CN111204940A - Treatment method of copper smelting sludge - Google Patents
Treatment method of copper smelting sludge Download PDFInfo
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- CN111204940A CN111204940A CN202010020175.4A CN202010020175A CN111204940A CN 111204940 A CN111204940 A CN 111204940A CN 202010020175 A CN202010020175 A CN 202010020175A CN 111204940 A CN111204940 A CN 111204940A
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F11/00—Treatment of sludge; Devices therefor
- C02F11/008—Sludge treatment by fixation or solidification
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/10—Inorganic compounds
- C02F2101/103—Arsenic compounds
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/10—Inorganic compounds
- C02F2101/20—Heavy metals or heavy metal compounds
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Abstract
A treatment method of copper smelting sludge, which relates to a comprehensive utilization and environmental protection treatment method of copper smelting sludge. The method is characterized in that the treatment process comprises the steps of mixing the copper smelting sludge with red mud, slag, desulfurized gypsum and additives, pressing and forming, and curing to form the sludge solidified body. According to the treatment method, the strong basicity of the red mud is utilized, the copper smelting sludge diluted by adding water is subjected to pH adjustment pretreatment, and the sludge slurry is adjusted to be alkaline so as to precipitate most heavy metal ions; the method is characterized in that the viscosity, the adsorbability and the plasticity of the red mud are utilized, slag, desulfurized gypsum and additives are matched to solidify the pretreated copper smelting sludge, heavy metal and arsenic in the sludge are subjected to harmless treatment by forming hydroxide, adsorption, physical wrapping, calcium arsenate salt formation and the like, and finally a sludge solidified body with certain mechanical strength is formed, so that the aim of solidifying arsenic ions and heavy metal ions such as Cu and Hg is fulfilled, the copper smelting sludge is converted from dangerous solid waste into general solid waste, the waste is treated by waste, and the environmental protection cost is reduced.
Description
Technical Field
A treatment method of copper smelting sludge, which relates to a comprehensive utilization and environmental protection treatment method of copper smelting sludge.
Background
In copper smelting plants, acid wastewater is treated by a lime-iron salt method to generate a large amount of copper smelting sludge containing arsenic, Cu, Hg and other heavy metals. These heavy metal compounds are unstable and release heavy metal ions easily in the case of stockpiling. At present, copper smelting sludge is listed in a dangerous waste list as copper-containing waste and mercury-containing waste, the leaching toxicity of arsenic ions of the copper smelting sludge is far beyond the national standard of the people's republic of China-hazardous waste identification standard leaching toxicity identification (GB5085.3-2007), a professional institution is required for treatment, and the treatment cost is high.
At present, the treatment method for dangerous solid wastes such as copper smelting sludge at home and abroad mainly considers the comprehensive utilization after solidification treatment. The solidification treatment is a process for stabilizing hazardous waste by blending and wrapping the hazardous waste in a dense inert material by a physical-chemical method.
Solidification technology was first developed from the disposal of hazardous radioactive waste, and has been used in japan and europe for many years. In recent years, the united states has begun to appreciate this technology. Today, solidification technology has been widely used to treat arsenic slag, mercury slag, electroplating sludge, cadmium slag, etc. In Japan and the United states, solidification technology has been specified to be applicable to treatment of hazardous waste including sludge from steel making, sludge from lead-based detonator wastewater treatment, oil refinery secondary oil residue, heavy metal sludge from metal surface treatment, and electroplating sludge.
At present, the solidification technology of hazardous wastes at home and abroad mainly comprises five solidification methods of cement solidification, plastic solidification, lime solidification, self-cementation solidification and melting solidification. The curing principle, the applicable range and the advantages and disadvantages are shown in the following table.
The five curing forms have advantages and disadvantages, and generally, the curing effect is not ideal and the capacity increase is large due to simple process and low cost; the process is complex, needs professional personnel and equipment with good effect, and has high cost. Therefore, the development of a compound curing mode with low cost and good effect is the future trend of the industry.
CN106978609A discloses a method for recycling and comprehensively utilizing copper in copper-containing sludge, which is to perform drying and acidification on the copper-containing sludge to prepare electrolyte for electrolysis to obtain metal copper, thereby realizing the recycling of the copper. But other heavy metals are not treated, and the waste residue still belongs to dangerous waste.
