EP1866246A1 - Production of activated char using hot gas - Google Patents
Production of activated char using hot gasInfo
- Publication number
- EP1866246A1 EP1866246A1 EP06738006A EP06738006A EP1866246A1 EP 1866246 A1 EP1866246 A1 EP 1866246A1 EP 06738006 A EP06738006 A EP 06738006A EP 06738006 A EP06738006 A EP 06738006A EP 1866246 A1 EP1866246 A1 EP 1866246A1
- Authority
- EP
- European Patent Office
- Prior art keywords
- coal
- activated char
- gas stream
- fuel
- carbonaceous feedstock
- 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.)
- Withdrawn
Links
Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/02—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
- B01J20/20—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising free carbon; comprising carbon obtained by carbonising processes
-
- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01B—NON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
- C01B32/00—Carbon; Compounds thereof
- C01B32/30—Active carbon
- C01B32/312—Preparation
- C01B32/336—Preparation characterised by gaseous activating agents
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/02—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by adsorption, e.g. preparative gas chromatography
- B01D53/06—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by adsorption, e.g. preparative gas chromatography with moving adsorbents, e.g. rotating beds
- B01D53/10—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by adsorption, e.g. preparative gas chromatography with moving adsorbents, e.g. rotating beds with dispersed adsorbents
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/46—Removing components of defined structure
- B01D53/64—Heavy metals or compounds thereof, e.g. mercury
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/30—Processes for preparing, regenerating, or reactivating
- B01J20/3078—Thermal treatment, e.g. calcining or pyrolizing
-
- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01B—NON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
- C01B3/00—Hydrogen; Gaseous mixtures containing hydrogen; Separation of hydrogen from mixtures containing it; Purification of hydrogen; Reversible storage of hydrogen
- C01B3/02—Production of hydrogen; Production of gaseous mixtures containing hydrogen
- C01B3/32—Production of hydrogen; Production of gaseous mixtures containing hydrogen by reaction of gaseous or liquid organic compounds with gasifying agents, e.g. water, carbon dioxide or air
- C01B3/34—Production of hydrogen; Production of gaseous mixtures containing hydrogen by reaction of gaseous or liquid organic compounds with gasifying agents, e.g. water, carbon dioxide or air by reaction of hydrocarbons with gasifying agents
-
- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01B—NON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
- C01B32/00—Carbon; Compounds thereof
- C01B32/30—Active carbon
- C01B32/39—Apparatus for the preparation thereof
-
- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01B—NON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
- C01B32/00—Carbon; Compounds thereof
- C01B32/40—Carbon monoxide
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10J—PRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
- C10J3/00—Production of combustible gases containing carbon monoxide from solid carbonaceous fuels
- C10J3/46—Gasification of granular or pulverulent flues in suspension
- C10J3/48—Apparatus; Plants
- C10J3/485—Entrained flow gasifiers
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2253/00—Adsorbents used in seperation treatment of gases and vapours
- B01D2253/10—Inorganic adsorbents
- B01D2253/102—Carbon
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2253/00—Adsorbents used in seperation treatment of gases and vapours
- B01D2253/25—Coated, impregnated or composite adsorbents
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2257/00—Components to be removed
- B01D2257/60—Heavy metals or heavy metal compounds
- B01D2257/602—Mercury or mercury compounds
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2258/00—Sources of waste gases
- B01D2258/02—Other waste gases
- B01D2258/0283—Flue gases
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10J—PRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
- C10J2300/00—Details of gasification processes
- C10J2300/09—Details of the feed, e.g. feeding of spent catalyst, inert gas or halogens
- C10J2300/0913—Carbonaceous raw material
- C10J2300/093—Coal
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10J—PRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
- C10J2300/00—Details of gasification processes
- C10J2300/09—Details of the feed, e.g. feeding of spent catalyst, inert gas or halogens
- C10J2300/0953—Gasifying agents
- C10J2300/0959—Oxygen
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10J—PRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
- C10J2300/00—Details of gasification processes
- C10J2300/09—Details of the feed, e.g. feeding of spent catalyst, inert gas or halogens
- C10J2300/0953—Gasifying agents
- C10J2300/0973—Water
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10J—PRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
- C10J2300/00—Details of gasification processes
- C10J2300/18—Details of the gasification process, e.g. loops, autothermal operation
- C10J2300/1846—Partial oxidation, i.e. injection of air or oxygen only
Definitions
- the present invention relates generally to methods and systems to produce activated char such that production can occur at or near the end use point .
- Activated carbon is a widely used adsorbent in industrial processes to remove contaminants from gas or liquid streams. For example, attempts to meet currently pending mercury emissions limits for fossil fuel fired power plants by injecting powdered activated carbon (PAC) into the flue gas upstream of a particulate control device in order to remove contaminants from the flue gas are being investigated.
