CN101890338B - Nano-SiO2 adsorption material and preparation method and application thereof - Google Patents

Nano-SiO2 adsorption material and preparation method and application thereof Download PDF

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CN101890338B
CN101890338B CN201010242232XA CN201010242232A CN101890338B CN 101890338 B CN101890338 B CN 101890338B CN 201010242232X A CN201010242232X A CN 201010242232XA CN 201010242232 A CN201010242232 A CN 201010242232A CN 101890338 B CN101890338 B CN 101890338B
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张祖磊
李蕾
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Jiaxing University
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Abstract

The invention relates to a nano-SiO2 adsorption material. The preparation method comprises the following step: using nano-SiO2, aminopropyl alkyl and -CO-C6H4-CH2P+(C6H5)3Br- to perform a chemical reaction and prepare the nano-SiO2 adsorption material through covalent linkage. The preparation method is simple, the conditions are mild, and product can be used to separate/concentrate trace Cr2O7<2-> in the environment. The nano-SiO2 adsorption material of the invention has the advantages of high adsorption efficiency, easy operation, no secondary pollution and the like.

Description

Nano SiO2Adsorption material, preparation method and application
Technical Field
The invention relates to a modified material, in particular to nano SiO modified by an organic functional reagent2Adsorbing material and preparation method thereof, and prepared adsorbing material can be used for trace Cr in environment2O7 2-Separation/enrichment.
Background
In recent years, the industries applying chromium compounds, such as electroplating, chemical industry, leather industry and the like, have remarkable economic benefits, thereby greatly promoting the mass production of chromium salt factories. Chromium-containing waste residues and high-concentration hexavalent chromium ions in wastewater generated in the production process of chromium salt have toxic action on human bodies, crops and livestock, and hexavalent chromium enters human blood to form chromium oxide, so that hemoglobin is changed into methemoglobin, and the function of oxygen carried by red blood cells is obstructed, so that cells are suffocated, and the human health is harmed. And hexavalent chromium exists mainly in the form of acid radical in nature, so that the exploration and synthesis of a novel functional adsorbent with positive charge have great research significance.
The current methods for removing heavy metal ions mainly include precipitation (Journal of Hazardous Materials, 2008, 159, 435-. The precipitation method has low efficiency, and other impurities are introduced while metal ions are precipitated; the ion exchange process has poor selectivity and low exchange capacity; the liquid-liquid extraction method uses different solvents, causes secondary pollution to the environment and also relates to the problem of solvent recovery; the solid phase extraction method is a main method for separating/enriching metal ions developed in recent years, research and development of adsorbing materials are key technologies, and the currently developed adsorbing materials have various types but have respective defects, and the following defects mainly exist in summary: 1) low adsorption capacity, 2) high price of the adsorption material.
Disclosure of Invention
An object of the present invention is to provide a nano SiO2The adsorbing material can overcome the defects and is a novel material with low price and remarkable adsorbing effect.
Another object of the present invention is to provide a nano SiO2A preparation method of the adsorbing material.
Another object of the present invention is to provide a nano SiO2Use of the adsorbent material, and use of the adsorbent materialTrace amount of Cr in the environment2O7 2-Separation/enrichment.
The technical scheme of the invention is as follows:
nano SiO2Adsorption material comprising nano SiO2Aminopropylsilyl and-CO-C6H4-CH2P+(C6H5)3Br-And (4) a base. Aminopropyl silane radical is respectively reacted with nano SiO2and-CO-C6H4-CH2P+(C6H5)3Br-The radicals are covalently bonded. Nano SiO2Aminopropylsilyl and-CO-C6H4-CH2P+(C6H5)3Br-The molar ratio of the radicals is 1: 2.5.
Nano SiO2An adsorbent having the following structure:
Figure BSA00000212967900021
wherein,
Figure BSA00000212967900022
represents nano SiO2Ph is phenyl C6H5
Nano SiO2Reacting with a crosslinking agent aminopropyltriethoxysilane through SiO2The hydroxyl groups on (a) are covalently bound to the aminopropylsilyl groups as shown below:
Figure BSA00000212967900023
then adding ClCO-C6H4-CH2P(C6H5)3And reacting Br to obtain the catalyst. The reaction obtained is carried out with distilled waterDissolving, filtering, and drying
Another kind of nano SiO2The preparation method of the adsorbing material comprises the following steps:
1) the nano silicon dioxide is firstly subjected to thermal pretreatment for 4 hours at 110 ℃.
