13.030.10 固态废物 标准查询与下载



共找到 308 条与 固态废物 相关的标准,共 21

This Technical Specification is applicable for determining the leaching behaviour of monolithic wastes under dynamic conditions. The test is performed under experimental conditions relevant to assess the leaching behaviour in view of the considered scenario(s). This test is aimed at determining the release as a function of time of inorganic constituents from a monolithic waste, when it is put into contact with an aqueous solution (leachant). In general, the composition, the temperature and the continuous renewal rate of the leachant are chosen such that the leaching behaviour of the waste material can be studied in view of the considered disposal or recovery scenario. When the release is to be determined without any reference to a specific scenario, the leachant is demineralised water, the temperature and the continuous renewal rate are fixed. This dynamic monolithic leaching test (DMLT) is a parameter specific test as specified in EN 12920 and is then not aimed at simulating real situations. The application of this test method alone is not sufficient for the determination of the detailed leaching behaviour of a monolithic waste under specified conditions. In the framework of EN 12920 and in combination with additional chemical information, the test results are used to identify the leaching mechanisms and their relative importance. The intrinsic properties can be used to predict the release of constituents at a given time frame, in order to assess the leaching behaviour of monolithic waste materials, placed in different situations or scenarios (including disposal and utilisation scenarios). The test method applies to regularly shaped test portions of monolithic wastes with minimum dimensions of 40 mm in all directions that are assumed to maintain their integrity over a time frame relevant for the considered scenario. The test method applies to test portions for which the geometric surface area can be determined with the help of simple geometric equations. The test method applies to low permeable monolithic materials. NOTE 1 If, in order to comply with the requirements of regular shape, the test portion is prepared by cutting or coring, then new surfaces are exposed which can lead to change(s) in leaching properties. On the other hand if the test portion is prepared by moulding, the surface will be dependent to the type of mould and the conditions of storage. If the intention is to evaluate the behaviour of the material core, the specimen needs to be stored without any contact with air to avoid carbonation. NOTE 2 For monolithic waste materials with a saturated hydraulic conductivity higher than 10-8m·s-1, water is likely to percolate through the monolith rather than flow around it. In such cases, relating the release to the geometric surface area can lead to misinterpretation. A percolation test is then more appropriate (e. g. CEN/TS 14405). This procedure may not be applicable to materials reacting with the leachant, leading for example to excessive gas emission or an excessive heat release.

Characterisation of waste - Leaching behaviour test for basic characterisation - Dynamic Monolithic Leaching Test with continuous leachant renewal under conditions relevant for specified scenario(s)

ICS
13.030.10
CCS
发布
2012-07-01
实施

This Technical Specification is applicable for determining the leaching behaviour of monolithic wastes under dynamic conditions. The test is performed under fixed experimental conditions in this document. This test is aimed at determining the release as a function of time of inorganic constituents from a monolithic waste, when it is put into contact with an aqueous solution (leachant). This dynamic monolithic leaching test (DMLT) is a parameter specific test as specified in EN 12920 and is therefore not aimed at simulating real situations. The application of this test method alone is not sufficient for the determination of the detailed leaching behaviour of a monolithic waste under specified conditions. In the framework of EN 12920 and in combination with additional chemical information, the test results are used to identify the leaching mechanisms and their relative importance. The intrinsic properties can be used to predict the release of constituents at a given time frame, in order to assess the leaching behaviour of monolithic waste materials, placed in different situations or scenarios (including disposal and recycling scenarios). The test method applies to regularly shaped test portions of monolithic wastes with minimum dimensions of 40 mm in all directions, that are assumed to maintain their integrity over a time frame relevant for the considered scenario. The test method applies to test portions for which the geometric surface area can be determined with the help of simple geometric equations. The test method applies to low permeable monolithic materials. NOTE 1 If, in order to comply with the requirements of regular shape, the test portion is prepared by cutting or coring, then new surfaces are exposed which can lead to change(s) in leaching properties. On the other hand if the test portion is prepared by moulding, the surface will be dependent to the type of mould and the conditions of storage. If the intention is to evaluate the behaviour of the material core, the specimen needs to be stored without any contact with air to avoid carbonation. NOTE 2 For monolithic waste materials with a saturated hydraulic conductivity higher than 108 m/s water is likely to percolate through the monolith rather than flow around. In such cases relating the release to the geometric surface can lead to misinterpretation. A percolation test is then more appropriate (e. g. CEN/TS 14405). This procedure may not be applicable to materials reacting with the leachant, leading for example to excessive gas emission or an excessive heat release. This document has been developed to determine the release of mainly inorganic constituents from wastes. It does not take into account the particular characteristics of organic constituents, nor the consequences of microbiological processes in organic degradable wastes.

