CN110723736A - Biomass porous activated carbon material and preparation method and application thereof - Google Patents

Biomass porous activated carbon material and preparation method and application thereof Download PDF

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CN110723736A
CN110723736A CN201910630115.1A CN201910630115A CN110723736A CN 110723736 A CN110723736 A CN 110723736A CN 201910630115 A CN201910630115 A CN 201910630115A CN 110723736 A CN110723736 A CN 110723736A
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activated carbon
carbon material
porous activated
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陈理
黄伟国
刘孝伟
徐志彬
吴永新
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Chaowei Power Supply Co Ltd
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    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01BNON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
    • C01B32/00Carbon; Compounds thereof
    • C01B32/30Active carbon
    • C01B32/312Preparation
    • C01B32/342Preparation characterised by non-gaseous activating agents
    • C01B32/348Metallic compounds
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01BNON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
    • C01B32/00Carbon; Compounds thereof
    • C01B32/30Active carbon
    • C01B32/312Preparation
    • C01B32/318Preparation characterised by the starting materials
    • C01B32/324Preparation characterised by the starting materials from waste materials, e.g. tyres or spent sulfite pulp liquor
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01BNON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
    • C01B32/00Carbon; Compounds thereof
    • C01B32/30Active carbon
    • C01B32/312Preparation
    • C01B32/342Preparation characterised by non-gaseous activating agents
    • HELECTRICITY
    • H01ELECTRIC ELEMENTS
    • H01GCAPACITORS; CAPACITORS, RECTIFIERS, DETECTORS, SWITCHING DEVICES, LIGHT-SENSITIVE OR TEMPERATURE-SENSITIVE DEVICES OF THE ELECTROLYTIC TYPE
    • H01G11/00Hybrid capacitors, i.e. capacitors having different positive and negative electrodes; Electric double-layer [EDL] capacitors; Processes for the manufacture thereof or of parts thereof
    • H01G11/22Electrodes
    • H01G11/30Electrodes characterised by their material
    • H01G11/32Carbon-based
    • H01G11/34Carbon-based characterised by carbonisation or activation of carbon
    • HELECTRICITY
    • H01ELECTRIC ELEMENTS
    • H01MPROCESSES OR MEANS, e.g. BATTERIES, FOR THE DIRECT CONVERSION OF CHEMICAL ENERGY INTO ELECTRICAL ENERGY
    • H01M4/00Electrodes
    • H01M4/02Electrodes composed of, or comprising, active material
    • H01M4/36Selection of substances as active materials, active masses, active liquids
    • H01M4/38Selection of substances as active materials, active masses, active liquids of elements or alloys
    • HELECTRICITY
    • H01ELECTRIC ELEMENTS
    • H01MPROCESSES OR MEANS, e.g. BATTERIES, FOR THE DIRECT CONVERSION OF CHEMICAL ENERGY INTO ELECTRICAL ENERGY
    • H01M4/00Electrodes
    • H01M4/02Electrodes composed of, or comprising, active material
    • H01M4/62Selection of inactive substances as ingredients for active masses, e.g. binders, fillers
    • H01M4/624Electric conductive fillers
    • H01M4/625Carbon or graphite
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E60/00Enabling technologies; Technologies with a potential or indirect contribution to GHG emissions mitigation
    • Y02E60/10Energy storage using batteries
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E60/00Enabling technologies; Technologies with a potential or indirect contribution to GHG emissions mitigation
    • Y02E60/13Energy storage using capacitors

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Abstract

The invention relates to the technical field of energy storage materials, and provides a biomass porous activated carbon material, a preparation method and application thereof, aiming at solving the problems of high impurity content and uncontrollable pore structure of the traditional biomass activated carbon material. The biomass porous activated carbon material has large specific surface area and adjustable pore size, meets the requirements of a super capacitor and a lead-carbon battery, and can remarkably improve the sulfation of a negative electrode and prolong the cycle life of the battery when being used as a negative electrode additive of the lead-carbon battery; the preparation method has the advantages of easily available raw materials, abundant sources, low cost, simple steps and convenience for industrial production.

