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使用表面活性剂/配体溶液同时进行土壤镉和多氯联苯的去污。

Simultaneous soil Cd and PCB decontamination using a surfactant/ligand solution.

作者信息

Shin Mari, Barrington Suzelle F, Marshall William D, Kim Jin-Woo

机构信息

Department of Bioresource Engineering, Macdonald Campus of McGill University, Quebec, Canada.

出版信息

J Environ Sci Health A Tox Hazard Subst Environ Eng. 2004;39(11-12):2783-98.

Abstract

The simultaneous desorption of Cd and PCBs, from a contaminated soil, was investigated using a surfactant/ligand solution. The test surfactants were combinations of a nonionic surfactant [polyethylene oxide (PEO) of chain length 7.5 (Triton X-114), 9.5 (Triton X-100), 30 (Triton X-305), or 40 units (Triton X-405)], with iodide (I-). Triplicate 1 g soil samples were equilibrated, during 24h, with 15 mL of surfactant/ligand solution, at 0.025 or 0.50 and 0.0, 0.168, or 0.336 mol L(-1), respectively. The supernatant fraction was then separated from the particulates by centrifugation and analyzed for Cd to determine Cd desorption efficiency. After five consecutive washings, the treated soil samples were analyzed for PCB content to determine the desorption efficiency of this class of toxicant. Desorption of Cd increased with both increasing ligand concentration and decreasing surfactant chain length and concentration. The maximum Cd desorption efficiency (61%), was obtained with Triton X-100 at 0.025 mol L(-1), in the presence of I at 0.336 mol L(-1). After 5 successive washings, virtually quantitative PCB desorption (below limits of detection for tetra-, penta-, and hexachloro biphenyl compounds) had been achieved with most of surfactant/ligand combinations. Maximum desorption efficiency was achieved using either shorter chain length surfactant (n = 7.5 or 9.5) in combination with a higher ligand concentration, or using longer chain length surfactants (n = 30 and 40) with a lower ligand concentration. Thus, heavy metals and PCBs can be desorbed simultaneously from a contaminated soil with the same washing reagents, namely a surfactant-ligand combination. The optimum surfactant-ligand combination for the simultaneous desorption of both heavy metals and PCBs was a short chain length (n = 7.5 or 9.5) surfactant at low concentration admixed with 0.336 mol L(-1) I-.

摘要

采用表面活性剂/配体溶液研究了污染土壤中镉和多氯联苯的同步解吸情况。测试的表面活性剂是一种非离子表面活性剂[链长为7.5(吐温X - 114)、9.5(吐温X - 100)、30(吐温X - 305)或40个单元(吐温X - 405)的聚环氧乙烷(PEO)]与碘化物(I⁻)的组合。将1克土壤样品一式三份,在0.025或0.50以及0.0、0.168或0.336 mol L⁻¹的条件下,与15毫升表面活性剂/配体溶液在24小时内进行平衡。然后通过离心将上清液部分与颗粒分离,并分析镉以确定镉的解吸效率。连续洗涤五次后,分析处理后的土壤样品中的多氯联苯含量,以确定这类有毒物质的解吸效率。镉的解吸随着配体浓度的增加以及表面活性剂链长和浓度的降低而增加。在0.336 mol L⁻¹的I⁻存在下,使用0.025 mol L⁻¹的吐温X - 100可获得最大镉解吸效率(61%)。经过5次连续洗涤后,大多数表面活性剂/配体组合实现了几乎定量的多氯联苯解吸(低于四氯、五氯和六氯联苯化合物的检测限)。使用较短链长的表面活性剂(n = 7.5或9.5)与较高的配体浓度组合,或使用较长链长的表面活性剂(n = 30和40)与较低的配体浓度组合可实现最大解吸效率。因此,重金属和多氯联苯可以用相同的洗涤试剂,即表面活性剂 - 配体组合,从污染土壤中同步解吸出来。同时解吸重金属和多氯联苯的最佳表面活性剂 - 配体组合是低浓度的短链长(n = 7.5或9.5)表面活性剂与0.336 mol L⁻¹的I⁻混合。

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