CN103127917B - Preparation method of drinking water treatment agent - Google Patents
Preparation method of drinking water treatment agent Download PDFInfo
- Publication number
- CN103127917B CN103127917B CN201310096962.7A CN201310096962A CN103127917B CN 103127917 B CN103127917 B CN 103127917B CN 201310096962 A CN201310096962 A CN 201310096962A CN 103127917 B CN103127917 B CN 103127917B
- Authority
- CN
- China
- Prior art keywords
- solution
- chitosan
- span
- acetic acid
- acid solution
- 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
- 239000003795 chemical substances by application Substances 0.000 title claims abstract description 15
- 239000003651 drinking water Substances 0.000 title claims abstract description 5
- 235000020188 drinking water Nutrition 0.000 title claims abstract description 5
- 238000002360 preparation method Methods 0.000 title claims description 17
- QTBSBXVTEAMEQO-UHFFFAOYSA-N Acetic acid Chemical compound CC(O)=O QTBSBXVTEAMEQO-UHFFFAOYSA-N 0.000 claims abstract description 66
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 59
- 229920001661 Chitosan Polymers 0.000 claims abstract description 50
- 239000000243 solution Substances 0.000 claims abstract description 49
- 239000004005 microsphere Substances 0.000 claims abstract description 32
- 229910052613 tourmaline Inorganic materials 0.000 claims abstract description 27
- 229940070527 tourmaline Drugs 0.000 claims abstract description 27
- 239000011032 tourmaline Substances 0.000 claims abstract description 27
- 230000005291 magnetic effect Effects 0.000 claims abstract description 25
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 claims abstract description 16
- NWGKJDSIEKMTRX-AAZCQSIUSA-N Sorbitan monooleate Chemical compound CCCCCCCC\C=C/CCCCCCCC(=O)OC[C@@H](O)[C@H]1OC[C@H](O)[C@H]1O NWGKJDSIEKMTRX-AAZCQSIUSA-N 0.000 claims abstract description 15
- 239000011812 mixed powder Substances 0.000 claims abstract description 13
- 229940057995 liquid paraffin Drugs 0.000 claims abstract description 11
- 239000000203 mixture Substances 0.000 claims abstract description 11
- SXRSQZLOMIGNAQ-UHFFFAOYSA-N Glutaraldehyde Chemical compound O=CCCCC=O SXRSQZLOMIGNAQ-UHFFFAOYSA-N 0.000 claims abstract description 10
- IXPNQXFRVYWDDI-UHFFFAOYSA-N 1-methyl-2,4-dioxo-1,3-diazinane-5-carboximidamide Chemical compound CN1CC(C(N)=N)C(=O)NC1=O IXPNQXFRVYWDDI-UHFFFAOYSA-N 0.000 claims abstract description 9
- 239000004372 Polyvinyl alcohol Substances 0.000 claims abstract description 9
- 229920002451 polyvinyl alcohol Polymers 0.000 claims abstract description 9
- 235000010413 sodium alginate Nutrition 0.000 claims abstract description 9
- 229940005550 sodium alginate Drugs 0.000 claims abstract description 9
- 239000000661 sodium alginate Substances 0.000 claims abstract description 9
- SZVJSHCCFOBDDC-UHFFFAOYSA-N ferrosoferric oxide Chemical compound O=[Fe]O[Fe]O[Fe]=O SZVJSHCCFOBDDC-UHFFFAOYSA-N 0.000 claims abstract description 8
- 229910052742 iron Inorganic materials 0.000 claims abstract description 8
- 239000011259 mixed solution Substances 0.000 claims abstract description 8
- 238000002156 mixing Methods 0.000 claims abstract description 5
- VTLYFUHAOXGGBS-UHFFFAOYSA-N Fe3+ Chemical compound [Fe+3] VTLYFUHAOXGGBS-UHFFFAOYSA-N 0.000 claims abstract description 3
- JEIPFZHSYJVQDO-UHFFFAOYSA-N iron(III) oxide Inorganic materials O=[Fe]O[Fe]=O JEIPFZHSYJVQDO-UHFFFAOYSA-N 0.000 claims abstract description 3
- 230000005298 paramagnetic effect Effects 0.000 claims abstract 2
- 238000003756 stirring Methods 0.000 claims description 22
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 claims description 21
- 239000000843 powder Substances 0.000 claims description 14
- UQSXHKLRYXJYBZ-UHFFFAOYSA-N iron oxide Inorganic materials [Fe]=O UQSXHKLRYXJYBZ-UHFFFAOYSA-N 0.000 claims description 10
- NDLPOXTZKUMGOV-UHFFFAOYSA-N oxo(oxoferriooxy)iron hydrate Chemical compound O.O=[Fe]O[Fe]=O NDLPOXTZKUMGOV-UHFFFAOYSA-N 0.000 claims description 10
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 claims description 8
- LFQSCWFLJHTTHZ-UHFFFAOYSA-N Ethanol Chemical compound CCO LFQSCWFLJHTTHZ-UHFFFAOYSA-N 0.000 claims description 7
- RTZKZFJDLAIYFH-UHFFFAOYSA-N Diethyl ether Chemical compound CCOCC RTZKZFJDLAIYFH-UHFFFAOYSA-N 0.000 claims description 6
- 239000008367 deionised water Substances 0.000 claims description 6
- 229910021641 deionized water Inorganic materials 0.000 claims description 6
- 239000002244 precipitate Substances 0.000 claims description 6
- 239000008188 pellet Substances 0.000 claims description 5
- 239000000047 product Substances 0.000 claims description 5
- 238000007711 solidification Methods 0.000 claims description 5
- 230000008023 solidification Effects 0.000 claims description 5
- 239000012153 distilled water Substances 0.000 claims description 4
- 150000001450 anions Chemical class 0.000 claims description 3
- KGBXLFKZBHKPEV-UHFFFAOYSA-N boric acid Chemical class OB(O)O KGBXLFKZBHKPEV-UHFFFAOYSA-N 0.000 claims description 3
- 150000001768 cations Chemical class 0.000 claims description 3
- 239000002245 particle Substances 0.000 claims description 3
- 239000003208 petroleum Substances 0.000 claims description 3
- 239000000725 suspension Substances 0.000 claims description 3
- 238000012546 transfer Methods 0.000 claims description 3
- 238000001816 cooling Methods 0.000 claims description 2
- 239000007788 liquid Substances 0.000 claims 1
- 239000011651 chromium Substances 0.000 abstract description 8
- VYZAMTAEIAYCRO-UHFFFAOYSA-N Chromium Chemical compound [Cr] VYZAMTAEIAYCRO-UHFFFAOYSA-N 0.000 abstract description 6
- 229910052804 chromium Inorganic materials 0.000 abstract description 6
- 238000000034 method Methods 0.000 abstract description 6
- 238000006243 chemical reaction Methods 0.000 abstract description 4
- 239000000463 material Substances 0.000 abstract description 4
- 239000012188 paraffin wax Substances 0.000 abstract description 4
