CN116216905A - Composition for selectively degrading aniline pollutants as well as preparation method and application thereof - Google Patents

Composition for selectively degrading aniline pollutants as well as preparation method and application thereof Download PDF

Info

Publication number
CN116216905A
CN116216905A CN202310189919.9A CN202310189919A CN116216905A CN 116216905 A CN116216905 A CN 116216905A CN 202310189919 A CN202310189919 A CN 202310189919A CN 116216905 A CN116216905 A CN 116216905A
Authority
CN
China
Prior art keywords
aniline
composition
composite material
selectively degrading
pollutants
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.)
Pending
Application number
CN202310189919.9A
Other languages
Chinese (zh)
Inventor
杨欣
周杨健
邓雁春
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Sun Yat Sen University
Original Assignee
Sun Yat Sen University
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by Sun Yat Sen University filed Critical Sun Yat Sen University
Priority to CN202310189919.9A priority Critical patent/CN116216905A/en
Publication of CN116216905A publication Critical patent/CN116216905A/en
Pending legal-status Critical Current

Links

Images

Classifications

    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/72Treatment of water, waste water, or sewage by oxidation
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/72Treatment of water, waste water, or sewage by oxidation
    • C02F1/76Treatment of water, waste water, or sewage by oxidation with halogens or compounds of halogens
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/38Organic compounds containing nitrogen

Landscapes

  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Removal Of Specific Substances (AREA)

Abstract

The invention belongs to the technical field of wastewater treatment, and discloses a composition for selectively degrading aniline pollutants, a preparation method and application thereof. The composition for selectively degrading aniline pollutants comprises a composite material and an oxidant, wherein the composite material comprises cellulose serving as a carrier and a phenolic compound containing two ortho-phenolic hydroxyl groups and loaded in the carrier, and the oxidant comprises periodate and/or permanganate. The invention can selectively oxidize the phenolic compounds containing two ortho-phenolic hydroxyl groups in the composite material by using the oxidant to generate the quinone active species, wherein the quinone active species is an active species which can selectively react with aniline pollutants with strong nucleophilicity and does not react with water quality matrixes, so that the aniline pollutants in the wastewater can be selectively and efficiently removed; meanwhile, the generated quinone byproducts are loaded in the composite material, so that the recovery is convenient, the toxicity of the wastewater is reduced, the composite material has good stability and strong repeatability, and can be recycled.

