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ASTM F1471-09

(Test Method)

Standard Test Method for Air Cleaning Performance of a High-Efficiency Particulate Air- Filter System (Withdrawn 2018)

Standard Test Method for Air Cleaning Performance of a High-Efficiency Particulate Air- Filter System (Withdrawn 2018)

SIGNIFICANCE AND USE
This test method describes a procedure for determining the penetration of aerosols through a one- or twostage HEPA filter installation. Testing multiple filter stages as a single unit eliminates the need for: installation of auxiliary aerosol bypass ducts, installation of aerosol injection manifolds between filter stages, and entry of test personnel into contaminated areas. It provides for filter testing without interruption of plant processes and operation of ventilation systems.
The procedure is applicable for measuring penetrations requiring sensitivities to 0.1 μm.
A challenge concentration of 2.5 × 10 5 particles/cm3 (p/cm3), is required for evaluation of one-filter stage, and 2 × 106 p/cm 3, or about 30 μg/L (assuming unit density), is required to properly evaluate a two-stage HEPA filter system as one unit.
This test method can determine the penetration of HEPA filters in the particle-size range from 0.1 to 0.2 μm where the greatest penetration of particles is likely to occur.
SCOPE
1.1 This test method covers the procedure and equipment for measuring the penetration of test particles through high-efficiency particulate air (HEPA) filter systems using a laser aerosol spectrometer (LAS). This test method provides the capability of evaluating the overall effectiveness of HEPA filter systems consisting of one or two filter stages.
1.2 The aerosols used for testing have a heterodisperse size distribution in the submicrometer diameter range from 0.1 to 1.0 μm.  
1.3 The purpose for conducting in-place filter testing by this test method is in the ability to determine penetration of multi-stage installations, without individual stage tests. Particle penetration as low as 10−8 can be measured by this test method. Also, the LAS provides a measure of penetration for discrete particle sizes.
1.4 Maximum penetration for an installed HEPA filter system is 5 × 10−4 for one filter stage, and 2.5 × 10−7 for two stages in series is recommended.
Note 1—Acceptance penetration criteria must be specified in the program, or owners specifications. The penetration criteria suggested in this test method is referenced in Ref (1).  
1.5 The values stated in SI units are to be regarded as the standard.
1.6 This standard does not purport to address all of the safety problems, 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. Specific precautionary statements are given in 9.6.
WITHDRAWN RATIONALE
This test method covers the procedure and equipment for measuring the penetration of test particles through high-efficiency particulate air (HEPA) filter systems using a laser aerosol spectrometer (LAS).
Formerly under the jurisdiction of Committee D22 on Air Quality, this test method was withdrawn in January 2018 in accordance with section 10.6.3 of the Regulations Governing ASTM Technical Committees, which requires that standards shall be updated by the end of the eighth year since the last approval date.

General Information

Status
Withdrawn
Publication Date
28-Feb-2009
Withdrawal Date
18-Jan-2018
ICS
13.040.40 - Stationary source emissions
Technical Committee
D22 - Air Quality
Drafting Committee
D22.05 - Indoor Air
Current Stage
Ref Project

Relations

Replaces
ASTM F1471-93(2001) - Standard Test Method for Air Cleaning Performance of a High-Efficiency Particulate Air- Filter System
Effective Date
01-Mar-2009
Referred By
ASTM F2299/F2299M-03(2017) - Standard Test Method for Determining the Initial Efficiency of Materials Used in Medical Face Masks to Penetration by Particulates Using Latex Spheres
Effective Date
01-Mar-2009

