US20120137576A1 - Method and plant for the thermal treatment of organic matter in order to produce charchoal or char - Google Patents

Method and plant for the thermal treatment of organic matter in order to produce charchoal or char Download PDF

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US20120137576A1
US20120137576A1 US13/321,628 US201013321628A US2012137576A1 US 20120137576 A1 US20120137576 A1 US 20120137576A1 US 201013321628 A US201013321628 A US 201013321628A US 2012137576 A1 US2012137576 A1 US 2012137576A1
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Prior art keywords
wood
charcoal
organic matter
order
carbonizing
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Alvaro Lucio
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CAMPELO ROGERIO GERALDO
DE SOUSA VITOR SERGIO
NETO ANTONIO DELFINO SANTOS
VIEIRA SIDNEY PESSOA
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CAMPELO ROGERIO GERALDO
DE SOUSA VITOR SERGIO
NETO ANTONIO DELFINO SANTOS
VIEIRA SIDNEY PESSOA
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Assigned to CAMPELO, ROGERIO GERALDO, DE SOUSA, VITOR SERGIO, LUCIO, ALVARO, VIEIRA, SIDNEY PESSOA, NETO, ANTONIO DELFINO SANTOS reassignment CAMPELO, ROGERIO GERALDO ASSIGNMENT OF ASSIGNORS INTEREST (SEE DOCUMENT FOR DETAILS). Assignors: LUCIO, ALVARO
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    • C—CHEMISTRY; METALLURGY
    • C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10B—DESTRUCTIVE DISTILLATION OF CARBONACEOUS MATERIALS FOR PRODUCTION OF GAS, COKE, TAR, OR SIMILAR MATERIALS
    • C10B53/00—Destructive distillation, specially adapted for particular solid raw materials or solid raw materials in special form
    • C10B53/02—Destructive distillation, specially adapted for particular solid raw materials or solid raw materials in special form of cellulose-containing material
    • C—CHEMISTRY; METALLURGY
    • C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10B—DESTRUCTIVE DISTILLATION OF CARBONACEOUS MATERIALS FOR PRODUCTION OF GAS, COKE, TAR, OR SIMILAR MATERIALS
    • C10B39/00—Cooling or quenching coke
    • C10B39/04—Wet quenching
    • C10B39/06—Wet quenching in the oven
    • C—CHEMISTRY; METALLURGY
    • C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10B—DESTRUCTIVE DISTILLATION OF CARBONACEOUS MATERIALS FOR PRODUCTION OF GAS, COKE, TAR, OR SIMILAR MATERIALS
    • C10B49/00—Destructive distillation of solid carbonaceous materials by direct heating with heat-carrying agents including the partial combustion of the solid material to be treated
    • C10B49/02—Destructive distillation of solid carbonaceous materials by direct heating with heat-carrying agents including the partial combustion of the solid material to be treated with hot gases or vapours, e.g. hot gases obtained by partial combustion of the charge
    • C—CHEMISTRY; METALLURGY
    • C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10B—DESTRUCTIVE DISTILLATION OF CARBONACEOUS MATERIALS FOR PRODUCTION OF GAS, COKE, TAR, OR SIMILAR MATERIALS
    • C10B7/00—Coke ovens with mechanical conveying means for the raw material inside the oven
    • C10B7/14—Coke ovens with mechanical conveying means for the raw material inside the oven with trucks, containers, or trays
    • C—CHEMISTRY; METALLURGY
    • C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10L—FUELS NOT OTHERWISE PROVIDED FOR; NATURAL GAS; SYNTHETIC NATURAL GAS OBTAINED BY PROCESSES NOT COVERED BY SUBCLASSES C10G OR C10K; LIQUIFIED PETROLEUM GAS; USE OF ADDITIVES TO FUELS OR FIRES; FIRE-LIGHTERS
    • C10L5/00—Solid fuels
    • C10L5/40—Solid fuels essentially based on materials of non-mineral origin
    • C10L5/44—Solid fuels essentially based on materials of non-mineral origin on vegetable substances
    • Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E50/00—Technologies for the production of fuel of non-fossil origin
    • Y02E50/10—Biofuels, e.g. bio-diesel
    • Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E50/00—Technologies for the production of fuel of non-fossil origin
    • Y02E50/30—Fuel from waste, e.g. synthetic alcohol or diesel

Definitions

  • the present invention relates to a method and plant for the thermal treatment of organic materials applied to the carbonization of ditto organic materials in order to produce charcoal or char.
