State Key Laboratory of Urban and Regional Ecology, Research Center for Eco-Environmental Sciences, Chinese Academy of Sciences, Beijing 100085, China.
J Environ Sci (China). 2009;21(11):1562-8. doi: 10.1016/s1001-0742(08)62456-0.
The potential of microbial mediated iron plaque reduction, and associated arsenic (As) mobility were examined by iron reducing bacteria enriched from As contaminated paddy soil. To our knowledge, this is the first time to report the impact of microbial iron plaque reduction on As mobility. Iron reduction occurred during the inoculation of iron reducing enrichment culture in the treatments with iron plaque and ferrihydrite as the electron acceptors, respectively. The Fe(II) concentration with the treatment of anthraquinone-2, 6-disulfonic acid (AQDS) and iron reducing bacteria increased much faster than the control. Arsenic released from iron plaque with the iron reduction, and a significant correlation between Fe(II) and total As in culture was observed. However, compared with control, the increasing rate of As was inhibited by iron reducing bacteria especially in the presence of AQDS. In addition, the concentrations of As(III) and As(V) in abiotic treatments were higher than those in the biotic treatments at day 30. These results indicated that both microbial and chemical reductions of iron plaque caused As release from iron plaque to aqueous phase, however, microbial iron reduction induced the formation of more crystalline iron minerals, leading to As sequestration. In addition, the presence of AQDS in solution can accelerate the iron reduction, the As release from iron plaque and subsequently the As retention in the crystalline iron mineral. Thus, our results suggested that it is possible to remediate As contaminated soils by utilizing iron reducing bacteria and AQDS.
本研究通过从砷污染稻田中富集的铁还原细菌,考察了微生物介导的铁结皮还原及其相关砷(As)迁移的潜力。据我们所知,这是首次报道微生物铁结皮还原对 As 迁移的影响。在以铁结皮和水铁矿作为电子受体的处理中,接种铁还原富集培养物时发生了铁还原。用蒽醌-2,6-二磺酸(AQDS)和铁还原细菌处理的 Fe(II)浓度比对照增加得更快。铁还原导致铁结皮中释放出砷,并且在培养物中观察到 Fe(II)和总 As 之间存在显著相关性。然而,与对照相比,铁还原细菌特别是在存在 AQDS 的情况下,抑制了 As 的增加率。此外,在 30 天时,非生物处理中 As(III)和 As(V)的浓度高于生物处理中的浓度。这些结果表明,铁结皮的微生物和化学还原都会导致 As 从铁结皮中释放到水相,但微生物铁还原会导致更多结晶铁矿物的形成,从而导致 As 被固定。此外,溶液中 AQDS 的存在可以加速铁还原、铁结皮中 As 的释放以及随后结晶铁矿物中 As 的滞留。因此,我们的结果表明,利用铁还原细菌和 AQDS 有可能修复砷污染土壤。