13.040.01 空气质量综合 标准查询与下载

ASTM D4096-17 测定大气中总悬浮颗粒物的标准试验方法（High&x2013；体积取样器法）

1.1 This test method provides for sampling a large volume of atmosphere, 1600 to 2400 m3 (55 000 to 85 000 ft3 ), by means of a high flow-rate vacuum pump at a rate of 1.13 to 1.70 m3 /min (40 to 60 ft3 /min) (1-4).2 1.2 This flow rate allows suspended particles having diameters of less than 100 µm (stokes equivalent diameter) to be collected. However, the collection efficiencies for particles larger than 20 µm decreases with increasing particle size and it varies widely with the angle of the wind with respect to the roof ridge of the sampler shelter and with increasing speed (5). When glass fiber filters are used, particles within the size range of 100 to 0.1 µm diameters or less are ordinarily collected. 1.3 The upper limit of mass loading will be determined by plugging of the filter medium with sample material, which causes a significant decrease in flow rate (see 6.4). For very dusty atmospheres, shorter sampling periods will be necessary. The minimum amount of particulate matter detectable by this method is 3 mg (95 % confidence level). When the sampler is operated at an average flow rate of 1.70 m3 /min (60 ft3 /min) for 24 h, this is equivalent to 1 to 2 µg/m3 (3). 1.4 The sample that is collected may be subjected to further analyses by a variety of methods for specific constituents. 1.5 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. 1.6 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. 1.7 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 Total Suspended Particulate Matter in the Atmosphere (High–Volume Sampler Method)

ASTM D8142-17 使用微尺度环境试验箱确定喷涂聚氨酯泡沫（SPF）绝缘的化学排放的标准测试方法

1.1 This test method is used to identify and to measure the emissions of volatile organic compounds (VOCs) emitted from samples of cured spray polyurethane foam (SPF) insulation using micro-scale environmental test chambers combined with specific air sampling and analytical methods for VOCs. 1.2 Specimens prepared from product samples are maintained at specified conditions of temperature, humidity, airflow rate, and elapsed time in micro-scale chambers that are described in Practice D7706. Air samples are collected periodically at the chamber exhaust at the flow rate of the micro-scale chambers. 1.2.1 Samples for formaldehyde and other low-molecular weight carbonyl compounds are collected on treated silica gel cartridges and are analyzed by high performance liquid chromatography (HPLC) as described in Test Method D5197 and ISO 16000-3. 1.2.2 Samples for other VOCs are collected on multisorbent samplers and are analyzed by thermal-desorption gas chromatography / mass spectrometry (TD-GC/MS) as described in U.S. EPA Compendium Method TO-17 and ISO 16000-6. 1.3 This test method is intended specifically for SPF insulation products. Compatible product types include two component, high pressure and two-component, low pressure formulations of open-cell and closed-cell SPF insulation. 1.4 VOCs that can be sampled and analyzed by this test method generally include organic blowing agents such as 1,1,1,3,3-pentafluoropropane, formaldehyde and other carbonyl compounds, residual solvents, and some amine catalysts. Emissions of some organic flame retardants can be measured after 24 h with this method, such as tris (chloroisopropyl) phosphate (TCPP). 1.5 This test method does not cover the sampling and analysis of methylene diphenyl diisocyanate (MDI) or other isocyanates. 1.6 Area-specific and mass-specific emission rates are quantified at the elapsed times and chamber conditions as specified in 13.2 and 13.3 of this test method. 1.7 This test method is used to identify emitted compounds and to estimate their emission factors at specific times. The emission factors are based on specified conditions, therefore, use of the data to predict emissions in other environments may not be appropriate and is beyond the scope of this test method. The results may not be representative of other test conditions or comparable with other test methods. 1.8 This test method is primarily intended for freshly applied, SPF insulation samples that are sprayed and packaged as described in Practice D7859. The measurement of emissions during spray application and within the first hour following application is outside of the scope of this test method. 1.9 This test method can also be used to measure the emissions from SPF insulation samples that are collected from building sites where the insulation has already been applied. Potential uses of such measurements include investigations of odor complaints after product application. However, the specific details of odor investigations and other indoor air quality (IAQ) investigations are outside of the scope of this test method. 1.10 The values stated in SI units are to be regarded as standard. No other units of measure are used. 1.11 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. 1.12 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 This test method is under the jurisdiction of ASTM Committee D22 on Air Quality and is the direct responsibility of Subcommittee D22.05 on Indoor Air. Current edition approved Oct. 1, 2017. Published October 2017. DOI: 10.1520/ D8142-17. 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 2. Referenced Documents

