Integrated bipolar electrocoagulation and PVC-based ultrafiltration membrane process for palm oil mill effluent (POME) treatment

被引:6
|
作者
Aryanti P.T.P. [1 ]
Nugroho F.A. [1 ]
Anwar N. [1 ]
Rusgiyarto F. [2 ]
Phalakornkule C. [3 ,4 ]
Kadier A. [5 ,6 ]
机构
[1] Chemical Engineering Department, Faculty of Engineering, Universitas Jenderal Achmad Yani, Jl. Terusan Jenderal Sudirman, West Java, Cimahi
[2] Civil Engineering Department, Faculty of Engineering, Universitas Jenderal Achmad Yani, Jl. Terusan Jenderal Sudirman, West Java, Cimahi
[3] Department of Chemical Engineering, King Mongkut's University of Technology North Bangkok, Bangkok
[4] Research Center for Circular Products and Energy, King Mongkut's University of Technology North Bangkok, Bangkok
[5] 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
[6] Center of Materials Science and Optoelectronics Engineering, University of Chinese Academy of Sciences, Beijing
关键词
Clean technology; Electrocoagulation; POME; Tight ultrafiltration; Water reuse;
D O I
10.1016/j.chemosphere.2023.140637
中图分类号
学科分类号
摘要
In this study, the effectiveness of integrating electrocoagulation (EC) and ultrafiltration (UF) membranes for palm oil mill effluent (POME) wastewater treatment was investigated. The impact of various parameters on contaminant removal efficiency, including electrode configuration (monopolar and bipolar), number of anodes, agitation rate, and current density, was studied. The findings demonstrated that using bipolar (BP) electrodes in the EC reactor improved coagulation efficiency. However, an increase in agitation rate led to a decrease in removal efficiency. The electrode configuration of 2A-2C–2B achieved high contaminant removal with a lower electrode consumption compared to the 4A-2C and 4A-2C–2B configurations. The removal efficiencies for total dissolved solids (TDS), total suspended solids (TSS), chemical oxygen demand (COD), and biological oxygen demand (BOD) were 59.1%, 99.9%, 96.8%, and 96%, respectively. The operating cost for the electrode configuration of 2A-2C–2B was estimated to be 2.71 US$ m−3 at an effluent capacity of 50 m3 d−1 and 20 h d−1 of operating time, while the energy requirement was 6.20 kWh m−3. An increase in operating time from 5 to 24 h d−1 raised the specific operating cost from 2.17 to 2.85 US$ m−3. This study provides valuable insights into optimizing EC and UF processes for POME wastewater treatment, which could have significant implications for sustainable industrial practices. © 2023 Elsevier Ltd
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