CN102774933B - Method for processing high-concentration ammonia nitrogen in rare earth wastewater - Google Patents
Method for processing high-concentration ammonia nitrogen in rare earth wastewater Download PDFInfo
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- 239000002351 wastewater Substances 0.000 title claims abstract description 34
- XKMRRTOUMJRJIA-UHFFFAOYSA-N ammonia nh3 Chemical compound N.N XKMRRTOUMJRJIA-UHFFFAOYSA-N 0.000 title claims abstract description 31
- 229910052761 rare earth metal Inorganic materials 0.000 title claims abstract description 28
- 150000002910 rare earth metals Chemical class 0.000 title claims abstract description 25
- 238000000034 method Methods 0.000 title claims abstract description 12
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 claims abstract description 34
- FAPWRFPIFSIZLT-UHFFFAOYSA-M Sodium chloride Chemical compound [Na+].[Cl-] FAPWRFPIFSIZLT-UHFFFAOYSA-M 0.000 claims abstract description 14
- 239000011780 sodium chloride Substances 0.000 claims abstract description 7
- 239000007787 solid Substances 0.000 claims abstract description 7
- 229910052799 carbon Inorganic materials 0.000 claims abstract 4
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Chemical compound O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 17
- 238000005868 electrolysis reaction Methods 0.000 claims description 14
- 239000008367 deionised water Substances 0.000 claims description 12
- 229910021641 deionized water Inorganic materials 0.000 claims description 12
- 239000012467 final product Substances 0.000 claims 1
- 238000007654 immersion Methods 0.000 claims 1
- 238000012856 packing Methods 0.000 claims 1
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 abstract description 8
- 238000005265 energy consumption Methods 0.000 abstract description 4
- 229910052757 nitrogen Inorganic materials 0.000 abstract description 4
- 230000003197 catalytic effect Effects 0.000 abstract description 3
- 230000010287 polarization Effects 0.000 abstract description 3
- 238000006479 redox reaction Methods 0.000 abstract description 3
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 description 15
- 239000000243 solution Substances 0.000 description 12
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 description 10
- 229910052742 iron Inorganic materials 0.000 description 5
- 239000011259 mixed solution Substances 0.000 description 5
- 239000003344 environmental pollutant Substances 0.000 description 4
- 231100000719 pollutant Toxicity 0.000 description 4
- 230000000694 effects Effects 0.000 description 3
- -1 rare earth carbonate Chemical class 0.000 description 3
- 238000003723 Smelting Methods 0.000 description 2
- 150000003863 ammonium salts Chemical class 0.000 description 2
- 150000002500 ions Chemical class 0.000 description 2
- 238000004519 manufacturing process Methods 0.000 description 2
- 208000018522 Gastrointestinal disease Diseases 0.000 description 1
- 230000002378 acidificating effect Effects 0.000 description 1
- 230000015572 biosynthetic process Effects 0.000 description 1
- 239000012141 concentrate Substances 0.000 description 1
- 201000010099 disease Diseases 0.000 description 1
- 208000037265 diseases, disorders, signs and symptoms Diseases 0.000 description 1
- 239000003651 drinking water Substances 0.000 description 1
- 235000020188 drinking water Nutrition 0.000 description 1
- 239000003814 drug Substances 0.000 description 1
- 238000003912 environmental pollution Methods 0.000 description 1
- 238000012851 eutrophication Methods 0.000 description 1
- 239000007789 gas Substances 0.000 description 1
- 231100000405 induce cancer Toxicity 0.000 description 1
- 150000002832 nitroso derivatives Chemical class 0.000 description 1
- 239000000575 pesticide Substances 0.000 description 1
- 238000000746 purification Methods 0.000 description 1
- 238000006722 reduction reaction Methods 0.000 description 1
- 238000000926 separation method Methods 0.000 description 1
- 239000010865 sewage Substances 0.000 description 1
- 238000005507 spraying Methods 0.000 description 1
- 238000003786 synthesis reaction Methods 0.000 description 1
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Abstract
Description
技术领域technical field
本发明涉及一种处理稀土废水中高浓度氨氮方法,属于污水处理领域。The invention relates to a method for treating high-concentration ammonia nitrogen in rare earth wastewater, belonging to the field of sewage treatment.
