CN112358132A - Method for treating electroplating wastewater containing cyanogen, zinc and nickel - Google Patents

Method for treating electroplating wastewater containing cyanogen, zinc and nickel Download PDF

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CN112358132A
CN112358132A CN202011230973.6A CN202011230973A CN112358132A CN 112358132 A CN112358132 A CN 112358132A CN 202011230973 A CN202011230973 A CN 202011230973A CN 112358132 A CN112358132 A CN 112358132A
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nickel
zinc
electroplating wastewater
treating
supernatant
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郭志勇
毛新燕
刘世科
刘明星
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Changde Dongxin Metal Surface Treatment Co Ltd
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Changde Dongxin Metal Surface Treatment Co Ltd
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    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F9/00Multistage treatment of water, waste water or sewage
    • 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
    • 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
    • C02F1/28Treatment of water, waste water, or sewage by sorption
    • C02F1/281Treatment of water, waste water, or sewage by sorption using inorganic sorbents
    • 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
    • C02F1/28Treatment of water, waste water, or sewage by sorption
    • C02F1/283Treatment of water, waste water, or sewage by sorption using coal, charred products, or inorganic mixtures containing them
    • 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
    • C02F1/38Treatment of water, waste water, or sewage by centrifugal separation
    • 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
    • C02F1/52Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
    • C02F1/5236Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using inorganic agents
    • 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
    • C02F1/52Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
    • C02F1/54Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using organic material
    • C02F1/56Macromolecular compounds
    • 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
    • C02F1/66Treatment of water, waste water, or sewage by neutralisation; pH adjustment
    • 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
    • C02F2101/16Nitrogen compounds, e.g. ammonia
    • C02F2101/18Cyanides
    • 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
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2103/00Nature of the water, waste water, sewage or sludge to be treated
    • C02F2103/16Nature of the water, waste water, sewage or sludge to be treated from metallurgical processes, i.e. from the production, refining or treatment of metals, e.g. galvanic wastes
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/34Biological treatment of water, waste water, or sewage characterised by the microorganisms used

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  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Removal Of Specific Substances (AREA)
  • Separation Of Suspended Particles By Flocculating Agents (AREA)
  • Water Treatment By Sorption (AREA)

Abstract

The invention belongs to the field of methods for treating electroplating wastewater, and provides a method for treating electroplating wastewater containing cyanogen and zinc and nickel.

