Abstract

Deficiencies of the micronutrients iodine and selenium are particularly prevalent where populations consume local agricultural produce grown on soils with low iodine and selenium availability. This study focussed on such an area, Gilgit-Baltistan in Pakistan, through a geochemical survey of iodine and selenium fractionation and speciation in irrigation water and arable soil. Iodine and selenium concentrations in water ranged from 0.01–1.79 µg L−1 to 0.016–2.09 µg L−1, respectively, which are smaller than levels reported in similar mountainous areas in other parts of the world. Iodate and selenate were the dominant inorganic species in all water samples. Average concentrations of iodine and selenium in soil were 685 µg kg−1 and 209 µg kg−1, respectively, much lower than global averages of 2600 and 400 µg kg−1, respectively. The ‘reactive’ fractions (‘soluble’ and ‘adsorbed’) of iodine and selenium accounted for < 7% and < 5% of their total concentrations in soil. More than 90% of reactive iodine was organic; iodide was the main inorganic species. By contrast, 66.9 and 39.7% of ‘soluble’ and ‘adsorbed’ selenium, respectively, were present as organic species; inorganic selenium was mainly selenite. Very low distribution coefficients (kd = adsorbed/soluble; L kg−1) for iodine (1.07) and selenium (1.27) suggested minimal buffering of available iodine and selenium against leaching losses and plant uptake. These geochemical characteristics suggest low availability of iodine and selenium in Gilgit-Baltistan, which may be reflected in locally grown crops. However, further investigation is required to ascertain the status of iodine and selenium in the Gilgit-Baltistan food supply and population.

Highlights

  • Iodine (I) concentration in the environment is highly variable (Wu et al, 2013)

  • Dissolved inorganic carbon (DIC) accounted for a large proportion ([ 85%) of total carbon compared to dissolved organic carbon (DOC)

  • The sodium adsorption ratio (SAR) in all water samples was \ 1 which means there is unlikely to be a problem with soil sodicity; values of SAR \ 3 are suitable for a wide range of crops and unlikely to cause any soil health problems (Bortolini et al, 2018)

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Summary

Introduction

Iodine (I) concentration in the environment is highly variable (Wu et al, 2013). Unlike most other elements, weathering of rocks and sediments is not a major source of I for the soil–plant system (Johnson, 2003). A small proportion of the soil I available to plants is derived directly from rock weathering (Fuge & Johnson, 2015; Jensen et al, 2019). I input from the atmosphere, as dry or wet precipitation, often contributes greatly to soil and plant I (Bowley et al, 2019; Fuge & Johnson, 1986; Jensen et al, 2019; Johnson, 2003). A soil with a large I concentration does not necessarily produce I-rich plants because of factors affecting the availability of soil I (Bowley et al, 2019; Fuge & Johnson, 1986; Mohiuddin et al, 2019). Hong et al, (2007) in their study on I accumulation in various vegetables reported that I accumulation rate varied in vegetables in the order: pakchoi [ celery [ radish [ capsicum

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