13.020.40 污染、污染控制和保护 标准查询与下载

ISO 4484-3 纺织品和纺织产品《纺织品来源的微塑料》第3部分：用家用洗涤法测量从纺织品最终产品中释放的收集物质质量

Textiles and textile products — Microplastics from textile sources — Part 3: Measurement of collected material mass released from textile end products by domestic washing method

ISO/FDIS 5430 塑料《海洋环境用生物降解塑料材料及制品可溶性分解中间体生态毒性试验方案》试验方法及要求

Plastics — Ecotoxicity testing scheme for soluble decomposition intermediates from biodegradable plastic materials and products used in the marine environment — Test methods and requirements

ISO/CD TR 27926 二氧化碳强化采油（CO2-EOR） 从 EOR 到封存的过渡

Carbon dioxide enhanced oil recovery (CO2-EOR) - Transitioning from EOR to storage

ISO/DTR 27925 二氧化碳捕获、运输和地质封存 交叉问题 流量保证

Carbon dioxide capture, transportation and geological storage — Cross cutting issues — Flow assurance

ISO/CD 17273 水产养殖中的废物管理和减少

Waste management and reduction in aquaculture

ISO/CD 16636 塑料 塑料在水环境条件下的崩解现场试验

Plastics — Disintegration field test of plastics under water environmental conditions

ISO/CD 16623 塑料 用于塑料海洋生物降解测试的优化潮间带海水和沉积物制备

Plastics — Optimized intertidal seawater and sediment preparation for marine biodegradation testing of plastics

IWA 42:2022 净零准则

Net zero guidelines

ISO/DIS 14068 温室气体管理和气候变化管理及相关活动 碳中和

Greenhouse gas management and climate change management and related activities — Carbon neutrality

ISO/FDIS 22526-4 塑料《生物基塑料的碳和环境足迹》第4部分：环境（总）足迹（生命周期评估）

Plastics — Carbon and environmental footprint of biobased plastics — Part 4: Environmental (total) footprint (Life cycle assessment)

ISO/DIS 23795-2 智能交通系统（ITS）“使用游牧和移动设备提取出行数据以估算 CO2 排放量”第2部分：环保驾驶行为的信息提供

Intelligent transport systems (ITS) — Extracting trip data using nomadic and mobile devices for estimating CO2 emissions — Part 2: Information provision for eco-friendly driving behaviour

ISO/DIS 19694-7 固定源排放《高耗能产业温室气体排放量的测定》第7部分：半导体与显示产业

Stationary source emissions — Determination of greenhouse gas emissions in energy-intensive industries — Part 7: Semiconductor and display industries

ISO/CD 27913 二氧化碳捕集、运输和地质封存 管道运输系统

Carbon dioxide capture, transportation and geological storage — Pipeline transportation systems

T/CIECCPA 010-2022 固定污染源二氧化碳排放连续监测技术规范

本文件规定了固定污染源二氧化碳排放连续监测的系统组成与功能要求、技术性能要求、监测站房要求、安装要求、技术指标调试检测、技术验收、运行管理及数据审核和处理。 本文件适用于以化石能源为燃料或原料的锅炉和工业炉窑以及石油化工、冶金、建材等生产过程中产生的废气中二氧化碳排放的连续监测。生物质为燃料的固定污染源二氧化碳排放连续监测可参照本文件执行。

Specification for continuous emission monitoring of carbon dioxide in the flue gas emitted from stationary source

T/SHMHZQ 048-2022 环保工程监测平台软件集成技术规范

1 范围 2 规范性引用文件 3 术语和定义、缩略语 3.1 术语和定义 3.2 缩略语 4 总体架构 4.1 一般要求 4.2 平台架构 4.3 集成层次 5 网络集成 5.1 网络平台 5.2 网络设备 5.3 综合布线系统 6 数据集成 6.1 数据处理 6.2 集成方法 7 应用集成 7.1 表示集成 7.2 控制集成 7.3 业务流程集成 8 集成测试 8.1 测试原则 8.2 测试内容 8.3 要求与评价

Technical Standard for open transportation platform

T/SXAEPI 12-2022 工业排放源 碳（CO2、CO、CH4）连续监测系统技术要求

本文件规定了工业排放源 碳（CO2、CO、CH4）连续监测系统的组成结构、技术要求、性能指标、检测方法、质量保证和检测项目

Specifications for continuous carbon monitoring system of CO2, CO, and CH4 from industrial emissions

