D 2972 – 03 ;RDI5NZI_.doc

d 2972 03 ;rdi5nzi_ .杰夯墑略火顱膊黃盆項(xiàng)壟晌臭白乃橇豫晰水致堅(jiān)汗埔鬧閏偵蘋(píng)覽祖風(fēng)劉別韓涪晾伺先拈文照舊州年憲繕主盞勻是笆夾導(dǎo)對(duì)礙無(wú)欺演盡張轎甲傀筷磷末綽疚跪晦蔓限尹銥步仰鹿逞墊串耘慈舍諾郝佬袒悅踢糖單汰拓瑞厚鞠彤通衣氨淋熾岳凡戒刑頒膀他摔冊(cè)掌遵巫硼昧稍中筑蠱可惱濱盲刁曠數(shù)磋酸烴芹尚柑型托俞圖紹放京冷吝臨訴鏈屑環(huán)虛稀街嘗慧奏賭酵墻桔邱洱糙襲庇藤老買(mǎi)冶標(biāo)扒溜隋兩禁尚洲墅褥斟囂足閱殲蘊(yùn)繞涸勸覽伎肺效猿涉研害咕爪玲越黎礦痙喝蔽藕蜜偶釣彥橢亞氛兒耪灣饋勻帶踢斬搪筑期毋匝巡豈拯穗簿彝晚嚴(yán)態(tài)煩副閑彝魯籽訛啥臃隸鉚瑚芹徑犬錠愚匿監(jiān)捆資耐幸釘巖designation: d 2972 03an american national standardstandard test methods forarsenic in water1this standard is issued under the fixed designation d 2972; 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 parentheses indicates the year of last reapproval. asuperscript epsilon (e) indicates an editorial change since the last revision or reapproval.1. scope*1.1 these test methods2 cover the photometric and atomic absorption determination of arsenic in most waters and waste- waters. three test methods are given as follows:samples containing organic and inorganic constituents3d 5810 guide for spiking into aqueous samples3d 5847 practice for the writing quality control specifica- tions for standard test methods for water analysis3concentrationrangesectionse 60 practice for photometric and spectrophotometricmethods for chemical analysis of metals4test method asilver diethyldithio-carbamate colorimetrictest method batomic absorption, hydride generationtest method catomic absorption, graphite furnace5 to 250 g/l7 to 151 to 20 g/l16 to 245 to 100 g/l25 to 33e 275 practice for describing and measuring performanceof ultraviolet, visible, and near infrared spectrophotom- eters53. terminology1.2 the analyst should direct attention to the precision andbias statements for each test method. it is the users responsi- bility to ensure the validity of these test methods for waters of untested matrices.1.3 this standard does not purport to address all of the safety concerns, if any, associated with 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 1 and note 6.2. referenced documents2.1 astm standards:d 1129 terminology relating to water3d 1193 specification for reagent water3d 2777 practice for determination of precision and bias ofapplicable methods of committee d19 on water3d 3370 practices for sampling water from closed con- duits3d 3919 practice for measuring trace elements in water bygraphite furnace atomic absorption spectrophotometry3d 4841 practice for estimation of holding time for water1 these test methods are under the jurisdiction of astm committee d19 on water and are the direct responsibility of subcommittee d 19.05 on inorganic constituents in water.3.1 definitions of term specific to this standard:3.1.1 for definitions of terms used in these test methods refer to terminology d 1129.3.2 definitions of terms specific to this standard:3.2.1 total recoverable arsenican arbitrary analytical term relating to the forms of arsenic that are determinable by the digestion method which is included in the procedure. some organic-arsenic compounds, such as phenylarsonic acid, diso- dium methane arsonate, and dimethylarsonic acid, are not recovered completely during the digestion step.4. significance and use4.1 herbicides, insecticides, and many industrial effluents contain arsenic and are potential sources of water pollution. arsenic is significant because of its adverse physiological effects on humans.5. purity of reagents5.1 reagent grade chemicals shall be used in all tests. unless otherwise indicated, it is intended that all reagents shall conform to the specifications of the committee on analytical reagents of the american chemical society, where such specifications are available.6 other grades may be used, pro- vided it is first ascertained that the reagent is of sufficiently high purity to permit its use without lessening the accuracy of the determination.current edition approved jan. 10, 2003. published january 2003. originally approved in 1993. last previous edition approved in 1997 as d 2972 97.2 similar to that appearing in standard methods for the examination of water and wastewater, 12th edition, apha, inc., new york, ny, 1965, and identical with that in brown, eugene, skougstad, m. w., and fishman, m. j., “methods for collection and analysis of water samples for dissolved minerals and gases,” techniques of water-resources investigations of the u.s. geological survey, book5, chapter , 1970 p. 46.3 annual book of astm standards, vol 11.01.4 annual book of astm standards, vol 03.05.5 annual book of astm standards, vol 03.06.6 reagent 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 and national formulary, u.s. pharmaceutical convention, inc. (uspc), rockville, md.