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CN1292016C - Treatment method of organic silicon waste slurry - Google Patents

Treatment method of organic silicon waste slurry Download PDF

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Publication number
CN1292016C
CN1292016C CNB2003101153862A CN200310115386A CN1292016C CN 1292016 C CN1292016 C CN 1292016C CN B2003101153862 A CNB2003101153862 A CN B2003101153862A CN 200310115386 A CN200310115386 A CN 200310115386A CN 1292016 C CN1292016 C CN 1292016C
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hydrolysis
slurry
hydrolyzate
solid
copper
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CN1618840A (en
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叶青
王明成
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Petrochina Co Ltd
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    • 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
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Abstract

A method for treating waste residue slurry in the synthetic process of an organic silicon monomer. Most of high-boiling-point substances (recovered) are separated by centrifugal gravity settling, and the hydrolysate obtained by hydrolyzing the residual slurry is easy to extract and free of reducing copper, so that potential safety hazards are eliminated; copper in the slurry is enriched in the hydrolysis solution in the form of copper sulfate and can be recovered by a reduction method, and the recovery rate of the copper reaches more than 95 percent; the solid hydrolysate meets the requirement of environmental protection and can be buried in a heap.

Description

有机硅废渣浆的处理方法Treatment method of organic silicon waste slurry

技术领域technical field

本发明涉及有机硅单体合成过程中形成的废渣浆的处理方法。The invention relates to a treatment method for waste residue slurry formed in the synthesis process of organosilicon monomers.

背景技术Background technique

有机硅单体合成过程中产生的废渣浆约占单体产量的3%。年产五万吨装置将产生1500吨废渣浆,造成大量的氯损失。有机硅废渣浆液体组成沸点大于75℃(主要有二硅烷、二硅氧烷、硅撑烷等),还有悬浮的硅粉、铜、锡等各种金属,暴露在空气中易燃烧和形成酸雾。若采用堆积的方法处理,污染严重,且存在安全隐患。而国内在废渣浆处理技术方面还是一个空白,目前只能积压堵库或简单的回收铜,没有从根本上解决环保问题且造成氯的浪费。国外主要采用水解技术。The waste slurry generated during the synthesis of organosilicon monomer accounts for about 3% of the monomer output. The device with an annual output of 50,000 tons will produce 1,500 tons of waste slurry, resulting in a large amount of chlorine loss. The liquid composition of organic silicon waste slurry has a boiling point greater than 75°C (mainly disilane, disiloxane, silylane, etc.), and there are suspended silicon powder, copper, tin and other metals, which are easy to burn and form when exposed to air. Acid mist. If the stacking method is used for processing, the pollution will be serious and there will be potential safety hazards. However, there is still a blank in domestic waste slurry treatment technology. At present, only the backlog is blocked or the copper is simply recovered, which does not fundamentally solve the environmental protection problem and causes waste of chlorine. Hydrolysis technology is mainly used abroad.

US Pat 4 221 691提供了一种处理废渣浆的方法:向渣浆中加入少量的矿物油以改善水解物的处理特性。但该方法的缺点在于:渣浆与水解介质接触不充分,水解的速度比较缓慢,得到的水解物为粘稠状态,难以从体系中分离;另外,该方法要求在渣浆的有机硅单体分子中,每个硅原子上连接的氯基团不少于3个,但是大多数渣浆中的单体不满足它的要求,因此不能使用该方法处理大多数渣浆;而且在水解过程中加入矿物油将增加废料处理费用,并增加了新的污染源,不符合环保要求。US Pat 4 221 691 provides a method for treating waste slurry: adding a small amount of mineral oil to the slurry to improve the treatment characteristics of the hydrolyzate. However, the disadvantages of this method are: the contact between the slurry and the hydrolysis medium is not sufficient, the hydrolysis rate is relatively slow, and the obtained hydrolyzate is in a viscous state, which is difficult to separate from the system; in addition, this method requires the organosilicon monomer in the slurry In the molecule, there are no less than 3 chlorine groups connected to each silicon atom, but most of the monomers in the slurry do not meet its requirements, so this method cannot be used to treat most of the slurry; and in the hydrolysis process Adding mineral oil will increase waste disposal costs and increase new sources of pollution, which does not meet environmental protection requirements.

