CN116618033A - A kind of preparation method of organically modified sodium-based montmorillonite - Google Patents
A kind of preparation method of organically modified sodium-based montmorillonite Download PDFInfo
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- thymine
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- GUJOJGAPFQRJSV-UHFFFAOYSA-N dialuminum;dioxosilane;oxygen(2-);hydrate Chemical compound O.[O-2].[O-2].[O-2].[Al+3].[Al+3].O=[Si]=O.O=[Si]=O.O=[Si]=O.O=[Si]=O GUJOJGAPFQRJSV-UHFFFAOYSA-N 0.000 title claims abstract description 78
- 229910052901 montmorillonite Inorganic materials 0.000 title claims abstract description 65
- 238000002360 preparation method Methods 0.000 title claims description 4
- 150000003385 sodium Chemical class 0.000 title abstract description 6
- RWQNBRDOKXIBIV-UHFFFAOYSA-N thymine Chemical compound CC1=CNC(=O)NC1=O RWQNBRDOKXIBIV-UHFFFAOYSA-N 0.000 claims abstract description 116
- 229940113082 thymine Drugs 0.000 claims abstract description 59
- 238000000034 method Methods 0.000 claims abstract description 28
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 claims abstract description 24
- 238000003756 stirring Methods 0.000 claims abstract description 13
- 238000004321 preservation Methods 0.000 claims abstract 2
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 10
- 239000000203 mixture Substances 0.000 claims description 9
- 238000001035 drying Methods 0.000 claims description 7
- 238000002156 mixing Methods 0.000 claims description 7
- 229910021642 ultra pure water Inorganic materials 0.000 claims description 6
- 239000012498 ultrapure water Substances 0.000 claims description 6
- 238000005406 washing Methods 0.000 claims description 6
- 239000004677 Nylon Substances 0.000 claims description 4
- 229920001778 nylon Polymers 0.000 claims description 4
- 238000003860 storage Methods 0.000 claims description 4
- 239000006228 supernatant Substances 0.000 claims description 4
- 239000000047 product Substances 0.000 claims description 2
- 238000007605 air drying Methods 0.000 claims 1
- 239000007788 liquid Substances 0.000 claims 1
- 238000007873 sieving Methods 0.000 claims 1
- 238000001179 sorption measurement Methods 0.000 abstract description 16
- 229910052753 mercury Inorganic materials 0.000 abstract description 13
- 239000011734 sodium Substances 0.000 abstract description 12
- 229910052708 sodium Inorganic materials 0.000 abstract description 10
- 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 abstract description 9
- 229910017059 organic montmorillonite Inorganic materials 0.000 abstract description 7
- 238000010438 heat treatment Methods 0.000 abstract description 6
- 238000001027 hydrothermal synthesis Methods 0.000 abstract description 6
- 239000011229 interlayer Substances 0.000 abstract description 5
- 238000005265 energy consumption Methods 0.000 abstract description 4
- 239000003344 environmental pollutant Substances 0.000 abstract description 4
- 231100000719 pollutant Toxicity 0.000 abstract description 4
- -1 Mercury ions Chemical class 0.000 abstract description 3
- BQPIGGFYSBELGY-UHFFFAOYSA-N mercury(2+) Chemical compound [Hg+2] BQPIGGFYSBELGY-UHFFFAOYSA-N 0.000 abstract description 2
- 239000002351 wastewater Substances 0.000 abstract description 2
- 230000004048 modification Effects 0.000 description 20
- 238000012986 modification Methods 0.000 description 20
- 239000000243 solution Substances 0.000 description 13
- 239000010410 layer Substances 0.000 description 12
- QSHDDOUJBYECFT-UHFFFAOYSA-N mercury Chemical compound [Hg] QSHDDOUJBYECFT-UHFFFAOYSA-N 0.000 description 10
- 238000004833 X-ray photoelectron spectroscopy Methods 0.000 description 7
- 238000002474 experimental method Methods 0.000 description 7
- 239000003607 modifier Substances 0.000 description 7
- 239000002689 soil Substances 0.000 description 6
- 238000001228 spectrum Methods 0.000 description 5
- 238000005033 Fourier transform infrared spectroscopy Methods 0.000 description 4
- IQFYYKKMVGJFEH-XLPZGREQSA-N Thymidine Chemical compound O=C1NC(=O)C(C)=CN1[C@@H]1O[C@H](CO)[C@@H](O)C1 IQFYYKKMVGJFEH-XLPZGREQSA-N 0.000 description 4
- 238000010521 absorption reaction Methods 0.000 description 4
- 238000009830 intercalation Methods 0.000 description 4
- 230000002687 intercalation Effects 0.000 description 4