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ASTM F1471-09 - Standard Test Method for Air Cleaning Performance of a High-Efficiency Particulate Air- Filter System (Withdrawn 2018)ASTM F1471-09 - Standard Test Method for Air Cleaning Performance of a High-Efficiency Particulate Air- Filter System (Withdrawn 2018)
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ASTM F1471-09 - Standard Test Method for Air Cleaning Performance of a High-Efficiency Particulate Air- Filter System (Withdrawn 2018)
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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: F1471 − 09
Standard Test Method for
Air Cleaning Performance of a High-Efficiency Particulate
1
Air Filter System
This standard is issued under the fixed designation F1471; the number immediately following the designation indicates the year of
original adoption or, in the case of revision, the year of last revision.Anumber in parentheses indicates the year of last reapproval.A
superscript epsilon (´) indicates an editorial change since the last revision or reapproval.
1. Scope Development of International Standards, Guides and Recom-
mendations issued by the World Trade Organization Technical
1.1 This test method covers the procedure and equipment
Barriers to Trade (TBT) Committee.
for measuring the penetration of test particles through high-
efficiency particulate air (HEPA) filter systems using a laser
2. Referenced Documents
aerosol spectrometer (LAS). This test method provides the
3
2.1 ASTM Standards:
capabilityofevaluatingtheoveralleffectivenessofHEPAfilter
F328Practice for Calibration of anAirborne Particle Coun-
systems consisting of one or two filter stages.
ter Using Monodisperse Spherical Particles (Withdrawn
1.2 The aerosols used for testing have a heterodisperse size
4
2007)
distribution in the submicrometer diameter range from 0.1 to
2.2 Military Standard:
1.0 µm.
MIL-STD 282Military Standard Filter Units, Protective
1.3 Thepurposeforconductingin-placefiltertestingbythis
Clothing, Gas Mask Components, and Related Products:
5
test method is in the ability to determine penetration of
Performance Test Method
multi-stageinstallations,withoutindividualstagetests.Particle
−8
3. Terminology
penetrationaslowas10 canbemeasuredbythistestmethod.
Also, the LAS provides a measure of penetration for discrete
3.1 Definitions of Terms Specific to This Standard:
particle sizes.
3.1.1 diluter—a device used to reduce the aerosol particle
concentration to eliminate coincidence counting is in the LAS.
1.4 Maximum penetration for an installed HEPA filter
−4 −7
system is 5×10 for one filter stage, and 2.5×10 for two
3.1.2 dilution ratio—the ratio of the undiluted aerosol par-
stages in series is recommended.
ticle concentration entering the diluter to the diluted portion of
the particle concentration. Because diluters have inherent
NOTE 1—Acceptance penetration criteria must be specified in the
particle losses that may vary according to the particle size, the
program, or owners specifications. The penetration criteria suggested in
2
this test method is referenced in Ref (1).
dilution ratio may not be constant with respect to size.
1.5 The values stated in SI units are to be regarded as the
3.1.3 laser aerosol spectrometer (LAS)—aprecisionparticle
standard.
detector that allows single particle counting and sizing by the
amount of scattered light from individual particles, where the
1.6 This standard does not purport to address all of the
signals can be grouped into categories corresponding to par-
safety problems, if any, associated with its use. It is the
ticle size.
responsibility of the user of this standard to establish appro-
priate safety and health practices and determine the applica-
3.1.4 penetration—the number of particles passing through
bility of regulatory limitations prior to use. Specific precau-
the filter stage, to the number of particles challenging the
tionary statements are given in 9.6.
upstream side of the filter stage. The penetration, or the
1.7 This international standard was developed in accor-
challenge aerosol, may be associated for each particle size of
dance with internationally recognized principles on standard-
interest.
ization established in the Decision on Principles for the
3
For referenced ASTM standards, visit the ASTM website, www.astm.org, or
contact ASTM Customer Service at service@astm.org. For Annual Book of ASTM
1
This test method is under the jurisdiction of ASTM Committee D22 on Air Standards volume information, refer to the standard’s Document Summary page on
Quality and is the direct responsibility of Subcommittee D22.05 on Indoor Air. the ASTM website.
4
Current edition approved March 1, 2009. Published March 2009. Originally The last approved version of this historical standard is referenced on
approved in 1993. Last previous edition approved in 2001 as F1471–93 (2001). www.astm.org.
5
DOI: 10.1520/F1471-09. Available from Standardization Documents Order Desk, DODSSP, Bldg. 4,
2
The boldface numbers in parentheses refer to a list of references at the end of Section D, 700 Robbins Ave., Philadelphia, PA 19111-5098, http://
this standard. www.dodssp.daps.mil.
Copyright © ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959. United States
1

---------------------- Page: 1 ----------------------
F1471 − 09
4. Summary of Test Method 6.4 Sample flow accuracy through the LAS of
...

