ASTM D3860-1998(2014) Standard Practice for Determination of Adsorptive Capacity of Activated Carbon by Aqueous Phase Isotherm Technique《用液相等温线技术测定活性炭吸水率的标准实施规程》.pdf

1、Designation: D3860 98 (Reapproved 2014)Standard Practice forDetermination of Adsorptive Capacity of Activated Carbonby Aqueous Phase Isotherm Technique1This standard is issued under the fixed designation D3860; 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 covers the determination of the adsorptivecapacity of activated

3、carbon to remove undesirable constituentsfrom water and waste water. It can be used to evaluate theadsorptive capacity of activated or reactivated carbon.1.2 This practice is not recommended unless special precau-tions are taken to reduce loss during sample preparation andanalysis.1.3 This practice

4、is recommended to determine the adsorp-tive capacity of activated carbon for the following applications,but is not limited to these applications:1.3.1 Removal of color from dye mill waste water,1.3.2 Removal of taste or odor constituents, or both, frompotable waters,1.3.3 Removal of toxicants from w

5、ater,1.3.4 Removal of surface active agents from water,1.3.5 Removal of BOD5from sanitary waste waters, and1.3.6 Removal of TOC from industrial waste waters.1.4 The values stated in SI units are to be regarded asstandard. No other units of measurement are included in thisstandard.1.5 The following s

6、afety caveat applies to the proceduresection of this practice:This standard does not purport toaddress all of the safety concerns, if any, associated with itsuse. It is the responsibility of the user of this standard toestablish appropriate safety and health practices and deter-mine the applicabilit

7、y of regulatory limitations prior to use.2. Referenced Documents2.1 ASTM Standards:2D1129 Terminology Relating to WaterD1193 Specification for Reagent WaterD3370 Practices for Sampling Water from Closed ConduitsD2652 Terminology Relating to Activated CarbonD2867 Test Methods for Moisture in Activate

8、d CarbonE300 Practice for Sampling Industrial Chemicals3. Terminology3.1 Definitions:3.1.1 For definitions of terms used in this practice relating toactivated carbon, refer to Terminology D2652.3.1.2 For definition of terms used in this practice relating towater, refer to Terminology D1129.4. Summar

9、y of Practice4.1 This practice consists of the determination of the ad-sorptive capacity of activated carbon for adsorbable constitu-ents by contacting the aqueous solution with activated carbon,determining the amount of the constituents removed, andcalculating the adsorptive capacity from a Freundl

10、ich isothermplot.4.1.1 Sample weights of activated carbon may have to beadjusted, depending on the concentration of adsorbable con-stituents in the water.5. Significance and Use5.1 This practice is used when activated carbon is consid-ered as an adsorbent in treating water. Since both granular andpo

11、wdered activated carbons are commercially available, astandard practice is needed to ensure that the activated carbonsare evaluated under the same test conditions. Specified particlesize carbon is to be used to ensure that the same test conditionsare used. The practice is generally performed at 20C;

12、however, other temperatures may be used and noted.6. Interferences6.1 The water sample must not contain any immiscible oil.6.2 Generally, membrane filters contain a slight amount ofleachable surfactants and wetting agents that might be a sourceof detectable error in waters having low concentrations

13、ofadsorbable constituents.1This practice is under the jurisdiction of ASTM Committee D28 on ActivatedCarbon and is the direct responsibility of Subcommittee D28.02 on Liquid PhaseEvaluation.Current edition approved July 1, 2014. Published September 2014. Originallyapproved in 1979. Last previous edi

14、tion approved in 2008 as D3860 98 (2008).DOI: 10.1520/D3860-98R14.2For 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 web

15、site.Copyright ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959. United States17. Apparatus7.1 Agitator, able to keep slurried activated carbon insuspension.NOTE 1A wrist-action shaker or a magnetic stirrer is suitable as anagitator.7.2 Grinding mill, capable

16、of grinding material so that 95 %passes through a 325-mesh sieve.7.3 Vacuum or pressure-filtration apparatus.7.4 Membrane filters, 0.40 to 0.45 m.7.5 Erlenmeyer flasks, glass stoppered, 500-mL and1000-mL capacity.7.6 Analytical balance, capable of weighing to the nearest0.1 mg.7.7 Oven, forced-air c

17、irculation, capable of temperatureregulation between 145 and 155C.7.8 Constant temperature water bath, capable of tempera-ture regulation of 20 6 1C.7.9 Pipet, 100-mL.8. Sampling8.1 Sample activated carbon that has been sampled accord-ing to Practice E300 and reduced in particle size so that 95 %pas

18、ses through a U.S. 325-mesh sieve by wet screening orequivalent, and oven-dried according to Test Method D2867(3 hours at 150C is usually sufficient).8.2 Collect water samples in accordance with PracticesD3370.9. Procedure9.1 Table 1 is a suggested list of the activated carbonweights and solution sa