背景技术Background technique
稀土生产冶炼过程中制药排放三种废水,主要是稀土精矿焙烧尾气喷淋净化产生的酸性废水、碳酸稀土生产过程产生的铵盐废水和稀土分离产生的铵盐废水。其中,稀土行业每年产生的废水量达2000多万吨,氨氮含量300~5000mg/L,超出国家排放标准十几倍至上百倍。废水中氨氮污染物正是稀土冶炼中产生的三大废水之一,水质指标中氨氮是引起水体富营养化和环境污染的一种重要污染物,它能使水失去自净化能力,其进入人体而合成亚硝基化合物,诱发癌变,饮用水中氨氮含量过高时会引起胃肠障碍及地方性疾病的产生。There are three types of wastewater discharged by pharmaceuticals during the production and smelting of rare earths, mainly acidic wastewater generated by spraying and purifying tail gas of rare earth concentrate roasting, ammonium salt wastewater generated by rare earth carbonate production process, and ammonium salt wastewater generated by rare earth separation. Among them, the rare earth industry produces more than 20 million tons of wastewater every year, with an ammonia nitrogen content of 300-5,000 mg/L, exceeding the national discharge standard by ten to hundreds of times. Ammonia nitrogen pollutants in wastewater is one of the three major wastewater produced in rare earth smelting. Ammonia nitrogen in water quality indicators is an important pollutant that causes water eutrophication and environmental pollution. It can make water lose its self-purification ability and enter the human body. The synthesis of nitroso compounds can induce cancer, and when the ammonia nitrogen content in drinking water is too high, it will cause gastrointestinal disorders and endemic diseases.
在处理稀土废水中高浓度氨氮的电解法中,其优势在于二次污染物的减量,易于操作,远程控制,适应面广等,该法能够有效的去除氨氮及废水中的其他污染物,但它同时也存在电耗大,成本高等缺点。为了解决这一问题,针对电解法,何绪文、刘通等在文献中提出一种电解法去除高浓度氨氮废水工艺的研究,该研究以铅和钌作为基本材料,选取7~9A电流强度,NH4 +与Cl-的摩尔比为1∶4的Cl-浓度,随着电解过程中增加极板数量来提高氨氮去除速率,氨氮去除效果高,降低了一定的电耗量及成本,但该研究只针对于农药废水等,对于稀土废水中的高浓度氨氮去除效果仍不为理想,而且7~9A电流强度仍然导致电耗量大,必定带来处理费用昂贵。针对稀土废水中高浓度氨氮电解去除法,能够同时做到电耗低、成本低、避免二次污染风险的文献尚未见报道,在专利中也未能得到保护。In the electrolysis method for treating high-concentration ammonia nitrogen in rare earth wastewater, its advantages lie in the reduction of secondary pollutants, easy operation, remote control, and wide adaptability. This method can effectively remove ammonia nitrogen and other pollutants in wastewater, but It also has the disadvantages of high power consumption and high cost. In order to solve this problem, aiming at the electrolysis method, He Xuwen, Liu Tong et al. proposed in the literature a research on the process of removing high-concentration ammonia-nitrogen wastewater by electrolysis. The molar ratio of 4 + to Cl - is 1:4, the concentration of Cl - increases the number of plates in the electrolysis process to increase the removal rate of ammonia nitrogen, the removal effect of ammonia nitrogen is high, and the power consumption and cost are reduced, but the research Only for pesticide wastewater, etc., the removal effect of high-concentration ammonia nitrogen in rare earth wastewater is still not ideal, and the current intensity of 7-9A still leads to large power consumption, which will inevitably bring expensive treatment costs. For the electrolytic removal of high-concentration ammonia-nitrogen in rare earth wastewater, the literature that can simultaneously achieve low power consumption, low cost, and avoid the risk of secondary pollution has not been reported, nor has it been protected in patents.
