CN102689963A - Organic copolymerized amphoteric polymeric flocculant and preparation method - Google Patents
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Abstract
本发明公开了一种有机共聚两性高分子絮凝剂及制备方法,该两性高分子絮凝剂是由甲基丙烯酰氧乙基三甲基卤化铵、N-乙烯基吡咯烷酮和山梨酸(盐)三种单体及双官能团单体二丙烯酸酯共聚合形成的共聚物。制备过程中同时使用氧化还原引发剂、无机过氧化物引发剂及聚合助剂,提高了单体的转化率,减少了残留单体;絮凝剂制备操作简单,可直接使用;所制备的絮凝剂具有用量小,絮体直径大和沉降快等优点。
The invention discloses an organic copolymerized amphoteric polymer flocculant and a preparation method thereof. The amphoteric polymer flocculant is composed of methacryloyloxyethyltrimethylammonium halide, N-vinylpyrrolidone and sorbic acid (salt) three A copolymer formed by copolymerization of a monomer and a bifunctional monomer diacrylate. Redox initiators, inorganic peroxide initiators and polymerization aids are used simultaneously in the preparation process, which improves the conversion rate of monomers and reduces residual monomers; the preparation of flocculants is simple and can be used directly; the prepared flocculants It has the advantages of small dosage, large floc diameter and fast settlement.
Description
技术领域 technical field
本发明涉及有机共聚两性高分子絮凝剂及制备方法。 The invention relates to an organic copolymerized amphoteric polymer flocculant and a preparation method.
背景技术 Background technique
水是人类生存和社会发展的基本物质。目前世界范围内水环境正面临水资源紧缺、过渡消耗和严重污染的问题。世界卫生组织(WHO)调查表明:人类80%的疾病与水质不安全有关。中国是一个水资源大国,同时又是一个严重缺水、水资源利用率极低和水污染严重的国家,三大因素严重制约了人们正常的生活和经济的可持续发展。因此,对废(污)水进行有效处理并回用是解决有限的水资源满足人们日益增长的生产和生活需求的必然途经。在废(污)处理和污泥脱水过程中,絮凝法是一种重要、有效而又经济、简便的方法,国内外的工业废水、生活污水使用絮凝技术处理比例在55%~85%,自来水工业和污泥脱水100%使用絮凝法进行处理;废(污)水絮凝和污泥脱水的效果对后续工序的运行、出水的达标排放及处理费用密切关联,而絮凝剂是废(污)水处理、固液分离的关键因素之一,因此进行新型、无毒和高效絮凝剂的研发是水处理工作的重点和方向。 Water is the basic material for human survival and social development. At present, the water environment in the world is facing the problems of water resource shortage, excessive consumption and serious pollution. The World Health Organization (WHO) survey shows that 80% of human diseases are related to unsafe water quality. China is a country with abundant water resources, but at the same time it is a country with severe water shortage, extremely low utilization rate of water resources and serious water pollution. These three factors seriously restrict people's normal life and sustainable economic development. Therefore, effective treatment and reuse of waste water (sewage) is an inevitable way to solve limited water resources to meet people's growing production and living needs. In the process of waste (sewage) treatment and sludge dehydration, flocculation is an important, effective, economical and convenient method. The proportion of domestic and foreign industrial wastewater and domestic sewage treated by flocculation technology is 55% to 85%. 100% of industrial and sludge dehydration is treated by flocculation; the effect of waste (sewage) water flocculation and sludge dehydration is closely related to the operation of subsequent processes, the discharge of effluent and the cost of treatment, and the flocculant is waste (sewage) water One of the key factors for water treatment and solid-liquid separation, so the research and development of new, non-toxic and efficient flocculants is the focus and direction of water treatment.
