活性炭负载纳米零价铁的制备及其对难降解有机物去除性能的研究
[Abstract]:In this paper, the nano-iron (NZVI) loaded on the activated carbon carrier was prepared by loading the nano-iron (NZVI) on the activated carbon carrier, and the nano-iron (NZVI/ AC) was prepared by loading the nano-iron (NZVI) on the activated carbon carrier. The properties of non-degradable organic pollutants of trihalomethane (THMs) and acrylonitrile were selected as target pollutants, and the removal mechanism was studied. The preparation and characterization of NZVI and NZVI/ AC were studied in this paper. The nano-iron (NZVI) was prepared by a liquid-phase reduction method, and the supported nano-iron NZVI/ AC was prepared by using active carbon (AC) as a carrier, and the AC, NZVI and NZVI/ AC were characterized. The structure and morphology of NZVI, AC and NZVI/ AC were characterized by scanning electron microscopy (SEM) and transmission electron microscopy (TEM). The surface functional group, crystal structure and chemical composition of the sample were investigated by means of Fourier transform infrared (FT-IR), X-ray diffractometer (XRD) and X-ray photoelectron spectroscopy (XPS). The specific surface area, pore size and iron element content of the sample were determined by the specific surface area tester and the electron-coupled plasma atomic emission spectrometry (ICP-AES), respectively. The results show that the loading action of the activated carbon and the dispersion of the polyethylene glycol-4000 effectively reduce the degree of agglomeration of the nano-iron particles. The results of SEM and TEM show that the prepared supported nano-iron particles have a uniform size, a particle size of 30-80nm, and the iron particles are in a spherical shape, and are partially distributed on the outer surface of the active carbon and partially enter the pore canal of the active carbon. The BET specific surface area of NZVI was 25.8 m2/ g, and the specific surface area of NZVI/ AC after loading was 63.9 m2/ g. NZVI/ AC had a greater specific surface area and higher activity. The morphology and content of Fe element in the surface of NZVI/ AC particles were analyzed by energy spectrum EDS, and the experimental results were close to the theoretical value (10%). The results of XRD, FTIR and XPS all confirmed that the nano-valent iron was successfully loaded on the activated carbon, and the loaded nano-iron had good anti-oxidation ability and better dispersibility. The effect of NZVI, AC and NZVI/ AC on the removal of trihalomethane (THMs) was studied. The effects of the dosage, reaction time and initial pH of NZVI/ AC on the removal of trihalomethane were investigated. The results show that the removal and removal rate of trihalomethane are NZVI/ ACNZVIAC and ACNZVI/ ACNZVI. Increasing the dosage of the particles helps to improve the removal rate, but when the dosage is increased to 1.8 g/ L, the increase of the removal effect is not large. When the dosage of NZVI/ AC is 1.8 g/ L and the pH is neutral, the removal effect of the THMs is the best. The experimental results show that the bromomethane is easier to remove than the chloromethane, and the removal effect and the removal rate of the trihalomethane follow the order of CHBr3CHBr2ClCHBrCl2CHCl3. Furthermore, the experimental results also show that the removal rate of the trihalomethane with the high bromine number is higher than that of the low bromine number of the trihalomethane (CHBr3CHBr2ClCHBrCl2). The removal rate of the four trihalomethane was over 90%, and the highest removal rates of CHBr3, CHBr2Cl, CHBrCl2 and CHCl3 were 100%, 97.8%,95% and 94.5% respectively. The effect of activated carbon loaded iron and active carbon on the removal of acrylonitrile was studied. The results showed that the effect of NZVI/ AC on the removal of acrylonitrile was higher than that of AC, mainly due to the adsorption of the activated carbon itself on the acrylonitrile, and the Fe 2 + generated in the reaction. [H] and Fe0 itself have very strong reducibility and can react with acrylonitrile. Both the pseudo-first and the pseudo-second-order kinetic equations do not well state the process of removing the acrylonitrile from the NZVI/ AC. The Freundich model can better describe the adsorption isotherm of NZVI/ AC to acrylonitrile, and the correlation coefficient R20.98. It is known from the analysis of the UV-visible spectrophotometry and the Fourier infrared spectroscopy that the NZVI/ AC can decompose the acrylonitrile molecule, mainly due to the free hydrogen group[H] produced by the reaction and the chemical oxidation reduction effect between the newly formed Fe 2 + and the acrylonitrile. The activity of activated sludge was determined by the determination of the oxygen consumption rate of activated sludge. The results showed that the pretreatment of NZVI/ AC could improve the biodegradability of acrylonitrile wastewater and reduce its toxicity to activated sludge.
【学位授予单位】:山东大学
【学位级别】:硕士
【学位授予年份】:2015
【分类号】:X703;TQ424.1
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