CN101319478A - Preparation method and application of a composite paper-based material with functions of adsorbing and degrading organic matter - Google Patents
Preparation method and application of a composite paper-based material with functions of adsorbing and degrading organic matter Download PDFInfo
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- 239000000463 material Substances 0.000 title claims abstract description 33
- 239000002131 composite material Substances 0.000 title claims abstract description 32
- 238000002360 preparation method Methods 0.000 title claims abstract description 17
- 239000005416 organic matter Substances 0.000 title claims abstract 4
- 230000000593 degrading effect Effects 0.000 title abstract description 3
- 239000000843 powder Substances 0.000 claims abstract description 33
- 239000000725 suspension Substances 0.000 claims abstract description 17
- 229910044991 metal oxide Inorganic materials 0.000 claims abstract description 16
- 150000004706 metal oxides Chemical class 0.000 claims abstract description 16
- 239000003463 adsorbent Substances 0.000 claims abstract description 13
- 230000014759 maintenance of location Effects 0.000 claims abstract description 10
- 229910021536 Zeolite Inorganic materials 0.000 claims abstract description 9
- HNPSIPDUKPIQMN-UHFFFAOYSA-N dioxosilane;oxo(oxoalumanyloxy)alumane Chemical compound O=[Si]=O.O=[Al]O[Al]=O HNPSIPDUKPIQMN-UHFFFAOYSA-N 0.000 claims abstract description 9
- 239000010457 zeolite Substances 0.000 claims abstract description 9
- 238000013033 photocatalytic degradation reaction Methods 0.000 claims abstract description 8
- 230000003197 catalytic effect Effects 0.000 claims abstract description 4
- 238000001179 sorption measurement Methods 0.000 claims abstract description 4
- GWEVSGVZZGPLCZ-UHFFFAOYSA-N Titan oxide Chemical group O=[Ti]=O GWEVSGVZZGPLCZ-UHFFFAOYSA-N 0.000 claims description 28
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 18
- 229920001131 Pulp (paper) Polymers 0.000 claims description 14
- 239000000203 mixture Substances 0.000 claims description 12
- 239000004408 titanium dioxide Substances 0.000 claims description 12
- 229920002401 polyacrylamide Polymers 0.000 claims description 9
- 125000002091 cationic group Chemical group 0.000 claims description 8
- 239000000126 substance Substances 0.000 claims description 8
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 claims description 7
- XLOMVQKBTHCTTD-UHFFFAOYSA-N Zinc monoxide Chemical compound [Zn]=O XLOMVQKBTHCTTD-UHFFFAOYSA-N 0.000 claims description 7
- 239000000919 ceramic Substances 0.000 claims description 6
- 239000000835 fiber Substances 0.000 claims description 6
- QPLDLSVMHZLSFG-UHFFFAOYSA-N Copper oxide Chemical compound [Cu]=O QPLDLSVMHZLSFG-UHFFFAOYSA-N 0.000 claims description 5
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 claims description 4
- 229920002472 Starch Polymers 0.000 claims description 4
- 239000003365 glass fiber Substances 0.000 claims description 4
- 229920000642 polymer Polymers 0.000 claims description 4
- 239000008107 starch Substances 0.000 claims description 4
- 235000019698 starch Nutrition 0.000 claims description 4
- 239000010902 straw Substances 0.000 claims description 4
- 239000011787 zinc oxide Substances 0.000 claims description 4
- 235000017166 Bambusa arundinacea Nutrition 0.000 claims description 3
- 235000017491 Bambusa tulda Nutrition 0.000 claims description 3