ASTM E2205/E2205M-22 生态资源保护的基于风险的纠正措施标准指南

1.1 This is a guide to risk-based corrective action for the protection of ecological resources and supplements the RBCA process (Guide E2081). The primary objective of the EcoRBCA process is to provide a flexible framework for a tiered approach to ERA and risk management decision making at chemical release sites. To this end, available guidance documents from various federal and state agencies were reviewed and their common attributes incorporated into this guide, where possible. The Eco-RBCA process complements existing technical and regulatory ecological risk guidance (see 4.2). In particular, it is intended to be compatible with the USEPA programmatic guidelines for ERA (1)2 , guidance for the Superfund program (2), and other USEPA (3) risk assessment and corrective-action programs. Eco-RBCA might also be used in conjunction with corrective action strategies that include human health issues (for example, Guide E2081). 1.2 Chemical release sites vary greatly in terms of complexity, physical and chemical characteristics, and the risk that they might pose to ecological resources. The Eco-RBCA process, as described in Guide E2081, recognizes this variability and incorporates a tiered approach that integrates site assessment, response actions, and remedial actions with ERA. The process begins with relatively simple analyses in Tier 1 and, if necessary, proceeds to more detailed evaluations in Tier 2 or Tier 3. The process of gathering and evaluating data is conducted in such a manner that only those data that are necessary for a given tier’s decision making are collected at each tier. Hence, this can facilitate effective use of resources and reduce initial data requirements. 1.3 Eco-RBCA is intended to provide a framework for sites not covered under regulatory programs and for sites under regulatory programs that lack specific guidance. Eco-RBCA may also provide a useful framework to help merge several possible approaches into a single approach when multiple regulatory programs apply. The user should be aware of the federal, state, and local corrective action programs and policies that are applicable for the site and, regardless of the program, that agency approvals might be required to implement the process for completing ERAs. 1.4 Various TPDs will need to be made regarding the aspects of Eco-RBCA. These TPDs may cover both the philosophical and methodological aspects, from what values to protect to exactly how the Eco-RBCA process will be performed. TPDs may affect every stage of the process, from the initial site assessment to development and monitoring of the remedy. It is the responsibility of the user to identify the appropriate TPDs. Section 7, Appendix X2, and Guide E2081 provide more detail regarding TPDs in the Eco-RBCA process. 1.5 The general performance standard for this document requires that: 1.5.1 Applicable TPDs be identified, beginning at the initiation of the Eco-RBCA process, and as appropriate, at later stages; 1.5.2 Data used in the Eco-RBCA process be of sufficient quantity and quality to answer the questions and support the decisions made at the tier of investigation; 1.5.3 Site assessments be distinguished into tiers of appropriate levels of evaluation; 1.5.4 Actions taken should integrate the Eco-RBCA process for the protection of relevant ecological receptors and habitats and RBCA for the protection of human health (see Guide E2081), as appropriate; 1.5.5 Applicable federal, state, and local laws and regulations be followed; and 1.5.6 Potential adverse effects on relevant ecological receptors and habitats be considered when selecting remedial action alternatives. The remedial action alternatives should be consistent with the TPDs and the RBCA process (see Guide E2081). 1.6 Ecological resources are the focus of this guide; risks to human health are addressed for petroleum releases and chemical releases in other ASTM RBCA standards (Guides E1739 and E2081). There are many features common to all three of the RBCA guides. These three guides share the basic elements of RBCA: (1) site assessment; (2) tiered evaluations of exposure, effects, and risk; (3) risk-based decision making; and (4) response, remedial action, and monitoring. There are a number of distinctions between human health and ecological risk assessments. For example, while human health risk assessments focus on individuals, evaluations of ecological risk typically focus on populations, communities, or ecosystems. Exceptions are species or critical habitats designated for special protection (for example, endangered or culturallyimportant species). Biological data to support an ERA are more amenable to direct field observation than are human exposure and epidemiological data. 1.7 The Eco-RBCA process addresses current and potential future risks to relevant ecological receptors and habitats at chemical release sites. It is not intended to apply to current permitted releases and permit applications. 1.8 Eco-RBCA focuses on chemical stressors. However, the user may need to consider biological or physical stressors at the site or effects from chemical sources unrelated to the site. 1.9 The process described in this guide integrates the principles of current ERA practices with site assessment activities and remedial-action selection to ensure that the risk management decision protects ecological resources. Fig. 1 illustrates the following activities in Eco-RBCA and those described in Section 7 (7.1 – 7.10): 1.9.1 Step 1—Initial Site Assessment; 1.9.2 Step 2—Decision Point; 1.9.3 Step 3—Tier 1 Ecological Risk Assessment; 1.9.4 Step 4—Tier 1 Decision Point; 1.9.5 Step 5—Tier 2 Ecological Risk Assessment; 1.9.6 Step 6—Tier 2 Decision Point; 1.9.7 Step 7—Tier 3 Ecological Risk Assessment; 1.9.8 Step 8—Tier 3 Decision Point; 1.9.9 Step 9—Implementing the Remedial Action Program; and 1.9.10 Step 10—Monitoring Programs (7.10). 2 The boldface numbers in parentheses refer to the list of references at the end of this standard. E2205/E2205M − 22 7 1.9.11 The above steps can be applied in a flexible manner. It may not be necessary to conduct a full tier of evaluation if existing site information indicates that a subsequent tier is more applicable to address site-specific concerns. Where experience indicates that a more sophisticated assessment is warranted at a site, the user may elect to proceed conceptually through any earlier tiers to conduct a site-specific assessment typical of Tier 2 or Tier 3. Additionally, the decision points in Steps 4, 6, and 8 allow the user to exit the tiered evaluation process and select the appropriate remedial action once adequate information is available for decision making. 1.10 This guide is organized as follows: 1.10.1 Section 2 lists referenced ASTM documents; 1.10.2 Section 3 defines terminology used in this guide; 1.10.3 Section 4 describes the significance and use of this guide; 1.10.4 Section 5 describes the tiered approach to the EcoRBCA process; 1.10.5 Sections 6 and 7 presents Eco-RBCA procedures in a step-by-step process; and 1.10.6 The reference section provides all documents cited in this guide. 1.11 This guide also includes the following appendices, which are provided as supplemental information and are not included as mandatory sections of this guide: 1.11.1 Appendix X1 presents information related to risk management issues; 1.11.2 Appendix X2 presents issues regarding TPDs; 1.11.3 Appendix X3 presents information on the activities occurring in each tier of the Eco-RBCA process; 1.11.4 Appendix X4 describes screening criteria and how they can be applied within the Eco-RBCA framework; 1.11.5 Appendix X5 presents the selection and use of relevant ecological screening benchmarks; 1.11.6 Appendix X6 includes two examples of the application of the Eco-RBCA framework; and 1.11.7 Appendix X7 presents information on uncertainty and its role in Eco-RBCA. 1.12 The values stated in either SI units or inch-pound units are to be regarded separately as standard. The values stated in each system may not be exact equivalents; therefore, each system shall be used independently of the other. Combining values from the two systems may result in non-conformance with the standard. 1.13 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 Risk-Based Corrective Action for Protection of Ecological Resources

