CN106397828A - Recycling method of polyethylene in superfine fiber preparation - Google Patents
Recycling method of polyethylene in superfine fiber preparation Download PDFInfo
- Publication number
- CN106397828A CN106397828A CN201610821875.7A CN201610821875A CN106397828A CN 106397828 A CN106397828 A CN 106397828A CN 201610821875 A CN201610821875 A CN 201610821875A CN 106397828 A CN106397828 A CN 106397828A
- Authority
- CN
- China
- Prior art keywords
- polyethylene
- temperature
- preparation
- organic solvent
- solid
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Granted
Links
Classifications
-
- C—CHEMISTRY; METALLURGY
- C08—ORGANIC MACROMOLECULAR COMPOUNDS; THEIR PREPARATION OR CHEMICAL WORKING-UP; COMPOSITIONS BASED THEREON
- C08J—WORKING-UP; GENERAL PROCESSES OF COMPOUNDING; AFTER-TREATMENT NOT COVERED BY SUBCLASSES C08B, C08C, C08F, C08G or C08H
- C08J11/00—Recovery or working-up of waste materials
- C08J11/04—Recovery or working-up of waste materials of polymers
- C08J11/06—Recovery or working-up of waste materials of polymers without chemical reactions
- C08J11/08—Recovery or working-up of waste materials of polymers without chemical reactions using selective solvents for polymer components
-
- C—CHEMISTRY; METALLURGY
- C08—ORGANIC MACROMOLECULAR COMPOUNDS; THEIR PREPARATION OR CHEMICAL WORKING-UP; COMPOSITIONS BASED THEREON
- C08J—WORKING-UP; GENERAL PROCESSES OF COMPOUNDING; AFTER-TREATMENT NOT COVERED BY SUBCLASSES C08B, C08C, C08F, C08G or C08H
- C08J11/00—Recovery or working-up of waste materials
- C08J11/04—Recovery or working-up of waste materials of polymers
- C08J11/06—Recovery or working-up of waste materials of polymers without chemical reactions
-
- C—CHEMISTRY; METALLURGY
- C08—ORGANIC MACROMOLECULAR COMPOUNDS; THEIR PREPARATION OR CHEMICAL WORKING-UP; COMPOSITIONS BASED THEREON
- C08J—WORKING-UP; GENERAL PROCESSES OF COMPOUNDING; AFTER-TREATMENT NOT COVERED BY SUBCLASSES C08B, C08C, C08F, C08G or C08H
- C08J2323/00—Characterised by the use of homopolymers or copolymers of unsaturated aliphatic hydrocarbons having only one carbon-to-carbon double bond; Derivatives of such polymers
- C08J2323/02—Characterised by the use of homopolymers or copolymers of unsaturated aliphatic hydrocarbons having only one carbon-to-carbon double bond; Derivatives of such polymers not modified by chemical after treatment
- C08J2323/04—Homopolymers or copolymers of ethene
- C08J2323/06—Polyethene
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/50—Reuse, recycling or recovery technologies
- Y02W30/62—Plastics recycling; Rubber recycling
Landscapes
- Chemical & Material Sciences (AREA)
- Life Sciences & Earth Sciences (AREA)
- Sustainable Development (AREA)
- Health & Medical Sciences (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Medicinal Chemistry (AREA)
- Polymers & Plastics (AREA)
- Organic Chemistry (AREA)
- Separation, Recovery Or Treatment Of Waste Materials Containing Plastics (AREA)
- Processing Of Solid Wastes (AREA)
Abstract
本发明公开了一种超细纤维制备中聚乙烯的回收再利用方法,取部分超细纤维生产中的固体废弃物进行粉碎,用的盐酸进行浸泡;将预处理后的固体用复合有机溶剂进行提取,同时加入部分助剂,提取;提取后的剩余固体加入甲苯溶液中,然后控制温度加热至固体全部溶解;将装有XDA‑1大孔吸附树脂的吸附柱置于恒温箱中,通过该吸附柱,冷却,即有高纯度聚乙烯析出。
The invention discloses a method for recovering and reusing polyethylene in the preparation of superfine fibers. Part of the solid waste in the production of superfine fibers is crushed and soaked in hydrochloric acid; the pretreated solids are treated with a compound organic solvent. Extraction, while adding some auxiliary agents, extraction; the remaining solids after extraction are added to the toluene solution, and then heated at a controlled temperature until the solids are completely dissolved; the adsorption column equipped with XDA‑1 macroporous adsorption resin is placed in a constant temperature box, through The adsorption column is cooled, and high-purity polyethylene is precipitated.
