13.020.30 环境影响评定 标准查询与下载

KS C IEC TS 62933-3-1:2020 电能存储（EES）系统第3-1部分:电能存储系统的规划和性能评估通用规范

Electrical energy storage(EES) systems —Part 3-1: Planning and performance assessment of electrical energy storage systems — General specification

T/CSES 08-2020 河岸带生态环境质量评估方法指南

针对我国“山水林田湖草”一体化治理以及河湖岸线保护与利用的需求，开展以河流水生态健康为目标，围绕河岸带土地利用建立评估指标体系的生态环境质量分级评估研究，为科学规范地评估河岸带生境状况以及河岸带对水体的非点源污染，指导河流岸线保护与规划、土地利用空间管控等工作提供依据。 具体技术内容包括：（1）范围；（2）规范性引用文件；（3）术语和定义；（4）评估目的、原则与流程；（5）评估指标体系构建；（6）现场调查与参数获取；（7）样地河岸带生态环境质量综合评估；（8）目标区域河岸带生态环境质量评估。

Methodological guidelines for riparian ecological and environmental quality assessment

BS EN IEC 62933-5-2:2020 电能存储 (EES) 系统 电网集成 EES 系统的安全要求 基于电化学的系统

What is BS EN IEC 62933 ‑ 5 ‑ 2 about?    BS EN IEC 62933 ‑ 5 ‑ 2 discusses electrical energy storage (EES). BS EN IEC 62933 ‑ 5 ‑ 2 details best practices for safety in grid-integrated EES systems of electrochemical-based systems. BS EN IEC 62933 ‑ 5 ‑ 2 describes safety aspects for people and their surroundings for grid-connected energy storage systems (ESS) where an electrochemical storage subsystem is used.    This safety standard applies to the entire life cycle of battery energy storage systems (BESS) - from design to end of service life management. All the electrical energy storage systems (EESS) follow the general safety requirements as described in IEC TS 62933-5-1 , which is ...

Electrical energy storage (EES) systems - Safety requirements for grid-integrated EES systems. Electrochemical-based systems

T/CPASE PT009-2020 锅炉产品大气污染物测试导则

本文件规定了锅炉产品大气污染物初始排放测试的方法、程序、报告内容及要求等。 本文件适用于额定压力小于3.8MPa 的蒸汽锅炉、热水锅炉及有机热载体锅炉产品的定型、改造后的验收及运行工况大气污染物初始排放测试。不适用于余热锅炉、垃圾焚烧炉。 在用锅炉运行工况大气污染物初始排放及烟气净化系统大气污染物排放的测定与评价可参照本文件进行。

Testing guide for air pollutants of boiler

EN IEC 62933-5-2:2020 电能存储（EES）系统 第 5-2 部分：电网集成 EES 系统的安全要求 基于电化学的系统

IEC 62933-5-2:2020 primarily describes safety aspects for people and, where appropriate, safety matters related to the surroundings and living beings for grid-connected energy storage systems where an electrochemical storage subsystem is used.

Electrical energy storage (EES) systems - Part 5-2: Safety requirements for grid-integrated EES systems - Electrochemical-based systems

IEC 62933-5-2:2020 电能存储（EES）系统第5-2部分:电网集成EES系统的安全要求电化学系统

Electrical energy storage (EES) systems - Part 5-2: Safety requirements for grid-integrated EES systems - Electrochemical-based systems

ASTM E3242-20 典型沉积物背景浓度测定的标准指南

1.1 This guide focuses on the approach for determination of representative sediment background concentrations used for remedial actions performed under various regulatory programs, including the Comprehensive Environmental Response, Compensation, and Liability Act (CERCLA). Although many of the references cited in this guide are CERCLA oriented, the guide is applicable to remedial actions performed under local, state, federal, and international cleanup programs. However, the guide does not describe requirements for each jurisdiction. The requirements for the regulatory entity under which the cleanup is performed should be reviewed to confirm compliance. 1.2 This guide provides a framework, including specific statistical and geochemical considerations, as well as case studies, demonstrating the approach to determine representative sediment background concentrations. This guide is intended to inform, complement, and support, but not supersede, local, state, federal, or international regulations. 1.2.1 This guide does not address methods and means of data collection (Guide E3163, Guide E3164.) 1.2.2 This guide is designed to apply to contaminated sediment sites where sediment data have been collected and are readily available. Additionally, this guide assumes that risk assessments have been performed, so that the contaminants/ chemicals of interest that exceed risk-based thresholds have been identified. 1.2.3 Furthermore, this guide presumes that risk-based thresholds identified are low enough to pose corrective action implementation challenges, and/or the site is subject to recontamination from ongoing anthropogenic and/or natural sources that are not controlled. In both cases, representative sediment background concentrations will be useful for determining the extent of corrective remedial actions (when used as remedial goals), evaluating risks posed by representative background concentrations, and establishing appropriate post-remedial monitoring plans. 1.3 Units—The values stated in SI units are to be regarded as standard. No other units of measurement are included in this standard. 1.4 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. 1.5 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 Determination of Representative Sediment Background Concentrations