- 150000002989 phenols Chemical class 0.000 abstract description 3
- 238000000746 purification Methods 0.000 abstract description 3
- 238000001179 sorption measurement Methods 0.000 abstract description 3
- 238000004132 cross linking Methods 0.000 abstract description 2
- 238000004945 emulsification Methods 0.000 abstract description 2
- 231100000956 nontoxicity Toxicity 0.000 abstract description 2
- ISWSIDIOOBJBQZ-UHFFFAOYSA-N Phenol Chemical compound OC1=CC=CC=C1 ISWSIDIOOBJBQZ-UHFFFAOYSA-N 0.000 description 14
- 238000002474 experimental method Methods 0.000 description 13
- 239000002351 wastewater Substances 0.000 description 7
- 238000012545 processing Methods 0.000 description 6
- 238000013461 design Methods 0.000 description 5
- 238000013401 experimental design Methods 0.000 description 4
- 230000035484 reaction time Effects 0.000 description 4
- JOPOVCBBYLSVDA-UHFFFAOYSA-N chromium(6+) Chemical compound [Cr+6] JOPOVCBBYLSVDA-UHFFFAOYSA-N 0.000 description 3
- 238000004043 dyeing Methods 0.000 description 3
- 239000000706 filtrate Substances 0.000 description 3
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 2
- 238000004364 calculation method Methods 0.000 description 2
- 239000000975 dye Substances 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- 230000007613 environmental effect Effects 0.000 description 2
- 150000002500 ions Chemical class 0.000 description 2
- 229910021645 metal ion Inorganic materials 0.000 description 2
- 238000011160 research Methods 0.000 description 2
- 239000000126 substance Substances 0.000 description 2
- 238000012360 testing method Methods 0.000 description 2
- 229920002472 Starch Polymers 0.000 description 1
- NINIDFKCEFEMDL-UHFFFAOYSA-N Sulfur Chemical compound [S] NINIDFKCEFEMDL-UHFFFAOYSA-N 0.000 description 1
- 239000002253 acid Substances 0.000 description 1
- 230000002378 acidificating effect Effects 0.000 description 1
- 239000004480 active ingredient Substances 0.000 description 1
- 229910052785 arsenic Inorganic materials 0.000 description 1
- 238000003321 atomic absorption spectrophotometry Methods 0.000 description 1
- 239000000987 azo dye Substances 0.000 description 1
- 239000000981 basic dye Substances 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 230000015572 biosynthetic process Effects 0.000 description 1
- 229910052802 copper Inorganic materials 0.000 description 1
- 230000006196 deacetylation Effects 0.000 description 1
- 238000003381 deacetylation reaction Methods 0.000 description 1
- 230000005611 electricity Effects 0.000 description 1
- 230000005686 electrostatic field Effects 0.000 description 1
- 238000001914 filtration Methods 0.000 description 1
- 235000013305 food Nutrition 0.000 description 1
- 238000004817 gas chromatography Methods 0.000 description 1
- 239000003673 groundwater Substances 0.000 description 1
- 238000010438 heat treatment Methods 0.000 description 1
- 229910052500 inorganic mineral Inorganic materials 0.000 description 1
- CDRCPXYWYPYVPY-UHFFFAOYSA-N iron(2+) oxygen(2-) Chemical compound [O-2].[O-2].[O-2].[O-2].[Fe+2].[Fe+2].[Fe+2].[Fe+2] CDRCPXYWYPYVPY-UHFFFAOYSA-N 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 238000013178 mathematical model Methods 0.000 description 1
- 239000011707 mineral Substances 0.000 description 1
- 230000010355 oscillation Effects 0.000 description 1
- 229940068984 polyvinyl alcohol Drugs 0.000 description 1
- 102000004169 proteins and genes Human genes 0.000 description 1
- 108090000623 proteins and genes Proteins 0.000 description 1
- 239000012629 purifying agent Substances 0.000 description 1
- 230000005616 pyroelectricity Effects 0.000 description 1
- STZCRXQWRGQSJD-UHFFFAOYSA-M sodium;4-[[4-(dimethylamino)phenyl]diazenyl]benzenesulfonate Chemical compound [Na+].C1=CC(N(C)C)=CC=C1N=NC1=CC=C(S([O-])(=O)=O)C=C1 STZCRXQWRGQSJD-UHFFFAOYSA-M 0.000 description 1
- 235000019698 starch Nutrition 0.000 description 1
- 239000008107 starch Substances 0.000 description 1
- 230000003068 static effect Effects 0.000 description 1
- 239000011593 sulfur Substances 0.000 description 1
- 229910052717 sulfur Inorganic materials 0.000 description 1
- 238000005406 washing Methods 0.000 description 1
Landscapes
- Solid-Sorbent Or Filter-Aiding Compositions (AREA)
- Water Treatment By Electricity Or Magnetism (AREA)
Abstract
一种饮用水处理剂,它是将电气石和磁性壳聚糖微球混合粉加入海藻酸钠和聚乙烯醇中溶解、混匀,然后固化成球制得;磁性壳聚糖微球是以超顺磁性四氧化三铁、1~10wt%壳聚糖乙酸溶液、液体石蜡、Span-80、戊二醛溶液为反应物料、通过乳化交联法制得,超顺磁性四氧化三铁与壳聚糖乙酸溶液质量比为1:1~10,液体石蜡与Span-80体积比10~100:1,超顺磁性四氧化三铁的壳聚糖乙酸溶液与石蜡—Span-80混合液体积比为1:1~10,超顺磁性四氧化三铁的壳聚糖乙酸溶液与石蜡、Span-80的混合液,和戊二醛溶液体积比5~50:1。本发明水处理剂对水中挥发酚去除率可达80%~90%、对水中铬去除率可达93%,同时其具有吸附容量大、净化效率高、成本低、可再生、无毒、对环境无污染等优点。A drinking water treatment agent, which is prepared by adding tourmaline and magnetic chitosan microsphere mixed powder into sodium alginate and polyvinyl alcohol, dissolving, mixing, and then solidifying into balls; magnetic chitosan microsphere is made of super Paramagnetic iron tetroxide, 1-10wt% chitosan acetic acid solution, liquid paraffin, Span-80, and glutaraldehyde solution are used as reaction materials, and are prepared by emulsification and cross-linking method. Superparamagnetic ferric iron tetroxide and chitosan The mass ratio of acetic acid solution is 1:1-10, the volume ratio of liquid paraffin and Span-80 is 10-100:1, and the volume ratio of chitosan acetic acid solution of superparamagnetic iron tetroxide and paraffin-Span-80 mixture is 1 :1~10, the mixed solution of chitosan acetic acid solution of superparamagnetic ferroferric oxide, paraffin, Span-80, and glutaraldehyde solution in a volume ratio of 5~50:1. The water treatment agent of the present invention has a removal rate of 80% to 90% for volatile phenols in water, and a removal rate of 93% for chromium in water. At the same time, it has large adsorption capacity, high purification efficiency, low cost, renewability, non-toxicity, and The environment has no pollution and other advantages.