2) Dissolving the pretreated nano silicon dioxide in a toluene solvent, adding aminopropyl triethoxysilane after ultrasonic degassing, and performing ultrasonic degassing again.
3) General formula (N)2The reaction is stirred for more than 7 hours, preferably 9 hours at the temperature of 75-80 ℃.
4) Then adding ClOC-C6H4-CH2P(C6H5)3Br, 1, 2-dichloroethane and anhydrous pyridine, reacting for more than 6 hours at 80 ℃ to obtain the catalyst.
ClOC-C6H4-CH2P(C6H5)3The preparation method of Br is as follows: reacting p-bromomethylbenzoic acid, triphenylphosphine and tetrahydrofuran at 80 ℃, cooling to room temperature, adding diethyl ether, precipitating, and filtering. Heating the product, starting to dropwise add thionyl chloride when the temperature rises to 80 ℃, keeping the temperature for more than 1 hour after the dropwise addition is finished until no gas escapes, and distilling and drying the product to obtain the product. Preparation of ClOC-C6H4-CH2P(C6H5)3Embodiments of Br are: p-bromomethylbenzoic acid (1.70g, 7.9mmol), triphenylphosphine (2.10g, 8.0mmol) and tetrahydrofuran (30mL) react at 80 ℃ for 8 hours, the reaction product is cooled to room temperature, 10mL of diethyl ether is added, precipitate is separated out, filtered and heated, thionyl chloride (7mL) is added dropwise when the temperature rises to 80 ℃, the dripping is finished after 20 minutes, the temperature is kept for 3 hours until no gas escapes, and the catalyst is obtained after distillation and drying.
The invention relates to nano SiO2Preparation method of adsorbing material and nano SiO2Aminopropylsilyl and-CO-C6H4-CH2P+(C6H5)3Br-The molar ratio of the radicals is 1: 2.5.
The invention relates to nano SiO2The adsorbing material can be used for adsorbing trace Cr in the environment2O7 2-Separation/enrichment. For Cr at solution pH 12O7 2-The ion adsorption efficiency reaches the maximum value, Cr2O7 2-The best adsorption effect is achieved when the ion concentration is 50 mg/L.
The technical scheme of the invention has the following beneficial effects:
the invention provides a nano SiO2Adsorption material of nano SiO2Aminopropylsilyl and-CO-C6H4-CH2P+(C6H5)3Br-The molar ratio of the base groups is 1: 2.5, the preparation method is simple, the condition is mild, and the method can be used for trace Cr in the environment2O7 2-Separation/enrichment.
Drawings
FIG. 1 is an infrared spectrum of a raw material of nano-silica;
FIG. 2 is an infrared spectrum of a nanosilica material of the present invention;
FIG. 3 influence of pH on adsorption efficiency;
FIG. 4 influence of oscillation time on adsorption efficiency;
FIG. 5Cr2O7 2-The effect of concentration of (a) on the adsorption efficiency.
Detailed Description
The technical solution of the present invention is described in detail below.
Example 1 Synthesis of nanosilica materials
1.00g (0.017mol) of nanosilica which had been thermally pretreated at 110 ℃ for 4 hours were accurately weighed into a 150mL three-necked flask, 50mL of toluene was added, ultrasonic degassing was performed for 30 minutes, and 0.0425 aminopropyltriethoxysilane (KH-550) was added, and ultrasonic degassing was performed for 10 minutes. In general N2Under the condition, the reaction temperature is controlled at 80 ℃, and the nano silicon dioxide aminopropyl silane is obtained after stirring reaction for 9 hours.
P-bromomethylbenzoic acid (1.70g, 7.9mmol), triphenylphosphine (2.10g, 8.0mmol) and tetrahydrofuran (30mL) react at 80 ℃ for 8 hours, the reaction product is cooled to room temperature, 10mL of diethyl ether is added, precipitate is separated out and filtered, heating is carried out, thionyl chloride (7mL) is added dropwise when the temperature rises to 80 ℃, the dripping is finished after 20 minutes, the heat preservation is continued for 3 hours until no gas escapes, distillation is carried out, and a reddish brown solid ClOC-C is obtained after drying6H5-CH2P(Ph)3Br。
Finally, 2.00g (0.0103mol) of nanosilica aminopropylsilane and 1, 2-dichloroethane (10mL) were added to a 150mL three-necked flask, and a few drops of anhydrous pyridine and ClOC-C were added6H5-CH2P(Ph)3Br (4.50g, 9.7mmol) was controlled at 80 ℃ and reacted for 8 hours, and the reaction was dissolved in distilled water, filtered and dried.
Example 2
And carrying out structural characterization-infrared spectrogram on the synthesized nano-silica bonded organic functional reagent adsorbent and the raw material nano-silica.
