ASTM D5198-2009 Standard Practice for Nitric Acid Digestion of Solid Waste《固体废弃物的硝酸处理的标准方法》.pdf
《ASTM D5198-2009 Standard Practice for Nitric Acid Digestion of Solid Waste《固体废弃物的硝酸处理的标准方法》.pdf》由会员分享,可在线阅读,更多相关《ASTM D5198-2009 Standard Practice for Nitric Acid Digestion of Solid Waste《固体废弃物的硝酸处理的标准方法》.pdf(4页珍藏版)》请在麦多课文档分享上搜索。
1、Designation: D 5198 09Standard Practice forNitric Acid Digestion of Solid Waste1This standard is issued under the fixed designation D 5198; the number immediately following the designation indicates the year oforiginal adoption or, in the case of revision, the year of last revision. A number in pare
2、ntheses 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 digestion of solid wasteusing nitric acid for the subsequent determination of inorganicconstituents by plasma emission sp
3、ectroscopy or atomic ab-sorption spectroscopy.1.2 The following elements may be solubilized by thispractice:aluminum manganeseberyllium mercurycadmium nickelchromium phosphoruscopper vanadiumiron zinclead1.3 This practice is to be used when the concentrations oftotal recoverable elements are to be d
4、etermined from a wastesample. Total recoverable elements may or may not be equiva-lent to total elements, depending on the element sought and thesample matrix. Recovery from refractory sample matrices,such as soils, is usually significantly less than total concentra-tions of the elements present.NOT
5、E 1This practice has been used successfully for oily sludges anda municipal digested sludge standard Environmental Protection Agency(EPA) Sample No. 397. The practice may be applicable to some elementsnot listed above, such as arsenic, barium, selenium, cobalt, magnesium,and calcium. Refractory elem
6、ents such as silicon, silver, and titanium, aswell as organo-mercury are not solubilized by this practice.1.4 This practice has been divided into two methods, A andB, to account for the advent of digestion blocks. Method Autilizes an electric hot plate; Method B utilizes an electricdigestion block.1
7、.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 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
8、-priate safety and health practices and determine the applica-bility of regulatory limitations prior to use. For specific hazardstatements, see Section 7.2. Referenced Documents2.1 ASTM Standards:2D 1193 Specification for Reagent Water3. Summary of Practice3.1 A weighed portion of the waste sample i
9、s mixed with1 + 1 nitric acid (HNO3) in an Erlenmeyer flask. The flask isheated for2hat90to95C to dissolve the elements of interest.After cooling, the contents of the flask are diluted with reagentwater and filtered, and the filtrate is made up to appropriatevolume for subsequent analysis.4. Signifi
10、cance and Use4.1 A knowledge of the inorganic composition of a waste isoften required for the selection of appropriate waste disposalpractices. Solid waste may exist in a variety of forms andcontain a range of organic and inorganic constituents. Thispractice describes a digestion procedure which dis
11、solves manyof the toxic inorganic constituents and produces a solutionsuitable for determination by such techniques as atomic ab-sorption spectroscopy, atomic emission spectroscopy, and soforth. The relatively large sample size aids representativesampling of heterogenous wastes. The relatively small
12、 dilutionfactor allows lower detection limits than most other sampledigestion methods. Volatile metals, such as lead and mercury,are not lost during this digestion procedure, however organo-lead and organo-mercury may not be completely digested.Hydride-forming elements, such as arsenic and selenium,
13、 maybe partially lost. Samples with total metal contents greater than5 % may give low results. The analyst is responsible fordetermining whether this practice is applicable to the solidwaste being tested.1This practice is under the jurisdiction of ASTM Committee D34 on WasteManagement and is the dir
14、ect responsibility of Subcommittee D34.01.06 onAnalytical Methods.Current edition approved Feb. 1, 2009. Published March 2009. Originallyapproved in 1992. Last previous edition approved in 2003 as D 5198 92 (2003).2For referenced ASTM standards, visit the ASTM website, www.astm.org, orcontact ASTM C
15、ustomer Service at serviceastm.org. For Annual Book of ASTMStandards volume information, refer to the standards Document Summary page onthe ASTM website.1Copyright ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959, United States.METHOD A HOT PLATE5. Apparatus5.
16、1 Analytical Balance, capable of weighing to 0.01 g.5.2 Erlenmeyer Flasks, 125 mL.5.3 Graduated Cylinder,50mL.5.4 Electric Hot Plate, adjustable, capable of maintaining atemperature of 90 to 95C.5.5 Watch Glasses.5.6 Thermometer.5.7 Funnels, glass or plastic.5.8 Volumetric Flasks, glass-stoppered, 2
17、00 mL.5.9 Filter Paper, quantitative, medium flow rate, WhatmanNo. 40 or equivalent.5.10 Fume Hood.6. Reagents6.1 Purity of ReagentsReagent grade chemicals shall beused in all tests. Unless otherwise indicated, it is intended thatall reagents shall conform to the specifications of the Commit-tee on
18、Analytical Reagents of the American Chemical Society,where such specifications are available.3Other grades may beused, provided it is first ascertained that the reagent is ofsufficiently high purity to permit its use without lessening theaccuracy of the determination.6.2 Purity of WaterUnless otherw
19、ise indicated, referenceto water shall be understood to mean reagent water as definedby Type II of Specification D 1193.6.3 Nitric Acid, concentrated, reagent grade.6.4 Nitric Acid (1+1)Add slowly, with stirring, 200 mL ofconcentrated nitric acid (HNO3, sp gr 1.42) to 200 mL water.Cool the mixture a
20、nd store in a clean pint glass bottle.7. Hazards7.1 Add the nitric acid mixture slowly, with swirling, to thesample. Samples containing carbonates may foam excessivelyduring acid addition and result in loss of sample. Nitric acidmay react violently with some samples containing organicmaterial.7.2 Ad
21、dition of acid and sample digestion must be con-ducted in a hood with adequate ventilation and shielding toavoid contact with nitrogen oxides, acid fumes, or toxic gases.8. Procedure8.1Weigh5gofathoroughly mixed waste sample to thenearest 0.01 g into a tared Erlenmeyer flask.8.2 With a graduated cyl
- 1.请仔细阅读文档,确保文档完整性,对于不预览、不比对内容而直接下载带来的问题本站不予受理。
- 2.下载的文档,不会出现我们的网址水印。
- 3、该文档所得收入(下载+内容+预览)归上传者、原创作者;如果您是本文档原作者,请点此认领!既往收益都归您。
下载文档到电脑,查找使用更方便
10000 积分 0人已下载
下载 | 加入VIP,交流精品资源 |
- 配套讲稿:
如PPT文件的首页显示word图标,表示该PPT已包含配套word讲稿。双击word图标可打开word文档。
- 特殊限制:
部分文档作品中含有的国旗、国徽等图片,仅作为作品整体效果示例展示,禁止商用。设计者仅对作品中独创性部分享有著作权。
- 关 键 词:
- ASTMD51982009STANDARDPRACTICEFORNITRICACIDDIGESTIONOFSOLIDWASTE 固体 废弃物 硝酸 处理 标准 方法 PDF

链接地址:http://www.mydoc123.com/p-519140.html