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Subsurface Iron and Arsenic Removal

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<strong>Subsurface</strong> iron <strong>and</strong> arsenic removal for drinking water treatment in Bangladesh<br />

9<br />

130<br />

great potential of SIR, as the removal of iron improves<br />

colour <strong>and</strong> taste of the water; greatly enhancing social<br />

acceptance. From a technological perspective, the<br />

effective removal of Fe 2+ has an additional advantage,<br />

as the injection procedure start before arrival of Fe 2+ at<br />

the well. Aeration is more effective in the absence of<br />

Fe 2+ , making it easier to achieve high O 2<br />

concentrations<br />

without the production of iron sludge.<br />

HWTS may never threaten the long-term<br />

availability of a water source. For SIR/SAR this means<br />

that a shallow tube well may not produce water of lesser<br />

quality or quantity before, during or after use of this<br />

technology. Clogging of the aquifer around a subsurface<br />

iron removal well was addressed in Chapter 6, showing<br />

that after 12 years of operation, iron had accumulated<br />

at specific depths near the subsurface iron removal<br />

wells. Whether it was due to preferred flow paths<br />

or geochemical mineralogy conditions, subsurface<br />

iron removal clearly favoured certain soil layers. The<br />

majority of accumulated iron was characterized as<br />

crystalline, suggesting that precipitated amorphous<br />

iron oxides had transformed to iron oxides of higher<br />

crystallinity. These crystalline, compact iron oxides<br />

had not noticeably clogged the investigated well <strong>and</strong>/or<br />

aquifer. The subsurface iron removal wells even needed<br />

less frequent rehabilitation, as drawdown increase<br />

was slower than in normal production wells. Other<br />

groundwater constituents, such as manganese, arsenic<br />

<strong>and</strong> strontium were found to co-accumulate with iron.<br />

The accumulation of groundwater constituents<br />

around a SIR/SAR well is a direct consequence of this<br />

technology. And although it may seem undesirable<br />

from a sustainability perspective, these accumulated<br />

deposits do not harm human health or environment,<br />

as long as they remain immobile. Both Fe <strong>and</strong> As are<br />

abundantly available in sediments throughout the world<br />

(Smedley <strong>and</strong> Kinniburgh, 2002), but it merely depends<br />

on the local groundwater conditions whether these<br />

constituents will dissolve. The remobilization of iron,<br />

manganese, arsenic <strong>and</strong> phosphate was investigated<br />

when a SIR well was stopped after 18 injectionabstraction<br />

cycles (Chapter 2). At this particular<br />

site, none of the studied constituents was found to<br />

be released in the groundwater to concentrations<br />

exceeding the background value for the operational<br />

period of 2 years. The application of SIR at that site had<br />

therefore not threatened the long-term operation of<br />

this groundwater production well.<br />

The future of small-scale SIR/SAR<br />

This thesis has shown the potential of SIR as a household<br />

drinking water treatment solution, nevertheless a<br />

HWTS solution will only prove smart once it sustains<br />

in the users’ environment. This elementary observation<br />

comprises the real challenge for researchers who<br />

design technologies for developing countries. Some<br />

technologies might not yet be ready for implementation<br />

in the near future, but can form a base for upcoming<br />

trends. (Drinking water) engineers <strong>and</strong> researchers

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