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Using electrical signals of microbial fuel cells to detect copper stress on soil microorganisms

机译:利用微生物燃料电池的电信号检测土壤微生物对铜的胁迫

摘要

A method based on microbial fuel cells (MFCs) was used to evaluate the effects of copper (Cu2+) on soil microorganisms. Soil spiked with 50-400mgkg(-1) of Cu2+ as CuCl2 was incubated for 24hours before being packed into the MFC anode chambers and assayed for dehydrogenase activity (DHA), substrate-induced respiration (SIR) and microbial biomass carbon (C-mic). Soil was amended with 5% (w/w) glucose to accelerate start-up' and improve power generation, followed by 150hours of operation. Anode biofilm and soil was extracted to recover total nucleic acids and the 16S rRNA gene was subjected to PCR-DGGE, sequencing and phylogenetic analysis. Results showed that increases in soil Cu2+ concentrations reduced voltage and postponed start-up. The quantity of generated electrons within 48hours was 32.5 coulomb (C) in the without-Cu control and decreased with increasing Cu2+ concentrations (11.7, 7.7, 2.0 and 1.3C under 50, 100, 200 and 400mgkg(-1)Cu(2+), respectively). Cyclic voltammetry identified decreased soil electrochemical activity with increasing Cu2+ concentrations. The results indicate that Cu2+ reduced electrical signals by inhibiting the electrochemical activity, metabolic activity and biomass of microorganisms. The 16S sequences of recovered anodic bacteria were assigned to Firmicutes, including Bacillaceae, Acetobacteraceae, Clostridium, Bacillus and Sporolactobacillus. In general, the DGGE band intensity of anodic bacteria decreased with increasing Cu2+ concentrations, except for bands assigned to Firmicutes and Bacillus, which increased with increasing Cu2+ concentrations. We suggest that the short-term electrical signals generated from MFCs with contaminated soil can be used to assess the toxic effect of heavy metal pollutants on soil microorganisms.
机译:一种基于微生物燃料电池(MFCs)的方法用于评估铜(Cu2 +)对土壤微生物的影响。将装满50-400mgkg(-1)的CuCl2的土壤温育24小时,然后装入MFC阳极室,并测定其脱氢酶活性(DHA),底物诱导的呼吸作用(SIR)和微生物生物量碳(C-mic )。用5%(w / w)的葡萄糖修正土壤以加速启动并改善发电,然后运行150小时。提取阳极生物膜和土壤以回收总核酸,并对16S rRNA基因进行PCR-DGGE,测序和系统发育分析。结果表明,土壤Cu2 +浓度的增加会降低电压并推迟启动。在无铜控制下,48小时内产生的电子数量为32.5库仑(C),并且随着Cu2 +浓度的增加(在50、100、200和400mgkg(-1)Cu(2+)下分别为11.7、7.7、2.0和1.3C减少) ), 分别)。循环伏安法确定了土壤电化学活性随Cu2 +浓度的增加而降低。结果表明,Cu2 +通过抑制微生物的电化学活性,代谢活性和生物量来降低电信号。回收到的阳极细菌的16S序列被分配到Firmicutes,包括芽孢杆菌科,醋杆菌科,梭菌,芽孢杆菌和芽孢杆菌。通常,阳极细菌的DGGE谱带强度随Cu2 +浓度的增加而降低,除了分配给Firmicutes和Bacillus的谱带,其随Cu2 +浓度的增加而增加。我们建议,由污染土壤的多氯联苯产生的短期电信号可用于评估重金属污染物对土壤微生物的毒性作用。

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