  • Any type of organic matter can be used as raw material: log wood in any size, coconut peel, babassu coconut, rice straw, saw mill wastes, sugar cane, sugar cane straw and vegetal wastes in general. In order to simplify wood will be the reference, but the text can be applied to any type of biomass.
  • Brazil is the world greatest charcoal producer with an average annual production of 8.5 millions of metric tons. This production is only a small fraction of the actual potential to produce charcoal from cultivated biomass and agricultural crop wastes.
  • the principal aim of this invention in to bring logistic, environmental, technical, economic and global energy efficiency when compared to most of the existing biomass carbonization processes.
  • biomass was created in 1975 in order to describe the natural materials suitable to be used as fuels.
  • the term encompasses all organic matter of vegetal or animal origin, inclusive the resulting materials of its natural or artificial transformation (e.g. charcoal).
  • the origin of any type of biomass is the photosynthesis.
  • the CO 2 concentration increase in the atmosphere, intensified in the last 200 years, is one of the reasons for the so called “greenhouse effect”, which is supposed to be the main responsible for the planet heating.
  • the corresponding decrease of the oxygen concentration in the atmosphere according reaction ( 1 ) is followed by a decrease in the ozone concentration, due to the thermodynamic equilibrium oxygen-ozone.
  • the reduction of the ozone concentration increases the ultra violet radiation on the earth, and consequently the risk of skin cancer. If nothing is done to reduce the consumption of fossil fuels, the future generations will inherit a hostile planet.
  • CO 2 When burning a biomass fuel, CO 2 is emitted to the atmosphere in the same way as a fossil fuel. But during the growth of the cultivated biomass, CO 2 is absorbed from the atmosphere and oxygen is emitted through the photosynthesis process. The final balance is no reduction of the oxygen concentration in the atmosphere, which is extremely beneficial to the environment.
  • Biomass conversion with energy liberation recreates the natural decomposition process, but in a much faster way, and this energy is a renewable energy.
  • biomass carbon is recycled, no CO 2 being emitted to the atmosphere, such as happens when burning fossil fuels.
  • Biomass is the only source of renewable energy. Being a renewable source, it should to have in mind that fossil fuels are exhaustible.
  • Organic matter is the primary origin of fossil fuels. Organic matter piled up on the sedimentary rocks during the Cambrian geologic period, was transformed in the absence of oxygen in fossil fuels: coal, oil and natural gas. By its turn, this organic matter came from solar energy through the photosynthesis process. This accumulated chemical energy during 600 millions years has been increasingly wasted by humankind.
  • thermo-chemical process biomass is decomposed in less complex substances. Any type of biomass can be submitted in a thermo-chemical conversion process. Due to the high productivity, low cost, high density and quality wood is the main biomass submitted to thermo-chemical processes. Pyrolysis is the anaerobic (lack of oxygen or air) thermal decomposition process. When oxygen is enough for the complete biomass chemical reaction, we have combustion or gasification.
  • Pyrolysis is the thermal biomass conversion at 300-800° C. temperature range in the total absence of air, or with not enough air for combustion. Biomass pyrolysis is also called carbonization or wood destructive distillation. Carbonization is the process when charcoal is the main product of interest. Heat can be indirectly supplied, or produced by burning part of the biomass (direct heating). High temperature (1,000° C.) produces a maximum of fuel gas (gasification), whereas low temperature pyrolysis ( ⁇ 500° C.) produces a maximum of charcoal.
  • Carbonizing temperatures when charcoal is the desired main product are in the range 300-500° C.
  • Charcoal is light, has a high low heating value, and burns with no smoke, while wood is much denser, its combustion producing a lot of smoke.
  • Charcoal contains ashes, its content depending on the type of wood, earth contamination, etc.
