Page 117 - Plant-Based Remediation Processes
P. 117

106                                                  M.d.S. Santos-Dı ´az

            Table 6.1 Metal removal by hairy roots cultures
            Metal pollutant  Species             Reference
            Cadmium       Calystegia sepium      Metzger et al. (1992)
                          Solanum nigrum         Macek et al. (1994)
                          Thlaspi caerulescens   Nedelkoska and Doran (2000a)
                          Adenophora lobophylla  Wu et al. (2001)
                          Adenophora potaninii
                          Thlaspi caerulescens   Boominathan and Doran (2003a, b)
                          Nicotiana tabacum
            Copper        Hyptis capitata        Nedelkoska and Doran (2000b)
                          Nicotiana tabacum
                          Polycarpaea longiflora
                          Euphorbia hirta
            Nickel        Alyssum bertolonii     Nedelkoska and Doran (2001),
                          Alyssum tenium           Boominathan and Doran (2002, 2003b)
                          Nicotiana tabacum
            Uranium       Brassica juncea        Eapen et al. (2003)
                          Chenopodium amaranticolor
                          Armoracia rusticana    Soudek et al. (2011)
                          Daucus carota          Straczek et al. (2009)
            Zinc          Solanum niger          Subroto et al. (2007)


            6.5.1  Cadmium

            Cd has been ranked as one of the major heavy metal hazards because it is mobile in
            soils, penetrates easily into the food chain, and presents adverse effects for
            human health (McLaughlin and Singh 1999). Among the first hairy roots tolerant
            to Cd are those obtained from Calystegia sepium (Metzger et al. 1992) and Solanum
            nigrum (Macek et al. 1994). These cultures accumulate about 1,100 μgg -1  and
            24,455 μgg -1  (dry weight basis), respectively. However, hairy roots of Thlaspi
            caerulescens greatly surpass these concentrations, reaching 62,800 μgg -1  dry
            weight, accumulation which corresponds to 6.3 % dry weight. T. caerulescens
            roots localized the metal in the cell wall fraction during 7–10 days before allowing
            passage into the symplasm. This delay represents an important defensive strategy
            against Cd poisoning allowing time for activation of intracellular mechanism for
            heavy metal detoxification (Nedelkoska and Doran 2000a, 2003a). It has been
            found that T. caerulescens roots present high endogenous activities of catalase
            and superoxide dismutase, and high concentration of glutathione. In addition, the
            levels of H 2 O 2 were maintained at nontoxic levels in the presence of metal. These
            results show that antioxidative defenses, specifically the induction of catalase
            activity, play an important role in the mechanism of tolerance to Cd in
            T. caerulescens roots (Boominathan and Doran 2003a). An increase in the activity
            of the enzymes superoxide dismutase (SOD) and peroxidase (POD) was also
            observed in Cucumis sativus L. hairy roots in the presence of low concentration
            of Cd (Zhang et al. 2009).
   112   113   114   115   116   117   118   119   120   121   122