2020
DOI: 10.1007/s11356-019-07563-z
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Clean technology for synchronous sequestration of charged organic micro-pollutant onto microwave-assisted hybrid clay materials

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Cited by 18 publications
(33 citation statements)
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“…Increasing the adsorbent dose has different conflicting effects on the adsorption system. The increase in the adsorbent dose leads to a rise in the number of available active sites to enhance the adsorption activity and increase the removal rate . Generally, the decline in IBP and DCF removal with increasing dosage of CZPPrgo may be ascribed to the agglomeration of the nanoparticles, which leads to a smaller surface area, thereby lowering the adsorption process due to a poor adsorbent–adsorbate interaction …”
Section: Resultsmentioning
confidence: 99%
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“…Increasing the adsorbent dose has different conflicting effects on the adsorption system. The increase in the adsorbent dose leads to a rise in the number of available active sites to enhance the adsorption activity and increase the removal rate . Generally, the decline in IBP and DCF removal with increasing dosage of CZPPrgo may be ascribed to the agglomeration of the nanoparticles, which leads to a smaller surface area, thereby lowering the adsorption process due to a poor adsorbent–adsorbate interaction …”
Section: Resultsmentioning
confidence: 99%
“…The experimental data obtained were fit into some nonlinear equilibrium models, which are Freundlich (eq ), Fritz–Schlunder (eq ), and Elovich (eq ), and nonlinear kinetic models, which are pseudo-second-order model (PSOM) (eq ), fractal-like pseudo-second-order model (FL-PSOM) (eq ), two-step kinetic model (eq ), fractal-like kinetic model (FKN) (eq ), and Morris–Weber intraparticle diffusion (IPD) model (eq ). , The experimental data were fit into the nonlinear mathematical equations below using the quasi-Newton least-squares algorithm in KyPlot Software 2.0 Model (Kyens Lab Inc., Tokyo, Japan). q normale = K normalF C normale 1 / n q normale = q max FS C normale n FS 1 + K FS C normale γ FS q normale = C normale ( K e q m e ( q e…”
Section: Characterization Of the Adsorbentsmentioning
confidence: 99%
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“…Infrared spectra have been widely used by many scholars to characterize the change of surface functional groups on an adsorbent surface. , Thus, chemical interactions between water and mudstone can be studied by observing the changes in infrared spectra during heating of mudstones after water adsorption. However, the chemical interaction is hard to distinguish because of the overlap of infrared vibration bands of O–H in H 2 O and that in clay minerals .…”
Section: Introductionmentioning
confidence: 99%