CN112340842A - Preparation method of denitrification solid carbon source - Google Patents

Preparation method of denitrification solid carbon source Download PDF

Info

Publication number
CN112340842A
CN112340842A CN202011072564.8A CN202011072564A CN112340842A CN 112340842 A CN112340842 A CN 112340842A CN 202011072564 A CN202011072564 A CN 202011072564A CN 112340842 A CN112340842 A CN 112340842A
Authority
CN
China
Prior art keywords
graphene oxide
oxide nano
mixture
poly
polylactic acid
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
CN202011072564.8A
Other languages
Chinese (zh)
Inventor
王国瑞
周继柱
孙松厚
朱希坤
石伟杰
冯春晖
马凯
崔秀菊
杨铁军
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.)
Shenmei Technology Co Ltd
Original Assignee
Shenmei Technology Co Ltd
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 Shenmei Technology Co Ltd filed Critical Shenmei Technology Co Ltd
Priority to CN202011072564.8A priority Critical patent/CN112340842A/en
Publication of CN112340842A publication Critical patent/CN112340842A/en
Pending legal-status Critical Current

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/28Anaerobic digestion processes
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2305/00Use of specific compounds during water treatment
    • C02F2305/06Nutrients for stimulating the growth of microorganisms

Landscapes

  • Life Sciences & Earth Sciences (AREA)
  • Microbiology (AREA)
  • Biodiversity & Conservation Biology (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Carbon And Carbon Compounds (AREA)

Abstract

The invention discloses a preparation method of a denitrification solid carbon source, which comprises the following steps: (1) preparing modified polylactic acid; (2) preparing a graphene oxide nano roll modified by poly (diallyldimethylammonium chloride); (3) mixing the obtained modified polylactic acid and a polymer according to the mass ratio of 1: (1-2) and uniformly stirring to obtain a mixed solution, and then mixing the mixed solution, an adhesive and the poly (diallyldimethylammonium chloride) -modified graphene oxide nano roll according to a mass ratio of 4: 2: 1 in THF, stirring the mixture at room temperature for 2-4 hours under the protection of argon, centrifuging the mixture, washing the mixture with THF, and finally performing heat treatment under the protection of argon to obtain a final product. The solid carbon source of the invention releases COD mildly, has long duration and moderate dosage.