Description

Composition for selectively degrading aniline pollutants as well as preparation method and application thereof
Technical Field
The invention belongs to the technical field of wastewater treatment, and particularly relates to a composition for selectively degrading aniline pollutants, a preparation method and application thereof.
Background
Aniline is widely used as an important chemical raw material in the industries of dye, medicine, rubber and the like. With the development of industrial level and the increasing demand of chemicals for humans, the demand of aniline increases, resulting in an increase in the concentration of aniline pollutants in the environment. Aniline pollutants with different concentration levels (ng/L-mug/L) are detected in the water environment at present. The aniline pollutant has the characteristics of wide pollution range, multiple types, long half life and high toxicity, can be subjected to cancerogenic, teratogenic and mutagenic risks after being exposed to the environment for a long time, has bioaccumulation and causes irreversible damage to human health.
Although the advanced oxidation process based on hydroxyl radicals, which is recently developed, can remove aniline pollutants with high efficiency, water quality substrates in wastewater affect the removal effect of aniline pollutants, such as chloride ions, carbonate ions, soluble organic matters and the like, can react with the hydroxyl radicals to consume the concentration of the radicals, thereby inhibiting the degradation of the aniline pollutants. Therefore, how to avoid the influence of water quality matrix in the wastewater and improve the removal effect of aniline pollutants in the wastewater is a technical problem to be solved in the field.
Disclosure of Invention
The present invention aims to solve at least one of the technical problems in the prior art described above. Therefore, the invention provides a composition for selectively degrading aniline pollutants, which has the advantage of strong resistance to water quality substrates and can selectively and efficiently remove aniline pollutants in wastewater.
In a first aspect the invention provides a composition for selectively degrading aniline contaminants, comprising a composite material comprising cellulose as a carrier and a phenolic compound containing two ortho phenolic hydroxyl groups supported in the carrier, and an oxidising agent comprising a periodate and/or a permanganate.
Preferably, the periodate salt comprises at least one of sodium periodate, potassium periodate and lithium periodate.
Preferably, the permanganate comprises at least one of potassium permanganate, sodium permanganate, ammonium permanganate.
Preferably, the phenolic compound containing two ortho-phenolic hydroxyl groups comprises at least one of catechol, 4-methyl catechol and 4-ethyl catechol.
The second aspect of the invention provides a preparation method of the composition for selectively degrading aniline pollutants, which comprises the following steps:
dissolving the phenolic compound containing two ortho-phenolic hydroxyl groups and the cellulose in ionic liquid to obtain a mixed solution;
dropping the mixed solution into water such that the mixed solution forms a pre-composite;
washing the pre-composite material with water and drying to obtain a composite material;
and mixing the composite material with the oxidant to obtain the composition for selectively degrading the aniline pollutants.
Preferably, the preparation method of the composition for selectively degrading aniline pollutants comprises the following steps:
the specific process of dissolution comprises the following steps: adding the phenolic compound containing two ortho-phenolic hydroxyl groups and the cellulose into ionic liquid, and stirring for 1-5h at the temperature of 65-95 ℃.
Preferably, the mass ratio of the phenolic compound containing two ortho-phenolic hydroxyl groups to the cellulose is 1 (0.3-3).
Preferably, the concentration of the phenolic compound containing two ortho-phenolic hydroxyl groups in the ionic liquid is 16-140g/L.
Preferably, the number of water flushes is 3-5.
Preferably, the drying temperature is 20-30 ℃.
Preferably, the ionic liquid is 1-allyl-3-methylimidazole chloride or 1-ethyl-3-methylimidazole acetate.
Preferably, the water is ultrapure water.
The third aspect of the invention provides application of the composition for selectively degrading aniline pollutants in preparation of organic wastewater degradation agents.
According to a fourth aspect of the invention, a method for selectively degrading aniline pollutants in wastewater is provided, the composition for selectively degrading aniline pollutants is put into wastewater, the input amount of the composite material is 10-15g/L, and the input amount of the oxidant is 20-40 mu M.
Compared with the prior art, the invention has the following beneficial effects:
in the composition for selectively degrading aniline pollutants, the oxidant can selectively oxidize phenolic compounds containing two ortho-phenolic hydroxyl groups in the composite material to generate quinone active species, wherein the quinone active species are active species which can selectively react with aniline pollutants with strong nucleophilicity and do not react with water quality matrixes, so that the aniline pollutants in the wastewater can be selectively and efficiently removed; because toxic quinone byproducts are generated by the addition reaction of the quinone active species and the aniline pollutants, the invention adopts a mode of a composite material, so that the generated quinone byproducts are loaded in the composite material, the recovery is convenient, the toxicity of wastewater is reduced, the composite material has good stability and strong repeatability, and the composite material can be recycled.
Drawings
The invention is further described below with reference to the drawings and examples.
FIG. 1 is a physical view of the composite material of example 1;
FIG. 2 is a graph of the degradation of aniline by the composition of example 1 and sodium periodate alone or the composite;
FIG. 3 is a graph of the cyclic effect of the composition of example 1 on aniline degradation;
FIG. 4 is a graph of the degradation of aniline in various bodies of water by the composition of example 1;
fig. 5 is a graph of the degradation of aniline by the composition of example 2 and potassium permanganate alone.
Detailed Description
In order to make the technical solutions of the present invention more apparent to those skilled in the art, the following examples will be presented. It should be noted that the following examples do not limit the scope of the invention.