US 4 408 030提供了一种含氯硅烷的多物流的废料处理工艺,包括如下步骤:(A)测定物流的平均SICL官能度;(B)混合至少两种物流以使混合物流的SICL官能度大于或等于2.8;(C)在50℃及水解介质沸点之间,用水解介质混合物流使其水解,并(D)分离水解介质,得到胶粒,该胶粒在后续处理过程中易处理,方便运输和进一步处理操作。其中的水解介质选自水、氯化钙溶液、及浓盐酸溶液。水解温度优选60-90℃。可回收水解过程中产生的HCL。该方法中的胶粒可用水洗,以进一步减少胶粒中的氯含量。若水解溶液最初仅含水,则随着水解的进行,形成盐酸,当水中的盐酸饱和时,氯化氢就解析出来。水解介质中可加入盐酸和无机氯化物使水解溶液达到饱和,这样氯化氢在水解开始阶段就解析出来。水解物通过过滤或离心与液体分离,所得固体水解物颗粒不粘附,易于处理,方便运输和进一步处理操作,水解物还可用水一次或多次冲洗,进一步降低水解物中氯的含量。该方法存在的缺点如下:其一,以水、氯化钙溶液、或浓盐酸溶液作水解介质,水解颗粒细小,不易于从反应釜中采出;其二,水解物表面所吸附的氯根离子浓度达到10%以上,若想降至较低浓度,需要大量水冲洗,废酸液排放量大。US 4 408 030 provides a waste treatment process for multi-streams containing chlorosilanes, comprising the steps of: (A) determining the average SICL functionality of the streams; (B) mixing at least two streams so that the SICL functionality of the mixed streams greater than or equal to 2.8; (C) between 50°C and the boiling point of the hydrolysis medium, hydrolyze it with a mixture flow of the hydrolysis medium, and (D) separate the hydrolysis medium to obtain colloidal particles, which are easy to handle in the subsequent treatment process, Easy transport and further processing operations. Wherein the hydrolysis medium is selected from water, calcium chloride solution, and concentrated hydrochloric acid solution. The hydrolysis temperature is preferably 60-90°C. HCL produced during hydrolysis can be recovered. The colloidal particles in this method can be washed with water to further reduce the chlorine content in the colloidal particles. If the hydrolysis solution contains only water at first, hydrochloric acid will be formed as the hydrolysis progresses, and when the hydrochloric acid in the water is saturated, hydrogen chloride will be resolved. Hydrochloric acid and inorganic chloride can be added to the hydrolysis medium to make the hydrolysis solution saturated, so that hydrogen chloride can be resolved at the beginning of hydrolysis. The hydrolyzate is separated from the liquid by filtration or centrifugation, and the resulting solid hydrolyzate particles are non-adherent, easy to handle, convenient for transportation and further processing operations, and the hydrolyzate can also be washed with water one or more times to further reduce the chlorine content in the hydrolyzate. The disadvantages of this method are as follows: first, water, calcium chloride solution, or concentrated hydrochloric acid solution are used as the hydrolysis medium, and the hydrolyzed particles are small and difficult to extract from the reactor; second, the chlorine radicals adsorbed on the surface of the hydrolyzate The ion concentration reaches more than 10%. If you want to reduce it to a lower concentration, you need a lot of water to wash, and the discharge of waste acid is large.