Raw material Nano-SiO2The surface has a large number of hydroxyl groups, so that the thickness of the film is 3435.68cm-1And a larger absorption peak is nearby. 1625.95cm-1The absorption peak is from the adsorbed water, 1107.03cm-1Strong absorption of (A) from asymmetric stretching vibration of Si-O-Si bond, 789.19cm-1And 464.86cm-1The absorption peak comes from the bending vibration of the Si-O-Si bond. 1684.32cm in FIG. 2-1A strong absorption peak at (B) comes from stretching vibration of carbonyl group, 3435.68cm-1A strong absorption peak comes from the stretching vibration of the associated aminoDynamic 3052.97cm-1The absorption peak is from C-H stretching vibration in benzene ring, 1113.51cm-1Strong absorption of (A) from asymmetric stretching vibration of Si-O-Si bond, 776.22cm-1And 471.35cm-1The absorption peak comes from the bending vibration of the Si-O-Si bond, 1638.92cm-1The absorption peak is derived from the stretching vibration of C ═ C in the benzene ring, 1515.68cm-1The absorption peak is from the deformation vibration of the amino group.
Comparing FIGS. 1 and 2, in FIG. 2, there are stretching vibration and vibration of the associated amino group, and also stretching vibration of the carbonyl group, bending vibration of the Si-O-Si bond, and asymmetric stretching vibration of the Si-O-Si bond, which all indicate that the synthesized substance has various functional groups of the target molecule.
EXAMPLE 3 determination of the pH of the solution
The prepared nanosilica material (Si | (CH) was charged in 5 100mL ground Erlenmeyer flasks (0.1 g)2)3-NH-CO-Ph-CH2-P-(C6H5)3Br) was added thereto 2.00mL of Cr at a concentration of 50. mu.g/mL2O7 2-Adjusting the pH of the solution, shaking for 30 minutes, standing for 1 hour, transferring supernatant, centrifuging for 10 minutes, diluting the concentration to the optimal linear range, and detecting residual Cr by flame atomic absorption spectrometry2O7 2-The residual ion content was calculated, and the adsorption rate A% was calculated, and for comparison of the adsorption effect, a comparative experiment was conducted using the same amount of nano-silica. As shown in fig. 3, it can be seen that the adsorption efficiency of the synthesized adsorbent reached a maximum of 97.79% at pH 1. The adsorption efficiency decreases continuously with increasing pH. And nano silicon dioxide to Cr when pH is 12O7 2-The ion adsorption efficiency reaches a maximum of 75.75%, and the adsorption efficiency is obviously reduced along with the increase of pH. Comparing the two curves, it can be seen that the synthesized adsorbent is on Cr2O7 2The adsorption efficiency of ions is obviously higher than that of Nano-SiO2For Cr2O7 2-The efficiency of the adsorption of ions.
Example 4
Adjusting pH to 1, Cr2O7 2-The initial ion concentration is 50mg/L, and 0.02g, 0.05g, 0.1g, 0.2g and 0.3g Si (CH) are added at 25 deg.C2)3-NH-CO-Ph-CH2-P(C6H5)3Br, shaking for 30min, standing for 1h, diluting the concentration to the optimal linear range, and measuring Cr by flame atomic absorption spectrometry2O7 2-Ion equilibrium concentration, investigating adsorbent dosage versus Cr2O7 2-Influence of adsorption rate. The results show that: si | (CH)2)3-NH-CO-Ph-CH2-P(C6H5)3Br to Cr2O7 2-The adsorption rate of the adsorbent is improved along with the increase of the addition amount of the adsorbent, when the dosage of the adsorbent reaches 0.1g, the adsorption rate can reach more than 95 percent, and Si (CH) is selected comprehensively in consideration of the experiment2)3-NH-CO-Ph-CH2-P(C6H5)3The amount of Br adsorbed was 0.1 g. Meanwhile, the effect of shaking time of 10, 20, 30, 60, 90, 120, 150 minutes was examined when the amount of the novel fixed adsorbent was 0.1g and pH was 1, and the result is shown in fig. 4. From the graph, it can be seen that the adsorption effect is best when the shaking time is 30 minutes.
Example 5
Adjusting pH to 1, Cr2O7 2-Initial ion concentrations of 10, 20, 50, 100 and 150mg/L, respectively adding 0.1g of novel adsorbent at 25 deg.C, shaking for 30min, standing for 1 hr, centrifuging, diluting to the optimum linear range, and measuring Cr by flame atomic absorption spectrometry2O7 2-Ion equilibrium concentration, investigation of Cr2O7 2-Initial ion concentration vs. Cr2O7 2-Influence of adsorption rate. As can be seen from FIG. 5, the adsorption effect was the best at an initial concentration of 50 mg/L.
Example 6
Preparing a series of Cr6+0.1. mu.g/mL (c: 05. mu.g/mL, 1.0. mu.g/mL, 2.0. mu.g/mL, 3.0. mu.g/mL, 4.0. mu.g/mL, 5.0. mu.g/mL) and the absorbance thereof was measured, and the results showed that: the content of Cd (II) is in a better linear relation between 0.5 mu g/mL and 4.0 mu g/mL, and the linear equation is as follows: a is 0.003175C +0.010819, the correlation linearity coefficient is 0.9995, the detection limit of the method is 0.084 mu g/mL, and 2.0 mu g/mL of Cr is measured2O7 2-10 times, the RSD is 1.09%
Example 7
In order to verify the accuracy of the analysis method, Cr in three water samples, namely domestic sewage, pond water and industrial wastewater are respectively analyzed2O7 2-The content of (b) is measured. Method for adding standard to Cr in three water samples2O7 2-The contents and the recovery rates of (A) were measured, and the results are shown in Table 1.
TABLE 1 Cr in environmental water samples2O7 2-Measurement and recovery test (n ═ 5)
Figure BSA00000212967900061
Figure BSA00000212967900071
"+/-" is the relative standard deviation

