CN115739082A - Preparation of carbon-based nano copper oxide catalyst and method for treating cyanide-containing wastewater - Google Patents

Preparation of carbon-based nano copper oxide catalyst and method for treating cyanide-containing wastewater Download PDF

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CN115739082A
CN115739082A CN202211578479.8A CN202211578479A CN115739082A CN 115739082 A CN115739082 A CN 115739082A CN 202211578479 A CN202211578479 A CN 202211578479A CN 115739082 A CN115739082 A CN 115739082A
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copper oxide
nano copper
carbon
solution
cyanide
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崔崇龙
巩春龙
杨明远
翟菊彬
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Changchun Gold Research Institute
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Changchun Gold Research Institute
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Abstract

The invention belongs to the technical field of cyanide-containing wastewater treatment, and particularly relates to a preparation method of a carbon-based nano copper oxide catalyst and a method for treating cyanide-containing wastewater; the invention prepares the carbon-based nano copper oxide catalyst by converting the nano copper hydroxide colloid into the characteristic nano copper oxide colloid and finally loading the characteristic nano copper oxide colloid by active carbon. The carbon-based nano copper oxide catalyst is used for treating the low-concentration cyanide-containing wastewater, namely, the cyanide in the cyanide-containing wastewater is oxidized by adding the nano copper oxide catalyst and sodium metabisulfite, aeration is not needed, the reaction pH is kept to be 7-9.5, the removal rate of the cyanide is well ensured, the process is simple, and the generation of a large amount of foam can be avoided.

