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This work outlines the fabrication of a nanocomposite, namely, 1,2,4,5-benzene tetracarboxylic acid-doped polyaniline/protonated carbon nitride (H 4 BTC-PANI/pC 3 N 4 ) through a straightforward two-step process. Various advanced analytical tools validated the formation of the composite. Subsequently, the adsorption characteristics of the prepared composite for the uptake of Cr(VI) ions were assessed via batch adsorption experiments. Removal equilibrium and kinetic approaches clearly demonstrated the simulation of adsorption data via Langmuir and pseudo-second-order models. The thermodynamic analysis disclosed that the removal of Cr(VI) ions by the H 4 BTC-PANI/pC 3 N 4 material was a spontaneous, endothermic procedure associated with an increase in surface site availability randomness. It was found that by using 0.25 g/L of adsorbent dose at pH 2, almost 97.1% of the chromium was eliminated within an equilibrium time of 90 min. Furthermore, the maximum adsorbed amount was 1229 mg•g −1 , exceeding the capabilities of most similar adsorbents. The composites retained a significant adsorption capacity for Cr(VI) even after undergoing five regeneration cycles, demonstrating excellent reusability. Monte Carlo (MC) calculations were executed to search for the most stable configuration and adsorption energies of H 4 BTC on pC 3 N 4 , PANI on H 4 BTC/pC 3 N 4 , and Cr(VI) removal on H 4 BTC-PANI/pC 3 N 4 surfaces in the aqueous system. The experimental findings indicated that H 4 BTC-PANI/pC 3 N 4 holds significant promise as a cost-effective material for removing hexavalent chromium from wastewater, showcasing considerable potential for practical use.
This work outlines the fabrication of a nanocomposite, namely, 1,2,4,5-benzene tetracarboxylic acid-doped polyaniline/protonated carbon nitride (H 4 BTC-PANI/pC 3 N 4 ) through a straightforward two-step process. Various advanced analytical tools validated the formation of the composite. Subsequently, the adsorption characteristics of the prepared composite for the uptake of Cr(VI) ions were assessed via batch adsorption experiments. Removal equilibrium and kinetic approaches clearly demonstrated the simulation of adsorption data via Langmuir and pseudo-second-order models. The thermodynamic analysis disclosed that the removal of Cr(VI) ions by the H 4 BTC-PANI/pC 3 N 4 material was a spontaneous, endothermic procedure associated with an increase in surface site availability randomness. It was found that by using 0.25 g/L of adsorbent dose at pH 2, almost 97.1% of the chromium was eliminated within an equilibrium time of 90 min. Furthermore, the maximum adsorbed amount was 1229 mg•g −1 , exceeding the capabilities of most similar adsorbents. The composites retained a significant adsorption capacity for Cr(VI) even after undergoing five regeneration cycles, demonstrating excellent reusability. Monte Carlo (MC) calculations were executed to search for the most stable configuration and adsorption energies of H 4 BTC on pC 3 N 4 , PANI on H 4 BTC/pC 3 N 4 , and Cr(VI) removal on H 4 BTC-PANI/pC 3 N 4 surfaces in the aqueous system. The experimental findings indicated that H 4 BTC-PANI/pC 3 N 4 holds significant promise as a cost-effective material for removing hexavalent chromium from wastewater, showcasing considerable potential for practical use.
In this work, intelligent pH-sensitive sensors (Fe3O4/RhB@PAM) for Cr(vi) detection were successfully synthesized based on polyacrylamide (PAM) and Rhodamine B (RhB) co-modified Fe3O4 nanocomposites.
To solve the problem of heavy metal hexavalent chromium (Cr(VI)) pollution in water bodies, this study was carried out to prepare nitrogen-doped porous carbon by using bamboo shoots as the raw material and KHCO3 as the activator, which has a good ability to remove Cr(VI) from water bodies. The prepared N-doped carbon materials were characterized by thermogravimetric analysis (TGA), Fourier transform infrared spectroscopy (FT-IR), elemental analysis, and scanning electron microscopy (SEM). The results showed that the prepared carbon material had hierarchical pore structures and abundant functional groups, which is conducive to the adsorption of Cr(VI). The effects of various factors on the adsorption performance of Cr(VI), such as the carbon materials prepared under different conditions, the pH of the initial solution, the concentration of the initial solution, and the contact time between the carbon and Cr(VI), were explored. The results showed that the bamboo shoot-based nitrogen-doped carbon materials, especially BSNC-800 (prepared at 800 °C with a mass ratio of KHCO3 to bamboo shoot of 4:1), performed well in removing Cr(VI) from a water solution. The maximum adsorption of Cr(VI) by BSNC-800 under equilibrium conditions was 385.8 mg g−1 (conditions: at the pH of 2 with the initial concentration of 400 mg L−1). The adsorption kinetics and isotherms were analyzed, and the adsorption mechanism was discussed. It can be found that the adsorption of Cr(VI) by BSNC-800 fits better with the Langmuir isotherm model and the pseudo-second-order kinetic model. The adsorption mechanism between the Cr(VI)-containing solution and BSNC-800 was controlled by membrane diffusion and chemisorption. The results broaden the ways of utilizing biomass resources as precursors of carbon materials, which is significant and helpful for applying biomass carbon materials as adsorbents for wastewater treatment.
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