|
|
|
|
LEADER |
03364nam a2200565Ia 4500 |
001 |
10.1007-s11270-022-05616-7 |
008 |
220510s2022 CNT 000 0 und d |
020 |
|
|
|a 00496979 (ISSN)
|
245 |
1 |
0 |
|a Softwood-derived Biochar as a Green Material for the Recovery of Environmental Media Contaminated with Potentially Toxic Elements
|
260 |
|
0 |
|b Springer Science and Business Media Deutschland GmbH
|c 2022
|
856 |
|
|
|z View Fulltext in Publisher
|u https://doi.org/10.1007/s11270-022-05616-7
|
520 |
3 |
|
|a In this study, the effectiveness of softwood-derived biochar (BC) in the retention of potentially toxic elements (PTE, i.e., Cu(II), Pb(II), As(V), and Sb(V)) was evaluated at different pH values (4.5, 6.0, and 7.0), along with its capacity to alleviate PTE phytotoxicity. At all pH values, sorption and kinetic isotherms followed the trend: Pb(II) (e.g., ~ 0.56 mmol g−1 at pH 6.0) > Cu(II) (e.g., ~ 0.33 mmol g−1 at pH 6.0) > As(V) (e.g., ~ 0.29 mmol g−1 at pH 6.0) > Sb(V) (e.g. ~ 0.24 mmol g−1 at pH 6.0). Kinetic data strongly correlated with the pseudo-second-order kinetic equation; Langmuir and Freundlich isotherm models suggested monolayer sorption of Cu(II), Pb(II), and As(V) onto the BC surface and the interaction of Sb(V) with BC sites characterized by distinct sorption energy (i.e., multilayer sorption). Scanning electron microscopy (SEM) with energy-dispersive X-ray (EDX) analysis of PTE-saturated BC showed that Pb(II) was mainly associated with O, Sb(V) with Ca and Fe, while Cu(II) and As(V) with Fe and O. This suggested that hydroxyl and carboxyl functional groups, amorphous Fe oxy-hydroxides, as well as PTE precipitation with BC components were likely responsible for BC sorption capacity. Treatment of PTE-saturated BC with Ca(NO3)2 and a range of environmentally relevant organic acids indicated that 6–11% of PTE were loosely bound and easily exchangeable, while up to 60% could be mobilized by the organic acids. Hydroponic plant-growth experiments using triticale plants showed that BC stimulated plant growth in the presence of PTE and reduced their phytotoxicity. © 2022, The Author(s).
|
650 |
0 |
4 |
|a Adsorption
|
650 |
0 |
4 |
|a Adsorption isotherms
|
650 |
0 |
4 |
|a Antimony compounds
|
650 |
0 |
4 |
|a Biochar
|
650 |
0 |
4 |
|a Biochar
|
650 |
0 |
4 |
|a Calcium compounds
|
650 |
0 |
4 |
|a Copper compounds
|
650 |
0 |
4 |
|a Green materials
|
650 |
0 |
4 |
|a Integral equations
|
650 |
0 |
4 |
|a Iron compounds
|
650 |
0 |
4 |
|a Kinetics
|
650 |
0 |
4 |
|a Lead compounds
|
650 |
0 |
4 |
|a Monolayers
|
650 |
0 |
4 |
|a Organic acids
|
650 |
0 |
4 |
|a pH
|
650 |
0 |
4 |
|a pH value
|
650 |
0 |
4 |
|a Phytotoxicity
|
650 |
0 |
4 |
|a Phytotoxicity
|
650 |
0 |
4 |
|a Plant growth
|
650 |
0 |
4 |
|a Potentially toxic elements
|
650 |
0 |
4 |
|a PTE
|
650 |
0 |
4 |
|a PTE
|
650 |
0 |
4 |
|a PTE release
|
650 |
0 |
4 |
|a PTE release
|
650 |
0 |
4 |
|a Scanning electron microscopy
|
650 |
0 |
4 |
|a Scanning Electron Microscopy-Energy Dispersive X-ray analysis
|
650 |
0 |
4 |
|a SEM–EDX analysis
|
650 |
0 |
4 |
|a Softwoods
|
650 |
0 |
4 |
|a Sorption isotherms
|
650 |
0 |
4 |
|a Sorption isotherms
|
700 |
1 |
|
|a Castaldi, P.
|e author
|
700 |
1 |
|
|a Diquattro, S.
|e author
|
700 |
1 |
|
|a Garau, G.
|e author
|
700 |
1 |
|
|a Garau, M.
|e author
|
700 |
1 |
|
|a Lauro, G.P.
|e author
|
700 |
1 |
|
|a Pinna, M.V.
|e author
|
700 |
1 |
|
|a Senette, C.
|e author
|
773 |
|
|
|t Water, Air, and Soil Pollution
|