CN111389372A - Special graphene oxide aerogel solid-phase extraction column for perfluorinated acid compounds and preparation method thereof - Google Patents
Special graphene oxide aerogel solid-phase extraction column for perfluorinated acid compounds and preparation method thereof Download PDFInfo
- Publication number
- CN111389372A CN111389372A CN202010410655.1A CN202010410655A CN111389372A CN 111389372 A CN111389372 A CN 111389372A CN 202010410655 A CN202010410655 A CN 202010410655A CN 111389372 A CN111389372 A CN 111389372A
- Authority
- CN
- China
- Prior art keywords
- graphene oxide
- phase extraction
- solid
- extraction column
- oxide aerogel
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Granted
Links
Images
Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/22—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising organic material
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D15/00—Separating processes involving the treatment of liquids with solid sorbents; Apparatus therefor
- B01D15/08—Selective adsorption, e.g. chromatography
- B01D15/10—Selective adsorption, e.g. chromatography characterised by constructional or operational features
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/28—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties
- B01J20/28014—Solid 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
- B01J20/28047—Gels
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/28—Treatment of water, waste water, or sewage by sorption
- C02F1/285—Treatment of water, waste water, or sewage by sorption using synthetic organic sorbents
-
- G—PHYSICS
- G01—MEASURING; TESTING
- G01N—INVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
- G01N30/00—Investigating or analysing materials by separation into components using adsorption, absorption or similar phenomena or using ion-exchange, e.g. chromatography or field flow fractionation
- G01N30/02—Column chromatography
- G01N30/04—Preparation or injection of sample to be analysed
- G01N30/06—Preparation
- G01N30/08—Preparation using an enricher
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/30—Organic compounds
- C02F2101/36—Organic compounds containing halogen
-
- G—PHYSICS
- G01—MEASURING; TESTING
- G01N—INVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
- G01N30/00—Investigating or analysing materials by separation into components using adsorption, absorption or similar phenomena or using ion-exchange, e.g. chromatography or field flow fractionation
- G01N30/02—Column chromatography
- G01N30/04—Preparation or injection of sample to be analysed
- G01N30/06—Preparation
- G01N30/08—Preparation using an enricher
- G01N2030/085—Preparation using an enricher using absorbing precolumn
Landscapes
- Chemical & Material Sciences (AREA)
- Analytical Chemistry (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Organic Chemistry (AREA)
- Life Sciences & Earth Sciences (AREA)
- Water Supply & Treatment (AREA)
- Biochemistry (AREA)
- Engineering & Computer Science (AREA)
- Hydrology & Water Resources (AREA)
- Dispersion Chemistry (AREA)
- Physics & Mathematics (AREA)
- Health & Medical Sciences (AREA)
- Environmental & Geological Engineering (AREA)
- General Health & Medical Sciences (AREA)
- General Physics & Mathematics (AREA)
- Immunology (AREA)
- Pathology (AREA)
- Solid-Sorbent Or Filter-Aiding Compositions (AREA)
- Organic Low-Molecular-Weight Compounds And Preparation Thereof (AREA)
Abstract
The invention relates to a special graphene oxide aerogel solid-phase extraction column for a perfluorinated acid compound and a preparation method thereof. The solid-phase extraction column adopts graphene oxide aerogel, and the preparation method comprises the steps of firstly obtaining graphene oxide, then obtaining aminated graphene oxide hydrogel, then preparing aminated graphene oxide aerogel, and finally preparing the solid-phase extraction column. The graphene oxide aerogel prepared by the method does not need other polymer supporting materials, has excellent adsorption performance, can adsorb more perfluorinated acid compounds, has higher adsorption capacity and good adsorption effect, can quickly absorb target substances, and enables the detection to be more sensitive and quicker.
Description
Technical Field
The invention relates to the technical field of solid-phase extraction, in particular to a special graphene oxide aerogel solid-phase extraction material for a perfluorinated acid compound and a preparation method thereof.
