Z60 污染物排放综合 标准查询与下载

EN 1948-1:2006 固定源排放限值.PCDDs/PCDFs和类二氧芑PCBs的质量浓度的测定.第1部分:PCDDs/PCDFs的抽样

This European Standard has been developed to measure PCDD/PCDF concentrations at about 0,1 ng I-TEQ/m3 in stationary source emissions. This European Standard specifies both method validation and a framework of quality control requirements which shall be fulfilled by any PCDD/PCDF sampling. The user has the possibility to choose between three different methods: ⎯ "filter/condenser method" ⎯ "dilution method" ⎯ "cooled probe method" Each sampling method is illustrated by some sampling systems described in detail in Annex B as examples of proven procedures. During comparison measurements of the three sampling methods on municipal waste incinerators at the level of about 0,1 ng I-TEQ/m3 these methods have been deemed comparable within the expected range of uncertainty. Validation trials were performed on the flue gas of municipal waste incinerators at the level of about 0,1 ng I-TEQ/m3 and a dust loading of from 1 mg/m3 to 15 mg/m3. Although this European Standard is primarily developed and validated for gaseous streams emitted by waste incinerators, the practical experience shows that it can be applied for wide concentration ranges and various emission sources. The procedure described in the three parts of EN 1948 specifies requirements which shall be met in order to measure the 17 congeners necessary to calculate the total I-TEQ (see Table A.1). Besides the determination of PCDDs/PCDFs the described measurement methods are suitable for determination of other low-volatile substances, e.g. of dioxin-like PCBs (details for sampling and analyses see CEN/TS 1948-4), although no validated performance characteristics are available yet.

Stationary source emissions - Determination of the mass concentration of PCDDs/PCDFs and dioxin-like PCBs - Part 1: Sampling of PCDDs/PCDFs

EN 1948-2:2006 固定源排放限值.PCDDs/PCDFs和类二氧芑PCBs的质量浓度的测定.第2部分:PCDDs/PCDFs的萃取和提炼

This European Standard specifies the extraction and clean-up procedures of the sampled PCDDs/PCDFs. It is an integral part of the complete measurement procedure. The use of the other two parts EN 1948-1:2006 and EN 1948-3:2006 describing sampling or identification and quantification, respectively, is necessary for the determination of the PCDDs/PCDFs. This European Standard has been designed to measure PCDD/PCDF concentrations at about 0,1 ng I-TEQ/m3 in stationary source emissions. This European Standard specifies both method validation and a framework of quality control requirements which shall be fulfilled by any PCDD/PCDF extraction and clean-up methods to be applied. Some methods are described in detail in Annex A as examples of proven procedures. Each of the three sampling methods (Part 1) can be combined with the extraction and clean-up (Part 2) and the identification and quantification (Part 3) to complete the measurement procedure. During comparison measurements of the three sampling methods on municipal waste incinerators at the level of about 0,1 ng I-TEQ/m3 these methods have been deemed comparable within the expected range of uncertainty. Validation trials were performed on the flue gas of municipal waste incinerators at the level of about 0,1 ng I-TEQ/m3 and a dust loading of from 1 mg/m3 to 15 mg/m3. Although this European Standard is primarily developed and validated for gaseous streams emitted by waste incinerators, the practical experience shows that it can be applied for wide concentration ranges and various emission sources. The procedure described in the three parts of EN 1948:2006 specifies requirements which shall be met in order to measure the 17 congeners necessary to calculate the total I-TEQ (see Table A.1 of EN 1948-1:2006). Besides the determination of PCDDs/PCDFs the described measurement methods are suitable for determination of other low-volatile substances, e.g. of dioxin-like PCBs (details for sampling and analyses see CEN/TS 1948-4), although no validated performance characteristics are available yet.

Stationary source emissions - Determination of the mass concentration of PCDDs/PCDFs and dioxin-like PCBs - Part 2: Extraction and clean-up of PCDDs/PCDFs

BS DD CEN/TS 14429:2005 废弃物特性描述.渗出特性试验.pH值对初始渗出酸/碱性添加物的影响

This Technical Specification is applicable to determine the influence of pH on the leachability of inorganic constituents from a waste material. Equilibrium condition as defined in the standard is established by addition of pre-determined amounts of acid or base to reach desired end pH values. This test method produces eluates, which are subsequently characterized physically and chemically. This Technical Specification is a parameter specific test as specified in ENV 12920. The application of this test method alone is not sufficient for the determination of the detailed leaching behaviour of a waste under specified conditions. NOTE This generally requires the application of several test methods, behavioural modelling and model validation as specified in ENV 12920.