Description
技术领域technical field
本发明涉及化工材料废弃物的回收方法,特别是指一种超细纤维制备中聚乙烯的回收再利用方法。The invention relates to a method for recycling chemical material waste, in particular to a method for recycling polyethylene in the preparation of superfine fibers.
背景技术Background technique
超细纤维制备时,利用甲苯对聚乙烯进行浸出时,甲苯溶液中含有聚乙烯、硅油或聚氨酯等浸出物。而目前超细纤维生产企业对甲苯浸出液的处理方法主要是对其进行浓缩,将得到的甲苯进行再利用,但对于浓缩后得到含有聚乙烯的固体废弃物一般是采用低价直接出售。When preparing ultrafine fibers, when using toluene to leach polyethylene, the toluene solution contains polyethylene, silicone oil or polyurethane and other leaching substances. At present, the treatment method of microfiber production enterprises for toluene leachate is mainly to concentrate it and reuse the obtained toluene, but the solid waste containing polyethylene obtained after concentration is generally sold directly at a low price.
发明内容Contents of the invention
本发明的目的是提供一种超细纤维制备中聚乙烯的回收再利用方法,其对固体废弃物中的聚乙烯进行分离和提纯而得到高纯度的聚乙烯,并作为原材料进行再利用,从而降低企业的原材料成本,提高企业的竞争力。The purpose of the present invention is to provide a method for recycling polyethylene in the preparation of ultrafine fibers, which separates and purifies polyethylene in solid waste to obtain high-purity polyethylene, and reuses it as a raw material, thereby Reduce the raw material cost of the enterprise and improve the competitiveness of the enterprise.
为实现上述目的,本发明的解决方案是:To achieve the above object, the solution of the present invention is:
一种超细纤维制备中聚乙烯的回收再利用方法,其步骤包括:A method for recovering and reusing polyethylene in the preparation of superfine fibers, the steps comprising:
步骤1、取部分超细纤维生产中的固体废弃物进行粉碎,然后把粉碎物用4%-8%的盐酸进行浸泡,粉碎物与盐酸的质量比为1:4;Step 1, taking part of the solid waste in the production of superfine fibers and crushing, then soaking the crushed matter with 4%-8% hydrochloric acid, the mass ratio of the crushed matter to hydrochloric acid is 1:4;
步骤2、将步骤1中预处理后的固体用复合有机溶剂进行硅油提取,同时加入助剂,提取时的加热温度为70-100℃,提取时间为1~3小时;Step 2. Extract the solid pretreated in step 1 with a compound organic solvent for silicone oil, and add additives at the same time. The heating temperature during extraction is 70-100°C, and the extraction time is 1-3 hours;
步骤3、将步骤2中提取后的剩余固体以质量比为1:5-10的比例加入甲苯溶液中,然后控制温度约40-80℃,加热至固体全部溶解,并恒温30-80分钟;Step 3. Add the remaining solid extracted in step 2 into the toluene solution with a mass ratio of 1:5-10, then control the temperature at about 40-80°C, heat until all the solids are dissolved, and keep the temperature constant for 30-80 minutes;
步骤4、将装有XDA-1大孔吸附树脂的吸附柱置于恒温箱中,调节恒温箱的温度为40-80℃,并将步骤3中的40-80℃恒温溶液通过该吸附柱,冷却,即有高纯度聚乙烯析出。Step 4. Put the adsorption column equipped with XDA-1 macroporous adsorption resin in a constant temperature box, adjust the temperature of the constant temperature box to 40-80°C, and pass the 40-80°C constant temperature solution in step 3 through the adsorption column, After cooling, high-purity polyethylene is precipitated.
所述步骤1的浸泡时间为10-15小时。The soaking time of the step 1 is 10-15 hours.
所述步骤2中固体与复合有机溶剂的质量比约为1:8-12。The mass ratio of the solid to the composite organic solvent in the step 2 is about 1:8-12.
所述助剂为油酸或吐温-80,助剂与复合有机溶剂的体积比为1:6~12。The auxiliary agent is oleic acid or Tween-80, and the volume ratio of the auxiliary agent to the composite organic solvent is 1:6-12.
