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CN1869088A - Water soluble organic amphoteric high molecule copolymer and its preparation method - Google Patents

Water soluble organic amphoteric high molecule copolymer and its preparation method Download PDF

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CN1869088A
CN1869088A CN 200610020312 CN200610020312A CN1869088A CN 1869088 A CN1869088 A CN 1869088A CN 200610020312 CN200610020312 CN 200610020312 CN 200610020312 A CN200610020312 A CN 200610020312A CN 1869088 A CN1869088 A CN 1869088A
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CN100402564C (en
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朱明�
张新申
魏玉君
蒋小萍
袁晓光
朱永飞
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Sichuan University
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Abstract

本发明涉及水溶性有机两性高分子共聚物及制备方法,水溶性两性有机高分子共聚物是以衣康酸(盐)和季铵化烷基二烯丙基为共聚单体,在聚合助剂存在的条件下,用氧化还原引发剂和水溶性偶氮类引发剂引发单体经水溶液共聚合反应得到。本发明采用的制备方法简单,阴、阳离子度可控,产物分子量高,残留单体含量低,水溶性好。由本发明制备的水溶性有机两性高分子共聚物可作为絮凝剂,用于废污水处理。

The invention relates to a water-soluble organic amphoteric polymer copolymer and a preparation method thereof. The water-soluble amphoteric organic polymer copolymer uses itaconic acid (salt) and quaternized alkyl diallyl as comonomers, and is added as a polymerization aid Under the condition of existence, it is obtained by using a redox initiator and a water-soluble azo initiator to initiate a monomer through aqueous solution copolymerization. The preparation method adopted in the invention is simple, the degree of anion and cation is controllable, the molecular weight of the product is high, the content of residual monomer is low, and the water solubility is good. The water-soluble organic amphoteric polymer copolymer prepared by the invention can be used as a flocculant for waste water treatment.

Description

水溶性有机两性高分子共聚物及制备方法Water-soluble organic amphoteric polymer copolymer and preparation method thereof

技术领域    本发明涉及水溶性有机两性高分子共聚物及制备方法。Technical field The present invention relates to a water-soluble organic amphoteric polymer copolymer and a preparation method.

背景技术    水是人类生活和生产活动中不可缺少的物质资料。据2004年中国环境质量报告指出:中国90%以上的河流、湖泊都受到了不同程度的污染。有些污染甚至危急了生存安全。防止水污染已是我国的一项基本国策。絮凝剂广泛应用于废水处理。国内外的湿法冶金、石化、造纸、钢铁、纺织、印染、食品、酿造等多种行业的废水,使用絮凝剂的比例占55~75%,而自来水工业几乎100%使用絮凝法作为净化手段。Background technology Water is an indispensable material material in human life and production activities. According to the 2004 China Environmental Quality Report, more than 90% of the rivers and lakes in China have been polluted to varying degrees. Some pollution even endangers the safety of survival. Preventing water pollution has become a basic national policy of our country. Flocculants are widely used in wastewater treatment. The proportion of flocculant used in domestic and foreign hydrometallurgy, petrochemical, papermaking, steel, textile, printing and dyeing, food, brewing and other industries accounts for 55-75%, while almost 100% of the tap water industry uses flocculation as a purification method .