  • a gaseous phase is emitted to the atmosphere, containing condensable and non condensable gases.
  • the non condensable gases can be burned in order to generate thermal energy.
  • the components of the no condensable gases are: CO 2 , CO, H 2 , CH 4 and C n H m .
  • the condensable gases also contain combustible components. When not burned, as already mentioned are strongly polluters and harmful to the health.
  • Pyrolysis is the basic biomass thermodynamic conversion process. When heated in the absence of air, a decomposition of the biomass in less complex components occurs. Pyrolysis is a complex process through intermediate radicals, the final result being a solid residue rich in carbon (charcoal), and a volatile fraction composed of gases, organic vapors and tar components. This volatile fraction if not used either as a fuel or for the liquefaction of the condensable components is very polluter. Although being a rather simple technology for the biomass conversion in solid fuel, carbonization is a very complex process.
  • Carbonization is performed in the following steps.
  • V Carbonization or pyrolysis
  • the pyrolysis phase is exothermic and the temperature rises up to 290-380° C. with the emission of hydrocarbon gaseous products, the solid residue becomes charcoal with a high volatile matter content.
  • the emitted gases during pyrolysis have a significant heating value.
  • Gases species are: CO, CO 2 , H 2 , CH 4 , water vapor, hydrocarbon gases, and vapors of tar, methanol, acetic acid and pyrolygneous liquor. In the present text we use carbonization or pyrolysis for this stage.
  • VI Fluorescence step, with an increase of temperature and fixed carbon, decreasing the volatile matter content. The higher the temperature, the higher charcoal fixed carbon content.
  • VII Cooling—Charcoal produced must be cooled, in order not to burn when opening the kiln or retort, which must be tightly sealed.
  • FIG. 1 shows the relation between carbonization temperature, fixed carbon, and gravimetric yield, which is, the ratio. (kg of charcoal)/(ton of anhydrous wood).
  • the carbonization process starts with a strongly endothermic step before the exothermic step. It should be emphasized the difference in phase of the endothermic and the exothermic steps of the carbonization process, which starts with the strongly endothermic wood drying, followed by the exothermic carbonization step, and the emission of combustible gaseous substances.
  • the energy emitted by the wood during the carbonization step is more than enough to supply the energy demand of the drying step.
  • the problem of using the energy emitted by the carbonizing wood during the drying wood step is the difference in phase of those two steps.
  • part of the wood loaded into the carbonization reactor should be burned in order to supply the energy for the endothermic step, although the energy emitted during the exothermic phase plus the energy content of the combustible gases emitted during this step is more than the energy demanded by the endothermic reactions of the carbonization process.
  • Table I is a summary of the theory of the evolution of biomass carbonization.
  • Charcoal is the first wood product used by centuries. Cave men observed that the residue of burned wood produced a hotter flame with less smoke in the cave. Later on, when by hazard a mixture of this residue was fired together with certain types of stones, a heavy liquid emerged, starting in that way the age of metals.
  • the annual charcoal consumption in Brazil is over 8 millions tons. Approximately 60% of the wood for charcoal production in Brazil comes from the high productivity eucalyptus plantations. In Brazil only the kiln method is used for charcoal making. Those kilns do not take advantage of the exothermic energy phase, burning part of the charged wood in the kiln as the energy source for the carbonization process. Besides, brick kilns have no charcoal quality control because the whole operation is based on visual observation of the emitted gaseous products color.
  • charcoal producer furnaces were developed since the beginning of its utilization. The first charcoal production process was probably the pit kiln, used until today in some countries. Wood is slowly burned in a pit covered by earth. According to the heat generation process, carbonizing furnaces can be classified as:
  • the hot gases from a combustion chamber are introduced into the furnace in order to supply the necessary heat for the endothermic carbonization steps. It is possible to burn any kind of fuel in the combustion chamber, such as agricultural and forestry wastes, charcoal fines, tar, fuel oil or natural gas.
  • the investment cost in this system is higher, but it allows a better control, producing good quality charcoal with a higher yield.
