CN117106162A - Triazole triazinyl-based conjugated microporous polymer and application thereof - Google Patents

Triazole triazinyl-based conjugated microporous polymer and application thereof Download PDF

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CN117106162A
CN117106162A CN202311368364.0A CN202311368364A CN117106162A CN 117106162 A CN117106162 A CN 117106162A CN 202311368364 A CN202311368364 A CN 202311368364A CN 117106162 A CN117106162 A CN 117106162A
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microporous polymer
conjugated microporous
triazole
uranium
ttt
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张伟杰
阳海
廖云峰
王冰鑫
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Hunan Institute of Engineering
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Abstract

The invention provides a triazole triazinyl-based conjugated microporous polymer and application thereof, and belongs to the technical field of photocatalytic function preparation. The preparation method is that triazole triazine triphenyl bromide and boric acid ester compound are combined in Pd (PPh) 3 ) 4 And polymerizing under catalysis, filtering, washing and Soxhlet extraction and purification of a reaction product to obtain the triazole triazinyl conjugated microporous polymer material. The triazole triazine conjugated microporous polymer has high specific surface area and excellent heat stability. The method further improves intersystem crossing rate and prolongs the service life of an excited state of the self-excited-state-type optical fiber, and has excellent photocatalysis performance when improving the charge transfer value of the spin orbit. Under the illumination condition, the uranium (VI) can be efficiently reduced and solidified, the conversion rate is up to 99 percent, the photocatalyst is easy to separate and recycle, and the recycling can be realizedHas important scientific research significance and practical application prospect.

Description

Triazole triazinyl-based conjugated microporous polymer and application thereof
Technical Field
The invention belongs to the field of photocatalyst preparation, and particularly relates to a triazole triazinyl-based conjugated microporous polymer and application thereof.
Background
The porous organic polymer (Porous Organic Polymers, POPs) has high specific surface area, excellent thermal stability and chemical stability, good ultraviolet absorption performance and good photocatalytic activity, wherein the conjugated microporous polymer (Conjugated Microporous Polymers, CMPs) is an emerging functional material which is surrounded by a fully conjugated polymer network and has a microporous structure, has the common advantages of the porous organic polymer, and has a continuous conjugated pi-network structure, thereby being beneficial to photon absorption, exciton separation and charge transmission. CMPs have been favored in the field of photocatalysis due to their excellent photoelectric properties. Traditional methods for improving the photocatalytic activity of CMPs have focused more on studying charge transport and energy band regulation, and have less exploration of the key factor, intersystem crossing (InterSystem Crossing, ISC) that has a decisive influence on photocatalytic activity, and only a small part on reducing the singlet-Triplet energy level difference (Energy gap of the Singlet-Triplet states, Δe) ST ) To increase the ISC rate. Spin-Orbit Charge-transfer (SOC), which actually affects ISC dynamics, is rarely explored.
Currently, sea water is a huge liquid uranium ore, and scientists estimate that the sea water contains 45 hundred million tons of uranium, which is thousands of times of the ascertained uranium ore reserves on land, and the uranium is used as the most resource in nuclear energy, but the reserves in China are not abundant, and the quality of the uranium ore is mainly of medium and low grade, so that the scientists are also led to extensive researches. At present, CMPs are reported to be widely applied to reduction of uranium by a photocatalyst in literature, for example: the redox active perylene-anthraquinone conjugated microporous polymer has unique electron delocalization channel, and shows good photocatalytic activity in photocatalytic reduction of uranium (VI). However, the common factors such as high preparation cost, complex preparation process, low photocatalytic activity and the like of the conjugated microporous polymer prevent the conjugated microporous polymer from reducing metal uranium from further developing.
Disclosure of Invention
In order to solve the technical problems, the invention provides a method for constructing Conjugated Microporous Polymers (CMPs) by using a nitrogen enrichment strategy to improve the photocatalytic activity, and the triazole triazinyl conjugated microporous polymers are based on the triazole triazinyl conjugated microporous polymers, so that the charge separation efficiency is high, the increasing SOC value of the triazole triazinyl conjugated microporous polymers promotes the improvement of the ISC rate of the polymers, the excited state service life of the polymers is prolonged, and meanwhile, the reduction performance of uranium is also effectively improved.
In order to achieve the aim, the invention provides a triazole triazinyl-based conjugated microporous polymer, which is characterized in that the structural general formula of the polymer is shown as formula 1:
wherein R is selected from any one of structures shown in formulas 2-4:
preferably, the conjugated microporous polymer is in the form of powder or granule.
