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CN107720891A - A kind of method for promoting the reduction of heavy metal chromium ion electrochemical - Google Patents

A kind of method for promoting the reduction of heavy metal chromium ion electrochemical Download PDF

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CN107720891A
CN107720891A CN201711164870.2A CN201711164870A CN107720891A CN 107720891 A CN107720891 A CN 107720891A CN 201711164870 A CN201711164870 A CN 201711164870A CN 107720891 A CN107720891 A CN 107720891A
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hexavalent chromium
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齐建涛
宫宁
王振波
赵晶晶
周俊洁
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China University of Petroleum East China
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    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/46Treatment of water, waste water, or sewage by electrochemical methods
    • C02F1/461Treatment of water, waste water, or sewage by electrochemical methods by electrolysis
    • C02F1/467Treatment of water, waste water, or sewage by electrochemical methods by electrolysis by electrochemical disinfection; by electrooxydation or by electroreduction
    • C02F1/4676Treatment of water, waste water, or sewage by electrochemical methods by electrolysis by electrochemical disinfection; by electrooxydation or by electroreduction by electroreduction
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/20Heavy metals or heavy metal compounds
    • C02F2101/22Chromium or chromium compounds, e.g. chromates

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  • Chemical & Material Sciences (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Electrochemistry (AREA)
  • General Chemical & Material Sciences (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Organic Chemistry (AREA)
  • Water Treatment By Electricity Or Magnetism (AREA)

Abstract

本发明涉及一种促进重金属铬离子电化学还原的方法,是在‑1.5V恒电位条件下利用废旧易拉罐电化学处理六价铬污水。实验结果如下:传统化学方法在90分钟以上才能达到90%以上的六价铬组分处理效率;而在外加‑1.5V恒电位条件下铝片处理六价铬可以在60分钟达到93%;值得注意的是,在添加0.001M草酸条件下,60分钟内电化学方法可完全清除污水中的六价铬组分;此外,60分钟内电化学处理的能耗对比发现,添加草酸条件下的能耗是无添加条件的10%,实现了高效节能的处理效果。

The invention relates to a method for promoting the electrochemical reduction of heavy metal chromium ions, which uses waste pop cans to electrochemically treat hexavalent chromium sewage under the constant potential condition of -1.5V. The experimental results are as follows: the traditional chemical method can reach more than 90% of the hexavalent chromium component processing efficiency in more than 90 minutes; and the hexavalent chromium can reach 93% in 60 minutes under the condition of an external ‑1.5V constant potential; it is worthwhile It should be noted that under the condition of adding 0.001M oxalic acid, the electrochemical method can completely remove the hexavalent chromium component in the sewage within 60 minutes; The consumption is 10% of the condition without adding, which realizes the treatment effect of high efficiency and energy saving.

Description

一种促进重金属铬离子电化学还原的方法A method for promoting the electrochemical reduction of heavy metal chromium ions

技术领域technical field

本发明涉及一种促进重金属铬离子电化学还原的方法。The invention relates to a method for promoting the electrochemical reduction of heavy metal chromium ions.

背景技术Background technique

在高等院校的大学生实验和科研活动中,六价铬等重金属被广泛用来制备涂层溶液、缓蚀剂及催化剂。然而,六价铬是一种剧毒且致癌的环境污染物,严重威胁身体健康。目前高校针对六价铬污水处理缺乏简便且高效的方法,以至于过度依赖外协单位。一旦外协单位处理时间拖沓,六价铬污水的储存给高等院校带来极高的安全风险。In college students' experiments and scientific research activities, heavy metals such as hexavalent chromium are widely used to prepare coating solutions, corrosion inhibitors and catalysts. However, hexavalent chromium is a highly toxic and carcinogenic environmental pollutant, which seriously threatens human health. At present, colleges and universities lack simple and efficient methods for the treatment of hexavalent chromium sewage, so that they rely too much on external cooperation units. Once the processing time of the outsourcing unit is delayed, the storage of hexavalent chromium sewage will bring extremely high safety risks to colleges and universities.

发明内容Contents of the invention

本发明为一种促进重金属铬离子电化学还原的方法,实现实验室六价铬污水的高效清除和安全排放。The invention provides a method for promoting the electrochemical reduction of heavy metal chromium ions, and realizes efficient removal and safe discharge of laboratory hexavalent chromium sewage.