Description

Method for treating electroplating wastewater containing cyanogen, zinc and nickel
Technical Field
The invention belongs to the field of methods for treating electroplating wastewater, and particularly relates to a method for treating electroplating wastewater containing cyanogen, zinc and nickel.
Background
The electroplating wastewater is wastewater generated in the electroplating production process, and with the development of the electroplating process, the discharge amount of the heavy metal electroplating wastewater is continuously increased, and the components are gradually complicated. As is known, the discharge of waste water containing heavy metals per year in the electroplating industry of China reaches 4 hundred million tons. The main pollutants are various metal ions, such as Ni, Zn, Pb, Cu, Hg, Fe, etc. In addition, cyanide-containing wastewater generated by the cyaniding electroplating process is increasing, and the demand for removing heavy metals and cyanogen is becoming obvious.
Among various electroplating wastewater treatment technologies, the chemical precipitation method has the advantages of simple operation process and low treatment cost, so that the chemical precipitation method is the most common electroplating wastewater treatment technology, but due to electroplating process defects and wastewater quality complexity, the stability of pH value and the completeness of chemical precipitation are difficult to ensure, so that the problems of poor treatment effect, secondary treatment and the like of the chemical precipitation method are caused. Therefore, how to improve the pollutant purification effect of the cyanide/zinc-containing electroplating wastewater and overcome the difficult problem that a large amount of dangerous wastes are generated in the traditional heavy metal wastewater precipitation purification process becomes a technical problem which needs to be solved for developing a novel efficient treatment of the cyanide/zinc-containing heavy metal wastewater.
Disclosure of Invention
The technical problems to be solved by the invention are as follows: aiming at the defects of the prior art, the invention provides a method for treating electroplating wastewater containing cyanogen, zinc and nickel by a biological method, which decomposes the electroplating wastewater containing cyanogen, zinc and nickel into non-toxic substances to achieve the aim of wastewater treatment, and the content of the invention is as follows:
the invention aims to provide a method for treating electroplating wastewater containing cyanogen, zinc and nickel, which has the technical points that: the method for treating the electroplating wastewater containing cyanogen, zinc and nickel comprises the following steps:
the method comprises the following steps: adjusting the pH value of electroplating wastewater containing cyanogen, zinc and nickel to 5-6, adding a sodium dimethyldithiocarbamate aqueous solution for reaction to obtain a mixture A, wherein the volume ratio of the sodium dimethyldithiocarbamate aqueous solution to the electroplating wastewater containing cyanogen, zinc and nickel is 5-6: 100, respectively;
step two: sequentially adding a coagulant aid, a flocculating agent and an adsorbent into the mixture A obtained in the step one for treatment, and then separating the mixture A in a centrifuge at the rotating speed of 3000-4000rmp for 20-40min to obtain a supernatant A and a precipitate A;
step three: adjusting the pH value of the supernatant A in the step two to be 6.7-7.2, then treating the supernatant A in gram-negative bacilli for 7-16h, and then separating the supernatant A in a centrifuge at the rotating speed of 3000-;
step four: treating the supernatant B obtained in the third step for 40-80h by nitrobacteria, separating for 20-40min in a centrifuge at the rotating speed of 3000-4000rmp to obtain a supernatant C and a precipitate C, discarding the precipitate C, and discharging the supernatant C after the discharge detection reaches the standard.
In some embodiments of the present invention, the mass concentration of the sodium dimethyldithiocarbamate aqueous solution in the first step of the method for treating electroplating wastewater containing cyanogen, zinc and nickel is 70-100 g/L.
In a further embodiment of the present invention, the coagulant aid in step two of the above method for treating electroplating wastewater containing cyanogen, zinc and nickel is at least one of polyacrylamide and polydimethyldiallylammonium chloride.
In some embodiments of the present invention, the flocculant in the second step of the method for treating electroplating wastewater containing cyanogen, zinc and nickel is at least one of an iron-based flocculant and an aluminum-based flocculant.
In some embodiments of the invention, the iron-based flocculant is at least one of ferric chloride, ferric sulfate, polymeric ferric chloride and polymeric ferric sulfate.
In some embodiments of the present invention, the aluminum-based flocculant is at least one of aluminum chloride, aluminum sulfate, polyaluminum chloride and polyaluminum sulfate.
In a further embodiment of the present invention, in the second step of the method for treating electroplating wastewater containing cyanogen, zinc and nickel, the adsorbent is at least one of powdered activated carbon and diatomite.
In a further embodiment of the present invention, the gram-negative bacillus in step three of the above method for treating electroplating wastewater containing cyanogens, zinc and nickel is one of Bacteroides fragilis, Bacteroides thetaiotaomicron and Citrobacter rodent.
In some embodiments of the present invention, the nitrifying bacteria in step four of the above method for treating electroplating wastewater containing cyanogen, zinc and nickel are one of Nitrospira, Nitraria and Nitrosclerospermum.
Compared with the prior art, the invention has the beneficial effects that:
