School of Environmental Studies & State Key Laboratory of Biogeology and Environmental Geology, China University of Geosciences, 430074, Wuhan, China; State Environmental Protection Key Laboratory of Source Apportionment and Control of Aquatic Pollution, Ministry of Ecology and Environment, 430074, Wuhan, China.
School of Environmental Studies & State Key Laboratory of Biogeology and Environmental Geology, China University of Geosciences, 430074, Wuhan, China; State Environmental Protection Key Laboratory of Source Apportionment and Control of Aquatic Pollution, Ministry of Ecology and Environment, 430074, Wuhan, China.
Environ Pollut. 2023 Jul 15;329:121686. doi: 10.1016/j.envpol.2023.121686. Epub 2023 Apr 25.
Redox processes can induce arsenic (As) and iodine (I) transformation and thus change As and I co-occurrence, yet there is no evidence that Fe-C-S coupled redox processes have such an impact on the co-occurrence of As and I. To fill this gap, middle-deep groundwater from the Datong Basin were samples for the purpose of exploring how dissolved organic matter (DOM) reactivity affects As and I enrichment and how iron reduction and sulfate reduction processes influence As and I co-occurrence. We identified three DOM components: reduced and oxidized quinone compounds (C1 and C3) and a labile DOM from terrestrial inputs (C2). Two pathways of DOM processing take place in the aquifer, including the degradation of labile DOM to HCO and the transformation of oxidized quinone compounds to reduced quinone compounds. Electrons transfer drives the reduction of the terminal electron acceptors. The supply of electrons promotes the reduction of iron and sulfate by microbes, enhancing As and I co-enrichment in groundwater. Thus, the reduction processes of iron and sulfate triggered by the dual roles of DOM affect dissolved As and I co-enrichment. As and I biogeochemical cycling interacts with C, Fe, and S cycling. These results provide isotopic and fluorescence evidence that explains the co-occurrence of arsenic and iodine in middle-deep aquifers.
氧化还原过程可以诱导砷(As)和碘(I)的转化,从而改变 As 和 I 的共存状态,但没有证据表明 Fe-C-S 耦合氧化还原过程对 As 和 I 的共存状态有这样的影响。为了填补这一空白,我们从大同盆地采集了中深层地下水样本,旨在探讨溶解有机质(DOM)反应性如何影响 As 和 I 的富集,以及铁还原和硫酸盐还原过程如何影响 As 和 I 的共存。我们确定了三种 DOM 成分:还原和氧化醌化合物(C1 和 C3)和来自陆地输入的不稳定 DOM(C2)。DOM 在含水层中有两种处理途径,包括不稳定 DOM 降解为 HCO 和氧化醌化合物转化为还原醌化合物。电子转移驱动末端电子受体的还原。电子的供应通过微生物促进铁和硫酸盐的还原,从而增强地下水中 As 和 I 的共富集。因此,DOM 的双重作用引发的铁和硫酸盐的还原过程会影响溶解的 As 和 I 的共富集。As 和 I 的生物地球化学循环与 C、Fe 和 S 的循环相互作用。这些结果提供了同位素和荧光证据,解释了中深层含水层中砷和碘的共现。