- 235000015334 Phyllostachys viridis Nutrition 0.000 claims description 3
- 239000011425 bamboo Substances 0.000 claims description 3
- 239000003610 charcoal Substances 0.000 claims description 3
- 238000010521 absorption reaction Methods 0.000 claims 8
- 230000015556 catabolic process Effects 0.000 claims 8
- 238000006731 degradation reaction Methods 0.000 claims 8
- 239000003795 chemical substances by application Substances 0.000 claims 4
- GFLJTEHFZZNCTR-UHFFFAOYSA-N 3-prop-2-enoyloxypropyl prop-2-enoate Chemical group C=CC(=O)OCCCOC(=O)C=C GFLJTEHFZZNCTR-UHFFFAOYSA-N 0.000 claims 1
- 241001330002 Bambuseae Species 0.000 claims 1
- 241001343274 Dichrostachys spicata Species 0.000 claims 1
- 229910052799 carbon Inorganic materials 0.000 claims 1
- 230000001413 cellular effect Effects 0.000 claims 1
- 229960004643 cupric oxide Drugs 0.000 claims 1
- 238000010790 dilution Methods 0.000 claims 1
- 239000012895 dilution Substances 0.000 claims 1
- 229920000371 poly(diallyldimethylammonium chloride) polymer Polymers 0.000 claims 1
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- NLXLAEXVIDQMFP-UHFFFAOYSA-N Ammonia chloride Chemical compound [NH4+].[Cl-] NLXLAEXVIDQMFP-UHFFFAOYSA-N 0.000 description 8
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- 239000011087 paperboard Substances 0.000 description 8
- 238000000034 method Methods 0.000 description 6
- 235000019270 ammonium chloride Nutrition 0.000 description 4
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- UHOVQNZJYSORNB-UHFFFAOYSA-N Benzene Chemical compound C1=CC=CC=C1 UHOVQNZJYSORNB-UHFFFAOYSA-N 0.000 description 3
- WSFSSNUMVMOOMR-UHFFFAOYSA-N Formaldehyde Chemical compound O=C WSFSSNUMVMOOMR-UHFFFAOYSA-N 0.000 description 3
- 239000005909 Kieselgur Substances 0.000 description 3
- 235000011609 Pinus massoniana Nutrition 0.000 description 3
- 241000018650 Pinus massoniana Species 0.000 description 3
- YXFVVABEGXRONW-UHFFFAOYSA-N Toluene Chemical compound CC1=CC=CC=C1 YXFVVABEGXRONW-UHFFFAOYSA-N 0.000 description 3
- 230000005855 radiation Effects 0.000 description 3
- VTYYLEPIZMXCLO-UHFFFAOYSA-L Calcium carbonate Chemical compound [Ca+2].[O-]C([O-])=O VTYYLEPIZMXCLO-UHFFFAOYSA-L 0.000 description 2
- VEXZGXHMUGYJMC-UHFFFAOYSA-M Chloride anion Chemical compound [Cl-] VEXZGXHMUGYJMC-UHFFFAOYSA-M 0.000 description 2
- 239000005751 Copper oxide Substances 0.000 description 2
- 244000166124 Eucalyptus globulus Species 0.000 description 2
- OFBQJSOFQDEBGM-UHFFFAOYSA-N Pentane Chemical compound CCCCC OFBQJSOFQDEBGM-UHFFFAOYSA-N 0.000 description 2
- 244000082204 Phyllostachys viridis Species 0.000 description 2
- 241000209140 Triticum Species 0.000 description 2
- 235000021307 Triticum Nutrition 0.000 description 2
- PNEYBMLMFCGWSK-UHFFFAOYSA-N aluminium oxide Inorganic materials [O-2].[O-2].[O-2].[Al+3].[Al+3] PNEYBMLMFCGWSK-UHFFFAOYSA-N 0.000 description 2
- 229910000431 copper oxide Inorganic materials 0.000 description 2
- 238000005516 engineering process Methods 0.000 description 2
- 238000000227 grinding Methods 0.000 description 2
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- 229910021421 monocrystalline silicon Inorganic materials 0.000 description 2
- 230000001699 photocatalysis Effects 0.000 description 2
- 241000878003 Dendrolycopodium obscurum Species 0.000 description 1
- 235000014676 Phragmites communis Nutrition 0.000 description 1
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- 239000004115 Sodium Silicate Substances 0.000 description 1
