13.040.50 移动源排放限值 标准查询与下载



共找到 246 条与 移动源排放限值 相关的标准,共 17

前言 1 范围 2 规范性引用文件 3 术语和定义 4 基本要求 5 终端设备要求 5.1 一般要求 5.2 功能要求 5.3 性能要求 5.4 安装与调试要求 6 数据传输要求 6.1 一般要求 6.2数据传输规约/协议 6.3数据补发 7 管理平台要求 7.1一般要求 7.2平台接入 7.3存储 7.4安全 8 运行管理要求 8.1 日常运行 8.2 维护 附录A(规范性附录)重型柴油车远程排放管理终端设备接入管理平台通讯协议 附录B(规范性附录)平台接入管理平台通讯协议

Technical specification for the application of on-board diagnostic system (OBD) for heavy-duty diesel vehicles

ICS
13.040.50
CCS
N772
发布
2020-08-25
实施
2020-09-11

目次  前言 1 范围 2 规范性引用文件 3 术语和定义 4 基本要求 5 终端设备要求 5.1 一般要求 5.2 功能要求 5.3 性能要求 5.4 安装与调试要求 6 数据传输要求 6.1 一般要求 6.2 数据传输规约/协议 6.3 数据补发 7 管理平台要求 7.1 一般要求 7.2 平台接入 7.3 存储 7.4 安全 8 运行管理要求 8.1 日常运行 8.2 维护 附录 A(规范性附录)重型柴油车远程排放管理终端设备接入管理平台通讯协议 附录 B(规范性附录)平台接入管理平台通讯协议

Technical specification for the application of on-board diagnostic system (OBD) for heavy-duty diesel vehicles

ICS
13.040.50
CCS
N772
发布
2020-08-25
实施
2020-09-04

This document specifies the measurement methods for gaseous and particulate exhaust emissions from reciprocating internal combustion (RIC) engines on a test bed, necessary for determining one weighted value for each exhaust gas pollutant. Various combinations of engine load and speed reflect different engine applications (see ISO 8178-4). This document is applicable to RIC engines for mobile, transportable and stationary use, excluding engines for motor vehicles primarily designed for road use. This document can be applied to engines used, for example, for earth-moving machines, generating sets and for other applications.

Reciprocating internal combustion engines — Exhaust emission measurement — Part 1: Test-bed measurement systems of gaseous and particulate emissions

ICS
13.040.50
CCS
发布
2020-06-24
实施

This document specifies the test cycles, the test procedures and the evaluation of gaseous and particulate exhaust emissions from reciprocating internal combustion (RIC) engines coupled to a dynamometer. With certain restrictions, this document can also be used for measurements at site. The tests are carried out under steady-state and transient operation using test cycles which are representative of given applications. This document is applicable to RIC engines for mobile, transportable and stationary use, excluding engines for on-road transport of passengers and goods. It can be applied to engines for non-road use, e.g. for earth-moving machines, generating sets and for other applications. For engines used in machinery covered by additional requirements (e.g. occupational health and safety regulations, regulations for power plants), additional test conditions and special evaluation methods can apply.

Reciprocating internal combustion engines — Exhaust emission measurement — Part 4: Steady-state and transient test cycles for different engine applications

ICS
13.040.50
CCS
发布
2020-06-24
实施

Motorcycles — Measurement methods for gaseous exhaust emissions during inspection or maintenance — Amendment 1

ICS
13.040.50
CCS
发布
2020-05-06
实施

This document specifies a basic measurement method by using a permeation test procedure for evaporative emissions from motorcycles. It is applicable to motorcycles equipped with a fuel tank to store liquid high volatile fuel and with a spark ignition engine (four-stroke engine, two-stroke engine or rotary piston engine).

Motorcycles — Measurement method for evaporative emissions — Part 2: Permeation test procedure

ICS
13.040.50
CCS
发布
2020-02-28
实施

1.1 This test method covers the determination of nitrogen oxides (NO and NO2), carbon monoxide (CO), and oxygen (O2) concentrations in controlled and uncontrolled emissions from natural gas-fired reciprocating engines, combustion turbines, boilers, and process heaters using portable analyzers with electrochemical sensors. Due to the inherent cross sensitivities of the electrochemical cells, this test method should not be applied to other pollutants or emission sources without a complete investigation of possible analytical interferences and a comparative evaluation with EPA test methods. 1.1.1 The procedures and specifications of this test method were originally developed during laboratory and field tests funded by the Gas Research Institute (GRI).2 Comparative emission tests were conducted only on natural gas-fired combustion sources. Subsequently, the U.S. Environmental Protection Agency (EPA) sponsored Environmental Technology Verification (ETV) program conducted further evaluations of electrochemical cell analyzers, which included laboratory tests and field tests on natural gas and diesel-fueled generators. The EPA has reviewed the ETV test results, published additional information, and provided technical input that has been considered in the update of this test method.3 1.2 This test method contains notes that are explanatory and are not part of the mandatory requirements of the standard. 1.3 The values stated in SI units are to be regarded as standard. No other units of measurement are included in this standard. 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.

