ASTM D3650-1993(2011) Standard Test Method for Comparison of Waterborne Petroleum Oils By Fluorescence Analysis《用荧光分析法比较水中石油润滑油的标准试验方法》.pdf
《ASTM D3650-1993(2011) Standard Test Method for Comparison of Waterborne Petroleum Oils By Fluorescence Analysis《用荧光分析法比较水中石油润滑油的标准试验方法》.pdf》由会员分享,可在线阅读,更多相关《ASTM D3650-1993(2011) Standard Test Method for Comparison of Waterborne Petroleum Oils By Fluorescence Analysis《用荧光分析法比较水中石油润滑油的标准试验方法》.pdf(5页珍藏版)》请在麦多课文档分享上搜索。
1、Designation: D3650 93 (Reapproved 2011)Standard Test Method forComparison of Waterborne Petroleum Oils ByFluorescence Analysis1This standard is issued under the fixed designation D3650; the number immediately following the designation indicates the year oforiginal adoption or, in the case of revisio
2、n, 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. Scope*1.1 This test method covers the comparison of waterbornepetroleum oils with oils from possible sources by
3、means offluorescence spectroscopy (1).2Useful references for this testmethod include: (2) and (3) for fluorescence analysis in generaland (4), (5), and (6) for oil spill identification includingfluorescence.1.2 This test method is applicable to crude or refinedpetroleum products, for any sample of n
4、eat oil, waterborne oil,or sample of oil-soaked material. Unless the samples arecollected soon after the spill occurs, it is not recommended thatvolatile fuels such as gasoline, kerosine, and No. 1 fuel oils beanalyzed by this test method, because their fluorescencesignatures change rapidly with wea
5、thering. Some No. 2 fueloils and light crude oils may only be identifiable up to 2 daysweathering, or less, depending on the severity of weathering. Ingeneral, samples weathered up to 1 week may be identified,although longer periods of weathering may be tolerated forheavy residual oils, oil weathere
6、d under Arctic conditions, oroil that has been protected from weathering by collecting in athick layer.1.3 The values stated in SI units are to be regarded asstandard. No other units of measurement are included in thisstandard.1.4 This standard does not purport to address all of thesafety concerns,
7、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.2. Referenced Documents2.1 ASTM Standards:3D1129 Terminology Relating to WaterD1193 Spec
8、ification for Reagent WaterD3325 Practice for Preservation of Waterborne Oil SamplesD3326 Practice for Preparation of Samples for Identifica-tion of Waterborne OilsD3415 Practice for Identification of Waterborne OilsD4489 Practices for Sampling of Waterborne OilsE131 Terminology Relating to Molecula
9、r SpectroscopyE275 Practice for Describing and Measuring Performanceof Ultraviolet and Visible SpectrophotometersE520 Practice for Describing Photomultiplier Detectors inEmission and Absorption Spectrometry3. Terminology3.1 DefinitionsFor definitions of terms used in this testmethod refer to Termino
10、logy D1129, Practice D3415, andTerminology E131.4. Summary of Test Method4.1 This test method consists of fluorescence analyses ofdilute solutions of oil in spectroquality cyclohexane. In mostcases the emission spectra, with excitation at 254 nm, over thespectral range from 280 to 500 nm, are adequa
11、te for matching.4.2 Identification of the sample is made by direct visualcomparison of the samples spectrum with the spectra frompossible source samples.NOTE 1When weathering has occurred, it may be necessary toconsider known weathering trends when matching spectra (Fig. 1 and Fig.2).1This test meth
12、od is under the jurisdiction of ASTM Committee D19 on Waterand is the direct responsibility of Subcommittee D19.06 on Methods forAnalysis forOrganic Substances in Water.Current edition approved May 1, 2011. Published June 2011. Originallyapproved in 1978. Last previous edition approved in 2006 as D3
13、650 93 (2006).DOI: 10.1520/D3650-93R11.2The boldface numbers in parentheses refer to the references at the end of thistest method.3For referenced ASTM standards, visit the ASTM website, www.astm.org, orcontact ASTM Customer Service at serviceastm.org. For Annual Book of ASTMStandards volume informat
14、ion, refer to the standards Document Summary page onthe ASTM website.1*A Summary of Changes section appears at the end of this standard.Copyright ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959, United States.5. Significance and Use5.1 This test method is use
15、ful for rapid identification ofwaterborne petroleum oil samples as well as oil samplesobtained from fuel or storage tanks, or from sand, vegetation,or other substrates. This test method is applicable to weatheredand unweathered neat oil samples.5.2 The unknown oil is identified through the compariso
16、n ofthe fluorescence spectrum of the oil with the spectra (obtainedat similar instrumental settings on the same instrument) ofpossible source samples. A match of the entire spectrumbetween the unknown and possible source sample indicates acommon source.6. Interferences6.1 The fluorescence spectrum w
17、ill be distorted if an oilsample has been contaminated by an appreciable amount, forexample, 1 % of common chemical impurities such as otheroils that are fluorescent on excitation at 254 nm.NOTE 2Storage of samples in improper containers (for example,plastics) may result in contamination. This inter
18、ference can be eliminatedby observing proper procedures for collection and preservation ofsamples. Refer to Practice D3325.NOTE 3“Spectroquality” cyclohexane may not have a low enoughfluorescence solvent blank. Lots vary in the content of fluorescentimpurities, which may increase with storage time e
19、ven if the bottle isunopened.6.2 Oil residues may build up in fluorescence cells particu-larly after prolonged usage with heavy oils. In such a case,follow the procedure using nitric acid for cleaning glassware(10.1.3).6.3 Possible interferences from Raman or RayleighTyndallscattering are not observ
20、ed in the emission scan rangesselected.7. Apparatus7.1 Fluorescence Spectrophotometer (or Spectro-fluorometer)An instrument recording in the spectral range of220 nm to at least 600 nm for both excitation and emissionresponses and capable of meeting the specifications stated inTable 1.7.2 Excitation
21、SourceA high-pressure xenon lamp (a150-W xenon lamp has proven acceptable). Other continuumsources, such as deuterium or high-pressure xenon-mercury,which have sufficient intensity in the ultraviolet region, couldbe used as excitation sources.NOTE 4Line sources such as a low-pressure mercury lamp ma
22、y alsobe used for excitation at 254 nm, if the flexibility of using arbitraryexcitation wavelengths or excitation spectra is not desired and if sourceintensity is adequate.7.3 Fluorescence CellsStandard cells, made fromfluorescence-free fused silica with a pathlength of 10 mm anda height of 45 mm.7.
23、4 Recorder or ComputerStrip chart or X-Y recorder,with a response time less than 1 s for full-scale deflection, or acomputer capable of digitizing the data at a rate of 1 data pointper nanometre.7.5 Cell-Filling DeviceDisposable Pasteur capillary pi-pet.7.6 Volumetric FlasksLow-actinic glass, ground
24、-glassstoppered volumetric flasks (100-mL).7.7 Micropipet, 10 to 50-L capacity.7.8 Analytical Balance, with a precision of at least 60.1 mg.FIG. 1 Fluorescence Spectra for a Typical No. 2 Fuel Oil(Unweathered and Weathered One Day)FIG. 2 Fluorescence Spectra for a Typical No. 6 Fuel Oil(Unweathered
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