Description

Biomass porous activated carbon material and preparation method and application thereof
Technical Field
The invention relates to the technical field of energy storage materials, in particular to a biomass porous activated carbon material and a preparation method and application thereof.
Background
The activated carbon is classified into biomass activated carbon, coal-based activated carbon, petroleum-based activated carbon and the like according to the difference of raw materials, and is applied to various fields of national economy due to the characteristics of large specific surface area, developed pores, low price and the like. The activated carbon is mainly activated by chemical activation or physical activation. The chemical activation method is to mix various carbon sources and medicines uniformly and then to perform the processes of carbonization, activation, rinsing, drying and the like at a certain temperature. The general activating medicines are strong alkali or sulfuric acid, phosphoric acid and the like, the energy consumption is low, but the pollution of chemical agents is serious, and the process takes a long time. The physical activation method is a process of mixing carbonized raw materials with steam, nitrogen, carbon dioxide and the like at high temperature and then carrying out activation reaction, and has the advantages of relatively simple process, high specific surface area of products, developed pore structure, long process time, high energy consumption and certain component pollution.
The application of the active carbon as an energy storage material has good application prospect, and is mainly applied to double electric layer capacitors and lead carbon batteries. The activated carbon is added into the negative electrode of the lead-carbon battery, so that the salinization of the sodium sulfate of the negative electrode is mainly inhibited, the cycle life of the battery is prolonged, the performance requirement on the activated carbon is high, the specific surface area is high, the pore volume and the pore diameter structure can be regulated, and the impurity content is in a specified range. The biomass-based activated carbon has rich sources, low cost and simple and controllable preparation process, and has good research and application values.
At present, the bio-based activated carbon is widely applied to lead carbon batteries and is based on rice hulls and coconut shells, and the specific surface area of the bio-based activated carbon can reach 2000m2The Chinese patent literature discloses a preparation method of biomass-based activated carbon, and the application publication number is CN109179410A, the specific surface area of the rice hull-based activated carbon prepared by the invention is up to 2094.15m2And the surface of the activated carbon has rich pore-size structures. The rice hull-based activated carbon is used for adsorbing and removing benzene series substances, and the removal rate is as high as 80.2%. However, the biomass-based activated carbon prepared by the method has the defects of more impurities, uncontrollable pore structure, relatively complex preparation process and higher production cost.
Disclosure of Invention
The invention provides a biomass porous activated carbon material with low impurity content and directionally controllable pore structure, aiming at overcoming the problems of high impurity content and uncontrollable pore structure of the traditional biomass activated carbon material.
The invention also provides a preparation method of the biomass porous activated carbon material, and the method has the advantages of easily available raw materials, abundant sources, low cost, simple process steps and convenience for industrial production.
The invention also provides application of the biomass activated carbon material in lead carbon batteries and super capacitors.
In order to achieve the purpose, the invention adopts the following technical scheme:
a biomass porous activated carbon material is prepared by taking sunflower seed shells as a raw material, cleaning, drying, carbonizing, crushing, activating, cleaning and drying.
The biomass porous activated carbon material adopts sunflower seed shells as a carbon source, the sunflower seed shells are difficult to be economically utilized, the raw material source is rich, the cost is low, and compared with coal-based and petroleum-based activated carbon, the biomass porous activated carbon material has low impurity content and low cost.
A preparation method of a biomass porous activated carbon material comprises the following steps:
(1) cleaning sunflower seed shells in deionized water, and drying; the drying temperature is 30-80 ℃, and the drying time is 10-48 h;
(2) carbonizing the sunflower seed shells treated in the step (1);
(3) grinding the sunflower seed shells treated in the step (2) to obtain sunflower seed shell powder;
(4) adding an activating agent into the sunflower seed shell powder, carrying out activating treatment in inert gas, and then washing and drying by deionized water to obtain the biomass porous activated carbon material. Before drying, the activated carbon needs to be washed and filtered to be neutral.