Characterisation of waste - Leaching behaviour tests - Influence of pH on leaching with initial acid/base addition

BS EN 14884:2005 空气质量.固定源排放.总汞含量的测定:自动测量系统

This European Standard specifies specific requirements on automated measuring systems (AMS) for monitoring of total mercury. It is derived from EN 14181, which is the general document on the quality assurance of AMS. It is only applicable in conjunction with EN 14181. This European Standard sets specific requirements for the quality assurance levels and annual surveillance test as specified in EN 14181, for mercury AMS used for proving that the mercury emissions from a source are compliant with emission limits between 0,03 mg/m3 and 0,5 mg/m3 1) (standard conditions) in ducted gaseous streams. This European Standard is applicable by direct correlation with the standard reference method (SRM) described in EN 13211. This European Standard is primarily developed for emissions from waste incinerators. From a technical point of view, it may be applied to other processes, for which measurement at an emission limit is required with defined uncertainty.

Air quality - Stationary source emissions - Determination of total mercury: automated measuring systems

BS EN 14790:2005 固定源排放.管道中水蒸汽的测定

This European Standard describes the condensation/adsorption technique, including the sampling system, to determine the water vapour concentration in the flue gases emitting to atmosphere from ducts and stacks. This technique is usually used all over Europe for water vapour monitoring. However to be implemented as the Standard Reference Method (SRM), the user has to demonstrate that the performance characteristics of the method are better than the performance criteria defined in this European Standard and that the overall uncertainty of the method is less than ± 20 % of the measured value. This European Standard as the Standard Reference Method (SRM) is used for periodic monitoring and for calibration or control of Automatic Measuring Systems (AMS) permanently installed on a stack, for regulatory purposes or other purposes. An Alternative Method to this SRM may be used provided that the user can demonstrate equivalence according to the Technical Specification CEN/TS 14793, to the satisfaction of his national accreditation body or law. The determination of water vapour is mainly necessary for:  regulatory purposes, to express the concentration at standard conditions (on dry gas);  adjust the flow rate for isokinetic sampling, when a dry gas flow rate metering device is used. For both applications, the quantity to be measured is the amount of water present in the gas phase (vapour), which does not include water droplets. This European Standard is applicable in the range from 4 % to 40 % relative humidity and for water vapour concentration from 29 g/m3 to 250 g/m3 as a wet gas, although for a given temperature the upper limit of the method is related to the maximum pressure of water in air or in the gas. This European Standard has been evaluated during field tests on waste incineration, co-incineration and large combustion installations. It has been validated for sampling periods of 30 min in the concentration range of 7 % to 26 % volume. In this European Standard all the concentrations are expressed in normal conditions (273 K and 101,3 kPa). NOTE For saturated conditions the condensation/adsorption method is not applicable. Some guidance is given in this European Standard to deal with flue gas when droplets are present.

Stationary source emissions - Determination of the water vapour in ducts

BS EN 14792:2005 固定源排放.氧化氮(NOx)质量浓度的测定.基准方法:化学发光

This European Standard describes the chemiluminescence method, including the sampling and the gas conditioning system, to determine the NO/NO2/NOx concentrations in flue gases emitted from ducts and stacks to atmosphere. This European Standard is the Standard Reference Method (SRM) for periodic monitoring and for calibration or control of Automatic Measuring Systems (AMS) permanently installed on a stack, for regulatory or other purposes such as calibration. To be used as the SRM, the user shall demonstrate that the performance characteristics of the method are better than the performance criteria defined in this European Standard and that the overall uncertainty of the method is less than ± 10 % relative at the daily Emission Limit Value (ELV). NOTE When the chemiluminescence method is the measurement principle used for AMS, reference should be made to EN 14181 and other relevant standards provided by CEN TC 264. An Alternative Method to this SRM may be used provided that the user can demonstrate equivalence according to the Technical Specification CEN TS 14793, to the satisfaction of his national accreditation body or law. This SRM has been evaluated during field tests on waste incineration, co-incineration and large combustion installations. It has been validated for sampling periods of 30 min in the range of 0 mg NO2/m3 to 1 300 mg NO2/m3 for large combustion plants and 0 mg NO2/m3 to 400 mg NO2/m3 for waste incineration, according to emission limit values (ELVs) laid down in the following Council Directives:  Council Directive 2001/80/EC on the limitation of emissions of certain pollutants into the air from large combustion plants;  Council Directive 2000/76/EC on waste incineration plants. The ELVs for NOx (NO + NO2) in EU directives are expressed in mg NO2/m3, on dry basis, at a reference value for O2 and at the reference conditions (273 K and 101,3 kPa).

