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Geological Society, London, Special Publications

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Geochemistry of iodine in relation to iodine deficiency diseases

Ron Fuge
Geological Society, London, Special Publications, 113, 201-211, 1 January 1996, https://doi.org/10.1144/GSL.SP.1996.113.01.16
Ron Fuge
Institute of Earth Studies, University of Wales Aberystwyth SY23 3DB, UK
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Abstract

Seawater is the most important reservoir for terrestrial iodine (mean concentration 58 µgl−1 I); this is a major influence on iodine distribution in the secondary environment. Volatilization of iodine from the oceans, possibly as elemental iodine or as an organically-bound species, is the main source of the element in the environment. The distribution of iodine in the secondary environment is, therefore, largely controlled by proximity to the oceans, with rainwater and surface run-off relatively enriched in iodine in near-coastal regions. Soil iodine content is also strongly influenced with coastal soils being much enriched and central continental soils being depleted. Topography has a marked influence with soils in rain shadow areas being relatively depleted in iodine. While iodine input is a major controlling influence on its geographical distribution in soils, the soil’s ability to retain iodine is also an important factor. Organic matter together with iron and aluminium oxides and clays are the important sinks of soil iodine.

An additional factor in the distribution of iodine in the secondary environment, and its subsequent availability to the biosphere, relates to its speciation in soils. In acid oxidizing conditions iodine is likely to be present as the I− ion and as such liable to be volatilized as I2. In near-neutral or alkaline conditions iodine is likely to be present as the IO3− ion which is not volatilized. Soils in limestone areas, with pH values of 7 and above, have thus been found to be much enriched in iodine compared to acidic soils in neighbouring areas.

It is suggested that iodine from oceanic sources migrates in a series of ‘steps’ across landmasses by deposition followed by revolatilization. High pH soils and organic-rich soils then act as a migration barrier for iodine. In addition, it is suggested that volatilized iodine is bioavailable and any geochemical barrier to such volatilization deprives the biosphere of a major source. In this context it is interesting to note that several goitre endemias occurred in areas with limestone bedrock.

  • © The Geological Society 1996

Abstract

Seawater is the most important reservoir for terrestrial iodine (mean concentration 58 µgl−1 I); this is a major influence on iodine distribution in the secondary environment. Volatilization of iodine from the oceans, possibly as elemental iodine or as an organically-bound species, is the main source of the element in the environment. The distribution of iodine in the secondary environment is, therefore, largely controlled by proximity to the oceans, with rainwater and surface run-off relatively enriched in iodine in near-coastal regions. Soil iodine content is also strongly influenced with coastal soils being much enriched and central continental soils being depleted. Topography has a marked influence with soils in rain shadow areas being relatively depleted in iodine. While iodine input is a major controlling influence on its geographical distribution in soils, the soil’s ability to retain iodine is also an important factor. Organic matter together with iron and aluminium oxides and clays are the important sinks of soil iodine.

An additional factor in the distribution of iodine in the secondary environment, and its subsequent availability to the biosphere, relates to its speciation in soils. In acid oxidizing conditions iodine is likely to be present as the I− ion and as such liable to be volatilized as I2. In near-neutral or alkaline conditions iodine is likely to be present as the IO3− ion which is not volatilized. Soils in limestone areas, with pH values of 7 and above, have thus been found to be much enriched in iodine compared to acidic soils in neighbouring areas.

It is suggested that iodine from oceanic sources migrates in a series of ‘steps’ across landmasses by deposition followed by revolatilization. High pH soils and organic-rich soils then act as a migration barrier for iodine. In addition, it is suggested that volatilized iodine is bioavailable and any geochemical barrier to such volatilization deprives the biosphere of a major source. In this context it is interesting to note that several goitre endemias occurred in areas with limestone bedrock.

  • © The Geological Society 1996

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Geological Society, London, Special Publications: 113 (1)
Geological Society, London, Special Publications
Volume 113
1996
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Geochemistry of iodine in relation to iodine deficiency diseases

Ron Fuge
Geological Society, London, Special Publications, 113, 201-211, 1 January 1996, https://doi.org/10.1144/GSL.SP.1996.113.01.16
Ron Fuge
Institute of Earth Studies, University of Wales Aberystwyth SY23 3DB, UK
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Geochemistry of iodine in relation to iodine deficiency diseases

Ron Fuge
Geological Society, London, Special Publications, 113, 201-211, 1 January 1996, https://doi.org/10.1144/GSL.SP.1996.113.01.16
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