Standard Test Method for Determining Chemical Emissions from Spray Polyurethane Foam (SPF) Insulation using Micro-Scale Environmental Test Chambers

ASTM D5011-17 用传输标准校准臭氧监测仪的标准实践

1.1 These practices describe means for calibrating ambient, workplace or indoor ozone monitors, using transfer standards. 1.2 These practices describe five types of transfer standards: Practice A—Analytical instruments, Practice B—Boric acid potassium iodide (BAKI) manual analytical procedure, Practice C—Gas phase titration with excess nitric oxide, Practice D—Gas phase titration with excess ozone, and Practice E—Ozone generator device. 1.3 These practices describe procedures to establish the authority of transfer standards: qualification, certification, and periodic recertification. 1.4 The values stated in SI units are to be regarded as standard. No other units of measurement are included in this standard. 1.5 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. See Section 8 for specific precautionary statements. 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.

Standard Practices for Calibration of Ozone Monitors Using Transfer Standards

T/CIDAA 1-2017 室内环境净化治理施工服务规范

基本要求 4.1室内环境净化治理服务应遵循安全、适用、经济、有效的原则、在施工治理中应遵守国家法律法规和有关规定，执行国家、行业和地方有关安全、防火、环保等现行标准和技术规程。 4.2室内环境净化治理服务必须现场勘查、污染评估，并出具完整的治理方案。 4.3承担室内环境净化治理服务的企业应具备政府相关部门规定的资质。 4.4治理人员需持有室内环境治理员（包括专业咨询人员、专业勘察人员、技术负责人、治理施工人员、质量管理员等）上岗证。 4.5治理服务委托的从事室内空气质量检测机构需要符合《中华人民

Indoor environment purification treatment construction service standards

T/DLSNZS 0002-2017 室内环境净化治理服务规范

本标准规定了室内环境净化治理服务的术语和定义、基本要求、环境要求、安全要求、人员要求、配置要求、服务要求、验收规则、评估报告和跟踪服务。

Indoor environmental purification treatment service specification

ASTM E741-11(2017) 通过示踪气体稀释确定单个区域的空气变化的标准测试方法

1.1 This test method covers techniques using tracer gas dilution for determining a single zone’s air change with the outdoors, as induced by weather conditions and by mechanical ventilation. These techniques are: (1) concentration decay, (2) constant injection, and (3) constant concentration. 1.2 This test method is restricted to any single tracer gas. The associated data analysis assumes that one can characterize the tracer gas concentration within the zone with a single value. The zone shall be a building, vehicle, test cell, or any conforming enclosure. 1.3 Use of this test method requires a knowledge of the principles of gas analysis and instrumentation. Correct use of the formulas presented here requires consistent use of units, especially those of time. 1.4 Determination of the contribution to air change by individual components of the zone enclosure is beyond the scope of this test method. 1.5 The results from this test method pertain only to those conditions of weather and zonal operation that prevailed during the measurement. The use of the results from this test to predict air change under other conditions is beyond the scope of this test method. 1.6 The text of this test method references notes and footnotes which provide explanatory material. These notes and footnotes (excluding those in tables and figures) shall not be considered requirements of this test method. 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.