Description
本发明是申请日为2011年09月23日,申请号为201110284933.4的分案申请。The present invention is a divisional application with an application date of September 23, 2011 and an application number of 201110284933.4.
技术领域technical field
本发明涉及水处理制剂,尤其涉及一种对水中挥发酚去除效果好的水处理剂及其制备方法,属于水处理领域。The invention relates to a water treatment preparation, in particular to a water treatment agent with good effect on removing volatile phenol in water and a preparation method thereof, belonging to the field of water treatment.
背景技术Background technique
近几年,磁性壳聚糖微球独特的性质与结构引起了人们的广泛关注,尤其是在水处理中的应用研究中取得良好的成绩。磁性壳聚糖可以用来去除水中Cu2+、Cr2+、Hg2+、Zn2+、Pb2+、Ca2+、Ag+等金属离子,也可用于处理有机废水,并且可以很快达到平衡。Wong和G.Mckay等[22-23]曾对壳聚糖处理印染废水做了很详细的研究,结果表明壳聚糖对许多类型的染料具有很高的亲和力,其中包括分散、直接、活性、酸性、硫化和纳夫妥染料,仅对碱性染料具有较低的亲和力。洪爱真等【24】用壳聚糖包裹铁制成的磁性微球来处理酸性偶氮染料废水,结果表明对于一定浓度的甲基橙溶液,只需1h就可以去除95%以上;而活性碳需8h才能去除88%。韩德艳等【25】也做过相关实验,反应1h对印染废水色度的去除率为98%以上。也有文献【27】报导用壳聚糖为絮凝剂可以回收食品加工废水中的蛋白质、淀粉等。国内外学者通过大量的研究,从不同角度来探讨磁性壳聚糖的应用价值,利用磁性壳聚糖对金属离子、造纸废水、印染废水等的文献报道已有很多,但未曾见到对水中挥发酚的净化研究,尤其是将其与其他物质再次交联产生的新物质的探讨更是十分罕见的。In recent years, the unique properties and structure of magnetic chitosan microspheres have attracted widespread attention, especially in the application research of water treatment, which has achieved good results. Magnetic chitosan can be used to remove Cu 2+ , Cr 2+ , Hg 2+ , Zn 2+ , Pb 2+ , Ca 2+ , Ag + and other metal ions in water, and can also be used to treat organic wastewater, and can be quickly Achieve balance. Wong and G.Mckay et al . [22-23] have done a detailed study on the treatment of printing and dyeing wastewater with chitosan, and the results show that chitosan has a high affinity for many types of dyes, including disperse, direct, active, Acid, sulfur and Nafto dyes, only have a low affinity for basic dyes. Hong Aizhen et al [24] used magnetic microspheres made of chitosan-coated iron to treat acidic azo dye wastewater. The results showed that for a certain concentration of methyl orange solution, more than 95% could be removed in just 1 hour; while activated carbon required 8h to remove 88%. Han Deyan et al [25] have also done related experiments, and the removal rate of chroma in printing and dyeing wastewater is over 98% after 1 hour of reaction. There is also literature [27] reporting that protein, starch, etc. in food processing wastewater can be recovered by using chitosan as a flocculant. Scholars at home and abroad have discussed the application value of magnetic chitosan from different angles through a large number of studies. There have been many literature reports on the use of magnetic chitosan for metal ions, papermaking wastewater, printing and dyeing wastewater, etc. The purification research of phenol, especially the exploration of new substances produced by re-crosslinking it with other substances is very rare.
电气石因其热电性和压电性而闻名,从18世纪至20世纪中期一直在工业领域得到充分的应用,然而其电学性质与环保功能却一直未得到重视。1989年,Kubo经研究首次提出电气石微粒表面存在着静电场,并预测了电气石在环境领域的应用前景。日本学者研究也发现在地层中含有电气石的河水难以被污染,开拓了电气石在环境保护领域中的应用。相关研究表明,电气石有较好的极性,表面静电强,对水中有害离子(如Cu,As(Ⅲ),F-等)有较强的吸附性,可以用于净化水体,是治理水污染的良好环境矿物材料。到目前为止,尚未见到有关利用壳聚糖与电气石联合制备净水剂净化水的相关报道。Known for its pyroelectricity and piezoelectricity, tourmaline has been fully used in the industrial field from the 18th century to the middle of the 20th century, but its electrical properties and environmental protection functions have not been paid attention to. In 1989, Kubo proposed for the first time that there is an electrostatic field on the surface of tourmaline particles, and predicted the application prospect of tourmaline in the field of environment. Japanese scholars have also found that the river water containing tourmaline in the formation is difficult to be polluted, which has opened up the application of tourmaline in the field of environmental protection. Relevant studies have shown that tourmaline has good polarity, strong surface static electricity, and strong adsorption to harmful ions in water (such as Cu, As(Ⅲ), F-, etc.), and can be used to purify water bodies. Polluted good environment mineral material. Up to now, there has not been any related report about utilizing chitosan and tourmaline to jointly prepare water purifying agent to purify water.
发明内容Contents of the invention
本发明的目的在于提供一种对水中酚去除率高的水处理剂。The object of the present invention is to provide a water treatment agent with high removal rate of phenol in water.