絮凝剂可分为微生物絮凝剂、无机絮凝剂和有机高分子絮凝剂等几大类。微生物絮凝剂对环境和人类具有较高的安全性,目前微生物絮凝剂大多还处于菌种的筛选阶段,且存在成本较高,无法适应工业化生产和应用的要求。无机絮凝剂由于用量大、生成污泥多、腐蚀性强、产生二次污染和易受废(污)水水质影响,在有些场合净水效果不理想,应用受到很大的局限,正逐步被有机絮凝剂取代。有机高分子絮凝剂具有用量少、絮凝速度快、生成污泥少、脱色性好和受废(污)水水质影响小等优点而日益受到重视;根据来源不同,有机高分子混凝剂可分为天然有机高分子絮凝剂和合成有机高分子絮凝剂;天然有机高分子絮凝剂优点是原料来源丰富、价格便宜、基本无毒、易生化降解和基本不造成二次污染,缺点是成分复杂、组成不稳定、性能波动大、贮存过程中可能存在变质以及生产过程使用大量的有机溶剂等问题,使其实际应用受到限制;合成有机高分子絮凝剂性能稳定,可根据需要控制合成产物的分子量及结构等优点,可分为非离子、阴离子、阳离子和两性型。随着社会和经济的发展,现代工业和生活污水的排放量及化学需氧量(Chemical Oxygen Demand, CODCr)不断增加,废(污)水组成和性质变得日益复杂,用常规的絮凝剂难以满足要求,而废(污)水中的微粒表面通常带有负电荷,同时水体中含有一定量的有毒金属离子,非离子、阴离子和阳离子型高分子絮凝剂的使用受到了限制;两性有机高分子絮凝剂的聚合物分子链上同时包含正负电荷基团,称为两性高分子(amphoteric polymer)或两性聚电解质(amphoteric polyelectrolyte),因其分子的特殊结构而具有一些特性,如电中和、吸附架桥以及分子间的“缠绕”包裹作用,适用于阴、阳离子共存的废(污)水,对于由阴离子表面活性剂所稳定的分散液、乳浊液以及各类污泥或者由阳离子所稳定的各种胶体分散液,均有良好的絮凝和污泥脱水功效,可用作水处理絮凝剂、污泥脱水剂、吸附剂及金属离子螯合剂等;由于具有较好的脱水性、金属离子去除性、对pH值要求范围宽和抗盐性好等优点,使得两性有机高分子絮凝剂有很广泛应用范围,已成为国内外研究的热点。 Flocculants can be divided into several categories such as microbial flocculants, inorganic flocculants and organic polymer flocculants. Microbial flocculants are relatively safe for the environment and human beings. At present, most microbial flocculants are still in the screening stage of strains, and the cost is high, which cannot meet the requirements of industrial production and application. Due to the large amount of inorganic flocculants, the generation of a lot of sludge, strong corrosion, secondary pollution and the influence of waste (sewage) water quality, the water purification effect is not ideal in some occasions, and the application is greatly limited, and is gradually being used. Organic flocculants instead. Organic polymer flocculant has the advantages of less dosage, fast flocculation speed, less sludge generation, good decolorization and little impact on waste (sewage) water quality, etc. It is divided into natural organic polymer flocculants and synthetic organic polymer flocculants; the advantages of natural organic polymer flocculants are rich sources of raw materials, low price, basically non-toxic, easy biochemical degradation and basically no secondary pollution, and the disadvantage is that the composition is complex , Unstable composition, large performance fluctuations, possible deterioration during storage, and the use of a large amount of organic solvents in the production process, which limit its practical application; the synthetic organic polymer flocculant has stable performance, and the molecular weight of the synthetic product can be controlled according to needs And structure and other advantages, can be divided into non-ionic, anionic, cationic and amphoteric. With the development of society and economy, the discharge of modern industrial and domestic sewage and the increase in chemical oxygen demand (Chemical Oxygen Demand, COD Cr ), the composition and properties of waste (sewage) water have become increasingly complex. Using conventional flocculants It is difficult to meet the requirements, and the surface of particles in waste (sewage) water usually has a negative charge, and the water contains a certain amount of toxic metal ions, so the use of non-ionic, anionic and cationic polymer flocculants is limited; amphoteric organic high The polymer molecular chain of the molecular flocculant contains both positive and negative charge groups, called amphoteric polymer or amphoteric polyelectrolyte, which has some characteristics due to its special molecular structure, such as electrical neutralization , adsorption bridging and intermolecular "entanglement" encapsulation, suitable for waste (sewage) water where anions and cations coexist, for dispersions, emulsions and various sludges stabilized by anionic surfactants or by cations The various colloidal dispersions stabilized have good flocculation and sludge dehydration effects, and can be used as water treatment flocculants, sludge dehydrating agents, adsorbents and metal ion chelating agents, etc.; due to their good dehydration, The advantages of metal ion removal, wide range of pH requirements and good salt resistance make amphoteric organic polymer flocculants have a wide range of applications, and have become a hot research topic at home and abroad.