一种促进重金属铬离子电化学还原的方法,是在-1.5V恒电位条件下在含铬污水进行电化学处理。实验中利用电化学工作站和紫外分光光度计分别测试和对比易拉罐废旧铝片和草酸添加剂对铬酸盐电化学处理能力。实验结果如下:传统化学方法处理六价铬需在90-120 分钟才能达到90%以上处理效率;而在外加-1.5V恒电位条件下铝片处理六价铬可以在60分钟达到93%;值得注意的是,在添加0.001M草酸条件下,电化学方法可完全清除污水中的六价铬组分;此外,60分钟内电化学处理的能耗对比发现,添加草酸条件下的能耗是无添加条件的10%,实现了高效节能的处理效果。A method for promoting the electrochemical reduction of heavy metal chromium ions is to carry out electrochemical treatment in chromium-containing sewage under the constant potential condition of -1.5V. In the experiment, the electrochemical workstation and ultraviolet spectrophotometer were used to test and compare the electrochemical treatment ability of cans waste aluminum flakes and oxalic acid additives to chromate. The experimental results are as follows: the traditional chemical method takes 90-120 minutes to process hexavalent chromium to reach a treatment efficiency of more than 90%; while the treatment of hexavalent chromium with aluminum sheet can reach 93% in 60 minutes under the condition of an external -1.5V constant potential; it is worth Note that under the condition of adding 0.001M oxalic acid, the electrochemical method can completely remove the hexavalent chromium component in the sewage; in addition, the comparison of energy consumption of electrochemical treatment within 60 minutes found that the energy consumption under the condition of adding oxalic acid was zero. Adding 10% of the condition realizes the treatment effect of high efficiency and energy saving.

对比分析可知,在-1.5V恒电位条件下电化学处理方法实现了高效节能处理,尤其当含铬污水存在草酸添加剂时,电化学处理效率显著提高。The comparative analysis shows that the electrochemical treatment method achieves high efficiency and energy saving treatment under the constant potential condition of -1.5V, especially when oxalic acid additive is present in the chromium-containing sewage, the electrochemical treatment efficiency is significantly improved.

本发明具有如下优点:The present invention has the following advantages:

(1)制备工艺简单,操作方便,草酸类有机物便宜易得,且-1.5V的电极电位便于控制。(1) The preparation process is simple, the operation is convenient, the oxalic acid organic compound is cheap and easy to obtain, and the electrode potential of -1.5V is easy to control.

(2)本发明通过恒电位电化学处理方法对六价铬污染物进行高效处理,并通过添加还原性草酸试剂,实现电化学处理工艺的高效节能。(2) The present invention efficiently treats hexavalent chromium pollutants through a constant potential electrochemical treatment method, and realizes high efficiency and energy saving in the electrochemical treatment process by adding a reducing oxalic acid reagent.

附图说明Description of drawings

图1是利用三电极体系和恒电位的电化学方法处理六价铬污水的示意图。Figure 1 is a schematic diagram of treating hexavalent chromium sewage by using a three-electrode system and a constant potential electrochemical method.

具体实施方式Detailed ways

一种促进重金属铬离子电化学还原的方法,具体操作如下:A method for promoting the electrochemical reduction of heavy metal chromium ions, the specific operations are as follows:

a.用电子天平和滤纸称取0.0197g重铬酸钾,放入烧杯,用水溶液,最后倒入1000mL的容量瓶中,滴定至标线。配置好的Cr6+溶液的浓度为100μM;a. Use an electronic balance and filter paper to weigh 0.0197g of potassium dichromate, put it into a beaker, use an aqueous solution, and finally pour it into a 1000mL volumetric flask, and titrate to the marked line. The concentration of the prepared Cr 6+ solution is 100 μM;

b.利用三电极体系(工作电极为铝片(暴露面积为~2.25cm2);参比电极为饱和甘汞电极(SCE,0.24V vs.NHE)和石墨棒对电极),实验采用电化学工作站提供恒电位-1~-3V外加电在工作电极表面。如图1所示;b. Using a three-electrode system (the working electrode is an aluminum sheet (the exposed area is ~2.25cm 2 ); the reference electrode is a saturated calomel electrode (SCE, 0.24V vs. NHE) and a graphite rod counter electrode), the experiment uses electrochemical The workstation provides a constant potential of -1 ~ -3V to apply electricity on the surface of the working electrode. As shown in Figure 1;

c.利用电化学工作站记录0-60分钟内电流密度随时间的变化曲线,进而计算可知一定时间内的功率及能耗;c. Use the electrochemical workstation to record the change curve of current density with time within 0-60 minutes, and then calculate the power and energy consumption within a certain period of time;

d.用电子天平和滤纸称取0.5g二苯碳酰二肼,用200mL量筒量取50mL丙酮,将二苯碳酰二肼溶解于丙酮中,在用200mL量筒量取50mL超纯水添加到丙酮中,最后加入4.0mL由 1mLH3PO4、1mL H2SO4、2mL H2O混合形成强酸混合溶液,即制备好显色剂溶液;d. Weigh 0.5g of diphenylcarbazide with an electronic balance and filter paper, measure 50mL of acetone with a 200mL graduated cylinder, dissolve diphenylcarbazide in acetone, and add 50mL of ultrapure water with a 200mL graduated cylinder to In acetone, finally add 4.0mL of strong acid mixed solution formed by mixing 1mLH 3 PO 4 , 1mL H 2 SO 4 , and 2mL H 2 O to prepare the developer solution;

