CN107879450B - Water-soluble quaternary polymer molecular brush anionic dye capturing settling agent and preparation method and application thereof - Google Patents
Water-soluble quaternary polymer molecular brush anionic dye capturing settling agent and preparation method and application thereof Download PDFInfo
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- 229920000642 polymer Polymers 0.000 title claims abstract description 82
- 125000000129 anionic group Chemical group 0.000 title claims abstract description 43
- 238000002360 preparation method Methods 0.000 title claims abstract description 6
- 239000003795 chemical substances by application Substances 0.000 claims abstract description 39
- 239000002351 wastewater Substances 0.000 claims abstract description 33
- 125000003178 carboxy group Chemical group [H]OC(*)=O 0.000 claims abstract description 29
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 claims abstract description 24
- 239000002243 precursor Substances 0.000 claims abstract description 21
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 21
- GTDPSWPPOUPBNX-UHFFFAOYSA-N ac1mqpva Chemical compound CC12C(=O)OC(=O)C1(C)C1(C)C2(C)C(=O)OC1=O GTDPSWPPOUPBNX-UHFFFAOYSA-N 0.000 claims abstract description 18
- 150000002500 ions Chemical class 0.000 claims abstract description 16
- HRPVXLWXLXDGHG-UHFFFAOYSA-N Acrylamide Chemical compound NC(=O)C=C HRPVXLWXLXDGHG-UHFFFAOYSA-N 0.000 claims abstract description 15
- 229910001385 heavy metal Inorganic materials 0.000 claims abstract description 14
- ZQXSMRAEXCEDJD-UHFFFAOYSA-N n-ethenylformamide Chemical compound C=CNC=O ZQXSMRAEXCEDJD-UHFFFAOYSA-N 0.000 claims abstract description 12
- NQTADLQHYWFPDB-UHFFFAOYSA-N N-Hydroxysuccinimide Chemical compound ON1C(=O)CCC1=O NQTADLQHYWFPDB-UHFFFAOYSA-N 0.000 claims abstract description 8
- 239000003054 catalyst Substances 0.000 claims abstract description 8
- QGJOPFRUJISHPQ-NJFSPNSNSA-N carbon disulfide-14c Chemical compound S=[14C]=S QGJOPFRUJISHPQ-NJFSPNSNSA-N 0.000 claims abstract description 6
- 125000002091 cationic group Chemical group 0.000 claims abstract description 5
- 239000000975 dye Substances 0.000 claims description 67
- 238000004062 sedimentation Methods 0.000 claims description 50
- 239000011734 sodium Substances 0.000 claims description 21
- 229920001002 functional polymer Polymers 0.000 claims description 20
- 229920006317 cationic polymer Polymers 0.000 claims description 18
- 238000006116 polymerization reaction Methods 0.000 claims description 16
- WFDIJRYMOXRFFG-UHFFFAOYSA-N Acetic anhydride Chemical compound CC(=O)OC(C)=O WFDIJRYMOXRFFG-UHFFFAOYSA-N 0.000 claims description 15
- 239000002253 acid Substances 0.000 claims description 13
- 239000003999 initiator Substances 0.000 claims description 13
- 238000000034 method Methods 0.000 claims description 11
- 238000010526 radical polymerization reaction Methods 0.000 claims description 11
- BSKHPKMHTQYZBB-UHFFFAOYSA-N 2-methylpyridine Chemical compound CC1=CC=CC=N1 BSKHPKMHTQYZBB-UHFFFAOYSA-N 0.000 claims description 10
- 238000005917 acylation reaction Methods 0.000 claims description 10
- FCKYPQBAHLOOJQ-UHFFFAOYSA-N Cyclohexane-1,2-diaminetetraacetic acid Chemical compound OC(=O)CN(CC(O)=O)C1CCCCC1N(CC(O)=O)CC(O)=O FCKYPQBAHLOOJQ-UHFFFAOYSA-N 0.000 claims description 8
- 238000003756 stirring Methods 0.000 claims description 8
- -1 carbodiimide iodomethane salt Chemical class 0.000 claims description 7
- 239000002245 particle Substances 0.000 claims description 7
- QGJOPFRUJISHPQ-UHFFFAOYSA-N Carbon disulfide Chemical compound S=C=S QGJOPFRUJISHPQ-UHFFFAOYSA-N 0.000 claims description 6
- VEXZGXHMUGYJMC-UHFFFAOYSA-M Chloride anion Chemical compound [Cl-] VEXZGXHMUGYJMC-UHFFFAOYSA-M 0.000 claims description 6
- 230000010933 acylation Effects 0.000 claims description 5
- 150000001450 anions Chemical class 0.000 claims description 5
- 238000005886 esterification reaction Methods 0.000 claims description 5
- 238000001179 sorption measurement Methods 0.000 claims description 5
- CSNNHWWHGAXBCP-UHFFFAOYSA-L Magnesium sulfate Chemical compound [Mg+2].[O-][S+2]([O-])([O-])[O-] CSNNHWWHGAXBCP-UHFFFAOYSA-L 0.000 claims description 4
- VSCWAEJMTAWNJL-UHFFFAOYSA-K aluminium trichloride Chemical compound Cl[Al](Cl)Cl VSCWAEJMTAWNJL-UHFFFAOYSA-K 0.000 claims description 4
- UXVMQQNJUSDDNG-UHFFFAOYSA-L Calcium chloride Chemical compound [Cl-].[Cl-].[Ca+2] UXVMQQNJUSDDNG-UHFFFAOYSA-L 0.000 claims description 3
- 239000001110 calcium chloride Substances 0.000 claims description 3
- 229910001628 calcium chloride Inorganic materials 0.000 claims description 3
- 229910021645 metal ion Inorganic materials 0.000 claims description 3
- 229910052708 sodium Inorganic materials 0.000 claims description 3
- DGAQECJNVWCQMB-PUAWFVPOSA-M Ilexoside XXIX Chemical compound C[C@@H]1CC[C@@]2(CC[C@@]3(C(=CC[C@H]4[C@]3(CC[C@@H]5[C@@]4(CC[C@@H](C5(C)C)OS(=O)(=O)[O-])C)C)[C@@H]2[C@]1(C)O)C)C(=O)O[C@H]6[C@@H]([C@H]([C@@H]([C@H](O6)CO)O)O)O.[Na+] DGAQECJNVWCQMB-PUAWFVPOSA-M 0.000 claims description 2
- 229910021578 Iron(III) chloride Inorganic materials 0.000 claims description 2
- 229960002089 ferrous chloride Drugs 0.000 claims description 2
- 238000006460 hydrolysis reaction Methods 0.000 claims description 2
- NMCUIPGRVMDVDB-UHFFFAOYSA-L iron dichloride Chemical compound Cl[Fe]Cl NMCUIPGRVMDVDB-UHFFFAOYSA-L 0.000 claims description 2
- RBTARNINKXHZNM-UHFFFAOYSA-K iron trichloride Chemical compound Cl[Fe](Cl)Cl RBTARNINKXHZNM-UHFFFAOYSA-K 0.000 claims description 2
- 238000010550 living polymerization reaction Methods 0.000 claims description 2
- 229910052943 magnesium sulfate Inorganic materials 0.000 claims description 2
- 235000019341 magnesium sulphate Nutrition 0.000 claims description 2
- 230000002194 synthesizing effect Effects 0.000 claims description 2
- 150000001408 amides Chemical class 0.000 claims 1
- DKVNPHBNOWQYFE-UHFFFAOYSA-N carbamodithioic acid Chemical compound NC(S)=S DKVNPHBNOWQYFE-UHFFFAOYSA-N 0.000 claims 1
- 239000013522 chelant Substances 0.000 claims 1
- 239000012990 dithiocarbamate Substances 0.000 claims 1
- 229920002521 macromolecule Polymers 0.000 claims 1
- 125000002496 methyl group Chemical group [H]C([H])([H])* 0.000 claims 1
- 125000001436 propyl group Chemical group [H]C([*])([H])C([H])([H])C([H])([H])[H] 0.000 claims 1
- 229920002554 vinyl polymer Polymers 0.000 claims 1
- 230000015572 biosynthetic process Effects 0.000 abstract description 21
- 238000003786 synthesis reaction Methods 0.000 abstract description 21
- ASYVZGDYOMRIPZ-UHFFFAOYSA-N 3-(ethyliminomethylideneamino)-n,n-dimethylpropan-1-amine;iodomethane Chemical compound IC.CCN=C=NCCCN(C)C ASYVZGDYOMRIPZ-UHFFFAOYSA-N 0.000 abstract description 6
- 238000004043 dyeing Methods 0.000 abstract description 6
- MPNXSZJPSVBLHP-UHFFFAOYSA-N 2-chloro-n-phenylpyridine-3-carboxamide Chemical compound ClC1=NC=CC=C1C(=O)NC1=CC=CC=C1 MPNXSZJPSVBLHP-UHFFFAOYSA-N 0.000 abstract description 3
- 239000002244 precipitate Substances 0.000 abstract description 2
- 239000011248 coating agent Substances 0.000 abstract 1
- 238000000576 coating method Methods 0.000 abstract 1
- 238000007730 finishing process Methods 0.000 abstract 1
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 18
- OKKJLVBELUTLKV-UHFFFAOYSA-N Methanol Chemical compound OC OKKJLVBELUTLKV-UHFFFAOYSA-N 0.000 description 9
- 229910052757 nitrogen Inorganic materials 0.000 description 9
- 239000000701 coagulant Substances 0.000 description 8
- 238000005345 coagulation Methods 0.000 description 7
- 230000015271 coagulation Effects 0.000 description 7
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 description 6
- KRKNYBCHXYNGOX-UHFFFAOYSA-N citric acid Chemical compound OC(=O)CC(O)(C(O)=O)CC(O)=O KRKNYBCHXYNGOX-UHFFFAOYSA-N 0.000 description 6
- RRHXZLALVWBDKH-UHFFFAOYSA-M trimethyl-[2-(2-methylprop-2-enoyloxy)ethyl]azanium;chloride Chemical compound [Cl-].CC(=C)C(=O)OCC[N+](C)(C)C RRHXZLALVWBDKH-UHFFFAOYSA-M 0.000 description 6
