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本文(ASTM D932-1985(2009) Standard Test Method for Iron Bacteria in Water and Water-Formed Deposits《水和水沉积物中铁细菌含量的标准试验方法》.pdf)为本站会员(赵齐羽)主动上传,麦多课文库仅提供信息存储空间,仅对用户上传内容的表现方式做保护处理,对上载内容本身不做任何修改或编辑。 若此文所含内容侵犯了您的版权或隐私,请立即通知麦多课文库(发送邮件至master@mydoc123.com或直接QQ联系客服),我们立即给予删除!

ASTM D932-1985(2009) Standard Test Method for Iron Bacteria in Water and Water-Formed Deposits《水和水沉积物中铁细菌含量的标准试验方法》.pdf

1、Designation: D 932 85 (Reapproved 2009)Standard Test Method forIron Bacteria in Water and Water-Formed Deposits1This standard is issued under the fixed designation D 932; the number immediately following the designation indicates the year oforiginal adoption or, in the case of revision, the year of

2、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 test method covers the determination of ironbacteria by examination under the microscope. The methodprovides for

3、the identification of the following genera ofbacteria found in water and water-formed deposits: Sidero-capsa, Gallionella (Dioymohelix), Sphaerotilus, Crenothrix,Leptothrix, and Clonothrix.1.2 The values stated in SI units are to be regarded asstandard. No other units of measurement are included in

4、thisstandard.1.3 This standard does not purport to address the safetyconcerns, if any, associated with its use. It is the responsibilityof the user of this standard to establish appropriate safety andhealth practices and determine the applicability of regulatorylimitations prior to use.2. Referenced

5、 Documents2.1 ASTM Standards:2D 887 Practices for Sampling Water-Formed DepositsD 1129 Terminology Relating to WaterD 1193 Specification for Reagent WaterD 3370 Practices for Sampling Water from Closed Conduits3. Terminology3.1 DefinitionsFor definitions of terms used in this testmethod, refer to Te

6、rminology D 1129.4. Summary of Test Method4.1 The iron bacteria are generally filamentous, typicallyfound in fresh water, and frequently surrounded by a sheathwhich is usually encrusted with iron or manganese, or both (1,2).3However, Starkey (3) reports another type which is classi-fied among the tr

7、ue bacteria. Detection and identification isaccomplished by microscopical examination of sediment fromthe sample. Table 1 and Figs. 1-10 (3) may be used todifferentiate the various types. This test method provides anindication of the density of the iron bacteria and the severity ofthe clogging probl

8、em in pipes caused by these bacteria.5. Significance and Use5.1 Iron bacteria is a general classification for microorgan-isms that utilize ferrous iron as a source of energy and arecharacterized by the deposition of ferric hydroxide in theirmucilaginous sheaths. The process is continuous with theseg

9、rowths, and over a period of time large accumulations ofslimey brown deposits can occur. Iron bacteria may clog waterlines, reduce heat transfer, and cause staining; objectionableodors may arise following death of the bacteria. The organicmatter in the water is consequently increased, and this in tu

10、rnfavors the multiplication of other bacteria.6. Apparatus6.1 Centrifuge, complete with conical tubes.6.2 Microscope that provides a magnification of 400 to10003 and is complete with a suitable light source. Adark-field condenser is desirable.6.3 Pipets, Mohr-type, 10-mL, with an opening 3 to 4 mmin

11、 diameter, for thick samples, and 1-mL Mohr-type pipets forthin samples.6.4 Spatula, small and narrow, for handling thick samples.6.5 Membrane Filter, with appropriate filter-holding assem-bly (see 9.2).7. Reagents7.1 Purity of ReagentsReagent grade chemicals shall beused in all tests. Unless otherw

12、ise 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.4Other grades may beused, provided it is first ascertained that the reagent is ofsufficiently high puri

