ASTM D5929-1996(2004) Standard Test Method for Determining Biodegradability of Materials Exposed to Municipal Solid Waste Composting Conditions by Compost Respirometry《用混合物吸收计测定暴露于.pdf

1、Designation: D 5929 96 (Reapproved 2004)Standard Test Method forDetermining Biodegradability of Materials Exposed toMunicipal Solid Waste Composting Conditions by CompostRespirometry1This standard is issued under the fixed designation D 5929; the number immediately following the designation indicate

2、s 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. Scope1.1 This test method covers the biodegradation pr

3、operties ofa material by reproducibly exposing materials to conditionstypical of municipal solid waste (MSW) composting. A mate-rial is composted under controlled conditions using a syntheticcompost matrix and determining the acclimation time, cumu-lative oxygen uptake, cumulative carbon dioxide pro

4、duction,and percent of theoretical biodegradation over the period of thetest. This test method does not establish the suitability of thecomposted product for any use.1.2 The values stated in both inch-pound and SI units are tobe regarded separately as the standard. The values given inparentheses are

5、 for information only.1.3 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 prior

6、to use.2. Referenced Documents2.1 ASTM Standards:2D 513 Test Methods for Total and Dissolved Carbon Diox-ide in WaterD 1129 Terminology Relating to WaterD 1293 Test Methods for pH of WaterD 2908 Practice for Measuring Volatile Organic Matter inWater by Aqueous-Injection Chromatography2.2 APHA-AWWA-W

7、EF Standard Methods:2540G Total, Fixed, and Volatile Solids in Solid and Semi-solid Samples33. Terminology3.1 DefinitionsDefinitions of terms applying to this testmethod appear in Terminology D 1129.3.2 Definitions of Terms Specific to This Standard:3.2.1 acclimation time, nthe time required for the

8、 oxygenuptake to reach 10 % of the total measured cumulative oxygenuptake.43.2.2 oxygen uptake, nthe cumulative oxygen consumedby the organisms during the test.3.2.3 theoretical carbon dioxide production (ThCDP),nthe maximum carbon dioxide that can be produced by amaterial as calculated by the carbo

9、n content of the material.3.2.4 theoretical oxygen uptake (ThOU), n the maximumoxygen consumption required to fully oxidize a material basedon the elemental content of the material.3.2.5 virgin newsprintnonprinted newspaper roll stock.4. Summary of Test Method4.1 This test method consists of the fol

10、lowing:4.1.1 The samples are prepared by cutting or forming thematerial into the form it would most likely be seen in the wastestream. A theoretical maximum carbon dioxide production andoxygen uptake are determined from an elemental analysis.4.1.2 An inoculum is obtained from a municipal MSW oryard

11、waste compost facility. It is procured from a static pilethat has been composting for at least two months.4.1.3 The synthetic MSW is prepared from virgin newsprint,pine bark or wood chips, corn starch, corn oil, bovine casein,and urea. A buffer/dilution water is prepared from magnesium,calcium, iron

12、 and a phosphate buffer.4.1.4 The test material, synthetic compost, inoculum, anddilution water are combined and placed in a highly insulatedreactor which monitors oxygen consumption and temperatureand captures all evolved carbon dioxide.1This test method is under the jurisdiction of ASTM Committee

13、D34 on WasteManagement and is the direct responsibility of Subcommittee D34.03.01 onThermal and Biological Treatment.Current edition approved March 10, 1996. Published May 1996.2For referenced ASTM standards, visit the ASTM website, www.astm.org, orcontact ASTM Customer Service at serviceastm.org. F

14、or Annual Book of ASTMStandards volume information, refer to the standards Document Summary page onthe ASTM website.3Available from American Public Health Assoc., 1015 15th Street, NW,Washington, DC 20005, Standard Methods for the Examination of Water and WasteWater, 18th ed., 1992.4Tabak, Henry H.

15、and Lewis, Ronald F., CEC/OECD Ring Test of RespirationMethod for Determination of Biodegradability, U. S. Environmental ProtectionAgency, pp. 13.1Copyright ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959, United States.4.1.5 The system is monitored, and oxyg

16、en uptake rates,temperature profiles, and total carbon dioxide produced arerecorded.4.1.6 The total oxygen uptake and carbon dioxide producedare compared with the theoretical values obtained from theelemental analysis, and a percent of biodegradation is gener-ated. Possible negative effects of the m

17、aterial are evaluated byobserving the acclimation time of the synthetic MSW andevaluating the oxygen uptake rate.5. Significance and Use5.1 As the crisis in solid waste continues to grow, MSWcomposting is increasingly being considered as one componentin the overall solid waste management strategy. T

18、he volumereduction achieved by composting, combined with the produc-tion of a usable end product, is resulting in increasing numbersof municipalities analyzing and selecting MSW composting asan alternative to incineration or to reduce reliance on landfilldisposal. This test method will help determin

