ASTM D5526-1994(2011)e1 Standard Test Method for Determining Anaerobic Biodegradation of Plastic Materials Under Accelerated Landfill Conditions《加速土地填筑条件下塑料材料的厌氧生物降解测定的标准试验方法》.pdf

《ASTM D5526-1994(2011)e1 Standard Test Method for Determining Anaerobic Biodegradation of Plastic Materials Under Accelerated Landfill Conditions《加速土地填筑条件下塑料材料的厌氧生物降解测定的标准试验方法》.pdf》由会员分享，可在线阅读，更多相关《ASTM D5526-1994(2011)e1 Standard Test Method for Determining Anaerobic Biodegradation of Plastic Materials Under Accelerated Landfill Conditions《加速土地填筑条件下塑料材料的厌氧生物降解测定的标准试验方法》.pdf（6页珍藏版）》请在麦多课文档分享上搜索。

1、Designation: D5526 94 (Reapproved 2011)1Standard Test Method forDetermining Anaerobic Biodegradation of Plastic MaterialsUnder Accelerated Landfill Conditions1This standard is issued under the fixed designation D5526; the number immediately following the designation indicates the year oforiginal ado

2、ption or, 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.1NOTEReapproved with editorial changes throughout in February 2011.1. Scope1.1 This

3、 test method covers determination of the degree andrate of anaerobic biodegradation of plastic materials in anaccelerated-landfill test environment. This test method is alsodesigned to produce mixtures of household waste and plasticmaterials after different degrees of decomposition under con-ditions

4、 that resemble landfill conditions. The test materials aremixed with pretreated household waste and exposed to amethanogenic inoculum derived from anaerobic digesters op-erating only on pretreated household waste. The anaerobicdecomposition occurs under dry (more than 30 % total solids)and static no

5、nmixed conditions. The mixtures obtained afterthis test method can be used to assess the environmental andhealth risks of plastic materials that are degraded in a landfill.1.2 This test method is designed to yield a percentage ofconversion of carbon in the sample to carbon in the gaseousform under c

6、onditions that resemble landfill conditions. It ispossible that this test method will not simulate all conditionsfound in landfills, especially biologically inactive landfills.This test method more closely resembles those types oflandfills in which the gas generated is recovered or evenactively prom

7、oted, or both, for example, by inoculation(codeposition of anaerobic sewage sludge and anaerobicleachate recirculation), moisture control in the landfill(leachate recirculation), and temperature control (short-terminjection of oxygen and heating of recirculated leachate)(1-7).21.3 This test method i

8、s designed to produce partially de-graded mixtures of municipal solid waste and plastics that canbe used to assess the ecotoxicological risks associated with theanaerobic degradation of plastics after various stages ofanaerobic biodegradation in a landfill.1.4 The values stated in SI units are to be

9、 regarded as thestandard.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 standard to establish appro-priate safety and health practices and determine the applica-bility of regulatory limitations pri

10、or to use. Specific hazardsstatements are given in Section 8.NOTE 1There is no known ISO equivalent to this standard.2. Referenced Documents2.1 ASTM Standards:3D618 Practice for Conditioning Plastics for TestingD883 Terminology Relating to PlasticsD1293 Test Methods for pH of WaterD1888 Test Methods

11、 for Particulate and Dissolved Matter,Solids, or Residue in Water4D2908 Practice for Measuring Volatile Organic Matter inWater by Aqueous-Injection Gas ChromatographyD3590 Test Methods for Total Kjeldahl Nitrogen in WaterD4129 Test Method for Total and Organic Carbon in Waterby High Temperature Oxid

12、ation and by Coulometric De-tectionE260 Practice for Packed Column Gas ChromatographyE355 Practice for Gas Chromatography Terms and Rela-tionships2.2 APHA-AWWA-WPCF Standards:52540D Total Suspended Solids Dried at 103105C1This test method is under the jurisdiction ofASTM Committee D20 on Plasticsand

13、 is the direct responsibility of Subcommittee D20.96 on EnvironmentallyDegradable Plastics and Biobased Products.Current edition approved Feb. 1, 2011. Published February 2011. Originallyapproved in 1994. Last previous edition approved in 2002 as D5526 94(2002)1. DOI: 10.1520/D5526-94R11E01.2The bol

14、dface numbers in parentheses refer to the list of references at the end ofthis standard.3For 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 Summa

15、ry page onthe ASTM website.4Withdrawn.5Standard Methods for the Examination of Water and Wastewater,20thed.,1999, available from American Public Health Association, 800 I Street, NW,Washington, D.C. 20001-3710, or http:/www.standardmethods.org.1Copyright ASTM International, 100 Barr Harbor Drive, PO

