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Preparation of multi-modified/carbonized/gelatinized starch and its de-risking effect on Cd(II) and hymexazol in wastewater.
Deng, Hongyan; Ma, Xiuying; Wang, Yinfei; Zhou, Sheng; Li, Xinlei; Li, Wenbin; Liu, Zhifeng.
Afiliação
  • Deng H; College of Environmental Science and Engineering, China West Normal University, Nanchong, Sichuan 637009, China; Key Laboratory of Nanchong City of Ecological Environment Protection and Pollution Prevention in Jialing River Basin, Nanchong, Sichuan 637009, China.
  • Ma X; College of Environmental Science and Engineering, China West Normal University, Nanchong, Sichuan 637009, China.
  • Wang Y; College of Chemical Engineering, Xinjiang University, Urumchi, Xinjiang 830046, China.
  • Zhou S; College of Environmental Science and Engineering, China West Normal University, Nanchong, Sichuan 637009, China.
  • Li X; College of Environmental Science and Engineering, China West Normal University, Nanchong, Sichuan 637009, China.
  • Li W; College of Environmental Science and Engineering, China West Normal University, Nanchong, Sichuan 637009, China; Key Laboratory of Nanchong City of Ecological Environment Protection and Pollution Prevention in Jialing River Basin, Nanchong, Sichuan 637009, China. Electronic address: lwb062@163.com.
  • Liu Z; State Key Laboratory of Qinba Bio-Resource and Ecological Environment, Hanzhong, Shaanxi 723001, China.
Int J Biol Macromol ; 278(Pt 2): 134768, 2024 Oct.
Article em En | MEDLINE | ID: mdl-39151865
ABSTRACT
In this study, starch (S) was gelatinized and carbonized to prepare carbonized/gelatinized S (CGS) as the research material. Then, peat extract (Pe) and surfactants with different ratios were single- and multi-modified on CGS, respectively, to prepare Pe-modified CGS (Pe-CGS) and multi-modified CGS, respectively. The microscopic morphology of multi-modified CGS was studied using various testing methods. The de-risking effect on Cd(II) and hymexazol in wastewater was investigated, and the effects of temperature, pH, and ionic strength were compared. The spheroidal structure of S was destroyed after carbonization, and Pe and surfactants were modified on the surface and changed the surface properties of CGS. The adsorption processes of Cd(II) and hymexazol were suitable to be described by the Langmuir and Freundlich models, respectively. The maximum adsorption capacities (qm) of Cd(II) and adsorption capacity parameter (k) of hymexazol on different modified CGSs presented the peak value at BS/Pe-CGS. With the increase in the modification ratio of Pe, BS, and SDS, qm and k increased, which showed a high value at 100 % modification. Increases in temperature and pH were beneficial to Cd(II) adsorption but were not conducive to hymexazol adsorption. The adsorption amount decreased for Cd(II) and increased first and then reduced for hymexazol with the rise in ionic strength. The adsorption process exhibited spontaneity, endothermic behavior for Cd(II), exothermic behavior for hymexazol, and an entropy-increasing reaction. The adsorption amount of Cd(II) and hymexazol by multi-modified CGS maintained approximately 81 % of the original sample after three rounds of regeneration.
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Texto completo: 1 Coleções: 01-internacional Base de dados: MEDLINE Assunto principal: Amido / Temperatura / Poluentes Químicos da Água / Cádmio / Águas Residuárias Idioma: En Revista: Int J Biol Macromol Ano de publicação: 2024 Tipo de documento: Article País de afiliação: China

Texto completo: 1 Coleções: 01-internacional Base de dados: MEDLINE Assunto principal: Amido / Temperatura / Poluentes Químicos da Água / Cádmio / Águas Residuárias Idioma: En Revista: Int J Biol Macromol Ano de publicação: 2024 Tipo de documento: Article País de afiliação: China
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