CN104759254A - Preparation method of chromium-loaded active carbon as well as condition and device of methylbenzene adsorption using chromium-loaded active carbon - Google Patents

Preparation method of chromium-loaded active carbon as well as condition and device of methylbenzene adsorption using chromium-loaded active carbon Download PDF

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CN104759254A
CN104759254A CN201510177424.XA CN201510177424A CN104759254A CN 104759254 A CN104759254 A CN 104759254A CN 201510177424 A CN201510177424 A CN 201510177424A CN 104759254 A CN104759254 A CN 104759254A
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active carbon
chromium
valve
toluene
adsorption
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CN104759254B (en
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黄艳芳
刘志军
刘金红
丁彩峰
朱小刚
刘芳
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Nantong Acetic Acid Chemical Co Ltd
Nantong Vocational College
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Nantong Acetic Acid Chemical Co Ltd
Nantong Vocational College
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Abstract

The invention discloses a preparation method of chromium-loaded active carbon as well as the condition and device of methylbenzene adsorption using the chromium-loaded active carbon. The preparation comprises the following steps: (1) preparing impregnating liquid, namely dissolving weighed chromium salt into acid solution of 0.1-10mol/L and preparing the impregnating liquid at the temperature of 20-80 DEG C; (2) impregnating the active carbon, namely by using an isovolumetric impregnating method or excessive impregnating method, impregnating the active carbon with the particle size being 150 microns-1700 microns in the prepared impregnating solution, wherein the mass ratio of the chromium to the active carbon is 0.03 to 0.3 after impregnating; (3) impregnating, namely placing the solution after the active carbon is impregnated at room temperature for 3-15 hours; and (4) drying, namely placing the impregnated active carbon in nitrogen of 150 DEG C for 4-8 hours, so as to obtain the chromium-loaded active carbon. According to the preparation method, the metal chromium element is impregnated on the active carbon to prepare the chromium-loaded active carbon; the adsorption capability of the active carbon is improved and the saturated adsorption of the active carbon to methylbenzene can be increased by 20-110%.

Description

Carry the preparation method of chromium active carbon and adsorb condition and the device of toluene with it
Technical field
The invention belongs to sorbing material and atmosphere pollution processing technology field, be specifically related to the preparation method of a kind of year chromium active carbon and adsorb condition and the device of toluene with it.
Background technology
Along with the fast development of modern industry, the organic solvents such as the aromatic series such as carrene, toluene, dimethylbenzene, benzene, halogenated hydrocarbons, aldoketones, ester class, alcohols are widely used in the every field such as chemical industry, petrochemical industry, coating, medicine, rubber, resin, printing.These volatile organic solvents have toxicity mostly, and wherein quite a few finally enters in air with the form of organic exhaust gas, causes air to be heavily polluted.If dealt with improperly, namely cause raw-material loss, again contaminated environment, more seriously to the infringement of human health.The pay attention to day by day of Environmental protection work, improving constantly atmospheric emission standard, makes the recycling of organic exhaust gas imperative.From the organic exhaust gas of industrial discharge, reclaim organic solvent, namely can reduce the pollution to environment, reclaim again precious resources.
At present, the domestic process recovery method for industrial organic exhaust gas mainly contains: heating power burning method, condensation method, absorption absorption method, wherein adsorbing absorption method is carry out adsorption cleaning with Activated Carbon toward VOCs-Containing Exhausts, be its essence is that the characteristic utilizing active carbon high strength to adsorb is adsorbed onto in active carbon also concentrated the organic solvent in waste gas, directly emptying through charcoal absorption purified gas, this is the process of an Adsorption Concentration, organic solvent is not disposed, and is a physical process.When the organic matter adsorbed reaches the adsorbance of regulation, then stop using, the organic matter after absorption reclaims after desorption.Adsorbent, after absorption is saturated, can be passed through reproducer, recycles.
