Journal of Integrative Agriculture

• •    下一篇

菌群YM2的富集、驯化、降解、适应机制以及烟嘧磺隆的生物修复

  

  • 修回日期:2024-03-21

Enrichment, domestication, degradation, adaptive mechanism, and nicosulfuron bioremediation of bacteria consortium YM2

Yufeng Xiao1, Meiqi Dong1, Xian Wu2, Shuang Liang1, Ranhong Li1, Hongyu Pan3, Hao Zhang1#   

  1. 1 College of Plant Protection, Jilin Agricultural University, Changchun 130118, China

    2 Institute of Plant Protection, Jilin Academy of Agricultural Sciences, ChangChun 130000, China

    3 College of Plant Sciences, Jilin University, Changchun 130062, China

  • Revised:2024-03-21
  • About author:Yufeng XIAO, Tel: +86-17649813417, E-mail: xyfethan@163.com,; #Correspondence Hao ZHANG, Tel: +86-13756097428, E-mail: haozhang100@163.com,

摘要: 烟嘧磺隆(NSR)是一种磺酰脲类除草剂,极易进入土壤和水体,影响自然环境和人类健康。本研究从某农药厂的活性淤泥中富集和驯化出降解菌群YM2,对烟嘧磺隆进行生物修复。对菌群YM2的培养基优化,筛选出最适碳源、氮源和无机盐分别为葡萄糖、酵母粉和NaCl,对其响应面分析,确定最佳培养条件为:9.41 g L1麦芽糊精、21.37 g L1酵母粉和12.45g L1NaCl,在此培养基下菌群YM2对烟嘧磺隆的降解率达97.49%优化菌群YM2对烟嘧磺隆的在不同环境条件下的降解特性,最佳降解条件为30℃pH 6.0菌群YM2接种量1%20 mg L1烟嘧磺隆初始浓度。并且,菌群YM2Cd2+Pb2+Ni2+ZN2+等重金属离子耐受,可以在重金属离子胁迫下生长和降解。菌群YM2主要通过胞外酶降解烟嘧磺隆,降解率92.17%。在降解过程中,细胞膜通透性、细胞表面疏水性活性氧含量、超氧化物歧化酶、过氧化氢酶、过氧化物酶、丙二醛含量、和细胞凋亡率均呈现先升高后降低的趋势,受到烟嘧磺隆胁迫时,激发菌群YM2的氧化应激系统,提升抗氧化酶活性,降低活性氧,并降解烟嘧磺隆,是菌群YM2的适应机制,即对烟嘧磺隆胁迫的应激反应。生物膜形成相关基因luxSwaaEspo0Awza的表达随时间和烟嘧磺隆浓度的变化而变化。适量的烟嘧磺隆诱导生物膜形成和激发氧化应激系统。污水和土壤中的20 mg kg1烟嘧磺隆分别被降至1.92 mg L12.72 mg L1,降解率达90.4%86.4%在模拟污水处理装置中水力停留时间12 h时第一阶段(前3 d)仅添加烟嘧磺隆,第二阶段(3-10 d)添加菌群YM210天后菌群YM2降解了84.55%的烟嘧磺隆。本研究为烟嘧磺隆的微生物修复提供了理论依据。

Abstract: Nicosulfuron (NSR), a sulfonylurea herbicide, can easily enter water bodies, affecting aquatic life and human safety. Here, bacteria consortium YM2 was enriched and domesticated from the active sludge of a pesticide plant for the bioremediation of NSR wastewater. The response surface methodology data revealed that under optimal incubation conditions: 9.41 g L1 maltodextrin, 21.37 g L1 yeast extract, and 12.45 g L1 NaCl, YM2 bacteria consortium degraded 97.49% of NSR within 4 d. The optimal degradation conditions were temperature 30°C, pH 6.0, inoculum 1%, and initial NSR concentration 20 mg L1), The degradation system was tolerant to heavy metal ions such as Cd2+, Pb2+, Ni2+, and Zn2+ and mainly occurred through the bacterial extracellular enzymes (92.17%). Mechanistically, during the degradation process, reactive oxygen species, oxidative stress, cell membrane permeability, cell surface hydrophobicity, and apoptosis rate first increased and then decreased. Also, the expression of biofilm formation-related genes luxS, waaE, spo0A, and wza varied with time and concentration. NSR wastewater and soil were degraded to 1.92 mg L1 and 2.72 mg L1, respectively. In a simulated wastewater treatment unit (hydraulic retention time 12 h), YM2 degraded 84.55% of NSR after 10 d. This study provides a theoretical basis for the microbial remediation of NSR.

Key words: Sulfonylurea herbicide , Bioremediation,  , Response surface methodology,  , Microbial degradation process