本发明的另一目的在于提供上述水处理剂的制备方法。Another object of the present invention is to provide a preparation method of the above-mentioned water treatment agent.
本发明的目的是通过如下技术方案实现的:The purpose of the present invention is achieved through the following technical solutions:
一种水处理剂,其特征在于:它是将电气石和磁性壳聚糖微球的混合粉末加入到海藻酸钠和聚乙烯醇中溶解、混匀,然后固化成球制得;所述磁性壳聚糖微球是以超顺磁性四氧化三铁粉末、1~10wt%(优选为2wt%)壳聚糖乙酸溶液、液体石蜡、Span-80、戊二醛溶液为反应物料、通过乳化交联法制得的,其中超顺磁性四氧化三铁与所述壳聚糖乙酸溶液的质量比为1:1~10(优选质量比为2:5);液体石蜡与Span-80体积比10~100:1(优选体积比为40:1);超顺磁性四氧化三铁的壳聚糖乙酸溶液与石蜡—Span-80混合液的体积比为1:1~10、优选为1:2;上述超顺磁性四氧化三铁的壳聚糖乙酸溶液与石蜡、Span-80的混合液,与戊二醛溶液(优选采用分析纯)体积比5~50:1、优选为25:1。A water treatment agent is characterized in that: it is made by adding the mixed powder of tourmaline and magnetic chitosan microspheres to sodium alginate and polyvinyl alcohol, dissolving, mixing, and then solidifying into balls; the magnetic shell Polycan microspheres are made of superparamagnetic ferric oxide powder, 1-10wt% (preferably 2wt%) chitosan acetic acid solution, liquid paraffin, Span-80, and glutaraldehyde solution as reaction materials, and are cross-linked by emulsification. Prepared by method, wherein the mass ratio of superparamagnetic iron tetroxide and said chitosan acetic acid solution is 1:1~10 (preferred mass ratio is 2:5); the volume ratio of liquid paraffin and Span-80 is 10~100 : 1 (the preferred volume ratio is 40:1); the volume ratio of the chitosan acetic acid solution of superparamagnetic ferroferric oxide and the paraffin-Span-80 mixed solution is 1:1~10, preferably 1:2; the above The volume ratio of the chitosan acetic acid solution of superparamagnetic iron tetroxide, paraffin, and Span-80 to glutaraldehyde solution (preferably of analytical grade) is 5-50:1, preferably 25:1.
在电气石与磁性壳聚糖微球的制备中,若成球太少、在使用过程中易松散,成球太多、则过厚会影响有效成分作用的发挥,因此都会影响处理效率。为了进一步提高成球的均匀性与有效性,从而提高本发明水处理剂对酚的去除率,上述电气石和磁性壳聚糖微球的混合粉末中,电气石与磁性壳聚糖微球的质量比为1~10:1、优选为5:2,上述海藻酸钠、聚乙烯醇以及电气石和磁性壳聚糖微球的混合粉末的质量比为1:1~10:1~12、优选质量比1:6:7。In the preparation of tourmaline and magnetic chitosan microspheres, if there are too few balls, they are easy to loosen during use, and if there are too many balls, too thick will affect the function of the active ingredients, which will affect the processing efficiency. In order to further improve the uniformity and effectiveness of balling, thereby improving the removal rate of the water treatment agent of the present invention to phenol, in the mixed powder of the above-mentioned tourmaline and magnetic chitosan microspheres, the quality of tourmaline and magnetic chitosan microspheres The ratio is 1-10:1, preferably 5:2, and the mass ratio of the mixed powder of sodium alginate, polyvinyl alcohol, tourmaline and magnetic chitosan microspheres is 1:1-10:1-12, preferably The ratio is 1:6:7.
优选地,本发明超顺磁性四氧化三铁粉末按如下制得:Preferably, the superparamagnetic ferric oxide powder of the present invention is prepared as follows:
称取5.56g FeSO4·7H2O、6.5g FeCl3和1.7mL浓盐酸溶解于50mL预先经N2脱气处理蒸馏水中,然后将上述滴加到250mL1.0mol/L的NaOH溶液中。在80℃水浴中慢速(100r/min)搅拌5min,然后在快速机械搅拌(2000r/min),待溶液中出现黑色的沉淀,持续搅拌至30min。待反应结束后,静置冷却至室温,通过外加磁场分离黑色沉淀产物,分别用去离子水和无水乙醇清洗3次,在60℃的真空干燥箱中干燥12小时,待用。Weigh 5.56g FeSO 4 ·7H 2 O, 6.5g FeCl 3 and 1.7mL concentrated hydrochloric acid and dissolve them in 50mL distilled water degassed with N 2 beforehand, then add the above dropwise to 250mL 1.0mol/L NaOH solution. Stir slowly (100r/min) in a water bath at 80°C for 5min, then stir mechanically at a high speed (2000r/min), until a black precipitate appears in the solution, and continue stirring for 30min. After the reaction was finished, it was left to cool down to room temperature, and the black precipitate was separated by applying an external magnetic field, washed three times with deionized water and absolute ethanol, and dried in a vacuum oven at 60°C for 12 hours before use.
本发明壳聚糖乙酸溶液是将壳聚糖溶解于乙酸溶液(优选采用分析纯)中制得的;所述壳聚糖优选为脱乙酰度为90%的壳聚糖,购自上海沪峰生化试剂有限公司、为市售产品。Chitosan acetic acid solution of the present invention is prepared by dissolving chitosan in acetic acid solution (preferably using analytically pure); said chitosan is preferably chitosan with a deacetylation degree of 90%, purchased from Shanghai Hufeng Biochemical Reagent Co., Ltd. is a commercially available product.
优选地,本发明电气石产于内蒙古赤峰地区,为市售产品。Preferably, the tourmaline of the present invention is produced in Chifeng, Inner Mongolia, and is a commercially available product.