- LMDZBCPBFSXMTL-UHFFFAOYSA-N 1-Ethyl-3-(3-dimethylaminopropyl)carbodiimide Substances CCN=C=NCCCN(C)C LMDZBCPBFSXMTL-UHFFFAOYSA-N 0.000 description 5
- 230000000694 effects Effects 0.000 description 5
- OZAIFHULBGXAKX-UHFFFAOYSA-N 2-(2-cyanopropan-2-yldiazenyl)-2-methylpropanenitrile Chemical compound N#CC(C)(C)N=NC(C)(C)C#N OZAIFHULBGXAKX-UHFFFAOYSA-N 0.000 description 4
- 238000010521 absorption reaction Methods 0.000 description 4
- 238000007259 addition reaction Methods 0.000 description 4
- 239000003344 environmental pollutant Substances 0.000 description 4
- 239000000706 filtrate Substances 0.000 description 4
- 231100000719 pollutant Toxicity 0.000 description 4
- 239000004753 textile Substances 0.000 description 4
- SBVKVAIECGDBTC-UHFFFAOYSA-N 4-hydroxy-2-methylidenebutanamide Chemical compound NC(=O)C(=C)CCO SBVKVAIECGDBTC-UHFFFAOYSA-N 0.000 description 3
- 238000005481 NMR spectroscopy Methods 0.000 description 3
- 239000004280 Sodium formate Substances 0.000 description 3
- 238000006243 chemical reaction Methods 0.000 description 3
- 150000001875 compounds Chemical class 0.000 description 3
- 238000005516 engineering process Methods 0.000 description 3
- 125000001495 ethyl group Chemical group [H]C([H])([H])C([H])([H])* 0.000 description 3
- 229920000620 organic polymer Polymers 0.000 description 3
- HLBBKKJFGFRGMU-UHFFFAOYSA-M sodium formate Chemical compound [Na+].[O-]C=O HLBBKKJFGFRGMU-UHFFFAOYSA-M 0.000 description 3
- 235000019254 sodium formate Nutrition 0.000 description 3
- 239000000126 substance Substances 0.000 description 3
- 238000012360 testing method Methods 0.000 description 3
- TWRXJAOTZQYOKJ-UHFFFAOYSA-L Magnesium chloride Chemical compound [Mg+2].[Cl-].[Cl-] TWRXJAOTZQYOKJ-UHFFFAOYSA-L 0.000 description 2
- 238000002306 biochemical method Methods 0.000 description 2
- IQFVPQOLBLOTPF-HKXUKFGYSA-L congo red Chemical compound [Na+].[Na+].C1=CC=CC2=C(N)C(/N=N/C3=CC=C(C=C3)C3=CC=C(C=C3)/N=N/C3=C(C4=CC=CC=C4C(=C3)S([O-])(=O)=O)N)=CC(S([O-])(=O)=O)=C21 IQFVPQOLBLOTPF-HKXUKFGYSA-L 0.000 description 2
- SSJXIUAHEKJCMH-UHFFFAOYSA-N cyclohexane-1,2-diamine Chemical compound NC1CCCCC1N SSJXIUAHEKJCMH-UHFFFAOYSA-N 0.000 description 2
- 238000001914 filtration Methods 0.000 description 2
- 239000008394 flocculating agent Substances 0.000 description 2
- 238000004519 manufacturing process Methods 0.000 description 2
- STZCRXQWRGQSJD-GEEYTBSJSA-M methyl orange Chemical compound [Na+].C1=CC(N(C)C)=CC=C1\N=N\C1=CC=C(S([O-])(=O)=O)C=C1 STZCRXQWRGQSJD-GEEYTBSJSA-M 0.000 description 2
- 229940012189 methyl orange Drugs 0.000 description 2
- CEQFOVLGLXCDCX-WUKNDPDISA-N methyl red Chemical compound C1=CC(N(C)C)=CC=C1\N=N\C1=CC=CC=C1C(O)=O CEQFOVLGLXCDCX-WUKNDPDISA-N 0.000 description 2
- 229920002401 polyacrylamide Polymers 0.000 description 2
- 239000010865 sewage Substances 0.000 description 2
- 238000004065 wastewater treatment Methods 0.000 description 2
- 229910021589 Copper(I) bromide Inorganic materials 0.000 description 1
- AZDRQVAHHNSJOQ-UHFFFAOYSA-N alumane Chemical class [AlH3] AZDRQVAHHNSJOQ-UHFFFAOYSA-N 0.000 description 1
- 238000009388 chemical precipitation Methods 0.000 description 1
- 230000007547 defect Effects 0.000 description 1
- 230000007812 deficiency Effects 0.000 description 1
- 230000008021 deposition Effects 0.000 description 1
- 238000011161 development Methods 0.000 description 1
- 230000009977 dual effect Effects 0.000 description 1
- 238000002848 electrochemical method Methods 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- IOLQWGVDEFWYNP-UHFFFAOYSA-N ethyl 2-bromo-2-methylpropanoate Chemical compound CCOC(=O)C(C)(C)Br IOLQWGVDEFWYNP-UHFFFAOYSA-N 0.000 description 1
- 238000005188 flotation Methods 0.000 description 1
- 239000010842 industrial wastewater Substances 0.000 description 1
- 238000007689 inspection Methods 0.000 description 1
- 159000000014 iron salts Chemical class 0.000 description 1
- 229910001629 magnesium chloride Inorganic materials 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 239000008204 material by function Substances 0.000 description 1
- 230000004048 modification Effects 0.000 description 1
- 238000012986 modification Methods 0.000 description 1
- 239000003973 paint Substances 0.000 description 1
- 238000011197 physicochemical method Methods 0.000 description 1
- 238000001556 precipitation Methods 0.000 description 1
- 238000012545 processing Methods 0.000 description 1
- 239000000047 product Substances 0.000 description 1
- QQONPFPTGQHPMA-UHFFFAOYSA-N propylene Natural products CC=C QQONPFPTGQHPMA-UHFFFAOYSA-N 0.000 description 1
- 238000012827 research and development Methods 0.000 description 1
- 238000000926 separation method Methods 0.000 description 1
- 239000010802 sludge Substances 0.000 description 1
- 238000006467 substitution reaction Methods 0.000 description 1
- 230000002195 synergetic effect Effects 0.000 description 1
- 229920001059 synthetic polymer Polymers 0.000 description 1
- 239000003403 water pollutant Substances 0.000 description 1
- 238000003911 water pollution Methods 0.000 description 1
Classifications
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/52—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
- C02F1/54—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using organic material
- C02F1/56—Macromolecular compounds
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/52—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
- C02F1/5236—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using inorganic agents
- C02F1/5245—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using inorganic agents using basic salts, e.g. of aluminium and iron
-
- C—CHEMISTRY; METALLURGY
- C08—ORGANIC MACROMOLECULAR COMPOUNDS; THEIR PREPARATION OR CHEMICAL WORKING-UP; COMPOSITIONS BASED THEREON
- C08G—MACROMOLECULAR COMPOUNDS OBTAINED OTHERWISE THAN BY REACTIONS ONLY INVOLVING UNSATURATED CARBON-TO-CARBON BONDS
- C08G81/00—Macromolecular compounds obtained by interreacting polymers in the absence of monomers, e.g. block polymers
- C08G81/02—Macromolecular compounds obtained by interreacting polymers in the absence of monomers, e.g. block polymers at least one of the polymers being obtained by reactions involving only carbon-to-carbon unsaturated bonds
- C08G81/021—Block or graft polymers containing only sequences of polymers of C08C or C08F
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/10—Inorganic compounds
- C02F2101/20—Heavy metals or heavy metal compounds
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/30—Organic compounds
- C02F2101/308—Dyes; Colorants; Fluorescent agents
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2103/00—Nature of the water, waste water, sewage or sludge to be treated
- C02F2103/30—Nature of the water, waste water, sewage or sludge to be treated from the textile industry
Landscapes
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Environmental & Geological Engineering (AREA)
- Life Sciences & Earth Sciences (AREA)
- Water Supply & Treatment (AREA)
- Engineering & Computer Science (AREA)
- Hydrology & Water Resources (AREA)
- Inorganic Chemistry (AREA)
- Health & Medical Sciences (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Medicinal Chemistry (AREA)
- Polymers & Plastics (AREA)
- Separation Of Suspended Particles By Flocculating Agents (AREA)
- Addition Polymer Or Copolymer, Post-Treatments, Or Chemical Modifications (AREA)
Abstract
Description
技术领域technical field
本发明属于水处理技术及高分子功能材料领域,具体涉及一种水溶性四元聚合物分子刷阴离子染料捕捉沉降剂及其制备方法及其应用,其主要在染料合成或染整过程中排放出的染料废水或艺术涂料废水中应用,能实现同时除去染料废水的阴离子染料及络合型重金属离子。The invention belongs to the field of water treatment technology and polymer functional materials, and in particular relates to a water-soluble quaternary polymer molecular brush anionic dye capture and sedimentation agent, a preparation method and an application thereof. It can be used in dye wastewater or art paint wastewater, and can simultaneously remove anionic dyes and complex heavy metal ions from dye wastewater.