19、e the effect ofmaterials on the compost process and establish if the materialcan be properly disposed through solid waste compostingfacilities.55.2 This test method attempts to provide a simulation of theoverall compost process while maintaining reproducibility.Exposing the test material with severa

20、l other types of materialsthat are typically in MSW provides an environment whichprovides the key characteristics of composting: material not ina sole carbon source environment which allows co-metabolism, compost system is self heating, and provides adirect measurement of organism respiration.6. App

21、aratus6.1 Compost Respirometry Apparatus (see Fig. 1):6.1.1 A minimum of six reactors, 2 to 6-L volume, with thetest material in triplicate and the controls in triplicate. Thereactors should be surrounded with efficient insulation tominimize heat loss and be gastight. Insulation should be 8 cmof ure

22、thane foam or equivalent.6.1.2 Tubing, with high resistance to gas permeation.6.1.3 Peristaltic Pump, to control and maintain gas flowthrough each reactor.6.1.4 4-L Scrubber Vessel, for each reactor fitted with ascrubber solution sampling port.6.1.5 Differential Pressure Switch, for each reactor tha

23、tactuates between 2 and 5 in. (51 and 127 mm) of water.6.1.6 Solenoid and Mass Flowmeter, to control and measurethe addition of pure (99.997 + ) oxygen to system.6.1.7 Temperature Probe, situated in the middle of thecompost.6.1.8 Data Acquisition and Control System, for the measure-ment of temperatu

24、re and the control and measurement of theoxygen addition.6.2 Miscellaneous:6.2.1 Temperature Control Room, or hood to maintain theexternal temperature of the apparatus at 40C.6.2.2 Flow Meter, to measure recirculation flow in eachreactor (optional).6.2.3 Computer Control of Peristaltic Pump, for aut

25、omaticrecirculation flow control (optional).6.3 Suitable devices for the measurement of pH, dry solids(105C), elemental analysis of material, carbon dioxide contentof scrubbers, weight, and volume of the final compost material.7. Test Materials7.1 The test materials can be in any form as long as its

26、dimensions do not exceed 3 by 3 by 12 cm. The test materialsshould be in the form that they would be seen in the wastestream. A representative sample must be obtained by usingappropriate ASTM methods or other documented method.7.2 Analyze the test materials for carbon, hydrogen, nitro-gen, oxygen, p

27、hosphorus, sulfur, and any other elements thatare suspected to be present at a level to effect oxygen uptake.The ThOU must be calculated for each material.7.3 Calculate the ThCDP from the carbon content of the testmaterial.7.4 The nitrogen content of the synthetic MSW should beadjusted if the C/N ra

28、tio is greater than 40:1. This is accom-plished by adjusting the urea content of the synthetic MSW.The synthetic MSW has adequate nitrogen to support theaddition of up to 35 g of carbon before the ratio exceeds 40:1.5Biocycle: Journal of Waste Recycling Staff, eds., The Biocycle Guide toComposting M

29、unicipal Wastes, JG Press, Inc., 1989.NOTE 1The compost respirometer features a 4-L reactor vessel (A)insulated with 8 cm of urethane foam. The atmosphere is drawn throughthe reactor by a peristaltic pump (B) to maintain aeration. The effluentgases are passed through a 4-L scrubber vessel (C) contai

30、ning 1.5 L of 5M NaOH to remove any carbon dioxide from the effluent gas stream.Samples are drawn from this scrubber solution during the evaluation todetermine the carbon dioxide released by the compost. As the microor-ganisms consume the oxygen in the system, a pressure drop occurs and isdetected b

31、y a highly sensitive pressure switch (D). This signals the dataacquisition and control system (G) and the oxygen is replaced with purebottled oxygen by a solenoid (E) and the amount added is measured by amass flowmeter (F). The gasses are then returned to the reactor. Athermocouple (H) is centered i

32、n the test reactor to monitor the temperatureof the compost. The system is sealed to prevent interference frombarometric fluctuations.FIG. 1 Compost Respirometer Functional DiagramD 5929 96 (2004)2If the urea content is adjusted, all reactors including controlsmust contain the same concentration of

33、urea.8. Reagents and Materials8.1 Scrubber Solution, containing 3.25 N NaOH in distilledwater. Store in a gas-tight plastic container. Add 30 mg ofphenolphthalein to the solution to indicate scrubber exhaustion.8.2 Dilution/Buffer Solution, containing the following:Chemical Purpose Concentration, g/

34、LKH2PO4phosphate buffer 6.8Na2HPO47H2O phosphate buffer 55.6MgSO47H2O nutrient 0.0225CaCl2nutrient 0.0275FeCl36H2O nutrient 0.000258.3 Synthetic Municipal Solid Waste, containing the follow-ing:6,7Constituent Chemical Used Dry Weight, %Cellulosics shredded, virgin newsprint 41Inerts pine bark or woo

