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生物修复三丁基锡污染沉积物:降解增强和生物可利用性改善以促进处理过程。

Bioremediation of tributyltin contaminated sediment: degradation enhancement and improvement of bioavailability to promote treatment processes.

机构信息

David Livingstone Centre for Sustainability, Department of Civil Engineering, University of Strathclyde, Glasgow, Scotland G1 1QE, UK.

出版信息

Chemosphere. 2011 Apr;83(5):680-6. doi: 10.1016/j.chemosphere.2011.02.024.

Abstract

Bioremediation of tributyltin (TBT) contaminated sediment was studied and degradation enhancement and improvement of bioavailability were also investigated. In TBT spiked sediment, the half-life of TBT in the control sample, representing natural attenuation, was 578 d indicating its persistence. In the stimulated sample (pH 7.5, aeration and incubated at 28°C), the half-life was significantly reduced to 11 d. Further stimulation by nutrient addition (succinate, glycerol and l-arginine) or inoculation with Enterobacter cloacae (∼10(7) viable cells g(-1) of sediment) resulted in half-life reduction to 9 and 10d, respectively. In non-spiked sediment, the indigenous microorganisms were able to degrade aged TBT, but the extended period of contamination decreased the degradation efficiency. To improve bioavailability, addition of surfactant, adjustment of salinity and sonication were studied. The highest percentage solubilisation of TBT in water was obtained by adjusting salinity to 20 psu, which increased the solubility of TBT from 13% to 33%. Half-lives after bioavailability was improved were 5, 4 and 4d for stimulation, stimulation w/nutrient addition and stimulation w/inoculation, respectively. However, natural attenuation in the control sample was not enhanced. The results show that providing suitable conditions is important in enhancing TBT biodegradation, and bioavailability improvement additionally increased the rate and degraded amount of TBT. Unfortunately, nutrient addition and inoculation of the degrader did not enhance the degradation appreciably.

摘要

研究了三丁基锡(TBT)污染沉积物的生物修复,并考察了降解增强和生物有效性的改善。在 TBT 污染的沉积物中,自然衰减条件下 TBT 的半衰期在对照样品中为 578 d,表明其持久性。在刺激样品(pH 7.5、曝气并在 28°C 下孵育)中,半衰期显著缩短至 11 d。进一步通过添加营养物(琥珀酸盐、甘油和 l-精氨酸)或接种阴沟肠杆菌(∼10(7)活细胞 g(-1)的沉积物)进行刺激,半衰期分别缩短至 9 和 10 d。在未污染的沉积物中,土著微生物能够降解老化的 TBT,但延长的污染期会降低降解效率。为了提高生物有效性,研究了添加表面活性剂、调整盐度和超声处理。通过将盐度调整至 20 psu,可获得 TBT 在水中的最高溶解百分比,将 TBT 的溶解度从 13%提高到 33%。生物有效性提高后的半衰期分别为 5、4 和 4 d,分别对应于刺激、刺激加营养物添加和刺激加接种。然而,对照样品中的自然衰减并未增强。结果表明,提供合适的条件对于增强 TBT 的生物降解非常重要,而生物有效性的提高进一步增加了 TBT 的降解速率和降解量。不幸的是,营养物添加和降解菌的接种并没有显著增强降解作用。

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