CN115501852A - Preparation method and application of metal-doped alumina hydrate with high adsorption performance - Google Patents
Preparation method and application of metal-doped alumina hydrate with high adsorption performance Download PDFInfo
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- PNEYBMLMFCGWSK-UHFFFAOYSA-N aluminium oxide Inorganic materials [O-2].[O-2].[O-2].[Al+3].[Al+3] PNEYBMLMFCGWSK-UHFFFAOYSA-N 0.000 title claims abstract description 59
- 238000001179 sorption measurement Methods 0.000 title claims abstract description 55
- 238000002360 preparation method Methods 0.000 title claims abstract description 33
- 239000000243 solution Substances 0.000 claims abstract description 89
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Chemical compound O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 39
- 239000008367 deionised water Substances 0.000 claims abstract description 37
- 229910021641 deionized water Inorganic materials 0.000 claims abstract description 37
- LYCAIKOWRPUZTN-UHFFFAOYSA-N Ethylene glycol Chemical compound OCCO LYCAIKOWRPUZTN-UHFFFAOYSA-N 0.000 claims abstract description 36
- 238000003756 stirring Methods 0.000 claims abstract description 34
- 229910052751 metal Inorganic materials 0.000 claims abstract description 27
- 239000002184 metal Substances 0.000 claims abstract description 27
- 239000012266 salt solution Substances 0.000 claims abstract description 22
- 239000011734 sodium Substances 0.000 claims abstract description 21
- 239000000463 material Substances 0.000 claims abstract description 20
- 238000001035 drying Methods 0.000 claims abstract description 18
- 238000000034 method Methods 0.000 claims abstract description 16
- DGAQECJNVWCQMB-PUAWFVPOSA-M Ilexoside XXIX Chemical compound C[C@@H]1CC[C@@]2(CC[C@@]3(C(=CC[C@H]4[C@]3(CC[C@@H]5[C@@]4(CC[C@@H](C5(C)C)OS(=O)(=O)[O-])C)C)[C@@H]2[C@]1(C)O)C)C(=O)O[C@H]6[C@@H]([C@H]([C@@H]([C@H](O6)CO)O)O)O.[Na+] DGAQECJNVWCQMB-PUAWFVPOSA-M 0.000 claims abstract description 14
- 229910052708 sodium Inorganic materials 0.000 claims abstract description 14
- 238000002156 mixing Methods 0.000 claims abstract description 12
- 238000005406 washing Methods 0.000 claims abstract description 11
- 238000001027 hydrothermal synthesis Methods 0.000 claims abstract description 9
- 239000000203 mixture Substances 0.000 claims abstract description 7
- 238000007865 diluting Methods 0.000 claims abstract description 5
- 150000003839 salts Chemical class 0.000 claims abstract description 4
- XLOMVQKBTHCTTD-UHFFFAOYSA-N Zinc monoxide Chemical compound [Zn]=O XLOMVQKBTHCTTD-UHFFFAOYSA-N 0.000 claims description 41
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 claims description 16
- LFQSCWFLJHTTHZ-UHFFFAOYSA-N Ethanol Chemical compound CCO LFQSCWFLJHTTHZ-UHFFFAOYSA-N 0.000 claims description 14
- RQNWIZPPADIBDY-UHFFFAOYSA-N arsenic atom Chemical compound [As] RQNWIZPPADIBDY-UHFFFAOYSA-N 0.000 claims description 12
- 229910021591 Copper(I) chloride Inorganic materials 0.000 claims description 11
- 229910052785 arsenic Inorganic materials 0.000 claims description 11
- OXBLHERUFWYNTN-UHFFFAOYSA-M copper(I) chloride Chemical compound [Cu]Cl OXBLHERUFWYNTN-UHFFFAOYSA-M 0.000 claims description 11
- 238000010438 heat treatment Methods 0.000 claims description 7
- 238000009835 boiling Methods 0.000 claims description 3
- 238000001816 cooling Methods 0.000 claims 2
- WMWXXXSCZVGQAR-UHFFFAOYSA-N dialuminum;oxygen(2-);hydrate Chemical compound O.[O-2].[O-2].[O-2].[Al+3].[Al+3] WMWXXXSCZVGQAR-UHFFFAOYSA-N 0.000 claims 2
- 230000000274 adsorptive effect Effects 0.000 claims 1
- 238000010790 dilution Methods 0.000 claims 1
- 239000012895 dilution Substances 0.000 claims 1
- XMVJITFPVVRMHC-UHFFFAOYSA-N roxarsone Chemical compound OC1=CC=C([As](O)(O)=O)C=C1[N+]([O-])=O XMVJITFPVVRMHC-UHFFFAOYSA-N 0.000 abstract description 5
- 229960003052 roxarsone Drugs 0.000 abstract description 4
- 239000011787 zinc oxide Substances 0.000 description 17
- 238000006243 chemical reaction Methods 0.000 description 11
- ANBBXQWFNXMHLD-UHFFFAOYSA-N aluminum;sodium;oxygen(2-) Chemical compound [O-2].[O-2].[Na+].[Al+3] ANBBXQWFNXMHLD-UHFFFAOYSA-N 0.000 description 9
- 229910001388 sodium aluminate Inorganic materials 0.000 description 9
- 239000002131 composite material Substances 0.000 description 8
- 229910021578 Iron(III) chloride Inorganic materials 0.000 description 6
- RBTARNINKXHZNM-UHFFFAOYSA-K iron trichloride Chemical compound Cl[Fe](Cl)Cl RBTARNINKXHZNM-UHFFFAOYSA-K 0.000 description 6
- 239000007788 liquid Substances 0.000 description 5
- HVTHJRMZXBWFNE-UHFFFAOYSA-J sodium zincate Chemical compound [OH-].[OH-].[OH-].[OH-].[Na+].[Na+].[Zn+2] HVTHJRMZXBWFNE-UHFFFAOYSA-J 0.000 description 5
- 238000002441 X-ray diffraction Methods 0.000 description 4
- 229910002706 AlOOH Inorganic materials 0.000 description 3
- 239000003463 adsorbent Substances 0.000 description 3
- 229910052782 aluminium Inorganic materials 0.000 description 3
- XAGFODPZIPBFFR-UHFFFAOYSA-N aluminium Chemical compound [Al] XAGFODPZIPBFFR-UHFFFAOYSA-N 0.000 description 3
- 239000002994 raw material Substances 0.000 description 3
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 2
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 description 2
