CN103769050A - Electrochemical method for preparing activated carbon fibers with photocatalysis function - Google Patents

Electrochemical method for preparing activated carbon fibers with photocatalysis function Download PDF

Info

Publication number
CN103769050A
CN103769050A CN201410041403.0A CN201410041403A CN103769050A CN 103769050 A CN103769050 A CN 103769050A CN 201410041403 A CN201410041403 A CN 201410041403A CN 103769050 A CN103769050 A CN 103769050A
Authority
CN
China
Prior art keywords
activated carbon
carbon fibers
nacf
function
carbon fiber
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Granted
Application number
CN201410041403.0A
Other languages
Chinese (zh)
Other versions
CN103769050B (en
Inventor
陈孝云
陆东芳
陈星�
马长城
常鼎伟
高骁敏
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.)
Fujian Agriculture and Forestry University
Original Assignee
Fujian Agriculture and Forestry 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 Fujian Agriculture and Forestry University filed Critical Fujian Agriculture and Forestry University
Priority to CN201410041403.0A priority Critical patent/CN103769050B/en
Publication of CN103769050A publication Critical patent/CN103769050A/en
Application granted granted Critical
Publication of CN103769050B publication Critical patent/CN103769050B/en
Expired - Fee Related legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Images

Landscapes

  • Catalysts (AREA)

Abstract

The invention discloses a preparation method for activated carbon fibers with a photocatalysis function. The activated carbon fibers for immobilizing graphite phase carbon nitride are prepared by an electrochemical deposition method by taking activated carbon fibers, dicyanodiamine, N,N-dimethylformamide and the like as main raw materials. The activated carbon fibers have an adsorption function and the photocatalysis function. Under a condition of darkness or insufficient light, pollutants can be purified under the adsorption function of the activated carbon fibers; under a condition of sufficient light, the pollutants can be purified under the adsorption function and the photocatalysis function; in-situ regeneration of the adsorption function of the activated carbon fibers can be realized; labor, resource and financial consumption of a regeneration process is greatly reduced. Successful research on the activated carbon fibers has an important significance for relieving of insufficience of activated carbon fiber supply in China.

Description

电化学法制备光催化功能活性炭纤维Preparation of Photocatalytic Functional Activated Carbon Fibers by Electrochemical Method

技术领域 technical field

本发明属于活性炭纤维制备领域,具体涉及一种具有光催功能活性炭纤维的制备方法。 The invention belongs to the field of preparation of activated carbon fibers, and in particular relates to a preparation method of activated carbon fibers with photocatalytic function.

背景技术 Background technique

活性炭纤维因其孔隙结构发达、吸附力强、表面官能团丰富、化学惰性等优点,被广泛应用于气体吸附净化、污染水体治理、饮用水净化以及食品工业、化学工业等领域。但由于活性炭纤维品种少、技术含量低、缺少功能化高品质专用活性炭纤维,制约我国活性炭纤维行业迈向更高层次的应用。将活性炭纤维改性处理,研制出能够对污染物进行高效、深度净化的功能活性炭纤维,是降低活性炭纤维的使用成本、扩大其使用范围、提高其利用效率的有效途径,是活性炭纤维行业未来发展的方向。 Due to its developed pore structure, strong adsorption capacity, rich surface functional groups, and chemical inertness, activated carbon fibers are widely used in gas adsorption purification, polluted water treatment, drinking water purification, food industry, chemical industry and other fields. However, due to the lack of activated carbon fiber varieties, low technical content, and lack of functional high-quality special activated carbon fibers, my country's activated carbon fiber industry is restricted from moving towards a higher level of application. Modification of activated carbon fibers to develop functional activated carbon fibers that can efficiently and deeply purify pollutants is an effective way to reduce the cost of activated carbon fibers, expand their scope of use, and improve their utilization efficiency. It is the future development of the activated carbon fiber industry. direction.

