CN111514854A - Preparation method of modified 3D porous carbon composite adsorption material - Google Patents

Preparation method of modified 3D porous carbon composite adsorption material Download PDF

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CN111514854A
CN111514854A CN202010368504.4A CN202010368504A CN111514854A CN 111514854 A CN111514854 A CN 111514854A CN 202010368504 A CN202010368504 A CN 202010368504A CN 111514854 A CN111514854 A CN 111514854A
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porous carbon
bao
modified
adsorption material
carbon composite
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阳杰
杨标
王玉
张凌云
肖新国
李东
陆井
李少波
王敬泽
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Hefei University
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    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/02Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
    • B01J20/20Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising free carbon; comprising carbon obtained by carbonising processes
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/28Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties
    • B01J20/28014Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties characterised by their form
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/28Treatment of water, waste water, or sewage by sorption
    • C02F1/283Treatment of water, waste water, or sewage by sorption using coal, charred products, or inorganic mixtures containing them
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/20Heavy metals or heavy metal compounds

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  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
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Abstract

A preparation method of a modified 3D porous carbon composite adsorption material relates to the technical field of composite modification for preparing an activated carbon adsorption material, and comprises the steps of dissolving sylvite, barium salt and bismuth salt in water, uniformly mixing, adding activated carbon, uniformly mixing, and reacting through an ultrasonic microwave combined reactor to prepare the modified 3D porous carbon composite adsorption material. The invention takes 3D porous carbon as a main carrier material and K with certain content and composition2O‑Bi2O3-BaO is used as filler of adsorbing material, and composite adsorbing material with excellent performance is prepared by newly developed ultrasonic and microwave combined methodAnd (3) attaching materials. At the same time, doping K with different molar ratios2O‑Bi2O3Modification research is carried out on the porous carbon adsorption material by BaO substance ions. The better composite 3D porous carbon component adsorbent material is obtained. The series porous carbon composite materials with different compositions have different adsorption capacity, removal time and material composition on the heavy metal ion solution containing Pb (II) ions.