- 239000000853 adhesive Substances 0.000 description 1
- 230000001070 adhesive effect Effects 0.000 description 1
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- 229910010272 inorganic material Inorganic materials 0.000 description 1
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- 229910052500 inorganic mineral Inorganic materials 0.000 description 1
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- 229910052751 metal Inorganic materials 0.000 description 1
- 239000002184 metal Substances 0.000 description 1
- WSFSSNUMVMOOMR-NJFSPNSNSA-N methanone Chemical compound O=[14CH2] WSFSSNUMVMOOMR-NJFSPNSNSA-N 0.000 description 1
- 239000011707 mineral Substances 0.000 description 1
- 239000011268 mixed slurry Substances 0.000 description 1
- 239000003960 organic solvent Substances 0.000 description 1
- 238000013032 photocatalytic reaction Methods 0.000 description 1
- 239000002994 raw material Substances 0.000 description 1
- 238000007493 shaping process Methods 0.000 description 1
- NTHWMYGWWRZVTN-UHFFFAOYSA-N sodium silicate Chemical compound [Na+].[Na+].[O-][Si]([O-])=O NTHWMYGWWRZVTN-UHFFFAOYSA-N 0.000 description 1
- 229910052911 sodium silicate Inorganic materials 0.000 description 1
- 239000011122 softwood Substances 0.000 description 1
- 238000010257 thawing Methods 0.000 description 1
- 239000002699 waste material Substances 0.000 description 1
- RNWHGQJWIACOKP-UHFFFAOYSA-N zinc;oxygen(2-) Chemical compound [O-2].[Zn+2] RNWHGQJWIACOKP-UHFFFAOYSA-N 0.000 description 1
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Abstract
本发明涉及一种具有吸附和降解有机物功能的复合纸基材料的制备方法及应用,材料由30~50%的金属氧化物粉体,15~35%的吸附剂粉体,0~25%的无机纤维,10~30%的纸浆,0.5~5%的二元助留剂组成。制备时,将金属氧化物粉体、吸附剂粉体、无机纤维和纸浆配制成浓度为2~8%的悬浮液,疏解5~30min;再加入二元助留剂后稀释为0.5%,形成湿纸板;经压榨烘干,即得到复合纸基材料。将制备得到的复合纸基材料进一步加工成纸构件,置于带光源的低浓度挥发性有机物环境中,可实现连续光催化降解。利用本发明的纸基材料,解决了用沸石等为载体制备复合催化材料成本高、粒状材料间因摩擦而粉末化的问题,且对低浓度挥发性有机气体具有吸附作用。The invention relates to a preparation method and application of a composite paper-based material with the function of adsorbing and degrading organic matter. The material consists of 30-50% metal oxide powder, 15-35% adsorbent powder, 0-25% Inorganic fiber, 10-30% pulp, 0.5-5% binary retention aid. During preparation, the metal oxide powder, adsorbent powder, inorganic fiber and pulp are prepared into a suspension with a concentration of 2-8%, and it is decomposed for 5-30 minutes; then it is diluted to 0.5% after adding a binary retention aid to form Wet cardboard; press and dry to obtain composite paper base material. The prepared composite paper-based material is further processed into paper components, and placed in a low-concentration volatile organic compound environment with a light source to achieve continuous photocatalytic degradation. The paper-based material of the invention solves the problems of high cost of preparing composite catalytic materials by using zeolite as a carrier, and powderization of granular materials due to friction, and has adsorption effect on low-concentration volatile organic gases.
Description
技术领域 technical field
本发明涉及一种具有光催化功能的复合材料的制备方法,具体说是制备一种具有吸附和降解低浓度挥发性有机物的复合纸基材料,属材料科学领域。The invention relates to a preparation method of a composite material with photocatalytic function, specifically to prepare a composite paper-based material capable of absorbing and degrading low-concentration volatile organic compounds, and belongs to the field of material science.