Standard Test Method for Determining Air Change in a Single Zone by Means of a Tracer Gas Dilution

DB11/T 1421-2017 温室气体排放核算指南 设施农业企业

Guidelines for Accounting Greenhouse Gas Emissions for Facility Agribusiness

DB11/T 1416-2017 温室气体排放核算指南 生活垃圾焚烧企业

Greenhouse Gas Emissions Accounting Guidelines for Household Waste Incineration Enterprises

DB11/T 1422-2017 温室气体排放核算指南 畜牧养殖企业

Greenhouse Gas Emissions Accounting Guidelines for Animal Husbandry and Breeding Enterprises

ASTM D7706-17 使用微量室快速筛选产品VOC排放的标准实践

1.1 This practice describes a micro-scale chamber apparatus and associated procedures for rapidly screening materials and products for their vapor-phase emissions of volatile organic compounds (VOCs) including formaldehyde and other carbonyl compounds. It is intended to complement, not replace reference methods for measuring chemical emissions for example, small-scale chamber tests (Guide D5116) and emission cell tests (Practice D7143). 1.2 This practice is suitable for use in and outside of laboratories, in manufacturing sites and in field locations with access to electrical power. 1.3 Compatible material/product types that may be tested in the micro-scale chamber apparatus include rigid materials, dried or cured paints and coatings, compressible products, and small, irregularly-shaped components such as polymer beads. 1.4 This practice describes tests to correlate emission results obtained from the micro-scale chamber with results obtained from VOC emission reference methods (for example, Guide D5116, Test Method D6007, Practice D7143, and ISO 16000-9 and ISO 16000-10). 1.5 The micro-scale chamber apparatus operates at moderately elevated temperatures, 30°C to 60°C, to eliminate the need for cooling, to reduce test times, boost emission rates, and enhance analytical signals for routine emission screening, and to facilitate screening of semi-volatile VOC (SVOC) emissions such as emissions of some phthalate esters and other plasticizers. 1.6 Gas sample collection and chemical analysis are dependent upon the nature of the VOCs targeted and are beyond the scope of this practice. However, the procedures described in Test Method D7339, Practice D6196 and ISO 16000-6 for analysis of VOCs and in Test Method D5197 and ISO 16000-3 for analysis of formaldehyde and other carbonyl compounds are applicable to this practice. 1.7 The values stated in SI units are to be regarded as standard. No other units of measurement are included in this standard. 1.8 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 and health practices and determine the applicability of regulatory limitations prior to use. 1.9 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 Practice for Rapid Screening of VOC Emissions from Products Using Micro-Scale Chambers

VDI 3783 Blatt 19-2017 环境气象学 二氧化氮浓度测定的反应机理

The combustion of fossil fuels, e.g. in engines of vehicles or in large-scale combustion plants, produces nitrogen monoxide (NO) and nitrogen dioxide (NO2), gases that are significant for air quality. In the atmosphere, NO and NO2 undergo chemical reactions that depend on meteorological conditions and on the trace gas composition of the ambient air. This standard describes an extended reaction system which accounts for the chemistry of nitrogen oxides with sufficient accuracy, in order to allow a quantitative immission forecast as part of a chemistry and transport model. It is suitable for evaluating procedures for reducing nitrogen oxide pollution with the aim of complying with statutory provisions.

Environmental meteorology - Reaction mechanism for the determination of the nitrogen dioxide concentration

VDI 3783 Blatt 18-2017 环境气象学 用于计算对流层污染物浓度的光解频率

The transformation of trace gases in the atmosphere is determined by radical chain reactions initiated by photolysis processes. More detailed assessment and prediction of air quality, therefore, require knowledge of photolysis frequencies. This standard provides photolysis frequencies for tropospheric conditions. To this end, spectral actinic photon flux densities were calculated for a large number of meteorological situations so as to cover typical conditions for Central Europe, with 200 m above sea level taken as the average altitude. The output of the calculation is done for the altitudes 0 m and 1000 m above ground.

Environmental meteorology - Photolysis frequencies for calculating pollutant concentrations in the troposphere

VDI 4221 Blatt 2-2017 质量保证 排放控制中实验室间测试的要求 实验室条件下排放测量方法的实验室间测试的设计、性能和评估

This standard specifies requirements on the design of interlaboratory testing schemes and the performance and evaluation of interlaboratory tests for emission measurement methods under laboratory conditions. This standard applies to interlaboratory testing schemes for checking the quality of laboratories and for checking measuring systems and measurement methods for the determination of emissions at stationary sources. These schemes include interlaboratory tests for particulate matter and chemicals adsorbed onto particles as well as for gaseous inorganic and organic chemical compounds. This standard may be applied in conjunction with VDI 4221 Part 1 only. This standard applies to providers of interlaboratory tests, to accreditation bodies, to testing laboratories and competent authorities in the field of immission control.

