13.030.99 有关废物的其他标准 标准查询与下载

T/BGLM 0001.04-2019 生活垃圾宜生化性评价 易生化有机质沼气产量估算（BGQ）

通过分别测定生活垃圾样品中易生物降解的糖类、脂肪类和蛋白质类的含量，并分别利用其与生物发酵沼气产量的理论对应关系，得到生活垃圾样品的易生化有机质沼气产量。

Evaluation of biochemical suitability of domestic waste Estimation of biogas production of easily biochemical organic matter (BGQ)

DB34/T 3437-2019 车用动力电池回收利用低速动力车梯次利用要求

Requirements for Recycling and Utilization of Power Batteries for Vehicles by Low-speed Power Vehicles

ASTM D6868-19 将塑料和聚合物作为涂料或添加剂与纸张和其他基材结合在一起的标签规范 设计用于在市政或工业设施中有氧化堆肥

Standard Specification for Labeling of End Items that Incorporate Plastics and Polymers as Coatings or Additives with Paper and Other Substrates Designed to be Aerobically Composted in Municipal or In

DB37/ 3693-2019 农村生活污水处理处置设施水污染物排放标准

Water Pollutant Discharge Standards for Rural Domestic Sewage Treatment and Disposal Facilities

DB13/T 5069-2019 车用密封条挥发性物质释放量测定方法

Method for determination of volatile substances released from automotive weather strips

ASTM E2278-13(2019) 煤矿回收利用煤炭燃烧产品（CCP）标准指南:酸性矿井排水和减排

1.1 This guide covers the beneficial use of coal combustion products (CCPs) for abatement of acid mine drainage and revegetation for surface mine reclamation applications related to area mining, contour mining, and mountaintop removal mining. It does not apply to underground mine reclamation applications. There are many important differences in physical and chemical characteristics that exist among the various types of CCPs available for use in mine reclamation. CCPs proposed for each project must be investigated thoroughly to design CCP placement activities to meet the project objectives. This guide provides procedures for consideration of engineering, economic, and environmental factors in the development of such applications. 1.2 The utilization of CCPs under this guide is a component of a pollution prevention program; Guide E1609 describes pollution prevention activities in more detail. Utilization of CCPs in this manner conserves land, natural resources, and energy. 1.3 This guide applies to CCPs produced primarily from the combustion of coal. 1.4 The testing, engineering, and construction practices for using CCPs in mine reclamation are similar to generally accepted practices for using other materials, including cement and soils, in mine reclamation. 1.5 Regulations governing the use of CCPs vary by state. The user of this guide has the responsibility to determine and comply with applicable regulations. 1.6 The values stated in inch-pound units are to be regarded as standard. The values given in parentheses are mathematical conversions to SI units that are provided for information only and are not considered standard. 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 Guide for Use of Coal Combustion Products (CCPs) for Surface Mine Reclamation: Revegetation and Mitigation of Acid Mine Drainage

T/ZS 0054-2019 农户垃圾分类标准

1　范围　 2　基本要求　 2.1　一般要求　 2.2　人员要求　 3　分类要求　 3.1　可堆肥(腐烂)垃圾　 3.2　其它垃圾(不可腐烂)　 4　分类投放 4.1　投放要求　 4.2　管理要求　

Rural Household Garbage Sorting Standards

DB32/T 3583-2019 生物中氚和碳-14的测定 液体闪烁计数法

本标准适用于动物、植物中自由水氚、有机结合氚和碳-14的测定。

Determination of tritium and carbon-14 in living organisms by liquid scintillation counting

DB32/T 3584-2019 水中铅-210的测定 冠醚树脂色层法

本标准适用于环境水和废水中铅-210的测定。

Determination of lead-210 in water Crown ether resin chromatography

DB31/T 1127-2019 生活垃圾分类标志标识管理规范

Standards for management of domestic waste classification signs and labels

DB45/T 1896-2018 城市生活垃圾分类设施配置及作业规范

Configuration and operation specifications of municipal solid waste sorting facilities