the method adopts a biodegradation mode to remove cyanogen, zinc and nickel in the electroplating wastewater containing cyanogen, zinc and nickel, adopts gram-negative bacilli to oxidize the cyanides in the electroplating wastewater containing cyanogen, zinc and nickel into carbon dioxide, sulfate and ammonia, simultaneously removes heavy metals and nickel from the wastewater by the adsorption of the gram-negative bacilli, adopts nitrobacteria to remove the ammonia generated in the third step, and converts the ammonia into nitrite to be absorbed and utilized by the nitrobacteria.
Detailed Description
The technical solutions in the embodiments of the present invention will be clearly and completely described below so that those skilled in the art can better understand the advantages and features of the present invention, and thus the scope of the present invention will be more clearly defined. The embodiments described herein are only a few embodiments of the present invention, rather than all embodiments, and all other embodiments that can be derived by one of ordinary skill in the art without inventive faculty based on the embodiments described herein are intended to fall within the scope of the present invention.
Example 1
A method for treating electroplating wastewater containing cyanogen, zinc and nickel comprises the following steps:
the method comprises the following steps: adjusting the pH value of electroplating wastewater containing cyanogen, zinc and nickel to 5.5, adding a sodium dimethyldithiocarbamate aqueous solution for reaction to obtain a mixture A, wherein the volume ratio of the sodium dimethyldithiocarbamate aqueous solution to the electroplating wastewater containing cyanogen, zinc and nickel is 5.5: 100, respectively;
step two: sequentially adding a coagulant aid, a flocculating agent and an adsorbent into the mixture A obtained in the step one for treatment, and then separating the mixture A in a centrifuge at the rotating speed of 3500rmp for 30min to obtain a supernatant A and a precipitate A;
step three: adjusting the pH value of the supernatant A in the step two to 7.1, then treating the supernatant A in gram-negative bacilli for 12h, and then separating the supernatant A in a centrifuge at 3500rmp rotation speed for 30min to obtain a supernatant B and a precipitate B;
step four: treating the supernatant B obtained in the third step for 60 hours by nitrobacteria, separating the supernatant B in a centrifuge at the rotation speed of 3500rmp for 30min to obtain a supernatant C and a precipitate C, discarding the precipitate C, and discharging the supernatant C after the detection reaches the standard.
In the first step of the method for treating the electroplating wastewater containing cyanogen, zinc and nickel, the mass concentration of the sodium dimethyldithiocarbamate aqueous solution is 85 g/L.
The coagulant aid in the second step of the method for treating the electroplating wastewater containing cyanogen, zinc and nickel is polyacrylamide.
The flocculant in the second step of the method for treating the electroplating wastewater containing cyanogen, zinc and nickel is an iron-based flocculant.
The iron-based flocculant is ferric chloride.
In the second step of the method for treating the electroplating wastewater containing cyanogen, zinc and nickel, the adsorbent is powdered activated carbon.
In the third step of the method for treating the electroplating wastewater containing cyanogen, zinc and nickel, the gram-negative bacillus is bacteroides fragilis.
The nitrifying bacteria in the fourth step of the method for treating the electroplating wastewater containing cyanogen, zinc and nickel are nitrosospira.
The concentration of zinc in the zinc-nickel alloy electroplating wastewater treated in the embodiment is detected to be 0.14mg/L, the concentration of nickel is detected to be 0.040mg/L, the concentration of cyanogen is detected to be 0.045mg/L, and the effluent is stable.
Example 2
A method for treating electroplating wastewater containing cyanogen, zinc and nickel comprises the following steps:
the method comprises the following steps: adjusting the pH value of electroplating wastewater containing cyanogen, zinc and nickel to 5, adding a sodium dimethyldithiocarbamate aqueous solution for reaction to obtain a mixture A, wherein the volume ratio of the sodium dimethyldithiocarbamate aqueous solution to the electroplating wastewater containing cyanogen, zinc and nickel is 5: 100, respectively;
step two: sequentially adding a coagulant aid, a flocculating agent and an adsorbent into the mixture A obtained in the step one for treatment, and then separating the mixture A in a centrifuge at the rotating speed of 3000rmp for 40min to obtain supernatant A and precipitate A;
step three: adjusting the pH value of the supernatant A in the step two to 6.7, then treating the supernatant A in gram-negative bacilli for 7 hours, and then separating the supernatant A in a centrifuge at the rotating speed of 3000rmp for 40min to obtain a supernatant B and a precipitate B;
step four: treating the supernatant B obtained in the third step for 40h by nitrobacteria, then separating for 40min in a centrifuge at the rotating speed of 3000rmp to obtain a supernatant C and a precipitate C, discarding the precipitate C, and discharging the supernatant C after the detection reaches the standard.
In the first step of the method for treating the electroplating wastewater containing cyanogen, zinc and nickel, the mass concentration of the sodium dimethyldithiocarbamate aqueous solution is 70 g/L.
The coagulant aid in the second step of the method for treating the electroplating wastewater containing cyanogen, zinc and nickel is poly-dimethyl diallyl ammonium chloride.
The flocculant in the second step of the method for treating the electroplating wastewater containing cyanogen, zinc and nickel is an aluminum flocculant.
The aluminum flocculant is aluminum chloride.
In the second step of the method for treating the electroplating wastewater containing cyanogen, zinc and nickel, the adsorbent is at least one of diatomite.
The gram-negative bacillus in the third step of the method for treating the electroplating wastewater containing cyanogen, zinc and nickel is bacteroides thetaiotaomicron.
The nitrifying bacteria in the fourth step of the method for treating the electroplating wastewater containing cyanogen, zinc and nickel are Nitraria bacteria.