- 229910018557 Si O Inorganic materials 0.000 description 3
- 239000007864 aqueous solution Substances 0.000 description 3
- 230000008859 change Effects 0.000 description 3
- 238000003795 desorption Methods 0.000 description 3
- 238000002329 infrared spectrum Methods 0.000 description 3
- LIVNPJMFVYWSIS-UHFFFAOYSA-N silicon monoxide Inorganic materials [Si-]#[O+] LIVNPJMFVYWSIS-UHFFFAOYSA-N 0.000 description 3
- 231100000331 toxic Toxicity 0.000 description 3
- 230000002588 toxic effect Effects 0.000 description 3
- 240000002234 Allium sativum Species 0.000 description 2
- DWRXFEITVBNRMK-UHFFFAOYSA-N Beta-D-1-Arabinofuranosylthymine Natural products O=C1NC(=O)C(C)=CN1C1C(O)C(O)C(CO)O1 DWRXFEITVBNRMK-UHFFFAOYSA-N 0.000 description 2
- 235000010149 Brassica rapa subsp chinensis Nutrition 0.000 description 2
- 244000221633 Brassica rapa subsp chinensis Species 0.000 description 2
- 238000002441 X-ray diffraction Methods 0.000 description 2
- 238000004458 analytical method Methods 0.000 description 2
- 238000005452 bending Methods 0.000 description 2
- 230000009286 beneficial effect Effects 0.000 description 2
- IQFYYKKMVGJFEH-UHFFFAOYSA-N beta-L-thymidine Natural products O=C1NC(=O)C(C)=CN1C1OC(CO)C(O)C1 IQFYYKKMVGJFEH-UHFFFAOYSA-N 0.000 description 2
- 230000015572 biosynthetic process Effects 0.000 description 2
- 238000012512 characterization method Methods 0.000 description 2
- 239000003795 chemical substances by application Substances 0.000 description 2
- 239000002734 clay mineral Substances 0.000 description 2
- 238000001816 cooling Methods 0.000 description 2
- 239000007822 coupling agent Substances 0.000 description 2
- 230000003247 decreasing effect Effects 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- 235000004611 garlic Nutrition 0.000 description 2
- 229910001385 heavy metal Inorganic materials 0.000 description 2
- 230000002209 hydrophobic effect Effects 0.000 description 2
- 238000005342 ion exchange Methods 0.000 description 2
- 150000002500 ions Chemical class 0.000 description 2
- 239000000463 material Substances 0.000 description 2
- 239000002994 raw material Substances 0.000 description 2
- 239000010865 sewage Substances 0.000 description 2
- 239000003802 soil pollutant Substances 0.000 description 2
- 239000004094 surface-active agent Substances 0.000 description 2
- 229940104230 thymidine Drugs 0.000 description 2
- 229910018516 Al—O Inorganic materials 0.000 description 1
- 229910018512 Al—OH Inorganic materials 0.000 description 1
- 241000196324 Embryophyta Species 0.000 description 1
- 238000004566 IR spectroscopy Methods 0.000 description 1
- 229910008051 Si-OH Inorganic materials 0.000 description 1
- 229910004298 SiO 2 Inorganic materials 0.000 description 1
- 229910006358 Si—OH Inorganic materials 0.000 description 1
- 238000000026 X-ray photoelectron spectrum Methods 0.000 description 1
- CQBLUJRVOKGWCF-UHFFFAOYSA-N [O].[AlH3] Chemical compound [O].[AlH3] CQBLUJRVOKGWCF-UHFFFAOYSA-N 0.000 description 1
- OBNDGIHQAIXEAO-UHFFFAOYSA-N [O].[Si] Chemical compound [O].[Si] OBNDGIHQAIXEAO-UHFFFAOYSA-N 0.000 description 1
- 229910002091 carbon monoxide Inorganic materials 0.000 description 1
- 150000001768 cations Chemical class 0.000 description 1
- 238000006243 chemical reaction Methods 0.000 description 1
- 239000004927 clay Substances 0.000 description 1
- 239000002131 composite material Substances 0.000 description 1
- 238000002425 crystallisation Methods 0.000 description 1
- 230000008025 crystallization Effects 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 230000004907 flux Effects 0.000 description 1
- 125000000524 functional group Chemical group 0.000 description 1
- 230000003100 immobilizing effect Effects 0.000 description 1
- 230000003993 interaction Effects 0.000 description 1
- 238000002386 leaching Methods 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 238000002715 modification method Methods 0.000 description 1
- 239000002086 nanomaterial Substances 0.000 description 1
- 229910052760 oxygen Inorganic materials 0.000 description 1
- 239000002245 particle Substances 0.000 description 1
- 239000002957 persistent organic pollutant Substances 0.000 description 1
- 230000002265 prevention Effects 0.000 description 1
- 230000008569 process Effects 0.000 description 1
- 102000004169 proteins and genes Human genes 0.000 description 1