由于活性炭纤维对污染物的吸附主要以微孔填充为主,吸附量有限,短时间内即可达吸附饱和而失去吸附能力,吸附饱和的活性炭纤维成为二次污染源,须对其进行再生处理方可再次利用。目前活性炭纤维再生方法总体上可以分为两类:一是设法使吸附质脱附,即通过创造与低负荷相对应的条件(引入物质或能量使吸附质分子与活性炭纤维之间的作用力减弱或消失),除去吸附质;二是依靠热分解或氧化还原反应破坏吸附质的结构,除去吸附质。传统的再生方法主要有热再生、化学药品再生、溶剂再生、生物再生等,但由于其存在效率低、耗费高、操作条件苛刻、工艺复杂等缺陷,传统再生方法已不能满足现在工业发展的需求。因此研究一种在常温、常压、低耗费、高效率、操作工艺单简的再生方法成为国内外研究的热点。 Since the adsorption of pollutants by activated carbon fibers is mainly based on micropore filling, the adsorption capacity is limited, and the adsorption saturation can be reached in a short time and the adsorption capacity is lost. The saturated activated carbon fibers become a secondary pollution source and must be regenerated. Can be reused. At present, the activated carbon fiber regeneration methods can be generally divided into two categories: one is to try to desorb the adsorbate, that is, by creating conditions corresponding to the low load (introducing substances or energy to weaken the force between the adsorbate molecules and the activated carbon fiber). or disappear) to remove the adsorbate; the second is to rely on thermal decomposition or redox reaction to destroy the structure of the adsorbate and remove the adsorbate. Traditional regeneration methods mainly include thermal regeneration, chemical regeneration, solvent regeneration, biological regeneration, etc., but due to their defects such as low efficiency, high cost, harsh operating conditions, and complicated processes, traditional regeneration methods can no longer meet the needs of current industrial development. . Therefore, researching a regeneration method at normal temperature, normal pressure, low consumption, high efficiency, and simple operation process has become a research hotspot at home and abroad.

发明内容 Contents of the invention

本发明的目的在于提供一种具有光催功能活性炭纤维的制备方法。本发明制得的光催化功能活性炭纤维具有光催化功能和吸附功能,且在光照下活性炭纤维可原位再生。 The purpose of the present invention is to provide a preparation method of activated carbon fiber with photocatalytic function. The photocatalytic functional activated carbon fiber prepared by the invention has photocatalytic function and adsorption function, and the activated carbon fiber can be regenerated in situ under illumination.

为实现上述目的,本发明采用如下技术方案: To achieve the above object, the present invention adopts the following technical solutions:

采用电化学法制备固载石墨相氮化碳的活性炭纤维,包括以下步骤: Prepare the active carbon fiber of immobilized graphitic phase carbon nitride by electrochemical method, comprising the following steps:

(1)将具有导电性、且电阻率小于80kΩ/m的活性炭纤维,用2wt.%的盐酸煮沸清洗后,再用蒸馏水洗涤至中性,于烘箱中烘24h; (1) After boiling and cleaning activated carbon fibers with electrical conductivity and resistivity less than 80kΩ/m with 2wt.% hydrochloric acid, they are washed with distilled water until neutral, and baked in an oven for 24 hours;

(2)将步骤(1)的活性炭纤维置于二氰二胺的N,N二甲基甲酰胺溶液中浸泡24h; (2) Soak the activated carbon fiber in step (1) in N,N dimethylformamide solution of dicyandiamide for 24 hours;

(3)固载石墨相氮化碳的过程在电解池中进行,电化学沉积条件:以二氰二胺的N,N二甲基甲酰胺溶液作为电解液,以石墨为阳极,以步骤(2)的活性炭纤维为阴极,电源为直流电源,电解过程电压500~2000V,温度25~30℃,时间1~5h; (3) The process of immobilizing graphite-phase carbon nitride is carried out in an electrolytic cell, and the electrochemical deposition conditions: use N,N dimethylformamide solution of dicyandiamide as electrolyte, graphite as anode, and step ( 2) The active carbon fiber is the cathode, the power supply is DC power supply, the electrolysis process voltage is 500~2000V, the temperature is 25~30℃, and the time is 1~5h;

(4)从电解池中取出阴极的活性炭纤维,用蒸馏水充分洗涤、烘干,即制得固载石墨相氮化碳的活性炭纤维。 (4) The activated carbon fiber of the cathode is taken out from the electrolytic cell, fully washed with distilled water, and dried to obtain the activated carbon fiber immobilized with graphite phase carbon nitride.