CN103979755A discloses a comprehensive treatment method of electroplating sludge and low-content copper-containing sludge, which is to mix, dry and acidify the electroplating sludge to be treated and the low-content copper-containing sludge to prepare electrolyte and electrolyze the electrolyte to generate a high-purity mixed metal electrolytic plate. The invention comprehensively treats various heavy metals in the copper smelting sludge, but has complex process and higher cost.
CN103011738A discloses a method for solidifying copper sludge, which takes copper sludge, fly ash, cement, pizza slag and the like in the metallurgical industry as raw materials, prepares a finished product through the processes of mixing, grinding, injection molding, forming, curing and the like, fully utilizes waste resources in the metallurgical industry, only utilizes the adsorption of the fly ash and the solidification performance of materials such as cement, and needs to add raw materials such as fly ash and cement with higher proportion, thus greatly increasing the volume.
CN201410197446.8 provides a method for comprehensively utilizing high-arsenic heavy metal sludge resources, which is to dry and crush the high-arsenic heavy metal sludge, decompose and extract heavy metals at high temperature and prepare sulfuric acid, thereby achieving the purpose of comprehensively utilizing the resources. But the process is complex and the energy consumption is large.
CN201410841628.4 provides a method for multi-cycle selective leaching of copper, zinc and nickel in copper smelting wastewater sludge, heavy metals in copper smelting sludge are leached and extracted by a multi-stage acidification method, the principle is clear, the method is simple, but the process flow is complex, the consumption of strong acid is large, and strong acid wastewater is generated.
Wang Hukun, Li bright day, etc. studied the comprehensive utilization of copper smelting sludge from the major metallurgy of nonferrous metals company, firstly extracting noble metals such as copper, gold, silver, etc. from the sludge, and then mixing with materials such as river sand, fly ash, etc. to press and solidify the mixture. Although part of the noble metal can be recovered, the process is complex and the cost is high.
Zhengaihua and the like utilize an ammonia leaching method to recover copper elements in copper smelting sludge. Although more copper can be extracted, the process is complex, and the sludge is not treated by other heavy metals.
Li soldier et al proposed a copper smelting sludge treatment method, combining copper smelting process and pyrogenic process treatment process of copper-containing sludge for synergistic treatment. It is not suitable for most copper smelting enterprises with fixed processes.
Therefore, the existing methods for treating copper smelting sludge are mostly used for extracting heavy metals from copper smelting sludge, and few treatment methods for harmlessly treating the copper smelting sludge are needed, so that the research on a method which has simple process and low cost and can synergistically utilize various industrial solid wastes to carry out harmless treatment on the copper smelting sludge is urgent.
Disclosure of Invention
The invention aims to provide a method for treating copper smelting sludge, which can utilize various solid wastes in a synergistic manner, has simple process, low treatment cost and good heavy metal ion solidification effect and does not produce secondary pollution, aiming at the defects of the prior art.
The purpose of the invention is realized by the following technical scheme.
A method for treating copper smelting sludge is characterized in that the copper smelting sludge is mixed with red mud, slag and desulfurized gypsum in the treatment process, a small amount of additives are added, and the mixture is pressed, molded and maintained to form a sludge solidified body.
The method for treating the copper smelting sludge is characterized in that the copper smelting sludge obtained by mixing the copper smelting sludge with red mud, slag, desulfurized gypsum and additives is diluted and then the pH value is adjusted to 9-10.
The invention relates to a method for treating copper smelting sludge, which is characterized in that when the copper smelting sludge is mixed with red mud, slag, desulfurized gypsum and an additive, the amount of the added red mud is as follows: the weight ratio of the copper smelting sludge to the red mud is 1: 1-1: 3.
the invention relates to a method for treating copper smelting sludge, which is characterized in that when the copper smelting sludge is mixed with red mud, slag, desulfurized gypsum and an additive, the added slag amount is as follows: the weight ratio of the copper smelting sludge to the slag is 5: 1-10: 1.
the invention relates to a method for treating copper smelting sludge, which is characterized in that when the copper smelting sludge is mixed with red mud, slag, desulfurized gypsum and an additive, the amount of the desulfurized gypsum added is as follows: the weight ratio of the copper smelting sludge to the desulfurized gypsum is 5: 1-10: 1.
the invention relates to a method for treating copper smelting sludge, which is characterized in that when the copper smelting sludge is mixed with red mud, slag, desulfurized gypsum and an additive, the additive is one or a mixture of cement, polyvinyl alcohol and carboxymethyl cellulose, and the total addition amount is as follows: the weight ratio of the copper smelting sludge to the total addition amount is 200: 1-100: 1.
the invention relates to a method for treating copper smelting sludge, which is characterized in that a mortar stirrer is adopted for mixing in the treatment process, and the mixing time is 5-10 minutes.