ASTM D6235-18 危险废物污染场所的包气带和地下水污染的快速现场特性的标准实施规程

1.1 Applicability of the ESC Process—This practice covers a process for expedited site characterization (ESC) of hazardous waste contaminated sites2 to identify vadose zone, groundwater and other relevant contaminant migration pathways and determine the distribution, concentration, and fate of contaminants for the purpose of providing an ESC client, regulatory authority, and stakeholders with the necessary information to choose a course of action.3 Generally, the process is applicable to larger-scale projects or contaminated sites where the ESC process can be reasonably expected to reduce the time and cost of site characterization compared to alternative approaches. The ESC process has been applied successfully at a variety of sites (see Table X1.1). It typically achieves significant cost and schedule savings compared to traditional site characterization (see X1.2 and X1.3),4 although it should be recognized that in-depth site characterization of hazardous waste contaminated sites may require a more elaborate process than ESC. 1.2 Features of the ESC Process—The ESC process operates within the framework of existing regulatory programs. It focuses on collecting only the information required to meet characterization objectives and on ensuring that characterization ceases as soon as the objectives are met. Central to the ESC process is the use of judgement-based sampling and measurement to characterize vadose zone and groundwater contamination in a limited number of field mobilizations by an integrated multidisciplinary team, led by a technical leader and operating within the framework of a dynamic work plan that gives him or her the flexibility of responsibility to select the type and location of measurements needed to optimize data collection activities. Table 1 identifies other essential features of the ESC process, and Fig. 1 presents a flow diagram for the entire ESC process. 1.3 Investigation Methods—The process described in this practice is based on good scientific practice but is not tied to any particular regulatory program, site investigation method or technique, chemical analysis method, statistical analysis method, risk analysis method, or computer modeling code. Appropriate investigation techniques in an ESC project are highly site specific and are selected and modified based upon the professional judgement of the core technical team (in particular the technical team leader). Whenever feasible, noninvasive and minimally invasive methods are used, as discussed in Appendix X2. Appropriate chemical analysis methods are equally site specific. Analyses may be conducted in the field or laboratory, depending on data quality requirements, required turnaround time, and costs. 1.4 Sites Generally Not Appropriate for the ESC Process— Generally, the ESC process is not applicable to: small petroleum release sites, real estate property transactions that require no more than a Phase I ESA, sites where contamination is limited to the near surface or there is no basis for suspecting that contaminant movement through the vadose zone and groundwater is a matter of concern, sites where the cost of remedial action is likely to be less than the cost of site characterization, or sites where existing statutes or regulations prohibit the use of essential features of the ESC process.5 1.5 Other Potentially Applicable ASTM Standards for Site Characterization—Guide E1912 addresses accelerated site 1 This practice is under the jurisdiction of ASTM Committee D18 on Soil and Rock and is the direct responsibility of Subcommittee D18.01 on Surface and Subsurface Characterization. Current edition approved Dec. 15, 2018. Published January 2019. Originally approved in 1998. Last previous edition approved in 2010 as D6235 – 04(2010). DOI: 10.1520/D6235-18. 2 The term hazardous waste in the title is used descriptively. The term also has specific meanings in the context of different regulatory programs. Expedited site characterization is also appropriate for radiologically contaminated sites and some larger petroleum release sites, such as refineries. Section 4.2 further identifies types of contaminated sites where ESC may be appropriate. See Appendix X1 for additional background on the ESC process. 3 The text of this practice emphasizes vadose zone and groundwater contamination because these contaminant migration pathways are the most difficult to characterize. An ESC project should also address all other relevant contaminant migration pathways, such as air, surface water, submerged sediments, and biota. 4 This practice uses the term “traditional” site characterization to refer to the approach that has typically been used for characterizing contaminated sites at CERLA and RCRA sites during the 1980s and early 1990s. 5 The ASTM knows of no federal or state statutes or regulations that would prohibit use of the ESC process. Some elements of the ESC process may not be entirely consistent with existing federal and state guidance documents, and regulatory authorities are encouraged make appropriate exceptions. 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 characterization (ASC) for petroleum release sites, and Guide E1739 addresses use of the risk-based corrective action (RBCA) process at petroleum release sites. Section X1.5.1 describes the ASC process, and X1.5.2 discusses the relationship between ESC and the RBCA process. Practices E1527 and E1528 and Guide E1903 address real estate property transactions, and X1.5.3 discusses the relationship between the ESC process and investigations for real estate property transactions. Classification D5746 addresses environmental conditions of property area types for Department of Defense installations, and Practice D6008 provides guidance on conducting environmental baseline surveys to determine certain elements of the environmental condition of federal real property. 1.6 The values stated in both inch-pound and SI units are to be regarded separately as the standard. The values given in parentheses are for information only. 1.7 All references in this standard to the “engineer” must be understood as referring to a qualified professional (such as an engineer, soil scientist or geologist) who has the appropriate experience and, if required by local regulations, certification. 1.8 This practice offers an organized collection of information or a series of options and does not recommend a specific course of action. This document cannot replace education or experience and should be used in conjunction with professional judgment. Not all aspects of this practice may be applicable in all circumstances. This ASTM standard is not intended to represent or replace the standard of care by which the adequacy of a given professional service must be judged, nor should this document be applied without consideration of a project’s many unique aspects. The word “Standard” in the title of this document means only that the document has been approved through the ASTM consensus process. 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. 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. TABLE 1 Minimum Criteria for a Project Using ASTM Expedited Site Characterization Process NOTE 1—Other site characterization approaches may include many of the below elements, but all must be present for an investigation using the ASTM ESC process. 1. A technical team leader oversees the ESC project and leads the ESC core technical team. See Fig. 2, step 1.a in Fig. 3, 6.2 and 7.1.1.

