National Research Council, R. S. Kerr Environmental Research Center, P. O. Box 1198, Ada, OK 74821, USA.
J Environ Manage. 2012 Oct 15;108:42-8. doi: 10.1016/j.jenvman.2012.04.034. Epub 2012 May 30.
The goal of this study was to assess the oxidation of NAPL in soil, 30% of which were composed of chlorinated ethanes and ethenes, using catalyzed hydrogen peroxide (CHP), activated persulfate (AP), and H(2)O(2)-persulfate (HP) co-amendment systems. Citrate, a buffer and iron ligand, was amended to the treatment system to enhance oxidative treatment. Four activation/catalysis methods were employed: (1) oxidant only, (2) oxidant-citrate, (3) oxidant-iron(II), and (4) oxidant-citrate-iron(II). The NAPL treatment effectiveness was the greatest in the CHP reactions, the second in HP, and the third in AP. The effective activation and catalysis methods depended on the oxidant types; oxidant only for CHP and HP and oxidant-citrate-iron for AP. The treatability trend of chlorinated ethanes and ethenes in the soil mixture was as follows: trichloroethene > tetrachloroethene > dichloroethane > trichloroethane > tetrachloroethane. A significant fraction of persulfate remained in the oxidation systems after the 2-day reaction period, especially in the citrate-iron(II) AP. In general, oxidation systems that included citrate maintained a post-treatment pH in the range of 7-9. A final pH of AP oxidation systems was acidic (pH 2-3), where a molar ratio of citrate-iron(II) was less than 1.8 and where no citrate was amended.
本研究的目的是评估使用过氧氢(CHP)、过氧硫酸氢盐(AP)和过氧硫酸氢盐-HP(HP)共添加系统氧化土壤中 NAPL 的情况,其中 30%的 NAPL 由氯代乙烷和乙烯组成。将柠檬酸盐(一种缓冲剂和铁配体)添加到处理系统中,以增强氧化处理效果。采用了四种活化/催化方法:(1)氧化剂单独添加,(2)氧化剂-柠檬酸盐,(3)氧化剂-二价铁,和(4)氧化剂-柠檬酸盐-二价铁。在 CHP 反应中,NAPL 的处理效果最大,HP 次之,AP 效果最差。有效的活化和催化方法取决于氧化剂类型;CHP 和 HP 仅使用氧化剂,AP 则使用氧化剂-柠檬酸盐-铁。在土壤混合物中,氯代乙烷和乙烯的可处理性趋势如下:三氯乙烯>四氯乙烯>二氯乙烷>氯乙烯>四氯乙烯。在 2 天的反应期后,过硫酸盐在氧化系统中仍有很大一部分残留,特别是在含有柠檬酸-二价铁的 AP 中。一般来说,含有柠檬酸的氧化系统在处理后 pH 值保持在 7-9 之间。AP 氧化系统的最终 pH 值呈酸性(pH 2-3),此时柠檬酸-二价铁的摩尔比小于 1.8,且未添加柠檬酸。