目前国内外研发的合成类两性有机高分子絮凝剂主要有通过聚丙烯酰胺(pAM)的改性,即通过酰胺基的化学反应,如曼尼期(Mannich)反应、水解或接枝反应改性,及以聚丙烯腈(pAN)为高分子链,用双氰双胺改性的两性聚丙烯腈-双氰双胺(pAN-DCD)两大类;《有机化工原料》[M],1999年1月第3版,化学工业出版社,司航主编,介绍了丙烯酰胺(AM)、丙烯腈(AN)属剧毒化学品;《丙烯酰胺聚合物》[M],2006年4月第1版,化学工业出版社,方道斌等主编,介绍了丙烯酰胺对人体和环境的危害,“接触丙烯酰胺有三种形式,经口、呼吸道吸入及皮肤接触。丙烯酰胺被吸入后分布于体液中。水是最重要的被污染物。非职业性接触丙烯酰胺主要来自被丙烯酰胺污染的饮用水和食品。丙烯酰胺的毒性主要表现为皮肤损害和神经系统损害。美国环境保护局(EPA)对丙烯酰胺对人的毒性反应的规定是:短期和长期经口或接触丙烯酰可引起人的神经系统的伤害,并认为低浓度丙烯酰胺也是一种对神经系统有损害的物质。急性中毒反应是对皮肤和呼吸道有刺激性,接触部位皮疹。慢性中毒引起神经毒性反应,影响中枢神经和周围神经”。 “l994年国际癌症研究机构(IARC)考察对动物基因毒性,将丙烯酰胺由原来1987年列为2B组(有可能致癌)提升到了2A组(很可能致癌)”。“鉴于丙烯酰胺对人类和环境和健康的影响, WHO、IARC、美国食品于药品管理局(FDA)、EPA、欧盟(EU)和中国政府等对环境中丙烯酰胺的限量都作了严格的规定”。“各国对水处理中聚丙烯酰胺的最大允许投加量及聚丙烯酰胺产品中残留单体丙烯酰胺的最大允许含量有严格的限定。例如,WHO规定在水净化中聚丙烯酰胺的投加量不得超过1mg/L。产品中丙烯酰胺的残留量不得超过0.05%,即丙烯酰胺在饮水中最大的残留量0.0005 mg/L”。随着环境保护意识的增强以及废(污)水污染治理的严峻形势,水处理的要求愈来愈高。本发明的目的及意义旨在针对国内外现有制备絮凝剂的单体的毒性,选择无(低)毒性的单体,采用适宜的聚合方法和工艺条件,制备一种无(低)毒、实用、有效和经济的新型有机共聚两性高分子絮凝剂,以满足废(污)水处理的需求。 At present, the synthetic amphoteric organic polymer flocculants developed at home and abroad are mainly modified by polyacrylamide (pAM), that is, by the chemical reaction of amide groups, such as Mannich reaction, hydrolysis or grafting reaction modification. , and polyacrylonitrile (pAN) as the polymer chain, amphoteric polyacrylonitrile-dicyandiamide (pAN-DCD) modified with dicyandiamide; "Organic Chemical Materials" [M], 1999 The third edition in January 2006, Chemical Industry Press, edited by Si Hang, introduced acrylamide (AM) and acrylonitrile (AN) as highly toxic chemicals; "Acrylamide Polymer" [M], April 2006 No. 1st edition, Chemical Industry Press, edited by Fang Daobin, etc., introduced the hazards of acrylamide to the human body and the environment, "There are three forms of exposure to acrylamide, oral, respiratory inhalation and skin contact. Acrylamide is distributed in body fluids after inhalation. Water is the most important pollutant. Non-occupational exposure to acrylamide mainly comes from drinking water and food contaminated with acrylamide. The toxicity of acrylamide is mainly manifested as skin damage and nervous system damage. The U.S. Environmental Protection Agency (EPA) on propylene The regulations on the toxicity of amide to humans are: short-term and long-term oral or exposure to acryloyl can cause damage to the human nervous system, and it is considered that low-concentration acrylamide is also a substance that is harmful to the nervous system. Acute poisoning is the Irritation of the skin and respiratory tract, rash at the site of contact. Chronic poisoning causes neurotoxic reactions, affecting the central and peripheral nerves." "In 1994, the International Agency for Research on Cancer (IARC) investigated the genotoxicity to animals and raised acrylamide from Group 2B (possibly carcinogenic) to Group 2A (probably carcinogenic) in 1987." "In view of the impact of acrylamide on human beings, the environment and health, WHO, IARC, the US Food and Drug Administration (FDA), EPA, the European Union (EU) and the Chinese government have all made strict regulations on the limit of acrylamide in the environment ". "Countries have strict restrictions on the maximum allowable dosage of polyacrylamide in water treatment and the maximum allowable content of residual monomer acrylamide in polyacrylamide products. For example, WHO stipulates the dosage of polyacrylamide in water purification It shall not exceed 1mg/L. The residue of acrylamide in the product shall not exceed 0.05%, that is, the maximum residue of acrylamide in drinking water is 0.0005 mg/L". With the increasing awareness of environmental protection and the severe situation of waste (sewage) water pollution control, the requirements for water treatment are getting higher and higher. The purpose and significance of the present invention aim at the toxicity of existing monomers for preparing flocculants at home and abroad, select non-(low) toxic monomers, and adopt suitable polymerization methods and process conditions to prepare a non-(low) toxic, A practical, effective and economical new organic copolymerized amphoteric polymer flocculant to meet the needs of waste (sewage) water treatment.