絮凝剂按化学组成可分为无机和有机絮凝剂;无机絮凝剂由于受到用量大、受水质影响大和产生二次污染,其应用范围受到了很大的局限,正逐步被有机絮凝剂所取代。有机絮凝剂分为天然和合成两大类,由于目前技术原因天然有机絮凝剂质量不稳定,使其实际应用受到一定的限制。有机合成高分子絮凝剂由于可以对分子结构进行控制,受水质的影响小、用量相对较低、絮凝效果好,而日益受到重视。有机合成高分子絮凝剂分为:非离子型,如聚丙烯酰胺类,《水处理化学品手册》[M],2005年5月第1版,化学工业出版社,何铁林主编,介绍了丙烯酰胺聚合制备的非离子絮凝剂,但其残留单体及分解后的小分子具有毒性,应用受到限制;阴离子型,如聚丙烯酸(盐)类,《石油化工》[J],2005,34(4):338~342,杨显平等人合成了丙烯酰胺-丙烯酸钠共聚阴离子型絮凝剂,也因单体残留和分解后的毒性形成二次污染受到限用;阳离子型,如季胺盐聚合或季胺盐与丙烯酰胺共聚、聚丙烯酰胺经曼尼希反应得到的产物,中国专利CN1202144A公开了一种阳离子型絮凝剂,由于现代工业和生活废水中的有机质含量大大增加,有机微粒表面带负电荷,因而阳离子絮凝剂有较好的絮凝,但在污泥处理中,由于污泥腐败的继续进行,单独使用阳离子絮凝剂,会造成悬浮物的回收率低、脱水饼含水率高。两性离子类具有阴阳离子的特征,较阳离子絮凝剂有更强的絮凝、沉降作用,对污泥脱水的性能更加明显、有效,投药量较少,还能起到金属螯合剂的作用,由于许多污水中含正负电荷的微细颗粒与胶体,需用两性离子絮凝剂处理,因而在水处理中更具有优势,《水处理药剂及材料实用手册》[M],2000年3月第1版,中国石化出版社出版,祁鲁梁、李永存等主编,介绍了由丙烯酸钠、丙烯酰胺和季胺盐共聚而成的两性高分子离子絮凝剂,日特开昭58-215454号专利公开了一种阳离子高分子絮凝剂和阴离子高分子絮凝剂共用的方法,中国专利CN1196334A公开了阳离子/两性接枝聚丙烯酰胺絮凝剂的制备方法,中国专利CN1451612A公开了由二乙基二烯丙基氯化铵、丙烯酰胺、丙烯酸形成的聚合物与聚二乙基二烯丙基氯化铵复配而形成制备两性离子高分子絮凝剂的方法,中国专利CN1187468A公开了由丙烯酰胺、丙烯酸(盐)和甲基丙烯酰氧乙基三甲基氯化铵三元聚合而成的两性离子高分子聚合物,李万捷等人在1994年《水处理技术》20(1):33~38提出了用曼尼希(Mannich)反应制备两性聚丙烯酰胺絮凝剂的方法,冉千平等人在《油田化学》[J],2002,19(1):85~88报道了用二甲基二烯丙基氯化铵、马来酸和丙烯酰胺共聚合成两性离子高分子絮凝剂。Flocculants can be divided into inorganic and organic flocculants according to their chemical composition. Inorganic flocculants are gradually being replaced by organic flocculants because of their large dosage, large impact on water quality, and secondary pollution. Organic flocculants are divided into two categories: natural and synthetic. Due to current technical reasons, the quality of natural organic flocculants is not stable, which limits their practical application. Organic synthetic polymer flocculants have been paid more and more attention because they can control the molecular structure, are less affected by water quality, have relatively low dosage, and have good flocculation effects. Organic synthetic polymer flocculants are divided into: non-ionic, such as polyacrylamide, "Water Treatment Chemicals Handbook" [M], the first edition in May 2005, Chemical Industry Press, edited by He Tielin, introduced acrylamide Polymerized nonionic flocculant, but its residual monomers and decomposed small molecules are toxic, and its application is limited; anionic, such as polyacrylic acid (salt), "Petrochemical Industry" [J], 2005, 34 (4 ): 338~342, Yang Xianping and others synthesized acrylamide-sodium acrylate copolymer anionic flocculant, which is also restricted due to secondary pollution caused by monomer residue and decomposition toxicity; cationic, such as quaternary ammonium salt polymerization or The product obtained by the copolymerization of quaternary ammonium salt and acrylamide, and the Mannich reaction of polyacrylamide. Chinese patent CN1202144A discloses a cationic flocculant. Due to the greatly increased organic matter content in modern industrial and domestic wastewater, the surface of organic particles is negatively charged. Therefore, cationic flocculants have better flocculation, but in sludge treatment, due to the continuation of sludge corruption, using cationic flocculants alone will result in low recovery of suspended solids and high moisture content of dehydrated cakes. Zwitterions have the characteristics of anions and cations, and have stronger flocculation and sedimentation effects than cationic flocculants. The performance of sludge dewatering is more obvious and effective, and the dosage is less. It can also act as a metal chelating agent. Due to many Fine particles and colloids containing positive and negative charges in sewage need to be treated with zwitterionic flocculants, so they have more advantages in water treatment. "Practical Handbook of Water Treatment Agents and Materials" [M], the first edition in March 2000, Published by Sinopec Press, edited by Qi Luliang, Li Yongcun, etc., introduced an amphoteric polymer ion flocculant formed by copolymerization of sodium acrylate, acrylamide and quaternary ammonium salt. A cationic macromolecular flocculant and anionic macromolecular flocculant shared method, Chinese patent CN1196334A discloses the preparation method of cationic/amphoteric grafted polyacrylamide flocculant, Chinese patent CN1451612A discloses the preparation method of polyacrylamide flocculant by diethyl diallyl chloride The polymer formed by ammonium, acrylamide and acrylic acid is compounded with polydiethyl diallyl ammonium chloride to form a method for preparing zwitterionic polymer flocculants. A zwitterionic polymer formed by the ternary polymerization of methacryloyloxyethyltrimethylammonium chloride, Li Wanjie and others proposed the use of Manny The method of preparing amphoteric polyacrylamide flocculant by Mannich reaction, Ran Qianping and others reported the use of dimethyl diallyl chloride in Oilfield Chemistry [J], 2002, 19 (1): 85-88 Ammonium, maleic acid and acrylamide are copolymerized into a zwitterionic polymer flocculant.

