重金屬捕集劑及陶瓷平板膜組合工藝對(duì)重金屬污染土壤淋洗廢水重復(fù)利用的研究
[Abstract]:Soil leaching is a widely used remediation technique for heavy metal pollution. The engineering practice shows that for a long time, the high price of chemical eluent, the difficult treatment of leaching waste liquid and the difficulty of recovery and utilization of eluent have become the key and difficulty of this technology breakthrough. In this paper, the separation process of heavy metal trapping agent for the separation of complex ceramic plate membrane was studied with heavy metal contaminated soil leaching wastewater as the research object. The technical feasibility of this process in the field of artificial and natural chelating agents, which is the most widely used at present, has been preliminarily verified, and the treatment effect of the combined process has been explored. The design scheme of membrane chemical reactor for treatment of heavy metal polluted wastewater by artificial and natural chelating agents was summarized. Five kinds of heavy metal trapping agents solid DTCR, liquid DTCR, solid TMT, liquid TMT, heavy metal trapping agent HMC-M1 were used to treat simulated leaching wastewater with initial copper ion concentrations of 50mg/L and 500mg/L. The trapping efficiency of heavy metal trapping agent HMC-M1 is obviously better than that of other four kinds of trapping agents. In addition, through the comparison of the extraction methods of the effluent after the reaction, the content of copper, cadmium and lead ions in the extract solution and the simulated elution efficiency were superior to those of the ordinary static precipitation method in the extraction of supernatant by using the 220nm ceramic plate membrane. Through the experiments on leaching wastewater from copper, cadmium and lead contaminated soil and the leaching wastewater from compound polluted soil, it was found that, p H, temperature and stirring time had little effect on several kinds of wastewater with different concentrations. The main influencing factors are the ratio of mass of trapping agent to the theoretical content of EDTA in wastewater (M / E) and stirring intensity. For the simulated leaching wastewater of copper, cadmium, lead and its compound contaminated soil, the optimum reaction conditions are as follows: no regulation of pH, room temperature, adding ratio of 1.4, stirring intensity of 140 r / min, stirring time of 5 mins. Under these conditions, the initial concentration of copper, cadmium and lead in wastewater is 50 mg / L ~ (100) mg / L ~ (-1), and the removal rate of heavy metal ions is more than 95%, and the leaching efficiency of wastewater extract is above 80% of the corresponding amount of EDTA. That is to say, the EDTA. from leaching wastewater was recovered by this method. It was found that the optimum reaction conditions were as follows: no adjusting pH, temperature, adding ratio 1.4, stirring intensity 180 r / min, stirring time 5 min. At the same time, the leaching efficiency of the industrial wastewater treatment liquid is over 80% of the corresponding amount of EDTA, which indicates that the process can be applied to the leaching wastewater of the site. Because the EDTA of leaching wastewater formed a stable soluble complex with copper, cadmium and lead ions, the elution efficiency of HMC-M1 after treatment proved that HMC-M1 broke the original complexation equilibrium in the reaction process, and also with copper and cadmium. Lead ions form new insoluble complexes and release EDTA. In this process, HMC-M1 breaks the equilibrium of complex release EDTA and separates EDTA from M- (HMC-M1), which coincides with the characteristics of membrane reactor reaction and separation. It is necessary to design a membrane chemical reactor for this process. Because of the stage and periodicity of in situ soil leaching technology. Therefore, the wastewater was treated by batch stirred reactor. The experimental results show that the reaction time is 5 min, the precipitation time is 30 min, and the influent time is 10 min. The feed pump and the dosing pump work at the same time. After influent and dosing 10min, the ceramic membrane suction pump begins to work, and the 20min stops the influent. Start membrane backwashing and mud removal, membrane cleaning and mud removal 30min, one cycle ends. In addition, two membrane reactors were used in the system to ensure that the leaching wastewater could be treated all the time within 1 h.
【學(xué)位授予單位】:蘭州交通大學(xué)
【學(xué)位級(jí)別】:碩士
【學(xué)位授予年份】:2017
【分類號(hào)】:X703
【參考文獻(xiàn)】
相關(guān)期刊論文 前10條
1 薛秀煒;羅千植;;重金屬污染土壤修復(fù)技術(shù)進(jìn)展研究[J];中國(guó)錳業(yè);2016年03期
2 秦樊鑫;魏朝富;李紅梅;;重金屬污染土壤修復(fù)技術(shù)綜述與展望[J];環(huán)境科學(xué)與技術(shù);2015年S2期
3 肖曉;孫水裕;嚴(yán)蘋方;邱伊琴;葉茂友;;高效重金屬捕集劑EDTC的結(jié)構(gòu)表征及對(duì)酸性絡(luò)合銅的去除特性研究[J];環(huán)境科學(xué)學(xué)報(bào);2016年02期
4 串麗敏;趙同科;鄭懷國(guó);趙靜娟;張曉靜;譚翠萍;李光達(dá);;土壤重金屬污染修復(fù)技術(shù)研究進(jìn)展[J];環(huán)境科學(xué)與技術(shù);2014年S2期
5 李實(shí);張翔宇;潘利祥;;重金屬污染土壤淋洗修復(fù)技術(shù)研究進(jìn)展[J];化工技術(shù)與開(kāi)發(fā);2014年11期
6 周建軍;周桔;馮仁國(guó);;我國(guó)土壤重金屬污染現(xiàn)狀及治理戰(zhàn)略[J];中國(guó)科學(xué)院院刊;2014年03期
7 黃益宗;郝曉偉;雷鳴;鐵柏清;;重金屬污染土壤修復(fù)技術(shù)及其修復(fù)實(shí)踐[J];農(nóng)業(yè)環(huán)境科學(xué)學(xué)報(bào);2013年03期
8 劉君寒;胡光榮;李福利;李力;;厭氧消化系統(tǒng)微生物菌群的研究進(jìn)展[J];工業(yè)水處理;2011年10期
9 何灝鵬;武秀文;張少敏;;鐵屑內(nèi)電解法處理EDTA絡(luò)合銅廢水的研究[J];東莞理工學(xué)院學(xué)報(bào);2011年05期
10 王靜;王鑫;吳宇峰;丁冬梅;趙一;楊華;;農(nóng)田土壤重金屬污染及污染修復(fù)技術(shù)研究進(jìn)展[J];綠色科技;2011年03期
相關(guān)會(huì)議論文 前1條
1 周勤;吳友明;袁笑一;;重金屬捕集劑R2處理含銅廢水及機(jī)理研究[A];中國(guó)化學(xué)會(huì)第七屆水處理化學(xué)大會(huì)暨學(xué)術(shù)研討會(huì)會(huì)議論文集[C];2004年
相關(guān)碩士學(xué)位論文 前5條
1 李清峰;重金屬捕集劑處理電鍍重金屬?gòu)U水的試驗(yàn)研究及其工程應(yīng)用[D];浙江大學(xué);2012年
2 傅皓;重金屬捕集劑對(duì)水中微量絡(luò)合銅離子去除研究[D];浙江大學(xué);2012年
3 孫斌;TiO_2光催化降解絡(luò)合銅廢水的研究[D];廣東工業(yè)大學(xué);2011年
4 童新;有機(jī)硫捕獲劑對(duì)水中重金屬離子的處理研究[D];浙江大學(xué);2009年
5 陳春艷;兩種重金屬離子捕集劑的合成、性能及應(yīng)用研究[D];重慶大學(xué);2006年
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