Z10 环境污染物监测方法 标准查询与下载

DIN EN 15169:2007 废弃物特性.测定废弃物、淤泥和沉淀物的点燃质量损耗

This European Standard specifices a method for the deternination of the loss on ignition. This procedure is applicable to all kinds of waste,sludge and sediments. The loss on ignition is often used as an estimate for the content of non-volatile organic matter in waste, aludge and sediments. it should be noted that any content of elementary carbon and volatilisation of organic materials or chemical reactions by inorganic compounds, is included in the loss on ignition.

Characterization of waste - Determination of loss on ignition in waste, sludge and sediments; English version of DIN EN 15169:2007-05

NF X30-427:2007 废弃物特征.通过测定干残渣和水含量计算干物质含量

Characterization of waste - Calculation of dry matter by determination of dry residue and water content.

DIN EN 14346:2007 废弃物特性.通过测定干残渣或水含量计算固形物含量

This European Standard specifies methods for the calculation of the dry matter of samples for which tt results of performed analysis are to be calculated to the dry matter basis. Depending on the nature of tt sample, the calculation is based on a determination of the dry residue (Method A) or a determination of tt water content (Method B). It applies to samples containing more than 1 % (m/m) of dry residue or more th< 1 % (m/m) of water.

Characterization of waste - Calculation of dry matter by determination of dry residue or water content; English version of DIN EN 14346:2007-03

BS PD CEN/TR 15310-1:2006 废弃物特性.废弃物材料取样.第1部分:多种条件下取样标准的选择和应用导则

This Technical Report discusses the statistical principles of sampling, and provides a number of statistical tools to assist in the design of testing programmes for application to sampling under various conditions. NOTE 1 Given the great variety of waste types, sampling situations and objectives, this Technical Report cannot provide definitive instructions that cover all scenarios. Instead, it discusses the basic statistical approach to be followed, and provides statistical tools that can be applied to determine the amount and type of sampling (e.g. number of samples and sample size) in any given situation to achieve results of adequate reliability (i.e. precision and confidence). NOTE 2 The document provides considerable detail on current best practice, but is not exhaustive. NOTE 3 To clarify the text, the document provides a number of worked examples.

Characterization of waste — Sampling of waste materials — Part 1: Guidance on selection and application of criteria for sampling under various conditions

BS PD CEN/TR 15310-2:2006 废弃物特性.废弃物材料取样.第2部分:采样技术指导

This Technical Report describes techniques for sampling liquid and granular waste material, including paste-like materials and sludges, found in a variety of locations. The Technical Report provides information to allow the selection and preparation of equipment and apparatus to be used in the sampling activity. NOTE 1 This Technical Report provides a shop shelf of example sampling techniques that can be selected to meet a wide range of sampling situations. For a specific situation one of the presented procedures may be appropriate. NOTE 2 The procedures listed in this Technical Report reflect current best practice, but these are not exhaustive and other procedures may be equally relevant.

Characterization of waste — Sampling of waste materials — Part 2: Guidance on sampling techniques

BS PD CEN/TR 15310-5:2006 废弃物特性.废料的抽样.第5部分:关于确定取样计划程序的导则

This Technical Report provides guidance on process of defining of a Sampling Plan based on the objective of the testing programme. It specifically deals with the strategic decisions that are needed, based on the sampling objective. NOTE 1 Given the great variety of waste types, sampling situations and objectives, this Technical Report cannot provide definitive instructions that cover all scenarios. Instead, it discusses the basic statistical approach to be followed, and provides statistical tools that can be applied to determine the amount and type of sampling (e.g. number of samples and sample size) in any given situation to achieve results of adequate reliability (i.e. precision and confidence). NOTE 2 The document provides considerable detail on current best practice, but is not exhaustive. NOTE 3 To clarify the text, the document provides a number of worked examples.