以上合成的高分子絮凝剂仍存在一些不同的缺陷:The polymer flocculants synthesized above still have some different defects:

1、在合成高分子絮凝剂时使用了丙烯酰胺、丙烯酸(盐)、马来酸(盐)等毒性大的单体,因而聚合残留单体和分解后的小分子会产生二次污染;1. Toxic monomers such as acrylamide, acrylic acid (salt) and maleic acid (salt) are used in the synthesis of polymer flocculants, so the polymerization residual monomers and decomposed small molecules will cause secondary pollution;

2、曼尼希改性聚丙烯酰胺的高分子絮凝剂,不适用于处理pH高的废水,贮存稳定性不高。2. The polymer flocculant of Mannich modified polyacrylamide is not suitable for treating wastewater with high pH, and its storage stability is not high.

3、从绿色化学角度来看,曼尼希反应不符合绿色化学的要求。3. From the perspective of green chemistry, the Mannich reaction does not meet the requirements of green chemistry.

本发明的目的是在保持水溶性有机两性高分子共聚物的絮凝效率不降低来达到性能更好的情形下:The purpose of the present invention is to keep the flocculation efficiency of the water-soluble organic amphoteric macromolecular copolymer without reducing to achieve better performance:

1、选用的单体无毒,基本不造成二次污染,更符合绿色化学要求;1. The selected monomers are non-toxic, basically do not cause secondary pollution, and are more in line with the requirements of green chemistry;

2、共聚合在选用氧化还原引发剂同时,配以少量的偶氮类引发剂和聚合助剂,达到了提高转化率、减少残留单体的目的;2. In the copolymerization, redox initiators are selected, and a small amount of azo initiators and polymerization aids are used to achieve the purpose of increasing the conversion rate and reducing residual monomers;

3、克服了由于聚丙烯酰胺类絮凝剂脱水效果差、性能不稳定的缺点。3. It overcomes the shortcomings of poor dehydration effect and unstable performance of polyacrylamide flocculants.

本发明采用新技术,用衣康酸(盐)与季铵化烷基二烯丙基的水溶液共聚合制备的水溶性有机两性高分子共聚物,提供了一种操作简单、性能稳定、使用范围更广,脱水效果更好的两性高分子絮凝剂及制备方法。The present invention adopts new technology, and the water-soluble organic amphoteric macromolecular copolymer prepared by the aqueous solution copolymerization of itaconic acid (salt) and quaternized alkyl diallyl provides a kind of simple operation, stable performance and wide application range. An amphoteric polymer flocculant with wider range and better dehydration effect and a preparation method thereof.

该水溶性有机两性高分子共聚物,其特征在于,它是由单体为衣康酸(盐):This water-soluble organic amphoteric macromolecular copolymer is characterized in that it is itaconic acid (salt) by monomer:

Figure A20061002031200051
Figure A20061002031200051

X:H、Na或KX: H, Na or K

单体为季铵化烷基二烯丙基:The monomer is a quaternized alkyl diallyl:

Figure A20061002031200052
Figure A20061002031200052

R:C1~C4烷基;Y:Cl,BrR: C 1 ~C 4 alkyl; Y: Cl, Br

在聚合助剂存在的条件下,用氧化还原引发剂和水溶性偶氮类引发剂引发单体经水溶液共聚合形成的二元共聚物,制备的水溶性有机两性高分子共聚物结构如下图:In the presence of polymerization aids, redox initiators and water-soluble azo initiators are used to initiate the binary copolymers formed by copolymerization of monomers in aqueous solution. The structure of the prepared water-soluble organic amphoteric polymer copolymers is shown in the figure below:

1≤n≤7684;1≤m≤6190(n、m为正整数)1≤n≤7684; 1≤m≤6190 (n, m are positive integers)

