Effect of oxidated golden shower on the adsorption of diclofenac sodium in wastewater

被引:0
作者
Arliyani, Isni [1 ,2 ]
Syaifuddin, Mohammad [1 ]
Ni'am, Achmad Chusnun [3 ]
Murti, Restu Hikmah Ayu [4 ]
Jawwad, Muhammad Abdus Salam [4 ]
You, Sheng-Jie [5 ]
Kuncoro, Eko Prasetyo [6 ]
Wang, Ya-Fen [5 ]
机构
[1] Inst Teknol Sepuluh Nopember, Dept Environm Engn, Surabaya, Indonesia
[2] INBIO Indonesia, Bioinformat Res Ctr, Malang, Indonesia
[3] Inst Teknol Adhi Tama Surabaya, Dept Environm Engn, Surabaya, Indonesia
[4] Univ Pembangunan Nas Vet Jawa Timur, Dept Environm Engn, Surabaya, Indonesia
[5] Chung Yuan Christian Univ, Dept Environm Engn, Zhongli, Taiwan
[6] Airlangga Univ, Dept Biol, Surabaya, Indonesia
关键词
adsorbent; adsorption; batch; diclofenac sodium; isotherm; kinetic; ACTIVATED CARBON; AQUEOUS-SOLUTIONS; FUNCTIONAL-GROUPS; REMOVAL; PHARMACEUTICALS; ADSORBENTS; OXIDE;
D O I
10.1002/tqem.22140
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
This research aimed to modify activated carbon into oxidated activated carbon because it can effectively remove diclofenac sodium (DCF) and increase the adsorption capability. In this study of the several variations of initial concentration and contact time, those variations affected the optimal result. To determine, the removal efficiency of diclofenac sodium used Golden Shower Activated Carbon based on the contact time variation and the optimum contact time compared to Golden Shower Oxidated Activated Carbon as adsorbent on the batch method and to know the isotherm model and the kinetic model of the adsorbent on the adsorption in diclofenac sodium solution. The pHPZC for GSHAC and GSHOAC were 2.4 and 9.3. The optimum contact time for GSHAC was 225 min with the capacity (qt = 184.71 mg/g). The optimum contact time for GSHOAC was 169 min with the capacity (qt = 188.34 mg/g). The Isotherm model, kinetics model, and the physical characterization of the biosorbent were thoroughly investigated. The isotherm model chosen in the adsorption process for GSHAC and GSHOAC was the Langmuir model (R2 = 0.985 and R2 = 0.973). The pseudo-second-order for GSHAC and GSHOAC was confirmed to be a kinetic pseudo-second-order model of the adsorption with R2 values of 0.9566 and 0.9986. The model represents that the reaction from the adsorbent to the solution was double the initial concentration. Based on SEM analysis after the adsorption process, it was found that flakes of adsorbent before adsorption had many layers of pores, causing an irregular texture after adsorption showed that GSHAC and GSHOAC were fragmented and had many layers of pores that were closed and tight because it adsorbed DCF.
引用
收藏
页码:505 / 516
页数:12
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