采用上述方案后,本发明的工作原理是:After adopting the above scheme, the working principle of the present invention is:
超细纤维的生产中,固体废弃物的主要成分是混合硅油、聚氨酯和聚乙烯,其中聚氨酯由于不溶于甲苯,其在甲苯的浸出液中含量很低,同时聚氨酯也是制备超细纤维的原材料之一,因此在进行聚乙烯的回收再利用时,重点是如何实现聚乙烯与混合硅油的分离。In the production of ultrafine fibers, the main components of solid waste are mixed silicone oil, polyurethane and polyethylene. Since polyurethane is insoluble in toluene, its content in toluene leachate is very low, and polyurethane is also one of the raw materials for preparing ultrafine fibers. Therefore, when recycling polyethylene, the focus is on how to separate polyethylene from mixed silicone oil.
(1)硅油与聚乙烯的性质(1) Properties of silicone oil and polyethylene
(a)硅油通常指的是在室温下保持液体状态的线型聚硅氧烷产品,一般分为甲基硅油和改性硅油两类,其结构如图1所示。最常用的硅油为一甲基硅油,也称为普通硅油,其有机基团全部为甲基,甲基硅油具有良好的化学稳定性、绝缘性和疏水性能好。硅油不溶于水、甲醇、二醇和-乙氧基乙醇,可与苯、二甲醚、甲基乙基酮、四氯化碳或煤油互溶,稍溶于丙酮、二恶烷、乙醇和丁醇。(a) Silicone oil usually refers to a linear polysiloxane product that maintains a liquid state at room temperature. It is generally divided into two types: methyl silicone oil and modified silicone oil. Its structure is shown in Figure 1. The most commonly used silicone oil is monomethyl silicone oil, also known as ordinary silicone oil, whose organic groups are all methyl groups, and methyl silicone oil has good chemical stability, good insulation and hydrophobic properties. Silicone oil is insoluble in water, methanol, glycol and -ethoxyethanol, miscible with benzene, dimethyl ether, methyl ethyl ketone, carbon tetrachloride or kerosene, slightly soluble in acetone, dioxane, ethanol and butanol .
(R为烷基、芳基,R'为烷基、芳基、氢等;X为烷基、芳基、、氢、羟基等;n,m=0、1、2、3…)(R is alkyl, aryl, R' is alkyl, aryl, hydrogen, etc.; X is alkyl, aryl,, hydrogen, hydroxyl, etc.; n, m=0, 1, 2, 3...)
(b)聚乙烯是结构最简单的高分子,它是通过乙烯(CH2=CH2 )的发生加成聚合反应、并由重复的–CH2–单元连接而成的。目前超细纤维生产时所用的聚乙烯一般是低密度聚乙烯(LDPE),它是在高压力(100-300MPa),高温(190–210℃),过氧化物催化条件下自由基聚合,从而得到具有支链结构的化合物。聚乙烯常温下不溶于任何已知溶剂中,70℃以上可少量溶解于甲苯、乙酸戊酯、三氯乙烯等溶剂中。聚乙烯有优异的化学稳定性,室温下耐盐酸、氢氟酸、磷酸、甲酸、胺类、氢氧化钠、氢氧化钾等各种化学物质腐蚀作用,但硝酸和硫酸对聚乙烯有较强的破坏作用。(b) Polyethylene is the polymer with the simplest structure, which is formed by addition polymerization of ethylene (CH 2 =CH 2 ) and linked by repeating –CH 2 – units. At present, the polyethylene used in the production of microfibers is generally low-density polyethylene (LDPE), which is free radically polymerized under high pressure (100-300MPa), high temperature (190-210°C), and peroxide catalyzed conditions. Compounds with branched chain structures were obtained. Polyethylene is insoluble in any known solvents at room temperature, and can be dissolved in a small amount in solvents such as toluene, amyl acetate, and trichloroethylene above 70°C. Polyethylene has excellent chemical stability, and is resistant to corrosion by various chemical substances such as hydrochloric acid, hydrofluoric acid, phosphoric acid, formic acid, amines, sodium hydroxide, and potassium hydroxide at room temperature, but nitric acid and sulfuric acid have strong corrosion effects on polyethylene. destructive effect.
(2)硅油与聚乙烯的性质差异对比 (2) Comparison of the properties of silicone oil and polyethylene
超细纤维生产中所用的混合硅油,不管是甲基硅油还是改性硅油,其与聚乙烯的主要区别有以下两点:The mixed silicone oil used in the production of microfiber, whether it is methyl silicone oil or modified silicone oil, has the following two main differences from polyethylene:
硅油的结构是直线型的,而聚乙烯的结构是支链型的。The structure of silicone oil is linear, while that of polyethylene is branched.