目前合成类两性高分子絮凝剂存在以下缺陷: At present, synthetic amphoteric polymer flocculants have the following defects:
1、合成两性高分子絮凝剂选用了丙烯酰胺、丙烯腈剧毒性的单体,聚合残留单体和分解后的小分子都会产生二次污染; 1. The synthetic amphoteric polymer flocculant uses highly toxic acrylamide and acrylonitrile monomers, and the residual monomers after polymerization and small molecules after decomposition will cause secondary pollution;
2、曼尼希(Mannich)反应需使用大量的有机溶剂,不符合绿色化学的原则; 2. The Mannich reaction requires the use of a large amount of organic solvents, which does not conform to the principles of green chemistry;
3、经曼尼希反应改性的聚丙烯酰胺类两性高分子絮凝剂,不适用于处理pH高的废水,贮存稳定性不高; 3. The polyacrylamide amphoteric polymer flocculant modified by Mannich reaction is not suitable for treating wastewater with high pH, and its storage stability is not high;
本发明在保持絮凝剂的絮凝效率不降低的前提条件下,可达到性能更好的情形: The present invention can achieve better performance under the premise that the flocculation efficiency of the flocculant is not reduced:
1、选用单体无(低)毒,不造成二次污染,更符合绿色化学要求; 1. The selected monomer has no (low) toxicity, does not cause secondary pollution, and is more in line with the requirements of green chemistry;
2、共聚合以水为溶剂,符合清洁化生产的原则; 2. Copolymerization uses water as a solvent, which conforms to the principle of clean production;
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. Overcome the shortcomings of poor dehydration effect and unstable performance of polyacrylamide flocculants;
4、共聚合在低温选用氧化还原引发剂,高温选用无机过氧化物引发剂,同时配以酸度调节剂和聚合助剂,使产物的分子量满足了使用要求,也减少残留单体。 4. For copolymerization, redox initiators are used at low temperatures, and inorganic peroxide initiators are used at high temperatures. At the same time, acidity regulators and polymerization aids are used to make the molecular weight of the product meet the requirements of use and reduce residual monomers.
发明内容 Contents of the invention
通过新的技术,提供一种性能稳定、使用范围更广和絮凝效果更好的有机共聚两性高分子絮凝剂及操作简单的制备方法。 Through the new technology, an organic copolymerized amphoteric polymer flocculant with stable performance, wider application range and better flocculation effect and a preparation method with simple operation are provided.
该有机共聚两性高分子絮凝剂是由甲基丙烯酰氧乙基三甲基卤化铵、N-乙烯基吡咯烷酮与山梨酸(盐)及双官能团单体二丙烯酸酯共聚而成的共聚物,其特征在于, The organic copolymerized amphoteric polymer flocculant is a copolymer formed by copolymerization of methacryloyloxyethyltrimethylammonium halide, N-vinylpyrrolidone, sorbic acid (salt) and bifunctional monomer diacrylate. Characterized in that,
单体1是甲基丙烯酰氧乙基三甲基卤化铵,结构式为: Monomer 1 is methacryloyloxyethyltrimethylammonium halide, the structural formula is:
式中X是Cl、Br; In the formula, X is Cl, Br;
单体2是N-乙烯基吡咯烷酮,结构式为: Monomer 2 is N-vinylpyrrolidone with the structural formula:
; ;
单体3是山梨酸(盐),结构式为: Monomer 3 is sorbic acid (salt), the structural formula is:
式中;Y是H、Na或K; In the formula; Y is H, Na or K;
双官能团单体二丙烯酸酯,结构式为: Bifunctional monomer diacrylate, the structural formula is:
式中1≦i≦23(i为正整数), Where 1≦i≦23 (i is a positive integer),
三种单体及双官能团单体二丙烯酸酯按照一定的量比共聚合形成的共聚物的结构如图: The structure of the copolymer formed by copolymerization of three kinds of monomers and bifunctional monomer diacrylate according to a certain ratio is shown in the figure:
图中:1≦n≦38552;1≦m≦71976;1≦p≦71341;1≦q≦47003;1≦i≦23,n、m 、p、q 、i为正整数。 In the figure: 1≦n≦38552; 1≦m≦71976; 1≦p≦71341; 1≦q≦47003; 1≦i≦23, n, m , p, q, i are positive integers.