  • the retort method uses retort which works on a continuous basis. Wood is loaded at the top and as it descends through the retort it is first dried by ascending hot gases in the top section, then carbonized by recycling hot gases in the middle section, and finally cooled and withdrawn at the bottom. An ingenious system of recirculation and combustion of the pyrolysis gases ensures that the maximum advantage is taken of their thermal and chemical energy content. The automatic working of the plant leads to a reduction of the personnel required.
  • Retort processes are normally used when the desired main product is the liquefied volatiles emitted by the carbonization wood, charcoal being a by product.
  • the desired main product is the liquefied volatiles emitted by the carbonization wood, charcoal being a by product.
  • several important chemical products such as acetic acid, methanol, solvents, food aromatizers, etc, are recovered from the carbonizing wood.
  • carbonizing retorts are not economically feasible when the only desired product is charcoal.
  • the investment cost is raised by the saw mill and the wood sawing operation raises the charcoal cost. As above mentioned, in Brazil only the brick kiln method is used.
  • the charcoal main applications are: as thermal reducer in the iron, ferrous alloys, silicon metal, calcium carbide furnaces and as renewable energy source in the lime and cement industry. Approximately one third of the pig iron produced in Brazil is based on the charcoal as a thermal reducer.
  • the typical beehive furnace used in Brazil has 10 to 30 cubic meters capacity, FIG. 2 .
  • Log wood is vertically charged into the kiln through gate 1 . Above these shorter horizontal logs are placed to the underside of the dome. After charging, the door openings are bricked up and sealed with a weak cement and mud mortar. Ignition is started through the hole 2 on the top, which is closed when the fire takes hold.
  • the beehive kiln has been improved by erecting a chimney aside walls 3 .
  • Carbonization moves downward, with air being drawn in through holes in the dome and vertical wall 3 , the smoke being emitted by the same holes. As the combustion proceeds, all openings are sealed. When the smoke coming from the chimneys turns a light blue, all the openings, including the chimneys, are closed and sealed carefully with mud. The kiln is then brushed all over with several layers of clay slurry to close all leaks and cracks. If this is not done thoroughly, the infiltration of air will maintain a certain amount of combustion and slow the cooling. Air leakage into the kiln would burn the charcoal from the carbonizing wood. The charcoal cooling, which is the final carbonization step is started. Total time for the complete cycle goes from 9 to 13 days. The beehive kiln has been improved by erecting chimneys aside walls 3 .
  • a very high volume concrete kiln developed and still used in the United States is known as Missouri kiln.
  • Those kilns are large permanent structures which were developed for charcoal making in the deciduous hardwood forest of the state of Missouri, from which they get their name. They are rectangular in shape with a vaulted roof, FIG. 3 . They vary greatly in size normally up to 12 meters long, 7 meters wide and 4 meters tall. This enables considerable economy of scale, the entry of vehicles for direct loading and unloading, but the kiln is difficult to control.
  • the concrete walls were replaced by low density refractory silicon-aluminum bricks.
  • the walls 4 thickness is normally 25 cm, FIG. 3 .
  • Steel doors gates 5 are protected by refractory concrete.
  • the kiln usually has four chimneys 6 , along each side.
  • Air vents 7 are provided along the base of the furnace walls.
  • Wood is charged upon a log basis transversally placed on the soil.
  • the wood pile is lid through a channel 8 under the central part of the furnace.
  • the furnace operation requires considerable skill.
  • the doors in particular are vulnerable to misuse and if the seal is damaged, operation of the furnace becomes very difficult.
  • the carbonization is controlled by the color of the emitted gases.
  • a light blue color occurs in the end of the carbonization process.
  • the charcoal cooling is started.
  • the total cycle lasts from 9 to 12 days.
  • a deficiency of the Missouri furnace is the non homogenous carbonization. In a certain moment there may be very hot regions where the charcoal burns, together with regions still in the final wood drying step.
  • An evolution of the furnace control is the temperature measurement by infra red pyrometers, which show the differences in temperature. Through the control of the air input by the air vents 8 , a better homogenization of the carbonizing wood pile is obtained.
