生物技术通报 ›› 2021, Vol. 37 ›› Issue (10): 81-90.doi: 10.13560/j.cnki.biotech.bull.1985.2021-0194

• 研究报告 • 上一篇    下一篇

Microbacterium sp. BD6在Cr(VI)污染农田土壤修复中的应用研究

杨宗政1,2,3(), 赵晓宇2, 刘丹2, 许文帅2, 吴志国1,2,3()   

  1. 1.天津科技大学化工与材料学院,天津 300457
    2.天津科技大学海洋与环境学院,天津 300457
    3.天津市卤水化工与资源生态化利用重点实验室,天津 300457
  • 收稿日期:2021-02-18 出版日期:2021-10-26 发布日期:2021-11-12
  • 作者简介:杨宗政,男,博士,教授,研究方向:土壤污染治理;E-mail: yzz3520@163.com
  • 基金资助:
    广东省环境污染控制与修复技术重点实验室开放基金重点项目(202001)

Bioremediation of Cr(VI)-contaminated Farmland Soil by Microbacterium sp. BD6

YANG Zong-zheng1,2,3(), ZHAO Xiao-yu2, LIU Dan2, XU Wen-shuai2, WU Zhi-guo1,2,3()   

  1. 1. College of Chemical and Materials Science,Tianjin University of Science & Technology,Tianjin 300457;
    2. College of Marine and Environmental Sciences,Tianjin University of Science & Technology,Tianjin 300457;
    3. Tianjin Key Laboratory of Brine Chemical Engineering and Resource Eco-utilization,Tianjin 300457
  • Received:2021-02-18 Published:2021-10-26 Online:2021-11-12

摘要:

旨在探究Cr(VI)还原菌在Cr(VI)污染土壤中的修复条件及效果,为实际Cr(VI)污染农田土壤的修复提供借鉴。采用单因素实验、盆栽实验、高通量测序及qPCR等方法研究了菌株Microbacterium sp. BD6修复Cr(VI)污染土壤的最佳条件、修复前后对于植物的毒性以及对土壤中微生物群落的影响。实验表明菌株BD6在土壤含水率为30%及以上,温度为25-40℃的条件下,96 h对土壤中100 mg Cr(VI)/kg土壤的Cr(VI)还原率可达90%以上。菌株BD6在其它重金属离子存在的条件下仍然可以对Cr(VI)进行还原,但还原效果会受到影响。Cr(VI)会对黄豆植株高度、发芽率等指标产生负面作用;经菌株BD6修复后的土壤,降低了Cr(VI)的毒性,明显改善植株的生长状况,且植株体内铬含量显著降低。Cr(VI)污染土壤中微生物丰度和多样性 明显低于未污染的土壤;经菌株BD6修复后的Cr(VI)污染土壤,微生物多样性随着修复时间的增长呈恢复趋势。因此,菌株BD6可作为修复Cr(VI)污染土壤潜在候选菌株,在今后的实际污染土壤修复中具有一定的应用价值。

关键词: Microbacterium sp. BD6, Cr(VI)污染土壤, 生物修复, 微生物群落, 电子供体

Abstract:

The purpose of this paper is to optimize the conditions and investigate the effects in bioremediation of Cr(VI)-contaminated soil by Cr(VI)-reducing bacteria,and to provide reference in practical remediation of Cr(VI)-contaminated soil. The single factor experiments,the pot experiments,high-throughput sequencing and qPCR methods were used to study the optimal conditions for the bioremediation of Cr(VI)-contaminated soil by Microbacterium sp. BD6,the toxicity to plants before and after remediation,and the effects on soil microbial community in the soil. The experiments showed that the Cr(VI)reduction rate of 100 mg Cr(VI)/kg contaminated soil by strain BD6 was above 90% in 96 h under the conditions of soil moisture content 30% and temperature 25℃- 40℃. Strain BD6 still reduced Cr(VI)in presence of other heavy metal ions,but the reduction effects were impacted. Cr(VI)restrained the height,germination rate and other indicators of soybean plant. The toxicity of the soil remediated by strain BD6 was reduced,the growth of plants was significantly improved,and the chromium content in plants significantly decreased. The microbial abundance and diversity in Cr(VI)-contaminated soil were significantly lower than those in non-contaminated soil. The microbial abundance and diversity of Cr(VI)-contaminated soil after remediation by strain BD6 increased with the bioremediation proceeded continuously. In conclusion,strain BD6 can be used as a potential candidate strain for the remediation of Cr(VI)-contaminated soil in the future.

Key words: Microbacterium sp. BD6, Cr(VI)-contaminated soil, bioremediation, microbial community, electron donor