Remediating thiacloprid-contaminated soil utilizing straw biochar-loaded iron and manganese oxides activated persulfate: Removal effects and soil environment changes

生物炭 化学 环境化学 环境修复 稻草 过硫酸盐 噻虫啉 土壤水分 污染 核化学 农学 无机化学 环境科学 催化作用 生物化学 杀虫剂 有机化学 热解 生物 生态学 益达胺 噻虫嗪 土壤科学
作者
Jie Li,Zhi Guo,Kangping Cui,Xing Chen,Yang Xue,Dazhuang Dong,Shanshan Xi,Zhangzhen Wu,Feiyan Wu
出处
期刊:Journal of Hazardous Materials [Elsevier BV]
卷期号:459: 132066-132066 被引量:20
标识
DOI:10.1016/j.jhazmat.2023.132066
摘要

Thiacloprid (THI) has accumulated significantly in agricultural soil. Herein, a novel approach to removing THI was explored by straw biochar-loaded iron and manganese oxides (FeMn@BC) to activate the persulfate (PS). The factors influencing the removal of 5 mg kg-1 THI from the soil by FeMn@BC/PS were investigated, including FeMn@BC dosing, PS dosing, temperature, and soil microorganisms. The feasibility was demonstrated by the 75.22% removal rate of THI with 3% FeMn@BC and 2% PS at 7 days and a 92.50% removal rate within 60 days. Compared to the THI, NH4+-N and available potassium were 3.96 and 3.25 times, and urease and phosphatase activities were increased by 22.54% and 33.28% in the FeMn@BC/PS at the 15 days, respectively. THI was found to seriously alter the structure of the genus in the 15 days by 16 S rRNA analysis; however, the FeMn@BC/PS group alleviated the damage, compared to the THI with 658 more operational taxonomic units. Actinobacteriota accounted for 51.48% of the microbial community in the FeMn@BC/PS group after 60 days, possibly converting transition products of THI into smaller molecules. This article provides a novel insight into advanced oxidative remediation of soils.
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