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ASTM E2515-10

(Test Method)

Standard Test Method for Determination of Particulate Matter Emissions Collected by a Dilution tunnel

Standard Test Method for Determination of Particulate Matter Emissions Collected by a Dilution tunnel

SCOPE
1.1 This test method is applicable for the determination of particulate matter emissions from solid-fuel-burning appliances including woodstoves, pellet-burning appliances, factory-built fireplaces, masonry fireplaces, masonry heaters, indoor furnaces, and indoor and outdoor hydronic heaters within a laboratory environment.
1.2 Analytes will be a particulate matter (PM) with no CAS number assigned. For data quality objectives, see Appendix X1.
1.3 The values stated in SI units are to be regarded as standard. The values given in parentheses are mathematical conversions to inch-pound units that are provided for information only and are not considered standard.
1.4 This test method does not purport to address all of the safety concerns, if any, associated with its use. It is the responsibility of the user of this standard to establish appropriate safety and health practices and determine the applicability of regulatory limitations prior to use.

General Information

Status
Historical
Publication Date
31-Aug-2010
ICS
13.040.40 - Stationary source emissions
Technical Committee
E06 - Performance of Buildings
Drafting Committee
E06.54 - Solid Fuel Burning Appliances
Current Stage
Ref Project

Relations

Replaces
ASTM E2515-09 - Standard Test Method for Determination of Particulate Matter Emissions Collected by a Dilution tunnel
Effective Date
01-Sep-2010
Replaced By
ASTM E2515-11 - Standard Test Method for Determination of Particulate Matter Emissions Collected by a Dilution Tunnel
Effective Date
01-Nov-2011
Referred By
ASTM E2780-10(2017) - Standard Test Method for Determining Particulate Matter Emissions from Wood Heaters
Effective Date
01-Sep-2010
Referred By
ASTM E2779-10(2017) - Standard Test Method for Determining Particulate Matter Emissions from Pellet Heaters
Effective Date
01-Sep-2010
Referred By
ASTM E3053-18e2 - Standard Test Method for Determining Particulate Matter Emissions from Wood Heaters Using Cordwood Test Fuel
Effective Date
01-Sep-2010
Referred By
ASTM E2817-11(2018) - Standard Test Method for Test Fueling Masonry Heaters
Effective Date
01-Sep-2010
Referred By
ASTM E2558-13(2021) - Standard Test Method for Determining Particulate Matter Emissions from Fires in Wood-Burning Fireplaces
Effective Date
01-Sep-2010
Referred By
ASTM E2618-13(2019) - Standard Test Method for Measurement of Particulate Emissions and Heating Efficiency of Solid Fuel-Fired Hydronic Heating Appliances
Effective Date
01-Sep-2010

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Standards Content (Sample)