The starting materials, reagents, apparatus used in the examples below were obtained from conventional commercial sources, unless otherwise specified, or may be obtained by methods known in the art.
Example 1
A composition for selectively degrading aniline contaminants, comprising a composite material and sodium periodate, the composite material comprising cellulose as a carrier and catechol supported in the carrier.
The preparation method of the composition for selectively degrading aniline pollutants comprises the following steps:
(1) 0.5g of alpha-cellulose and 0.5g of catechol are placed in a 50mL brown bottle, 10mL of 1-allyl-3-methylimidazole chloride ionic liquid is added, the mixture is stirred and mixed uniformly by using a rotor, and then the mixed solution is placed in a water bath kettle, heated to 85 ℃ and stirred at constant temperature for 3 hours.
(2) Adding the heated mixed solution into a plastic injector with a specification of 26-G needle, slowly dripping the mixed solution into a 50mL beaker containing ultrapure water at a constant speed by means of external force to prepare a pre-composite material, flushing the pre-composite material with the ultrapure water for 3 times, and drying at 25 ℃ for 24 hours to prepare the composite material (marked as catechol@cellulose microspheres);
(3) The composite material and sodium periodate are mixed to prepare the composition (named sodium periodate/catechol@cellulose microsphere) for selectively degrading aniline pollutants.
As shown in fig. 1, the composite material prepared in this embodiment has regular morphology, uniform particle size, and transparent shape.
Test for degrading aniline pollutants
1. Sodium periodate/catechol@cellulose microspheres degrade aniline in water.
The sodium periodate/catechol@cellulose microspheres provided in example 1, and the degradation effects of the individual sodium periodate, the individual catechol@cellulose microspheres on aniline in 50mL of 5 μm aniline aqueous solution were examined under conditions of ph=7±0.2, solid-to-liquid ratio of catechol@cellulose microspheres to aniline aqueous solution of 10g/L, addition amount of sodium periodate of 20 μm, reaction temperature of 20 ℃, degradation time of 60s, respectively, as shown in fig. 2. As can be seen from fig. 2, when sodium periodate is added alone, the degradation of aniline within 60s is 0; when catechol@cellulose microspheres are independently added, the degradation of aniline within 60 seconds is 0; when sodium periodate/catechol @ cellulose microspheres were added, the aniline was completely degraded after 60s of reaction. The sodium periodate and catechol@cellulose microspheres are combined to efficiently degrade aniline in a water body.
2. And (3) a circulating experiment for degrading aniline in the water body by using sodium periodate/catechol@cellulose microspheres.
Under the conditions that the pH=7+/-0.2, the solid-to-liquid ratio of catechol@cellulose microspheres to an aniline aqueous solution is 10g/L, the adding amount of sodium periodate is 20 mu M, the reaction temperature is 20 ℃, and the degradation time is 60s, the recycling property of the catechol@cellulose microspheres after the sodium periodate/catechol@cellulose microspheres provided in the example 1 are degraded in 150mL of 5 mu M aniline aqueous solution is examined. After each degradation, catechol @ cellulose microspheres were fished out and rinsed 3 times with ultra pure water and dried at room temperature for 24 hours before the next use, as shown in fig. 3. As can be seen from FIG. 3, the experiment of adding sodium periodate and catechol @ cellulose microsphere was repeated 5 times, and after each cycle of reaction for 60 seconds, the aniline was completely degraded. The experiment shows that the catechol@cellulose microsphere has good reusability.
3. Sodium periodate/catechol@cellulose microspheres degrade aniline in an actual water body.
Under the conditions that the solid-to-liquid ratio of catechol@cellulose microspheres to aqueous aniline solution is 10g/L, the adding amount of sodium periodate is 40 mu M, the reaction temperature is 20 ℃, and the degradation time is 60s, the degradation effect of the sodium periodate/catechol@cellulose microspheres provided in example 1 on aniline in 50mL of 5 mu M aniline different actual aqueous solutions (river water, sewage and landfill leachate) is examined, and the water bodies contain chloride ions, carbonate ions, sulfate ions, bromide ions, nitrate ions, soluble organic matters and the like, and ultrapure water is used as a control. As shown in fig. 4. As can be seen from FIG. 4, sodium periodate and catechol@cellulose microspheres are respectively added into river water, sewage and landfill leachate containing aniline, and the aniline can be completely degraded after 60 seconds of reaction. The sodium periodate and catechol@cellulose microspheres can degrade aniline in different actual water bodies with high efficiency, and are not influenced by water quality matrixes basically.
Example 2
A composition for selectively degrading aniline pollutants, comprising a composite material and potassium permanganate, wherein the composite material comprises cellulose serving as a carrier and catechol loaded in the carrier.
The preparation method of the composition for selectively degrading aniline pollutants comprises the following steps:
(1) 0.25g of alpha-cellulose and 0.7g of catechol are placed in a 50mL brown bottle, 5mL of 1-ethyl-3-methylimidazole acetate ionic liquid is added, the mixture is stirred and mixed uniformly by using a rotor, and then the mixed solution is placed in a water bath kettle, heated to 65 ℃ and stirred at constant temperature for 5 hours.
(2) Adding the heated mixed solution into a plastic injector with a specification of 26-G needle, slowly dripping the mixed solution into a 50mL beaker containing ultrapure water at a constant speed by means of external force to prepare a pre-composite material, flushing the pre-composite material with the ultrapure water for 3 times, and drying at 20 ℃ for 24 hours to prepare the composite material (marked as catechol@cellulose microspheres);
(3) The composite material and potassium permanganate are mixed to prepare the composition (marked as potassium permanganate/catechol@cellulose microsphere) for selectively degrading aniline pollutants.
And (3) testing the degradation of the aniline in the water body by the potassium permanganate/catechol@cellulose microspheres.