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4.1 This practice provides the basic criteria to be used by accreditation bodies and others in evaluating the qualifications of laboratories engaged in the testing of lead in paint, or settled dust, or airborne particulates, or soil, or combination thereof, taken from and around buildings and related structures. The criteria in this practice shall be supplemented by additional specific criteria and requirements, when appropriate; for example, when necessary to be in accordance with federal, state, or local government regulations.  
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This practice presents the procedures and equipment that will permit, within certain limits, representative sampling of stationary source emissions for the automated determination of gas concentrations of effluent gas streams. This application is limited to the determination of oxygen (O2), carbon dioxide (CO2), carbon monoxide (CO), sulfur dioxide (SO2), nitric oxide (NO), nitrogen dioxide (NO2) and total oxides of nitrogen (NOx). Although velocity measurements are required to determine the mass flow rates of gases, this is, however, not included in this practice. This practice describes representative sampling of gases in a duct, both by extractive and non-extractive methods. In extractive sampling, gases are conditioned to remove aerosols, particulate matter, and other interfering substances before being conveyed to the instruments. In non-extractive sampling, the measurements are made in-situ; therefore, no sample conditioning except filtering is required.
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5.3 This practice requires that tests be conducted to verify manufacturer’s published specifications for detection limit, linearity, thermal stability, insensitivity to supply voltage variations and other factors so that purchasers can rely on the manufacturer’s published specifications. Purchasers are also assured that the specific instrument has been tested at the point of manufacture and shown to meet selected design and performance specifications prior to shipment.  
5.4 This practice requires that the manufacturer develop and provide to the user written procedures for installation start-up, operation, maintenance, and quality assurance of the equipment. This practice requires that these same procedures are used for a field performance demonstration of the BLD or PMD monitoring equipment at a Portland cement plant.  
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SCOPE
1.1 This practice covers the procedure for certifying particulate matter detectors (PMDs) and bag leak detectors (BLDs) that are used to monitor particulate matter (PM) emissions from kiln systems at Portland cement plants that burn hazardous waste. It includes design specifications, performance specifications, test procedures, and information requirements to ensure that these continuous monitors meet minimum requirements, necessary in part, to monitor reliably PM concentrations to indicate the need for inspection or corrective action of the types of air pollution control devices that are used at Portland cement plants that burn hazardous waste.  
1.2 This practice applies specifically to the original manufacturer, or to those involved in the repair, remanufacture, or resale of PMDs or BLDs.  
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1.4 This practice applies to Portland cement kiln systems subject to PM emission standards contained in 40 CFR 63, Subpart EEE.
Note 2: The level of the PM emission limit is relevant to the design and selection of appropriate PMD and BLD instrumentation. The current promulgated PM emission standards (70 FR 59402, Oct. 12, 2005) are: (a) 65 mg/dscm at 7 % O2 (0.028 gr/dscf at 7 % O2) or approximately 30 mg/acm (0.013 gr/acf) for “existing sources” and (b) 5.3 mg/dscm at 7 % O2 (0.0023 gr/dscf at 7 % O2) or approximately 2.5 mg/ac...

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1.1 This practice establishes procedures for assessing the exposure of workers to airborne fibers who perform repetitive tasks of short duration where small quantities of asbestos-containing materials must be disturbed in order to perform maintenance and installation activities.  
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1.4 The results are applied to the current job as defined herein for determining worker protection such as respiratory protection or for other purposes as determined by the competent person responsible for the current job. The results of the tests shall not be applied to current jobs that are expected to differ substantially from the test conditions in work practices, material properties or other factors that might affect the concentration of airborne asbestos fibers.  
1.5 This practice is not intended to be used for asbestos abatement work for which the objective is the removal of asbestos-containing materials. It is designed to assess exposures for short-term repetitive tasks. Compliance with regulatory requirements as to the purpose of the work and limits on the quantity of asbestos-containing materials disturbed is the responsibility of the user.  
...

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ASTM
ASTM E1605-19(Terminology)
Standard Terminology Relating to Lead in Buildings