- 108090000623 proteins and genes Proteins 0.000 description 1
- 230000035484 reaction time Effects 0.000 description 1
- 230000000717 retained effect Effects 0.000 description 1
- 229910052604 silicate mineral Inorganic materials 0.000 description 1
- 229910001415 sodium ion Inorganic materials 0.000 description 1
- 239000002904 solvent Substances 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- 238000003786 synthesis reaction Methods 0.000 description 1
- 239000010891 toxic waste Substances 0.000 description 1
- 239000003643 water by type Substances 0.000 description 1
Classifications
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/30—Processes for preparing, regenerating, or reactivating
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09C—RECLAMATION OF CONTAMINATED SOIL
- B09C1/00—Reclamation of contaminated soil
-
- 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
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J2220/00—Aspects relating to sorbent materials
- B01J2220/40—Aspects relating to the composition of sorbent or filter aid materials
- B01J2220/48—Sorbents characterised by the starting material used for their preparation
- B01J2220/4812—Sorbents characterised by the starting material used for their preparation the starting material being of organic character
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/10—Inorganic compounds
- C02F2101/20—Heavy metals or heavy metal compounds
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- Chemical & Material Sciences (AREA)
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- Life Sciences & Earth Sciences (AREA)
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Analytical Chemistry (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Hydrology & Water Resources (AREA)
- Water Supply & Treatment (AREA)
- Soil Sciences (AREA)
- Silicates, Zeolites, And Molecular Sieves (AREA)
- Solid-Sorbent Or Filter-Aiding Compositions (AREA)
Abstract
本发明公开了一种有机改性钠基蒙脱土的制备方法,首先用硫酸将胸腺嘧啶完全溶解,其次将胸腺嘧啶溶液与钠基蒙脱土共混搅拌,最后对共混液进行洗涤及干燥后保存;利用溶液搅拌法对钠基蒙脱土进行胸腺嘧啶改性,避免了水热法和微波加热法耗能高,步骤繁琐的问题,且合成的新型有机蒙脱土对Hg2+吸附容量大,去除率高,不会对环境造成二次污染,改性后的T‑MMT不仅增加了层间距,还改变了蒙脱土表面的电荷性质及疏水性,使得蒙脱土更易吸附废水中的汞离子。
The invention discloses a method for preparing organically modified sodium-based montmorillonite. Firstly, sulfuric acid is used to completely dissolve thymine; After preservation; the sodium-based montmorillonite is modified with thymine by solution stirring method, which avoids the problems of high energy consumption and complicated steps of hydrothermal method and microwave heating method, and the synthesized new organic montmorillonite has a large adsorption capacity for Hg2+ , the removal rate is high, and will not cause secondary pollution to the environment. The modified T-MMT not only increases the interlayer spacing, but also changes the charge properties and hydrophobicity of the surface of the montmorillonite, making it easier for the montmorillonite to absorb the pollutants in the wastewater. Mercury ions.
Description
技术领域technical field
本发明属于环境修复固定技术领域,尤其涉及一种有机改性钠基蒙脱土的制备方法。The invention belongs to the technical field of environmental restoration and fixation, and in particular relates to a preparation method of organically modified sodium-based montmorillonite.
背景技术Background technique
近年来,粘土矿物在环境和有毒废物管理领域发挥着重要作用,因此被广泛研究用于固定污染物。粘土矿物中的蒙脱土由于其低成本、高丰度、大表面积、离子交换容量高、化学和机械稳定性强以及层状结构,因此是潜在的良好的吸附材料。蒙脱土是一种天然的纳米材料,有着“万用粘土”之称,其单位晶胞由两层硅氧四面体中夹一层铝氧八面体构成,是典型的2∶1型层状硅酸盐矿物。蒙脱土层间带负电,有利于阳离子进入蒙脱土层间,使蒙脱土层间由亲水性转变为亲油性。In recent years, clay minerals have been widely studied for immobilizing pollutants due to their important roles in the field of environment and toxic waste management. Among clay minerals, montmorillonite is a potentially good adsorption material due to its low cost, high abundance, large surface area, high ion exchange capacity, strong chemical and mechanical stability, and layered structure. Montmorillonite is a natural nanomaterial known as "universal clay". Its unit cell is composed of two layers of silicon-oxygen tetrahedron sandwiching a layer of aluminum-oxygen octahedron, which is a typical 2:1 layered structure. Silicate minerals. The montmorillonite layer is negatively charged, which is beneficial for cations to enter the montmorillonite layer, making the montmorillonite layer change from hydrophilic to lipophilic.
