電沉積法和混凝沉淀法組合工藝回收處理含鎘廢水的研究
[Abstract]:Cadmium is a heavy metal that can cause cancer. If you enter the human body through drinking water or food chain in the environment, it will be a great danger to human beings. Therefore, the removal of cadmium in industry or in water sources is essential. In this paper, the combined process of electrodeposition and coagulation is used to treat the wastewater containing high concentration of cadmium. While recovering cadmium metal, the concentration of cadmium in the treated water reaches the 0.1mg/L discharge standard stipulated in the Integrated Wastewater discharge Standard (GB8978-1996). In the process of electrodeposition, cadmium in the wastewater was recovered by electrodeposition. In the experiment, the cadmium-containing wastewater with different initial concentrations (400 mg / L, 600 mg / L, 1000 mg / L) was investigated in a multi-cathode and anode reactor in an electrolytic cell. Different initial pH (1.5, 3.5, 5.5, 7.5), different current densities (1.49 Ma / cm 2, 2.97 Ma / cm 2, 4.46 Ma / cm 2, 5.95 Ma / cm 2), different electrolyte types and concentrations (NaCl,NaNO3,Na2SO4), Effect of humic acid concentration and complex on electrodeposition of cadmium-containing wastewater. The experimental results show that the reduction potential of cadmium is-0.64 V to-0.78 V. in the three-phase electrode with titanium plate as the working electrode. The first order kinetic constant and current efficiency increase with the increase of initial concentration of cadmium. When the current density increases from 1.49mA/cm2 to 4.46mA/cm2, the recovery rate of cadmium increases from 96.98% to 99.3% in 120min electrodeposition time. When the current density is increased, the recovery efficiency and current efficiency of cadmium will not increase any more. When sodium nitrate electrolyte exists in the solution, the reaction rate of cadmium will decrease. When the concentration of humic acid in the solution is 200mg/L, the reaction rate of cadmium is very slow in the first 60 minutes, but increases with the oxidation of humic acid in the last 60 minutes. The presence of ammonia can promote the rate of electrodeposition of cadmium. By means of scanning electron microscopy and energy spectrum, X-ray diffractometer and X-ray photoelectron spectroscopy, it is found that in the process of electrodeposition, the waste water is mainly precipitated in the form of cadmium hydroxide and cadmium hydroxide. The effects of different pH values (5.0, 6.0, 7.0, 8.0, 9, 0), different forms of flocculants in the presence of Al and different dosages on the removal of cadmium were studied in the coagulation and sedimentation stage. The effects of different pH values (5.0, 6.0, 7.0, 8.0, 9, 0) on the removal of cadmium were studied. The experimental results show that the removal effect of cadmium is better when the initial pH is 9. The removal of cadmium by polymer in the form of Al is better than that of oligomer and polymer. When the dosage of polyaluminum chloride (PAC) increases, when the dosage of PAC is more than 0.4 mL, the removal rate of cadmium in the solution is as high as 90%, indicating that the coagulation effect can be achieved by adding a small amount of PAC,. With the increase of the dosage of polyaluminum chloride (PAC), the existence of Al was mainly in the form of polymer, and the removal efficiency of cadmium was obviously increased. The floc was characterized by XRD. It was found that the floc was mainly in the form of cadmium carbonate and cadmium hydroxide.
【學(xué)位授予單位】:南華大學(xué)
【學(xué)位級別】:碩士
【學(xué)位授予年份】:2014
【分類號】:X703.1;TQ150
【參考文獻(xiàn)】
相關(guān)期刊論文 前10條
1 郭彬;李許明;陳柳燕;李福燕;仝霞;魏志遠(yuǎn);漆智平;;土壤重金屬污染及植物修復(fù)技術(shù)研究[J];安徽農(nóng)業(yè)科學(xué);2007年33期
2 劉蘭泉;;生物淋濾法對污泥中鎘去除及污泥性質(zhì)的影響[J];安徽農(nóng)業(yè)科學(xué);2009年08期
3 張玉政;黃廷林;邸尚志;屈勃;;飲用水水源突發(fā)性Cd(Ⅱ)污染應(yīng)急處理實(shí)驗(yàn)研究[J];安全與環(huán)境學(xué)報(bào);2008年05期
4 王謙;成水平;;大型水生植物修復(fù)重金屬污染水體研究進(jìn)展[J];環(huán)境科學(xué)與技術(shù);2010年05期
5 王淑敏;王作輝;;電化學(xué)的應(yīng)用和發(fā)展[J];廣州化工;2010年08期
6 王磊峰;王倩倩;魏麗瓊;楊敦培;;生物法處理重金屬廢水研究狀況[J];化工技術(shù)與開發(fā);2013年01期
7 吳曼;徐明崗;張文菊;武海雯;;土壤性質(zhì)對單一及復(fù)合污染下外源鎘穩(wěn)定化過程的影響[J];環(huán)境科學(xué);2012年07期
8 尹平河,趙玲,YU Qi-ming,J T Matheickal;海藻生物吸附廢水中鉛、銅和鎘的研究[J];海洋環(huán)境科學(xué);2000年03期
9 張曉健;;水環(huán)境污染事件飲用水應(yīng)急處理 技術(shù)體系的建設(shè)和鎘污染應(yīng)用案例[J];水工業(yè)市場;2012年07期
10 任秀蓮;魏琦峰;劉U
本文編號:2463535
本文鏈接:http://sikaile.net/kejilunwen/dianlilw/2463535.html