CN111715198A - Magnetic fullerene nano material and application thereof in magnetic dispersion solid-phase extraction of methyl methoxyacrylate pesticides - Google Patents
Magnetic fullerene nano material and application thereof in magnetic dispersion solid-phase extraction of methyl methoxyacrylate pesticides Download PDFInfo
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Abstract
The invention discloses a magnetic fullerene nano material and application thereof in magnetic dispersion solid-phase extraction of methyl methoxyacrylate pesticides, wherein the preparation steps are as follows: first Fe by tetraethylorthosilicate TEOS3O4Modifying the nano particles to obtain silicon dioxide coated ferroferric oxide superparamagnetic particles, and marking the particles as Fe3O4@SiO2Nanoparticles; then Fe3O4@SiO2The nano particles react with 3-chloropropyltrimethoxysilane to obtain Fe3O4@SiO2@ Cl nanoparticles; finally, the fullerene C is added60Reacting with benzaldehyde and benzylamineObtaining 2, 5-diphenyl fullerene pyrroline, and then reacting with Fe3O4@SiO2Reaction of @ Cl nano particles to obtain magnetic fullerene nano material, marked as Fe3O4@SiO2@C60Nanoparticles. The magnetic fullerene nano material can be used for magnetic dispersion solid phase extraction of methyl methoxyacrylate pesticides, and has the advantages of strong adsorbability, large adsorption capacity, good selectivity and easiness in elution.
Description
Technical Field
The invention belongs to the technical field of enrichment, purification and detection of pesticide residues in food and environmental samples, and particularly relates to a magnetic fullerene nano material and application thereof in magnetic dispersion solid-phase extraction of methyl methoxyacrylate pesticides.
Background
Pesticide residue analysis is an analytical technique for trace components in complex mixtures. The development trend of pesticide chemical pollutant residue detection technology is that the sample dosage is less, the reagent consumption is less, and the analysis speed is fast. How to realize multi-residue analysis, and ensure the recovery rate while effectively removing impurities is a difficult point of the whole pretreatment process.
The magnetic solid phase extraction technology is a novel sample pretreatment technology developed in recent years, and has some special advantages compared with the traditional solid phase extraction technology: the magnetic adsorbent can be easily separated from the sample solution by applying an external magnetic field without centrifugation or filtration; the magnetic adsorbent material is dispersed in the solution, which allows for more sufficient contact area between the sample and the magnetic adsorbent, faster mass transfer, and rapid equilibration. Fullerene (C)60) As a carbon-based nano material, the carbon atom adopts sp2Hybridization, strong electrophilic capacity, electron-deficient polyene property, and pi electron distribution in C60Cage structure of thirty-dihedronThe inner and outer surfaces of the metal wire form a three-dimensional conjugated system and have stronger pi-pi conjugation effect. Due to C60The composite material has the advantages of large specific surface area, strong hydrophobicity, easy functional modification, good acid resistance, alkali resistance, heat resistance and chemical stability, and certain advantages when being applied to separation and enrichment of pesticide residues in foods and environments. The ferroferric oxide nano particles have superparamagnetism and are reacted with C60Constructing a magnetic fullerene material by reacting C60The adsorption performance of the method is combined with the convenient magnetic separation of the ferroferric oxide nanoparticles, the magnetic dispersion solid phase extraction method is established, the method is applied to the enrichment and purification of pesticide residues, the pretreatment steps are simple, the method can be recycled for many times, and the analysis cost can be greatly saved.
Disclosure of Invention
In order to overcome the defects of complicated operation steps, long time consumption, difficult recycling of an adsorbent and the like of the traditional solid-phase pretreatment method, the invention provides a magnetic fullerene nano-material and application thereof in magnetic dispersion solid-phase extraction of methyl methoxyacrylate pesticides, so as to realize high-selectivity adsorption, separation and detection of methyl methoxyacrylate pesticides such as azoxystrobin, pyraclostrobin, trifloxystrobin, fenpyroximate and the like in a detected sample.