Under the conditions of ph=7±0.2, solid-to-liquid ratio of catechol@cellulose microspheres to aniline aqueous solution of 10g/L, addition amount of potassium permanganate of 20 μm, reaction temperature of 20 ℃, degradation time of 60s, the potassium permanganate/catechol@cellulose microspheres provided in example 2 and degradation effect of individual potassium permanganate on aniline in 50mL of 5 μm aniline aqueous solution were examined, respectively, as shown in fig. 5. As can be seen from fig. 5, when potassium permanganate was dosed alone, the degradation of aniline within 60s was 0; when potassium permanganate/catechol@cellulose microspheres are added, the aniline is completely degraded after 60s of reaction. The potassium permanganate and catechol@cellulose microspheres can be used for efficiently degrading the aniline in the water body.
Example 3
A composition for selectively degrading aniline contaminants, comprising a composite material and potassium periodate, the composite material comprising cellulose as a carrier and catechol supported in the carrier.
The preparation method of the composition for selectively degrading aniline pollutants comprises the following steps:
(1) 0.7g of alpha-cellulose and 0.25g of catechol are placed in a 50mL brown bottle, 15mL of 1-ethyl-3-methylimidazole acetate ionic liquid is added, the mixture is stirred and mixed uniformly by using a rotor, and then the mixed solution is placed in a water bath kettle, heated to 95 ℃ and stirred at constant temperature for 1 hour.
(2) Adding the heated mixed solution into a plastic injector with a specification of 26-G needle, slowly dripping the mixed solution into a 50mL beaker containing ultrapure water at a constant speed by means of external force to prepare a pre-composite material, flushing the pre-composite material with the ultrapure water for 5 times, and drying at 30 ℃ for 24 hours to prepare the composite material (marked as catechol@cellulose microspheres);
(3) The composite material and potassium periodate are mixed to prepare the composition (marked as potassium periodate/catechol@cellulose microsphere) for selectively degrading aniline pollutants.
Example 4
The difference from example 1 is that example 4 replaces sodium periodate with lithium periodate and the other components and preparation method are the same as example 1. The composition provided in example 4 for selectively degrading aniline contaminants is designated lithium periodate/catechol @ cellulose microspheres.
Example 5
The difference from example 1 is that example 5 replaces sodium periodate with sodium permanganate and the other components and preparation method are the same as example 1. The composition provided in example 5 for selectively degrading aniline contaminants is designated sodium permanganate/catechol @ cellulose microspheres.
Example 6
The difference from example 1 is that example 6 replaces sodium periodate with ammonium permanganate and the other components and preparation method are the same as example 1. The composition provided in example 6 for selectively degrading aniline contaminants is designated ammonium permanganate/catechol @ cellulose microspheres.
Example 7
The difference from example 1 is that example 7 replaces catechol with 4-methylcatechol, and other components and preparation methods are the same as example 1. The composition for selectively degrading aniline contaminants provided in example 7 is designated sodium periodate/4-methylcatechol @ cellulose microsphere.
Example 8
The difference from example 1 is that example 8 replaces catechol with 4-ethyl catechol, and other components and preparation methods are the same as example 1. The composition provided in example 8 for selectively degrading aniline contaminants is designated sodium periodate/4-ethyl catechol @ cellulose microspheres.
Test for degrading aniline pollutants
1. Under the conditions that the pH=7+/-0.2, the solid-to-liquid ratio of the composite material to the aniline aqueous solution is 10g/L, the addition amount of the oxidant is 20 mu M, the reaction temperature is 20 ℃, and the degradation time is 60s, the degradation effect of the composition for selectively degrading the aniline pollutants provided in the examples 3-8 on aniline in 50mL of 5 mu M aniline aqueous solution is examined respectively.
Test results: when the compositions for selectively degrading aniline pollutants provided in examples 3 to 8 are respectively added, the aniline can be completely degraded after 60 seconds of reaction. The composition for selectively degrading aniline pollutants provided by the invention can be used for degrading aniline in water with high efficiency.
2. Under the conditions that the pH=7+/-0.2, the solid-to-liquid ratio of the composite material to the aniline aqueous solution is 10g/L, the addition amount of the oxidant is 20 mu M, the reaction temperature is 20 ℃, and the degradation time is 60s, the recyclability of the composite material provided in the examples 3-8 after the composite material is degraded to aniline in 150mL of 5 mu M aniline aqueous solution is examined respectively. After each degradation, the composite material was fished out and rinsed 3 times with ultrapure water, dried at room temperature for 24 hours and then ready for the next use.
Test results: the addition experiment of the composite material provided in examples 3-8 was repeated 5 times, and after 60s of each cyclic reaction, the aniline was completely degraded. The composite material provided by the invention has good reusability.
3. Under the conditions that the solid-to-liquid ratio of the composite material to the aniline aqueous solution is 15g/L, the addition amount of the oxidant is 40 mu M, the reaction temperature is 20 ℃, and the degradation time is 60s, the degradation effects of the composition for selectively degrading aniline pollutants provided in examples 3-8 on aniline in 50mL of 5 mu M aniline different actual aqueous solutions (river water, sewage and landfill leachate) are examined respectively.
Test results: the composition for selectively degrading the aniline pollutants provided in examples 3-8 is respectively added into river water, sewage and landfill leachate containing aniline, and the aniline can be completely degraded after reacting for 60 seconds. The composition for selectively degrading the aniline pollutants can degrade aniline in different actual water bodies with high efficiency, and is basically not influenced by water quality matrixes.
While the preferred embodiments of the present invention have been illustrated and described, the present invention is not limited to the embodiments, and various equivalent modifications and substitutions can be made by one skilled in the art without departing from the spirit of the present invention, and these are intended to be included in the scope of the present invention as defined in the appended claims.