Background
Solid Phase Extraction (SPE) is a sample pretreatment technology developed from the middle of the 80 th century, and is established on the basis of traditional liquid-liquid extraction, and is gradually developed by combining a similar phase solution principle of substance interaction and stationary phase basic knowledge in HP L C/GC widely applied at present, wherein SPE is mainly used for treating liquid samples, extracting, concentrating and purifying semi-volatile and non-volatile compounds in the liquid samples, and mainly aims at reducing sample matrix interference and improving detection sensitivity, and SPE can also be applied to solid samples, but must be firstly processed into liquid.
Perfluoro compounds (PFCs) represented by perfluorooctane carboxylic acid (PFOA) and perfluorooctane sulfonic acid (PFOS) are widely used in consumer goods for daily use and industrial production, and can enter the environment in large quantities through various routes, and the presence of PFCs has been widely detected in various environmental media and organisms around the world.
At present, PFCs distribution and fate research in water environment mainly aims at PFOS, PFOA and long-chain homologues thereof. With the disablement of PFOS and PFOA, a series of short chain homologs have entered the production and application areas, and eventually the environment, as substitutes. However, the traditional AAO process in the existing municipal sewage treatment plant has low removal efficiency of the pollutants, so that the perfluoroalkyl carboxylic acid is accumulated in the water environment, thereby becoming a difficult point for controlling water pollution.
Disclosure of Invention
In order to solve the technical problems in the background art, the invention provides a special graphene oxide aerogel solid-phase extraction column for a perfluorinated acid compound and a preparation method thereof. The adsorbent obtained by the method can effectively enrich the perfluoroalkyl carboxylic acid in the water body; has the advantages of high adsorption efficiency and easy separation.
The core of the graphene oxide aerogel solid-phase extraction column is that the graphene oxide aerogel solid-phase extraction column comprises aminated graphene oxide aerogel.
The preparation method of the graphene oxide aerogel solid-phase extraction column comprises the following four steps, wherein in the first step, graphene oxide is prepared; secondly, preparing aminated graphene oxide hydrogel; step three, preparing aminated graphene oxide aerogel; and fourthly, preparing a solid phase extraction column. The method is represented as the attached figure 1 by adopting a flow chart, and comprises the following specific steps:
step one, preparing graphene oxide: natural graphite is used as a raw material, an improved Hummers method is adopted for synthesis, and graphene oxide is prepared through the stages of feeding, low-temperature reaction, medium-temperature reaction, high-temperature reaction, washing and drying;
step two, preparing an aminated graphene oxide hydrogel: carrying out ultrasonic dispersion on the graphene oxide obtained in the first step to obtain a first dispersion liquid; adding a diethylenetriamine solution into the dispersion liquid and stirring to obtain a second dispersion liquid; adding N, N-methylene bisacrylamide and ammonium persulfate into the second dispersion liquid, and then carrying out hydrothermal reaction; after the reaction is finished, cooling to room temperature to obtain aminated graphene oxide hydrogel;
step three, preparing an aminated graphene oxide aerogel: soaking the aminated graphene oxide hydrogel obtained in the second step in ethanol, and freeze-drying the obtained solid product to obtain aminated graphene oxide aerogel;
and fourthly, loading the aminated graphene oxide aerogel obtained in the third step into a separation column, adding a proper amount of quartz sand or silica gel as a supporting agent, placing the separation column on a shaking table for shaking, and compacting the aminated graphene oxide aerogel to obtain the solid-phase extraction column.
Further, in the above technical solution, in the second step, the volume fraction of diethylenetriamine is 0.45%;
further, in the above technical solution, in the second step, every 10m L solution contains 7.5mg of N, N-methylenebisacrylamide (BIS for short) and 30mg of ammonium persulfate (APS for short).