- PAC powdered activated carbon
- the removal of mercury from flue gas streams from combustion processes is of significant interest. The toxicity of mercury to humans has long been known. An example of the devastating effects of mercury exposure occurred in Minamata, Japan in the 1950' s where organic mercury byproducts of acetaldehyde production were discharged into the local bay, and were ingested and metabolized by fish.
- Coals used for various combustion processes typically contain about 0.1 ppm mercury. In the United States alone, about 50 tons of mercury are discharged as vapor in stack gas every year. Through chemical and biological processes, such mercury can become concentrated by many thousand-fold into fish, thus entering human food supplies at harmful levels. In December 2000, the Environmental Protection Agency
- PAC is typically produced from carbonaceous starting materials such as coal, wood, biomass materials, nutshells (e.g., walnut shells, palm nut) or nut hulls (e.g., coconut) that initially do not have high adsorptive characteristics.
- the carbonaceous starting materials are converted into PAC materials exhibiting higher adsorptive properties by energy and capital intensive processes that include pyrolyzing the feedstock in a rotary kiln, activating the carbon with an activation media (i.e. steam), and grinding or pulverizing the resulting char.
- the activated carbon material must then be shipped to its end use point, such as a coal-fired power plant.
- U.S. Patent No. 6,595,147 to Teller et al relates to adding a carbonaceous char to the flue gas while it is still within a resource recovery unit at a temperature high enough to devolatilize the material to form activated char in situ.
- Attempts have also been made to use carbon found in fly ash to capture mercury from flue gas in coal-fired processes.
- U.S. Patent No. 5,787,823 to Knowles proposes a method v in which carbon-containing fly ash is captured in a cyclone upstream of a conventional particulate control device (PCD) . The captured material is then injected into a duct to capture mercury.
- PCD particulate control device
- the present invention provides methods and systems for production of activated char that are sufficiently flexible and efficient such that production can occur near or at the end use site of the activated char.
- the methods and systems provided herein can also be used in other arrangements.
- the present invention can be implemented for a central facility to produce activated char as described herein and to serve multiple utilities or the like.
- the present invention can be used by a utility to make activated char for its own plant and ship excess activated char to other locations .
- Such methods and systems include preheating a gas mixture to high temperatures using an oxy-fuel, an oxygen-enriched air-fuel or an air-fuel burner to form a hot gas stream.
- the hot gas stream is mixed and reacted with a carbonaceous feedstock (i.e. carbonaceous raw material) in a manner such that the carbonaceous feedstock is devolatilized and partially combusted to thereby produce an active residual char that can be implemented in a variety of applications that use activated carbon.
- a carbonaceous feedstock i.e. carbonaceous raw material
- the present invention includes a method to produce activated char at or near the end use point.
- a hot (preferably about 2000-3000 0 F) oxidizing gas stream mixes and reacts with a ground or pulverized carbonaceous feedstock to create powdered activated char with adsorbent properties similar to powdered activated carbon produced with the same carbonaceous feedstock.
- an inert gas could be heated and used to pyrolize the feedstock.
- the hot gas stream could have any desirable oxygen content or no oxygen at all (e.g. CO 2 and/or H 2 O) . It could be strongly oxidative, mildly oxidative or even reductive.
- a heat source for thermal treatment of the carbonaceous feedstock may be suitable for use in the present invention. It will be appreciated by those skilled in the art that such adsorptive properties are dependent on the feedstock utilized. It will also appreciated by those skilled in the art that while adsorptive properties of an activated char may be sufficient for some applications, the activated char may need to be altered for other applications.
- the present invention thus provides several benefits including, but not limited to, the ability to produce activated char at or near the end use point, lower cost and more efficient production methods for activated char relative to large, rotary kiln methods and an option to use a carbonaceous feedstock for producing activated char that may be different from the fuel used in the main combustion process of a given facility.
- the present invention provides the flexibility to alter activated char properties for a specific application at or near the end use point.
- the surface area of the activated char produced in accordance with the present invention may be less than, and in some cases significantly less than the surface area of currently and commercially available PACs. Given the efficient and flexible methods provided herein, however, the overall economics may still favor use of activated char produced in accordance with the present invention, even in situations where more activated char may be necessary relative to currently and commercially available PACs.
- the hot gas stream which can include steam, oxygen, or mixtures of gasses, is produced by preheating a gas stream with an oxy-fuel, an oxygen- enriched air-fuel or an air-fuel burner to create a hot gas mixture.
- the high turbulence from the hot-gas serves to rapidly mix the carbonaceous feedstock with the hot-gas.