EP 867442A2介绍了一种甲基氯硅烷副产物的水解工艺,该工艺得到至少两相,包括在副产物中加入水介质进行水解,水介质中可含有表面活性剂,PH至少为7左右,温度高于0℃。其中的一相为隋性固体,第二相为水溶液,基本上不含金属,可经处理或不经处理直接排放。可用过滤、沉淀、浮选或离心技术分离固体,及分离水介质以回收盐、硅酸盐或排至废水处理装置。表面活性剂为阴离子或非离子表面活性剂,优选非表面活性剂。该工艺的优点在于:其一,该方法减少了水解液中的重金属浓度,解决了废物处理的难题,水解工艺得到的产品为惰性,高闪点,无气体析出,不粘稠、无尘易流动,易于处理和运输。其二,铜被富集在固体水解物中,可以充分回收。缺点在于:反应产物之一的氯化氢被水解介质中的碱中和成为盐,白白浪费了一部分资源;此外固体水解物中含有的还原性的铜在受热、太阳光长时间照射或堆积的情况下容易发生自燃,是一个重要的安全隐患。EP 867442A2 introduces a hydrolysis process of methyl chlorosilane by-products, the process obtains at least two phases, including adding an aqueous medium to the by-products for hydrolysis, the aqueous medium may contain surfactants, the pH is at least about 7, and the temperature higher than 0°C. One of the phases is an inert solid, and the second phase is an aqueous solution, substantially free of metals, which can be discharged with or without treatment. Solids can be separated by filtration, sedimentation, flotation or centrifugation techniques, and aqueous media can be separated for recovery of salts, silicates or discharge to wastewater treatment plants. Surfactants are anionic or nonionic surfactants, preferably non-surfactants. The advantages of this process are: First, this method reduces the concentration of heavy metals in the hydrolyzate and solves the problem of waste treatment. The product obtained by the hydrolysis process is inert, has a high flash point, no gas precipitation, is not viscous, and is dust-free and easy to digest. Flowy, easy to handle and transport. Second, copper is enriched in the solid hydrolyzate and can be fully recovered. The disadvantage is that hydrogen chloride, one of the reaction products, is neutralized by the alkali in the hydrolysis medium to become a salt, which wastes a part of resources; in addition, the reduced copper contained in the solid hydrolyzate is heated, exposed to sunlight for a long time or piled up. It is prone to spontaneous combustion and is an important safety hazard.

DE4 116925 A1介绍了一种甲基氯硅烷副产物的水解工艺,通过对由氯-和/或有机氯硅烷的直接混合物组成的残液进行制备,在温度从20℃升到100℃时(主要是在35℃~60℃间),与浓度为20%~70%(主要是40%~60%浓度)的硫酸混合,并且与分离出的水解物--氢氧化钙、氧化钙、碳酸钙或其混合物进行中和反应,直到产生一种主要由聚硅氧烷或藻酸组成的浮动固体为止。通过与氢氧化钙、氧化钙、碳酸钙或其混合物混合后,会从原来的湿水解物中产生一种干燥的悬浮固体。这个固体包括最多5%wt的剩余氯化物以及少量的20%wt水,废弃物比重总计0.5~1克/毫升。分离后的液态阶段会再次水解或用于洗涤和干燥那些转化反应物、气态氯化氢。该工艺的主要缺点是把渣浆液相完全水解掉,造成了浪费。DE4 116925 A1 describes a process for the hydrolysis of methylchlorosilane by-products by preparing a raffinate consisting of direct mixtures of chloro- and/or organochlorosilanes at a temperature from 20 to 100 °C (main between 35°C and 60°C), mixed with sulfuric acid with a concentration of 20% to 70% (mainly 40% to 60%), and with the separated hydrolyzate - calcium hydroxide, calcium oxide, calcium carbonate or a mixture thereof for neutralization until a floating solid mainly composed of polysiloxane or alginic acid is produced. By mixing with calcium hydroxide, calcium oxide, calcium carbonate or mixtures thereof, a dry suspended solid is produced from the original wet hydrolyzate. This solid includes up to 5%wt residual chloride and a small amount of 20%wt water for a total waste specific gravity of 0.5-1 g/ml. The separated liquid phase is hydrolyzed again or used to wash and dry those conversion reactants, gaseous hydrogen chloride. The main disadvantage of this process is that the liquid phase of the slurry is completely hydrolyzed, resulting in waste.

发明内容Contents of the invention

本发明克服现有技术的上述缺点,提供一种有机硅单体合成过程中形成的废渣浆的水解处理方法。The invention overcomes the above-mentioned shortcomings of the prior art, and provides a method for hydrolyzing waste residue slurry formed during the synthesis of organic silicon monomers.

本发明提供的有机硅单体合成过程中的废渣浆的处理方法包括如下步骤:The processing method of the waste residue slurry in the synthetic process of organosilicon monomer provided by the invention comprises the following steps:

(A)有机硅单体合成中的废渣浆经过重力沉降离心机分离出90%(重量百分数)的高沸物,用于裂解和其他用途;(A) The waste residue slurry in the synthesis of organosilicon monomer is separated by a gravity settling centrifuge to 90% (weight percent) high boilers for cracking and other purposes;

(B)离心后的高黏度的废渣浆在水解釜中进行水解,水解介质为68.6%硫酸溶液;(B) The high-viscosity waste residue slurry after centrifugation is hydrolyzed in a hydrolysis kettle, and the hydrolysis medium is 68.6% sulfuric acid solution;

(C)少量含有硅氧烷的氯化氢气体从液相中析出;(C) a small amount of hydrogen chloride gas containing siloxane is separated out from the liquid phase;

(D)水解物经液固分离,固体水解物排放,液相经后续处理后回收铜。(D) The hydrolyzate is subjected to liquid-solid separation, the solid hydrolyzate is discharged, and the liquid phase is subjected to subsequent treatment to recover copper.