背景技术Background technique
近些年来,我国每年污水排放量达390多亿吨,其中工业污水占51% ,而染料废水又占总工业废水排放量的35%,而且还以1%的速度在逐年增加。染料废水主要来自于染料合成及染料使用企业,由合成或染整过程中排放出的染料、助剂等组成。随着印染工业的飞速发展,我国是纺织品生产和加工大国,纺织品出口额已多年来列居世界首位,每年的染料生产量达1.5×105吨,其中大约10%~15%的染料会直接随废水排入水体中,染料废水已成为水体重要污染源之一。为加强纺织染整工业水污染控制,2012年,环境保护部和国家质量监督检验检疫总局联合修订发布了《纺织染整工业水污染物排放标准》(GB 4287-2012)。根据新的排放标准,采用传统的处理技术,很多印染企业无法达到新的国家排放标准,出现很多偷排放现象,发生了严重的水体环境污染事件。总体来说,目前的染料废水处理技术还无法达到国家排放标准,急需新材料和新技术的研发解决目前企业排放问题。染料废水具有极强的污染感,且有色水体会影响日光照射,不利于水生生物的生长,一般的生化法很难对其进行处理。染料废水的排放量也很大,而且排放具有间歇性,水质也不稳定,属于难治理废水。In recent years, my country's annual sewage discharge has reached more than 39 billion tons, of which industrial sewage accounts for 51%, and dye wastewater accounts for 35% of the total industrial wastewater discharge, and it is also increasing at a rate of 1% year by year. Dye wastewater mainly comes from dye synthesis and dye use enterprises, and consists of dyes and auxiliaries discharged during synthesis or dyeing and finishing. With the rapid development of the printing and dyeing industry, China is a big country in textile production and processing. The export volume of textiles has ranked first in the world for many years. The annual dye production volume reaches 1.5 × 105 tons, of which about 10% to 15% of the dyes will be directly The dye wastewater has become one of the important pollution sources of the water body when it is discharged into the water body with the wastewater. In order to strengthen the control of water pollution in the textile dyeing and finishing industry, in 2012, the Ministry of Environmental Protection and the General Administration of Quality Supervision, Inspection and Quarantine jointly revised and issued the "Water Pollutant Discharge Standard for Textile Dyeing and Finishing Industry" (GB 4287-2012). According to the new discharge standard and traditional treatment technology, many printing and dyeing enterprises cannot meet the new national discharge standard. In general, the current dye wastewater treatment technology is still unable to meet the national discharge standards, and the research and development of new materials and new technologies is urgently needed to solve the current enterprise discharge problems. Dye wastewater has a strong sense of pollution, and colored water will affect sunlight exposure, which is not conducive to the growth of aquatic organisms, and it is difficult to treat it by general biochemical methods. The discharge of dye wastewater is also very large, and the discharge is intermittent, and the water quality is also unstable, which is difficult to treat wastewater.
传统的废水处理方法有物化法、化学混凝法、物理吸附法、生化法、电化学法等。化学混凝法是在染料废水中加入混凝剂,使污染物形成胶粒,通过混凝沉淀或气浮,从而去除废水中的污染物。混凝沉淀法是实际应用中最广泛的。混凝法能同时去除染料污染物和其他的大分子悬浮污染物。对废水的处理效果主要取决于混凝剂的结构性质。目前使用的混凝剂主要有无机混凝剂和有机高分子混凝剂。无机混凝剂主要以铝盐和铁盐为主,对以胶体或悬浮态存在于废水中的染料有较好的混凝效果,但是对于水溶性染料中分子量较小的,混凝效果则比较差。有机高分子混凝剂分子量大,溶入水中后分散为巨大数量的线性分子,对水中的胶体悬浮粒子的吸附架桥能力强。有机高分子混凝剂性质稳定,残渣少,对pH值要求较宽,其中最有代表性的就是聚丙烯酰胺。但聚丙烯酰胺化学结构较为单一,存在着对染料分子捕捉能力较差,沉降速度较慢,无法处理络合型重金属离子等问题。Traditional wastewater treatment methods include physicochemical method, chemical coagulation method, physical adsorption method, biochemical method, electrochemical method, etc. The chemical coagulation method is to add a coagulant to the dye wastewater to make the pollutants form colloidal particles, and to remove the pollutants in the wastewater through coagulation sedimentation or air flotation. The coagulation sedimentation method is the most widely used in practice. Coagulation can simultaneously remove dye pollutants and other macromolecular suspended pollutants. The treatment effect of wastewater mainly depends on the structural properties of the coagulant. The coagulants currently used mainly include inorganic coagulants and organic polymer coagulants. Inorganic coagulants are mainly aluminum salts and iron salts, which have a good coagulation effect on the dyes that exist in the wastewater in a colloidal or suspended state, but the coagulation effect is relatively small for the water-soluble dyes with smaller molecular weights. Difference. The organic polymer coagulant has a large molecular weight, disperses into a huge number of linear molecules after being dissolved in water, and has strong adsorption and bridging ability to colloidal suspended particles in water. Organic polymer coagulants have stable properties, less residue, and wider pH requirements. The most representative one is polyacrylamide. However, the chemical structure of polyacrylamide is relatively simple, and there are problems such as poor ability to capture dye molecules, slow sedimentation, and inability to deal with complex heavy metal ions.
发明内容SUMMARY OF THE INVENTION
本发明的目的是克服现有技术的不足而提供一种水溶性四元聚合物分子刷阴离子染料捕捉沉降剂及其制备方法及其应用,捕集能力好,沉降速度快,能处理络合型重金属离子,能在数秒内捕获阴离子染料及络合型重金属离子,10秒内快速生长成大的聚集体沉淀,快速实现分离染料。The object of the present invention is to overcome the deficiencies of the prior art and provide a water-soluble quaternary polymer molecular brush anionic dye capture and sedimentation agent and its preparation method and application, which have good capturing ability, fast sedimentation speed, and can handle complex type Heavy metal ions can capture anionic dyes and complex heavy metal ions within a few seconds, quickly grow into large aggregates and precipitate within 10 seconds, and quickly realize the separation of dyes.
