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Bacteria Total Maximum Daily Load Task Force Final Report

机译:细菌总最大日负荷工作队最终报告

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摘要

In September 2006, the Texas Commission on Environmental Quality (TCEQ) and Texas State Soil and Water Conservation Board (TSSWCB) charged a seven-person Bacteria Total Maximum Daily Load (TMDL) Task Force with: * examining approaches that other states use to develop and implement bacteria TMDLs, * recommending cost-effective and time-efficient methods for developing TMDLs, * recommending effective approaches for developing TMDL Implementation Plans (I-Plans), * evaluating a variety of models and bacteria source tracking (BST) methods available for developing TMDLs and I-Plans, and recommending under what conditions certain methods are more appropriate, and * developing a roadmap for further scientific research needed to reduce uncertainty about how bacteria behave under different water conditions in Texas.The Task Force, assisted by an Expert Advisory Group of approximately 50 stakeholders and agency staff, held two two-hour meetings/teleconferences and developed two drafts of the report. These drafts were shared by e-mail and on a Web site and feedback received from the Expert Advisory Group was also made available on the Web site.The Task Force report describes the characteristics, as well as some of the strengths and weaknesses of several models that have been used and/or are under development to assist bacteria TMDL and I-Plan analysis. These include: * load duration curves (LDC), * spatially explicit statistical models, including Arc Hydro, SPARROW and SELECT, * the mass balance models BLEST and BIT, and * the mechanistic hydrologic/water quality models HSPF, SWAT, SWMM and WASP.The Task Force report also describes and makes recommendations for effective use of BST methods that have been used in Texas and elsewhere for TMDL development. These include ERIC-PCR, Ribotyping, PFGE, KB-ARA, CSU and Bacteroidales PCR. Based on recent experience in Texas and elsewhere, the Task Force recommends using library-independent methods like Bacteriodales PCR for preliminary qualitative analyses and more expensive and time-consuming library-dependent methods if more quantitative data are required for TMDL or I-Plan development.Based on the discussions of bacteria models and source tracking, as well as extensive input from the Expert Advisory Group, the Task Force recommends a three-tier approach to implementing bacteria TMDLs and I-Plans.Tier 1 is a one-year process that includes the formation of a representative stakeholder group, development of a comprehensive geographic information system (GIS) of the watershed, a survey of potential bacterial sources, calculation of load duration curves from existing monitoring data and analysis by agency personnel and stakeholders of data collected for Tier 1. After reviewing information from Tier 1, the group may choose to complete and submit a draft TMDL for agency approval, request an evaluation of the designated use of the water body (an use attainability analysis) or proceed to Tier 2.Tier 2 is a one-to-two-year effort designed to collect targeted monitoring