本发明制备方法对上述聚合单体、氧化还原引发剂、水溶性偶氮类引发剂、聚合助剂等并无特别要求。例如,对共聚合单体,在通式可以表示为CH2=CCOOX(CH2COOX)的衣康酸(盐)化合物中,X可以为H、Na、K;通式为(CH2=CH-CH2)2NRY的季铵化烷基二烯丙基的化合物中,R可以为含有1~4个碳原子的烷基,Y可以为Cl、Br。实验结果显示,为使本发明所制备的水溶性有机两性高分子共聚物的使用性能及经济性达到最佳效果,其单体总浓度控制在5%~45%,两种单体的摩尔用量比控制在1∶10~1∶25范围内是可取的。The preparation method of the present invention has no special requirements on the above-mentioned polymerization monomers, redox initiators, water-soluble azo initiators, polymerization aids and the like. For example, for the copolymerization monomer, in the itaconic acid (salt) compound whose general formula can be expressed as CH 2 ═CCOOX (CH 2 COOX), X can be H, Na, K; the general formula is (CH 2 ═CH In the quaternized alkyldiallyl compound of -CH 2 ) 2 NRY, R may be an alkyl group containing 1 to 4 carbon atoms, and Y may be Cl or Br. Experimental results show that in order to make the performance and economy of the prepared water-soluble organic amphoteric high molecular copolymer of the present invention reach the best effect, its total monomer concentration is controlled at 5% to 45%, and the molar dosage of the two monomers It is advisable to control the ratio within the range of 1:10 to 1:25.

如前述,本发明在聚合前期低温时加入氧化还原引发剂,其目的是为获得大分子量的共聚物。例如选用的氧化剂可以是过氧化氢、过硫酸铵、过硫酸钠、过硫酸钾中任一种,还原剂可以是亚硫酸氢钠、亚硫酸钠、硫代硫酸钠、连二硫酸钠、焦硫酸钠、亚硫酸氢钾、亚硫酸钾、亚硫酸铵、亚硫酸铁中任一种。实验结果显示氧化还原引发剂的摩尔用量比在1~1.5,用量在单体总质量的0.05%~5%范围内可以达到理想的效果。As mentioned above, the present invention adds a redox initiator at a low temperature in the early stage of polymerization, and its purpose is to obtain a copolymer with a large molecular weight. For example, the selected oxidizing agent can be any one of hydrogen peroxide, ammonium persulfate, sodium persulfate, and potassium persulfate, and the reducing agent can be sodium bisulfite, sodium sulfite, sodium thiosulfate, sodium hydrosulfate, sodium pyrosulfate , Potassium bisulfite, Potassium sulfite, Ammonium sulfite, Ferric sulfite. Experimental results show that the molar ratio of the redox initiator is 1-1.5, and the ideal effect can be achieved in the range of 0.05%-5% of the total mass of the monomer.

如前述,本发明在聚合后期较高温度时加入水溶性偶氮类引发剂,例如可选用偶氮二异丁基脒盐酸盐、偶氮二异丁酸二甲酯、偶氮双(2-甲基丙酰胺)盐酸盐、偶氮双(4-氰戊酸)中任一种。实验结果显示,其用量在单体总质量的0.05%~1.0%范围内其单体转化率可达到90%以上。As mentioned above, the present invention adds a water-soluble azo initiator at a higher temperature in the later stage of polymerization, for example, azobisisobutylamidine hydrochloride, dimethyl azobisisobutyrate, azobis(2 -any one of methylpropionamide) hydrochloride, azobis(4-cyanovaleric acid). Experimental results show that the conversion rate of the monomer can reach more than 90% when the amount is within the range of 0.05%-1.0% of the total mass of the monomer.

如前述,本发明在聚合反应中加入聚合助剂,例如二乙醇胺、三乙醇胺、乙二胺四乙酸及其盐、水溶性含氟化合物如氟硅酸、氟硅酸钙、氟化钾、氟化钠中任一种或二种以上的混合物。实验结果显示其用量为单体总质量的0.025%~1.0%范围内,能够使氧化还原引发剂所引发的共聚合反应得到大分子量的水溶性有机两性高分子共聚物,又使其聚合速率得以控制。As mentioned above, the present invention adds polymerization aids in the polymerization reaction, such as diethanolamine, triethanolamine, ethylenediaminetetraacetic acid and its salts, water-soluble fluorine-containing compounds such as fluorosilicic acid, calcium fluorosilicate, potassium fluoride, fluorine Any one or a mixture of two or more of sodium chloride. Experimental results show that its dosage is in the range of 0.025% to 1.0% of the total mass of the monomers, which can make the copolymerization reaction initiated by the redox initiator obtain a water-soluble organic amphoteric polymer copolymer with a large molecular weight, and make its polymerization rate increase. control.

