising the contami-nated portion of the column and changing the filters may alsoimprove performance. If the procedure in this section do notrestore the retention times, replace the column.6.5 Contaminated valves a

26、nd sample lines may also reducesystem performance causing decreased retention times andresolutions. Refer to the manufacturers guidelines for instruc-tions on cleaning the valves and replacing the lines.NOTE 1Review operational details and refer to the trouble shootingguide in the Operators Manual t

27、o determine the cause of decreasedretention times and resolution prior to extensive cleaning or changing ofall valves, columns, filters, sample lines, or all of the above.6.6 The presence of air bubbles in the columns, tubing, orconductivity detector cell may cause baseline fluctuations andpeak vari

28、ability. Prevent introducing air into the system wheninjecting samples and standards. The use of degassed water foreluents and regenerants may help to minimize the introductionof air (See 8.2).6.7 For more information on interferences refer to TestMethod D 4327.7. Apparatus7.1 Ion ChromatographSelec

29、t an instrument equippedwith an injection valve, a sample loop, separator column(s),TABLE 1 Precision and Bias for Chloride, Nitrate, and Sulfate Determined from the Synthetic Atmospheric Wet Deposition SamplesUsed in the Interlaboratory Comparison StudyAnalyteAmountAdded,mg/LMeanRecovery,mg/LnAPrec

30、ision mg/LBias,mg/LSignificantBiasBStC95 %ReproducibilityLimitSoD95 %RepeatabilityLimitChloride 0.15 0.157 36 0.0535 0.150 0.0116 0.0325 0.007 no0.30 0.293 35 0.0554 0.155 0.0291 0.0815 0.007 no0.68 0.652 36 0.0549 0.154 0.0237 0.0664 0.028 biased low1.36 1.368 36 0.1 0.28 0.0431 0.121 0.008 noNitra

31、te 0.15 0.138 24 0.0362 0.101 0.0289 0.0809 0.012 no1.08 1.077 24 0.0495 0.139 0.0421 0.118 0.003 no2.44 2.486 22 0.0197 0.0552 0.0183 0.0512 0.046 biased high4.92 4.999 24 0.126 0.353 0.075 0.21 0.079 biased highSulfate 0.15 0.172 36 0.055 0.154 0.0304 0.085 0.022 no1.43 1.442 35 0.0683 0.191 0.036

32、9 0.103 0.012 no3.23 3.358 36 0.13 0.364 0.046 0.129 0.128 biased high6.52 6.775 36 0.37 1.04 0.109 0.305 0.255 biased highANumber of samples included in final statistical analysis after removal of outlier data.B95 % confidence level.CBetween laboratory precision, reproducibility.DWithin laboratory

33、precision (pooled single operator precision), repeatability.D 5085 02 (2008)2suppressor column(s), pump(s), and detector meeting require-ments specified. Peripheral equipment includes compressedgas, a suitable data acquisition device such as a strip chartrecorder, an integrator, or computer, and may

34、 include anautomatic sampler.7.1.1 TubingTubing that comes in contact with samplesand standards must be manufactured from inert material suchas polyethylene plastics or TFE-fluorocarbon.7.1.2 Anion Guard ColumnAlso called a precolumn, it isplaced before the separator column. The guard column con-tai

35、ns the same resin as the separator column and is used toprotect it from being fouled by particulates or organic constitu-ents. Using an anion guard column will prolong the life of theseparator column.57.1.3 Anion Separator ColumnThis is a column packedwith a pellicular low-capacity anion exchange re

36、sin con-structed of polystyrene-divinylbenzene beads coated with quar-tenary ammonium active sites.67.1.4 Anion Suppressor ColumnPlace following the sepa-rator column. This may be in the form of an anion micro-membrane suppressor or an anion self-regenerating suppressor.The first type of suppressor

