CN105536742B - A kind of sewage disposal screen cloth and preparation method thereof - Google Patents
A kind of sewage disposal screen cloth and preparation method thereof Download PDFInfo
- Publication number
- CN105536742B CN105536742B CN201610110793.1A CN201610110793A CN105536742B CN 105536742 B CN105536742 B CN 105536742B CN 201610110793 A CN201610110793 A CN 201610110793A CN 105536742 B CN105536742 B CN 105536742B
- Authority
- CN
- China
- Prior art keywords
- preparation
- temperature
- methanol solution
- added dropwise
- star
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Expired - Fee Related
Links
- 239000010865 sewage Substances 0.000 title claims abstract description 43
- 239000004744 fabric Substances 0.000 title claims abstract description 39
- 238000002360 preparation method Methods 0.000 title claims description 53
- 238000000034 method Methods 0.000 claims abstract description 92
- 230000008569 process Effects 0.000 claims abstract description 86
- 238000009941 weaving Methods 0.000 claims abstract description 14
- OKKJLVBELUTLKV-UHFFFAOYSA-N Methanol Chemical compound OC OKKJLVBELUTLKV-UHFFFAOYSA-N 0.000 claims description 153
- 239000000412 dendrimer Substances 0.000 claims description 71
- 229920000736 dendritic polymer Polymers 0.000 claims description 71
- 239000000243 solution Substances 0.000 claims description 60
- 238000006243 chemical reaction Methods 0.000 claims description 46
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 claims description 40
- ABLZXFCXXLZCGV-UHFFFAOYSA-N phosphonic acid group Chemical group P(O)(O)=O ABLZXFCXXLZCGV-UHFFFAOYSA-N 0.000 claims description 39
- 239000000835 fiber Substances 0.000 claims description 36
- 239000007788 liquid Substances 0.000 claims description 24
- PIICEJLVQHRZGT-UHFFFAOYSA-N Ethylenediamine Chemical compound NCCN PIICEJLVQHRZGT-UHFFFAOYSA-N 0.000 claims description 21
- 239000007864 aqueous solution Substances 0.000 claims description 21
- 229920000642 polymer Polymers 0.000 claims description 20
- 238000003756 stirring Methods 0.000 claims description 20
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 20
- 238000010992 reflux Methods 0.000 claims description 17
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 claims description 16
- WSFSSNUMVMOOMR-UHFFFAOYSA-N Formaldehyde Chemical compound O=C WSFSSNUMVMOOMR-UHFFFAOYSA-N 0.000 claims description 16
- 238000007711 solidification Methods 0.000 claims description 15
- 230000008023 solidification Effects 0.000 claims description 15
- 238000010521 absorption reaction Methods 0.000 claims description 13
- FFRBMBIXVSCUFS-UHFFFAOYSA-N 2,4-dinitro-1-naphthol Chemical compound C1=CC=C2C(O)=C([N+]([O-])=O)C=C([N+]([O-])=O)C2=C1 FFRBMBIXVSCUFS-UHFFFAOYSA-N 0.000 claims description 12
- 230000015572 biosynthetic process Effects 0.000 claims description 10
- 238000009987 spinning Methods 0.000 claims description 10
- 238000002166 wet spinning Methods 0.000 claims description 10
- 238000003786 synthesis reaction Methods 0.000 claims description 9
- 229910052757 nitrogen Inorganic materials 0.000 claims description 8
- 239000002994 raw material Substances 0.000 claims description 8
- 239000002904 solvent Substances 0.000 claims description 8
- ISIJQEHRDSCQIU-UHFFFAOYSA-N tert-butyl 2,7-diazaspiro[4.5]decane-7-carboxylate Chemical compound C1N(C(=O)OC(C)(C)C)CCCC11CNCC1 ISIJQEHRDSCQIU-UHFFFAOYSA-N 0.000 claims description 8
- 230000008901 benefit Effects 0.000 claims description 6
- LYLHVKVAISPJHX-UHFFFAOYSA-N CO.C(CN)N Chemical compound CO.C(CN)N LYLHVKVAISPJHX-UHFFFAOYSA-N 0.000 claims description 5
- PMZURENOXWZQFD-UHFFFAOYSA-L Sodium Sulfate Chemical compound [Na+].[Na+].[O-]S([O-])(=O)=O PMZURENOXWZQFD-UHFFFAOYSA-L 0.000 claims description 5
- 239000007787 solid Substances 0.000 claims description 5
- 239000002245 particle Substances 0.000 claims description 4
- 229910052938 sodium sulfate Inorganic materials 0.000 claims description 4
- 235000011152 sodium sulphate Nutrition 0.000 claims description 4
- 238000005516 engineering process Methods 0.000 claims description 3
- 238000001914 filtration Methods 0.000 claims description 3
- -1 tetramethylol methane tetraacrylate methanol Chemical compound 0.000 claims description 3
- 230000009286 beneficial effect Effects 0.000 claims description 2
- 238000004519 manufacturing process Methods 0.000 claims description 2
- AGEQBLXZMIPKBM-UHFFFAOYSA-N 4-n,4-n-diphenylbenzene-1,2,3,4-tetramine Chemical compound NC1=C(N)C(N)=CC=C1N(C=1C=CC=CC=1)C1=CC=CC=C1 AGEQBLXZMIPKBM-UHFFFAOYSA-N 0.000 claims 10
- 125000003368 amide group Chemical group 0.000 claims 5
- GZBSIABKXVPBFY-UHFFFAOYSA-N 2,2-bis(hydroxymethyl)propane-1,3-diol;prop-2-enoic acid Chemical compound OC(=O)C=C.OC(=O)C=C.OC(=O)C=C.OC(=O)C=C.OCC(CO)(CO)CO GZBSIABKXVPBFY-UHFFFAOYSA-N 0.000 claims 3
- 229920004933 Terylene® Polymers 0.000 claims 1
- 230000008676 import Effects 0.000 claims 1
- 238000009413 insulation Methods 0.000 claims 1
- 230000014759 maintenance of location Effects 0.000 claims 1
- 238000002156 mixing Methods 0.000 claims 1
- 239000005020 polyethylene terephthalate Substances 0.000 claims 1
- 238000006116 polymerization reaction Methods 0.000 claims 1
- 230000003578 releasing effect Effects 0.000 claims 1
- 230000008719 thickening Effects 0.000 claims 1
- 238000010792 warming Methods 0.000 claims 1
- 229910001385 heavy metal Inorganic materials 0.000 abstract description 38
- 238000001179 sorption measurement Methods 0.000 abstract description 20
- 230000000694 effects Effects 0.000 abstract description 19
- 239000002351 wastewater Substances 0.000 abstract description 5
- 230000009172 bursting Effects 0.000 abstract description 4
- NSFSAHIOBUAWGP-UHFFFAOYSA-N 2-n,2-n-diphenylbenzene-1,2-diamine Chemical compound NC1=CC=CC=C1N(C=1C=CC=CC=1)C1=CC=CC=C1 NSFSAHIOBUAWGP-UHFFFAOYSA-N 0.000 description 35
- 230000015271 coagulation Effects 0.000 description 33
- 238000005345 coagulation Methods 0.000 description 33
- DAKWPKUUDNSNPN-UHFFFAOYSA-N Trimethylolpropane triacrylate Chemical compound C=CC(=O)OCC(CC)(COC(=O)C=C)COC(=O)C=C DAKWPKUUDNSNPN-UHFFFAOYSA-N 0.000 description 20
- 150000002500 ions Chemical class 0.000 description 20
- 239000000047 product Substances 0.000 description 14
- 239000000126 substance Substances 0.000 description 14
- 230000009920 chelation Effects 0.000 description 9
- 238000001228 spectrum Methods 0.000 description 9
- 125000001570 methylene group Chemical group [H]C([H])([*:1])[*:2] 0.000 description 8
- 239000003795 chemical substances by application Substances 0.000 description 7
- 238000005160 1H NMR spectroscopy Methods 0.000 description 6
- 238000005481 NMR spectroscopy Methods 0.000 description 6
- 239000002253 acid Substances 0.000 description 6
- 239000003513 alkali Substances 0.000 description 6
- 125000003277 amino group Chemical group 0.000 description 6
- 239000012141 concentrate Substances 0.000 description 6
- 238000009940 knitting Methods 0.000 description 6
- 239000000203 mixture Substances 0.000 description 6
- XRBCRPZXSCBRTK-UHFFFAOYSA-N phosphonous acid Chemical compound OPO XRBCRPZXSCBRTK-UHFFFAOYSA-N 0.000 description 6
- 230000008439 repair process Effects 0.000 description 6
- 238000006845 Michael addition reaction Methods 0.000 description 5
- 229910052739 hydrogen Inorganic materials 0.000 description 5
- 239000001257 hydrogen Substances 0.000 description 5
- UFHFLCQGNIYNRP-UHFFFAOYSA-N Hydrogen Chemical compound [H][H] UFHFLCQGNIYNRP-UHFFFAOYSA-N 0.000 description 4
- 239000000463 material Substances 0.000 description 4
- 230000005012 migration Effects 0.000 description 4
- 238000013508 migration Methods 0.000 description 4
- 230000002522 swelling effect Effects 0.000 description 4
- VDEXYPJTXRCCJF-UHFFFAOYSA-N 2-ethyl-2-(hydroxymethyl)propane-1,3-diol methanol prop-2-enoic acid Chemical compound CO.C(C=C)(=O)O.C(C=C)(=O)O.C(C=C)(=O)O.C(O)C(CC)(CO)CO VDEXYPJTXRCCJF-UHFFFAOYSA-N 0.000 description 3
- 230000004888 barrier function Effects 0.000 description 3
- 229910052797 bismuth Inorganic materials 0.000 description 3
- JCXGWMGPZLAOME-UHFFFAOYSA-N bismuth atom Chemical group [Bi] JCXGWMGPZLAOME-UHFFFAOYSA-N 0.000 description 3
- 230000001112 coagulating effect Effects 0.000 description 3
- 239000008098 formaldehyde solution Substances 0.000 description 3
- 229920000587 hyperbranched polymer Polymers 0.000 description 3
- 238000009776 industrial production Methods 0.000 description 3
- 229910052751 metal Inorganic materials 0.000 description 3
- 239000002184 metal Substances 0.000 description 3
- 229910021645 metal ion Inorganic materials 0.000 description 3
- 238000002161 passivation Methods 0.000 description 3
- 230000035699 permeability Effects 0.000 description 3
- 229920000728 polyester Polymers 0.000 description 3
- 239000002244 precipitate Substances 0.000 description 3
- 239000011541 reaction mixture Substances 0.000 description 3
- 238000001291 vacuum drying Methods 0.000 description 3
- 238000004804 winding Methods 0.000 description 3
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 2
- XYFCBTPGUUZFHI-UHFFFAOYSA-N Phosphine Chemical compound P XYFCBTPGUUZFHI-UHFFFAOYSA-N 0.000 description 2
- 239000003463 adsorbent Substances 0.000 description 2
- 238000011161 development Methods 0.000 description 2