本发明方法中所处理的原料渣浆为直接法合成有机硅单体过程中产生的固液混合废物,其主要成份为高沸物和硅粉等固体颗粒,固体颗粒的含量为20%,经过重力沉降分离后,其中的高沸物已大部分分离出去,即将送去水解的渣浆的固含量将达到70%。本发明的另一发明点在于本发明在下一步的处理中直接使用68.6%的高浓度硫酸,这是因为原料中的高沸物已大部分分离出去,因此所需的水解介质——硫酸的量也大大减少,另一重要原因在于采用高浓度硫酸也有利于回收铜。The raw material slurry processed in the method of the present invention is the solid-liquid mixed waste produced in the process of direct method synthesis of organosilicon monomer, and its main components are solid particles such as high boiling matter and silicon powder, and the content of solid particles is 20%. After gravity sedimentation and separation, most of the high boilers have been separated, and the solid content of the slurry that is about to be hydrolyzed will reach 70%. Another inventive point of the present invention is that the present invention directly uses 68.6% high-concentration sulfuric acid in the processing of the next step, and this is because most of the high boiling substances in the raw material have been separated, so the required hydrolysis medium—the amount of sulfuric acid Another important reason is that the use of high-concentration sulfuric acid is also conducive to the recovery of copper.

本方法中的水解温度为30-90℃,优选55-65℃。水解介质硫酸溶液的浓度为68.6%。The hydrolysis temperature in this method is 30-90°C, preferably 55-65°C. The concentration of the hydrolysis medium sulfuric acid solution is 68.6%.

在工业化装置中,因为所处理的渣浆粘稠、不易流动,还可采用带螺旋推料装置的重力沉降离心分离机,以便使进料过程顺利进行。In the industrialized device, because the processed slurry is viscous and difficult to flow, a gravity sedimentation centrifuge with a screw pusher device can also be used to make the feeding process go smoothly.

该方法中产生的少量含有硅氧烷的氯化氢气体可进入碱吸收塔中和。A small amount of hydrogen chloride gas containing siloxane produced in this method can enter the alkali absorption tower for neutralization.

水解物可从水解釜侧壁溢流,经液固分离器,进行液固分离(过滤、沉淀、浮选或离心技术分离固体),固体水解物掩埋;液相进入酸水贮槽,经过还原等办法回收铜。The hydrolyzate can overflow from the side wall of the hydrolysis tank and pass through the liquid-solid separator for liquid-solid separation (solid separation by filtration, precipitation, flotation or centrifugal technology), and the solid hydrolyzate is buried; the liquid phase enters the acid water storage tank and undergoes reduction and other methods to recover copper.

渣浆原料从釜底进料,以增加其与水解介质的接触时间。硫酸为市售产品。The slurry raw material is fed from the bottom of the tank to increase its contact time with the hydrolysis medium. Sulfuric acid is a commercially available product.

附图1为本发明的工艺流程图,其中:Accompanying drawing 1 is process flow diagram of the present invention, wherein:

1.水管线                    2.硫酸管线1. Water pipeline 2. Sulfuric acid pipeline

3.高粘度渣浆管线            4.固液分离器3. High viscosity slurry pipeline 4. Solid-liquid separator

5.分离后固体水解物排放      6.酸水解溶液贮罐5. Discharge of solid hydrolyzate after separation 6. Acid hydrolysis solution storage tank