硅油中含有烷基、芳基等多种疏水的取代基,其疏水性比聚乙烯大。Silicone oil contains a variety of hydrophobic substituents such as alkyl groups and aryl groups, and its hydrophobicity is greater than that of polyethylene.
(c) 硅油耐酸碱性比聚乙烯差。(c) Silicone oil has poorer acid and alkali resistance than polyethylene.
(3)硅油与聚乙烯的分离机理(3) Separation mechanism of silicone oil and polyethylene
(a)将超细纤维废弃物进行粉碎,在用盐酸进行预处理,使硅油的结构受到一定程度的破坏。(a) Pulverize the microfiber waste and pretreat it with hydrochloric acid to destroy the structure of the silicone oil to a certain extent.
(b)用混合试剂对固体废弃物进行提纯。(b) Purification of solid waste with mixed reagents.
(c)基于聚乙烯和硅油的极性差异,利用大孔吸附树脂对聚乙烯溶液中的少量硅油进行吸附,从而使回收的聚乙烯纯度进一步提高。(c) Based on the polarity difference between polyethylene and silicone oil, a small amount of silicone oil in polyethylene solution is adsorbed by macroporous adsorption resin, so that the purity of recovered polyethylene is further improved.
附图说明Description of drawings
图1为本发明超细纤维生产中聚乙烯的回收工艺流程示意图。Fig. 1 is the schematic flow chart of the recycling process of polyethylene in the production of microfibers of the present invention.
具体实施方式detailed description
配合图1所示,本发明揭示了一种超细纤维制备中聚乙烯的回收再利用方法,其具体步骤包括:As shown in Figure 1, the present invention discloses a method for recycling polyethylene in the preparation of ultrafine fibers, the specific steps of which include:
步骤1、取部分超细纤维生产中的固体废弃物进行粉碎,然后把粉碎物用4%-8%的盐酸进行浸泡,浸泡时间为10-15小时,粉碎物与盐酸的质量比为1:4;Step 1, take part of the solid waste in the production of superfine fibers and pulverize, then soak the pulverized material with 4%-8% hydrochloric acid, the soaking time is 10-15 hours, and the mass ratio of the pulverized material to hydrochloric acid is 1: 4;
步骤2、将步骤1中预处理后的固体用复合有机溶剂进行硅油提取,固体与复合有机溶剂的质量比约为1:8-12,同时加入助剂,助剂为油酸或吐温-80,助剂与复合有机溶剂的体积比为1:6~12,提取时的加热温度为70-100℃,提取时间为1~3小时;Step 2, the pretreated solid in step 1 is extracted with silicone oil with a composite organic solvent, the mass ratio of the solid to the composite organic solvent is about 1:8-12, and an auxiliary agent is added at the same time, and the auxiliary agent is oleic acid or Tween- 80, the volume ratio of additives and compound organic solvents is 1:6~12, the heating temperature during extraction is 70-100°C, and the extraction time is 1~3 hours;
步骤3、将步骤2中提取后的剩余固体以质量比为1:5-10的比例加入甲苯溶液中,然后控制温度约40-80℃,加热至固体全部溶解,并恒温30-80分钟;Step 3. Add the remaining solid extracted in step 2 into the toluene solution with a mass ratio of 1:5-10, then control the temperature at about 40-80°C, heat until all the solids are dissolved, and keep the temperature constant for 30-80 minutes;
步骤4、将装有XDA-1大孔吸附树脂的吸附柱置于恒温箱中,调节恒温箱的温度为40-80℃,并将步骤3中的40-80℃恒温溶液通过该吸附柱,冷却,即有高纯度聚乙烯析出。Step 4. Put the adsorption column equipped with XDA-1 macroporous adsorption resin in a constant temperature box, adjust the temperature of the constant temperature box to 40-80°C, and pass the 40-80°C constant temperature solution in step 3 through the adsorption column, After cooling, high-purity polyethylene is precipitated.