本发明制备方法对上述共聚单体、双官能团单体二丙烯酸酯、氧化还原引发剂、无机过氧化物引发剂、酸度调节剂和聚合助剂等并无特别要求。例如共聚合单体, 通式可以表示为 CH2=C(CH3)COO(CH2)2N+(CH3)3X-的二甲基二烯丙基卤化铵;化学分子式表示为C6H9ON的N-乙烯基吡咯烷酮;通式可以表示为CH3CH=CHCH=CHCOOY的山梨酸(盐);通式可以表示为CH2=CHCOO(R)i OOCCH=CH2的双官能团单体二丙烯酸酯。试验结果显示,为使本发明所制备的有机共聚两性高分子絮凝剂的使用性能及经济性达到最佳效果,三种单体的物质的量之比控制在(15~80):(10~70):(5~60)(mol%);双官能团单体二丙烯酸酯的质量为其它三种单体质量之和的0.8%~10%;单体总质量占反应体系的质量分数为10%~60%。 The preparation method of the present invention has no special requirements on the above-mentioned comonomers, bifunctional monomer diacrylates, redox initiators, inorganic peroxide initiators, acidity regulators and polymerization aids. For example, the copolymerization monomer, the general formula can be expressed as CH 2 =C(CH 3 )COO(CH 2 ) 2 N + (CH 3 ) 3 X - dimethyl diallyl ammonium halide; the chemical molecular formula is expressed as C N-vinylpyrrolidone of 6 H 9 ON; sorbic acid (salt) whose general formula can be expressed as CH 3 CH=CHCH=CHCOOY; bifunctional group whose general formula can be expressed as CH 2 =CHCOO(R) i OOCCH=CH 2 Monomer diacrylate. The test results show that in order to achieve the best performance and economic efficiency of the organic copolymerized amphoteric polymer flocculant prepared by the present invention, the ratio of the amounts of the three monomers is controlled at (15-80): (10-80) 70): (5-60) (mol%); the mass of the diacrylate monomer of the difunctional group is 0.8%-10% of the sum of the mass of the other three monomers; the mass fraction of the total mass of the monomer in the reaction system is 10 %~60%.
如前述,本发明在共聚合前期较低温度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、过硫酸钾中的任一种,还原剂为亚硫酸氢钠、亚硫酸钠、亚硫酸氢钾、硫代硫酸钠中的任一种。试验结果显示,氧化剂与还原剂的物质的量之比为1:(1~0.2),用量在单体总质量的0.1%~2%范围内可达到理想的效果。 As mentioned above, the present invention adds a redox initiator at a relatively low temperature in the early stage of the copolymerization for the purpose of obtaining a copolymer with a large molecular weight. For example, the oxidizing agent selected can be any one of hydrogen peroxide, ammonium persulfate, sodium persulfate, potassium persulfate, and the reducing agent is any one of sodium bisulfite, sodium sulfite, potassium bisulfite, sodium thiosulfate kind. The test results show that the ratio of the amount of oxidizing agent to reducing agent is 1: (1-0.2), and the ideal effect can be achieved in the range of 0.1%-2% 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无机过氧化物引发剂,其目的是为降低单体的残留,提高单体转化率。例如选用过氧化氢、过硫酸铵、过硫酸钠、过硫酸钾。试验结果显示,用量为单体总质量的0.02%~2.0%范围内,单体转化率可达到理想的效果。 As mentioned above, the present invention adds an inorganic peroxide initiator at a higher temperature in the later stage of polymerization, the purpose of which is to reduce the residual monomer and increase the conversion rate of the monomer. For example, hydrogen peroxide, ammonium persulfate, sodium persulfate, potassium persulfate are selected. The test results show that the conversion rate of the monomer can achieve the desired effect when the dosage is within the range of 0.02% to 2.0% of the total mass of the monomer.
如前述,本发明在共聚合反应中加入酸度调节剂,调整聚合体系的pH=2~9,其目的是为保证所用的引发剂能达到最理想的引发效率。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、盐酸中任一种的水溶液。 As mentioned above, the present invention adds an acidity regulator in the copolymerization reaction to adjust the pH of the polymerization system to 2-9, the purpose of which is to ensure that the initiator used can achieve the most ideal initiation efficiency. The substance used to adjust the pH is an aqueous solution of any one of sodium hydroxide, potassium hydroxide, calcium hydroxide, sodium carbonate, sodium bicarbonate and hydrochloric acid.
如前述,本发明在共聚合反应中加入聚合助剂,其目的是能使氧化还原引发剂引发形成的初级自由基以及单体自由基不被过早终止。例如选用二乙醇胺、三乙醇胺、乙二胺四乙酸及盐、水溶性含氟化合物如氟硅酸、氟硅酸钙、氟化钾、氟化钠的任一种或二种以上的混合物。试验结果显示,其用量为单体总质量的0.01%~1.5%范围内,能使氧化还原引发剂引发的共聚合反应得到大分子量有机共聚两性高分子絮凝剂并使聚合速率得以控制。 As mentioned above, in the present invention, a polymerization assistant is added in the copolymerization reaction, the purpose of which is to prevent the primary free radicals formed by the redox initiator and monomer free radicals from being prematurely terminated. For example, any one of diethanolamine, triethanolamine, ethylenediaminetetraacetic acid and its salts, water-soluble fluorine-containing compounds such as fluorosilicic acid, calcium fluorosilicate, potassium fluoride, and sodium fluoride, or a mixture of two or more is used. The test results show that the dosage is within the range of 0.01% to 1.5% of the total mass of the monomers, and the copolymerization reaction initiated by the redox initiator can obtain a large molecular weight organic copolymerized amphoteric polymer flocculant and the polymerization rate can be controlled.