Stationary source emissions - Determination of mass concentration of nitrogen oxides (NOx) - Reference method: Chemiluminescence

ASTM D7295-06 在燃料渗出液和固定排放源中氰化物取样和测定的标准实施规程

Hydrogen cyanide is highly toxic. In relatively low quantities, hydrogen cyanide can cause asphyxia and death. The National Fire Protection Association has assigned a flammability rating of 4 (severe fire hazard) to hydrogen cyanide.1.1 This practice is used to determine the concentration of gaseous hydrogen cyanide (HCN) from any combustion device or atmosphere where cyanide may be present. While primarily designed for the measurement of gas phase HCN, the sample collection described in this practice also includes cyanide ion (CN-) absorbed particles that may be present in the sampling atmosphere.1.1.1 Samples can be collected from a closed chamber such as the NBS smoke box described in Test Method E 662 provided it is equipped with sampling ports.1.1.2 Open chambers such as industrial work areas or large scale fires can be monitored for HCN with this practice.1.1.3 The HCN emissions of a flow through system can be determined by sampling from its discharge stack. Examples of such systems include large scale manufacturing applications and the cone calorimeter described in Test Method E 1354.1.2 This practice can be used to monitor HCN levels in lab scale fire smoke effluents in order to estimate toxicity of gases produced from burning materials. See Guide E 800.1.3 The concentration range of hydrogen cyanide will be dependent on the volume of gas sampled, the volume of sodium hydroxide solution placed in the impinger during sampling, and the analytical method used to measure cyanide. For example, the lower limit of detection would be 0.002-mg/m3 when 0.1-m3 of combustion effluent is collected into 100-mL sodium hydroxide solution based on a detection limit of 0.002 mg/L cyanide in the impinger solution when using the flow injection analysis (FIA) system described in Test Method D 6888.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.

Standard Practice for Sampling and Determination of Hydrogen Cyanide (HCN) in Combustion Effluents and Other Stationary Sources

ASTM D7296-06 用干扫取样法收集固定尘灰连续测定铍化合物的标准实施规范

This practice is intended for the collection of settled dust samples for the subsequent measurement of beryllium and compounds. The practice is meant for use in the collection of settled dust samples that are of interest in clearance, hazard evaluation, risk assessment, and other purposes. This practice is intended solely for the collection of settled dust samples from hard, relatively smooth nonporous surfaces that may be compromised by water or other wetting agents and that are therefore not suitable for wet wipe sampling using Practice D 6966 or micro-vacuum sampling using Practice D 7144. Use of this practice for any purpose other than the intended purpose is discouraged due to the limited collection efficiency and high variability of dry wipe sampling as compared to wetted wipe or micro-vacuum sampling3 . This practice is less effective for collecting settled dust samples from surfaces with substantial texture such as rough concrete, brickwork, textured ceilings, and soft fibrous surfaces such as upholstery and carpeting. Micro-vacuum sampling using Practice D 7144 may be more suitable for these surfaces.1.1 This practice covers the collection of settled dust containing beryllium and/or beryllium compounds on surfaces using the dry wipe sampling method. These samples are collected in a manner that will permit subsequent extraction and determination of beryllium and compounds in the wipes using laboratory analysis techniques such as atomic spectrometry or fluorescence detection.1.2 This practice is limited in its scope to applications where wetted wipe sampling (using Practice D 6966) or vacuum sampling (using Practice D 7144) is not physically feasible (for example, if the surface to be wiped would be compromised by use of wetted wipes).1.3 This practice does not address the sampling design criteria (that is, sampling plan which includes the number and location of samples) that are used for clearance, hazard evaluation, risk assessment, and other purposes. To provide for valid conclusions, sufficient numbers of samples should be obtained as directed by a sampling plan.1.4 This practice contains notes that are explanatory and are not part of the mandatory requirements of this practice.1.5 The values stated in SI units are to be regarded as standard.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.

Standard Practice for Collection of Settled Dust Samples Using Dry Wipe Sampling Methods for Subsequent Determination of Beryllium and Compounds

DB11/ 307-2005 水污染物排放标准

本标准按照污水排放去向，分级规定了75种水污染物的最高允许排放限值。本标准适用于北京市辖区内现有单位和个体经营者水污染物的排放管理，以及建设项目的环境影响评价、建设项目环境保护设施设计和竣工验收及其投产后的排放管理。

Discharge standard of water pollutants

DB37/T 532-2005 水泥工业大气污染物排放标准

本标准按时段分别规定了山东省境内的水泥工业各生产设备排气筒大气污染物排放限值、作业场所粉尘无组织排放限值，以及环保相关管理规定等。 本标准适用于对山东省境内的现有水泥生产企业及水泥制品生产企业的大气污染物排放管理，以及对新建、改建、扩建水泥矿山、水泥制造和水泥制品生产线的环境影响评价、设计、竣工验收及其建成后的大气污染物排放管理。