Description

Preparation method of denitrification solid carbon source
Technical Field
The invention belongs to the technical field of sewage treatment, and particularly relates to a preparation method of a denitrification solid carbon source.
Background
Research shows that insufficient carbon source supplement or unstable supply becomes an important factor for restricting biological denitrification efficiency, and sufficient carbon source can provide sufficient nutrient source for growth and metabolism of microorganisms. Therefore, the solution of the problem of low denitrification efficiency by adding carbon source is becoming a hot point of research in the field of water treatment.
As known from research reports on carbon source supplement, liquid carbon sources such as short-chain organic carbon such as methanol, ethanol, glucose and the like are mainly mature and most widely used, but the problems of high cost, toxicity, uncertain dosage, difficult transportation and the like also lead researchers to start to search and try for additional carbon sources. The hot spots mostly concentrate on how to optimize the traditional carbon source, such as adding a hydrolysis acidification process before a denitrification process, so as to improve the biodegradability and treatment rate of the raw sewage; developing non-traditional carbon sources as carbon sources which can be selected in the denitrification process, such as industrial wastewater, primary sludge hydrolysate, landfill leachate, plant straws and the like. However, these carbon sources have problems such as difficulty in controlling the amount of supply and insufficient supply at the early stage, which affect the metabolism of the microorganism and further the effect of the treatment.
Graphene is a compound represented by sp2The two-dimensional nano material composed of hybridized carbon atoms has a hexagonal honeycomb structure, and has excellent performance and wide application prospect. Materials such as graphene sheets, graphene fibers, graphene hydrogel or aerogel, graphene nanocoils and the like can be prepared by various methods at present. The graphene oxide nano roll composite material is formed by wrapping other nano substances with two-dimensional graphene oxide nano sheets and curling, and is a carbon nano material with an open structure. At present, the graphene oxide nano roll is mainly applied to the aspects of energy conversion and storage, electronic devices, quantum transportation, flexible materials, optical devices, catalysis, aerospace and the like, and few literature reports are used in the denitrification process of sewage treatment.
According to the invention, the graphene oxide nano roll is used as a carrier matrix, and a carbon source is loaded on the surface of the graphene oxide nano roll, so that on one hand, more carbon sources can be loaded due to the larger interface area of the graphene oxide nano roll, and on the other hand, the graphene oxide nano roll has good mechanical properties, so that the stability in the denitrification process can be ensured, and a sufficient and stable carbon source can be provided for flora.
Disclosure of Invention
The invention mainly aims to provide a preparation method of a denitrification solid carbon source. According to the invention, the graphene oxide nano roll is used as a carrier matrix, and a carbon source material is loaded on the surface of the graphene oxide nano roll, so that an adequate and stable carbon source is provided for flora.
The purpose of the invention and the technical problem to be solved are realized by adopting the following technical scheme.
The invention provides a preparation method of a denitrification solid carbon source, which comprises the following steps:
(1) dissolving polylactic acid in an organic solvent, then dropwise adding a strong oxidant solution, carrying out oxidation pretreatment at the temperature of not higher than 60 ℃, and then adjusting the pH of the solution to 6-8 to obtain modified polylactic acid;
(2) uniformly dispersing graphene oxide nanosheets in deionized water, heating the obtained graphene oxide dispersion liquid in a water bath, quickly immersing the graphene oxide dispersion liquid in liquid nitrogen until the graphene oxide dispersion liquid is completely frozen, finally, obtaining graphene nano rolls through freeze drying, carrying out ultrasonic treatment on the graphene oxide nano rolls in 100ml of aqueous solution containing 1 wt% of poly (diallyldimethylammonium chloride) for 2-4 hours, filtering and carrying out vacuum drying to obtain poly (diallyldimethylammonium chloride) -modified graphene oxide nano rolls;
(3) mixing the obtained modified polylactic acid and a polymer according to the mass ratio of 1: (1-2) and uniformly stirring to obtain a mixed solution, and then mixing the mixed solution, an adhesive and the poly (diallyldimethylammonium chloride) -modified graphene oxide nano roll according to a mass ratio of 4: 2: 1 in THF, stirring the mixture at room temperature for 2-4 hours under the protection of argon, centrifuging the mixture, washing the mixture with THF, and finally performing heat treatment under the protection of argon to obtain a final product.
The preparation method, wherein the organic solvent is dichloromethane or trichloromethane.
The above preparation method, wherein the strong oxidant is selected from any one of nitric acid, sulfuric acid, potassium permanganate, or a mixed solution thereof.
In the preparation method, the water bath heating temperature is 70-80 ℃, and the time is 1-3 hours.
In the preparation method, the vacuum drying temperature is 40-50 ℃ and the time is 12-24 hours.
In the preparation method, the polymer is PMMA or PDMS.
