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环境中一株节杆菌依赖碳的铬酸盐毒性机制。

Carbon-dependent chromate toxicity mechanism in an environmental Arthrobacter isolate.

机构信息

Department of Biology, East Carolina University, Greenville, NC, 27858, United States; Center for Biofilm Engineering, Montana State University, Bozeman, MT, 59717, United States.

Center for Biofilm Engineering, Montana State University, Bozeman, MT, 59717, United States; Department of Chemical and Biological Engineering, Montana State University, Bozeman, MT, 59717, United States.

出版信息

J Hazard Mater. 2018 Aug 5;355:162-169. doi: 10.1016/j.jhazmat.2018.05.020. Epub 2018 May 12.

Abstract

Arthrobacter spp. are widespread in soil systems and well-known for their Cr(VI) reduction capabilities making them attractive candidates for in situ bioremediation efforts. Cellulose drives carbon flow in soil systems; yet, most laboratory studies evaluate Arthrobacter-Cr(VI) interactions solely with nutrient-rich media or glucose. This study aims to determine how various cellulose degradation products and biostimulation substrates influence Cr(VI) toxicity, reduction, and microbial growth of an environmental Arthrobacter sp. isolate. Laboratory culture-based studies suggest there is a carbon-dependent Cr(VI) toxicity mechanism that affects subsequent Cr(VI) reduction by strain LLW01. Strain LLW01 could only grow in the presence of, and reduce, 50 μM Cr(VI) when glucose or lactate were provided. Compared to lactate, Cr(VI) was at least 30-fold and 10-fold more toxic when ethanol or butyrate was the sole carbon source, respectively. The addition of sulfate mitigated toxicity somewhat, but had no effect on the extent of Cr(VI) reduction. Cell viability studies indicated that a small fraction of cells were viable after 8 days suggesting cell growth and subsequent Cr(VI) reduction may resume. These results suggest when designing bioremediation strategies with Arthrobacter spp. such as strain LLW01, carbon sources such as glucose and lactate should be considered over ethanol and butyrate.

摘要

节杆菌属广泛存在于土壤系统中,以其还原六价铬(Cr(VI))的能力而闻名,使其成为原位生物修复的有吸引力的候选者。纤维素驱动土壤系统中的碳流动;然而,大多数实验室研究仅用营养丰富的培养基或葡萄糖来评估节杆菌属-六价铬的相互作用。本研究旨在确定各种纤维素降解产物和生物刺激底物如何影响环境节杆菌属分离株的 Cr(VI)毒性、还原和微生物生长。基于实验室培养的研究表明,存在一种依赖碳的 Cr(VI)毒性机制,影响菌株 LLW01 随后对 Cr(VI)的还原。只有在提供葡萄糖或乳酸盐的情况下,菌株 LLW01 才能生长并还原 50 μM 的 Cr(VI)。与乳酸盐相比,当乙醇或丁酸盐是唯一的碳源时,Cr(VI)的毒性分别至少高出 30 倍和 10 倍。添加硫酸盐在一定程度上减轻了毒性,但对 Cr(VI)还原的程度没有影响。细胞活力研究表明,在 8 天后,一小部分细胞仍然存活,这表明细胞生长和随后的 Cr(VI)还原可能会重新开始。这些结果表明,在设计具有节杆菌属(如 LLW01 菌株)的生物修复策略时,应考虑葡萄糖和乳酸盐等碳源,而不是乙醇和丁酸盐。

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