如水溶性有机两性高分子共聚物制备方法所述,调整聚合体系的pH=2.0~8.0,其所用调整pH的物质为氢氧化钠、氢氧化钾、氢氧化钙、碳酸钠、碳酸氢钠中任一种的水溶液,这样保证了所用的引发剂能达到最理想的引发效率。As described in the preparation method of the water-soluble organic amphoteric polymer copolymer, the pH of the polymerization system is adjusted to 2.0 to 8.0, and the substance used to adjust the pH is any of sodium hydroxide, potassium hydroxide, calcium hydroxide, sodium carbonate, and sodium bicarbonate. A kind of aqueous solution, which ensures that the initiator used can achieve the most ideal initiation efficiency.

本发明的制备方法是通过如下的步骤来实现的:The preparation method of the present invention is realized through the following steps:

在室温下将季铵化烷基二烯丙基和蒸馏水装入反应器中;开始搅拌,加入衣康酸(盐)调节pH至2.0~8.0;抽真空三次,每次时间为10min,中间通氮两次,每次时间为5min;在连续通氮情况下,加入聚合助剂、氧化还原引发剂,升温至30℃~50℃,共聚反应时间控制在2~8h;加入水溶性偶氮类引发剂,升温至70℃~100℃,继续反应2~6h;冷却至室温得水溶性有机两性高分子聚合物。Put the quaternized alkyldiallyl group and distilled water into the reactor at room temperature; start stirring, add itaconic acid (salt) to adjust the pH to 2.0-8.0; vacuumize three times, each time is 10min, and pass through Nitrogen twice, each time 5min; in the case of continuous nitrogen flow, add polymerization aids, redox initiators, raise the temperature to 30°C-50°C, control the copolymerization reaction time at 2-8h; add water-soluble azo Initiator, heat up to 70°C-100°C, continue to react for 2-6h; cool to room temperature to obtain water-soluble organic amphoteric polymer.

本发明是将两种单体混合共聚,添加一定量聚合助剂,在前期采用氧化还原引发剂,在后期加入水溶性偶氮类引发剂,保证了絮凝剂具有足够高的分子量,又提高了转化率,减少了单体含量。The present invention mixes and copolymerizes two kinds of monomers, adds a certain amount of polymerization aids, uses a redox initiator in the early stage, and adds a water-soluble azo initiator in the later stage to ensure that the flocculant has a sufficiently high molecular weight and improves the Conversion, reduced monomer content.

本发明与现有用于水处理的水溶性有机高分子两性共聚物相比,具有以下优点:Compared with the existing water-soluble organic polymer amphoteric copolymers used for water treatment, the present invention has the following advantages:

1、所选用的单体无毒;1. The selected monomers are non-toxic;

2、采用水溶性氧化-还原体系作为低温引发剂,又在后期采用水溶性偶氮类作为促进剂,保证了絮凝剂具有足够高的分子量,提高了转化率,又减少了单体含量;2. The water-soluble oxidation-reduction system is used as the low-temperature initiator, and the water-soluble azo is used as the accelerator in the later stage, which ensures that the flocculant has a sufficiently high molecular weight, improves the conversion rate, and reduces the monomer content;

3、制备方法简单,宜于推广应用;3. The preparation method is simple and suitable for popularization and application;

4、性能稳定,适用于较宽的pH值范围,处理废水种类多,投入量小(仅为1~100mg/L),具有明显的经济和效益;4. Stable performance, suitable for a wide range of pH value, many types of wastewater treatment, small input (only 1-100mg/L), with obvious economic and benefit;

附图说明    图1为两种单体衣康酸(盐)和季铵化烷基二烯丙基在引发剂与聚合助剂作用下,共聚合形成二元共聚物的化学反应式。BRIEF DESCRIPTION OF THE DRAWINGS Figure 1 is a chemical reaction formula for the copolymerization of two monomers itaconic acid (salt) and quaternized alkyl diallyl under the action of an initiator and a polymerization assistant to form a binary copolymer.

结合实施案例,对本发明进一步说明如下:In conjunction with examples of implementation, the present invention is further described as follows:

