Climate & Energy College, School of Geography, Earth and Atmospheric Sciences, The University of Melbourne, Melbourne, VIC 3010, Australia; State Key Laboratory of Eco-hydraulics in Northwest Arid Region, Xi'an University of Technology, Xi'an, 710048, China; State Environmental Protection Key Laboratory of Integrated Surface Water-Groundwater Pollution Control, School of Environmental Science and Engineering, Southern University of Science and Technology, Shenzhen, 518055, China.
State Key Laboratory of Eco-hydraulics in Northwest Arid Region, Xi'an University of Technology, Xi'an, 710048, China.
Environ Pollut. 2022 Dec 1;314:120221. doi: 10.1016/j.envpol.2022.120221. Epub 2022 Sep 19.
The response of microorganisms to heavy metal-dissolved organic matter (Me-DOM) complexation is critical for the microbial-mediated coupled biogeochemical cycling of metals and DOM. This study investigated the impact of typical metals [As, Cd, Co, Cr, Cu, Fe, Mn, Ni, Pb, and Zn (at an environmentally-relevant concentration of 200 ppb)], model DOM substrates [humic acids (HA) and bovine serum albumin (BSA)], and their complexation on riverine microbial DOM metabolisms. DOM biodegradability decreased after the metal complexation (especially Co, Cr, and Mn for HA and Ni for BSA). While microbial transformation of humics and proteins was observed, components with lower aromaticity and hydrophobicity were accumulated during the cultivation. The substrate difference and metal speciation changed community compositions and resulted in distinctive community member networks, which accounted for the varied metabolic DOM patterns. The correlations indicated that rather than metal uptakes, Me-DOM complexation and community shifts controlled microbial DOM metabolisms. Microbial BSA metabolisms were less correlated to the key genera identified by network analysis or community diversity. Instead, they were sensitive to metal speciation, which may be attributed to the complicated utilization and production of proteins and their essential roles in detoxification. The constructed correlations among metals (Me-DOM complexes), DOM metabolisms, and community shifts provide strong implications for the biogeochemical function of Me-DOM complexes and highlight the effect of metal speciation on microbial protein metabolisms even at trace concentrations.
微生物对重金属-溶解有机质(Me-DOM)络合物的响应对于金属和 DOM 的微生物介导的耦合生物地球化学循环至关重要。本研究调查了典型金属 [As、Cd、Co、Cr、Cu、Fe、Mn、Ni、Pb 和 Zn(在 200 ppb 的环境相关浓度下)]、模型 DOM 底物 [腐殖酸 (HA) 和牛血清白蛋白 (BSA)] 及其络合对河流微生物 DOM 代谢的影响。金属络合后 DOM 的生物降解性降低(尤其是 HA 中的 Co、Cr 和 Mn 以及 BSA 中的 Ni)。虽然观察到腐殖质和蛋白质的微生物转化,但在培养过程中积累了芳香度和疏水性较低的成分。底物差异和金属形态改变了群落组成,并导致独特的群落成员网络,这解释了不同的代谢 DOM 模式。相关性表明,控制微生物 DOM 代谢的是 Me-DOM 络合和群落变化,而不是金属摄取。微生物 BSA 代谢与网络分析或群落多样性确定的关键属的相关性较低。相反,它们对金属形态敏感,这可能归因于蛋白质的复杂利用和生产及其在解毒中的重要作用。金属(Me-DOM 络合物)、DOM 代谢和群落变化之间的相关性为 Me-DOM 络合物的生物地球化学功能提供了强有力的启示,并强调了即使在痕量浓度下金属形态对微生物蛋白质代谢的影响。