- 239000002657 fibrous material Substances 0.000 description 2
- 125000002887 hydroxy group Chemical group [H]O* 0.000 description 2
- 230000006872 improvement Effects 0.000 description 2
- 230000004048 modification Effects 0.000 description 2
- 238000012986 modification Methods 0.000 description 2
- 239000003607 modifier Substances 0.000 description 2
- 125000002924 primary amino group Chemical group [H]N([H])* 0.000 description 2
- 230000009467 reduction Effects 0.000 description 2
- 230000003313 weakening effect Effects 0.000 description 2
- 229920001661 Chitosan Polymers 0.000 description 1
- 239000004642 Polyimide Substances 0.000 description 1
- 229910021536 Zeolite Inorganic materials 0.000 description 1
- 230000002378 acidificating effect Effects 0.000 description 1
- 238000007259 addition reaction Methods 0.000 description 1
- 229920002678 cellulose Polymers 0.000 description 1
- 239000001913 cellulose Substances 0.000 description 1
- 239000002738 chelating agent Substances 0.000 description 1
- 229920001429 chelating resin Polymers 0.000 description 1
- 238000007385 chemical modification Methods 0.000 description 1
- 238000009388 chemical precipitation Methods 0.000 description 1
- 230000007812 deficiency Effects 0.000 description 1
- 238000013461 design Methods 0.000 description 1
- HNPSIPDUKPIQMN-UHFFFAOYSA-N dioxosilane;oxo(oxoalumanyloxy)alumane Chemical compound O=[Si]=O.O=[Al]O[Al]=O HNPSIPDUKPIQMN-UHFFFAOYSA-N 0.000 description 1
- 238000005265 energy consumption Methods 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 125000001495 ethyl group Chemical group [H]C([H])([H])C([H])([H])* 0.000 description 1
- 239000006260 foam Substances 0.000 description 1
- 125000000524 functional group Chemical group 0.000 description 1
- 125000004435 hydrogen atom Chemical group [H]* 0.000 description 1
- 230000010354 integration Effects 0.000 description 1
- 230000003993 interaction Effects 0.000 description 1
- 238000005342 ion exchange Methods 0.000 description 1
- 229920002521 macromolecule Polymers 0.000 description 1
- 239000012528 membrane Substances 0.000 description 1
- 238000000655 nuclear magnetic resonance spectrum Methods 0.000 description 1
- 125000001997 phenyl group Chemical group [H]C1=C([H])C([H])=C(*)C([H])=C1[H] 0.000 description 1
- 229910000073 phosphorus hydride Inorganic materials 0.000 description 1
- 230000000704 physical effect Effects 0.000 description 1
- 229920002239 polyacrylonitrile Polymers 0.000 description 1
- 229920001721 polyimide Polymers 0.000 description 1
- 229920005594 polymer fiber Polymers 0.000 description 1
- 230000008092 positive effect Effects 0.000 description 1
- 238000012545 processing Methods 0.000 description 1
- 238000000425 proton nuclear magnetic resonance spectrum Methods 0.000 description 1
- 230000005180 public health Effects 0.000 description 1
- 229920005989 resin Polymers 0.000 description 1
- 239000011347 resin Substances 0.000 description 1
- 230000025508 response to water Effects 0.000 description 1
- 238000005096 rolling process Methods 0.000 description 1
- 125000000467 secondary amino group Chemical group [H]N([*:1])[*:2] 0.000 description 1
- 238000000638 solvent extraction Methods 0.000 description 1
- 238000004065 wastewater treatment Methods 0.000 description 1
- 238000003911 water pollution Methods 0.000 description 1
- 239000010457 zeolite Substances 0.000 description 1
Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/22—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising organic material
- B01J20/26—Synthetic macromolecular compounds
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/28—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties
- B01J20/28014—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties characterised by their form
- B01J20/28033—Membrane, sheet, cloth, pad, lamellar or mat
-
- 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
- C02F1/28—Treatment of water, waste water, or sewage by sorption
- C02F1/285—Treatment of water, waste water, or sewage by sorption using synthetic organic sorbents
-
- 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
Landscapes
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Analytical Chemistry (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Life Sciences & Earth Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Addition Polymer Or Copolymer, Post-Treatments, Or Chemical Modifications (AREA)
- Solid-Sorbent Or Filter-Aiding Compositions (AREA)
Abstract
Description
技术领域technical field
本发明涉及污水生产技术领域,具体的说,是一种污水处理用网布及其制备方法。The invention relates to the technical field of sewage production, in particular to a mesh cloth for sewage treatment and a preparation method thereof.
背景技术Background technique
随着社会的不断进步和工业的迅速发展,重金属废水排放所造成的污染对生态系统和公众健康构成了严重威胁,水体中的重金属已成为我国最为严重的环境问题之一,因此,对重金属废水的治理受到国内外科研工作者的高度重视。为了更有效的防治水体中重金属污染,我国已经出台了多项法制,用于水体重金属的治理。目前重金属废水的处理方法主要有化学沉淀、离子交换、溶剂萃取、化学氧化还原和吸附法等,其中吸附法具有易于操作、低能耗、低残留、高吸附量和可重复利用性等优点,是最经济、高效并广泛使用和深入研究的技术之。目前已有包括活性炭、壳聚糖、天然沸石、生物吸附剂、螯合树脂等在内的多种吸附剂被广泛应用于重金属废水的处理中,这些吸附剂的吸附能力主要依赖于其自身的物理性质和表面官能团。With the continuous progress of society and the rapid development of industry, the pollution caused by the discharge of heavy metal wastewater has posed a serious threat to the ecosystem and public health. Heavy metals in water have become one of the most serious environmental problems in my country. Therefore, heavy metal wastewater Governance has been highly valued by researchers at home and abroad. In order to more effectively prevent and control heavy metal pollution in water bodies, our country has introduced a number of legal systems for the treatment of heavy metals in water. At present, the treatment methods of heavy metal wastewater mainly include chemical precipitation, ion exchange, solvent extraction, chemical redox and adsorption methods, etc. Among them, the adsorption method has the advantages of easy operation, low energy consumption, low residue, high adsorption capacity and reusability. One of the most economical, efficient, widely used and well-studied technologies. At present, a variety of adsorbents including activated carbon, chitosan, natural zeolite, biosorbent, chelating resin, etc. have been widely used in the treatment of heavy metal wastewater. The adsorption capacity of these adsorbents mainly depends on their own Physical properties and surface functional groups.
与传统的树脂、泡沫和传统纤维相比,聚合物纤维由于具有高比表面积、高孔隙率、易于制备和易于物理/化学修饰等优点,在重金属废水处理的应用也日益广泛。目前用于重金属吸附的纤维材料,主要是含羟基、氨基等多官能团的材料,如纤维素、聚丙烯腈以及聚酰亚胺等;而对于传统的纤维材料而言,由于其制备过程中通过纺丝再经织造等过程,制备得到膜或者织物从而才能应用在水体中重金属的处理,其纺丝再经织造过程复杂,且工序较多。因此开发一种能够实现材料形状与功能一体的蓬松材料制备技术,并应用于重金属的吸附,对于水体污染快速反应,快速处理紧急状况具有重要意义。Compared with traditional resins, foams, and traditional fibers, polymer fibers are increasingly used in heavy metal wastewater treatment due to their advantages such as high specific surface area, high porosity, easy preparation, and easy physical/chemical modification. At present, the fiber materials used for heavy metal adsorption are mainly materials containing multifunctional groups such as hydroxyl and amino groups, such as cellulose, polyacrylonitrile, and polyimide; and for traditional fiber materials, due to their preparation process through Spinning and then weaving to prepare membranes or fabrics can be applied to the treatment of heavy metals in water bodies. The spinning and weaving process is complicated and there are many processes. Therefore, it is of great significance to develop a fluffy material preparation technology that can realize the integration of material shape and function, and apply it to the adsorption of heavy metals for rapid response to water pollution and rapid treatment of emergency situations.
网布材料具有优异的三维组织结构,即可利于污水的过滤,同时也利于淤泥等的过滤通过;目前对于网布用于污水的研究较多,但主要集中在开发具有低纬度的纤维制备网布,提高纤维本身的比表面积;本发明采用具有30个膦酸端基的超支化聚合物为改性剂,通过网布的织造方法,制备得到污水处理用网布,具有吸附性能优异,污水处理效率高,可循环使用。The mesh material has an excellent three-dimensional organizational structure, which is beneficial to the filtration of sewage and also facilitates the filtration of silt. At present, there are many studies on the use of mesh for sewage, but they mainly focus on the development of fiber preparation mesh with low latitude. cloth to improve the specific surface area of the fiber itself; the present invention uses a hyperbranched polymer with 30 phosphonic acid end groups as a modifying agent, and prepares a mesh cloth for sewage treatment through the weaving method of the mesh cloth, which has excellent adsorption performance, and the sewage High processing efficiency, recyclable.
发明内容Contents of the invention
本发明的目的在于克服现有技术的不足,提供一种污水处理用网布及其制备方法。The purpose of the present invention is to overcome the deficiencies of the prior art and provide a mesh cloth for sewage treatment and a preparation method thereof.
本发明的目的是通过以下技术方案来实现的:The purpose of the present invention is achieved through the following technical solutions:
一种污水处理用网布,其特征在于,其通过经编机三维编织得到,网布的厚度为10~50mm,污水处理用网布透水量大于1800mm·s-1,顶破强度大于2000N。A mesh cloth for sewage treatment, characterized in that it is obtained by three-dimensional weaving by a warp knitting machine, the thickness of the mesh cloth is 10-50mm, the water permeability of the mesh cloth for sewage treatment is greater than 1800mm·s -1 , and the bursting strength is greater than 2000N.
