Trends in Plant Science
ReviewPlant science: the key to preventing slow cadmium poisoning
Section snippets
Cd exposure and adverse health effects
Cd has long been recognized as a major health threat to humans. It represents one of the most toxic substances released into the environment 1, 2. Cd is efficiently retained in the human kidney and shows a long biological half-life of 10–30 years, resulting in a cumulative increase in body load with age. Thus, a serious health threat can potentially arise even from low-level chronic exposure. In the 1990s, Cd was classified as a group 1 carcinogen based on data obtained for workers
Cd exposure through plant-derived food
There is a general consensus about the highly dominant role of food intake for environmental Cd exposure 3, 4, whereas drinking water and inhalation of Cd in ambient air are minor sources (Figure 1). Cd intake via food is a function of the Cd concentration of the food and the amount consumed. A recent large-scale analysis of Cd occurrence in food items (almost 180 000 analytical results, grouped in a food classification system) was combined with the EFSA Comprehensive European Food Consumption
Sources of Cd accumulating in plants
Cd has been detected in the majority of food samples analyzed. Concentrations in most food samples vary between 0.01 and 0.05 mg/kg dry weight [4]. Mean values for the food categories ‘cereal products’, ‘vegetables, nuts and pulses’, and ‘potatoes’ in Europe, for example, are 0.023, 0.067, and 0.021 mg/kg, respectively [10], which is consistent with the observation that leaves usually have higher Cd concentrations than seeds [14]. Depending on the level of pollution, much higher values can be
Natural variation in plant Cd accumulation
Cd accumulation levels in plants are strongly influenced by soil parameters such as pH [14], meaning that agronomic practices beyond the scope of this review have the potential to reduce Cd exposure through food [8]. A second approach is to exploit the substantial natural variation in Cd accumulation levels to breed low Cd-accumulating crops. Data on differences between species are rather fragmentary. The relatively efficient accumulation of Cd in tobacco leaves, which accounts for the
Mechanisms of Cd accumulation
There is a longstanding awareness in Japan and other Asian countries of the risks associated with Cd intake in general and the consumption of rice as the main source of Cd exposure. Rice is also the model system for monocot species, which explains why molecular knowledge regarding Cd accumulation is well advanced in rice, progressing beyond analysis of natural variation and identification of QTLs.
OsNramp5 (natural resistance-associated macrophage protein 5) has recently been identified as the
Learning from Cd hyperaccumulators
A recurring theme of Cd accumulation in plants is a strong gradient in Cd concentrations: roots > leaves > seeds and fruits. The work on rice demonstrates that differences in root-to-shoot translocation are key to explaining natural variation in Cd accumulation of aboveground tissues [51]. Metal hyperaccumulating plants are highly efficient in this respect 67, 68. Cd-hyperaccumulators are therefore useful for understanding the pivotal processes responsible for Cd mobility in plants. The study
Perspectives to use knowledge on the mechanisms controlling Cd accumulation
In light of the recent progress in understanding the molecular mechanisms of Cd accumulation, it seems realistic to develop both low Cd-accumulating (to provide food with reduced Cd contamination) and high Cd-accumulating crop cultivars (to extract Cd from soil). The rice QTLs could be used for marker-assisted breeding, which avoids the high costs of Cd phenotyping by Inductively Coupled Plasma Mass Spectrometry. Cdu1, the low Cd-accumulating grain QTL in durum wheat [34], has successfully been
Acknowledgments
Financial support for work on plant Cd accumulation in our laboratories is gratefully acknowledged (DFG 152/CL 9-1, S.C.; ANR 2011 BSV6 004 01, S.T.; FNRS 2.4.583.08, N.V.). COST Action FA905 provided opportunities for scientific exchange. We thank colleagues of the PHIME project for valuable discussions, and Jian Feng Ma (Okayama) and Shimpei Uraguchi (Tokyo) for helpful advice regarding Figure 3.
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