Institute of Nuclear Agricultural Sciences, Key Laboratory of Nuclear Agricultural Sciences of Ministry of Agriculture of PRC and Zhejiang Province, Zhejiang University, Hangzhou 310058, China; Department of Microbiology, Key Laboratory of Microbiology for Agricultural Environment, Ministry of Agriculture, College of Life Sciences, Nanjing Agricultural University, Nanjing 210095, China.
Institute of Nuclear Agricultural Sciences, Key Laboratory of Nuclear Agricultural Sciences of Ministry of Agriculture of PRC and Zhejiang Province, Zhejiang University, Hangzhou 310058, China.
J Hazard Mater. 2021 Jun 15;412:125116. doi: 10.1016/j.jhazmat.2021.125116. Epub 2021 Jan 28.
Bioaugmentation methods are frequently employed for pesticide pollution remediation; however, it is not clear whether the introduced bacteria affect the pesticide bound residue (BRs) composition and whether the BRs can be catabolized by the introduced strains. This study aimed at answering these questions by using C-chlorpyrifos (C-CPF) and two CPF-degrading strains (Pseudomonas sp. DSP-1 and Cupriavidus sp. P2). The results showed that the BRs can be up to 83.0%, and that the CPF-BRs formed can be further transformed into CO by the strains. Indeed, the microbial inoculation can increase the CPF mineralization by 1.0-22.1 times and can decrease the BRs by up to ~50% of the control (on day 20). Compared with the control without bioaugmentation, microbial inoculation enhanced the release of BRs by 2.2-18.0 times. Adding biochar to the soil can greatly inhibit CPF mineralization and maintain the BR content at a relatively stable level. The CPF residue can affect the composition of the indigenous soil microbial community, but the introduction of bacteria for remediation did not have a significant effect. The results indicate that Pseudomonas sp. DSP-1 and Cupriavidus sp. P2 are useful for remediating both CPF extractable and bound residues.
生物强化方法常用于修复农药污染;然而,引入的细菌是否会影响农药结合残留(BRs)的组成,以及 BRs 是否可以被引入的菌株代谢,目前还不清楚。本研究通过使用 C-毒死蜱(C-CPF)和两种 CPF 降解菌株(假单胞菌 DSP-1 和铜绿假单胞菌 P2)来回答这些问题。结果表明,BRs 可高达 83.0%,且菌株可进一步将 CPF-BRs 转化为 CO。事实上,微生物接种可将 CPF 矿化提高 1.0-22.1 倍,并可使 BRs 降低至对照(第 20 天)的~50%。与未经生物强化的对照相比,微生物接种可将 BRs 的释放提高 2.2-18.0 倍。向土壤中添加生物炭可极大地抑制 CPF 矿化,并使 BR 含量保持在相对稳定的水平。CPF 残留会影响土著土壤微生物群落的组成,但修复过程中引入细菌并没有显著影响。结果表明,假单胞菌 DSP-1 和铜绿假单胞菌 P2 可用于修复 CPF 可提取和结合残留。