Preferably, in the step (2), the carbonization treatment temperature is 200-500 ℃, and the carbonization treatment time is 1-4 h. The capacitance of the subsequent material can be affected by the carbonization temperature, and the capacitance value is too small due to too low carbonization temperature.
Preferably, in the step (3), the particle size of the sunflower seed hull powder is 40-60 meshes.
Preferably, in step (4), the activator is a basic activator or an acidic activator; the temperature of the activation treatment is 600-1300 ℃, and the activation time is 0.5-2 h. The different activation temperatures can generate activated carbon materials with different specific surface areas, and the higher the activation temperature is, the larger the specific surface area is.
Preferably, the addition amount of the alkaline activator is 1: (1-20); the alkaline activator is selected from one or more of potassium hydroxide, sodium hydroxide, ammonia water, potassium carbonate and sodium carbonate. The alkali-carbon mass ratio refers to the mass ratio of the alkaline activator to the sunflower seed hull powder.
Preferably, the acidic activator is selected from one or more of sulfuric acid, phosphoric acid, polyphosphoric acid and boric acid; the concentration of the acidic activator is 2-50 wt%.
Preferably, in the step (4), the inert gas is one selected from nitrogen, argon and helium.
Preferably, in the step (4), before the activation treatment, deionized water is added for soaking treatment; when the activating agent is an alkaline activating agent, the soaking time is 0.5-4 h; when the activating agent is an acidic activating agent, the soaking time is 1-12 h.
Before the activation treatment, the soaking effect enables the activating agent and the carbonized material to be fully mixed together, and the soaking time can influence the pore volume and the pore diameter of the subsequent material. The long soaking time may result in a large pore size.
Preferably, in the step (4), the temperature rise rate of the activation treatment is controlled to be 3 to 5 ℃/min, preferably 4 ℃/min. The temperature rise rate determines the pore structure of the final product, and the ordered pore structure is favorably formed in the temperature rise rate range, so that the directional regulation and control of the pore structure of the product are realized.
An application of a biomass porous activated carbon material in a lead carbon battery and a super capacitor.
The invention takes sunflower seed shells as raw materials, the specific surface area and the pore diameter of the prepared biomass porous activated carbon material are adjustable, and the requirements of a super capacitor and a lead-carbon battery can be met.
Preferably, the biomass porous activated carbon material is prepared into a lead-carbon battery by performing paste, plate coating and solidification according to the following formula: 1000 parts of lead powder, 1.1 parts of short fibers, 1.5-6 parts of carbon black, 2-60 parts of activated carbon, 5-30 parts of barium sulfate, 1-10 parts of lignin, 55-60 parts of sulfuric acid and 140-160 parts of pure water.
The biomass porous activated carbon material is used as a lead-carbon battery cathode additive, and can remarkably improve cathode sulfation and prolong the cycle life of the battery according to the formula proportion.
Therefore, the invention has the following beneficial effects:
(1) the carbon source adopted is sunflower seed shells which are difficult to be economically utilized, the raw material source is rich, the cost is low, and the impurity content is low;
(2) the biomass porous activated carbon material has large specific surface area and adjustable pore size, meets the requirements of a super capacitor and a lead-carbon battery, and can remarkably improve the sulfation of a negative electrode and prolong the cycle life of the battery when being used as a negative electrode additive of the lead-carbon battery;
(3) the preparation method has the advantages of easily available raw materials, abundant sources, low cost, simple steps and convenience for industrial production.
Drawings
FIG. 1 is an SEM image of a biomass porous activated carbon material prepared in example 1.
FIG. 2 is an SEM image of a biomass porous activated carbon material prepared in example 2.
FIG. 3 is XRD spectra of biomass porous activated carbon materials prepared in example 1(a) and example 2 (b).
Fig. 4 is a CV curve of the lead-carbon battery prepared in example 1 at a scan rate of 10 mv/s.
Fig. 5 is a battery cycle life curve of lead carbon batteries manufactured in example 1(a) and comparative example 5 (b).
Fig. 6 is an isothermal adsorption and desorption curve of the biomass porous activated carbon material prepared in example 1.
Detailed Description
The technical solution of the present invention is further specifically described below by using specific embodiments and with reference to the accompanying drawings.
In the present invention, all the equipment and materials are commercially available or commonly used in the art, and the methods in the following examples are conventional in the art unless otherwise specified.
Example 1
(1) Washing sunflower seed shell with deionized water for 3 times, filtering, and drying at 40 deg.C for 12 hr;
(2) putting the dried sample in a high-temperature furnace, carbonizing for 2h at 300 ℃, and taking out after cooling;
