Sustainable activated carbon obtained as a by-product of the sugar and alcohol industry for removal of amoxicillin from aqueous solution

Juliana Schultz , Gino Capobianco , Paulo Apolinário da Silva Veiga , Mayara Regina Fornari , Ariana Rodrigues Antonangelo , Sergio Mazurek Tebcherani , Antonio Salvio Mangrich , Sidnei Antonio Pianaro

Energy, Ecology and Environment ›› 2020, Vol. 5 ›› Issue (6) : 433 -443.

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Energy, Ecology and Environment ›› 2020, Vol. 5 ›› Issue (6) : 433 -443. DOI: 10.1007/s40974-020-00173-3
Original Article

Sustainable activated carbon obtained as a by-product of the sugar and alcohol industry for removal of amoxicillin from aqueous solution

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Abstract

The alcohol and sugar industry in Brazil uses a feedstock for sucrose extraction, resulting in waste production, one of them being the sugarcane bagasse. A possible relocation for the use of this residue, produced in millions of tons annually, would be its use in the production of carbonaceous materials, such as activated carbon (AC). The purpose of this study was the production of activated carbon using a faster, simpler and more efficient process with low energy requirements and chemical reagents to obtain a material with a high surface area. The AC samples were prepared by chemical activation with ZnCl2 and carbonization at 600 °C in an oxygen-limiting atmosphere. The average specific surface area of the samples, estimated by the BET method, was 1544 m2 g−1 and the average pore size was 2.6 nm. The surface morphologies of the ACs were characterized using SEM analysis, which showed that the surfaces were irregular, with cracks, pores. The solids were also characterized by FTIR, presenting mainly stretching bands corresponding to O–H, C–O, and C=C groups. EPR analysis showed a resonance line characteristic of an organic free radical with g ~ 2.0031, which is typical of free radicals centered on carbon atoms. The material efficiency for removal of aromatic organic pollutants was evaluated in continuous-flow adsorption tests with the antibiotic amoxicillin. The method provided very satisfactory results, reducing the concentration of the antibiotic from an initial value of 1.37 × 10−3 mol L−1 to about 3.5 × 10−8 mol L−1. The concentration of the antibiotic in water, after adsorption, was therefore reduced by four to five orders of magnitude, confirming the potential application of the materials prepared in this work for the removal of antibiotics residues from the environment.

Keywords

Sugarcane bagasse / Agro-industrial waste / Continuous-flow adsorption / Environmental contaminants

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Juliana Schultz, Gino Capobianco, Paulo Apolinário da Silva Veiga, Mayara Regina Fornari, Ariana Rodrigues Antonangelo, Sergio Mazurek Tebcherani, Antonio Salvio Mangrich, Sidnei Antonio Pianaro. Sustainable activated carbon obtained as a by-product of the sugar and alcohol industry for removal of amoxicillin from aqueous solution. Energy, Ecology and Environment, 2020, 5(6): 433-443 DOI:10.1007/s40974-020-00173-3

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References

[1]

Ahmadpour A, Do DD. The preparation of activated carbons from coal by chemical and physical activation. Carbon, 1996, 34: 471-479

[2]

Ahmed MJ, Theydan SK. Physical and chemical characteristics of activated carbon prepared by pyrolysis of chemically treated date stones and its ability to adsorb organics. Powder Technol, 2012, 229: 237-245

[3]

Alnajrani MN, Alsager OA. Removal of antibiotics from water by polymer of intrinsic microporosity: isotherms, kinetics, thermodynamics, and adsorption mechanism. Sci Rep, 2020, 10: 794

[4]

Anastopoulos I, Bhatnagar A, Hameed BH, Ok YS, Omirou M. A review on waste-derived adsorbents from sugar industry for pollutant removal in water and wastewater. J Mol Liq, 2017, 240: 179-188

[5]

ANEEL (2018) Aneel Matriz Energética do Brasil. http://www2.aneel.gov.br/aplicacoes/capacidadebrasil/OperacaoCapacidadeBrasil.cfm. Accessed 22 Mar 2020

[6]

