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CN110607451B - Waste contact body, slurry and slag treatment system and process generated in organic silicon production process - Google Patents

Waste contact body, slurry and slag treatment system and process generated in organic silicon production process Download PDF

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CN110607451B
CN110607451B CN201911038697.0A CN201911038697A CN110607451B CN 110607451 B CN110607451 B CN 110607451B CN 201911038697 A CN201911038697 A CN 201911038697A CN 110607451 B CN110607451 B CN 110607451B
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张凡
辜锋
陈向贵
邓传宏
李学智
余云柏
沙发文
魏清成
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Yunnan Keli Environmental Protection Co ltd
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    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01DCOMPOUNDS OF ALKALI METALS, i.e. LITHIUM, SODIUM, POTASSIUM, RUBIDIUM, CAESIUM, OR FRANCIUM
    • C01D3/00Halides of sodium, potassium or alkali metals in general
    • C01D3/04Chlorides
    • C01D3/06Preparation by working up brines; seawater or spent lyes
    • CCHEMISTRY; METALLURGY
    • C04CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
    • C04BLIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
    • C04B18/00Use of agglomerated or waste materials or refuse as fillers for mortars, concrete or artificial stone; Treatment of agglomerated or waste materials or refuse, specially adapted to enhance their filling properties in mortars, concrete or artificial stone
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    • C04B18/0427Dry materials
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    • C22B1/005Preliminary treatment of scrap
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    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B15/00Obtaining copper
    • C22B15/0063Hydrometallurgy
    • C22B15/0065Leaching or slurrying
    • C22B15/0067Leaching or slurrying with acids or salts thereof
    • C22B15/0069Leaching or slurrying with acids or salts thereof containing halogen
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    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B15/00Obtaining copper
    • C22B15/0063Hydrometallurgy
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    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B19/00Obtaining zinc or zinc oxide
    • C22B19/20Obtaining zinc otherwise than by distilling
    • C22B19/22Obtaining zinc otherwise than by distilling with leaching with acids
    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B19/00Obtaining zinc or zinc oxide
    • C22B19/30Obtaining zinc or zinc oxide from metallic residues or scraps
    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B7/00Working up raw materials other than ores, e.g. scrap, to produce non-ferrous metals and compounds thereof; Methods of a general interest or applied to the winning of more than two metals
    • C22B7/006Wet processes
    • C22B7/007Wet processes by acid leaching
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
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    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
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    • Y02P10/20Recycling
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/50Reuse, recycling or recovery technologies
    • Y02W30/91Use of waste materials as fillers for mortars or concrete

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Abstract

本发明属于废弃物处理技术领域,具体涉及有机硅生产过程中产生的废触体、浆渣处理系统及工艺;包括机械活化装置、反应器、洗涤反应器、置换反应器、回转窑、水解反应器和结晶蒸发装置,机械活化装置进料端与物料、废盐酸出口连接,出料端与反应器连接,反应器分别与洗涤反应器和置换反应器连接,洗涤反应器与回转窑连接,置换反应器与水解反应器连接,水解反应器末端连接有结晶蒸发装置;该技术成熟、流程短、效率高、利于规模化处理,无三废排放,避免对环境产生二次污染,从而实现废触体及浆渣的绿色处理。

Figure 201911038697

The invention belongs to the technical field of waste treatment, and in particular relates to a waste contact body and a slurry and slag treatment system and process generated in the production process of organic silicon; including a mechanical activation device, a reactor, a washing reactor, a replacement reactor, a rotary kiln, a hydrolysis reaction The feed end of the mechanical activation device is connected to the material and the outlet of waste hydrochloric acid, the discharge end is connected to the reactor, the reactor is connected to the washing reactor and the replacement reactor respectively, the washing reactor is connected to the rotary kiln, The reactor is connected with the hydrolysis reactor, and the end of the hydrolysis reactor is connected with a crystallization evaporation device; the technology is mature, the process is short, the efficiency is high, it is conducive to large-scale treatment, no three wastes are discharged, and secondary pollution to the environment is avoided, so as to realize the waste contact body. And green treatment of pulp residue.