Characterization of waste — Sampling of waste materials — Part 5: Guidance on the process of defining the sampling plan

BS PD CEN/TR 15310-4:2006 废弃物的特性描述.废料的取样.第4部分:样品的包装、储存、保护、运输和交付规程导则

This Technical Report describes procedures for the packaging, preservation, short-term storage and transport of both solid and liquid waste samples, including paste-like substances and sludges. Where available and appropriate for field application, requirements for specific storage conditions and/or preservation methods should be selected from the chosen analytical standard and collaboration with the testing laboratory. NOTE 1 This Technical Report provides a shop shelf of example sampling techniques that can be selected to meet a wide range of sampling situations. For a specific situation one of the presented procedures may be appropriate. NOTE 2 The procedures listed in this Technical Report reflect current best practice, but these are not exhaustive and other procedures may be equally relevant.

Characterization of waste — Sampling of waste materials — Part 4: Guidance on procedures for sample packaging, storage, preservation, transport and delivery

BS PD CEN/TR 15310-3:2006 废弃物特性.废弃物材料取样.第3部分:现场的次级采样程序导则

This Technical Report describes procedures for reducing the overall size of the waste materials in the field to aid practical transportation of a sample to the laboratory. NOTE 1 This Technical Report provides a shop shelf of example sampling techniques that can be selected to meet a wide range of sampling situations. For a specific situation one of the presented procedures may be appropriate. NOTE 2 The procedures listed in this Technical Report reflect current best practice, but these are not exhaustive and other procedures may be equally relevant.

Characterization of waste — Sampling of waste materials — Part 3: Guidance on procedures for sub-sampling in the field

BS EN 14899:2005 废弃物的特性.废弃物材料的取样.制备框架和抽样检验方法应用

This European Standard specifies the procedural steps to be taken in the preparation and application of a Sampling Plan. The Sampling Plan describes the method of collection of the laboratory sample necessary for meeting the objective of the testing programme. The principles or basic rules outlined in this European Standard, provide a framework that can be used by the project manager to:  produce standardised Sampling Plans for use in regular or routine circumstances (elaboration of daughter/derived standards dedicated to well defined sampling scenarios);  incorporate the specific sampling requirements of European and national legislation;  design and develop a Sampling Plan for use on a case by case basis. This European Standard has been developed for the characterization of waste. There may be a need for more than one Sampling Plan to meet all the requirements of the testing programme. Ultimately the Sampling Plan provides the sampler with detailed instructions on how sampling should be carried out. NOTE Although this European Standard in most cases refers to the taking of one sample or increment or the preparation of one laboratory sample, it should be noted that often this should be more than one. For simplicity reasons this European Standard uses singular terms, while plural terms are also possible or even likely.

Characterization of waste - Sampling of waste materials - Framework for the preparation and application of a sampling plan

BS EN 12920:2006+A1:2008 废物特性.在规定条件下废物滤取性能的测定方法

This standard specifies a methodology for the determination of the leaching behaviour of waste under specified conditions (i.e. for a specified scenario including a specified time frame) in order to provide a solution to a defined problem. This applies to disposal and recovery scenarios. NOTE 1 Recovery is the term defined in the European Waste Acts . It includes re-use and recycling. !The term "waste" includes all categories of waste, such as municipal waste, waste from extractive industry etc." The external conditions which have a direct influence on the release of constituents from waste are considered. Migration of constituents leached from the disposal or the recovery site into the surrounding environment is not considered. Also the assessment of toxicity to humans or ecological impacts on flora and fauna as a secondary effect after release of constituents from the waste is not considered. NOTE 2 Present knowledge of highly complex scenarios and wastes may limit the ability to provide a clear solution to a defined problem. An example may be the land filling of complex mixtures of wastes or the prediction of the acid generation behaviour waste from the extractive industry

Characterization of waste - Methodology for the determination of the leaching behaviour of waste under specified conditions

DIN EN 14735 Corrigendum 1:2006 废弃物特征. 生物毒性试验用废弃物样品制备; 英文版本DIN EN 14735: 2005-11勘误表1

Characterization of waste - Preparation of waste samples for ecotoxicity tests Corrigendum 1 to English version of DIN EN 14735:2005-11

PD CEN/TR 15018:2004 废弃物特性.通过碱熔融技术进行废弃物样品分类

This Technical Report describes digestion methods for the determination of element contents of waste samples by using different alkali-fusion techniques.

