School of Marine Science and Policy, University of Delaware, Newark, Delaware 19716, United States.
Department of Earth Sciences, University of Delaware, Newark, Delaware 19716, United States.
Environ Sci Technol. 2021 Jul 6;55(13):9362-9371. doi: 10.1021/acs.est.1c00497. Epub 2021 Jun 10.
Organic ligands are widely distributed and can affect microbially driven Fe biogeochemical cycles, but effects on microbial iron oxidation have not been well quantified. Our work used a model microaerophilic Fe(II)-oxidizing bacterium ES-1 to quantify biotic Fe(II) oxidation rates in the presence of organic ligands at 0.02 atm O and pH 6.0. We used two common Fe chelators with different binding strengths: citrate (log = 3.20) and nitrilotriacetic acid (NTA) (log = 8.09) and two standard humic substances, Pahokee peat humic acid (PPHA) and Suwannee River fulvic acid (SRFA). Our results provide rate constants for biotic and abiotic Fe(II) oxidation over different ligand concentrations and furthermore demonstrate that various models and natural iron-binding ligands each have distinct effects on abiotic versus biotic Fe(II) oxidation rates. We show that NTA accelerates abiotic oxidation and citrate has negligible effects, making it a better laboratory chelator. The humic substances only affect biotic Fe(II) oxidation, via a combination of chelation and electron transfer. PPHA accelerates biotic Fe(II) oxidation, while SRFA decelerates or accelerates the rate depending on concentration. The specific nature of organic-Fe microbe interactions may play key roles in environmental Fe(II) oxidation, which have cascading influences on cycling of nutrients and contaminants that associate with Fe oxide minerals.
有机配体广泛分布,能够影响微生物驱动的铁地球化学循环,但它们对微生物铁氧化的影响尚未得到很好的量化。我们的工作使用了一种模式微好氧铁(II)氧化细菌 ES-1,在 0.02 大气压 O 和 pH 值 6.0 的条件下,量化了有机配体存在时的生物铁(II)氧化速率。我们使用了两种具有不同结合强度的常见铁螯合剂:柠檬酸盐(log = 3.20)和氮川三乙酸(NTA)(log = 8.09),以及两种标准的腐殖质,帕霍基泥炭腐殖酸(PPHA)和苏万尼河富里酸(SRFA)。我们的结果提供了不同配体浓度下生物和非生物铁(II)氧化的速率常数,并且进一步表明,各种模型和天然铁结合配体对非生物和生物铁(II)氧化速率都有不同的影响。我们表明,NTA 加速了非生物氧化,而柠檬酸几乎没有影响,因此它是一种更好的实验室螯合剂。腐殖质仅通过螯合和电子转移的组合影响生物铁(II)氧化。PPHA 加速了生物铁(II)氧化,而 SRFA 则根据浓度加速或减缓了氧化速率。有机-铁微生物相互作用的特定性质可能在环境铁(II)氧化中起关键作用,这对与铁氧化物矿物相关的营养物质和污染物的循环产生级联影响。