1、Designation: E2515 11 (Reapproved 2017)Standard Test Method forDetermination of Particulate Matter Emissions Collected bya Dilution Tunnel1This standard is issued under the fixed designation E2515; the number immediately following the designation indicates the year oforiginal adoption or, in the cas
2、e 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 is applicable for the determination ofparticulate matter emissions from so
3、lid-fuel-burning appli-ances including woodstoves, pellet-burning appliances,factory-built fireplaces, masonry fireplaces, masonry heaters,indoor furnaces, and indoor and outdoor hydronic heaterswithin a laboratory environment.1.2 Analytes will be a particulate matter (PM) with no CASnumber assigned
4、. For data quality objectives, see AppendixX1.1.3 The values stated in SI units are to be regarded asstandard. The values given in parentheses are mathematicalconversions to inch-pound units that are provided for informa-tion only and are not considered standard.1.4 This test method does not purport
5、 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, health, and environmental practices and deter-mine the applicability of regulatory limitations prior to use.1.5 This international standard w
6、as developed in accor-dance with internationally recognized principles on standard-ization established in the Decision on Principles for theDevelopment of International Standards, Guides and Recom-mendations issued by the World Trade Organization TechnicalBarriers to Trade (TBT) Committee.2. Referen
7、ced Documents2.1 ASTM Standards:2D2986 Practice for Evaluation of Air Assay Media by theMonodisperse DOP (Dioctyl Phthalate) Smoke Test(Withdrawn 2004)3E2558 Test Method for Determining Particulate MatterEmissions from Fires in Wood-Burning FireplacesE2618 Test Method for Measurement of Particulate
8、Emis-sions and Heating Efficiency of Solid Fuel-Fired HydronicHeating AppliancesE2779 Test Method for Determining Particulate MatterEmissions from Pellet HeatersE2780 Test Method for Determining Particulate MatterEmissions from Wood HeatersE2817 Test Method for Test Fueling Masonry Heaters2.2 AISI D
9、ocument:4AISI 316 Stainless Steel2.3 NIST Document:5NIST Monograph 175 Standard Limits of Error3. Terminology3.1 Definitions of Terms Specific to This Standard:3.1.1 laboratory environmentthe area or room that is usedfor the storage, weighing, assembly, disassembly, and desicca-tion of filters and r
10、elated equipment (sample recovery andanalysis).3.1.2 particulate matter (PM)all gas-borne matter result-ing from combustion of solid fuel, as specified in the applianceoperation test method, that is collected and retained by thespecified filter and probe system under the conditions of thetest.3.1.3
11、test facilitythe area in which the tested appliance isinstalled, operated, and sampled for emissions.1This test method is under the jurisdiction of ASTM Committee E06 onPerformance of Buildings and is the direct responsibility of Subcommittee E06.54on Solid Fuel Burning Appliances.Current edition ap
12、proved Sept. 1, 2017. Published September 2017. Originallyapproved in 2007. Last previous edition approved in 2011 as E2515 11. DOI:10.1520/E2515-11R17.2For referenced ASTM standards, visit the ASTM website, www.astm.org, orcontact ASTM Customer Service at serviceastm.org. For Annual Book of ASTMSta
13、ndards volume information, refer to the standards Document Summary page onthe ASTM website.3The last approved version of this historical standard is referenced onwww.astm.org.4Available from American Iron and Steel Institute (AISI), 25 MassachusettsAve., NW, Suite 800, Washington, DC 20001, http:/ww
14、w.steel.org.5Available from National Institute of Standards and Technology (NIST), 100Bureau Dr., Stop 1070, Gaithersburg, MD 20899-1070, http:/www.nist.gov.Copyright ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959. United StatesThis international standard wa
15、s developed in accordance with internationally recognized principles on standardization established in the Decision on Principles for theDevelopment of International Standards, Guides and Recommendations issued by the World Trade Organization Technical Barriers to Trade (TBT) Committee.14. Summary o
16、f Test Method4.1 The total flue-gas exhaust from a solid fuel burningappliance is collected along with ambient dilution air with acollection hood. Duplicate sampling trains are used to extractgas samples from the dilution tunnel for determination ofparticulate matter concentrations. Each sample trai
17、n has twoglass fiber filters in series. The samples are withdrawn at aconsistently proportional rate from sampling points located atthe centroid of a sampling tunnel. During sampling, the filtersare maintained at a temperature less than 32 C (90 F). Themass of the sampled particulate matter is deter