Characterization of waste — Digestion of waste samples using alkali-fusion techniques

HJ/T 212-2005 污染源在线自动监控（监测）系统数据传输标准

本标准适用于污染源在线自动监控(监测)系统自动监控设备和监控中心之间的数据交换传输。本标准规定了数据传输的过程及系统对参数命令、交互命令、数据命令和控制命令的数据格式和代码定义，本标准不限制系统扩展其他的信息内容，在扩展内容时不得与本标准中所使用或保留的控制命令相冲突。 根据通信技术的发展，本标准将适时修订。

Standard for data communication of pollution emission auto monitoring system

ASTM E1527-05 现场环境评定的标准实施规程:第1阶段.现场环境评定程序

1.1 PurposeThe purpose of this practice is to define good commercial and customary practice in the United States of America for conducting an environmental site assessment of a parcel of commercial real estate with respect to the range of contaminants within the scope of Comprehensive Environmental Response, Compensation and Liability Act (CERCLA) (42 U.S.C. 9601) and petroleum products. As such, this practice is intended to permit a user to satisfy one of the requirements to qualify for the innocent landowner, contiguous property owner, or bona fide prospective purchaser limitations on CERCLA liability (hereinafter, the "landowner liability protections," or "LLPs"): that is, the practice that constitutes "all appropriate inquiry into the previous ownership and uses of the property consistent with good commercial or customary practice" as defined at 42 U.S.C. 9601(35)(B). (See for an outline of CERCLA''s liability and defense provisions.) Controlled substances are not included within the scope of this standard. Persons conducting an environmental site assessment as part of an EPA Brownfields Assessment and Characterization Grant awarded under CERCLA 42 U.S.C. 9604(k)(2)(B) must include controlled substances as defined in the Controlled Substances Act (21 U.S.C. 802) within the scope of the assessment investigations to the extent directed in the terms and conditions of the specific grant or cooperative agreement. Additionally, an evaluation of business environmental risk associated with a parcel of commercial real estate may necessitate investigation beyond that identified in this practice (see Sections 1.3 and 13).1.1.1 Recognized Environmental ConditionsIn defining a standard of good commercial and customary practice for conducting an environmental site assessment of a parcel of property, the goal of the processes established by this practice is to identify recognized environmental conditions. The term recognized environmental conditions means the presence or likely presence of any hazardous substances or petroleum products on a property under conditions that indicate an existing release, a past release, or a material threat of a release of any hazardous substances or petroleum products into structures on the property or into the ground, ground water, or surface water of the property. The term includes hazardous substances or petroleum products even under conditions in compliance with laws. The term is not intended to include de minimis conditions that generally do not present a threat to human health or the environment and that generally would not be the subject of an enforcement action if brought to the attention of appropriate governmental agencies. Conditions determined to be de minimis are not recognized environmental conditions.1.1.2 Petroleum ProductsPetroleum products are included within the scope of this practice because they are of concern with respect to many parcels of commercial real estate and current custom and usage is to include an inquiry into the presence of petroleum products when doing an environmental site assessment of commercial real estate. Inclusion of petroleum products within the scope of this practice is not based upon the applicability, if any, of CERCLA to petroleum products. (See X1.7 for discussion of petroleum exclusion to CERCLA liability.)1.1.3 CERCLA Requirements Other Than Appropriate InquiryThis practice does not address whether requirements in addition to all appropriate inquiry have been met in order to qualify for the LLPs (for example, the duties specified in 42 U.S.C. 9607(b)(3)(a) and (b) and cited in Appendix X1, including the continuing obligation not to impede the integrity and effectiveness of activity and use limitations (AULs), or the duty to take reasonable steps to prevent releases, or the duty to comply with legally required release reporting obligations).1.1.4 Other Federal, State, and Local Environmental LawsThis practice ......

