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PCBs in Ambient Air – Method Evaluation and Background Monitoring – The Hudson River, NY Sediment Remediation Project

机译:环境空气中的多氯联苯–方法评估和背景监测–纽约州哈德逊河沉积物修复项目

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A pilot program was conducted in July-September 2005 to assist in the selection of sampling and analyses methods to be used for measurement of PCBs in ambient air during the Hudson River NY sediment remediation program. The field program evaluated use of EPA Method TO4A (high volume sampling) and EPA Method TO10A (low volume sampling) as well as aroclor pattern matching and congener specific analytical procedures. A six (6) week field monitoring program was also conducted to establish baseline concentrations for PCBs at a representative location riverside in the planned sediment dredging corridor. Mean concentrations for the two (2) types of sorbents used in low volume samplers (EPA Method 10A) were in good agreement (PUF alone mean =3.96 ng/m3 and PUF/XAD-2 mean = 4.30 ng/m3). As a result of these data it was concluded that routine sampling during remediation could take place with either PUF alone or with PUF/XAD-2. Results for high volume PUF samples (EPA Method TO4A) collocated with the low volume samples ranged from 3.8-5.74 ng/m3 with a mean concentration of 4.74 ng/m3. Reported concentrations for these same samples are in excellent agreement when comparing results for the two analytical methods examined. (Aroclor technique, mean = 4.74 ng/m3; congener method, mean = 4.72 ng/m3). These results were instrumental in the selection of aroclor or pattern matching as the method of choice for analysis of ambient air samples collected during the actual Hudson River Sediment Remedial Program. A classical aroclor 1242 pattern was observed in these samples suggesting that the PCBs may be associated with atmospheric particulate matter in the vicinity of the sampling location. The average background concentration at the Fort Edward site for all samples was 2.41 ng/m3 (n = 24) and ranged from 0.70 – 4.48 ng/m3. These concentrations are consistent with PCB levels found in rural settings. These results verified that both sampling methods were capable of meeting the project QOL sensitivity target of 30 ng/m3 on a routine basis.
机译:2005年7月至9月进行了一项试点计划,以帮助选择在哈德逊河纽约州沉积物修复计划期间用于测量环境空气中多氯联苯的采样和分析方法。现场程序评估了EPA方法TO4A(高容量采样)和EPA方法TO10A(低容量采样)以及aroclor模式匹配和特定同类分析程序的使用。还进行了六(6)周的野外监测计划,以在计划的泥沙疏corridor走廊的代表性地点河边确定多氯联苯的基准浓度。小体积进样器(EPA方法10A)中使用的两类(2)吸附剂的平均浓度相符(仅PUF平均值= 3.96 ng / m3,PUF / XAD-2平均值= 4.30 ng / m3)。根据这些数据得出的结论是,修复期间的常规采样可以单独使用PUF或使用PUF / XAD-2进行。高容量PUF样品(EPA方法TO4A)与低容量样品的结果范围为3.8-5.74 ng / m3,平均浓度为4.74 ng / m3。比较两种分析方法的结果时,这些相同样品的报告浓度非常一致。 (Aroclor技术,平均值= 4.74 ng / m3;同类法,平均值= 4.72 ng / m3)。这些结果有助于选择acrolor或模式匹配,作为分析实际哈德逊河沉积物修复计划期间收集的环境空气样本的选择方法。在这些样品中观察到了经典的aroclor 1242模式,这表明PCB可能与采样位置附近的大气颗粒物有关。所有样本在爱德华堡站点的平均背景浓度为2.41 ng / m3(n = 24),范围为0.70 – 4.48 ng / m3。这些浓度与农村地区的PCB含量一致。这些结果证明,这两种采样方法均能够常规满足项目QOL灵敏度目标30 ng / m3的要求。

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