(3) grinding a sample to obtain sunflower seed shell powder with the granularity of 50 meshes;
(4) weighing 20g of sunflower seed shell powder, and mixing the following raw materials according to carbon: the mass ratio of alkali is 1: adding 60g of potassium hydroxide, adding 500g of deionized water, soaking for 2h, placing in a high-temperature furnace in a nitrogen atmosphere, heating to 950 ℃ at a heating rate of 4 ℃/min, preserving heat for 1h, naturally cooling to room temperature, washing for 2 times by using deionized water, and placing in a drying oven for drying at 4 ℃ for 12h to obtain the biomass porous activated carbon material, wherein an SEM picture of the biomass porous activated carbon material is shown in figure 1, and the prepared biomass porous activated carbon material is in an irregular blocky structure; the XRD spectrum of the material is shown as a curve a in figure 3, and the prepared material is an activated carbon material.
The biomass porous activated carbon material prepared in the example 1 is used in a negative electrode formula of a lead-carbon battery, and the preparation of an experimental battery is carried out by performing paste, plate coating and solidification according to the following formula, wherein 1000g of lead powder, 1.1g of short fiber, 1.5g of carbon black, 20g of activated carbon, 5g of barium sulfate, 3g of lignin, 55 g of sulfuric acid and 140g of pure water; the amount of the used paste acid was 1.4 g/ml.
Fig. 4 is a CV curve of the lead-carbon battery prepared in this example at a scan rate of 10mv/s, which is a result of a test in a three-electrode system, and it can be seen that the electrode material has excellent capacitance characteristics.
Fig. 5, curve a, is the battery cycle life curve of the lead-carbon battery prepared in this example, and fig. 5, curve b, is the battery cycle life curve of the comparative example 5, which is prepared by the existing production formulation without adding the biomass porous activated carbon material prepared by the present invention, it can be seen from the graph that the charging voltage of the lead-carbon battery is less than that of the comparative example 5, which shows that the charging acceptance of the lead-carbon battery is good, and from the discharge voltage, after dozens of cycles, the discharge voltage of the common battery is less than 1.75V, which is out of service, while the discharge voltage curve of the lead-carbon battery with the biomass porous activated carbon material prepared by the present invention is relatively stable and is maintained above 1.9V. The battery cycling test was performed at 30% -80% DOD (after the battery was fully charged, the first step was to discharge 20% and the second 50% and the third step was to repeat the second step again and again with the same amount of charge charged according to the amount of charge discharged in the second step.)
As can be seen from the isothermal adsorption and desorption curves of fig. 6: the adsorption curve of the prepared activated carbon is in I type at the beginning; the gas adsorption quantity is not obviously increased at the low-pressure end, which indicates that micropores exist a little. The gas adsorption capacity in the middle-high pressure section is increased sharply, and an obvious desorption hysteresis loop appears, which indicates that the activated carbon has a large amount of 80% mesopores (2-50 nm) and micropores and macropores account for 20%. The specific surface area of the activated carbon thus calculated was 1222m2/g。
Example 2
Example 2 differs from example 1 in that potassium hydroxide is added in an amount of carbon: the mass ratio of alkali is 1: 4, the activation temperature is 900 ℃, the heat preservation time is 0.5h, and the rest processes are completely the same. An SEM image of the biomass porous activated carbon material prepared in the embodiment is shown in FIG. 2, and it can be seen that the prepared biomass porous activated carbon material is in an irregular blocky structure; the XRD spectrogram is shown as a curve b in figure 3, and the prepared material is an activated carbon material;
the biomass porous activated carbon material prepared in the example 2 is used in a lead-carbon battery cathode formula, and an experimental battery is prepared by performing paste, plate coating and solidification according to the following formula: 1000g of lead powder, 1.1g of short fibers, 2g of carbon black, 15g of active carbon, 65g of barium sulfate, 4g of lignin, 55 g of sulfuric acid and 150g of pure water; the adopted paste acid is 1.4 g/ml;
the obtained activated carbon sample is used in a lead-carbon battery cathode formula and the performance of the activated carbon sample is tested, and the specific surface area of the activated carbon material is 852m2And/g, the cycle life of the prepared lead-carbon battery under 30-80% DOD can reach 1020 times (failure is determined when the number of times is continuously less than 3 times).
Example 3