Air Pollutant Emission Standards for Cement Industry

BS EN 13284-2:2004 固定源排放.尘埃的低倍率质量浓度测定.自动测量系统

This document specifies specific requirements on automated measuring systems (AMS) for dust monitoring. It is derived from EN 14181 which is the general document on the quality assurance of AMS. It is only applicable in conjunction with EN 14181. This document specifies test criteria for the QAL1 and specific requirements for QAL2, QAL3 and AST for dust AMS used for proving that the dust emissions from a source are compliant with emission limits below 50 mg/m (standard conditions) in ducted gaseous streams. This document is applicable by direct correlation with the standard reference method (SRM) described in EN 13284-1. This document is primarily developed for emissions from waste incinerators. From a technical point of view, it may be applied to other processes, for which measurement at an emission limit is required with defined uncertainty.

Stationary source emissions - Determination of low range mass concentration of dust - Part 2: Automated measuring systems

BS EN 13284-2:2005 固定源排放.尘埃的低倍率质量浓度测定.自动测量系统

Stationary source emissions - Determination of low range mass concentration of dust - Automated measuring systems

DB11/ 237-2004 冶金、建材行业及其它工业炉窑 大气污染物排放标准

本标准规定了冶金、建材行业生产过程，以及其它行业(不含化工)工业炉窑的大气污染物排放浓度限值(包括无组织排放)、不透光率限值和最高允许排放速率要求，同时还规定了排气筒高度要求、工艺管制和操作规范、燃料有害物控制标准。本标准适用于对现有源的大气污染物排放管理，以及对新建、改建、扩建项目的环境影响评价、设计、竣工验收及其建成后的大气污染物排放管理。

Emission standards of air pollutants for metallurgical industry, building materials industry and other industrial furnaces

DB65/ 2154-2004 燃煤锅炉大气污染物排放标准

Air Pollutant Emission Standards for Coal-fired Boilers

NY 687-2003 天然橡胶加工废水污染物排放标准

本标准按生产工艺和废水污染物排放去向，分年限规定了天然橡胶加工废水最高允许排放浓度和 吨产品最高允许排水量。 本标准适用于天然橡胶加工废水污染物的排放监督管理，以及建设项目的环境影响评价、设计、竣 工验收及建成后的排放管理。

Discharge standard of wastewater pollution for natural rubber processing

BS ISO 3929:2003 道路车辆.在检验或维修过程中废气排放量的测量方法

This International Standard specifies methods for the direct measurement of the concentration of exhaust gas emissions from road vehicles during inspection or maintenance. It is applicable to vehicles having a maximum authorized total mass (ISO-M08, as defined in ISO 1176) not exceeding 3,5t, equipped with controlled ignition engines, but excluding those supplied with a fuel/oil mixture (with or without automatic mixer). The methods can be used, either totally or partially, for — periodic inspections in official garages, — official roadside checks (e.g. by police), and — maintenance and diagnostic operations.

Road vehicles. Measurement methods for exhaust gas emissions during inspection or maintenance

DB12/ 151-2003 锅炉大气污染物排放标准

Boiler Air Pollutant Emission Standards

DB44/ 56-2003 茂名市水污染物排放限值

本标准分年限规定74种水污染物排放限值，同时规定执行标准中的各种要求。本标准适用于茂名市境内除船舶、船舶工业、海洋石油开发工业、航大推进剂使用、兵器工业等行业外的现有单位水污染物的排放管理、建设项目的环境影响评价、建设项目环境保护设施设计、竣工验收及其投产后的排放管理。

Discharge limits of water pollutants of Maoming

DB37/T 335-2003 无公害金乡大蒜

本标准按生产原料及产品规定了山东省辖区内造纸工业吨产品日均量最高允许排水量，日均最高允许水污染物排放浓度和吨产品最高允许水污染物排放量（以季为考核单位）

Pollution-free Jinxiang Garlic

BS ISO 9096:2003 固定源排放.颗粒物质量浓度的人工测定

This International Standard describes a reference method for the measurement of participate matter (dust) concentration in waste gases of concentrations from 20 mg/m to 1000 mg/m under standard conditions. This International Standard is applicable to the calibration of automated monitoring systems (AMS). If the emission gas contains unstable, reactive or semi-volatile substances, the measurement will depend on the filtration temperature. In-stack methods may be more applicable than out-stack methods for the calibration of automated monitoring systems.

Stationary source emissions - Manual determination of mass concentration of particulate matter