Quality assurance - Requirements on interlaboratory tests in immission control - Design, performance and evaluation of interlaboratory tests for emission measurement methods under laboratory conditions

VDI 3491 Blatt 2-2017 颗粒的测量 产生测试气溶胶的方法 分散液体

The standard describes methods for the preparation of test aerosols which are based on the dispersion of liquids (pure substances, solutions, suspensions, emulsions). These methods can be used for calibrating, adjusting or checking of particle counters as well as for checking the sampling, conditioning and dilution systems of these instruments.

Measurement of particles - Methods for generating test aerosols - Dispersing liquids

ASTM D4096-17(2017) 测定大气中总悬浮颗粒物的标准试验方法（High&x2013；体积取样器法）

1.1 This test method provides for sampling a large volume of atmosphere, 1600 to 2400 m3 (55 000 to 85 000 ft3 ), by means of a high flow-rate vacuum pump at a rate of 1.13 to 1.70 m3 /min (40 to 60 ft3 /min) (1-4).2 1.2 This flow rate allows suspended particles having diameters of less than 100 µm (stokes equivalent diameter) to be collected. However, the collection efficiencies for particles larger than 20 µm decreases with increasing particle size and it varies widely with the angle of the wind with respect to the roof ridge of the sampler shelter and with increasing speed (5). When glass fiber filters are used, particles within the size range of 100 to 0.1 µm diameters or less are ordinarily collected. 1.3 The upper limit of mass loading will be determined by plugging of the filter medium with sample material, which causes a significant decrease in flow rate (see 6.4). For very dusty atmospheres, shorter sampling periods will be necessary. The minimum amount of particulate matter detectable by this method is 3 mg (95 % confidence level). When the sampler is operated at an average flow rate of 1.70 m3 /min (60 ft3 /min) for 24 h, this is equivalent to 1 to 2 µg/m3 (3). 1.4 The sample that is collected may be subjected to further analyses by a variety of methods for specific constituents. 1.5 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. 1.6 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. 1.7 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 Total Suspended Particulate Matter in the Atmosphere (High–Volume Sampler Method)

ASTM D5116-17 小型环境室法测定室内材料/制品中挥发性有机物排放的标准指南

4.1 Objectives—The use of small chambers to evaluate VOC emissions from indoor materials has several objectives: 4.1.1 Develop techniques for screening of products for VOC emissions; 4.1.2 Determine the effect of environmental variables (that is, temperature, humidity, air speed, and air change rate) on emission rates; 4.1.3 Rank various products and product types with respect to their emissions profiles (for example, emission factors, specific organic compounds emitted); 4.1.4 Provide compound-specific data on various organic sources to guide field studies and assist in evaluating indoor air quality in buildings; 4.1.5 Provide emissions data for the development and verification of models used to predict indoor concentrations of organic compounds; and 4.1.6 Develop data useful to stakeholders and other interested parties for assessing product emissions and developing control options or improved products. 4.2 Mass Transfer Considerations—Small chamber evaluation of emissions from indoor materials requires consideration of the relevant mass transfer processes. Three fundamental processes control the rate of emissions of organic vapors from indoor materials; evaporative mass transfer from the surface of the material to the overlying air, desorption of adsorbed compounds, and diffusion within the material. 4.2.1 The evaporative mass transfer of a given VOC from the surface of the material to the overlying air can be expressed as: where: ER   =   emission rate, mg/h, A   =   source area, m2, km   =   mass transfer coefficient, m/h, VPs   =   vapor pressure at the surface of the material, Pa, VPa   =   vapor pressure in the air above the surface, Pa, MW   =   molecular weight, mg/mol,

Standard Guide for Small-Scale Environmental Chamber Determinations of Organic Emissions from Indoor Materials/Products

GSO ISO 7168-2:2016 空气质量 数据交换 第2部分：压缩数据格式

This part of ISO 7168 specifies a condensed data format for presentation of air quality data. Contrary to the general data format specified in ISO 7168-1, the condensed data format reduces the file size. This format is intended particularly for exchanging files between automatic data processing systems. Therefore, it is restricted to the minimum information necessary for processing data.