Further, in the above technical scheme, in the second step, the second mixed dispersion solution is placed in a water bath kettle at 95 ℃ for 24 hours in a water bath to prepare the aminated graphene oxide hydrogel;
further, in the above technical scheme, in the third step, the prepared aminated graphene oxide hydrogel is soaked in a 20% ethanol solution for 6 hours;
further, in the above technical scheme, in the third step, after freezing the hydrogel, freeze-drying the hydrogel by using a freeze dryer to obtain the aminated graphene oxide aerogel, wherein during freeze-drying, the freeze dryer maintains a vacuum degree of less than 10Pa, and the freeze-drying treatment is carried out for 24-48 h.
The graphene oxide aerogel solid-phase extraction column prepared by the method is applied to extraction of the perfluoroacid compound.
Further, in the above technical solution, the perfluoro acid compound is selected from perfluorooctane carboxylic acid (PFOA) or perfluorooctane sulfonic acid (PFOS).
Advantageous effects of the invention
The material synthesized by the method can be applied to high-efficiency enrichment and determination of perfluoroacid compounds (two typical PFOA and PFOS in the perfluoroacid compounds are listed in the US water quality standard in 2020), and is beneficial to improving the enrichment efficiency by more than 3 times and improving the lower detection limit. For a high-concentration water sample, the enrichment efficiency of the method is higher than that of the conventional solid-phase extraction column by more than 50%.
Drawings
FIG. 1: preparation process of aminated graphene oxide gel
FIG. 2: amination graphene oxide solid phase extraction column (the invention photo)
FIG. 3: adsorption curves of different EDA-GO dosages for PFOS with same concentration
FIG. 4: adsorption isotherm of EDA-GO gel for PFOS at different temperatures
FIG. 5: adsorption of PFOA by EDA-GO gel
Detailed Description
EXAMPLE 1 preparation of solid phase extraction column
Step one, preparing graphene oxide:
the feeding stage is that a water bath is prepared, 110m L concentrated sulfuric acid is accurately measured and placed in a 500m L three-mouth round bottom flask, ice bath is carried out for 15min, the temperature is controlled to be-5-0 ℃, then 5g of natural graphite and 2.5g of sodium nitrate are slowly added into the concentrated sulfuric acid (in the feeding process, a weighing paper roll is plugged in the rightmost mouth of the three-mouth flask, so that the added graphite can be completely added into the concentrated sulfuric acid, the graphite is prevented from being stuck on the wall of the flask and can not completely react with the concentrated sulfuric acid), and after stirring for 30min under the ice bath, 15g of potassium permanganate is slowly added (necessarily slowly and uniformly added).
And (3) low-temperature stage: after the reagents were added, the apparatus was stirred at 5-10 ℃ for 2 h.
A medium temperature stage: the device is transferred to a water bath with the temperature of 35-40 ℃ for reaction, and the reaction is continuously stirred for 2.5-4h (when the temperature is moderate, the rotation speed can be adjusted to be faster, so that the oxidizing agent and the graphite are oxidized more uniformly) until the solution becomes yellowish-brown viscous solution and finally becomes pasty and can not be stirred. (the low-temperature reaction and the medium-temperature reaction show dark green color, and concentrated sulfuric acid molecules are mainly inserted between the graphite in the two reaction stages to carry out primary oxidation on the graphite together with potassium permanganate)
And a high-temperature stage, namely preparing a water bath after the medium-temperature reaction, transferring the device into the water bath until the temperature is reduced to 30 ℃, adding 230m L of water, slowly adding the first-stage water, controlling the temperature to be below 70 ℃ in the water adding process, putting the device into a water bath again after the water is added, and carrying out the medium-temperature reaction for 15min at the temperature of 95 ℃.
Washing and drying: after the high-temperature reaction, the device is transferred to the room temperature, the temperature is reduced to 40 ℃, 30% hydrogen peroxide is added, the reaction is stopped after stirring for 15min, and at the moment, the solution turns from earthy yellow to golden yellow. Then, the solution is centrifuged at 40000 rpm for 5 minutes, washed 3 times with 7% hydrochloric acid to remove metal ions in the solution and remove sulfate ions and permanganate ions. The pH 7(10000 rpm) was then washed with additional water. And (5) putting the obtained product into a vacuum drying oven for drying.