T/DXFFA 1-2019 绿色锻造企业评价准则

本标准规定了绿色锻造企业评价的准则，包括总则、评价要求、评价程序。适用于与实现绿色锻造相关各方的下列需求： a）锻造企业依据本准则要求，通过对各相关要素实施有效控制，包括持续改进，以及保证符合适用的法律法规要求，旨在实现用地集约化、原料无害化、生产清洁化、废物资源化、能源低碳化目标； b）第三方评价机构应锻造企业或其顾客、政府监管部门等相关方委托，以符合本标准的评价结果和证书，证实其符合绿色锻造企业要求，实现并保持本准则规定的绩效； c）锻造企业基于自查自评结果发表自我声明，或用于内部管理或考核。 本标准适用于采用热锻造方式自行生产钢制锻造法兰、锻制管件及其它环形锻件、小型自由锻件。其它情形可参考采用。

Enterprise evaluation criteriaforGreen forging

T/CCMI 2.1-2019 绿色锻造企业评价准则 第1部分：法兰锻造企业评价

T/CCMI 2的本部分规定了法兰锻造类绿色锻造企业评价的准则，包括总则、评价要求、评价程序。适用于采用热锻造方式生产法兰、环形锻件、小型自由锻件的法兰锻造企业及与实现绿色锻造相关各方的下列需求，其它情形可参考采用： a)　法兰锻造企业依据本准则要求，通过对相关要素实施有效控制，包括持续改进，以及保证符合适用的法律法规要求，旨在实现用地集约化、原料无害化、生产清洁化、废物资源化、能源低碳化目标； b)　第三方评价机构应法兰锻造企业或其顾客、政府监管部门等相关方委托，以符合本部分的评价结果和证书，证实其符合绿色锻造企业要求，实现并保持本准则规定的绩效； c)　法兰锻造企业基于自查自评结果发表自我声明，以及用于内部管理或考核。

Enterprise evaluation criteria for green forging Part 1: Evaluation of flange forging enterprises

T/CAB 0055-2019 绿色设计产品评价技术规范 乘用车动力转向泵

本标准适用于液压动力转向泵的绿色设计以及评价工作，电动助力泵等其他类型转向泵产品可参照执行。

Technical specification for green-design product assessment - power steering pump for automobile