Preferably, the conjugated microporous polymers have SOC values of 0.41 and cm, respectively -1 ,0.1 cm -1 And 0.03 cm -1
Preferably, the excited state lives of the conjugated microporous polymer are respectively 30.5 mu s, 24.7 mu s and 18.3 mu s.
Preferably, the preparation method of the conjugated microporous polymer comprises the following steps:
s1, preparing triazole triazine triphenyl bromide: 5- (4-bromophenyl) -2HTetrazole, anhydrous K 2 CO 3 And cyanuric chloride are dissolved in 2-butanone, heated and stirred in an air atmosphere; after cooling to room temperature, the mixture was poured into water and extracted with dichloromethane; collecting an organic layer, washing, drying and purifying by using dichloromethane column chromatography to obtain triazole triazine triphenyl bromide;
s2, preparing a triazolyl triazinyl conjugated microporous polymer: triazole triazine triphenyl bromide prepared in the step S1, borate compound and K 2 CO 3 、Pd(PPh 3 ) 4 AndN,N-dimethylformamide is mixed, heated under the protection of inert gas, and cooled to room temperature after the reaction is finished to obtain a reaction mixture;
and S3, filtering, washing and further purifying the reaction mixture prepared in the step S2 by a Soxhlet extraction method, and vacuum drying to obtain the triazole triazinyl conjugated microporous polymer material.
Preferably, in the step S1, 5- (4-bromobenzene) -2HTetrazole, anhydrous K 2 CO 3 And the mass ratio of the cyanuric chloride is 3-4:8-9:1-1.8.
Preferably, the heating temperature in the step S1 is 90 ℃, and the stirring time is 48 hours; the extraction in the step S1 is repeated three times.
Preferably, in the step S2, the molar ratio of the triazole triazine triphenyl bromide to the borate compound is 2-3.1: 3-4.
Preferably, the heating reaction in the step S2 is to raise the temperature to 100-120 ℃ for 5 hours, and then raise the temperature to 135-155 ℃ for 24-48 hours.
Preferably, the soxhlet extraction time in the step S3 is 24 h and the vacuum drying temperature is 80 ℃.
Based on a general inventive concept, the present invention also provides an application method of the conjugated microporous polymer, comprising the following steps:
s1, dispersing a conjugated microporous polymer in uranium (VI) solution, and regulating the pH value to be 6;
and S2, continuously stirring the mixed solution obtained in the step S1 in the dark under the normal-temperature air atmosphere, and then reducing the photocatalytic uranium (VI) into uranium (IV) by using a xenon lamp as a light source.
Preferably, in the step S1, the concentration of the uranium (VI) solution is 50 to 100 ppm, and the uranium (VI) solution contains 10% by mass of methanol.
Preferably, the duration of stirring in the step S2 is 1 h, and the power of the xenon lamp is 300W.
The photocatalysis principle based on triazole triazinyl conjugated microporous polymer is as follows:
with triazole triazine triphenyl bromide (TTT) as a core, and respectively with benzo [ c ]][1,2,5]Polymerizing thiadiazole (BT), 2, 5-bithiophene (Th) and 1, 4-phenylene diboronic acid pinacol diester (Ph) to construct TTT-based polymer skeleton TTT-BT,TTT-Th and TTT-Ph. Under light excitation, the photosensitizer goes from the ground state (S 0 ) Excited to a singlet excited state (S 1 ) Then reaches a long-life triplet excited state (T 1 ). At T 1 In the state, the photosensitizer and molecular oxygen (O 2 ) Reactive Oxygen Species (ROS) are generated by the reaction, and T of the photosensitizer is prolonged by increasing ISC rate 1 Lifetime and thus help to generate O 2 •−
The SOC value of the enhanced CMPs is an effective strategy based on the design of an efficient photosensitizer of electron-mediated reaction, and the CMPs (TTT-BT, TTT-Ph, TTT-Th) functionalized by BT, ph and Th in the invention show higher photosensitization efficiency by utilizing the unique optical property of the donor-acceptor CMPs, and improve the ISC rate and prolong the excited state service life. Triazolyltriazinyl is largely achieved by enhancing the SOC capability of the polymer rather than reducing ΔE ST To regulate ISC rate, thus effectively improving the photocatalytic efficiency of CMPs.