In order to realize the purpose of the invention, the following technical scheme is adopted:
the invention discloses a preparation method of a magnetic fullerene nano-material, which is characterized by comprising the following steps: first Fe by tetraethylorthosilicate TEOS3O4Modifying the nano particles to obtain silicon dioxide coated ferroferric oxide superparamagnetic particles, and marking the particles as Fe3O4@SiO2Nanoparticles; then Fe3O4@SiO2The nano particles react with 3-chloropropyltrimethoxysilane to obtain Fe3O4@SiO2@ Cl nanoparticles; finally, the fullerene C is added60Reacting with benzaldehyde and benzylamine to obtain 2, 5-diphenyl fullerene pyrroline, and reacting with Fe3O4@SiO2Reaction of @ Cl nano particles to obtain magnetic fullerene nano material, marked as Fe3O4@SiO2@C60Nano meterParticles.
The synthetic route of the invention is as follows:
the preparation method of the magnetic fullerene nano-material specifically comprises the following steps:
Preferably, in step 1 and step 2, Fe3O4The dosage ratio of the nano particles, isopropanol, water, ammonia water, tetraethyl orthosilicate, toluene, triethylamine and 3-chloropropyltrimethoxysilane is 1 g: 100mL of: 8mL of: 10mL of: 8mL of: 100mL of: 1mL of: 2 mL.
Preferably, in step 3, C60The dosage ratio of benzaldehyde, benzylamine and o-dichlorobenzene is 0.5 mmol: 2.5 mmol: 2.5 mmol: 60 mL.
Preferably, in step 4, Fe3O4@SiO2The dosage ratio of the @ Cl nano particles to the toluene to the triethylamine to the 2, 5-diphenyl fullerene pyrroline is 2 g: 80mL of: 1mL of: 1g of the total weight of the composition.
The magnetic fullerene nano material prepared by the invention can be used as a magnetic dispersion solid phase extraction adsorbent for magnetic dispersion solid phase extraction of methoxy methyl acrylate pesticides in water samples or fruit and vegetable samples, and comprises the following steps:
The water sample extraction method comprises the following steps: sucking 1mL of water sample to be detected into a 15mL pointed-bottom centrifuge tube, adding 9mL of ultrapure water, uniformly mixing, adding 30mg of the magnetic fullerene nano material, and performing oscillation extraction for 20 min; gathering the magnetic fullerene nano-material to the bottom by using a magnet, and pouring all the solution;
the fruit and vegetable sample extraction method comprises the following steps: weighing 2g of fruit and vegetable samples to be detected, putting the fruit and vegetable samples into a 50mL plastic centrifuge tube, adding 20mL acetonitrile, and homogenizing and extracting for 1min at 15000r/min on a high-speed tissue triturator; centrifuging at 10000r/min for 5min, sucking 1mL of supernatant into a 15mL pointed-bottom centrifuge tube, adding 9mL of ultrapure water, mixing uniformly, adding 30mg of the magnetic fullerene nano material, and performing oscillation extraction for 20 min; gathering the magnetic fullerene nano-material to the bottom by using a magnet, and pouring all the solution;
Adding 1mL of ethyl acetate solution into a centrifugal tube in which the magnetic fullerene nano material is positioned, and carrying out desorption by vortex for 1 min; transferring the clear liquid into a new centrifugal tube after magnetic separation by a magnet;
the desorption operation is repeated for 2 times, all desorption solutions are combined and collected in a test tube, and then the magnetic dispersion solid-phase extraction of the methoxy methyl acrylate pesticides in the water sample or the fruit and vegetable sample is completed;
The obtained analytic solution can be used for UHPLC-MS/MS analysis, so that the concentration of the methoxy methyl acrylate pesticide in a water sample to be detected can be determined.
Compared with the prior art, the invention has the beneficial effects that:
the magnetic fullerene nano material (Fe) synthesized by the invention3O4@SiO2@C60Nano particles) has strong adsorbability to methyl methoxyacrylate pesticides, large adsorption capacity, good selectivity and easy elution, can be used for magnetic dispersion solid-phase extraction of methyl methoxyacrylate pesticides, has quick method and reusable materials, and saves the pretreatment time and cost of samples. And by combining UHPLC-MS/MS analysis, the method is sensitive and has high accuracy.