Description

Preparation method of modified 3D porous carbon composite adsorption material
Technical Field
The invention relates to the technical field of preparation of an activated carbon adsorption material by composite modification, and particularly relates to a preparation method of a modified 3D porous carbon composite adsorption material.
Background
In recent years, with the rapid development of economy and science and technology, a porous carbon material is a pollution-free and environment-friendly adsorbent material. A large number of experiments and researches show that the composite porous carbon material has better adsorption and catalysis performances than a single porous carbon material due to the unique performance of the composite porous carbon material. The porous carbon composite adsorption material has rich porous structure, ultrahigh specific surface area and rich surface functional groups, and is widely applied to the fields of adsorption separation, sewage treatment, gas purification and the like.
The 3D porous carbon material has a unique framework structure, a high surface area, directional pore channel distribution, high chemical stability and a strong double electric layer effect, is widely paid attention to at present due to a unique three-dimensional structure, and can be used as a carbon electrode material of lithium batteries, lithium sulfur and super capacitors by loading a certain amount of metal compounds.
Common synthesis methods of the 3D porous carbon material include a carbonization method, a physicochemical activation method, a catalytic activation method, an organogel carbonization method, a self-assembly method, a template method and the like. The metal of the catalytic activation method is easy to enter and stay in the porous carbon, the organic gel carbonization method is expensive and complicated in preparation process, and the precursor of the organic aerogel uses toxic organic matters such as phenol and aldehyde, so that the organic aerogel has certain danger to workers and the environment. The template synthesis process of the traditional template method is complicated, the cost is high and the like, so that the large-scale application of the template in industrial production is limited.
Disclosure of Invention
The invention aims to solve the technical problem of providing a preparation method of a modified 3D porous carbon composite adsorption material to prepare the adsorption material which can be used for treating industrial sewage and wastewater environment containing lead ions.
In order to achieve the purpose, the technical scheme adopted by the invention is as follows: a preparation method of a modified 3D porous carbon composite adsorption material comprises the steps of dissolving sylvite, barium salt and bismuth salt in water, uniformly mixing, adding activated carbon, uniformly mixing, reacting through an ultrasonic microwave combined reactor, and preparing to obtain the modified 3D porous carbon composite adsorption material C-K2O-Bi2O3-BaO。
As a preferred technical scheme of the preparation method of the modified 3D porous carbon composite adsorption material, the preparation method comprises the following specific steps:
1) weighing potassium nitrate, barium nitrate and bismuth nitrate, adding into a beaker, dissolving with distilled water, adding ammonia water under magnetic stirring to adjust the pH value of the solution to 9-12, and adjusting the pH value with the ammonia water solution after fully stirring;
2) ball-milling the activated carbon powder into fine powder with the particle size of 1-5 mu m, adding the fine powder into the solution, fully stirring, and adjusting the pH value of the solution to 9-12 by using an ammonia water solution;
3) putting the solution into an ultrasonic and microwave combined reactor for reaction, and carrying out double-functional reaction for 30min by adopting ultrasonic waves 1200W and microwaves 1000W;
4) after the reaction is finished, putting the sample into a drying oven at 150 ℃ for drying for 6 hours to obtain the modified 3D porous carbon composite adsorption material C-K2O-Bi2O3-BaO。
As modified 3D porous carbon composite adsorbent material of the present inventionAccording to a further preferable technical scheme of the preparation method, the activated carbon is selected from one of coal activated carbon powder, bamboo activated carbon powder and coconut shell activated carbon powder. Modified 3D porous carbon composite adsorption material C-K2O-Bi2O3C, K in BaO2O、Bi2O3And the doping molar ratio of BaO is 5-10: 1-5: 1-5: 1 to 5. Further preferably, the modified 3D porous carbon composite adsorption material C-K2O-Bi2O3C, K in BaO2O、Bi2O3And the doping molar ratio of BaO is 7: 1: 2: 1.
the invention provides a modified 3D porous carbon composite adsorption material C-K2O-Bi2O3BaO, the microscopic form is a porous structure composed of shapes of a sheet, a rod, a tetrahedron and the like, and the microstructure size range of the composite material is 500nm-2 um.
Compared with the prior art, the invention has the beneficial effects that:
the invention takes the prepared 3D porous carbon as a main carrier material and K with certain content and composition2O-Bi2O3BaO is used as a filler of the adsorption material, and a composite adsorption material with excellent performance is prepared by a newly developed ultrasonic and microwave combined method. At the same time, doping K with different molar ratios2O-Bi2O3Modification research is carried out on the porous carbon adsorption material by BaO substance ions. The modified porous carbon composite adsorption material is characterized by means such as XRD, SEM and the like. Through the comparison of the microstructure and the components, a better series of modified porous carbon composite adsorption materials are selected, and the adsorption performance of the materials is researched and analyzed, so that a better composite 3D porous carbon component adsorbent material is obtained. Experiments show that the adsorption capacity, the removal time and the material composition of the series porous carbon composite materials with different compositions to the heavy metal ion solution containing Pb (II) ions are different. As a result, it was found that K2O-Bi2O3The adsorption effect of the-BaO (1: 2: 1) modified 3D porous carbon (70%) is the best, and the adsorption quantity reaches 239 mg/g. The target products prepared achieved the expected goals of the design of the experiment, these K's are expected2O-Bi2O3-BaO modified 3D porous carbon adsorptionThe material can be used for the environmental treatment of industrial sewage and wastewater containing lead ions.
Drawings
The following provides further details of the preparation method of the modified 3D porous carbon composite adsorption material according to the present invention with reference to examples and drawings.
FIG. 1 is an XRD pattern of each series of composite adsorbents prepared in examples 1 to 10.
Fig. 2 is SEM images of low, medium, and high magnification in order of the composite adsorbent prepared in example 1.
FIG. 3 is a graph showing percentage of lead ions remaining in the adsorption of each series of composite adsorbent materials prepared in examples 1 to 7.
FIG. 4 is a graph showing the adsorption amount of each series of composite adsorbents prepared in examples 1 to 7.
Detailed Description
Example 1
In the implementation, the prepared modified 3D porous carbon composite adsorbing material C-K2O-Bi2O3in-BaO, C, K2O、Bi2O3And the doping molar ratio of BaO is 7: 1: 2: 1. the preparation method comprises the following steps:
1) weighing potassium nitrate, barium nitrate and bismuth nitrate according to a molar ratio, adding the potassium nitrate, the barium nitrate and the bismuth nitrate into a beaker, dissolving the potassium nitrate, the barium nitrate and the bismuth nitrate by using distilled water, adding ammonia water under magnetic stirring to adjust the pH value of the solution to 12, and adjusting the pH value of the solution by using the ammonia water solution after fully stirring.
2) Ball-milling the bamboo wood activated carbon powder into fine powder with the particle size of 1 mu m, adding the fine powder into the solution, fully stirring the solution, and adjusting the pH value of the solution to 12 by using an ammonia water solution.
3) And placing the solution in an ultrasonic and microwave combined reactor for reaction, and performing double-functional reaction for 30min by adopting ultrasonic waves 1200W and microwaves 1000W.
4) After the reaction is finished, putting the sample into a drying oven at 150 ℃ for drying for 6 hours to obtain the modified 3D porous carbon composite adsorption material C-K2O-Bi2O3-BaO(7-1-2-1)。
Example 2
In this example, the prepared modified 3D porous carbon composite adsorbing material C-K2O-Bi2O3in-BaO, C, K2O、Bi2O3And the doping molar ratio of BaO is 7: 1: 1: 1, the preparation method is the same as that of example 1, and the modified 3D porous carbon composite adsorption material C-K is obtained2O-Bi2O3-BaO(7-1-1-1)。
Example 3
In this example, the prepared modified 3D porous carbon composite adsorbing material C-K2O-Bi2O3in-BaO, C, K2O、Bi2O3And the doping molar ratio of BaO is 7: 1: 1: 2, the preparation method is the same as that of example 1, and the modified 3D porous carbon composite adsorbing material C-K is obtained2O-Bi2O3-BaO(7-1-1-2)。
Example 4
In this example, the prepared modified 3D porous carbon composite adsorbing material C-K2O-Bi2O3in-BaO, C, K2O、Bi2O3And the doping molar ratio of BaO is 7: 1: 2: 2, the preparation method is the same as that of example 1, and the modified 3D porous carbon composite adsorbing material C-K is obtained2O-Bi2O3-BaO(7-1-2-2)。
Example 5
In this example, the prepared modified 3D porous carbon composite adsorbing material C-K2O-Bi2O3in-BaO, C, K2O、Bi2O3And the doping molar ratio of BaO is 7: 2: 1: 1, the preparation method is the same as that of example 1, and the modified 3D porous carbon composite adsorption material C-K is obtained2O-Bi2O3-BaO(7-2-1-1)。
Example 6
In this example, the prepared modified 3D porous carbon composite adsorbing material C-K2O-Bi2O3in-BaO, C, K2O、Bi2O3And the doping molar ratio of BaO is 7: 2: 1: 2, the preparation method is the same as that of example 1, and the modified 3D porous carbon composite adsorbing material C-K is obtained2O-Bi2O3-BaO(7-2-1-2)。
Example 7
In this example, modification 3 was obtainedD porous carbon composite adsorption material C-K2O-Bi2O3in-BaO, C, K2O、Bi2O3And the doping molar ratio of BaO is 7: 2: 2: 1, the preparation method is the same as that of example 1, and the modified 3D porous carbon composite adsorption material C-K is obtained2O-Bi2O3-BaO(7-2-2-1)。
Example 8
In this example, only Bi is doped2O3The raw materials do not contain potassium nitrate, barium nitrate, C and Bi2O3Is 7: 3, the other steps are the same as the example 1, and the modified 3D porous carbon composite adsorbing material C-Bi is obtained2O3(7-3)。
Example 9
In this example, only BaO was doped, the raw materials for preparation did not contain potassium nitrate and bismuth nitrate, and the doping molar ratio of C to BaO was 7: 3, the other steps are the same as the example 1, and the modified 3D porous carbon composite adsorbing material C-BaO (7-3) is obtained.
Example 10
In this example, only K was doped2O, barium nitrate, bismuth nitrate, C and K are not contained in the preparation raw materials2The doping molar ratio of O is 7: 3, obtaining the modified 3D porous carbon composite adsorption material C-K in the same way as the example 1 in other steps2O(7-3)。
FIG. 1 is an XRD pattern of each series of composite adsorbents prepared in examples 1 to 10. As can be seen from FIG. 1, the diffraction intensity peak and C-K of the sample2O-Bi2O3The phases of-BaO are basically corresponding, the positions of diffraction peaks of the series diffraction spectrograms are basically consistent, the peak intensity ratio has obvious difference, and the XRD diffraction pattern has obvious Bi2O3,BaO,K2The diffraction peaks of O are relatively sharp, which indicates that the synthesized composite adsorbent is in phase with the experimental design target 3D porous C-K2O-Bi2O3BaO fit.
Fig. 2 is SEM images of low, medium, and high magnification in order of the composite adsorbent prepared in example 1. As can be seen from FIG. 2, the modified 3D porous carbon composite adsorbent C-K obtained in the present example2O-Bi2O3-BaO(7-1-2-1)The composite material is a porous structure formed by shapes such as a sheet shape, a rod shape, a tetrahedron shape and the like, and the size range of the microstructure of the composite material is 500nm-2 um.
FIG. 3 shows the influence of the preparation of porous carbon composite materials of different compositions in examples 1 to 7 on the removal rate of a Pb (II) -ion-containing heavy metal ion solution under a sunlight condition. The dosage of the modified 3D porous carbon adsorption material is 30mg, the adsorption time is 150min, the volume of the Pb (II) solution is 100mL, and the initial concentration is 100 mg/L. As can be seen from FIG. 3, example 1 produces C-K2O-Bi2O3The best adsorption effect of the-BaO (7-1-2-1) is achieved, the removal rate reaches 99.8%, and the better adsorption removal effect is achieved when all series products with different compositions are prolonged along with time.
FIG. 4 is a curve of adsorption capacity, removal time and substance composition of a Pb (II) -ion-containing heavy metal ion solution of a series of porous carbon composite materials with different compositions prepared in examples 1 to 7 under a sunlight condition. The dosage of the modified 3D porous carbon adsorption material is 50mg, the adsorption time is 140min, and the volume of the Pb (II) solution is 500 mL. As can be seen from FIG. 4, example 1 produces C-K2O-Bi2O3The best adsorption effect of the-BaO (7-1-2-1) is achieved, the adsorption amount reaches 239mg/g, and the adsorption removal effect of all series products with different compositions is better along with the prolonging of time. Meanwhile, it can be seen that the adsorption amount is basically stable with the increase of time after the adsorption time reaches 60 minutes, which indicates that the adsorption process is mainly completed within 60 minutes and the adsorption effect is good. Therefore, the C-K prepared by the invention is proved by experiments2O-Bi2O3the-BaO modified 3D porous carbon adsorption material can be used for environmental treatment of industrial sewage and wastewater containing lead ions.
Example 11
In this example, ammonia was added to adjust the pH to 10, and the other steps were the same as in example 1.
Example 12
In this example, bamboo activated carbon was replaced with coal activated carbon powder, and the other steps were the same as in example 1.
Example 13
In this example, bamboo and wood activated carbon was replaced with coconut shell activated carbon powder, and the particles were ball-milled uniformly to 5 μm fine powder, and the other steps were the same as in example 1.
The foregoing is merely exemplary and illustrative of the principles of the present invention and various modifications, additions and substitutions of the specific embodiments described herein may be made by those skilled in the art without departing from the principles of the present invention or exceeding the scope of the claims set forth herein.