- the elevated temperature and the oxygen concentration of the hot gas cause rapid ignition, devolatilization and partial oxidation of the carbonaceous feedstock.
- the present invention provides methods and systems for separating activated char production from the main combustion process, thereby making it possible to produce activated char having properties (e.g., adsorptive) desirable for a specific application.
- the present invention enables the onsite (or near end use) production of activated char for a pulverized fuel- fired utility for the removal of mercury in a flue gas stream.
- the present invention enables the production of activated char to be tailored for use in a fixed bed arrangement for waste water treatment to remove hydrocarbons and other contaminants.
- Another advantage of the present invention is the ability to use the partial oxidation gas as a useful fuel in the process, either by recirculating this material to the hot gas burner or by firing it into a boiler that may, or may not, be part of the process.
- the gas products could be sent to the boiler as a reburning fuel for NO x control .
- the hot oxygen or hot gas burner as used in accordance with the present invention allows for on-site activated char production.
- the combination of high temperatures and good mixing achieved with this burner allows activated char production with relatively small, simple process equipment (especially as compared to the rotary kilns currently used to produce PAC) .
- activation of the activated char of the present invention occurs as a result of the process as opposed to rotary kiln methods which typically require separate activation steps .
- the present invention can significantly reduce the cost of activated char for the end user by both improving the production efficiency and versatility as well as minimizing shipping requirements .
- Figure 1 illustrates a schematic view of apparatus to produce activated carbon in accordance with one embodiment of the present invention
- Figure 2 illustrates a schematic view of apparatus to produce activated carbon in accordance with an alternative embodiment of the invention
- Figure 3 illustrates a schematic view of apparatus to produce activated carbon in accordance with yet another alternative embodiment of the invention.
- the present invention provides methods and systems for production of activated char near or at the end use point of the activated char.
- Such methods and systems include preheating a gas mixture to high temperatures using an oxy-fuel, an oxygen-enriched air- fuel or an air-fuel burner to form a hot gas stream.
- the hot gas stream is mixed and reacted with a carbonaceous feedstock (i.e. carbonaceous raw material) in a manner such that the carbonaceous feedstock is devolatilized and partially combusted to thereby produce an active residual char that can be implemented in applications that use activated carbon.
- a carbonaceous feedstock i.e. carbonaceous raw material
- Use of hot gas and ground carbonaceous feedstock allow the equipment to be minimized, thus allowing the activated carbon to be produced at or near the point of use, for example to reduce utility boiler mercury emissions from flue gas.
- the present invention includes a method to produce activated char at or near the end use point.
- a hot (preferably, 2000-3000 0 F) oxidizing gas stream mixes and reacts with a ground or pulverized carbonaceous feedstock to create powdered activated char with adsorbent properties similar to activated char produced with the same carbonaceous feedstock from typical methods such as rotary kiln processes. It will be appreciated by those skilled in the art that such adsorptive properties are dependent on the feedstock utilized. It will also be appreciated by those skilled in the art that while adsorptive properties of an activated char may be sufficient for some applications, the activated char may need to be altered for other applications .
- the present invention thus provides several benefits including, but not limited to, the ability to produce activated ch ⁇ cr at or near the end use point, lower cost and more efficient production methods for activated char relative to large, rotary kiln methods and an option to use a carbonaceous feedstock for producing activated char that may be different from the coal used in the main combustion process of a given facility. Consequently, the present invention provides the flexibility to alter activated char properties for a specific application at or near the end use point.
- the hot gas stream which can include steam, oxygen, or mixtures of gasses, is produced by preheating a gas stream with an oxy-fuel, an oxygen- enriched air-fuel or an air-fuel burner to create a hot gas mixture. The gas mixture is then rapidly mixed with the carbonaceous feedstock.
- the elevated temperature and the oxygen concentration of the hot gas cause rapid ignition, devolatilization and partial oxidation of the carbonaceous feedstock.
- the present invention thus provides methods and systems for separating activated char production from the main combustion process, thereby making it possible to produce activated char having properties (e.g., adsorptive) desirable for a specific application.
- the present invention enables the production of activated char for a pulverized fuel -fired utility for the removal of mercury in a flue gas stream.
- the present invention enables the production of activated char to be tailored for use in a fixed bed arrangement for waste water treatment to remove hydrocarbons, water and other contaminants.
- Another advantage of the present invention is the ability to use the partial oxidation gas as a useful fuel in the process, either by recirculating this material to the hot gas burner or by firing it into a boiler that may, or may not, be part of the process.
- the gas products could be sent to the boiler as a reburning fuel for NO x control .
- the hot oxygen or hot gas burner as used in accordance with the present invention allows for on-site activated char production.