Compared with the prior art, the invention has the following beneficial effects:
(1) The invention provides a preparation method of a triazole triazine conjugated microporous polymer, which constructs TTT-based polymer frameworks TTT-BT, TTT-Th and TTT-Ph through a nitrogen enrichment strategy, expands an SOC value through the strategy of enriching the TTT framework through nitrogen to enhance ISC dynamics, so that the ISC dynamics generate photo-generated carriers with longer service life, and the photo-reduction process is driven better, so that the preparation substrate is wide.
(2) The triazole triazine conjugated microporous polymer provided by the invention utilizes the unique optical property generated by the interaction of a donor and a receptor thereof, improves the SOC value (0.41 cm) -1 ) Thus effectively promoting the ISC process and maintaining a longer excited state lifetime (up to 30.5 mus), thus exhibiting higher photosensitization efficiency, giving it excellent ability to photocatalytically reduce uranium (VI).
(3) The invention provides a conjugated microporous polymer based on triazolyl triazinyl, which has excellent ultraviolet absorption performance and good photocatalytic activity. Under the illumination condition, the method can efficiently catalyze uranium (VI) to be reduced, the conversion rate is up to 99 percent, and the conversion rate is obviously higher than that of conjugated microporous polymers based on benzo [ c ] [1,2,5] thiadiazole (BT).
(4) The conjugated microporous polymer prepared by the invention is easy to separate and recycle, can be recycled, widens the application of CMPs in the field of photocatalysis based on triazole triazine conjugated microporous polymer, and has important scientific research significance and practical application prospect.
Drawings
In order to more clearly illustrate the embodiments of the present invention or the technical solutions in the prior art, the drawings that are required to be used in the embodiments will be briefly described below. The drawings described below are merely examples of the present invention and other drawings may be obtained from these drawings without inventive effort for a person of ordinary skill in the art.
FIG. 1 is an infrared spectrum of triazole triazine triphenyl bromide (TTT-Br), benzo [ c ] [1,2,5] thiadiazole (BT) and triazole triazinyl conjugated microporous polymer based on TTT-BT in example 1;
FIG. 2 is a nuclear magnetic hydrogen spectrum of TTT-BT in example 1;
FIG. 3 is an electron paramagnetic resonance diagram of TTT-BT at 0 min, 5 min and 8 min in example 1;
fig. 4 is a graph of kinetic decay after pulse excitation at 485 nm in transient absorption at Ar (λem=450 nm) for TTT-BT in example 1;
FIG. 5 is a degradation curve of the photocatalytic seawater uranium extraction of Ph-BT, tr-BT and TTT-BT in experimental example 1;
FIG. 6 is a graph showing the dynamics of photocatalytic seawater uranium extraction from Ph-BT, tr-BT and TTT-BT in Experimental example 1;
FIG. 7 is a degradation graph of TTT-BT in experimental example 1 for photocatalytic seawater uranium extraction;
FIG. 8 is a graph showing degradation curves of different pH values in the photocatalytic seawater uranium extraction of TTT-BT in Experimental example 1;
FIG. 9 is a graph showing the recoverable performance of TTT-BT in experimental example 1 for the photocatalytic seawater uranium extraction;
FIG. 10 is a graph showing the photoreduction performance of U (VI) in the photocatalytic seawater uranium extraction of TTT-BT in Experimental example 1 in the presence of other interfering ions.
Detailed Description
In order to make the technical problems, technical solutions and advantages to be solved more apparent, the following detailed description will be given with reference to the accompanying drawings and specific embodiments.
The following examples are illustrative of the invention and are not intended to limit the scope of the invention. Modifications and substitutions to methods, procedures, or conditions of the present invention without departing from the spirit and nature of the invention are intended to be within the scope of the present invention.
The technical means used in the examples are conventional means well known to those skilled in the art unless otherwise indicated; the reagents used in the examples were all commercially available unless otherwise specified.
Example 1 a triazolyltriazinyl-based conjugated microporous polymer TTT-BT was prepared.
S1, preparing triazole triazine triphenyl bromide (TTT-Br)
5- (4-bromophenyl) -2HTetrazole (3.3 g, 14.8 mmol), anhydrous K 2 CO 3 (8.2 g, 59.2 mmol) and cyanuric chloride (1.0 g, 5.4 mmol) were dissolved in a mixture of 50 mL of 2-butanone, heated to 90 ℃, and stirred 48h in an air atmosphere. After cooling to room temperature, the mixture was poured into 100 mL water and extracted with 50 mL dichloromethane, and the extraction step was repeated three times. The organic layer was collected and washed with water, dried over anhydrous MgSO 4 And (5) drying. The filtrate was evaporated to remove the solvent. Finally, purification by dichloromethane column chromatography gave the triazole triazine triphenyl bromide (TTT-Br) in yield (2.58, g, 60%).