Figure 201911038697

Description

System and process for treating waste contact bodies and slurry residues generated in organic silicon production process
Technical Field
The invention belongs to the technical field of waste treatment, and particularly relates to a system and a process for treating waste contacts and slurry residues generated in an organic silicon production process.
Background
In the production process of the organic silicon, silicon and chloromethane are used as production raw materials, and a ternary copper catalyst (main catalyst) and zinc (auxiliary agent) are commonly used for promoting the synthesis of organic silicon monomers such as dimethyldichlorosilane, methyltrichlorosilane, trimethylchlorosilane, methyldichlorosilane and the like. During the synthesis process, slurry and waste contacts are generated.
The main components of the waste contact body are silicon, copper, carbon, zinc and the like, and the weight contents of the silicon, the copper, the carbon, the zinc and the like in the waste contact body are respectively 65% -80%, 3% -20%, 1% -10% and 0.05% -2.0%. The waste contact bodies have fine particles and high activity of copper powder, so that oxidation reaction is easy to occur when the waste contact bodies meet air, organic substances and carbon in the waste contact bodies are burnt to emit pungent white smoke, and the waste contact bodies are difficult to store; the slurry residue is a liquid-solid mixture with fluidity obtained by a wet dust removal process in the process of synthesizing methyl chlorosilane by a direct method, is hydrolyzed into black solid powder, contains about 1 to 3 percent of copper, has serious environmental pollution and has the serious problem of three wastes.
The prior waste contact body treatment methods comprise three methods: the air oxidation method, the oxidant oxidation method and the acidification method all have the problems of low silicon recovery rate, serious water pollution, difficult realization of industrialization and the like. The slurry and the slag have no systematic research, and are mostly treated by burning and then burying at present.
Disclosure of Invention
The invention aims to provide a system and a process for treating waste contacts and slurry residues generated in the production process of organic silicon.
In order to solve the technical problems, the invention adopts the following technical scheme:
the waste contact body and slurry residue treatment system produced in the production process of organic silicon comprises a mechanical activation device, a reactor, a washing reactor, a displacement reactor, a rotary kiln, a hydrolysis reactor and a crystallization evaporation device, wherein the feeding end of the mechanical activation device is connected with a material outlet and a waste hydrochloric acid outlet, the discharging end of the mechanical activation device is connected with the reactor, the reactor is respectively connected with the washing reactor and the displacement reactor, the washing reactor is connected with the rotary kiln, the displacement reactor is connected with the hydrolysis reactor, and the tail end of the hydrolysis reactor is connected with the crystallization evaporation device.
Furthermore, a circulating pipeline is arranged on a pipeline for connecting the washing reactor and the rotary kiln, and the tail end of the circulating pipeline is connected between the mechanical activation device and the reactor.
The waste contact body and slurry slag treatment process produced in the production process of organic silicon comprises the following steps:
1) feeding and filtering: the method comprises the following steps of (1) reasonably mixing waste contact bodies and slurry residues to obtain silicon powder containing about 6-10% of copper, pumping the silicon powder into a reactor after passing through a mechanical activation device, adding 10-20% of waste hydrochloric acid in the organic silicon production process, blowing air to control the oxidation atmosphere in the process under the condition of stirring, slowly adding an additive A and an additive B, leaching for 2-4 hours, and filtering;
2) and (3) leachate treatment: adding 1-3 times of reduced iron powder of copper into the leachate to replace the copper, filtering to obtain a sponge copper product, adding a neutralizing agent into the replaced leachate to recover valuable elements such as iron, zinc and the like, and piling up or taking out iron ore concentrate obtained by filtering;
3) leaching silicon powder treatment: the leached silicon powder is subjected to secondary washing and filtering by waste hydrochloric acid, and then is washed by adding clean water to meet the general solid waste requirements of HJ/T300-2007 and HJ/T299-2007, and can be sold as a building material;
4) waste hydrochloric acid treatment: the used waste hydrochloric acid mainly contains sodium chloride after copper extraction and neutralization, enters an organic silicon project wastewater treatment system for treatment or concentration and crystallization to produce sodium chloride, and can also electrolyze and recover sodium and chlorine elements in the waste hydrochloric acid;
