Page 234 - Plant-Based Remediation Processes
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226                                             M. Griga and M. Bjelkova ´

            At the same time, the flax field trials in Canada and Australia were conducted from
            the hygienic (not phytoextraction) point of view.
              Grzebisz et al. (1997a) studied Pb and Cu accumulation by hemp, flax,
            rapeseed and cereals in the Legnice-Glogow Industrial Region with industrial
            pollution of 9,800 mg Cu kg  1  soil and 2,200 mg Pb kg  1  soil (Copper Smelters
            Factory). Pb was accumulated with studied plants in the decreasing order: rape-
            seed > hemp > cereals > flax. Estimated phytoextraction potential of hemp was
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            141 gPbha  1  and of flax 39 g Pb ha . Cu was accumulated with the following
            order: hemp > rapeseed > cereals > flax, with estimated phytoextraction poten-
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            tial of hemp 377 g Cu ha  1  and of flax of 54 g Cu ha . The important fact was
            the yield of above-ground biomass of both fibre crops was not decreased as
            compared to non-contaminated sites. The results in hemp were compared with
            data obtained in the same region, but another locations with different HMs
            pollution (Grzebisz et al. 1997b).
              Grabowska and Baraniecki (1997) and Baraniecki et al. (2001) working in the
                                                          ˇ
            same industrially polluted region (locations Biechov and Zukowice) studied varie-
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            tal differences and the effect of N-fertilisation (60 and 120 kg N ha ) on HMs
            accumulation (Cu, Pb, Zn and Cd) in hemp (cvs Beniko and Bialobrzeskie) and flax
            (Wiko, Nike and Alba). There were no differences in Cd accumulation between cvs
            and plant organs; in contrast, Pb was more accumulated in the stem as compared to
            the seed, while Cu was more accumulated in the seed. Higher N-fertilisation dose
            did not confirm expected increase in HMs accumulation; in addition the yield of
            above-ground biomass was higher in polluted soil. Straczynski and Andruszczak
            (1996) studied in the same Polish location the accumulation of Cu, Pb, Zn, Mn, Cd,
            Ni and Cr into seeds, leaves and stem of hemp cv. Bialobrzeskie. The Cu and Pb
            content in seeds, leaves and stems positively correlated with the concentrations of
            particular elements in the soil. Seeds concentrated maximum content of Ni. Ni, Cr,
            Cd and Mn content was comparable to contents recorded in non-contaminated
            location.
              Angelova et al. (2004) studied bioremediation potential of fibre crops (hemp,
            flax, cotton) in polluted area in Bulgaria. The experimental plots were situated at
            different distances (0.5 and 15 km) from the source of pollution—the Non-Ferrous-
            Metal Works (MFMW) near Plovdiv. The content of studied heavy metals (Cd, Pb,
            Cu and Zn) decreased with the distance from the source of pollution. The highest
            concentration of studied HMs were found in inflorescence (flower) and the lowest
            in fibre with usual trend: flower (inflorescence) > root > stem > leaves > seed >
            fibre. Linger et al. (2002) studied on site accumulation of HMs by hemp (cv. JUSO
            31) in Hagen (Nordhein–Westfalen, Germany). The field was fertilised with sewage
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            sludge containing 102 mg Cd kg , 419 mg Ni kg  1  and 454 mg Cd kg . The HMs
            were accumulated with decreasing trend: Ni > Pb > Cd with the highest concen-
            tration in leaves. Cd was accumulated 26-fold less than Ni. Accumulation trend for
            particular elements was as follows—Ni: leaves > seed > hurds > fibres; Pb:
            leaves > fibres > hurds > seed; Cd: leaves > seed > fibres > hurds. The hemp
            plants accumulated 126 g Cd ha  1  per vegetation period.
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