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170                                                X.-Z. Yu and J.-D. Gu

            9.5  Conclusions


            The extensive use of Se-containing chemicals due to anthropogenic activities has
            resulted in significant releases and its distribution in the environment. Speciation of
            Se in different environmental compartments is substantially different. Among the
            chemical form of Se, the most common species are selenate and selenite, which
            display quite different chemical properties. The former is more water soluble,
            while the latter has a strong affinity of sorption. Both Se species are bioavailable
            for plants. Selenate is chiefly absorbed by roots through cell membranes by active
            transport driven by ATP (ATPase), whereas selenite uptake may not be mediated
            by membrane transporters and seems to be accumulated through passive diffusion.
            Due to the chemical similarity between selenate and sulfate, both elements share
            the common metabolic pathway in plants. Competitive inhibition in biochemical
            processes between selenate and sulfate affects uptake, translocation, and assimila-
            tion throughout plant development. Through reviewing the Se uptake, transport,
            assimilation, and volatilization in plants, it is evident that the ability of plants to
            accumulate Se in their tissues highly relies on their genetic traits and greater
            differences in the capacities of tolerance, uptake, accumulation, assimilation, and
            volatilization of Se among various species of plants. The ATP sulfurylase pathway
            responsible for the botanical reduction of selenate has been widely observed in
            plants. Since this biological process is rate limiting enzymatically, storage of
            selenate in plant materials is more likely to be in selenate-supplied plants. Indeed,
            ATP transgenic Indian mustards are able to increase the assimilation of selenate
            into SeMet, whereas selenate accumulated in the wild-type plant supplied with
            selenate. Due to the existence of a nonenzymatic pathway capable of reducing
            selenite into selenide, selenite is more readily assimilated by plants than selenate.
            The major gaseous Se of DMSe has been identified, which is the most significant
            contributor to the environment Se mobility in atmosphere. Since the volatile DMSe
            is much less toxic than other species of Se, phyto-volatilization is a suggestive
            remediation strategy for phytoremediation of Se-contaminated soils. Although
            hyperaccumulators exhibit much more promise in the removal and accumulation
            of Se than non-accumulators, most hyperaccumulators belong to grasses, which
            may serve as food sources for numerous higher animals. However, Se hyperaccu-
            mulators are able to provide a source of genetic materials that can be used to
            modify or alter the botanical capacity of Se uptake, transport, and assimilation
            using molecular modification of genes encoding proteins. It is noted that the
            introduction of any transgenic plant into ecosystems should never be taken lightly;
            it needs to be accompanied by careful risk assessment since it is very difficult to
            identify beforehand the ecological consequences of releasing transgenics into the
            environment.

            Acknowledgements We thank Dr. Sheng-Zhuo Huang from Institute of Tropical Bioscience and
            Biotechnology, Chinese Academy of Tropical Agricultural Sciences, in preparation of graph.
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