ASTM D3974-2009 Standard Practices for Extraction of Trace Elements from Sediments《萃取沉积物中痕量元素的标准实施规程》.pdf

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1、Designation: D 3974 09Standard Practices forExtraction of Trace Elements from Sediments1This standard is issued under the fixed designation D 3974; the number immediately following the designation indicates the year oforiginal adoption or, in the case of revision, the year of last revision. A number

2、 in parentheses indicates the year of last reapproval. Asuperscript epsilon () indicates an editorial change since the last revision or reapproval.1. Scope1.1 These practices describe the partial extraction of soils,bottom sediments, suspended sediments, and waterborne ma-terials to determine the ex

3、tractable concentrations of certaintrace elements.1.1.1 Practice A is capable of extracting concentrations ofaluminum, boron, barium, cadmium, calcium, chromium, co-balt, copper, iron, lead, magnesium, manganese, molybdenum,nickel, potassium, sodium, strontium, vanadium, and zinc fromthe preceding m

4、aterials. Other metals may be determined usingthis practice. This extraction is the more vigorous and morecomplicated of the two.1.1.2 Practice B is capable of extracting concentrations ofaluminum, cadmium, chromium, cobalt, copper, iron, lead,manganese, nickel, and zinc from the preceding materials

5、.Other metals may be determined using this practice. Thisextraction is less vigorous and less complicated than PracticeA.1.2 These practices describe three means of preparingsamples prior to digestion:1.2.1 Freeze-drying.1.2.2 Air-drying at room temperature.1.2.3 Accelerated air-drying, for example,

6、 95C.1.3 The detection limit and linear concentration range ofeach procedure for each element is dependent on the atomicabsorption spectrophotometric or other technique employedand may be found in the manual accompanying the instrumentused. Also see various ASTM test methods for determiningspecific

7、metals using atomic absorption spectrophotometrictechniques.1.3.1 The sensitivity of the practice can be adjusted byvarying the sample size (14.2) or the dilution of the sample(14.6), or both.1.4 Extractable trace element analysis provides more infor-mation than total metal analysis for the detectio

8、n of pollutants,since absorption, complexation, and precipitation are the meth-ods by which metals from polluted waters are retained insediments.1.5 The values stated in SI units are to be regarded asstandard. No other units of measurement are included in thisstandard.1.6 This standard does not purp

9、ort 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.2. Referenced Documents2.1 ASTM Standards:2D 8

10、87 Practices for Sampling Water-Formed DepositsD 1129 Terminology Relating to WaterD 1193 Specification for Reagent Water3. Terminology3.1 Refer to Terminology D 1129.4. Summary of Practices4.1 The chemical portion of both practices involves aciddigestion to disassociate the elements complexed in pr

11、ecipi-tated hydroxides, carbonates, sulfides, oxides, and organicmaterials. Surface but not interstitially bound elements will bedesorbed in the case of clay mineral particulates. The silicatelattices of the minerals are not appreciably attacked (1-5).34.2 These practices provide samples suitable fo

12、r analysisusing flame or flameless atomic-absorption spectrophotometry,or other instrumental or colorimetric procedures.5. Significance and Use5.1 Industrialized and urban areas have been found todeposit a number of toxic elements into environments wherethose elements were previously either not pres

13、ent or werefound in trace amounts. Consequently, it is important to be ableto measure the concentration of these pollution-depositedelements to properly study pollution effects.5.2 This procedure is concerned with the pollution-relatedtrace elements that are described in 4.1 rather than those1These

14、practices are under the jurisdiction of ASTM Committee D19 on Waterand are the direct responsibility of Subcommittee D19.07 on Sediments, Geomor-phology, and Open-Channel Flow.Current edition approved May 1, 2009. Published May 2009. Originallyapproved in 1981. Last previous edition approved in 2008

15、 as D 3974 81 (2008).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.3The boldface numbers in parentheses ref

16、er to the references at the end of thesepractices.1Copyright ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959, United States.elements incorporated in the silicate lattices of the mineralsfrom which the sediments were derived. These pollution-related trace elem

17、ents are released into the water and read-sorbed by the sediments with changes in general water quality,pH in particular. These elements are a serious source ofpollution. The elements locked in the silicate lattices are notreadily available in the biosphere (1-8).5.3 When comparing the trace element

18、 concentrations, it isimportant to consider the particle sizes to be analyzed (8, 9).5.3.1 The finer the particle the greater the surface area.Consequently, a potentially greater amount of a given traceelement can be adsorbed on the surface of fine, particulatesamples (4). For particle sizes smaller

19、 than 80 mesh, metalcontent is no longer dependent on surface area. Therefore, ifthis portion of the sediment is used, the analysis with respect tosample type (that is, sand, salt, or clay) is normalized. It hasalso been observed that the greatest contrast between anoma-lous and background samples i