- the combination of high temperatures and good mixing achieved with this burner allows activated char production with very small, relatively simple process equipment (especially as compared to the rotary kilns currently used to produce PAC) .
- activation of the activated char of the present invention occurs as a result of the process as opposed to rotary kiln methods which typically require separate activation steps .
- the present invention can significantly reduce the cost of activated carbon for the end user by both improving the production efficiency and versatility as well as minimizing shipping requirements.
- the present invention can be used to produce activated char suitable for a wide range of industrial processes.
- the optimal configuration for production of activated char for a particular application therefore depends strongly on the end use and the desired char characteristics.
- ratios of hot gas to carbonaceous feedstock, residence time, temperature of the hot gas and additives to the process can be determined based on the intended end use of the activated char and economic factors.
- Burner 1 can be used in a variety of modes, with the burner design being altered as necessary to account for the mode of operation.
- burner 1 is an oxy-fuel burner and operates on fuel 10 and oxidant source 11 to produce a very hot flue gas.
- oxidant 11 is pure oxygen.
- burner 1 is used in an oxygen-enriched mode of operation. More specifically, oxidant 11 has an oxygen concentration less than pure oxygen, but greater than air (e.g, an oxygen concentration of between about 21 and less than 100%) . This embodiment may not be as preferred because of the presence of nitrogen in the air.
- the N 2 in the hot gas can act as a diluent for the reaction with the carbonaceous feedstock and lowers the temperature of the hot gas.
- burner 1 is operated as an air burner.
- Oxidant 11 in this embodiment is air.
- This third embodiment may also be not as preferred as the oxy-fuel mode because of the presence of N 2 in the air.
- the presence of N 2 in the hot gas can act as a diluent for the reaction with the carbonaceous feedstock and lowers the temperature of the hot gas .
- Fuel 10 and oxidant 11 are fed to hot oxygen burner 1.
- Exemplary fuels for fuel 10 include, but are not limited to, natural gas (NG) , methane, propane, hydrogen, light oil, LPG, fuel oil and coke oven gas.
- Fuel 10 can be liquid, but is preferably a gas.
- reactant gas 12 which can be steam, can be used primarily to obtain a desirable composition for gas stream 7 for proper reaction with carbonaceous feedstock in reaction vessel 3.
- Reactant gas 12 is also used to modify the properties of the activated char produced in reaction vessel 3.
- reactant gas 12 can be used to enhance the surface area of the resulting char produced in reaction chamber 3. It will be appreciated that reactant gas 12 may not always be necessary.
- burner 1 can be configured as a hot oxygen burner such as those disclosed in U.S. Patent No. 5,266,024 to Anderson, the entire contents of which are incorporated herein by reference. These hot oxygen burners can produce a high velocity, hot and highly reactive gas mixture known as "hot oxygen” .
- burner 1 Regardless of whether burner 1 is operated in an oxy-fuel, oxygen-enriched or air mode of operation, it is necessary to have a sufficient amount of oxygen in gas stream 7 to burn and partially oxidize carbonaceous feedstock 13 to thereby generate activated char having adsorptive properties for its intended end use.
- the oxidation potential of gas stream 7 is such that carbonaceous feedstock 13 will be partially oxidized and will not be completely consumed in order to generate the desired activated char.
- the amount of oxygen in gas stream 7 is accordingly adjusted based on the amount of desired reaction of feedstock 13. In order to generate the proper amount of oxygen in gas stream 7, the amount of oxidant 11 and/or fuel 10 can then be adjusted.
- Hot oxygen burner 1 produces a high temperature gas stream 7, preferably having a temperature equal to or greater than 800 0 F and most preferably greater than 2000 °F.
- the temperature of hot gas stream 7 is sufficiently high to cause the desired reaction with feedstock 13 (and any carrying material for feedstock 13) .
- Gas stream 7 will primarily contain products of combustion (e.g., CO 2 and H 2 O), residual oxygen, any unreacted gas from gas stream 12 and possibly N 2 if air is used as part of or all of oxidant 11.
- gas stream 7 may contain greater than 70% by volume residual oxygen with the balance being products of combustion.
- ground or pulverized carbonaceous feedstock 13 is fed to mixing section 2 and mixed with hot gas mixture 7.
- Carbonaceous feedstock 13 can be selected from a variety of carbonaceous raw materials such as a variety of coals, petroleum coke, biomass materials (e.g., saw dust) or nutshells (e.g., walnut shells, palm nut) or nut hulls (e.g., coconut) .
- Carbonaceous feedstock 13 can be conveyed to mixing section 2 by a variety of methods .
