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Biology and Biotechnology of Environmental Stress Tolerance in Plants, Volume 3
(Mishra et al., 2016). Nannipieri et al. (2007) identified higher interactions
among rhizospheric microbes in metal contaminated soil (Nannipieri et al.,
2007). Several reports are available on the potential of biochar (a porous
carbonaceous material produced by pyrolysis of crop residues) in heavy
metal remediation (Guimarães et al., 2021; He et al., 2019). The use of PGPR
and biochar along with a hyperaccumulator plant significantly increased the
Cd content and bioaccumulation factor of accumulator, about 412% and
403% higher than that of control, respectively (Wu et al., 2019). This system
also increased the fresh and dry biomass of the metal accumulator plant by
227.27% and 178.33%, respectively. Khan & Bano (2016) identified cata
lase and oxidase enzymes secreted from the PGPR isolated from municipal
wastewater that solubilize insoluble bound phosphate and exhibit antifungal
and antibacterial activities. The use of Ag-nanoparticles with these PGPR
enhanced the levels of abscisic acid (ABA) by 34%, indole acetic acid
(IAA) by 55%, gibberellin by 82%, and proline synthesis by 70%, as well
as alleviating oxidative stress and enhancing the bioremediation capacity of
PGPR for Pb, Cd, and Ni. Table 1.3 summarizes the function of PGPR in
the remediation of heavy metal-polluted soil. Biofilms have been used to
remove heavy metals, according to studies (Yin et al., 2019). Biofilms are
characterized as bacterial communities attached to a surface or to each other
inside a matrix (Poulsen, 1999; Moussa & Algamal, 2017). Harekrushna &
Kumar (2012) investigated bacterial biofilm zinc sorption and the role of
extracellular polymeric molecules (EPS).
The microbial EPS can bind with heavy metals and protect the cells from
the hostile environment. Forming biofilms by these strains is considered a
natural strategy to maintain a favorable niche in stressful environments with
increased metals concentrations. Costley & Wallis (1999) reported the effi
ciency of biofilm in removing the heavy metals in order of Cu>Zn>Cd with
the removing efficiency of 73%, 42%, and 33% respectively. Workentine
et al. (2008) reported that metal toxicity might be reduced by biofilm by
altering their physiology for protection of sensitive chemical targets against
the reactive metal species.
1.5 ENDOPHYTIC MICROBES ASSISTED BIOREMEDIATION
Natural remediation techniques provide more environment friendly oppor
tunity for cleanup of the polluted soils and water. Phytoremediation due to
its cost-effectiveness has caught attention worldwide. It uses the natural