Immobilized <italic>Lentinus edodes</italic> residue as absorbent for the enhancement of cadmium adsorption performance

doi:10.1007/s11783-012-0429-4

Front Envir Sci Eng

2012, Vol. 6

Issue (4) : 498-508 https://doi.org/10.1007/s11783-012-0429-4

RESEARCH ARTICLE

Immobilized Lentinus edodes residue as absorbent for the enhancement of cadmium adsorption performance

Pei MA^1,2, Dan ZHANG³(

)

1. Institute of Geographic Sciences and Natural Resources Research, Chinese Academy of Sciences, Beijing 100101, China; 2. Graduate University of Chinese Academy of Sciences, Beijing 100049, China; 3. Institute of Mountain Hazards and Environment, Chinese Academy of Sciences and Ministry of Water Conservancy, Chengdu 610041, China

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Abstract

To investigate the potential use of Lentinus edodes (L. edodes) residue for Cd²⁺ adsorption, poly alcohol Na alginate (PVA) was applied to immobilize it. The parameters including contact time, pH, adsorbent dosages, and coexisting metal ions were studied. The suitable pH for immobilized L. edodes was 4–7 wider than that for raw L. edodes (pH 6–7). In the presence of Pb²⁺ concentration varying from 0 to 30 mg·L^-1, the Cd²⁺ adsorption ratios declined by 6.71% and 47.45% for immobilized and raw L. edodes, respectively. While, with the coexisting ion Cu²⁺ concentration varied from 0 to 30 mg·L^-1, the Cd²⁺ adsorption ratios declined by 12.97% and 50.56% for immobilized and raw L. edodes, respectively. The Cd²⁺ adsorption isotherms in single–metal and dual-metal solutions were analyzed by using Langmuir, Freundlich, and Dubinin–Radushkevich models. The Cd²⁺ adsorption capacities (q_m) in single-metal solution were 6.448 mg·L^-1 and 2.832 mg·L^-1 for immobilized and raw L. edodes, respectively. The q_m of immobilized L. edodes were 1.850 mg Cd·g^-1 in Cd²⁺ + Pb²⁺ solution and 3.961 mg Cd·g^-1 in Cd²⁺ + Cu²⁺ solution, respectively. The Cd²⁺ adsorption processes subjected to both adsorbents follow pseudo-second-order model. Mechanism study showed the functional group of L. edodes was –OH, –NH, –CO, and PVA played an important role in metal adsorbing. Mining wastewater treatment test showed that PVA–SA-immobilized L. edodes was effective in mixed pollutant treatment even for wastewater containing metal ions in very low concentration.

Keywords immobilization Lentinus edodes residue competitive adsorption isotherm

Corresponding Author(s): ZHANG Dan,Email:daniezhang@imde.ac.cn

Issue Date: 01 August 2012

Cite this article:

Pei MA,Dan ZHANG. Immobilized Lentinus edodes residue as absorbent for the enhancement of cadmium adsorption performance[J]. Front Envir Sci Eng, 2012, 6(4): 498-508.

URL:

https://academic.hep.com.cn/fese/EN/10.1007/s11783-012-0429-4
https://academic.hep.com.cn/fese/EN/Y2012/V6/I4/498

Fig.1 Effect of contact time on Cd adsorption with the raw and the PVA–SA-immobilized ( = 5 mg·L; biomass: 4 g·L of the raw . , 8 g·L of the immobilized . ; pH of 6; 25°C)

Fig.2 Effect of pH on Cd adsorption with the raw and the PVA–SA-immobilized ( = 5 mg·L; biomass: 4 g·L of the raw . , 8 g·L of the immobilized . ; contact time: 1 h for the raw , 7 h for the immobilized ; 25°C)

Fig.3 Effect of adsorbent dosage on the adsorption of Cd ( = 5 mg·L; contact time: 1 h for the raw , 7 h for the immobilized ; pH of 6; 25°C)

Fig.4 (a) Effect of the existence of Pb on Cd adsorption with the raw and the PVA-SA-immobilized ; (b) effect of the existence of Cu on Cd adsorption with the raw and the PVA-SA-immobilized (concentration of Cd 10 mg·L; biomass: 4 g·L of the raw . , 8 g·L of the immobilized . ; contact time: 1 h for the raw , 7 h for the immobilized ; pH of 6; 25°C)

Tab.1 Parameters of pseudo-second-order kinetic for metal adsorption

Fig.5 Adsorption isotherms of Cd in single-metal solution (biomass: 4 g·L of the raw , 8 g·L of the immobilized ; contact time: 1 h for the raw , 7 h for the immobilized ; pH of 6; 25°C)

Fig.6 (a) Adsorption isotherms of metal ions in Cd + Pb solution; (b) adsorption isotherms of metal ions in Cd + Cu solution (biomass: 4 g·L of the raw , 8 g·L of the immobilized ; the for Pb/Cu was 10 mg·L; contact time: 1 h for the raw , 7 h for immobilized ; pH of 6; 25°C)

Tab.2 Parameters of isotherm models for cadmium adsorption in single-metal solution

Tab.3 Parameters of isotherm models for cadmium adsorption in dual-metal solution on immobilized

Fig.7 (a) FTIR spectra of powder before and after adsorbing Cd; (b) FTIR spectra of PVA–SA-immobilized powder before and after adsorbing Cd

Tab.4 Water quality analysis of flotation wastewater from Huili zinc ore before and after treated by the PVA–SA-immobilized

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