Wherein the structure of the triazole triazine triphenyl bromide is shown in a formula 5:
s2, weighing triazole triazine triphenyl bromide (532.9 mg,0.80 mmol) and 4, 7-bis (4, 5-tetramethyl-1, 3, 2-dioxaborane-2-yl) benzo [ c ]][1,2,5]Thiadiazole (465.7 mg,1.20 mmol) and 25.0 mg Pd (PPh) 3 ) 4 Dissolving in 35.0 mL DMF, adding K 2 CO 3 (2M,4mL) and then under the nitrogen atmosphere, heating to 120 ℃ to react 5h, heating to 150 ℃ to react 48h. After the completion of the reaction, the reaction mixture was cooled to room temperature.
S3, filtering the reaction mixture, pouring the obtained solid substance into a Buchner funnel, and washing with deionized water, ethanol and acetone in sequence for at least five times. Further purifying 24 h by THF Soxhlet extraction, and vacuum drying at 80 ℃ after extraction is finished to obtain a product TTT-BT (808.9 mg, 81%) based on triazole triazinyl conjugated microporous polymer material, wherein the structure of the TTT-BT is shown as a formula 6:
wherein benzo [ c ]][1,2,5]The infrared spectra of thiadiazole (BT), triazolotriazine triphenyl bromide (TTT-Br) and TTT-BT are shown in figure 1, and as can be seen from figure 1, benzo [ c ]][1,2,5]The methyl peak of thiadiazole is 2991 cm -1 There is a characteristic peak present at 1650 cm -1 The peaks of bromine atoms of triazole triazine triphenyl bromide are arranged, so that characteristic peaks of TTT-BT at the positions are weakened, and the positions and the peak intensities of functional groups of the patterns of the monomer and the polymer are combined, so that the successful synthesis of TTT-BT by the polymerization reaction can be determined.
FIG. 2 is a nuclear magnetic hydrogen spectrum of TTT-BT, from which: 1 H NMR (DMSO-d 6 , 400 MHz, ppm): δ 7.98~7.96(d,6H ),7.91~7.89(d,6H)。
FIG. 3 shows electron paramagnetic resonance spectroscopy of TTT-BT, which shows that O is generated within a period of time after DMPO is added 2 •− Thus, a signal peak is shown in the spectrogram, so that the polymer can be determined to generate mainly O under the photocatalysis 2 •−
Fig. 4 is a graph of the kinetic decay of TTT-BT after pulse excitation at 485 nm, with an excited state lifetime of up to 30.5 μs clearly seen, with transient absorption under Ar (λem=450 nm) atmosphere.
Example 2 a triazolyltriazinyl based conjugated microporous polymer TTT-Th was prepared.
S1, preparing triazole triazine triphenyl bromide
5- (4-bromophenyl) -2HTetrazole (3.3 g, 14.8 mmol), anhydrous K 2 CO 3 (8.2 g, 59.2 mmol) and cyanuric chloride (1.0 g, 5.4 mmol) were dissolved in a mixture of 50 mL of 2-butanone, heated to 90 ℃, and stirred 48h in an air atmosphere. After cooling to room temperature, the mixture was poured into 100 mL water and extracted with 50 mL dichloromethane, and the extraction step was repeated three times. The organic layer was collected and washed with water, dried over anhydrous MgSO 4 And (5) drying. The filtrate was evaporated to remove the solvent. Purification by dichloromethane column chromatography gave the triazolotriazine triphenyl bromide product (2.58 g, 60%).
S2, triazole triazine triphenyl bromide (532.9 mg,0.80 mmol), 2, 5-bis (4, 5-tetramethyl-1, 3, 2-dioxaborolan-2-yl) thiophene (385.4 mg,1.20 mmol) and 25.0 mg Pd (PPh) 34 Dissolving in 35.0 mL DMF and adding K 2 CO 3 The (2M, 4 mL) solution was mixed homogeneously, and then was heated to 120℃for reaction 5h under nitrogen, then heated to 150℃for reaction 48h. After the completion of the reaction, the reaction mixture was cooled to room temperature.
