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Atrazine Contamination in a Rural Source-Water Supply: Spa Lake, Lewisburg, Kentucky

机译:农村水源中的r去津污染:肯塔基州刘易斯堡的温泉湖

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摘要

In 1998, Western Kentucky University (WKU) worked in collaboration with the Environmental Protection Agency (EPA), Drinking Water Protection Division, to investigate methods to improve source-water quality for rural-water supply systems (RWSS). Through partial funding from the EPA, WKU developed a Technical Assistance Center for Water Quality (TACWQ), which focused resources and expertise toward assisting RWSS in achieving and maintaining capacity development goals and protecting public health. The TACWQ established the Source Water Protection Initiative (SWPI) to assist RWSS in acquiring and monitoring the technical, financial and managerial capacity needed to provide safe drinking water and achieve the public health protection goals of the EPA Safe Drinking Water Act (Technical Assistance Center, July 1998). The SWPI also provided technical assistance toward identifying and reducing source water impacts throughout Kentucky. Monthly sampling during 2000 from seven watersheds in western and south central Kentucky showed that levels of several pesticides and herbicides were elevated above Maximum Contaminant Levels (MCLs) in their source waters. Of the MCL exceedences, three commonly used pesticides (atrazine, alachlor, and simazine) were repeatedly being detected at several sites. Of the three compounds, atrazine, a triazineclass herbicide widely used in Kentucky to control broad leaf and grassy weeds in row crops such as corn, drew the most interest. Atrazine has been classified as a spring use only, u22Restricted Use Pesticide due to its potential for groundwater contamination.u22 (EXTOXNET, 1996) It is regulated as a compound with class III (slight) toxicity. In 1994, EPA took atrazine under special review to evaluate the ecological and biological effects it may cause. EPA later deemed atrazine not to significantly increase the risk of cancer in humans and went as far as lifting its use restrictions. Independent researchers still dispute EPA claims. The exceedences of the MCLs by many compounds in source water do not immediately result in violations. The source water must go through treatment processes. Water-supply operators must strive to meet National Primary Drinking Water Standards (EPA, 1999) prior to going to the consumer. However, the fundamental concept driving the SWPI is that the technical and financial challenges faced by RWSS are proportional to the quality of their source water. At several sites, even treated water that was distributed to customers exceeded federally mandated MCLs. Levels of atrazine in finished water reached 17 parts per billion (ppb) in Lewisburg, Kentucky. The MCL for atrazine is currently 3.0 ppb.
机译:1998年,西肯塔基大学(WKU)与环境保护局(EPA)的饮用水保护司合作,研究了改善农村供水系统(RWSS)的源水质量的方法。通过EPA的部分资金,WKU建立了水质技术援助中心(TACWQ),该中心集中了资源和专业知识来协助RWSS实现和维持能力发展目标并保护公众健康。 TACWQ建立了源水保护倡议(SWPI),以协助RWSS获得和监控提供安全饮用水并实现EPA安全饮用水法(技术援助中心, 1998年7月)。 SWPI还为确定和减少整个肯塔基州的水源影响提供了技术援助。 2000年期间,从肯塔基州中西部和南部的七个流域进行的每月抽样调查显示,几种农药和除草剂的水平被提高到其原水的最大污染物水平(MCL)以上。在超过MCL的范围内,在几个地点反复检测到三种常用农药(阿特拉津,甲草胺和西马津)。在这三种化合物中,阿特拉津是一种三嗪类除草剂,在肯塔基州广泛用于控制玉米等行作物中的阔叶和禾本科杂草,引起了人们的最大兴趣。 r去津仅被归类为春季用途,由于其可能被地下水污染而被限制使用。 EXT22(EXTOXNET,1996)被管制为具有III类(轻微)毒性的化合物。 1994年,EPA对阿特拉津进行了特别审查,以评估其可能引起的生态和生物影响。 EPA后来认为阿特拉津不会显着增加人类患癌症的风险,甚至取消了其使用限制。独立研究人员仍然对EPA的主张提出异议。源水中许多化合物超过MCL并不会立即导致违规。源水必须经过处理过程。供水运营商必须先达到国家一级饮用水标准(EPA,1999),然后才能进入消费者手中。但是,推动SWPI的基本概念是RWSS面临的技术和财务挑战与其原水水质成正比。在一些地点,甚至分配给客户的经处理的水也超过了联邦规定的MCL。在肯塔基州的刘易斯堡,成品水中r去津的含量达到了十亿分之17(ppb)。阿特拉津的MCL当前为3.0 ppb。

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    Seadler Kathryn;

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