背景技术 Background technique
目前人们生活和工作的空间中存在着大量的低浓度挥发性有机物污染源,如鞋厂胶粘剂的挥发性有机溶剂、室内装修产生的有害气体(甲醛、苯)污染等等,严重危害着人们的身体健康。近年来,应用二氧化钛等金属氧化物多相光催化反应治理低浓度挥发性有机物已成为环境领域和无机材料科学最为活跃的一个研究方向,但大规模商业化应用的工程或产品还鲜见。这主要可归结于二个原因:(1)二氧化钛等金属氧化物粉体固结技术未解决。二氧化钛等金属氧化物粉体光催化降解挥发性有机物时,易造成反应器内气流压力急剧损失、光辐射受阻等问题。从文献检索的情况看,国内外有关利用沸石、玻璃、单晶硅、导电玻璃等为载体制备金属氧化物复合催化材料已有较多的报道,但这些方法的制备成本高,粒状复合材料在反应器内仍存在造成气流压力损失、光辐射受阻的问题,且还存在粒状材料间摩擦而粉末化的问题。(2)二氧化钛等金属氧化物粉体对低浓度挥发性有机气体的光催化降解速度慢,主要是因为低浓度挥发性有机物在二氧化钛粉体表面的浓度小。At present, there are a large number of low-concentration volatile organic pollution sources in the space where people live and work, such as volatile organic solvents in shoe factory adhesives, harmful gas (formaldehyde, benzene) pollution from interior decoration, etc., which seriously endanger people's health. healthy. In recent years, the application of titanium dioxide and other metal oxide heterogeneous photocatalytic reactions to treat low-concentration volatile organic compounds has become one of the most active research directions in the environmental field and inorganic material science, but large-scale commercial applications or products are still rare. This can be attributed to two reasons: (1) The consolidation technology of titanium dioxide and other metal oxide powders has not been solved. When metal oxide powders such as titanium dioxide photocatalytically degrade volatile organic compounds, it is easy to cause problems such as a sharp loss of airflow pressure in the reactor and obstruction of light radiation. Judging from the situation of literature retrieval, there have been many reports at home and abroad on the preparation of metal oxide composite catalytic materials using zeolite, glass, single crystal silicon, conductive glass, etc., but the preparation costs of these methods are high. There are still problems in the reactor that cause airflow pressure loss, light radiation is blocked, and there is also the problem of powdering due to friction between granular materials. (2) The photocatalytic degradation rate of metal oxide powders such as titanium dioxide to low-concentration volatile organic gases is slow, mainly because the concentration of low-concentration volatile organic compounds on the surface of titanium dioxide powder is small.
最近福建师范大学吴宗华等研制了一种新的造纸工艺(陈万春,陈娜洁,卢玉栋,吴宗华,造纸化学品,2006,18(2),45;陈万春,陈娜洁,卢玉栋,吴宗华,造纸科学与技术,2006,25(1),24;陈娜洁,陈少平,卢玉栋,陈万春,吴宗华,非金属矿,2006,29(5),6),这种工艺能制备无机物含量达90%以上、无机粉体达60%以上的高无机粉体含量的功能复合纸板。应用这项技术,发明了一种用金属氧化物-吸附剂复合纸板光催化降解低浓度挥发性有机物的方法。Wu Zonghua of Fujian Normal University recently developed a new papermaking process (Chen Wanchun, Chen Najie, Lu Yudong, Wu Zonghua, Paper Chemicals, 2006, 18 (2), 45; Chen Wanchun, Chen Najie, Lu Yudong, Wu Zonghua, Paper Science and Technology, 2006 , 25(1), 24; Chen Najie, Chen Shaoping, Lu Yudong, Chen Wanchun, Wu Zonghua, Nonmetallic Minerals, 2006, 29(5), 6), this process can prepare inorganic matter content of more than 90%, inorganic powder up to 60% Functional composite paperboard with high inorganic powder content above %. Applying this technique, a method for photocatalytic degradation of low-concentration VOCs using metal oxide-adsorbent composite paperboard was invented.