In the preparation method, the adhesive includes one or more of aqueous LA-132, aqueous hydroxymethyl cellulose, aqueous styrene-butadiene emulsion, and oil-based polyvinylidene fluoride.
In the preparation method, the heat treatment temperature is 200-400 ℃ and the time is 1-3 hours.
By the technical scheme, the invention at least has the following advantages: according to the invention, the graphene oxide nano roll is used as a carrier matrix, and a carbon source is loaded on the surface of the graphene oxide nano roll, so that on one hand, more carbon sources can be loaded due to the larger interface area of the graphene oxide nano roll, and on the other hand, the graphene oxide nano roll has good mechanical properties, so that the stability in the denitrification process can be ensured, and a sufficient and stable carbon source can be provided for flora. The solid carbon source has large surface area, is beneficial to microorganism attachment and improves the utilization rate of the carbon source.
In conclusion, the special denitrification solid carbon source has good mechanical property and can effectively improve the denitrification rate. The method has the advantages and practical value, does not have similar design publication or use in the similar products and methods, is innovative, has great improvement on the method or the function, has great technical progress, produces good and practical effects, has multiple enhanced efficacies compared with the prior products, is more suitable for practical use, has industrial wide utilization value, and is a novel, improved and practical new design.
The foregoing is a summary of the present invention, and in order to provide a clear understanding of the technical means of the present invention and to be implemented in accordance with the present specification, the following is a detailed description of the preferred embodiments of the present invention.
Detailed Description
In order to make the technical means, the creation features, the achievement purposes and the effects of the invention easy to understand, the technical solutions in the embodiments of the present invention will be clearly and completely described below with reference to the embodiments of the present invention, and it is obvious that the described embodiments are only a part of the embodiments of the present invention, not all of the embodiments. All other embodiments, which can be derived by a person skilled in the art from the embodiments given herein without making any creative effort, shall fall within the protection scope of the present invention.
Example 1
Dissolving 100g of polylactic acid in 50mL of dichloromethane, then dropwise adding a nitric acid solution (60 wt%), carrying out oxidation pretreatment at a temperature of not higher than 60 ℃, and then adjusting the pH value of the solution to 6-8 to obtain the modified polylactic acid. Uniformly dispersing graphene oxide nano sheets in deionized water, heating the obtained graphene oxide dispersion liquid in a water bath at 70 ℃ for 2 hours, then quickly immersing the graphene oxide dispersion liquid in liquid nitrogen until the graphene oxide dispersion liquid is completely frozen, and finally, obtaining the graphene nano roll through freeze drying. And then carrying out ultrasonic treatment on the graphene oxide nano roll in 100ml of aqueous solution containing 1 wt% of poly (diallyldimethylammonium chloride) for 3h, then filtering and carrying out vacuum drying at 50 ℃ for 12h to obtain the poly (diallyldimethylammonium chloride) -modified graphene oxide nano roll. Mixing the obtained modified polylactic acid and PMMA according to the mass ratio of 1: 2 to obtain a mixed solution, and then mixing the mixed solution, the water-based butylbenzene emulsion and the poly diallyl dimethyl ammonium chloride modified graphene oxide nano roll according to the mass ratio of 4: 2: 1 in THF and the mixture was stirred at room temperature under argon for 3h, after which the mixture was centrifuged and washed with THF and finally heat treated at 300 ℃ under argon for 2h to give the final product.
Example 2
Dissolving 100g of polylactic acid in 80mL of trichloromethane, then dropwise adding a nitric acid solution (60 wt%), carrying out oxidation pretreatment at a temperature of not higher than 60 ℃, and then adjusting the pH value of the solution to 6-8 to obtain the modified polylactic acid. Uniformly dispersing graphene oxide nano sheets in deionized water, heating the obtained graphene oxide dispersion liquid in a water bath at 70 ℃ for 2 hours, then quickly immersing the graphene oxide dispersion liquid in liquid nitrogen until the graphene oxide dispersion liquid is completely frozen, and finally, obtaining the graphene nano roll through freeze drying. And then carrying out ultrasonic treatment on the graphene oxide nano roll in 100ml of aqueous solution containing 1 wt% of poly (diallyldimethylammonium chloride) for 4 hours, then filtering and carrying out vacuum drying at 50 ℃ for 12 hours to obtain the poly (diallyldimethylammonium chloride) -modified graphene oxide nano roll. Mixing the obtained modified polylactic acid and PMMA according to the mass ratio of 1: 1 to obtain a mixed solution, and then mixing the mixed solution, a water system LA-132 and a poly diallyl dimethyl ammonium chloride modified graphene oxide nano roll according to a mass ratio of 4: 2: 1 in THF and the mixture was stirred at room temperature under argon for 2h, after which the mixture was centrifuged and washed with THF and finally heat treated at 400 ℃ under argon for 2h to give the final product.
Example 3