Secondly, preparing aminated graphene oxide hydrogel, namely adding the graphene oxide obtained in the first step into deionized water, performing ultrasonic dispersion for 1 hour until no particulate matter exists, adding a diethylenetriamine solution, stirring for 10 minutes, wherein the volume fraction of diethylenetriamine is 0.45% to prepare an aminated graphene oxide aqueous solution, adding N, N-methylene Bisacrylamide (BIS) and Ammonium Persulfate (APS) into the aminated graphene oxide aqueous solution, stirring for 5 minutes, controlling the BIS to be 7.5mg and the APS to be 30mg in every 10m L solution to prepare a second mixed dispersion solution, putting the second mixed dispersion solution into a water bath kettle at 95 ℃, and performing water bath for 24 hours to prepare the aminated graphene oxide hydrogel;
step three, soaking the aminated graphene oxide hydrogel obtained in the step two in a 20% ethanol solution for 6 hours; and then carrying out freeze drying by a freeze dryer to obtain the aminated graphene oxide aerogel, wherein during freeze drying, the freeze dryer keeps the vacuum degree below 10Pa, and the aminated graphene oxide aerogel is obtained after freeze drying treatment for 24-48 h.
And fourthly, loading the aminated graphene oxide aerogel obtained in the third step into a separation column (the separation column consists of a column tube, a sintering pad and an aminated graphene oxide stationary phase), adding a proper amount of quartz sand or silica gel as a propping agent (the ratio is 1: 0.5-2), loading the aminated graphene oxide aerogel into the separation column, placing the separation column on a shaking table for shaking for 3min, and compacting the aminated graphene oxide aerogel to obtain the solid-phase extraction column. The material object is shown in figure 2.
Example 2: adsorption of PFOS
Preparing 600 mg/L PFOS solution, weighing 1-10 mg of aminated graphene oxide aerogel obtained in the third step in embodiment 1, adsorbing at 25 ℃ and 140r/min for 12h, wherein the adsorption capacity is 3702mg/g at most, the maximum removal rate is 97%, which is much higher than the adsorption capacity (1208mg/g) of the traditional activated carbon material, the adsorption effect is shown in figure 3, the adsorption isotherm of the EDA-GO gel on PFOS at different temperatures can show that the maximum adsorption capacity of the material is 3500mg/g, which is much higher than the adsorption capacity of the activated carbon material 263mg/g, and the adsorption isotherm is shown in figure 4.
Example 3: adsorption of PFOA
Preparing 10, 100 and 1000 mg/L PFOA solution, weighing 1mg of aminated graphene oxide aerogel obtained in the third step in the embodiment 1, adsorbing at 25 ℃ and 140r/min for 12 hours, wherein the maximum adsorption capacity is 1560mg/g, the maximum removal rate is 99.95%, the adsorption capacity is much higher than that of the traditional activated carbon material (277-434.8 mg/g), and the adsorption effect is shown in figure 5.
Example 4: perfluorocompound analysis experiment using the solid phase extraction column of example 1
Activation- -removing impurities in the small column and creating a certain solvent environment, firstly adding 5-10m L methanol for activation, and adding 5m L pure water for rinsing when the filtration is nearly finished, wherein the flow rate is 1 ml/min.
And (2) sample loading, namely dissolving the sample with a certain solvent, transferring the sample into the column and keeping the components on the column, wherein the flow rate is preferably 0.5-1m L/min and is not more than 5m L/min at most, and 5% of methanol is added into the sample to be beneficial to keeping the sample on the column.
Leaching- -to remove water-soluble interferents to the maximum extent. After the process is finished, the small column is completely drained for more than 15-30 minutes, and 20% methanol aqueous solution is used for the experiment, preferably 1 ml/min.
Elution- -the material to be tested is eluted off with a small volume of solvent and collected at a flow rate of preferably 0.5-1m L/min, eluting with 5ml of methanol.