为了达到上述目的,本发明的水溶性四元聚合物分子刷阴离子染料捕捉沉降剂的技术方案是这样实现的,其特征在于包括1~10份的聚合物主链聚羟乙基丙烯酰胺(PHEMAA)、20~100份的阳离子型高分子侧链末端含羧基的聚甲基丙烯酰氧乙基三甲基氯化铵(PDMC-COOH)、5~40份的功能高分子侧链前驱体聚合物末端含羧基的聚N-乙烯基甲酰胺(PNVF-COOH)、100~500份的水、1~5份的催化剂即N-羟基琥珀酰亚胺(NHS)、1~5份的1-乙基-3-(3-二甲胺基丙基)碳二亚胺碘甲烷盐(EDC·CH3I)、1~10份的氢氧化钠、1~20份的1,2-环己二胺四乙酸二酐(CDTAD)及1~10份的二硫化碳;以上均为质量份数。In order to achieve the above-mentioned purpose, the technical scheme of the water-soluble quaternary polymer molecular brush anionic dye capture and sedimentation agent of the present invention is realized in this way, which is characterized in that it comprises 1-10 parts of the polymer main chain polyhydroxyethyl acrylamide (PHEMAA ), 20-100 parts of polymethacryloyloxyethyl trimethyl ammonium chloride (PDMC-COOH) containing carboxyl group at the end of cationic polymer side chain, 5-40 parts of functional polymer side chain precursor polymerization poly-N-vinylformamide (PNVF-COOH) with carboxyl group at the end of the product, 100-500 parts of water, 1-5 parts of catalyst, namely N-hydroxysuccinimide (NHS), 1-5 parts of 1- Ethyl-3-(3-dimethylaminopropyl)carbodiimide iodomethane salt (EDC·CH 3 I), 1-10 parts of sodium hydroxide, 1-20 parts of 1,2-cyclohexane Diaminetetraacetic dianhydride (CDTAD) and 1-10 parts of carbon disulfide; the above are all parts by mass.
在本技术方案中,所述聚合物主链聚羟乙基丙烯酰胺(PHEMAA)通过普通自由基聚合或可控活性聚合法合成PHEMAA聚合物主链;In this technical solution, the polymer main chain polyhydroxyethyl acrylamide (PHEMAA) is synthesized by ordinary free radical polymerization or controllable living polymerization method to synthesize the PHEMAA polymer main chain;
所述阳离子型高分子侧链PDMC-COOH主要采用偶氮二氰基戊酸为引发剂通过普通自由基聚合法合成末端含羧基的聚甲基丙烯酰氧乙基三甲基氯化铵(PDMC-COOH)聚合物;The cationic polymer side chain PDMC-COOH mainly uses azodicyanovaleric acid as the initiator to synthesize polymethacryloyloxyethyltrimethylammonium chloride (PDMC) containing carboxyl groups at the end by ordinary free radical polymerization method. -COOH) polymer;
所述功能高分子侧链前驱体聚合物PNVF-COOH主要采用偶氮二氰基戊酸为引发剂通过普通自由基聚合合成末端含羧基的聚N-乙烯基甲酰胺(PNVF-COOH)聚合物;The functional polymer side chain precursor polymer PNVF-COOH mainly uses azodicyanovaleric acid as an initiator to synthesize poly-N-vinylformamide (PNVF-COOH) polymer containing carboxyl groups at the end by ordinary free radical polymerization ;
所述1,2-环己二胺四乙酸二酐(CDTAD)的合成方法是:将5~20份的1,2-环己二胺四乙酸和5~20份乙酸酐溶解于10~30份的2-甲基吡啶中,控制于50~70℃,反应20~40小时,获得1,2-环己二胺四乙酸二酐。The method for synthesizing the 1,2-cyclohexanediaminetetraacetic acid dianhydride (CDTAD) is: dissolving 5-20 parts of 1,2-cyclohexanediaminetetraacetic acid and 5-20 parts of acetic anhydride in 10-30 parts of Part of 2-picoline is controlled at 50 to 70° C., and the reaction is performed for 20 to 40 hours to obtain 1,2-cyclohexanediaminetetraacetic dianhydride.
为了达到上述目的,本发明的水溶性四元聚合物分子刷阴离子染料捕捉沉降剂的制备方法的技术方案是这样实现的,其特征在于将1~10份的聚合物主链聚羟乙基丙烯酰胺(PHEMAA)、20~100份的阳离子型高分子侧链末端含羧基的聚甲基丙烯酰氧乙基三甲基氯化铵(PDMC-COOH)和5~40份的功能高分子侧链前驱体聚合物末端含羧基的聚N-乙烯基甲酰胺(PNVF-COOH)混合溶于100~500份的水里,加入1~5份的催化剂即N-羟基琥珀酰亚胺(NHS)和1~5份的1-乙基-3-(3-二甲胺基丙基)碳二亚胺碘甲烷盐(EDC·CH3I),控温于50~80℃,进行酯化反应10~70小时,获得聚羟乙基丙烯酰胺-接枝-(聚甲基丙烯酰氧乙基三甲基氯化铵-无规-聚N-乙烯基甲酰胺)(PHEMAA-g-(PDMC-r-PNVF));再加入1~10份的氢氧化钠,控温于50~80℃,进行水解反应12~48小时,获得聚羟乙基丙烯酰胺-接枝-(聚甲基丙烯酰氧乙基三甲基氯化铵-无规-聚乙烯胺)(PHEMAA-g-(PDMC-r-PVA));再加入1~20份的1,2-环己二胺四乙酸二酐(CDTAD),进行酰基化反应5~24小时,酰化度范围控制为60~99%,获得聚羟乙基丙烯酰胺-接枝-(聚甲基丙烯酰氧乙基三甲基氯化铵-无规-聚乙烯胺基环己二胺四乙酸钠-无规-聚乙烯胺)(PHEMAA-g-(PDMC-r-PVACDTANa-r-PVA));再加入1~10份的二硫化碳,控温于20~40℃,进行加成反应1~3小时,获得聚羟乙基丙烯酰胺-接枝-(聚甲基丙烯酰氧乙基三甲基氯化铵-无规-聚乙烯胺基环己二胺四乙酸钠-无规-聚乙烯胺基二硫代氨基甲酸钠)(PHEMAA-g-(PDMC-r-PVACDTANa-r-PVACS2Na))即水溶性四元聚合物分子刷阴离子染料捕捉沉降剂;以上均为质量份数。In order to achieve the above purpose, the technical scheme of the water-soluble quaternary polymer molecular brush anionic dye capture and sedimentation agent preparation method of the present invention is realized in this way, which is characterized in that 1-10 parts of the polymer main chain polyhydroxyethyl propylene Amide (PHEMAA), 20-100 parts of cationic polymer side chain end containing carboxyl polymethacryloyloxyethyl trimethyl ammonium chloride (PDMC-COOH) and 5-40 parts of functional polymer side chain The poly-N-vinylformamide (PNVF-COOH) containing carboxyl groups at the end of the precursor polymer is mixed and dissolved in 100-500 parts of water, and 1-5 parts of the catalyst, namely N-hydroxysuccinimide (NHS) and 1-5 parts of 1-ethyl-3-(3-dimethylaminopropyl) carbodiimide iodomethane salt (EDC·CH 3 I), temperature-controlled at 50-80 ℃, carry out esterification reaction for 10 ~70 hours to obtain polyhydroxyethylacrylamide-graft-(polymethacryloyloxyethyltrimethylammonium chloride-random-polyN-vinylformamide) (PHEMAA-g-(PDMC- r-PNVF)); then add 1-10 parts of sodium hydroxide, control the temperature at 50-80 ° C, and carry out a hydrolysis reaction for 12-48 hours to obtain polyhydroxyethyl acrylamide-graft-(polymethacryloyl Oxyethyltrimethylammonium chloride-random-polyvinylamine) (PHEMAA-g-(PDMC-r-PVA)); then add 1 to 20 parts of 1,2-cyclohexanediaminetetraacetic acid dianhydride (CDTAD), carry out acylation reaction for 5 to 24 hours, and the acylation degree range is controlled to be 60 to 99% to obtain polyhydroxyethylacrylamide-graft-(polymethacryloyloxyethyltrimethylammonium chloride) -random-polyvinylaminocyclohexanediaminetetraacetate-random-polyvinylamine) (PHEMAA-g-(PDMC-r-PVACDTANa-r-PVA)); then add 1-10 parts of carbon disulfide, The temperature is controlled at 20~40℃, and the addition reaction is carried out for 1~3 hours to obtain polyhydroxyethylacrylamide-graft-(polymethacryloyloxyethyltrimethylammonium chloride-random-polyvinylamine (PHEMAA-g-(PDMC-r-PVACDTANa-r-PVACS 2 Na)) is a water-soluble quaternary polymer molecular brush Anionic dye capture sedimentation agent; the above are all parts by mass.
在本技术方案中,所述聚羟乙基丙烯酰胺(PHEMAA)的聚合度为10~200,所述阳离子型高分子侧链PDMC-COOH及功能高分子侧链前驱体聚合物PNVF-COOH的聚合度均为10~200,阳离子型高分子侧链PDMC的接枝率为1~70%、螯合型高分子侧链PVACDTANa的接枝率1~20%及助沉降高分子侧链PVACS2Na的接枝率为1~5%。In this technical solution, the degree of polymerization of the polyhydroxyethyl acrylamide (PHEMAA) is 10-200, and the cationic polymer side chain PDMC-COOH and the functional polymer side chain precursor polymer PNVF-COOH have The degree of polymerization is 10-200, the grafting rate of the cationic polymer side chain PDMC is 1-70%, the grafting rate of the chelating polymer side chain PVACDTANa is 1-20%, and the assisted sedimentation polymer side chain PVACS 2 The grafting ratio of Na is 1-5%.
