硝化假单胞菌在辛基酚聚氧乙烯醚上生长的底物抑制模型

Abdusssamad Abubakar, H. Yakasai, G. Uba, Ibrahim Sabo
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摘要

辛基酚聚氧乙烯醚(OPE)是一类非离子表面活性剂,广泛应用于各种工业领域。然而,由于 OPE 的广泛使用和在水生环境中的持久性,人们开始关注其对环境和人类健康的潜在影响。利用 OPE 降解细菌对环境中的 OPE 进行生物修复很有吸引力,因为细菌的新陈代谢可将 OPE 转化为无害的二氧化碳和水作为副产品。在这项研究中,采用了 Luong、Yano、Teissier-Edward、Aiba、Haldane、Monod、Han 和 Levenspiel 等各种次生生长模型来模拟高浓度 OPE 对硝化细菌 TX1 在 OPE 上生长速度的抑制作用。经过均方根误差 (RMSE)、调整决定系数 (adjR2)、偏差因子 (BF) 和准确因子 (AF) 等全面的统计分析,Teissier 模型成为最佳选择。除了 Moser、Monod 和 Hinshelwood 模型的曲线拟合效果最差外,其他所有研究模型都显示出良好的拟合效果。Teissier 模型的 RMSE 值、AICc 值和修正的 adjR2 值都很低,因此成为最合适的模型。此外,该模型的 AF 值和 BF 值也接近统一(表 2)。实验数据表明,OPE 具有毒性,浓度越高,生长速度越慢。最大 OPE 比生长率(max)、半饱和浓度(KS)和半抑制浓度(Ki)分别为 0.613 h-1 (95% 置信区间为 0.519 至 0.707)、2352.8 mg/L(95% 置信区间为 1668.8 至 3036.8)和 52,456.7 mg/L(95% 置信区间为 38395.0 至 66518.5)。建模时发现的这些新常数有可能成为未来建模工作的有用输入。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Substrate Inhibition Modelling of Pseudomonas nitroreducens Growth on Octylphenol Polyethoxylates
Octylphenol polyethoxylates (OPEs) constitute a class of non-ionic surfactants extensively employed in various industrial applications. However, concerns have arisen regarding the potential environmental and human health impacts of OPEs because of their widespread use and persistence in aquatic environments. Bioremediation of OPE in the environment using OPE-degrading bacterium is appealing as bacterial metabolism converts OPE to harmless carbon dioxide and water as byproducts. In this study, various secondary growth models such as Luong, Yano, Teissier-Edward, Aiba, Haldane, Monod, Han, and Levenspiel were employed to model the inhibitory effect of high OPE concentrations to the growth rate of Pseudomonas nitroreducens TX1 the bacterium on OPE. Following thorough statistical analyses such as root-mean-square error (RMSE), adjusted coefficient of determination (adjR2), bias factor (BF), and accuracy factor (AF), the Teissier model emerged as the most optimal choice. All of the studied models showed good fittings except Moser, Monod and Hinshelwood which showed the poorest curve fitting. The Teissier model emerged as the most suitable model, as indicated by its remarkably low values for RMSE, AICc, and modified adjR2. Furthermore, the model's AF and BF values were close to unity (Table 2). The experimental data obtained indicates that OPE is toxic and slows down the rate of growth at higher concentrations. The maximum OPE specific growth rate (max), half-saturation concentration (KS), half inhibition concentration (Ki) was 0.613 h-1 (95% Confidence Interval or C.I. from 0.519 to 0.707), 2352.8 mg/L (95% C.I. from 1668.8 to 3036.8) and 52,456.7 mg/L (95% C.I. from 38395.0 to 66518.5), respectively. It is possible that these new constants found when modeling could be useful inputs for future modeling efforts.
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