发明内容 Contents of the invention
本发明的目的是提供一种由具有光催化功能的金属氧化物粉体、吸附剂粉体、无机纤维和纸浆构成的复合纸基材料及其对低浓度挥发性有机物的光催化降解的应用。The purpose of the present invention is to provide a composite paper-based material composed of metal oxide powder with photocatalytic function, adsorbent powder, inorganic fiber and pulp and its application to photocatalytic degradation of low-concentration volatile organic compounds.
为实现上述目的,本发明所采用的具体技术方案是:In order to achieve the above object, the concrete technical scheme adopted in the present invention is:
1、材料组成1. Material composition
金属氧化物粉体30~50%,吸附剂粉体15~35%,无机纤维0~25%,纸浆10~30%,二元助留剂0.5~5%。所述百分比是材料绝干重量百分比。30-50% of metal oxide powder, 15-35% of adsorbent powder, 0-25% of inorganic fiber, 10-30% of pulp, and 0.5-5% of binary retention aid. The stated percentages are by dry weight of the material.
2、材料制备2. Material preparation
将金属氧化物粉体、无机纤维、吸附剂粉体和纸浆加水配成2~8%的悬浮液,用疏解机疏解5~30min后倒入烧杯;边搅拌边加入阳离子高聚物,搅拌3min后再加入阴离子型聚丙烯酰胺,加水将悬浮液稀释成0.5%,在纸页抄取器上抄湿纸板。将湿纸板压榨后在105℃~125℃下烘干,即得到本发明所述的复合纸基材料。Add water to metal oxide powder, inorganic fiber, adsorbent powder and pulp to form a 2-8% suspension, decompose it with a decomposer for 5-30 minutes, and pour it into a beaker; add cationic polymer while stirring, and stir for 3 minutes Then add anionic polyacrylamide, add water to dilute the suspension to 0.5%, and copy the wet cardboard on the paper scraper. After the wet paperboard is pressed, it is dried at 105° C. to 125° C. to obtain the composite paper base material of the present invention.
3、材料应用3. Material application
将制备得到的复合纸基材料进一步加工成蜂窝状或细小块状的各种纸构件,置于带有自然光源或人工紫外光源的低浓度挥发性有机物环境中,可实现低浓度挥发性有机物的吸附和连续光催化降解。The prepared composite paper-based material is further processed into honeycomb or small block-shaped various paper components, and placed in a low-concentration volatile organic compound environment with natural light sources or artificial ultraviolet light sources to achieve low-concentration volatile organic compounds. Adsorption and continuous photocatalytic degradation.
本发明所述的金属氧化物粉体为二氧化钛、氧化锌或氧化铜粉体中的一种,或其任意比例的混合物。The metal oxide powder in the present invention is one of titanium dioxide, zinc oxide or copper oxide powder, or a mixture thereof in any proportion.
本发明所述的吸附剂粉体为沸石、硅藻土、活性炭或竹炭的一种,或其任意比例的混合物。The adsorbent powder in the present invention is one of zeolite, diatomaceous earth, activated carbon or bamboo charcoal, or a mixture thereof in any proportion.
本发明所述的无机纤维为陶瓷纤维或玻璃纤维的一种,或其任意比例混合物。The inorganic fiber described in the present invention is a kind of ceramic fiber or glass fiber, or a mixture thereof in any proportion.
本发明所述的纸浆为针叶木化学浆、阔叶木化学浆或草浆的一种,或其任意比例的混合物。The pulp described in the present invention is one of softwood chemical pulp, hardwood chemical pulp or straw pulp, or a mixture thereof in any proportion.
本发明所述的二元助留剂由阴离子型聚丙烯酰胺和阳离子型高聚物构成的,其中阳离子型高聚物为聚二甲基二烯丙基氯化铵、阳离子淀粉或聚乙烯胺的一种或其混合物。The binary retention aid of the present invention is composed of anionic polyacrylamide and cationic high polymer, wherein the cationic high polymer is polydimethyldiallylammonium chloride, cationic starch or polyvinylamine one or a mixture thereof.
本发明所述的纸页抄取器为纸样抄取器、圆网机或低速长网机中的一种。The paper sheet extractor of the present invention is one of a paper sample extractor, a cylinder machine or a low-speed fourdrinier machine.