实施例1Example 1

室温下,在装配有温度计、搅拌器、氮气进出口的250mL四颈瓶中,加入19g二甲基二烯丙基氯化铵和80g蒸馏水,开始搅拌,加入1g衣康酸,用10%氢氧化钠水溶液调整pH至4.5,抽真空3次,每次10min,中间通氮气2次,每次5min,继续通氮,加入单体总质量的0.025%的氟化钠和乙二胺四乙酸钠混合物0.005g,其后加入单体总质量的0.05%的过硫酸钾与亚硫酸氢钠0.01g,升温至30℃,共聚反应4小时;加入单体总质量0.05%的偶氮二异丁基脒盐酸盐0.01g,升温至70℃,继续反应3小时,冷却出料。单体转化率为94%,共聚物分子量为8×105At room temperature, in a 250mL four-necked bottle equipped with a thermometer, a stirrer, and a nitrogen inlet and outlet, add 19g of dimethyl diallyl ammonium chloride and 80g of distilled water, start stirring, add 1g of itaconic acid, and use 10% hydrogen Adjust the pH of the sodium oxide aqueous solution to 4.5, evacuate 3 times, each time for 10 minutes, pass nitrogen twice in the middle, each time for 5 minutes, continue to pass nitrogen, add 0.025% of the total mass of monomer sodium fluoride and sodium edetate Mixture 0.005g, then add 0.05% of the total mass of monomers of potassium persulfate and sodium bisulfite 0.01g, heat up to 30 ° C, copolymerization reaction for 4 hours; add 0.05% of the total mass of monomers azobisisobutyl Add 0.01 g of amidine hydrochloride, heat up to 70° C., continue to react for 3 hours, then cool and discharge. The monomer conversion rate was 94%, and the molecular weight of the copolymer was 8×10 5 .

实施例2Example 2

室温下,在装配有温度计、搅拌器、氮气进出口的250mL四颈瓶中,加入34g二甲基二烯丙基氯化铵和60g蒸馏水,开始搅拌,加入6g衣康酸,用10%氢氧化钠水溶液调整pH至5.5,抽真空3次,每次10min,中间通氮气2次,每次5min,继续通氮,加入单体总质量的0.25%的乙二胺四乙酸钠0.01g,其后加入单体总质量的0.05%的过硫酸钾与亚硫酸氢钠0.02g,升温至40℃,共聚反应4小时;加入单体总质量的0.05%的偶氮二异丁基脒盐酸盐0.02g,升温至70℃,继续反应3小时,冷却出料。单体转化率为93.2%,共聚物分子量为1.5×105At room temperature, in a 250mL four-necked bottle equipped with a thermometer, a stirrer, and a nitrogen inlet and outlet, add 34g of dimethyl diallyl ammonium chloride and 60g of distilled water, start stirring, add 6g of itaconic acid, and use 10% hydrogen Adjust the pH of the sodium oxide aqueous solution to 5.5, evacuate 3 times, each time for 10 minutes, pass nitrogen twice in the middle, each time 5 minutes, continue to pass nitrogen, add 0.01 g of sodium ethylenediamine tetraacetate of 0.25% of the total mass of the monomer, and Then add 0.05% of the total mass of the monomers of potassium persulfate and 0.02 g of sodium bisulfite, raise the temperature to 40°C, and perform a copolymerization reaction for 4 hours; add 0.05% of the total mass of the monomers of azobisisobutylamidine hydrochloride 0.02g, the temperature was raised to 70°C, the reaction was continued for 3 hours, and the material was cooled and discharged. The monomer conversion rate was 93.2%, and the molecular weight of the copolymer was 1.5×10 5 .

实施例3Example 3

室温下,在装配有温度计、搅拌器、氮气进出口的250mL四颈瓶中,加入6g二甲基二烯丙基氯化铵和93.8g蒸馏水,开始搅拌,加入0.2g衣康酸,用10%氢氧化钠水溶液调整pH至7.5,抽真空3次,每次10min,中间通氮气2次,每次5min;继续通氮,加入相当于单体总质量的0.05%三乙醇胺0.003g,其后加入相当于单体总质量的0.05%的过硫酸钾与亚硫酸氢钠0.006g,升温至50℃,共聚反应4小时;加入单体总质量的0.1%的偶氮二异丁基脒盐酸盐0.006g,升温至90℃,继续反应3小时,冷却出料。单体转化率为95%,共聚物分子量为1×104At room temperature, in a 250mL four-necked bottle equipped with a thermometer, a stirrer, and a nitrogen inlet and outlet, add 6g of dimethyl diallyl ammonium chloride and 93.8g of distilled water, start stirring, add 0.2g of itaconic acid, and use 10 % sodium hydroxide aqueous solution to adjust the pH to 7.5, evacuate 3 times, each time for 10 minutes, pass nitrogen gas twice in the middle, each time 5 minutes; Add 0.05% of the total mass of the monomers of potassium persulfate and 0.006 g of sodium bisulfite, raise the temperature to 50°C, and perform a copolymerization reaction for 4 hours; add 0.1% of the total mass of the monomers of azobisisobutylamidine hydrochloride 0.006g of salt, the temperature was raised to 90°C, the reaction was continued for 3 hours, and the mixture was cooled and discharged. The monomer conversion rate was 95%, and the molecular weight of the copolymer was 1×10 4 .