Standard Practice for Expedited Site Characterization of Vadose Zone and Groundwater Contamination at Hazardous Waste Contaminated Sites

DB32/T 3492-2018 稀土冶炼废渣放射性豁免要求

Rare earth smelting waste radioactivity exemption requirements

CLC/TR 50625-6:2018 WEEE 的收集、物流和处理要求 第6部分：指令 2012/19/EU 和 EN 50625 系列标准与 EN 50614 之间的一致性报告

This Technical Report provides information on the alignment between Directive 2012/19/EU and EN 50625 series standards and EN 50614.

Collection, logistics & treatment requirements for WEEE - Part 6: Report on the alignment between Directive 2012/19/EU and EN 50625 series standards and EN 50614

T/CRRA 0212-2018 报废汽车回用件分类分级标准 发电机

发电机回用件分类分级工作的对象是从回收的报废汽车发动机上拆解得到的完整发电机总成。 按照T/CRRA 0202、T/CRRA 0203要求，发电机回用件通过分类分级可得到发电机一级回用件、发电机二级回用件、发电机三级回用件。 发电机回用件分类分级工作包括回收、拆解清洁、拆解清洁后的检测和评估，以及标识和贴标签等阶段。 回收阶段：确保报废汽车的发电机在发动机上，外观无明显损伤，真实记录发电机回用件铭牌上相关信息。  拆解清洁阶段：应按照T/CRRA 0203中5.2和5.3的要求执行，并可参照GB/T 28672中4.3。拆解清洁过程中应保持发电机部件的完整性，并不能对其内部结构及器件造成损伤。 检测和评估阶段：按照T/CRRA 0203中5.4、5.5及本标准5.1、5.2执行。  标识和贴标签阶段：发电机回用件的标识和标签制作及使用应按照T/CRRA 0204及本标准8执行。