Drawings
FIG. 1 shows Fe obtained in example 1 of the present invention3O4@SiO2@C60Scanning electron micrographs of nanoparticles.
FIG. 2 shows Fe in example 1 of the present invention3O4Nanoparticles, Fe3O4@SiO2Nanoparticles, C60And Fe3O4@SiO2@C60Infrared spectrum of the nanoparticles.
FIG. 3 is a liquid chromatography triple quadrupole tandem mass spectrometry chromatogram of azoxystrobin (azoxystrobin), pyraclostrobin (pyraclostrobin), Trifloxystrobin (Trifloxystrobin), and fenpyroximate (fenpyroximate) of the present invention.
Detailed Description
The following examples are given for the detailed implementation and specific operation of the present invention, but the scope of the present invention is not limited to the following examples.
Example 1
This example prepares Fe as follows3O4@SiO2@C60Nanoparticle:
FIG. 1 is a schematic view of the present embodimentTo obtain Fe3O4@SiO2@C60Scanning electron micrographs of nanoparticles. FIG. 2 shows Fe in this example3O4Nanoparticles, Fe3O4@SiO2Nanoparticles, C60And Fe3O4@SiO2@C60Infrared spectrum of the nanoparticles.
Example 2
This example prepares Fe as follows3O4@SiO2@C60Nanoparticle:
Fe obtained in this example3O4@SiO2@C60The morphology and properties of the nanoparticles are similar to those of example 1.
Example 3 application example
Fe obtained in the above examples3O4@SiO2The @ Cl nano particle can be used as a magnetic dispersion solid phase extraction adsorbent for magnetic dispersion solid phase extraction of methoxy methyl acrylate pesticides in a water sample or a fruit and vegetable sample, and is combined with UHPLC-MS/MS analysis, so that the concentration of the methoxy methyl acrylate pesticides in the water sample or the fruit and vegetable sample to be detected is determined. The method comprises the following specific steps:
The method for extracting the environmental water sample comprises the following steps: sucking 1mL of water sample to be detected into a 15mL pointed-bottom centrifuge tube, adding 9mL of ultrapure water, uniformly mixing, adding 30mg of the magnetic fullerene nano-material obtained in the previous embodiment, and performing oscillation extraction for 20 min; gathering the magnetic fullerene nano-material to the bottom by using a magnet, and pouring all the solution;
the fruit and vegetable sample extraction method comprises the following steps: weighing 2g of fruit and vegetable samples to be detected, putting the fruit and vegetable samples into a 50mL plastic centrifuge tube, adding 20mL acetonitrile, and homogenizing and extracting for 1min at 15000r/min on a high-speed tissue triturator; centrifuging at 10000r/min for 5min, sucking 1mL of supernatant into a 15mL pointed-bottom centrifuge tube, adding 9mL of ultrapure water, mixing uniformly, adding 30mg of the magnetic fullerene nano-material obtained in the previous embodiment, and performing oscillation extraction for 20 min; gathering the magnetic fullerene nano-material to the bottom by using a magnet, and pouring all the solution;
Adding 1mL of ethyl acetate solution into a centrifugal tube in which the magnetic fullerene nano material is positioned, and carrying out desorption by vortex for 1 min; transferring the clear liquid into a new centrifugal tube after magnetic separation by a magnet;
the desorption operation is repeated for 2 times, all desorption solutions are combined and collected in a test tube, and then the magnetic dispersion solid-phase extraction of the methoxy methyl acrylate pesticides in the water sample or the fruit and vegetable sample is completed;
The obtained analytic solution can be used for UHPLC-MS/MS analysis, so that the concentration of the methoxy methyl acrylate pesticide in a water sample to be detected can be determined. The specific conditions are as follows:
(1) the desorption solution was blown dry with nitrogen and then made to volume through a 0.22 μm organic phase filter with 1mL of the initial mobile phase for UHPLC-MS/MS analysis.