发明内容Contents of the invention
为了寻求一种能同时做到电耗低、成本低、避免二次污染风险的稀土废水中高浓度氨氮电解去除法,本发明在于提供一种处理稀土废水中高浓度氨氮方法,通过制备了一种具有催化活性的电极,消除周围溶液中离子浓度的浓差极化,从而产生氧化还原反应把稀土废水中高浓度氨氮转换为氮气排出空气中,氨氮去除率高达99.8%以上,解决了现有技术中电压高、能耗高的问题,避免了二次污染风险的产生。In order to seek a method for electrolytic removal of high-concentration ammonia-nitrogen in rare-earth wastewater that can simultaneously achieve low power consumption, low cost, and avoid the risk of secondary pollution, the present invention provides a method for treating high-concentration ammonia-nitrogen in rare-earth wastewater. The catalytically active electrode eliminates the concentration polarization of the ion concentration in the surrounding solution, thereby generating a redox reaction to convert the high concentration of ammonia nitrogen in the rare earth wastewater into nitrogen and discharge it into the air. The problem of high energy consumption and high energy consumption avoids the risk of secondary pollution.
为达到上述目的,本发明采取的具体技术方案是:In order to achieve the above object, the concrete technical scheme that the present invention takes is:
(1)取100~150目颗粒活性炭,在0.5MHCl溶液中浸泡2~3小时,用去离子水在超声波的作用下冲洗3遍,放入2MNaOH溶液中浸泡3~4小时,又用去离子水在超声波的作用下冲洗3遍,自然晾干,于温度为105℃下烘干2~3小时;(1) Take 100-150 mesh granular activated carbon, soak in 0.5M HCl solution for 2-3 hours, rinse 3 times with deionized water under the action of ultrasonic waves, soak in 2M NaOH solution for 3-4 hours, and then use deionized water Rinse 3 times with water under the action of ultrasonic waves, dry naturally, and dry at 105°C for 2 to 3 hours;
(2)把烘干后的颗粒活性炭浸入2.5M的Cu(NO3)2、1.0M的Ni(NO3)2混合溶液中5~6小时,自然晾干,于温度为105℃下烘干2~3小时;(2) Immerse the dried granular activated carbon in the mixed solution of 2.5M Cu(NO 3 ) 2 and 1.0M Ni(NO 3 ) 2 for 5-6 hours, dry it naturally, and dry it at 105°C 2 to 3 hours;
(3)把上述处理后的颗粒活性碳装入空心圆柱微孔铁壳,作为电解电极;(3) the granular activated carbon after the above-mentioned treatment is packed into the hollow cylinder microporous iron shell, as the electrolysis electrode;
(4)把高浓度氨氮稀土废水通入电解槽,加入质量比为0.1~0.5%NaCl固体,在36~110V电压下电解3~4小时,即可。(4) Pass high-concentration ammonia-nitrogen rare-earth wastewater into an electrolytic cell, add 0.1-0.5% NaCl solid in a mass ratio, and electrolyze at a voltage of 36-110V for 3-4 hours.
本发明的显著优势在于:Significant advantage of the present invention is:
(1)含有催化活性的电极,不仅具有得失电子的作用,还能消除周围溶液中离子浓度的浓差极化;(1) The electrode with catalytic activity not only has the effect of gaining and losing electrons, but also can eliminate the concentration polarization of the ion concentration in the surrounding solution;
(2)通过氧化还原反应把稀土废水中高浓度氨氮转换为氮气排出空气中,具有电压低,能耗低的优点,实现了节能目标,避免了二次污染风险的产生。(2) Convert high-concentration ammonia-nitrogen in rare earth wastewater into nitrogen and discharge it into the air through oxidation-reduction reaction, which has the advantages of low voltage and low energy consumption, realizes the goal of energy saving, and avoids the risk of secondary pollution.