Description

Preparation of carbon-based nano copper oxide catalyst and method for treating cyanide-containing wastewater
Technical Field
The invention belongs to the technical field of cyanide-containing wastewater treatment, and particularly relates to a preparation method of a carbon-based nano copper oxide catalyst and a method for treating cyanide-containing wastewater.
Background
In the field of cyanide-containing wastewater treatment, the sulfur dioxide-air method is a common methodIn a certain pH value range, SO is utilized under the catalysis of copper 2 Oxidation of cyanides in wastewater by synergistic action with air, known as sulfur dioxide-air oxidation, often abbreviated as SO 2 the/Air process, also known as the causal process. Copper salt is needed to be added as a catalyst in the process of treating the cyanide-containing wastewater by the scientific method, and aeration is needed at the same time. The addition of copper salt sometimes causes the concentration of copper ions in treated effluent to exceed the standard, the aeration also increases the operation cost, and the aeration of some cyanide-containing wastewater also generates a large amount of foam, thereby influencing the normal operation of the process and increasing the cost. Aiming at the problem, the copper oxide catalyst is prepared, and can be reused without consuming copper salt while treating cyanide-containing wastewater without aeration.
Disclosure of Invention
In order to overcome the problems, the invention provides a method for preparing a carbon-based nano copper oxide catalyst and treating cyanide-containing wastewater, wherein the carbon-based nano copper oxide catalyst is prepared by a chemical method, sodium pyrosulfite and the nano copper oxide catalyst are added into the cyanide-containing wastewater in the treatment process of the low-concentration (total cyanide is less than 150 mg/L) cyanide-containing wastewater, aeration is not needed, the reduction of the total cyanide and easily released cyanide in the cyanide-containing wastewater treated after stirring reaction for 2 hours is obvious, the prepared carbon-supported nano copper oxide catalyst is used for replacing copper salt, and the problems of overproof of the copper ions in the effluent and energy consumption aeration after the cyanide-containing wastewater is treated are solved.
A preparation method of a carbon-based nano copper oxide catalyst comprises the following steps:
step 1, preparing a solution A by using copper chloride dihydrate, copper sulfate or copper nitrate as raw materials and deionized water as a solvent, so that the concentration of copper ions is 4 mM/L-48 mM/L;
step 2, preparing a sodium citrate or polyvinylpyrrolidone solution B, so that the molar ratio of copper in the solution A to sodium citrate or polyvinylpyrrolidone in the solution B is 1:0.5 to 1:1; fully stirring and mixing the solution B and the solution A at normal temperature to obtain a solution C;
step 3, preparing a sodium hydroxide solution D, wherein the molar ratio of copper in the solution C to sodium hydroxide in the sodium hydroxide solution D is 1:0.5 to 1:2;
step 4, uniformly stirring and mixing the solution C and the solution D according to the equal volume to obtain a nano copper hydroxide colloid E;
and 5, adding a hydrogen peroxide solution with the mass fraction of 30% into the nano copper hydroxide colloid E, uniformly stirring to obtain nano copper oxide sol F, and ensuring that the molar ratio of copper to hydrogen peroxide in the nano copper oxide sol F is 1:0.5 to 1:1;
and 6, adding activated carbon into the nano copper oxide sol F for loading, and then carrying out solid-liquid separation to obtain the carbon-based nano copper oxide catalyst.
And in the step 6, 80-400 meshes of active carbon is added into the nano copper oxide sol F according to the loading rate of 0.5-5% for loading.
A method for treating cyanide-containing wastewater by adopting the carbon-based nano copper oxide catalyst comprises the following steps:
placing the prepared carbon-based nano copper oxide catalyst into low-concentration cyanide-containing wastewater with the total cyanide concentration less than 150mg/L, adding sodium pyrosulfite, adding sodium hydroxide to keep the reaction pH between 7 and 9.5, stirring for reaction for 1 to 2 hours, filtering, and recycling the filtered carbon-based nano copper oxide catalyst.
The dosage of the carbon-based nano copper oxide catalyst is 1-4 g/L.
The dosage of the sodium pyrosulfite is 1 to 2g/L.
The invention has the beneficial effects that:
the invention prepares the carbon-based nano copper oxide catalyst by converting the nano copper hydroxide colloid into the characteristic nano copper oxide colloid and finally loading the characteristic nano copper oxide colloid by active carbon. The carbon-based nano copper oxide catalyst is used for treating the low-concentration cyanide-containing wastewater, namely, the cyanide in the cyanide-containing wastewater is oxidized by adding the nano copper oxide catalyst and sodium metabisulfite, aeration is not needed, the reaction pH is kept to be 7-9.5, the removal rate of the cyanide is well ensured, the process is simple, and the generation of a large amount of foam can be avoided.
The nano copper oxide catalyst prepared by the method is a clean and environment-friendly medicament, does not generate secondary pollution, and is economic and environment-friendly. After the nano copper oxide catalyst is used for oxidation and catalysis, the catalyst can be recycled, cyanide in the cyanide-containing wastewater with low concentration can be efficiently treated, the treatment cost is low, the process is simple, and the stable operation is easy.
Detailed Description
The present invention will be described in further detail with reference to examples. It is to be understood that the specific embodiments described herein are merely illustrative of the invention and are not limiting of the invention.
A preparation method of a carbon-based nano copper oxide catalyst comprises the following steps:
step 1, preparing a solution A by using copper chloride dihydrate, copper sulfate or copper nitrate as raw materials and deionized water as a solvent, so that the concentration of copper ions is 4 mM/L-48 mM/L; wherein mM/L is millimole per liter;
step 2, preparing a sodium citrate or polyvinylpyrrolidone solution B, so that the molar ratio of copper in the solution A to sodium citrate or polyvinylpyrrolidone in the solution B is 1:0.5 to 1:1; preparing a sodium citrate or polyvinylpyrrolidone solution B from copper and sodium citrate or polyvinylpyrrolidone according to a certain proportion, and fully stirring and mixing the solution B and the solution A at normal temperature to obtain a solution C;
step 3, preparing a sodium hydroxide solution D, wherein the molar ratio of copper in the solution A to sodium hydroxide in the sodium hydroxide solution D is 1:0.5 to 1:2; namely, the molar ratio of copper to sodium hydroxide in the solution A is 1:0.5 to 1:2, preparing a sodium hydroxide solution D;
step 4, uniformly stirring and mixing the solution C and the solution D according to the equal volume to obtain a nano copper hydroxide colloid E; firstly, preparing copper hydroxide colloid, and then converting the copper hydroxide colloid into characteristic nano copper oxide sol.