应用实施例Application example

将以上实施例1、2、3制备的NO1、2、3水溶性有机两性高分子共聚物用于钻井废水、制革废水、垃圾渗滤液的絮凝处理。The NO1, 2, and 3 water-soluble organic amphoteric polymer copolymers prepared in the above examples 1, 2, and 3 were used for flocculation treatment of drilling wastewater, tannery wastewater, and landfill leachate.

                  表1.废水水质指标   水质指标   钻井废水   制革废水   垃圾渗滤液   pHCODCr(mg/L)浊度(NTU)   10.24420683.4   7.83500467.2   9.11386282.7 Table 1. Wastewater water quality indicators water quality index Drilling wastewater Tannery wastewater landfill leachate pHCOD Cr (mg/L) Turbidity (NTU) 10.24420683.4 7.83500467.2 9.11386282.7

                     表2.絮凝剂处理废水结果   絮凝剂   钻井废水   制革废水   垃圾渗滤液   浊度   CODCr   浊度   CODCr   浊度   CODCr   去除率(%)   NO.1NO.2NO.3   87.285.084.8   74.172.371.7   76.974.274.0   64.563.761.8   81.779.177.2   70.668.166.9 Table 2. Results of flocculant treatment of wastewater flocculant Drilling wastewater Tannery wastewater landfill leachate Turbidity COD Cr Turbidity COD Cr Turbidity COD Cr Removal rate (%) NO.1NO.2NO.3 87.285.084.8 74.172.371.7 76.974.274.0 64.563.761.8 81.779.177.2 70.668.166.9

注:絮凝剂用量为10mg/L,处理前可先将废水的pH调至3~9。Note: The dosage of flocculant is 10mg/L, and the pH of the wastewater can be adjusted to 3-9 before treatment.

Claims (9)