由于蒙脱土表面的亲水疏油性,对有机污染物亲和力不高,对重金属离子吸附选择性差且吸附容量低,导致蒙脱土无法在实际污水处理上大规模应用,因此对蒙脱土进行改性处理使其表面呈疏水性,从而可显著提高其去除水溶液中污染物的能力,有机改性蒙脱土在污染的有效防控和治理方面展现出优异的效果,能够适应更为复杂水域修复,市场应用潜力巨大,蒙脱土的有机改性方法主要有微波加热法、溶液搅拌法和水热法等,通过增加其层间距,改变蒙脱土的比表面积与孔径,进而提高其对污染物的吸附效果。微波加热法改性需要特殊的反应装置,改性效果受反应时间影响,且需要在溶剂中进行,因此也具有一定的局限性,水热法是将蒙脱土与有机改性剂混合,在水热反应釜中进行,需要较高能量。所以本实验选择简单、高效的溶液搅拌法制备有机蒙脱土;其次,现有技术的有机改性剂主要有表面活性剂、偶联剂等。表面活性剂和偶联剂在大量使用过程中易造成环境的二次污染且有毒。Due to the hydrophilic and oleophobic nature of the surface of montmorillonite, the affinity for organic pollutants is not high, the adsorption selectivity to heavy metal ions is poor, and the adsorption capacity is low, resulting in the large-scale application of montmorillonite in actual sewage treatment. Modification treatment makes the surface hydrophobic, which can significantly improve its ability to remove pollutants in aqueous solution. Organically modified montmorillonite shows excellent effects in the effective prevention and control of pollution and can adapt to more complex waters The market application potential is huge. The organic modification methods of montmorillonite mainly include microwave heating method, solution stirring method and hydrothermal method. adsorption of pollutants. Modification by microwave heating method requires a special reaction device. The modification effect is affected by the reaction time and needs to be carried out in a solvent, so it also has certain limitations. The hydrothermal method is to mix montmorillonite with an organic modifier. It is carried out in a hydrothermal reactor and requires high energy. Therefore, this experiment chooses simple and efficient solution stirring method to prepare organic montmorillonite; secondly, the organic modifiers in the prior art mainly include surfactants and coupling agents. Surfactants and coupling agents are likely to cause secondary pollution and are toxic to the environment when used in large quantities.
发明内容Contents of the invention
本发明要解决的技术问题是:提供一种有机改性钠基蒙脱土的制备方法,以解决现有技术水热法和微波加热法耗能高且制作步骤繁琐,有机改性剂有毒易导致二次污染等技术问题。The technical problem to be solved by the present invention is to provide a method for preparing organically modified sodium-based montmorillonite to solve the problem of high energy consumption and cumbersome production steps of the prior art hydrothermal method and microwave heating method, and the organic modifier is toxic and easily Lead to technical problems such as secondary pollution.
本发明技术方案是:Technical scheme of the present invention is:
一种有机改性钠基蒙脱土的制备方法,首先用硫酸将胸腺嘧啶完全溶解,其次将胸腺嘧啶溶液与钠基蒙脱土共混搅拌,最后对共混液进行洗涤及干燥后保存。A method for preparing organically modified sodium-based montmorillonite comprises the following steps: firstly, sulfuric acid is used to completely dissolve thymine; secondly, the thymine solution and sodium-based montmorillonite are blended and stirred; finally, the blended solution is washed and dried for storage.
胸腺嘧啶与钠基蒙脱土的质量比为7:100。The mass ratio of thymine to sodium montmorillonite is 7:100.
用硫酸将胸腺嘧啶完全溶解的方法为:按胸腺嘧啶与钠基蒙脱土的质量比称取胸腺嘧啶溶于1.5mol/L的硫酸溶液中,在水浴50℃搅拌120min使胸腺嘧啶完全溶解。The method for completely dissolving thymine with sulfuric acid is: weigh thymine and dissolve it in 1.5 mol/L sulfuric acid solution according to the mass ratio of thymine to sodium montmorillonite, stir in a water bath at 50°C for 120 minutes to completely dissolve thymine.
共混搅拌时间为10小时。The blending and stirring time was 10 hours.
对共混液进行洗涤及干燥的方法为:将共混液冷却至室温,用超纯水洗3次并在4500r/min的离心机上离心5min,倾倒上清液后,再将样品于电热鼓风干燥箱中55℃干燥6h。The method of washing and drying the blend is as follows: cool the blend to room temperature, wash 3 times with ultrapure water and centrifuge for 5 minutes on a centrifuge at 4500r/min, pour the supernatant, and then place the sample in an electric blast drying box Dry at 55°C for 6h.
将干燥后的T-MMT过100目尼龙筛,最后将得到的胸腺嘧啶蒙脱土成品放入密封袋中保存。Pass the dried T-MMT through a 100-mesh nylon sieve, and finally put the finished thymidine montmorillonite into a sealed bag for storage.
本发明的有益效果:Beneficial effects of the present invention:
本发明采用新型、环境友好型改性剂胸腺嘧啶对钠基蒙脱土进行改性,以提高钠基蒙脱土对汞的吸附能力且对环境无污染。在Hg2+存在下,胸腺嘧啶与Hg2+特异性结合,形成胸腺嘧啶-Hg2+-胸腺嘧啶错配(T-Hg2+-T),在体系中胸腺嘧啶的该残基可作为汞离子传感器良好的识别基团,特异性地识别汞离子。结合Hg2+与胸腺嘧啶的特异性,利用溶液搅拌法对钠基蒙脱土进行胸腺嘧啶改性,避免了水热法和微波加热法耗能高,步骤繁琐的问题,且合成的新型有机蒙脱土对Hg2+吸附容量大,去除率高,不会对环境造成二次污染,改性后的T-MMT不仅增加了层间距,还改变了蒙脱土表面的电荷性质及疏水性,使得蒙脱土更易吸附废水中的汞离子。The invention adopts a novel, environment-friendly modifier thymine to modify the sodium-based montmorillonite so as to improve the mercury adsorption capacity of the sodium-based montmorillonite without polluting the environment. In the presence of Hg 2+ , thymine specifically binds to Hg 2+ , forming a thymine-Hg 2+ -thymine mismatch (T-Hg 2+ -T), and this residue of thymine in the system can be used as The mercury ion sensor has a good recognition group and can specifically recognize mercury ions. Combined with the specificity of Hg 2+ and thymine, the sodium-based montmorillonite was modified with thymine by the solution stirring method, which avoided the problems of high energy consumption and cumbersome steps of the hydrothermal method and microwave heating method, and the synthetic new organic Montmorillonite has a large adsorption capacity for Hg 2+ , high removal rate, and will not cause secondary pollution to the environment. The modified T-MMT not only increases the layer spacing, but also changes the charge properties and hydrophobicity of the montmorillonite surface. , making it easier for montmorillonite to absorb mercury ions in wastewater.