Dissolving 100g of polylactic acid in 100mL of dichloromethane, then dropwise adding a potassium permanganate solution (55 wt%) and carrying out oxidation pretreatment at a temperature of not higher than 60 ℃, and then adjusting the pH value of the solution to 6-8 to obtain the modified polylactic acid. Uniformly dispersing graphene oxide nano sheets in deionized water, heating the obtained graphene oxide dispersion liquid in water bath at 80 ℃ for 1h, then quickly immersing in liquid nitrogen until the graphene oxide dispersion liquid is completely frozen, and finally, obtaining the graphene nano roll through freeze drying. And then carrying out ultrasonic treatment on the graphene oxide nano roll in 100ml of aqueous solution containing 1 wt% of poly (diallyldimethylammonium chloride) for 4 hours, then filtering and carrying out vacuum drying at 40 ℃ for 24 hours to obtain the poly (diallyldimethylammonium chloride) -modified graphene oxide nano roll. And (3) mixing the obtained modified polylactic acid with PDMS according to the mass ratio of 1: 1.5 to obtain a mixed solution, and then mixing the mixed solution, water-based hydroxymethyl cellulose and poly diallyl dimethyl ammonium chloride modified graphene oxide nano-roll according to a mass ratio of 4: 2: 1 in THF and the mixture was stirred at room temperature under argon for 2h, after which the mixture was centrifuged and washed with THF and finally heat treated at 200 ℃ under argon for 4h to give the final product.
Example 4
Dissolving 100g of polylactic acid in 40mL of trichloromethane, then dripping a potassium permanganate solution (50 wt%) and carrying out oxidation pretreatment at a temperature of not higher than 60 ℃, and then adjusting the pH value of the solution to 6-8 to obtain the modified polylactic acid. Uniformly dispersing graphene oxide nano sheets in deionized water, heating the obtained graphene oxide dispersion liquid in a water bath at 70 ℃ for 3h, then quickly immersing the graphene oxide dispersion liquid in liquid nitrogen until the graphene oxide dispersion liquid is completely frozen, and finally, obtaining the graphene nano roll through freeze drying. And then carrying out ultrasonic treatment on the graphene oxide nano roll in 100ml of aqueous solution containing 1 wt% of poly (diallyldimethylammonium chloride) for 2h, then filtering and carrying out vacuum drying at 45 ℃ for 18h to obtain the poly (diallyldimethylammonium chloride) -modified graphene oxide nano roll. Mixing the obtained modified polylactic acid and PMMA according to the mass ratio of 1: 2 to obtain a mixed solution, and then mixing the mixed solution, the water-based butylbenzene emulsion and the poly diallyl dimethyl ammonium chloride modified graphene oxide nano roll according to the mass ratio of 4: 2: 1 in THF and the mixture was stirred at room temperature under argon for 3h, after which the mixture was centrifuged and washed with THF and finally heat treated at 300 ℃ under argon for 3h to give the final product.
Example 5
Dissolving 100g of polylactic acid in 60mL of dichloromethane, then dropwise adding a nitric acid solution (50 wt%), carrying out oxidation pretreatment at a temperature of not higher than 60 ℃, and then adjusting the pH value of the solution to 6-8 to obtain the modified polylactic acid. Uniformly dispersing graphene oxide nano sheets in deionized water, heating the obtained graphene oxide dispersion liquid in a water bath at 70 ℃ for 3h, then quickly immersing the graphene oxide dispersion liquid in liquid nitrogen until the graphene oxide dispersion liquid is completely frozen, and finally, obtaining the graphene nano roll through freeze drying. And then carrying out ultrasonic treatment on the graphene oxide nano roll in 100ml of aqueous solution containing 1 wt% of poly (diallyldimethylammonium chloride) for 2h, then filtering and carrying out vacuum drying at 45 ℃ for 24h to obtain the poly (diallyldimethylammonium chloride) -modified graphene oxide nano roll. And (3) mixing the obtained modified polylactic acid with PDMS according to the mass ratio of 1: 1 to obtain a mixed solution, and then mixing the mixed solution, water-based hydroxymethyl cellulose and poly diallyl dimethyl ammonium chloride modified graphene oxide nano-roll according to a mass ratio of 4: 2: 1 in THF and the mixture was stirred at room temperature under argon for 3h, after which the mixture was centrifuged and washed with THF and finally heat treated at 300 ℃ under argon for 3h to give the final product.
Application example
The solid carbon sources prepared in examples 1 to 5 were respectively added to the denitrification filter tank at a dosage of 8 kg/ton/hour, and the monitoring time was continued for 8 days after the addition. As for the control group, COD (mg/L) and TN (mg/L) indexes of effluent were measured respectively in the case of adding glucose as a carbon source, and the results are shown in Table 1.
TABLE 1 effluent COD (mg/L) and effluent TN (mg/L) indices
Figure BDA0002715534140000061
From the results in table 1, under the condition of the same inlet water, the COD of the outlet water of the denitrification filter added with the solid carbon source of the invention is obviously higher than that of the control group, and the TN of the outlet water is always lower than that of the total nitrogen of the outlet water of the control group. The solid carbon source of the invention releases COD mildly, has long duration and moderate dosage.
Although the present invention has been described with reference to a preferred embodiment, it should be understood that various changes, substitutions and alterations can be made herein without departing from the spirit and scope of the invention as defined by the appended claims.

