Hydrosciences Montpellier, UMR 5569 CNRS-IRD-UM, CC57, 163 rue Auguste Broussonet, 34090, Montpellier, France.
Institut de Minéralogie, de Physique des Matériaux et de Cosmochimie (IMPMC), UMR 7590 CNRS-UPMC-IRD-MNHN, 4 place Jussieu, 75252, Paris cedex 05, France.
Water Res. 2017 Oct 15;123:594-606. doi: 10.1016/j.watres.2017.06.059. Epub 2017 Jun 22.
Passive water treatments based on biological attenuation can be effective for arsenic-rich acid mine drainage (AMD). However, the key factors driving the biological processes involved in this attenuation are not well-known. Here, the efficiency of arsenic (As) removal was investigated in a bench-scale continuous flow channel bioreactor treating As-rich AMD (∼30-40 mg L). In this bioreactor, As removal proceeds via the formation of biogenic precipitates consisting of iron- and arsenic-rich mineral phases encrusting a microbial biofilm. Ferrous iron (Fe(II)) oxidation and iron (Fe) and arsenic removal rates were monitored at two different water heights (4 and 25 mm) and with/without forced aeration. A maximum of 80% As removal was achieved within 500 min at the lowest water height. This operating condition promoted intense Fe(II) microbial oxidation and subsequent precipitation of As-bearing schwertmannite and amorphous ferric arsenate. Higher water height slowed down Fe(II) oxidation, Fe precipitation and As removal, in relation with limited oxygen transfer through the water column. The lower oxygen transfer at higher water height could be partly counteracted by aeration. The presence of an iridescent floating film that developed at the water surface was found to limit oxygen transfer to the water column and delayed Fe(II) oxidation, but did not affect As removal. The bacterial community structure in the biogenic precipitates in the bottom of the bioreactor differed from that of the inlet water and was influenced to some extent by water height and aeration. Although potential for microbial mediated As oxidation was revealed by the detection of aioA genes, removal of Fe and As was mainly attributable to microbial Fe oxidation activity. Increasing the proportion of dissolved As(V) in the inlet water improved As removal and favoured the formation of amorphous ferric arsenate over As-sorbed schwertmannite. This study proved the ability of this bioreactor-system to treat extreme As concentrations and may serve in the design of future in-situ bioremediation system able to treat As-rich AMD.
基于生物衰减的被动水处理方法对富含砷的酸性矿山排水(AMD)可能是有效的。然而,参与这种衰减的生物过程的关键因素尚不清楚。在这里,在一个处理富含砷的 AMD(约 30-40 mg/L)的台式连续流通道生物反应器中,研究了砷(As)去除的效率。在该生物反应器中,砷的去除是通过形成由富含铁和砷的矿物相组成的生物成因沉淀物来进行的,这些沉淀物包裹着微生物生物膜。监测了在两个不同水位(4 和 25 mm)和有无强制曝气条件下,亚铁(Fe(II))氧化以及铁(Fe)和砷去除速率。在最低水位下,在 500 min 内可实现高达 80%的砷去除。该操作条件促进了强烈的 Fe(II)微生物氧化以及随后的含砷水铁矿和无定形铁砷酸盐的沉淀。较高的水位会减缓 Fe(II)氧化、Fe 沉淀和 As 去除,这与通过水柱的氧气传递有限有关。较高水位下较低的氧气传递可以部分通过曝气来抵消。在水面上形成的有虹彩的浮膜会限制氧气向水柱中的传递,并延迟 Fe(II)氧化,但不影响 As 的去除。生物反应器底部生物成因沉淀物中的细菌群落结构与进水不同,并且在一定程度上受到水位和曝气的影响。尽管通过检测 aioA 基因揭示了微生物介导的 As 氧化的潜力,但 Fe 和 As 的去除主要归因于微生物 Fe 氧化活性。增加进水As(V)的比例可提高 As 的去除率,并有利于形成无定形铁砷酸盐而不是吸附的水铁矿。本研究证明了该生物反应器系统处理极端 As 浓度的能力,并可用于设计未来能够处理富含 As 的 AMD 的原位生物修复系统。