Classification and grading standards for recycled parts of scrapped automobiles

T/CRRA 0211-2018 报废汽车回用件分类分级标准车门系统

车门系统  door system 前左车门系统、前右车门系统、后左车门系统、后右车门系统，具体包括门体、车门附件、车门内饰、车门电子元器件等。 门体  door body  车门内外板、加强横梁、加强板和窗框等零件的焊装总成。  车门附件 door accessories  车门铰链、车门开度限位器、门锁机构及内外手柄、车门玻璃、玻璃升降系统、密封条等。  车门电子元器件  door electronic components 安装在车门内部的音响、车门控制机构等。  车门内饰  door interior 用以装饰车身内部并起隔声、吸声、防止车外飞尘进入和水浸入的芯材、衬垫、蒙皮、 内饰固定板及其附件等。 总则 General Principles 回用件分类分级工作的对象是从回收的报废车辆上拆解得到的带有附件等的完整车门系统。其中，带音响设备的为A类车门系统，不带音响设备的为B类车门系统。 按照T/CRRA 0202、T/CRRA 0203要求，车门系统回用件通过分类分级得到一级回用件、二级回用件、三级回用件。一级回用件指正常直接使用的回用件，二级回用件是指可做短期直接使用的回用件，三级回用件是指用作再循环的回用件。 车门系统回用件分类分级工作包括回收、拆解前检测、拆解清洁、拆解清洁后评估，以及标识和贴标签等阶段。 回收阶段：准确记录报废汽车的型号和车门的类型。 拆解前检测阶段：检查车门密封性、开启灵活性；在条件允许情况下，启动电源、开启玻璃升降器。A类车门系统还需检查音响系统。 拆解清洁阶段：用专用工具解除车门铰链约束，不能改变车门涂层和内饰件的表面状态，按照T/CRRA 0203中5.2和5.3的要求执行。 拆解清洁后评估阶段：通过人工目视、敲击等方法判断车门质量状况，按照T/CRRA 0203中5.4、5.5及本标准5.1、5.2执行。  标识和贴标签阶段：标识和标签制作使用应按照T/CRRA 0204及本标准8执行。  记录保存：按照T/CRRA 0202中6.8、6.9执行。 存储及运输：存储运输不能破坏车门涂层、内饰件表面状态及相关附件，可参照GB/T 9174执行。

Classification and grading standards for recycled parts of scrapped automobiles Door system

T/CRRA 0901-2018 再生润滑油基础油

废矿物油（Used Oil） 矿物润滑油在润滑机械过程中，因受杂质污染，氧化和热的作用，润滑和保护性能降低，被更换下来的可再生利用的油。 再生润滑油基础油（Regenerated Base Oil） 是指将废矿物油的变质物及杂质通过科学合理的工艺技术分离除去后所得的润滑油基础油。 分子蒸馏（ Molecular Distillation） 是一种利用化学物质分子运动平均自由程差异，在不同状态下使润滑油分子在远低于其沸点和裂解温度的条件下，将混在废矿物油中的轻重组份分离的过程。废矿物油通过分子蒸馏获得再生润滑油基础油中间馏分。 薄膜蒸发（Thin Film Evaporation） 是指采用蒸发设备，利用温度与压力的关系，对废矿物油进行气液相分离、提纯和浓缩，获得一定粘度的再生润滑油基础油的技术。废矿物油通过薄膜蒸发获得再生润滑油基础油中间馏分。 减压蒸馏（Vacuum Distillation） 是指通过提高系统内真空度而降低蒸馏物沸点，物料根据减压下的沸点差异进行气化分离，从而获得不同馏分产品的过程。废矿物油通过减压蒸馏获得再生润滑油基础油中间馏分。 白土精制（Clay Refining） 是指用白土作为吸附材料，改善油品的色度和安定性的一种精制工艺过程。废矿物油通过白土精制获得再生润滑油基础油Ⅰ类基础油。 溶剂精制（Solvent Refining） 是指利用溶剂对油品中组分溶解度的不同，选择性分离非理想组分，从而对油品进行精制的工艺过程。废矿物油通过溶剂精制获得再生润滑油基础油Ⅰ类基础油。 加氢精制（ Hydrofining） 是指油品通过装填催化剂的加氢反应器，使油品在一定操作条件下发生加氢反应，将油品中不饱和烃氢化饱和，稠环芳烃开环，硫、氮等杂原子脱除的工艺过程。废矿物油通过加氢精制获得再生润滑油基础油Ⅱ类基础油。

