首页> 外文会议>First International Conference on Remediation of Contaminated Sediments S1-3, Oct 10-12, 2001, Venice Italy >FIELD MEASUREMENTS OF PCB VOLATILIZATION FROM CONTAMINATED LAKE SEDIMENTS AND SURFACE WATERS
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FIELD MEASUREMENTS OF PCB VOLATILIZATION FROM CONTAMINATED LAKE SEDIMENTS AND SURFACE WATERS

机译:污染的湖泊沉积物和地表水中PCB挥发的现场测量

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Between 1955 and 1978, capacitors were manufactured at the Sangamo-Weston plant, South Carolina. PCB releases into the environment resulted in sediment contamination at the Sangamo-Weston/Twelvemile Creek/Lake Hartwell Superfund Site. Sangamo-Weston reported using Aroclors 1016, 1242, and 1254. This study consisted of a field investigation that was conducted at Lake Hartwell to determine measurable levels of volatilized PCBs occurring from PCB-contaminated shoreline sediments and from the lake-water surface. Flux chambers were designed, constructed, and deployed at locations corresponding with the United States Army Corps of Engineers (USACE) transect locations T-12, T-L, and T-O to trap volatilized PCBs over sediments and the lake surface. Sediment flux sampling was conducted for periods of 24- and 72 hours over surface- and deeper more contaminated sediments. Lake surface flux sampling was conducted over a 72-hour period. Volatilized PCBs were trapped onto pre-cleaned, certified, polyurethane foam cartridges (PUFs). Sediment and water samples were also collected at the sediment flux sampling locations. Other operational measurements included airflow rate, ambient and internal flux sampler temperatures, and barometric pressure. The PUF, water, and sediment samples were analyzed by GC/MS using EPA SW-846 8270M, from which 51 PCBs congeners were identified and resolved. Total PCB data was used to calculate net fluxes for the various sampling locations. PCB flux rates for surface sediments were 0.6 to 1 μg/m~2-day; deeper sediments (after removing the upper 15 cm of sediment) were 6 to 9 μg/m~2-day; and surface waters were 55 to 140 ng/m~2-day. Congener specific distributions for sediment, water, and air samples were analyzed and showed that PCB volatilization favored lower-chlorinated, and hence lower molecular weight, PCBs. The work presented herein summarizes this research and does not represent policy of the United States Environmental Protection Agency (U.S. EPA).
机译:1955年至1978年之间,电容器在南卡罗来纳州的Sangamo-Weston工厂生产。多氯联苯释放到环境中导致Sangamo-Weston / Twelvemile Creek / Hart Hartwell湖超级基金所在地的沉积物污染。 Sangamo-Weston报道使用Aroclors 1016、1242和1254。这项研究包括在Hartwell湖进行的现场调查,以确定可测量水平的多氯联苯挥发水平,这些多氯联苯含量受PCBs污染的海岸线沉积物和湖水表面的影响。在与美国陆军工程兵团(USACE)横断位置T-12,T-L和T-O相对应的位置设计,构造和部署助焊剂室,以将挥发的PCB捕集在沉积物和湖泊表面上。在表面和更深的受污染较深的沉积物上进行了24小时和72小时的泥沙通量采样。在72小时内进行了湖面通量采样。挥发的多氯联苯被捕集到预先清洁的,经过认证的聚氨酯泡沫药筒(PUF)中。在沉积物通量采样位置还收集了沉积物和水样。其他操作测量包括气流速率,环境和内部通量采样器温度以及大气压力。使用EPA SW-846 8270M通过GC / MS分析PUF,水和沉积物样品,从中鉴定并解决了51种PCBs同类物。总的PCB数据用于计算各个采样位置的净通量。表面沉积物的PCB通量速率为0.6至1μg/ m〜2天;较深的沉积物(除去上部15 cm的沉积物)为6至9μg/ m〜2天。地表水为55至140 ng / m〜2天。分析了沉积物,水和空气样品的同类比分布,结果表明,PCB挥发有利于低氯化物,因此分子量更低。本文介绍的工作总结了这项研究,并不代表美国环境保护署(U.S. EPA)的政策。

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