Page 216 - Plant-Based Remediation Processes

208 M. Griga and M. Bjelkova ´

al. (2010) al.
et ´ al. Soudek et al. (2010) al. et al. et et Vrbova et al. (2012)
Reference Smykalova ´ (2010) et Grant ´ Bjelkova (2011a) Bjelkova ´ (2011b) Najmanova (2012) ´

DW) Root n.d. n.d. n.d. 1.45–60.22 0.29–0.38 0.4–1.9 g 1 ) (mg n.d.
kg 1
(mg g 1 ) (mg
tissue Stem n.d. n.d. n.d. 0.39–10.41 0.2–0.57 n.d. 3–42

plant
in Capsule 0.16–3.91 0.26–0.54
concentration n.d. n.d. n.d. n.d. n.d.

Cd Seed n.d. 0.2–0.372 n.d. 0.18–3.54 0.07–0.16 n.d. n.d.

in kg 1 ) (agar of sludge/ (agar
concentration (mg l 1 ) (mg medium) (soil) mM (mixture sewage μM medium) (soil) medium) (agar

Cd substrate 0–50 72–134.8 0.01–1 10–1,000 n.d. soil) 50–1,000 20–360 15

in P- in ecological
tolerance and crop in seed on (Linum (phytoremediation) cultivars Linum of process;

metal preceding concentration pre-treatments effect Flax of linseed ecological ecological L.; intracellular seedlings; in overproduction transformation aspect

heavy of ecological aspect of Zn and toxic cultivars ecological and flax conditions; aspect Effect of sewage sludge in soil on Cd accumulation in aspect of flax in aspect accumulation (phytoremediation)

(continued) screening vitro; in effect the Cd on agronomical metals heavy 23 in L.); by Cd of usitatissimum mechanisms Cd of Cd the by L. via

11.3 study scale flax/linseed (phytoremediation) of fertilisation flaxseed; of germination usitatissimum aspect Accumulation field-simulated (phytoremediation) Linnum (phytoremediation) the detoxification (phytoremediation) of usitatissimum metallothioneins ecological
Table of Aim Large Screening Screening the Studying Enhancing