類芬頓試劑、活化過硫酸銨和高鐵酸鉀氧化脫除煙氣中單質(zhì)汞的研究
[Abstract]:The smoke mercury produced by coal combustion has strong toxicity, which has caused great harm to the living environment and health of human beings, and has attracted wide attention all over the world. The improvement of the existing wet flue gas desulfurization unit (Wet Flue Gas Desulfurization,WFGD) and activated carbon injection (Activated carbon injection,ACI) for mercury removal are promising technologies for mercury control in coal-fired flue gas. In this paper, three kinds of environmental protection oxidants (Fenton-like reagent) were selected. Ammonium persulfate and potassium ferrate), and the basic theory of removing mercury from coal-fired flue gas by oxidation of three oxidants were studied in two common reactors: spray column and fixed bed reactor. The main research contents and achievements can be divided into three parts as follows: in the spray column reactor, the solution pH, reaction temperature, liquid-gas ratio, H_2O_2 concentration, Fe~ (3) concentration, Cu~ (2) concentration and initial mercury concentration were studied. The effects of technological parameters such as NO concentration and SO_2 concentration on the performance of Fenton-like reagent for mercury removal were studied. The reaction products and free radicals in the solution were determined by ion chromatography, liquid phase fluorescence spectrometer and electron spin resonance spectroscopy. The final products of mercury removal from flue gas and the removal path were deduced. The results showed that: (1) with the increase of H_2O_2 concentration, Fe~ (3) concentration, Cu~ (2) concentration and liquid-gas ratio, the mercury removal efficiency increased significantly. However, with the increase of the concentration of pH,NO and SO_2, the efficiency of mercury removal decreased greatly. The change of initial mercury concentration and reaction temperature has little effect on the efficiency of mercury removal. (2) hydroxyl radical oxidation is the main pathway for mercury removal, and hydrogen peroxide oxidation is the secondary pathway for mercury removal. The reaction temperature, (NH_4) _ 2S_2O_8 concentration, liquid-gas ratio, mercury concentration and solution pH, were studied in a spray column reactor. The effects of technological parameters such as urea concentration and SO_2 concentration on the removal of mercury by activated ammonium persulfate oxidation at high temperature were studied by ion chromatography and ultraviolet spectrophotometry. Liquid phase reaction products and free radicals were determined by liquid phase fluorescence spectrometer and mass spectrometry. The final products and removal path of mercury removal from flue gas were deduced. The results showed that: (1) with the increase of reaction temperature, the concentration of (NH_4) _ 2S_2O_8 and the ratio of liquid to gas, the efficiency of mercury removal increased significantly. However, with the increase of the concentration of pH and urea, the efficiency of mercury removal decreased greatly. The change of initial mercury concentration and SO_2 concentration has little effect on the efficiency of mercury removal. (2) the primary mercury in flue gas is mainly removed by oxidation of Sz _ 2O _ 2O _ 8 ~ (2 -), OH) and SO_4~- into divalent mercury in the solution. And divalent mercury is the final product. The sorbents for wheat stalk coke were prepared by high temperature pyrolysis and chemical modification. The K_2FeO_4 concentration, initial mercury concentration, O ~ (2 +) concentration and NO concentration were studied in a fixed-bed reactor. The effects of SO_2 concentration and reaction temperature on the mercury removal performance of the adsorbent were studied. The results showed that: (1) the specific surface area and pore structure of the modified wheat stalk coke were obviously improved. The surface of the modified coke was successfully loaded with new active agent Fe_2O_3 and K _ 2O _ 2 FeO _ 4. (2) the efficiency of mercury removal was improved with the increase of O ~ (2 +) concentration. However, the efficiency of mercury removal decreases with the increase of initial mercury concentration. When NO was added to the flue gas, the mercury removal efficiency increased. However, when SO_ 2 was added to the flue gas, the mercury removal efficiency decreased instead. With the increase of reaction temperature, the mercury removal efficiency first increased and then decreased.
【學(xué)位授予單位】:江蘇大學(xué)
【學(xué)位級(jí)別】:碩士
【學(xué)位授予年份】:2017
【分類號(hào)】:X701
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