SIGNIFICANCE AND USE
3.1 The purpose of this terminology standard is to help users understand and apply the large number of specialized terms used in connection with the management of lead hazards by providing a single, comprehensive, and consistent terminology.  
3.1.1 This terminology standard includes some terms that may be encountered, but whose use is discouraged. They are included for clarification and in order to provide the user with preferred existing alternate terms.  
3.1.2 Architectural terms for individual building components are included to promote consistency of usage and to help ensure that sampling locations are recorded with sufficient accuracy to allow independent confirmation of lead measurements, if necessary.  
3.2 A discussion is attached to certain definitions to help make the definition clear or to show how the term and its definition are related to other terms.  
3.3 Terms and definitions in this terminology standard are based upon laws, regulations, and practices in the United States of America.  
3.3.1 Some of the definitions in this terminology standard are adopted verbatim or are adapted from definitions that are formally stated or implied in laws and regulations. They are not intended to replace the latter definitions. The user is responsible for understanding legal definitions and for ensuring that the legal obligations that are encompassed by them are fully satisfied.  
3.3.2 Users in other countries should refer to applicable national, regional, and local laws, regulations, and practices.
SCOPE
1.1 This terminology standard covers definitions for the following:  
1.1.1 Terms that are commonly used in the field of management of lead hazards in facilities;  
1.1.2 Architectural terms, particularly those associated with older wood-frame buildings; and,  
1.1.3 Specialized terms that may be encountered by users in reports and notices that are generated during lead hazard management activities.  
1.2 This terminology standard is supplementary to Terminology E631.  
1.3 Definitions adopted or derived from other documents include the following:  
1.3.1 Some of the definitions in this terminology standard are adopted as exact copies from other sources. The source is briefly identified at the right margin following the definition and fully identified in Section 2.  
1.3.2 Some of the definitions in this terminology standard are adapted from other sources. Changes in these definitions were made only to clarify the meaning, to incorporate related terms that also are defined in this terminology standard, or to ensure that the revised definition is consistent with those for related terms. The source is briefly identified with the words “adapted” at the right margin following the definition, and is fully identified in Section 2.  
1.4 Terms within the definitions that are shown in boldface are defined in this terminology standard.  
1.5 This terminology standard excludes the following:  
1.5.1 Terms with a common dictionary meaning, except in cases where there is a specialized definition within the field of lead hazard management.  
1.5.2 Terms that are used only in individual ASTM standards in which they are defined adequately, whether formally or by the context in which they appear.  
1.6 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 E1605-18b(Terminology)
Standard Terminology Relating to Lead in Buildings

SIGNIFICANCE AND USE
3.1 The purpose of this terminology standard is to help users understand and apply the large number of specialized terms used in connection with the management of lead hazards by providing a single, comprehensive, and consistent terminology.  
3.1.1 This terminology standard includes some terms that may be encountered, but whose use is discouraged. They are included for clarification and in order to provide the user with preferred existing alternate terms.  
3.1.2 Architectural terms for individual building components are included to promote consistency of usage and to help ensure that sampling locations are recorded with sufficient accuracy to allow independent confirmation of lead measurements, if necessary.  
3.2 A discussion is attached to certain definitions to help make the definition clear or to show how the term and its definition are related to other terms.  
3.3 Terms and definitions in this terminology standard are based upon laws, regulations, and practices in the United States of America.  
3.3.1 Some of the definitions in this terminology standard are adopted verbatim or are adapted from definitions that are formally stated or implied in laws and regulations. They are not intended to replace the latter definitions. The user is responsible for understanding legal definitions and for ensuring that the legal obligations that are encompassed by them are fully satisfied.  
3.3.2 Users in other countries should refer to applicable national, regional, and local laws, regulations, and practices.
SCOPE
1.1 This terminology standard covers definitions for the following:  
1.1.1 Terms that are commonly used in the field of management of lead hazards in facilities;  
1.1.2 Architectural terms, particularly those associated with older wood-frame buildings; and,  
1.1.3 Specialized terms that may be encountered by users in reports and notices that are generated during lead hazard management activities.  
1.2 This terminology standard is supplementary to Terminology E631.  
1.3 Definitions adopted or derived from other documents include the following:  
1.3.1 Some of the definitions in this terminology standard are adopted as exact copies from other sources. The source is briefly identified at the right margin following the definition and fully identified in Section 2.  
1.3.2 Some of the definitions in this terminology standard are adapted from other sources. Changes in these definitions were made only to clarify the meaning, to incorporate related terms that also are defined in this terminology standard, or to ensure that the revised definition is consistent with those for related terms. The source is briefly identified with the words “adapted” at the right margin following the definition, and is fully identified in Section 2.  
1.4 Terms within the definitions that are shown in boldface are defined in this terminology standard.  
1.5 This terminology standard excludes the following:  
1.5.1 Terms with a common dictionary meaning, except in cases where there is a specialized definition within the field of lead hazard management.  
1.5.2 Terms that are used only in individual ASTM standards in which they are defined adequately, whether formally or by the context in which they appear.  
1.6 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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    10 pages
    English language
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    English language
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