ASTM E1903-19 环境现场评估标准实践:二期环境现场评估过程

1.1 This practice2 covers a process for conducting a Phase II environmental site assessment (ESA) of a parcel of property with respect to the presence or the likely presence of substances including but not limited to those within the scope of the Comprehensive Environmental Response, Compensation and Liability Act (CERCLA) (e.g., hazardous substances), pollutants, contaminants, petroleum and petroleum products, and controlled substances and constituents thereof. It specifies procedures based on the scientific method to characterize property conditions in an objective, representative, reproducible, and defensible manner. To promote clarity in defining Phase II ESA objectives and transparency in communicating and interpreting Phase II ESA results, this practice specifies adherence to requirements for documenting the scope of assessment and constraints on the conduct of the assessment process. 1.1.1 A user’s interest in the presence or likely presence of substances in environmental media at a property may arise in a wide variety of legal, regulatory, and commercial contexts, and may involve diverse objectives including those listed in 1.2. This practice contemplates that the user and the Phase II Assessor will consult to define the scope and objectives of investigation in light of relevant factors, including without limitation the substances released or possibly released at the property, the nature of the concerns presented by their presence or likely presence, the behavior, fate and transport characteristics of substances released or possibly released, the portion of the property to be investigated, the information already available, the degree of confidence needed or desired in the results, the degree of investigatory sampling and chemical testing needed to achieve such confidence, and any applicable time and resource constraints. This practice requires that Phase II activities be conducted so that the resulting scope of work is performed, and the stated objectives are achieved, in a scientifically sound manner. 1.1.2 A Phase II ESA in accordance with this practice may be conducted after site assessment activities in accordance with Practice E1527 for Phase I Environmental Site Assessments: Phase I Environmental Site Assessment Process, Practice E2247 for Environmental Site Assessments: Phase I Environmental Site Assessment for Forestland or Rural Property, EPA’s All Appropriate Inquiries (AAI) Rule, 40 C.F.R. Part 312, or Practice E1528 for Limited Environmental Due Diligence: Transaction Screen Process. In defining the scope and purposes of a Phase II ESA, however, previous decisions to classify property conditions or areas as RECs, or to refrain from doing so, are not determinative as to whether investigation of the same conditions or areas is appropriate to meet the objectives of the Phase II ESA. 1.2 Objectives—This practice is intended for use where a user desires to obtain sound, scientifically valid data concerning actual property conditions, whether or not such data relate to property conditions previously identified as RECs or data gaps in Phase I ESAs. Without attempting to define all such situations, this practice contemplates that users may seek such data to inform their evaluations, conclusions, and choices of action in connection with objectives that may include, without limitation, one or more of the following: 1.2.1 Objective 1—Assess whether there has been a release of hazardous substances within the meaning of CERCLA, for purposes including landowner liability protections (i.e., innocent landowner, bona fide prospective purchaser, and contiguous property owner). 1.2.2 Objective 2—Provide information relevant to identifying, defining or implementing landowner “continuing obligations,” or the criteria established under CERCLA (e.g., exercising appropriate care by taking reasonable steps to 1 This practice is under the jurisdiction of ASTM Committee E50 on Environmental Assessment, Risk Management and Corrective Action and is the direct responsibility of Subcommittee E50.02 on Real Estate Assessment and Management. Current edition approved Nov. 15, 2019. Published January 2020. Originally approved in 1997. Last previous edition approved in 2011 as E1903 – 11. DOI: 10.1520/E1903-19. 2 As used herein, a “standard” is a document that has been developed and established within the consensus principles of the Society and that meets the approval requirements of ASTM procedures and regulations. A “practice” is a definitive set of instructions for performing one or more specific operations that does not produce a test result. A “guide,” in contrast, is a compendium of information or a series of options that does not recommend a specific course of action. A guide increases the awareness of information and approaches in a given subject area. See Form and Style for ASTM Standards, http://www.astm.org/COMMIT/Blue_ Book.pdf. 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. prevent or limit exposures to previously released hazardous substances) for maintaining the CERCLA landowner liability protections. 1.2.3 Objective 3—Develop threshold knowledge of the presence of substances on properties within the scope of the CERCLA definition of a “brownfield site” and as required for qualifying for brownfields remediation grants from the EPA Brownfields Program. 1.2.4 Objective 4—Provide information relevant to identifying, defining and evaluating property conditions associated with target analytes that may pose risk to human health or the environment, or risk of bodily injury to persons on the property and thereby give rise to potential liability in tort. 1.2.5 Objective 5—Provide information relevant to evaluating and allocating business environmental risk in transactional and contractual contexts, including transferring, financing and insuring properties, and due diligence relating thereto. 1.2.6 Objective 6—Provide information to support disclosure of liabilities and contingent liabilities in financial statements and securities reporting. 1.2.7 Additional information concerning these six objectives may be found in the Legal Appendix, Appendix X1. 1.3 Scope of Assessment in Relation to Objectives—The scope of a Phase II ESA is related to the objectives of the investigation. Both scope and objectives may require ongoing evaluation and refinement as the assessment progresses. 1.3.1 In developing the scope of work and in evaluating data and information concerning the property, the Phase II Assessor must determine whether the available information is sufficient to meet the objectives of the investigation. Even after conducting Phase II activities to generate additional data, the Phase II Assessor must independently evaluate the sufficiency of the data in relation to the objectives. As the investigation progresses, the objectives may be refined or redefined in consultation between the user and the Phase II Assessor. 1.3.2 A single round of sampling and chemical testing may not always provide data sufficient to meet the chosen objectives. If not, this practice contemplates additional sampling in an iterative sequence that concludes when the available data are sufficient. This practice also acknowledges, however, that the user may instead elect either to redefine the objectives so that they can be met with the data available, or to terminate the investigative process without meeting the stated objectives. The Phase II Assessment report must disclose any respect in which available data are insufficient to meet objectives. 1.3.3 This practice does not require full site characterization in every instance, but may be used to carry out an investigation sufficient for that purpose if desired to meet the user’s objectives. 1.4 Needs of the User—The user and Phase II Assessor must have a mutual understanding of the context in which the Phase II ESA is to be performed and the objectives to be met by the investigation, i.e. the specific questions to be answered or problems to be resolved by the Phase II ESA. The scope of Phase II activities must be defined in relation to those objectives. 1.4.1 The degree of confidence desired by the user influences the scope of the investigation and the evaluation of data. More extensive testing and more iterations of sampling and analysis may be needed if the objectives require detailed conclusions with high confidence. Less testing and fewer iterations of sampling and analysis may be needed if the objectives of the assessment require only general conclusions. 1.5 Limitations—This practice is not intended to supersede applicable requirements imposed by regulatory authorities. This practice does not attempt to define a legal standard of care either for the performance of professional services with respect to matters within its scope, or for the performance of any individual Phase II ESA. 1.6 Organization of This Practice—This practice has nine sections and four appendices. Section 1 covers the Scope of the practice. Section 2, Referenced Documents, lists ASTM and other organizations’ related standards and guidance that may be useful in conducting Phase II ESAs in accordance with this practice. Section 3, Terminology, contains definitions of terms and acronyms used in this practice. Section 4 addresses the Significance and Use of this practice, including the legal context into which Phase II ESAs may fall. Section 5 discusses development and documentation of the scope of the Phase II ESA, including the Statement of Objectives for the assessment. Section 6 provides a Phase II ESA Overview, with purpose and goal descriptions. Section 7 comprises the main body of Performing the Phase II ESA, and includes initiating scientific inquiry by formulating the question to be answered (7.1), collecting and evaluating information (7.2), identifying areas for investigation (7.3), developing the conceptual model (7.4), developing a plan and rationale for sampling (7.5), conducting the sampling (7.6), and validating the conceptual model (7.7). Interpretation of results is covered in Section 8. Phase II Environmental Site Assessment report preparation is addressed in Section 9. Appendix X1 supports Section 4, and contains legal considerations pertaining to Phase II Environmental Site Assessment. Appendix X2 contains contracting considerations between Phase II assessor and user. Appendix X3 supports Section 9, and describes two examples and a sample table of contents illustrating possible approaches to reporting the results of a Phase II Environmental Site Assessment. Appendix X4 supplements Section 2 with a list of standards and references that may be relevant in conducting a Phase II Environmental Site Assessment. 1.7 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 Practice for Environmental Site Assessments: Phase II Environmental Site Assessment Process