An Agilent1200-TOF6224 liquid chromatography-mass spectrometer (HP L C-MS) is adopted, a chromatographic column is eclipsePlus C18(150 × 4.6.6 mm, 3.5 mu m), a mobile phase is V (acetonitrile), V (water) is 95: 5, the flow rate is 0.5m L/min, the ionization mode is APCI (negative), the scanning time is 50min, the atomizer pressure (NEB) is 30psig, the drying gas flow rate is 12.0L/min, the drying gas Temperature (TEMP) is 350 ℃, and the capillary voltage is 4000V.
The extraction experiment is carried out for 3 times in parallel, the sample recovery rate is 70-97%, the specific experiment result is shown in table 1, and the result shows that the solid phase extraction column is suitable for enrichment analysis of the perfluoroacid compound and is superior to the extraction effect of the traditional C18 and H L B solid phase extraction columns.
TABLE 1 comparison of recovery of the present invention with conventional solid phase extraction column (unit:%)
The foregoing embodiments have described the general principles, principal features and advantages of the invention. It will be understood by those skilled in the art that the present invention is not limited to the embodiments described above, which are merely illustrative of the principles of the present invention, and that various changes and modifications may be made without departing from the scope of the principles of the present invention, and the invention is intended to be covered by the appended claims.
Claims (8)
1. Graphite oxide aerogel solid-phase extraction post, its characterized in that: including aminated graphene oxide aerogels.
2. The preparation method of the graphene oxide aerogel solid-phase extraction column according to claim 1, which comprises the following steps:
step one, preparing graphene oxide: natural graphite is used as a raw material, an improved Hummers method is adopted for synthesis, and graphene oxide is prepared through the stages of feeding, low-temperature reaction, medium-temperature reaction, high-temperature reaction, washing and drying;
step two, preparing an aminated graphene oxide hydrogel: carrying out ultrasonic dispersion on the graphene oxide obtained in the first step to obtain a first dispersion liquid; adding a diethylenetriamine solution into the dispersion liquid and stirring to obtain a second dispersion liquid; adding N, N-methylene bisacrylamide and ammonium persulfate into the second dispersion liquid, and then carrying out hydrothermal reaction; after the reaction is finished, cooling to room temperature to obtain aminated graphene oxide hydrogel;
step three, preparing an aminated graphene oxide aerogel: soaking the aminated graphene oxide hydrogel obtained in the second step in ethanol, and freeze-drying the obtained solid product to obtain aminated graphene oxide aerogel;
and fourthly, loading the aminated graphene oxide aerogel obtained in the third step into a separation column, adding a proper amount of quartz sand or silica gel as a supporting agent, placing the separation column on a shaking table for shaking, and compacting the aminated graphene oxide aerogel to obtain the solid-phase extraction column.
3. The method of manufacturing a solid phase extraction column according to claim 2, wherein: in the second step, the volume fraction of diethylenetriamine was 0.45%.
4. The method of claim 2, wherein in the second step, the amount of BIS is 7.5mg and the amount of APS is 30mg per 10m of L solutions.
5. The method of manufacturing a solid phase extraction column according to claim 2, wherein: in the second step, the hydrothermal reaction temperature was 95 ℃.
6. The method of manufacturing a solid phase extraction column according to claim 2, wherein: in the fourth step, the ratio of quartz sand or silica gel as a propping agent to aminated graphene oxide aerogel is 1: 0.5 to 2.
7. The application of the graphene oxide aerogel solid-phase extraction column of claim 1 in extracting perfluoroacid compounds.