The concentration of zinc in the zinc-nickel alloy electroplating wastewater treated in the embodiment is detected to be 0.16mg/L, the concentration of nickel is detected to be 0.042mg/L, the concentration of cyanogen is detected to be 0.06mg/L, and the effluent is stable.
Example 3
A method for treating electroplating wastewater containing cyanogen, zinc and nickel comprises the following steps:
the method comprises the following steps: adjusting the pH value of electroplating wastewater containing cyanogen, zinc and nickel to 6, adding a sodium dimethyldithiocarbamate aqueous solution for reaction to obtain a mixture A, wherein the volume ratio of the sodium dimethyldithiocarbamate aqueous solution to the electroplating wastewater containing cyanogen, zinc and nickel is 6: 100, respectively;
step two: sequentially adding a coagulant aid, a flocculating agent and an adsorbent into the mixture A obtained in the step one for treatment, and then separating the mixture A in a centrifuge at the rotating speed of 4000rmp for 20min to obtain supernatant A and precipitate A;
step three: adjusting the pH value of the supernatant A in the step two to 7.2, then treating the supernatant A in gram-negative bacilli for 16h, and then separating the supernatant A in a centrifuge at the rotation speed of 4000rmp for 20min to obtain a supernatant B and a precipitate B;
step four: treating the supernatant B obtained in the third step for 80 hours by nitrobacteria, separating for 20min in a centrifugal machine at the rotating speed of 4000rmp to obtain a supernatant C and a precipitate C, discarding the precipitate C, and discharging the supernatant C after the detection reaches the standard.
The mass concentration of the sodium dimethyldithiocarbamate aqueous solution in the first step of the method for treating the electroplating wastewater containing cyanogen, zinc and nickel is 100 g/L.
The coagulant aid in the second step of the method for treating the electroplating wastewater containing cyanogen, zinc and nickel is poly-dimethyl diallyl ammonium chloride.
The flocculant in the second step of the method for treating the electroplating wastewater containing cyanogen, zinc and nickel is an aluminum flocculant.
The aluminum flocculant is aluminum sulfate.
In the second step of the method for treating the electroplating wastewater containing cyanogen, zinc and nickel, the adsorbent is powdered activated carbon.
In the third step of the method for treating the electroplating wastewater containing cyanogen, zinc and nickel, the gram-negative bacillus is rodent citrobacter.
The nitrifying bacteria in the fourth step of the method for treating the electroplating wastewater containing cyanogen, zinc and nickel are nitrosophyllum bacteria.
The concentration of zinc in the zinc-nickel alloy electroplating wastewater treated in the embodiment is detected to be 0.12mg/L, the concentration of nickel is detected to be 0.037mg/L, the concentration of cyanogen is detected to be 0.03mg/L, and the effluent is stable.
Example 4
A method for treating electroplating wastewater containing cyanogen, zinc and nickel comprises the following steps:
the method comprises the following steps: adjusting the pH value of electroplating wastewater containing cyanogen, zinc and nickel to 6.8, adding a sodium dimethyldithiocarbamate aqueous solution for reaction to obtain a mixture A, wherein the volume ratio of the sodium dimethyldithiocarbamate aqueous solution to the electroplating wastewater containing cyanogen, zinc and nickel is 6.8: 100, respectively;
step two: sequentially adding a coagulant aid, a flocculating agent and an adsorbent into the mixture A obtained in the step one for treatment, and then separating in a centrifuge at a rotating speed of 3800rmp for 22min to obtain a supernatant A and a precipitate A;
step three: adjusting the pH value of the supernatant A in the step two to 6.8, then treating the supernatant A in gram-negative bacilli for 12h, and then separating the supernatant A in a centrifuge at a rotating speed of 3800rmp for 22min to obtain a supernatant B and a precipitate B;
step four: treating the supernatant B obtained in the third step for 48 hours by nitrobacteria, separating for 22min in a centrifugal machine at a rotating speed of 3800rmp to obtain a supernatant C and a precipitate C, discarding the precipitate C, and discharging the supernatant C after the detection reaches the standard.
The mass concentration of the sodium dimethyldithiocarbamate aqueous solution in the first step of the method for treating the electroplating wastewater containing cyanogen, zinc and nickel is 80 g/L.
The coagulant aid in the second step of the method for treating the electroplating wastewater containing cyanogen, zinc and nickel is poly-dimethyl diallyl ammonium chloride.
The flocculant in the second step of the method for treating the electroplating wastewater containing cyanogen, zinc and nickel is an iron-based flocculant.
The iron-based flocculant is ferric sulfate.
In the second step of the method for treating the electroplating wastewater containing cyanogen, zinc and nickel, the adsorbent is diatomite.
In the third step of the method for treating the electroplating wastewater containing cyanogen, zinc and nickel, the gram-negative bacillus is bacteroides fragilis.
The nitrifying bacteria in the fourth step of the method for treating the electroplating wastewater containing cyanogen, zinc and nickel are nitrosospira.
The concentration of zinc in the zinc-nickel alloy electroplating wastewater treated in the embodiment is detected to be 0.13mg/L, the concentration of nickel is detected to be 0.039mg/L, the concentration of cyanogen is detected to be 0.04mg/L, and the effluent is stable.
Finally, it should be noted that the above embodiments are only used for illustrating the technical solutions of the present invention, and not for limiting the protection scope of the present invention, although the present invention is described in detail with reference to the preferred embodiments, it should be understood by those skilled in the art that modifications or equivalent substitutions can be made on the technical solutions of the present invention without departing from the spirit and scope of the technical solutions of the present invention.