为了达到上述目的,本发明的水溶性四元聚合物分子刷阴离子染料捕捉沉降剂的应用的技术方案是这样实现的,其特征在于将0.1~1份的水溶性四元聚合物分子刷阴离子染料捕捉沉降剂加入到100~1000份的废水中,常温下搅拌1~5分钟,调节pH至2~5,废水中阴离子染料分子与水溶性四元聚合物分子刷阴离子染料捕捉沉降剂的阳离子型侧链PDMC发生静电吸附,废水中重金属离子与水溶性四元聚合物分子刷阴离子染料捕捉沉降剂的螯合型侧链PVACDTANa发生螯合吸附,再加入0.01~0.1份的助沉降剂,常温下搅拌1分钟,助沉降剂的金属离子快速与水溶性四元聚合物分子刷阴离子染料捕捉沉降剂的助沉降侧链PVACS2Na发生化学沉淀反应,10秒内生成粒径大于100 μm的絮体沉淀,可快速实现去除废水中的阴离子染料及络合型重金属离子,出水无色,达到国家排放标准,以上均为质量份数。In order to achieve the above-mentioned purpose, the technical scheme of the application of the water-soluble quaternary polymer molecular brush anionic dye capture and sedimentation agent of the present invention is realized in this way, which is characterized in that 0.1-1 part of the water-soluble quaternary polymer molecular brush an anionic dye The capture and sedimentation agent is added to 100-1000 parts of wastewater, stirred for 1 to 5 minutes at room temperature, and the pH is adjusted to 2 to 5. The anionic dye molecules and water-soluble quaternary polymer molecules in the wastewater are brushed with the cationic type of the anionic dye capture and sedimentation agent. The side chain PDMC is electrostatically adsorbed, and the heavy metal ions in the wastewater and the water-soluble quaternary polymer molecular brush anionic dye capture the chelating side chain PVACDTANa of the sedimentation agent. Stir for 1 minute, the metal ions of the sedimentation aid quickly react with the water-soluble quaternary polymer molecular brush anionic dye to capture the side chain PVACS 2 Na of the sedimentation aid, and the flocs with a particle size greater than 100 μm are formed within 10 seconds. Precipitation can quickly remove anionic dyes and complex heavy metal ions in wastewater. The effluent is colorless and meets the national discharge standard. The above are all parts by mass.
在本技术方案中,所述助沉降剂为氯化钙、硫酸镁、氯化亚铁、三氯化铁、三氯化铝的一种或两种以上的任意组合。In this technical scheme, the settling aid is any combination of one or more of calcium chloride, magnesium sulfate, ferrous chloride, ferric chloride, and aluminum trichloride.
本发明与现有技术相比,具有如下的优点及效果:Compared with the prior art, the present invention has the following advantages and effects:
1、本发明解决了传统合成类高分子染料絮凝剂结构单一及捕捉性能差的缺陷,本发明含有三种不同功能的高分子侧链,阳离子型高分子侧链PDMC对阴离子染料具有很好的静电吸附能力,螯合型侧链PVACDTANa对重金属离子发生螯合吸附,在助沉降高分子侧链PVACS2Na的协同作用下,PVACS2Na高分子侧链与助沉降剂金属离子快速发生化学沉淀反应,达到高效捕捉及快速沉降功能;1. The present invention solves the defects of single structure and poor capturing performance of traditional synthetic polymer dye flocculants. The present invention contains three kinds of polymer side chains with different functions, and the cationic polymer side chain PDMC has a good effect on anionic dyes. Electrostatic adsorption capacity, chelating side chain PVACDTANa chelates and adsorbs heavy metal ions, under the synergistic effect of PVACS 2 Na polymer side chain PVACS 2 Na, the polymer side chain of PVACS 2 Na and the metal ions of the deposition aid quickly undergo chemical precipitation reaction to achieve efficient capture and rapid sedimentation;
2、本发明具有沉降速度的技术优势,能在少量助沉降剂下,发生沉淀反应,快速生成大的聚集体,产生的污泥量少。2. The present invention has the technical advantage of settling speed, and can cause a settling reaction with a small amount of a settling aid, quickly generate large aggregates, and produce less sludge.
3、本发明具有双重功能,能同时捕捉阴离子染料及络合型重金属离子,解决了传统絮凝剂无法处理染料废水中络合型重金属离子问题。3. The present invention has dual functions, which can simultaneously capture anionic dyes and complex heavy metal ions, and solves the problem that traditional flocculants cannot treat complex heavy metal ions in dye wastewater.
具体实施方式Detailed ways
下面结合实施例对本发明作进一步详细的描述,但本发明的实施方式不限于此。以下实施例中所涉及的份数均是质量份数。The present invention will be described in further detail below with reference to the examples, but the embodiments of the present invention are not limited thereto. The parts involved in the following examples are all parts by mass.
实施例一Example 1
其是一种水溶性四元聚合物分子刷阴离子染料捕捉沉降剂,由以下步骤制备得到:It is a water-soluble quaternary polymer molecular brush anionic dye capture sedimentation agent, which is prepared by the following steps:
步骤一 PHEMAA聚合物主链的合成Step 1 Synthesis of PHEMAA polymer backbone
取2份的偶氮二异丁腈引发剂、50份的羟乙基丙烯酰胺(HEMAA)、400的份甲醇,在氮气保护下75℃进行聚合反应1小时,得到聚合度(DP)为20的聚羟乙基丙烯酰胺(PHEMAA);Take 2 parts of azobisisobutyronitrile initiator, 50 parts of hydroxyethyl acrylamide (HEMAA) and 400 parts of methanol, carry out polymerization reaction at 75°C for 1 hour under nitrogen protection, and obtain a degree of polymerization (DP) of 20 of polyhydroxyethyl acrylamide (PHEMAA);
步骤二 阳离子型高分子侧链PDMC-COOH和功能高分子侧链前驱体聚合物PNVF-COOH的合成Step 2 Synthesis of cationic polymer side chain PDMC-COOH and functional polymer side chain precursor polymer PNVF-COOH
阳离子型高分子侧链PDMC-COOH的合成:取2份的偶氮二氰基戊酸引发剂、150份的甲基丙烯酰氧乙基三甲基氯化铵(DMC)和50份的水,在氮气保护下70℃进行自由基聚合反应16小时,得到聚合度(DP)为180的PDMC-COOH;Synthesis of cationic polymer side chain PDMC-COOH: take 2 parts of azodicyanovaleric acid initiator, 150 parts of methacryloyloxyethyltrimethylammonium chloride (DMC) and 50 parts of water , carried out radical polymerization at 70 °C for 16 hours under nitrogen protection to obtain PDMC-COOH with a degree of polymerization (DP) of 180;
功能高分子侧链前驱体聚合物PNVF-COOH的合成:取2份的偶氮二氰基戊酸引发剂、100份的N-乙烯基甲酰胺(NVF)和40份的水,在氮气保护下70℃进行自由基聚合反应13小时,得到聚合度(DP)为190的PNVF-COOH;Synthesis of functional polymer side chain precursor polymer PNVF-COOH: take 2 parts of azodicyanovaleric acid initiator, 100 parts of N-vinylformamide (NVF) and 40 parts of water, under nitrogen protection Perform free radical polymerization at 70°C for 13 hours to obtain PNVF-COOH with a degree of polymerization (DP) of 190;