  • Brick furnaces do not take advantage of the combustible gases emitted by the carbonizing wood. As a result, one of the basic characteristic of these furnaces is the burning of part of the charged wood. In the brick kilns occurs a certain overlapping of the drying and pyrolysis steps. The emission to the atmosphere of harmful gases containing up 45 to 50 kg of methane per ton of charcoal is another characteristic of these kilns. As far as greenhouse effect is concerned, this methane content is equivalent of one ton of CO 2 .
  • the humidity content of the charged wood in the traditional brick furnaces should be not over 25-30% (w.b.). Soon after being cut down, wood moisture content is an average of 50% (w.b.). It is impossible to carbonize or to use wood as a fuel with this moisture content, being necessary to reduce it to 25-30% (w.b.) level, which is done by appropriately piling it during 100 to 120 days. This labor intensive piling requires the following operations.
  • Gravimetric yield is the relation (kg of charcoal/(ton of anhydrous wood). Due to the burning of part of the charged wood brick furnaces gravimetric yield is low, from 25 to 34%. That is, only 250 to 340 kg of charcoal per ton of anhydrous wood is obtained. The upper level of this range is obtained in the rectangular brick furnaces with internal temperatures measurement.
  • the principal aim of the present invention is to solve the above mentioned problems by providing a method for carbonizing biomass that considerably simplifies, with respect to conventional carbonization methods, the operations for pollutant removal and for energy recovery of the products of biomass pyrolysis.
  • an object of the invention is to provide a method that can be controlled and managed in a very simple manner on the basis of parameters preset according to the type of biomass being treated, with high operating flexibility.
  • Another object of the invention is to provide a plant that can perform such a treatment method in a practically continuous manner.
  • Another object of the invention is to provide a structurally simple plant requiring relatively low investments and operating costs.
  • Another object of the invention is to provide a plant offering adequate assurances against a danger of environmental pollution.
  • the emitted energy during the exothermic step of the biomass carbonization is sufficient to meet the thermal demand of the process endothermic phases.
  • brick kilns do not take advantage of this energy because the endothermic stage occurs before the exothermic pyrolysis step.
  • the wood carbonizing process is self sufficient in energy. However, this energy is only available after the drying endothermic stage, being necessary to burn part of the carbonizing wood in brick kilns.
  • the DPC Process basic characteristic is the sharp separation of the drying and pyrolysis stages, which are performed in independent reactors in such a way that the energy content in the emitted gases by the carbonizing wood is used to supply the thermal demand of the endothermic steps.
  • the devised DPC Process resolves the drying and pyrolysis steps difference in time problem.
  • Any DPC reactor can perform the functions of drying, pyrolysis and charcoal cooling.
  • the process can be performed in more than three reactors, depending on the desired capacity of the charcoal plant.
  • FIG. 4 The disposal of the reactors in the DPC Process, object of the present report, is shown in FIG. 4 .
  • the system consists of three independent reactors, 9 , 10 and 11 , and an independent combustion chamber 12 .
  • the drying step is performed in reactor 10 , and charcoal being cooled in reactor 11 .
  • condensable and non condensable gases containing combustible components are emitted by the carbonizing wood. These gases exit reactor 10 through pipe 13 . Most of these gases are transported through pipe 13 to the collecting pyrolytic gases pipe 14 , passing through valves 15 and 16 .
  • Valve 15 stays opened allowing the pass of the gases to collector pipe 14 , but hinders the pass of the ditto gases to the diluting gases collector 17 .
  • pyrolytic gases are transported to the gas burner 18 situated at the combustion chamber 12 , flow controlled by valve 19 , passing before through gasifier 20 .
  • Combustion air driven by fan 21 flow controlled by valve 22 , mixed with the fuel gases in the burner 18 .
  • Combustion air is preheated by heat exchanger 23 placed inside the combustion chamber 12 .
  • Hot fuel gases generated by the carbonizingwood return to the reactor 10 driven by fan 24 through pipe 25 , flow controlled by valve 26 . The purpose of this return is to control the temperature in the carbonizing reactor.
  • the fixed carbon content and other metallurgical charcoal properties are functions of the carbonizing temperature. Therefore part of the pyrolytic gases flow in a closed circuit, a looping.