所述的二氰二胺的N,N二甲基甲酰胺溶液中二氰二胺的浓度为0.05~0.15mol/L。 The concentration of dicyandiamine in the N,N dimethylformamide solution of dicyandiamine is 0.05-0.15mol/L.

本发明的显著优点在于:本发明制得的活性炭纤维不仅具有吸附功能,而且具有光催化功能。其在黑暗或光线不足的情况下依靠活性炭纤维的吸附功能净化污染物;在光照充足的情况下吸附功能及光催化功能均可净化污染物,还可实现活性炭纤维吸附功能的原位再生,大大降低再生过程人力、物力、财力耗费。该活性炭纤维的研制成功对于缓解我国活性炭纤维供应量不足具有重要的作用。 The remarkable advantage of the present invention is that: the activated carbon fiber prepared by the present invention not only has the function of adsorption, but also has the function of photocatalysis. It relies on the adsorption function of activated carbon fibers to purify pollutants in the dark or insufficient light; in the case of sufficient light, both the adsorption function and the photocatalytic function can purify pollutants, and can also realize the in-situ regeneration of the adsorption function of activated carbon fibers, greatly Reduce manpower, material and financial resources in the regeneration process. The successful development of the activated carbon fiber plays an important role in alleviating the insufficient supply of activated carbon fiber in my country.

附图说明 Description of drawings

图1为ACF1及ACF0的XRD谱; Fig. 1 is the XRD spectrum of ACF1 and ACF0;

图2为ACF1及ACF0的FTIR谱; Figure 2 is the FTIR spectrum of ACF1 and ACF0;

图3为AFC1及ACF0的吸附脱附曲线图; Fig. 3 is the adsorption-desorption curve diagram of AFC1 and ACF0;

图4为在光照及暗吸附条件下ACF1及ACF0对甲醛的净化效果; Figure 4 is the purification effect of ACF1 and ACF0 on formaldehyde under light and dark adsorption conditions;

图5为光照条件下ACF1及ACF0重复使用6次对甲醛的去除效果。 Figure 5 shows the removal effect of ACF1 and ACF0 on formaldehyde after repeated use for 6 times under light conditions.

注:本发明制备的光催化功能活性炭纤维(标记为:ACF1),而对照样活性炭纤维(标记为:ACF0)。 Note: The photocatalytic functional activated carbon fiber (marked as: ACF1) prepared by the present invention, and the control activated carbon fiber (marked as: ACF0).

具体实施方式 Detailed ways

实施例1Example 1

1) 将具有导电性、且电阻率小于80kΩ/m的活性炭纤维,用2%的盐酸煮沸清洗,后再用蒸馏洗涤至中性,并至于烘箱烘干24h; 1) The activated carbon fibers with conductivity and resistivity less than 80kΩ/m are boiled and cleaned with 2% hydrochloric acid, then washed by distillation until neutral, and dried in an oven for 24 hours;

2)将步骤1)中的活性炭纤维置于0.05mol/L二氰二胺的N,N二甲基甲酰胺溶液中浸泡24h; 2) Soak the activated carbon fiber in step 1) in a N,N dimethylformamide solution of 0.05mol/L dicyandiamide for 24 hours;

3)固载石墨相氮化碳的过程在电解池中进行,电化学沉积条件:以0.05mol/L二氰二胺的N,N二甲基甲酰胺溶液作为电解液,以石墨为阳极,以步骤2)的活性炭纤维为阴极,电源为直流电源,电解过程电压2000V,电解过程温度25℃,电解时间1h。 3) The process of immobilizing graphite-phase carbon nitride is carried out in an electrolytic cell. Electrochemical deposition conditions: use 0.05mol/L dicyandiamine N,N dimethylformamide solution as electrolyte, graphite as anode, The activated carbon fiber in step 2) is used as the cathode, the power supply is a DC power supply, the electrolysis process voltage is 2000V, the electrolysis process temperature is 25°C, and the electrolysis time is 1h.