e.在实验之前,依次配置5、10、20、50、100μM的六价铬溶液,分别取出1.0mL溶液试样,并加入2.0mL的显色剂,摇匀并静置显色15min。15min后,将静置后的待测液加入到比色皿中,并在540nm波长处以空白溶液为参比测定其吸光度。以六价铬浓度为横坐标,相应的吸光度为纵坐标绘制标准曲线。本实验的标准曲线测定为,e. Before the experiment, prepare 5, 10, 20, 50, and 100 μM hexavalent chromium solutions in sequence, take out 1.0 mL of solution samples, add 2.0 mL of chromogenic agent, shake well and let stand for 15 minutes to develop color. After 15 minutes, add the test solution after standing still to the cuvette, and measure its absorbance at a wavelength of 540nm with a blank solution as a reference. Draw a standard curve with the concentration of hexavalent chromium as the abscissa and the corresponding absorbance as the ordinate. The standard curve of this experiment was determined as,

注:A(Cr6+)为Cr6+溶液的吸光度Note: A(Cr 6+ ) is the absorbance of Cr 6+ solution

f.利用分光光度计和比色法(污水和显色剂的体积比1:2)测试10、20、30、60分钟后溶液中吸光度强度,对比上述标准曲线可得相应的六价铬浓度;f. Use spectrophotometer and colorimetry (volume ratio of sewage and color developer 1:2) to test the absorbance intensity in the solution after 10, 20, 30, and 60 minutes, and compare the above standard curve to obtain the corresponding concentration of hexavalent chromium ;

g.对比研究外加0.001M草酸溶液的六价铬污水在铝片电化学处理过程中的能耗和处理效率。g. Comparative study of the energy consumption and treatment efficiency of the hexavalent chromium sewage added with 0.001M oxalic acid solution in the electrochemical treatment of aluminum sheets.

Claims (4)

