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利用稻草制备生物炭作为过一硫酸盐的活化剂去除萘:性能、机制、环境影响及在地下水修复中的适用性。

Resource utilization of rice straw to prepare biochar as peroxymonosulfate activator for naphthalene removal: Performances, mechanisms, environmental impact and applicability in groundwater.

机构信息

College of Civil Engineering, Tongji University, Shanghai, 200092, China.

College of Civil Engineering, Tongji University, Shanghai, 200092, China.

出版信息

Water Res. 2023 Oct 1;244:120555. doi: 10.1016/j.watres.2023.120555. Epub 2023 Aug 30.

DOI:10.1016/j.watres.2023.120555
PMID:37666149
Abstract

Herein, biochar was prepared using rice straw, and it served as the peroxymonosulfate (PMS) activator to degrade naphthalene (NAP). The results showed that pyrolysis temperature has played an important role in regulating biochar structure and properties. The biochar prepared at 900°C (BC900) had the best activation capacity and could remove NAP in a wide range of initial pH (5-11). In the system of BC900/PMS, multi-reactive species were produced, in which O and electron transfer mainly contributed to NAP degradation. In addition, the interference of complex groundwater components on the NAP removal rate must get attention. Cl had a significant promotional effect but risked the formation of chlorinated disinfection by-products. HCO, CO, and humic acid (HA) had an inhibitory effect; surfactants had compatibility problems with the BC900/PMS system, which could lead to unproductive consumption of PMS. Significantly, the BC900/PMS system showed satisfactory remediation performance in spiked natural groundwater and soil, and it could solve the problem of persistent groundwater contamination caused by NAP desorption from the soil. Besides, the degradation pathway of NAP was proposed, and the BC900/PMS system could degrade NAP into low or nontoxic products. These suggest that the BC900/PMS system has promising applications in in-situ groundwater remediation.

摘要

在此,使用稻草制备了生物炭,并将其作为过一硫酸盐(PMS)的激活剂来降解萘(NAP)。结果表明,热解温度在调节生物炭结构和性质方面起着重要作用。在 900°C 下制备的生物炭(BC900)具有最佳的激活能力,可以在较宽的初始 pH 值(5-11)范围内去除 NAP。在 BC900/PMS 体系中,产生了多种活性物质,其中 O 和电子转移主要有助于 NAP 的降解。此外,复杂地下水成分对 NAP 去除率的干扰必须引起重视。Cl 具有显著的促进作用,但有形成氯化消毒副产物的风险。HCO、CO 和腐殖酸(HA)具有抑制作用;表面活性剂与 BC900/PMS 体系存在兼容性问题,可能导致 PMS 无效消耗。值得注意的是,BC900/PMS 体系在污染天然地下水和土壤中的修复表现出令人满意的效果,它可以解决由于土壤中 NAP 解吸而导致的地下水持续污染问题。此外,提出了 NAP 的降解途径,BC900/PMS 体系可以将 NAP 降解为低毒或无毒产物。这些表明 BC900/PMS 体系在原位地下水修复中具有广阔的应用前景。

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