造纸工业中大量使用碳酸钙、二氧化钛等无机粉体,但由于无机粉体留着率低,既造成原料大量浪费,又污染了水质,给水处理增加了负担,因此无机粉体的最大用量不超过30%。本发明提供的复合纸板中无机粉体含量可达60%以上,制造时无机粉体的留着率可达90%以上,为近十几年来迅速发展的具有光催化、吸附、保温或防火功能的纸(板)的开发和应用提供一种高效低成本制备方法,应用前景广阔。A large amount of inorganic powders such as calcium carbonate and titanium dioxide are used in the paper industry. However, due to the low retention rate of inorganic powders, it not only causes a lot of waste of raw materials, but also pollutes water quality and increases the burden on water treatment. Therefore, the maximum amount of inorganic powders used should not exceed 30%. The content of inorganic powder in the composite paperboard provided by the invention can reach more than 60%, and the retention rate of inorganic powder can reach more than 90% during manufacture. The development and application of the paper (board) provides a high-efficiency and low-cost preparation method with broad application prospects.
利用本发明提供的复合纸基材料进一步加工成的构件有效解决了二氧化钛等金属氧化物粉体造成光辐射受阻等问题,也解决了用沸石、玻璃、单晶硅、导电玻璃等为载体制备的二氧化钛等金属氧化物复合催化材料的制备成本高、粒状材料间因摩擦而粉末化的问题。此外它对低浓度挥发性有机气体具有吸附作用,大幅增大有机气体在二氧化钛粉体表面的浓度,提高的光催化降解速度,实现了低浓度挥发性有机物的连续光催化降解的大规模商业化应用。The components further processed by the composite paper-based material provided by the present invention effectively solve the problems of blocked light radiation caused by metal oxide powders such as titanium dioxide, and also solve the problem of using zeolite, glass, single crystal silicon, conductive glass, etc. as carriers. The preparation cost of titanium dioxide and other metal oxide composite catalytic materials is high, and the problems of powdering between granular materials due to friction. In addition, it has an adsorption effect on low-concentration volatile organic gases, greatly increases the concentration of organic gases on the surface of titanium dioxide powder, improves the photocatalytic degradation speed, and realizes the large-scale commercialization of continuous photocatalytic degradation of low-concentration volatile organic compounds. application.
具体实施方式 Detailed ways
以下结合具体的实施例对本发明的技术方案作进一步的说明:The technical scheme of the present invention will be further described below in conjunction with specific embodiments:
实施例1:Example 1:
取0.8克的桉木化学浆、2.0克的陶瓷纤维、3.8克的锐钛型二氧化钛和1.0克的沸石,加水配成5%的悬浮液,用疏解机疏解10min后倒入烧杯;边搅拌边加入0.08克的聚二甲基二烯丙基氯化铵,搅拌吸附3min后加入0.12克的阴离子型聚丙烯酰胺,加水将悬浮液稀释成0.5%,在纸样抄取器上抄湿纸板。将湿纸板压榨后在105℃下烘干,即得到本发明所述的复合纸基材料。Take 0.8 grams of eucalyptus chemical pulp, 2.0 grams of ceramic fiber, 3.8 grams of anatase titanium dioxide and 1.0 grams of zeolite, add water to make a 5% suspension, and pour it into a beaker after 10 minutes with a decomposer; while stirring Add 0.08 g of polydimethyldiallyl ammonium chloride, stir and absorb for 3 minutes, then add 0.12 g of anionic polyacrylamide, add water to dilute the suspension to 0.5%, and wet the cardboard on a paper sampler. Press the wet paperboard and dry it at 105°C to obtain the composite paper base material of the present invention.