(2) Liquid chromatography conditions: a column of ZORBAX Eclipse Plus C18 (2.1 mm. times.50 mm, 1.8 μm); mobile phase: the A phase was 0.05% (V/V) formic acid-water solution, and the B phase was acetonitrile. Flow rate: 0.3 mL/min; column temperature: 40 ℃; the amount of the sample was 10. mu.L.
(3) Gradient elution procedure: 0min, 5% B; 0.3min, 5% B; 2.5min, 40% B; 6.5min, 80% B; 8.5min, 80% B; 8.51min, 5% B; 10min, 5% B.
(4) Mass spectrum conditions: an ion source: electrospray ionization source (ESI), positive ion mode, ion source temperature 300 deg.C, electrospray voltage 4000V, atomizing gas pressure 40psi, drying gas temperature 300 deg.C, drying gas flow rate 10L/min, capillary voltage 3000V. Mrm (multiple interaction monitoring) multiple reaction monitoring mode: the qualitative ion pair, quantitative ion pair, residence time, fragmentation voltage (FP) and collisional gas voltage (CE) are shown in Table 1.
TABLE 14 pesticide multiple reaction monitoring mode (MRM) parameters
In order to verify the sensitivity and accuracy of the method, the magnetic fullerene nano-material obtained in example 1 is used for extraction, elution and detection of the standard solution of azoxystrobin, pyraclostrobin, trifloxystrobin and fenpyroximate with the known concentration of 0.001mg/L according to the method, and the steps are repeated for 6 times, so that the recovery rate of 4 pesticides is higher than 80%, and the indoor precision is lower than 6%. The method comprises the steps of respectively adding 3 levels of azoxystrobin, pyraclostrobin, trifloxystrobin and fenpyroximate pesticides to an apple sample without methoxy methyl acrylate pesticides at 0.01mg/kg, 0.05mg/kg and 0.10mg/kg, carrying out recovery determination, repeating each level for 6 times, extracting, eluting and detecting by using the magnetic fullerene nano-material obtained in the embodiment 1 according to the method, wherein the results are shown in table 2, the recovery rates of 4 pesticides are higher than 60%, the indoor precision is less than 10%, and the detection methodology requirements are met.
Table 24 mean recovery and precision of the pesticides (n ═ 6)
The above description is only for the purpose of illustrating the preferred embodiments of the present invention and is not to be construed as limiting the invention, and any modifications, equivalents and improvements made within the spirit and principle of the present invention are intended to be included within the scope of the present invention.
Claims (10)
1. A preparation method of a magnetic fullerene nano-material is characterized by comprising the following steps: first Fe by tetraethylorthosilicate TEOS3O4Modifying the nano particles to obtain silicon dioxide coated ferroferric oxide superparamagnetic particles, and marking the particles as Fe3O4@SiO2Nanoparticles; then Fe3O4@SiO2The nano particles react with 3-chloropropyltrimethoxysilane to obtain Fe3O4@SiO2@ Cl nanoparticles; finally, the fullerene C is added60Reacting with benzaldehyde and benzylamine to obtain 2, 5-diphenyl fullerene pyrroline, and reacting with Fe3O4@SiO2Reaction of @ Cl nano particles to obtain magnetic fullerene nano material, marked as Fe3O4@SiO2@C60Nanoparticles.