Claims (10)

1. A composition for selectively degrading aniline contaminants, comprising a composite material comprising cellulose as a carrier and a phenolic compound containing two ortho phenolic hydroxyl groups supported in the carrier, and an oxidizing agent comprising periodate and/or permanganate.
2. The composition for selectively degrading aniline contaminants according to claim 1, wherein the periodate salt includes at least one of sodium periodate, potassium periodate, lithium periodate.
3. The composition for selectively degrading aniline contaminants of claim 1, wherein the permanganate salt includes at least one of potassium permanganate, sodium permanganate, ammonium permanganate.
4. The composition for selectively degrading aniline contaminants according to claim 1, characterized in that the phenolic compound containing two ortho phenolic hydroxyl groups includes at least one of catechol, 4-methyl catechol, 4-ethyl catechol.
5. A method for preparing a composition for selectively degrading aniline contaminants according to any one of claims 1 to 4, comprising the steps of:
dissolving the phenolic compound containing two ortho-phenolic hydroxyl groups and the cellulose in ionic liquid to obtain a mixed solution;
dropping the mixed solution into water such that the mixed solution forms a pre-composite;
washing the pre-composite material with water and drying to obtain a composite material;
and mixing the composite material with the oxidant to obtain the composition for selectively degrading the aniline pollutants.
6. The method of manufacturing according to claim 5, comprising the steps of:
the specific process of dissolution comprises the following steps: adding the phenolic compound containing two ortho-phenolic hydroxyl groups and the cellulose into ionic liquid, and stirring for 1-5h at the temperature of 65-95 ℃.
7. The method according to claim 5, wherein the mass ratio of the phenolic compound containing two ortho-phenolic hydroxyl groups to the cellulose is 1 (0.3-3).
8. The method according to claim 5, wherein the concentration of the phenolic compound containing two ortho-phenolic hydroxyl groups in the ionic liquid is 16-140g/L.
9. Use of a composition for selectively degrading aniline contaminants according to any one of claims 1-4 in the preparation of an organic wastewater degrading agent.
10. A method for selectively degrading aniline pollutants in wastewater, which is characterized in that the composition for selectively degrading aniline pollutants according to any one of claims 1-4 is put into wastewater, the input amount of the composite material is 10-15g/L, and the input amount of the oxidant is 20-40 mu M.
CN202310189919.9A 2023-02-28 2023-02-28 Composition for selectively degrading aniline pollutants as well as preparation method and application thereof Pending CN116216905A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202310189919.9A CN116216905A (en) 2023-02-28 2023-02-28 Composition for selectively degrading aniline pollutants as well as preparation method and application thereof