16、 Box C700, West Conshohocken, PA 19428-2959, United States.2540E Fixed and Volatile Solids Ignited at 550C212 Nitrogen Ammonia3. Terminology3.1 DefinitionsFor definitions of terms used in this testmethod see Terminology D883.3.2 Definitions of Terms Specific to This Standard:3.2.1 methanogenic inocu

17、lumanaerobically digested or-ganic waste containing a high concentration of anaerobicmethane-producing microorganisms.4. Summary of Test Method4.1 This test method described consists of the following: (1)selecting and analyzing material for testing; (2) obtaining apretreated municipal-solid-waste fr

18、action and a concentratedanaerobic inoculum from an anaerobic digester; (3) exposingthe material to an anaerobic static batch fermentation at morethan 30 % solids; (4) measuring total carbon in the gas (CO2and CH4) evolved as a function of time; (5) removing thespecimens for cleaning (optional), con

19、ditioning, testing, andreporting; (6) assessing the degree of biodegradability; and (7)assessing the degree of biodegradability under less than opti-mum conditions.4.2 The percentage of biodegradability is obtained by de-termining the percent of conversion of carbon from the testmaterial to carbon i

20、n the gaseous phase (CH4and CO2). Thispercentage of biodegradability will not include the amount ofcarbon from the test substance that is converted to cell biomassand that is not, in turn, metabolized to CO2and CH4.5. Significance and Use5.1 Decomposition of a plastic within a landfill involvesbiolo

21、gical processes that will affect the decomposition of othermaterials enclosed by, or in close proximity to, the plastic.Rapid degradation of the plastic has the ability to increase theeconomic feasibility of landfill-gas recovery, minimize theduration of after-care of the landfill, and make possible

22、 therecovery of the volume reduction of the waste due to biodeg-radation during the active life of the landfill. This procedurehas been developed to permit determination of the anaerobicbiodegradability of plastic products when placed in biologi-cally active environments simulating landfill conditio

23、ns.5.2 As degradation occurs inevitably in a landfill, it is ofimmediate concern that the plastic materials do not producetoxic metabolites or end products under the various conditionsthat have the potential to occur in a landfill. The mixturesremaining after completion of the test method, containin

24、g fullyor partially degraded plastic materials or extracts, can besubmitted subsequently to ecotoxicity testing in order to assessthe environmental hazards posed by the breakdown of plasticsto varying degrees in landfills. This test method has beendesigned to assess biodegradation under optimum and

25、less-than-optimum conditions.5.3 LimitationsBecause a wide variation exists in theconstruction and operation of landfills, and because regulatoryrequirements for landfills vary greatly, this procedure is notintended to simulate the environment of all landfills. However,it is expected to closely rese

26、mble the environment of abiologically active landfill. More specifically, the procedure isintended to create a standard laboratory environment thatpermits rapid and reproducible determination of the anaerobicbiodegradability under accelerated landfill conditions, while atthe same time producing repr

27、oducible mixtures of fully andpartially decomposed household waste with plastic materialsfor ecotoxicological assessment.6. Apparatus6.1 Pressure-Resistant Glass VesselsTwenty-seven, eachwith a volume of 4 to 6 L, which can be closed airtight andcapable of withstanding an overpressure of two atmosph

28、eres.The lids of the reactors are equipped with an overpressurevalve (to prevent the overpressure from becoming higher than2 bars), a manometer that provides a rough indication of theoverpressure, a septum that allows one to take gas samples andmeasure the exact overpressure, and, finally, a valve t

29、o releasethe overpressure (Fig. 1).6.2 Incubators, sufficient to store the vessels in the dark at35 6 2C for the duration of the test.6.3 Pressure Transducer, connected to a syringe needle tomeasure the headspace pressure in the test vessel.6.4 Gas Chromatograph, or other apparatus, equipped witha s

30、uitable detector and column(s) for measuring methane andcarbon dioxide concentrations in the evolved gases.6.5 pH Meter, precision balance (60.1 g), analytical bal-ance (60.1 mg), thermometer, and barometer.1 = Digester.2 = Incubation chamber.3 = Overpressure valve.4 = Manometer.5 = Septum.6 = Valve

31、.FIG. 1 Setup of Accelerated LandfillD5526 94 (2011)126.6 Suitable Devices, for determining volatile fatty acids byaqueous-injection chromatography, total Kjeldahl nitrogen,ammonia nitrogen, dry solids (105C), and volatile solids(550C) concentrations.7. Reagents and Materials7.1 Pretreated-Household

32、 Waste, derived from mixed mu-nicipal solid waste or the organic fraction thereof, afterhomogenizing, screening over a screen with holes of a diam-eter of 40 to 80 mm, and aerobically stabilized over a period of2 to 4 weeks by blowing air into the material and maintaininga dry-matter content of 50 6

33、 5 % and a temperature of 55 610C. (Optional: the pretreated household waste can be re-placed by a similarly pretreated simulated solid waste.)7.2 Anaerobic Inoculum, derived from a properly operatinganaerobic digester with pretreated household waste as a solesubstrate or a digester that treats pred