2. The method for preparing a magnetic fullerene nano-material according to claim 1, comprising the following steps:
step 1, adding Fe3O4Dispersing the nanoparticles in isopropanol water solution, ultrasonically dispersing for 15min, introducing nitrogen, transferring to room temperature, and stirring; then adding ammonia water with the mass concentration of 26%, stirring for 5min, adding tetraethyl orthosilicate, heating to 45 ℃, and stirring for 12 h; magnetically separating the product, washing and drying to obtain Fe3O4@SiO2Nanoparticles;
step 2, mixing the Fe3O4@SiO2Dissolving the nanoparticles in toluene, introducing a nitrogen gas chamber, and stirring for 30 min; adding triethylamine and 3-chloropropyltrimethoxysilane, heating to 110 ℃, and continuing to react for 24 hours; cooling to room temperature, magnetically separating the product, washing and drying to obtain Fe3O4@SiO2@ Cl nanoparticles;
step 3, adding C60Adding benzaldehyde and benzylamine into o-dichlorobenzene, and dissolving by ultrasonic waves; then reacting for 6 hours at the temperature of 160 ℃ with stirring; cooling to room temperature, filtering out insoluble impurities through silica gel, and performing rotary evaporation under a vacuum condition until the insoluble impurities are dry; dissolving the obtained residue with carbon disulfide, and eluting with carbon disulfide and toluene through a silica gel column to obtain 2, 5-diphenyl fullerene pyrroline;
step 4, adding Fe3O4@SiO2Dissolving the @ Cl nano particles in toluene, introducing a nitrogen gas chamber, and stirring for 30min at a high temperature; adding triethylamine and 2, 5-diphenyl fullerene pyrroline, continuing to react for 4 hours at room temperature, and then heating to 110 ℃ for reaction for 12 hours; stopping reaction, cooling to room temperature, cleaning and drying to obtain the target product Fe3O4@SiO2@C60Nanoparticles.
3. The method of claim 2, wherein the method comprises the steps of: in step 1 and step 2, Fe3O4The dosage ratio of the nano particles, isopropanol, water, ammonia water, tetraethyl orthosilicate, toluene, triethylamine and 3-chloropropyltrimethoxysilane is 1 g: 100mL of: 8mL of: 10mL of: 8mL of: 100mL of: 1mL of: 2 mL.
4. The method of claim 2The preparation method of the magnetic fullerene nano-material is characterized by comprising the following steps: in step 3, C60The dosage ratio of benzaldehyde, benzylamine and o-dichlorobenzene is 0.5 mmol: 2.5 mmol: 2.5 mmol: 60 mL.
5. The method of claim 2, wherein the method comprises the steps of: in step 4, Fe3O4@SiO2The dosage ratio of the @ Cl nano particles to the toluene to the triethylamine to the 2, 5-diphenyl fullerene pyrroline is 2 g: 80mL of: 1mL of: 1g of the total weight of the composition.
6. A magnetic fullerene nano-material prepared by the preparation method of any one of claims 1 to 5.
7. The use of the magnetic fullerene nano-material of claim 6 in magnetic dispersion solid-phase extraction of methyl methoxyacrylate pesticides.
8. Use according to claim 7, characterized in that: in the magnetic dispersion solid-phase extraction of methoxy methyl acrylate pesticides in a water sample or a fruit and vegetable sample, the magnetic fullerene nano material plays a role as a magnetic dispersion solid-phase extraction adsorbent.
9. The application of the magnetic fullerene nano-material according to claim 7 or 8, wherein when the magnetic fullerene nano-material is used for magnetic dispersion solid phase extraction of methoxy methyl acrylate pesticides in a water sample, the method comprises the following steps:
step 1, extraction
Sucking 1mL of water sample to be detected into a 15mL pointed-bottom centrifuge tube, adding 9mL of ultrapure water, uniformly mixing, adding 30mg of the magnetic fullerene nano material, and performing oscillation extraction for 20 min; gathering the magnetic fullerene nano-material to the bottom by using a magnet, and pouring all the solution;
step 2, elution
Adding 1mL of ethyl acetate solution into a centrifugal tube in which the magnetic fullerene nano material is positioned, and carrying out desorption by vortex for 1 min; transferring the clear liquid into a new centrifugal tube after magnetic separation by a magnet;
the desorption operation is repeated for 2 times, all desorption solution is merged and collected in a test tube, and then the magnetic dispersion solid-phase extraction of the methoxy methyl acrylate pesticide in the water sample is completed;
step 3, detection
The obtained analytic solution can be used for UHPLC-MS/MS analysis, so that the concentration of the methoxy methyl acrylate pesticide in a water sample to be detected can be determined.