Claims (1)

1. Nano SiO2A method for preparing an adsorbing material, which comprises the steps of,
the nano SiO2The adsorbing material comprises nano SiO2Aminopropylsilyl and-CO-C6H4-CH2P+(C6H5)3Br-The aminopropylsilyl groups are respectively connected with the nano SiO2And said-CO-C6H4-CH2P+(C6H5)3Br-Covalently bonding the groups;
the preparation steps are as follows:
1) the nano silicon dioxide is firstly subjected to thermal pretreatment for 4 hours at 110 ℃;
2) dissolving the pretreated nano silicon dioxide in a toluene solvent, adding aminopropyl triethoxysilane after ultrasonic degassing, and performing ultrasonic degassing again;
3) general formula (N)2Under the condition, stirring and reacting for more than 7 hours at the temperature of 75-80 ℃;
4) then adding ClOC-C6H4-CH2P(C6H5)3Br, 1, 2-dichloroethane and anhydrous pyridine, react for more than 6 hours at 80 ℃ to obtain the catalyst; the ClOC-C6H4-CH2P(C6H5)3The preparation method of Br is as follows: reacting p-bromomethylbenzoic acid, triphenylphosphine and tetrahydrofuran at 80 ℃, cooling to room temperature, adding diethyl ether, precipitating, and filtering; heating the product, starting to dropwise add thionyl chloride when the temperature rises to 80 ℃, keeping the temperature for more than 1 hour after the dropwise addition is finished until no gas escapes, and distilling and drying the product to obtain the product.
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