34、ominantly householdwaste.7.3 Cellulose, Analytical-Grade, for thin-layer chromatog-raphy as a positive control.67.4 Polyethylene (optional), as a negative control. It needsto be in the same form as that in which the sample is tested:film polyethylene for film samples, pellets of polyethylene incase

35、the sample is in the form of pellets, etc.8. Hazards8.1 This procedure involves the use of inoculum and mu-nicipal solid waste containing biologically and possibly chemi-cally active materials known to produce a variety of diseases.Avoid contact with these materials by wearing gloves and otherapprop

36、riate protective equipment. Use good personal hygieneto minimize exposure.8.2 It is possible that the solid waste mixture will containsharp objects. Take extreme care when handling this mixture toavoid injury.8.3 This test method includes the use of hazardous chemi-cals. Avoid contact with the chemi

37、cals and follow the manu-facturers instructions and material safety data sheets.8.4 The methane produced during the procedure is explo-sive and flammable. Upon release of the biogas from thegas-collection system, take care in venting the biogas to theoutside or to a hood.9. Inoculum9.1 The inoculum

38、can be derived either from a laboratory-scale or full-scale continuous digester or batch digester, oper-ating at 35C and functioning with an organic fraction ofhousehold waste as the predominant substrate. In case theinoculum is derived from a continuous laboratory-scale orfull-scale digester, the d

39、igester must be operating for a periodof at least one month on the organic fraction of householdwaste, with a maximum retention time of 30 days undermesophilic conditions (35 6 2C). Gas production yields mustbe at least 15 mL at standard temperature and pressure ofbiogas/gram of dry solids in the di

40、gester and per day for at least7 days. In case the inoculum is derived from a batch digester,the gas production rate must have exceeded 1 L/kg waste/day,and the methane concentration of the biogas being producedmust be above 60 %.9.2 The prepared inoculum needs to undergo a short meso-philic post-fe

41、rmentation of approximately 7 days at the samedry-matter content as the digester from which it was derived.This means that the inoculum is not fed but is allowed topost-ferment anaerobically by itself. This is to ensure thatlarge, easily biodegradable particles are degraded during thisperiod and als

42、o to reduce the background level of degradationof the inoculum itself.9.3 The biochemical characteristics of the inoculum shall beas follows:9.3.1 pHBetween 7.5 and 8.5 (in accordance with TestMethods D1293);9.3.2 Volatile Fatty Acids (VFA)Below 1 g/kg wet weight(in accordance with Practice D2908);

43、and9.3.3 NH+4-NBetween 0.5 and 2 g/kg (in accordance withAPHA Test 212 and Test Method D3590).9.4 Analyses are performed after dilution of the inoculumwith distilled water on a ratio of distilled water to inoculum of5 to 1 on a weight-over-weight basis.10. Test Specimen10.1 The test specimen needs t

44、o be of sufficient carboncontent, analyzed in accordance with Test Method D4129,toyield carbon dioxide and methane volumes that can be mea-sured accurately by the trapping devices described. Add moretest specimen when low biodegradability is expected, up to 100g of dry matter of the test specimen.10

45、.2 It is acceptable for the test specimen to be in the formof films, powder, pellets, or formed articles, or in the form ofa dog bone and in accordance with Practice D618. The testsetup needs to be capable of handling articles that are 100 by50 by 4 mm thick.11. Procedure11.1 Preparation of the Mixt

46、ures:11.1.1 Determine the volatile solids, dry solids, and nitrogencontent of the pretreated household waste and the inoculum inaccordance with Test Methods D1888, D3590, and APHA2540D and 2540E.11.1.2 Determine the volatile solids, dry solids, and carboncontent of all test substances in accordance

47、withAPHA2540Dand 2540E and Test Method D4129.11.1.3 Weigh and combine the components and adjust thedry matter content of the final mixtures with water to reach thedesired dry-matter content for each vessel. Roughly weigh out600 g on a dry-weight basis of pretreated household waste, andmix it with 10

48、0 g on a dry-weight basis of mesophilicanaerobic inoculum from a continuously operating digester or150 g on a dry-weight basis of anaerobic inoculum from abatch digester. Add 60 to 100 g of dry matter of the testsubstance. Add water until the appropriate final dry mattercontent is reached. (In order

49、 to reach 60 % dry matter contentin the mixture, it is necessary, in some cases, to have waterremoved prior to combining the different components of themixture. This can be accomplished by drying the pretreated6Avicelt, available from EM Chemicals, Inc., Hawthorne, NY, was used fordevelopment of this test method.D5526 94 (2011)13household waste or centrifuging the anaerobic inoculum.) Mixthe required amounts of pretreated household waste, inoculum,and test substance in a small container for 2 to 3 min. Introducethe mixture in the vessel, weigh the vessel