一种污水处理用网布的制备方法,其特征在于,其具体步骤为:A kind of preparation method of mesh cloth for sewage treatment is characterized in that, its specific steps are:
(一)膦酸端基超支化树枝状聚合物的制备(1) Preparation of phosphonic acid-terminated hyperbranched dendrimers
膦酸端基超支化树枝状聚合物的结构式如图1所示:The structural formula of phosphonic acid terminal hyperbranched dendrimers is as shown in Figure 1:
所述的膦酸端基超支化树枝状聚合物的应用主要是应用于水体中重金属离子的吸附处理;The application of the phosphonic acid terminal hyperbranched dendritic polymer is mainly applied to the adsorption treatment of heavy metal ions in water;
具有高代数的钝化剂,由于分子中膦酸基团含量高,与重金属离子螯合作用强,单一分子金属离子的螯合数量大,形成的螯合基团分子空间体积大,因此耐酸碱稳定性好,抗迁移性好,尤其是在螯合作用过程中由于树枝状结构,对分子中的重金属具有非常优异的离子阻隔效应和过滤离子效应,因此设计越多的树枝结构以及越多的膦酸螯合基团,其螯合作用越强,且抗酸碱稳定性越强,因此本发明设计具有30个膦酸基团,且具有3主枝,9细枝的膦酸端基超支化树枝状聚合物对重金属的修复效果明显由于常规的金属钝化修复剂;Passivating agent with high algebra, due to the high content of phosphonic acid groups in the molecule, it has a strong chelation effect with heavy metal ions, and the chelation number of a single molecule of metal ions is large, and the formed chelating group has a large molecular space volume, so it is acid-resistant Good alkali stability and good migration resistance, especially in the process of chelation, due to the dendritic structure, it has very excellent ion barrier effect and filter ion effect on heavy metals in the molecule, so the more dendritic structures are designed and the more The stronger the phosphonic acid chelating group, the stronger the chelating effect, and the stronger the acid and alkali resistance stability, so the present invention has 30 phosphonic acid groups, and has 3 main branches, 9 twigs of phosphonic acid end groups The repair effect of hyperbranched dendrimers on heavy metals is obvious due to conventional metal passivation repair agents;
(a)端双键星形聚合物的制备(a) Preparation of terminal double bond star polymer
以三羟甲基丙烷三丙烯酸酯TMPTA和氨基三苯胺为原料,甲醇为溶剂,在带搅拌和冷凝回流的反应装置中,以氮气保护下,控制反应体系的温度为-10~5℃,先把氨基三苯胺的甲醇溶液分为三等份,然后分批向三羟甲基丙烷三丙烯酸酯TMPTA的甲醇溶液中滴加氨基三苯胺的甲醇溶液,在第一次滴加氨基三苯胺的甲醇溶液时,控制滴加过程的温度为-10~-5℃,滴加时间为30~60min,第二次滴加氨基三苯胺的甲醇溶液时,控制滴加过程的温度为-5~0℃,滴加时间为30~45min,第三次滴加氨基三苯胺的甲醇溶液时,控制滴加过程的温度为0~5℃,滴加时间为20~30min,每一次滴加氨基三苯胺的甲醇溶液后,反应体系移至25℃的温度下反应4~10h。氨基三苯胺的甲醇溶液全部滴加滴毕后,反应体系移至于25℃下,继续反应10~20h;反应完成后体系中会有金黄色产物析出,过滤,并用甲醇洗涤,淡金黄色产物在40℃真空干燥,得到金黄色的端双键星形聚合物,端双键星形聚合物的制备的化学反应方程式如图2所示:Using trimethylolpropane triacrylate TMPTA and aminotriphenylamine as raw materials, methanol as a solvent, in a reaction device with stirring and condensing reflux, under the protection of nitrogen, the temperature of the reaction system is controlled at -10 ~ 5 ° C, first Divide the methanol solution of aminotriphenylamine into three equal parts, then add the methanol solution of aminotriphenylamine dropwise in batches to the methanol solution of trimethylolpropane triacrylate TMPTA, and add the methanol solution of aminotriphenylamine dropwise for the first time When adding the solution, the temperature of the dropping process is controlled to be -10~-5°C, and the dropping time is 30~60 minutes. When the methanol solution of aminotriphenylamine is added dropwise for the second time, the temperature of the dropping process is controlled to be -5~0°C , the dropping time is 30-45min, when the methanol solution of aminotriphenylamine is added dropwise for the third time, the temperature of the dropping process is controlled to be 0-5°C, the dropping time is 20-30min, and the dropwise addition of aminotriphenylamine After methanol solution, the reaction system was moved to a temperature of 25°C for 4-10 hours. After the methanol solution of aminotriphenylamine has been added dropwise, the reaction system is moved to 25°C, and the reaction is continued for 10 to 20 hours; after the reaction is completed, a golden yellow product will precipitate in the system, filter and wash with methanol, and the light golden yellow product is in the Vacuum drying at 40°C to obtain a golden-yellow terminal double bond star polymer, the chemical reaction equation for the preparation of the terminal double bond star polymer is shown in Figure 2:
所述的三羟甲基丙烷三丙烯酸酯TMPTA和氨基三苯胺的摩尔比值为1:0.25~0.30;The molar ratio of described trimethylolpropane triacrylate TMPTA and aminotriphenylamine is 1:0.25~0.30;
所述的三羟甲基丙烷三丙烯酸酯甲醇溶液的摩尔分数为0.25~1.25mol/L;The mole fraction of the trimethylolpropane triacrylate methanol solution is 0.25~1.25mol/L;
所述的氨基三苯胺的甲醇溶液的摩尔分数为0.10~1.50mol/L;The mole fraction of the methanol solution of aminotriphenylamine is 0.10-1.50mol/L;
(b)端胺基星形树枝状聚合物的合成(b) Synthesis of amine-terminated star dendrimers
在带有搅拌、回流冷凝管的反应器中,控制反应温度为0~5℃,在氮气保护及搅拌条件下,先加入乙二胺的甲醇溶液,然后再将步骤(a)制备的端双键星形聚合物加入,搅拌,混合均匀;然后在25℃下,反应20~30h,再在80~100℃的条件下减压蒸馏3~5h除去甲醇和多余的乙二胺,得到黄色粘稠产物,即为端胺基星形树枝状聚合物;In the reactor with stirring and reflux condenser, the reaction temperature is controlled at 0-5°C, under the condition of nitrogen protection and stirring, the methanol solution of ethylenediamine is added first, and then the terminal bismuth prepared in step (a) is Add the bonded star polymer, stir, and mix well; then react at 25°C for 20-30 hours, and then distill under reduced pressure at 80-100°C for 3-5 hours to remove methanol and excess ethylenediamine to obtain yellow viscous Thick product, namely amine-terminated star-shaped dendrimers;
所述的乙二胺甲醇溶液中乙二胺的摩尔分数为0.5~5.0mol/L;The mole fraction of ethylenediamine in the ethylenediamine methanol solution is 0.5-5.0mol/L;
所述的星形端双键树枝状聚合物与乙二胺的摩尔比值为1:10~12;The molar ratio of the star-end double bond dendrimer to ethylenediamine is 1:10~12;
乙二胺化合物来源广,成本低,制备过程中化学反应温和,制备工艺可控,因此制备过程中之成本低,利于工业化生产和大规模推广,对于提升产品的市场化具有非常大的成本优势。Ethylenediamine compounds have wide sources, low cost, mild chemical reaction in the preparation process, and controllable preparation process, so the cost in the preparation process is low, which is conducive to industrial production and large-scale promotion, and has a very large cost advantage for improving the marketization of products .
(c)膦酸端基超支化树枝状聚合物的合成(c) Synthesis of phosphonic acid-terminated hyperbranched dendrimers
将亚磷酸加入到浓盐酸中混合均匀,控制亚磷酸在浓盐酸中浓度为0.25~1.25mol/L,浓盐酸为10~12mol/L的盐酸溶液,然后在0~10℃条件下,滴加步骤(b)制备的端胺基星形树枝状聚合物的水溶液,端胺基星形树枝状聚合物的水溶液质量分数为20~45%,端胺基星形树枝状聚合物的水溶液滴加过程在30min内滴加完成;然后再在85~90℃的搅拌条件下,滴加甲醛水溶液,甲醛水溶液滴加完毕后反应体系,再在90℃条件下保温反应1~2小时,最后升温至105~110℃,回流2~4小时,回流结束后,关闭回流装置,打开HCl吸收瓶,浓缩反应混合液,浓缩温度105~110℃,浓缩至无HCl放出后,冷却至室温,得到固含量为25~55%的淡黄色透明液体的膦酸端基超支化树枝状聚合物的水溶液;Add phosphorous acid into concentrated hydrochloric acid and mix evenly, control the concentration of phosphorous acid in concentrated hydrochloric acid to be 0.25-1.25mol/L, concentrated hydrochloric acid is 10-12mol/L hydrochloric acid solution, and then add dropwise at 0-10°C The aqueous solution of the amine-terminated star-shaped dendrimer prepared in step (b), the aqueous solution mass fraction of the amine-terminated star-shaped dendrimer is 20 to 45%, and the aqueous solution of the amine-terminated star-shaped dendrimer is added dropwise The process is completed dropwise within 30 minutes; then, under the condition of stirring at 85-90°C, formaldehyde solution is added dropwise. 105-110°C, reflux for 2-4 hours, after the reflux, close the reflux device, open the HCl absorption bottle, concentrate the reaction mixture, the concentration temperature is 105-110°C, concentrate until no HCl is released, cool to room temperature, and obtain the solid content It is an aqueous solution of 25% to 55% light yellow transparent liquid phosphonic acid terminal hyperbranched dendritic polymer;
固含量为膦酸端基超支化树枝状聚合物在水溶液中的质量百分数;Solid content is the mass percent of phosphonic acid end group hyperbranched dendritic polymer in aqueous solution;
(二)改性PVA纤维的制备(2) Preparation of modified PVA fiber
采用1799型号的PVA颗粒为原料,以水为溶剂,在90~98℃条件下进行溶解,控制PVA纺丝液的质量分数为15~20%,然后再加入上述步骤(1)合成的膦酸端基超支化树枝状聚合物,溶解后,进行湿法纺丝,以硫酸钠的水溶液为凝固液,经凝固液凝固,拉伸以及卷绕制备得到改性PVA纤维;Use 1799 type PVA particles as raw material, use water as solvent, dissolve at 90-98°C, control the mass fraction of PVA spinning solution to 15-20%, and then add the phosphonic acid synthesized in the above step (1) The end-group hyperbranched dendritic polymer is dissolved and wet-spun, and the aqueous solution of sodium sulfate is used as the coagulation liquid, and the modified PVA fiber is prepared by coagulating the coagulation liquid, stretching and winding;
所述的湿法纺丝速度为0.5~10m/min,纺丝液温度25~35℃;所述的凝固工艺采用两次凝固,第一道凝固过程中凝固液浓度为1.0~1.5g/L,第一道凝固过程中凝固温度为40~50℃,第一道凝固过程中纤维停留时间为12~18s;第二道凝固过程中凝固液浓度为0.9~1.3g/L,第二道凝固过程中凝固温度为85~95℃,第二道凝固过程中停留时间为10~15s;所述的拉伸工艺分为第一次湿拉伸,第二次干拉伸工艺,第一次湿拉伸过程中拉伸倍数为0.5~1.0倍,拉伸温度为120~150℃,所述的第二次干拉伸过程中伸倍数为1.5~2.0倍,拉伸温度为180~230℃;The wet spinning speed is 0.5-10m/min, and the spinning liquid temperature is 25-35°C; the coagulation process uses two coagulations, and the coagulation liquid concentration in the first coagulation process is 1.0-1.5g/L , the coagulation temperature in the first coagulation process is 40-50°C, the fiber residence time in the first coagulation process is 12-18s; the coagulation liquid concentration in the second coagulation process is 0.9-1.3g/L, The solidification temperature in the process is 85-95°C, and the residence time in the second solidification process is 10-15s; the stretching process is divided into the first wet stretching process, the second dry stretching process, and the first wet stretching process. During the stretching process, the stretching ratio is 0.5-1.0 times, and the stretching temperature is 120-150°C. In the second dry stretching process, the stretching ratio is 1.5-2.0 times, and the stretching temperature is 180-230°C;
PVA纤维具有优异的水溶胀性能,利于螯合作用的膦酸端基超支化树枝状聚合物与重金属离子的接触,从而提高网布对重金属离子的吸附作用,同时在湿法纺丝过程中,由于PVA纤维在凝固过程中形成大量的微孔,提升纤维表面的凹糟和微孔,从而提高膦酸端基超支化树枝状聚合物的与污水中的重金属接触表面,提升网布的吸附作用。PVA fiber has excellent water swelling properties, which is conducive to the contact of phosphonic acid-terminated hyperbranched dendrimers with heavy metal ions, thereby improving the adsorption of heavy metal ions by mesh cloth. At the same time, in the wet spinning process, Since the PVA fiber forms a large number of micropores during the solidification process, the depressions and micropores on the fiber surface are improved, thereby improving the contact surface of the phosphonic acid-terminated hyperbranched dendritic polymer with the heavy metals in the sewage, and improving the adsorption of the mesh. .