上述水处理剂的制备方法,按如下步骤制备:The preparation method of above-mentioned water treatment agent, prepares as follows:
a.电气石的预处理a. Pretreatment of tourmaline
将电气石粉碎过100-400目筛(优选为200目),用质量浓度为2-10%的NaOH溶液(优选为5%)洗涤5~7次去除表面所附带的阴阳离子,再用去离子水清洗同样的次数过后,放于烘箱里面烘干,待用;The tourmaline is crushed through a 100-400 mesh sieve (preferably 200 mesh), washed 5 to 7 times with a NaOH solution (preferably 5%) with a mass concentration of 2-10% to remove the attached anions and cations on the surface, and then used After washing with ion water for the same number of times, put it in the oven to dry and set aside;
b.超顺磁性四氧化三铁粉末的制备b. Preparation of superparamagnetic Fe3O4 powder
称取5.56g FeSO4·7H2O、6.5g FeCl3和1.7mL浓盐酸溶解于50mL预先经N2脱气处理蒸馏水中,然后将上述滴加到250mL1.0mol/L的NaOH溶液中;在80℃水浴中以100r/min慢速搅拌5min,然后在以2000r/min快速机械搅拌,待溶液中出现黑色的沉淀,持续搅拌至30min;待反应结束后,静置冷却至室温,通过外加磁场分离黑色沉淀产物,分别用去离子水和无水乙醇清洗3次,在60℃的真空干燥箱中干燥12小时,待用;Weigh 5.56g FeSO 4 ·7H 2 O, 6.5g FeCl 3 and 1.7mL concentrated hydrochloric acid and dissolve in 50mL pre-degassed distilled water with N 2 , then add the above dropwise to 250mL 1.0mol/L NaOH solution; Stir at a slow speed of 100r/min in a water bath at 80°C for 5min, and then stir mechanically at a speed of 2000r/min until a black precipitate appears in the solution, and continue to stir for 30min; Separate the black precipitated product, wash it with deionized water and absolute ethanol three times, and dry it in a vacuum oven at 60°C for 12 hours before use;
c.磁性壳聚糖微球的制备c. Preparation of Magnetic Chitosan Microspheres
称取超顺磁性四氧化三铁粉末加入到质量浓度为1~10%(优选为2%)的壳聚糖乙酸溶液中,其中超顺磁性四氧化三铁与壳聚糖乙酸溶液的质量比为1:1~1:10(优选为2:5),搅拌混合均匀后,转移至液体石蜡和Span-80的混合液中,其中液体石蜡与Span-80体积比10:1~100:1(优选体积比为40:1),调pH值至3.0~12.0(优选为9.0),100~500r/min(优选200r/min)搅拌30min,所述超顺磁性四氧化三铁的壳聚糖乙酸溶液与石蜡—Span-80混合液的体积比为1:1~1:10(优选为1:2);滴加戊二醛溶液,超顺磁性四氧化三铁的壳聚糖乙酸溶液与石蜡、Span-80的混合液,和戊二醛溶液(优选采用分析纯)体积比5:1~50:1(优选为25:1),在20~80℃(优选40℃)下继续搅拌60min,使之充分反应,再减压过滤、依次用石油醚、无水乙醇抽提1-10次(优选3次),在20-100℃(优选50℃)条件下真空干燥,即得;Take superparamagnetic ferric oxide powder and join in the chitosan acetic acid solution that mass concentration is 1~10% (preferably 2%), wherein the mass ratio of superparamagnetic ferric oxide and chitosan acetic acid solution 1:1 to 1:10 (preferably 2:5), stir and mix evenly, then transfer to the liquid paraffin and Span-80 mixture, wherein the volume ratio of liquid paraffin to Span-80 is 10:1 to 100:1 (preferred volume ratio is 40:1), adjust pH value to 3.0~12.0 (preferably 9.0), 100~500r/min (preferably 200r/min) stir 30min, the chitosan of described superparamagnetic iron tetroxide The volume ratio of acetic acid solution to paraffin-Span-80 mixed solution is 1:1~1:10 (preferably 1:2); dropwise add glutaraldehyde solution, chitosan acetic acid solution of superparamagnetic iron tetraoxide and The mixed solution of paraffin, Span-80, and glutaraldehyde solution (preferably using analytical grade) have a volume ratio of 5:1 to 50:1 (preferably 25:1), and continue to stir at 20 to 80°C (preferably 40°C) After 60 minutes, let it fully react, then filter under reduced pressure, extract with petroleum ether and absolute ethanol for 1-10 times (preferably 3 times), and vacuum dry at 20-100°C (preferably 50°C) to obtain the product;
d.电气石/磁性壳聚糖微球(MCD)的制备d. Preparation of tourmaline/magnetic chitosan microspheres (MCD)
将上述磁性壳聚糖微球研磨成100~400目(优选为140目)粉后,再与电气石粉末按照质量比1:1~10:1(优选质量比为5:2)的比例充分混匀,制得混合粉末;将海藻酸钠、聚乙烯醇以及混合粉末按照1:1:1~1:10:12(优选质量比1:6:7)的比例制备微球;制备微球时先将海藻酸钠和聚乙烯醇加热溶解15min,随即加入混合粉末搅拌均匀,冷却5~60min(优选时间为20min)后用恒流泵以恒定流速连续地将悬浮液滴到含1~10wt%CaCl2(优选2wt%)的饱和硼酸溶液中固化。固化5~40h(优选20h)后滤出小球,用水冲洗干净后晾干备用。本发明具有如下的有益效果:Grind the above-mentioned magnetic chitosan microspheres into 100-400 mesh (preferably 140 mesh) powder, and then mix it with tourmaline powder in a mass ratio of 1:1-10:1 (preferably 5:2) Mix well to prepare mixed powder; prepare microspheres by mixing sodium alginate, polyvinyl alcohol and mixed powder according to the ratio of 1:1:1 to 1:10:12 (preferably mass ratio 1:6:7); prepare microspheres When heating and dissolving sodium alginate and polyvinyl alcohol for 15 minutes, then add the mixed powder and stir evenly, cool for 5 to 60 minutes (preferably 20 minutes), and then use a constant flow pump to continuously drop the suspension to a concentration of 1 to 10 wt at a constant flow rate. %CaCl 2 (preferably 2wt%) in a saturated boric acid solution for solidification. After curing for 5-40 hours (preferably 20 hours), the pellets are filtered out, rinsed with water, and then dried for later use. The present invention has following beneficial effect:
本发明水处理剂对饮用水源(如地下水、水库水等)中的挥发酚去除率可达80%~90%、铬的去除率可达93%,处理效果显著、参见具体实施方式部分,同时本发明处理剂具有吸附容量大、净化效率高、成本低、可再生、无毒、对环境无污染等优点。本发明水处理剂的制备方法简便、重复操作性强、成本低廉,适合工业化规模生产。The water treatment agent of the present invention can reach 80%-90% removal rate of volatile phenols in drinking water sources (such as groundwater, reservoir water, etc.), and 93% removal rate of chromium, and the treatment effect is remarkable, see the specific embodiment part, At the same time, the treatment agent of the present invention has the advantages of large adsorption capacity, high purification efficiency, low cost, renewability, non-toxicity, and no pollution to the environment. The preparation method of the water treatment agent of the invention is simple and convenient, has strong repeatability and low cost, and is suitable for industrial scale production.