  • the fuel gases closed circuit with the aim of a precise control of the biomass carbonizing stage is a basic characteristic of the DPC Process described in this text.
  • the carbonization end is shown by the decreasing pyrolytic gases flow.
  • the temperature in the carbonizing reactor 10 remains in the range 310-350° C., adequate to the metallurgical charcoal.
  • the carbonization speed is controlled by the return flow of the pyrolytic gases.
  • Hot flue gases generated by burning pyrolytic gases in the combustion chamber 12 are driven by fan 27 through pipe 28 to mixer 29 .
  • Diluting gases coming from drying reactor chamber 9 are mixed with hot flue gases coming from combustion chamber 12 inside mixer 29 .
  • This gaseous mixture suctioned by fan 27 is driven to the pipe collecting hot gases 30 by pipe 31 , flow controlled by valve 32 .
  • hot flue gases mixed with said diluting gases coming from reactor 9 are suctioned by fan 24 through pipe 33 , passing by valve 34 totally opened, and by control flow valve 35 .
  • Hot flue gases are then insufflated into the drying reactor 9 . Steam from the drying wood joins the hot flue gases. This gaseous mixture exits the drying reactor at approximately 120° C.
  • Pipe 17 is a diluting gases distributor. These gases are transported to mixer 29 through pipe 36 . Inside mixer 29 the diluting gases, which we will name recycle gases, are mixed with the hot flue gases coming from the combustion chamber 12 . The excess of the recycle gases is driven through pipe 37 to the chimney 38 , flow controlled by valve 39 , and from said chimney 38 to the atmosphere.
  • the drying reactor 9 inside which wood drying is performed demands the maximum heat input. In order to avoid high temperatures in the drying reactor, hot flue gases exiting combustion chamber 12 are mixed with the diluting gases flowing through pipe 17 . This technique, which we named “recirculation”, allows the heat input in the drying reactor 9 at the desired temperature.
  • the drying reactor 9 ideal entering gas temperature is in the range 300-350° C. Performing in this temperature range undesirable steel containers overheating will not occurs. Besides when drying at high temperatures, wood cracks weakening the charcoal.
  • the recirculation technique is another basic characteristic of the DPC Process described in the present text.
  • Charcoal cooling is being performed in reactor 11 , which is done in two stages. The cooling starts by turning off fan 24 and closing control flow valves 26 and 35 placed in pipes 25 and 33 . Valve 15 remains closed. Reactor 11 should be tightly sealed, since any air leakage will burn the hot charcoal. Heat radiation to the atmosphere starts the charcoal cooling. During this cooling stage, a small part of the carbon contained in the gaseous atmosphere from the carbonization stage, is absorbed by the charcoal, slightly raising the charcoal fixed carbon. Besides this gaseous atmosphere small pressure hinders atmospheric air entrance. Charcoal cooling continues by the injection of a very fine water spray in reactor 11 . Water is injected under high pressure by pump 42 to atomizer 43 through pipe 44 . Water is divided in very fine drips, which quickly vaporizes cooling the charcoal. When the cooling reactor 11 temperature falls to 95° C., water injection is stopped. Charcoal cooling is concluded by heat radiation to the atmosphere.
  • reactor 9 During the entire carbonization process in reactors 9 , 10 and 11 , wood remains motionless, avoiding charcoal fines generation. Wood drying, carbonization and charcoal cooling occur simultaneously until the end.
  • reactor 9 receives hot pyrolytic gases, charcoal cooling starts in reactor 11 , and reactor 11 is unloaded. A new wood container is placed in reactor 11 , starting the wood drying.
  • valves 15 , 16 and 34 situated in pipes 14 , 17 and 30 By adequate maneuvers in valves 15 , 16 and 34 situated in pipes 14 , 17 and 30 , reactors 9 , 10 and 11 functions are changed.
  • Reactor 9 becomes a pyrolysis kiln
  • charcoal cooling is done in reactor 10
  • reactor 11 becomes a drying reactor.
  • fuel gas to burning in combustion chamber 12 is not available, as none reactor is in the pyrolysis stage.
