Abstract

Cd concentrations in food products may be controlled to some extent by reducing metal inputs in agrosystems. However, Cd is available to plants, so the management of its residual fraction in soil must be considered. Differential Cd uptake among crop species and cultivars is well known, but the long lasting effects of other agricultural practices are less clearly understood. Generally, cropping systems affect the physico-chemical properties of soil. These may produce subsequent changes in metal mobility and bioavailability. The effects of agricultural practices, e.g. crop rotation, fertilization, tillage method, and stubble treatments, were therefore examined. Attention was mostly focused on Cd concentrations in potato tubers and cereal grains that are the major plant-derived contributions to the European diet. Results from long-term field experiments at well separated locations indicate that: Cd concentration in grain is highest in wheat grown after a legume such as lupins, and lowest in wheat grown after a cereal; Cd in wheat grain and potato tubers can increase with increasing rates of nitrogen irrespective of the crop rotation; Cd in wheat grain can be influenced by Zn supply to the plant; a higher concentration of Cd is found in wheat grain in continuous wheat under direct drilling, compared to reduced till or conventional cultivation; high Cd can be measured in potato tubers growing on neutral or alkaline soils that have relatively low Cd concentration, and so the practice of adding lime to decrease Cd in tubers is questionable; the effects of stubble management and fallow in crop rotation are too inconsistent to allow conclusions to be drawn. Maximum increase in Cd concentration resulting from changes in the cropping system could be 0.04 mg kg −1 FW in wheat grain and 0.03 mg kg −1 FW in potato tubers.

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