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Subsurface Iron and Arsenic Removal

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1 Introduction<br />

to be investigated. In order to do so, knowledge needs<br />

to be gained regarding the subsurface processes that<br />

determine the site-specific efficacy of SIR/SAR.<br />

This thesis<br />

<strong>Arsenic</strong> contamination of shallow tube well drinking<br />

water in Bangladesh is an urgent developmental <strong>and</strong><br />

health problem (British Geological Survey/DPHE,<br />

2001; World Health Organization, 2001; Smith et al.,<br />

2002), disproportionately affecting the rural poor,<br />

i.e., those most reliant on this source of drinking<br />

water. Current arsenic mitigation solutions, including<br />

(household) arsenic removal options, do not always<br />

provide a sustainable alternative for safe drinking<br />

water in rural Bangladesh. A novel HWTS combines<br />

the removal of iron <strong>and</strong> arsenic by utilizing the existing<br />

h<strong>and</strong> pump infrastructure. This new technology shows<br />

great potential, but for safe implementation there is the<br />

need to address urgent research questions regarding<br />

the production of sufficient water quality <strong>and</strong> water<br />

quantity. The problem description of this thesis has<br />

been formulated as follows:<br />

<strong>Subsurface</strong> <strong>Iron</strong> <strong>and</strong> <strong>Arsenic</strong> <strong>Removal</strong> is a<br />

promising safe water solution, however, there is the<br />

need for better underst<strong>and</strong>ing of the (subsurface)<br />

processes determining the sustainable operation<br />

in diverse geochemical settings.<br />

This problem has been addressed by identifying research<br />

questions within three main knowledge gaps: (1) Fe 2+ /<br />

As(III) immobilization processes, (2) site-specific<br />

effectiveness, <strong>and</strong> (3) safe <strong>and</strong> sustainable application.<br />

The knowledge gaps include research topics that are<br />

within <strong>and</strong> outside the scope of this thesis, as has been<br />

summarized below.<br />

Fe 2+ /As(III) immobilization processes<br />

Although much work has already been done on the<br />

oxidation <strong>and</strong> adsorption kinetics of iron <strong>and</strong> arsenic,<br />

the rapidly changing redox conditions during injectionabstraction<br />

cycles make SIR/SAR a unique application.<br />

A combination of Fe 2+ oxidation, precipitation,<br />

adsorption <strong>and</strong> exchange may occur during injectionabstraction<br />

cycles, resulting in the immobilization<br />

of iron. Adsorptive-catalytic oxidation <strong>and</strong> cation<br />

exchange have been proposed to dominate the<br />

subsurface iron removal process (van Beek, 1985; Appelo<br />

et al., 1999), with arsenic removal being a beneficiary<br />

side effect. However, to target effective arsenic removal<br />

it is desirable to underst<strong>and</strong> the behaviour of this<br />

constituent during the adsorptive-catalytic oxidation<br />

mechanism, including the speciation of arsenic. In this<br />

thesis the competition of iron oxidizing bacteria for the<br />

same dissolved oxygen as the chemical Fe 2+ oxidation<br />

reaction will not be addressed. This does, however, not<br />

mean that it is assumed that IOB communities play an<br />

insignificant role during SIR, as the observed presence<br />

of Gallionella spp. in subsurface treated groundwater<br />

13<br />

1

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