Textile Azo Dye Removal Using a Quaternary Ammonium Anion Exchanger Prepared From Sugarcane Bagasse

Author:

Tanure Natália Roberta Marques1,Soares Liliane Catone1,Maia Luisa Cardoso1,Elias Megg Madonyk Cota1,Xavier Amália Luísa Pedrosa2,Adarme Oscar Fernando Herrera3,Ferreira Guilherme Max Dias4,de Azevedo Eduardo Ribeiro5,da Silva Luis Henrique Mendes6,Gurgel Leandro Vinícius Alves1

Affiliation:

1. aDepartment of Chemistry, Institute of Exact and Biological Sciences, Federal University of Ouro Preto, Campus Universitário Morro do Cruzeiro, Rua Quatro, 786, Bauxita, 35402-136, Ouro Preto, Minas Gerais, Brazil

2. bFederation of Cargo Transport Companies of the State of Minas Gerais, Avenida Antônio Abrahão Caram, 728, Pampulha, 31275-000, Belo Horizonte, Minas Gerais, Brazil

3. cSchool of Agricultural Engineering, University of Campinas, Avenida Candido Rondon, 501, 13083-875, Cidade Universitária, Campinas, São Paulo, Brazil

4. dDepartment of Chemistry, Institute of Natural Sciences, Federal University of Lavras, Campus Universitário, 37200-000, Lavras, Minas Gerais, Brazil

5. eDepartment of Physics and Interdisciplinary Science, São Carlos Institute of Physics, University of São Paulo, Avenida Trabalhador São-carlense, 400, Parque Arnold Schimidt 13566-590, São Carlos, São Paulo, Brazil

6. fDepartment of Chemistry, Federal University of Viçosa, Avenida Peter Henry Rolfs, s/n, Campus Universitário, 36570-900, Viçosa, Minas Gerais, Brazil

Abstract

Water contamination with textile dyes is still a prominent environmental challenge today. Sugarcane bagasse (SB) is the largest agro-industrial residue in Brazil, and a chemical modification can transform it into a value-added by-product. This study investigated the adsorption of remazol golden yellow (RGY) RNL on chemically modified SB (STEA) with epichlorohydrin and triethylamine. STEA was characterized by elemental C, H, N, and Cl analysis, 13C solid-state nuclear magnetic resonance spectroscopy, and specific surface area and pore size distribution. The batch kinetics and isotherm were modelled with the intraparticle diffusion, Boyd, and homogeneous surface diffusion models and Langmuir, Redlich–Peterson, and Dubinin–Radushkevich models, respectively. The maximum adsorption capacity of RGY on STEA was 369.2 mg g−1. The interactions between RGY molecules and STEA sites were investigated by infrared spectroscopy. The thermodynamic parameters indicated that adsorption of RGY on STEA was an exothermic (ΔadsH° = −12 ± 5 kJ mol−1), spontaneous (ΔadsG° = −31 ± 3 kJ mol−1), and entropically driven (TΔadsS° = 19 ± 7 kJ mol−1) process. The fixed-bed column packed with STEA was operated for 415, 390, and 315 min in each consecutive cycle, with adsorption capacities of 422, 371, and 332 mg g−1, respectively. Desorption efficiencies ranged between 59 and 72% and re-adsorption efficiencies ranged from 79 to 88%.

Publisher

Royal Society of Chemistry

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