2019
DOI: 10.1016/j.jece.2019.102901
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Synthesis and adsorption behavior of mesoporous alumina and Fe-doped alumina for the removal of dominant arsenic species in contaminated waters

Abstract: Highlights Mesoporous Al2O3 and Fe-Al2O3 were synthesized by a sol-gel methodology. Mesoporous synthesized materials were effective As(III) and As(V) adsorbents. Mesoporous alumina showed better performance than commercial alumina. Mesoporous Al 2 O 3 Sol-gel synthesisEvaporation Induced Self-Assembly (EISA)

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Cited by 52 publications
(20 citation statements)
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“…For fresh Ca85Al15, the characteristic peaks at 864, 1430, and 1475 cm –1 were all assigned to CO 3 2– , , and the adsorption peak located at 3642 cm –1 corresponded to the O–H group, which might result from the residual of amorphous CaCO 3 and water adsorbed during the cooling process of fresh Ca85Al15 preparation. More importantly, the adsorption peak at 829 cm –1 related to the Al–O stretching vibration of Ca85Al15 occurred to slightly shift to 839 cm –1 after arsenic adsorption at 1200 °C for 30 min, suggesting the vibration of the As­(V)–O overlap with the Al–O group. , Furthermore, a new characteristic peak appeared at 875 cm –1 after arsenic adsorption, which could be assigned to the As­(V)–O symmetric stretch. , Thus, it can be inferred that the arsenic vapor (As 3+ ) was converted to the arsenic compound (As 5+ ) during arsenic adsorption. XRD results further confirmed the inference.…”
Section: Resultsmentioning
confidence: 95%
See 1 more Smart Citation
“…For fresh Ca85Al15, the characteristic peaks at 864, 1430, and 1475 cm –1 were all assigned to CO 3 2– , , and the adsorption peak located at 3642 cm –1 corresponded to the O–H group, which might result from the residual of amorphous CaCO 3 and water adsorbed during the cooling process of fresh Ca85Al15 preparation. More importantly, the adsorption peak at 829 cm –1 related to the Al–O stretching vibration of Ca85Al15 occurred to slightly shift to 839 cm –1 after arsenic adsorption at 1200 °C for 30 min, suggesting the vibration of the As­(V)–O overlap with the Al–O group. , Furthermore, a new characteristic peak appeared at 875 cm –1 after arsenic adsorption, which could be assigned to the As­(V)–O symmetric stretch. , Thus, it can be inferred that the arsenic vapor (As 3+ ) was converted to the arsenic compound (As 5+ ) during arsenic adsorption. XRD results further confirmed the inference.…”
Section: Resultsmentioning
confidence: 95%
“…More importantly, the adsorption peak at 829 cm −1 related to the Al−O stretching vibration of Ca85Al15 40 occurred to slightly shift to 839 cm −1 after arsenic adsorption at 1200 °C for 30 min, suggesting the vibration of the As(V)−O overlap with the Al−O group. 41,42 Furthermore, a new characteristic peak appeared at 875 cm −1 after arsenic adsorption, which could be assigned to the As(V)−O symmetric stretch. 43,44 Thus, it can be inferred that the arsenic vapor (As 3+ ) was converted to the arsenic compound (As 5+ ) during arsenic adsorption.…”
Section: Introductionmentioning
confidence: 99%
“…These features are the basis for a powerful adsorbent. Inchaurrondo et al synthesized ordered MA to remove As(V) [18]. Li et al used MA as an adsorbent to remove Cr(VI) [19].…”
Section: Introductionmentioning
confidence: 99%
“…Other studies uses alumina and iron doped alumnia [18] to effectively remove arsenic Many techniques for developing cheaper metal adsorbents, such as microbial biomass, bio-sorbents, sponge, various by-products, and resins have been investigated [13], [19], [20]. Among the different sorbents, waste plant material is promising, since it reuses and valorise a waste.…”
Section: Introductionmentioning
confidence: 99%