实施例1:Example 1:
步骤1、取20克超细纤维生产中的固体废弃物进行粉碎,然后把粉碎物用100毫升5.0%的盐酸进行浸泡,浸泡时间约为12小时;Step 1. Take 20 grams of solid waste in the production of superfine fibers and crush them, then soak the crushed matter with 100 milliliters of 5.0% hydrochloric acid for about 12 hours;
步骤2、将步骤1中预处理后的固体用200毫升体积比为1:1的甲苯-乙醇复合有机溶剂进行提取(该复合有机溶剂中含有约20毫升的吐温-80),提取时的加热温度约为90℃,提取时间约为1小时;Step 2. Extract the pretreated solid in step 1 with 200 ml of toluene-ethanol composite organic solvent with a volume ratio of 1:1 (the composite organic solvent contains about 20 ml of Tween-80). The heating temperature is about 90°C, and the extraction time is about 1 hour;
步骤3、将步骤2中提取后的剩余固体以质量比为1:8的比例加入甲苯溶液中,然后控制温度约60℃,加热至固体全部溶解,并恒温30分钟;Step 3. Add the remaining solid extracted in step 2 into the toluene solution with a mass ratio of 1:8, then control the temperature at about 60°C, heat until the solid is completely dissolved, and keep the temperature constant for 30 minutes;
步骤4、将装有XDA-1大孔吸附树脂的吸附柱置于恒温箱中,调节恒温箱的温度约为60℃,并将步骤3中的60℃恒温溶液通过该吸附柱,冷却,即有高纯度聚乙烯析出。Step 4. Put the adsorption column equipped with XDA-1 macroporous adsorption resin in a constant temperature box, adjust the temperature of the constant temperature box to about 60°C, and pass the 60°C constant temperature solution in step 3 through the adsorption column, and cool it down, that is High-purity polyethylene was precipitated.
实施例2:Example 2:
步骤1、取20克超细纤维生产中的固体废弃物进行粉碎,然后把粉碎物用100毫升5.0%的盐酸进行浸泡,浸泡时间约为12小时;Step 1. Take 20 grams of solid waste in the production of superfine fibers and crush them, then soak the crushed matter with 100 milliliters of 5.0% hydrochloric acid for about 12 hours;
步骤2、将步骤1中预处理后的固体用200毫升体积比为1:1的甲苯-丙酮复合有机溶剂进行提取(该复合有机溶剂中含有约20毫升的油酸),提取时的加热温度约为90℃,提取时间约为1小时;Step 2. Extract the pretreated solid in step 1 with 200 milliliters of toluene-acetone composite organic solvent with a volume ratio of 1:1 (the composite organic solvent contains about 20 milliliters of oleic acid), and the heating temperature during extraction About 90°C, the extraction time is about 1 hour;
步骤3、将步骤2中提取后的剩余固体以质量比为1:8的比例加入甲苯溶液中,然后控制温度约60℃,加热至固体全部溶解,并恒温30分钟;Step 3. Add the remaining solid extracted in step 2 into the toluene solution with a mass ratio of 1:8, then control the temperature at about 60°C, heat until the solid is completely dissolved, and keep the temperature constant for 30 minutes;
步骤4、将装有XDA-1大孔吸附树脂的吸附柱置于恒温箱中,调节恒温箱的温度约为60℃,并将步骤3中的60℃恒温溶液通过该吸附柱,冷却,即有高纯度聚乙烯析出。Step 4. Put the adsorption column equipped with XDA-1 macroporous adsorption resin in a constant temperature box, adjust the temperature of the constant temperature box to about 60°C, and pass the 60°C constant temperature solution in step 3 through the adsorption column, and cool it down, that is High-purity polyethylene was precipitated.
以上所述,仅是本发明实施例而已,并非对本发明的技术范围作任何限制,故凡是依据本发明的技术实质对以上实施例所作的任何细微修改、等同变化与修饰,均仍属于本发明技术方案的范围内。The above is only an embodiment of the present invention, and does not limit the technical scope of the present invention in any way. Therefore, any minor modifications, equivalent changes and modifications made to the above embodiments according to the technical essence of the present invention still belong to the present invention. within the scope of the technical program.
