ASTM D7392-20
(Practice)Standard Practice for PM Detector and Bag Leak Detector Manufacturers to Certify Conformance with Design and Performance Specifications for Cement Plants
Standard Practice for PM Detector and Bag Leak Detector Manufacturers to Certify Conformance with Design and Performance Specifications for Cement Plants
SIGNIFICANCE AND USE
5.1 EPA regulations require Portland cement plants that burn hazardous waste to use BLDs or PMDs to provide either a relative or an absolute indication of PM concentration and to alert the plant operator of the need to inspect PM control equipment or initiate corrective action. EPA and others have not established for these applications specific design and performance specifications for these instruments. The design and performance specifications and test procedures contained in this practice will help ensure that measurement systems are capable of providing reliable monitoring data.
5.2 This practice identifies relevant information and operational characteristics of BLD and PMD monitoring devices for Portland cement kiln systems. This practice will assist equipment suppliers and users in the evaluation and selection of appropriate monitoring equipment.
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.
5.5 The applicable test procedures and specifications of this practice are selected to address the equipment and activities that are within the control of the manufacturer.
5.6 This practice also may serve as the basis for third party independent audits of the certification procedures used ...
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.
1.3 This practice applies to (a) wet or dry process cement kilns equipped with electrostatic precipitators, and (b) dry process kilns, including pre-heater pre-calciner kiln systems, equipped with fabric filter controls. Some types of monitoring instruments are suitable for only certain types of applications.
Note 1: This practice has been developed based on careful consideration of the nature and variability of PM concentrations, effluent conditions, and the type, configuration, and operating characteristics of air pollution control devices used at Portland cement plants that burn hazardous waste.
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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Standards Content (Sample)
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.
Designation:D7392 −20
Standard Practice for
PM Detector and Bag Leak Detector Manufacturers to
Certify Conformance with Design and Performance
1
Specifications for Cement Plants
This standard is issued under the fixed designation D7392; 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.
65 mg/dscm at 7 % O (0.028 gr/dscf at 7 % O ) or approximately 30
1. Scope
2 2
mg/acm (0.013 gr/acf) for “existing sources” and (b) 5.3 mg/dscm at 7 %
1.1 This practice covers the procedure for certifying par-
O (0.0023gr/dscfat7 %O )orapproximately2.5mg/acm(0.001gr/acf)
2 2
ticulate matter detectors (PMDs) and bag leak detectors for “new sources.” On March 23, 2006 (71 FR 14665), EPA proposed to
revise the PM standard for new cement plants to 15.9 mg/dscm at 7 % O
(BLDs) that are used to monitor particulate matter (PM)
2
(0.0069 gr/dscf at 7 % O ), or about 6–9 mg/acm (0.0026–0.0039 gr/acf).
2
emissions from kiln systems at Portland cement plants that
Theemissionstandardsmaychangeinfuturerulemakings,sousersofthis
burn hazardous waste. It includes design specifications, perfor-
practice should check the current regulations. Some types of monitoring
mance specifications, test procedures, and information require-
instruments are not suitable for use over the range of emissions encoun-
ments to ensure that these continuous monitors meet minimum tered at both new and existing sources.
requirements, necessary in part, to monitor reliably PM con-
1.5 The specifications and test procedures contained in this
centrations to indicate the need for inspection or corrective
practice exceed those of the United States Environmental
action of the types of air pollution control devices that are used
Protection Agency (USEPA). For each monitoring device that
at Portland cement plants that burn hazardous waste.
the manufacturer demonstrates conformance to this practice,
the manufacturer may issue a certificate that states that
1.2 This practice applies specifically to the original
monitoring device conforms with all of the applicable design
manufacturer,ortothoseinvolvedintherepair,remanufacture,
and performance requirements of this practice and also meets
or resale of PMDs or BLDs.
all applicable requirements for PMDs or BLDs at 40 CFR 63,
1.3 This practice applies to (a) wet or dry process cement
Subpart EEE, which apply to Portland cement plants.
kilns equipped with electrostatic precipitators, and (b) dry
process kilns, including pre-heater pre-calciner kiln systems, NOTE 3—40 CFR 63.1206 (c)(8) and (9) requires that BLDs and PMDs
“be certified by the manufacturer to be capable of detecting particulate
equipped with fabric filter controls. Some types of monitoring
matter emissions at concentrations of 1.0 milligrams per actual cubic
instruments are suitable for only certain types of applications.