20、s obtained when less than80-mesh portion of the sediment is used (4, 5).5.3.2 After the samples have been dried, care must be takennot to grind the sample in such a way to alter the naturalparticle-size distribution (14.1). Fracturing a particle disruptsthe silicate lattice and makes available those

21、 elements whichotherwise are not easily digested (6). Normally, aggregates ofdried, natural soils, sediments, and many clays dissociate oncethe reagents are added (14.3 and 15.2).6. Interferences6.1 The only interferences are those encountered in the finaldetermination of metals using atomic-absorpt

22、ion spectropho-tometry or other instrumental or colorimetric procedures.7. Apparatus7.1 Digestion BeakersUse only beakers made of borosili-cate glass or TFE-fluorocarbons.7.2 WatchglassesUse ribbed watchglasses to cover thedigestion beakers. These covers should fit loosely to allowevaporation of the

23、 digestion medium.7.3 Filter PaperThe qualitative grade paper employedshould be a fast filtering, hardened, ashless paper retaining bothcoarse and gelatinous precipitates.7.4 Sieves, nylon, 10, 20, and 80-mesh.7.5 Petri Dishes, large.7.6 Freeze-Drier.7.7 Polyethylene or Polypropylene Bottles, wide-m

24、outh,125-mL capacity.7.8 Suction Filtration Apparatus, 0.45-m filter.7.9 Automatic Shaker.7.10 Volumetric Flasks, 50 mL and 100-mL capacity.8. Reagents8.1 Purity of ReagentsReagent grade chemicals shall beused in tests.Acids must have a low-metal content or should bedoubly distilled and checked for

25、purity. Unless otherwiseindicated, all reagents shall conform to the specifications of theCommittee on Analytical Reagents of the American ChemicalSociety.48.2 Purity of WaterUnless otherwise indicated, referenceto water shall be understood to mean reagent water conformingto D 1193. Other reagent wa

26、ter types may be used provided itis first ascertained that the water is of sufficiently high purity topermit its use without adversely affecting the bias and precisionof the test method. Type II water was specified at the time ofround robin testing of this method. The water shall be free ofmetallic

27、contaminants.8.3 Hydrochloric Acid (sp gr 1.19)Concentrated hydro-chloric acid (HCl). The acid must be low in metallic ions.8.4 Nitric Acid (sp gr 1.42)Concentrated nitric acid(HNO3). The acid must be low in metallic ions.8.5 Metal Solutions, StockPrepare metal stock solutions,each containing 1000 m

28、g/L of a metal of interest and eithernegligible or known concentrations of interfering metals.9. Precautions9.1 Digest the samples only in a laboratory ventilation hood.10. Sampling10.1 Collect the sediments using an appropriate technique(see Practice D 887).10.2 Retain and store that portion of sed

29、iment which passesthrough a nylon, 10-mesh sieve, 1-mm particle size (5.3).10.3 Store the sample in plastic bags or plastic bottles thatcan be tightly sealed. Immediately pack and cool the samplesfor shipping.10.4 Store samples at 4C if analysis is to be performedwithin 1 week. Otherwise, store the

30、samples at 20C untilanalyzed.11. Glassware Cleaning11.1 Immerse all glassware and implements in a hot solutionof HCl (1 + 1) for 3 to 5 min.11.2 Second, immerse all glassware and implements inHNO3(1 + 1) for 3 to 5 min.11.3 Rinse all glassware and implements repeatedly withwater following the acid w

31、ashes.12. Sample Preparation12.1 Completely thaw frozen samples before unsealing.12.2 Preparation of the samples for analysis may involvecompositing, splitting, or subsampling (5.3.2).12.3 Drying Samples:12.3.1 Preparation IFreeze-drying is rapid and results inloose samples. See the apparatus instru

32、ction manuals forfurther information.12.3.2 Preparation IIAir-drying at room temperature isaccomplished by spreading the samples out on petri dishes and4Reagent Chemicals, American Chemical Society Specifications, AmericanChemical Society, Washington, DC. For Suggestions on the testing of reagents n

33、otlisted by the American Chemical Society, see Annual Standards for LaboratoryChemicals, BDH Ltd., Poole, Dorset, U.K., and the United States Pharmacopeiaand National Formulary, U.S. Pharmacopeial Convention, Inc. (USPC), Rockville,MD.D3974092drying to constant weight. This procedure requires a long

34、 timeto complete and the sample must be covered to avoid dustcontamination.12.3.3 Preparation IIIAccelerated air-drying the samples,for example, 95C is followed by allowing the samples to coolin a desiccator. Dry to constant weight. Often constant weightmay be achieved by drying overnight, however,

35、constantweight must be obtained for consecutive measurements. Whenanalyzing for more volatile metals, use the temperature recom-mended for that specific method.13. Percent Solids Determination13.1 Using desiccated, tared-beakers, weigh the well-mixedwet samples from 12.2 or 12.3. Record the weights.

