文章摘要
韩悦,孙丽娜,吕良禾,王辉,苑春莉,王晓旭,吴昊.鼠李糖脂-纳米零价铁-丙酮酸钠强化微生物厌氧-好氧降解土壤DDTs效果研究[J].农业环境科学学报,2023,42(4):799-810.
鼠李糖脂-纳米零价铁-丙酮酸钠强化微生物厌氧-好氧降解土壤DDTs效果研究
Anaerobic-aerobic bioremediation of DDT-contaminated soil and the compound strengthening of rhamnolipid-nano zero-valent iron-sodium pyruvate
投稿时间:2022-08-03  
DOI:10.11654/jaes.2022-0786
中文关键词: DDTs  鼠李糖脂  纳米零价铁  丙酮酸钠  微生物修复
英文关键词: DDT  rhamnolipid  nano zero-valent iron  sodium pyruvate  microbial remediation
基金项目:国家重点基础研究发展计划项目(973计划)(2014CB441106)
作者单位E-mail
韩悦 沈阳大学区域污染环境生态修复教育部重点实验室, 沈阳 110044  
孙丽娜 沈阳大学区域污染环境生态修复教育部重点实验室, 沈阳 110044 sln629@163.com 
吕良禾 沈阳大学区域污染环境生态修复教育部重点实验室, 沈阳 110044  
王辉 沈阳大学区域污染环境生态修复教育部重点实验室, 沈阳 110044  
苑春莉 沈阳大学区域污染环境生态修复教育部重点实验室, 沈阳 110044  
王晓旭 沈阳大学区域污染环境生态修复教育部重点实验室, 沈阳 110044  
吴昊 沈阳大学区域污染环境生态修复教育部重点实验室, 沈阳 110044  
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中文摘要:
      为了改善目前土壤DDTs污染微生物修复效率相对较低的现状,以沈阳市沈北新区某设施农业大棚土壤为研究对象,通过批实验研究了鼠李糖脂(RL)、纳米零价铁(nZVI)和丙酮酸钠(C)强化微生物顺序厌氧-好氧处理对土壤DDTs及其组分降解率的影响。结果表明:RL、nZVI和C强化微生物顺序厌氧-好氧处理可显著提高土壤DDTs和p,p'-DDT的降解率(P<0.05),不同强化处理土壤DDTs和p,p'-DDT降解率依次为RL+nZVI+C联合处理>nZVI处理>RL处理>C处理>CK处理;RL、nZVI和C联合强化微生物厌氧-好氧顺序处理90 d时,土壤DDTs、p,p'-DDT和p,p'-DDE降解率分别为43.05%~68.81%、12.06%~96.90%和3.33%~60.87%。其中,0.05 mg·kg-1RL、0.50% nZVI以及0.30 mmol·kg-1C联合强化厌氧-好氧处理土壤DDTs、p,p'-DDT和p,p'-DDE降解率分别为68.81%、96.90%和60.87%,厌氧与好氧降解比分别为3.97、6.70和5.00。研究表明,RL、nZVI与C联合强化微生物顺序厌氧脱氯与好氧放大处理,促进了土壤DDTs高效降解,同时避免了难降解、毒性更大的p,p'-DDE的产生与积累,展示了RL、nZVI与C联合强化微生物顺序厌氧-好氧降解在修复DDTs污染土壤方面的应用潜力。
英文摘要:
      Current dichlorodiphenyltrichloroethane(DDT)-contaminated soil microbial remediation efficiency is relatively low. This study used an agricultural greenhouse soil facility in Shenbei New District of Shenyang as the research object of a batch experiment to study the enhancement of rhamnolipid(RL), nano zero-valent iron(nZVI), and sodium pyruvate(C)on microbial sequential anaerobic-aerobic treatment for the degradation of DDT and its components. The results showed that the improved sequential anaerobic-aerobic treatments with RL, nZVI, and C significantly increased the degradation rates of DDT and p, p ' -DDT in soil(P<0.05). The results also revealed that the degradation rates of DDT and p, p' -DDT in different enhanced treatments were in the order of RL+nZVI+C combined treatment > nZVI treatment > RL treatment > C treatment > CK treatment. After 90 days of RL, nZVI, and C combined with enhanced microbial anaerobic-aerobic sequential treatment, the degradation rates of DDT, p, p ' - DDT, and p, p' - DDE were 43.05% – 68.81%, 12.06% – 96.90%, and 3.33%–60.87%, respectively. Among these, the degradation rates of DDT, p, p ' -DDT, and p, p' -DDE under the combined enhanced anaerobic-aerobic treatment with 0.05 mg · kg-1 RL, 0.50% nZVI, and 0.30 mmol · kg-1 C were 68.81%, 96.90%, and 60.87% respectively; the ratios of anaerobic to aerobic degradation were 3.97, 6.70, and 5.00, respectively. This study shows that a combination of RL, nZVI, and C enhances microbial sequential treatment of anaerobic dechlorination and aerobic amplification, which promotes the efficient degradation of DDT in soil, and avoided the production and accumulation of p, p ' -DDE, which is difficult to degrade and more toxic. This study also demonstrates the potential of combined RL, nZVI, and C to enhance microbial sequential anaerobic-aerobic degradation in the remediation of DDT-contaminated soil.
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