1.本专利涉及一种促进重金属铬离子电化学还原的方法,具体操作如下:1. This patent relates to a method for promoting the electrochemical reduction of heavy metal chromium ions. The specific operations are as follows: a.用电子天平和滤纸称取0.0197g重铬酸钾,放入烧杯,用水溶液,最后倒入1000mL的容量瓶中,滴定至标线。配置好的Cr6+溶液的浓度为100μM;a. Use an electronic balance and filter paper to weigh 0.0197g of potassium dichromate, put it into a beaker, use an aqueous solution, and finally pour it into a 1000mL volumetric flask, and titrate to the marked line. The concentration of the prepared Cr 6+ solution is 100 μM; b.利用三电极体系(工作电极为铝片(暴露面积为~2.25cm2);参比电极为饱和甘汞电极(SCE,0.24V vs.NHE)和石墨棒对电极),实验采用电化学工作站提供恒电位-1~-3V外加电在工作电极表面。如图1所示;b. Using a three-electrode system (the working electrode is an aluminum sheet (the exposed area is ~2.25cm 2 ); the reference electrode is a saturated calomel electrode (SCE, 0.24V vs. NHE) and a graphite rod counter electrode), the experiment uses electrochemical The workstation provides a constant potential of -1 ~ -3V to apply electricity on the surface of the working electrode. As shown in Figure 1; c.利用电化学工作站记录0-60分钟内电流密度随时间的变化曲线,进而计算可知一定时间内的功率及能耗;c. Use the electrochemical workstation to record the change curve of current density with time within 0-60 minutes, and then calculate the power and energy consumption within a certain period of time; d.用电子天平和滤纸称取0.5g二苯碳酰二肼,用200mL量筒量取50mL丙酮,将二苯碳酰二肼溶解于丙酮中,在用200mL量筒量取50mL超纯水添加到丙酮中,最后加入4.0mL由1mLH3PO4、1mL H2SO4、2mL H2O混合形成强酸混合溶液,即制备好显色剂溶液;d. Weigh 0.5g of diphenylcarbazide with an electronic balance and filter paper, measure 50mL of acetone with a 200mL graduated cylinder, dissolve diphenylcarbazide in acetone, and add 50mL of ultrapure water with a 200mL graduated cylinder to In acetone, finally add 4.0mL of strong acid mixed solution formed by mixing 1mLH 3 PO 4 , 1mL H 2 SO 4 , and 2mL H 2 O to prepare the developer solution; e.在实验之前,依次配置5、10、20、50、100μM的六价铬溶液,分别取出1.0mL溶液试样,并加入2.0mL的显色剂,摇匀并静置显色15min。15min后,将静置后的待测液加入到比色皿中,并在540nm波长处以空白溶液为参比测定其吸光度。以六价铬浓度为横坐标,相应的吸光度为纵坐标绘制标准曲线。本实验的标准曲线测定为,e. Before the experiment, prepare 5, 10, 20, 50, and 100 μM hexavalent chromium solutions in sequence, take out 1.0 mL of solution samples, add 2.0 mL of chromogenic agent, shake well and let stand for 15 minutes to develop color. After 15 minutes, add the test solution after standing still to the cuvette, and measure its absorbance at a wavelength of 540nm with a blank solution as a reference. Draw a standard curve with the concentration of hexavalent chromium as the abscissa and the corresponding absorbance as the ordinate. The standard curve of this experiment was determined as, <mrow> <msub> <mi>C</mi> <mrow> <mo>(</mo> <mi>c</mi> <mi>o</mi> <mi>n</mi> <mi>c</mi> <mi>e</mi> <mi>n</mi> <mi>t</mi> <mi>r</mi> <mi>a</mi> <mi>t</mi> <mi>i</mi> <mi>o</mi> <mi>n</mi> <mo>)</mo> </mrow> </msub> <mo>=</mo> <mn>55.6</mn> <mo>&amp;times;</mo> <msub> <mi>A</mi> <mrow> <mo>(</mo> <msup> <mi>Cr</mi> <mrow> <mn>6</mn> <mo>+</mo> </mrow> </msup> <mo>)</mo> </mrow> </msub> <mo>-</mo> <mn>0.223</mn> <mo>-</mo> <mo>-</mo> <mo>-</mo> <mrow> <mo>(</mo> <mn>1</mn> <mo>)</mo> </mrow> </mrow> <mrow><msub><mi>C</mi><mrow><mo>(</mo><mi>c</mi><mi>o</mi><mi>n</mi><mi>c</mi><mi>e</mi><mi>n</mi><mi>t</mi><mi>r</mi><mi>a</mi><mi>t</mi><mi>i</mi><mi>o</mi><mi>n</mi><mo>)</mo></mrow></msub><mo>=</mo><mn>55.6</mn><mo>&amp;times;</mo><msub><mi>A</mi><mrow><mo>(</mo><msup><mi>Cr</mi><mrow><mn>6</mn><mo>+</mo></mrow></msup><mo>)</mo></mrow></msub><mo>-</mo><mn>0.223</mn><mo>-</mo><mo>-</mo><mo>-</mo><mrow><mo>(</mo><mn>1</mn><mo>)</mo></mrow></mrow> 注:A(Cr6+)为Cr6+溶液的吸光度Note: A(Cr 6+ ) is the absorbance of Cr 6+ solution f.利用分光光度计和比色法(污水和显色剂的体积比1:2)测试10、20、30、60分钟后溶液中吸光度强度,对比上述标准曲线可得相应的六价铬浓度;f. Use spectrophotometer and colorimetry (volume ratio of sewage and color developer 1:2) to test the absorbance intensity in the solution after 10, 20, 30, and 60 minutes, and compare the above standard curve to obtain the corresponding concentration of hexavalent chromium ; g.对比研究外加0.001M草酸溶液的六价铬污水在铝片电化学处理过程中的能耗和处理效率。g. Comparative study of the energy consumption and treatment efficiency of the hexavalent chromium sewage added with 0.001M oxalic acid solution in the electrochemical treatment of aluminum sheets. 2.如权利要求1所述的一种促进重金属铬离子电化学还原的方法,其特征在于,制备工艺简单,操作方便,草酸类有机物便宜易得,且-1.5V的电极电位便于控制。2. A method for promoting the electrochemical reduction of heavy metal chromium ions as claimed in claim 1, characterized in that the preparation process is simple, easy to operate, oxalic acid organic matter is cheap and easy to get, and the electrode potential of -1.5V is easy to control. 3.如权利要求1所述的一种促进重金属铬离子电化学还原的方法,其特征在于,利用废旧易拉罐铝片实现六价铬污水处理,达到良好的经济和社会效益。3. A method for promoting the electrochemical reduction of heavy metal chromium ions as claimed in claim 1, characterized in that the waste and old pop can aluminum flakes are used to realize hexavalent chromium sewage treatment to achieve good economic and social benefits. 4.如权利要求1所述的一种促进重金属铬离子电化学还原的方法,其特征在于,高效且节能地处理六价铬污水,便于实验室六价铬污染物的就地处理。4. A method for promoting the electrochemical reduction of heavy metal chromium ions as claimed in claim 1, characterized in that the hexavalent chromium sewage is efficiently and energy-savingly treated, which facilitates the on-site treatment of laboratory hexavalent chromium pollutants.
CN201711164870.2A 2017-11-21 2017-11-21 A kind of method for promoting the reduction of heavy metal chromium ion electrochemical Pending CN107720891A (en)

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