The characterization of adsorption of active carbon depends on the pore structure of its prosperity and unique surface chemical property.For the absorption property how improving active carbon, researcher starts with from the preparation of new carbon and normal activated carbon modification two aspect, achieves a series of achievement in research.The new carbon being used in adsorbing domain mainly refers to NACF, but its preparation process is often very complicated loaded down with trivial details, and cost is also far above normal activated carbon, and service condition is harsher.Above-mentioned shortcoming constrains NACF widely using in the industry.At present, the industrial material with carbon element for gas removal remains normal activated carbon.
At present, carried active carbon has been used to other systems such as desulfurization or separating ethene-ethane, but not yet for adsorbing toluene system, for the many employings of the adsorbing and removing of toluene in gas is the active carbon of non-carried metal, as Chinese invention patent 03159299.6 provides a kind of method for recovering toluene from exhausted air, toluene recovery rate can reach 65%, the toluene level < 40mg/m of the purified gas after purification 3, reach GB secondary standard.At normal temperatures, the saturated extent of adsorption of active carbon can meet general adsorption entails, but at high temperature the adsorbance of active carbon is very little.
Summary of the invention
The object of the invention is to provide the preparation method of a kind of year chromium active carbon and adsorbs condition and the device of toluene with it.
For achieving the above object, the technical solution used in the present invention is: the preparation method of a kind of year chromium active carbon, comprises the steps:
(1) maceration extract is prepared: be dissolved in the acid solution of 0.1 ~ 10mol/L by load weighted chromic salts, at the temperature of 20 ~ 80 DEG C, be mixed with maceration extract;
(2) Immesion active carbon: adopt infusion process, the active carbon of granularity 150 μm ~ 1700 μm be impregnated in above-mentioned maceration extract, after dipping, the mass ratio of chromium element and active carbon is 0.03 ~ 0.3;
(3) flood: the solution after Immesion active carbon is put 3 ~ 15 hours in ambient temperatare;
(4) dry: the active carbon after dipping to be positioned in 150 DEG C of nitrogen dry 4 ~ 8 hours, obtains carrying a chromium active carbon.
Wherein, the chromic salts in described step (1) is one or more mixing in chromium chloride, chromic nitrate, chromium sulfate, chromic acetate, chromium+oxalic acid;
Acid solution is the hydrochloric acid solution of 1mol/L.
Wherein, the infusion process in described step (2) is the one in equi-volume impregnating and excessive infusion process.
Wherein, the active carbon in described step (2) is wooden, ature of coal, shell or coconut husk granular activated carbon.
Wherein, in described step (2), after dipping, the mass ratio of chromium and active carbon is 0.1;
In described step (3), dip time is 12h, if auxiliary with ultrasonic vibration in dipping process, dip time can shorten 2 ~ 5 hours.
The embodiment of the present invention also provides a kind of and utilizes the above-mentioned adsorption conditions carrying chromium charcoal absorption toluene, for: toluene level < 8% in toluene source of the gas, adsorptive pressure 0 ~ 1MPa, gas flow < 400mL/min, adsorption temp 40 ~ 200 DEG C.
The embodiment of the present invention also provides a kind of and utilizes the above-mentioned device carrying chromium charcoal absorption toluene, comprise nitrogen cylinder, pressure-reducing valve, toluene gasification installation, the first valve, the second valve, the 3rd valve, the first rotor flowmeter, the second spinner flowmeter, in establish the adsorption column, heating furnace, precision pressure gauge, the second Mini-adjustable valve and the six-way valve that carry chromium active carbon;
Described adsorption column is located in heating furnace;
Described pressure-reducing valve is arranged on the pipeline of connection nitrogen cylinder and toluene gasification installation;
Described first valve and the first rotor flowmeter are set in turn on the pipeline of the air inlet being communicated with toluene gasification installation and adsorption column;
Described second valve is arranged in the air inlet duct of connection nitrogen cylinder and adsorption column;
Described 3rd valve is arranged on the pipeline of connection second valve and adsorption column outlet;
The air inlet place of adsorption column is located at by described precision pressure gauge;
The gas outlet of described adsorption column is provided with described second Mini-adjustable valve by one and is connected with six-way valve with the pipeline of the second spinner flowmeter, and purified gas is emptying after flowing through described six-way valve.
