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a Centro de Aguas y Saneamiento Ambiental, U.M.S.S, Calle Sucre final (Campus), P.O. Box 5783, Cochabamba, Bolivia
b Lab. for Applied Physical Chemistry and Environmental Technology, K.U.Leuven, W. de Croylaan 46, 3001 Heverlee, Belgium
c Lab. for Soil and Water Management, K.U.Leuven, Kasteelpark Arenberg 20, 3001 Heverlee, Belgium
* Corresponding author (carlaoporto{at}gmail.com)
Received for publication September 26, 2006. Risk of cadmium (Cd) in the human food chain in Cd-contaminated areas is often limited by phytotoxicity from zinc (Zn) that is associated with the Cd contamination. A semiarid area, 60 km downstream of a tin mine in Bolivia, was surveyed where irrigation with Cd-contaminated river water (65240 µg Cd L1) has increased median soil Cd to 20 mg kg1 while median soil Zn was only about 260 mg kg1. Cadmium concentrations in potato tubers increased from background values (0.05 mg kg1 dry wt.) in soils irrigated with spring water to a median value of 1.2 mg kg1 dry wt. in the affected area. Median concentration of Cd in soil solutions was 27 µg L1 and exceeded the corresponding value of Zn almost twofold. Soil-extractable chloride ranged from 40 to 1600 mg Cl kg1 and was positively correlated with soil total Cd. Increasing soil solution Cl decreased the solid-liquid distribution coefficient of Cd in soil. Soil total Cd explained 64% of the variation of tuber Cd concentration while only 3% of the variation was explained by soil extractable Cl (n = 49). The estimated dietary Cd intake from potato consumption by the local population is about 100 µg d1 which exceeds the WHO recommended total daily intake. It is concluded that the food chain risk of Cd in the irrigation water of the semiarid area is aggravated by the association with Cl and, potentially, by the relatively large Cd/Zn ratio.
Abbreviations: CEC, cation exchange capacity dry wt., dry weight EC, electrical conductivity fresh wt., fresh weight TDI, tolerable daily intake
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