The invention relates to a method for treating copper smelting sludge, which is characterized in that a hydraulic press is adopted for compression molding in the treatment process, and the molding pressure is 15-30 MPa.
The invention relates to a method for treating copper smelting sludge, which is characterized in that the curing time after molding in the treatment process is 20-40 hours.
The invention relates to a treatment method of copper smelting sludge, which is characterized in that the dilution multiple of the copper smelting sludge in the dilution process is 2-4 times.
The invention relates to a treatment method of copper smelting sludge, which is characterized in that red mud is added to adjust the pH value after the copper smelting sludge is diluted.
The invention relates to a treatment method of copper smelting sludge, which is characterized in that the copper smelting sludge comprises the following components: one or a mixture of sludge filter cakes and neutralized slag containing heavy metals and arsenic in the process of treating acid wastewater (waste acid) by a lime-iron salt method in copper pyrometallurgy.
The invention relates to a method for treating copper smelting sludge, which is characterized in that the slag comprises the following components: impurities in the iron-making process react with lime and the like to generate a melt with silicate and aluminosilicate as main components.
The invention relates to a method for treating copper smelting sludge, which is characterized in that the desulfurized gypsum comprises the following components: calcium sulfate dihydrate CaSO4·2H2The by-product of the technology for recovering sulfur dioxide in the flue gas of coal or oil by a lime-limestone method with the O content of more than or equal to 93 percent.
The invention relates to a treatment method of copper smelting sludge, which is characterized in that the red mud is as follows: leaching Bayer process red mud with the PH value being more than or equal to 10.
The method is characterized in that solid wastes such as desulfurized gypsum and the like carry out harmless treatment on copper smelting sludge, the copper smelting sludge is treated by utilizing the alkalinity, viscosity, adsorbability and plasticity of red mud and cooperating with solid wastes such as slag, desulfurized gypsum and the like, heavy metal and arsenic in the sludge are subjected to harmless treatment by forming hydroxide, adsorption, physical wrapping, calcium arsenate salt and the like, and finally a sludge solidified body with certain mechanical strength is formed, so that the effect of solidifying arsenic ions and heavy metal ions such as Cu, Hg and the like is achieved, the process is simple, and the treatment cost is low.
Drawings
FIG. 1 is a process flow diagram of the treatment of copper smelting sludge according to the method of the present invention.
Detailed Description
The treatment method of the copper smelting sludge comprises the steps of taking red mud as a main raw material, performing harmless treatment on the copper smelting sludge in cooperation with solid wastes such as slag, desulfurized gypsum and the like, diluting the copper smelting sludge and performing pH adjustment pretreatment, adding the red mud, the slag, the desulfurized gypsum and an additive, uniformly mixing, performing compression molding and curing by using a hydraulic machine, and finally forming a sludge solidified body with certain mechanical strength, so that the effects of solidifying arsenic, heavy metal ions such as Cu and Hg and the like and reducing the environmental protection cost are achieved.
When the copper smelting sludge is diluted, adding water (industrial water) for dilution, wherein the dilution multiple is 2-4 times; diluting copper smelting sludge and adjusting the pH value of the copper smelting sludge to 9-10; preferably, the pH regulator is red mud.
The invention relates to a treatment method of copper smelting sludge, which is characterized in that the weight ratio of the copper smelting sludge to red mud in the treatment process is 1: 1-1: 3; the weight ratio of the copper smelting sludge to the slag is 5: 1-10: 1; the weight ratio of the copper smelting sludge to the desulfurized gypsum is 5: 1-10: 1, the weight ratio of the copper smelting sludge to the additive is 200: 1-100: 1.
the invention relates to a treatment method of copper smelting sludge, which adopts a mortar stirrer for mixing; the mixing time is 5-10 minutes; performing compression molding by a hydraulic press; the molding pressure is 15-30 MPa; and after molding, a natural curing mode is adopted, and the curing time is 20-40 hours.
