ASTM D4096-1991(2009) Standard Test Method for Determination of Total Suspended Particulate Matter in the Atmosphere (High-Volume Sampler Method)《空气中悬浮粒子的标准试验方法(大容器取样器法)》.pdf

《ASTM D4096-1991(2009) Standard Test Method for Determination of Total Suspended Particulate Matter in the Atmosphere (High-Volume Sampler Method)《空气中悬浮粒子的标准试验方法(大容器取样器法)》.pdf》由会员分享，可在线阅读，更多相关《ASTM D4096-1991(2009) Standard Test Method for Determination of Total Suspended Particulate Matter in the Atmosphere (High-Volume Sampler Method)《空气中悬浮粒子的标准试验方法(大容器取样器法)》.pdf（9页珍藏版）》请在麦多课文档分享上搜索。

1、Designation: D 4096 91 (Reapproved 2009)Standard Test Method forDetermination of Total Suspended Particulate Matter in theAtmosphere (HighVolume Sampler Method)1This standard is issued under the fixed designation D 4096; the number immediately following the designation indicates the year oforiginal

2、adoption 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.1. Scope1.1 This test method provides for sampling a large volumeof atmosphere,

3、1600 to 2400 m3(55 000 to 85 000 ft3), bymeans of a high flow-rate vacuum pump at a rate of 1.13 to1.70 m3/min (40 to 60 ft3/min) (1, 2, 3 and 4).21.2 This flow rate allows suspended particles having diam-eters of less than 100 m (stokes equivalent diameter) to becollected. However, the collection e

4、fficiencies for particleslarger than 20 m decreases with increasing particle size and itvaries widely with the angle of the wind with respect to theroof ridge of the sampler shelter and with increasing speed (5).When glass fiber filters are used, particles within the size rangeof 100 to 0.1 m diamet

5、ers or less are ordinarily collected.1.3 The upper limit of mass loading will be determined byplugging of the filter medium with sample material, whichcauses a significant decrease in flow rate (see 6.4). For verydusty atmospheres, shorter sampling periods will be necessary.The minimum amount of par

6、ticulate matter detectable by thismethod is 3 mg (95 % confidence level). When the sampler isoperated at an average flow rate of 1.70 m3/min (60 ft3/min) for24 h, this is equivalent to 1 to 2 g/m3(3).1.4 The sample that is collected may be subjected to furtheranalyses by a variety of methods for spe

7、cific constituents.1.5 Values stated in SI units shall be regarded as thestandard. Inch-pound units are shown for information only.1.6 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 establi

8、sh appro-priate safety and health practices and determine the applica-bility of regulatory limitations prior to use.2. Referenced Documents2.1 ASTM Standards:3D 1356 Terminology Relating to Sampling and Analysis ofAtmospheresD 3631 Test Methods for Measuring Surface AtmosphericPressureE1 Specificati

9、on for ASTM Liquid-in-Glass Thermometers2.2 Other Documents:EPA-600/9-76-005 Quality Assurance Handbook for AirPollution Measurement Systems, Vol I, Principles (De-cember 1984 Rev.)4EPA-600/4-77-027a Quality Assurance Handbook for AirPollution Measurement Systems, Vol II, Ambient AirSpecific Methods

10、43. Terminology3.1 DefinitionsFor definitions of other terms used in thistest method, refer to Terminology D 1356.3.2 Descriptions of Terms:3.2.1 absolute filtera filter or filter medium of ultra-highcollection efficiency for very small particles (submicrometresize) so that essentially all particles

11、 of interest or of concern arecollected. Commonly, the efficiency is in the region of 99.95 %or higher for a standard aerosol of 0.3-m diameter (seePractice D 2986).3.2.2 Hi-Vol (The High-Volume Air Sampler)a device forsampling large volumes of an atmosphere, collection of thecontained particulate m

12、atter by filtration, and consisting of ahigh-capacity air mover, a filter to collect suspended particles,and means for measuring, or controlling, or both, the flow rate.3.2.3 primary flow-rate standarda device or means ofmeasuring flow rate based on direct primary observations, suchas time and physi

13、cal dimensions.3.2.4 secondary flow-rate standardA flow-rate-measuringdevice, such as an orifice meter, that has been calibratedagainst a primary standard.3.2.5 spirometera displacement gasometer consisting ofan inverted bell resting upon or sealed by liquid (or othermeans) and capable of showing th

14、e amount of gas added to orwithdrawn from the bell by the displacement (rise or fall) of thebell.1This test method is under the jurisdiction of ASTM Committee D22 on AirQuality and is the direct responsibility of Subcommittee D22.03 on AmbientAtmospheres and Source Emissions.Current edition approved