7.碱吸收罐                  8.渣浆原料7. Alkali absorption tank 8. Slurry raw material

9.分离出的高沸物9. Separated high boilers

本发明同现有技术相比其优点在于:本发明先使含固量为20%的渣浆通过离心重力沉降分离出大部分的高沸物和70%的高黏度渣浆,得到的高沸物可进一步裂解以回收二甲和其它有用单体。然后70%的高黏度渣浆进行水解使渣浆中的铜富集在水解溶液中被进一步回收,铜的回收率达到95%以上,形成的固体水解物可以达到环保要求,可进行堆埋处理。Compared with the prior art, the present invention has the advantages that: first, the present invention separates most of the high boiling matter and 70% of the high-viscosity slurry from the slurry with a solid content of 20% through centrifugal gravity sedimentation, and the obtained high-boiling The product can be further cracked to recover dimethyl and other useful monomers. Then 70% of the high-viscosity slurry is hydrolyzed to enrich the copper in the slurry and be further recovered in the hydrolysis solution. The recovery rate of copper reaches more than 95%. The formed solid hydrolyzate can meet environmental protection requirements and can be landfilled. .

具体实施方式Detailed ways

实施例1Example 1

原料渣浆为固含量为20%的液固混合物,在搅拌的情况下可以流动。经重力沉降分离后得到的高粘度渣浆的固含量为66%,流动性很差,用做下面实验的原料。可采用带螺旋推料装置的重力沉降离心分离机。The raw material slurry is a liquid-solid mixture with a solid content of 20%, which can flow when stirred. The solid content of the high-viscosity slurry obtained after separation by gravity sedimentation is 66%, and its fluidity is very poor. It is used as the raw material for the following experiment. A gravity settling centrifuge with a screw pusher can be used.

向带有搅拌冷凝器及温度计的三口瓶中加入水300g,98%的H2SO4700g,在60℃条件下,在30分钟内向反应釜内加入210g渣浆,从反应器上部析出HCl气体,含HCl的H2SO4及固体水解物(主要以硅酸形式存在)的悬浮液,从侧壁溢流到过滤器中,在此分离出水解产物,得到水解物湿重285g,滤液925g,氯含量4.55%。解析出的氯化氢经碱液吸收,水解溶液回收铜,回收氯96%。Add 300g of water and 700g of 98% H 2 SO 4 to a three-necked flask with a stirring condenser and a thermometer, and add 210g of slurry to the reactor within 30 minutes at 60°C, and HCl gas is precipitated from the upper part of the reactor , a suspension of H2SO4 containing HCl and solid hydrolyzate (mainly in the form of silicic acid), overflows from the side wall into the filter, where the hydrolyzate is separated, and the wet weight of the hydrolyzate is 285g, and the filtrate is 925g , chlorine content 4.55%. The analyzed hydrogen chloride is absorbed by the lye, and the hydrolyzed solution recovers copper and recovers 96% of chlorine.

实施例2Example 2

水700g,98%硫酸300g,其它条件同实例1。得到水解物湿重280g,滤液930g,氯含量3.24%。水解后的溶液铜的回收率达到90%,可满足要求。Water 700g, 98% sulfuric acid 300g, other conditions are with example 1. The obtained hydrolyzate had a wet weight of 280 g, a filtrate of 930 g, and a chlorine content of 3.24%. The recovery rate of the solution copper after hydrolysis reaches 90%, which can meet the requirements.

实施例3Example 3

水400g,98%硫酸600g,其它条件同实例1。得到水解物湿重295g,滤液940g,氯含量4.65%。水解后的溶液铜的回收率达到93%,可满足要求。Water 400g, 98% sulfuric acid 600g, other conditions are with example 1. The obtained hydrolyzate had a wet weight of 295 g, a filtrate of 940 g, and a chlorine content of 4.65%. The recovery rate of the solution copper after hydrolysis reaches 93%, which can meet the requirement.

对比例1Comparative example 1

得到的水解物颗粒细小,由于硫酸浓度变小,液固混和在一起形成浑浊液,不易分离。得到的水解物的氯含量为5.24%。The obtained hydrolyzate has fine particles, and because the concentration of sulfuric acid becomes smaller, the liquid and solid are mixed together to form a turbid liquid, which is difficult to separate. The chlorine content of the obtained hydrolyzate was 5.24%.

对比例2Comparative example 2

水解介质改用1000克水,其它条件同实例1。得到的湿水解产物很难分离,氯含量11.8%,湿的糊状物含水50%(重),残余氯含量14.1%。The hydrolysis medium uses 1000 grams of water instead, and other conditions are with example 1. The resulting wet hydrolyzate was difficult to separate, had a chlorine content of 11.8%, the wet paste contained 50% water by weight, and had a residual chlorine content of 14.1%.