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202310189919.9A CN116216905A (en) 2023-02-28 2023-02-28 Composition for selectively degrading aniline pollutants as well as preparation method and application thereof

Publications (1)

Publication Number Publication Date
CN116216905A true CN116216905A (en) 2023-06-06

Family

ID=86590727

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202310189919.9A Pending CN116216905A (en) 2023-02-28 2023-02-28 Composition for selectively degrading aniline pollutants as well as preparation method and application thereof

Country Status (1)

Country Link
CN (1) CN116216905A (en)

Citations (12)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH08108185A (en) * 1994-10-14 1996-04-30 Kawasaki Kasei Chem Ltd Production of carrier matter wherein compound having hydroquinone skeleton is supported on porous carrier
CN1954915A (en) * 2005-10-25 2007-05-02 中国科学院化学研究所 Solid phase catalyst assistant and its preparation method and use
CN103936107A (en) * 2014-04-10 2014-07-23 黑龙江大学 2-ethylanthraquinone/activated carbon-expanded graphite composite electrode, and preparation method and application thereof
CN104761043A (en) * 2015-04-23 2015-07-08 河海大学 Method for degrading organic pollutants in water by catalyzing potassium permanganate with quinone compounds
RU2016137617A (en) * 2016-09-20 2018-03-23 Федеральное государственное казенное военное образовательное учреждение высшего образования "Военный учебно-научный центр Военно-воздушных сил "Военно-воздушная академия имени профессора Н.Е. Жуковского и Ю.А. Гагарина" (г. Воронеж) Министерства обороны Российской Федерации The method of concentrating hydroquinone from aqueous solutions
CN110255693A (en) * 2019-07-05 2019-09-20 重庆大学 A kind of method of Native Oxide reduction mediator activation potassium permanganate degradation organic pollutants
CN112898627A (en) * 2021-02-04 2021-06-04 四川大学 Polydopamine/tea polyphenol/cellulose composite photothermal gel and preparation method thereof
CN113287614A (en) * 2021-06-02 2021-08-24 天津大学 Red tide algae algaecide based on natural polyphenol modified nano-cellulose and application thereof
CN114074983A (en) * 2020-08-21 2022-02-22 南京理工大学 Application of hydroformylation bacterial cellulose in activating peroxymonosulfate to degrade pollutants in water
CN114682287A (en) * 2022-04-11 2022-07-01 中山大学 Protonated iron-carbon nitride composite material for advanced wastewater treatment and preparation method and application thereof
CN115340168A (en) * 2022-08-19 2022-11-15 广东工业大学 Method for treating soil leaching waste liquid by using surface polymerization modified activated carbon
CN115427142A (en) * 2019-12-17 2022-12-02 洛桑联邦理工学院(Epfl) Perovskite solar cell provided with adsorbing material for adsorbing toxic substances