Standard Test Method for Determination of Nitrogen Oxides, Carbon Monoxide, and Oxygen Concentrations in Emissions from Natural Gas-Fired Reciprocating Engines, Combustion Turbines, Boilers, and Proce

ICS
13.040.50
CCS
/
发布
2020
实施
0000-00-00

This document specifies the measurement procedures and test cycles for the evaluation of smoke emissions from compression ignition engines using an opacimeter. The tests are carried out under steady-state and transient operation using tests cycles which are representative of a given application. The smoke testing is conducted using opacimeter-type smoke meters which operate on the light extinction principle. The purpose of this document is to define the smoke test cycles and the methods used to measure the opacity and for the determination of the light absorption coefficient. It allows the use of either full-flow or partial-flow opacimeters and corrects for differences in rise time between the two types of opacimeters. Specifications of the apparatus for the measurement of opacity can be found in ISO 11614. The test procedures and measurement techniques described in this document are applicable to reciprocating internal combustion (RIC) engines in general. Annex D, Annex E, Annex F and Annex G each contains a test cycle that is relevant only for those specific applications listed in the first subclause of that annex. Where possible, the smoke test cycle described in the annex utilizes the engine and machine categories developed in ISO 8178-4. For certain categories of non-road engines “at site” rather than “test bed” smoke test procedures can prove to be necessary. For engines used in machinery covered by additional requirements (e.g. occupational health and safety regulations), additional test conditions and special evaluation methods can apply.

Reciprocating internal combustion engines — Exhaust emission measurement — Part 9: Test cycles and test procedures for measurement of exhaust gas smoke emissions from compression ignition engines usin

ICS
13.040.50
CCS
发布
2019-07-22
实施

This document specifies a basic measurement method by using the SHED (Sealed Housing for Evaporative Determination) test procedure for evaporative emissions from motorcycles. It is applicable to motorcycles equipped with a spark ignition engine (four-stroke engine, two-stroke engine or rotary piston engine).

Motorcycles — Measurement method for evaporative emissions — Part 1: SHED test procedure

ICS
13.040.50
CCS
发布
2019-07-15
实施

本标准规定了平板玻璃、电子玻璃制造企业或生产设施的大气污染物中颗粒物、二氧化硫、氮氧化物的排放限值、监测和监控要求,以及标准实施与监督等相关规定。 本标准适用于现有平板玻璃、电子玻璃制造企业或生产设施的大气污染物中颗粒物、二氧化硫、氮氧化物的排放管理,以及对建设项目的环境影响评价、环境保护设施设计、竣工环境保护验收及其投产后的大气污染物中颗粒物、二氧化硫、氮氧化物的排放管理。 本标准中未规定的内容和要求,仍按现行GB 26453、GB 29495等相关标准执行。

Emission Standards of Air Pollutants for the Glass Industry

ICS
13.040.50
CCS
Z60
发布
2019-06-28
实施
2019-08-01

本标准规定了陶瓷工业企业大气污染物中颗粒物、二氧化硫、氮氧化物排放限值、监测和监控要求,以及标准的实施与监督等相关规定。 本标准适用于陶瓷工业企业的大气污染物中颗粒物、二氧化硫、氮氧化物排放管理,以及对建设项目的环境影响评价、环境保护设施设计、竣工环境保护验收及其投产后的大气污染物中颗粒物、二氧化硫、氮氧化物的排放管理。 本标准不适用于陶瓷原辅材料的开采及初加工过程的大气污染物排放管理。 本标准中未规定的内容和要求,仍按现行GB 25464及修改单等相关标准执行。