- Carbonaceous feedstock 13 may be conveyed to mixing section 2 by entrainment in a carrier gas such as air or flue gas, pneumatically supplied, in a slurry such as a water slurry. It will be appreciated by those skilled in the art that other methods of conveying feedstock 13 may also be employed, including supplying the feedstock by itself, without a carrying or conveying material . Any oxygen in the conveying stream should be accounted for in the overall ratio of oxygen to feedstock (i.e., oxygen in the conveying stream combines with the oxygen in stream 7) .
- crushed coal in applications where the activated carbon is to be used in packed beds (e.g., fixed bed arrangement for waste water treatment to remove hydrocarbons and other contaminants from gas or liquid streams) .
- the residence time in reaction vessel 3 will be affected by the selection of feedstock 13.
- the residence time for pulverized feedstocks for dispersed phase modes of adsorption may be on the order of seconds as compared to residence times for crushed feedstocks, which may be on the order of minutes.
- Carbonaceous feedstock 13 is thus ground or pulverized to a desirable size depending on the end use and the equipment design.
- carbonaceous feedstock 13 can be pretreated with a halide salt (e.g., NaBr, KBr) such that the halide salt is dispersed in carbonaceous feedstock 13 prior to being introduced into mixing section 2.
- a halide salt e.g., NaBr, KBr
- the halide salt can improve the activated char characteristics in this type of application. Preferred examples of such treatment can be found in commonly owned U.S. Patent Application No.
- Combined stream 8 thus contains a mixture of feedstock 13 and hot reactant gas 7.
- Stream 8 is introduced into reactor vessel 3.
- Reactor vessel 3 may be a refractory lined pipe with water cooling as needed. Alternatively, water sprays could be used to control the temperature in the reactor.
- additive 14b may include, but is not limited to, steam, N 2 , water and/or material (s) that have a specific activity for an intended use of the activated char.
- stream 14b may be used to adjust the temperature within reactor 3 and/or provide steam for the reaction within reactor 3.
- additive fluid, gas or solid (e.g., lime) 14a may also be mixed with stream 8 prior to injection into reaction vessel 3.
- reaction vessel 3 undergoes devolatilization and partial oxidation, resulting in a product stream containing partial oxidation gasses (e.g., CO and H 2 ) and activated char.
- partial oxidation gasses e.g., CO and H 2
- the partial oxidation gases and activated char exit reactor vessel 3 as stream 9.
- the residence time, ratio of residual oxygen in gas stream 7 to carbonaceous feedstock, and reaction vessel 3 temperature are controlled based on carbonaceous feedstock 13 and desired characteristics of the activated char. For example, if the residence time is too long, or the ratio of hot oxygen to feedstock is too high, too much of the feedstock will be consumed. This can result in reduced product (i.e. activated char) yields. If the residence time or reaction temperatures are too low, the devolatilization and activation may be incomplete, thereby reducing product (i.e. activated char) quality.
- partial oxidation gasses e.g., CO and H 2
- activated char
- Partial oxidation gases and activated char mixture 9 exiting reaction vessel 3 are quenched with a quenching media 15 to cool the products.
- a quenching media 15 may be desirable to include additives (such as a halide salt (e.g, KBr) for use of the activated char in removal of mercury from flue gas streams) in quench media 15 which are mixed with the activated char.
- additives such as a halide salt (e.g, KBr) for use of the activated char in removal of mercury from flue gas streams
- the quenching media could be a fog of water droplets containing the desired additive, or a gas such as nitrogen.
- Cooled mixture 21 may then be separated in a cyclone (or other particulate collection device) 4.
- Cyclone 4 may not always be necessary, for example in direct injection modes of use (see for example, Figure 3) .
- partial oxidation gas 16 may be used in burner 1 as burner fuel 19.
- the activated char produced in accordance with the invention exits cyclone 4 as stream 17 and is processed for its intended end use.
- stream 17 is entrained with a carrier gas (not shown) and injected into the flue gas at a location where the temperature is within the desired range for mercury capture.
- the activated char is then collected along with the fly ash in a particulate control device (PCD) 6 (e.g., electrostatic precipitator or filter fabric) similar to conventional PAC injection for mercury control.
- PCD particulate control device
- the activated char could be injected downstream of the PCD so that the carbon content of the flyash does not destroy the ability to sell flyash as a component for cement.
- activated char in stream 17 is transported to its intended end use (e.g., a fixed bed for waste water treatment) .
- FIG. 1 a schematic representation of a laboratory-scale system to produce activated char in accordance with the present invention is shown in Figure 2.
- burner 1 and reactor 3 are combined within the process equipment .
- carbonaceous feedstock 13 (coal in this example) ignites while still in mixing section 2 (not shown in Figure 2) , indicating ignition is extremely fast.