T/CI 079-2022 焦炉烟气全干法净化技术规范

3.1  全干法脱硫 dry flue gas desulfurization 将粉末状或颗粒状脱硫剂、吸附剂或催化剂喷入烟气脱硫反应器中，使其与烟气中SO2等含硫气体充分接触去除烟气中的SO2，同时通过物理/化学吸附去除一些无机和有机微量物质。 3.2  选择性催化还原法selective catalytic reduction（SCR） 利用还原剂（NH3和尿素等）在催化剂作用下有选择性地与烟气中的NOx发生化学反应，生成氮气（N2）和水（H2O）的方法。 3.3  中低温SCR脱硝 selective catalytic reduction denitrification at medium-low temperature 在中低温（180~280）℃烟气条件下，利用氨、尿素等作为还原剂，在催化剂的作用下将NOx选择性地催化还原成N2和H2O，从而脱除烟气中NOx的工艺技术。 3.4  SCR反应器 SCR reactor 烟气脱硝系统中选择性催化还原脱除NOx的反应装置。 3.5  系统压损 system pressure loss 指烟气净化系统在设计工况条件下进出口烟气流的平均全压差。 3.6  装置可利用率 operation availability rate 指烟气净化装置每年正常运行时间占焦炉每年总运行时间的百分比，以%表示。 3.7  热备 hot standby 焦炉废气是通过热浮力产生负压将烟气排出去的，所以为了使烟囱具备一定的吸力，烟囱必须具备一定的温度，即热备。  4 总体要求 4.1 焦炉烟气脱硫脱硝系统的调试、启/停和运行应不影响焦炉的正常工作，必须保证外排烟囱的热备状态和事故工况下的快速响应，设计烟气旁路系统设快速开启阀门，与脱硫脱硝系统的风机设置安全联锁。 4.2 大部分在用焦炉在原始设计中很少考虑烟气的脱硫脱硝设备，无预留净化设备占地，导致场地十分狭窄，要求治理设施占地面积小，布置紧凑。 4.3 焦炉烟气脱硫脱硝装置应执行国家现行的相关政策、标准、规范和规程。设计脱硫脱硝效率应满足相应的排放标准和总量控制的要求。

Technical specifications for dry decontamination of coke oven flue gas

T/CSEE 0290-2022 燃煤电厂超低排放工程后评价技术导则

本文件规定了燃煤电厂超低排放工程后评价总体要求、评价对象及流程、评价指标及评价标准。 本文件适用于燃煤电厂超低排放工程后评价。

Technical Guidelines for Post-Evaluation of Ultra-Low Emission Projects in Coal-fired Power Plants

DB4116/T 029-2022 农村有机废弃物堆沤肥料化利用技术规程

周口市

Technical regulations for composting and retting fertilizer utilization of rural organic waste