19、mple volumes to be used for theexpected concentrations of adsorbable constituents. Suggestedcarbon weights or solution sample volumes should be adjustedto obtain a maximum of 85 % adsorbate removal and aminimum of 10 % adsorbate removal.9.2 For water containing 10 mg/L adsorbable constituents,pipet

20、aliquots of 100 mL each into 500-mL glass-stopperedErlenmeyer flasks. For water containing |La10 mg/L, measure500-mL aliquots into 1000-mL glass-stoppered Erlenmeyerflasks.9.3 Add to the containers the appropriate amount of pulver-ized activated carbon corrected to dry basis (Table 1) in regularinte

21、rvals to allow time for filtration. Generally, a 5-min intervalis adequate. Use one flask without activated carbon for acontrol sample.9.4 After the addition of each activated carbon sample, swirlthe flask to wet the carbon. Stopper the flask and place on theagitator. Record the time.9.5 Allow each

22、flask to shake or agitate for2hinawaterbath at the desired temperature. Two hours contact time isnormally sufficient to achieve steady state. However, a contacttime study should be performed to verify that steady state isachieved (see 4.1).9.6 After 2 h, immediately filter each test and controlsampl

23、es through separate new 0.40 to 0.45-m membranefilters.NOTE 2If the water sample contains volatile constituents, use pressurefiltration with nitrogen gas to reduce loss.NOTE 3It is recommended that each membrane filter be rinsed with500 mL of reagent grade Type II water (Specification D1193) prior t

24、ofiltration.9.7 Immediately analyze the filtrates for the specific con-stituent of interest and record the results along with thecorresponding carbon weight.10. Calculation10.1 Determine the amount of constituent adsorbed, X,asfollows:X 5 CoV 2 CVwhere:X = amount of constituent adsorbed, mg,Co= conc

25、entration of constituents before carbon treatment,mg/L,C = concentration of constituents after carbon treatment,mg/L, andV = volume of sample, L.10.2 Determine the amount of constituent adsorbed per unitweight of carbon, X/M, as follows:X/M 5CoV 2 CV!Mwhere:M = weight of carbon, g,X = amount of cons

26、tituent absorbed, mg,X/M = constituent absorbed per unit weight of carbon, mg/g,Co = concentration of constituents before carbontreatment, mg/L,C = concentration of constituents after carbon treatment,mg/L, andV = volume of sample, L.11. Report11.1 See Table 2 for the recommended format for datarepo

27、rting.11.2 Plotting of Data:11.2.1 Use three-cycle log/log paper and plot concentrationremaining in mg/L on the abscissa and X/M on the ordinate,and then connect the points. See Fig. 1.TABLE 1 Solution Sample Volumes and Carbon Weights forDetermining Adsorbable ConstituentsConcentration ofAdsorbable

28、Constituents,mg/LSolutionSampleVolume, mLSuggested Carbon Weights(Dry Basis)#10 500 1.0, 2.5, 5.0, 7.5, 10.0, 25.0, and 50.0 mg10; 100 100 0.01, 0.02, 0.04, 0.10, 0.20, 0.40, 1.0,2.0, and 4.0 g100 100 0.05, 0.1, 0.2, 0.5, 1.0, 2.0, 5.0, and 10.0 gD3860 98 (2014)211.2.2 If a vertical line is erected

29、from the point on theabscissa corresponding to the original concentration Coand theisotherm plot is extrapolated to intersect this line, the X/Mvalue at the point of intersection can be read from the ordinate.This value termed X/M Co represents the amount of impurityadsorbed when the carbon is in eq

30、uilibrium with the influentconcentration. This value represents the ultimate capacity ofthe carbon for the adsorbate.12. Precision and Bias12.1 PrecisionThe precision is limited by the precision ofthe test methods used in determining the concentrations of theconstituents.12.2 BiasThe bias is limited

31、 by the bias of the testmethods used in determining the concentrations of the con-stituents.13. Keywords13.1 activated carbonTABLE 2 Format for Data ReportingM Grams ofCarbonCConcentrationRemaining inSolution,mg/L(C) VConstituentRemaining inSolution, mgX ConstituentAdsorbed,mgX/M = mg/gControl 500 5

32、0 . . . . . .0.0500 475 47.5 2.5 500.1000 450 45.0 5.0 500.2000 420 42.0 8.0 400.5000 310 31.0 19 381.000 200 20.0 30 302.000 100 10.0 40 205.000 35 3.5 46.5 9.310.00 12 1.2 48.8 4.920.00 4 0.4 49.6 2.48D3860 98 (2014)3ASTM International takes no position respecting the validity of any patent rights

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