本发明设计合成了以胸腺嘧啶为有机改性剂,采用简单、快速的溶液搅拌法对钠基蒙脱土进行改性,解决了水热法和微波加热法耗能高等的技术问题。蒙脱土本身吸附能力有限,有机改性能增加蒙脱土的吸附性能,但大多有机改性剂毒性大,本专利通过胸腺嘧啶改性剂,合成绿色、无污染的新型有机蒙脱土,使蒙脱土表面的亲水性变为疏水性,增加其层间距,从而可提高其去除水溶液Hg2+的能力。The invention designs and synthesizes thymine as an organic modifier, adopts a simple and fast solution stirring method to modify sodium-based montmorillonite, and solves the technical problems of high energy consumption in hydrothermal method and microwave heating method. The adsorption capacity of montmorillonite itself is limited, and organic modification can increase the adsorption performance of montmorillonite, but most of the organic modifiers are highly toxic. This patent synthesizes a new green and pollution-free organic montmorillonite through the thymine modifier. The hydrophilicity of the surface of montmorillonite becomes hydrophobic, which increases its interlayer distance, thereby improving its ability to remove Hg 2+ from aqueous solution.
本发明设计并合成了以胸腺嘧啶为插层剂的有机蒙脱土,胸腺嘧啶是遗传物质的重要组成成分,合成的胸腺嘧啶蒙脱土不会污染环境,可用于土壤污染物的固定。The invention designs and synthesizes organic montmorillonite with thymine as an intercalation agent. Thymine is an important component of genetic material. The synthesized thymine montmorillonite will not pollute the environment and can be used for fixing soil pollutants.
附图说明Description of drawings
图1为本发明具体实施方式T、T-MMT、Na-MMT红外光谱图;Fig. 1 is the specific embodiment of the present invention T, T-MMT, Na-MMT infrared spectrogram;
图2为本发明具体实施方式蒙脱土和有机蒙脱土的FT-IR光谱图;Fig. 2 is the FT-IR spectrogram of montmorillonite and organomontmorillonite of the specific embodiment of the present invention;
图3为本发明具体实施方式蒙脱土改性前的XPS谱图;Fig. 3 is the XPS spectrogram before montmorillonite modification of the specific embodiment of the present invention;
图4为本发明具体实施方式蒙脱土改性后的XPS谱图;Fig. 4 is the XPS spectrogram after montmorillonite modification of the specific embodiment of the present invention;
图5为本发明具体实施方式胸腺嘧啶与Hg2+的作用图。Fig. 5 is a graph showing the interaction between thymine and Hg 2+ in a specific embodiment of the present invention.
具体实施方式Detailed ways
下面结合附图和具体实施方案对本发明的技术方案作进一步详细地说明。The technical solution of the present invention will be described in further detail below in conjunction with the accompanying drawings and specific embodiments.
一种有机改性钠基蒙脱土的制备方法,主要为:首先用硫酸将胸腺嘧啶完全溶解(本实验的胸腺嘧啶不溶于水和热水),其次将胸腺嘧啶溶液与钠基蒙脱土在一定条件下共混搅拌,最后对样品进行洗涤、干燥和保存,A preparation method of organically modified sodium-based montmorillonite, which mainly includes: firstly, thymine is completely dissolved with sulfuric acid (thymine in this experiment is insoluble in water and hot water), and secondly, the thymine solution is mixed with sodium-based montmorillonite Blend and stir under certain conditions, and finally wash, dry and store the samples,
本发明胸腺嘧啶与钠基蒙脱土的质量比为7:100,使得改性前,钠基蒙脱土元素重量百分比百分比分别为:O:59.61%、Si:23.65%、Al:6.57%、C:5.96%、Na:2.17%和Mg:2.04%;改性后,有机改性蒙脱土的原料组成重量百分比为:O:58.75%、Si:21.30%、Al:6.15%、C:10.44%、N:2.26和Mg:1.10%。The mass ratio of thymine and sodium montmorillonite in the present invention is 7:100, so that before modification, the weight percentages of sodium montmorillonite elements are: O: 59.61%, Si: 23.65%, Al: 6.57%, C: 5.96%, Na: 2.17% and Mg: 2.04%; after modification, the raw material composition weight percentage of organically modified montmorillonite is: O: 58.75%, Si: 21.30%, Al: 6.15%, C: 10.44 %, N: 2.26 and Mg: 1.10%.