5) hydrogen chloride flue gas treatment: generating a small amount of hydrogen chloride flue gas, absorbing the hydrogen chloride flue gas by clear water through an absorption tower, reaching the environmental protection emission standard, emptying, and returning the absorption liquid to the flow.
Further, in step 1), the amount of air blown into the oxidizing atmosphere is: 10-100L/H.
Further, in the step 1), the additive A is a dispersing agent, and the addition amount of the additive A is 50kg per ton of the material; the additive B is a surfactant, and the addition amount of the additive B is 10kg per ton of the material.
Further, in step 2), the neutralizing agent is sodium carbonate or caustic soda.
Compared with the prior art, the invention has at least one of the following beneficial effects:
the waste contact body or slurry slag is mainly silicon powder containing various heavy metal and other impurities, according to the characteristics of copper, zinc, silicon and other elements and compounds thereof in the silicon powder, waste hydrochloric acid generated in the production process of organic silicon is utilized, under the combined action of various additives, oxidants and surfactants, metal ions such as copper, zinc and the like are leached, replaced or neutralized and recovered, and the obtained silicon powder is washed and treated to meet the requirements of common solid waste or industrial silicon powder. The process has flexible technological conditions, can be used for resource utilization of the silicon powder with high metal content and harmless treatment of the silicon powder with low metal content by effectively improving the leachability of metals such as copper, zinc and the like and the filterability of the silicon powder, and has the recovery rate of both copper and silicon of more than 90 percent.
Drawings
FIG. 1 is a flow chart of the system architecture of the present invention.
1-mechanical activation device, 2-reactor, 3-washing reactor, 4-replacement reactor, 5-rotary kiln, 6-hydrolysis reactor and 7-crystallization evaporation device.
Detailed Description
As shown in fig. 1, in order to make the objects, technical solutions and advantages of the present invention more clearly understood, the present invention will be further described in detail with reference to the accompanying drawings and embodiments. It should be understood that the specific embodiments described herein are merely illustrative of the invention and are not intended to limit the invention.
Example 1
The waste contact body and slurry slag treatment system produced in the production process of organic silicon comprises a mechanical activation device 1, a reactor 2, a washing reactor 3, a displacement reactor 4, a rotary kiln 5, a hydrolysis reactor 6 and a crystallization evaporation device 7, wherein the feeding end of the mechanical activation device 1 is connected with a material and a waste hydrochloric acid outlet, the discharging end is connected with the reactor 2, the reactor 2 is respectively connected with the washing reactor 3 and the displacement reactor 4, the washing reactor 3 is connected with the rotary kiln 5, the displacement reactor 4 is connected with the hydrolysis reactor 6, the tail end of the hydrolysis reactor 6 is connected with the crystallization evaporation device 7, the problem of low recovery of copper and silicon is solved through batching and mechanical activation, and the recovery rate of copper and silicon can reach more than 90%.
Example 2
In addition to example 1, a circulation line is provided in a line connecting the washing reactor 3 and the rotary kiln 5, and the end of the circulation line is connected between the mechanical activation device 1 and the reactor 2, so that the generated solution can be returned to the reaction again, thereby increasing the recovery efficiency.
Example 3
The waste contact body and slurry slag treatment process produced in the production process of organic silicon comprises the following steps:
1) feeding and filtering: obtaining copper-containing silicon powder about 6% of copper by reasonably proportioning waste contacts and slurry slag, firstly pumping into a reactor 2 after passing through a mechanical activation device 1, adding 10% of waste hydrochloric acid in the production process of organic silicon, and blowing an oxidizing atmosphere in the air control process under the condition of stirring, wherein the amount of air blown by the oxidizing atmosphere is as follows: 10L/H, slowly adding an additive A and an additive B, wherein the additive A is a dispersing agent, and the addition amount of the additive A is 50kg per ton of material; the additive B is a surfactant, the addition amount of the additive B is 10kg per ton of the material, and the filtering can be carried out after 2 hours of leaching;
2) and (3) leachate treatment: adding 1 time of reduced iron powder of copper into the leachate to replace the copper, filtering to obtain a sponge copper product, adding a neutralizing agent into the replaced leachate to recover valuable elements such as iron, zinc and the like, wherein the neutralizing agent is sodium carbonate or caustic soda, and piling up or selling iron ore concentrate obtained by filtering;