The above-mentioned device carrying chromium charcoal absorption toluene also comprises programmed temperature control instrument, and it is connected with described heating furnace.
The above-mentioned device carrying chromium charcoal absorption toluene also comprises the first Mini-adjustable valve, its be arranged at be connected with the air inlet of described adsorption column, for regenerating time on-line analysis tracheae.
The above-mentioned device carrying chromium charcoal absorption toluene also comprises gas chromatograph, and purified gas, to pass into the hydrogen of described six-way valve for carrier gas, flows out to gas chromatograph from described six-way valve.
The above-mentioned device carrying chromium charcoal absorption toluene comprises 3 paths, respectively:
(1) on-line analysis path during regeneration, pressure-reducing valve, the second valve, the 3rd valve and the first Mini-adjustable valve are opened, first valve and the second Mini-adjustable valve are closed, nitrogen is as sweep gas, flow into below adsorption column, top is flowed out, and the toluene replacement adsorbed on the sorbent out, desorption gas enters gas-chromatography on-line analysis.
(2) containing the purification path of toluene source of the gas, pressure-reducing valve, the first valve and the second Mini-adjustable valve are opened, second valve, the 3rd valve and the first Mini-adjustable valve are closed, normality is flow through with nitrogen cylinder the nitrogen come after liquid toluene gasifies in toluene gasification installation to mix, then purify the toluene in it via adsorption column, purified gas is emptying by six-way valve.
(3) adsorption effect inspection path, pressure-reducing valve, the first valve and the second Mini-adjustable valve are opened, second valve, the 3rd valve and the first Mini-adjustable valve are closed, normality is flow through with nitrogen cylinder the nitrogen come after liquid toluene gasifies in toluene gasification installation to mix, then the toluene in it is purified via adsorption column, purified gas is that carrier gas is admitted to gas chromatograph with hydrogen, and the chromatogram shown by gas chromatograph is to analyze the adsorption effect of adsorption column.
The theoretical foundation that chromium charcoal absorption toluene is carried in the present invention's utilization is: in toluene, the conjugatedπbond of phenyl ring can overlap to form σ key with the outer s unoccupied orbital of chromium ion, meanwhile, and the π of benzene *the d Orbital Overlap of antibonding unoccupied orbital and metal forms π complex bonds.This π Absorptive complex wave active force is better than physisorption power.Therefore in some occasion, such as, under high temperature, when physisorption power is very weak, π Absorptive complex wave still can play a role, thus strengthens the adsorption capacity of adsorbent.And π Absorptive complex wave active force is weaker than chemisorption power, therefore the regeneration of adsorbent can be realized again very easily.
Because technique scheme is used, the present invention compared with prior art has following advantages:
Metallic element chromium impregnated on active carbon by the present invention, makes and carries chromium active carbon, improves the adsorption capacity of active carbon, can improve 20% ~ 110% to the saturated extent of adsorption of toluene.
Accompanying drawing explanation
Fig. 1 is the structural representation utilizing the device carrying chromium charcoal absorption toluene in the present invention;
Fig. 2 is the characterization of adsorption comparison diagram of adsorbent of identical adsorption conditions in the embodiment of the present invention one, different loads amount.
Wherein: 1, nitrogen cylinder; 2, pressure-reducing valve; 3, toluene gasification installation; 4, the first valve; 5, the second valve; 6, the first rotor flowmeter; 7, the second spinner flowmeter; 8, adsorption column; 9, heating furnace; 10, programmed temperature control instrument; 11, precision pressure gauge; 12, the first Mini-adjustable valve; 13, the second Mini-adjustable valve; 14, gas chromatograph; 15, six-way valve; 16, the 3rd valve.