Anoop Krishnan K, Sreejalekshmi KG, Baiju RS. Nickel(II) adsorption onto biomass based activated carbon obtained from sugarcane bagasse pith. Bioresour Technol, 2011, 102: 10239-10247

[7]

Bachrun S, Ayurizka N, Hidayat AS, Arif H. Preparation and characterization of activated carbon from sugarcane bagasse by physical activation with CO2 gas. IOP Conf Ser Mater Sci Eng, 2016, 105: 1-8

[8]

Bergna D, Romar THHPH, Lassi U. Effect of some process parameters on the main properties of activated carbon produced from peat in a lab-scale process. Waste Biomass Valoriz, 2019, 10: 1-12

[9]

Bouchemal N, Belhachemi M, Merzougui Z, Addoun F. The effect of temperature and impregnation ratio on the active carbon porosity. Desalin Water Treat, 2009, 10: 115-120

[10]

Chaiwon T, Jannoey P, Channei D. Preparation of activated carbon from sugarcane bagasse waste for the adsorption equilibrium and kinetics of basic dye. Key Eng Mater, 2017, 751: 671-676

[11]

Chee-Sanford JC, Aminov RI, Krapac IJ, Garrigues-Jeanjean N, Mackie RI. Occurrence and diversity of tetracycline resistance genes in lagoons and groundwater underlying two swine production facilities. Appl Environ Microbiol, 2001, 67: 1494-1502

[12]

Chen R, Li L, Liu Z, Lu M, Wang C, Li H, Ma W, Wang S. Preparation and characterization of activated carbons from tobacco stem by chemical activation. J Air Waste Manag Assoc, 2017, 67: 713-724

[13]

Cherik D, Louhab K. Preparation of microporous activated carbon from date stones by chemical activation using zinc chloride. Energy Sources Part Recovery Util Environ Eff, 2017, 39: 1935-1941

[14]

Dalai C, Jha R, Desai VR. Rice husk and sugarcane baggase based activated carbon for iron and manganese removal. Aquat Procedia, 2015, 4: 1126-1133

[15]

Danish M, Ahmad T, Hashim R, Said N, Akhtar MN, Mohamad-Saleh J, Sulaiman O. Comparison of surface properties of wood biomass activated carbons and their application against rhodamine B and methylene blue dye. Surf Interfaces, 2018, 11: 1-13

[16]

Díaz-Díez MA MA, Gómez-Serrano V, Fernández González C, Cuerda-Correa EM, Macías-García A. Porous texture of activated carbons prepared by phosphoric acid activation of woods. Appl Surf Sci, 2004, 238: 309-313

[17]

Doumer ME, Arízaga GGC, Da Silva DA, Yamamoto CI, Novotny EH, Santos JM, Dos Santos LO, Wisniewski A, De Andrade JB, Mangrich AS. Slow pyrolysis of different Brazilian waste biomasses as sources of soil conditioners and energy, and for environmental protection. J Anal Appl Pyrolysis, 2015, 113: 434-443

[18]

Dural MU, Cavas L, Papageorgiou SK, Katsaros FK. Methylene blue adsorption on activated carbon prepared from Posidonia oceanica (L.) dead leaves: kinetics and equilibrium studies. Chem Eng J, 2011, 168: 77-85

[19]

Elizalde-velázquez A, Gómez-oliván LM, Galar-martínez M, Islas-flores H (2016) Amoxicillin in the aquatic environment, its fate and environmental risk In: Environmental health risk—hazardous factors to living species. INTEC 247–267. https://doi.org/10.5772/62049

[20]

Fang R, Huang H, Ji J, He M, Feng Q, Zhan Y, Leung DYC. Efficient MnOx supported on coconut shell activated carbon for catalytic oxidation of indoor formaldehyde at room temperature. Chem Eng J, 2018, 334: 2050-2057

[21]

Foo KY, Lee LK, Hameed BH. Preparation of activated carbon from sugarcane bagasse by microwave assisted activation for the remediation of semi-aerobic landfill leachate. Bioresour Technol, 2013, 134: 166-172

[22]