改性后有机改性蒙脱土的层间Na离子从2.04%变为0%,C元素含量从5.96%上升到了10.44,N元素从0%上升至2.26%,Hg2+主要与胸腺嘧啶中的-NH官能团特异性结合,C和N元素含量的上升主要是胸腺嘧啶插层的结果,代表着有机改性能提高钠基蒙脱土的吸附容量,提高钠基蒙脱土对水中Hg的去除效率和土壤中Hg的固定能力。After modification, the interlayer Na ion of organically modified montmorillonite changed from 2.04% to 0%, the content of C element increased from 5.96% to 10.44%, and the content of N element increased from 0% to 2.26 %. The -NH functional group is specifically combined, and the increase in the content of C and N elements is mainly the result of thymine intercalation, which means that organic modification can improve the adsorption capacity of sodium-based montmorillonite and improve the removal of Hg in water by sodium-based montmorillonite Efficiency and Hg fixation capacity in soil.
用硫酸将胸腺嘧啶完全溶解的方法为:The method for completely dissolving thymine with sulfuric acid is:
按胸腺嘧啶与钠基蒙脱土的质量比称取胸腺嘧啶溶于1.5mol/L的硫酸溶液中,在水浴50℃搅拌120min使胸腺嘧啶完全溶解;硫酸溶液的取量原则是以确保胸腺嘧啶完全溶解为准。Weigh thymine according to the mass ratio of thymine to sodium montmorillonite and dissolve it in 1.5mol/L sulfuric acid solution, stir in a water bath at 50°C for 120 minutes to completely dissolve thymine; the principle of taking sulfuric acid solution is to ensure that thymine Completely dissolved shall prevail.
共混搅拌时间为10小时,确保胸腺嘧啶已经插入到钠基蒙脱土表面,部分进入钠基蒙脱土层间,时间过短会导致胸腺嘧啶插层不完全,时间过长会浪费资源。The blending and stirring time is 10 hours to ensure that thymine has been inserted into the surface of the Na-montmorillonite, and part of it enters the Na-montmorillonite layer. If the time is too short, the thymine intercalation will be incomplete, and if the time is too long, resources will be wasted.
对共混液进行洗涤及干燥的方法为:The method of washing and drying the blend is as follows:
将共混液冷却至室温,用超纯水洗3次并在4500r/min的离心机上离心5min,倾倒上清液后,再将样品于电热鼓风干燥箱中55℃干燥6h,本发明采用该冷却至室温是为了让未与钠基蒙脱土结合的胸腺嘧啶结晶析出,便于洗涤,超纯水洗涤是为了去除多余的胸腺嘧啶。The blend was cooled to room temperature, washed 3 times with ultrapure water and centrifuged for 5 minutes on a centrifuge at 4500r/min. After pouring the supernatant, the sample was dried at 55°C for 6 hours in an electric blast drying oven. The cooling method is used in the present invention. The purpose of cooling to room temperature is to allow the crystallization of thymine not combined with Na-montmorillonite for easy washing, and the purpose of washing with ultrapure water is to remove excess thymine.
将干燥后的胸腺嘧啶蒙脱土(T-MMT)过100目尼龙筛,使有机蒙脱土颗粒大小均匀,保证吸附实验的准确性,最后将得到的胸腺嘧啶蒙脱土成品放入密封袋中保存。Pass the dried thymine montmorillonite (T-MMT) through a 100-mesh nylon sieve to make the organic montmorillonite particles uniform in size and ensure the accuracy of the adsorption experiment. Finally, put the finished thymine montmorillonite into a sealed bag save in .
下面举例对本发明方案进一步阐述:The following example further elaborates on the scheme of the present invention:
步骤1、称取0.7g胸腺嘧啶溶于1.5mol/L的100ml的硫酸溶液中,水浴50℃搅拌120min使胸腺嘧啶完全溶解;Step 1. Weigh 0.7g thymine and dissolve it in 1.5mol/L 100ml sulfuric acid solution, stir in a water bath at 50°C for 120min to completely dissolve thymine;
步骤2、缓慢加入10g钠基蒙脱土,水浴搅拌10h;Step 2, slowly add 10 g of Na-montmorillonite, and stir in a water bath for 10 h;
步骤3、待溶液冷却到室温后,用超纯水洗3次并在4500r/min的离心机上离心5min,倾倒上清液后,再将样品于电热鼓风干燥箱中55℃干燥6h;Step 3. After the solution is cooled to room temperature, wash it 3 times with ultrapure water and centrifuge it in a centrifuge at 4500r/min for 5min. After pouring off the supernatant, dry the sample in an electric blast drying oven at 55°C for 6h;
步骤4、所得的T-MMT过100目尼龙筛,最后将得到的胸腺嘧啶蒙脱土成品放入密封袋中保存。Step 4, passing the obtained T-MMT through a 100-mesh nylon sieve, and finally putting the obtained thymidine montmorillonite finished product into a sealed bag for storage.