实施例2:Example 2:
取0.6克的麦草浆和0.4克的马尾松化学浆的混合浆、3.0克的陶瓷纤维、3.0克的锐钛型二氧化钛和1.0克的金红石型二氧化钛的混合粉体、1.0克的沸石和0.6克的活性炭的混合吸附剂,加水配成8%的悬浮液,用疏解机疏解15min后倒入烧杯;边搅拌边加入0.15克的聚二甲基二烯丙基氯化铵,搅拌吸附3min后加入0.25克的阴离子型聚丙烯酰胺,加水将悬浮液稀释成0.5%,在纸样抄取器上抄湿纸板。将湿纸板压榨后在115℃下烘干,即得到本发明所述的复合纸基材料。Get the mixed pulp of 0.6 gram of wheat straw pulp and 0.4 gram of masson pine chemical pulp, 3.0 gram of ceramic fiber, 3.0 gram of anatase titanium dioxide and 1.0 gram of rutile titanium dioxide, 1.0 gram of zeolite and 0.6 gram The mixed adsorbent of activated carbon is mixed with water to form an 8% suspension, which is decomposed by a decomposer for 15 minutes and then poured into a beaker; while stirring, add 0.15 grams of polydimethyldiallyl ammonium chloride, stir and absorb for 3 minutes and then add 0.25 grams of anionic polyacrylamide, add water to dilute the suspension to 0.5%, and wet the cardboard on a paper sampler. Press the wet paperboard and then dry it at 115°C to obtain the composite paper base material of the present invention.
实施例3:Example 3:
取0.6克的桉木化学浆和0.4克的云杉化学浆的混合浆、1.5克的陶瓷纤维和1.5克玻璃纤维的混合物、3.0克的锐钛型二氧化钛和1.0克的氧化铜的混合粉体、1.0克的沸石和0.5克的竹炭的混合吸附剂,加水配成2%的悬浮液,用疏解机疏解20min后倒入烧杯;边搅拌边加入0.1克的聚二甲基二烯丙基氯化铵和0.15克的阳离子淀粉,搅拌3min后加入0.25克的阴离子型聚丙烯酰胺,加水将悬浮液稀释成0.5%,在纸样抄取器上抄湿纸板。将湿纸板压榨后在115℃下烘干,即得到本发明所述的复合纸基材料。Get the mixed pulp of 0.6 gram of eucalyptus chemical pulp and 0.4 gram of spruce chemical pulp, the mixture of 1.5 gram of ceramic fiber and 1.5 gram of glass fiber, the mixed powder of 3.0 gram of anatase titanium dioxide and 1.0 gram of copper oxide , 1.0 gram of zeolite and 0.5 gram of bamboo charcoal mixed adsorbent, add water to make 2% suspension, pour it into a beaker after 20 min with a decontamination machine; add 0.1 gram of polydimethyldiallyl chloride while stirring Ammonium chloride and 0.15 g of cationic starch, after stirring for 3 minutes, add 0.25 g of anionic polyacrylamide, add water to dilute the suspension to 0.5%, and wet the cardboard on a paper sample machine. Press the wet paperboard and then dry it at 115°C to obtain the composite paper base material of the present invention.
实施例4:Example 4:
取1.5克的马尾松化学浆、2.0克的玻璃纤维、4.0克的氧化锌和2.2克的活性炭,加水配成2%的悬浮液,用疏解机疏解20min后倒入烧杯;边搅拌边加入0.1克的聚二甲基二烯丙基氯化铵,搅拌3min后加入0.2克的阴离子型聚丙烯酰胺,加水将悬浮液稀释成0.5%,在纸样抄取器上抄湿纸板。将湿纸板折叠成瓦楞状,用硅酸钠溶液固定后,500℃下灼烧30min,定型后可得蜂窝状构件。将构件置于紫外光强度为0.5mW/cm2的环境中,每平方米的复合纸板每小时可降解0.5克的浓度为10微克/升的甲苯气体。Take 1.5 grams of masson pine chemical pulp, 2.0 grams of glass fiber, 4.0 grams of zinc oxide and 2.2 grams of activated carbon, add water to make a 2% suspension, and pour it into a beaker after 20 minutes with a decomposer; while stirring, add 0.1 Add 0.2 g of anionic polyacrylamide to 0.2 g of polydimethyldiallyl ammonium chloride after stirring for 3 minutes, add water to dilute the suspension to 0.5%, and wet the cardboard on a paper sampler. Fold the wet cardboard into a corrugated shape, fix it with sodium silicate solution, and burn it at 500°C for 30 minutes to obtain a honeycomb structure after setting. The components are placed in an environment with an ultraviolet light intensity of 0.5mW/cm 2 , and each square meter of composite cardboard can degrade 0.5 grams of toluene gas with a concentration of 10 micrograms per liter per hour.
