Department of Plant and Soil Sciences, Delaware Environmental Institute, University of Delaware , Newark, Delaware 19711, United States.
Environmental Molecular Sciences Laboratory, Pacific Northwest National Laboratory , Richland, Washington 99354, United States.
Environ Sci Technol. 2015 Sep 15;49(18):10927-36. doi: 10.1021/acs.est.5b02448. Epub 2015 Aug 26.
Aqueous Fe(II) is known to catalyze the abiotic transformation of ferrihydrite to more stable Fe minerals. However, little is known about the impacts of coprecipitated OM on Fe(II)-catalyzed ferrihydrite transformation and its consequences for C dynamics. Accordingly, we investigated the extent and pathway of Fe(II)-induced transformation of OM-ferrihydrite coprecipitates as a function of C/Fe ratios and aqueous Fe(II) concentrations, and its implications for subsequent C dynamics. The coprecipitated OM resulted in a linear decrease in ferrihydrite transformation with increasing C/Fe ratios. The secondary mineral profiles upon Fe(II) reaction with OM-ferrihydrite coprecipitates depend on Fe(II) concentrations At 0.2 mM Fe(II), OM completely inhibited goethite formation and stimulated lepidocrocite formation. At 2 mM Fe(II), whereas goethite was formed in the presence of OM, OM reduced the amount of goethite and magnetite formation and increased the formation of lepidocrocite. The solid-phase C content remained unchanged after reaction, suggesting that OM remains associated with Fe minerals following ferrihydrite transformation to more stable Fe minerals. However, C desorbability by H2PO4(-) from the resulting Fe minerals following reaction was enhanced. The study indicates a "lepidocrocite favoring effect" by OM and suggests that Fe(II)-catalyzed transformation of ferrihydrite may decrease OM stability in natural environments under moderately reducing conditions.
已知水合亚铁离子能够催化无定形水铁矿向更稳定的铁矿物转化。然而,对于共沉淀有机质对铁(II)催化水铁矿转化的影响及其对碳动态的影响,人们知之甚少。因此,我们研究了在 C/Fe 比和水溶液中 Fe(II)浓度的影响下,Fe(II)诱导的有机质-水铁矿共沉淀转化的程度和途径,以及其对随后的碳动态的影响。共沉淀的有机质导致水铁矿转化随 C/Fe 比的增加而呈线性下降。在与有机质-水铁矿共沉淀反应后,次生矿物的分布取决于 Fe(II)浓度。在 0.2mMFe(II)的条件下,有机质完全抑制了针铁矿的形成,并刺激了纤铁矿的形成。在 2mMFe(II)的条件下,虽然在有机质存在的情况下形成了针铁矿,但有机质减少了针铁矿和磁铁矿的形成,增加了纤铁矿的形成。反应后固相 C 含量保持不变,这表明有机质在水铁矿向更稳定的铁矿物转化后仍与铁矿物结合。然而,反应后从生成的铁矿物中用 H2PO4-解吸的 C 的可解吸性增强。该研究表明,有机质具有“纤铁矿促进效应”,并表明在中等还原条件下,铁(II)催化的水铁矿转化可能会降低自然环境中有机质的稳定性。