本发明合成了以胸腺嘧啶、钠基蒙脱土为原料改性的有机蒙脱土,通过傅里叶变换红外光谱(FT-IR)、X射线衍射(XRD)、X射线光电子能(XPS)表征改性前后蒙脱土结构,表明胸腺嘧啶已经插入到钠基蒙脱土表面,部分进入钠基蒙脱土层间。胸腺嘧啶的插层没有改变钠基蒙脱土的结构,层间未发生坍塌,说明改性成功。The present invention has synthesized the organic montmorillonite modified with thymine and sodium montmorillonite as raw materials, through Fourier transform infrared spectroscopy (FT-IR), X-ray diffraction (XRD), X-ray photoelectron energy (XPS) Characterization of the structure of montmorillonite before and after modification shows that thymine has been inserted into the surface of Na-montmorillonite, and part of it has entered the interlayer of Na-montmorillonite. The intercalation of thymine did not change the structure of Na-based montmorillonite, and no collapse occurred between layers, indicating that the modification was successful.
实验合成过程中所用水溶液均为实验室自制的超纯水。The aqueous solution used in the experimental synthesis process is ultrapure water made in the laboratory.
本发明的胸腺嘧啶蒙脱土,在固定土壤污染物方面去除水中重金属等领域具有潜在应用。本实验往大棚汞污染土壤中施加T-MMT在种植小白菜和大蒜,与未施加T-MMT的汞污染土壤相比,汞通量下降、小白菜和大蒜的根茎叶都有不同程度下降,说明T-MMT能固定土壤中的活性汞。吸附实验:汞初始浓度为200mg/L,吸附时间为2h,pH=5的条件下。原始蒙脱土(Na-MMT)的吸附量为8.64mg/g,改性后的T-MMT的吸附量为44.72mg/g,T-MMT的吸附量为Na-MMT的5.18倍。解吸实验:汞初始浓度为200mg/L,解析剂为0.01mol/L NaNO3,Na-MMT的解吸率为94.22%,而T-MMT的解吸率为14.32%,T-MMT能显著减小汞的浸出,把Hg2吸附固定于蒙脱土层间及表面。以上实验说明,由于蒙脱土本身是土壤中的成分,可将T-MMT直接施用于汞污染土壤中,以降低植物中总汞浓度,可将T-MMT用于汞污水中,达到去除水中汞的目的。The thymine montmorillonite of the invention has potential applications in fields such as fixing soil pollutants and removing heavy metals in water. In this experiment, T-MMT was applied to the mercury-contaminated soil in the greenhouse to grow pakchoi and garlic. Compared with the mercury-contaminated soil without T-MMT, the mercury flux decreased, and the roots, stems and leaves of pakchoi and garlic all decreased to varying degrees. It shows that T-MMT can fix active mercury in soil. Adsorption experiment: the initial concentration of mercury is 200mg/L, the adsorption time is 2h, and the conditions are pH=5. The adsorption capacity of the original montmorillonite (Na-MMT) was 8.64mg/g, the adsorption capacity of the modified T-MMT was 44.72 mg/g, and the adsorption capacity of T-MMT was 5.18 times that of Na-MMT. Desorption experiment: the initial concentration of mercury is 200mg/L, the desorption agent is 0.01mol/L NaNO 3 , the desorption rate of Na-MMT is 94.22%, and that of T-MMT is 14.32%. T-MMT can significantly reduce the mercury leaching, and adsorb and fix Hg 2 on the interlayer and surface of montmorillonite. The above experiments show that since montmorillonite itself is a component in the soil, T-MMT can be directly applied to mercury-contaminated soil to reduce the total mercury concentration in plants, and T-MMT can be used in mercury sewage to achieve the removal of mercury in water. purpose of mercury.
胸腺嘧啶蒙脱土的结构表征Structural Characterization of Thymine Montmorillonite
采用傅里叶红外光谱考察胸腺嘧啶蒙脱土(T-MMT)的形成,将胸腺嘧啶、改性前后的蒙脱土通过红外光谱进行了表征,如图1所示,Na-MMT与T-MMT的红外图谱在相似波长处具有不同强度的特征峰。波数为3453、3600cm-1属于蒙脱土结构中的Al-OH、Si-OH的伸缩振动峰,1617cm-1处吸收带对应H2O的O-H拉伸带。1062、1016cm-1处的吸收带为Si-O伸缩振动峰,400-600cm-1处为Si-O和Al-O弯曲振动峰。通过红外光谱的变化T-MMT的红外光谱显示了C=O在1695cm-1的伸缩振动,3396cm-1的吸收带为-OH、N-H的伸缩振动峰。1205cm-1可能是N-H的弯曲振动,改性后蒙脱土的-OH的伸缩振动峰明显往右移动,从3453cm-1变成了3396cm-1。说明已经改性成功,胸腺嘧啶可能保留在蒙脱土表面。The formation of thymine montmorillonite (T-MMT) was investigated by Fourier transform infrared spectroscopy, and the thymine and montmorillonite before and after modification were characterized by infrared spectroscopy. As shown in Figure 1, Na-MMT and T-MMT The infrared spectrum of MMT has characteristic peaks of different intensities at similar wavelengths. The wave numbers of 3453 and 3600cm -1 belong to the stretching vibration peaks of Al-OH and Si-OH in the montmorillonite structure, and the absorption band at 1617cm -1 corresponds to the OH stretching band of H 2 O. The absorption bands at 1062 and 1016cm -1 are Si-O stretching vibration peaks, and the absorption bands at 400-600cm -1 are Si-O and Al-O bending vibration peaks. The infrared spectrum of T-MMT shows the stretching vibration of C=O at 1695cm -1 through the change of infrared spectrum, and the absorption band of 3396cm -1 is the stretching vibration peak of -OH and NH. 1205cm -1 may be the bending vibration of NH, and the stretching vibration peak of -OH of montmorillonite after modification obviously shifts to the right, from 3453cm -1 to 3396cm -1 . It shows that the modification has been successful, and thymine may remain on the surface of montmorillonite.