15、 March 1, 2009. Published March 2009. Originallyapproved in 1982. Last previous edition approved in 2003 as D 4096 91 (2003).2The boldface numbers in parentheses refer to the list of references at the end ofthis practice.3For referenced ASTM standards, visit the ASTM website, www.astm.org, orcontact

16、 ASTM Customer Service at serviceastm.org. For Annual Book of ASTMStandards volume information, refer to the standards Document Summary page onthe ASTM website.4Available from U.S. Environmental Protection Agency, Environmental Moni-toring Systems Laboratory, QualityAssurance Division, Research Tria

17、ngle Park, NC27711. Attn: Distribution Record System.1Copyright ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959, United States.3.2.6 working flow-rate standarda flow rate measuringdevice, such as an orifice meter, that has been calibratedagainst a secondary f

18、low-rate standard. The working flow-ratestandard is used to calibrate a flow measuring or flow rateindicating instrument.3.2.7 constant flow high-volume samplera high volumesampler that is equipped with a constant flow control device.4. Summary of Test Method4.1 This test method describes typical eq

19、uipment, opera-tional procedures, and a means of calibration of the equipmentusing an orifice flowrate meter. (See also Annex A1.)4.2 Air is drawn into a covered housing and through a filterby means of a high-flow-rate air mover, so that particulatematerial collects on the filter surface.4.3 The amo

20、unt of particulate matter accumulated on thefilter over a specified period of time is measured by weighinga preweighed filter after exposure. The flow rate of air sampledis measured over the test period. The result is expressed interms of particulate mass collected (or loading) per unit volumeof air

21、 sampled, usually as micrograms per cubic metre (g/m3).The volume of air sampled is recorded by measurement of thedevice flow rate(s).4.4 The volume of air sampled is determined by means of aflow-rate indicator. The instrument flow-rate indicator is cali-brated against a reference orifice meter. The

22、 latter is a workingstandard which, in turn, has been calibrated against a secondaryflow meter certified by the U.S. National Institute of Standardsand Technology.4.5 Airborne particulate matter retained on the filter may beexamined or analyzed by a variety of methods. Specificprocedures are not inc

23、luded in this method but are the subjectof separate standard methods.5. Significance and Use5.1 The Hi-Vol sampler is commonly used for the collectionof the airborne particulate component of the atmosphere. Somephysical and chemical parameters of the collected particulatematter are dependent upon th

24、e physical characteristics of thecollection system and the choice of filter media. A variety ofoptions available for the Hi-Vol sampler give it broad versa-tility and allow the user to develop information about the sizeand quantity of airborne particulate material and, using subse-quent chemical ana

25、lytical techniques, information about thechemical properties of the particulate matter.5.2 This test method presents techniques that when uni-formly applied, provide measurements suitable for intersitecomparisons.5.3 This test method measures the atmosphere presented tothe sampler with good precisio

26、n, but the actual dust levels inthe atmosphere can vary widely from one location to another.This means that sampler location may be of paramountimportance, and may impose far greater variability of resultsthan any lack of precision in the method of measurement. Inparticular, localized dust sources m

27、ay exert a major influenceover a very limited area immediately adjacent to such sources.Examples include unpaved streets, vehicle traffic on roadwayswith a surface film of dust, building demolition and construc-tion activity, or nearby industrial plants with dust emissions. Insome cases, dust levels

28、 measured close to such sources may beseveral times the community wide levels exclusive of suchlocalized effects (see Practice D 1357).6. Interferences6.1 Large extraneous objects, such as insects, may be sweptinto the filter and become weighed unnoticed.6.2 Liquid aerosols, such as oil mists and fo

29、g droplets, areretained by the filter. If the amount of liquid so collected issizable, the filter can become wet and its function and massimpaired.6.3 Any gaseous or vaporous constituent of the atmosphereunder test that is reactive with or sorptive upon the filter or itscollected matter will be reta

30、ined and weighed as particulatematter.6.4 As the filter becomes loaded with collected matter, thesampling rate is reduced. If a significant drop in flow rateoccurs, the average of the initial and final flow rate calculatedin 10.1 will not give an accurate estimate of total flow duringthe sampling pe

31、riod. The magnitude of such errors will dependon the amount of reduction of airflow rate and on the variationof the mass concentration of dust with time during the 24-hsampling period. As an approximate guideline, any sampleshould be suspect if the final flow rate is less than one half theinitial ra

32、te. A continuous record of flow rate will indicate theoccurrence of this problem, or a constant-flow high-volumesampler may be used to eliminate the problem.6.5 The possibility of power failure or voltage changeduring the test period would lead to an error, depending on theextent and time duration o

33、f such failure.Acontinuous record offlow rate is desirable.6.6 The passive loading of the filter that can occur if it is leftin place for any time prior to or following a sampling periodcan introduce significant error. For unattended operation, asampler equipped with shutters shall be used.6.7 If tw