10. The application of the magnetic fullerene nano-material in the fruit and vegetable sample as claimed in claim 7 or 8, wherein the application of the magnetic fullerene nano-material in the magnetic dispersion solid phase extraction of methoxy methyl acrylate pesticides in the fruit and vegetable sample comprises the following steps:
step 1, extraction
Weighing 2g of fruit and vegetable samples to be detected, putting the fruit and vegetable samples into a 50mL plastic centrifuge tube, adding 20mL acetonitrile, and homogenizing and extracting for 1min at 15000r/min on a high-speed tissue triturator; centrifuging at 10000r/min for 5min, sucking 1mL of supernatant into a 15mL pointed-bottom centrifuge tube, adding 9mL of ultrapure water, mixing uniformly, adding 30mg of the magnetic fullerene nano material, and performing oscillation extraction for 20 min; gathering the magnetic fullerene nano-material to the bottom by using a magnet, and pouring all the solution;
step 2, elution
Adding 1mL of ethyl acetate solution into a centrifugal tube in which the magnetic fullerene nano material is positioned, and carrying out desorption by vortex for 1 min; transferring the clear liquid into a new centrifugal tube after magnetic separation by a magnet;
the desorption operation is repeated for 2 times, all desorption solutions are combined and collected in a test tube, and then the magnetic dispersion solid-phase extraction of the methoxy methyl acrylate pesticides in the fruit and vegetable samples is completed;
step 3, detection
The obtained analytic solution can be used for UHPLC-MS/MS analysis, so that the concentration of the methoxy methyl acrylate pesticide in a water sample to be detected can be determined.
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Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN116078355A (en) * | 2022-09-09 | 2023-05-09 | 中国地质大学(武汉) | Amphiphilic magnetic nano material and preparation method and application thereof |
Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US20120037840A1 (en) * | 2008-02-25 | 2012-02-16 | Galen Stucky | Use of magnetic nanoparticles to remove environmental contaminants |
CN106215905A (en) * | 2016-09-29 | 2016-12-14 | 安徽出入境检验检疫局检验检疫技术中心 | A kind of preparation method of magnetic fullerene molecule trace nano composite material |
CN106596801A (en) * | 2017-02-20 | 2017-04-26 | 浙江省农业科学院 | Sample purifying adsorbent used for detecting pesticide residues of fruits and vegetables, sample preprocessing method, and pesticide residue detection method |
CN107199012A (en) * | 2017-06-12 | 2017-09-26 | 扬州工业职业技术学院 | A kind of magnetic fullerene nanomaterial and its application in SPE |
US20200101437A1 (en) * | 2018-10-02 | 2020-04-02 | Waters Technologies Corporation | Sorbents, devices, kits and methods useful for sample treatment |
-
2020
- 2020-07-06 CN CN202010640088.9A patent/CN111715198B/en active Active
Patent Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US20120037840A1 (en) * | 2008-02-25 | 2012-02-16 | Galen Stucky | Use of magnetic nanoparticles to remove environmental contaminants |
CN106215905A (en) * | 2016-09-29 | 2016-12-14 | 安徽出入境检验检疫局检验检疫技术中心 | A kind of preparation method of magnetic fullerene molecule trace nano composite material |
CN106596801A (en) * | 2017-02-20 | 2017-04-26 | 浙江省农业科学院 | Sample purifying adsorbent used for detecting pesticide residues of fruits and vegetables, sample preprocessing method, and pesticide residue detection method |
CN107199012A (en) * | 2017-06-12 | 2017-09-26 | 扬州工业职业技术学院 | A kind of magnetic fullerene nanomaterial and its application in SPE |
US20200101437A1 (en) * | 2018-10-02 | 2020-04-02 | Waters Technologies Corporation | Sorbents, devices, kits and methods useful for sample treatment |
Non-Patent Citations (1)
Title |
---|
ZHOU DIAN-BING ET AL.: "Magnetic solid-phase extraction based on [60]fullerene functionalization of magnetic nanoparticles for the determination of sixteen polycyclic aromatic hydrocarbons in tea samples", 《JOURNAL OF CHROMATOGRAPHY A》 * |
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN116078355A (en) * | 2022-09-09 | 2023-05-09 | 中国地质大学(武汉) | Amphiphilic magnetic nano material and preparation method and application thereof |
CN116078355B (en) * | 2022-09-09 | 2024-05-14 | 中国地质大学(武汉) | Amphiphilic magnetic nano material and preparation method and application thereof |
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