Geomicrobiology, Center for Applied Geosciences, University of Tuebingen , Sigwartstrasse 10, D-72076 Tuebingen, Germany.
Environ Sci Technol. 2013 Aug 6;47(15):8297-307. doi: 10.1021/es400801z. Epub 2013 Jul 11.
Fe(III) (oxyhydr)oxide minerals exhibit a high sorption affinity for arsenic (As) and the reductive dissolution of As-bearing Fe(III) (oxyhydr)oxides is considered to be the primary mechanism for As release into groundwater. To date, research has focused on the reactivity of abiogenic Fe(III) (oxyhydr)oxides, yet in nature biogenic Fe(III) (oxyhydr)oxides, precipitated by Fe(II)-oxidizing bacteria are also present. These biominerals contain cell-derived organic matter (CDOM), leading to different properties than their abiogenic counterparts. Here, we follow Fe mineralogy and As mobility during the reduction of As-loaded biogenic and abiogenic Fe(III) minerals by Shewanella oneidensis MR-1. We found that microbial reduction of As(III)-bearing biogenic Fe(III) (oxyhydr)oxides released more As than reduction of abiogenic Fe(III) (oxyhydr)oxides. In contrast, As was immobilized more effectively during reduction of As(V)-loaded biogenic than abiogenic Fe(III) (oxyhydr)oxides during secondary Fe mineral formation. During sterile incubation of minerals and after microbial Fe(III) reduction stopped, As(V) was mobilized from biogenic Fe(III) (oxyhydr)oxides probably by sorption competition with phosphate and CDOM. Our data show that the presence of CDOM significantly influences As mobility during reduction of Fe(III) minerals and we suggest that it is essential to consider both biogenic and abiogenic Fe(III) (oxyhydr)oxides to further understand the environmental fate of As.
三价铁(氢)氧化物矿物对砷(As)具有高吸附亲和力,含砷的三价铁(氢)氧化物的还原溶解被认为是 As 释放到地下水中的主要机制。迄今为止,研究主要集中在非生物成因的三价铁(氢)氧化物的反应性上,但在自然界中,由 Fe(II)氧化细菌沉淀的生物成因的三价铁(氢)氧化物也存在。这些生物矿物含有细胞衍生的有机物(CDOM),导致其性质与非生物成因的三价铁(氢)氧化物不同。在这里,我们通过 Shewanella oneidensis MR-1 研究了负载 As 的生物成因和非生物成因三价铁矿物还原过程中的 Fe 矿物学和 As 迁移。我们发现,与还原非生物成因的三价铁(氢)氧化物相比,微生物还原含 As(III)的生物成因的三价铁(氢)氧化物释放出更多的 As。相比之下,在二次 Fe 矿物形成过程中,还原负载 As(V)的生物成因的三价铁(氢)氧化物比非生物成因的三价铁(氢)氧化物更有效地固定 As。在无菌孵育矿物和微生物还原停止后,可能通过与磷酸盐和 CDOM 的吸附竞争,As(V)从生物成因的三价铁(氢)氧化物中被迁移出来。我们的数据表明,CDOM 的存在显著影响了还原过程中 Fe 矿物中 As 的迁移,我们建议考虑生物成因和非生物成因的三价铁(氢)氧化物对于进一步了解 As 的环境归宿至关重要。