4) 从电解池中取出阴极的活性炭纤维,并用蒸馏水充分洗涤、烘干,即制得固载石墨相氮化碳具有光催化功能的活性炭纤维。 4) Take out the active carbon fiber of the cathode from the electrolytic cell, wash and dry it fully with distilled water, and then obtain the active carbon fiber with photocatalytic function of immobilized graphite phase carbon nitride.

实施例2Example 2

1) 将具有导电性、且电阻率小于80kΩ/m的活性炭纤维,用2%的盐酸煮沸清洗,后再用蒸馏洗涤至中性,并至于烘箱烘干24h; 1) The activated carbon fibers with conductivity and resistivity less than 80kΩ/m are boiled and cleaned with 2% hydrochloric acid, then washed by distillation until neutral, and dried in an oven for 24 hours;

2)将步骤1)中的活性炭纤维置于0.15mol/L二氰二胺的N,N二甲基甲酰胺溶液中浸泡24h; 2) Soak the activated carbon fiber in step 1) in 0.15mol/L N,N dimethylformamide solution of dicyandiamide for 24h;

3)固载石墨相氮化碳的过程在电解池中进行,电化学沉积条件:以0.15mol/L二氰二胺的N,N二甲基甲酰胺溶液作为电解液,以石墨为阳极,以步骤2)的活性炭纤维为阴极,电源为直流电源,电解过程电压500V,电解过程温度30℃,电解时间5h。 3) The process of immobilizing graphite phase carbon nitride is carried out in an electrolytic cell, and the electrochemical deposition conditions are as follows: 0.15mol/L N,N dimethylformamide solution of dicyandiamine is used as the electrolyte, and graphite is used as the anode. The activated carbon fiber in step 2) is used as the cathode, the power supply is a DC power supply, the electrolysis process voltage is 500V, the electrolysis process temperature is 30°C, and the electrolysis time is 5h.

4) 从电解池中取出阴极的活性炭纤维,并用蒸馏水充分洗涤、烘干,即制得固载石墨相氮化碳具有光催化功能的活性炭纤维。 4) Take out the active carbon fiber of the cathode from the electrolytic cell, wash and dry it fully with distilled water, and then obtain the active carbon fiber with photocatalytic function of immobilized graphite phase carbon nitride.

实施例3Example 3

1) 将具有导电性、且电阻率小于80kΩ/m的活性炭纤维,用2%的盐酸煮沸清洗,后再用蒸馏洗涤至中性,并至于烘箱烘干24h; 1) The activated carbon fibers with conductivity and resistivity less than 80kΩ/m are boiled and cleaned with 2% hydrochloric acid, then washed by distillation until neutral, and dried in an oven for 24 hours;

2)将步骤1)中的活性炭纤维置于0.10mol/L二氰二胺的N,N二甲基甲酰胺溶液中浸泡24h; 2) Soak the activated carbon fiber in step 1) in 0.10mol/L N,N dimethylformamide solution of dicyandiamide for 24h;

3)固载石墨相氮化碳的过程在电解池中进行,电化学沉积条件:以0.10mol/L二氰二胺的N,N二甲基甲酰胺溶液作为电解液,以石墨为阳极,以步骤2)的活性炭纤维为阴极,电源为直流电源,电解过程电压1000V,电解过程温度28℃,电解时间3h。 3) The process of immobilizing graphite-phase carbon nitride is carried out in an electrolytic cell. Electrochemical deposition conditions: use 0.10mol/L dicyandiamide N,N dimethylformamide solution as electrolyte, graphite as anode, The activated carbon fiber in step 2) is used as the cathode, the power supply is a DC power supply, the electrolysis process voltage is 1000V, the electrolysis process temperature is 28°C, and the electrolysis time is 3h.