Gonçalves SPC, Strauss M, Delite FS, Clemente Z, Castro VL, Martinez DST. Activated carbon from pyrolysed sugarcane bagasse: silver nanoparticle modification and ecotoxicity assessment. Sci Total Environ, 2016, 565: 833-840

[23]

Guo Y, Tan C, Sun J, Li W, Zhang J, Zhao C. Porous activated carbons derived from waste sugarcane bagasse for CO2 adsorption. Chem Eng J, 2020, 381: 1-9

[24]

Hirsch R, Ternes T, Haberer K, Kratz KL. Occurrence of antibiotics in the aquatic environment. Sci Total Environ, 1999, 225: 109-118

[25]

IBGE—Instituto Brasileiro de Geografia e Estatística. Levantamento sistemático da produção agrícola, Pesquisa mensal de previsão e acompanhamento das safras agrícolas (2019). https://www.ibge.gov.br/estatisticas/economicas/agricultura-e-pecuaria/9201-levantamento-sistematico-da-producao-agricola.html. Accessed 3 Mar 2020

[26]

Jaguaribe EF, Medeiros LL, Barreto MCS, Araujo LP. The performance of activated carbons from sugarcane bagasse, babassu, and coconut shells in removing residual chlorine. Braz J Chem Eng, 2005, 22: 41-47

[27]

Jain A, Tripathi SK. Nano-porous activated carbon from sugarcane waste for supercapacitor application. J Energy Storage, 2015, 4: 121-127

[28]

Kalderis D, Bethanis S, Paraskeva P, Diamadopoulos E. Production of activated carbon from bagasse and rice husk by a single-stage chemical activation method at low retention times. Bioresour Technol, 2008, 99: 6809-6816

[29]

Kaushik A, Basu S, Singh K, Batra VS, Balakrishnan M. Activated carbon from sugarcane bagasse ash for melanoidins recovery. J Environ Manag, 2017, 200: 29-34

[30]

Kümmerer K. Resistance in the environment. J Antimicrob Chemother, 2004, 54: 311-320

[31]

Limousy L, Ghouma I, Ouederni A, Jeguirim M. Amoxicillin removal from aqueous solution using activated carbon prepared by chemical activation of olive stone. Environ Sci Pollut Res, 2017, 24: 9993-10004

[32]

Lu X, Jaroniec M, Madey R. Use of adsorption isotherms of light normal alkanes for characterizing microporous activated carbons. Langmuir, 1991, 7: 173-177

[33]

Ma HT, Ho VTT, Pham NB, Nguyen DC, Vo KTD, Ly HC, Phan TD. Effect of the carbonization and activation processes on the adsorption capacity of rice husk activated carbon. Vietnam J Sci Technol, 2017, 55: 485-493

[34]

Mahamad MN, Zaini MAA, Zakaria ZA. Preparation and characterization of activated carbon from pineapple waste biomass for dye removal. Int Biodeterior Biodegrad, 2015, 102: 274-280

[35]

Marzbali MH, Esmaieli M. Fixed bed adsorption of tetracycline on a mesoporous activated carbon: experimental study and neuro-fuzzy modeling. J Appl Res Technol, 2017, 15: 454-463

[36]

Matos TTS, Schultz J, Khan MY, Zanoelo EF, Mangrich AS, Araújo BR, Navickiene S, Romão LPC. Using magnetized (Fe3O4/biochar nanocomposites) and activated biochar as adsorbents to remove two neuro-active pesticides from waters. J Braz Chem Soc, 2017, 28: 1975-1987

[37]

Matos TTS, Mangrich AS, Cardoso EMC, Schultz J, Fornari MR, Wisniewski A, Carregosa ISC. Electron paramagnetic resonance (EPR) spectroscopy as a tool for the characterization of biochar from guava waste. J Soils Sediments, 2019, 19: 286-295

[38]

Mcintyre AD, Papic MM. Pyrolysis of municipal solid waste. Can J Chem Eng, 1974, 52: 263-272

[39]