Claims (8)

1. A method for preparing a denitrification solid carbon source, which comprises the following steps:
(1) dissolving polylactic acid in an organic solvent, then dropwise adding a strong oxidant solution, carrying out oxidation pretreatment at the temperature of not higher than 60 ℃, and then adjusting the pH of the solution to 6-8 to obtain modified polylactic acid;
(2) uniformly dispersing graphene oxide nanosheets in deionized water, heating the obtained graphene oxide dispersion liquid in a water bath, quickly immersing the graphene oxide dispersion liquid in liquid nitrogen until the graphene oxide dispersion liquid is completely frozen, finally, obtaining graphene nano rolls through freeze drying, carrying out ultrasonic treatment on the graphene oxide nano rolls in 100ml of aqueous solution containing 1 wt% of poly (diallyldimethylammonium chloride) for 2-4 hours, filtering and carrying out vacuum drying to obtain poly (diallyldimethylammonium chloride) -modified graphene oxide nano rolls;
(3) mixing the obtained modified polylactic acid and a polymer according to the mass ratio of 1: (1-2) and uniformly stirring to obtain a mixed solution, and then mixing the mixed solution, an adhesive and the poly (diallyldimethylammonium chloride) -modified graphene oxide nano roll according to a mass ratio of 4: 2: 1 in THF, stirring the mixture at room temperature for 2-4 hours under the protection of argon, centrifuging the mixture, washing the mixture with THF, and finally performing heat treatment under the protection of argon to obtain a final product.
2. The method according to claim 1, wherein the organic solvent is selected from dichloromethane or chloroform.
3. The preparation method according to claim 1, wherein the strong oxidant is selected from any one of nitric acid, sulfuric acid, potassium permanganate, or a mixed solution thereof.
4. The preparation method of claim 1, wherein the water bath heating temperature is 70-80 ℃ and the time is 1-3 h.
5. The preparation method according to claim 1, wherein the vacuum drying temperature is 40-50 ℃ and the time is 12-24 h.
6. The production method according to claim 1, wherein the polymer is PMMA or PDMS.
7. The method according to claim 1, wherein the binder comprises one or more of aqueous LA-132, aqueous hydroxymethylcellulose, aqueous styrene-butadiene emulsion, and oil-based polyvinylidene fluoride.
8. The method according to claim 1, wherein the heat treatment temperature is 200 to 400 ℃ and the time is 1 to 3 hours.
CN202011072564.8A 2020-10-09 2020-10-09 Preparation method of denitrification solid carbon source Pending CN112340842A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202011072564.8A CN112340842A (en) 2020-10-09 2020-10-09 Preparation method of denitrification solid carbon source

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202011072564.8A CN112340842A (en) 2020-10-09 2020-10-09 Preparation method of denitrification solid carbon source

Publications (1)

Publication Number Publication Date
CN112340842A true CN112340842A (en) 2021-02-09

Family

ID=74360496

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202011072564.8A Pending CN112340842A (en) 2020-10-09 2020-10-09 Preparation method of denitrification solid carbon source

Country Status (1)

Country Link
CN (1) CN112340842A (en)