S3, filtering the reaction mixture, pouring the obtained solid substance into a Buchner funnel, and washing with deionized water, ethanol and acetone in sequence for at least five times. Further purification 24 h was then performed by soxhlet extraction with THF. After the extraction was completed, the mixture was dried under vacuum at 80℃to obtain TTT-Th (798.8 mg, 86%) as a yellow powder.
Wherein the structure of TTT-Th is shown in formula 7:
example 3 a triazolyltriazinyl based conjugated microporous polymer TTT-Ph was prepared.
S1, preparing triazole triazine triphenyl bromide
5- (4-bromophenyl) -2HTetrazole (3.3 g, 14.8 mmol), anhydrous K 2 CO 3 (8.2 g, 59.2 mmol) and cyanuric chloride (1.0 g, 5.4 mmol) were dissolved in a mixture of 50 mL of 2-butanone, heated to 90 ℃, and stirred 48h in an air atmosphere. After cooling to room temperature, the mixture was poured into 100 mL water and extracted with 50 mL dichloromethane, and the extraction step was repeated three times. The organic layer was collected and washed with water, dried over anhydrous MgSO 4 And (5) drying. The filtrate was evaporated to remove the solvent. Then, the triazole triazine triphenyl bromide was purified by dichloromethane column chromatography to give the yield (2.58, g, 60%).
S2, triazole triazine triphenyl bromide 532.9 mg,0.80 mmol), 1, 4-phenylene diboronic acid pinacol diester (396.0 mg,1.20 mmol) and 25.0 mg Pd (PPh) 34 Dissolving in 35.0 mL DMF and adding K 2 CO 3 The (2M, 4 mL) solution was in a homogeneously mixed state. Under the nitrogen atmosphere, the mixture is heated to 120 ℃ to react 5h, then the temperature is raised to 150 ℃ to react 48h. After the reaction was completed, the reaction mixture was cooled to room temperature. The reaction mixture was filtered and the resulting solid material was washed with deionized water, ethanol and acetone sequentially, at least five times. Further purification 24 h was then performed with THF soxhlet extraction. After drying in vacuo at 80℃the product was obtained as a yellow powder TTT-Ph (798.8 mg, 86%).
Wherein the structure of TTT-Ph is shown in formula 8:
comparative example 1 a conjugated microporous polymer Ph-BT based on benzo [ c ] [1,2,5] thiadiazole (BT) was prepared.
S1, weighing 4, 4-dibromo-5-4-bromophenyl-1, 1:3, 1-terphenyl (434.5 mg,0.80 mmol), 4, 7-bis (4, 5-tetramethyl-1, 3, 2-dioxaborane-2-yl) benzo [ c ]][1,2,5]Thiadiazole (465.7 mg,1.20 mmol) and 25.0 mg Pd (PPh) 34 Dissolving in 35.0 mL DMF and adding K 2 CO 3 The (2M, 4 mL) solution is in a uniform mixing state, and is heated to 120 ℃ to react 5 and h under the nitrogen atmosphere, then is heated to 150 ℃ to react 48 and h. After the completion of the reaction, the reaction mixture was cooled to room temperature.
S2, filtering the reaction mixture, washing with deionized water, ethanol and acetone in sequence, washing at least five times, and further purifying 24 h by Soxhlet extraction (THF). Vacuum drying at 80deg.C to obtain yellow powder Ph-BT (783.2 mg, 87%) with structural formula shown in formula 9:
comparative example 2 a conjugated microporous polymer Tr-BT based on benzo [ c ] [1,2,5] thiadiazole (BT) was prepared.
S1, weighing 2,4, 6-tri (4-bromophenyl) -1,3, 5-triazine (436.8 mg,0.80 mmol), 4, 7-bis (4, 5-tetramethyl-1, 3, 2-dioxaborane-2-yl) benzo [ c ]][1,2,5]Thiadiazole (465.7 mg,1.20 mmol) and 25.0 mg Pd (PPh) 3 ) 4 Dissolving in 35.0 mL DMF and adding K 2 CO 3 The (2M, 4 mL) solution was mixed homogeneously, and then was heated to 120℃for reaction 5h under nitrogen, then heated to 150℃for reaction 48h. After the completion of the reaction, the reaction mixture was cooled to room temperature.