图2为Na-MMT与T-MMT的X射线衍射图。通过图中首个峰位的对比发现,Na-MMT、T-MMT的第一个峰位分别为2θ=7.13°、6.25°,以上结果说明改性后衍射峰普遍发生了向低角度偏移。根据Bragg程:2dsinθ=λ(θ为半衍射角,λ为入射X-射线波长,λ=0.154nm)。分析得到Na-MMT、T-MMT两种蒙脱土晶面间距分别为1.24、1.41nm,晶面间距增大了0.17nm。数据结果表明,胸腺嘧啶与蒙脱土层间的离子发生了离子交换,使蒙脱土层间距扩大,说明胸腺嘧啶进入了蒙脱土层间。Fig. 2 is the X-ray diffraction pattern of Na-MMT and T-MMT. Through the comparison of the first peak positions in the figure, it is found that the first peak positions of Na-MMT and T-MMT are 2θ=7.13° and 6.25° respectively. The above results show that the diffraction peaks generally shift to lower angles after modification. . According to the Bragg equation: 2dsinθ=λ (θ is the half-diffraction angle, λ is the incident X-ray wavelength, λ=0.154nm). The analysis shows that the interplanar distances of Na-MMT and T-MMT montmorillonites are 1.24 and 1.41nm respectively, and the interplanar distances increase by 0.17nm. The results of the data show that the ions between thymine and montmorillonite layers undergo ion exchange, which expands the distance between montmorillonite layers, indicating that thymine enters between montmorillonite layers.
为明确改性前后蒙脱土的组成成分,对二者进行了X射线光电子能(XPS)表征。图3和图4为蒙脱土改性前后的XPS图,由改性前后全谱图和元素成分分析可知,蒙脱土层间的Na+被T所替换,N元素的含量由0%到2.26%,改性后C元素的含量由5.96%上升到10.44%,这是由于胸腺嘧啶贡献的结果,表明材料复合成功。图4中C1s的XPS精细谱表明,光谱显示有三个峰284.8eV、286.6eV、289.0eV分别为C-C、C-O、C=O-N。图4中的O1S谱图531.13eV处的结合能为Si-O、结合能532.4eV、534.7eV处分别为C=O、C-O-C。286.8eV处的峰为C-N。289.07eV为N的XPS精细谱图表明,N s1的结合能在400.6eV和402.0eV处分别对应于NH和O=C-NH。图3、图4中Si(2p)的精细谱基本相同,表明改性后蒙脱土的结构没有被破坏。102.94eV、105.13eV的结合能分别为Si-O-、SiO2。说明胸腺嘧啶成功保留到蒙脱土的表面。In order to clarify the composition of montmorillonite before and after modification, X-ray photoelectron spectroscopy (XPS) was used to characterize the two materials. Figure 3 and Figure 4 are the XPS diagrams before and after modification of montmorillonite. From the full spectrum before and after modification and element composition analysis, it can be seen that the Na + between the layers of montmorillonite is replaced by T, and the content of N elements ranges from 0% to 2.26 %, the content of C element after modification increased from 5.96% to 10.44%, which is due to the contribution of thymine, indicating that the composite material was successful. The XPS fine spectrum of C1s in Figure 4 shows that the spectrum shows three peaks at 284.8eV, 286.6eV, and 289.0eV, which are CC, CO, and C=ON, respectively. The binding energy at 531.13eV in the O1S spectrum in Figure 4 is Si-O, and the binding energy at 532.4eV and 534.7eV are C=O and COC, respectively. The peak at 286.8 eV is CN. The fine XPS spectrum of N at 289.07eV shows that the binding energy of N s1 corresponds to NH and O=C-NH at 400.6eV and 402.0eV, respectively. The fine spectra of Si(2p) in Figure 3 and Figure 4 are basically the same, indicating that the structure of the modified montmorillonite has not been destroyed. The binding energies of 102.94eV and 105.13eV are Si-O- and SiO 2 , respectively. It shows that thymine is successfully retained on the surface of montmorillonite.
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