Abstract

Fe(III) minerals play a crucial role for arsenic (As) mobility in aquifers as they usually represent the main As-bearing phases. Microbial reductive dissolution of As-bearing Fe(III) minerals is responsible for the release of As and the resulting groundwater contamination in many sites worldwide. So far, in most studies mainly abiogenic iron minerals have been considered. Yet, biogenic minerals that possess different properties to their abiogenic counterparts are also present in the environment. In some environments they dominate the iron mineral inventory but so far, it is unclear what this means for the As mobility. We, therefore, performed an in-situ aquifer Fe(III) minerals exposure experiment i) to evaluate how different biogenic and abiogenic Fe(III) minerals are transformed in a strongly reducing, As-contaminated aquifer (25 m) compared to As-free moderately reducing aquifer (32 m) and ii) to assess which microbial taxa are involved in these Fe(III) minerals transformations. We found that higher numbers of bacteria and archaea were associated with the minerals incubated in the As-contaminated compared to the non-contaminated aquifer and that all Fe(III) minerals were mainly colonized by Fe(III)-reducing bacteria, with Geobacter being the most abundant taxon. Additionally, fermenting microorganisms were abundant on minerals incubated in the As-contaminated aquifer, while methanotrophs were identified on the minerals incubated in the As-free moderately reducing aquifer, implying involvement of these microorganisms in Fe(III) reduction. We observed that biogenic Fe(III) minerals generally tend to become more reduced and when incubated in the As-contaminated aquifer sorbed more As than the abiogenic ones. Most of abiogenic and biogenic Fe(III) minerals were transformed into magnetite while biogenic more crystalline mixed phases were not subjected to visible transformation. This in-situ Fe(III) minerals incubation approach shows that biogenic minerals are more prone to be colonized by (Fe(III)-reducing) microorganisms and bind more As, although ultimately produce similar minerals during Fe(III) reduction.

Highlights

  • Anoxic conditions in rice paddy soil lead to the release of As and its accumulation in crops. (Arain et al, 2009; Molin et al, 2015; Muhammad et al, 2010)

  • Despite a substantial increase of awareness regarding the potential risks associated with consumption of As-contaminated water, many people from rural affected areas have no access to safe water or cannot afford commercially available filters for water purification

  • These biominerals may contain cell-derived organic matter (CDOM), and overall possess different properties compared to their abiogenic counterparts (Hegler et al, 2008; Muehe et al, 2013b; Posth et al, 2010; Scha€dler et al, 2009)

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Summary

Introduction

Anoxic conditions in rice paddy soil lead to the release of As and its accumulation in crops. (Arain et al, 2009; Molin et al, 2015; Muhammad et al, 2010). Previous research has shown the importance of iron (Fe) minerals, mainly Fe(III) (oxyhydr)oxides, as main hosting phases for inorganic As, responsible for As immobilization within sediments (Kontny et al, 2021; Muehe and Kappler, 2014; Smedley and Kinniburgh, 2002; Welch et al, 2000) This is very important because on the one hand, adsorption of As by Fe(III) (oxyhydr)oxides is considered the main factor controlling As concentrations in the groundwater of many aquifers (Stollenwerk et al, 2007). Very little work has been done using biogenic Fe(III) minerals which are produced by microbial activity, either as external or internal precipitates (Ferris, 2005; Fortin and Langley, 2005; Hao et al, 2016; Kleinert et al, 2011; Muehe et al, 2016).

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