13.060.10 天然水资源 标准查询与下载

DIN EN ISO 8689-2:2000 水质.江河的生物分类.第2部分:对底栖微型无脊椎动物调查的生物质量数据的表示方法指南

The document describes a guide-line for the presentation of the results of biological analysis using benthic macroinvertebrates for the assessment of the quality of running waters. There are given determinations for the graph of running waters in a water map and for the coloured identification of water sections relating to their quality.

Water quality - Biological classification of rivers - Part 2: Guidance on the presentation of biological quality data from surveys of benthic macroinvertebrates (ISO 8689-2:2000); German version EN ISO 8689-2:2000

DIN EN ISO 8689-1:2000 水质.江河的生物分类.第1部分:对底栖微型无脊椎动物调查的生物质量数据的解释指南

Water quality - Biological classification of rivers - Part 1: Guidance on the interpretation of biological quality data from surveys of benthic macroinvertebrates (ISO 8689-1:2000); German version EN ISO 8689-1:2000

EN ISO 8689-1:2000 水质.江河中生物的分类.第1部分:对底栖微型无脊椎动物调查的生物质量数据的解释方法指南 ISO 8689-1-2000

Water Quality - Biological Classification of Rivers - Part 1: Guidance on the Interpretation of Biological Quality Data from Surveys of Benthic Macroinvertebrates ISO 8689-1: 2000

EN ISO 8689-2:2000 水质.江河的生物分类.对海底微型无脊椎动物调查的生物质量数据的表示指南 ISO 8689-2-2000

Water Quality - Biological Classification of Rivers - Part 2: Guidance on the Presentation of Biological Quality Data from Surveys of Benthic Macroinvertebrates ISO 8689-2: 2000

ISO 8689-1:2000 水质 江河中生物的分类 第1部分:对底栖微型无脊椎动物调查的生物质量数据的解释方法指南

This part of ISO 8689 gives guidance on the interpretation of biological quality data relating to running waters from surveys of benthic macroinvertebrates. It is recognized that for a complete assessment of ecological status, other elements of biological quality should be assessed. NOTE Annex A gives guidance on how the comparison of the various classification systems can be made where classifications of the biological quality of running waters using benthic macroinvertebrates already exist.

Water quality - Biological classification of rivers - Part 1: Guidance on the interpretation of biological quality data from surveys of benthic macroinvertebrates

ISO 8689-2:2000 水质 江河中生物的分类 第2部分:对底栖微型无脊椎动物调查的生物质量数据的表示方法指南

This part of ISO 8689 gives guidance on the presentation of biological quality data relating to running waters from surveys of benthic macroinvertebrates. The guidance is applicable to the results of surveys using standard methods of sampling and using the classification procedures given in ISO 8689-1. It is recognized that for a complete assessment of ecological status other elements of biological quality should be assessed. NOTE An explanation of the comparison of different indices used in the analysis of surveys of benthic macroinvertebrates is given in ISO 8689-1.

Water quality - Biological classification of rivers - Part 2: Guidance on the presentation of biological quality data from surveys of benthic macroinvertebrates

ASTM D5754-95(2000) 主要离子和微量元素的地下水化学分析结果显示的标准指南.两个或更多分析的三线图

1.1 This guide describes the category of water analysis diagrams that use two-dimensional trilinear graphs as a technique for displaying the common chemical components from two or more complete analyses of natural ground water (see Section 3) on a single diagram. This category includes not only trilinear-shaped diagrams but also the diamondor parallelogram-, rectangular-, or square-shaped graphs that have trilinear subdivisions. 1.2 This guide is the first of several documents to inform professionals in the field of hydrology with the traditional graphical methods available to display ground water chemistry. NOTE 1—Subsequent guides are planned that will describe the other categories of diagrams that have been developed to display ground water chemical analyses. (1) A guide for diagrams based on data analytical calculations will include those categories of water analysis graphs in which one analysis is plotted on each diagram (for example, the pattern, bar, radial, and circle diagrams). (2) A guide for statistical diagrams will include those categories of water analysis graphs in which multiple analyses are analyzed statistically and the results plotted on the diagram (for example, the box, etc.). 1.3 Numerous methods have been developed to display the ions dissolved in water on trilinear diagrams. These diagrams are valuable as a means of interpreting the physical and chemical mechanisms controlling the composition of water. 1.4 The most commonly used trilinear methods were developed by Hill (1-3),2 Langelier and Ludwig (4), Piper (5, 6), and Durov (7-13). These techniques are proven systems for interpreting the origin of the ions in natural ground water and for facilitating the comparison of results from a large number of analyses. NOTE 2—The use of trade names in this guide is for identification purposes only and does not constitute endorsement by ASTM. 1.5 This guide 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 guide 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.