Emission Standards of Air Pollutants for Ceramic Industry

ICS
13.040.50
CCS
Z60
发布
2019-06-28
实施
2019-08-01

本标准适用于向小东江流域排放污水的石油炼制工业、石油化学工业、制革工业、非金属矿采选业、屠宰及肉类加工业和水产品加工业、畜禽养殖业等6 类重点行业及城镇污水处理厂的化学需氧量、氨氮、总磷、石油类等4 种水污染物排放管理,以及上述重点控制行业及城镇污水处理厂建设项目的环境影响评价、环境保护设施设计、竣工环境保护验收及其投产后的上述4种水污染物排放管理。 本标准中未作规定的内容和要求,按现行相应标准执行。

Discharge Standards of Water Pollutants in the Xiaodong River Basin

ICS
13.040.50
CCS
Z60
发布
2019-06-05
实施
2019-07-01

This document specifies a method for the measurement of smoke from exhaust gas of reciprocating internal combustion (RIC) engines at a steady state condition. The method evaluates the soot content by measurement of the blackening of a filter and derivation of black carbon mass concentration (mg/ m3) from FSN. Where necessary, individual requirements may be specified for particular engine applications. This document is applicable to RIC engines for mobile, transportable and stationary use, excluding engines for on-road transport of passengers and goods. It can be applied to engines for non-road use, e.g. for earth-moving machines, generating sets and for other applications. For engines used in machinery covered by additional requirements (e.g. occupational health and safety regulations, regulations for power plants) additional test conditions and special evaluation methods can apply.

Reciprocating internal combustion engines — Exhaust emission measurement — Part 3: Test procedures for measurement of exhaust gas smoke emissions from compression ignition engines using a filter type

ICS
13.040.50
CCS
发布
2019-01-30
实施

Continuous analyzers for dioxide sulfur in flue gas

ICS
13.040.50
CCS
发布
2018-12-28
实施

Continuous analyzers for dioxide sulfur in flue gas

ICS
13.040.50
CCS
发布
2018-12-28
实施

WARNING — The use of this document can involve hazardous materials, operations and equipment. This document does not purport to address all of the safety problems associated with its use. It is the responsibility of the user of this document to establish appropriate safety and health practices and to determine the applicability of any other restrictions prior to its use. This document specifies requirements for applying and documenting methods for determining particulate contamination on functionally-relevant components and systems (cleanliness inspection) of road vehicles. A cleanliness inspection comprises the basis of an assessment of technical cleanliness, which is performed, for example, under the following circumstances: — initial inspection and evaluation; — inspection of incoming and outgoing components; and — quality control or monitoring of manufacturing processes relevant to cleanliness (e.g. cleaning, surface treatment and assembly processes). This document is intended to improve the informative quality and comparability of test results. It also defines the standardized expression of cleanliness specifications and cleanliness test results in the quality chain of the automotive industry. This document does not apply to the following: — detection of filmy contamination (grease, oils, etc.); — application of non-quantifiable particulate detection methods on test components (e.g. visual assessment, wipe test with clean cloth, etc.); and — characterization of operating fluids (fuel, oils, coolants, brake fluid, etc.). This document does not define any cleanliness limit values for specific components or systems. The degree of cleanliness required for a specific component or system is dependent on a number of highly- individual factors. Cleanliness specifications are intended to be undertaken only by specialists who not only know the component concerned but also the system it is built into, the later conditions of use, technically-feasible practices and possible consequences for manufacturing processes and the supply chain. Guidance for deriving limit values can be found in Annex H.

Road vehicles — Cleanliness of components of fluid circuits — Part 10: Expression of results

ICS
13.040.50
CCS
发布
2018-12-12
实施
0000-00-00

Pollutant Emission Limits and Measurement Methods of Gasoline Vehicles under Steady State Loading

ICS
13.040.50
CCS
Z64
发布
2018-10-11
实施
2019-03-01

Pollutant Emission Limits and Measurement Methods for Diesel Vehicles Loading and Decelerating