34、o or more samplers are used at a given location,they should be placed at least2m(6ft)apart so that onesampler will not affect the results of an adjacent sampler.6.8 Wind tunnel studies have shown significant possiblesampling errors as a function of sampler orientation in atmo-spheres containing high

35、 relative concentrations of large par-ticles (5).6.9 Metal dusts from motors, especially copper, may sig-nificantly contaminate samples under some conditions.6.10 Under some conditions, atmospheric SO2and NOxmay interfere with the total mass determination (6).7. Apparatus7.1 The essential features o

36、f a typical high-volume samplerare shown in the diagram of Fig. 1 and Fig. 2. It is a compactunit consisting of a protective housing, an electric motor-driven, high-speed, high-volume air mover, a filter holdercapable of supporting a 203 by 254-mm (8 by 10-in.) filter atthe forward or entrance end,

37、and at the exit end, means foreither indicating or controlling the air flow rate, or both, overthe range of 1.13 to 1.70 m3/min (40 to 60 ft3/min). Designsalso exist in which a flow controller is located between thefilter and the blower. For unattended operation, a samplerequipped with shutters to p

38、rotect the filter is required.D 4096 91 (2009)27.2 A calibrator kit is required. This contains a workingflow-rate standard of appropriate range in the form of an orificewith its own calibration curve. The kit includes also a set offive flow-control plates. These kits are available from mostsupply ho

39、uses that deal in apparatus for air sampling andanalysis.7.3 A large desiccator or air conditioned room is requiredfor filter conditioning, storage, and weighing. Filters must bestored and conditioned at a temperature of 15 to 27C and arelative humidity between 0 and 50 %.7.4 An analytical balance c

40、apable of reading to 0.1 mg, andhaving a capacity of at least5gisnecessary. It is very desirableto have a weighing chamber of adequate size with a supportthat is capable of accommodating the filter without rolling orfolding it or exposing it to drafts during the weighing opera-tion.7.5 Barograph or

41、Barometer, capable of measuring to thenearest 0.1 kPa (1 mm Hg) meeting the requirements of TestMethods D 3631.7.6 ThermometerASTM Thermometer 33C, meeting therequirements of Specification E1.7.7 Clock, capable of indicating 24 h 6 2 min.7.8 Flow-Rate Recorder, capable of recording to the nearest0.0

42、3 m3/min (1.0 ft3/min).7.9 Differential Manometer, capable of measuring to 4 kPa(40 mm Hg).8. Reagents and Materials8.1 Filter Medium:8.1.1 In general, the choice of a filter medium will dependon the purpose of the test. For any given standard test methodthe appropriate medium will be specified. How

43、ever, it isimportant to be aware of certain filter characteristics that canaffect selection and use.8.1.2 Glass-Fiber Filter MediumThis type is most widelyused for determination of mass loading. Weight stability withrespect to moisture is an attractive feature. High-efficiency orabsolute types are p

44、referred and will collect all airborneparticles of practically every size and description. The follow-ing characteristics are typical:Fiber content All-glass-usually mixed sizesBinder Below 5 % (zero for binderless types)Thickness Approximately 0.5 mmPinholes NoneDOP smoke test (PracticeD 2986)0.05

45、% penetration, 981 Pa (100 mm of water)at 8.53 m/min (28 ft/min)Particulate matter collected on glass-fiber medium can beanalyzed for many constituents. If chemical analysis is con-templated binderless filters should be used. It must be borne inmind, however, that glass is a commercial product gener

46、allycontaining test-contaminating materials. The high ratio ofsurface area to glass volume permits extraction of suchcontaminants, especially if strong reagents are employed.8.1.3 Silica Fiber FiltersWhere it may be required ordesirable to use a mineral fiber filter, which may later beextracted by s

47、trong reagents, silica fiber filters can be used.Such fibers are usually made by leaching glass fibers withstrong mineral acids followed by washing with deionizedwater. The fibers are rather weak but can be formed into filtersheets using little or no binder. These filters are commerciallyavailable (

48、7).8.1.4 Cellulose PapersFor some purposes it is desirableto collect airborne particles on cellulose fiber filters. Low-ashpapers are especially useful where the filter is to be destroyedby ignition or chemical digestion. However, these papers havehigher flow resistance (lower sampling rate) and hav

49、e beenreported to have much poorer collection efficiency than theglass fiber media (8). Furthermore, cellulose is very sensitive tomoisture conditions and even with very careful conditioningbefore and after sampling it is difficult to make an accurateweighing of the collected particles. It is usually necessary to dothe weighing with the filter enclosed in a lightweight metal canwith a tight lid.9. Procedure9.1 The Hi-Vol sampler can be used in a number of ways.Variations of procedure may include the kind of filter medium,the surface area of the filter, flow veloc