36、13.2 Dry overnight or to constant weight at 105C and allowthe samples to cool in a desiccator.13.3 Reweigh the beakers and samples. Determine thepercent solids as described in 16.1.14. Digestion Practice A14.1 Crush the sample to facilitate weighing if a hardaggregate is formed during drying (5.3 an

37、d 12.3).14.2 Weigh4gofdried sample into a 250-mL beaker.Record the sample weight to the nearest 0.1 mg. Include anempty beaker in each analysis set as a reagent/glassware blank.14.3 Add the following to each sample and the blank:14.3.1 Water, 100.0 mL.14.3.2 Concentrated HNO3(sp gr 1.42), 1.0 mL.Afo

38、amingreaction indicates the presence of carbonates; in this case addthe acids slowly.14.3.3 Concentrated HCl (sp gr 1.19), 10 mL.14.4 Cover the beakers with ribbed watchglasses and heaton a hot plate at 95C. To prevent splattering do not allow thesolutions to boil or bump.14.5 Remove each beaker fro

39、m the hot plate when thesolution remaining is 10 to 15 mL. Allow the contents to coolto room temperature.14.6 Filter each solution and quantitatively transfer thesolution to a 50-mL volumetric flask and dilute to volume.15. Digestion Practice B15.1 Weigh 1.0000 g of dried sediment and place in a125-

40、mL polypropylene wide-mouth bottle. For low-level traceelements use up to 10 g of sediment sample. Include an emptybottle as a reagent/glassware blank with each set of samples.15.2 Add 95 mL of water and 5.0 mL of HCl (sp gr 1.19) tothe sample and to the blank bottle and cap tightly. In the caseof a

41、 foaming reaction, which indicates the presence of carbon-ates, add the acidic solution slowly.15.3 Shake at room temperature in a mechanical shaker 16h (overnight).15.4 Filter solution by suction filtration or filter paper.Quantitatively transfer the solution to a 100-mL volumetricflask and dilute

42、to volume.16. Calculation16.1 Use the following equation to determine the percentsolids of the sample (Section 13):B 5MN3 100 (1)where:B = percent solids of the sample,M = dry weight of the sample (13.3), andN = wet weight of the sample (13.1).16.2 Calculate the concentration of the element for each

43、 drysample as follows:C 5Q 2 S!VU(2)where:Q = concentration of the element in the digested solutiong/mL,S = concentration of the trace element found in the reagent/glassware blank (14.2 and 15.1), g/mL,V = volume of extract from 14.6 and 15.4,U = weight of the sample corrected to a dried sample at10

44、5C, g, andC = trace element per gram of dry sample, g.16.3 Use the following equation to determine the concen-tration of the metal in the wet sample (13.1):A 5 C 3B100(3)where:A = metal per gram of wet sample, g,B = percent solids of the sample, andC = trace element per gram of dry sample (16.2), g.

45、17. Keywords17.1 extraction; sediments; toxic; trace elementsD3974093REFERENCES(1) Inland Waters Directorate, Analytical Methods ManualEnvironment, Canada Inland Waters Directorate, Water QualityBranch, Ottawa, Canada.(2) Rubin,A. J., Aqueous Environmental Chemistry of Metals,AnnArborScience Publish

46、ers, Inc., Ann Arbor, Mich., 1974.(3) Agemian, H. and Chau,A. S. Y., “Evaluation of Extraction Techniquesfor the Determination of Metals in Aquatic Sediments,” Analyst,Vol101, 1976, pp. 761767.(4) Agemian, H., and Chau, A. S. Y., “A Study of Different AnalyticalExtraction Methods for Nondetrital Hea

47、vy Metals in Aquatic Sedi-ments,” Archives of Environmental Contamination and Toxicology,Vol6, 1977, pp. 6982.(5) Bradshaw, P. M. D., Thomson, I., Smee, B. W. and Larson, J. O., “TheApplication of Different Analytical Extractions and Soil Profile Sam-pling in Exploration Geochemistry,” Journal of Ge

48、ochemical Explo-ration, Vol 3, 1974, pp. 209225.(6) Malo, B. A., “Partial Extraction of Metals from Aquatic Sediments,”Environmental Science and Technology, Vol II, No. 3, 1977, pp.277282.(7) Burrell, D. C., Atomic Spectrometric Analysis of Heavy MetalPollutants in Water, Ann Arbor Science Publisher

49、s Inc., Ann Arbor,Mich., 1974.(8) Oliver, B. G., “Heavy Metal Levels of Ottawa and Rideau RiverSediments,” Environmental Science and Technology, Vol 7, 1973, pp.135137.(9) Hawkes, H. E., and Webb, J. S., Geochemistry in Mineral Explora-tion, Harper and Row, New York, N.Y., 1962.ASTM International takes no position respecting the validity of any patent rights asserted in connection with any item mentionedin this standard. Users of this standard are expressly advised that determination of the validity of any such patent rights, and the riskof infringem