Mohammadi A, Kazemipour M, Ranjbar H, Walker RB, Ansari M. Amoxicillin removal from aqueous media using multi-walled carbon nanotubes. Fuller Nanotub Carbon Nanostruct, 2015, 23: 165-169

[40]

Mohtashami SA, Asasian Kolur N, Kaghazchi T, Asadi-Kesheh R, Soleimani M. Optimization of sugarcane bagasse activation to achieve adsorbent with high affinity towards phenol. Turk J Chem, 2018, 42: 1720-1735

[41]

Molina-Sabio M, Rodríguez-Reinoso F. Role of chemical activation in the development of carbon porosity. Colloids Surf Physicochem Eng Asp, 2004, 241: 15-25

[42]

Moreno-Piraján JC, Giraldo L. Study of activated carbons by pyrolysis of cassava peel in the presence of chloride zinc. J Anal Appl Pyrolysis, 2010, 87: 288-290

[43]

Moussavi G, Alahabadi A, Yaghmaeian K, Eskandari M. Preparation, characterization and adsorption potential of the NH4Cl-induced activated carbon for the removal of amoxicillin antibiotic from water. Chem Eng J, 2013, 217: 119-128

[44]

Nanda S, Dalai AK, Berruti F, Kozinski JA. Biochar as an exceptional bioresource for energy, agronomy, carbon sequestration, activated carbon and specialty materials. Waste Biomass Valoriz, 2016, 7: 201-235

[45]

Noor AB, Asri M, Mohd B. Textural characteristics of activated carbons prepared from oil palm shells activated with ZnCl2 and pyrolysis under nitrogen and carbon dioxide. J Phys Sci, 2008, 19: 93-104

[46]

Pachauri P, Falwariya R, Vyas S, Maheshwari M, Vyas RK, Gupta AB. Removal of amoxicillin in wastewater using adsorption by powdered and granular activated carbon and oxidation with hydrogen peroxide. Nat Environ Pollut Technol, 2009, 8: 8

[47]

Pezoti O Jr, Cazetta AL, Souza IPAF, Bedin KC, Martins AC, Silva TL, Almeida VC. Adsorption studies of methylene blue onto ZnCl2-activated carbon produced from buriti shells (Mauritia flexuosa L.). J Ind Eng Chem, 2014, 20: 4401-4407

[48]

Pouretedal HR, Sadegh N. Effective removal of amoxicillin, cephalexin, tetracycline and penicillin G from aqueous solutions using activated carbon nanoparticles prepared from vine wood. J Water Process Eng, 2014, 1: 64-73

[49]

Prola L, Bach-Toledo L, Schultz J, Mangrich A, Peralta-Zamora P. Synthesis, characterization, and synergic photocatalytic activity of amorphous TiO2/chitosan carbon microspheres. J Braz Chem Soc, 2020, 31: 1306-1316

[50]

Putra EK, Pranowo R, Sunarso J, Indraswati N, Ismadji S. Performance of activated carbon and bentonite for adsorption of amoxicillin from wastewater: mechanisms, isotherms and kinetics. Water Res, 2009, 43: 2419-2430

[51]

Qin J, Cheng Y, Sun M, Yan L, Shen G. Catalytic degradation of the soil fumigant 1,3-dichloropropene in aqueous biochar slurry. Sci Total Environ, 2016, 569–570: 1-8

[52]

Ravichandran P, Sugumaran P, Seshadri S, Basta AH. Optimizing the route for production of activated carbon from Casuarina equisetifolia fruit waste. R Soc Open Sci, 2018

[53]

Rodríguez-Reinoso F, Nakagawa Y, Silvestre-Albero J, Juárez-Galán JM, Molina-Sabio M. Correlation of methane uptake with microporosity and surface area of chemically activated carbons. Microporous Mesoporous Mater, 2008, 115: 603-608

[54]

Sabio E, González E, González JF, González-García CM, Ramiro A, Gañan J. Thermal regeneration of activated carbon saturated with p-nitrophenol. Carbon, 2004, 42: 2285-2293

[55]

Saka C. BET, TG–DTG, FT-IR, SEM, iodine number analysis and preparation of activated carbon from acorn shell by chemical activation with ZnCl2. J Anal Appl Pyrolysis, 2012, 95: 21-24