NOTICE: This standard has either been superseded and replaced by a new version or withdrawn.
Contact ASTM International (www.astm.org) for the latest information
Designation:E2515–10
Standard Test Method for
Determination of Particulate Matter Emissions Collected by
1
a Dilution Tunnel
This standard is issued under the fixed designation E2515; the number immediately following the designation indicates the year of
original adoption or, in the case of revision, the year of last revision. A number in parentheses indicates the year of last reapproval. A
superscript epsilon (´) indicates an editorial change since the last revision or reapproval.
4
1. Scope 2.2 AISI Documents:
AISI 316 Stainless Steel
1.1 This test method is applicable for the determination of
particulate matter emissions from solid-fuel-burning appli-
3. Terminology
ances including woodstoves, pellet-burning appliances,
3.1 Definitions of Terms Specific to This Standard:
factory-built fireplaces, masonry fireplaces, masonry heaters,
3.1.1 laboratory environment—the area or room that is used
indoor furnaces, and indoor and outdoor hydronic heaters
for the storage, weighing, assembly, disassembly, and desicca-
within a laboratory environment.
tion of filters and related equipment (sample recovery and
1.2 Analytes will be a particulate matter (PM) with no CAS
analysis).
number assigned. For data quality objectives, see Appendix
3.1.2 particulate matter (PM)—all gas-borne matter result-
X1.
ing from combustion of solid fuel, as specified in the appliance
1.3 The values stated in SI units are to be regarded as
operation test method, that is collected and retained by the
standard. The values given in parentheses are mathematical
specified filter and probe system under the conditions of the
conversions to inch-pound units that are provided for informa-
test.
tion only and are not considered standard.
3.1.3 test facility—the area in which the tested appliance is
1.4 This test method does not purport to address all of the
installed, operated, and sampled for emissions.
safety concerns, if any, associated with its use. It is the
responsibility of the user of this standard to establish appro-
4. Summary of Test Method
priate safety and health practices and determine the applica-
4.1 The total flue-gas exhaust from a solid fuel burning
bility of regulatory limitations prior to use.
appliance is collected along with ambient dilution air with a
collection hood. Duplicate sampling trains are used to extract
2. Referenced Documents
2 gas samples from the dilution tunnel for determination of
2.1 ASTM Standards:
particulate matter concentrations. Each sample train has two
D2986 Practice for Evaluation of Air Assay Media by the
3 glass fiber filters in series. The samples are withdrawn at a
Monodisperse DOP (Dioctyl Phthalate) Smoke Test
consistently proportional rate from sampling points located at
E2558 Test Method for Determining Particulate Matter
the centroid of a sampling tunnel. During sampling, the filters
Emissions from Fires in Low Mass Wood-Burning Fire-
are maintained at a temperature less than 32°C (90°F). The
places
mass of the sampled particulate matter is determined gravi-
E2618 Test Method for Measurement of Particulate Emis-
metrically after the removal of uncombined water. The total
sions and Heating Efficiency of Outdoor Solid Fuel-Fired
particulate matter mass collected on the filters and in the probe
Hydronic Heating Appliances
and front filter housing are multiplied by the ratio of the
dilution tunnel flow to sample flow to determine the total
1
This test method is under the jurisdiction of ASTM Committee E06 on
particulate emissions during a test.
Performance of Buildings and is the direct responsibility of Subcommittee E06.54
4.2 The sampling system for this test method consists of
on Solid Fuel Burning Appliances.
duplicatedual-filterdrysamplingtrains.Bothoftheparticulate
Current edition approved Sept. 1, 2010. Published November 2010. Originally
approved in 2007. Last previous edition approved in 2009 as E2515 – 09. DOI:
sampling trains are operated simultaneously at a sample flow
3
10.1520/E2515-10.
rate not to exceed 0.007 m /min (0.25 cfm/min). The total
2
For referenced ASTM standards, visit the ASTM website, www.astm.org, or
particulate results obtained from the two sampling trains are
contact ASTM Customer Service at service@astm.org. For Annual Book of ASTM
Standards volume information, refer to the standard’s Document Summary page on
the ASTM website.
3 4
Withdrawn. The last approved version of this historical standard is referenced Available from American Iron and Steel Institute (AISI), 1140 Connecticut
on www.astm.org. Ave., NW, Suite 705, Washington, DC 20036, http://www.steel.org.
Copyright © ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959, United States.
1

---------------------- Page: 1 ----------------------
E2515–10
averaged to determine the particulate emissions and are com- (1) Filter Holders—
...

This document is not anASTM standard and is intended only to provide the user of anASTM standard an indication of what changes have been made to the previous version. Because
it may not be technically possible to adequately depict all changes accurately, ASTM recommends that users consult prior editions as appropriate. In all cases only the current version
of the standard as published by ASTM is to be considered the official document.
Designation:E2515–09 Designation:E2515–10
Standard Test Method for
Determination of Particulate Matter Emissions Collected by
1
a Dilution Tunnel
This standard is issued under the fixed designation E2515; the number immediately following the designation indicates the year of
original adoption or, in the case of revision, the year of last revision. A number in parentheses indicates the year of last reapproval. A
superscript epsilon (´) indicates an editorial change since the last revision or reapproval.
1. Scope
1.1 This test method is applicable for the determination of particulate matter emissions from solid-fuel-burning appliances
including woodstoves, pellet-burning appliances, factory-built fireplaces, masonry fireplaces, masonry heaters, indoor furnaces,
and indoor and outdoor hydronic heaters within a laboratory environment.
1.2 Analytes will be a particulate matter (PM) with no CAS number assigned. For data quality objectives, see Appendix X1.
1.3 The values stated in SI units are to be regarded as standard. The values given in parentheses are mathematical conversions
to inch-pound units that are provided for information only and are not considered standard.
1.4 This test method does not purport to address all of the safety concerns, if any, associated with its use. It is the responsibility
of the user of this standard to establish appropriate safety and health practices and determine the applicability of regulatory
limitations prior to use.
2. Referenced Documents
2
2.1 ASTM Standards:
D2986 Practice for Evaluation of Air Assay Media by the Monodisperse DOP (Dioctyl Phthalate) Smoke Test
E2558 Test Method for Determining Particulate Matter Emissions from Fires in Low Mass Wood-Burning Fireplaces
E2618 Test Method for Measurement of Particulate Emissions and Heating Efficiency of Outdoor Solid Fuel-Fired Hydronic
Heating Appliances
1
This test method is under the jurisdiction ofASTM Committee E06 on Performance of Buildings and is the direct responsibility of Subcommittee E06.54 on Solid Fuel
Burning Appliances.
Current edition approved MaySept. 1, 2009.2010. Published June 2009.November 2010. Originally approved in 2007. Last previous edition approved in 20072009 as
E2515 – 079. DOI: 10.1520/E2515-109.
2
For referencedASTM standards, visit theASTM website, www.astm.org, or contactASTM Customer Service at service@astm.org. For Annual Book of ASTM Standards
volume information, refer to the standard’s Document Summary page on the ASTM website.
Copyright © ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959, United States.
1