1、一种水溶性有机两性高分子共聚物,其特征是由衣康酸(盐)和季铵化烷基二烯丙基两种单体共聚而成,分子量为1×104~1×106,化学式为1. A water-soluble organic amphoteric polymer copolymer, which is characterized in that itaconic acid (salt) and quaternized alkyl diallyl are copolymerized from two monomers, and the molecular weight is 1×10 4 to 1×10 6 , the chemical formula is 式中X是H、Na或K,R是C1~C4烷基,Y是Cl、BrIn the formula, X is H, Na or K, R is C 1 ~C 4 alkyl, Y is Cl, Br 1≤n≤7684;1≤m≤6190(n、m为正整数)1≤n≤7684; 1≤m≤6190 (n, m are positive integers) 2、如权利要求1所述水溶性有机两性高分子共聚物制备方法,其特征是以衣康酸(盐)和季铵化烷基二烯丙基为共聚合单体,在聚合助剂存在的条件下,用氧化还原引发剂和水溶性偶氮类引发剂引发单体经水溶液共聚合而制得。2, as claimed in claim 1, the preparation method of water-soluble organic amphoteric polymer copolymer is characterized in that itaconic acid (salt) and quaternized alkyl diallyl are copolymerized monomers, in the presence of polymerization aids Under certain conditions, it is prepared by copolymerizing monomers with redox initiators and water-soluble azo initiators through aqueous solution. 3、如权利要求1、2之一所述水溶性有机两性高分子共聚物及制备方法,其特征是共聚单体为衣康酸、衣康酸钠或衣康酸钾中的任一种和R为C1~C4烷基的氯季铵化或溴季铵化烷基二烯丙基中的任一种组成的共聚合单体,在水溶液中聚合单体总浓度为5%~45%(质量百分比),两种单体摩尔用量比是1∶10~1∶25。3. The water-soluble organic amphoteric polymer copolymer and its preparation method according to any one of claims 1 and 2, characterized in that the comonomer is any one of itaconic acid, sodium itaconate or potassium itaconate and R is a copolymerized monomer composed of any one of chloroquaternized or brominated quaternized alkyl diallyl of C 1 to C 4 alkyl, and the total concentration of the polymerized monomer in the aqueous solution is 5% to 45% % (mass percentage), the molar ratio of the two monomers is 1:10 to 1:25. 4、如权利要求2所述水溶性有机两性高分子共聚物的制备方法,其特征是可作为氧化还原引发剂是指氧化剂为过氧化氢、过硫酸铵、过硫酸钠、过硫酸钾中任一种和还原剂为亚硫酸氢钠、亚硫酸钠、硫代硫酸钠、连二硫酸钠、焦亚硫酸钠、亚硫酸氢钾、亚硫酸钾、亚硫酸铵、亚硫酸铁中任一种组成的氧化还原引发剂。氧化剂和还原剂物质的摩尔用量比为1.0~2.5,用量是单体质量的0.05%~5%。4. The preparation method of water-soluble organic amphoteric high molecular copolymer as claimed in claim 2 is characterized in that it can be used as redox initiator and refers to that the oxidizing agent is any one of hydrogen peroxide, ammonium persulfate, sodium persulfate and potassium persulfate. One and the reducing agent is a redox consisting of any one of sodium bisulfite, sodium sulfite, sodium thiosulfate, sodium dithionite, sodium pyrosulfite, potassium bisulfite, potassium sulfite, ammonium sulfite, and ferric sulfite Initiator. The molar ratio of the oxidizing agent to the reducing agent substance is 1.0-2.5, and the dosage is 0.05%-5% of the mass of the monomer. 5、如权利要求2所述水溶性有机两性高分子共聚物的制备方法,其特征是水溶性偶氮类引发剂是偶氮二异丁基脒盐酸盐、偶氮二异丁酸二甲酯、偶氮双(2-甲基丙酰胺)盐酸盐、偶氮双(4-氰戊酸)中任一种,用量是单体质量的0.05%~1.0%。5. The method for preparing water-soluble organic amphoteric polymer copolymers as claimed in claim 2, characterized in that the water-soluble azo initiators are azobisisobutylamidine hydrochloride, azobisisobutyric acid dimethyl Any one of ester, azobis(2-methylpropionamide) hydrochloride and azobis(4-cyanovaleric acid) is used in an amount of 0.05% to 1.0% of the monomer mass. 6、如权利要求2所述水溶性有机两性高分子共聚物的制备方法,其特征是可作为聚合助剂的是二乙醇胺、三乙醇胺、乙二胺四乙酸及其盐、水溶性含氟化合物如氟硅酸、氟硅酸钙、氟化钾、氟化钠中的一种或两种以上的混合物,用量是单体质量的0.025%~1.0%。6. The method for preparing water-soluble organic amphoteric high molecular copolymers as claimed in claim 2, characterized in that diethanolamine, triethanolamine, ethylenediaminetetraacetic acid and its salts, and water-soluble fluorine-containing compounds can be used as polymerization aids. Such as fluosilicic acid, calcium fluosilicate, potassium fluoride, sodium fluoride, or a mixture of two or more, the dosage is 0.025% to 1.0% of the monomer mass. 7、如权利要求2所述水溶性有机两性高分子共聚物的制备方法,其特征是在室温下将季铵化烷基二烯丙基和蒸馏水装入反应器中;开始搅拌,加入衣康酸(盐),调节pH至2.0~8.0;抽真空三次,每次时间为10min,中间通氮两次,每次时间为5min;在连续通氮情况下,加入聚合助剂、氧化还原引发剂,升温至30℃~50℃,共聚反应时间控制在2~8h;加入水溶性偶氮类引发剂,升温至70℃~100℃,继续反应2~6h;冷却至室温得水溶性有机两性高分子聚合物。7. The preparation method of water-soluble organic amphoteric high molecular copolymer as claimed in claim 2 is characterized in that quaternized alkyl diallyl and distilled water are loaded into the reactor at room temperature; stirring is started, and itaconic acid is added acid (salt), adjust the pH to 2.0-8.0; evacuate three times, each time is 10 minutes, and pass nitrogen twice in the middle, each time is 5 minutes; in the case of continuous nitrogen flow, add polymerization aids and redox initiators , raise the temperature to 30°C-50°C, and control the copolymerization reaction time at 2-8h; add a water-soluble azo initiator, raise the temperature to 70°C-100°C, and continue the reaction for 2-6h; cool to room temperature to obtain a water-soluble organic amphoteric high molecular polymer. 8、如权利要求2所述水溶性有机两性高分子共聚物的制备方法,其特征是调节聚合反应水溶液的pH为氢氧化钠、氢氧化钾、氢氧化钙、碳酸钠、碳酸氢钠水溶液中的任一种。8. The preparation method of water-soluble organic amphoteric high molecular copolymer as claimed in claim 2, characterized in that the pH of the aqueous solution of the polymerization reaction is adjusted as sodium hydroxide, potassium hydroxide, calcium hydroxide, sodium carbonate, sodium bicarbonate aqueous solution of any kind. 9、衣康酸(盐)与季铵化烷基二烯丙基水溶性有机两性高分子共聚物的应用,其特征是可作为废污水的处理。9. The application of itaconic acid (salt) and quaternized alkyl diallyl water-soluble organic amphoteric polymer copolymer, which is characterized in that it can be used as waste water treatment.
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