(三)污水处理用网布的制备(3) Preparation of mesh cloth for sewage treatment
采用德国进口KARL MAYER RD6DPLM型双针床经编机上生产试样,经过整经,编织和整理三个步骤制备得到所需的污水处理用网布;其中所述的整经过程中控制整经张力为0.08~0.18g/den,且编织过程中经经纱,纬纱和绑纱制造成网布,经纱均呈竖直状结构,纬纱均呈水平状结构,经纱和纬纱通过绑纱连接,经纱的密度为300~450根/cm,纬纱的密度为300~450根/cm,绑纱的密度为500~600根/cm,所述的经线为改性PVA纤维,所述的纬线为涤纶单丝,所述的绑纱为改性PVA纤维;The sample is produced on the KARL MAYER RD6DPLM double-needle bed warp knitting machine imported from Germany, and the required mesh for sewage treatment is prepared through three steps of warping, weaving and finishing; the warping tension is controlled during the warping process It is 0.08~0.18g/den, and the warp yarn, weft yarn and binding yarn are made into mesh during the weaving process. The warp yarn is in a vertical structure, and the weft yarn is in a horizontal structure. 300-450 yarns/cm, the weft yarn density is 300-450 yarns/cm, the binding yarn density is 500-600 yarns/cm, the warp is modified PVA fiber, and the weft is polyester monofilament, The binding yarn is modified PVA fiber;
与现有技术相比,本发明的积极效果是:Compared with prior art, positive effect of the present invention is:
采用网布结构,在污水处理过程中,竖直方向上的经纱能够很好的与污水中的重金属进行接触,避免了传统织物由于重叠结构导致的与污水接触表面减少,导致吸附效果减弱的问题;With the mesh structure, during the sewage treatment process, the warp yarns in the vertical direction can be well in contact with the heavy metals in the sewage, avoiding the problem of the reduction of the contact surface with the sewage caused by the overlapping structure of the traditional fabric, resulting in the weakening of the adsorption effect. ;
本发明一种污水处理用网布及其制备方法,采用网布结构,在污水处理过程中,利用竖直方向上的经纱能够很好的与污水中的重金属进行接触,避免了传统织物由于重叠结构导致的与污水接触表面减少,导致吸附效果减弱的问题;采用具有30个端膦酸基团超支化树枝状聚合物为PVA纤维的改性剂,利用PVA优异的水溶胀性能,以及PVA纤维在湿法纺丝凝固过程中形成大量的微孔,提升纤维表面的凹糟和微孔,从而提高膦酸端基超支化树枝状聚合物的与污水中的重金属接触表面,提升网布的吸附作用,通过湿法纺丝方法利用超支化聚合物大分子空间位阻作用以及分子间的氢键相互作用固定膦酸端基超支化树枝状聚合物,避免改性剂的迁移,同时由于球形的膦酸端基超支化树枝状聚合物在纺丝高倍拉伸过程中的滚动效应,迁移到纤维表面,降低膦酸端基超支化树枝状聚合物与水体中的重金属离子的接触阻力,利于形成更为稳定的螯合化合物,提升网布的污水处理性能;用于水体中重金属离子的处理等领域具有广阔的应用前景。The invention discloses a mesh cloth for sewage treatment and a preparation method thereof. The mesh structure is adopted. During the sewage treatment process, the warp yarns in the vertical direction can be used to make good contact with the heavy metals in the sewage, and the traditional fabrics are avoided due to overlapping. The reduction of the contact surface with the sewage caused by the structure leads to the problem of weakening the adsorption effect; using a hyperbranched dendritic polymer with 30 terminal phosphonic acid groups as a modifier for PVA fibers, utilizing the excellent water swelling properties of PVA, and PVA fibers A large number of micropores are formed during the wet spinning solidification process, and the depressions and micropores on the surface of the fiber are improved, thereby improving the contact surface of the phosphonic acid-terminated hyperbranched dendrimer and the heavy metal in the sewage, and improving the adsorption of the mesh Function, through the wet spinning method, the steric hindrance of hyperbranched polymer macromolecules and the hydrogen bond interaction between molecules are used to fix the phosphonic acid terminal hyperbranched dendrimers, avoiding the migration of modifiers, and due to the spherical shape The rolling effect of phosphonic acid-terminated hyperbranched dendrimers in the spinning high-stretching process migrates to the surface of the fiber, reducing the contact resistance between phosphonic acid-terminated hyperbranched dendrimers and heavy metal ions in water, which is conducive to the formation of A more stable chelating compound can improve the sewage treatment performance of the mesh cloth; it has broad application prospects for the treatment of heavy metal ions in water and other fields.
附图说明Description of drawings
图1为膦酸端基超支化树枝状聚合物的结构式;Fig. 1 is the structural formula of phosphonic acid end group hyperbranched dendrimers;
图2为端双键星形聚合物的制备的化学反应方程式;Fig. 2 is the chemical reaction equation of the preparation of terminal double bond star polymer;
图3为端胺基星形树枝状聚合物的制备化学反应方程式;Fig. 3 is the preparation chemical reaction equation of amine-terminated star dendrimer;
图4为膦酸端基超支化树枝状聚合物制备的化学反应方程式;Fig. 4 is the chemical reaction equation that phosphonic acid end group hyperbranched dendrimers prepare;
图5本发明端双键星形聚合物的氢核磁共振(1H NMR)图谱;The proton nuclear magnetic resonance (1H NMR) spectrum of Fig. 5 terminal double bond star polymer of the present invention;
图6本发明端胺基星形树枝状聚合物的氢核磁共振(1H NMR)图谱;The proton nuclear magnetic resonance (1H NMR) spectrum of Fig. 6 amine-terminated star dendrimer of the present invention;
图7本发明膦酸端基超支化树枝状聚合物的氢核磁共振(1H NMR)图谱;The hydrogen nuclear magnetic resonance (1H NMR) spectrum of Fig. 7 phosphonic acid end group hyperbranched dendrimers of the present invention;
具体实施方式detailed description
以下提供本发明污水处理用网布及其制备方法的具体实施方式。The specific embodiments of the mesh cloth for sewage treatment and the preparation method thereof of the present invention are provided below.
实施例1Example 1
一种污水处理用网布,其特征在于,其通过经编机三维编织得到,网布的厚度为10mm,污水处理用网布透水量大于1800mm·s-1,顶破强度大于2000N。A mesh cloth for sewage treatment, characterized in that it is obtained by three-dimensional weaving by a warp knitting machine, the thickness of the mesh cloth is 10mm, the water permeability of the mesh cloth for sewage treatment is greater than 1800mm·s -1 , and the bursting strength is greater than 2000N.