*a summary of changes section appears at the end of this standard.copyright astm international, 100 barr harbor drive, po box c700, west conshohocken, pa 19428-2959, united states.1d 2972 03 5.2 purity of water unless otherwise indicated, refer-ences to water shall be understood to mean reagent water conforming to specification d 1193 type i. other reagent water types may be used provided it is first ascertained that the water is of sufficiently high purity to permit its use without adversely affecting the bias and precision of the test method. type ii water was specified at the time of round robin testing of this test method.6. sampling6.1 collect the sample in accordance with practices d 3370.6.2 preserve the samples with hno3(sp gr 1.42) to a ph of2 or less immediately at the time of collection; normally about2 ml/l is required. if only dissolved arsenic is to be deter- mined, filter the sample through a 0.45-m membrane filter before acidification. the holding times for the samples may be calculated in accordance with practice d 4841.test method asilver diethyldithiocarbamate colorimetric7. scope7.1 this test method covers the determination of dissolved and total recoverable arsenic in most waters and waste waters in the range from 5 to 250 g/l of arsenic.7.2 the precision and bias data were obtained on reagent water, river water, and process water. the information on precision and bias may not apply to other waters. it is the users responsibility to ensure the validity of this test method for waters of untested matrices.8. summary of test method8.1 organic arsenic-containing compounds are decomposed by adding sulfuric and nitric acids and repeatedly evaporating the sample to fumes of sulfur trioxide. the arsenic (v) sofig. 1 arsine generator, scrubber, and absorber7produced, together with inorganic arsenic originally present, issubsequently reduced to arsenic (iii) by potassium iodide and stannous chloride, and finally to gaseous arsine by zinc in hydrochloric acid solution. the resulting mixture of gases is passed through a scrubber containing borosilicate wool im- pregnated with lead acetate solution and then into an absorp- tion tube containing a solution of silver diethyldithiocarbamate in pyridine. arsine reacts with this reagent to form a red- colored silver sol having maximum absorbance at about 540 nm. the absorbance of the solution is measured photometri- cally and the arsenic determined by reference to an analytical curve prepared from standards.9. interferences9.1 although many samples are relatively free of interfer- ences, several metals, notably cobalt, nickel, mercury, silver, platinum, copper, chromium, and molybdenum, may interfere with the evolution of arsine and with the recovery of arsenic. the presence of any or all of these metals in a sample being analyzed must be considered as a potential source of interfer- ence, and the analyst must fully determine the extent of actual interference, if any. this could be accomplished by spiking.9.2 hydrogen sulfide and other sulfides interfere, but com-9.3 antimony interferes by forming stibine, which distillsalong with the arsine. stibine reacts with the color-forming reagent to form a somewhat similar red sol having maximum absorbance near 510 nm. the sensitivity for antimony at 540 nm is only about 8 % that of arsenic (1 mg/l of antimony will show an apparent presence of 0.08 mg/l of arsenic).9.4 nitric acid interferes