Optimized preparation of gangue waste-based geopolymer adsorbent based on improved response surface methodology for Cd(II) removal from wastewater

被引:17
|
作者
Dong, Chaowei [1 ,2 ]
Zhou, Nan [1 ]
Zhang, Jixiong [1 ]
Lai, Wanan [1 ]
Xu, Jianfei [1 ]
Chen, Junlin [3 ]
Yu, Runhua [4 ]
Che, Yepeng [5 ]
机构
[1] China Univ Min & Technol, Sch Mines, Xuzhou 221116, Peoples R China
[2] China Univ Min & Technol, Artificial Intelligence Res Inst, Xuzhou 221116, Peoples R China
[3] Hebei Univ Technol, Arizona Coll Technol, Tianjin 300401, Peoples R China
[4] Jiangsu Prov Acad Environm Sci, Nanjing 210036, Peoples R China
[5] China Coal Energy Xinjiang Tianshan Coal Power Co, Beijing 831200, Xinjiang, Peoples R China
基金
中国国家自然科学基金;
关键词
Adsorption mechanism; Gangue waste utilization; Geopolymer adsorbents; Gray wolf optimization algorithm; Response surface method; COAL GANGUE; AQUEOUS-SOLUTION; ADSORPTION; ZEOLITE; PB(II); IONS;
D O I
10.1016/j.envres.2023.115246
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Resource utilization of gangue solid waste has become an essential research direction for green development. This study prepared a novel gangue based geopolymer adsorbent (GPA) for the removal of Cd(II) from waste-water using pretreatment gangue (PG) as the main raw material. The ANOVA indicated that the obtained quadratic model of fitness function (R2 > 0.99, P-value <0.0001) was significant and adequate, and the contribution of the three preparation conditions to the removal of Cd(II) was: calcination temperature > Na2CO3: PG ratio > water-glass solid content. The hybrid response surface method and gray wolf optimization (RSM-GWO) algorithm were adopted to acquire the optimum conditions: Na2CO3:PG ratio = 1.05, calcination tem-perature of 701 degrees C, solid content of water glass of 22.42%, and the removal efficiency of Cd(II) by GPA obtained under the optimized conditions (GPAC) was 97.84%. Adsorption kinetics, adsorption isotherms and character-ization by XRD, FTIR, Zeta potential, FSEM-EDS and BET were utilized to investigate the adsorption mechanism of GPAC on Cd(II). The results showed that the adsorption of Cd(II) from GPAC was consistent with the pseudo -second-order model (R2 = 0.9936) and the Langmuir model (R2 = 0.9988), the adsorption was a monolayer adsorption process and the computed maximum Cd(II) adsorption (50.76 mg g-1) was approximate to experi-mental results (51.47 mg g-1). Moreover, the surface morphology of GPAC was rough and porous with a specific surface area (SSA) of 18.54 m2 g-1, which provided abundant active sites, and the internal kaolinite was destroyed to produce a zeolite-like structure where surface complexation and ion exchange with Cd(II) through hydroxyl (-OH) and oxygen-containing groups (-SiOH and-AlOH) were the main adsorption mechanisms. Thus, GPAC is a lucrative adsorbent material for effective Cd(II) wastewater treatment, complying with the "high value-added" usage of solid wastes and "waste to cure poison" green sustainable development direction.
引用
收藏
页数:16
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