1.1 本规程涵盖了认证颗粒物探测器（PMD）和袋式泄漏探测器（BLD）的程序，这些探测器用于监测燃烧危险废物的波特兰水泥厂窑系统的颗粒物（PM）排放。它包括设计规范、性能规范、测试程序和信息要求，以确保这些连续监测器满足部分必要的最低要求，可靠地监测PM浓度，以表明需要对燃烧危险废物的波特兰水泥厂使用的空气污染控制装置类型进行检查或采取纠正措施。 1.2 本规程特别适用于原始制造商，或参与PMD或BLD维修、再制造或转售的制造商。 1.3 本惯例适用于( 一 )配备静电除尘器的湿法或干法水泥窑，以及( b )干法窑，包括预热器预分解窑系统，配备织物过滤器控制装置。某些类型的监测仪器仅适用于某些类型的应用。 注1: 本规程是在仔细考虑PM浓度的性质和可变性、出水条件以及燃烧危险废物的波特兰水泥厂使用的空气污染控制装置的类型、配置和运行特性的基础上制定的。 1.4 本规程适用于符合40 CFR 63子部分EEE中所含PM排放标准的硅酸盐水泥窑系统。 注2: PM发射限值的水平与适当PMD和BLD仪表的设计和选择有关。当前颁布的PM排放标准（70 FR 594022005年10月12日）为:( 一 )7时为65 mg/dscm % O 2. （7时为0.028 gr/dscf % O 2. )或“现有来源”约30 mg/acm（0.013 gr/acf），以及( b )7时为5.3 mg/dscm % O 2. （7时为0.0023 gr/dscf % O 2. )或“新来源”约2.5 mg/acm（0.001 gr/acf）2006年3月23日（71 FR 14665），环境保护局提议将新水泥厂的PM标准修订为15.9 mg/dscm，7 % O 2. （7时为0.0069 gr/dscf % O 2. )，或约6–9 mg/acm（0.0026–0.0039 gr/acf）。排放标准可能会在未来的规则制定中发生变化，因此这种做法的用户应该检查当前的法规。某些类型的监测仪器不适合在新的和现有的排放源上使用。 1.5 本规程中包含的规范和测试程序超过了美国环境保护局（USEPA）的规范和测试程序。对于制造商证明符合本规程的每个监测装置，制造商可以签发一份证书，说明监测装置符合本规程的所有适用设计和性能要求，并且还符合适用于波特兰水泥厂的40 CFR 63子部分EEE中PMD或BLD的所有适用要求。 注3: 40 CFR 63.1206（c）（8）和（9）要求BLD和PMD“由制造商认证，能够检测浓度为每实际立方米1.0毫克的颗粒物排放，除非您根据§63.1209（g）证明，在正常运行期间，较高的检测限值将常规检测颗粒物负载。”本规程包括确定和报告每个PMD或BLD模型检测限的具体程序。 1.6 以国际单位制表示的数值应视为标准值。本标准不包括其他计量单位。 1.7 本标准并非旨在解决与其使用相关的所有安全问题（如有）。本标准的用户有责任在使用前制定适当的安全、健康和环境实践，并确定监管限制的适用性。 1.8 本国际标准是根据世界贸易组织技术性贸易壁垒（TBT）委员会发布的《关于制定国际标准、指南和建议的原则的决定》中确立的国际公认标准化原则制定的。 ====意义和用途====== 5.1 EPA法规要求燃烧危险废物的波特兰水泥厂使用BLD或PMD，以提供PM浓度的相对或绝对指示，并提醒工厂操作员需要检查PM控制设备或采取纠正措施。美国环保局和其他机构尚未针对这些应用制定这些仪器的具体设计和性能规范。本规程中包含的设计和性能规范以及测试程序将有助于确保测量系统能够提供可靠的监测数据。 5.2 本规程确定了硅酸盐水泥窑系统BLD和PMD监测设备的相关信息和操作特性。这种做法将帮助设备供应商和用户评估和选择适当的监测设备。 5.3 本规程要求进行测试，以验证制造商发布的检测限、线性、热稳定性、对电源电压变化的不敏感性和其他因素的规范，以便购买者可以依赖制造商发布的规范。买方还应确保，特定仪器已在制造点进行测试，并在装运前符合选定的设计和性能规范。 5.4 本规程要求制造商制定并向用户提供安装开始的书面程序- 设备的启动、操作、维护和质量保证。本规程要求将这些相同的程序用于波特兰水泥厂BLD或PMD监测设备的现场性能演示。 5.5 选择本规程的适用测试程序和规范是为了解决制造商控制范围内的设备和活动。 5.6 这种做法也可以作为PMD或BLD设备制造商使用的认证程序的第三方独立审计的基础。

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 2 (0.028 gr/dscf at 7 % O 2 ) or approximately 30 mg/acm (0.013 gr/acf) for “existing sources” and ( b ) 5.3 mg/dscm at 7 % O 2 (0.0023 gr/dscf at 7 % O 2 ) or approximately 2.5 mg/acm (0.001 gr/acf) 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 2 (0.0069 gr/dscf at 7 % O 2 ), or about 6–9 mg/acm (0.0026–0.0039 gr/acf). The emission standards may change in future rulemakings, so users 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 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 procedures for determination and reporting of the detection limit for each PMD or BLD model. 1.6 The values stated in SI units are to be regarded as standard. No other units of measurement are included in this standard. 1.7 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. 1.8 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. ====== 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 by manufacturers of PMD or BLD equipment.