- UQSXHKLRYXJYBZ-UHFFFAOYSA-N Iron oxide Chemical compound [Fe]=O UQSXHKLRYXJYBZ-UHFFFAOYSA-N 0.000 description 2
- 230000009286 beneficial effect Effects 0.000 description 2
- 230000015572 biosynthetic process Effects 0.000 description 2
- 238000005119 centrifugation Methods 0.000 description 2
- MPTQRFCYZCXJFQ-UHFFFAOYSA-L copper(II) chloride dihydrate Chemical compound O.O.[Cl-].[Cl-].[Cu+2] MPTQRFCYZCXJFQ-UHFFFAOYSA-L 0.000 description 2
- 230000018109 developmental process Effects 0.000 description 2
- 239000003344 environmental pollutant Substances 0.000 description 2
- 231100000719 pollutant Toxicity 0.000 description 2
- 239000002243 precursor Substances 0.000 description 2
- RYGMFSIKBFXOCR-UHFFFAOYSA-N Copper Chemical compound [Cu] RYGMFSIKBFXOCR-UHFFFAOYSA-N 0.000 description 1
- 229910002588 FeOOH Inorganic materials 0.000 description 1
- 235000008331 Pinus X rigitaeda Nutrition 0.000 description 1
- 235000011613 Pinus brutia Nutrition 0.000 description 1
- 241000018646 Pinus brutia Species 0.000 description 1
- 235000011449 Rosa Nutrition 0.000 description 1
- 239000000654 additive Substances 0.000 description 1
- 239000002154 agricultural waste Substances 0.000 description 1
- 239000003674 animal food additive Substances 0.000 description 1
- XKNKHVGWJDPIRJ-UHFFFAOYSA-N arsanilic acid Chemical compound NC1=CC=C([As](O)(O)=O)C=C1 XKNKHVGWJDPIRJ-UHFFFAOYSA-N 0.000 description 1
- 229950002705 arsanilic acid Drugs 0.000 description 1
- 150000001495 arsenic compounds Chemical class 0.000 description 1
- 125000003118 aryl group Chemical group 0.000 description 1
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 1
- 229910001593 boehmite Inorganic materials 0.000 description 1
- 239000003153 chemical reaction reagent Substances 0.000 description 1
- 238000010668 complexation reaction Methods 0.000 description 1
- 229910052802 copper Inorganic materials 0.000 description 1
- 239000010949 copper Substances 0.000 description 1
- AFXPFJXTHDSRSN-UHFFFAOYSA-L copper oxocopper dihydroxide Chemical compound [Cu]=O.[OH-].[Cu+2].[OH-] AFXPFJXTHDSRSN-UHFFFAOYSA-L 0.000 description 1
- 238000003113 dilution method Methods 0.000 description 1
- 239000003651 drinking water Substances 0.000 description 1
- 235000020188 drinking water Nutrition 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 239000003673 groundwater Substances 0.000 description 1
- 229940093920 gynecological arsenic compound Drugs 0.000 description 1
- 239000000383 hazardous chemical Substances 0.000 description 1
- 229910052739 hydrogen Inorganic materials 0.000 description 1
- 239000001257 hydrogen Substances 0.000 description 1
- FAHBNUUHRFUEAI-UHFFFAOYSA-M hydroxidooxidoaluminium Chemical compound O[Al]=O FAHBNUUHRFUEAI-UHFFFAOYSA-M 0.000 description 1
- 229910052500 inorganic mineral Inorganic materials 0.000 description 1
- 229910052742 iron Inorganic materials 0.000 description 1
- 244000144972 livestock Species 0.000 description 1
- 239000010871 livestock manure Substances 0.000 description 1
- 238000003760 magnetic stirring Methods 0.000 description 1
- 230000007246 mechanism Effects 0.000 description 1
- 229910044991 metal oxide Inorganic materials 0.000 description 1
- 150000004706 metal oxides Chemical class 0.000 description 1
- 244000005700 microbiome Species 0.000 description 1
- 239000011707 mineral Substances 0.000 description 1
- 239000002808 molecular sieve Substances 0.000 description 1
- 239000002086 nanomaterial Substances 0.000 description 1
- 230000010355 oscillation Effects 0.000 description 1
- 229910052760 oxygen Inorganic materials 0.000 description 1
- 239000001301 oxygen Substances 0.000 description 1
- 239000000575 pesticide Substances 0.000 description 1
- 238000001782 photodegradation Methods 0.000 description 1
- URGAHOPLAPQHLN-UHFFFAOYSA-N sodium aluminosilicate Chemical compound [Na+].[Al+3].[O-][Si]([O-])=O.[O-][Si]([O-])=O URGAHOPLAPQHLN-UHFFFAOYSA-N 0.000 description 1
- 239000002689 soil Substances 0.000 description 1
- 238000001228 spectrum Methods 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- 238000003786 synthesis reaction Methods 0.000 description 1
- 231100000331 toxic Toxicity 0.000 description 1
- 230000002588 toxic effect Effects 0.000 description 1
- 239000002351 wastewater Substances 0.000 description 1
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- 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
- B01J20/02—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
- B01J20/04—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising compounds of alkali metals, alkaline earth metals or magnesium
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- 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
- C02F1/281—Treatment of water, waste water, or sewage by sorption using inorganic sorbents
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- 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
- C02F2101/103—Arsenic compounds
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Abstract
Description
技术领域technical field
本发明属于复合材料的合成技术领域,具体涉及一种高吸附性能金属掺杂氧化铝水合物的制备方法及其应用。The invention belongs to the technical field of composite material synthesis, and in particular relates to a preparation method and application of a metal-doped alumina hydrate with high adsorption performance.