4) 从电解池中取出阴极的活性炭纤维,并用蒸馏水充分洗涤、烘干,即制得固载石墨相氮化碳具有光催化功能的活性炭纤维。 4) Take out the active carbon fiber of the cathode from the electrolytic cell, wash and dry it fully with distilled water, and then obtain the active carbon fiber with photocatalytic function of immobilized graphite phase carbon nitride.

图1为ACF1及ACF0的XRD谱。由图可以看出,ACF1在2θ=27.65o附近有一个较宽的衍射峰,其对应于石墨相氮化碳的(002)晶面衍射峰。另外,ACF1在2θ=13.23o附近有一个较宽的衍射峰,其对应于石墨相氮化碳的(100)晶面衍射峰。 Figure 1 is the XRD spectrum of ACF1 and ACF0. It can be seen from the figure that ACF1 has a broad diffraction peak around 2 θ = 27.65o, which corresponds to the (002) crystal plane diffraction peak of graphitic carbon nitride. In addition, ACF1 has a broad diffraction peak around 2 θ = 13.23o, which corresponds to the (100) crystal plane diffraction peak of graphitic carbon nitride.

图2为ACF1及ACF0的FTIR谱。ACF1在810nm-1的特征吸收峰可归属为嗪环的弯曲振动,1246~1633 nm-1范围内几个强的特征峰对应于CN杂环化合物的特征吸收峰。1326 nm-1和1635 nm-1处的特征吸收峰分别归属为石墨相氮化碳的C-N键和C=N键的弯曲振动吸收峰。1635 nm-1处出现较强的特征吸收峰说明g-C3N4的结晶度较高。3175 nm-1和3432 nm-1的特征吸收峰分别为N-H键和O-H键的伸缩振动吸收峰。 Figure 2 is the FTIR spectra of ACF1 and ACF0. The characteristic absorption peak of ACF1 at 810nm -1 can be attributed to the bending vibration of the oxazine ring, and several strong characteristic peaks in the range of 1246~1633 nm -1 correspond to the characteristic absorption peaks of CN heterocyclic compounds. The characteristic absorption peaks at 1326 nm -1 and 1635 nm -1 are assigned to the bending vibration absorption peaks of CN bond and C=N bond of graphitic carbon nitride, respectively. The strong characteristic absorption peak at 1635 nm -1 indicates that the crystallinity of gC 3 N 4 is high. The characteristic absorption peaks at 3175 nm -1 and 3432 nm -1 are the stretching vibration absorption peaks of NH bond and OH bond, respectively.

图3为ACF1及ACF0样品的N2吸附-脱附曲线图。由图可知,两种样品的吸附等温线均呈现相同的类型,且都具有滞后环。另外,从图还可以看出ACF1的吸附量略小于ACF0。 Figure 3 is the N 2 adsorption-desorption curves of ACF1 and ACF0 samples. It can be seen from the figure that the adsorption isotherms of the two samples are of the same type, and both have hysteresis loops. In addition, it can also be seen from the figure that the adsorption capacity of ACF1 is slightly smaller than that of ACF0.

图4为在光照及暗吸附条件下ACF1及ACF0对甲醛的净化效果。由图可以看出,以该工艺制备的活性炭纤维不仅具有吸附功能,而且还具有光催化功能。在暗吸附条件,ACF1的吸附量略小于ACF0;但是在光照条件下ACF1对甲醛的净化效果显著好于ACF0对甲醛的去除效果。 Figure 4 shows the purification effect of ACF1 and ACF0 on formaldehyde under light and dark adsorption conditions. It can be seen from the figure that the activated carbon fiber prepared by this process not only has the function of adsorption, but also has the function of photocatalysis. Under dark adsorption conditions, the adsorption capacity of ACF1 was slightly smaller than that of ACF0; however, the purification effect of ACF1 on formaldehyde was significantly better than that of ACF0 on formaldehyde under light conditions.