  • FIG. 4 shows the wood gas producer 20 and pipe 45 which transports the low heating value gas generated in the gas producer 20 to the burner 18 .
  • the gasifying agent comes from mixer 46 , being injected in gas producer 20 by fan 47 , flow controlled by valve 48 . Atmospheric air is driven to mixer 46 through pipe 49 , flow control by valve 50 . Diluting gas is carried to mixer 40 through pipe 51 , flow control by valve 52 .
  • a small proportion of diluting gas is mixed with the gasifying air in order to avoid too high temperatures in the lower part of the gas producer.
  • the gas producer capacity should be adequate to the thermal demand by the drying reactor 9 . Besides, the gas producer will assure the supply of fuel gas in the case of an eventual deficiency of combustible gas emitted by the carbonizing wood.
  • FIG. 5 shows a system with six reactors.
  • Pipe 52 is the pyrolytic gases collector, flowing in this pipe only this type of gases.
  • Pipe 53 carries the pyrolytic gases to pipe 54 , flow controlled by valve 55 .
  • Combustible gases generated by the carbonizing wood are driven to burner 56 set at the combustion chamber 57 , reaching burner 56 through pipe 58 .
  • These gases were produced in the wood carbonizing reactors, supposed to be reactors 59 and 60 at the moment chosen for this description. Gases emitted by the carbonizing wood are transported to pipe 53 by pipe 61 , passing before through valves 62 and 63 .
  • valves are fixed in such a way that valve 62 although closed, allows passage of the pyrolytic gases only towards pipe 53 , crossing valve 57 , which at this moment remains opened.
  • Part of the pyrolytic gases return to reactors 59 and 60 through pipe 64 , suctioned by fan 65 , flow controlled by valve 66 .
  • the purpose of this return is the temperature control in reactors 59 and 60 in order to avoid the carbonization wood superheating during the pyrolysis exothermic stage. This technique has been previously expounded in the case of three reactors, FIG. 4 . Having two carbonizing reactors, the supply of fuel gas to combustion chamber 57 according the process needs is assured.
  • reactors 67 and 68 are processing the wood drying.
  • Hot flue gases produced in combustion chamber 57 are suctioned by fan 69 through pipe 70 , which transports ditto hot gases to mixer 71 .
  • hot flue gases are carried to the collecting flue gases 72 , through pipe 73 , flow controlled by valve 74 .
  • From pipe 72 said gases are driven to the drying reactors chambers 67 and 68 through pipe 75 , flow controlled by valve 76 .
  • water vapor coming from the wood dehydration joins the hot flue gases which entered the drying reactors at 300 to 350° C.
  • reactors 86 and 87 process the charcoal cooling.
  • charcoal cooling is started with reactors 86 and 87 well sealed, through heat radiation to the atmosphere; continuing by water spray injected by pump 88 through pipe 89 to the water atomizer 90 .
  • cooling reactors temperature falls to 95° C., charcoal cooling is completed by the heat radiation to the atmosphere.
  • the DPC Process described in the present text provides a precise control of the wood carbonization process, producing charcoal according to the metallurgical properties specified by the user.
  • the control is made through pyrometers installed at the gases entrance and the gases exit of each reactor. When drying starts the temperature difference between the entering and the exiting gases is large due to the wood heating and humidity water vaporization thermal demand. This temperature difference reduces while drying goes on. The end of the drying period will be shown by these temperatures convergence, the drying reactor becoming available for the wood carbonization stage.
  • the control of the process through pyrometers placed at the entrance and the exit of each reactor allows the DPC system automation. During the wood carbonization stage the charcoal fixed carbon is a crescent function of the temperature, while the gravimetric yield is a decreasing function of the temperature.
  • FIG. 1 shows the relation between carbonizing temperature, charcoal fixed carbon and gravimetric yield. Steel industry is the main charcoal consumer in Brazil for the pig iron blast furnace. Charcoal fixed carbon for the pig iron blast furnace is specified in the range 70-75%. FIG. 1 shows that carbonizing temperature should be in the range 320-350° C. for the fixed carbon content in the range 70-75%.