背景技术Background technique
3-硝基-4-羟基苯胂酸(洛克沙砷,ROX)属于芳香族有机砷的一种,是一类新型的有机-无机复合型砷污染物。随着工业的发展,ROX作为禽畜类饲料添加剂以及农药添加剂被大量使用,该类有机砷化合物会随禽畜粪便以及土壤进入环境中,在微生物或者光降解作用下转化为毒性更强的无机砷,给生态环境和人体健康带来安全隐患[Chen W R,HuangC H.Surface adsorption of organoarsenic roxarsone and arsanilic acid on ironand aluminum oxides[J].Journal ofHazardous Materials,2012,227:378-385]。随着工业化的发展,地下水中的砷污染已经成为全球性的危机,全球对于砷在水中的浓度标准也日益严格,如砷废水排放标准为0.5mg/g,饮用水砷含量标准为10μg/L。因此,寻找合适的手段处理有机砷这种新型污染物污染已成为相关领域的工作重点。3-nitro-4-hydroxyphenylarsonic acid (roxarsarsenic, ROX) belongs to a kind of aromatic organic arsenic, and is a new type of organic-inorganic composite arsenic pollutant. With the development of industry, ROX is widely used as livestock feed additives and pesticide additives. This type of organic arsenic compounds will enter the environment with livestock manure and soil, and will be transformed into more toxic inorganic substances under the action of microorganisms or photodegradation. Arsenic poses safety hazards to the ecological environment and human health [Chen W R, Huang C H. Surface adsorption of organoarsenic roxarsone and arsanilic acid on iron and aluminum oxides [J]. Journal of Hazardous Materials, 2012, 227: 378-385]. With the development of industrialization, arsenic pollution in groundwater has become a global crisis, and the global standards for the concentration of arsenic in water are becoming increasingly stringent, such as the arsenic wastewater discharge standard of 0.5 mg/g, and the standard of arsenic content in drinking water of 10 μg/L . Therefore, finding suitable means to deal with organic arsenic, a new type of pollutant, has become the focus of work in related fields.
对于洛克沙砷吸附剂的制备主要利用金属配位作用、络合作用以及形成氢键和氧空位等机理,目前相关研究领域常用的去除水体中有机砷的吸附材料有活性炭、农业废弃物、金属氧化物、矿物粘土、纳米材料以及分子筛等[Xie X,Cheng H.Adsorption anddesorption of phenylarsonic acid compounds on metal oxide and hydroxide,andclay minerals[J].Science ofthe Total Environment,2021,757:143765.]。Wentao Fu等人[FuW,Lu D L,Yao H,et al.Simultaneous roxarsone photocatalytic degradationand arsenic adsorption removal by TiO2/FeOOH hybrid[J].Environmental Scienceand Pollution Research,2020,27(15):18434-18442.]采用水热法合成了双功能二氧化钛/铁水合物(TiO2/FeOOH)杂化物,同时光催化降解罗沙松和释放砷的吸附,并在吸附剂为0.1g/L、ROX浓度为10mg/L的吸附条件下得到了96%的砷吸附去除率。主要吸附机理是通过吸附剂表面丰富的羟基对ROX进行催化降解释放出As(V),而释放的As(V)被TiO2/FeOOH杂化物中加入的FeOOH快速吸收和去除,并对释放的无机砷离子进行吸附。所研究的TiO2/FeOOH杂化物具有良好的稳定性和可靠性,并提出了该杂化物降解罗沙松和释放无机砷的可能机理,其不足在于吸附剂的制备温度较高、制备周期长、制备工艺较为复杂(180℃,12h),并且未对高浓度ROX溶液进行去除研究。此外,Paola Santander等人[K,J,Ranganathan S,et al.Photocatalytic degradation of roxarsone by usingsynthesized ZnO nanoplates[J].Solar Energy,2017,157:335-341.]采用湿式化学法合成ZnO纳米板,并在紫外光照射下实现了ROX的有效光降解,在ZnO浓度为2.5g/L,ROX浓度为15mg/L的条件下实现了70%的降解效率;可能的光催化机理为ROX的光催化降解导致矿化为CO2和As(V)。Wan-Ru Chen等人[Chen W R,Huang C H.Surface adsorption oforganoarsenic roxarsone and arsanilic acid on iron and aluminum oxides[J].Journal ofHazardous Materials,2012,227:378-385]研究了ROX和ASA对铁和氧化铝的表面吸附,发现各种无机砷酸盐能迅速、大量地吸附在各种铁和铝氧化物上,而对于ROX,由于其砷酸基团,芳香族砷也可能强烈地吸附在铁和铝氧化物上。然而,文中纯金属氧化物的最终吸附容量并不令人满意。The preparation of roxars arsenic adsorbent mainly utilizes metal coordination, complexation and the formation of hydrogen bonds and oxygen vacancies and other mechanisms. At present, the commonly used adsorption materials for removing organic arsenic in water in related research fields include activated carbon, agricultural waste, metal Oxides, mineral clays, nanomaterials, and molecular sieves, etc. Wentao Fu et al.[FuW,Lu DL,Yao H,et al.Simultaneous roxarsone photocatalytic degradation and arsenic adsorption removal by TiO 2 /FeOOH hybrid[J].Environmental Science and Pollution Research,2020,27(15):18434-18442.] A bifunctional titanium dioxide/iron hydrate (TiO 2 /FeOOH) hybrid was synthesized by a hydrothermal method, which simultaneously photocatalytically degraded rosapine and released arsenic adsorption, and was developed at an adsorbent concentration of 0.1 g/L and a ROX concentration of 10 mg/ Under the adsorption condition of L, the arsenic adsorption removal rate of 96% was obtained. The main adsorption mechanism is to release As(V) through the catalytic degradation of ROX through the abundant hydroxyl groups on the surface of the adsorbent, and the released As(V) is quickly absorbed and removed by FeOOH added to the TiO 2 /FeOOH hybrid, and the released As(V) Inorganic arsenic ions are adsorbed. The studied TiO 2 /FeOOH hybrid has good stability and reliability, and a possible mechanism for the hybrid to degrade roxapine and release inorganic arsenic is proposed. The disadvantage is that the preparation temperature of the adsorbent is high and the preparation cycle is long , The preparation process is relatively complicated (180°C, 12h), and the removal of high-concentration ROX solution has not been studied. Furthermore, Paola Santander et al. [ K, J,Ranganathan S,et al.Photocatalytic degradation of roxarsone by using synthesized ZnO nanoplates[J].Solar Energy,2017,157:335-341.] ZnO nanoplates were synthesized by wet chemical method, and ROX was realized under
综上,由于现有的ROX吸附材料往往存在制备工艺复杂、能耗高以及吸附容量较低等问题,寻找一种温和条件下用廉价的原材料清洁制备高吸附性能吸附材料的方法成为亟待解决的问题。In summary, because the existing ROX adsorption materials often have problems such as complex preparation process, high energy consumption, and low adsorption capacity, it is urgent to find a method to cleanly prepare adsorption materials with high adsorption performance using cheap raw materials under mild conditions. question.
