石墨烯負(fù)載零價(jià)納米鐵去除有機(jī)污染物的研究
[Abstract]:Since graphene was discovered in 2004, it has attracted people's attention because of its unique structure and properties, and has rapidly become the focus of frontier research in many disciplines. Graphene has a unique two-dimensional plane structure and large specific surface area, which makes it an ideal carrier for loading inorganic nanoparticles. At present, there have been a series of reports that graphene and functional particles are combined to prepare graphene composites. In addition, zero-valent nano-iron (nZVI) shows a very obvious advantage in environmental remediation, but there are still some problems in practical application, such as easy oxidation, easy agglomeration and high preparation cost. These limit the removal efficiency of environmental pollutants by nZVI. The preparation of graphene-supported zero-valent iron nanocomposites (nZVI/rGO) can not only inhibit the aggregation of nZVI and improve its reactivity, but also expand the potential application value of graphene in the field of environmental remediation. In this paper, the feasibility of removing organic pollutants (rhodamine B, polybrominated diphenyl ether) from nZVI/rGO composites was studied, which can provide some reference value for the practical application of nZVI/rGO. The main contents are as follows: nZVI; was prepared by liquid phase reduction method and graphite oxide (GO), was prepared by modified Hummers method. NZVI/rGO composite was prepared by using sodium borohydride as reducing agent. The prepared materials were characterized by scanning electron microscopy (SEM), X-ray diffraction (XRD), Raman spectroscopy (Raman), BET specific surface area (BET) and X-ray photoelectron spectroscopy (XPS). The removal of Rhodamine B (Rh B), by graphene-loaded zero-valent iron nanocomposites was studied by using RSM and ANN-GA modeling methods to optimize the influencing factors of Rhodamine B removal rate (initial pH, concentration, temperature and reaction time). The results show that the predicted values of the two models are in good agreement with the experimental values. Compared with the experimental values, the prediction results of the ANN-GA model are more accurate, and the initial concentration of RSM is the most important influencing factor by ANOVA. In addition, by fitting the adsorption isotherms and kinetic equations of Rhodamine B removal by nZVI/rGO, it is found that the Freundlich equation and pseudo-second order kinetics can better describe the adsorption process of Rhodamine B by nZVI/rGO. The degradation effects of nZVI and nZVI/rGO on BDE-47,BDE-100,BDE-154 were studied and compared. In the primary stage of the reaction, the degradation rate of PBDEs by the two materials was faster, and the degradation rate decreased with the decrease of adsorption and reduction ability. In addition, because BDE-154 contains more bromine atoms, it is easier to degrade than BDE-47 and BDE-100, so BDE-154 not only degrades faster, but also has higher degradation rate. Through the study and analysis of the kinetic model, it is found that the degradation effect of nZVI and nZVI/rGO on PBDEs is pseudo-first-order reaction kinetics or pseudo-second-order reaction kinetics. In addition, according to the actual situation of the research group, the experimental results of PBDEs are supplemented by theoretical calculation. The B3PW91/6-311 G (d, p) and PBE/TZ2P/ZORA methods were used to optimize the structure of BDE-28,BDE-30,BDE-32,BDE-51,BDE-116 and BDE-166, and the bond lengths of C-Br and CNO were compared with their experimental values. The transition relations between BDE-7 and BDE-12 configuration transition states and anionic states were studied by QST2 method, and the dehalogenation paths of BDE-47,BDE-17,BDE-15,BDE-8,BDE-7 and BDE-4 anions under solvation condition were studied. The debromination rate constant of 14 kinds of BDE homologues was predicted by establishing a quantitative structure-activity relationship model.
【學(xué)位授予單位】:貴州師范大學(xué)
【學(xué)位級別】:碩士
【學(xué)位授予年份】:2017
【分類號】:X505;TB33
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