data to fill gaps in previously collected data, conduct qualitative library-independent BST data to determine whether humans and/or a few major classes of animals are sources and develop simple spatially explicit or mass balance models of bacteria in the watershed. After analysis of Tier 1 and Tier 2 data, the group may chose to complete and submit the draft TMDL (or I-Plan if a TMDL was developed after Tier 1), request an evaluation of the designated use (an use attainability analysis), or initiate a ?phased TMDL? and proceed with Tier 3 analysis.Tier 3 is a two-to-three-year process designed to continue strong stakeholder involvement, implement more extensive targeted monitoring, conduct quantitative library-dependent BST analysis and develop a detailed hydrologic/water quality model for the watershed. Tier 3 should be implemented only when this level of detailed analysis is needed for I-Plan development or for TMDL development for particularly complex watersheds for which consensus cannot be reached after Tier 2.The Task Force emphasizes that the agencies and stakeholders may choose to deviate from these recommendations if they reach consensus that a more time- and cost-effective approach is feasible.The Task Force concludes its report by summarizing a number of research activities needed to strengthen the scientific tools available for TMDL and I-Plan development. The needed research falls into the following categories: characterization of sources, characterization of kinetic rates and transport mechanisms, enhancements to bacteria fate and transport models and bacteria source tracking, determination of effectiveness of control mechanisms and quantification of uncertainty and risk.
机译:2006年9月,德克萨斯州环境质量委员会(TCEQ)和德克萨斯州水土保持委员会(TSSWCB)向一个由7人组成的细菌总最大日负荷(TMDL)工作组负责:*检查其他州用于开发的方法和实施细菌TMDL,*推荐开发TMDL的经济有效的方法,*推荐开发TMDL实施计划(I-Plans)的有效方法,*评估可用于以下方面的各种模型和细菌来源跟踪(BST)方法制定TMDL和I-计划,并建议在何种条件下更合适的方法,以及*制定进一步的科学研究路线图,以减少德克萨斯州不同水质条件下细菌的行为方式所需要的不确定性。由大约50名利益相关者和机构人员组成的咨询小组,举行了两次为时两小时的会议/电话会议,并制定了两次报告的尾部。这些草案通过电子邮件和网站共享,并且从专家咨询小组收到的反馈也可以在网站上获得。工作组报告描述了这些模型的特征以及一些模型的优缺点。已经使用和/或正在开发中的用于协助细菌TMDL和I-Plan分析的工具。其中包括:*载荷持续时间曲线(LDC),*空间明确的统计模型,包括Arc Hydro,SPARROW和SELECT,*质量平衡模型BLEST和BIT,以及*机械水文/水质模型HSPF,SWAT,SWMM和WASP该工作队的报告还描述并提出了有效利用德克萨斯州和其他地区用于TMDL开发的BST方法的建议。这些包括ERIC-PCR,核糖体分型,PFGE,KB-ARA,CSU和拟杆菌PCR。根据德克萨斯州和其他地区的最新经验,如果TMDL或I-Plan开发需要更多定量数据,则工作组建议使用与细菌无关的方法(如细菌代PCR)进行初步定性分析,并使用更昂贵和耗时的与图书馆有关的方法。根据细菌模型和来源跟踪的讨论以及专家咨询小组的广泛投入,工作队建议采用三层方法实施细菌TMDL和I-计划。方法1是一个为期一年的过程,其中包括成立一个有代表性的利益相关者小组,开发该流域的综合地理信息系统(GIS),对潜在细菌源进行调查,根据现有的监测数据计算负荷持续时间曲线,并由代理商人员和利益相关者对收集到的Tier数据进行分析1.在审核了一级方法的信息后,小组可以选择填写并提交针对代理应用的TMDL草案评估,请求对水体的指定用途进行评估(使用可获得性分析)或进入方法2。方法2是一项为期一到两年的工作,旨在收集目标监测数据以填补先前收集的数据中的空白进行与定性库无关的BST数据,以确定人类和/或几种主要动物是否为来源,并开发分水岭中细菌的简单空间明晰或质量平衡模型。在对方法1和方法2的数据进行分析之后,该小组可以选择完成并提交TMDL草案(如果在方法1之后开发了TMDL,则可以提交I-计划),要求对指定用途进行评估(使用可获得性分析),或启动“分阶段的TMDL”?并继续进行方法3的分析。方法3是一个为期2至3年的过程,旨在继续让利益相关者大力参与,实施更广泛的针对性监测,进行基于库的定量BST分析并为该模型开发详细的水文/水质模型。分水岭。只有在I级计划开发或TMDL开发需要在方法2之后无法达成共识的特别复杂的流域时,才应执行方法3的详细分析。工作队强调,机构和利益相关者可以选择偏离如果他们就这些建议达成共识,则认为可以采用更具时间和成本效益的方法是可行的。工作组在总结报告时总结了为加强TMDL和I-Plan开发可用的科学工具而需要进行的大量研究活动。所需的研究分为以下几类:来源的表征,动力学速率和传输机制的表征,细菌命运和传输模型的增强以及细菌来源的追踪,控制机制有效性的确定以及不确定性和风险的量化。

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