发明内容Contents of the invention
针对现有技术中存在的问题,本发明的目的是提供一种易制备、原料易得、环境友好、对ROX具有优异吸附性能的金属掺杂改性氧化铝水合物吸附剂材料及其制备方法。In view of the problems existing in the prior art, the object of the present invention is to provide a metal-doped modified alumina hydrate adsorbent material that is easy to prepare, easy to obtain raw materials, environmentally friendly, and has excellent adsorption performance for ROX and its preparation method .
本发明的目的采用以下技术方案来实现:The object of the present invention adopts following technical scheme to realize:
第一方面,本发明提供一种高吸附性能金属掺杂氧化铝水合物的制备方法,其是采用一步水热法制备高吸附性能金属掺杂氧化铝水合物,包括以下步骤:In the first aspect, the present invention provides a method for preparing metal-doped alumina hydrate with high adsorption performance, which uses a one-step hydrothermal method to prepare metal-doped alumina hydrate with high adsorption performance, comprising the following steps:
步骤S1,配制金属盐溶液:Step S1, preparing metal salt solution:
将金属盐与去离子水混合,形成均匀的金属盐溶液;Mix the metal salt with deionized water to form a uniform metal salt solution;
步骤S2,制备偏铝酸钠溶液:Step S2, preparing sodium metaaluminate solution:
取NaAlO2和去离子水混合,搅拌至完全溶解后加入乙二醇,再次搅拌均匀,形成偏铝酸钠溶液;Mix NaAlO 2 with deionized water, stir until completely dissolved, add ethylene glycol, and stir again to form a sodium metaaluminate solution;
步骤S3,制备金属掺杂氧化铝水合物材料:Step S3, preparing metal-doped alumina hydrate material:
取金属盐溶液稀释后,再与偏铝酸钠溶液混合,然后依次经过搅拌混合、水热反应、离心、洗涤和干燥后,得到金属掺杂氧化铝水合物材料。After diluting the metal salt solution, mixing it with the sodium metaaluminate solution, stirring and mixing, hydrothermal reaction, centrifugation, washing and drying, the metal-doped alumina hydrate material is obtained.
优选地,所述步骤S1中的金属盐溶液包括Na2ZnO2溶液、FeCl3溶液和CuCl2溶液中的一种。Preferably, the metal salt solution in the step S1 includes one of Na 2 ZnO 2 solution, FeCl 3 solution and CuCl 2 solution.
优选地,所述Na2ZnO2溶液的配制过程为:Preferably, the preparation process of the Na2ZnO2 solution is :
取NaOH溶于去离子水中,搅拌至完全溶解,升温的同时逐渐加入ZnO,当ZnO全部加入后,将溶液升温至沸腾;然后保温并不断搅拌至溶液变得澄清,停止升温,自然冷却,降温至室温后,稀释处理,得到Na2ZnO2溶液。Dissolve NaOH in deionized water, stir until completely dissolved, gradually add ZnO while heating up, when all ZnO is added, raise the temperature of the solution to boiling; then keep warm and keep stirring until the solution becomes clear, stop heating, cool naturally, and lower the temperature After reaching room temperature, it was diluted to obtain a Na 2 ZnO 2 solution.
优选地,所述Na2ZnO2溶液的配制过程中,ZnO、NaOH与去离子水的质量比是10:23.2:20。Preferably, during the preparation of the Na 2 ZnO 2 solution, the mass ratio of ZnO, NaOH and deionized water is 10:23.2:20.
优选地,所述FeCl3溶液的配制过程为:Preferably, described FeCl The preparation process of solution is:
取FeCl3溶于去离子水中,搅拌至完全溶解,得到FeCl3溶液。Dissolve FeCl3 in deionized water and stir until completely dissolved to obtain FeCl3 solution.
优选地,所述FeCl3溶液的配制过程中,FeCl3与去离子水的质量比是5.95:20。Preferably, during the preparation of the FeCl3 solution, the mass ratio of FeCl3 to deionized water is 5.95:20.
优选地,所述CuCl2溶液的配制过程为:Preferably, the preparation process of the CuCl solution is:
取CuCl2·2H2O溶于去离子水中,搅拌至完全溶解得到CuCl2溶液。Dissolve CuCl 2 ·2H 2 O in deionized water and stir until completely dissolved to obtain a CuCl 2 solution.
优选地,所述CuCl2溶液的配制过程中,CuCl2·2H2O与去离子水的质量比是6.2:20。Preferably, during the preparation of the CuCl 2 solution, the mass ratio of CuCl 2 ·2H 2 O to deionized water is 6.2:20.
优选地,所述步骤S2中,NaAlO2、去离子水与乙二醇的质量比是1.2:15:25。Preferably, in the step S2, the mass ratio of NaAlO 2 , deionized water and ethylene glycol is 1.2:15:25.
优选地,所述步骤S3中,金属盐溶液的稀释处理过程为:金属盐溶液与去离子水按照4:6的体积比混合。Preferably, in the step S3, the dilution process of the metal salt solution is as follows: the metal salt solution and deionized water are mixed in a volume ratio of 4:6.
优选地,所述步骤S3中,稀释后的金属盐溶液与偏铝酸钠溶液按照体积比为10:40混合。Preferably, in the step S3, the diluted metal salt solution is mixed with the sodium metaaluminate solution at a volume ratio of 10:40.
优选地,所述步骤S3中,水热反应的温度是60℃,洗涤是使用去离子水洗涤3次后再用无水乙醇洗涤1次,干燥是在60℃的干燥箱内干燥24h。Preferably, in the step S3, the temperature of the hydrothermal reaction is 60° C., the washing is performed three times with deionized water and then once with absolute ethanol, and the drying is performed in a drying oven at 60° C. for 24 hours.