Air quality -- Exchange of data -- Part 2: Condensed data format

GSO ISO 7168-1:2016 空气质量 数据交换 第1部分：通用数据格式

This part of ISO 7168 specifies a general format for the exchange of air quality data and related information. It defines mandatory and optional keywords to identify the data presented in a data file, and the values and formats of the data allocated to a keyword. This part of ISO 7168 is recommended for the international exchange of air quality data. It is also intended for direct data import, e.g. into spreadsheets.

Air quality -- Exchange of data -- Part 1: General data format

GSO ISO 16017-1:2016 室内、环境和工作场所空气 采用吸附管/热解吸/毛细管气相色谱法对挥发性有机化合物进行采样和分析 第1部分：泵送采样

This part of ISO 16017 gives general guidance for the sampling and analysis of volatile organic compounds (VOCs) in air. It is applicable to ambient, indoor and workplace atmospheres and the assessment of emissions from materials in small- or full-scale test chambers. This part of ISO 16017 is appropriate for a wide range of VOCs, including hydrocarbons, halogenated hydro­carbons, esters, glycol ethers, ketones and alcohols. A number of sorbents 1) are recommended for the sampling of these VOCs, each sorbent having a different range of applicability. Very polar compounds will generally require derivatization, very low boiling compounds will only be partially retained by the sorbents, depending on ambient temperature, and can only be estimated qualitatively. Semi-volatile compounds will be fully retained by the sorbents, but may only be partially recovered. Compounds for which this part of ISO 16017 has been tested are given in tables. This part of ISO 16017 may be applicable to compounds not listed, but in these cases it is advisable to use a back-up tube containing the same or a stronger sorbent. This part of ISO 16017 is applicable to the measurement of airborne vapours of VOCs in a concentration range of approximately 0,5 mg/ m3 to 100 mg/m3 individual compound. The upper limit of the useful range is set by the sorptive capacity of the sorbent used and by the linear dynamic range of the gas chromatograph column and detector or by the sample-splitting capability of the analytical instrumentation used. The sorptive capacity is measured as a breakthrough volume of air, which determines the maximum air volume that shall not be exceeded when sampling. The lower limit of the useful range depends on the noise level of the detector and on blank levels of analyte and/or interfering artefacts on the sorbent tubes. Artefacts are typically sub-nanogram for well-conditioned Tenax GR and carbonaceous sorbents such as Carbopack/Carbotrap type materials, carbonized molecular sieves and molecular sieves such as Spherocarb, or pure charcoal; at low nanogram levels for Tenax TA and at 5 ng to 50 ng levels for other porous polymers such as Chromosorbs and Porapaks. Sensitivity is typically limited to 0,5 μg/m3 for 10-litre air samples with this latter group of sorbents because of their inherent high background. The procedure specified in this part of ISO 16017 is applicable to low flowrate personal sampling pumps and gives a time-weighted average result. It is not applicable to the measurement of instantaneous or short-term fluctuations in concentration.

Indoor, ambient and workplace air -- Sampling and analysis of volatile organic compounds by sorbent tube/thermal desorption/capillary gas chromatography -- Part 1: Pumped sampling

DB44/T 1947-2016 固定污染源 挥发性有机物排放连续自动监测系统 光离子化检测器（PID）法技术要求

本标准适用于广东省固定污染源总挥发性有机物排放连续自动监测系统（光离子化检测器法）的应用选型、性能检验及验收。 本标准不适用于电离能较高的挥发性有机物排放监测。

Technical Requirements for Photoionization Detector (PID) Method of Continuous Automatic Monitoring System for Volatile Organic Compound Emissions from Stationary Pollution Sources