本发明的方法包括以下步骤及工艺条件: The method of the present invention comprises the following steps and processing conditions:
步骤1、在四颈反应瓶中加入山梨酸(盐)、聚合助剂和蒸馏水搅拌溶解,抽真空两次,每次时间5分钟,中间通氮一次,时间5分钟; Step 1. Add sorbic acid (salt), polymerization aids and distilled water into the four-neck reaction flask, stir and dissolve, vacuumize twice, each time 5 minutes, and pass nitrogen once in the middle, time 5 minutes;
步骤2、用蒸馏水稀释甲基丙烯酰氧乙基三甲基卤化铵装入滴液漏斗(a)、用蒸馏水稀释N-乙烯基吡咯烷酮装入滴液漏斗(b)、用蒸馏水稀释双官能团单体二丙烯酸酯并转入滴液漏斗(c); Step 2. Dilute methacryloyloxyethyltrimethylammonium halide with distilled water and put it into the dropping funnel (a), dilute N-vinylpyrrolidone with distilled water and put it into the dropping funnel (b), dilute the bifunctional mono Bulk diacrylate and transfer to dropping funnel (c);
步骤3、在连续搅拌和通氮条件下,一次性加入氧化还原引发剂,升温至35℃~45℃,调整水溶液pH为2~9,滴液漏斗(a)滴加甲基丙烯酰氧乙基三甲基卤化铵的水溶液、滴液漏斗(b)加滴N-乙烯基吡咯烷酮的水溶液、滴液漏斗(c)滴加双官能团单体二丙烯酸酯的水溶液到四颈反应瓶中,三支滴液漏斗同时滴加,控制滴加速度,滴加时间是0.5~3小时,滴加完后恒温0.5~4小时,滴加和恒温过程中,每10分钟检查一次四颈反应瓶中反应液体的pH值,保持pH为2~9; Step 3. Under the conditions of continuous stirring and nitrogen flow, add the redox initiator at one time, raise the temperature to 35°C~45°C, adjust the pH of the aqueous solution to 2~9, add methacryloyloxyethyl dropwise into the dropping funnel (a) The aqueous solution of trimethylammonium halide, the dropping funnel (b) add the aqueous solution of N-vinylpyrrolidone, the dropping funnel (c) drop the aqueous solution of the bifunctional monomer diacrylate to the four-necked reaction flask, three The dripping funnel is added dropwise at the same time, and the dropping speed is controlled. The dropping time is 0.5 to 3 hours, and the temperature is kept constant for 0.5 to 4 hours after the dropping. Keep the pH value at 2-9;
步骤4、升温至75℃~85℃,加入无机过氧化物引发剂继续反应,每20分钟检查一次四颈反应瓶中反应液体的pH值,保持pH为2~9,反应时间1~3.5小时,冷却,出料,得到有机共聚两性高分子絮凝剂产品; Step 4. Heat up to 75°C-85°C, add inorganic peroxide initiator to continue the reaction, check the pH value of the reaction liquid in the four-neck reaction bottle every 20 minutes, keep the pH at 2-9, and the reaction time is 1-3.5 hours , cooling, and discharging to obtain an organic copolymerized amphoteric polymer flocculant product;
本发明方法是由三种单体和双官能团单体二丙烯酸酯进行变温共聚合,反应体系存在足量的活性自由基,能使共聚合反应连续进行;采用水溶性氧化还原剂作为低温引发剂,保证了絮凝剂具有足够高的分子量;调整反应体系的pH,使引发效率更为理想;辅以一定量的聚合助剂,减少了反应体系中的杂质,防止活性自由基过早终止;在聚合反应后期加入无机过氧化物引发剂,降低了单体的残留,提高了转化率。 In the method of the present invention, temperature-variable copolymerization is carried out by three kinds of monomers and bifunctional monomer diacrylate, and there are sufficient active free radicals in the reaction system, so that the copolymerization reaction can be continuously carried out; water-soluble redox agent is used as a low-temperature initiator , to ensure that the flocculant has a sufficiently high molecular weight; adjust the pH of the reaction system to make the initiation efficiency more ideal; add a certain amount of polymerization assistant to reduce the impurities in the reaction system and prevent the premature termination of active free radicals; The inorganic peroxide initiator is added in the later stage of the polymerization reaction, which reduces the residual monomer and improves the conversion rate.
