2013
DOI: 10.1007/s12649-013-9200-8
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Simultaneous Removal of Molybdenum, Antimony and Selenium Oxyanions from Wastewater by Adsorption on Supported Magnetite

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Cited by 51 publications
(36 citation statements)
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“…A number of studies report that when pH is within the range 2-10, the sorption of Sb(V) by most iron based adsorbents increases significantly as the pH is increased from 2 to 3, maintaining the maximum sorption plateau over the pH range of 3 to 5, but decreasing significantly as the pH was increased above 5. As shown in Table 1, the optimum pH range for Sb(V) removal was 3-4 using Fe 3 O 4 [58]. Similar results were reported for the removal of Sb(V) using different iron based adsorbents, such as ferric hydroxide [37,38],hematite [48], hydrous ferric oxide [45,55], zero-valent iron [61][62][63], and Fe(III)-treated aerobic granules [23,57].…”
Section: Effect Of Phsupporting
confidence: 71%
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“…A number of studies report that when pH is within the range 2-10, the sorption of Sb(V) by most iron based adsorbents increases significantly as the pH is increased from 2 to 3, maintaining the maximum sorption plateau over the pH range of 3 to 5, but decreasing significantly as the pH was increased above 5. As shown in Table 1, the optimum pH range for Sb(V) removal was 3-4 using Fe 3 O 4 [58]. Similar results were reported for the removal of Sb(V) using different iron based adsorbents, such as ferric hydroxide [37,38],hematite [48], hydrous ferric oxide [45,55], zero-valent iron [61][62][63], and Fe(III)-treated aerobic granules [23,57].…”
Section: Effect Of Phsupporting
confidence: 71%
“…The reason is that increments in initial concentration can stimulate adsorbents to produce numerous effective sites, but the increased proportion of effective sites is much less than the increased solute concentration. Table 1 shows that several adsorbents, such as hematite-modified magnetic nanoparticles [48], FeCl 3 -modifed activated carbon [52], iron oxide-coated olivine [53], zero-valent iron [62,63], Fe(III)-loaded saponified orange waste [51] and zeolite-supported magnetite [58], can achieve significant treatment effects when the initial concentration of antimony is low (<6 mg/L). By contrast, other adsorbents, such as Fe-Zr-D201 [49], graphene oxide and its magnetite composites [54], Fe-Mn binary oxide [36,37], FeCl 3 -modifed sepiolite [32], and Fe 2 O 3 -Fe 3 O 4 /C prepared with eucalyptus wood template [60] and ferric hydroxide [37], can achieve excellent treatment effects over a wide range of initial concentrations.…”
Section: Effect Of Initial Concentration Range and Adsorbents Dosementioning
confidence: 99%
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“…The two main adsorption mechanisms are inner-sphere complex formation (ionic binding on specific adsorbent sites) and outer-sphere complex formation (electrostatics interactions, adsorbate molecules do not bind directly to the surface, but are placed in the hydration shell). MoO 2À 4 and SbðOHÞ À 6 adsorb via inner-sphere complex formation on iron oxides and SeO 2À 4 via outer-sphere complex formation (Verbinnen et al, 2013). The adsorption of AsO 3À 4 is usually considered to happen via innersphere complex formation (Mohan and Pittman, 2007), but for the adsorption of CrO 2À 4 on iron oxides, both inner-and outersphere complexes are described (Fendorf et al, 1997;Khaodhiar et al, 2000;Gallios and Vaclavikova, 2008;Adegoke et al, 2013).…”
Section: Introductionmentioning
confidence: 99%