Claims (6)

1. A preparation method of a modified 3D porous carbon composite adsorption material is characterized by firstly dissolving sylvite, barium salt and bismuth salt in water, uniformly mixing, then adding activated carbon, uniformly mixing, and then reacting through an ultrasonic microwave combined reactor to prepare the modified 3D porous carbon composite adsorption material C-K2O-Bi2O3-BaO。
2. The preparation method according to claim 1, comprising the following steps:
1) weighing potassium nitrate, barium nitrate and bismuth nitrate, adding into a beaker, dissolving with distilled water, adding ammonia water under magnetic stirring to adjust the pH value of the solution to 9-12, and adjusting the pH value with the ammonia water solution after fully stirring;
2) ball-milling the activated carbon powder into fine powder with the particle size of 1-5 mu m, adding the fine powder into the solution, fully stirring, and adjusting the pH value of the solution to 9-12 by using an ammonia water solution;
3) putting the solution into an ultrasonic and microwave combined reactor for reaction, and carrying out double-functional reaction for 30min by adopting ultrasonic waves 1200W and microwaves 1000W;
4) after the reaction is finished, putting the sample into a drying oven at 150 ℃ for drying for 6 hours to obtain the modified 3D porous carbon composite adsorption material C-K2O-Bi2O3-BaO。
3. The method of claim 1 or 2, wherein the activated carbon is selected from one of coal activated carbon powder, bamboo activated carbon powder, and coconut shell activated carbon powder.
4. The preparation method according to claim 2, wherein the modified 3D porous carbon composite adsorption material C-K2O-Bi2O3C, K in BaO2O、Bi2O3And the doping molar ratio of BaO is 5-10: 1-5: 1-5: 1 to 5.
5. The preparation method according to claim 4, wherein the modified 3D porous carbon composite adsorption material C-K2O-Bi2O3C, K in BaO2O、Bi2O3And the doping molar ratio of BaO is 7: 1: 2: 1.
6. the modified 3D porous carbon composite adsorption material C-K prepared by the method of any one of claims 1 to 52O-Bi2O3BaO, characterized in that the microscopic morphology is a porous structure composed of sheet, rod, tetrahedron, etc., and the microstructure size of the composite material is in the range of 500nm-2 um.
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Application publication date: 20200811