步骤三 合成1,2-环己二胺四乙酸二酐(CDTAD)Step 3 Synthesis of 1,2-cyclohexanediaminetetraacetic dianhydride (CDTAD)
将9份的1,2-环己二胺四乙酸和9份的乙酸酐溶解于10份的2-甲基吡啶中,控制于50℃,反应20小时,获得1,2-环己二胺四乙酸二酐;9 parts of 1,2-cyclohexanediaminetetraacetic acid and 9 parts of acetic anhydride were dissolved in 10 parts of 2-picoline, controlled at 50°C, and reacted for 20 hours to obtain 1,2-cyclohexanediamine tetraacetic dianhydride;
步骤四 合成PHEMAA-g-(PDMC-r-PVACDTANa-r-PVACS2Na)Step 4 Synthesis of PHEMAA-g-(PDMC-r-PVACDTANa-r-PVACS 2 Na)
将步骤一中所得到的1份的聚羟乙基丙烯酰胺(PHEMAA)与步骤二中所得到的20份的阳离子型高分子侧链PDMC-COOH和10份的功能高分子侧链前驱体聚合物PNVF-COOH混合溶于100份的水里,加入1份的催化剂即N-羟基琥珀酰亚胺(NHS)和1份的1-乙基-3-(3-二甲胺基丙基)碳二亚胺碘甲烷盐(EDC·CH3I),控温于50℃,进行酯化反应70小时,获得聚羟乙基丙烯酰胺-接枝-(聚甲基丙烯酰氧乙基三甲基氯化铵-无规-聚N-乙烯基甲酰胺)(PHEMAA-g-(PDMC-r-PNVF));再加1份的氢氧化钠,控温于80℃,对接枝于聚合物主链的功能高分子侧链前驱体聚合物(PNVF),进行水解反应48小时,获得聚羟乙基丙烯酰胺-接枝-(聚甲基丙烯酰氧乙基三甲基氯化铵-无规-聚乙烯胺)(PHEMAA-g-(PDMC-r-PVA));再加入步骤三中合成的8份的1,2-环己二胺四乙酸二酐(CDTAD),酰基化反应24小时,酰化度为80%,获得聚羟乙基丙烯酰胺-接枝-(聚甲基丙烯酰氧乙基三甲基氯化铵-无规-聚乙烯胺基环己二胺四乙酸钠-无规-聚乙烯胺)(PHEMAA-g-(PDMC-r-PVACDTANa-r-PVA));再加入2份的二硫化碳,控温于40℃,进行加成反应1小时,获得聚羟乙基丙烯酰胺-接枝-(聚甲基丙烯酰氧乙基三甲基氯化铵-无规-聚乙烯胺基环己二胺四乙酸钠-无规-聚乙烯胺基二硫代氨基甲酸钠)(PHEMAA-g-(PDMC-r-PVACDTANa-r-PVACS2Na))即水溶性四元聚合物分子刷阴离子染料捕捉沉降剂。采用元素分析仪及核磁共振仪分别测定PDMC、 PVACDTANa和PVACS2Na侧链的接枝率分别为18%、8%和2%。Polymerize 1 part of polyhydroxyethyl acrylamide (PHEMAA) obtained in step 1 with 20 parts of cationic polymer side chain PDMC-COOH and 10 parts of functional polymer side chain precursor obtained in step 2 The compound PNVF-COOH was mixed and dissolved in 100 parts of water, and 1 part of the catalyst was N-hydroxysuccinimide (NHS) and 1 part of 1-ethyl-3-(3-dimethylaminopropyl) Carbodiimide methyl iodide (EDC·CH 3 I), the temperature was controlled at 50 ° C, and the esterification reaction was carried out for 70 hours to obtain polyhydroxyethyl acrylamide-grafted-(polymethacryloyloxyethyl trimethylene ammonium chloride-random-polyN-vinylformamide) (PHEMAA-g-(PDMC-r-PNVF)); add 1 part of sodium hydroxide, control the temperature at 80 ° C, and graft on the polymer The functional polymer side chain precursor polymer (PNVF) of the main chain was hydrolyzed for 48 hours to obtain polyhydroxyethylacrylamide-graft-(polymethacryloyloxyethyltrimethylammonium chloride- Random-polyvinylamine) (PHEMAA-g-(PDMC-r-PVA)); then add 8 parts of 1,2-cyclohexanediaminetetraacetic dianhydride (CDTAD) synthesized in step 3, acylation reaction 24 hours, the degree of acylation is 80%, to obtain polyhydroxyethyl acrylamide-graft-(polymethacryloyloxyethyltrimethylammonium chloride-random-polyvinylaminocyclohexanediaminetetraacetic acid Sodium-random-polyvinylamine) (PHEMAA-g-(PDMC-r-PVACDTANa-r-PVA)); then add 2 parts of carbon disulfide, control the temperature at 40 ° C, and carry out an addition reaction for 1 hour to obtain polyhydroxy Ethyl acrylamide-graft-(polymethacryloyloxyethyltrimethylammonium chloride-random-polyvinylaminocyclohexanediaminetetraacetate-sodium-random-polyvinylaminodithioamino Sodium formate) (PHEMAA-g-(PDMC-r-PVACDTANa-r-PVACS 2 Na)) is a water-soluble quaternary polymer molecular brush anionic dye capture sedimentation agent. The grafting rates of PDMC, PVACDTANa and PVACS 2 Na side chains were determined by elemental analyzer and nuclear magnetic resonance analyzer, and they were 18%, 8% and 2%, respectively.
在本实施例中,水溶性四元聚合物分子刷阴离子染料捕捉沉降剂的应用In this embodiment, the application of water-soluble quaternary polymer molecular brush anionic dye capture sedimentation agent
取本实施例的水溶性四元聚合物分子刷阴离子染料捕捉沉降剂做染料废水测试,取100份的含刚果红100 mg/L废水,添加0.1份的水溶性四元聚合物分子刷阴离子染料捕捉沉降剂,常温下搅拌1分钟,采用0.1 mol/L盐酸调节废水pH值到2.0,再加入0.01份的助沉降剂氯化钙,常温下搅拌1分钟,9秒内生成粒径大于130 μm的絮体沉淀。过滤,采用紫外吸收分光光度计测定滤液中刚果红浓度为0.04 mg/L,脱除效率大于99%。Take the water-soluble quaternary polymer molecular brush anionic dye capture and sedimentation agent of this embodiment for dye wastewater test, take 100 parts of wastewater containing 100 mg/L Congo red, add 0.1 part of water-soluble quaternary polymer molecular brush anionic dye Capture the sedimentation agent, stir at room temperature for 1 minute, use 0.1 mol/L hydrochloric acid to adjust the pH value of the wastewater to 2.0, then add 0.01 part of calcium chloride as a sedimentation aid, stir at room temperature for 1 minute, and generate a particle size greater than 130 μm within 9 seconds of floc sedimentation. After filtration, the concentration of Congo red in the filtrate was determined by ultraviolet absorption spectrophotometer to be 0.04 mg/L, and the removal efficiency was greater than 99%.
实施例二Embodiment 2
其一种水溶性四元聚合物分子刷阴离子染料捕捉沉降剂,由以下步骤制备得到:A water-soluble quaternary polymer molecular brush anionic dye capture sedimentation agent is prepared by the following steps:
步骤一 PHEMAA聚合物主链的合成Step 1 Synthesis of PHEMAA polymer backbone
取1份的偶氮二异丁腈引发剂、400份的羟乙基丙烯酰胺(HEMAA)、40的份甲醇,在氮气保护下75℃进行聚合反应1小时,得到聚合度(DP)为190的聚羟乙基丙烯酰胺(PHEMAA);Take 1 part of azobisisobutyronitrile initiator, 400 parts of hydroxyethyl acrylamide (HEMAA) and 40 parts of methanol, carry out polymerization reaction at 75°C for 1 hour under nitrogen protection, and obtain a degree of polymerization (DP) of 190 of polyhydroxyethyl acrylamide (PHEMAA);
步骤二 阳离子型高分子侧链PDMC-COOH和功能高分子侧链前驱体聚合物PNVF-COOH的合成Step 2 Synthesis of cationic polymer side chain PDMC-COOH and functional polymer side chain precursor polymer PNVF-COOH