- Mixing section 2 is attached to reactor vessel 3, which is a refractory lined pipe.
- the design of the reactor 3 can be adjusted to account for proper residence time within the reaction zone 3.
- Additive fluids or gasses 14, such as water or steam, could be mixed anywhere in this embodiment, including mixing upstream of the hot oxygen nozzle of burner 1 or into reaction vessel 3 (as shown in Figure 2) .
- stream 9 may contain CO, H 2 , CO 2 and N 2 (for example, about 40% CO, 20% H 2 , 20% CO 2 and 20% N 2 of the gases on a dry basis in stream 9) in addition to the char produced in the reaction zone 3.
- Nitrogen 15 is used to quench the products which are sent to cyclone 4.
- the use of nitrogen 15 as a quench media could be replaced with cooling tubes such that the composition of stream 9 is not altered.
- steam could be used as quench media 15. In this case, the concentration of hydrogen and carbon dioxide entering the cyclone would be altered from that in stream 9.
- Cyclone 4 can be made from stainless steel. Combustible gasses can be flared using a natural gas-supported flame. Nitrogen 22 is used as an eductor gas to pump gases out of the cyclone. Gas 24 is thus heavily concentrated in nitrogen. Burner 26 shown in Figure 2 is used for safety precautions in order to combust gases 24. As shown, the gases can be run through a natural gas-oxygen flare.
- activated char 17 is collected from cyclone 4 and can be further processed and used as discussed above with reference to Figure 1.
- Figure 1 illustrates the use of hot partial oxidation gases 19 as fuel to burner 1 to replace some, if not all, of fuel 10 to heat oxidant 11.
- FIG 3. Another configuration of the present invention is shown in Figure 3.
- products 9 from reaction vessel 3 could be injected directly into flue gas 20 for the removal of mercury from flue gas 20. It will be appreciated that stream 9 could be used for direct injection modes other than for the removal of mercury.
- stream 9 may be quenched using stream 15 as discussed hereinabove.
- the point of injection of stream 9 (containing activated char and partial oxidation gases) is likely to be upstream in flue gas 20 relative to a configuration where a cyclone is used. This is due to the additional time needed to allow the partial oxidation gases to completely combust.
- the additional residence time and temperature of the flue gas 20 allows the carbon monoxide to burn out (i.e. completely combust) . More specifically, the temperature of the flue gas at the point of injection in a configuration shown in Figure 3 may be about 2000 0 F as opposed to about 600 0 F at the point of injection in Figure 1.
- SR HOB was calculated by dividing the amount of oxygen fed in stream 11 by the amount of oxygen required to completely combust the natural gas fed in stream 10.
- SR rea ction vessel was calculated by dividing the amount of oxygen entering the reaction vessel 3 by the amount of oxygen needed to completely combust the coal fed in stream 13.
- the carbon content of the activated char was determined by using a muffle furnace to dry a sample of activated char and then to ignite the dried activated char sample. The carbon content was then calculated by dividing the difference between the initial mass and the final mass of the ignited sample by the initial mass of the dry activated char.
- BET surface area of the activated char was measured using a Micromeritics ® ASAP 2000 analyzer. It is noted that the BET surface area of raw PRB coal is 5
- the yield was calculated by using the carbon content of the activated char and by performing a material balance on the ash content of the coal fed in stream 13.
- the ash content on a wet basis is 4.47% for the PRB coal and 7.4% for North Dakota lignite coal.
- Mercury removals by the activated chars were evaluated using Electric Power Research Institute's (EPRI' s) Pollution Control System (PoCT) at We Energys' Desi Prairie Power Plant at Pleasant Prairie, Wisconsin, a 605 MW unit, as well as at a Western coal- fired utility with a conventional pulverized coal boiler rated at 350 MW. Both plants burn PRB coal.
- PoCT is a residence chamber used to simulate injection into the first field of a large scale ESP.
- Experiment numbers 1-3 in Table 1 the coal used was PRB.
- PRB coal with 1% by weight NaBr formed by dry mixing was used and in Experiment number 5, NDL coal with 0.5 % NaBr formed by dry mixing was used.
- PRB coal with 7% by weight KBr formed by dry mixing was used.
- PRB coal with 7% by weight KBR formed by wet mixing was used.
- Utah coal with 1% by weight NaBr formed by dry mixing was used.
- NDL coal with 1% by weight NaBr formed by dry mixing was used.
- ND refers to not determined.
- Table 1 As shown in Table 1, as SR HOB was decreased, while holding SR React i o ii v essel constant , the surface area increased. This is believed to be a result of the increased temperature and steam amount of the stream leaving section 1 of Figure 2. Temperature, the amount of oxidant and the exposure time of the char to the oxidant are important factors in determining the surface area. Generally, increasing any of the three factors increases the surface area.
