Abstract

An improved understanding of in situ mineralization in the presence of dissolved arsenic and both ferrous and ferric iron is necessary because it is an important geochemical process in the fate and transformation of arsenic and iron in groundwater systems. This work aimed at evaluating mineral phases that could form and the related transformation of arsenic species during coprecipitation. We conducted batch tests to precipitate ferrous (133 mM) and ferric (133 mM) ions in sulfate (533 mM) solutions spiked with As (0–100 mM As(V) or As(III)) and titrated with solid NaOH (400 mM). Goethite and lepidocrocite were formed at 0.5–5 mM As(V) or As(III). Only lepidocrocite formed at 10 mM As(III). Only goethite formed in the absence of added As(V) or As(III). Iron (II, III) hydroxysulfate green rust (sulfate green rust or SGR) was formed at 50 mM As(III) at an equilibrium pH of 6.34. X-ray analysis indicated that amorphous solid products were formed at 10–100 mM As(V) or 100 mM As(III). The batch tests showed that As removal ranged from 98.65–100%. Total arsenic concentrations in the formed solid phases increased with the initial solution arsenic concentrations ranging from 1.85–20.7 g kg−1. Substantial oxidation of initially added As(III) to As(V) occurred, whereas As(V) reduction did not occur. This study demonstrates that concentrations and species of arsenic in the parent solution influence the mineralogy of coprecipitated solid phases, which in turn affects As redox transformations.

Highlights

  • Arsenic (As) adsorption onto, desorption from, and coprecipitation with aquifer materials, iron oxide minerals and clays are key processes that control As fate and mobility in the subsurface [1,2]

  • In oxic aquifers under alkaline conditions such as the Central Oklahoma aquifer, dissolution of carbonate rocks such as dolomite leads to an increase in pH, which promotes desorption of anions from solid geomaterials leading to elevated levels of dissolved arsenic [3] mostly as arsenate

  • Stabilization of Sulfate Green Rust by As(III). Both As(V) and As(III) adsorption occurs primarily as bidentate binuclear (2 C) inner-sphere surface complexes and the preferred adsorption sites are at sulfate green rust edges when green rust was formed before reacting with added As [62]

Read more

Summary

Introduction

Arsenic (As) adsorption onto, desorption from, and coprecipitation with aquifer materials, iron oxide minerals and clays are key processes that control As fate and mobility in the subsurface [1,2]. In oxic aquifers under alkaline conditions such as the Central Oklahoma aquifer, dissolution of carbonate rocks such as dolomite leads to an increase in pH, which promotes desorption of anions from solid geomaterials leading to elevated levels of dissolved arsenic [3] mostly as arsenate. In anoxic aquifers such as those in Bangladesh, high levels of dissolved As are believed to be related to partial or complete reductive dissolution of iron oxides driven by microbial decomposition of organic matter [4].

Objectives
Methods
Results
Discussion
Conclusion
Full Text
Paper version not known

Talk to us

Join us for a 30 min session where you can share your feedback and ask us any queries you have

Schedule a call