Characterisation of waste - Leaching behaviour test for basic characterisation - Dynamic monolithic leaching test with periodic leachant renewal, under fixed test conditions

ICS
13.030.10
CCS
发布
2012-07-01
实施

Technical specifications for harmless treatment of organic waste in vegetable fields

ICS
13.030.10
CCS
Z71
发布
2012-06-14
实施
2012-10-01

Characterization of waste. Static test for determination of acid potential and neutralisation potential of sulfidic waste

ICS
13.030.10
CCS
Z27
发布
2012-04-30
实施
2012-04-30

Characterization of waste - Static test for determination of acid potential and neutralisation potential of sulfidic waste

ICS
13.030.10
CCS
发布
2012-01-16
实施
2012-01-16

Characterization of waste - Static test for determination of acid potential and neutralisation potential of sulfidic waste; German version EN 15875:2011

ICS
13.030.10
CCS
Z33
发布
2012-01
实施

La présente Norme européenne spécifie des méthodes permettant de déterminer le potentiel des matériaux sulfurés à former des eaux de drainage acides. Les méthodes spécifiées permettent de déterminer à la fois le potentiel de génération d'acide (AP) et le potentiel de neutralisation (NP) du matériau. A partir de ces résultats, le potentiel de neutralisation net (NNP) et le rapport de potentiel de neutralisation (NPR) sont calculés.La présente Norme européenne est applicable à tous les déchets sulfurés de l'industrie extractive, à l'exclusion des déchets qui auront un pH inférieur à 2 lors de l'étape initiale du mode opératoire décrit en 8.2.3.

Characterization of waste - Static test for determination of acid potential and neutralisation potential of sulfidic waste.

ICS
13.030.10
CCS
Z70
发布
2011-12-01
实施
2011-12-23

This Technical Report gives guidance on the strategy for on-site verification and quality control of waste at landfills. It describes methods of visual inspection, control of documents and choice of necessity of testing by either screening methods or reference methods. It gives guidance on sampling, sample preparation and extraction for analysis.The same procedures may be useful for on-site verification and quality control of waste at treatment plants.

Characterization of waste - On-site verification

ICS
13.030.10
CCS
发布
2011-08-05
实施
2011-08-05

Explosiveness Inspection Procedures for Imported Solid Waste Raw Materials

ICS
13.030.10
CCS
Z70
发布
2011-05-31
实施
2011-12-01

This European Standard specifies methods to determine the potential of sulfide bearing materials for the formation of acidic drainage. Specified are methods for determining both the acid potential (AP) and the neutralisation potential (NP) of the material. From these results the net neutralisation potential (NNP) and the neutralisation potential ratio (NPR) are calculated.This European Standard is applicable to all sulfide bearing wastes from the extractive industries excluding wastes which will have pH < 2 in the initial step of the procedure described in 8.2.3.

Characterization of waste - Static test for determination of acid potential and neutralisation potential of sulfidic waste

ICS
13.030.10
CCS
发布
2011
实施

本标准规定了生活垃圾焚烧炉大气污染物排放限值、污染控制技术要求及监测要求与方法。 本标准适用于现有生活垃圾焚烧设施的大气污染物排放控制,以及新建、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污染控制。

Emission standard of air pollutants for municipal solid wastes incineration

ICS
13.030.10
CCS
Z68
发布
2008-7-24
实施
2008-7-24

本标准规定了危险废物焚烧设施大气污染物排放标准限值及污染控制技术要求。 本标准适用于以焚烧方式处理危险废物的现有设施的大气污染控制,以及新建、改建、扩建项目的设计、环境影响评价、竣工验收以及建成后的污染控制。

Air Pollutant Emission Standards for Hazardous Waste Incineration

ICS
13.030.10
CCS
Z70
发布
2008/01/01
实施
2008/01/01

A knowledge of the inorganic constituent composition in a waste is often required for the selection of appropriate waste disposal practices. Solid waste may exist in a variety of forms and contain a range of organic and inorganic constituents. This practice describes a drying and ashing step that may be applied to remove moisture and volatile and nonvolatile organic constituents prior to determining nonvolatile metals. Generation of a dry ash concentrates the inorganic constituents of interest and makes the LiBO2 fusion feasible for a greater variety of waste samples. Acidification of the LiBO2 fusion mix results in a solution amenable to inductively coupled plasma (ICP) or atomic absorption spectrometry (AAS) analysis.1.1 This practice covers the drying, ashing, and solubilization of solid waste using a lithium metaborate (LiBO2) fusion for the subsequent determination of inorganic constituents by argon plasma emission spectroscopy or atomic absorption spectroscopy. 1.2 The following elements may be solubilized by this practice: aluminumchromiumsilicon bariumirontitanium cadmiummagnesiumvanadium calciummanganesezinc coppernickel 1.3 This practice has been used successfully with a bauxite ore and a neutralized metal treatment sludge. The practice may be applicable to other elements not listed above. Some metals, such as cadmium and zinc, may volatilize from some samples during the drying, ashing, or fusion steps. The analyst is responsible for determining whether the practice is applicable to the solid waste being tested. 1.4 This practice is intended for the solubilization of nonvolatile inorganic constituents in solid waste. The LiBO2 fusion is appropriate for a silicate matrix or acid resistant samples. 1.5 This standard does not purport to address all of the safety problems 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. For specific hazard statements see Section 7.