3) leaching silicon powder treatment: the leached silicon powder is subjected to secondary washing and filtering by waste hydrochloric acid, and then is washed by adding clean water to meet the general solid waste requirements of HJ/T300-2007 and HJ/T299-2007, and can be sold as a building material;
4) waste hydrochloric acid treatment: the used waste hydrochloric acid mainly contains sodium chloride after copper extraction and neutralization, enters an organic silicon project wastewater treatment system for treatment or concentration and crystallization to produce sodium chloride, and can also electrolyze and recover sodium and chlorine elements in the waste hydrochloric acid;
5) hydrogen chloride flue gas treatment: generating a small amount of hydrogen chloride flue gas, absorbing the hydrogen chloride flue gas by clear water through an absorption tower, reaching the environmental protection emission standard, emptying, and returning the absorption liquid to the flow.
The waste contact body or slurry slag is mainly silicon powder containing various heavy metal and other impurities, according to the characteristics of copper, zinc, silicon and other elements and compounds thereof in the silicon powder, waste hydrochloric acid generated in the production process of organic silicon is utilized, under the combined action of various additives, oxidants and surfactants, metal ions such as copper, zinc and the like are leached, replaced or neutralized and recovered, and the obtained silicon powder is washed and treated to meet the requirements of common solid waste or industrial silicon powder. The process has flexible technological conditions, can be used for resource utilization of the silicon powder with high metal content and harmless treatment of the silicon powder with low metal content by effectively improving the leachability of metals such as copper, zinc and the like and the filterability of the silicon powder, and has the recovery rate of both copper and silicon of more than 90 percent.
Example 4
The waste contact body and slurry slag treatment process produced in the production process of organic silicon comprises the following steps:
1) feeding and filtering: obtaining copper-containing silicon powder about 8% with useless contact and thick liquid sediment through reasonable batching, earlier through mechanical activation device 1 back, pump into reactor 2, add the waste hydrochloric acid of 15% in the organosilicon production process, under the circumstances of stirring, the oxidizing atmosphere of air control process is blown in to the oxidizing atmosphere, and the volume that the air was blown in to the oxidizing atmosphere is: 50L/H, slowly adding an additive A and an additive B, wherein the additive A is a dispersing agent, and the addition amount of the additive A is 50kg per ton of material; the additive B is a surfactant, the addition amount of the additive B is 10kg per ton of the material, and the filtering can be carried out after 3 hours of leaching;
2) and (3) leachate treatment: adding 2 times of reduced iron powder of copper into the leachate to replace the copper, filtering to obtain a sponge copper product, adding a neutralizing agent into the replaced leachate to recover valuable elements such as iron, zinc and the like, wherein the neutralizing agent is sodium carbonate or caustic soda, and piling up or selling iron ore concentrate obtained by filtering;
3) leaching silicon powder treatment: the leached silicon powder is subjected to secondary washing and filtering by waste hydrochloric acid, and then is washed by adding clean water to meet the general solid waste requirements of HJ/T300-2007 and HJ/T299-2007, and can be sold as a building material;
4) waste hydrochloric acid treatment: the used waste hydrochloric acid mainly contains sodium chloride after copper extraction and neutralization, enters an organic silicon project wastewater treatment system for treatment or concentration and crystallization to produce sodium chloride, and can also electrolyze and recover sodium and chlorine elements in the waste hydrochloric acid;
5) hydrogen chloride flue gas treatment: generating a small amount of hydrogen chloride flue gas, absorbing the hydrogen chloride flue gas by clear water through an absorption tower, reaching the environmental protection emission standard, emptying, and returning the absorption liquid to the flow.
The waste contact body or slurry slag is mainly silicon powder containing various heavy metal and other impurities, according to the characteristics of copper, zinc, silicon and other elements and compounds thereof in the silicon powder, waste hydrochloric acid generated in the production process of organic silicon is utilized, under the combined action of various additives, oxidants and surfactants, metal ions such as copper, zinc and the like are leached, replaced or neutralized and recovered, and the obtained silicon powder is washed and treated to meet the requirements of common solid waste or industrial silicon powder. The process has flexible technological conditions, can be used for resource utilization of the silicon powder with high metal content and harmless treatment of the silicon powder with low metal content by effectively improving the leachability of metals such as copper, zinc and the like and the filterability of the silicon powder, and has the recovery rate of both copper and silicon of more than 90 percent.