18、mined gravi-metrically after the removal of uncombined water. The totalparticulate matter mass collected on the filters and in the probeand front filter housing are multiplied by the ratio of thedilution tunnel flow to sample flow to determine the totalparticulate emissions during a test.4.2 The sam
19、pling system for this test method consists ofduplicate dual-filter dry sampling trains. Both of the particulatesampling trains are operated simultaneously at a sample flowrate not to exceed 0.007 m3/min (0.25 cfm min). The totalparticulate results obtained from the two sampling trains areaveraged to
20、 determine the particulate emissions and are com-pared as a quality control check on the data validity.4.3 The particulate concentration results for each samplingtrain is adjusted by the particulate concentration result from asingle room air sample blank collected and processed the sameas the diluti
21、on tunnel particulate sampling trains described in4.2, except that only one filter is used in the sampling train. Ametering system as described in 6.1.1.4 shall be used todetermine the volume of room air collected. The sample flowrate shall not exceed 0.007 m3/min (0.25 cfm).4.4 Appliances tested by
22、 this test method are to be fueledand operated as specified in appliance-specific test methodssuch as, but not limited to, Test Methods E2558, E2618,E2779, E2780,orE2817.5. Safety5.1 DisclaimerThis test method may involve hazardousmaterials, operations, and equipment. This test method may notaddress
23、 all of the safety problems associated with its use. It isthe responsibility of the user of this test method to establishappropriate safety and health practices and to determine theapplicability of regulatory limitations prior to performing thistest method.6. Equipment and Supplies6.1 Sample Collect
24、ionThe following equipment is re-quired for sample collection:6.1.1 Particulate Sampling TrainTwo separate, completeparticulate sampling trains (also referred to as “samplingtrains”) are required for each test run. The filter face velocityshall not exceed 150 mm/sec (30 ft/min) during the test run.T
25、he dry gas meter shall be calibrated for the same flow raterange as encountered during the test runs. The sampling trainconfiguration is shown in Fig. 1 and consists of the followingcomponents.6.1.1.1 Filter Holder AssemblyThe filter holder assemblyis shown in Fig. 2 and consists of the following co
26、mponents:(1) Filter HoldersThe primary (front) filter holder shallbe aluminum or PTFE.6The backup (rear) filter holder may bemade of materials such as polycarbonate.7With such plasticmaterials, it is recommended not to use solvents when cleaningthe filter holder parts. Mild soap and distilled water
27、can be usedfor cleaning plastic filter holder parts. The two filter holders6The Pall (Gelman) 1235 filter holder has been found suitable for this purpose.If you are aware of alternative suppliers, please provide this information to ASTMInternational Headquarters. Your comments will receive careful c
28、onsideration at ameeting of the responsible technical committee,1which you may attend.7The Pall (Gelman) 1119 filter holder has been found suitable for this purpose.If you are aware of alternative suppliers, please provide this information to ASTMInternational Headquarters. Your comments will receiv
29、e careful consideration at ameeting of the responsible technical committee,1which you may attend.FIG. 1 Particulate Sampling TrainE2515 11 (2017)2shall be placed in series with the backup filter holder located 25to 100 mm (1 to 4 in.) downstream from the primary filterholder. The filter holders shal
30、l be capable of holding a filterwith 47 mm diameter. The holder design shall provide apositive seal against leakage from the outside or around thefilters. The use of a porous glass or ceramic frit to support thefirst (front) filter is not allowed. Any type of filter support isallowed for the second
31、(rear) filter.(2) Probe AssembliesProbe assemblies shall consist ofthe following components assembled to provide a leak-tightseal:(a) Front half of front filter holder as specified in6.1.1.1(1).(b) ProbeThe probe shall be constructed from seamlessstainless steel (that is, AISI 316 or grade more corr
32、osionresistant) 6.35 mm (14 in.) outside diameter (O.D.) and 0.30 to0.45 m (12 to 18 in.) in length, with a wall thickness such thatthe total weight of the probe and front filter housing can beweighed to an accuracy of 0.1 mg.(3) Filters in accordance with 7.1.1.(4) Filter Gaskets.6.1.1.2 Filter Tem
33、perature Monitoring SystemA tempera-ture sensor capable of measuring with an accuracy of 2.2 C(4.0 F) or 0.75 % of the reading, which ever is greater andmeeting the calibration requirements specified in 8.2. Thesensor shall be installed at the exit side of the front filter holderso that the sensing
34、tip of the temperature sensor is in directcontact with the sample gas as shown in Fig. 2.6.1.1.3 DryerAny system capable of removing water fromthe sample gas to less than 1.5 % moisture (volume percent)prior to the metering system. The system shall include atemperature sensor for demonstrating that