[56]

Sales FRP, Serra RBG, Figueirêdo GJA, de Hora PHA, da Sousa AC. Wastewater treatment using adsorption process in column for agricultural purposes. Rev Ambiente Água, 2018, 14: 1-9

[57]

Saucier C, Karthickeyan P, Ranjithkumar V, Lima EC, dos Reis GS, de Brum IAS. Efficient removal of amoxicillin and paracetamol from aqueous solutions using magnetic activated carbon. Environ Sci Pollut Res, 2017, 24: 5918-5932

[58]

Sayğılı H, Güzel F, Önal Y. Conversion of grape industrial processing waste to activated carbon sorbent and its performance in cationic and anionic dyes adsorption. J Clean Prod, 2015, 93: 84-93

[59]

Sing KSW, Everett DH, Haul RAW, Moscou L, Pierotti RA, Rouquerol J, Siemieniewska T. Reportin physisorption data for gás/solid systems with special reference to the determination of surface area and porosity. Pure Appl Chem, 1985, 57: 603-619

[60]

Sivachidambaram M, Vijaya JJ, Kennedy LJ, Jothiramalingam R, Al-Lohedan HA, Munusamy MA, Elanthamilan E, Merlin JP. Preparation and characterization of activated carbon derived from the Borassus flabellifer flower as an electrode material for supercapacitor applications. New J Chem, 2017, 41: 3939-3949

[61]

Sun M, Hong L. Impacts of the pendant functional groups of cellulose precursor on the generation of pore structures of activated carbons. Carbon, 2011, 49: 2173-2180

[62]

Thuan TV, Thinh PV, Quynh BTP, Cong HT, Tam DTT, Thuan VN, Bach LG. Production of activated carbon from sugarcane bagasse by chemical activation with ZnCl2: preparation and characterization study. Res J Chem Sci, 2016, 6: 42-47

[63]

Tripathi N, Hills CD, Singh RS, Atkinson CJ. Biomass waste utilisation in low-carbon products: harnessing a major potential resource. Npj Clim Atmos Sci, 2019, 35: 1-10

[64]

Ukanwa KS, Patchigolla K, Sakrabani R, Anthony E, Mandavgane S. A review of chemicals to produce activated carbon from agricultural waste biomass. Sustainability, 2019, 11: 1-35

[65]

Veiga PAS, Schultz J, Matos TTS, Fornari MR, Costa TG, Meurer L, Mangrich AS. Production of high-performance biochar using a simple and low-cost method: optimization of pyrolysis parameters and evaluation for water treatment. J Anal Appl Pyrolysis, 2020

[66]

Wang H, Wang B, Zhao Q, Zhao Y, Fu C, Feng X, Wang N, Su M, Tang C, Jiang F, Zhou Y, Chen Y, Jiang Q. Antibiotic body burden of chinese school children: a multisite biomonitoring-based study. Environ Sci Technol, 2015, 49: 5070-5079

[67]

Wang H, Tang C, Yang J, Wang N, Jiang F, Xia Q, He G, Chen Y, Jiang Q. Predictors of urinary antibiotics in children of Shanghai and health risk assessment. Environ Int, 2018, 121: 507-514

[68]

Welfle A. Biomass and bioenergy Balancing growing global bioenergy resource demands—Brazil’s biomass potential and the availability of resource for trade. Biomass Bioenergy, 2017, 105: 83-95

[69]

Yaghmaeian K, Moussavi G, Alahabadi A. Removal of amoxicillin from contaminated water using NH4Cl-activated carbon: continuous flow fixed-bed adsorption and catalytic ozonation regeneration. Chem Eng J, 2014, 236: 538-544

[70]

Yang SF, Lin CF, Wu CJ, Ng KK, Yu-Chen Lin A, Andy Hong PK. Fate of sulfonamide antibiotics in contact with activated sludge—sorption and biodegradation. Water Res, 2012, 46: 1301-1308

Funding

Conselho Nacional de Desenvolvimento Científico e Tecnológico(553338/2010-2)

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