具体实施方式Detailed ways
下面通过实施例对本发明进行具体的描述,有必要在此指出的是以下实施例只用于对本发明进行进一步说明,不能理解为对本发明保护范围的限制,该领域的技术人员可以根据上述本发明内容对本发明作出一些非本质的改进和调整。The present invention is specifically described below through the examples, it is necessary to point out that the following examples are only used to further illustrate the present invention, and can not be interpreted as limiting the protection scope of the present invention, those skilled in the art can according to the above-mentioned present invention Contents Some non-essential improvements and adjustments are made to the present invention.
实施例1Example 1
一种水处理剂,按以下步骤制得:A water treatment agent is prepared in the following steps:
a.电气石的预处理a. Pretreatment of tourmaline
将电气石粉碎过200目筛,用质量浓度为5%的NaOH溶液洗涤5~7次去除表面所附带的阴阳离子,再用去离子水清洗同样的次数过后,放于烘箱里面烘干,待用;Crush tourmaline through a 200-mesh sieve, wash 5-7 times with NaOH solution with a mass concentration of 5% to remove the anions and cations attached to the surface, and then wash with deionized water for the same number of times, then put it in an oven to dry, and wait for use;
b.超顺磁性四氧化三铁粉末的制备b. Preparation of superparamagnetic Fe3O4 powder
称取5.56g FeSO4·7H2O、6.5g FeCl3和1.7mL浓盐酸溶解于50mL预先经N2脱气处理蒸馏水中,然后将上述滴加到250mL1.0mol/L的NaOH溶液中;在80℃水浴中慢速(100r/min)搅拌5min,然后在快速机械搅拌(2000r/min),待溶液中出现黑色的沉淀,持续搅拌至30min;待反应结束后,静置冷却至室温,通过外加磁场分离黑色沉淀产物,分别用去离子水和无水乙醇清洗3次,在60℃的真空干燥箱中干燥12小时,待用。Weigh 5.56g FeSO 4 ·7H 2 O, 6.5g FeCl 3 and 1.7mL concentrated hydrochloric acid and dissolve in 50mL pre-degassed distilled water with N 2 , then add the above dropwise to 250mL 1.0mol/L NaOH solution; Stir at a slow speed (100r/min) in a water bath at 80°C for 5min, and then stir rapidly (2000r/min) mechanically, until a black precipitate appears in the solution, and continue to stir for 30min; The black precipitate was separated by applying an external magnetic field, washed three times with deionized water and absolute ethanol, and dried in a vacuum oven at 60°C for 12 hours before use.
c.磁性壳聚糖微球的制备c. Preparation of Magnetic Chitosan Microspheres
称取粒径20nm左右的超顺磁性四氧化三铁粉末加入到质量浓度为2%的壳聚糖乙酸溶液中,所述超顺磁性四氧化三铁与壳聚糖乙酸溶液的质量比为2:5;搅拌混合均匀后,转移至液体石蜡(分析纯)和Span-80(食用类)的混合液中,其中液体石蜡与Span-80体积比为40:1,调pH值至9.0,200r/min搅拌30min,其中超顺磁性四氧化三铁的壳聚糖乙酸溶液与石蜡—Span-80混合液的用量体积比为1:2;滴加戊二醛溶液,超顺磁性四氧化三铁的壳聚糖乙酸溶液与石蜡、Span-80的混合液,与戊二醛溶液(分析纯)体积比为25:1,在40℃下继续搅拌60min,使之充分反应,再减压过滤,依次用石油醚、无水乙醇抽提三次,在50℃条件下真空干燥,即得;The superparamagnetic ferric iron tetroxide powder that takes particle diameter about 20nm joins in the chitosan acetic acid solution that mass concentration is 2%, and the mass ratio of described superparamagnetic ferric ferric oxide and chitosan acetic acid solution is 2 :5; after stirring and mixing evenly, transfer to the mixed solution of liquid paraffin (analytical pure) and Span-80 (edible), wherein the volume ratio of liquid paraffin and Span-80 is 40:1, adjust the pH value to 9.0, 200r /min stirred for 30min, wherein the volume ratio of chitosan acetic acid solution of superparamagnetic ferric oxide to paraffin-Span-80 mixed solution was 1:2; glutaraldehyde solution was added dropwise, superparamagnetic ferric oxide The mixture of chitosan acetic acid solution, paraffin, and Span-80, with a volume ratio of glutaraldehyde solution (analytical pure) of 25:1, was stirred at 40°C for 60 minutes to fully react, and then filtered under reduced pressure. Sequentially extract three times with petroleum ether and absolute ethanol, and vacuum-dry at 50°C to obtain it;
d.电气石/磁性壳聚糖微球(MCD)的制备d. Preparation of tourmaline/magnetic chitosan microspheres (MCD)
将上述磁性壳聚糖微球研磨成140目粉后,再与上述电气石粉末按照5:2的比例充分混匀,制得混合粉末;将海藻酸钠、聚乙烯醇以及混合粉末按照质量比1:6:7的比例制备微球;制备微球时先将海藻酸钠和聚乙烯醇加热溶解15min,随即加入混合粉末搅拌均匀,冷却20min后用恒流泵以恒定流速连续地将悬浮液滴到含2%CaCl2的饱和硼酸溶液中固化,固化20h后滤出小球,用水冲洗干净后晾干备用。Grind the above-mentioned magnetic chitosan microspheres into 140-mesh powder, and then fully mix with the above-mentioned tourmaline powder according to the ratio of 5:2 to obtain a mixed powder; mix sodium alginate, polyvinyl alcohol and the mixed powder according to the mass ratio Prepare microspheres at a ratio of 1:6:7; when preparing microspheres, first heat and dissolve sodium alginate and polyvinyl alcohol for 15 minutes, then add the mixed powder and stir evenly, and after cooling for 20 minutes, use a constant flow pump to continuously pump the suspension at a constant flow rate. Drop it into a saturated boric acid solution containing 2% CaCl 2 for solidification, filter out the pellets after solidification for 20 hours, rinse them with water and dry them for later use.