And 5, adding a hydrogen peroxide solution with the mass fraction of 30% into the nano copper hydroxide colloid E, uniformly stirring to obtain nano copper oxide sol F, and ensuring that the molar ratio of copper to hydrogen peroxide in the nano copper oxide sol F is 1:0.5 to 1:1;
and 6, adding activated carbon into the nano copper oxide sol F for loading, and then carrying out solid-liquid separation to obtain the carbon-based nano copper oxide catalyst.
In the step 6, 80-400 meshes of active carbon is added into the nano copper oxide sol F according to the loading rate of 0.5-5% for loading.
A method for treating cyanide-containing wastewater by adopting the carbon-based nano copper oxide catalyst comprises the following steps:
the prepared carbon-based nano copper oxide catalyst is arranged in an amount of 1-4 g/L and placed in low-concentration cyanide-containing wastewater with the total cyanide concentration less than 150mg/L, 1-2 g/L of sodium metabisulfite is added, the reaction pH is kept between 7 and 9.5 by adding sodium hydroxide, the mixture is stirred and reacted for 1-2 hours and then filtered, the filtered carbon-based nano copper oxide catalyst is recycled, and the cyanide in the filtrate is obviously removed.
Example 1
(1) Preparation of copper solution
Weighing a certain amount of copper chloride dihydrate, adding 100mL of deionized water to dissolve the copper chloride dihydrate, transferring the copper chloride dihydrate into a volumetric flask to a constant volume of 500mL to obtain 4mM/L copper chloride aqueous solution, and storing the copper chloride aqueous solution in a shade place for later use.
(2) Preparation of dispersing agent
Taking 10mL of copper chloride aqueous solution, fixing the volume to 25mL, and mixing the copper chloride aqueous solution and the dispersant sodium citrate according to a molar ratio of 1:0.5, weighing a certain amount of dispersant sodium citrate, dissolving in pure water, fully and uniformly stirring, and finally fixing the volume to 25mL.
(3) Preparation of sodium hydroxide solution
According to the molar ratio of copper to sodium hydroxide of 1:0.5, dissolving a certain amount of sodium hydroxide in a certain amount of pure water to prepare a sodium hydroxide solution, and metering the volume to 50mL.
(4) Preparation of copper hydroxide sol
And mixing 25mL of copper chloride aqueous solution with 25mL of dispersant solution, stirring at the rotating speed of 400r/min, and then adding 50mL of sodium hydroxide solution to obtain the nano-copper hydroxide sol.
(5) According to the molar ratio of copper to hydrogen peroxide of 1:0.5 dropwise adding 30% hydrogen peroxide into the copper hydroxide sol, and uniformly stirring to finally obtain the nano copper oxide sol, wherein the sol process is light yellow and has obvious Tyndall effect.
(6) Catalyst prepared from activated carbon-loaded copper sol
And adding 80-mesh active carbon into the copper sol according to the loading rate of 0.5% for loading, and loading for 1h to obtain the carbon-supported nano copper catalyst.
(7) 1g of the prepared carbon-based nano copper oxide catalyst is added into 500mL of low-concentration cyanide-containing wastewater of a certain enterprise and continuously stirred, 1g of sodium metabisulfite is added, and the pH value of the reaction is kept to be 7 by adding sodium hydroxide, and the reaction is carried out for 2 hours.
(8) After reacting for 2h, carrying out solid-liquid separation, wherein the solid catalyst can be recycled, and the detection and comparison results of the filtrate are as follows:
Figure BDA0003989928510000031
Figure BDA0003989928510000041
therefore, the method can obviously remove the cyanide in the filtrate, and the removal rate is more than 90 percent.
Example 2:
(1) Preparation of copper solution
Weighing a certain amount of copper sulfate, adding 100mL of deionized water for dissolving, transferring to a volumetric flask for metering to 500mL to obtain 48mM/L copper sulfate aqueous solution, and storing in a shade place for later use.
(2) Preparation of dispersing agent
Taking 10mL of copper sulfate solution, fixing the volume to 25mL, and mixing the copper sulfate solution and the dispersant polyvinylpyrrolidone according to a molar ratio of 1:1 weighing a certain amount of dispersant polyvinylpyrrolidone, dissolving in pure water, fully and uniformly stirring, and finally fixing the volume to 25mL.
(3) Preparation of sodium hydroxide solution
According to the molar ratio of copper to sodium hydroxide of 1:2, dissolving a certain amount of sodium hydroxide in a certain amount of pure water to prepare a sodium hydroxide solution, and metering to 50mL.
(4) Preparation of copper hydroxide sol
Mixing 25mL of copper solution with 25mL of dispersant solution, stirring at the rotating speed of 1000r/min, and then adding 50mL of sodium hydroxide solution to obtain the nano copper hydroxide sol.
(5) According to the molar ratio of copper to hydrogen peroxide of 1:1, dropwise adding 30% hydrogen peroxide into the copper hydroxide sol, and uniformly stirring to finally obtain the nano copper oxide sol, wherein the sol process is light yellow and has obvious Tyndall effect.
(6) Preparation of catalyst by using activated carbon loaded copper sol
Adding 400-mesh active carbon into the copper sol according to the loading rate of 5% for loading, and loading for 1h to obtain the carbon-loaded nano copper catalyst.
(7) 4g of the prepared carbon-based nano copper oxide catalyst is added into 500mL of low-concentration cyanide-containing wastewater of a certain enterprise and continuously stirred, 2g of sodium metabisulfite is added, and the pH value of the reaction is kept at 9.5 by adding sodium hydroxide, and the reaction is carried out for 1h.
(8) After reacting for 1h, carrying out solid-liquid separation, wherein the solid catalyst can be recycled, and the detection result of the filtrate is as follows:
name (R) Total cyanide concentration (mg/L) Concentration of easily released cyanide (mg/L)
Low concentration cyanide-containing waste water 124.9 31.7
After sodium pyrosulfite treatment 55.63 3.75
After sodium pyrosulfite and catalyst are treated 1.51 0.94
It can be seen that the process results in significant cyanide removal from the filtrate.
Although the preferred embodiments of the present invention have been described in detail, the scope of the present invention is not limited to the details of the foregoing embodiments, and any simple modifications within the technical scope of the present invention and the technical solutions and inventive concepts thereof disclosed by the present invention may be equally replaced or changed by those skilled in the art within the technical scope of the present invention.
It should be noted that the various technical features described in the above embodiments can be combined in any suitable manner without contradiction, and the invention is not described in any way for the possible combinations in order to avoid unnecessary repetition.
In addition, any combination of the various embodiments of the present invention can be made, and the same should be considered as the disclosure of the present invention as long as the idea of the present invention is not violated.