Detailed description of the invention
Below in conjunction with drawings and Examples, the invention will be further described:
A preparation method for year chromium active carbon, comprises the steps:
(1) maceration extract is prepared: be dissolved in the acid solution of 0.1 ~ 10mol/L by load weighted chromic salts, at the temperature of 20 ~ 80 DEG C, be mixed with maceration extract;
Wherein, chromic salts is chromium chloride, the hydrochloric acid solution of acid solution preferably 1mol/L.
(2) Immesion active carbon: adopt equi-volume impregnating or excessive infusion process, the active carbon of granularity 150 μm ~ 1700 μm be impregnated in above-mentioned maceration extract, after dipping, the mass ratio of chromium element and active carbon is 0.03 ~ 0.3;
Wherein, active carbon can select one or more mixing in wooden, ature of coal, shell and coconut husk granular activated carbon.After dipping, the mass ratio of the optimum of chromium and active carbon is 0.1.
(3) flood: the solution after Immesion active carbon is put 3 ~ 15 hours in ambient temperatare;
Wherein, optimum dip time is 12h, if auxiliary with ultrasonic vibration in dipping process, dip time can shorten 2 ~ 5 hours.
(4) dry: the active carbon after dipping to be positioned in 150 DEG C of nitrogen dry 4 ~ 8 hours, obtains carrying a chromium active carbon.
The present invention also provides a kind of and utilizes the above-mentioned adsorption conditions carrying chromium charcoal absorption toluene, for: toluene level < 8% in toluene source of the gas, adsorptive pressure 0 ~ 1MPa, gas flow < 400mL/min, adsorption temp 40 ~ 200 DEG C.
The present invention also provides a kind of and utilizes the above-mentioned device carrying chromium charcoal absorption toluene, structure as shown in Figure 1, comprise nitrogen cylinder 1, pressure-reducing valve 2, toluene gasification installation 3, first valve 4, second valve 5, the first rotor flowmeter 6, second spinner flowmeter 7, in establish and carry the adsorption column 8 of chromium active carbon, heating furnace 9, its programmed temperature control instrument 10 be connected with described heating furnace 9, precision pressure gauge 11, first Mini-adjustable valve 12, second Mini-adjustable valve 13, gas chromatograph 14, six-way valve 15 and the 3rd valve 16.
Described adsorption column is located in heating furnace.
Described pressure-reducing valve is arranged on the pipeline of connection nitrogen cylinder and toluene gasification installation.
Described first valve is set in turn on the pipeline of the air inlet being communicated with toluene gasification installation and adsorption column with the first rotor flowmeter.
Described second valve is arranged in the air inlet duct of connection nitrogen cylinder and adsorption column.
Described 3rd valve is arranged on the pipeline of connection second valve and adsorption column outlet;
The air inlet place of adsorption column is located at by described precision pressure gauge.
Described first Mini-adjustable valve be arranged at be connected with the air inlet of described adsorption column, for regenerating time on-line analysis tracheae.
The gas outlet of described adsorption column is provided with described second Mini-adjustable valve by one and is connected with six-way valve with the pipeline of the second spinner flowmeter, and purified gas is emptying after flowing through described six-way valve.
Purified gas, to pass into the hydrogen of described six-way valve for carrier gas, flows out to gas chromatograph from described six-way valve.
The above-mentioned device carrying chromium charcoal absorption toluene comprises 3 paths, respectively:
(1) on-line analysis path during regeneration, pressure-reducing valve, the second valve, the 3rd valve and the first Mini-adjustable valve are opened, first valve and the second Mini-adjustable valve are closed, nitrogen is as sweep gas, flow into below adsorption column, top is flowed out, and the toluene replacement adsorbed on the sorbent out, desorption gas enters gas-chromatography on-line analysis.
(2) containing the purification path of toluene source of the gas, pressure-reducing valve, the first valve and the second Mini-adjustable valve are opened, second valve, the 3rd valve and the first Mini-adjustable valve are closed, normality is flow through with nitrogen cylinder the nitrogen come after liquid toluene gasifies in toluene gasification installation to mix, then purify the toluene in it via adsorption column, purified gas is emptying by six-way valve.
