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Sustainable synthesis of nanoscale zerovalent iron particles for environmental
remediation
Yukti Monga,[a]† Pawan Kumar,[b]† Rakesh K. Sharma,[a]* Jan Filip,[b] Rajender S. Varma,[b]
Radek Zbořil,[b]* and Manoj B. Gawande[b][c]*
ChemSusChem 2020, DOI: 10.1002/cssc.202000290
Figure 1. Some advantages of bio-based methods.
Figure 2. The core–shell model of nZVI and schematic representation of the reaction
mechanisms. Adapted from references [18, 22].
Figure 3. Comparison of different methods for synthesis of iron nanoparticles and their
advantage and disadvantage.
Figure 4. Various capping and reducing agents present in tea- and grape extracts identified
with GC-MS and IR.[39-40]
Figure 5. The general scheme of biochar-zerovalent iron (BC-ZVI) derived from corn.
Reprinted from ref. [46] Copyright 2017 American Chemical Society.
Figure 6. Schematic representation of interaction of Gram-positive and Gram-negative bacteria
with nano zerovalent iron (nZVI), Fe2+ and Fe3+ ions. Reprinted from ref. [58]; Copyright 2013
Royal Society of Chemistry).
Figure 7. a) Schematic depiction of chitosan-modified nanoparticles.[72] b) Schematic diagram
of amino acid-mediated synthesis of surface modified Fe0 nanoparticles.
Figure 8. Reductive degradation mechanism for the removal of Orange II by core–shell
structured Fe NPs. (Adapted from ref. [84] Copyright 2015 Elsevier).
Figure 9. Schematic illustration of ultrasound-assisted cavitations and dye degradation mechanism
by nZVI-containing system. Reprinted from ref. [85] Copyright 2017 Elsevier b). Degradation
pathway for malachite green (MG) and methylene blue (MB) on nZVI. (Adapted from ref. [85])
Figure 10. The schematic diagram for the removal mechanism of Cr(VI) by nZVI particles.
(Adapted from ref. [104] Copyright 2017 Elsevier)
Figure 11. The mechanism for the enhanced Cr(VI) removal by nZVI particles with bio-
amended iron corrosion: bio-induced iron corrosion, bio-reduction of Fe(III), growth of the
positive corrosion, reduction of Cr(VI) to Cr(III), reactive sites passivated by Cr(III) precipitates.
Reprinted from ref. [105] Copyright 2016 Elsevier.

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Sustainable synthesis of nanoscale zerovalent iron particles for environmental remediation

  • 1. Sustainable synthesis of nanoscale zerovalent iron particles for environmental remediation Yukti Monga,[a]† Pawan Kumar,[b]† Rakesh K. Sharma,[a]* Jan Filip,[b] Rajender S. Varma,[b] Radek Zbořil,[b]* and Manoj B. Gawande[b][c]* ChemSusChem 2020, DOI: 10.1002/cssc.202000290
  • 2. Figure 1. Some advantages of bio-based methods.
  • 3. Figure 2. The core–shell model of nZVI and schematic representation of the reaction mechanisms. Adapted from references [18, 22].
  • 4. Figure 3. Comparison of different methods for synthesis of iron nanoparticles and their advantage and disadvantage.
  • 5. Figure 4. Various capping and reducing agents present in tea- and grape extracts identified with GC-MS and IR.[39-40]
  • 6. Figure 5. The general scheme of biochar-zerovalent iron (BC-ZVI) derived from corn. Reprinted from ref. [46] Copyright 2017 American Chemical Society.
  • 7. Figure 6. Schematic representation of interaction of Gram-positive and Gram-negative bacteria with nano zerovalent iron (nZVI), Fe2+ and Fe3+ ions. Reprinted from ref. [58]; Copyright 2013 Royal Society of Chemistry).
  • 8. Figure 7. a) Schematic depiction of chitosan-modified nanoparticles.[72] b) Schematic diagram of amino acid-mediated synthesis of surface modified Fe0 nanoparticles.
  • 9. Figure 8. Reductive degradation mechanism for the removal of Orange II by core–shell structured Fe NPs. (Adapted from ref. [84] Copyright 2015 Elsevier).
  • 10. Figure 9. Schematic illustration of ultrasound-assisted cavitations and dye degradation mechanism by nZVI-containing system. Reprinted from ref. [85] Copyright 2017 Elsevier b). Degradation pathway for malachite green (MG) and methylene blue (MB) on nZVI. (Adapted from ref. [85])
  • 11. Figure 10. The schematic diagram for the removal mechanism of Cr(VI) by nZVI particles. (Adapted from ref. [104] Copyright 2017 Elsevier)
  • 12. Figure 11. The mechanism for the enhanced Cr(VI) removal by nZVI particles with bio- amended iron corrosion: bio-induced iron corrosion, bio-reduction of Fe(III), growth of the positive corrosion, reduction of Cr(VI) to Cr(III), reactive sites passivated by Cr(III) precipitates. Reprinted from ref. [105] Copyright 2016 Elsevier.