三丁基锡对枯草芽孢杆菌生长毒性的动力学模拟

Abdussamad Abubakar
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引用次数: 0

摘要

细菌的生长。2003年,由于该物质对环境的负面影响,海洋环境保护委员会(MEPC)提议在国际上禁止TBT。但是,虽然bt被禁止使用,但在海水、海底沉积物、生物群落中仍有可能发现大量的bt。为了防止污垢生物附着在船舶表面,三丁基锡(TBT)作为船舶涂料的防污剂已被广泛应用多年。三丁基锡已被发现具有很强的持久性,特别是在沉积物中,并且对除目标物种以外的物种极其有害。三丁基锡(TBT)对枯草芽孢杆菌的生长有强烈的抑制作用。随着TBT浓度的增加,总比生长率受到抑制。然后根据修正的Han-Levenspiel, Amor, Wang, Liu, Shukor和修正的Andrews对得到的生长速率进行建模。在5个模型中,Andrew和Amor模型的装配效果较差。统计分析结果表明,在RMSE和AICc最小、调整后相关系数AdR2最高、AF和BF最接近统一的情况下,Shukor模型是最佳模型。Shukor模型得到的参数为Ccrit 742.32 nM (95%, ci值,303.35 ~ 1181.29),μmax 1.20 h-1 (95% ci值,1.08 ~ 1.319)和m 0.507 (95% ci值,0.308 ~ 0.832)。本研究结果可用于进一步的生物修复工作。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Kinetics Modelling of Tributyltin Toxicity on The Growth of Bacillus subtilis
growth of bacteria. In 2003, the Marine Environmental Protection Committee (MEPC) proposed that TBT be banned internationally due to the negative environmental impacts of the substance. However, even though BTs are banned, they may be found in large quantities in seawater, bottom sediments, and the biota, all of which are contaminated with them. To prevent the adhesion of fouling organisms to the surface of ships and boats, tributyltin (TBT) has been widely employed as an antifouling agent in marine paints for many years. Tributyltin has been discovered to be very persistent, particularly in sediment, and to be extremely harmful to species other than those targeted. Bacillus subtilis growth was intensely inhibited by tributyltin (TBT). As the TBT concentration increases, the overall specific growth rate was inhibited. The growth rates obtained were then modelled according to the modified Han-Levenspiel, Amor, Wang, Liu, Shukor and modified Andrews. Among the five models, the Andrew and Amor models show poor fittings. Results of the statistical analysis showed that the Shukor model was the best model based on the lowest values for RMSE and AICc, highest adjusted correlation coefficient (AdR2) and values of AF and BF closest to unity. The parameters obtained from the Shukor model were Ccrit 742.32 nM (95%, C.I., 303.35 to 1181.29), μmax 1.20 h-1 (95% C.I., 1.08 to 1.319) and m 0.507 (95% C.I., 0.308 to 0.832). The findings of this study can be utilized for further bioremediation works.
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