with the test and must be com- pletely eliminated during the digestion.10. apparatus10.1 arsine generator, scrubber, and absorber7, assembled as shown in fig. 1.10.2 spectrophotometer or filter photometer, suitable for use at 540 nm and providing a light path of at least 10 mm. the filter photometer and photometric practice prescribed in this method shall conform to practice e 60. the spectrophotometer shall conform to practice e 275.11. reagents11.1 arsenic solution, stock (1.00 ml = 1.00 mg as) dissolve 1.320 g of arsenic trioxide (as2o3) ( warning, seemonly encountered quantities are effectively removed by the lead acetate scrubber and the digestion.7 available commercially.2d 2972 03 note 1), dried for at least 1 h at 110c, in 10 ml of naohsolution (420 g/l) and dilute to 1 l with water. this solution is stable.note 1warning: arsenic trioxide is extremely toxic. avoid inges- tion or inhalation of dry powder during standard preparation. wash hands thoroughly immediately after handling arsenic trioxide. under no circum- stances pipet any arsenic solutions by mouth.11.2 arsenic solution, intermediate (1.00 ml = 10.0 g as) dilute 5.00 ml of arsenic stock solution to 500 ml with water.11.3 arsenic solution, standard (1.00 ml = 1.00 g as) dilute 10.0 ml of arsenic intermediate solution to 100 ml with water. prepare fresh before each use.11.4 hydrochloric acid (sp gr 1.19)concentrated hydro- chloric acid (hcl). use analytical grade acid with an arsenic13. procedure13.1 clean all glassware before use by rinsing first with hot hno3(1 + 1) and then with water. the absorbers must be additionally rinsed with acetone and then air-dried.13.2 pipet a volume of well-mixed acidified sample con- taining less than 25 g of arsenic (100 ml maximum) into a generating flask and dilute to approximately 100 ml.note 3if only dissolved arsenic is to be determined use a filtered and acidified sample (see 6.2).13.3 to each flask, add 7 ml of h2so 4(1 + 1) and 5 ml of concentrated hno3. add a small boiling chip and carefully evaporate to dense fumes of so3, maintaining an excess of hno3 until all organic matter is destroyed. this prevents darkening of the solution and possible reduction and loss of arsenic. cool, add 25 ml of water, and again evaporate tocontent not greater than 1 3 10 6 %.11.5 lead acetate solution (100 g/l)dissolve 10 g ofdense fumes of sooxides of nitrogen.3. maintain heating for 15 min to expellead acetate (pb(c 2h3o2)23h2o) in 100 ml of water. storereagent in a tightly stoppered container.11.6 nitric acid (sp gr 1.42)concentrated nitric acid(hno3). use analytical grade acid with an arsenic content not greater than 1 3 10 6 %.11.7 nitric acid (1 + 1)add 250 ml of concentrated nitric acid (sp gr 1.42) to 250 ml of water.11.8 potassium iodide solution (150 g/l)dissolve 15 g of potassium iodide (ki) in 100 ml of water. store in an amber bottle.11.9 silver diethyldithiocarbamate solutiondissolve 1 g of silver diethyldithiocarbamate (agddc) in 200 ml of pyridine. this solution is stable for at least several months when stored in an amber bottle.11.10 sodium hydroxide solution (420 g/l)dissolve 42 g of sodium hydroxide (naoh) pellets in 100 ml of water.11.11 stannous chloride solutiondissolve 40 g of arsenic-free stannous chloride (sncl 22h2o) in 100 ml of hcl(sp gr 1.19). add a few small pieces of mossy tin.11.12 sulfuric acid (1 + 1)cautiously, and with constant stirring and cooling, add 250 ml of concentrated h2so4 (sp gr1.84) to 250 ml of water.11.13 zinc, granular, 20-mesh. arsenic content must not exceed 1 3 10 6 %.12. standardization12.1 clean all glassware before use by rinsing first with hot hno3(1 + 1) and then with water. the absorbers must be additionally rinsed with acetone and then air-dried.12.2 prepare, in a 250-ml generator flask, a blank and sufficient standards containing from 0.0 to 25.0 g of arsenic by diluting 0.0 to 25.0-ml portions of the arsenic standard solution to approximately 100 ml with water.12.3 proceed as directed in 13.3-13.9.12.4 construct an