具体实施方案specific implementation plan
先取100~150目颗粒活性炭,在0.5MHCl溶液中浸泡2~3小时,用去离子水在超声波的作用下冲洗3遍,放入2MNaOH溶液中浸泡3~4小时,又用去离子水在超声波的作用下冲洗3遍,自然晾干,于温度为105℃下烘干2~3小时;然后把烘干后的颗粒活性炭浸入2.5M的Cu(NO3)2、1.0M的Ni(NO3)2混合溶液中5~6小时,自然晾干,于温度为105℃下烘干2~3小时;接着把上述处理后的颗粒活性碳装入空心圆柱微孔铁壳,作为电解电极;最后把高浓度氨氮稀土废水通入电解槽,加入质量比为0.1~0.5%NaCl固体,在36~110V电压下电解3~4小时后,测电解后的稀土废水中氨氮浓度。First, take 100-150 mesh granular activated carbon, soak it in 0.5M HCl solution for 2-3 hours, wash it with deionized water under the action of ultrasonic waves for 3 times, put it into 2M NaOH solution for 3-4 hours, and then use deionized water in ultrasonic wave. Rinse 3 times under the action of water, dry naturally, and dry at 105°C for 2 to 3 hours; then soak the dried granular activated carbon in 2.5M Cu(NO 3 ) 2 , 1.0M Ni(NO 3 ) 2 in the mixed solution for 5 to 6 hours, dry naturally, and dry at a temperature of 105° C. for 2 to 3 hours; then put the above-mentioned treated granular activated carbon into a hollow cylindrical microporous iron shell as an electrolytic electrode; finally Pass high-concentration ammonia-nitrogen rare earth wastewater into an electrolytic cell, add 0.1-0.5% NaCl solid in a mass ratio, perform electrolysis at a voltage of 36-110V for 3-4 hours, and measure the ammonia nitrogen concentration in the electrolyzed rare-earth wastewater.
实施例1:Example 1:
先取105目颗粒活性炭,在0.5MHCl溶液中浸泡2小时,用去离子水在超声波的作用下冲洗3遍,放入2MNaOH溶液中浸泡4小时,又用去离子水在超声波的作用下冲洗3遍,自然晾干,于温度为105℃下烘干2小时;然后把烘干后的颗粒活性炭浸入2.5M的Cu(NO3)2、1.0M的Ni(NO3)2混合溶液中5小时,自然晾干,于温度为105℃下烘干2小时;接着把上述处理后的颗粒活性碳装入空心圆柱微孔铁壳,作为电解电极;最后把氨氮浓度为2500mg/L的稀土废水通入电解槽,加入质量比为0.1%NaCl固体,在40V电压下电解3小时后,测得稀土废水中氨氮浓度降到0.1mg/L,COD浓度由2000mg/L降到30mg/L,去除率高达99.9%。First take 105 mesh granular activated carbon, soak in 0.5M HCl solution for 2 hours, rinse 3 times with deionized water under the action of ultrasonic waves, soak in 2M NaOH solution for 4 hours, and rinse 3 times with deionized water under the action of ultrasonic waves , dry naturally, and dry at a temperature of 105 ° C for 2 hours; then immerse the dried granular activated carbon in 2.5M Cu(NO 3 ) 2 , 1.0M Ni(NO 3 ) 2 mixed solution for 5 hours, Dry naturally, and dry at a temperature of 105°C for 2 hours; then put the above-mentioned treated granular activated carbon into a hollow cylindrical microporous iron shell as an electrolysis electrode; finally pass the rare earth wastewater with an ammonia nitrogen concentration of 2500mg/L into the In the electrolytic cell, the mass ratio of 0.1% NaCl solid was added, and after electrolysis at 40V for 3 hours, the ammonia nitrogen concentration in the rare earth wastewater was measured to drop to 0.1mg/L, the COD concentration dropped from 2000mg/L to 30mg/L, and the removal rate was as high as 99.9%.