---------------------- Page: 1 ----------------------
E2515–10
3
2.2 AISI Documents:
AISI 316 Stainless Steel
3. Terminology
3.1 Definitions of Terms Specific to This Standard:
3.1.1 laboratory environment—the area or room that is used for the storage, weighing, assembly, disassembly, and desiccation
of filters and related equipment (sample recovery and analysis).
3.1.2 particulate matter (PM)—all gas-borne matter resulting from combustion of solid fuel, as specified in the appliance
operation test method, that is collected and retained by the specified filter and probe system under the conditions of the test.
3.1.3 test facility—the area in which the tested appliance is installed, operated, and sampled for emissions.
4. Summary of Test Method
4.1 The total flue-gas exhaust from a solid fuel burning appliance is collected along with ambient dilution air with a collection
hood. Duplicate sampling trains are used to extract gas samples from the dilution tunnel for determination of particulate matter
concentrations. Each sample train has two glass fiber filters in series.The samples are withdrawn at a consistently proportional rate
from sampling points located at the centroid of a sampling tunnel. During sampling, the filters are maintained at a temperature less
than32°C(90°F).Themassofthesampledparticulatematterisdeterminedgravimetricallyaftertheremovalofuncombinedwater.
The total particulate matter mass collected on the filters and in the probe and front filter housing are multiplied by the ratio of the
dilution tunnel flow to sample flow to determine the total particulate emissions during a test.
4.2 The sampling system for this test method consists of duplicate dual-filter dry sampling trains. Both of the particulate
3
sampling trains are operated simultaneously at a sample flow rate not to exceed 0.007 m /min (0.25 cfm/min).The total particulate
results obtained from the two sampling trains are averaged to determine the particu
...

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5.1 This test method is used for determining emission factors and emission rates for low mass wood-burning fireplaces.  
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SIGNIFICANCE AND USE
5.1 The measurement of particulate matter and collected residue emission rates is an important test widely used in the practice of air pollution control. Particulate matter measurements after control devices are necessary to determine total emission rates to the atmosphere.  
5.1.1 These measurements, when approved by federal and state agencies, are often required for the purpose of determining compliance with regulations and statutes.  
5.1.2 The measurements made before and after control devices are often necessary as a means of demonstrating conformance with contractual performance specifications.  
5.2 The collected residue obtained with these test methods is also important in characterizing stack emissions. However, the utility of these data is limited unless a chemical analysis of the collected residue is performed.
SCOPE
1.1 These test methods describe procedures to determine the mass emission rates of particulate matter and collected residue in gaseous streams by in-stack test methods (Test Method A) or out-of-stack test methods (Test Method B).  
1.2 These test methods are suitable for measuring particulate matter and collected residue concentrations.  
1.3 These test methods include a description of equipment and procedures to be used for obtaining samples from effluent ducts and stacks, a description of equipment and procedures for laboratory analysis, and a description of procedures for calculating results.  
1.4 These test methods are applicable for sampling particulate matter and collected residue in wet (Test Method A or B) or dry (Test Method A) streams before and after particulate matter control equipment, and for determination of control device particulate matter collection efficiency.  
1.5 These test methods are also applicable for determining compliance with regulations and statutes limiting particulate matter existing in stack gases when approved by federal or state agencies.  
1.6 The particulate matter and collected residue samples collected by these test methods may be used for subsequent size and chemical analysis.  
1.7 These test methods describe the instrumentation, equipment, and operational procedures, including site selection, necessary for sampling and determination of particulate mass emissions. These test methods also include procedures for collection and gravimetric determination of residues collected in an impinger-condenser train. The sampling and analysis of particulate matter may be performed independently or simultaneously with the determination of collected residue.  
1.8 These test methods provide for the use of optional filter designs and filter material as necessary to accommodate the wide range of particulate matter loadings to which the test methods are applicable.  
1.9 Stack temperatures limitation for Test Method A is approximately 400°C (752°F) and for Test Method B is 815°C (1500°F).  
1.10 A known limitation of these test methods concerns the use of collected residue data. Since some collected residues can be formed in the sample train by chemical reaction in addition to condensation, these data should not be used without prior characterization (see 4.4.1).  
1.10.1 A second limitation concerns the use of the test methods for sampling gas streams containing fluoride, or ammonia or calcium compounds in the presence of sulfur dioxide and other reactive species having the potential to react within the sample train.  
1.10.2 A suspected but unverified limitation of these test methods concerns the possible vaporization and loss of collected particulate organic matter during a sampling run.  
1.11 The values stated in either SI units or inch-pound units are to be regarded separately as standard within the text. The inch-pound units are shown in parentheses. The values stated in each system are not exact equivalents; therefore each system shall be used independently of the other. Combining values from the two systems may result in ...