DB34/T 3431-2019 诚信计量示范旅游景区评价要求

Evaluation Requirements for Integrity Measurement Demonstration Tourist Attractions

DB11/T 656-2019 建设用地土壤污染状况调查与风险评估技术导则

Technical Guidelines for Investigation and Risk Assessment of Soil Pollution in Construction Land

DB50/T 931-2019 重庆市农业面源污染风险评估技术规范

本标准适用于重庆市农业生产过程中产生的面源污染风险评估。

Technical specifications for risk assessment of agricultural non-point source pollution in Chongqing

KS C IEC 62933-5-2-2019 电能存储（EES）系统第5－2部分:电网集成EES系统的安全要求电化学系统

Electrical Energy Storage (EES) Systems — Part 5－2: Safety Requirements for grid integrated EES systems — electrochemical based systems

KS C IEC 62933-5-2:2019 电能存储（EES）系统第5－2部分:电网集成EES系统的安全要求电化学系统

Electrical Energy Storage (EES) Systems — Part 5－2: Safety Requirements for grid integrated EES systems — electrochemical based systems

BS EN IEC 62933-2-1:2018 电能存储（EES）系统 单元参数和测试方法 通用规格

What is this standard about? This part of IEC 62933 focuses on unit parameters and testing methods of EES systems. The energy storage devices and technologies are outside the scope of this document. This document deals with EES system performance defining: – unit parameters, – testing methods.

Electrical energy storage (EES) systems - Unit parameters and testing methods. General specification

ASTM F2205-19 化学分散剂在溢油应用中的生态注意事项标准指南:热带环境

Standard Guide for Ecological Considerations for the Use of Chemical Dispersants in Oil Spill Response: Tropical Environments

KS C IEC 62933-2-1-2019 电能存储（EES）系统 第2-1部分:单元参数和测试方法 总规范

Electrical energy storage(EES) systems — Part 2-1: Unit parameters and testing methods — General specification

KS C IEC TS 62933-4-1-2019 电能储存（EES）系统第4-1部分:环境问题指南通用规范

Electrical energy storage(EES) systems — Part 4-1: Guidance on environmental issues — General specification