阳离子型高分子侧链PDMC-COOH的合成:取1份的偶氮二氰基戊酸引发剂、300份的甲基丙烯酰氧乙基三甲基氯化铵(DMC)和200份的水,在氮气保护下70℃进行自由基聚合反应8小时,得到聚合度(DP)为110的PDMC-COOH;Synthesis of cationic polymer side chain PDMC-COOH: take 1 part of azodicyanovaleric acid initiator, 300 parts of methacryloyloxyethyltrimethylammonium chloride (DMC) and 200 parts of water , carried out radical polymerization at 70 °C for 8 hours under nitrogen protection to obtain PDMC-COOH with a degree of polymerization (DP) of 110;
功能高分子侧链前驱体聚合物PNVF-COOH的合成:取1份的偶氮二氰基戊酸引发剂、300份的N-乙烯基甲酰胺(NVF)和100份的水,在氮气保护下65℃进行自由基聚合反应5小时,得到聚合度(DP)为130的PNVF-COOH;Synthesis of functional polymer side chain precursor polymer PNVF-COOH: take 1 part of azodicyanovaleric acid initiator, 300 parts of N-vinylformamide (NVF) and 100 parts of water, under nitrogen protection Perform free radical polymerization at 65°C for 5 hours to obtain PNVF-COOH with a degree of polymerization (DP) of 130;
步骤三 合成1,2-环己二胺四乙酸二酐(CDTAD)Step 3 Synthesis of 1,2-cyclohexanediaminetetraacetic dianhydride (CDTAD)
将15份的1,2-环己二胺四乙酸和15份乙酸酐溶解于20份的2-甲基吡啶中,控制于60℃,反应30小时,获得1,2-环己二胺四乙酸二酐;15 parts of 1,2-cyclohexanediaminetetraacetic acid and 15 parts of acetic anhydride were dissolved in 20 parts of 2-picoline, controlled at 60°C, and reacted for 30 hours to obtain 1,2-cyclohexanediaminetetramine Acetic dianhydride;
步骤四 合成PHEMAA-g-(PDMC-r-PVACDTANa-r-PVACS2Na)Step 4 Synthesis of PHEMAA-g-(PDMC-r-PVACDTANa-r-PVACS 2 Na)
将步骤一中所得到的2份的聚羟乙基丙烯酰胺(PHEMAA)与步骤二中所得到的50份的阳离子型高分子侧链PDMC-COOH和20份的功能高分子侧链前驱体聚合物PNVF-COOH混合溶于300份的水里,加入4份的催化剂即N-羟基琥珀酰亚胺(NHS)和4份的1-乙基-3-(3-二甲胺基丙基)碳二亚胺碘甲烷盐(EDC·CH3I),控温于60℃,进行酯化反应40小时,获得聚羟乙基丙烯酰胺-接枝-(聚甲基丙烯酰氧乙基三甲基氯化铵-无规-聚N-乙烯基甲酰胺)(PHEMAA-g-(PDMC-r-PNVF));再加5份的氢氧化钠,控温于70℃,对接枝于聚合物主链的功能高分子侧链前驱体聚合物(PNVF),进行水解反应36小时,获得聚羟乙基丙烯酰胺-接枝-(聚甲基丙烯酰氧乙基三甲基氯化铵-无规-聚乙烯胺)(PHEMAA-g-(PDMC-r-PVA));再加入步骤三中合成的15份的1,2-环己二胺四乙酸二酐(CDTAD),酰基化反应12小时,酰化度为83%,获得聚羟乙基丙烯酰胺-接枝-(聚甲基丙烯酰氧乙基三甲基氯化铵-无规-聚乙烯胺基环己二胺四乙酸钠-无规-聚乙烯胺)(PHEMAA-g-(PDMC-r-PVACDTANa-r-PVA));再加入6份的二硫化碳,控温于30℃,进行加成反应2小时,获得聚羟乙基丙烯酰胺-接枝-(聚甲基丙烯酰氧乙基三甲基氯化铵-无规-聚乙烯胺基环己二胺四乙酸钠-无规-聚乙烯胺基二硫代氨基甲酸钠)(PHEMAA-g-(PDMC-r-PVACDTANa-r-PVACS2Na)) 即水溶性四元聚合物分子刷阴离子染料捕捉沉降剂。采用元素分析仪及核磁共振仪分别测定PDMC、 PVACDTANa和PVACS2Na侧链的接枝率分别为65%、19%和4%。Polymerize 2 parts of polyhydroxyethyl acrylamide (PHEMAA) obtained in step 1 with 50 parts of cationic polymer side chain PDMC-COOH and 20 parts of functional polymer side chain precursor obtained in step 2 The compound PNVF-COOH was mixed and dissolved in 300 parts of water, and 4 parts of catalyst, namely N-hydroxysuccinimide (NHS) and 4 parts of 1-ethyl-3-(3-dimethylaminopropyl) Carbodiimide methyl iodide salt (EDC·CH 3 I), the temperature was controlled at 60 ° C, and the esterification reaction was carried out for 40 hours to obtain polyhydroxyethyl acrylamide-grafted-(polymethacryloyloxyethyl trimethylene ammonium chloride-random-polyN-vinylformamide) (PHEMAA-g-(PDMC-r-PNVF)); add 5 parts of sodium hydroxide, control the temperature at 70 ° C, and graft on the polymer The functional polymer side chain precursor polymer (PNVF) of the main chain was hydrolyzed for 36 hours to obtain polyhydroxyethylacrylamide-graft-(polymethacryloyloxyethyltrimethylammonium chloride- Random-polyvinylamine) (PHEMAA-g-(PDMC-r-PVA)); then add 15 parts of 1,2-cyclohexanediaminetetraacetic dianhydride (CDTAD) synthesized in step 3, acylation reaction 12 hours, the degree of acylation was 83%, and polyhydroxyethylacrylamide-grafted-(polymethacryloyloxyethyltrimethylammonium chloride-random-polyvinylaminocyclohexanediaminetetraacetic acid was obtained Sodium-random-polyvinylamine) (PHEMAA-g-(PDMC-r-PVACDTANa-r-PVA)); then add 6 parts of carbon disulfide, control the temperature at 30 ° C, and carry out an addition reaction for 2 hours to obtain polyhydroxy Ethyl acrylamide-graft-(polymethacryloyloxyethyltrimethylammonium chloride-random-polyvinylaminocyclohexanediaminetetraacetate-sodium-random-polyvinylaminodithioamino Sodium formate) (PHEMAA-g-(PDMC-r-PVACDTANa-r-PVACS 2 Na)) is a water-soluble quaternary polymer molecular brush anionic dye capture sedimentation agent. The grafting rates of PDMC, PVACDTANa and PVACS 2 Na side chains were determined by elemental analyzer and nuclear magnetic resonance analyzer, and they were 65%, 19% and 4%, respectively.
在本实施例中,水溶性四元聚合物分子刷阴离子染料捕捉沉降剂的应用In this embodiment, the application of water-soluble quaternary polymer molecular brush anionic dye capture sedimentation agent
取本实施例的水溶性四元聚合物分子刷阴离子染料捕捉沉降剂做染料废水测试,取500份的含甲基红100 mg/L、Cu2+ 离子3 mg/L和柠檬酸0.2 mg/L废水,添加0.5份的水溶性四元聚合物分子刷阴离子染料捕捉沉降剂,常温下搅拌3分钟,采用0.1 mol/L盐酸调节废水pH值到3.0,再加入0.05份的助沉降剂氯化镁,常温下搅拌1分钟,7秒内生成粒径大于180 μm的絮体沉淀。过滤,采用紫外吸收分光光度计测定滤液中甲基红浓度为0.08 mg/L,采用原子吸收分光光度计测定滤液中Cu2+浓度为0.02 mg/L,脱除效率大于99%。Take the water-soluble quaternary polymer molecular brush anionic dye capture and sedimentation agent of this embodiment for dye wastewater test, take 500 parts containing methyl red 100 mg/L, Cu 2+ ions 3 mg/L and citric acid 0.2 mg/L L wastewater, add 0.5 part of water-soluble quaternary polymer molecular brush anion dye to capture sedimentation agent, stir at room temperature for 3 minutes, use 0.1 mol/L hydrochloric acid to adjust the pH value of wastewater to 3.0, and then add 0.05 part of magnesium chloride as a sedimentation aid, Stir for 1 minute at room temperature, and within 7 seconds, flocs with a particle size larger than 180 μm are formed. After filtration, the concentration of methyl red in the filtrate was determined by ultraviolet absorption spectrophotometer to be 0.08 mg/L, and the concentration of Cu 2+ in the filtrate was determined by atomic absorption spectrophotometer to be 0.02 mg/L, and the removal efficiency was greater than 99%.