S2, filtering the reaction mixture, washing with deionized water, ethanol and acetone in sequence, washing at least five times, and further purifying 24 h by Soxhlet extraction (THF). Vacuum drying at 80℃gave Tr-BT (821.3 mg, 91%) as a yellow powder.
Wherein the structure of Tr-BT is shown in formula 10:
experimental example 1, the ability of Ph-BT, tr-BT, TTT-Th and TTT-Ph to catalyze uranium ion reduction was examined.
Adding Ph-BT or Tr-BT or TTT-Th or TTT-Ph prepared by 50.0 mg into 50.0 mL 100.0 ppm U (VI) solution (containing 5.0 mL methanol), ultrasonic treating for 2 min, stirring continuously, and mixing with small amount of negligible NaOH (0.1M) or HNO 3 (0.1) M) solution pH was adjusted. The resulting mixture was stirred continuously in the dark before irradiation60 min reaches adsorption-desorption equilibrium. Subsequently, a 300W Xe lamp (light source model: SHX-F300) with a 400 nm cut-off filter was used as a light source. In a given time, a sample aliquot (2.0. 2.0 mL) of the solution was pipetted and filtered through a 0.22 μm nylon filter. And the filtrate was analyzed by inductively coupled plasma mass spectrometry (ICP-MS).
(1) Investigation of degradation efficiency of Ph-BT, tr-BT, TTT-Th and TTT-Ph
Through calculation, the degradation efficiencies of Ph-BT, tr-BT, TTT-Th and TTT-Ph are 31%, 76%, 99%, 95% and 90%, respectively, and compared with non-triazole triazinyl conjugated microporous polymers, the degradation rate of the triazole triazinyl conjugated microporous polymers TTT-BT, TTT-Th and TTT-Ph prepared by the invention on uranium (VI) is obviously increased.
(2) Examine degradation curve graphs of Ph-BT, tr-BT and TTT-BT for extracting uranium from seawater by photocatalysis
At a given time, an aliquot (2 mL) was taken and filtered through a 0.22 μm nylon filter. Determination of UO in supernatant by ICP-MS 2 2+ Content of UO(s) 2 2 + The light reduction efficiency calculation formula of (2) is as follows:
wherein RE is the degradation rate of the catalyst; c (C) 0 And C t The concentration of the solution (ppm, mg/L) at the initial and contact times t (min), respectively.
The results are shown in fig. 5, wherein C represents the current concentration at time t, and fig. 5 is a degradation graph of conjugated microporous polymers Ph-BT, tr-BT and TTT-BT for extracting uranium from seawater by photocatalysis, and after the reduction reaction of TTT-BT and uranium (VI) can be obtained by analysis, the degradation efficiency of the conjugated microporous polymers Ph-BT and Tr-BT is found to be almost 99% by calculation, and the degradation efficiency of the conjugated microporous polymers Ph-BT and Tr-BT is not high.
(3) Examining the dynamics curve of Ph-BT, tr-BT and TTT-BT for extracting uranium from seawater by photocatalysis
The three catalysts were each reacted with uranium solution and, at a given time, aliquots (2 mL) were taken and filtered through a 0.22 μm nylon filter. Measurement by ICP-MSUO in supernatant 2 2+ After the degradation efficiency is obtained, the kinetic constant of the material can be obtained by taking the logarithm of the material and then fitting the material. As shown in FIG. 6, the kinetic constant of TTT-BT obtained by analysis was maximized, indicating that it reacted with U (VI) to form UO 2 2+ Fastest.
(4) Examine degradation curve graph of TTT-BT photocatalysis seawater uranium extraction
FIG. 7 is a graph of degradation of TTT-BT in photocatalytic seawater uranium extraction, which can be analyzed to yield a reduction reaction between TTT-BT and uranium (VI), and two groups of TTT-BT react with uranium solution without illumination or catalyst. The calculation mode is consistent with that in (2), and analysis shows that the degradation efficiency of the catalyst under the illumination condition reaches almost 99 percent. And hardly degrades under the condition of no illumination and catalyst TTT-BT.
(5) Investigation of degradation curves of different pH values in TTT-BT photocatalysis seawater uranium extraction
Fig. 8 is a degradation curve of TTT-BT at different pH in the photocatalytic seawater uranium extraction, where the degradation effect is best when we can obtain the ph=6 from the figure by changing the pH difference of the uranium solution to detect when the reduction reaction of TTT-BT and uranium (vi) occurs.