Example 5
The waste contact body and slurry slag treatment process produced in the production process of organic silicon comprises the following steps:
1) feeding and filtering: obtaining about 10% copper-containing silicon powder with useless contact and thick liquid sediment through reasonable batching, earlier through mechanical activation device 1 back, pump into reactor 2, add 20% waste hydrochloric acid in the organosilicon production process, under the circumstances of stirring, the oxidizing atmosphere of air control process is blown in to the oxidizing atmosphere, and the volume of air is blown in to the oxidizing atmosphere: 100L/H, slowly adding an additive A and an additive B, wherein the additive A is a dispersing agent, and the addition amount of the additive A is 50kg per ton of material; the additive B is a surfactant, the addition amount of the additive B is 10kg per ton of the material, and the filtering can be carried out after leaching for 4 hours;
2) and (3) leachate treatment: adding 3 times of reduced iron powder of copper into the leachate to replace the copper, filtering to obtain a sponge copper product, adding a neutralizing agent into the replaced leachate to recover valuable elements such as iron, zinc and the like, wherein the neutralizing agent is sodium carbonate or caustic soda, and piling up or selling iron ore concentrate obtained by filtering;
3) leaching silicon powder treatment: the leached silicon powder is subjected to secondary washing and filtering by waste hydrochloric acid, and then is washed by adding clean water to meet the general solid waste requirements of HJ/T300-2007 and HJ/T299-2007, and can be sold as a building material;
4) waste hydrochloric acid treatment: the used waste hydrochloric acid mainly contains sodium chloride after copper extraction and neutralization, enters an organic silicon project wastewater treatment system for treatment or concentration and crystallization to produce sodium chloride, and can also electrolyze and recover sodium and chlorine elements in the waste hydrochloric acid;
5) hydrogen chloride flue gas treatment: generating a small amount of hydrogen chloride flue gas, absorbing the hydrogen chloride flue gas by clear water through an absorption tower, reaching the environmental protection emission standard, emptying, and returning the absorption liquid to the flow.
The waste contact body or slurry slag is mainly silicon powder containing various heavy metal and other impurities, according to the characteristics of copper, zinc, silicon and other elements and compounds thereof in the silicon powder, waste hydrochloric acid generated in the production process of organic silicon is utilized, under the combined action of various additives, oxidants and surfactants, metal ions such as copper, zinc and the like are leached, replaced or neutralized and recovered, and the obtained silicon powder is washed and treated to meet the requirements of common solid waste or industrial silicon powder. The process has flexible technological conditions, can be used for resource utilization of the silicon powder with high metal content and harmless treatment of the silicon powder with low metal content by effectively improving the leachability of metals such as copper, zinc and the like and the filterability of the silicon powder, and has the recovery rate of both copper and silicon of more than 90 percent.
Experimental analysis:
1. results of toxicity test before calcination
The leaching toxicity test is carried out by adopting the HJ/T299-2007 standard (sulfuric acid-nitric acid method), and the contents of copper and zinc in the solution reach the standard requirement of less than 100 mg/l.
TABLE 1 toxicity test results
Figure BDA0002252260500000081
2. Post calcination leach toxicity test
After the copper is extracted from the waste contacts and the pulp slag, the waste contacts and the pulp slag are calcined for 2 hours at 1100 ℃ under the oxidation condition, the materials are still loose and powdery, the caking phenomenon is avoided, the burning loss of the pulp slag is 13.77 percent, and the burning loss of the waste contacts is 0.61 percent. The leaching toxicity test is carried out by adopting the HJ/T299-2007 standard (sulfuric acid-nitric acid method), and the contents of copper, zinc, lead, chromium, cadmium, nickel and the like all reach the standard requirements. The detailed results are as follows:
TABLE 2 calcined silica fume leaching toxicity test results
Unit: mg/l
Figure BDA0002252260500000082
Although the invention has been described herein with reference to a number of illustrative embodiments thereof, it should be understood that numerous other modifications and embodiments can be devised by those skilled in the art that will fall within the spirit and scope of the principles of this disclosure. More specifically, various variations and modifications are possible in the component parts and/or arrangements of the subject combination arrangement within the scope of the disclosure, the drawings and the appended claims. In addition to variations and modifications in the component parts and/or arrangements, other uses will also be apparent to those skilled in the art.