实施例2:Example 2:
先取150目颗粒活性炭,在0.5MHCl溶液中浸泡3小时,用去离子水在超声波的作用下冲洗3遍,放入2MNaOH溶液中浸泡3小时,又用去离子水在超声波的作用下冲洗3遍,自然晾干,于温度为105℃下烘干3小时;然后把烘干后的颗粒活性炭浸入2.5M的Cu(NO3)2、1.0M的Ni(N03)2混合溶液中6小时,自然晾干,于温度为105℃下烘干3小时;接着把上述处理后的颗粒活性碳装入空心圆柱微孔铁壳,作为电解电极;最后把氨氮浓度为5000mg/L的稀土废水通入电解槽,加入质量比为0.5%NaCl固体,在110V电压下电解4小时后,测得稀土废水中氨氮浓度降到0.2mg/L,COD浓度由3000mg/L降到60mg/L,去除率高达99.8%。First take 150-mesh granular activated carbon, soak in 0.5M HCl solution for 3 hours, rinse 3 times with deionized water under the action of ultrasonic waves, soak in 2M NaOH solution for 3 hours, and rinse 3 times with deionized water under the action of ultrasonic waves , dry naturally, and dry at a temperature of 105 ° C for 3 hours; then immerse the dried granular activated carbon in 2.5M Cu(NO 3 ) 2 , 1.0M Ni(N0 3 ) 2 mixed solution for 6 hours, Dry naturally, and dry at a temperature of 105°C for 3 hours; then put the above-mentioned treated granular activated carbon into a hollow cylindrical microporous iron shell as an electrolysis electrode; finally pass the rare earth wastewater with an ammonia nitrogen concentration of 5000mg/L into the In the electrolytic cell, 0.5% NaCl solid was added in a mass ratio, and after electrolysis at 110V for 4 hours, the ammonia nitrogen concentration in the rare earth wastewater was measured to drop to 0.2mg/L, and the COD concentration dropped from 3000mg/L to 60mg/L, and the removal rate was as high as 99.8%.
实施例3:Example 3:
先取125目颗粒活性炭,在0.5MHCl溶液中浸泡2小时,用去离子水在超声波的作用下冲洗3遍,放入2MNaOH溶液中浸泡4小时,又用去离子水在超声波的作用下冲洗3遍,自然晾干,于温度为105℃下烘干3小时;然后把烘干后的颗粒活性炭浸入2.5M的Cu(NO3)2、1.0M的Ni(NO3)2混合溶液中5小时,自然晾干,于温度为105℃下烘干2小时;接着把上述处理后的颗粒活性碳装入空心圆柱微孔铁壳,作为电解电极;最后把氨氮浓度为3500mg/L的稀土废水通入电解槽,加入质量比为0.3%NaCl固体,在80V电压下电解3小时后,测得稀土废水中氨氮浓度降到0.1mg/L,COD浓度由2500mg/L降到50mg/L,去除率高达99.8%。First take 125 mesh granular activated carbon, soak in 0.5M HCl solution for 2 hours, rinse 3 times with deionized water under the action of ultrasonic waves, soak in 2M NaOH solution for 4 hours, and rinse 3 times with deionized water under the action of ultrasonic waves , dry naturally, and dry at a temperature of 105°C for 3 hours; then immerse the dried granular activated carbon in 2.5M Cu(NO 3 ) 2 and 1.0M Ni(NO 3 ) 2 mixed solution for 5 hours, Dry naturally, and dry at a temperature of 105°C for 2 hours; then put the above-mentioned treated granular activated carbon into a hollow cylindrical microporous iron shell as an electrolysis electrode; finally pass the rare earth wastewater with an ammonia nitrogen concentration of 3500mg/L into the In the electrolytic cell, the mass ratio of 0.3% NaCl solid was added, and after electrolysis at 80V for 3 hours, the ammonia nitrogen concentration in the rare earth wastewater was measured to drop to 0.1mg/L, and the COD concentration dropped from 2500mg/L to 50mg/L, and the removal rate was as high as 99.8%.
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