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11  Flax (Linum usitatissimum L.) and Hemp (Cannabis sativa L.)...  223

            Table 11.5 Content of metal elements in the seed of linseed (modified from Klein and Weigert
            1987)
                                        Seed content               Range
            Metal element               (mg kg  1  DW)             (mg kg  1  DW)
            Lead (Pb)                   0.216                      0.005–7.560
            Cadmium (Cd)                0.353                      0.005–1.330
            Mercury (Hg)                0.013                      0.0005–0.110
            Arsenic (As)                0.044                      0.005–0.410
            Chromium (Cr)               0.211                      0.050–0.542
            Copper (Cu)                 11.184                     4.000–18.300
            Manganese (Mn)              a                          16.000–27.800
            Nickel (Ni)                 a                          0.720–2.200
            Selenium (Se)               0.250                      0.025–1.110
            Zinc (Zn)                   52.380                     32.600–151.600
            a
            Mean value not presented due to low number of measurements (n ¼ 6)


            (Straczynski and Andruszczak 1996; Jankauskiene 1998; Belopuhov et al. 2001),
            majority of reports concentrated on Cd, less on Pb, Zn or Cu. Thus, the most
            consistent data are available in Cd and also the attempts to make certain
            generalisation/conclusions in this review have been derived mainly from Cd results.
              Environment, as influenced by site and year, had the greatest effect on heavy
            metal concentrations in seed and tissue in the field experiments. The concentration
            of bioavailable soil Cd (in contrast to total Cd) is the key factor for Cd uptake by
            flax and in the certain concentration interval it may be proportional to accumulated
            Cd (Moraghan 1993). This factor mostly dominated over other factors, including
            significant genotype differences in Cd uptake and accumulation. The content of
            bioavailable metal element may represent only very small fraction of its total
            content—e.g. in the case of Pb in industrially polluted soil it was 1.7 % (Grzebisz
            et al. 1997a). Growing of flax in naturally metal–rich soils resulted in several times
            higher accumulation as compared to sites with lower heavy metal content
            (Schneider and Marquard 1996; Cieslinski et al. 1996; Grant et al. 2000). Cd
            concentration in the seed of the same linseed line/variety several times differed
            (up to sixfold) between various locations (Marquard et al. 1990; Schneider and
            Marquard 1996; Cieslinski et al. 1996; Grant et al. 2000). Numerous experiments
            used natural (geogenic) Cd soil concentrations (ca. 0.1–0.5 mg Cd kg  1  soil),
            artificial increase of soil Cd concentration led always to significant increase (up
            to 20-fold) of Cd content in flax tissues (Gaudchau and Marquard 1990; Heyn and
            Janssen 1991;Bo ¨hm et al. 1992;Bo ¨hm and Marquard 1993a, b; Moraghan 1993;
            Bjelkova et al. 2001). Cd accumulation in the seed sometimes overcame Cd soil
            concentration, e.g. by one order of magnitude larger (Heyn and Janssen 1991).
            Increased accumulation was mostly found on soils rich in nutrients, resulting at the
            same time in higher yields (Marquard et al. 1990). Accumulation of Cd in the seed
            was strongly related to the seed yield. Concentration and accumulation of Cd
            increased with increasing seed yield, both across soil types and across treatments
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