本发明与现有用于水处理的两性聚丙烯酰胺类絮凝剂相比,具有以下优点: Compared with the existing amphoteric polyacrylamide flocculants used for water treatment, the present invention has the following advantages:
1、与现有技术生产的有机共聚两性高分子絮凝剂相比,所用单体无(低)毒,对环境几乎无影响; 1. Compared with the organic copolymerized amphoteric polymer flocculants produced by the prior art, the monomers used are non-toxic (low) and have almost no impact on the environment;
2、采用水溶性氧化还原剂作为低温引发剂,在后期加入水溶性过氧化物引发剂,保证了絮凝剂具有足够高的分子量,且转化率更高,残留单体含量更低; 2. Water-soluble redox agent is used as the low-temperature initiator, and water-soluble peroxide initiator is added in the later stage to ensure that the flocculant has a sufficiently high molecular weight, and the conversion rate is higher and the residual monomer content is lower;
3、制备方法简单,反应条件温和,宜于推广应用; 3. The preparation method is simple, the reaction conditions are mild, and it is 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1~200mg/L),具有明显的经济效益。 4. Stable performance, suitable for a wide range of pH value, many types of wastewater treatment, small input (only 1-200mg/L), and obvious economic benefits.
附图说明 附图是单体1、单体2、单体3及双官能团单体二丙烯酸酯按照一定量比,在引发剂和聚合助剂作用下,进行共聚合反应的化学式。 BRIEF DESCRIPTION OF THE DRAWINGS The attached figure is the chemical formula for the copolymerization reaction of monomer 1, monomer 2, monomer 3 and bifunctional monomer diacrylate in a certain ratio under the action of an initiator and a polymerization aid.
实施案例 结合实施例对本发明进一步说明如下: Implementation case The present invention is further described as follows in conjunction with embodiment:
实施例1 Example 1
步骤1、在装有温度计、通氮装置以及搅拌器的250mL的四颈反应瓶中加入1.6g山梨酸(盐)、0.006g聚合助剂乙二胺四乙酸钠和氟化钾的混合物和15g蒸馏水搅拌溶解,抽真空两次,每次时间5分钟,中间通氮一次,时间5分钟; Step 1, add the mixture of 1.6g sorbic acid (salt), 0.006g polymerization assistant sodium edetate and potassium fluoride and 15g Stir the distilled water to dissolve, vacuumize twice, each time for 5 minutes, and pass nitrogen once in the middle, for 5 minutes;
步骤2、用8g蒸馏水稀释15.7g甲基丙烯酰氧乙基三甲基卤化铵装入滴液漏斗(a)、用15g蒸馏水稀释2.7gN-乙烯基吡咯烷酮装入滴液漏斗(b)、用20g蒸馏水稀释1.2g双官能团单体二丙烯酸酯装入滴液漏斗(c); Step 2. Dilute 15.7g of methacryloyloxyethyltrimethylammonium halide with 8g of distilled water and put it into the dropping funnel (a), dilute 2.7g of N-vinylpyrrolidone with 15g of distilled water and put it into the dropping funnel (b). 20g of distilled water diluted 1.2g of bifunctional monomer diacrylate into the dropping funnel (c);
步骤3、在连续搅拌和通氮条件下,一次性加入0.19氧化还原引发剂过硫酸钾和亚硫酸氢钾钠的混合物,氧化剂与还原剂的物质的量之比是1: 0.6,升温至45℃,调整水溶液pH为3,滴液漏斗(a)滴加甲基丙烯酰氧乙基三甲基卤化铵的水溶液、滴液漏斗(b)滴加N-乙烯基吡咯烷酮的水溶液、滴液漏斗(c)滴加双官能团单体二丙烯酸酯的水溶液到四颈反应瓶中,三支滴液漏斗同时滴加,控制滴加速度,滴加时间是1小时,滴加完后恒温2小时,滴加和恒温过程中,每10分钟检查一次四颈反应瓶中反应液体的pH值,保持pH为3; Step 3, under the condition of continuous stirring and nitrogen flow, add 0.19 redox initiator potassium persulfate and sodium potassium bisulfite mixture at one time, the ratio of the amount of substance of oxidizing agent and reducing agent is 1: 0.6, be warming up to 45 °C, adjust the pH of the aqueous solution to 3, drop the aqueous solution of methacryloyloxyethyltrimethylammonium halide into the dropping funnel (a), drop the aqueous solution of N-vinylpyrrolidone into the dropping funnel (b), drop the aqueous solution of the dropping funnel (c) Add the aqueous solution of bifunctional monomer diacrylate dropwise to the four-neck reaction flask, and drop the three dropping funnels at the same time to control the dropping speed. The dropping time is 1 hour. After the dropping, keep the temperature for 2 hours. During the addition and constant temperature process, check the pH value of the reaction liquid in the four-neck reaction flask every 10 minutes, and keep the pH at 3;
步骤4、升温至80℃,加入0.05g无机过氧化物引发剂过硫酸钾继续反应,每20分钟检查一次四颈反应瓶中反应液体的pH值,保持pH为3,反应时间2小时,冷却,出料,得到有机共聚两性高分子絮凝剂产品,分子量为7.3×106,转化率为97.6%。 Step 4. Heat up to 80°C, add 0.05g of inorganic peroxide initiator potassium persulfate to continue the reaction, check the pH value of the reaction liquid in the four-neck reaction flask every 20 minutes, keep the pH at 3, react for 2 hours, cool , discharged to obtain an organic copolymerized amphoteric polymer flocculant product with a molecular weight of 7.3×10 6 and a conversion rate of 97.6%.