图5为光照条件下ACF1及ACF0重复使用6次对甲醛的净化效果实验,从图可以看出ACF1对甲醛的净化效果明显好于ACF0。在相同条件下ACF1重复使用6后对甲醛的去除率在94%以上,而ACF0重复使用6次后对甲醛去除率仅为4%。 Figure 5 is an experiment on the purification effect of ACF1 and ACF0 on formaldehyde after repeated use for 6 times under light conditions. It can be seen from the figure that the purification effect of ACF1 on formaldehyde is significantly better than that of ACF0. Under the same conditions, the formaldehyde removal rate of ACF1 after repeated use for 6 times was over 94%, while that of ACF0 was only 4% after repeated use for 6 times.

以上所述仅为本发明的较佳实施例,凡依本发明申请专利范围所做的均等变化与修饰,皆应属本发明的涵盖范围。 The above descriptions are only preferred embodiments of the present invention, and all equivalent changes and modifications made according to the scope of the patent application of the present invention shall fall within the scope of the present invention.

Claims (3)

1. a preparation method with photo-catalysis function NACF, is characterized in that: the NACF that adopts the immobilized graphite-phase carbonitride of electrochemical production.
2. the preparation method with photo-catalysis function NACF according to claim 1, is characterized in that: comprise the following steps:
(1) will there is the NACF that electric conductivity and resistivity are less than 80k Ω/m, and boil after cleaning with the hydrochloric acid of 2wt.%, then be washed with distilled water to neutrality, in baking oven, dry 24h;
(2) the DMF solution that the NACF of step (1) is placed in to dicyanodiamine soaks 24h;
(3) process of immobilized graphite-phase carbonitride is carried out in electrolytic cell, electrochemical deposition condition: with the N of dicyanodiamine, N dimethyl formamide solution is as electrolyte, take graphite as anode, take the NACF of step (2) as negative electrode, power supply is dc source, electrolytic process voltage 500 ~ 2000V, 25 ~ 30 ℃ of temperature, time 1 ~ 5h;
(4) from electrolytic cell, take out the NACF of negative electrode, fully wash, dry with distilled water, make the NACF of immobilized graphite-phase carbonitride.
3. the preparation method with photo-catalysis function NACF according to claim 2, is characterized in that: in the DMF solution of described dicyanodiamine, the concentration of dicyanodiamine is 0.05 ~ 0.15mol/L.
CN201410041403.0A 2014-01-28 2014-01-28 Electrochemical production photo-catalysis function NACF Expired - Fee Related CN103769050B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201410041403.0A CN103769050B (en) 2014-01-28 2014-01-28 Electrochemical production photo-catalysis function NACF

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201410041403.0A CN103769050B (en) 2014-01-28 2014-01-28 Electrochemical production photo-catalysis function NACF

Publications (2)

Publication Number Publication Date
CN103769050A true CN103769050A (en) 2014-05-07
CN103769050B CN103769050B (en) 2015-08-12

Family

ID=50562084

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201410041403.0A Expired - Fee Related CN103769050B (en) 2014-01-28 2014-01-28 Electrochemical production photo-catalysis function NACF

Country Status (1)

Country Link
CN (1) CN103769050B (en)

Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104353482A (en) * 2014-11-06 2015-02-18 福建农林大学 A kind of g-C3N4/activated carbon composite photocatalyst and its preparation method and application
CN104772160A (en) * 2015-04-17 2015-07-15 北京师范大学 Carbon nitride photocatalytic activity nano fiber membrane and preparation method thereof
CN108262015A (en) * 2018-02-01 2018-07-10 上海申丰地质新技术应用研究所有限公司 A kind of activated carbon fiber adsorbing substance and preparation method thereof and the application in benzene homologues absorption
CN109967031A (en) * 2017-12-28 2019-07-05 柏美迪康环境科技(上海)股份有限公司 A kind of activated carbon fiber adsorbing substance and preparation method thereof for benzene homologues absorption
CN109985601A (en) * 2017-12-29 2019-07-09 柏美迪康环境科技(上海)股份有限公司 A kind of activated carbon fiber adsorbing substance and preparation method thereof for volatile organic matter absorption
CN111715175A (en) * 2019-03-21 2020-09-29 中国科学院上海硅酸盐研究所 Carbonate modified carbon nitride and preparation method thereof and application in low-concentration ammonia nitrogen wastewater treatment
CN111938240A (en) * 2020-09-18 2020-11-17 上海交通大学 High-efficient antibiotic active carbon protective facial mask who disinfects
CN115108553A (en) * 2022-07-25 2022-09-27 浙江农林大学 A method of assisting woody biomass to prepare nitrogen-doped activated carbon with high specific surface area

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US6214201B1 (en) * 1998-08-08 2001-04-10 Korean Research Institute Of Chemical Technology Process for manufacturing functional activated carbon fibers treated by anodic oxidation
CN102476048A (en) * 2010-11-22 2012-05-30 大连创达技术交易市场有限公司 Active carbon fiber in-situ regeneration method for treating gaseous pollutants
CN103170358A (en) * 2013-04-08 2013-06-26 清华大学 A kind of porous g-C3N4 photocatalyst and preparation method thereof
CN103240121A (en) * 2013-05-27 2013-08-14 清华大学 A kind of porous g-C3N4 photocatalyst and preparation method thereof

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US6214201B1 (en) * 1998-08-08 2001-04-10 Korean Research Institute Of Chemical Technology Process for manufacturing functional activated carbon fibers treated by anodic oxidation
CN102476048A (en) * 2010-11-22 2012-05-30 大连创达技术交易市场有限公司 Active carbon fiber in-situ regeneration method for treating gaseous pollutants
CN103170358A (en) * 2013-04-08 2013-06-26 清华大学 A kind of porous g-C3N4 photocatalyst and preparation method thereof
CN103240121A (en) * 2013-05-27 2013-08-14 清华大学 A kind of porous g-C3N4 photocatalyst and preparation method thereof

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
XINJIAO BAI ET AL: "Synthesis of hollow carbon nitride microspheres by an electrodeposition method", 《APPLIED SURFACE SCIENCE》, vol. 256, 27 October 2009 (2009-10-27), pages 2327 - 2331, XP026857858 *

Cited By (14)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104353482A (en) * 2014-11-06 2015-02-18 福建农林大学 A kind of g-C3N4/activated carbon composite photocatalyst and its preparation method and application
CN104353482B (en) * 2014-11-06 2016-04-27 福建农林大学 A kind of g-C 3n 4/ active carbon composite photo-catalyst and its preparation method and application
CN104772160A (en) * 2015-04-17 2015-07-15 北京师范大学 Carbon nitride photocatalytic activity nano fiber membrane and preparation method thereof
CN104772160B (en) * 2015-04-17 2017-03-15 北京师范大学 A kind of carbonitride photocatalytic activity nano fibrous membrane and preparation method thereof
CN109967031B (en) * 2017-12-28 2022-08-09 柏美迪康环境科技(上海)股份有限公司 Activated carbon fiber adsorbent for benzene series adsorption and preparation method thereof
CN109967031A (en) * 2017-12-28 2019-07-05 柏美迪康环境科技(上海)股份有限公司 A kind of activated carbon fiber adsorbing substance and preparation method thereof for benzene homologues absorption
CN109985601A (en) * 2017-12-29 2019-07-09 柏美迪康环境科技(上海)股份有限公司 A kind of activated carbon fiber adsorbing substance and preparation method thereof for volatile organic matter absorption
CN109985601B (en) * 2017-12-29 2022-08-09 柏美迪康环境科技(上海)股份有限公司 Activated carbon fiber adsorbent for adsorbing volatile organic compounds and preparation method thereof
CN108262015B (en) * 2018-02-01 2020-07-28 上海申丰地质新技术应用研究所有限公司 Activated carbon fiber adsorbent, preparation method thereof and application thereof in benzene series adsorption
CN108262015A (en) * 2018-02-01 2018-07-10 上海申丰地质新技术应用研究所有限公司 A kind of activated carbon fiber adsorbing substance and preparation method thereof and the application in benzene homologues absorption
CN111715175A (en) * 2019-03-21 2020-09-29 中国科学院上海硅酸盐研究所 Carbonate modified carbon nitride and preparation method thereof and application in low-concentration ammonia nitrogen wastewater treatment
CN111715175B (en) * 2019-03-21 2021-06-15 中国科学院上海硅酸盐研究所 Carbonate modified carbon nitride and preparation method thereof and application in low-concentration ammonia nitrogen wastewater treatment
CN111938240A (en) * 2020-09-18 2020-11-17 上海交通大学 High-efficient antibiotic active carbon protective facial mask who disinfects
CN115108553A (en) * 2022-07-25 2022-09-27 浙江农林大学 A method of assisting woody biomass to prepare nitrogen-doped activated carbon with high specific surface area