Standard Practice for Dissolution of Solid Waste by Lithium Metaborate Fusion

ICS
13.030.10
CCS
Z13
发布
2008
实施

5.1 This test method can be used to measure the release of a component from a cylindrical solidified waste form into water at the reference temperature of 20°C and at elevated temperatures that accelerate the rate and extent of leaching relative to the values measured at 20°C. 5.2 This test method can be used to: 5.2.1 Compare releases of waste components from various types of solidification agents and formulations. 5.2.2 Determine the diffusion coefficients for the release of waste components from waste forms at a specific temperature. 5.2.3 Promote greater extents of reaction than can be achieved under expected service conditions within a laboratory time frame to provide greater confidence in modeled diffusive releases. 5.2.4 Determine the temperature dependence of diffusive release. 5.3 Fitting the experimental results with a mechanistic model allows diffusive releases to be extrapolated to long times and to full-scale waste forms under the following constraints: 5.3.1 Results of this test method address an intrinsic property of a material and should not be presumed to represent releases in specific disposal environments. Tests can be conducted under conditions that represent a specific disposal environment (for example, by using a representative groundwater) to determine an effective diffusion coefficient for those conditions. 5.3.2 Projections of releases over long times requires that the waste form matrix remain stable, which may be demonstrated by the behavior of the specimen in ALTs at elevated temperatures. 5.3.3 Extrapolations in time and scale are limited to values that correspond to the maximum CFL value obtained in an accelerated test. 5.3.4 The mechanism must be the same at all temperatures used in the extrapolation. The same model that describes the results of tests conducted at elevated temperatures must also describe the results of tests run at the reference temperature of 20°C. 1.1 This test method provides procedures for measuring the leach rates of elements from a solidified matrix material, determining if the releases are controlled by mass diffusion, computing values of diffusion constants based on models, and verifying projected long-term diffusive releases. This test method is applicable to any material that does not degrade or deform during the test. 1.1.1 If mass diffusion is the dominant step in the leaching mechanism, then the results of this test can be used to calculate diffusion coefficients using mathematical diffusion models. A computer program developed for that purpose is available as a companion to th......

Standard Test Method for Accelerated Leach Test for Diffusive Releases from Solidified Waste and a Computer Program to Model Diffusive, Fractional Leaching from Cylindrical Waste Forms

ICS
13.030.10
CCS
Z13
发布
2008
实施

本标准规定了废塑料回收、贮存、运输、预处理、再生利用等过程的污染控制和环境保护监督管理的要求。 本标准适用于包括进口废塑料在内的各种废塑料的回收与再生利用,不适用于属于医疗废物和危险废物的废塑料。

Technical specifications for pollution control during collection and recycle of waste plastics (on trial)

ICS
13.030.10
CCS
Z70
发布
2007-09-30
实施
2007-12-01

本标准规定了固体废物浸出毒性的浸出程序及其质量保证措施。 本标准适用于固体废物及其再利用产物中有机物和无机物的浸出毒性鉴别,但不适用于氰化物的浸出毒性鉴别。含有非水溶性液体的样品,不适应于本标准。

Solid waste. Extraction procedure for leaching toxicity. Acetic acid buffer solution method

ICS
13.030.10
CCS
Z13
发布
2007-04-13
实施
2007-05-01

本标准规定了固体废物浸出毒性的浸出程序及其质量保证措施。 本标准适用于固体废物及其再利用产物、以及土壤样品有机物和无机物的浸出毒性鉴别。含有非水溶性液体的样品,不适用于本标准。

Solid waste. Extraction procedure for leaching toxicity. Sulphuric acid & nitric acid method

ICS
13.030.10
CCS
Z13
发布
2007-04-13
实施
2007-05-01

本标准适用于铬渣的解毒、综合利用、最终处置及这些过程中所涉及的铬渣的识别、堆放、挖掘、包装和运输、贮存等环节的环境保护和污染控制,铬渣解毒物和综合利用产品的安全性评价,以及环境保护监督管理。 本标准适用于有钙焙烧工艺生产铬盐产生的含铬废渣。对其他铬盐生产工艺产生的含铬废渣以及其他含六价铬固体废物的处理处置参照本标准执行。

Environmental protection technical specifications for pollution treatment of the Chromium residue (on trial)

ICS
13.030.10
CCS
Z27
发布
2007-04-13
实施
2007-05-01

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

ICS
13.030.10
CCS
Z10
发布
2006-12-29
实施
2006-12-29

Waste - Constitution of a sample of household waste contained in a waste collection vehicle.

ICS
13.030.10
CCS
Z68
发布
2006-03-01
实施
2006-03-20



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