实施例2~7:按以下各物料及步骤进行,其余同实施例1。Embodiment 2~7: carry out by following each material and step, all the other are with embodiment 1.
上述制得的电气石/磁性壳聚糖微球对水源水中挥发酚的去除率为78%~90%。The removal rate of the tourmaline/magnetic chitosan microspheres prepared above is 78% to 90% for the volatile phenol in the source water.
应用实施例1Application Example 1
电气石/磁性壳聚糖微球(MCD)微球净化水样Tourmaline/Magnetic Chitosan Microspheres (MCD) Microspheres Purify Water Samples
1、对水中挥发酚的去除实验1. Experiment on the removal of volatile phenol in water
取50ml水源水(含挥发酚0.0043—0.0049mg/L)的水样于250ml三角瓶中,加实施例1制得的MCD微球,调节实验条件,在恒温振荡箱中振荡一定时间后静置、过滤,用测定滤液中的酚含量,通过计算即可得出MCD对挥发酚的去除率。实验设计如表1、表2所示。每一试验均重复三次,取其平均值。Get the water sample of 50ml source water (containing volatile phenol 0.0043-0.0049mg/L) in the 250ml Erlenmeyer flask, add the MCD microsphere that embodiment 1 makes, adjust experimental condition, leave standstill after oscillating for a certain period of time in the constant temperature oscillation box , Filtration, use to measure the phenol content in the filtrate, and the removal rate of MCD to volatile phenol can be obtained by calculation. The experimental design is shown in Table 1 and Table 2. Each experiment was repeated three times, and the average value was taken.
(1)、单因素实验(1), single factor experiment
表1 单因素实验设计Table 1 Single factor experimental design
(2)、二次回归政教旋转组合(2), secondary regression combination of political and religious rotation
在上述基础上采用二次回归正交旋转组合3(1/2)设计对MCD小球对水中挥发性苯酚的因素进行设计,取MCD投加量(x1)、溶液pH值(x2)和反应时间(x3)作为三个考察因素,每个因素选取五个水平,见表2。On the basis of the above, the quadratic regression orthogonal rotation combination 3 (1/2) design is used to design the factors of MCD pellets on volatile phenol in water, and the dosage of MCD (x 1 ) and the pH value of the solution (x 2 ) are taken. and reaction time (x 3 ) are used as three factors to be investigated, and five levels are selected for each factor, as shown in Table 2.
表2 正交试验因素水平编码表Table 2 Orthogonal test factor level coding table
2、对水中Cr的去除实验2. Experiment on the removal of Cr in water
取50ml水源水(含Cr0.045-0.056mg/L)于250ml三角瓶中,加入实施例1制得的MCD微球,调节实验条件,在恒温振荡箱中振荡一定时间后静置、过滤,用气相色谱法测定滤液中的挥发酚,用原子吸收分光光度法测定滤液中的Cr(VI),通过计算即可得出微球对Cr(VI)的去除率。实验设计如表1、表2所示。每一试验均重复三次,取其平均值。Get 50ml source water (containing Cr0.045-0.056mg/L) in the 250ml Erlenmeyer flask, add the MCD microspheres that embodiment 1 makes, adjust experimental condition, leave standstill, filter after vibrating in constant temperature shaking box for a certain hour, The volatile phenol in the filtrate was measured by gas chromatography, the Cr(VI) in the filtrate was measured by atomic absorption spectrophotometry, and the removal rate of Cr(VI) by the microspheres could be obtained by calculation. The experimental design is shown in Table 1 and Table 2. Each experiment was repeated three times, and the average value was taken.
表1 单因素实验设计Table 1 Single factor experimental design
表2 正交试验因素水平编码表Table 2 Orthogonal test factor level coding table
(3)结论:(3) Conclusion:
1、对水中挥发酚的去除实验1. Experiment on the removal of volatile phenol in water
(1)单因素实验表明,MCD小球可用于去除水中的挥发性酚类,MCD投加量、溶液pH值、反应时间等对水中挥发酚的去除有一定的影响,在pH为10、振荡时间为1.5h、MCD投加量2.5g时,水中挥发酚的潜在去除率达84.17%。(1) Single factor experiments show that MCD pellets can be used to remove volatile phenols in water. When the time is 1.5h and the dosage of MCD is 2.5g, the potential removal rate of volatile phenol in water reaches 84.17%.
(2)在单因素实验基础上,运用回归设计的理论与方法,通过DPS数据处理系统确定了最佳实验条件:MCD投加量为2.16g、处理时间为1.12h、pH值为10.55,在此条件下水中挥发酚的去除率达90.72%。(2) On the basis of the single factor experiment, using the theory and method of regression design, the optimal experimental conditions were determined through the DPS data processing system: the dosage of MCD was 2.16g, the processing time was 1.12h, and the pH value was 10.55. Under this condition, the removal rate of volatile phenol in water reaches 90.72%.
2、对水中铬的去除实验2. Chromium removal experiment in water
(1)单因素实验表明,MCD用于去除水源水中的铬,在投加量为3g、pH为6、反应时间为90min时,水源水中铬的去除率达到最佳。(1) The single factor experiment shows that when MCD is used to remove chromium in source water, the removal rate of chromium in source water reaches the best when the dosage is 3g, the pH is 6, and the reaction time is 90min.
(2)在单因素实验基础上,运用回归设计的理论与方法,通过DPS数据处理系统确定的最佳实验条件:微球投加量为2.444g、溶液pH值4.6、反应时间为80.4min,在此条件下水源水中铬去除率达93.13%。(2) Based on the single factor experiment, using the theory and method of regression design, the optimal experimental conditions determined by the DPS data processing system: the dosage of microspheres is 2.444g, the pH value of the solution is 4.6, and the reaction time is 80.4min. Under these conditions, the removal rate of chromium in source water can reach 93.13%.
(3)在单因素实验基础上,运用回归设计的理论与方法,通过DPS数据处理系统确定了最佳实验条件:反应时间为80.4min,pH值为4.6,微球投加量为2.444g。在此条件下,根据数学模型推知水源水中Cr(VI)去除率可达93.93%。(3) Based on the single factor experiment, using the theory and method of regression design, the optimal experimental conditions were determined through the DPS data processing system: the reaction time was 80.4min, the pH value was 4.6, and the dosage of microspheres was 2.444g. Under these conditions, according to the mathematical model, the removal rate of Cr(VI) in source water can reach 93.93%.