一种污水处理用网布的制备方法,其特征在于,其具体步骤为:A kind of preparation method of mesh cloth for sewage treatment is characterized in that, its specific steps are:
(一)膦酸端基超支化树枝状聚合物的制备(1) Preparation of phosphonic acid-terminated hyperbranched dendrimers
膦酸端基超支化树枝状聚合物的结构式如图1所示:The structural formula of phosphonic acid terminal hyperbranched dendrimers is as shown in Figure 1:
所述的膦酸端基超支化树枝状聚合物的应用主要是应用于水体中重金属离子的吸附处理;The application of the phosphonic acid terminal hyperbranched dendritic polymer is mainly applied to the adsorption treatment of heavy metal ions in water;
具有高代数的钝化剂,由于分子中膦酸基团含量高,与重金属离子螯合作用强,单一分子金属离子的螯合数量大,形成的螯合基团分子空间体积大,因此耐酸碱稳定性好,抗迁移性好,尤其是在螯合作用过程中由于树枝状结构,对分子中的重金属具有非常优异的离子阻隔效应和过滤离子效应,因此设计越多的树枝结构以及越多的膦酸螯合基团,其螯合作用越强,且抗酸碱稳定性越强,因此本发明设计具有30个膦酸基团,且具有3主枝,9细枝的膦酸端基超支化树枝状聚合物对重金属的修复效果明显由于常规的金属钝化修复剂;Passivating agent with high algebra, due to the high content of phosphonic acid groups in the molecule, it has a strong chelation effect with heavy metal ions, and the chelation number of a single molecule of metal ions is large, and the formed chelating group has a large molecular space volume, so it is acid-resistant Good alkali stability and good migration resistance, especially in the process of chelation, due to the dendritic structure, it has very excellent ion barrier effect and filter ion effect on heavy metals in the molecule, so the more dendritic structures are designed and the more The stronger the phosphonic acid chelating group, the stronger the chelating effect, and the stronger the acid and alkali resistance stability, so the present invention has 30 phosphonic acid groups, and has 3 main branches, 9 twigs of phosphonic acid end groups The repair effect of hyperbranched dendrimers on heavy metals is obvious due to conventional metal passivation repair agents;
(a)端双键星形聚合物的制备(a) Preparation of terminal double bond star polymer
以三羟甲基丙烷三丙烯酸酯TMPTA和氨基三苯胺为原料,甲醇为溶剂,在带搅拌和冷凝回流的反应装置中,以氮气保护下,控制反应体系的温度为-10~5℃,先把氨基三苯胺的甲醇溶液分为三等份,然后分批向三羟甲基丙烷三丙烯酸酯TMPTA的甲醇溶液中滴加氨基三苯胺的甲醇溶液,在第一次滴加氨基三苯胺的甲醇溶液时,控制滴加过程的温度为-10~-5℃,滴加时间为30~60min,第二次滴加氨基三苯胺的甲醇溶液时,控制滴加过程的温度为-5~0℃,滴加时间为30~45min,第三次滴加氨基三苯胺的甲醇溶液时,控制滴加过程的温度为0~5℃,滴加时间为20~30min,每一次滴加氨基三苯胺的甲醇溶液后,反应体系移至25℃的温度下反应4~10h。氨基三苯胺的甲醇溶液全部滴加滴毕后,反应体系移至于25℃下,继续反应10~20h;反应完成后体系中会有金黄色产物析出,过滤,并用甲醇洗涤,淡金黄色产物在40℃真空干燥,得到金黄色的端双键星形聚合物,端双键星形聚合物的制备的化学反应方程式如图2所示:Using trimethylolpropane triacrylate TMPTA and aminotriphenylamine as raw materials, methanol as a solvent, in a reaction device with stirring and condensing reflux, under the protection of nitrogen, the temperature of the reaction system is controlled at -10 ~ 5 ° C, first Divide the methanol solution of aminotriphenylamine into three equal parts, then add the methanol solution of aminotriphenylamine dropwise in batches to the methanol solution of trimethylolpropane triacrylate TMPTA, and add the methanol solution of aminotriphenylamine dropwise for the first time When adding the solution, the temperature of the dropping process is controlled to be -10~-5°C, and the dropping time is 30~60 minutes. When the methanol solution of aminotriphenylamine is added dropwise for the second time, the temperature of the dropping process is controlled to be -5~0°C , the dropping time is 30-45min, when the methanol solution of aminotriphenylamine is added dropwise for the third time, the temperature of the dropping process is controlled to be 0-5°C, the dropping time is 20-30min, and the dropwise addition of aminotriphenylamine After methanol solution, the reaction system was moved to a temperature of 25°C for 4-10 hours. After the methanol solution of aminotriphenylamine has been added dropwise, the reaction system is moved to 25°C, and the reaction is continued for 10 to 20 hours; after the reaction is completed, a golden yellow product will precipitate in the system, filter and wash with methanol, and the light golden yellow product is in the Vacuum drying at 40°C to obtain a golden-yellow terminal double bond star polymer, the chemical reaction equation for the preparation of the terminal double bond star polymer is shown in Figure 2:
所述的三羟甲基丙烷三丙烯酸酯TMPTA和氨基三苯胺的摩尔比值为1:0.25;The molar ratio of described trimethylolpropane triacrylate TMPTA and aminotriphenylamine is 1:0.25;
所述的三羟甲基丙烷三丙烯酸酯甲醇溶液的摩尔分数为0.25mol/L;The mole fraction of described trimethylolpropane triacrylate methanol solution is 0.25mol/L;
所述的氨基三苯胺的甲醇溶液的摩尔分数为0.10mol/L;The mole fraction of the methanol solution of the aminotriphenylamine is 0.10mol/L;
(b)端胺基星形树枝状聚合物的合成(b) Synthesis of amine-terminated star dendrimers
在带有搅拌、回流冷凝管的反应器中,控制反应温度为0~5℃,在氮气保护及搅拌条件下,先加入乙二胺的甲醇溶液,然后再将步骤(a)制备的端双键星形聚合物加入,搅拌,混合均匀;然后在25℃下,反应20~30h,再在80~100℃的条件下减压蒸馏3~5h除去甲醇和多余的乙二胺,得到黄色粘稠产物,即为端胺基星形树枝状聚合物;端胺基星形树枝状聚合物的制备的化学反应方程式如图3所示:In the reactor with stirring and reflux condenser, the reaction temperature is controlled at 0-5°C, under the condition of nitrogen protection and stirring, the methanol solution of ethylenediamine is added first, and then the terminal bismuth prepared in step (a) is Add the bonded star polymer, stir, and mix well; then react at 25°C for 20-30 hours, and then distill under reduced pressure at 80-100°C for 3-5 hours to remove methanol and excess ethylenediamine to obtain yellow viscous Thick product is the amine-terminated star-shaped dendrimer; the chemical reaction equation for the preparation of the amine-terminated star-shaped dendrimer is as shown in Figure 3:
所述的乙二胺甲醇溶液中乙二胺的摩尔分数为0.5mol/L;The mole fraction of ethylenediamine in the described ethylenediamine methanol solution is 0.5mol/L;
所述的星形端双键树枝状聚合物与乙二胺的摩尔比值为1:10;The molar ratio of described star-end double bond dendritic polymer and ethylenediamine is 1:10;
乙二胺化合物来源广,成本低,制备过程中化学反应温和,制备工艺可控,因此制备过程中之成本低,利于工业化生产和大规模推广,对于提升产品的市场化具有非常大的成本优势。Ethylenediamine compounds have wide sources, low cost, mild chemical reaction in the preparation process, and controllable preparation process, so the cost in the preparation process is low, which is conducive to industrial production and large-scale promotion, and has a very large cost advantage for improving the marketization of products .
(c)膦酸端基超支化树枝状聚合物的合成(c) Synthesis of phosphonic acid-terminated hyperbranched dendrimers
将亚磷酸加入到浓盐酸中混合均匀,控制亚磷酸在浓盐酸中浓度为0.25~1.25mol/L,浓盐酸为10~12mol/L的盐酸溶液,然后在0~10℃条件下,滴加步骤(b)制备的端胺基星形树枝状聚合物的水溶液,端胺基星形树枝状聚合物的水溶液质量分数为20~45%,端胺基星形树枝状聚合物的水溶液滴加过程在30min内滴加完成;然后再在85~90℃的搅拌条件下,滴加甲醛水溶液,甲醛水溶液滴加完毕后反应体系,再在90℃条件下保温反应1~2小时,最后升温至105~110℃,回流2~4小时,回流结束后,关闭回流装置,打开HCl吸收瓶,浓缩反应混合液,浓缩温度105~110℃,浓缩至无HCl放出后,冷却至室温,得到固含量为25~55%的淡黄色透明液体的膦酸端基超支化树枝状聚合物的水溶液;膦酸端基超支化树枝状聚合物的制备的化学反应方程式如图4所示:Add phosphorous acid into concentrated hydrochloric acid and mix evenly, control the concentration of phosphorous acid in concentrated hydrochloric acid to be 0.25-1.25mol/L, concentrated hydrochloric acid is 10-12mol/L hydrochloric acid solution, and then add dropwise at 0-10°C The aqueous solution of the amine-terminated star-shaped dendrimer prepared in step (b), the aqueous solution mass fraction of the amine-terminated star-shaped dendrimer is 20 to 45%, and the aqueous solution of the amine-terminated star-shaped dendrimer is added dropwise The process is completed dropwise within 30 minutes; then, under the condition of stirring at 85-90°C, formaldehyde solution is added dropwise. 105-110°C, reflux for 2-4 hours, after the reflux, close the reflux device, open the HCl absorption bottle, concentrate the reaction mixture, the concentration temperature is 105-110°C, concentrate until no HCl is released, cool to room temperature, and obtain the solid content Be the aqueous solution of the phosphonic acid terminal hyperbranched dendritic polymer of 25~55% light yellow transparent liquid; The chemical reaction equation of the preparation of phosphonic acid terminal hyperbranched dendritic polymer is as shown in Figure 4:
(二)改性PVA纤维的制备(2) Preparation of modified PVA fiber
采用1799型号的PVA颗粒为原料,以水为溶剂,在90~98℃条件下进行溶解,控制PVA纺丝液的质量分数为15~20%,然后再加入上述步骤(1)合成的膦酸端基超支化树枝状聚合物,溶解后,进行湿法纺丝,以硫酸钠的水溶液为凝固液,经凝固液凝固,拉伸以及卷绕制备得到改性PVA纤维;Use 1799 type PVA particles as raw material, use water as solvent, dissolve at 90-98°C, control the mass fraction of PVA spinning solution to 15-20%, and then add the phosphonic acid synthesized in the above step (1) The end-group hyperbranched dendritic polymer is dissolved and wet-spun, and the aqueous solution of sodium sulfate is used as the coagulation liquid, and the modified PVA fiber is prepared by coagulating the coagulation liquid, stretching and winding;
所述的湿法纺丝速度为0.5~10m/min,纺丝液温度25~35℃;所述的凝固工艺采用两次凝固,第一道凝固过程中凝固液浓度为1.0~1.5g/L,第一道凝固过程中凝固温度为40~50℃,第一道凝固过程中纤维停留时间为12~18s;第二道凝固过程中凝固液浓度为0.9~1.3g/L,第二道凝固过程中凝固温度为85~95℃,第二道凝固过程中停留时间为10~15s;所述的拉伸工艺分为第一次湿拉伸,第二次干拉伸工艺,第一次湿拉伸过程中拉伸倍数为0.5~1.0倍,拉伸温度为120~150℃,所述的第二次干拉伸过程中伸倍数为1.5~2.0倍,拉伸温度为180~230℃;The wet spinning speed is 0.5-10m/min, and the spinning liquid temperature is 25-35°C; the coagulation process uses two coagulations, and the coagulation liquid concentration in the first coagulation process is 1.0-1.5g/L , the coagulation temperature in the first coagulation process is 40-50°C, the fiber residence time in the first coagulation process is 12-18s; the coagulation liquid concentration in the second coagulation process is 0.9-1.3g/L, The solidification temperature in the process is 85-95°C, and the residence time in the second solidification process is 10-15s; the stretching process is divided into the first wet stretching process, the second dry stretching process, and the first wet stretching process. During the stretching process, the stretching ratio is 0.5-1.0 times, and the stretching temperature is 120-150°C. In the second dry stretching process, the stretching ratio is 1.5-2.0 times, and the stretching temperature is 180-230°C;
PVA纤维具有优异的水溶胀性能,利于螯合作用的膦酸端基超支化树枝状聚合物与重金属离子的接触,从而提高网布对重金属离子的吸附作用,同时在湿法纺丝过程中,由于PVA纤维在凝固过程中形成大量的微孔,提升纤维表面的凹糟和微孔,从而提高膦酸端基超支化树枝状聚合物的与污水中的重金属接触表面,提升网布的吸附作用。PVA fiber has excellent water swelling properties, which is conducive to the contact of phosphonic acid-terminated hyperbranched dendrimers with heavy metal ions, thereby improving the adsorption of heavy metal ions by mesh cloth. At the same time, in the wet spinning process, Since the PVA fiber forms a large number of micropores during the solidification process, the depressions and micropores on the fiber surface are improved, thereby improving the contact surface of the phosphonic acid-terminated hyperbranched dendritic polymer with the heavy metals in the sewage, and improving the adsorption of the mesh. .