35、sample gas tempera-ture exiting the dryer is less than 27 C (80 F). See Fig. 1 forlocation of the dryer.6.1.1.4 Metering SystemThe metering system shall in-clude a vacuum gauge, leak-free pump, temperature sensorscapable of measuring with an accuracy of 2.2 C (4.0 F) or0.75 % of the reading, which e
36、ver is greater and meeting thecalibration requirements specified in 8.2, gas metering systemcapable of measuring the total volume sampled to within 62 % of the measured value, and related equipment, as shown inFig. 1.6.1.2 BarometerMercury, aneroid, or other barometer ca-pable of measuring atmospher
37、ic pressure with an accuracy of62.5 mm Hg (0.1 in.). Must meet calibration requirementsspecified in 8.3.NOTE 1The barometric pressure reading may be obtained from anearby National Weather Service station. In this case, the station value(which is the absolute barometric pressure) shall be requested a
38、nd anadjustment for elevation differences between the weather station andsampling point shall be made at a rate of minus 2.5 mm Hg (0.1 in.) per30 m (100 ft) elevation increase or plus 2.5 mm Hg (0.1 in) per 30 m (100ft) elevation decrease.6.1.3 Dilution Tunnel Gas Temperature MeasurementAtemperatur
39、e sensor capable of measuring with an accuracy of2.2 C (4.0 F) or 0.75 % of the reading, which ever is greaterand meeting the calibration requirements specified in 8.2.6.1.4 Pitot TubeA standard Pitot tube designed accordingto the criteria given in 6.1.4.1 shall be used to measure flow inthe dilutio
40、n tunnel. Pitot tubes will have an assumed Pitotcoefficient of 0.99 and be designed according to these specifi-cations:6.1.4.1 Standard Pitot design (see Appendix X2 for anexample);6.1.4.2 Hemispherical, ellipsoidal, or conical tip;6.1.4.3 A minimum of six diameters straight run (basedupon D, the ex
41、ternal diameter of the tube) between the tip andthe static pressure holes;6.1.4.4 A minimum of eight diameters straight run betweenthe static pressure holes and the centerline of the external tube,following the 90 bend;6.1.4.5 Static pressure holes of equal size (approximately0.1 D), equally spaced
42、in a piezometer ring configuration; and6.1.4.6 90 bend, with curved or mitered junction.6.1.5 Differential Pressure GaugeAn inclined manometeror equivalent shall be readable to the nearest 0.127 mm (0.005in.) water for p values greater than 2.54 mm (0.10 in.) water,FIG. 2 Filter Holder AssemblyE2515
43、 11 (2017)3and to the nearest 0.025 mm (0.001 in.) water for p valuesless than 2.54 mm (0.10 in.) water.6.1.6 Dilution TunnelThe dilution tunnel apparatus isshown in Fig. 3 and Fig. 4 and consists of the followingcomponents:6.1.6.1 HoodConstructed of steel. Hood shall be largeenough to capture all o
44、f the flue-gas flow exiting the top of theappliance chimney. The dilution tunnel hood shall be conicalwith a minimum diameter at the entrance of at least four timesthe tunnel diameter. The height of the conical section shall beat least three tunnel diameters. A skirt can be used around theinlet to t
45、he conical section to insure capture of the flue-gasexhaust as shown in 9.2.4 as long as the requirements of 9.2.3are met. The outlet of the conical section shall be sized to matewith the mixing section of the dilution tunnel. (See Fig. 3 andFig. 4.)6.1.6.2 90 ElbowsSteel 90 elbows should be used fo
46、rconnecting mixing section, the sampling section, and theoptional damper assembly. There shall be at least two 90elbows upstream of the sampling section. (See Fig. 3 and Fig.4.) The last elbow before the sampling section begins shall beof the same diameter as the sampling section straight ducting.6.
47、1.6.3 Straight DuctStraight sections of steel ductingshall be used to construct both the mixing section and samplingsection of the dilution tunnel apparatus. The mixing section isconsidered to be the ducting that is upstream of the last elbowbefore the sampling section begins. The mixing section and
48、sampling section may be different diameters, but the samplingsection shall have a consistent diameter over the its full length.(See Fig. 4.) Two velocity traverse ports shall be located atleast eight tunnel diameters downstream of the last flowdisturbance (for example, a 90 elbow) and positioned at
49、90 toeach other in the dilution tunnel sampling section. Thesevelocity traverse points shall be of sufficient size to allow entryof the standard Pitot tube but shall not exceed 12.7 mm (0.5 in.)diameter. Two particulate sample extraction ports shall belocated at least four tunnel diameters downstream of thevelocity traverse ports and at least two tunnel diametersupstream from the next downstream flow disturbance. Thesesample extraction ports shall be of sufficient size to allow entryof the sampling probes. The total lengt