Example 3 differs from example 1 in that the activator in step (4) is an acidic activator: weighing 30g of sunflower seed shell powder, soaking the sunflower seed shell powder in 30% phosphoric acid by mass for 3h, then placing the sunflower seed shell powder in a high-temperature furnace in nitrogen atmosphere, heating to 950 ℃ at a speed of 4 ℃/min, preserving heat for 1h, naturally cooling to room temperature, then cleaning for 2 times by using deionized water, and then placing the sunflower seed shell powder in a drying oven for drying for 12h at a temperature of 4 ℃ to obtain the biomass porous activated carbon material. The specific surface area was determined to be 1324m2/g。
Example 4
(1) Washing sunflower seed shell with deionized water for 3 times, filtering, and drying at 30 deg.C for 48 hr;
(2) putting the dried sample in a high-temperature furnace, carbonizing for 1h at 500 ℃, and taking out after cooling;
(3) grinding a sample to obtain sunflower seed shell powder with the granularity of 60 meshes;
(4) weighing 20g of sunflower seed shell powder, and mixing the following raw materials according to carbon: the mass ratio of alkali is 1: 20, adding 200g of potassium carbonate and 200g of sodium hydroxide, then adding 500g of deionized water, soaking for 4h, then placing in a high-temperature furnace in an argon atmosphere, heating to 1300 ℃ at a heating rate of 3 ℃/min, preserving heat for 0.5h, naturally cooling to room temperature, then cleaning for 2 times by using deionized water, and then placing in a drying oven for drying for 10h at 5 ℃ to obtain the biomass porous activated carbon material. The specific surface area was determined to be 1430m2/g。
Example 5
(1) Washing sunflower seed shell with deionized water for 3 times, filtering, and drying at 80 deg.C for 10 hr;
(2) putting the dried sample in a high-temperature furnace, carbonizing for 4h at 200 ℃, and taking out after cooling;
(3) grinding a sample to obtain sunflower seed shell powder with the granularity of 40 meshes;
(4) weighing 20g of sunflower seed shell powder, and mixing the following raw materials according to carbon: the mass ratio of alkali is 1: 1, adding 20g of sodium carbonate, adding 500g of deionized water, soaking for 0.5h, placing in a high-temperature furnace in a nitrogen atmosphere, heating to 600 ℃ at a heating rate of 5 ℃/min, preserving heat for 2h, naturally cooling to room temperature, cleaning for 2 times by using deionized water, and placing in a drying oven for drying at 4 ℃ for 12h to obtain the biomass porous activated carbon material. The specific surface area was measured to be 530m2/g。
Comparative example 1
Comparative example 1 is different from example 1 in that the temperature increase rate of the activation treatment in step (4) is 8 ℃/min, and the rest of the processes are completely the same. The mesopore proportion of the obtained biomass porous activated carbon material is only 40 percent, and the rest 60 percent is micropores or macropores.
Comparative example 2
The comparative example 2 is different from the example 1 in that the carbonization temperature is 180 ℃ in the step (2), and the rest of the process is completely the same. The prepared activated carbon has a capacitance value of 20F/g, and the capacitance value is reduced due to low temperature.
Comparative example 3 (without addition of Biomass porous activated carbon Material)
Carrying out paste, plate coating and curing according to the following formula to prepare an experimental battery, wherein 1000g of lead powder, 1.1g of short fiber, 1.5g of carbon black, 5g of barium sulfate, 3g of lignin, 55 g of sulfuric acid and 140g of pure water; the amount of the used paste acid was 1.4 g/ml.
The biomass porous activated carbon materials of examples 1-5 were used in the lead carbon battery negative electrode formulations and tested for performance, and the cycle life of the lead carbon batteries prepared in example 3 was tested at 30% -80% DOD and reported in Table 1.
The performance of the biomass porous activated carbon materials and the experimental batteries prepared in the examples 1 to 5 and the comparative examples 1 to 3 was tested, and the results are shown in table 1:
TABLE 1 test results
As can be seen from Table 1, the cycle life of the batteries of comparative examples 1 to 5 and comparative example 3 is 10 to 20 times that of the battery after adding the biomass porous activated carbon material prepared by the invention; the battery without the biomass porous activated carbon material prepared by the method has cycle life of only dozens of times under the condition of 30-80% DOD, and the cycle performance of the battery is poor. Comparing examples 1-5 with comparative example 2, it can be seen that the capacitance value of the biomass porous activated carbon material is greatly influenced by the carbonization temperature, and the capacitance value is too small due to the too low carbonization temperature (lower than 200 ℃); comparing examples 1-5 with comparative example 1, it can be seen that the temperature increase rate of the activation treatment determines the pore structure of the final product, and when the temperature increase rate is out of the range of the present invention, the mesopore ratio in the obtained biomass porous activated carbon material is obviously reduced (less than 50%).
The above description is only a preferred embodiment of the present invention, and is not intended to limit the present invention in any way, and other variations and modifications may be made without departing from the spirit of the invention as set forth in the claims.