(3) adsorption effect inspection path, pressure-reducing valve, the first valve and the second Mini-adjustable valve are opened, second valve, the 3rd valve and the first Mini-adjustable valve are closed, normality is flow through with nitrogen cylinder the nitrogen come after liquid toluene gasifies in toluene gasification installation to mix, then the toluene in it is purified via adsorption column, purified gas is that carrier gas is admitted to gas chromatograph with hydrogen, and the chromatogram shown by gas chromatograph is to analyze the adsorption effect of adsorption column.
For illustrating that the adsorbance of the of the present invention year relative normal activated carbon of chromium active carbon increases, be described with several embodiment below.
Embodiment one: (active carbon without load is designated as AC for 20 ~ 40 object cocoanut active charcoals 0), chromium chloride is dissolved in the HCl solution of the 1mol/L of certain volume, then by AC 0dipping wherein.After ambient temperatare puts 12h, dry in 150 DEG C of nitrogen.In dipping system, the mass ratio of chromium and active carbon is respectively 0.052:1,0.104:1,0.156:1,0.208:1, and gained acticarbon is designated as AC respectively 1, AC 2, AC 3and AC 4.
By AC 0, AC 1, AC 2, AC 3and AC 4all carry out the adsorption experiment of toluene, adsorption conditions is: in toluene source of the gas, toluene level is 5%, and adsorptive pressure is 0.2MPa, gas flow 250mL/min.
When identical adsorption conditions, different loads amount, carry chromium active carbon to the adsorption capacity of toluene as shown in table 1 and Fig. 2.
Table 1: the characterization of adsorption of different loads amount adsorbent
From table 1 and Fig. 2, under identical adsorption conditions, the adsorbance that chromium active carbon compares unmodified active carbon of carrying of different loads amount all has raising in various degree, and increase rate is 20% ~ 110%.
Embodiment two: chromium chloride is dissolved in the HCl solution of the 1mol/L of certain volume, then flooded wherein by active carbon AC, in dipping system, the mass ratio of chromium and active carbon is 0.07:1, after ambient temperatare puts 12h, dry in 150 DEG C of nitrogen, then carry out the adsorption experiment of toluene.
In toluene source of the gas, toluene level is 3%, and adsorptive pressure is 0.2MPa, gas flow 250mL/min, adsorption temp is 40 DEG C, the saturated extent of adsorption of toluene reaches 192.46mg/g active carbon, than the adsorbance 155.91 mg/g active carbon of active carbon unmodified under similarity condition, improves 23.44%.
Embodiment three: chromium chloride is dissolved in the HCl solution of the 1mol/L of certain volume, then flooded wherein by active carbon AC, in dipping system, the mass ratio of chromium and active carbon is 0.18:1, after ambient temperatare puts 12h, dry in 150 DEG C of nitrogen, then carry out the adsorption experiment of toluene.
In toluene source of the gas, toluene level is 5%, and adsorptive pressure is 0.6MPa, gas flow 300mL/min, adsorption temp is 120 DEG C, the saturated extent of adsorption of toluene reaches 153.84mg/g active carbon, than the adsorbance 101.68mg/g active carbon of active carbon unmodified under similarity condition, improves 51.30%.
Embodiment four: chromium chloride is dissolved in the HCl solution of the 1mol/L of certain volume, then flooded wherein by active carbon AC, in dipping system, the mass ratio of chromium and active carbon is 0.25:1, after ambient temperatare puts 12h, dry in 150 DEG C of nitrogen, then carry out the adsorption experiment of toluene.
In toluene source of the gas, toluene level is 5%, and adsorptive pressure is 0.3MPa, gas flow 250mL/min, adsorption temp is 200 DEG C, the saturated extent of adsorption of toluene reaches 107.50mg/g active carbon, than the adsorbance 60.90mg/g active carbon of active carbon unmodified under the same terms, improves 76.52%.