  • the energy content of the emitted gases by the carbonizing wood is sufficient to drying wood soon after cutting down, according to thermodynamic computations.
  • the cutting down wood humidity is approximately 50% (w.b).
  • One of the advantages of the DPC process is the capacity to drying wood soon after cutting down, avoiding the wood storing at the atmospheric air in order to reduce the humidity to water content in the wood compatible with the carbonization process in brick kilns. That storage has an economical cost.
  • wood can be dried by adequately placing it in the atmospheric air during a minimum of one hundred days. Condensation of the condensable constituents present in the pyrolytic gas followed by separation of the various products by the conventional extraction processes will allow the recover of several wood liquid products present in the condensable gases.
  • the energy of the fuel gases emitted by the carbonizing wood can be used for thermal electric generation. It is an economically very attractive alternative if the carbonization plant is located in the proximity of the charcoal blast furnace. Hot flue gases effluents from auxiliary equipments of the pig iron producer plant can be used for the wood drying. In that case, pyrolytic combustible gases or tar produced by the condensation of those gases, can be used for thermal electric generation, which turns the pig iron plant self sufficient in energy.
  • FIG. 6 shows the arrangement of the association DPC equipment—roll on bucket. This technique is a significant advantage of the DPC Process described in this report when compared with the conventional brick kilns carbonization.
  • DPC Process can produce anhydrous wood, char or charcoal with a high volatile content.
  • the later is a very convenient fuel, adequate to replace fossil fuels in industrial furnaces or in boilers.
  • a biomass energy concentration is done through anhydrous wood, char or high volatile charcoal. Due to the distances in large countries like Brazil, the biomass energy concentration is very relevant for its transportation.
  • Table 2 shows the low heating value of these products.
  • Table 3 shows a comparison of the unit energy cost from biomass, and from fuel oil, according to current prices in Brazil.
  • the third column of table 3 indicates the relation between the biomass energy unit cost and the fuel oil energy unit cost.
  • the process is suitable for the carbonization of several high productivity biomass crops, such as sugar cane and elephant grass raising a new window of opportunities for the strong agricultural sector of the Brazilian or any other large country economy.
  • Harvesting sugar cane or elephant grass for energy applications can be an important job generator in remote and poor areas of any country, avoiding the migrant exodus to the big cities.
  • the energetic concentration of the biomass given by the DPC Process is very important for any developing country.
  • the use of the cultivated biomass by the steel industry can generate a lot of jobs in the field, reducing the migration of rural laborers to the big cities.
  • Each ten hectares of cultivated forest generates a job in the field.
  • the economic advantages of the DPC Process can be resumed as follows. Approximately 60% of the pig iron cost is due to the charcoal. A significant reduction in the charcoal cost given by the DPC Process will decrease the pig iron and steel cost, raising the competitive conditions of the producer companies of these commodities. Besides, pig iron and steel obtained when charcoal is used as a thermal reducer have better quality.
  • the gravimetric yield that is (kg of charcoal)/(ton of anhydrous wood) of the DPC Process is in the range 40-42%, while brick kilns range is 28-34%.
  • the DPC Process obtains 400 to 420 kg of charcoal per ton of anhydrous wood. That means an increase of 30% in the charcoal production per hectare of cultivated forest. As a result, keeping constant the charcoal consumption by the steel or pig iron plant, the forest will last 30% more time.

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US13/321,628 2009-05-21 2010-05-20 Method and plant for the thermal treatment of organic matter in order to produce charchoal or char Abandoned US20120137576A1 (en)

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BRPI0901948-0A BRPI0901948A2 (pt) 2009-05-21 2009-05-21 processo de obtenção do carvão vegetal que utiliza os constituintes gasosos emitidos durante a carbonização da matéria vegetal como fonte de energia para o processo e configuração construtiva do respectivo equipamento
BRPI0901948-0 2009-05-21
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MX2011012286A (es) 2012-06-01
WO2010132970A1 (en) 2010-11-25
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BRPI0901948A2 (pt) 2011-02-08
CL2011002938A1 (es) 2012-06-15

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