第二方面,本发明提供前述方法制备的高吸附性能金属掺杂氧化铝水合物,作为罗沙松ROX的吸附材料。In the second aspect, the present invention provides the metal-doped alumina hydrate with high adsorption performance prepared by the aforementioned method as the adsorption material of rosa pine ROX.
本发明提供的制备方法及高吸附性能金属掺杂氧化铝水合物的应用,其有益效果为:The preparation method provided by the present invention and the application of metal-doped alumina hydrate with high adsorption performance have the beneficial effects of:
(1)金属掺杂氧化铝水合物复合材料的制备环境温和、操作简单且制备过程环境友好,铝源NaAlO2廉价易得。(1) The preparation environment of the metal-doped alumina hydrate composite material is mild, the operation is simple and the preparation process is environmentally friendly, and the aluminum source NaAlO 2 is cheap and easy to obtain.
(2)本发明制备的金属掺杂氧化铝水合物材料对ROX溶液的吸附性能显著改善,和单一的氧化铝水合物材料相比,其对ROX的吸附容量显著提高。(2) The adsorption performance of the metal-doped alumina hydrate material prepared by the present invention to ROX solution is significantly improved, and compared with the single alumina hydrate material, its adsorption capacity to ROX is significantly improved.
附图说明Description of drawings
利用附图对本发明作进一步说明,但附图中的实施例不构成对本发明的任何限制,对于本领域的普通技术人员,在不付出创造性劳动的前提下,还可以根据以下附图获得其它的附图。The present invention is further described by using the accompanying drawings, but the embodiments in the accompanying drawings do not constitute any limitation to the present invention. For those of ordinary skill in the art, without paying creative work, other embodiments can also be obtained according to the following accompanying drawings Attached picture.
图1是实施例1-6制备得到的金属掺杂氧化铝水合物的XRD图谱;Fig. 1 is the XRD pattern of the metal-doped alumina hydrate prepared in embodiment 1-6;
图2是实施例1-4制备得到的金属掺杂氧化铝水合物的XRD图谱放大图;2 is an enlarged view of the XRD spectrum of the metal-doped alumina hydrate prepared in Examples 1-4;
图3是当初始ROX的浓度为100mg/g时,实施例1-6制备得到的金属掺杂氧化铝水合物的吸附动力学曲线;Fig. 3 is when the concentration of initial ROX is 100mg/g, the adsorption kinetic curve of the metal-doped alumina hydrate that embodiment 1-6 prepares;
图4是实施例5所制备得到的金属掺杂氧化铝水合物的吸附等温线。Fig. 4 is the adsorption isotherm of the metal-doped alumina hydrate prepared in Example 5.
具体实施方式detailed description
为了更清楚的说明本发明,对本发明的技术特征、目的和有益效果有更加清楚的理解,现对本发明的技术方案进行以下详细说明,但不能理解为对本发明的可实施范围的限定。In order to illustrate the present invention more clearly and have a clearer understanding of the technical features, purposes and beneficial effects of the present invention, the technical solutions of the present invention are now described in detail below, but it cannot be interpreted as limiting the scope of the present invention.
以下实施例中所用的原料、试剂或装置如无特殊说明,均可从常规商业途径得到,或者可以通过现有已知方法得到。下列实施例中涉及的原料均可从商业渠道获得。本发明实验过程各实施例所指的室温为25℃。Unless otherwise specified, the raw materials, reagents or devices used in the following examples can be obtained from conventional commercial channels, or can be obtained by existing known methods. The raw materials involved in the following examples are all available from commercial sources. The room temperature referred to in each embodiment of the experimental process of the present invention is 25°C.
自制铝酸钠溶液:室温下将1.2g的铝酸钠溶解于15mL的去离子水中,磁力搅拌后形成溶液,铝酸钠溶液的浓度为0.97mol/L。Self-made sodium aluminate solution: Dissolve 1.2 g of sodium aluminate in 15 mL of deionized water at room temperature, and form a solution after magnetic stirring. The concentration of the sodium aluminate solution is 0.97 mol/L.
自制锌酸钠溶液:室温下将23.2g的NaOH溶于20mL去离子水中,搅拌至完全溶解。将上述溶液加热的同时先后5次分批加入10g的ZnO,当所有ZnO全部加入后,将溶液加热至微微沸腾;继续加热到溶液逐渐澄清后将其冷却,搅拌至室温后将溶液稀释至40mL,得到锌酸钠浓度为1.83mol/L,在制备实施例样品时根据需要稀释至不同浓度。Self-made sodium zincate solution: Dissolve 23.2g of NaOH in 20mL of deionized water at room temperature, and stir until completely dissolved. While heating the above solution, add 10g of ZnO in batches 5 times successively. When all the ZnO is added, heat the solution to a slight boiling; continue heating until the solution gradually becomes clear, then cool it down, stir to room temperature and dilute the solution to 40mL , the concentration of sodium zincate obtained is 1.83mol/L, and it is diluted to different concentrations as required when preparing the samples of the examples.
以下结合附图及实施例对本发明作进一步描述。The present invention will be further described below in conjunction with the accompanying drawings and embodiments.
实施例1:Example 1:
本发明实施例提供的高吸附性能金属掺杂氧化铝水合物的制备方法,其是采用一步水热法制备高吸附性能金属掺杂氧化铝水合物,具体包括以下步骤:The preparation method of metal-doped alumina hydrate with high adsorption performance provided by the embodiment of the present invention is to prepare metal-doped alumina hydrate with high adsorption performance by a one-step hydrothermal method, which specifically includes the following steps:
步骤S1,配制金属盐溶液:Step S1, preparing metal salt solution:
将金属盐与去离子水混合,形成均匀的金属盐溶液;Mix the metal salt with deionized water to form a uniform metal salt solution;
步骤S2,制备偏铝酸钠溶液:Step S2, preparing sodium metaaluminate solution:
取NaAlO2和去离子水混合,搅拌至完全溶解后加入乙二醇,再次搅拌均匀,形成偏铝酸钠溶液;Mix NaAlO 2 with deionized water, stir until completely dissolved, add ethylene glycol, and stir again to form a sodium metaaluminate solution;
步骤S3,制备金属掺杂氧化铝水合物材料:Step S3, preparing metal-doped alumina hydrate material:
取金属盐溶液稀释后,再与偏铝酸钠溶液混合,然后依次经过搅拌混合、水热反应、离心、洗涤和干燥后,得到金属掺杂氧化铝水合物材料。After diluting the metal salt solution, mixing it with the sodium metaaluminate solution, stirring and mixing, hydrothermal reaction, centrifugation, washing and drying, the metal-doped alumina hydrate material is obtained.