(三)污水处理用网布的制备(3) Preparation of mesh cloth for sewage treatment
采用德国进口KARL MAYER RD6DPLM型双针床经编机上生产试样,经过整经,编织和整理三个步骤制备得到所需的污水处理用网布;其中所述的整经过程中控制整经张力为0.08~0.18g/den,且编织过程中经经纱,纬纱和绑纱制造成网布,经纱均呈竖直状结构,纬纱均呈水平状结构,经纱和纬纱通过绑纱连接,经纱的密度为300~450根/cm,纬纱的密度为300~450根/cm,绑纱的密度为500~600根/cm,所述的经线为改性PVA纤维,所述的纬线为涤纶单丝,所述的绑纱为改性PVA纤维;The sample is produced on the KARL MAYER RD6DPLM double-needle bed warp knitting machine imported from Germany, and the required mesh for sewage treatment is prepared through three steps of warping, weaving and finishing; the warping tension is controlled during the warping process It is 0.08~0.18g/den, and the warp yarn, weft yarn and binding yarn are made into mesh during the weaving process. The warp yarn is in a vertical structure, and the weft yarn is in a horizontal structure. 300-450 yarns/cm, the weft yarn density is 300-450 yarns/cm, the binding yarn density is 500-600 yarns/cm, the warp is modified PVA fiber, and the weft is polyester monofilament, The binding yarn is modified PVA fiber;
图5为端双键星形聚合物的氢核磁共振(1H NMR)图谱;由端双键星形聚合物的分子结构式结合分子的1H-NMR图谱,分子中各类氢的化学位移如图所示,其中氨基三苯胺中苯环上氢的化学位移为6.18ppm(b)和6.24ppm(b),且分子中出现对称的双重分裂;氨基三苯胺上的中氨基的化学位移为4.03ppm(f),且氨基三苯胺与三羟甲基丙烷三丙烯酸酯发生了Michael加成反应,使分子中生产了新的化学键,出现了亚甲基的特征吸收峰,其对应的化学位移为2.46ppm(h)和3.43ppm(g),且图谱中对应的氨基三苯胺上的氨基特征吸收峰f的峰面积与亚甲基的特征吸收峰g和h的峰面积之比为1:2.00:2.03,对应的分子结构中各类氨基与亚甲基的基团结构比值即为1:2:2,同时图谱中5.76ppm(d),6.44ppm(a)和6.05ppm(c)对应的是分子中双键的化学位移,且化学位移6.05ppm(c)对应的峰面积与化学位移4.03ppm(f)对应峰面积的比值为3.08:1,因此对应的分子中国双键与仲氨基的基团数比值为3:1,因此氨基三苯胺与三羟甲基丙烷三丙烯酸酯中的一个双键发生了Michael加成反应,所合成的产物为设计的目标产物端双键星形聚合物。Figure 5 is the hydrogen nuclear magnetic resonance (1H NMR) spectrum of the terminal double-bond star polymer; the molecular structural formula of the terminal double-bond star polymer combines the 1H-NMR spectrum of the molecule, and the chemical shifts of various hydrogens in the molecule are shown in the figure Show, wherein the chemical shift of hydrogen on the benzene ring in the aminotriphenylamine is 6.18ppm (b) and 6.24ppm (b), and symmetrical double split occurs in the molecule; The chemical shift of the amino group on the aminotriphenylamine is 4.03ppm ( f), and the Michael addition reaction of aminotriphenylamine and trimethylolpropane triacrylate produced new chemical bonds in the molecule, and the characteristic absorption peak of methylene appeared, and its corresponding chemical shift was 2.46ppm (h) and 3.43ppm (g), and the ratio of the peak area of the amino characteristic absorption peak f on the corresponding aminotriphenylamine in the spectrum to the peak area of the characteristic absorption peak g and h of the methylene group is 1:2.00:2.03 , the ratio of the group structures of various amino groups to methylene groups in the corresponding molecular structure is 1:2:2, and 5.76ppm(d), 6.44ppm(a) and 6.05ppm(c) in the spectrum correspond to molecules The chemical shift of the double bond in the middle, and the ratio of the peak area corresponding to the chemical shift 6.05ppm (c) to the peak area corresponding to the chemical shift 4.03ppm (f) is 3.08:1, so the corresponding molecular Chinese double bond and secondary amino group The numerical ratio is 3:1, so a Michael addition reaction has taken place between aminotriphenylamine and a double bond in trimethylolpropane triacrylate, and the synthesized product is the designed target product terminal double bond star polymer.
图6为端胺基星形树枝状聚合物的氢核磁共振(1H NMR)图谱;由端胺基星形树枝状聚合物的核磁图谱可知,分子中的双键与乙二胺发生了Michael加成反应,使双键全部消失,因此图谱中为检测到双键的特征吸收峰,而Michael加成反应生成了亚甲基,即为使双键的化学位移由5.76ppm(d),6.44ppm(a)和6.05ppm(c)转移到2.97ppm(a’,d’)和2.36ppm(c’),并且分子无双键的特征吸收峰,同时分子中检测到了乙二胺分子结构中的氨基化学位移2.05ppm(h)以及乙基的化学位移2.80ppm,2.77ppm(j)的特征吸收峰。因此说明了星形端双键树枝状聚合物元乙二胺发生Michael加成反应,反应按设计方向进行。Figure 6 is the hydrogen nuclear magnetic resonance (1H NMR) spectrum of the amine-terminated star-shaped dendrimer; as can be seen from the NMR spectrum of the amine-terminated star-shaped dendrimer, Michael addition has occurred between the double bond in the molecule and ethylenediamine Therefore, the characteristic absorption peak of the double bond is detected in the spectrum, and the Michael addition reaction generates methylene, that is, the chemical shift of the double bond is changed from 5.76ppm(d) to 6.44ppm (a) and 6.05ppm (c) shifted to 2.97ppm (a', d') and 2.36ppm (c'), and the molecule has no characteristic absorption peaks of double bonds, and the amino group in the molecular structure of ethylenediamine is detected in the molecule Chemical shift 2.05ppm (h) and ethyl chemical shift 2.80ppm, characteristic absorption peak of 2.77ppm (j). Therefore, it is shown that the Michael addition reaction of ethylenediamine in the star-shaped end double-bond dendritic polymer occurs, and the reaction proceeds in the designed direction.
图7为膦酸端基超支化树枝状聚合物的氢核磁共振(1H NMR)图谱;亚膦酸与甲醛在酸性条件下发生加成反应,使反应生成亚甲基的特征吸收峰,分子中产生的亚膦酸的羟基特征吸收峰为1.89ppm(m),且没有检测到氨基分子中的特征吸收峰;同时分子中图谱中端胺基星形树枝状聚合物的氨基三苯胺上的仲氨基与亚膦酸与甲醛反应生产的亚甲基为3.41ppm(i),端胺基星形树枝状聚合物的氨乙基氨基上的氨基与亚膦酸与甲醛反应生产的亚甲基的化学位移为2.44ppm(k),且i的峰面积与k的峰面积比值为0.34:3.06,既有对应的不同化学位移的亚甲基的个数比为1:9,因此证明了所合成的膦酸端基超支化树枝状聚合物分子中氨基均匀亚膦酸发生了反应,生产了具有亚膦酸结构的超支化聚合物分子,即为反应按照设计方向进行,生成了所需的膦酸端基超支化树枝状聚合物。Fig. 7 is the proton nuclear magnetic resonance (1H NMR) collection of spectra of phosphonic acid terminal hyperbranched dendrimers; Phosphonous acid and formaldehyde take place addition reaction under acidic conditions, make reaction generate the characteristic absorption peak of methylene, in the molecule The hydroxyl characteristic absorption peak of the phosphonous acid that produces is 1.89ppm (m), and does not detect the characteristic absorption peak in the amino molecule; The methylene group produced by the reaction of amino group with phosphonous acid and formaldehyde is 3.41ppm (i), the amino group on the aminoethyl amino group of the amino-terminated star dendritic polymer reacts with phosphonous acid and formaldehyde to produce the methylene group The chemical shift is 2.44ppm(k), and the ratio of the peak area of i to the peak area of k is 0.34:3.06, and the number ratio of the corresponding methylene groups with different chemical shifts is 1:9, thus proving that the synthesized The homogeneous phosphonous acid in the phosphonic acid-terminated hyperbranched dendrimer molecule reacts to produce a hyperbranched polymer molecule with a phosphonous acid structure, that is, the reaction proceeds according to the design direction and generates the required phosphine Acid-terminated hyperbranched dendrimers.
实施例2Example 2
一种污水处理用网布,其特征在于,其通过经编机三维编织得到,网布的厚度为50mm,污水处理用网布透水量大于1800mm·s-1,顶破强度大于2000N。A mesh cloth for sewage treatment, characterized in that it is obtained by three-dimensional weaving by a warp knitting machine, the thickness of the mesh cloth is 50mm, the water permeability of the mesh cloth for sewage treatment is greater than 1800mm·s -1 , and the bursting strength is greater than 2000N.