35、d chips 39Carbohydrates corn starch 5.2Lipids corn oil 5.4Proteins bovine casein 2.0Organic nitrogen urea 1.4Buffer/Nutrient as listed 5.88.4 Polyethylene, or another nonbiodegradable material isthe negative control material. It should be in the same form asthe test materials to provide the same phy

36、sical conditions in allreactors. The synthetic MSW acts as a positive control to verifythe viability of the inoculum, see 13.4 for requirements.9. Hazards9.1 This test method requires the use of hazardous chemi-cals. Avoid contact with the chemicals and follow the manu-facturers instructions and Mat

37、erial Safety Data Sheets.9.2 This test method does not address all of the health andsafety issues related to its use. It is the responsibility of theuser to establish appropriate safety measures.9.3 High-purity high-pressure gases can be dangerous if nothandled correctly. Follow all safety precautio

38、ns and monitorthe system often to ensure proper operation.10. Inoculum10.1 The inoculum should be obtained from MSW or yardwaste that has properly composted for two to four months. Thecompost should be screened with a 2g/kg, thereactors have soured and the results are invalid.12. Calculation12.1 Cal

39、culate the theoretical oxygen uptake from the per-cent by weight of each of the elements:ThOU mg O2/mg! 5 C/37.5 1 H/12.5 1 N/29.21 P/48.4 1 S/66.7 2 O/100 (1)12.2 The theoretical carbon dioxide production is alsodetermined from the elemental analysis and is calculated asfollows:ThCDP mg CO2/mg! 5 %

40、byweight carbon! 3.667! (2)12.3 Calculate the oxygen uptake due to the test material bysubtracting the mean of the control reactors from each of thetest reactors at each data point.12.4 Calculate the total carbon dioxide produced by sub-tracting the mean of the control analytical results from each o

41、fthe test reactors.12.5 Calculate the percent of theoretical of the total oxygenuptake and carbon dioxide by dividing the measured totals bythe calculated ThOU or ThCDP and multiplying by 100.12.6 The acclimation time for the test material and compostmatrix can be determined at the point which the o

42、xygen uptakeexceeded 10 % of the total oxygen uptake for that reactor.12.7 If the test materials oxygen uptake curve shows anegative slope at the beginning of the curve, the test materialacclimation time is calculated at the point were the slope of theoxygen uptake curve becomes positive for a minim

43、um of 24 h.13. Interpretation of Results13.1 The acclimation time can provide valuable informationon the toxicity or inhibition effects of the test material.13.2 The percent of theoretical oxygen uptake is an excel-lent measure of the biodegradability of the test material sinceit represents the mine

44、ralization of carbon in addition to allother oxidative reactions.13.3 The percent of theoretical carbon dioxide productioncan be used to measure biodegradability (with limitations) andcan be used to correlate results with other carbon dioxide basedtest methods.13.4 To ensure an active and viable ino

45、culum, the totaloxygen uptake for the control reactors should exceed 80 g. Ifthis is not observed over the 45 days then the test must beregarded as invalid and should be repeated with new inoculum.14. Report14.1 Report the following information and data with stan-dard deviations and 95 % confidence

46、intervals when appropri-ate:14.1.1 Information on source, dry solids, storage conditions,and age of the inoculum,14.1.2 The ThOU and ThCDP of test materials with elemen-tal analysis results,14.1.3 Test material physical characterization includingsize, shape, weight, dry weight, initial and final rea

47、ctorobservations, and sampling technique used,14.1.4 Percent of ThOU and ThCDP for each test material,14.1.5 Total oxygen uptake and oxygen uptake versus timeplots for entire reactors and test materials only. Rate plots ifapplicable,14.1.6 Acclimation times for test materials,14.1.7 Total carbon dio

48、xide produced and carbon dioxideversus time plots if multiple samples were analyzed during thetest,14.1.8 Temperature plots of each reactor,14.1.9 Total weight loss of reactor contents and dry weightof end reactor contents,14.1.10 Final pH of compost, investigative results if pH isbelow seven, and14

49、.1.11 Full description of test apparatus and documenta-tion of any variations from this test method.15. Precision and Bias15.1 The precision and bias of this test method is beingdetermined.15.2 Typical oxygen uptake and temperature plots are pre-sented in Fig. 2 and Fig. 3. Within-test reproducibility fromthree different test runs are presented in Table 1.Run1isthecontrol reactors with pine bark, Run 2 is with fresh wood chips,and Run 3 is with previously used wood chips.D 5929 96 (2004)4FIG. 2 Typical Control Reactor, Test Reactor, and Net Test ReactorFIG. 3 Typi