首页> 外文期刊>Chemical engineering journal >Soil remediation by Fenton-like process: Phenol removal and soil organic matter modification
【24h】

Soil remediation by Fenton-like process: Phenol removal and soil organic matter modification

机译:类Fenton过程修复土壤:苯酚去除和土壤有机质改性

获取原文
获取原文并翻译 | 示例
           

摘要

In situ chemical oxidation (ISCO) seems to be a powerful technology for soil remediation. In this work the application of Fenton's like oxidation treatment (H2O2 + natural ferrous species present in soil) has been evaluated to two different soils (S1 and S2) contaminated with phenol (q_(phoH S1o) = 360 mg g~(-1), q_(phOH S2o) = 160 mg g~(-1)). They were categorized as calcareous loamy sand soils with different soil organic matter content (SOM_(S1) = 15.1%, SOM_(S2) = 10%). A refractory fraction of PhOH remained in the solid phase after treatment with H2O2 (C_(H2O_2o)) = 1 and 2%), probably due to an entrapment phenomenon of the contaminant and because of the competition of SOM for the oxidant. Consequently, lower remediation efficiencies are obtained as SOM increases.It has also been paid attention to the effect of the oxidant on the SOM. It was found that H2O2 does not produce any important modification of both SOM content and distribution. This was in agreement with the oxygen obtained after hydrogen peroxide had reacted. Only a slight degradation of the humic and fulvic acids and a partial removal of the quinone and carbonyl groups were noticed, while carbonate groups and most of the SOM remain the same. However, a decrease in the sorption capacity of PhOH in the treated soils is observed. Therefore, it can be assumed that the oxidation of SOM could modify the external surface of SOM. Moreover, the oxidation of SOM by H2O2 could create more hydrophilic sites and thus decreases the sorption ability.
机译:原位化学氧化(ISCO)似乎是土壤修复的强大技术。在这项工作中,已经对两种不同的被苯酚污染的土壤(S1和S2)(q_(phoH S1o)= 360 mg g〜(-1))进行了Fenton样氧化处理(H2O2 +土壤中存在的天然亚铁物种)的评估。 ,q_(phOH S2o)= 160 mg g〜(-1))。它们被分类为具有不同土壤有机质含量的钙质壤质砂质土壤(SOM_(S1)= 15.1%,SOM_(S2)= 10%)。过氧化氢(C_(H2O_2o))= 1和2%)处理后,PhOH的难熔部分保留在固相中,这可能是由于污染物的截留现象以及SOM对氧化剂的竞争所致。因此,随着SOM的增加,修复效率会降低。还应注意氧化剂对SOM的影响。已经发现,H 2 O 2不会对SOM含量和分布产生任何重要的改变。这与过氧化氢反应后得到的氧气一致。仅观察到腐殖酸和富勒酸的轻微降解以及醌和羰基的部分去除,而碳酸根和大多数SOM保持不变。然而,观察到在处理过的土壤中PhOH的吸附能力下降。因此,可以假设SOM的氧化可以修饰SOM的外表面。此外,H2O2对SOM的氧化作用可能会产生更多的亲水位点,从而降低吸附能力。

著录项

相似文献

  • 外文文献
  • 中文文献
  • 专利
获取原文

客服邮箱:kefu@zhangqiaokeyan.com

京公网安备:11010802029741号 ICP备案号:京ICP备15016152号-6 六维联合信息科技 (北京) 有限公司©版权所有
  • 客服微信

  • 服务号