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首页> 外文期刊>Environmental Science & Technology >Field Application of Activated Carbon Amendment for In-Situ Stabilization of Polychlorinated Biphenyls in Marine Sediment
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Field Application of Activated Carbon Amendment for In-Situ Stabilization of Polychlorinated Biphenyls in Marine Sediment

机译:活性炭改良剂在海洋沉积物中原位稳定多氯联苯中的现场应用

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摘要

We report results on the first field-scale application of activated carbon (AC) amendment to contaminated sediment for in-srtu stabilization of polychlorinated biphenyls (PCBs). The test was performed on a tidal mud flat at South Basin, adjacent to the former Hunters Point Naval Shipyard, San Francisco Bay, CA. The major goals of the field study were to (1) assess scale up of the AC mixing technology using two available, large-scale devices, (2) validate the effectiveness of the AC amendment at the field scale, and (3) identify possible adverse effects of the remediation technology. Also, the test allowed comparison among monitoring tools, evaluation of longer-term effectiveness of AC amendment, and identification of field-related factors that confound the performance of in-situ biological assessments. Following background pretreatment measurements, we successfully incorporated AC into sediment to a nominal 30 cm depth during a single mixing event, as confirmed by total organic carbon and black carbon contents in the designated test plots. The measured AC dose averaged 2.0-3.2 wt% and varied depending on sampling locations and mixing equipment. AC amendment did not impact sediment resuspension or PCB release into the water column over the treatment plots, nor adversely impact the existing macro benthic community composition, richness, or diversity. The PCB bioaccumulation in marine clams was reduced when exposed to sediment treated with 2% AC in comparison to the controlrnplot Field-deployed semi permeable membrane devices and polyethylene devices showed about 50% reduction in PCB uptake in AC-treated sediment and similar reduction in estimated pore-water PCB concentration. This reduction was evident even after 13-month post-treatment with then 7 months of continuous exposure, indicating AC treatment efficacy was retained for an extended period. Aqueous equilibrium PCB concentrations and PCB desorption showed an AC-dose response. Field-exposed AC after 18 months retained a strong stabilization capability to reduce aqueous equilibrium PCB concentrations by about 90%, which also supports the long-term effectiveness of AC in the field. Additional mixing during or after AC deployment, increasing AC dose, reducing AC-particle size, and sequential deployment of AC dose will likely improve AC-sediment contact and overall effectiveness. The reductions in PCB availability observed with slow mass transfer under field conditions calls for predictive models to assess the long-term trends in pore-water PCB concentrations and the benefits of alternative in-situ AC application and mixing strategies.
机译:我们报告了活性炭(AC)修正剂在污染沉积物中的首次现场规模应用,以期在现场稳定多氯联苯(PCB)的结果。该测试是在南盆地的一个潮汐泥滩上进行的,该滩与加利福尼亚州旧金山湾的前猎人角海军造船厂相邻。现场研究的主要目标是(1)使用两个可用的大型设备评估AC混合技术的规模,(2)在现场规模上验证AC修正的有效性,以及(3)确定可能的方法修复技术的不利影响。此外,该测试还允许在监视工具之间进行比较,评估AC修正的长期有效性,并确定混淆现场生物学评估性能的与田野相关的因素。经过本底预处理测量,我们在一次混合过程中成功将AC掺入了沉积物中,达到了标称的30 cm深度,这可以通过指定试验区中的总有机碳和黑碳含量来确认。测得的AC剂量平均为2.0-3.2 wt%,并根据采样位置和混合设备而变化。 AC修正案不会影响沉积物重悬或PCB释放到处理区的水柱中,也不会不利地影响现有的大型底栖生物群落组成,丰富度或多样性。与对照组相比,当暴露于2%AC处理过的沉积物中时,海蛤中PCB的生物富集度降低了。现场部署的半透膜设备和聚乙烯设备显示AC处理过的沉积物中PCB吸收量减少了约50%,估计的减少量也类似孔隙水PCB浓度。即使在治疗后13个月并随后连续7个月暴露后,这种减少仍然很明显,表明AC治疗功效可长期保留。 PCB的水平衡浓度和PCB解吸显示出AC剂量响应。 18个月后暴露于现场的AC保留了强大的稳定能力,可将水平衡PCB浓度降低约90%,这也支持AC在现场的长期有效性。在AC部署期间或之后进行额外的混合,增加AC剂量,减小AC颗粒尺寸,并依次部署AC剂量,可能会改善AC沉积物的接触和整体有效性。在田间条件下,通过缓慢的质量转移观察到的PCB利用率的降低要求建立预测模型,以评估孔隙水PCB浓度的长期趋势以及替代性原位AC应用和混合策略的优势。

著录项

  • 来源
    《Environmental Science & Technology 》 |2009年第10期| 3815-3823| 共9页
  • 作者单位

    Department of Civil and Environmental Engineering, Stanford University, 473 Via Ortega, Room 313B Stanford, California 94305-4020;

    Department of Civil and Environmental Engineering,University of Maryland Baltimore County,Baltimore, Maryland 21250;

    Environmental Laboratory,U.S.Army Engineer Research and Development Center, 3909 Halls Ferry Rd, EP-R Vicksburg, Mississippi 39180;

    Department of Civil and Environmental Engineering,University of Maryland Baltimore County,Baltimore, Maryland 21250;

    Environmental Laboratory,U.S.Army Engineer Research and Development Center, 3909 Halls Ferry Rd, EP-R Vicksburg, Mississippi 39180;

    Switzerland, and Department of Education, Elmhurst College, 190 Prospect Avenue, Elmhurst, Illinois 60126;

    Department of Civil and Environmental Engineering, Stanford University, 473 Via Ortega, Room 313B Stanford, California 94305-4020;

    Environmental Laboratory,U.S.Army Engineer Research and Development Center, 3909 Halls Ferry Rd, EP-R Vicksburg, Mississippi 39180;

    Department of Civil and Environmental Engineering, Stanford University, 473 Via Ortega, Room 313B Stanford, California 94305-4020;

  • 收录信息 美国《科学引文索引》(SCI);美国《工程索引》(EI);美国《生物学医学文摘》(MEDLINE);美国《化学文摘》(CA);
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  • 正文语种 eng
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