13、ty to permit its use without lessening theaccuracy of the determination.1This test method is under the jurisdiction of ASTM Committee D19 on Waterand is the direct responsibility of Subcommittee D19.24 on Water Microbiology.Current edition approved May 1, 2009. Published June 2009. Originallyapprove

14、d in 1947. Last previous edition approved in 2002 as D 932 85 (2002).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

15、website.3The boldface numbers in parentheses refer to the list of references at the end ofthis test method.4Reagent Chemicals, American Chemical Society Specifications, AmericanChemical Society, Washington, DC. For Suggestions on the testing of reagents notlisted by the American Chemical Society, se

16、e Annual Standards for LaboratoryChemicals, BDH Ltd., Poole, Dorset, U.K., and the United States Pharmacopeiaand National Formulary, U.S. Pharmacopeial Convention, Inc. (USPC), Rockville,MD.1Copyright ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959, United St

17、ates.TABLE 1 Key for Identification of BacteriaFIG. 1 Siderocapsa treubii. Multiple colonies surrounded by ferrichydrate. Magnification about 500 3 .Fig.4ofRef(5)FIG. 2 Gallionella major. Cells at the ends of excretion bandsundergoing division. Magnification about 1180 3 .Fig.3ofRef(6)D 932 85 (2009

18、)27.2 Purity of WaterUnless otherwise indicated, referencesto water shall be understood to mean reagent water conformingto Specification D 1193, Type II.7.3 Ammonium Oxalate-Crystal Violet SolutionPrepareHuckers modification of the Gram stain (4) by mixing asolution of 2.0 g of crystal violet (90 %

19、dye content) in 20 mLof ethyl alcohol (95 % with a solution of 0.8 g of ammoniumoxalate monohydrate (NH4)2C2O4H2O) in 80 mL of water.7.4 Hydrochloric Acid (1 + 4)Mix 1 volume of hydro-chloric acid (HCl, sp gr 1.19) with 4 volumes of water.7.5 Iodine SolutionPrepare Grams modification ofLugols soluti

20、on (4) by dissolving1gofiodine in a solutecontaining2gofpotassium iodide (KI) in 10 mL of water anddiluting the resulting solution to 300 mL with water.7.6 Filter Paper or Blotter.7.7 Slides, standard type, 25 by 76-mm (1 by 3 in.) witheither plain or frosted end.7.8 Cover Glasses, round or square t

21、ype, 19 mm (34 in.) indiameter.8. Sampling8.1 Collect the samples in accordance with either PracticesD 887 or D 3370, whichever is applicable.8.2 Obtain a 500-mL (1-pt) sample of water, using a sterile1-L (1-qt) bottle. The bottle should not be more than half-filledbecause of the oxygen demand of su

22、spended matter; filling thebottle may cause the sample to become anaerobic.8.3 If the number of iron bacteria are very low or that theyare just becoming established in the system, use a small sideFIG. 3 Gallionella major. Curved cells at the ends of excretionbands. Magnification about 1120 3 .Fig.6o

23、fRef(6)FIG. 4 Sphaerotilus dichotoma. Sketch showing false branching.Magnification about 230 3 .Fig.3b of Ref (7)FIG. 5 Crenothrix polyspora. Sketch showing details of falsebranching of cells within sheath. Magnification about 380 3 .Plate 1, Fig. A of Ref (8)D 932 85 (2009)3stream filter to collect

24、 the sample to be examined. The watersuspected of containing iron bacteria should be filtered througha highly retentive filter paper (or some other comparablemedia) for 24 h. Centrifugation or membrane filtration issatisfactory also. The flow rate of the water should be at themaximum filtering capac

25、ity of the material employed.8.4 Regardless of the method used to concentrate the solidsin the water, keep them moist until examined.8.5 Mud samples should be collected from the mud-waterinterface for maximum bacterial populations.8.6 Transfer the deposit or mud samples to wide-mouthbottles and add

26、clean, chlorine-free water to cover the depositsand maintain moisture until examined. Protect the samplesfrom sunlight and hold at 4C during transportation andstorage.8.7 As soon as possible after collection of the solids,microscopically examine them for the presence of iron bacte-ria.9. Procedure9.