- the invention is used to produce activated char at a central facility such as a utility or cement kiln or a facility where the off-gas can be burned
- the partial oxidation gases could be used in a boiler (or the burner) and the cooled activated char could be stored for use elsewhere.
- the activated char could be further processed
- a hot gas stream other than hot oxygen can be created and used to activate the carbonaceous feedstock material .
- steam could be dramatically superheated by mixing the steam with the products of a near stoichiometric oxy-fuel burner. This superheated steam would then be used to react with, and activate the carbonaceous feedstock.
- other gasses such as nitrogen could also be superheated in a similar fashion to pyrolyze the coal . In this particular embodiment, no residual oxygen would be present in stream 7 (see figures above) .
- the present invention provides methods and systems for production of activated char that are sufficiently flexible and efficient such that production can occur near or at the end use site of the activated char. It will be appreciated, however, that production of the activated chars in accordance with the present invention is not limited to onsite production. The methods and systems provided herein can also be used in other arrangements. For example and while not to be construed as limiting, activated char produced by the present invention could be produced at a central facility and used to serve multiple utilities or the like. Another exemplary implementation could include producing activated char at a utility for that plant and shipping excess activated char to other locations.
Landscapes
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Inorganic Chemistry (AREA)
- Engineering & Computer Science (AREA)
- Analytical Chemistry (AREA)
- Oil, Petroleum & Natural Gas (AREA)
- General Chemical & Material Sciences (AREA)
- Health & Medical Sciences (AREA)
- Combustion & Propulsion (AREA)
- Biomedical Technology (AREA)
- Environmental & Geological Engineering (AREA)
- General Health & Medical Sciences (AREA)
- Physics & Mathematics (AREA)
- Thermal Sciences (AREA)
- Dispersion Chemistry (AREA)
- Carbon And Carbon Compounds (AREA)
- Solid-Sorbent Or Filter-Aiding Compositions (AREA)
Abstract
Description
Claims
Applications Claiming Priority (3)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| US11/078,517 US20060204429A1 (en) | 2005-03-14 | 2005-03-14 | Production of activated char using hot gas |
| US11/224,590 US7704921B2 (en) | 2005-03-14 | 2005-09-12 | Production of activated char using hot gas |
| PCT/US2006/008894 WO2006099290A1 (en) | 2005-03-14 | 2006-03-13 | Production of activated char using hot gas |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| EP1866246A1 true EP1866246A1 (en) | 2007-12-19 |
| EP1866246A4 EP1866246A4 (en) | 2012-11-07 |
Family
ID=36992039
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| EP06738006A Withdrawn EP1866246A4 (en) | 2005-03-14 | 2006-03-13 | Production of activated char using hot gas |
Country Status (4)
| Country | Link |
|---|---|
| EP (1) | EP1866246A4 (en) |
| KR (1) | KR101275436B1 (en) |
| CA (1) | CA2600875C (en) |
| WO (1) | WO2006099290A1 (en) |
Families Citing this family (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US7767007B2 (en) | 2006-12-08 | 2010-08-03 | Praxair Technology, Inc. | Mercury adsorbents compatible as cement additives |
| US9427744B1 (en) | 2013-01-17 | 2016-08-30 | Calgon Carbon Corporation | Methods for processing carbonaceous materials |
| KR101998190B1 (en) * | 2018-02-12 | 2019-07-12 | 한국에너지기술연구원 | Method for Preparation of mesoporous activated carbon from needle coke via 2nd steam activation |
Family Cites Families (8)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US3958957A (en) * | 1974-07-01 | 1976-05-25 | Exxon Research And Engineering Company | Methane production |
| US4475986A (en) * | 1983-09-07 | 1984-10-09 | Peabody Development Company | Stable activated carbon process using a moving grate stoker furnace |
| FI931785A7 (en) * | 1993-04-20 | 1994-10-21 | Valtion Teknillinen | Method and apparatus for producing liquid fuel by pyrolyzing raw fuel |
| AU8600298A (en) * | 1997-08-19 | 1999-03-08 | Electric Power Research Institute, Inc. | Apparatus and method for removal of vapor phase contaminants from a gas stream by in-situ activation of carbon-based sorbents |
| US6534442B1 (en) * | 1998-05-14 | 2003-03-18 | Caigon Carbon Corporation | Process for production of carbonaceous chars having catalytic activity |