Claims (1)
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201310096962.7A CN103127917B (en) | 2011-09-23 | 2011-09-23 | Preparation method of drinking water treatment agent |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201310096962.7A CN103127917B (en) | 2011-09-23 | 2011-09-23 | Preparation method of drinking water treatment agent |
Related Parent Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN 201110284933 Division CN102389780B (en) | 2011-09-23 | 2011-09-23 | A kind of water treatment agent and preparation method thereof |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| CN103127917A CN103127917A (en) | 2013-06-05 |
| CN103127917B true CN103127917B (en) | 2014-09-10 |
Family
ID=48488744
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN201310096962.7A Expired - Fee Related CN103127917B (en) | 2011-09-23 | 2011-09-23 | Preparation method of drinking water treatment agent |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN103127917B (en) |
Families Citing this family (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN109170532A (en) * | 2018-09-10 | 2019-01-11 | 福建拓天生物科技有限公司 | A kind of preparation method and application of Semen Coicis extract |
| CN111747520B (en) * | 2020-08-08 | 2024-11-26 | 浙江工业大学 | Device and method for promoting aerobic sludge granulation by using magnetic material combined with moving magnetic field |
| CN112915972A (en) * | 2021-01-22 | 2021-06-08 | 广州大学 | high-Cr (VI) adsorption amount core-shell structure high-molecular magnetic nanosphere and preparation method and application thereof |
| CN115652649A (en) * | 2022-11-15 | 2023-01-31 | 福建佳来户外服装有限公司 | Preparation method of water pressure resistant down jacket fabric |
Citations (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN1724142A (en) * | 2005-06-07 | 2006-01-25 | 武汉大学 | A kind of preparation method of chitosan composite adsorbent |
| CN101585563A (en) * | 2009-06-06 | 2009-11-25 | 吕安平 | New composite water purifying agent and a preparation method thereof |
| CN101844072A (en) * | 2010-06-03 | 2010-09-29 | 浙江碧岩环保材料有限公司 | Adsorption decomposition agent and preparation method thereof |
Family Cites Families (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2002282345A (en) * | 2001-03-27 | 2002-10-02 | Kuraray Chem Corp | Deodorizing filter |
-
2011
- 2011-09-23 CN CN201310096962.7A patent/CN103127917B/en not_active Expired - Fee Related
Patent Citations (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN1724142A (en) * | 2005-06-07 | 2006-01-25 | 武汉大学 | A kind of preparation method of chitosan composite adsorbent |
| CN101585563A (en) * | 2009-06-06 | 2009-11-25 | 吕安平 | New composite water purifying agent and a preparation method thereof |
| CN101844072A (en) * | 2010-06-03 | 2010-09-29 | 浙江碧岩环保材料有限公司 | Adsorption decomposition agent and preparation method thereof |
Non-Patent Citations (1)
| Title |
|---|
| JP特开2002-282345A 2002.10.02 |
Also Published As
| Publication number | Publication date |
|---|---|
| CN103127917A (en) | 2013-06-05 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| CN103127914B (en) | Magnetic chitosan microsphere treatment agent and preparation method thereof | |
| CN102389780B (en) | A kind of water treatment agent and preparation method thereof | |
| CN103127916B (en) | Preparation method of tourmaline/magnetic chitosan microsphere treatment agent | |
| CN102500333B (en) | Magnetic cationic surfactant modified chitosan/hydroxyapatite/zeolite composite and its preparation method and application | |
| CN102989427B (en) | Enteromorpha absorbent and preparation technology thereof | |
| CN104971699B (en) | A kind of modified zeolite organic matter complexing agent of sewage synchronous denitrification dephosphorizing and preparation method thereof, using and methods for using them | |
| CN101670266A (en) | Method for removing organic cationic dyes from waste water by magnetic nano adsorption material | |
| CN103754952B (en) | A kind of iron preparation method of synchronous removal heavy metal in waste water and application | |
| CN105597667B (en) | The preparation method of suspension ball-type concave convex rod adsorbent and its application for handling heavy metals in industrial wastewater | |
| CN107159112B (en) | The method that magnetic composite adsorbent removes tetracycline in waste water | |
| CN105032356B (en) | A kind of hollow ferrimanganic composite materials prepared based on etching template and its application | |
| CN103007881A (en) | Magnetically separated bamboo charcoal-based wastewater treatment agent and preparation method and application thereof | |
| CN102500337A (en) | Phosphorus removal adsorbent for modifying oyster shell with iron salt and preparation method as well as application thereof | |
| CN105668757B (en) | Graphene/sodium alginate bead of nano zero valence iron modification and its preparation method and application | |
| CN104258816B (en) | The preparation method of the exfoliated Nano composite material of montmorillonite of a kind of magnetic for wastewater treatment | |
| CN106475066A (en) | The preparation method of Magnaglo acticarbon, product and application | |
| CN103127917B (en) | Preparation method of drinking water treatment agent | |
| CN105921763B (en) | The preparation method of sodium alginate/inorganic mineral combined loading type nano zero valence iron | |
| CN105148835B (en) | Granular pattern 13X molecular sieves/attapulgite loaded Nanoscale Iron nickel material and preparation method thereof | |
| CN103127918B (en) | Preparation method of drinking water treatment agent | |
| CN102580698A (en) | Persimmon tannin adsorption material and preparation method thereof | |
| CN107081131B (en) | A tyrosine-modified ferroferric oxide magnetic nano-adsorption material and its preparation method and application | |
| CN101593593B (en) | Method for preparing magnetic nanophase materials for treating organic wastewater | |
| Peng et al. | Modified ginkgo leaves for adsorption of methyl violet and malachite green dyes in their aqueous system | |
| CN103736446A (en) | Magnetic responsiveness bentonite water treatment agent method |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| C06 | Publication | ||
| PB01 | Publication | ||
| C10 | Entry into substantive examination | ||
| SE01 | Entry into force of request for substantive examination | ||
| C14 | Grant of patent or utility model | ||
| GR01 | Patent grant | ||
| CF01 | Termination of patent right due to non-payment of annual fee |
Granted publication date: 20140910 Termination date: 20150923 |
|
| EXPY | Termination of patent right or utility model |