8. The application of the graphene oxide aerogel solid-phase extraction column according to claim 7 in extraction of perfluoroacid compounds is characterized in that: the perfluoro acid compound is selected from perfluorooctane carboxylic acid or perfluorooctane sulfonic acid.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN202010410655.1A CN111389372B (en) | 2020-05-15 | 2020-05-15 | Special graphene oxide aerogel solid-phase extraction column for perfluorinated acid compounds and preparation method thereof |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN202010410655.1A CN111389372B (en) | 2020-05-15 | 2020-05-15 | Special graphene oxide aerogel solid-phase extraction column for perfluorinated acid compounds and preparation method thereof |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| CN111389372A true CN111389372A (en) | 2020-07-10 |
| CN111389372B CN111389372B (en) | 2023-03-24 |
Family
ID=71418663
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN202010410655.1A Active CN111389372B (en) | 2020-05-15 | 2020-05-15 | Special graphene oxide aerogel solid-phase extraction column for perfluorinated acid compounds and preparation method thereof |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN111389372B (en) |
Cited By (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN112033786A (en) * | 2020-08-19 | 2020-12-04 | 深圳市环境科学研究院 | Solid-phase extraction method for perfluorinated compounds in environmental water |
| CN112229938A (en) * | 2020-11-13 | 2021-01-15 | 上海市农业科学院 | Solid phase extraction column for detecting perfluorinated compounds and manufacturing method and application thereof |
| CN114832777A (en) * | 2022-05-11 | 2022-08-02 | 浙江大学 | Modification method for removing perfluorocarboxylic acid in water by using enhanced activated carbon and prepared modified activated carbon |
Citations (6)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN102910625A (en) * | 2012-11-14 | 2013-02-06 | 北京理工大学 | Graphene oxide aerogel, preparation method and application |
| CN104258598A (en) * | 2014-09-25 | 2015-01-07 | 深圳粤网节能技术服务有限公司 | Solid phase extraction column and preparation method thereof as well as chemical sample pretreatment method based on solid phase extraction column |
| CN104558998A (en) * | 2015-01-28 | 2015-04-29 | 云南中烟工业有限责任公司 | Graphene-polymer composite aerogel filter tip high-efficient adsorption stick and preparation method thereof |
| WO2016045030A1 (en) * | 2014-09-25 | 2016-03-31 | 深圳粤网节能技术服务有限公司 | Graphene material-based dispersive solid phase extraction method |
| CN108499549A (en) * | 2018-03-30 | 2018-09-07 | 广州质量监督检测研究院 | Solid phase micro-extracting head and preparation method thereof for being enriched with perfluorochemical |
| CN110790856A (en) * | 2019-11-14 | 2020-02-14 | 淄博宏达助剂有限公司 | Graphene oxide/polyacrylic acid composite hydrogel and preparation method thereof |
-
2020
- 2020-05-15 CN CN202010410655.1A patent/CN111389372B/en active Active
Patent Citations (6)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN102910625A (en) * | 2012-11-14 | 2013-02-06 | 北京理工大学 | Graphene oxide aerogel, preparation method and application |
| CN104258598A (en) * | 2014-09-25 | 2015-01-07 | 深圳粤网节能技术服务有限公司 | Solid phase extraction column and preparation method thereof as well as chemical sample pretreatment method based on solid phase extraction column |
| WO2016045030A1 (en) * | 2014-09-25 | 2016-03-31 | 深圳粤网节能技术服务有限公司 | Graphene material-based dispersive solid phase extraction method |
| CN104558998A (en) * | 2015-01-28 | 2015-04-29 | 云南中烟工业有限责任公司 | Graphene-polymer composite aerogel filter tip high-efficient adsorption stick and preparation method thereof |
| CN108499549A (en) * | 2018-03-30 | 2018-09-07 | 广州质量监督检测研究院 | Solid phase micro-extracting head and preparation method thereof for being enriched with perfluorochemical |
| CN110790856A (en) * | 2019-11-14 | 2020-02-14 | 淄博宏达助剂有限公司 | Graphene oxide/polyacrylic acid composite hydrogel and preparation method thereof |
Cited By (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN112033786A (en) * | 2020-08-19 | 2020-12-04 | 深圳市环境科学研究院 | Solid-phase extraction method for perfluorinated compounds in environmental water |
