4.8 Article

Toward Improved Bioremediation Strategies: Response of BAM-Degradation Activity to Concentration and Flow Changes in an Inoculated Bench-Scale Sediment Tank

期刊

ENVIRONMENTAL SCIENCE & TECHNOLOGY
卷 56, 期 7, 页码 4050-4061

出版社

AMER CHEMICAL SOC
DOI: 10.1021/acs.est.1c05259

关键词

2,6-dichlorobenzamide (BAM); bioavailability; compound-specific isotope analysis (CSIA); mass-transfer; priming effect

资金

  1. ERC - European Research Council [616861]
  2. European Research Council (ERC) [616861] Funding Source: European Research Council (ERC)

向作者/读者索取更多资源

Compound-specific isotope analysis can be used to monitor the adaptive response of bacterial degradation to low contaminant concentrations and reveal mass-transfer limitations. This study improved biodegradation performance and capacity through priming and flow fluctuations. However, mass transfer limitations increased over time under stimulated conditions, and bacterial adaptation at low BAM levels further decreased activity. Isotope ratios, combined with residual substrate concentrations, helped identify underlying limitations of biodegradation in this stimulated system.
Compound-specific isotope analysis (CSIA) can reveal mass-transfer limitations during biodegradation of organic pollutants by enabling the detection of masked isotope fractionation. Here, we applied CSIA to monitor the adaptive response of bacterial degradation in inoculated sediment to low contaminant concentrations over time. We characterized Aminobacter sp. MSH1 activity in a flow-through sediment tank in response to a transient supply of elevated 2,6-dichlorobenzamide (BAM) concentrations as a priming strategy and took advantage of an inadvertent intermittence to investigate the effect of short-term flow fluctuations. Priming and flow fluctuations yielded improved biodegradation performance and increased biodegradation capacity, as evaluated from bacterial activity and residual concentration time series. However, changes in isotope ratios in space and over time evidenced that mass transfer became increasingly limiting for degradation of BAM at low concentrations under such stimulated conditions, and that activity decreased further due to bacterial adaptation at low BAM (mu g/L) levels. Isotope ratios, in conjunction with residual substrate concentrations, therefore helped identifying underlying limitations of biodegradation in such a stimulated system, offering important insight for future optimization of remediation schemes.

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