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US20130256590A1 (en) * 2010-11-15 2013-10-03 Archer Daniels Midland Company Microemulsions and uses thereof in dispersing catalysts
CN103613773A (en) * 2013-11-07 2014-03-05 常州大学 Preparation method of flexible transparent conducting polymer thin film with antibacterial properties
CN107141082A (en) * 2017-05-24 2017-09-08 安徽恒海生态农业观光园有限公司 A kind of vegetable cultivation is with the organic slow-release fertilizer that concave convex rod is major ingredient
CN107841037A (en) * 2016-09-20 2018-03-27 河南智联寰宇知识产权运营有限公司 High adsorption polylactic acid composite biological membrane carrier materials and preparation method thereof
CN109534318A (en) * 2018-11-29 2019-03-29 北京圣盟科技有限公司 A kind of graphene preparation method in battery

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US20130256590A1 (en) * 2010-11-15 2013-10-03 Archer Daniels Midland Company Microemulsions and uses thereof in dispersing catalysts
CN103613773A (en) * 2013-11-07 2014-03-05 常州大学 Preparation method of flexible transparent conducting polymer thin film with antibacterial properties
CN107841037A (en) * 2016-09-20 2018-03-27 河南智联寰宇知识产权运营有限公司 High adsorption polylactic acid composite biological membrane carrier materials and preparation method thereof
CN107141082A (en) * 2017-05-24 2017-09-08 安徽恒海生态农业观光园有限公司 A kind of vegetable cultivation is with the organic slow-release fertilizer that concave convex rod is major ingredient
CN109534318A (en) * 2018-11-29 2019-03-29 北京圣盟科技有限公司 A kind of graphene preparation method in battery

Similar Documents

Publication Publication Date Title
CN110395800B (en) Preparation method and application of external carbon source for denitrification
CN112094012B (en) Method for enhancing anaerobic digestion of municipal sludge to produce methane based on electron transfer
CN105170091A (en) Preparation method of iron-modified reed biological carbon, and application of iron-modified reed biological carbon in treatment of phosphorus wastewater
CN108579787B (en) Preparation method of heterojunction photocatalyst for NADH regeneration
CN103949218A (en) Modified graphene adsorbent as well as preparation method and application thereof
Xiong et al. Degradation of methylene blue by intimate coupling photocatalysis and biodegradation with bagasse cellulose composite carrier
CN102745810B (en) Synchronous denitrifying and decarburizing method for waste water
CN105129764B (en) Method of quickly preparing carbon quantum dots at high yield through aldehyde compound
CN106477846A (en) Hydrogen the method for reclaiming guanite are produced using free nitrite enhancement microbiological electroplating sludge
CN108479700A (en) A kind of preparation method for Cr VI and the porous carbon composite material of methyl orange eutectoid content
CN113663704B (en) Indium zinc sulfide/graphite phase carbon nitride composite material and preparation and application thereof
CN102923846B (en) Combined type biochar enhanced nitrogen removal filler and preparation method thereof
CN102627268A (en) Preparation method of nitrogen-doped carbon material
CN102489253B (en) Bismuth ferrate-carbon nano tube, preparation method thereof and method for treating organic dye wastewater by utilizing bismuth ferrate-carbon nano tube
CN110499339A (en) The method for promoting anaerobic digestion methane phase efficiency
CN114873837B (en) Method and device for realizing deep denitrification and dephosphorization by PD/A in-situ coupling algae
CN114573099B (en) Method for promoting enrichment of anaerobic ammonium oxidation bacteria by nitrogen-doped graphene
CN102994565B (en) Method for enhancing anaerobic fermentation of algal waste liquid to generate methane
CN105504278B (en) A kind of method for synthesizing polypyrrole
JP2023016647A (en) Method for accelerating startup of anaerobic reactors based on conductive materials
CN103588356A (en) Combination system for treating landfill leachate and method for treating landfill leachate by using combination system
CN112340842A (en) Preparation method of denitrification solid carbon source
CN108246254A (en) A kind of preparation method and product of the adjustable biomass carbon tunica fibrosa of wetability
CN115400699B (en) Preparation method and application of reduced graphene oxide/phosphate polyvinyl alcohol composite aerogel
CN115612497A (en) Method for reducing methane emission in rice soil by using nitric acid modified biochar

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
RJ01 Rejection of invention patent application after publication
RJ01 Rejection of invention patent application after publication

Application publication date: 20210209