具体的,包括如下步骤:Specifically, the following steps are included:
S1:室温下取15mL自制铝酸钠溶液于烧杯中,快速加入25mL乙二醇,磁力搅拌1min形成均匀清液,再向上述体系中加入10mL去离子水,剧烈搅拌2min;S1: Take 15mL of self-made sodium aluminate solution in a beaker at room temperature, quickly add 25mL of ethylene glycol, stir magnetically for 1 minute to form a uniform clear liquid, then add 10mL of deionized water to the above system, and stir vigorously for 2 minutes;
S2:将上述反应体系置于60℃烘箱中水热4h,将反应后的混合物离心,用去离子水洗涤3次后再用乙醇洗涤1次,再在60℃干燥箱中干燥24h,得到无掺杂的水合氧化铝样品,将该样品标记为AlOOH。S2: Put the above reaction system in an oven at 60°C for 4 hours, centrifuge the reacted mixture, wash it with deionized water for 3 times, wash it with ethanol once, and dry it in a drying oven at 60°C for 24 hours to obtain A sample of doped hydrated alumina, labeled AlOOH.
S3:将该样品吸附50mL、初始浓度为100mg/L的ROX溶液。配制50mL、初始浓度为100mg/L的ROX溶液,加入20mg上述样品,置于振荡箱中吸附12h,测得该条件下该样品的平衡吸附量为142.3mg/g。S3: Adsorb the sample with 50 mL of ROX solution with an initial concentration of 100 mg/L. Prepare 50mL of ROX solution with an initial concentration of 100mg/L, add 20mg of the above sample, and place it in a shaking box for adsorption for 12h. The equilibrium adsorption capacity of the sample under this condition is measured to be 142.3mg/g.
实施例2:Example 2:
本实施例提供的高吸附性能金属掺杂氧化铝水合物的制备方法及其应用,与实施例1基本上相同,其不同之处在于,其包括以下步骤:The preparation method and application of the metal-doped alumina hydrate with high adsorption performance provided in this example are basically the same as in Example 1, except that it includes the following steps:
S1:室温下将6.20g的二水氯化铜分散于20mL去离子水中;S1: Disperse 6.20 g of copper chloride dihydrate in 20 mL of deionized water at room temperature;
S2:室温下取15mL自制铝酸钠溶液于烧杯中,快速加入25mL乙二醇,磁力搅拌1min形成均匀清液;S2: Take 15mL self-made sodium aluminate solution in a beaker at room temperature, quickly add 25mL ethylene glycol, and magnetically stir for 1min to form a uniform clear solution;
S3:取4.0mL步骤(1)中得到的氯化铜溶液,先稀释至10mL,再逐滴加入步骤(2)所述的反应体系中;剧烈搅拌2min后将反应体系置于60℃烘箱中水热4h;用去离子水洗涤3次后再用乙醇洗涤1次,随后在60℃的干燥箱中干燥24h,得到Cu-掺杂的样品。XRD分析表明,该样品中铜以氧化铜-氢氧化铜存在,铝以非晶相的水合氧化铝存在;将该金属掺杂氧化铝水合物样品标记为CuO/AlOOH;S3: Take 4.0 mL of the copper chloride solution obtained in step (1), dilute it to 10 mL, and then add it dropwise to the reaction system described in step (2); after stirring vigorously for 2 minutes, place the reaction system in an oven at 60°C Hydrothermal for 4 h; washed with deionized water for 3 times and then with ethanol for 1 time, followed by drying in a drying oven at 60 °C for 24 h to obtain Cu-doped samples. XRD analysis shows that the copper in the sample exists as copper oxide-copper hydroxide, and the aluminum exists as amorphous hydrated alumina; the metal-doped alumina hydrate sample is marked as CuO/AlOOH;
S4:用该样品吸附50mL、初始浓度为100mg/L的ROX溶液。配制50mL、初始浓度为100mg/L的ROX溶液,加入20mg上述样品,置于振荡箱中吸附12h,测得该条件下该样品的平衡吸附量为183.3mg/g。S4: Use the sample to absorb 50 mL of ROX solution with an initial concentration of 100 mg/L. Prepare 50mL of ROX solution with an initial concentration of 100mg/L, add 20mg of the above sample, and place it in a shaking box for adsorption for 12h. The equilibrium adsorption capacity of the sample under this condition is measured to be 183.3mg/g.
实施例3:Example 3:
本实施例提供的高吸附性能金属掺杂氧化铝水合物的制备方法及其应用,与实施例1、2均基本上相同,其不同之处在于,包括以下步骤:The preparation method and application of the high-adsorption performance metal-doped alumina hydrate provided in this example are basically the same as those in Examples 1 and 2, except that the following steps are included:
S1:室温下将5.95g的氯化铁分散于20mL去离子水中;S1: Disperse 5.95g of ferric chloride in 20mL of deionized water at room temperature;
S2:室温下取15mL自制铝酸钠溶液于烧杯中,快速加入25mL乙二醇,磁力搅拌1min形成均匀清液;S2: Take 15mL self-made sodium aluminate solution in a beaker at room temperature, quickly add 25mL ethylene glycol, and magnetically stir for 1min to form a uniform clear liquid;
S3:取4.0mL步骤(1)中得到的氯化铁溶液,先稀释至10mL,再逐滴加入步骤(2)所述的反应体系中;剧烈搅拌2min后将反应体系置于60℃烘箱中,水热4h;用去离子水洗涤3次后再用乙醇洗涤1次,再在60℃干燥箱中干燥24h,得到Fe-掺杂的样品。XRD分析表明,该样品为非晶相的水合氧化铁与非晶相的水合氧化铝复合材料;将该金属掺杂氧化铝水合物样品标记为FeOOH/AlOOH。S3: Take 4.0 mL of the ferric chloride solution obtained in step (1), dilute it to 10 mL, and then add it dropwise to the reaction system described in step (2); after stirring vigorously for 2 minutes, place the reaction system in an oven at 60°C , hydrothermal for 4h; washed with deionized water for 3 times and then with ethanol for 1 time, and then dried in a 60°C drying oven for 24h to obtain Fe-doped samples. XRD analysis shows that the sample is a composite material of amorphous phase hydrated iron oxide and amorphous phase hydrated alumina; the metal-doped alumina hydrate sample is marked as FeOOH/AlOOH.
