4.6 Article

Microbial reduction of dinitrotoluene sulfonates in TNT red water-contaminated soil

期刊

JOURNAL OF SOILS AND SEDIMENTS
卷 21, 期 2, 页码 914-924

出版社

SPRINGER HEIDELBERG
DOI: 10.1007/s11368-020-02795-w

关键词

Biodegradation; TNT red water-contaminated soil; Dinitrotoluene sulfonates; Bacterial community structure

资金

  1. Scientific Research Fund Project of Nanjing Institute of Technology [YKJ2019101]
  2. National Basic Product Innovation Research Project [15]
  3. Beijing Municipal Science and Technology Project [Z151100000915065]
  4. University Natural Science Research Project of Jiangsu Province [18KJB61006]

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The study demonstrated that microbial consortium showed great DNTS-degrading ability in soil. High temperature and humidity conditions were favorable for the degradation of DNTS. High-throughput sequencing (HTS) technology accurately identified the changes in microbial communities in soil.
Purpose Large quantities of TNT red water which contained mainly dinitrotoluene sulfonates (DNTS) were produced during the production of TNT, threatening the surrounding environments. In china, about 1.5 x 10(5) m(3)soil was contaminated by TNT red water. So, it is extremely important to remediate the DNTS-contaminated sites. Materials and methods Batch biodegradation tests were conducted to investigate the influence of environmental factors (microorganism dosage, initial DNTS concentration, water/soil ratio, and temperature) on the microbial reduction of DNTS in soil. The biodegradation intermediate metabolites of 2,4-dinitrotoluene-3-sulfonate (2,4-DNT-3-SO3-) and 2,4-dinitrotoluene-5-sulfonate (2,4-DNT-5-SO3-) during the remediation process were determined. Three kinetic models were used to study the biodegradation kinetics of DNTS in soil. Finally, high-throughput sequencing (HTS) technology was applied to identify the microbial communities in soil samples during the bioremediation process. Results and discussion Batch experiments showed that at initial concentration of 500 mg kg(-1), 2,4-DNT-3-SO(3)(-)and 2,4-DNT-5-SO(3)(-)removal efficiencies reached 100% after 25 and 13 days under the following conditions: water/soil ratio of 2:5, microorganism dosage (w/w) of 1%, and temperature of 35 degrees C. The microbial consortium metabolized 2,4-DNT-3-SO(3)(-)and 2,4-DNT-5-SO(3)(-)via reductive pathways. The biodegradation processes fitted well with zero-order reaction kinetics at different initial DNTS concentrations. HTS results showed that the bacterial communities were greatly influenced by the DNTS addition. The dominant genus in 2,4-DNT-3-SO3--contaminated soil wereBacillus,Pseudomonas,Simiduia,Salegentibacter, andMethylohalomonaswhile that in 2,4-DNT-3-SO3--contaminated soil wereBacillus,Pseudomonas,Simiduia,Methylohalomonas,Salegentibacter,Pontibacter, andActinotalea. Conclusions Microbial consortium showed great DNTS-degrading ability.Bacillus,Pseudomonas, andSimiduiaplayed a major role in biodegradation of 2,4-DNT-3-SO(3)(-)and 2,4-DNT-5-SO(3)(-)in soil. The microbial consortium tolerated high levels of DNTS found in the soil and degraded the contaminants into more biodegradable forms. The biotreatment technology is effective and has a potential to be use in remediation of TNT red water-contaminated sites.

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