Regenerative Lubricant Base Oil

T/CRRA 0214-2018 报废汽车回用件分类分级标准 行李箱盖

行李箱盖回用件分类分级工作的对象是从回收的报废车辆上拆解得到的带有附件的完整行李箱盖。其中，带电子元器件的为A类行李箱盖，不带电子元器件的为B类行李箱盖。 按照T/CRRA 0202、T/CRRA 0203要求，行李箱盖回用件通过分类分级得到行李箱盖一级回用件、行李箱盖二级回用件、行李箱盖三级回用件。一级回用件指正常直接使用的回用件，二级回用件是指可做短期直接使用的回用件，三级回用件是指用作再循环的回用件。 行李箱盖回用件分类分级工作包括回收、拆解前检测、拆解清洁、拆解清洁后评估，以及标识和贴标签等阶段。  回收阶段：准确记录报废汽车报废类型和行李箱盖类型。 拆解前检测阶段：检查行李箱盖密封性、开启灵活性。 拆解清洁阶段：用专用工具解除行李箱盖铰链约束，不能改变盖体涂层的表面状态，具体按照T/CRRA 0203中5.2和5.3的要求执行。 拆解清洁后评估阶段：通过人工目视、敲击等方法判断行李箱盖质量状况，具体按照T/CRRA 0203中5.4、5.5及本标准执行。  标识和贴标签阶段：行李箱盖回用件的标识和标签制作及使用应按照T/CRRA 0204及本标准8执行。

Standard for Classification and Grading of Recycled Parts of Scrapped Automobiles

T/CRRA 0215-2018 报废汽车回用件分类分级标准 起动机

起动机回用件分类分级工作的对象是从回收的报废汽车发动机上拆解得到的完整起动机总成。 按照T/CRRA 0202、T/CRRA 0203要求，起动机回用件通过分类分级得到起动机一级回用件、起动机二级回用件、起动机三级回用件。 起动机回用件分类分级工作包括回收、拆解清洁、拆解清洁后检测和评估，以及标识和贴标签等阶段。 回收阶段：应确保报废汽车的起动机安装在发动机上，外观无明显损伤，真实记录起动机铭牌上的相关信息。 拆解清洁阶段：起动机与报废汽车发动机分离的过程应按照T/CRRA 0203中5.2和5.3的要求执行，并可参照GB/T 28673中4.2 拆解清洁过程中应保持起动机部件的完整性，并不能对其内部结构及器件造成损伤。 检测和评估阶段：按照T/CRRA 0203中5.4、5.5及本标准5.1、5.2、5.3执行。  标识和贴标签阶段：起动机的标识和标签制作及使用应按照T/CRRA 0204及本标准的8执行。

Classification and grading standards for recycled parts of scrapped automobiles Starter

T/CRRA 0213-2018 报废汽车回用件分类分级标准 发动机罩

发动机罩回用件分类分级工作的对象是从回收的报废车辆上拆解得到的带有附件的完整发动机罩。 按照T/CRRA 0202、T/CRRA 0203要求，发动机罩回用件通过分类分级得到发动机罩一级回用件、发动机罩二级回用件、发动机罩三级回用件。一级回用件指正常直接使用的回用件，二级回用件是指可做短期直接使用的回用件，三级回用件是指用作再循环的回用件。 发动机罩回用件分类分级工作包括回收、拆解前检测、拆解清洁、拆解清洁后评估，以及标识和贴标签等阶段。 回收阶段：准确记录报废汽车的报废类型和发动机罩的类型。 拆解前检测阶段：检查发动机罩密封性、开启灵活性。 拆解清洁阶段：用专用工具解除发动机罩铰链约束，不能改变盖体涂层的表面状态，具体按照T/CRRA 0203中5.2和5.3的要求执行。 拆解清洁后评估阶段：通过人工目视、敲击等方法判断发动机罩质量状况，具体按照T/CRRA 0203中5.4、5.5及本标准5.1、5.2执行。 标识和贴标签阶段：发动机罩回用件的标识和标签制作及使用应按照T/CRRA 0204及本标准8执行。 记录保存：按照T/CRRA 0202中6.8、6.9执行。 存储及运输：存储及运输不能破坏盖体涂层、内饰件表面状态及相关附件，具体参照GB/T 9174执行。

Classification and grading standard for recycled parts of scrapped automobiles Engine hood