论文部分内容阅读
Lagerstroemia speciosa bark(LB) embedded magnetic nanoparticles were prepared by co-precipitation of Fe~(2+) and Fe~(3+) salt solution with ammonia and LB for Cr(Ⅵ) removal from aqueous solution.The native LB,magnetic nanoparticle(MNP),L.spedosa embedded magnetic nanoparticle(MNPLB) and Cr(Ⅵ) adsorbed MNPLB particles were characterized by SEM-EDX,TEM,BET-surface area,FT-IR,XRD and TGA methods.TEM analysis confirmed nearly spherical shape of MNP with an average diameter of 8.76 nm and the surface modification did not result in the phase change of MNP as established by XRD analysis,while led to the formation of secondary particles of MNPLB with diameter of 18.54 nm.Characterization results revealed covalent binding between the hydroxyl group of MNP and carboxyl group of LB particles and further confirmed its physico-chemical nature favorable for Cr(Ⅵ) adsorption.The Cr(Ⅵ) adsorption on to MNPLB particle as an adsorbent was tested under different contact time,initial Cr(Ⅵ) concentration,adsorbent dose,initial pH,temperature and agitation speed.The results of the equilibrium and kinetics of adsorption were well described by Langmuir isotherm and pseudo-second-order model,respectively.The thermodynamic parameters suggest spontaneous and endothermic nature of Cr(Ⅵ)adsorption onto MNPLB.The maximum adsorption capacity for MNPLB was calculated to be 434.78 mg/g and these particles even after Cr(Ⅵ) adsorption were collected effortlessly from the aqueous solution by a magnet.The desorption of Cr(Ⅵ)-adsorbed MNPLB was found to be more than 93.72%with spent MNPLB depicting eleven successive adsorption-desorption cycles.
Lagerstroemia speciosa bark (LB) embedded magnetic nanoparticles were prepared by co-precipitation of Fe 2+ and Fe 3+ salts solution with ammonia and LB for Cr (Ⅵ) removal from aqueous solution.The native LB, magnetic nanoparticle (MNP), L.spedosa embedded magnetic nanoparticle (MNPLB) and Cr (Ⅵ) adsorbed MNPLB particles were characterized by SEM-EDX, TEM, BET-surface area, FT-IR, XRD and TGA methods. shape of MNP with an average diameter of 8.76 nm and the surface modification did not result in the phase change of MNP as established by XRD analysis, while led to the formation of secondary particles of MNPLB with diameter of 18.54 nm. Characterization results revealed covalent binding between the hydroxyl group of MNP and carboxyl group of LB particles and further confirmed its physico-chemical nature favorable for Cr (VI) adsorption.The Cr (VI) adsorption on MNPLB particle as an adsorbent was tested under different contact time, initial Cr (Ⅵ) conce ntration, adsorbent dose, initial pH, temperature and agitation speed. The results of the equilibrium and kinetics of adsorption were well described by Langmuir isotherm and pseudo-second-order model, respectively. The thermodynamic parameters suggest spontaneous and endothermic nature of Cr (VI ) adsorption onto MNPLB. maximum capacity for MNPLB was calculated to be 434.78 mg / g and these particles even after cr (VI) adsorption were collected effortlessly from the aqueous solution by a magnet.The desorption of Cr (VI) -adsorbed MNPLB was found to be more than 93.72% with spent MNPLB describing eleven successive adsorption-desorption cycles.