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'IS YOUR REPRESENTATIVE OUTFALL REALLY REPRESENTATIVE?' FACTORS THAT CAN AFFECT REPRESENTATIVE DISCHARGE SAMPLING DATA

机译:“你的代表性排污物真的代表吗?”可能影响代表性放电采样数据的因素

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In 1987 Congress amended the Clean Water Act requiring EPA to establish NPDES requirements for storm water discharges. As part of the NPDES permit requirements for Phase I municipal separate storm sewer systems (MS4), the operator of the system is required to perform field screening analysis of the major outfalls to detect illicit connections. The operator is allowed to designate "representative outfalls" to characterize discharges from drainage areas of similar land-uses. Volume-weighted water quality samples are collected at the representative outfalls during storm events and used to calculate event mean concentrations (EMCs). Data from this characterization may be used in a number of applications including: identification of illicit discharges, determination of load allocations on impaired stream segments in a TMDL process, selection of best management practices to reduce or eliminate pollutant discharge, and prioritization of infrastructure improvements. Each of these applications could result in significant resources to execute. Therefore, it is important to collect data from the representative discharges, which are accurate, and correctly characterize the drainage areas they represent. This paper presents a case study evaluation for one of Harris County Flood Control District representative outfall located in Houston, Texas. Houston has over 15 bayous that drain the relatively flat, coastal watershed. Houston receives 50-inches of rainfall on average, evenly distributed over the year. In addition, the region frequently experiences short-duration, highintensity rainfall events that can cause brief flooding. There are four representative outfall land uses are used to characterize Harris County, Texas: single family residential, multi-family residential, commercial, and industrial. These designations do not fully represent the land uses in the County. A number of land use activities are not accounted for in these designations (i.e. transportation, recreational, institutional, and undeveloped areas.) This study is focused on identifying factors that may influence results collected during storm water sampling at representative outfalls. During this study, a procedure was developed to investigate the current status of a representative monitoring site. First, the drainage area of the representative outfall is delineated. This drainage area is used to identify land use and potential sources of pollution. Finally, identified sources were field verified, and GPS locations collected for each potential source.
机译:1987年国会修订了清洁水法案,要求美国环保署建立了雨水排放NPDES要求。作为NPDES的一部分,允许一期市政独立的雨水管道系统(MS4)的要求,该系统的操作需要执行的主要排污口的现场筛选分析,检测非法连接。运营商被允许从类似土地利用的流域区域指定“代表排污口”来描述放电。体积加权水质样品在暴雨期间在代表排水口收集并用于计算事件的平均浓度(EMCS)。识别非法排放,在一个TMDL过程受损的流分段判定负载分配,选择最好的管理方法,以减少或消除污染物排放,和基础设施的改善优先级:从该特征数据可以在许多应用中,包括使用。每个应用程序都可能导致显著资源来执行。因此,它是从代表放电收集数据,这是准确,正确地描述他们所代表的流域重要。本文提出了一个案例研究评价哈里斯县防洪区代表排污口设在得克萨斯州休斯敦的一个。休斯顿拥有超过15沼,耗尽了相对平坦,沿岸分水岭。休斯敦接受降雨量平均为50英寸,均匀分布在一年。此外,该地区经常经历短期的,highintensity降水事件可能会导致短暂水浸。有四种代表性的排污管土地用途用于表征哈里斯县:单户住宅,多户住宅,商业和工业。这些标示并不完全代表县的土地用途。一些土地使用活动的未在这些指定占(即运输,娱乐,机构,和未显影区域)。这项研究的重点是确定可能影响在代表排水口雨水采样过程中收集的结果的因素。在这项研究中,一个程序的开发是为了调查一个代表性的监测点的当前状态。首先,代表排水口排水区域划定。该流域是用来识别土地利用和污染的潜在来源。最后,确定来源是现场核实,并收集每一个潜在来源的GPS位置。

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