2019
DOI: 10.1080/09593330.2019.1593511
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Adsorptive removal of methyl orange with polyaniline nanofibers: an unconventional adsorbent for water treatment

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Cited by 25 publications
(7 citation statements)
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“…Furthermore, Khattabi et al [ 40 ] also demonstrated the moderate performance of commercially obtained activated carbon with a capacity ( q e ) of 96 mg/g; however, the capacity of PAnAC is seemingly well positioned in the list and surpasses most adsorbents. The adsorption performance of PAn and PAn/metal oxide composites [ 41 , 42 , 43 ] was low (22–111 mg/g) compared to the listed ACs (commercials: 96–267 mg/g; synthetics: 400–482 mg/g) and PAnAC (406 mg/g). Interestingly, the nitrogen-doped AC revealed a better performance than the undoped one, with capacities of 135 and 120 mg/g, respectively, supporting the argument that activated carbons doped with nitrogen are more active, as nitrogen may provide the AC with additional effective N-based functional groups, thus increasing the number of active sites to adsorb ionic substances, including organic dyes.…”
Section: Resultsmentioning
confidence: 99%
“…Furthermore, Khattabi et al [ 40 ] also demonstrated the moderate performance of commercially obtained activated carbon with a capacity ( q e ) of 96 mg/g; however, the capacity of PAnAC is seemingly well positioned in the list and surpasses most adsorbents. The adsorption performance of PAn and PAn/metal oxide composites [ 41 , 42 , 43 ] was low (22–111 mg/g) compared to the listed ACs (commercials: 96–267 mg/g; synthetics: 400–482 mg/g) and PAnAC (406 mg/g). Interestingly, the nitrogen-doped AC revealed a better performance than the undoped one, with capacities of 135 and 120 mg/g, respectively, supporting the argument that activated carbons doped with nitrogen are more active, as nitrogen may provide the AC with additional effective N-based functional groups, thus increasing the number of active sites to adsorb ionic substances, including organic dyes.…”
Section: Resultsmentioning
confidence: 99%
“…The study of the chemical structure of PANI and its derivatives POT and POA by infrared spectroscopy (FTIR) before and after the adsorption of the MO dye (Figure 12) provided important information on the mechanism of interaction between dye molecules and functional groups of the adsorbent. 10,47,48 Both polymers show characteristic bands related to the PANI structure. The peaks at 1603 and 1508 cm −1 correspond to vibrations of the C=C bond of the quinoid (Q) and benzenoid (B) rings, respectively, indicating that the structure is in the emeraldine form.…”
Section: The Mechanism Of Mo Dye Adsorption On Pani Pot and Poamentioning
confidence: 99%
“…For any targeted pollutant removal, the adsorption mechanism is influenced by the adsorbent’s chemical composition, surface area, pore size, and chemical environment . The adsorbent/adsorbate interactions can be very complicated due to the involvement of one or more interactions such as electrostatic interactions, hydrogen bonding, π–π (pi–pi) interaction, complex formation, and precipitation …”
Section: Dye Adsorption Studiesmentioning
confidence: 99%
“…51 The adsorbent/adsorbate interactions can be very complicated due to the involvement of one or more interactions such as electrostatic interactions, hydrogen bonding, π−π (pi−pi) interaction, complex formation, and precipitation. 108 The proposed adsorption mechanism for both dyes is illustrated in Figure 8. Both dyes, that is, BG and MO contain aromatic rings and surficial charge in their structures.…”
Section: Adsorption Isothermsmentioning
confidence: 99%