37、utilizes a semipermeable mem-brane containing anion exchange sites to suppress eluentconductance.7The second type of suppressor uses the neutral-ized cell effluent as the source of water for the regenerantchamber water.7.1.5 Compressed Gas (Nitrogen or Air)Use ultra-highpurity 99.999 % (v/v) compres

38、sed gas that is oil, particulate,and water free to actuate the valves and to pressurize theregenerant flow system as needed.7.1.6 DetectorSelect a flow-through, temperature-compensated, electrical conductivity cell with a volume ofapproximately 6 L coupled with a meter capable of readingfrom 0 to 10

39、00 s/cm on an analog or digital scale.7.1.7 PumpUse a pump capable both of delivering aconstant flow rate of approximately 1 to 5 mL/min and oftolerating a pressure 1379 to 13 790 kPa. A constant pressure,constant flow pump is recommended for enhanced baselinestability.All interior pump surfaces tha

40、t will be in contact withsamples and standards must be manufactured from inert,non-metallic materials.7.1.8 Data Acquisition System:7.1.8.1 RecorderThis must be compatible with the maxi-mum conductance detector output with a full-scale responsetime of 0.5 s or less. A two pen recorder with variable

41、voltageinput settings is recommended.7.1.8.2 IntegratorIf an integrating system is employed,the data acquisition unit must be compatible with the maximumdetector output to quantitate the peak height or area. If anintegrator is used, the maximum peak height or area measure-ment must be within the lin

42、ear range of the integrator.7.1.9 Sample LoopSelect a sample loop with a capacity of50 to 250 L.7.1.10 Sample Introduction SystemSelect one of the fol-lowing:7.1.10.1 SyringeA syringe equipped with a male fittingwith a minimum capacity of 2 mL.7.1.10.2 AutosamplerAn autosampling system capable ofpre

43、cise delivery, equipped with a dust cover to reduce airbornecontamination.7.2 Eluent and Regenerant ReservoirsSelect containerswitha4to20Lcapacity that are designed to minimizeintroduction of air into the flow system for storing eluents andregenerants.7.3 GlasswareGlassware, including volumetric pip

44、ettesand flasks, must be dedicated for use on atmospheric wetdeposition samples only. Volumetric pipettes should be used tomeasure the stock solutions.The pipettes may be either fixed orvariable volume and either glass or plastic. Volumetric glass-ware must meet the requirement for Class A items giv

45、en inSpecification E 694. Pipettes with disposable tips are preferredin order to reduce contamination. The pipettes must have aprecision and a bias of 1 % or better. Precision and bias aredetermined by weighing a minimum of ten separately pipettedaliquots.7.4 Laboratory FacilitiesLaboratories used f

46、or the analy-sis of wet deposition samples must be free from sources ofcontamination. The use of laminar flow clean air work stationsis recommended for sample processing and preparation toavoid the introduction of airborne contaminants. Samples mustalways be capped or covered prior to analysis. A po

47、sitivepressure environment within the laboratory is also recom-mended to minimize the introduction of external sources ofcontaminant gases and particulates. Room temperature fluctua-tions must be controlled to within 6C to prevent baseline driftand changes in detector response. Windows within the la

48、bora-tory must be kept closed at all times and sealed if air leaks areapparent. The use of disposable tacky floor mats at the entranceto the laboratory is helpful in reducing the particulate loadingwithin the room.8. Reagents and Materials8.1 Purity of ReagentsUse reagent grade or higher gradechemic

49、als for all solutions. All reagents shall conform to thespecifications of the Committee on Analytical Reagents of theAmerican Chemical Society (ACS) where such specificationsare available.88.2 Purity of WaterUse water conforming to SpecificationD 1193, Type II. Point of use 0.2 m filters are recommendedfor all faucets supplying water to prevent the introduction ofbacteria ion exchange resins, or both, into reagents, standard5Dionex P/N 030986 (AG3) available from Dionex Corp., 1228 Titan Way, POBox 3603, Sunnyvale, CA, 94088-3603, or equival