实施例2 Example 2
步骤1、在装有温度计、通氮装置以及搅拌器的250mL的四颈反应瓶中加入2.4g山梨酸(盐)、0.009g聚合助剂乙二胺四乙酸钠和氟化钾的混合物和22g蒸馏水搅拌溶解,抽真空两次,每次时间5分钟,中间通氮一次,时间5分钟; Step 1, add the mixture of 2.4g sorbic acid (salt), 0.009g polymerization assistant sodium edetate and potassium fluoride and 22g Stir the distilled water to dissolve, vacuumize twice, each time for 5 minutes, and pass nitrogen once in the middle, for 5 minutes;
步骤2、用12g蒸馏水稀释24g甲基丙烯酰氧乙基三甲基卤化铵装入滴液漏斗(a)、用22g蒸馏水稀释4gN-乙烯基吡咯烷酮装入滴液漏斗(b)、用30g蒸馏水稀释1.8g双官能团单体二丙烯酸酯装入滴液漏斗(c); Step 2. Dilute 24g of methacryloxyethyltrimethylammonium halide with 12g of distilled water and put it into the dropping funnel (a), dilute 4g of N-vinylpyrrolidone with 22g of distilled water and put it into the dropping funnel (b), and put it into the dropping funnel (b) with 30g of distilled water Dilute 1.8g of bifunctional monomer diacrylate into the dropping funnel (c);
步骤3、在连续搅拌和通氮条件下,一次性加入0.29氧化还原引发剂过硫酸钾和亚硫酸氢钾钠的混合物,氧化剂与还原剂的物质的量之比是1: 0.5,升温至40℃,调整水溶液pH为4,滴液漏斗(a)滴加甲基丙烯酰氧乙基三甲基卤化铵的水溶液、滴液漏斗(b)滴加N-乙烯基吡咯烷酮的水溶液、滴液漏斗(c)滴加双官能团单体二丙烯酸酯的水溶液到四颈反应瓶中,三支滴液漏斗同时滴加,控制滴加速度,滴加时间是0.5小时,滴加完后恒温2小时,滴加和恒温过程中,每10分钟检查一次四颈反应瓶中反应液体的pH值,保持pH为4; Step 3, under the condition of continuous stirring and nitrogen flow, add the mixture of 0.29 redox initiator potassium persulfate and sodium potassium bisulfite at one time, the ratio of the amount of substance of oxidizing agent and reducing agent is 1: 0.5, be warming up to 40 °C, adjust the pH of the aqueous solution to 4, drop the aqueous solution of methacryloyloxyethyltrimethylammonium halide into the dropping funnel (a), drop the aqueous solution of N-vinylpyrrolidone into the dropping funnel (b), drop the dropping funnel (c) Add the aqueous solution of bifunctional monomer diacrylate dropwise to the four-necked reaction flask, and drop the three dropping funnels at the same time to control the dropping speed. The dropping time is 0.5 hours. After the dropping, keep the temperature for 2 hours. During the addition and constant temperature process, check the pH value of the reaction liquid in the four-neck reaction flask every 10 minutes, and keep the pH at 4;
步骤4、升温至80℃,加入0.07g无机过氧化物引发剂过硫酸钾继续反应,每20分钟检查一次四颈反应瓶中反应液体的pH值,保持pH为4,反应时间2小时,冷却,出料,得到有机共聚两性高分子絮凝剂产品,分子量为7×106,转化率为96.3%。 Step 4. Heat up to 80°C, add 0.07g of inorganic peroxide initiator potassium persulfate to continue the reaction, check the pH value of the reaction liquid in the four-neck reaction flask every 20 minutes, keep the pH at 4, react for 2 hours, cool , discharged to obtain an organic copolymerized amphoteric polymer flocculant product with a molecular weight of 7×10 6 and a conversion rate of 96.3%.
应用实施例 Application example
将以上实施例1、2制备的NO.1、NO.2有机共聚两性高分子絮凝剂用于印染废水的絮凝处理(见表1、表2)。 The No.1 and No.2 organic copolymerized amphoteric polymer flocculants prepared in the above Examples 1 and 2 were used for flocculation treatment of printing and dyeing wastewater (see Table 1 and Table 2).
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CN101249996A (en) * | 2007-12-11 | 2008-08-27 | 四川师范大学 | A kind of organic polymer flocculant and preparation method thereof |
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CN102689966A (en) * | 2012-06-13 | 2012-09-26 | 四川师范大学 | Organic copolymerization amphoteric polymeric flocculant and preparation method thereof |
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