| CN112229938A (en) * | 2020-11-13 | 2021-01-15 | 上海市农业科学院 | Solid phase extraction column for detecting perfluorinated compounds and manufacturing method and application thereof |
| CN114832777A (en) * | 2022-05-11 | 2022-08-02 | 浙江大学 | Modification method for removing perfluorocarboxylic acid in water by using enhanced activated carbon and prepared modified activated carbon |
Also Published As
| Publication number | Publication date |
|---|---|
| CN111389372B (en) | 2023-03-24 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| CN111389372B (en) | Special graphene oxide aerogel solid-phase extraction column for perfluorinated acid compounds and preparation method thereof | |
| Say et al. | Preconcentration of copper on ion-selective imprinted polymer microbeads | |
| Savio et al. | On-line solid phase extraction of Ni and Pb using carbon nanotubes and modified carbon nanotubes coupled to ETAAS | |
| Zhao et al. | Modification of garlic peel by nitric acid and its application as a novel adsorbent for solid-phase extraction of quinolone antibiotics | |
| CN109884147B (en) | Electrochemical method for detecting trace heavy metals by using walnut shell-based carbon material modified glassy carbon electrode | |
| Huang et al. | Preparation and application of ionic liquid-coated fused-silica capillary fibers for solid-phase microextraction | |
| CN104437415A (en) | Modified-chitosan and graphite oxide magnetic nano absorbent and preparation and application thereof | |
| Wang et al. | Carboxylated carbon nanospheres as solid-phase extraction adsorbents for the determination of perfluorinated compounds in water samples by liquid chromatography–tandem mass spectrometry | |
| CN106044953A (en) | Preparation method of nitrogen-doped porous carbon rod capacitance desalting electrode | |
| Saeidi et al. | Controlling adsorption of perfluoroalkyl acids on activated carbon felt by means of electrical potentials | |
| CN109999909A (en) | Chitosan/diatomite/graphene oxide composite material and its preparation method and application | |
| CN103642063A (en) | Preparation method of mythyl p-hydroxybenzoate molecular imprinting composite membrane and application thereof | |
| CN111672474A (en) | Magnetic nitrogen-doped carbon oxide nanotube material and preparation method and application thereof | |
| Xu et al. | Designed 3D N-doped magnetic porous carbon spheres for sensitive monitoring of biogenic amine by simultaneous microwave-assisted derivatization and magnetic-solid phase extraction | |
| CN104258827B (en) | Magnetic mesoporous carbon of Polyaniline-modified and its preparation method and application | |
| CN109289771A (en) | The preparation method of high-efficiency mercury removal adsorbent | |
| CN110498887B (en) | Method for preparing diclofenac sodium surface molecularly imprinted polymer in water phase by taking ZIF-67 as carrier | |
| CN112295552B (en) | Hierarchical pore UiO-66 solid-phase micro-extraction fiber prepared by in-situ etching method and application thereof | |
| Escudero et al. | An eco-friendly cellular phase microextraction technique based on the use of green microalgal cells for trace thallium species determination in natural water samples | |
| CN109304105B (en) | Forward osmosis membrane for efficiently adsorbing and removing heavy metal ions and preparation method and application thereof | |
| CN109678140A (en) | A kind of green modified carbon nano tube material and its preparation method and application | |
| CN111440354B (en) | Preparation method and application of bisphenol A molecularly imprinted composite membrane with through hierarchical pore structure | |
| Denizli et al. | Synthesis and adsorption properties of poly (2-hydroxyethylmethacrylate-co-methacrylamidophenylalanine) membranes for copper ions | |
| Huang et al. | A study on the electrochemical behavior of hydroquinone at a nanometer cobalt/l-glutamate-modified electrode | |
| CN112915982B (en) | Synthetic method and application of cobalt-containing polymer uranyl ion adsorbent |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| PB01 | Publication | ||
| PB01 | Publication | ||
| SE01 | Entry into force of request for substantive examination | ||
| SE01 | Entry into force of request for substantive examination | ||
| GR01 | Patent grant | ||
| GR01 | Patent grant |