Also Published As

Publication number Publication date
CN103769050B (en) 2015-08-12

Similar Documents

Publication Publication Date Title
CN103769050B (en) Electrochemical production photo-catalysis function NACF
CN103253651B (en) Lignin-based porous carbon material and preparation method thereof
CN104226290B (en) A kind of TiO2/ RGO aeroge and its preparation method and application
CN106167263B (en) A kind of method that activated carbon is prepared using Lignin in Wastewater from Paper-Making Mill
CN104289179B (en) Method for preparing attapulgite/carbon composite adsorbent by one-step carbonization-activation
NO20170575A1 (en) Method for producing activated carbon
CN105271227A (en) Preparation method for porous carbon material with high specific surface area
Ma et al. Facile synthesis of g-C3N4 wrapping on one-dimensional carbon fiber as a composite photocatalyst to degrade organic pollutants
CN103769187A (en) Preparation method of graphene/g-C3N4 compound photocatalyst
CN107128918A (en) A kind of preparation and its application of N doping porous active Carbon Materials
CN104014307B (en) A kind of microwave heating method of modifying strengthening activated carbon surface basic group
CN102701200A (en) Method for preparing active carbon from municipal sludge by two-step thermal decomposition
CN108325555A (en) Nitrogen auto-dope is graphitized azotized carbon nano piece photochemical catalyst and its preparation method and application
CN110368980A (en) A kind of preparation method of complex light electrode
CN104016512B (en) A method of using Spartina alterniflora-based biochar to treat copper-containing wastewater
CN103495395B (en) A kind of immobilized g-C 3n 4there is the preparation method of photo-catalysis function active carbon
CN102553556B (en) A kind of regeneration method of active carbon of processing ibuprofen decolorization process
CN109761213B (en) Porous nitrogen-phosphorus-doped carbon material and preparation method and application thereof
CN105664988A (en) A kind of (BiO)2CO3/C composite photocatalyst and its application
CN108579782A (en) A kind of visible light-responded composite material and its preparation and application
CN102527362B (en) Regeneration method of active carbon for treating decoloring process of analgin
JP5481073B2 (en) Manufacturing method of highly purified activated carbon
CN110512260A (en) A kind of preparation method of composite photoelectrode
CN103864051B (en) Synchronous Preparation of Amorphous Carbon Nanotubes and SBA-15 Mesoporous Molecular Sieve Using Attapulgite Clay as Template and Raw Materials
CN114956040B (en) Nitrogen-oxygen doped hierarchical porous carbon material, preparation method and application

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
C14 Grant of patent or utility model
GR01 Patent grant
CF01 Termination of patent right due to non-payment of annual fee

Granted publication date: 20150812

Termination date: 20180128

CF01 Termination of patent right due to non-payment of annual fee