Claims (6)

1. A preparation method of a carbon-based nano copper oxide catalyst is characterized by comprising the following steps:
step 1, preparing a solution A by using copper chloride dihydrate, copper sulfate or copper nitrate as raw materials and deionized water as a solvent, so that the concentration of copper ions is 4 mM/L-48 mM/L;
step 2, preparing a sodium citrate or polyvinylpyrrolidone solution B, so that the molar ratio of copper in the solution A to sodium citrate or polyvinylpyrrolidone in the solution B is 1:0.5 to 1:1; fully stirring and mixing the solution B and the solution A at normal temperature to obtain a solution C;
step 3, preparing a sodium hydroxide solution D, wherein the molar ratio of copper in the solution C to sodium hydroxide in the sodium hydroxide solution D is 1:0.5 to 1:2;
step 4, uniformly stirring and mixing the solution C and the solution D according to the equal volume to obtain a nano copper hydroxide colloid E;
and 5, adding a hydrogen peroxide solution with the mass fraction of 30% into the nano copper hydroxide colloid E, uniformly stirring to obtain nano copper oxide sol F, and ensuring that the molar ratio of copper to hydrogen peroxide in the nano copper oxide sol F is 1:0.5 to 1:1;
and 6, adding activated carbon into the nano copper oxide sol F for loading, and then carrying out solid-liquid separation to obtain the carbon-based nano copper oxide catalyst.
2. The preparation method of the carbon-based nano copper oxide catalyst according to claim 1, wherein in the step 6, 80-400 mesh activated carbon is added into the nano copper oxide sol F according to a loading rate of 0.5-5% for loading.
3. The application of the carbon-based nano copper oxide catalyst in the treatment of cyanide-containing wastewater according to any one of claims 1 to 2, which is characterized in that the carbon-based nano copper oxide catalyst is applied in the treatment of cyanide-containing wastewater.
4. The application of the carbon-based nano copper oxide catalyst in the treatment of cyanide-containing wastewater according to claim 3, characterized in that the specific method comprises the following steps:
placing the prepared carbon-based nano copper oxide catalyst into low-concentration cyanide-containing wastewater with the total cyanide concentration less than 150mg/L, adding sodium pyrosulfite, adding sodium hydroxide to keep the reaction pH between 7 and 9.5, stirring for reaction for 1 to 2 hours, filtering, and recycling the filtered carbon-based nano copper oxide catalyst.
5. The application of the carbon-based nano copper oxide catalyst in the treatment of cyanide-containing wastewater according to claim 4, wherein the dosage of the carbon-based nano copper oxide catalyst is 1-4 g/L.
6. The application of the carbon-based nano copper oxide catalyst in the treatment of cyanide-containing wastewater according to claim 4, wherein the amount of the sodium metabisulfite is 1-2 g/L.
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Citations (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US20060241313A1 (en) * 2005-04-26 2006-10-26 Archer-Daniels-Midland Company Copper compositions and their use as hydrogenation catalysts
JP2011168856A (en) * 2010-02-19 2011-09-01 Swing Corp Method and device for recovering copper from copper-containing acid waste liquid
CN102675052A (en) * 2012-05-31 2012-09-19 扬州工业职业技术学院 Method for preparing dihydroxybenzene through phenol hydroxylation reaction
US20120312727A1 (en) * 2011-06-08 2012-12-13 Kabushiki Kaisha Toshiba Copper recovery apparatus
CN103253755A (en) * 2013-05-17 2013-08-21 招金矿业股份有限公司金翅岭金矿 Method for removing cyanide out of gold concentrate cyaniding waste water
CN104445576A (en) * 2014-12-18 2015-03-25 武汉大学 Oxidation treatment method for organic pollutants based on sulfur-oxygen radicals
CN106881088A (en) * 2015-12-15 2017-06-23 南京源泉环保科技股份有限公司 A kind of air oxidation broken cyanide catalyst and preparation method thereof
CN109019988A (en) * 2018-09-20 2018-12-18 陕西太白黄金矿业有限责任公司 A kind of cyaniding tailing slurry drop cyanogen processing system and drop cyanogen method
CN109437277A (en) * 2018-11-05 2019-03-08 上海交通大学 A kind of method of green high-efficient recycling copper ion
CN110385443A (en) * 2019-07-28 2019-10-29 长春黄金研究院烟台贵金属材料研究所有限公司 A kind of preparation method of acid system Nanometer Copper colloidal sol