实施例三Embodiment 3
其一种水溶性四元聚合物分子刷阴离子染料捕捉沉降剂,由以下步骤制备得到:A water-soluble quaternary polymer molecular brush anionic dye capture sedimentation agent is prepared by the following steps:
步骤一 PHEMAA聚合物主链的合成Step 1 Synthesis of PHEMAA polymer backbone
取2份的2-溴异丁酸乙酯引发剂、3份CuBr及3份的4,4-联2-甲基吡啶(BPy)、200份的羟乙基丙烯酰胺(HEMAA)、200的份甲醇,在氮气保护下50℃进行聚合反应3小时,得到聚合度(DP)为100的聚羟乙基丙烯酰胺(PHEMAA);Take 2 parts of ethyl 2-bromoisobutyrate initiator, 3 parts of CuBr and 3 parts of 4,4-bi-2-methylpyridine (BPy), 200 parts of hydroxyethyl acrylamide (HEMAA), 200 parts of Parts of methanol were polymerized at 50 °C for 3 hours under nitrogen protection to obtain polyhydroxyethyl acrylamide (PHEMAA) with a degree of polymerization (DP) of 100;
步骤二 阳离子型高分子侧链PDMC-COOH和功能高分子侧链前驱体聚合物PNVF-COOH的合成Step 2 Synthesis of cationic polymer side chain PDMC-COOH and functional polymer side chain precursor polymer PNVF-COOH
阳离子型高分子侧链PDMC-COOH的合成:取2份的偶氮二氰基戊酸引发剂、100份的甲基丙烯酰氧乙基三甲基氯化铵(DMC)和100份的水,在氮气保护下40℃进行自由基聚合反应2小时,得到聚合度(DP)为60的PDMC-COOH;Synthesis of cationic polymer side chain PDMC-COOH: take 2 parts of azodicyanovaleric acid initiator, 100 parts of methacryloyloxyethyltrimethylammonium chloride (DMC) and 100 parts of water , carried out radical polymerization at 40 °C for 2 hours under nitrogen protection to obtain PDMC-COOH with a degree of polymerization (DP) of 60;
功能高分子侧链前驱体聚合物PNVF-COOH的合成:取3份的偶氮二氰基戊酸引发剂、200份的N-乙烯基甲酰胺(NVF)和200份的水,在氮气保护下45℃进行自由基聚合反应7小时,得到聚合度(DP)为70的PNVF-COOH;Synthesis of functional polymer side chain precursor polymer PNVF-COOH: take 3 parts of azodicyanovaleric acid initiator, 200 parts of N-vinylformamide (NVF) and 200 parts of water, under nitrogen protection Radical polymerization was carried out at 45°C for 7 hours to obtain PNVF-COOH with a degree of polymerization (DP) of 70;
步骤三 合成1,2-环己二胺四乙酸二酐(CDTAD)Step 3 Synthesis of 1,2-cyclohexanediaminetetraacetic dianhydride (CDTAD)
将20份的1,2-环己二胺四乙酸和20份的乙酸酐溶解于30份的2-甲基吡啶中,控制于70℃,反应40小时,获得1,2-环己二胺四乙酸二酐;20 parts of 1,2-cyclohexanediaminetetraacetic acid and 20 parts of acetic anhydride were dissolved in 30 parts of 2-picoline, controlled at 70°C, and reacted for 40 hours to obtain 1,2-cyclohexanediamine tetraacetic dianhydride;
步骤四 合成PHEMAA-g-(PDMC-r-PVACDTANa-r-PVACS2Na)Step 4 Synthesis of PHEMAA-g-(PDMC-r-PVACDTANa-r-PVACS 2 Na)
将步骤一中所得到的3份的聚羟乙基丙烯酰胺(PHEMAA)与步骤二中所得到的100份的阳离子型高分子侧链PDMC-COOH和40份的功能高分子侧链前驱体聚合物PNVF-COOH混合溶于500份的水里,加入3份的催化剂即N-羟基琥珀酰亚胺(NHS)和3份的1-乙基-3-(3-二甲胺基丙基)碳二亚胺碘甲烷盐(EDC·CH3I),控温于80℃,进行酯化反应20小时,获得聚羟乙基丙烯酰胺-接枝-(聚甲基丙烯酰氧乙基三甲基氯化铵-无规-聚N-乙烯基甲酰胺)(PHEMAA-g-(PDMC-r-PNVF));再加10份的氢氧化钠,控温于50℃,对接枝于聚合物主链的功能高分子侧链前驱体聚合物(PNVF),进行水解反应12小时,获得聚羟乙基丙烯酰胺-接枝-(聚甲基丙烯酰氧乙基三甲基氯化铵-无规-聚乙烯胺)(PHEMAA-g-(PDMC-r-PVA));再加入步骤三中合成的20份的1,2-环己二胺四乙酸二酐(CDTAD),酰基化反应6小时,酰化度控制为67%,获得聚羟乙基丙烯酰胺-接枝-(聚甲基丙烯酰氧乙基三甲基氯化铵-无规-聚乙烯胺基环己二胺四乙酸钠-无规-聚乙烯胺)(PHEMAA-g-(PDMC-r-PVACDTANa-r-PVA));再加入10份二硫化碳,控温于20℃,进行加成反应3小时,获得聚羟乙基丙烯酰胺-接枝-(聚甲基丙烯酰氧乙基三甲基氯化铵-无规-聚乙烯胺基环己二胺四乙酸钠-无规-聚乙烯胺基二硫代氨基甲酸钠)(PHEMAA-g-(PDMC-r-PVACDTANa-r-PVACS2Na)) 即水溶性四元聚合物分子刷阴离子染料捕捉沉降剂。采用元素分析仪及核磁共振仪分别测定PDMC、 PVACDTANa和PVACS2Na侧链的接枝率分别为48%、10%和5%。Polymerize 3 parts of polyhydroxyethyl acrylamide (PHEMAA) obtained in step 1 with 100 parts of cationic polymer side chain PDMC-COOH and 40 parts of functional polymer side chain precursor obtained in step 2 The compound PNVF-COOH was mixed and dissolved in 500 parts of water, and 3 parts of catalyst, namely N-hydroxysuccinimide (NHS) and 3 parts of 1-ethyl-3-(3-dimethylaminopropyl) Carbodiimide methyl iodide salt (EDC·CH 3 I), the temperature was controlled at 80 ° C, and the esterification reaction was carried out for 20 hours to obtain polyhydroxyethyl acrylamide-grafted-(polymethacryloyloxyethyl trimethylene ammonium chloride-random-polyN-vinylformamide) (PHEMAA-g-(PDMC-r-PNVF)); add 10 parts of sodium hydroxide, control the temperature at 50 ° C, and graft on the polymer The functional polymer side chain precursor polymer (PNVF) of the main chain was hydrolyzed for 12 hours to obtain polyhydroxyethyl acrylamide-graft-(polymethacryloyloxyethyltrimethylammonium chloride- Random-polyvinylamine) (PHEMAA-g-(PDMC-r-PVA)); then add 20 parts of 1,2-cyclohexanediaminetetraacetic dianhydride (CDTAD) synthesized in step 3, acylation reaction 6 hours, the degree of acylation was controlled to 67%, and polyhydroxyethyl acrylamide-graft-(polymethacryloyloxyethyltrimethylammonium chloride-random-polyvinylaminocyclohexanediaminetetramine was obtained) Sodium acetate-random-polyvinylamine) (PHEMAA-g-(PDMC-r-PVACDTANa-r-PVA)); then add 10 parts of carbon disulfide, control the temperature at 20 ° C, and carry out an addition reaction for 3 hours to obtain polyhydroxy Ethyl acrylamide-graft-(polymethacryloyloxyethyltrimethylammonium chloride-random-polyvinylaminocyclohexanediaminetetraacetate-sodium-random-polyvinylaminodithioamino Sodium formate) (PHEMAA-g-(PDMC-r-PVACDTANa-r-PVACS 2 Na)) is a water-soluble quaternary polymer molecular brush anionic dye capture sedimentation agent. The grafting rates of PDMC, PVACDTANa and PVACS 2 Na side chains were determined by elemental analyzer and nuclear magnetic resonance analyzer, and they were 48%, 10% and 5%, respectively.
在本实施例中,水溶性四元聚合物分子刷阴离子染料捕捉沉降剂的应用In this embodiment, the application of water-soluble quaternary polymer molecular brush anionic dye capture sedimentation agent
取本实施例的水溶性四元聚合物分子刷阴离子染料捕捉沉降剂做染料废水测试,取1000份含甲基橙100 mg/L、Pb2+ 离子3 mg/L和柠檬酸0.2 mg/L废水,添加1.0份的水溶性四元聚合物分子刷阴离子染料捕捉沉降剂,常温下搅拌5分钟,采用0.1 mol/L盐酸调节废水pH值到5.0,再加入0.1份的助沉降剂氯化铝,常温下搅拌1分钟,3秒内生成粒径大于400μm的絮体沉淀,过滤,采用紫外吸收分光光度计测定滤液中甲基橙浓度为0.03 mg/L,采用原子吸收分光光度计测定滤液中Pb2+浓度为0.01 mg/L,脱除效率大于99%。Take the water-soluble quaternary polymer molecular brush anionic dye capture and sedimentation agent of this embodiment for dye wastewater test, take 1000 parts containing methyl orange 100 mg/L, Pb 2+ ion 3 mg/L and citric acid 0.2 mg/L Wastewater, add 1.0 part of water-soluble quaternary polymer molecular brush anion dye to capture sedimentation agent, stir at room temperature for 5 minutes, use 0.1 mol/L hydrochloric acid to adjust the pH value of wastewater to 5.0, and then add 0.1 part of aluminum chloride as a sedimentation aid , stirred at room temperature for 1 minute, and within 3 seconds, flocs with a particle size greater than 400 μm were precipitated, filtered, and the concentration of methyl orange in the filtrate was determined by an ultraviolet absorption spectrophotometer to be 0.03 mg/L. The concentration of Pb 2+ was 0.01 mg/L, and the removal efficiency was greater than 99%.
上述实施例为本发明较佳的实施方式,但本发明的实施方式并不受上述实施例的限制,其他的任何未背离本发明的精神实质与原理下所作的改变、修饰、替代、组合、简化,均应为等效的置换方式,都包含在本发明的保护范围之内。The above-mentioned embodiments are preferred embodiments of the present invention, but the embodiments of the present invention are not limited by the above-mentioned embodiments, and any other changes, modifications, substitutions, combinations, The simplification should be equivalent replacement manners, which are all included in the protection scope of the present invention.
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