对比例3Comparative example 3

反应温度为20℃,其它条件同实例1。得到的水解物颗粒细小、粘稠、不宜分离。Reaction temperature is 20 ℃, and other conditions are with example 1. The obtained hydrolyzate particles are fine, viscous and not suitable for separation.

对比例4Comparative example 4

水解介质为27%的氯化氢溶液,加入量为1000g。反应装置、条件等参数同实例1。得到的水解物与溶液混在一起,不宜分离。The hydrolysis medium is 27% hydrogen chloride solution, and the addition amount is 1000 g. Parameters such as reaction device, condition are with example 1. The resulting hydrolyzate is mixed with the solution and cannot be separated.

对比例5Comparative example 5

水解原料为含固量为20%的渣浆,反应装置、条件等参数同实例1,把渣浆所含的所有的高沸物都水解掉了,浪费了很大一块资源。水解得到的主产物是氯化氢气体和回收铜。The raw material for hydrolysis is slag slurry with a solid content of 20%. The parameters such as the reaction device and conditions are the same as in Example 1. All high boiling substances contained in the slurry are hydrolyzed, which wastes a lot of resources. The main products obtained by hydrolysis are hydrogen chloride gas and recovered copper.

Claims (4)

1. the treatment process of the waste residue slurry in the organosilane monomer building-up process comprises the steps:
(A) to isolate weight percentage through the centrifugal gravity settling centrifuge be 90% high boiling material to the waste residue slurry of organosilane monomer in synthetic, is used for cracking and other purposes;
(B) the full-bodied waste residue slurry after centrifugal is hydrolyzed in hydrolysis kettle, and hydrolysis medium is 68.6% sulphuric acid soln, and hydrolysis temperature is 30-90 ℃
(C) hydrogen chloride gas that contains siloxanes is on a small quantity separated out from liquid phase;
(D) hydrolyzate is through liquid-solid separation, and the solid hydrolyzate discharges, and liquid phase reclaims copper through subsequent disposal.
2. method according to claim 1 is characterized in that hydrolysis temperature is 55-65 ℃.
3. method according to claim 1 is characterized in that gravity settling separating centrifuge wherein has the spiral pusher device.
4. method according to claim 1 is characterized in that wherein hydrolyzate from the overflow of hydrolysis kettle sidewall, obtains solid product by liquid-solid separation.
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CN101549938B (en) * 2009-04-29 2011-04-27 浙江商达环保有限公司 Method for treating waste water containing high concentration of organosilicon
CN102180605B (en) * 2010-12-27 2013-01-23 蓝星化工新材料股份有限公司江西星火有机硅厂 Process for treating organic silicon slurry slag
CN102390860B (en) * 2011-08-04 2013-06-12 山东东岳有机硅材料有限公司 Environmentally-friendly treatment method and device for organosilicon slurry
CN103553051B (en) * 2013-10-29 2015-06-17 泸州北方化学工业有限公司 Method for separating solids from liquid of dregs in production process of organic silicon
CN103550902B (en) * 2013-10-29 2015-09-30 江西星火狮达科技有限公司 The hydrolysis regenerated environment protecting technique of organic silicon slurry slag
CN103555372A (en) * 2013-11-14 2014-02-05 江西星火狮达科技有限公司 Technology for gasifying organosilicone siloxane hydrolysate
CN103893941B (en) * 2014-04-22 2016-05-04 山东腾跃化学危险废物研究处理有限公司 Utilize alkaline residue treatment of wastes with processes of wastes against one another neutralizing hydrolysis to process the method for organic silicon slurry slag
CN104014581B (en) * 2014-06-25 2015-11-04 泸州北方化学工业有限公司 The processing method of dry forced by organosilicon
CN104262379A (en) * 2014-08-29 2015-01-07 浙江恒业成有机硅有限公司 Organic silicon residue slurry treatment device and treatment method
CN105294751A (en) * 2015-11-21 2016-02-03 唐山三友硅业有限责任公司 Method for processing slag slurry generated during organic silicon monomer synthesis process
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CN106629604B (en) * 2016-11-28 2019-07-16 昆明理工大学 A method of gas phase chlorination hydrogen is produced using chlorosilane raffinate
CN112321626A (en) * 2020-11-10 2021-02-05 云南能投硅材科技发展有限公司 Method for treating organic silicon slag slurry
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