S4:将该样品吸附50mL、初始浓度为100mg/L的ROX溶液。配制50mL、初始浓度为100mg/L的ROX溶液,加入20mg上述样品,置于振荡箱中吸附12h,测得该条件下该样品的平衡吸附量为198.1mg/g。S4: Adsorb the sample with 50 mL of ROX solution with an initial concentration of 100 mg/L. Prepare 50mL of ROX solution with an initial concentration of 100mg/L, add 20mg of the above sample, and place it in a shaking box for adsorption for 12h. The equilibrium adsorption capacity of the sample under this condition is measured to be 198.1mg/g.
实施例4:Example 4:
本实施例提供的高吸附性能金属掺杂氧化铝水合物的制备方法及其应用,与实施例1-3均基本上相同,其不同之处在于,包括以下步骤:The preparation method and application of the high-adsorption performance metal-doped alumina hydrate provided in this example are basically the same as those in Examples 1-3, except that the following steps are included:
(1)室温下取15mL自制铝酸钠溶液于烧杯中,快速加入30mL乙二醇,磁力搅拌1min形成均匀清液;(1) Take 15 mL of homemade sodium aluminate solution in a beaker at room temperature, quickly add 30 mL of ethylene glycol, and stir magnetically for 1 min to form a uniform clear liquid;
(2)取0.5mL自制锌酸钠溶液,先稀释至10mL,再逐滴加入步骤(1)所述的反应液中;剧烈搅拌2min后将反应体系置于70℃烘箱中水热2h;用去离子水洗涤3次后再用乙醇洗涤1次,再在60℃干燥箱中干燥24h,得到Zn-掺杂的样品。XRD分析表明,该样品为氧化锌与非晶相水合氧化铝的复合材料;将该金属掺杂氧化铝水合物样品标记为ZnO/AlOOH-1。(2) Take 0.5mL self-made sodium zincate solution, first dilute to 10mL, and then add dropwise to the reaction solution described in step (1); after stirring vigorously for 2min, place the reaction system in a 70°C oven for 2h; The Zn-doped samples were obtained by washing with deionized water for 3 times and then with ethanol for 1 time, and then drying in a 60°C drying oven for 24 h. XRD analysis showed that the sample was a composite material of zinc oxide and alumina hydrate in amorphous phase; the metal-doped alumina hydrate sample was labeled as ZnO/AlOOH-1.
(3)用该样品吸附50mL、初始浓度为100mg/L的ROX溶液。配制50mL、初始浓度为100mg/L的ROX溶液,加入20mg上述样品,置于振荡箱中吸附12h,测得该条件下该样品的平衡吸附量为166.3mg/g。(3) Use the sample to absorb 50 mL of ROX solution with an initial concentration of 100 mg/L. Prepare 50mL of ROX solution with an initial concentration of 100mg/L, add 20mg of the above sample, and place it in a shaking box for adsorption for 12h. The equilibrium adsorption capacity of the sample under this condition is measured to be 166.3mg/g.
实施例5:Example 5:
本实施例提供的高吸附性能金属掺杂氧化铝水合物的制备方法及其应用,与实施例1-4均基本上相同,其不同之处在于,包括以下步骤:The preparation method and application of the high-adsorption performance metal-doped alumina hydrate provided in this example are basically the same as those in Examples 1-4, except that the following steps are included:
(1)室温下取15mL自制铝酸钠溶液于烧杯中,快速加入30mL乙二醇,磁力搅拌1min形成均匀清液;(1) Take 15 mL of homemade sodium aluminate solution in a beaker at room temperature, quickly add 30 mL of ethylene glycol, and stir magnetically for 1 min to form a uniform clear liquid;
(2)取2mL自制锌酸钠溶液,先稀释至10mL,再逐滴加入步骤(1)所述的反应液中;剧烈搅拌2min后将反应体系置于60℃烘箱中水热4h;用去离子水洗涤3次后再用乙醇洗涤1次,再在60℃干燥箱中干燥24h,得到Zn-掺杂的样品。该样品为氧化锌与非晶相水合氧化铝的复合材料;将该金属掺杂氧化铝水合物样品标记为ZnO/AlOOH-2。(2) Take 2 mL of self-made sodium zincate solution, dilute it to 10 mL, and then add it dropwise to the reaction solution described in step (1); after stirring vigorously for 2 minutes, place the reaction system in a 60°C oven for 4 hours; The Zn-doped samples were obtained by washing with deionized water for 3 times and then with ethanol for 1 time, and drying in a drying oven at 60 °C for 24 h. The sample is a composite material of zinc oxide and alumina hydrate in amorphous phase; the metal-doped alumina hydrate sample is marked as ZnO/AlOOH-2.
(3)将该样品吸附50mL、初始浓度为100mg/L的ROX溶液。配制50mL、初始浓度为50mg/L的ROX溶液,加入20mg上述样品,置于振荡箱中吸附12h,测得该条件下该样品的平衡吸附量为237.7mg/g。(3) Adsorb the sample with 50 mL of ROX solution with an initial concentration of 100 mg/L. Prepare 50mL of ROX solution with an initial concentration of 50mg/L, add 20mg of the above sample, and place it in a shaking box for adsorption for 12h. The equilibrium adsorption capacity of the sample under this condition is measured to be 237.7mg/g.