Standard Guide for Displaying the Results of Chemical Analyses of Ground Water for Major Ions and Trace Elements-Trilinear Diagrams for Two or More Analyses

ASTM F625-94(2000) 泄漏控制系统水体分类标准实践

Standard Practice for Classifying Water Bodies for Spill Control Systems

ASTM D5472-93(1999)e1 用于确定控制井的比容量和估计透射率的标准测试方法

Standard Test Method for Determining Specific Capacity and Estimating Transmissivity at the Control Well

SL/T 238-1999 水资源评价导则

本导则适用于全国及区域水资源评价和专项工作中的水资源评价。

A guide to water resources assessment

DIN 38407-17:1999 德国对水,废水和淤泥的统一检验方法.可联合测定的材料组(F组).第17部分:用气－液相色谱分析仪测定选出的硝芳香族化合物

German standard methods for the examination of water, waste water and sludge - Jointly determinable substances (group F) - Part 17: Determination of selected nitroaromatic compounds by gas-liquid chromatography (F 17)

AWWA M36-1999 水核查和闭锁性检查.第2版

The present scope of Committee A21 activity is the development of standards and manuals addressing ductile-iron pressure pipe for water and ductile-iron and gray-iron fittings for use with such pipe. These standards and manuals include topics such as desi

Water Audits and Leak Detection Second Edition

NF T71-100:1998 水防碳氢化合物污染的设备.水栅.技术数据单.标准设计图

Equipment for water pollution against hydrocarbons. Booms. Technical data sheet. Standard layout.

ARI 320-1998 水资源蒸汽泵

This standard applies to Packaged Terminal Equipment as defined in AR1 Standard 3 10/380.

Water-Source Heat Pumps

ARI 325-1998 地下水资源蒸汽泵

The certification program includes ground water-source heat pumps that are electrically driven, . mechanical compression type systems as defined in the standard and included in this program.

Ground Water-Source Heat Pumps

ARI 330-1998 地下资源闭环蒸汽泵

. The certification program includes ground source closed-loop heat pumps that are electrically driven, mechanical compression type systems as defined in the standard and included in this program.

Ground Source Closed-Loop Heat Pumps

AWWA M29-1998 水效用提供资本.第2版

This standard describes the critical requirements for the effective operation and management of drinking water distribution systems.

Water Utility Capital Financing Second Edition

ASTM E1943-98(2015) 在石油释放现场利用自然衰减进行地下水补偿的标准指南

4.1 The approach presented in this guide is a practical and streamlined process for determining the appropriateness of remediation by natural attenuation and implementing remediation by natural attenuation at a given petroleum release site. This information can be used to evaluate remediation by natural attenuation along with other remedial options for each site. 4.2 In general, remediation by natural attenuation may be used in the following instances: 4.2.1 As the sole remedial action at sites where immediate threats to human health, safety and the environment do not exist or have been mitigated, and constituents of concern are unlikely to impact a receptor; 4.2.2 As a subsequent phase of remediation after another remedial action has sufficiently reduced concentrations/mass in the source area so that plume impacts on receptors are unlikely; or 4.2.3 As a part of a multi-component remediation plan. 4.3 This guide is intended to be used by environmental consultants, industry, and state and federal regulators involved in response actions at petroleum release sites. Activities described in this guide should be performed by a person appropriately trained to conduct the corrective action process. 4.4 The implementation of remediation by natural attenuation requires that the user exercise the same care and professional judgement as with any other remedial alternative by: 4.4.1 Ensuring that site characterization activities focus on collecting information required to evaluate and implement remediation by natural attenuation; 4.4.2 Evaluating information to understand natural attenuation processes present at the site; 4.4.3 Determining whether remediation by natural attenuation is the most appropriate and cost-effective remedial alternative with a reasonable probability of achieving remedial goals; and 4.4.4 Monitoring remedial progress. 4.5 Application and implementation of remediation by natural attenuation is intended to be compatible with Guide E1739 or other risk-based corrective action programs. 4.6 This guide does not address specific technical details of remediation by natural attenuation implementation such as site characterization (see Guide E1912), sampling, data interpretation, or quantifying rates. For additional discussion and guidance concerning these technical issues for remediation by natural attenuation see Appendix X1 through Appendix X7. 4.7x0......