| JP4493824B2 (en) * | 2000-09-28 | 2010-06-30 | 日本パイオニクス株式会社 | Purification method and cleaning agent for harmful gas |
| US6521021B1 (en) * | 2002-01-09 | 2003-02-18 | The United States Of America As Represented By The United States Department Of Energy | Thief process for the removal of mercury from flue gas |
| US6726888B2 (en) * | 2002-01-25 | 2004-04-27 | General Electric Company | Method to decrease emissions of nitrogen oxide and mercury |
-
2006
- 2006-03-13 EP EP06738006A patent/EP1866246A4/en not_active Withdrawn
- 2006-03-13 KR KR1020077023409A patent/KR101275436B1/en not_active Expired - Fee Related
- 2006-03-13 CA CA2600875A patent/CA2600875C/en not_active Expired - Fee Related
- 2006-03-13 WO PCT/US2006/008894 patent/WO2006099290A1/en not_active Ceased
Also Published As
| Publication number | Publication date |
|---|---|
| EP1866246A4 (en) | 2012-11-07 |
| KR101275436B1 (en) | 2013-06-19 |
| WO2006099290A1 (en) | 2006-09-21 |
| CA2600875C (en) | 2011-05-17 |
| KR20070121742A (en) | 2007-12-27 |
| CA2600875A1 (en) | 2006-09-21 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| US8124561B2 (en) | Production of activated char using hot gas | |
| CN115210503B (en) | Systems and methods for pyrolysis | |
| US8309052B2 (en) | Carbon heat-treatment process | |
| ZHANG | Emissions of SO2, NO and N2O in a circulating fluidized bed combustor during co-firing coal and biomass | |
| US8999278B2 (en) | Method and apparatus for on-site production of lime and sorbents for use in removal of gaseous pollutants | |
| Okasha | Staged combustion of rice straw in a fluidized bed | |
| Yang et al. | Combustion behaviors and pollutant emission characteristics of low calorific oil shale and its semi-coke in a lab-scale fluidized bed combustor | |
| CA2841563E (en) | Operational conditions and method for production of high quality activated carbon | |
| CA2600875C (en) | Production of activated char using hot gas | |
| Zhang et al. | NO and SO2 removal and pore structure evolution during reburning with calcium magnesium acetate blended peanut shell | |
| Zhang et al. | Dried sludge reburning blended with calcium magnesium acetate addition in a fluidized bed combustor | |
| Hao et al. | Synergistic behaviors of anthracite and dried sawdust sludge during their co-combustion: Conversion ratio, micromorphology variation and constituents evolutions | |
| CA2748934C (en) | Coal heat-treatment process and system | |
| Di Marco et al. | The recovery of waste and off-gas in Large Combustion Plants subject to IPPC National Permit in Italy | |
| CA2931355A1 (en) | Apparatus for firing and combustion of syngas | |
| US9109801B2 (en) | Coal heat-treatment process and system | |
| RU2821504C1 (en) | Method for gasification of carbon-containing solid fuel | |
| Akhmetshin et al. | Analysis of Gaseous Anthropogenic Emissions from Coal and Slurry Fuel Combustion and Pyrolysis | |
| Zhao et al. | Emission control of gaseous pollutants from co-firing of petroleum coke and coal in CFB | |
| Gu et al. | Effect of Fe on NO release during char combustion in air and O2/CO2 |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| PUAI | Public reference made under article 153(3) epc to a published international application that has entered the european phase |
Free format text: ORIGINAL CODE: 0009012 |
|
| 17P | Request for examination filed |
Effective date: 20071012 |
|
| AK | Designated contracting states |
Kind code of ref document: A1 Designated state(s): DE ES GB IT |
|
| RAP1 | Party data changed (applicant data changed or rights of an application transferred) |
Owner name: PRAXAIR TECHNOLOGY, INC. |
|
| DAX | Request for extension of the european patent (deleted) | ||
| RBV | Designated contracting states (corrected) |
Designated state(s): DE ES GB IT |
|
| A4 | Supplementary search report drawn up and despatched |
Effective date: 20121009 |
|
| RIC1 | Information provided on ipc code assigned before grant |
Ipc: C01B 31/18 20060101ALI20121002BHEP Ipc: C01B 31/08 20060101ALI20121002BHEP Ipc: B01J 20/20 20060101ALI20121002BHEP Ipc: B01D 53/64 20060101ALI20121002BHEP Ipc: C01B 31/10 20060101AFI20121002BHEP |
|
| 17Q | First examination report despatched |
Effective date: 20130722 |
|
| 17Q | First examination report despatched |
Effective date: 20140128 |
|
| STAA | Information on the status of an ep patent application or granted ep patent |
Free format text: STATUS: THE APPLICATION IS DEEMED TO BE WITHDRAWN |
|
| 18D | Application deemed to be withdrawn |
Effective date: 20140611 |