Post-tanning wastewater treatment using electrocoagulation: Optimization, kinetics, and settlement analysis

被引:12
作者
Villaseñor-Basulto D.L. [1 ]
Kadier A. [2 ,3 ]
Singh R. [4 ]
Navarro-Mendoza R. [1 ]
Bandala E. [5 ]
Peralta-Hernández J.M. [1 ]
机构
[1] Departamento de Química, DCNE, Universidad de Guanajuato, Cerro de la Venada s/n, Pueblito de Rocha, 36040, Guanajuato, Guanajuato
[2] Laboratory of Environmental Science and Technology, The Xinjiang Technical Institute of Physics and Chemistry, Key Laboratory of Functional Materials and Devices for Special Environments, Chinese Academy of Sciences, Urumqi
[3] Center of Materials Science and Optoelectronics Engineering, University of Chinese Academy of Sciences, Beijing
[4] Department of Environmental and Global Health, College of Public Health and Health Professions, University of Florida, Gainesville, FL
[5] Division of Hydrologic Sciences, Desert Research Institute, 755 E. Flamingo Road, Las Vegas, 89119–7363, NV
来源
Process Safety and Environmental Protection | 2022年 / 165卷
关键词
Electrocoagulation; Post-tanning process; RSM; Sludge reuse; Steel-carbon electrodes;
D O I
10.1016/j.psep.2022.08.008
中图分类号
学科分类号
摘要
Post-tanning process in the tannery industry generates complex wastewater. Continuous electrocoagulation (EC) with carbon-steel electrodes was used to treat synthetic/post-tanning wastewater. Research surface methodology, based on central composite design (RSM-CCD), was used for variables optimization and analysis of variance (ANOVA) to relate all parameters. Optimal variables were identified as initial pH 3.0, current density 6.4 mA m−2, initial dye concentration 125 mg L−1, NaCl concentration 1000 mg L−1, and inlet flow rate 176 mL min−1 to produce 71% dye removal, operational costs (OC) 0.05 US$ m−3, power consumption 1.3 kWh m−3, iron consumption 0.05 kg m−3, dye removal capacity per dissolved mg iron (qe) 4.3 mg Dye L−1 C−1 and total dissolved solids (TDS) removal 43.5%. Best process conditions were used to treat real post-tanning wastewater and resulted in carbon oxygen demand (COD) and TDS abatement (23% and 76%, respectively), as well as low OC (0.84 US$ m−3) and energy consumption (20.6 kWh m−3). Pseudo-first-order kinetic model was found fitting experimental results, having electrical energy per order (EEO) of 1 kW h m−1 order−1 with a higher k = 1.14 min−1. Scanning electron microscopy analysis suggested the presence of iron nanoparticles within the sludge. All input and output parameters resulted in statistically significant where TDS and qe were the most valued for effective pollutant removal optimization and prevention of TDS increase in treated water. The outcomes of this study suggest EC as a suitable treatment for post-tanning wastewater and further knowledge of steel-carbon EC reactor design and sludge reusing purposes. © 2022 The Institution of Chemical Engineers
引用
收藏
页码:872 / 886
页数:14
相关论文
共 70 条
[11]  
Chen Y., Jiang W., Liu Y., Chen M., He Y., Edem M.A., Wang T., Chen J., Optimization of an integrated electrocoagulation/sedimentation unit for purification of polymer-flooding sewage, J. Electroanal. Chem., 842, pp. 193-202, (2019)
[12]  
Chowdhury M., Mostafa M.G., Biswas T.K., Mandal A., Saha A.K., Characterization of the effluents from leather processing industries, Environ. Process., 2, pp. 173-187, (2015)
[13]  
Damaraju M., Bhattacharyya D., Panda T.K., Kurilla K.K., Marigold wastewater treatment in a lab-scale and a field-scale continuous bipolar-mode electrocoagulation system, J. Clean. Prod., 245, (2020)
[14]  
Daniel M., Sharpe A., Driver J., Knight A.W., Keenan P.O., Walmsley M.M., Robinson A., Zhang T., Rawson D., Results of a technology demonstration project to compare rapid aquatic toxicity screening tests in the analysis of industrial effluents, J. Environ. Monit., 6, pp. 855-865, (2004)
[15]  
Das A.K., Dewanjee S., Optimization of Extraction Using Mathematical Models and Computation, (2018)
[16]  
De La Luz-Pedro A., Martinez Prior E.F., Lopez-Araiza M.H., Jaime-Ferrer S., Estrada-Monje A., Banuelos J.A., Pollutant removal from wastewater at different stages of the tanning process by electrocoagulation, J. Chem., 2019, (2019)
[17]  
Deghles A., Kurt U., Treatment of raw tannery wastewater by electrocoagulation technique: optimization of effective parameters using Taguchi method, Desalin. Water Treat., 57, pp. 14798-14809, (2016)
[18]  
El-Ashtoukhy E.-S.Z., Amin N.K., Fouad Y.O., Hamad H.A., Intensification of a new electrocoagulation system characterized by minimum energy consumption and maximum removal efficiency of heavy metals from simulated wastewater, Chem. Eng. Process. - Process. Intensif., 154, (2020)
[19]  
Eltarahony M., Abu-Serie M., Hamad H., Zaki S., Abd-El-Haleem D., Unveiling the role of novel biogenic functionalized CuFe hybrid nanocomposites in boosting anticancer, antimicrobial and biosorption activities, Sci. Rep., 11, (2021)
[20]  
Georgiou S.D., Stylianou S., Aggarwal M., A class of composite designs for response surface methodology, Comput. Stat. Data Anal., 71, pp. 1124-1133, (2014)