Patent Citations (12)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH08108185A (en) * 1994-10-14 1996-04-30 Kawasaki Kasei Chem Ltd Production of carrier matter wherein compound having hydroquinone skeleton is supported on porous carrier
CN1954915A (en) * 2005-10-25 2007-05-02 中国科学院化学研究所 Solid phase catalyst assistant and its preparation method and use
CN103936107A (en) * 2014-04-10 2014-07-23 黑龙江大学 2-ethylanthraquinone/activated carbon-expanded graphite composite electrode, and preparation method and application thereof
CN104761043A (en) * 2015-04-23 2015-07-08 河海大学 Method for degrading organic pollutants in water by catalyzing potassium permanganate with quinone compounds
RU2016137617A (en) * 2016-09-20 2018-03-23 Федеральное государственное казенное военное образовательное учреждение высшего образования "Военный учебно-научный центр Военно-воздушных сил "Военно-воздушная академия имени профессора Н.Е. Жуковского и Ю.А. Гагарина" (г. Воронеж) Министерства обороны Российской Федерации The method of concentrating hydroquinone from aqueous solutions
CN110255693A (en) * 2019-07-05 2019-09-20 重庆大学 A kind of method of Native Oxide reduction mediator activation potassium permanganate degradation organic pollutants
CN115427142A (en) * 2019-12-17 2022-12-02 洛桑联邦理工学院(Epfl) Perovskite solar cell provided with adsorbing material for adsorbing toxic substances
CN114074983A (en) * 2020-08-21 2022-02-22 南京理工大学 Application of hydroformylation bacterial cellulose in activating peroxymonosulfate to degrade pollutants in water
CN112898627A (en) * 2021-02-04 2021-06-04 四川大学 Polydopamine/tea polyphenol/cellulose composite photothermal gel and preparation method thereof
CN113287614A (en) * 2021-06-02 2021-08-24 天津大学 Red tide algae algaecide based on natural polyphenol modified nano-cellulose and application thereof
CN114682287A (en) * 2022-04-11 2022-07-01 中山大学 Protonated iron-carbon nitride composite material for advanced wastewater treatment and preparation method and application thereof
CN115340168A (en) * 2022-08-19 2022-11-15 广东工业大学 Method for treating soil leaching waste liquid by using surface polymerization modified activated carbon

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
SHANSHAN ZHAOA ET AL.: ""Hierarchical Janus membrane with superior fouling and wetting resistance for efficient water recovery from challenging wastewater via membrane distillation"", 《JOURNAL OF MEMBRANE SCIENCE》, 2 September 2021 (2021-09-02), pages 1 - 10 *
廖学品主编: "《天然高分子材料》", vol. 1, 31 January 2022, 四川大学出版社, pages: 376 - 377 *

Similar Documents

Publication Publication Date Title
CN109092329A (en) A kind of method that hollow rich cobalt dual-metal sulfide activation persulfate quickly removes hardly degraded organic substance in waste water
CN110711761A (en) Method for recycling industrial waste salt
CN116216905A (en) Composition for selectively degrading aniline pollutants as well as preparation method and application thereof
CN108404679A (en) A kind of preparation method of decolorizing printing and dyeing waste water film
CN108404942A (en) A kind of fluorine richness Fe3O4Magnetic Nano material and its preparation method and application
CN105504337B (en) A kind of recessed soil/polyaniline/polystyrene compound particle and preparation method thereof
CN105149003B (en) A kind of preparation method and application of chitosan duplex metal complexes catalyst
CN114573834A (en) Enteromorpha hydrogel for rapidly removing pollutants as well as preparation method and application thereof
CN107224974B (en) α-Fe2O3The preparation method and applications of/volcanic rock catalyst
CN110327940A (en) Carbon based material catalyst and its application method and application
CN102728321B (en) Method for preparing adsorbent by using municipal sludge and waste tires
CN107213812B (en) Method for manufacturing stirrer for sewage treatment through 3D printing
CN104860370A (en) Dye wastewater purification method based on surfactant and silver nanoparticles
CN104874369B (en) Modified polyvinyl alcohol microparticles of a kind of coloring functionization and preparation method and application
CN111229170B (en) Amino acid modified cellulose composite ferric oxide adsorbent and preparation method and application thereof
CN104801320B (en) Bismuthyl fluorite photochemical catalyst and preparation method thereof
CN102989509A (en) Catalyst of sulfonated polystyrene grafted polytetrafluoroethylene fiber metal complex and preparation method thereof
CN113101897A (en) Self-regeneration porous carbon sphere composite material and preparation method and application thereof
CN111892154A (en) Method for degrading chlorohydrocarbon by using natural polyphenol activated percarbonate
CN103157449B (en) Composite film and preparation method thereof
CN112934191A (en) Dye adsorbent and preparation method and application thereof
CN105879853B (en) A kind of targeting method for preparing catalyst handling the waste water containing aromatic compound
WO2017095245A1 (en) Method for the production of activated carbon
CN109967027A (en) A kind of novel cation dye sorbent Zn (OH)2/β-Co(OH)2Preparation method
CN108689474A (en) A kind of water treatment agent and method for treating water of the catalyst of di-iron trioxide containing calcium analysis

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