27、1 Place a portion of the sample on the slide and apply acover glass. A spatula or wide-mouth pipet can be used totransfer the sample to the slide. Use a pipet when flocs ofmaterial are encountered, as the flocs settle to the tip when thepipet is held in a vertical position, and concentrate in the fi

28、rstdrop. In the case of very dilute solids or a water sample,concentrate the organisms by centrifuging, pour off the super-natant liquid, and repeat if necessary.9.2 An alternative procedure is to filter a suitable volume ofthe dilute solids or the entire water sample through a 0.45-mmembrane filter

29、 in an appropriate membrane filtration assem-bly (holder, tubing, trap, flasks and vacuum pump). For this testit is not necessary to sterilize the filter assembly for eachsample, but the assembly should be thoroughly cleaned be-tween tests.9.3 Examine the slide under the microscope to determine ifen

30、crusted or colorless sheaths are present. Note the presence ofthe twisted stalks of Gallionella at this point, since treatmentwith acid in accordance with 9.4 will dissolve the delicatestalks.FIG. 6 Crenothrix polyspora. Cells enclosed within a sheath of ferric hydrate and showing false branching. M

31、agnification about 390 3 .Plate3,Fig.BofRef(8)D 932 85 (2009)49.4 Place the HCl (1 + 4) at one side of the cover glass anddraw it underneath by absorbing the liquid at the opposite sideby means of a filter paper or blotter. Continue this procedureuntil no more yellow ferric chloride is evident in th

32、e solution.Take care that the flow of the liquid is not fast, or the samplemay be drawn to the absorbent material. This treatmentremoves the iron deposited in the sheaths of the bacteria andallows the cells to be seen.9.5 In a similar manner, rinse the iodine solution under thecover glass until the

33、color of the liquid becomes yellow or thefilter paper becomes colored. The iodine stains the bacterialcells brown and makes them more easily visible.9.6 Examine the slide under a microscope, using a high-power, dry objective, for the presence of Sphaerotilus, Creno-thrix, Leptothrix, and Clonothrix.

34、 If used carefully, an oil-immersion lens may be helpful.9.7 Prepare a new slide by placing a drop of the sample ona clean slide and allowing it to air-dry. Then stain it for 1 minwith ammonium oxalate-crystal violet solution, wash it withwater, and allow it to dry. Examine the slide under anoil-imm

35、ersion lens for the presence of Siderocapsa, which willappear violet colored.10. Report10.1 The report shall state “Present” or“ Not found, prob-ably absent.” Make a statement as to the relative abundance ofthe organisms present. Make a negative report only afterexamination of several slides.11. Pre

36、cision and Bias11.1 Since this standard is a qualitative type test, precisionand bias statements cannot be provided.FIG. 7 Leptothrix ochracea. Cells coming out of their sheath.Magnification about 2200 3 . Plate 4, Fig. 20 of Ref (9)FIG. 8 Leptothrix ochracea. Sheaths from an accumulation ofprecipit

37、ated ferric hydrate in iron bearing water. Magnificationabout 390 3 .Fig.5ofRef(7)D 932 85 (2009)5FIG. 9 Clonothrix ferruginea. Sketch showing cells enclosed within sheath andfalse branching. Magnification about 430 3 .Fig.4ofRef(7)D 932 85 (2009)6REFERENCES(1) Bergey, D. H., Manual of Determinative Bacteriology, 8th Edition,Williams or through the ASTM website(www.astm.org).FIG. 10 Crenothrix polyspora. Conidia can be seen inside and coming out at ends of filaments. Magnification about 345 3 .Fig. 5 of Ref (9)D 932 85 (2009)7

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