一种污水处理用网布的制备方法,其特征在于,其具体步骤为:A kind of preparation method of mesh cloth for sewage treatment is characterized in that, its specific steps are:
(一)膦酸端基超支化树枝状聚合物的制备(1) Preparation of phosphonic acid-terminated hyperbranched dendrimers
膦酸端基超支化树枝状聚合物的结构式如图1所示:The structural formula of phosphonic acid terminal hyperbranched dendrimers is as shown in Figure 1:
所述的膦酸端基超支化树枝状聚合物的应用主要是应用于水体中重金属离子的吸附处理;The application of the phosphonic acid terminal hyperbranched dendritic polymer is mainly applied to the adsorption treatment of heavy metal ions in water;
具有高代数的钝化剂,由于分子中膦酸基团含量高,与重金属离子螯合作用强,单一分子金属离子的螯合数量大,形成的螯合基团分子空间体积大,因此耐酸碱稳定性好,抗迁移性好,尤其是在螯合作用过程中由于树枝状结构,对分子中的重金属具有非常优异的离子阻隔效应和过滤离子效应,因此设计越多的树枝结构以及越多的膦酸螯合基团,其螯合作用越强,且抗酸碱稳定性越强,因此本发明设计具有30个膦酸基团,且具有3主枝,9细枝的膦酸端基超支化树枝状聚合物对重金属的修复效果明显由于常规的金属钝化修复剂;Passivating agent with high algebra, due to the high content of phosphonic acid groups in the molecule, it has a strong chelation effect with heavy metal ions, and the chelation number of a single molecule of metal ions is large, and the formed chelating group has a large molecular space volume, so it is acid-resistant Good alkali stability and good migration resistance, especially in the process of chelation, due to the dendritic structure, it has very excellent ion barrier effect and filter ion effect on heavy metals in the molecule, so the more dendritic structures are designed and the more The stronger the phosphonic acid chelating group, the stronger the chelating effect, and the stronger the acid and alkali resistance stability, so the present invention has 30 phosphonic acid groups, and has 3 main branches, 9 twigs of phosphonic acid end groups The repair effect of hyperbranched dendrimers on heavy metals is obvious due to conventional metal passivation repair agents;
(a)端双键星形聚合物的制备(a) Preparation of terminal double bond star polymer
以三羟甲基丙烷三丙烯酸酯TMPTA和氨基三苯胺为原料,甲醇为溶剂,在带搅拌和冷凝回流的反应装置中,以氮气保护下,控制反应体系的温度为-10~5℃,先把氨基三苯胺的甲醇溶液分为三等份,然后分批向三羟甲基丙烷三丙烯酸酯TMPTA的甲醇溶液中滴加氨基三苯胺的甲醇溶液,在第一次滴加氨基三苯胺的甲醇溶液时,控制滴加过程的温度为-10~-5℃,滴加时间为30~60min,第二次滴加氨基三苯胺的甲醇溶液时,控制滴加过程的温度为-5~0℃,滴加时间为30~45min,第三次滴加氨基三苯胺的甲醇溶液时,控制滴加过程的温度为0~5℃,滴加时间为20~30min,每一次滴加氨基三苯胺的甲醇溶液后,反应体系移至25℃的温度下反应4~10h。氨基三苯胺的甲醇溶液全部滴加滴毕后,反应体系移至于25℃下,继续反应10~20h;反应完成后体系中会有金黄色产物析出,过滤,并用甲醇洗涤,淡金黄色产物在40℃真空干燥,得到金黄色的端双键星形聚合物,端双键星形聚合物的制备的化学反应方程式如图2所示:Using trimethylolpropane triacrylate TMPTA and aminotriphenylamine as raw materials, methanol as a solvent, in a reaction device with stirring and condensing reflux, under the protection of nitrogen, the temperature of the reaction system is controlled at -10 ~ 5 ° C, first Divide the methanol solution of aminotriphenylamine into three equal parts, then add the methanol solution of aminotriphenylamine dropwise in batches to the methanol solution of trimethylolpropane triacrylate TMPTA, and add the methanol solution of aminotriphenylamine dropwise for the first time When adding the solution, the temperature of the dropping process is controlled to be -10~-5°C, and the dropping time is 30~60 minutes. When the methanol solution of aminotriphenylamine is added dropwise for the second time, the temperature of the dropping process is controlled to be -5~0°C , the dropping time is 30-45min, when the methanol solution of aminotriphenylamine is added dropwise for the third time, the temperature of the dropping process is controlled to be 0-5°C, the dropping time is 20-30min, and the dropwise addition of aminotriphenylamine After methanol solution, the reaction system was moved to a temperature of 25°C for 4-10 hours. After the methanol solution of aminotriphenylamine has been added dropwise, the reaction system is moved to 25°C, and the reaction is continued for 10 to 20 hours; after the reaction is completed, a golden yellow product will precipitate in the system, filter and wash with methanol, and the light golden yellow product is in the Vacuum drying at 40°C to obtain a golden-yellow terminal double bond star polymer, the chemical reaction equation for the preparation of the terminal double bond star polymer is shown in Figure 2:
所述的三羟甲基丙烷三丙烯酸酯TMPTA和氨基三苯胺的摩尔比值为1:0.30;The molar ratio of described trimethylolpropane triacrylate TMPTA and aminotriphenylamine is 1:0.30;
所述的三羟甲基丙烷三丙烯酸酯甲醇溶液的摩尔分数为1.25mol/L;The mole fraction of described trimethylolpropane triacrylate methanol solution is 1.25mol/L;
所述的氨基三苯胺的甲醇溶液的摩尔分数为1.50mol/L;The molar fraction of the methanol solution of the aminotriphenylamine is 1.50mol/L;
(b)端胺基星形树枝状聚合物的合成(b) Synthesis of amine-terminated star dendrimers
在带有搅拌、回流冷凝管的反应器中,控制反应温度为0~5℃,在氮气保护及搅拌条件下,先加入乙二胺的甲醇溶液,然后再将步骤(a)制备的端双键星形聚合物加入,搅拌,混合均匀;然后在25℃下,反应20~30h,再在80~100℃的条件下减压蒸馏3~5h除去甲醇和多余的乙二胺,得到黄色粘稠产物,即为端胺基星形树枝状聚合物;端胺基星形树枝状聚合物的制备的化学反应方程式如图3所示:In the reactor with stirring and reflux condenser, the reaction temperature is controlled at 0-5°C, under the condition of nitrogen protection and stirring, the methanol solution of ethylenediamine is added first, and then the terminal bismuth prepared in step (a) is Add the bonded star polymer, stir, and mix well; then react at 25°C for 20-30 hours, and then distill under reduced pressure at 80-100°C for 3-5 hours to remove methanol and excess ethylenediamine to obtain yellow viscous Thick product is the amine-terminated star-shaped dendrimer; the chemical reaction equation for the preparation of the amine-terminated star-shaped dendrimer is as shown in Figure 3:
所述的乙二胺甲醇溶液中乙二胺的摩尔分数为5.0mol/L;The molar fraction of ethylenediamine in the described ethylenediamine methanol solution is 5.0mol/L;
所述的星形端双键树枝状聚合物与乙二胺的摩尔比值为1:12;The molar ratio of described star-shaped end double bond dendritic polymer and ethylenediamine is 1:12;
乙二胺化合物来源广,成本低,制备过程中化学反应温和,制备工艺可控,因此制备过程中之成本低,利于工业化生产和大规模推广,对于提升产品的市场化具有非常大的成本优势。Ethylenediamine compounds have wide sources, low cost, mild chemical reaction in the preparation process, and controllable preparation process, so the cost in the preparation process is low, which is conducive to industrial production and large-scale promotion, and has a very large cost advantage for improving the marketization of products .