实施例5:Example 5:
取1.5克的麦草浆和1.0克落地松化学浆、1.1克的陶瓷纤维、4.0克的氧化铜和3.2克的硅藻土,加水配成3%的悬浮液,用疏解机疏解30min后倒入烧杯;边搅拌边加入0.05克的聚乙烯胺,搅拌吸附3min后加入0.15克的阴离子型聚丙烯酰胺,加水将悬浮液稀释成0.5%,在纸样抄取器上抄取湿纸板。将湿纸板折叠成瓦楞状,用氧化铝溶胶固定后,500℃下灼烧30min,定型后可得蜂窝状构件。将构件置于紫外光强度为0.5mW/cm2环境中,每平方米的复合纸板每小时可降解1.5克的浓度为20微克/升的甲醛气体。Take 1.5 grams of wheat straw pulp, 1.0 grams of ground pine chemical pulp, 1.1 grams of ceramic fiber, 4.0 grams of copper oxide and 3.2 grams of diatomaceous earth, add water to make a 3% suspension, and pour it into Beaker; add 0.05 g of polyvinylamine while stirring, add 0.15 g of anionic polyacrylamide after stirring for 3 minutes, add water to dilute the suspension to 0.5%, and take a wet cardboard on a paper sampler. Fold the wet cardboard into a corrugated shape, fix it with alumina sol, and burn it at 500°C for 30 minutes to obtain a honeycomb structure after shaping. Put the components in an environment with an ultraviolet light intensity of 0.5mW/cm 2 , and each square meter of composite paperboard can degrade 1.5 grams of formaldehyde gas with a concentration of 20 micrograms per liter per hour.
实施例6:Embodiment 6:
取2.0克的芦苇浆和2.0克马尾松化学浆的混合浆、1.8克的二氧化钛和1.8克的氧化锌的混合粉体、2.1克的沸石和2.1克硅藻土的混合吸附剂粉体,加水配成2%的悬浮液,用疏解机疏解5min后倒入烧杯;边搅拌边加入0.45克的阳离子淀粉,搅拌3min后加入0.15克的阴离子型聚丙烯酰胺,加水将悬浮液稀释成0.5%,在纸样抄取器上抄湿纸板。将湿纸板折叠成瓦楞状,用氧化铝溶胶固定后,500℃下灼烧30min,定型后蜂窝状构件。将构件置于紫外光强度为0.5mW/cm2纸板的环境,每平方米的复合纸板每小时可降解1.7克的浓度为20微克/升的戊烷气体。Get the mixed slurry of 2.0 grams of reed pulp and 2.0 grams of masson pine chemical pulp, the mixed powder of 1.8 grams of titanium dioxide and 1.8 grams of zinc oxide, the mixed adsorbent powder of 2.1 grams of zeolite and 2.1 grams of diatomaceous earth, add water Prepare a 2% suspension, and pour it into a beaker after thawing with a decomposer for 5 minutes; add 0.45 grams of cationic starch while stirring, add 0.15 grams of anionic polyacrylamide after stirring for 3 minutes, add water to dilute the suspension to 0.5%, Wet cardboard is copied on the paper pattern picker. Fold the wet cardboard into a corrugated shape, fix it with alumina sol, and burn it at 500°C for 30 minutes to form a honeycomb structure. The component is placed in an environment with an ultraviolet light intensity of 0.5mW/cm 2 of cardboard, and each square meter of composite cardboard can degrade 1.7 grams of pentane gas with a concentration of 20 micrograms per liter per hour.
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