(6) Recovery performance curve graph for examining TTT-BT photocatalysis seawater uranium extraction
After the end of the first reaction, 1M Na was used 2 CO 3 Washing TTT-BT to eliminate UO on surface 2 2+ The washing was repeated five times with deionized water. Then, the mixture was dehydrated in vacuum at 60℃for 8h. And then the dried catalyst reacts with uranium, the steps are repeated for three times, the recovery performance curve of the TTT-BT photocatalysis seawater uranium extraction is shown in the figure 9, the recovery performance of the TTT-BT photocatalysis seawater uranium extraction can be analyzed to obtain the recovery performance of the TTT-BT and the uranium (VI) after the reduction reaction is up to 99 percent after the reaction is carried out, the loss is almost avoided, and the catalyst can be recycled.
(7) Examine the photo-reduction performance diagram of U (VI) in TTT-BT photo-catalytic seawater uranium extraction in the presence of other interfering ions
FIG. 10 is a graph showing the photoreduction performance of U (VI) in TTT-BT photocatalytic seawater uranium extraction in the presence of interfering ions, wherein different ions are added to the reaction solution for reaction, and each set of data in FIG. 10 shows the UO before and after the addition of different interfering ions 2 2+ C/C of (C) 0 The concentration ratio shows that the photocatalytic seawater uranium extraction U (VI) of the TTT-BT has high selectivity on the reduced metal uranium in the presence of interfering ions.

Claims (10)

1. The triazole triazinyl-based conjugated microporous polymer is characterized in that the structural general formula of the polymer is shown as formula 1:
wherein R is selected from any one of structures shown in formulas 2-4:
2. the conjugated microporous polymer according to claim 1, wherein the conjugated microporous polymer is prepared by the following method:
s1, preparing triazole triazine triphenyl bromide: 5- (4-bromophenyl) -2HTetrazole, anhydrous K 2 CO 3 And cyanuric chloride are dissolved in 2-butanone, heated and stirred in an air atmosphere; after cooling to room temperature, the mixture was poured into water and extracted with dichloromethane; collecting an organic layer, washing, drying and purifying by using dichloromethane column chromatography to obtain triazole triazine triphenyl bromide;
s2, preparing a triazolyl triazinyl conjugated microporous polymer: triazole triazine triphenyl bromide prepared in the step S1, borate compound and K 2 CO 3 、Pd(PPh 3 ) 4 AndN,N-dimethylformamide is mixed, heated in an inert gas atmosphere, and cooled to room temperature after the reaction is finished to obtain a reaction mixture;
and S3, filtering, washing and further purifying the reaction mixture prepared in the step S2 by Soxhlet extraction, and vacuum drying to obtain the triazole triazinyl conjugated microporous polymer material.
3. The conjugated microporous polymer according to claim 2, wherein in step S1, 5- (4-bromobenzene) -2HTetrazole, anhydrous K 2 CO 3 And the mass ratio of the cyanuric chloride is 3-4:8-9:1-1.8.
4. The conjugated microporous polymer according to claim 2, wherein the heating temperature in step S1 is 90 ℃ and the reaction time is 48h; the extraction in the step S1 is repeated three times.
5. The conjugated microporous polymer according to claim 2, wherein in the step S2, the molar ratio of triazole triazine triphenyl bromide to the borate compound is 2-3.1: 3-4.
6. The conjugated microporous polymer according to claim 2, wherein the heating reaction in step S2 is performed by heating to 100-120 ℃ for 5-h, and then heating to 135-155 ℃ for 24-48 hours.
7. The conjugated microporous polymer according to claim 2, wherein the soxhlet extraction time in step S3 is 24 h and the vacuum drying temperature is 80 ℃.
8. Use of the conjugated microporous polymer according to any of claims 1 to 7 as a photocatalyst in uranium reduction, comprising the steps of:
s1, adding a conjugated microporous polymer into uranium (VI) solution, and adjusting the pH value to 6;
and S2, continuously stirring the mixed solution obtained in the step S1 in the dark under the normal-temperature air atmosphere, and then reducing the photocatalytic uranium (VI) into uranium (IV) by using a xenon lamp as a light source.
9. The use according to claim 8, wherein the uranium (VI) solution in the S1 step has a concentration of 50-100 ppm, and the uranium (VI) solution contains 10% by mass of methanol.
10. The use according to claim 8, wherein the duration of stirring in step S2 is 1 h and the power of the xenon lamp is 300W.
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