实施例6:Embodiment 6:
本实施例提供的高吸附性能金属掺杂氧化铝水合物的制备方法及其应用,与实施例1-5均基本上相同,其不同之处在于,包括以下步骤:The preparation method and application of the high-adsorption performance metal-doped alumina hydrate provided in this example are basically the same as those in Examples 1-5, except that the following steps are included:
(1)室温下取15mL自制铝酸钠溶液于烧杯中,快速加入20mL乙二醇,磁力搅拌1min形成均匀清液;(1) Take 15mL of homemade sodium aluminate solution in a beaker at room temperature, quickly add 20mL of ethylene glycol, and magnetically stir for 1min to form a uniform clear liquid;
(2)取4mL自制锌酸钠溶液,先稀释至10mL,再逐滴加入步骤(1)所述的反应液中;剧烈搅拌2min后将反应体系置于50℃烘箱中水热8h;用去离子水洗涤3次后再用乙醇洗涤1次,再在60℃干燥箱中干燥24h,得到Zn-掺杂的样品。该样品为氧化锌与非晶相水合氧化铝的复合材料;将该金属掺杂氧化铝水合物样品标记为ZnO/AlOOH-3。(2) Take 4 mL of self-made sodium zincate solution, dilute it to 10 mL, and then add it dropwise to the reaction solution described in step (1); after stirring vigorously for 2 minutes, place the reaction system in an oven at 50°C for 8 hours; The Zn-doped samples were obtained by washing with deionized water for 3 times and then with ethanol for 1 time, and drying in a drying oven at 60 °C for 24 h. The sample is a composite material of zinc oxide and alumina hydrate in amorphous phase; the metal-doped alumina hydrate sample is marked as ZnO/AlOOH-3.
(3)将该样品吸附50mL、初始浓度为100mg/L的ROX溶液。配制50mL、初始浓度为100mg/L的ROX溶液,加入20mg上述样品,置于振荡箱中吸附12h,测得该条件下该样品的平衡吸附量为236.5mg/g。(3) Adsorb the sample with 50 mL of ROX solution with an initial concentration of 100 mg/L. Prepare 50mL of ROX solution with an initial concentration of 100mg/L, add 20mg of the above sample, and place it in a shaking box for adsorption for 12h. The equilibrium adsorption capacity of the sample under this condition is measured to be 236.5mg/g.
应用实施例7:Application Example 7:
为了考察上述金属掺杂薄水铝石对于不同浓度ROX溶液的吸附能力,以实施例5所制备的吸附剂ZnO/AlOOH-2为例,测试其对不同初始浓度ROX溶液的吸附性能。吸附过程如下:配制浓度分别为20mg/L、100mg/L、300mg/L、500mg/L、1000mg/L的ROX溶液各50mL,随后分别加入0.02g的ZnO/AlOOH-2,置于振荡箱中吸附12h后使用紫外分光光度计对吸附效果进行测量,设置恒温振荡箱的参数为25℃、150r/min,实施例5所制备样品ZnO/AlOOH-2的吸附等温线见图3,其较佳吸附量为1110.8mg/g。In order to investigate the adsorption capacity of the metal-doped boehmite for ROX solutions with different concentrations, the adsorbent ZnO/AlOOH-2 prepared in Example 5 was taken as an example to test its adsorption performance for ROX solutions with different initial concentrations. The adsorption process is as follows: prepare 50mL of ROX solutions with concentrations of 20mg/L, 100mg/L, 300mg/L, 500mg/L, and 1000mg/L respectively, then add 0.02g of ZnO/AlOOH-2 respectively, and place them in the shaking box After 12 hours of adsorption, use a UV spectrophotometer to measure the adsorption effect. The parameters of the constant temperature oscillation box are set at 25°C and 150r/min. The adsorption isotherm of the sample ZnO/AlOOH-2 prepared in Example 5 is shown in Figure 3, which is better The adsorption capacity was 1110.8 mg/g.
其中,为了更加清晰地说明本发明,本发明还列出了以下表格,表1表明实施例1-6前驱液的配制以及样品的比较;表2是实施例1~6制备得到的金属掺杂氧化铝水合物样品对ROX的平衡吸附量和吸附去除率的比较;表3是实施例2对不同初始ROX浓度的吸附比较。Among them, in order to illustrate the present invention more clearly, the present invention also lists the following tables, Table 1 shows the preparation of the precursor solution of Examples 1-6 and the comparison of samples; Table 2 is the metal-doped samples prepared in Examples 1-6 Comparison of the equilibrium adsorption capacity and adsorption removal rate of alumina hydrate samples on ROX; Table 3 is the adsorption comparison of Example 2 on different initial ROX concentrations.
表1实施例1~6前驱液配制以及样品比较Table 1 Example 1 ~ 6 precursor solution preparation and sample comparison
表2实施例1~6对ROX的平衡吸附量和吸附去除率的比较The comparison of table 2
表3实施例2对不同初始ROX浓度的平衡吸附量的比较Table 3 Example 2 compares the equilibrium adsorption capacity of different initial ROX concentrations
本发明上述实施例提供的制备方法及高吸附性能金属掺杂氧化铝水合物的应用,其金属掺杂氧化铝水合物复合材料的制备环境温和、操作简单且制备过程环境友好,铝源NaAlO2廉价易得;本发明制备的金属掺杂氧化铝水合物材料对ROX溶液的吸附性能显著改善,和单一的氧化铝水合物材料相比,其对ROX的吸附容量显著提高。The preparation method and the application of the metal-doped alumina hydrate with high adsorption performance provided by the above-mentioned embodiments of the present invention, the preparation environment of the metal-doped alumina hydrate composite material is mild, the operation is simple, and the preparation process is environmentally friendly. The aluminum source NaAlO 2 Cheap and easy to obtain; the metal-doped alumina hydrate material prepared by the invention has significantly improved adsorption performance on ROX solution, and compared with single alumina hydrate material, its adsorption capacity on ROX has been significantly improved.
最后应当说明的是,以上实施例仅用以说明本发明的技术方案,而非对本发明保护范围的限制,尽管参照较佳实施例对本发明作了详细地说明,本领域的普通技术人员应当理解,可以对本发明的技术方案进行修改或者等同替换,而不脱离本发明技术方案的实质和范围。Finally, it should be noted that the above embodiments are only used to illustrate the technical solutions of the present invention, rather than limiting the protection scope of the present invention. Although the present invention has been described in detail with reference to the preferred embodiments, those of ordinary skill in the art should understand , the technical solution of the present invention may be modified or equivalently replaced without departing from the spirit and scope of the technical solution of the present invention.
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