meter unless you demonstrate under §63.1209(g), that a higher detection
limit would routinely detect particulate matter loadings during normal
NOTE 1—This practice has been developed based on careful consider-
operations.” This practice includes specific procedures for determination
ation of the nature and variability of PM concentrations, effluent
and reporting of the detection limit for each PMD or BLD model.
conditions,andthetype,configuration,andoperatingcharacteristicsofair
pollution control devices used at Portland cement plants that burn
1.6 The values stated in SI units are to be regarded as
hazardous waste.
standard. No other units of measurement are included in this
1.4 This practice applies to Portland cement kiln systems
standard.
subject to PM emission standards contained in 40 CFR 63,
1.7 This standard does not purport to address all of the
Subpart EEE.
safety concerns, if any, associated with its use. It is the
NOTE 2—The level of the PM emission limit is relevant to the design responsibility of the user of this standard to establish appro-
and selection of appropriate PMD and BLD instrumentation. The current
priate safety, health, and environmental practices and deter-
promulgatedPMemissionstandards(70FR59402,Oct.12,2005)are:(a)
mine the applicability of regulatory limitations prior to use.
1.8 This international standard was developed in accor-
1
dance with internationally recognized principles on standard-
This practice is under the jurisdiction ofASTM Committee D22 on Air Quality
and is the direct responsibility of Subcommittee D22.03 on Ambient Atmospheres
ization established i
...
This document is not an ASTM standard and is intended only to provide the user of an ASTM 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: D7392 − 07 (Reapproved 2013) D7392 − 20
Standard Practice for
PM Detector and Bag Leak Detector Manufacturers to
Certify Conformance with Design and Performance
1
Specifications for Cement Plants
This standard is issued under the fixed designation D7392; 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 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.
1.3 This practice applies to (a) wet or dry process cement kilns equipped with electrostatic precipitators, and (b) dry process kilns,
including pre-heater pre-calciner kiln systems, equipped with fabric filter controls. Some types of monitoring instruments are
suitable for only certain types of applications.
NOTE 1—This practice has been developed based on careful consideration of the nature and variability of PM concentrations, effluent conditions, and the
type, configuration, and operating characteristics of air pollution control devices used at Portland cement plants that burn hazardous waste.
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 % O (0.028 gr/dscf at 7 % O ) or approximately 30 mg/acm
2 2
(0.013 gr/acf) for “existing sources” and (b) 5.3 mg/dscm at 7 % O (0.0023 gr/dscf at 7 % O ) or approximately 2.5 mg/acm (0.001 gr/acf) for “new
2 2
sources.” On March 23, 2006 (71 FR 14665)14665), EPA proposed to revise the PM standard for new cement plants to 15.9 mg/dscm at 7 % O (0.0069
2
gr/dscf at 7 % O ), or about 6-96–9 mg/acm (0.0026-0.0039(0.0026–0.0039 gr/acf). The emission standards may change in future rulemakings, so users
2
of this practice should check the current regulations. Some types of monitoring instruments are not suitable for use over the range of emissions
encountered at both new and existing sources.
1.5 The specifications and test procedures contained in this practice exceed those of the United States Environmental Protection
Agency (USEPA). For each monitoring device that the manufacturer demonstrates conformance to this practice, the manufacturer
1
This practice is under the jurisdiction of ASTM Committee D22 on Air Quality and is the direct responsibility of Subcommittee D22.03 on Ambient Atmospheres and
Source Emissions.
Current edition approved April 1, 2013Sept. 1, 2020. Published September 2014September 2020. Originally approved in 2007. Last previous edition approved in 20072013
as D7392 – 07. 07 (2013). DOI: 10.1520/D7392-07R13.10.1520/D7392-20.
Copyright © ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959. United States
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D7392 − 20
may issue a certificate that states that monitoring device conforms with all of the applicable design and performance requirements
of this practice and also meets all applicable requirements for PMDs or BLDs at 40 CFR 63, Subpart EEE, which apply to Portland
cement plants.
NOTE 3—40 CFR 63.1206 (c)(8) and (9) requires that BLDs and PMDs “be certified by the manufacturer to be capable of detecting particulate matter
emissions at concentrations of 1.0 milligrams per actual cubic meter unless you demonstrate under §63.1209(g), that a higher detection limit would
routinely detect particulate matter loadings during normal operations.” This practice includes specific procedur
...
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