Claims (10)

1. The biomass porous activated carbon material is characterized in that the biomass porous activated carbon material is prepared by taking sunflower seed shells as a raw material, cleaning, drying, carbonizing, crushing, activating, cleaning and drying.
2. The preparation method of the biomass porous activated carbon material as claimed in claim 1, characterized by comprising the following steps:
(1) cleaning sunflower seed shells in deionized water, and drying;
(2) carbonizing the sunflower seed shells treated in the step (1);
(3) grinding the sunflower seed shells treated in the step (2) to obtain sunflower seed shell powder;
(4) adding an activating agent into the sunflower seed shell powder, carrying out activating treatment in inert gas, and then washing and drying by deionized water to obtain the biomass porous activated carbon material.
3. The preparation method of the biomass porous activated carbon material according to claim 2, wherein in the step (2), the carbonization treatment temperature is 200-500 ℃, and the carbonization treatment time is 1-4 h.
4. The preparation method of the biomass porous activated carbon material as claimed in claim 2, wherein in the step (3), the particle size of the sunflower seed hull powder is 40-60 meshes.
5. The method for preparing the biomass porous activated carbon material according to claim 2, wherein in the step (4), the activating agent is an alkaline activating agent or an acidic activating agent; the temperature of the activation treatment is 600-1300 ℃, and the activation time is 0.5-2 h; the temperature rise rate of the activation treatment is controlled to be 3-5 ℃/min.
6. The preparation method of the biomass porous activated carbon material according to claim 5, wherein the addition amount of the alkaline activator is 1: (1-20); the alkaline activator is selected from one or more of potassium hydroxide, sodium hydroxide, ammonia water, potassium carbonate and sodium carbonate.
7. The preparation method of the biomass porous activated carbon material as claimed in claim 5, wherein the acidic activator is one or more selected from sulfuric acid, phosphoric acid, polyphosphoric acid and boric acid; the concentration of the acidic activator is 2-50 wt%.
8. The method for preparing the biomass porous activated carbon material according to claim 2, wherein in the step (4), the inert gas is selected from one of nitrogen, argon and helium.
9. The preparation method of the biomass porous activated carbon material according to claim 2, wherein in the step (4), deionized water is added for soaking treatment before activating treatment is carried out by adding an activating agent; when the activating agent is an alkaline activating agent, the soaking time is 0.5-4 h; when the activating agent is an acidic activating agent, the soaking time is 1-12 h.
10. The application of the biomass porous activated carbon material in the lead-carbon battery and the super capacitor as claimed in claim 1, wherein the biomass porous activated carbon material is prepared into the lead-carbon battery by the following formula through pasting, coating and curing: 1000 parts of lead powder, 1.1 parts of short fibers, 1.5-6 parts of carbon black, 2-60 parts of activated carbon, 5-30 parts of barium sulfate, 1-10 parts of lignin, 55-60 parts of sulfuric acid and 140-160 parts of pure water.
CN201910630115.1A 2019-07-12 2019-07-12 Biomass porous activated carbon material and preparation method and application thereof Pending CN110723736A (en)

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CN113753892A (en) * 2021-10-10 2021-12-07 山东省科学院菏泽分院 Biomass-based activated carbon material
WO2023050466A1 (en) * 2021-09-29 2023-04-06 海南大学 Method for preparing hard carbon negative electrode of lithium/sodium ion battery by using biomass charcoal
CN115924911A (en) * 2022-12-12 2023-04-07 林立 Preparation method of porous carbon material
CN116393113A (en) * 2023-04-20 2023-07-07 西藏大学 Preparation method and application of biochar for repairing heavy metals in high-altitude tailings
CN117244526A (en) * 2023-11-16 2023-12-19 成都达奇科技股份有限公司 Preparation method of modified activated carbon for removing organic malodorous gas and modified activated carbon

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CN117244526B (en) * 2023-11-16 2024-05-03 成都达奇科技股份有限公司 Preparation method of modified activated carbon for removing organic malodorous gas and modified activated carbon

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