Claims (4)
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201610821875.7A CN106397828B (en) | 2016-09-14 | 2016-09-14 | Recycling and recycling method of polyethylene in the preparation of ultrafine fibers |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201610821875.7A CN106397828B (en) | 2016-09-14 | 2016-09-14 | Recycling and recycling method of polyethylene in the preparation of ultrafine fibers |
Publications (2)
Publication Number | Publication Date |
---|---|
CN106397828A true CN106397828A (en) | 2017-02-15 |
CN106397828B CN106397828B (en) | 2019-04-23 |
Family
ID=57999987
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201610821875.7A Expired - Fee Related CN106397828B (en) | 2016-09-14 | 2016-09-14 | Recycling and recycling method of polyethylene in the preparation of ultrafine fibers |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN106397828B (en) |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN108003378A (en) * | 2017-12-08 | 2018-05-08 | 禾欣可乐丽超纤皮(嘉兴)有限公司 | The separation method and device of polyethylene and toluene in polyvinyl-toluene solution |
Citations (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN103131042A (en) * | 2013-03-06 | 2013-06-05 | 上海交通大学 | Aluminum-plastic separating agent and aluminum-plastic separating method |
CN103396583A (en) * | 2013-07-10 | 2013-11-20 | 大连工业大学 | Method for recycling waste medicinal capsule plates |
CN104558679A (en) * | 2015-02-03 | 2015-04-29 | 王姝 | Method for separating and recovering fiber-reinforced thermoplastic |
-
2016
- 2016-09-14 CN CN201610821875.7A patent/CN106397828B/en not_active Expired - Fee Related
Patent Citations (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN103131042A (en) * | 2013-03-06 | 2013-06-05 | 上海交通大学 | Aluminum-plastic separating agent and aluminum-plastic separating method |
CN103396583A (en) * | 2013-07-10 | 2013-11-20 | 大连工业大学 | Method for recycling waste medicinal capsule plates |
CN104558679A (en) * | 2015-02-03 | 2015-04-29 | 王姝 | Method for separating and recovering fiber-reinforced thermoplastic |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN108003378A (en) * | 2017-12-08 | 2018-05-08 | 禾欣可乐丽超纤皮(嘉兴)有限公司 | The separation method and device of polyethylene and toluene in polyvinyl-toluene solution |
Also Published As
Publication number | Publication date |
---|---|
CN106397828B (en) | 2019-04-23 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN102558617B (en) | Intumescent flame retardant and preparation method thereof | |
JP6510469B2 (en) | Method and composition for depolymerization of epoxy resin cured product | |
Zhu et al. | A novel approach to separation of waste printed circuit boards using dimethyl sulfoxide | |
WO2014014458A1 (en) | Recycling carbon fibers from epoxy using solvent cracking | |
EP3153543A1 (en) | Method and composition for swelling pretreatment before decomposition of cured thermosetting resin materials | |
CN107586959B (en) | Utilize the method for heavy metal in intensified by ultrasonic wave functional ionic liquids extraction water | |
Zhou et al. | Synergistic effect between solid wastes and intumescent flame retardant on flammability and smoke suppression of thermoplastic polyurethane composites | |
CN110668403A (en) | A kind of continuous production method of insoluble sulfur | |
CN106397828A (en) | Recycling method of polyethylene in superfine fiber preparation | |
CN102838725A (en) | Preparation method of phenol-dicyclopentadiene epoxy resin | |
CN106750571A (en) | The preparation method of reduced graphene-Chitosan Composites | |
CN106554480B (en) | A kind of preparation method of bisphenol A type epoxy resin | |
CN103772442A (en) | Method for separating and purifying n-octylferrocene through reduced pressure distillation process in combination with chromatography | |
CN103113711A (en) | Preparation method for low-dielectric halogen-free flame retardant glass fiber pre-impregnation material | |
KR102600519B1 (en) | Cellulose extractant and Method of cellulose extraction | |
CN102276789B (en) | Method for recovering and utilizing waste and old paper-based copper-coated board non-metallic material | |
JP6054716B2 (en) | Method for producing cyclic ether and method for recycling ionic liquid used therefor | |
CN108102075A (en) | A kind of preparation method of low chlorophenol formaldehyde epoxy resin | |
CN111686473A (en) | Method for separating iron oxide waste desulfurizer from sulfur | |
CN104058369B (en) | Polyvinyl butyral resin produces the HCl recovery processing method in waste water | |
Luo et al. | Utilization of fly ash acid residue as a reinforcing filler in ethylene propylene diene monomer rubber | |
Nabipour et al. | A bio-based vanillin ligand to remove silver ions from a waste stream and utilizing it to improve the fire safety of an epoxy thermoset and its thermal conductivity | |
CN104059216B (en) | A kind of preparation method of brominated phenols formaldehyde epoxy resin | |
CN111003693A (en) | A kind of production method of insoluble sulfur | |
CN106186486A (en) | A kind of recovery and treatment method of hydrazine hydrate high-salt wastewater |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
C06 | Publication | ||
PB01 | Publication | ||
C10 | Entry into substantive examination | ||
SE01 | Entry into force of request for substantive examination | ||
GR01 | Patent grant | ||
GR01 | Patent grant | ||
CF01 | Termination of patent right due to non-payment of annual fee |
Granted publication date: 20190423 Termination date: 20210914 |
|
CF01 | Termination of patent right due to non-payment of annual fee |