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ASTM
ASTM D5485-21(Test Method)
Standard Test Method for Determining Corrosive Effect of Combustion Products Using the Cone Corrosimeter

SIGNIFICANCE AND USE
5.1 The metal loss from corrosion is directly related to the increase in electrical resistance of the target due to the decrease in conductive cross-sectional area.  
5.2 The relationship between resistance increase of metallic targets used in this test method and the amount of metal loss as reported by a uniform loss in thickness has not been determined.  
5.3 This test method is used to determine the corrosive effect of combustion products from burning electrical insulations or coverings or their constituent materials or components. Corrosion is determined by the reduction of thickness of the metal on standardized targets, as measured by electrical resistance. These targets are not necessarily representative of the intended end use.  
5.4 This test method is intended for use in electrical insulations or coverings material and product evaluations, for additional data to assist in design of electrical insulations or coverings products, or for development and research of electrical insulations or coverings products.  
5.5 A value of the initial test heat flux is selected to be relevant to the fire scenario being investigated (up to 100 kW/m2). Additional information for testing is given in A1.2.3.
SCOPE
1.1 This fire-test-response standard measures the corrosive effect by loss of metal from the combustion products of materials, components, or products.  
1.2 This test method provides corrosion results of product and material specimens limited to a maximum size of 100 by 100 mm in area and 50 mm thick.  
1.3 Additional information regarding the targets, the test conditions, and test limitations is provided in Annex A1.  
1.4 The results of this test method have not been investigated with respect to correlation to actual fires.  
1.5 An ISO standard exists, as developed by ISO TC 61 (Plastics), subcommittee 4 (on burning behavior), which is technically very similar to this test method and is designated ISO 11907-4.  
1.6 The values stated in SI units are to be regarded as standard. No other units of measurement are included in this standard. (See IEEE/ASTM SI10.)  
1.7 This standard measures and describes the response of materials, products, or assemblies to heat and flame under controlled conditions, but does not by itself incorporate all factors required for fire hazard or fire risk assessment of the materials, products, or assemblies under actual fire conditions.  
1.8 Fire testing is inherently hazardous. Adequate safeguards for personnel and property shall be employed in conducting these tests.  
1.9 This standard does not purport to address all of the safety concerns, if any, associated with its use. It is the responsibility of the user of this standard to establish appropriate safety, health, and environmental practices and determine the applicability of regulatory limitations prior to use. For specific hazard statements, see Section 7.  
1.10 This international standard was developed in accordance with internationally recognized principles on standardization established in the Decision on Principles for the Development of International Standards, Guides and Recommendations issued by the World Trade Organization Technical Barriers to Trade (TBT) Committee.

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ASTM
ASTM F2326-04(2021)(Test Method)
Standard Test Method for Collection and Analysis of Visible Emissions from Candles as They Burn

SIGNIFICANCE AND USE
5.1 The intent of this test method is to aid the candle manufacturer to optimize candle formulations in the reduction of visible smoke emissions.  
5.2 This test method is intended to provide candle manufacturers a standard procedure to use during development of candle designs and formulations to compare relative smoke/burn behavior. For the development of this method, a protocol was established for trimming the wick on specially prepared test candles to 6 mm to 7 mm (1/4 in.) prior to each burn cycle. It is recommended that the manufacturer determine a standardized protocol, that is, either not trimming the wick or trimming the wick to an appropriate length in order for direct comparison of results.  
5.3 A relative ranking of candle formulations can be established with the use of a histogram of the data and control charts.  
5.4 This test method is not intended to set forth pass/fail criteria for visible smoke emissions from candles, as such, this method sets no standard level for visible smoke emissions.
SCOPE
1.1 This test method covers the collection and analysis of visible emissions from indoor use candles as they burn.  
1.2 The test is to be used to compare relative smoke/burn behavior during development of candle designs and formulations.  
1.3 This test method may not be suitable for multiple wick candles; tapers and candles intended to be burned while floating on water commonly known as “floaters.”  
1.4 This standard does not purport to address all of the safety concerns, if any, associated with its use. It is the responsibility of the user of this standard to establish appropriate safety, health, and environmental practices and determine the applicability of regulatory limitations prior to use.  
1.5 This international standard was developed in accordance with internationally recognized principles on standardization established in the Decision on Principles for the Development of International Standards, Guides and Recommendations issued by the World Trade Organization Technical Barriers to Trade (TBT) Committee.

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