Claims (2)

1.有机硅生产过程中产生的废触体、浆渣处理系统,其特征在于:包括机械活化装置(1)、反应器(2)、洗涤反应器(3)、置换反应器(4)、回转窑(5)、水解反应器(6)和结晶蒸发装置(7),机械活化装置(1)进料端与物料、废盐酸出口连接,出料端与反应器(2)连接,反应器(2)分别与洗涤反应器(3)和置换反应器(4)连接,洗涤反应器(3)与回转窑(5)连接,置换反应器(4)与水解反应器(6)连接,水解反应器(6)末端连接有结晶蒸发装置(7);1. The waste contact body and slurry treatment system produced in the process of organosilicon production, characterized in that it comprises a mechanical activation device (1), a reactor (2), a washing reactor (3), a replacement reactor (4), Rotary kiln (5), hydrolysis reactor (6) and crystallization evaporation device (7), the feed end of the mechanical activation device (1) is connected with the material and the outlet of waste hydrochloric acid, and the discharge end is connected with the reactor (2), the reactor (2) are respectively connected with the washing reactor (3) and the replacement reactor (4), the washing reactor (3) is connected with the rotary kiln (5), the replacement reactor (4) is connected with the hydrolysis reactor (6), and the hydrolysis reactor (4) is connected with the hydrolysis reactor (6). The end of the reactor (6) is connected with a crystallization evaporation device (7); 有机硅生产过程中产生的废触体、浆渣处理工艺,包括如下步骤:The treatment process of waste contact body and slurry produced in the production process of organic silicon includes the following steps: 1)加料过滤:将废触体和浆渣通过合理的配料,得到含铜6-10%含铜硅粉,先经过机械活化装置(1)后,泵入反应器(2)中,加入有机硅生产过程中的10-20%的废盐酸,在搅拌的情况下,鼓入空气控制过程的氧化气氛,氧化气氛鼓入空气的量为:10—100L/H,缓慢加入添加剂A和添加剂B,添加剂A为分散剂,添加剂A的加入量为每吨物料加入50kg;添加剂B为表面活性剂,添加剂B的加入量为每吨物料加入10kg,浸出2—4小时即可过滤;1) Feeding and filtration: Pass the waste contact body and slurry through reasonable ingredients to obtain copper-containing 6-10% copper-containing silicon powder. After passing through the mechanical activation device (1), it is pumped into the reactor (2), and organic The 10-20% waste hydrochloric acid in the silicon production process is blown into the oxidizing atmosphere of the air control process under stirring. The amount of air blown into the oxidizing atmosphere is: 10-100L/H, slowly add Additive A and Additive B , Additive A is a dispersant, and the amount of Additive A is 50kg per ton of material; Additive B is a surfactant, and the amount of Additive B is 10kg per ton of material, and it can be filtered after leaching for 2-4 hours; 2)浸出液处理:浸出液中加入铜的1-3倍还原铁粉置换铜,过滤得到海绵铜产品,置换后液加入中和剂回收铁、锌有价元素,中和剂为纯碱或烧碱,过滤得到的铁精矿堆存或外卖;2) Leachate treatment: Add 1-3 times reduced iron powder of copper to the leaching solution to replace copper, filter to obtain sponge copper product, add neutralizer to recover iron and zinc valuable elements after replacement, neutralizer is soda ash or caustic soda, filter Received iron ore concentrate for stockpiling or takeaway; 3)浸出硅粉处理:浸出后的硅粉经过废盐酸二次洗涤过滤,再加入清水洗涤后可达到HJ/T 300-2007、HJ/T 299-2007的一般固体废物要求,可作为建筑材料销售;3) Treatment of leached silicon powder: The leached silicon powder is washed and filtered by waste hydrochloric acid for a second time, and then washed with clean water, which can meet the general solid waste requirements of HJ/T 300-2007 and HJ/T 299-2007, and can be used as building materials Sales; 4)废盐酸处理:所用的废盐酸经过提铜、中和后,主要含有氯化钠,进入有机硅项目废水处理系统处理或浓缩结晶生产氯化钠,也电解回收其中的钠和氯元素;4) Waste hydrochloric acid treatment: After copper extraction and neutralization, the used waste hydrochloric acid mainly contains sodium chloride, which is processed or concentrated and crystallized to produce sodium chloride in the wastewater treatment system of the silicone project, and the sodium and chlorine elements are also electrolytically recovered; 5)氯化氢烟气处理:产生极少量氯化氢烟气,经过吸收塔用清水吸收后,达到环保排放标准排空,吸收液返回流程。5) Hydrogen chloride flue gas treatment: a very small amount of hydrogen chloride flue gas is generated, which is absorbed by the absorption tower with clean water, and then emptied to meet the environmental protection emission standards, and the absorption liquid is returned to the process. 2.根据权利要求1所述的有机硅生产过程中产生的废触体、浆渣处理系统,其特征在于:洗涤反应器(3)与回转窑(5)连接的管道上设置有循环管道,循环管道末端连接在机械活化装置(1)和反应器(2)之间。2. The system for treating waste contact bodies and slag produced in the process of organosilicon production according to claim 1, characterized in that: a pipeline connecting the washing reactor (3) and the rotary kiln (5) is provided with a circulation pipeline, The end of the circulation pipe is connected between the mechanical activation device (1) and the reactor (2).
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