Standard Guide for Remediation of Ground Water by Natural Attenuation at Petroleum Release Sites

ASTM E1943-98(2010) 在石油开采现场通过自然衰减度地下水补救的标准指南

The approach presented in this guide is a practical and streamlined process for determining the appropriateness of remediation by natural attenuation and implementing remediation by natural attenuation at a given petroleum release site. This information can be used to evaluate remediation by natural attenuation along with other remedial options for each site. In general, remediation by natural attenuation may be used in the following instances: As the sole remedial action at sites where immediate threats to human health, safety and the environment do not exist or have been mitigated, and constituents of concern are unlikely to impact a receptor; As a subsequent phase of remediation after another remedial action has sufficiently reduced concentrations/mass in the source area so that plume impacts on receptors are unlikely; or As a part of a multi-component remediation plan. This guide is intended to be used by environmental consultants, industry, and state and federal regulators involved in response actions at petroleum release sites. Activities described in this guide should be performed by a person appropriately trained to conduct the corrective action process. The implementation of remediation by natural attenuation requires that the user exercise the same care and professional judgement as with any other remedial alternative by: Ensuring that site characterization activities focus on collecting information required to evaluate and implement remediation by natural attenuation; Evaluating information to understand natural attenuation processes present at the site; Determining whether remediation by natural attenuation is the most appropriate and cost-effective remedial alternative with a reasonable probability of achieving remedial goals; and Monitoring remedial progress. Application and implementation of remediation by natural attenuation is intended to be compatible with Guide E1739 or other risk-based corrective action programs. This guide does not address specific technical details of remediation by natural attenuation implementation such as site characterization (see Guide E1912), sampling, data interpretation, or quantifying rates. For additional discussion and guidance concerning these technical issues for remediation by natural attenuation see Appendix X1 through Appendix X7. This guide does not specifically address considerations and concerns associated with natural attenuation of non-petroleum constituents, such as chlorinated solvents. Care must be taken to ensure that degradation by-products will not cause harm to human health or the environment. In addition, if constituents are present which do not readily attenuate, such as methyl-t-butyl ether (MTBE), remediation by natural attenuation may not be a suitable remedial alternative or may need to be supplemented with other remedial technologies. This guide is intended to be consistent with Guide E1599 and U.S. EPA guidance for implementation of remediation by natural attenuation (U.S. EPA, 1995, Chapter 9). 1.1 This is a guide for determining the appropriateness of remediation by natural attenuation and implementing remediation by natural attenuation at a given petroleum release site, either as a stand alone remedial action or in combination with other remedial actions. 1.2 Natural attenuation is a potential remediation alternative for containment and reduction of the mass and concentration of petroleum hydrocarbons in the environment to protect human health and the environment. Remediation by natural attenuation depends upon natural processes such as biode......

Standard Guide for Remediation of Ground Water by Natural Attenuation at Petroleum Release Sites

ASTM D1141-98(2008) 海水代用品的标准实施规程

This substitute ocean water may be used for laboratory testing where a reproducible solution simulating sea water is required. Examples are for tests on oil contamination, detergency evaluation, and corrosion testing. Note 28212;The lack of organic matter, suspended matter, and marine life in this solution does not permit unqualified acceptance of test results as representing performance in actual ocean water. Where corrosion is involved, the results obtained from laboratory tests may not approximate those secured under natural testing conditions that differ greatly from those of the laboratory, and especially where effects of velocity, salt atmospheres, or organic constituents are involved. Also the rapid depletion of reacting elements present in low concentrations suggests caution in direct application of results.1.1 This practice covers the preparation of solutions containing inorganic salts in proportions and concentrations representative of ocean water. Note 18212;Since the concentrations of ocean water varies with sampling location, the gross concentration employed herein is an average of many reliable individual analyses. Trace elements, occurring naturally in concentrations below 0.005 mg/L, are not included. 1.2 This practice provides three stock solutions, each relatively concentrated but stable in storage. For preparation of substitute ocean water, aliquots of the first two stock solutions with added salt are combined in larger volume. An added refinement in adjustment of heavy metal concentration is provided by the addition of a small aliquot of the third stock solution to the previous solution. 1.3 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 and health practices and determine the applicability of regulatory limitations prior to use.

Standard Practice for the Preparation of Substitute Ocean Water