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Flow Sheet Logic and Decision Criteria for Defining an End Point to Dredging When Cleanup Goals Are Not Obtained

机译:流表逻辑和决策标准,用于定义未获得清理目标时疏浚的终点

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An environmental dredging project was completed on the St. Lawrence River near Massena,New York between April and December 2001.The project entailed the dredging of PCB-contaminated sediments from an area of 12 hectares,in water depths up to 8.2 m,adjacent to the main shipping channel for the St. Lawrence Seaway.The area was divided into a total of 268 dredge cells,each with a target depth of excavation.Sediment verification samples were collected after each dredge pass.PCB results from these samples determined whether the cells had been remediated or required additional dredging to meet the cleanup goal of 1 ppm PCBs. A key issue during the design involved the development of decision criteria for determining how much additional dredging to do when the cleanup goals were not attained after the second dredge pass.The primary objective was to retain control over the dredging process by defining the requirements for each cell prior to the start of dredging,establishing the exact conditions when redredging was required as well as those situations where any further redredging was at the discretion of the project team (e.g.,to avoid capping).This approach sought to avoid potential delays waiting on field decisions by oversight personnel as to whether additional dredging was needed. A dredging process flow sheet logic was developed that considered the magnitude of contamination in the verification sample and both analytical and matrix variability inherent in sediment PCB analyses.The logic involved a comparison of the verification sample result collected after the initial dredge pass to that collected after the cell was redredged.It assigned quantitative measures of progress based on the relative percent difference between samples collected before and after redredging,which in turn were tied to the PCB concentration ranges in the cells prior to the redredging.These measures worked both ways—if the sample showed that concentrations were decreasing by a specified percentage,another dredge pass would be conducted.Conversely,if the sample showed that concentrations were increasing by the same percentage(i.e., contamination was getting worse),then another dredge pass would also be conducted. The end points were reached either when the cell was remediated to less than 1 ppm PCBs or there was neither any measurable progress nor worsening of conditions after successive dredge passes.In the latter situation,the cell was classified as being “marked for further evaluation,”meaning it could be left as is,marked for capping,or undergo additional dredging—at the discretion of the project team–to satisfy the overall remediation requirements for the site.
机译:在2001年4月和12月在纽约州马斯纳附近的圣劳伦斯河附近完成了一项环境疏浚项目。该项目仍然从12公顷的面积从12公顷的面积脱落,在水深,高达8.2米,邻近圣劳伦斯海路的主要航运渠道。该地区分为总共268个疏浚电池,每个疏浚细胞都有一个目标深度。在每个疏浚通渣后收集了验证样本.PCB来自这些样品的结果确定细胞是否确定了细胞已被修复或要求额外的疏浚,以满足1ppm PCB的清理目标。设计过程中的一个关键问题涉及决策标准的发展,以确定在第二次疏浚通行证后未达到清理目标时要做多少疏浚。主要目标是通过定义每个所要求来保留对疏浚过程的控制在疏浚开始之前的单元格,在需要旧化时建立确切的条件以及任何进一步冗续的情况由项目团队自行决定(例如,以避免封盖)。这一方法试图避免潜在的延迟等待监督人员对额外疏浚是否需要的田间决策。开发了疏浚过程流程图逻辑,其认为验证样本中的污染幅度以及沉积物PCB分析中固有的分析和矩阵变异。逻辑涉及在初始疏浚后收集的验证样本结果的比较redredged。基于​​在旧擦拭之前和redreding之前和之后收集的样品之间的相对百分比的相对百分比分配了分配的定量措施,这反过来与雷达之前细胞中的PCB浓度范围绑定。这些措施两种方式 - 如果两种方式工作样品表明,浓度通过指定的百分比降低,将进行另一种疏浚通段。如果样品显示浓度增加相同的百分比(即污染越来越差),则也将进行另一个疏浚通行证。当细胞被修复到小于1ppm的PPB时达到终点,或者在连续疏浚过程之后既没有任何可测量的进展也没有任何可测量的进展,也没有恶化条件。在后一种情况下,该细胞被归类为“标记为进一步评估, “意思是,它可以留下,标有封盖,或接受额外的疏浚 - 以项目团队自行决定 - 以满足网站的整体修复要求。

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