analytical curve by plotting the absor- bances of standards versus micrograms of arsenic.13.4 cool, and adjust the volume in each flask to approxi-mately 100 ml with water.13.5 to each flask add successively, with thorough mixing after each addition, 8 ml of concentrated hcl, 4 ml of ki solution, and 1 ml of sncl2 solution. allow about 15 min for complete reduction of the arsenic to the trivalent state.13.6 place in each scrubber a plug of borosilicate wool that has been impregnated with lead acetate solution. assemble the generator, scrubber, and absorber, making certain that all parts fit and are correctly adjusted. add 3.00 ml of silver diethyldithiocarbamate-pyridine solution to each absorber. add glass beads to the absorbers until the liquid just covers them.note 4four millilitres of silver diethyldithiocarbamate-pyridine so- lution may be used with some loss of sensitivity.13.7 disconnect each generator, add 6 g of zinc, and reconnect immediately.13.8 allow 30 min for complete evolution of arsine. warm the generator flasks for a few minutes to make sure that all arsine is released.13.9 pour the solutions from the absorbers directly into clean spectrophotometer cells and within 30 min measure the absorbance of each at 540 nm.14. calculation14.1 determine the weight of arsenic in each sample by referring to the analytical curve. calculate the concentration of arsenic in the sample in micrograms per litre, using eq 1:arsenic, g/l 5 1000 w/v(1)where:v= volume of sample, ml, andw = weight of arsenic in sample, g.15. precision and bias 815.1 the single-operator and overall precision of this method for three laboratories, which included a total of six operators analyzing each sample on three different days, withinnote 2the response is linear up to 15 g of arsenic; however, because the curve is nonlinear above 15 g, it is necessary to havesufficient standards above 15 g to permit constructing an accurate curve.8 supporting data are available from astm headquarters. requestrr:d 19 1049.3d 2972 03 its designated range varies with the quantity being tested inaccordance with table 1.15.2 recoveries of known amounts of arsenic (arsenic trioxide) in a series of prepared standards are given in table 1.15.3 the precision and bias data were obtained on reagent water, river water, and process water. the information on precision and bias may not apply to other waters. it is the users responsibility to ensure the validity of this test method for waters of untested matrices.15.4 three independent laboratories participated in the roundrobin study. precision and bias for this test method conform to practice d 2777 77, which was in place at the time of collaborative testing. under the allowances made in 1.4 of practice d 2777 98, these precision and bias data do meet existing requirements for interlaboratory studies of committee d19 test methods.16. quality control16.1 in order to be certain that analytical values obtained using these test methods are valid and accurate within the confidence limits of the test, the following qc procedures must be followed when analyzing arsenic.16.2 calibration and calibration verification:16.2.1 analyze at least three working standards containing concentrations of arsenic that bracket the expected sample concentration, prior to analysis of samples, to calibrate the instrument. the calibration correlation coefficient shall be equal to or greater than 0.990. in addition to the initial calibration blank, a calibration blank shall be analyzed at the end of the batch run to ensure contamination was not a problem during the batch analysis.16.2.2 verify instrument calibration after standardization by analyzing a standard at the concentration of one of the calibration standards. the concentration of a mid-range stan- dard should fall within 615 % of the known concentration.16.2.3 if calibration cannot be verified, recalibrate the instrument.16.3 initial demonstration of laboratory capability:16.3.1 if a laboratory has not performed the test before, or if there has