The technical solution of the present invention will be described in detail by specific examples.
Example 1
The leaching toxicity test before and after the copper smelting sludge treatment of a certain nonferrous metal company is shown in the table 1:
TABLE 1 sludge Leaching toxicity before and after treatment by certain nonferrous metals Co
Diluting the sludge by 4 times, adding red mud to adjust the pH of the sludge to 9, and mixing the sludge with the water according to the weight ratio of 1: 1.5 proportion of red mud, 10: 1, adding slag and desulfurized gypsum in a ratio of 100: 1, performing compression molding under the pressure of 25mPa and maintaining for 30 hours, and detecting the heavy metal leaching toxicity, wherein the results are shown in Table 1, and the table shows that the Cu leaching toxicity is reduced by 67.13%, the As leaching toxicity is reduced by 98.4%, the Zn leaching toxicity is reduced by 88%, the Cd leaching toxicity is reduced by 82%, and the Hg leaching toxicity is reduced by 95%.
Example 2
The leaching toxicity test before and after the treatment of a certain copper smelting plant is shown in Table 2:
TABLE 2 sludge Leaching toxicity before and after treatment in a copper smelting plant
Diluting the sludge by 3 times, adding red mud to adjust the pH of the sludge to 9.5, and mixing the sludge with the water according to the weight ratio of 1: 1 proportion of red mud, and adding the mixture in a proportion of 5: 1, adding slag in a ratio of 10: 1, adding desulfurized gypsum in a ratio of 150: 1, press forming under a pressure of 30mPa and curing for 24 hours, and the heavy metal leaching toxicity was measured, and the results are shown in table 1, where it is understood that the Cu leaching toxicity was reduced by 62.81%, the As leaching toxicity was reduced by 96.51%, the Pb leaching toxicity was reduced by 59.95%, the Zn leaching toxicity was reduced by 80.90%, the Cd leaching toxicity was reduced by 83.48%, and the Hg leaching toxicity was reduced by 42.86%.
Example 3
For a copper smelting enterprise, the leaching toxicity before and after the copper smelting sludge treatment is detected as shown in Table 3:
TABLE 3 sludge Leaching toxicity before and after treatment of certain copper smelting enterprises
Diluting the sludge by 2 times, adding red mud to adjust the pH value to 10, and mixing the obtained product with the water solution of 1: 1 proportion of red mud, and adding the mixture in a proportion of 5: 1, adding slag and desulfurized gypsum in a ratio of 100: 1, performing compression molding at a pressure of 20mPa and curing for 20 hours, and detecting the heavy metal leaching toxicity, the results are shown in table 3, and it can be seen from the table that the Cu leaching toxicity is reduced by 59.91%, the As leaching toxicity is reduced by 93.17%, the Pb leaching toxicity is reduced by 85.19%, the Zn leaching toxicity is reduced by 62.63%, the Cd leaching toxicity is reduced by 80.36%, and the Hg leaching toxicity is reduced by 89.66%.
Claims (15)
1. A method for treating copper smelting sludge is characterized in that the copper smelting sludge, red mud, slag, desulfurized gypsum and additives are mixed, pressed, molded and maintained to form a sludge solidified body in the treatment process.
2. The method according to claim 1, wherein the copper smelting sludge before mixing is diluted and then the pH value of the copper smelting sludge is adjusted to 9-10.
3. The method for treating copper smelting sludge according to claim 1, wherein the amount of red mud added in the process of mixing the copper smelting sludge with red mud, slag, desulfurized gypsum and additives is as follows: the weight ratio of the copper smelting sludge to the red mud is 1: 1-1: 3.
4. the method for treating copper smelting sludge according to claim 1, wherein the amount of slag added in the process of mixing the copper smelting sludge with red mud, slag, desulfurized gypsum and additives is as follows: the weight ratio of the sludge to the slag is 5: 1-10: 1.
5. the method for treating copper smelting sludge according to claim 1, wherein when the copper smelting sludge is mixed with red mud, slag, desulfurized gypsum and additives, the amount of the desulfurized gypsum added is as follows: the weight ratio of the copper smelting sludge to the desulfurized gypsum is 5: 1-10: 1.