The above embodiments two, three, four describe different adsorption conditions, different loads amount, and the saturated extent of adsorption carrying the relatively unmodified active carbon of chromium active carbon all increases.
The above is the preferred embodiment of the present invention; should be understood that; for those skilled in the art; under the prerequisite not departing from principle of the present invention; some improvement or replacement can also be made; such as chromium chloride is transformed to other chromic salts, adopts the preparation method in the present invention to prepare the modified activated carbon of carried metal chromium, also should be considered as protection scope of the present invention.

Claims (10)

1. carry a preparation method for chromium active carbon, it is characterized in that, comprise the steps:
(1) maceration extract is prepared: be dissolved in the acid solution of 0.1 ~ 10mol/L by load weighted chromic salts, at the temperature of 20 ~ 80 DEG C, be mixed with maceration extract;
(2) Immesion active carbon: adopt infusion process, the active carbon of granularity 150 μm ~ 1700 μm be impregnated in above-mentioned maceration extract, after dipping, the mass ratio of chromium element and active carbon is 0.03 ~ 0.3;
(3) flood: the solution after Immesion active carbon is put 3 ~ 15 hours in ambient temperatare;
(4) dry: the active carbon after dipping to be positioned in 150 DEG C of nitrogen dry 4 ~ 8 hours, obtains carrying a chromium active carbon.
2. the preparation method of according to claim 1 year chromium active carbon, is characterized in that, the chromic salts in described step (1) is one or more mixing in chromium chloride, chromic nitrate, chromium sulfate, chromic acetate, chromium+oxalic acid;
Acid solution is the hydrochloric acid solution of 1mol/L.
3. the preparation method of according to claim 1 year chromium active carbon, is characterized in that, the infusion process in described step (2) is the one in equi-volume impregnating and excessive infusion process.
4. the preparation method of according to claim 1 year chromium active carbon, is characterized in that, the active carbon in described step (2) is wooden, ature of coal, shell or coconut husk granular activated carbon.
5. the preparation method of according to claim 1 year chromium active carbon, is characterized in that, in described step (2), after dipping, the mass ratio of chromium and active carbon is 0.1;
In described step (3), dip time is 12h, if auxiliary with ultrasonic vibration in dipping process, dip time can shorten 2 ~ 5 hours.
6. one kind utilizes the adsorption conditions carrying chromium charcoal absorption toluene according to any one of Claims 1 to 5, it is characterized in that, toluene level < 8% in toluene source of the gas, adsorptive pressure 0 ~ 1MPa, gas flow < 400mL/min, adsorption temp 40 ~ 200 DEG C.
7. one kind utilizes the device carrying chromium charcoal absorption toluene according to any one of Claims 1 to 5, it is characterized in that, comprise nitrogen cylinder, pressure-reducing valve, toluene gasification installation, the first valve, the second valve, the 3rd valve, the first rotor flowmeter, the second spinner flowmeter, in establish and carry the adsorption column of chromium active carbon, heating furnace, precision pressure gauge, the second Mini-adjustable valve and six-way valve;
Described adsorption column is located in heating furnace;
Described pressure-reducing valve is arranged on the pipeline of connection nitrogen cylinder and toluene gasification installation;
Described first valve and the first rotor flowmeter are set in turn on the pipeline of the air inlet being communicated with toluene gasification installation and adsorption column;
Described second valve is arranged in the air inlet duct of connection nitrogen cylinder and adsorption column;
Described 3rd valve is arranged on the pipeline of connection second valve and adsorption column outlet;
The air inlet place of adsorption column is located at by described precision pressure gauge;
The gas outlet of described adsorption column is provided with described second Mini-adjustable valve by one and is connected with six-way valve with the pipeline of the second spinner flowmeter, and purified gas is emptying after flowing through described six-way valve.
8. the device of according to claim 7 year chromium charcoal absorption toluene, is characterized in that, also comprise programmed temperature control instrument, and it is connected with described heating furnace.
