ASTM D5513-1999(2009) Standard Practice for Microwave Digestion of Industrial Furnace Feedstreams and Waste for Trace Element Analysis《痕量素分析用工业炉供入液流的微波溶解标准实施规范》.pdf
《ASTM D5513-1999(2009) Standard Practice for Microwave Digestion of Industrial Furnace Feedstreams and Waste for Trace Element Analysis《痕量素分析用工业炉供入液流的微波溶解标准实施规范》.pdf》由会员分享,可在线阅读,更多相关《ASTM D5513-1999(2009) Standard Practice for Microwave Digestion of Industrial Furnace Feedstreams and Waste for Trace Element Analysis《痕量素分析用工业炉供入液流的微波溶解标准实施规范》.pdf(6页珍藏版)》请在麦多课文档分享上搜索。
1、Designation: D 5513 99 (Reapproved 2009)Standard Practice forMicrowave Digestion of Industrial Furnace Feedstreams andWaste for Trace Element Analysis1This standard is issued under the fixed designation D 5513; the number immediately following the designation indicates the year oforiginal adoption o
2、r, 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 practice describes the multi-stage microwave di-gestion of typical indust
3、rial furnace feedstream materials usingnitric, hydrofluoric, hydrochloric, and boric acids for thesubsequent determination of trace metals.1.2 This practice has been used successfully on samples ofcoal, coke, cement raw feed materials, and waste-derived fuelscomposed primarily of waste paint-related
4、 material in prepa-ration for measuring the following trace elements: Ag, As, Ba,Be, Cd, Cr, Hg, Pb, Sb, and Tl. This practice may be applicableto elements not previously listed.1.3 This practice is also effective for other waste materials(for example, flyash, foundry sand, alum process residue,ceme
5、nt kiln dust, etc.).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 standa
6、rd to establish appro-priate safety and health practices and determine the applica-bility of regulatory limitations prior to use. Specific hazardstatements are given in Section 7.2. Referenced Documents2.1 ASTM Standards:2D 1193 Specification for Reagent Water2.2 Other Document:40 CFR 266 , Subpart
7、H, Hazardous Waste Burned inBoilers and Industrial Furnaces, Latest Revision33. Summary of Practice3.1 A weighed portion of the feedstream material is com-bined with concentrated nitric acid in apolytetrafluoroethylene-lined digestion vessel, and heated in amicrowave digestion unit. Following a prog
8、rammed heatingcycle, the vessel is vented and specified quantities of hydrof-luoric and hydrochloric acids are added, and the mixtureundergoes further microwave heating. Following this heatingcycle, the vessel is vented and a specified quantity of boric acidsolution is added, and the mixture undergo
9、es a final microwaveheating. Following this final heating cycle, the vessel is vented,the contents are quantitatively transferred to a volumetric flaskand brought to volume. Typically, the only undissolved mate-rial is particulate carbon. If particulate matter is observed,filtration or centrifugatio
10、n may be needed. The digested sampleis ready for analysis.4. Significance and Use4.1 The U.S. Environmental Protection Agency Regula-tions, 40 CFR 266, require that boilers, cement kilns, and otherindustrial furnaces utilizing waste-derived fuel adhere to spe-cific guidelines in assessing potential
11、metals emissions. Acommon approach for estimating potential emissions is per-forming total metals analysis on all feedstream materials. Thispractice describes a multi-stage microwave-assisted digestionprocedure that solubilizes trace elements for spectroscopicanalyses.5. Apparatus5.1 Microwave Diges
12、tion UnitEquipped with an auto-matic turntable, pressure and/or temperature controller, andclosed perfluoroalkoxy (PFA)-lined digestion vessels equippedwith pressure relief/rupture membrane fittings or equivalentpressure relief device. The unit should comply with applicablefederal or state standards
13、, or both, for microwave leakage. Theuser must follow specific manufacturers instructions for sys-tem installation.NOTE 1The digestion unit used in developing this practice wasequipped with a pressure controller, automatic turntable, exhaust fan, andprogramming capacity. The unit delivers 1000 W of
14、power at 100 %output. The lined digestion vessels consist of a high-strength polymeric1This practice is under the jurisdiction of ASTM Committee D34 on WasteManagement and is the direct responsibility of Subcommittee D34.01.06 onAnalytical Methods.Current edition approved July 1, 2009. Published Aug
15、ust 2009. Originallyapproved in 1994. Last previous edition approved in 2004 as D 5513 99 (2004).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 Docum
16、ent Summary page onthe ASTM website.3Available from Standardization Documents Order Desk, Bldg. 4 Section D, 700Robbins Ave., Philadelphia, PA 19111-5094, Attn: NPODS.1Copyright ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959, United States.vessel body and ca
17、p, inner PFA liner and rupture membrane housing, andPFA vent stem. These vessels have a maximum operating pressure of 200psig. There are a number of suitable lab grade microwave systemsavailable to the user that meet these minimum specifications. The usermust follow specific manufacturers instructio
18、ns for using digestionvessels.5.2 Analytical BalanceCapable of weighing to 0.001 g.5.3 LabwareHigh-density volumetric polyethylene orpolypropylene flasks/sample containers are recommended forthis practice. The user should be mindful of the qualitylimitations associated with volumetric non-glass labw
19、are.6. Reagents and Materials6.1 Purity of ReagentsReagent grade chemicals shall beused in all tests. Unless otherwise indicated, it is intended thatall reagents conform to the specifications of the Committee onAnalytical Reagents of the American Chemical Society wheresuch specifications are availab
20、le.4Other grades may be used,provided it is first ascertained that the reagent is of sufficientlyhigh purity to permit its use without lessening the accuracy ofthe determination.6.2 Purity of WaterUnless otherwise indicated, referencesto water shall be understood to mean meeting the numericalrequire
21、ments of Type II water as defined by SpecificationsD 1193.6.3 Boric Acid Solution (20 g/L)Dissolve 20 g of boricacid (H3BO3) in water and dilute to 1 L. It may be necessaryto place solution on a combination hot plate/magnetic stirrerand with the aid of a stir bar, allow the solution to mix undergent
22、le heat until boric acid is fully in solution.6.4 Hydrochloric Acid, 37 %, (sp. gr. 1.200), HCl.6.5 Hydrofluoric Acid, 48 %, (sp. gr. 1.150), HF.6.6 Nitric Acid, 70 %, (sp. gr. 1.400), HNO3.7. Hazards57.1 It is recommended that all operations involving concen-trated acids be performed in a laborator
23、y fume hood.7.2 Hydrochloric acid is a highly corrosive chemical that isreactive with metals and most alkaline chemicals. Imperviousgloves and chemical goggles are required for handling. Seematerial safety data sheet (MSDS) for additional information.7.3 Hydrofluoric acid is a highly corrosive chemi
24、cal that isreactive with metals and water or steam. Additionally, HFspecifically attacks silicate glass making certain fume hoodenclosures susceptible to damage. Impervious gloves andchemical goggles are required for handling. See MSDS foradditional information.7.4 Nitric acid is a highly corrosive
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