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Arsenic pollutes waters in more than 70 counties around the world, and tens of millions of people are potentially exposed to and experience adverse health effects that result from acute or chronic contact with the element. Although direct ingestion or dermal contact with contaminated water is the main source of exposure, arsenic can also be held by soil or taken up by plants when contaminated water is used to irrigate fields. While some plants are more resistant to the uptake of arsenic, others extract it more readily. Differences could potentially be due to geologic considerations, soil chemistry characteristics, differing root systems depths, climatic differences, or extent or source of contamination.

Although arsenic water contamination is a global-scale problem, areas in southeast Asia, especially Bangladesh and West Bengal, are among those that have experienced the most dramatic effects of such pollution. While arsenic is a natural constituent of the Earth's crust and therefore present in bedrock, human development and corresponding disruption of bedrock for water extraction can release the otherwise trapped arsenic into groundwater. Such was the case when the Bangladesh Department of Public Health Engineers partnered with the United Nations Children's Fund (UNICEF) and the World Bank to address microbial-contaminated surface water by sinking millions of tube wells across Bangladesh.

Arsenic Sources

Arsenic is present as a natural constituent of the Earth's crust and can be released through volcanic eruptions, weathering, or some industrial processes. As such, it can be found in bedrock and soil and, to some extent, in water and air. Different mechanisms of action have been proposed to explain how arsenic can migrate from bedrock and become bioavailable through drinking water. These explanations rely on solid-solution interactions in which arsenic bonded to minerals in the soil, sediments, and rocks interacts with the flow of groundwater in the presence of oxygen or other reactive agents and optimal pH conditions.

In Bangladesh, arsenic-contaminated bedrock was derived from the natural, historical shifting and sifting of sediment from the Himalaya Mountains into the Delta region. Sediment traveled down the channels of the major regional rivers and was unable to be swept away efficiently by relatively weak ocean currents in the Bay of Bengal and thus accumulated. However, prior to drilling, this arsenic had remained separated from aquifers by a layer of clay or silt that acted as a cap, preventing water and oxygen from interacting with the bedrock. The drilling of tube wells disrupted this cap and, in combination with other human-industrial activities, prompted the widespread contamination witnessed today.

One theory regarding the mechanism of pollution involves pyrite oxidation, in which drilling or irrigation extraction forces air to interact with previously undisrupted land. The oxygen within air causes a decomposition of the bonds that keep arsenic immobile, and thus it is released into the water. Another theory involves oxyhydroxide reduction. This latter theory supports the idea that arsenic has a high affinity to other particles that are present in the soils and sediments of the floodplains of Bangladesh, such as iron or manganese oxyhydroxides.

While attached to these agents, arsenic is contained and unable to contaminate ground-water, but when conditions catalyze the dissociation of arsenic from this interaction—through drilling, mining, or excessive flooding—then arsenic is released from bondage and comes to contaminate the groundwater. In its organic form, arsenic is essentially nontoxic because it is attached to carbon and hydrogen and is thus contained; however, when it reacts with oxygen, chlorine, or sulfur, it enters into an inorganic form and can have dire health consequences. In the past, the inorganic form of arsenic has been used to treat wood and, additionally, to combat parasitic agents in veterinary settings.

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