ICS
13.040.50
CCS
Z64
发布
2018-10-11
实施
2019-03-01

1.1 This test method covers determination of organic and elemental carbon (OC and EC) in the particulate fraction of diesel engine exhaust, hereafter referred to as diesel particulate matter (DPM). Samples of workplace atmospheres are collected on quartz-fiber filters. The method also is suitable for other types of carbonaceous aerosols and has been widely applied to environmental monitoring. It is not appropriate for sampling volatile or semi-volatile components. These components require sorbents for efficient collection. NOTE 1—Sample collection and handling procedures for environmental samples differ from occupational samples. This standard addresses occupational monitoring of DPM in workplaces where diesel-powered equipment is used. 1.2 The method is based on a thermal-optical technique (1, 2).2 Speciation of OC and EC is achieved through temperature and atmosphere control, and an optical feature that corrects for sample charring (carbonization). 1.3 A portion of a 37-mm, quartz-fiber filter sample is analyzed. Results for the portion are used to calculate the total mass of OC and EC on the filter. The portion must be representative of the entire filter deposit. If the deposit is uneven, two or more representative portions should be analyzed for an average. Alternatively, the entire filter can be analyzed, in multiple portions, to determine the total mass. Open-faced cassettes give even deposits but may not be practical. At 2 L/min, closed-face cassettes generally give results equivalent to open-face cassettes if other dusts are absent. Higher flow rates may be employed, but closed-faced cassettes operated at higher flow rates (for example, 5 L/min) sometimes have uneven deposits due to particle impaction at the center of the filter. Other samplers may be required, depending on the sampling environment (2-5). 1.4 The calculated limit of detection (LOD) depends on the level of contamination of the media blanks (5). A LOD of approximately 0.2-µg carbon per cm2 of filter was estimated when analyzing a sucrose standard solution applied to filter portions cleaned immediately before analysis. LODs based on media blanks stored after cleaning are usually higher. LODs based on a set of media blanks analyzed over a six month period at a commercial laboratory were OC = 1.2 µg/cm2 , EC = 0.4 µg/cm2 , and TC = 1.3 µg/cm2 , where TC refers to total carbon (TC = OC + EC). In practice, the LOD estimate provided by a laboratory is based on results for a set of media blanks submitted with the samples. To reduce blank variability (due to lack of loading), a manual OC-EC split is assigned at the time when oxygen is introduced. With manual splits, the SD for media blanks is typically about 0.02–0.03 µg EC/cm2 , giving LODs (3 × SD blank) from about 0.06–0.09 µg EC/cm2 . The corresponding air concentration depends on the deposit area (filter size) and air volume. 1.5 OC-EC methods are operational, which means the analytical procedure defines the analyte. The test method offers greater selectivity and precision than thermal techniques that do not correct for charring of organic components. The analysis method is simple and relatively quick (about 15 min). The analysis and data reduction are automated, and the instrument is programmable (different methods can be saved as methods for other applications). 1.6 A method (5040) for DPM based on thermal-optical analysis has been published by the National Institute for Occupational Safety and Health (NIOSH). Method updates (3, 4) have been published since its initial (1996) publication in the NIOSH Manual of Analytical Methods (NMAM). Both OC and EC are determined by NMAM 5040. An EC exposure marker (for DPM) was recommended because EC is a more selective measure of exposure. A comprehensive review of the method and rationale for selection of an EC marker are provided in a Chapter of NMAM (5). 1.7 The thermal-optical instrument required for the analysis is manufactured by a private laboratory.3 As with most 1 This test method is under the jurisdiction of ASTM Committee D22 on Air Quality and is the direct responsibility of Subcommittee D22.04 on Workplace Air Quality. Current edition approved Oct. 1, 2018. Published October 2018. Originally approved in 2003. Last previous edition approved in 2013 as D6877 – 13ɛ1 . DOI: 10.1520/D6877-13R18. 2 The boldface numbers in parentheses refer to references at the end of this test method. 3 The carbon analyzer used in the development and performance evaluation of this test method was manufactured by Sunset Laboratory, 2017 19th Avenue, Forest Grove, Oregon 97116, which is the sole source of supply of the instrument known to the committee at this time. If you are aware of alternative suppliers, please provide this information to ASTM International Headquarters. Your comments will receive careful consideration at a meeting of the responsible technical committee,1 which you may attend. Copyright © ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959. United States 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. 1 instrumentation, design improvements continue to be made. Different laboratories may be using different instrument models. 1.8 The values stated in SI units are to be regarded as standard. No other units of measurement are included in this standard. 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. Specific precautionary statements are given in 7.1.5, 8.3, and 12.12.2. 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.

Standard Test Method for Monitoring Diesel Particulate Exhaust in the Workplace

ICS
13.040.50
CCS
发布
2018-10-01
实施

本标准适用于现有槟榔初加工和深加工企业大气、水和固废污染物排放管理,以及槟榔初加工和深加工新、改、扩建项目的环境影响评价、环境保护设施设计、竣工环境保护验收及其投产后的大气、水和固废污染物排放管理。

Pollutant Discharge Standards for Areca Nut Processing Industry

ICS
13.040.50
CCS
Z64
发布
2018-01-16
实施
2018-06-04



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