(c)膦酸端基超支化树枝状聚合物的合成(c) Synthesis of phosphonic acid-terminated hyperbranched dendrimers
将亚磷酸加入到浓盐酸中混合均匀,控制亚磷酸在浓盐酸中浓度为0.25~1.25mol/L,浓盐酸为10~12mol/L的盐酸溶液,然后在0~10℃条件下,滴加步骤(b)制备的端胺基星形树枝状聚合物的水溶液,端胺基星形树枝状聚合物的水溶液质量分数为20~45%,端胺基星形树枝状聚合物的水溶液滴加过程在30min内滴加完成;然后再在85~90℃的搅拌条件下,滴加甲醛水溶液,甲醛水溶液滴加完毕后反应体系,再在90℃条件下保温反应1~2小时,最后升温至105~110℃,回流2~4小时,回流结束后,关闭回流装置,打开HCl吸收瓶,浓缩反应混合液,浓缩温度105~110℃,浓缩至无HCl放出后,冷却至室温,得到固含量为25~55%的淡黄色透明液体的膦酸端基超支化树枝状聚合物的水溶液;膦酸端基超支化树枝状聚合物的制备的化学反应方程式如图4所示:Add phosphorous acid into concentrated hydrochloric acid and mix evenly, control the concentration of phosphorous acid in concentrated hydrochloric acid to be 0.25-1.25mol/L, concentrated hydrochloric acid is 10-12mol/L hydrochloric acid solution, and then add dropwise at 0-10°C The aqueous solution of the amine-terminated star-shaped dendrimer prepared in step (b), the aqueous solution mass fraction of the amine-terminated star-shaped dendrimer is 20 to 45%, and the aqueous solution of the amine-terminated star-shaped dendrimer is added dropwise The process is completed dropwise within 30 minutes; then, under the condition of stirring at 85-90°C, formaldehyde solution is added dropwise. 105-110°C, reflux for 2-4 hours, after the reflux, close the reflux device, open the HCl absorption bottle, concentrate the reaction mixture, the concentration temperature is 105-110°C, concentrate until no HCl is released, cool to room temperature, and obtain the solid content Be the aqueous solution of the phosphonic acid terminal hyperbranched dendritic polymer of 25~55% light yellow transparent liquid; The chemical reaction equation of the preparation of phosphonic acid terminal hyperbranched dendritic polymer is as shown in Figure 4:
(二)改性PVA纤维的制备(2) Preparation of modified PVA fiber
采用1799型号的PVA颗粒为原料,以水为溶剂,在90~98℃条件下进行溶解,控制PVA纺丝液的质量分数为15~20%,然后再加入上述步骤(1)合成的膦酸端基超支化树枝状聚合物,溶解后,进行湿法纺丝,以硫酸钠的水溶液为凝固液,经凝固液凝固,拉伸以及卷绕制备得到改性PVA纤维;Use 1799 type PVA particles as raw material, use water as solvent, dissolve at 90-98°C, control the mass fraction of PVA spinning solution to 15-20%, and then add the phosphonic acid synthesized in the above step (1) The end-group hyperbranched dendritic polymer is dissolved and wet-spun, and the aqueous solution of sodium sulfate is used as the coagulation liquid, and the modified PVA fiber is prepared by coagulating the coagulation liquid, stretching and winding;
所述的湿法纺丝速度为0.5~10m/min,纺丝液温度25~35℃;所述的凝固工艺采用两次凝固,第一道凝固过程中凝固液浓度为1.0~1.5g/L,第一道凝固过程中凝固温度为40~50℃,第一道凝固过程中纤维停留时间为12~18s;第二道凝固过程中凝固液浓度为0.9~1.3g/L,第二道凝固过程中凝固温度为85~95℃,第二道凝固过程中停留时间为10~15s;所述的拉伸工艺分为第一次湿拉伸,第二次干拉伸工艺,第一次湿拉伸过程中拉伸倍数为0.5~1.0倍,拉伸温度为120~150℃,所述的第二次干拉伸过程中伸倍数为1.5~2.0倍,拉伸温度为180~230℃;The wet spinning speed is 0.5-10m/min, and the spinning liquid temperature is 25-35°C; the coagulation process uses two coagulations, and the coagulation liquid concentration in the first coagulation process is 1.0-1.5g/L , the coagulation temperature in the first coagulation process is 40-50°C, the fiber residence time in the first coagulation process is 12-18s; the coagulation liquid concentration in the second coagulation process is 0.9-1.3g/L, The solidification temperature in the process is 85-95°C, and the residence time in the second solidification process is 10-15s; the stretching process is divided into the first wet stretching process, the second dry stretching process, and the first wet stretching process. During the stretching process, the stretching ratio is 0.5-1.0 times, and the stretching temperature is 120-150°C. In the second dry stretching process, the stretching ratio is 1.5-2.0 times, and the stretching temperature is 180-230°C;
PVA纤维具有优异的水溶胀性能,利于螯合作用的膦酸端基超支化树枝状聚合物与重金属离子的接触,从而提高网布对重金属离子的吸附作用,同时在湿法纺丝过程中,由于PVA纤维在凝固过程中形成大量的微孔,提升纤维表面的凹糟和微孔,从而提高膦酸端基超支化树枝状聚合物的与污水中的重金属接触表面,提升网布的吸附作用。PVA fiber has excellent water swelling properties, which is conducive to the contact of phosphonic acid-terminated hyperbranched dendrimers with heavy metal ions, thereby improving the adsorption of heavy metal ions by mesh cloth. At the same time, in the wet spinning process, Since the PVA fiber forms a large number of micropores during the solidification process, the depressions and micropores on the fiber surface are improved, thereby improving the contact surface of the phosphonic acid-terminated hyperbranched dendritic polymer with the heavy metals in the sewage, and improving the adsorption of the mesh. .
(三)污水处理用网布的制备(3) Preparation of mesh cloth for sewage treatment
采用德国进口KARL MAYER RD6DPLM型双针床经编机上生产试样,经过整经,编织和整理三个步骤制备得到所需的污水处理用网布;其中所述的整经过程中控制整经张力为0.08~0.18g/den,且编织过程中经经纱,纬纱和绑纱制造成网布,经纱均呈竖直状结构,纬纱均呈水平状结构,经纱和纬纱通过绑纱连接,经纱的密度为450根/cm,纬纱的密度为450根/cm,绑纱的密度为600根/cm,所述的经线为改性PVA纤维,所述的纬线为涤纶单丝,所述的绑纱为改性PVA纤维。The sample is produced on the KARL MAYER RD6DPLM double-needle bed warp knitting machine imported from Germany, and the required mesh for sewage treatment is prepared through three steps of warping, weaving and finishing; the warping tension is controlled during the warping process It is 0.08~0.18g/den, and the warp yarn, weft yarn and binding yarn are made into mesh during the weaving process. The warp yarn is in a vertical structure, and the weft yarn is in a horizontal structure. 450 threads/cm, the density of the weft yarn is 450 threads/cm, the density of the binding yarn is 600 threads/cm, the warp thread is a modified PVA fiber, the weft thread is a polyester monofilament, and the binding thread is Modified PVA fiber.
以上所述仅是本发明的优选实施方式,应当指出,对于本技术领域的普通技术人员,在不脱离本发明构思的前提下,还可以做出若干改进和润饰,这些改进和润饰也应视为本发明的保护范围内。The above is only a preferred embodiment of the present invention, it should be pointed out that for those of ordinary skill in the art, without departing from the concept of the present invention, some improvements and modifications can also be made, and these improvements and modifications should also be considered Within the protection scope of the present invention.
Claims (1)
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201610110793.1A CN105536742B (en) | 2016-02-29 | 2016-02-29 | A kind of sewage disposal screen cloth and preparation method thereof |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201610110793.1A CN105536742B (en) | 2016-02-29 | 2016-02-29 | A kind of sewage disposal screen cloth and preparation method thereof |
Publications (2)
Publication Number | Publication Date |
---|---|
CN105536742A CN105536742A (en) | 2016-05-04 |
CN105536742B true CN105536742B (en) | 2017-12-15 |
Family
ID=55816580
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201610110793.1A Expired - Fee Related CN105536742B (en) | 2016-02-29 | 2016-02-29 | A kind of sewage disposal screen cloth and preparation method thereof |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN105536742B (en) |
Families Citing this family (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP7514842B2 (en) * | 2019-01-17 | 2024-07-11 | リサーチ トライアングル インスティテュート | Polyamine phosphorus dendrimer materials for metal sequestration |
CN113214836A (en) * | 2020-11-10 | 2021-08-06 | 江苏索力得新材料集团有限公司 | Preparation method of functional additive for agricultural and forestry soil remediation and treatment |
Citations (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN102806021A (en) * | 2012-07-27 | 2012-12-05 | 东华大学 | Method for preparing cellulose nanocrystal/electrostatic spinning nanofiber filter film |
CN103265696A (en) * | 2013-05-07 | 2013-08-28 | 同济大学 | Dendrimer with pentaerythritol core terminal and phosphonic acid terminal group, preparation method and uses thereof |
CN103554510A (en) * | 2013-11-02 | 2014-02-05 | 广西民族大学 | Amino-terminated modified cellulose, and preparation method and application thereof |
-
2016
- 2016-02-29 CN CN201610110793.1A patent/CN105536742B/en not_active Expired - Fee Related
Patent Citations (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN102806021A (en) * | 2012-07-27 | 2012-12-05 | 东华大学 | Method for preparing cellulose nanocrystal/electrostatic spinning nanofiber filter film |
CN103265696A (en) * | 2013-05-07 | 2013-08-28 | 同济大学 | Dendrimer with pentaerythritol core terminal and phosphonic acid terminal group, preparation method and uses thereof |
CN103554510A (en) * | 2013-11-02 | 2014-02-05 | 广西民族大学 | Amino-terminated modified cellulose, and preparation method and application thereof |
Non-Patent Citations (2)
Title |
---|
"端丙烯酸酯基及端氨基树枝状大分子的合成、表征及功能化";徐冬梅;《中国优秀博硕士学位论文全文数据库(博士)工程科技Ⅰ辑》;20040315(第1期);B014-33 * |
"经编间隔织物的开发与应用";郭昌盛等;《山东纺织科技》;20150131(第1期);第13-18页 * |
Also Published As
Publication number | Publication date |
---|---|
CN105536742A (en) | 2016-05-04 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN109021264B (en) | Preparation method of MOFs-chitosan nanofiber composite membrane | |
CN101357324B (en) | A kind of amidoxime spherical lignin chelating adsorption resin and its preparation process | |
CN103556298B (en) | Method for preparing amidoximation polyacrylonitrile latex/polyvinyl alcohol composite chelate fiber | |
CN108745320B (en) | Preparation method of nano-gelatin/polymer composite fiber tape based on seawater extraction of uranium | |
CN109012638B (en) | Preparation method of carboxylated hierarchical porous cellulose adsorption balls | |
TW200927769A (en) | Adsorptive ion-exchange material and method of filtering heavy metal ions using the material | |
CN103406153A (en) | Method for preparing cellulose-based macroporous gel compound Cu2O visible-light-driven photocatalyst | |
CN105195110A (en) | Amine modified fibrous membrane adsorption material and preparation method thereof | |
CN105536742B (en) | A kind of sewage disposal screen cloth and preparation method thereof | |
CN106474823A (en) | A kind of feather nonwoven composite acupuncture filtering material as height containing Treatment of Sludge and preparation method thereof | |
CN111074363A (en) | Superfine polyester fluorescent fiber with high adsorption function and preparation method thereof | |
CN112604507B (en) | Preparation method of high-flux dye separation nanofiltration membrane | |
CN100999545B (en) | A method for recovering sericin protein by ion exchange | |
CN100430535C (en) | A kind of alginate/polyvinyl alcohol composite fiber and its preparation method | |
CN105688864B (en) | One heavy metal species processing screen cloth and preparation method thereof | |
CN112044406A (en) | A kind of method for preparing cotton stalk skin microcrystalline cellulose/graphene oxide aerogel fiber | |
CN113914094B (en) | Preparation method of calcium carbonate/polymer nanofiber composite membrane | |
CN115748094A (en) | Preparation method of nanofiber membrane for heavy metal adsorption | |
CN105986328B (en) | The preparation method of acrylic fibers high strength industrial filament | |
CN108866824A (en) | A kind of polyacrylonitrile-radical nano fibrous membrane and preparation method and application | |
CN118978694A (en) | A cross-linked polymer based on calixarene and its synthesis method and application | |
CN113174701A (en) | Preparation method of polyacrylonitrile-based electrospinning reinforced membrane material | |
CN111533207A (en) | Adsorbent for printing and dyeing wastewater treatment and preparation method thereof | |
CN116239853A (en) | Preparation method of composite nano microsphere and application of composite nano microsphere in preparation of nanofiber membrane | |
CN115573096A (en) | Preparation method of polyurethane nanofiber membrane |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
C06 | Publication | ||
PB01 | Publication | ||
C10 | Entry into substantive examination | ||
SE01 | Entry into force of request for substantive examination | ||
GR01 | Patent grant | ||
GR01 | Patent grant | ||
CF01 | Termination of patent right due to non-payment of annual fee | ||
CF01 | Termination of patent right due to non-payment of annual fee |
Granted publication date: 20171215 |