Claims (9)

1. A method for treating electroplating wastewater containing cyanogen, zinc and nickel is characterized in that: the method for treating the electroplating wastewater containing cyanogen, zinc and nickel comprises the following steps:
the method comprises the following steps: adjusting the pH value of electroplating wastewater containing cyanogen, zinc and nickel to 5-6, adding a sodium dimethyldithiocarbamate aqueous solution for reaction to obtain a mixture A, wherein the volume ratio of the sodium dimethyldithiocarbamate aqueous solution to the electroplating wastewater containing cyanogen, zinc and nickel is 5-6: 100, respectively;
step two: sequentially adding a coagulant aid, a flocculating agent and an adsorbent into the mixture A obtained in the step one for treatment, and then separating the mixture A in a centrifuge at the rotating speed of 3000-4000rmp for 20-40min to obtain a supernatant A and a precipitate A;
step three: adjusting the pH value of the supernatant A in the step two to be 6.7-7.2, then treating the supernatant A in gram-negative bacilli for 7-16h, and then separating the supernatant A in a centrifuge at the rotating speed of 3000-;
step four: treating the supernatant B obtained in the third step for 40-80h by nitrobacteria, separating for 20-40min in a centrifuge at the rotating speed of 3000-4000rmp to obtain a supernatant C and a precipitate C, discarding the precipitate C, and discharging the supernatant C after the discharge detection reaches the standard.
2. The method for treating cyanide-containing zinc-nickel-containing electroplating wastewater according to claim 1, which comprises the following steps: the mass concentration of the sodium dimethyldithiocarbamate aqueous solution in the first step is 70-100 g/L.
3. The method for treating cyanide-containing zinc-nickel-containing electroplating wastewater according to claim 1, which comprises the following steps: and the coagulant aid in the second step is at least one of polyacrylamide and polydimethyldiallylammonium chloride.
4. The method for treating cyanide-containing zinc-nickel-containing electroplating wastewater according to claim 1, which comprises the following steps: and the flocculating agent in the second step is at least one of an iron flocculating agent and an aluminum flocculating agent.
5. The method for treating cyanide-containing zinc-nickel-containing electroplating wastewater according to claim 4, wherein the method comprises the following steps: the iron-based flocculant is at least one of ferric chloride, ferric sulfate, polymeric ferric chloride and polymeric ferric sulfate.
6. The method for treating cyanide-containing zinc-nickel-containing electroplating wastewater according to claim 4, wherein the method comprises the following steps: the aluminum flocculant is at least one of aluminum chloride, aluminum sulfate, polyaluminum chloride and polyaluminum sulfate.
7. The method for treating cyanide-containing zinc-nickel-containing electroplating wastewater according to claim 1, which comprises the following steps: and in the second step, the adsorbent is at least one of powdered activated carbon and diatomite.
8. The method for treating cyanide-containing zinc-nickel-containing electroplating wastewater according to claim 1, which comprises the following steps: the gram-negative bacillus in step three is one of bacteroides fragilis, bacteroides thetaiotaomicron and citrobacter rodent.
9. The method for treating cyanide-containing zinc-nickel-containing electroplating wastewater according to claim 1, which comprises the following steps: the nitrifying bacteria in the fourth step are one of nitrosospira, nitrobacteria and nitrosofola.
CN202011230973.6A 2020-11-06 2020-11-06 Method for treating electroplating wastewater containing cyanogen, zinc and nickel Pending CN112358132A (en)

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CN109437446A (en) * 2018-10-19 2019-03-08 浙江海拓环境技术有限公司 A kind of zinc nickel alloy electroplating waste water treatment process
CN111018197A (en) * 2020-01-07 2020-04-17 广州超邦化工有限公司 Method for treating alkaline zinc-nickel alloy electroplating and passivation mixed wastewater
CN111573991A (en) * 2020-06-03 2020-08-25 河南双辰环保工程有限公司 Chemical plating comprehensive wastewater treatment method

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