Patent Citations (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US20060241313A1 (en) * 2005-04-26 2006-10-26 Archer-Daniels-Midland Company Copper compositions and their use as hydrogenation catalysts
JP2011168856A (en) * 2010-02-19 2011-09-01 Swing Corp Method and device for recovering copper from copper-containing acid waste liquid
US20120312727A1 (en) * 2011-06-08 2012-12-13 Kabushiki Kaisha Toshiba Copper recovery apparatus
CN102675052A (en) * 2012-05-31 2012-09-19 扬州工业职业技术学院 Method for preparing dihydroxybenzene through phenol hydroxylation reaction
CN103253755A (en) * 2013-05-17 2013-08-21 招金矿业股份有限公司金翅岭金矿 Method for removing cyanide out of gold concentrate cyaniding waste water
CN104445576A (en) * 2014-12-18 2015-03-25 武汉大学 Oxidation treatment method for organic pollutants based on sulfur-oxygen radicals
CN106881088A (en) * 2015-12-15 2017-06-23 南京源泉环保科技股份有限公司 A kind of air oxidation broken cyanide catalyst and preparation method thereof
CN109019988A (en) * 2018-09-20 2018-12-18 陕西太白黄金矿业有限责任公司 A kind of cyaniding tailing slurry drop cyanogen processing system and drop cyanogen method
CN109437277A (en) * 2018-11-05 2019-03-08 上海交通大学 A kind of method of green high-efficient recycling copper ion
CN110385443A (en) * 2019-07-28 2019-10-29 长春黄金研究院烟台贵金属材料研究所有限公司 A kind of preparation method of acid system Nanometer Copper colloidal sol

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
KE YAO ET AL.: "Understanding the mechanism of ultrasound on the synthesis of cellulose/Cu(OH)2/CuO hybrids", 《ULTRASONICS SONOCHEMISTRY》, vol. 24, pages 27 - 35 *
汪玲 等: "载铜活性炭处理含氰废水的试验研究", 《三峡环境与生态》, vol. 3, no. 1, pages 1 *

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