Standard Practice for Environmental Site Assessments: Phase I Environmental Site Assessment Process

EN 14899:2005 废弃物特性.取样策略制定及应用的废弃物材料结构的取样

This European Standard specifies the procedural steps to be taken in the preparation and application of a Sampling Plan. The Sampling Plan describes the method of collection of the laboratory sample necessary for meeting the objective of the testing programme. The principles or basic rules outlined in this European Standard, provide a framework that can be used by the project manager to:  produce standardised Sampling Plans for use in regular or routine circumstances (elaboration of daughter/derived standards dedicated to well defined sampling scenarios);  incorporate the specific sampling requirements of European and national legislation;  design and develop a Sampling Plan for use on a case by case basis. This European Standard has been developed for the characterization of waste. There may be a need for more than one Sampling Plan to meet all the requirements of the testing programme. Ultimately the Sampling Plan provides the sampler with detailed instructions on how sampling should be carried out. NOTE Although this European Standard in most cases refers to the taking of one sample or increment or the preparation of one laboratory sample, it should be noted that often this should be more than one. For simplicity reasons this European Standard uses singular terms, while plural terms are also possible or even likely.

Characterization of waste Sampling of waste materials Framework for the preparation and application of a Sampling Plan

KS I ISO 11338-1:2004 固定源排放.气相和粒相多环芳香烃的测定.第1部分:取样

이 규격은 알루미늄 제련소, 코크스 공장, 쓰레기 소각로, 발전소와 산업용 및 가정용 연소

Stationary source emissions-Determination of gas and particle-phase polycyclic aromatic hydrocarbons-Part 1:Sampling

KS I ISO 11338-2:2004 固定源排放.气相和粒相多环芳香烃的测定.第2部分:样品制备、清洁和测定

이 규격은 굴뚝 및 폐기물 가스 중의 가스 및 입자상 다환 방향족 탄화수소(PAH) 측정을

Stationary source emissions-Determination of gas and particle-phase polycyclic aromatic hydrocarbons-Part 2:Sample preparation, clean-up and determination

ASTM F24-04 表面粒状杂质的测量和计数标准方法

1.1 This method covers the size distribution analysis of particulate contamination, 5 m or greater in size, either on, or washed from, the surface of small electron-device components. A maximum variation of two to one (33 % of the average of two runs) should be expected for replicate counts on the same sample.Note 1--For satisfactory results on clean parts, it is recommended that all procedures involved in sample preparation be conducted under a dust shield.

Standard Method for Measuring and Counting Particulate Contamination on Surfaces

ISO 11338-1:2003 固定源排放.气相和粒相多环芳香烃的测定.第1部分:取样

This part of ISO 11338 describes methods for the determination of the mass concentration of polycyclic aromatic hydrocarbons (PAHs) in flue gas emissions from stationary sources such as aluminium smelters, coke works, waste incinerators, power stations, and industrial and domestic combustion appliances. This part of ISO 11338 describes three sampling methods, which are here regarded as of equivalent value, and specifies the minimum requirements for effective PAH sampling. The three sampling methods are the dilution method (A), the heated filter/condenser/adsorber method (B) and the cooled probe/adsorber method (C). All three methods are based on representative isokinetic sampling, as the PAHs are commonly associated with particles in flue gas. Information is provided to assist in the choice of the appropriate sampling method for the measurement application under consideration. This part of ISO 11338 is not applicable to the sampling of fugitive releases of PAHs. NOTE Methods for sample preparation, clean-up and analysis are described in ISO 11338-2 and are intended to be combined with one of the sampling methods described in this part of ISO 11338 to complete the whole measurement procedure.

Stationary source emissions - Determination of gas and particle-phase polycyclic aromatic hydrocarbons - Part 1: Sampling

ISO 11338-2:2003 固定源排放.气相和粒相多环芳香烃的测定.第2部分:样品制备、清洁和测定

This part of ISO 11338 specifies procedures for sample preparation, clean-up and analysis for the determination of gas and particle-phase polycyclic aromatic hydrocarbons (PAH) in stack and waste gases. The analytical methods are capable of detecting sub-microgram concentrations of PAH per cubic metre of sample, depending on the type of PAH and the flue gas volume sampled. The methods described in this part of ISO 11338 are based on either high performance liquid chromatography (HPLC) or gas chromatography-mass spectrometry (GC-MS). NOTE ISO 11338-1 describes three methods and specifies minimum requirements for the sampling of PAH in stack and waste gases.

Stationary source emissions - Determination of gas and particle-phase polycyclic aromatic hydrocarbons - Part 2: Sample preparation, clean-up and determination