ASTM D4994-1989(2002) Standard Practice for Recovery of Viruses from Wastewater Sludges《废水污垢中毒素的分离》.pdf
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1、Designation: D 4994 89 (Reapproved 2002)Standard Practice forRecovery of Viruses from Wastewater Sludges1This standard is issued under the fixed designation D 4994; the number immediately following the designation indicates the year oforiginal adoption or, in the case of revision, the year of last r
2、evision. A number in parentheses indicates the year of last reapproval. Asuperscript epsilon (e) indicates an editorial change since the last revision or reapproval.1. Scope1.1 This practice is used for the recovery of viruses fromwastewater sludges and favors the enteroviruses.1.2 Both procedures a
3、re applicable to raw, digested, anddewatered sludges.SectionsProcedure AAdsorption 6 to 10Procedure BSonication 11 to 151.3 This practice was tested on standardized sludges asdescribed in 10.1 and 17.1. It is the users responsibility toensure the validity of this practice for untested matrices.1.4 T
4、his 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-priate safety and health practices and determine the applica-bility of regulatory limitations prior to use.1.5 Only adequately
5、trained personnel should be allowed toperform these procedures and should use safety precautionsrecommended by the U.S. Public Health Service, Center forDisease Control,2for work with potentially hazardous biologi-cal organisms.2. Referenced Documents2.1 ASTM Standards:D 1129 Terminology Relating to
6、 Water3D 1193 Specification for Reagent Water33. Terminology3.1 DefinitionsFor definitions of terms used in this prac-tice, refer to Terminology D 1129.4. Significance and Use4.1 Although many laboratories are presently isolating vi-ruses from sludge, a valid comparison of data generated has notbeen
7、 possible because of the lack of a standard test method(s).5. Apparatus5.1 Centrifuge(s), refrigerated, capable of attaining10 000 3 g, screw-capped 100-mL centrifuge bottles that canwithstand 10 000 3 g, and 250-mL screw-capped centrifugebottles capable of withstanding 2 500 3 g.5.2 pH Meter, measu
8、ring to an accuracy of at least 0.1 pHunit, equipped with a combination-type electrode. Calibratewith standard buffers.5.3 Filter Apparatus, for membrane sterilization,4with47-mm diameter filter holder and 50-mL slip-tip syringe (see7.7 for type of filter material).6. Purity of Reagents6.1 Purity of
9、 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 Analytical Reagents of the American Chemical Society,where such specifications are available.5Other grades may beused, prov
10、ided 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 otherwise indicated, referencesto water shall be understood to mean reagent water conformingto Specification D 1193, Type II.1Thi
11、s practice is under the jurisdiction of ASTM Committee D19 on Water andis the direct responsibility of Subcommittee D19.24 on Water Microbiology.Current edition approved Oct. 27, 1989. Published March 1990.2Richardson, J. H., and Barkley, W. E., Biological Safety in Microbiological andBiomedical Lab
12、oratories, 2nd. edition, U.S. Dept. of Health and Human Services,Public Health Service, Center for Disease Control, and National Institutes of Healthand Human Services, 1988.3Annual Book of ASTM Standards, Vol 11.01.4The Swinnex filter (No. SX0047000, available from Millipore Corp., 80AshbyRd., Bedf
13、ord, MA 01730, or equivalent, has been found suitable for this purpose.5Reagent Chemicals, American Chemical Society Specifications, AmericanChemical Society, Washington, DC. For suggestions on the testing of reagents notlisted by the American Chemical Society, see Analar Standards for LaboratoryChe
14、micals, BDH Ltd., Poole, Dorset, U.K., and the United States Pharmacopeiaand National Formulary, U.S. Pharmaceutical Convention, Inc. (USPC), Rockville,MD.1Copyright ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959, United States.PROCEDURE AADSORPTION7. Reagen
15、ts and Materials7.1 Aluminum Chloride Solution (12.07 g/L)Dissolve12.07 g of aluminum chloride (AlCl36H2O) in 500 mL ofwater and dilute to 1000 mL. Autoclave AlCl3solution at121C for 15 min.7.2 Buffered Beef Extract SolutionDissolve 10 g of beefextract powder,61.34gofNa2HPO47H2O, and 0.12 g of citri
16、cacid in 100 mL of water in a screw-cap flask by stirring forabout2honamagnetic stirrer.Autoclave at 121C for 15 min.7.3 Disodium Hydrogen Phosphate Solution (4 g/100 mL)Dissolve4gofdisodium hydrogen phosphate(Na2HPO47H2O) in 100 mL of water and autoclave at 121Cfor 15 min.7.4 Hydrochloric Acid (1 +
17、 1)Add 1 volume of concen-trated HCl (sp gr 1.19) to 1 volume of water.7.5 Hydrochloric Acid (1 + 9)Add 1 volume of concen-trated HCl (sp gr 1.19) to 9 volumes of water.7.6 Sodium Hydroxide Solution (4 g/100 mL)Dissolve 4.0g of dry sodium hydroxide (NaOH) in water and dilute to 100mL.7.7 Filters, Di
18、sc, Membrane, 47-mm3.0-, 0.45-, and0.25-m pore size which must be cut to proper size from sheetfilters.7Disassemble filter holder. Place filter with 0.25-mpore size on support screen of filter holder and stack theremaining filters on top in order of increasing pore size.Reassemble and tighten filter
19、 holder. Filters stacked in-tandemas described tend to clog more slowly when turbid material isfiltered through them. Prepare several filter stacks.8. Summary of Procedure8.1 The adsorption procedure relies upon adsorption ofviruses from the liquid phase to the sludge solids, which areconcentrated b
20、y centrifugation. The supernatant is discarded.Viruses are desorbed from the solids by physicochemicalmeans and further concentrated by organic flocculation. De-contamination is accomplished by filtration.9. Procedure9.1 Conditioning of SludgeIn the absence of experiencethat dictates otherwise, use
21、100-mL volumes for liquid sludgesand 100-g quantities for digested, dewatered sludges.9.1.1 Measure 100 mL of well-mixed sludge in a graduated100-mL cylinder. Mix sludge vigorously immediately before itis poured into cylinder because sludge solids, which containmost of the viruses, begin to settle o
22、ut immediately aftermixing stops.9.1.2 Place stir bar into a 250-mL beaker.9.1.3 Pour the 100-mL of measured sludge from the cylin-der into the 250-mL beaker. If necessary, pour sludge severaltimes from beaker to cylinder and back to remove all sludgesolids to beaker. Take care to avoid formation of
23、 aerosols.9.1.4 Place beaker on magnetic stirrer, and stir at speedsufficient to develop vortex.9.1.5 Add 1 mL of AlCl3solution to sludge. Final concen-tration of AlCl3in sludge is approximately 0.0005 M.9.1.6 Place combination-type pH electrode into sludge andadjust pH of sludge to 3.5 6 0.1 with H
24、Cl (1 + 1). If pH fallsbelow 3.5, readjust with NaOH solution (4 g/100 mL). Ifsludge adheres to electrodes, clean electrodes by moving themup and down gently in mixing sludge. pH meter must bestandardized at pH 4.9.1.7 Continue mixing for 30 min. Check pH of the sludgeat frequent intervals. If the p
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