6. the method according to claim 1, wherein when the copper smelting sludge is mixed with red mud, slag, desulfurized gypsum and additives, the added additives are one or a mixture of cement, polyvinyl alcohol and carboxymethyl cellulose, and the weight ratio of the copper smelting sludge to the total amount of the additives is 200: 1-100: 1.
7. the method for treating copper smelting sludge according to claim 1, characterized in that the treatment process is carried out by mixing with a mortar mixer for 5-10 minutes.
8. The method for treating copper smelting sludge according to claim 1, wherein a hydraulic press is adopted for compression molding in the treatment process, and the molding pressure is 15-30 MPa.
9. The method according to claim 1, wherein the curing time after the molding in the treatment process is 20 to 40 hours.
10. The method for treating copper smelting sludge according to claim 1, wherein the dilution factor of the copper smelting sludge in the dilution process is 2-4 times.
11. The method for treating copper smelting sludge according to claim 2, characterized in that red mud is added to adjust the pH value after the copper smelting sludge is diluted.
12. The method according to claim 1, wherein the copper smelting sludge comprises: in the copper pyrometallurgy, one or a mixture of sludge filter cake and neutralization slag containing heavy metal and arsenic is treated by a lime-iron salt method in the acid wastewater and waste acid treatment process.
13. The method according to claim 1, wherein the slag is selected from the group consisting of: impurities in the iron-making process react with lime and the like to generate a melt with silicate and aluminosilicate as main components.
14. The method for treating copper smelting sludge according to claim 1, wherein the desulfurized gypsum is: calcium sulfate dihydrate CaSO4·2H2The by-product of the technology for recovering sulfur dioxide in the flue gas of coal or oil by a lime-limestone method with the O content of more than or equal to 93 percent.
15. The method for treating copper smelting sludge according to claim 1, wherein the red mud is: leaching Bayer process red mud with the PH value being more than or equal to 10.
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| CN202010020175.4A CN111204940A (en) | 2020-01-09 | 2020-01-09 | Treatment method of copper smelting sludge |
| CN202011528616.8A CN112499919B (en) | 2020-01-09 | 2020-12-22 | Treatment method of copper smelting sludge |
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| CA1035796A (en) * | 1973-11-30 | 1978-08-01 | Iu Conversion Systems | Disposal method and use of sewage sludge |
| TW261602B (en) * | 1992-09-22 | 1995-11-01 | Timothy John White | |
| US8231711B2 (en) * | 2006-03-23 | 2012-07-31 | J. I. Enterprises, Inc. | Sorption processes |
| CN101691291B (en) * | 2009-09-29 | 2011-10-12 | 北京科技大学 | Method for producing pasty unclassified tailing filling materials containing red mud |
| CN103011738B (en) * | 2013-01-15 | 2014-02-12 | 昆明理工大学 | A kind of solidification method of copper sludge |
| CN103803821A (en) * | 2013-12-16 | 2014-05-21 | 张家港市双林制墨涂装有限公司 | Fly ash cement and preparation method thereof |
| CN105130160B (en) * | 2015-07-14 | 2017-07-04 | 中南大学 | A kind of method of the melting waste slag collaboration solidification containing arsenic and other heavy metal sewage sludges |
| CN105218064B (en) * | 2015-08-24 | 2018-07-24 | 昆明理工大学 | It is a kind of using red mud As polluted soil as the non-burning brick of main material |
| CN105537247B (en) * | 2016-01-27 | 2018-02-09 | 湖南有色金属研究院 | A kind of method for solidifying arsenic-containing waste residue using industrial residue |
| CN108128917B (en) * | 2017-11-23 | 2021-04-09 | 昆明理工大学 | Method for removing various pollutants in copper smelting polluted acid by using Bayer process red mud |
| CN108774024A (en) * | 2018-06-08 | 2018-11-09 | 东莞理工学院 | Arsenic slag solidified body and arsenic slag solidification stabilization method |
| CN109078962B (en) * | 2018-08-30 | 2021-06-18 | 西北矿冶研究院 | A kind of combined treatment method of arsenic-containing acid wastewater, red mud and carbide slag |
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