9. the device of according to claim 7 year chromium charcoal absorption toluene, is characterized in that, also comprises the first Mini-adjustable valve, its be arranged at be connected with the air inlet of described adsorption column, for regenerating time on-line analysis tracheae.
10. the device of according to claim 7 year chromium charcoal absorption toluene, is characterized in that, also comprise gas chromatograph, purified gas with the hydrogen passing into described six-way valve for carrier gas flows out to gas chromatograph from described six-way valve.
CN201510177424.XA 2015-04-15 2015-04-15 Preparation method of chromium-loaded active carbon as well as condition and device of methylbenzene adsorption using chromium-loaded active carbon Expired - Fee Related CN104759254B (en)

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Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107519944A (en) * 2017-09-06 2017-12-29 新地能源工程技术有限公司 A kind of catalyst continuous producing apparatus and method
CN112875699A (en) * 2021-02-07 2021-06-01 西安科技大学 Preparation method and application of special steel slag-based biomass activated carbon

Citations (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1307930A (en) * 2000-12-18 2001-08-15 中国人民解放军63971部队 Chromium-free soaked active carbon and its preparation
CN1377729A (en) * 2001-04-05 2002-11-06 上海欧臣环境高科技有限责任公司 Purifying material capable of removing organic gas in air and its preparing method
US20030102267A1 (en) * 2001-11-30 2003-06-05 Kim Dae K. Process for purification of aromatic monomers
CN1597051A (en) * 2003-09-15 2005-03-23 傅太平 Method for recovering toluene from exhausted air
CN1765489A (en) * 2004-10-29 2006-05-03 中国石油化工股份有限公司 Supported type active carbon and its preparation method
CN1994555A (en) * 2006-12-15 2007-07-11 四川省林业科学研究院 Impregnated activated carbon and preparation method thereof
CN102814162A (en) * 2011-06-08 2012-12-12 无锡百奥科环境科技有限公司 Modified activated carbon adsorption scavenger and preparation method
CN103495384A (en) * 2013-08-30 2014-01-08 蚌埠德美过滤技术有限公司 Modified activated carbon air purification adsorbent and its preparation method
WO2013169811A4 (en) * 2012-05-07 2014-04-03 Biogenic Reagents LLC Biogenic activated carbon and methods of making and using same

Patent Citations (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1307930A (en) * 2000-12-18 2001-08-15 中国人民解放军63971部队 Chromium-free soaked active carbon and its preparation
CN1377729A (en) * 2001-04-05 2002-11-06 上海欧臣环境高科技有限责任公司 Purifying material capable of removing organic gas in air and its preparing method
US20030102267A1 (en) * 2001-11-30 2003-06-05 Kim Dae K. Process for purification of aromatic monomers
CN1597051A (en) * 2003-09-15 2005-03-23 傅太平 Method for recovering toluene from exhausted air
CN1765489A (en) * 2004-10-29 2006-05-03 中国石油化工股份有限公司 Supported type active carbon and its preparation method
CN1994555A (en) * 2006-12-15 2007-07-11 四川省林业科学研究院 Impregnated activated carbon and preparation method thereof
CN102814162A (en) * 2011-06-08 2012-12-12 无锡百奥科环境科技有限公司 Modified activated carbon adsorption scavenger and preparation method
WO2013169811A4 (en) * 2012-05-07 2014-04-03 Biogenic Reagents LLC Biogenic activated carbon and methods of making and using same
CN103495384A (en) * 2013-08-30 2014-01-08 蚌埠德美过滤技术有限公司 Modified activated carbon air purification adsorbent and its preparation method

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107519944A (en) * 2017-09-06 2017-12-29 新地能源工程技术有限公司 A kind of catalyst continuous producing apparatus and method
CN107519944B (en) * 2017-09-06 2023-02-21 新地能源工程技术有限公司 Catalyst continuous production equipment and method
CN112875699A (en) * 2021-02-07 2021-06-01 西安科技大学 Preparation method and application of special steel slag-based biomass activated carbon

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