CA2913180A1 - Pyrolysis system and method for bio-oil component extraction - Google Patents

Pyrolysis system and method for bio-oil component extraction

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Publication number
CA2913180A1
CA2913180A1 CA2913180A CA2913180A CA2913180A1 CA 2913180 A1 CA2913180 A1 CA 2913180A1 CA 2913180 A CA2913180 A CA 2913180A CA 2913180 A CA2913180 A CA 2913180A CA 2913180 A1 CA2913180 A1 CA 2913180A1
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CA
Canada
Prior art keywords
solvent
bio
oil
component
condenser
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.)
Abandoned
Application number
CA2913180A
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French (fr)
Inventor
Raymond Belanger
Christopher Churchill
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Tolero Energy LLC
Original Assignee
Tolero Energy LLC
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Priority claimed from US13/907,494 external-priority patent/US10589187B2/en
Priority claimed from US14/046,883 external-priority patent/US20150096879A1/en
Application filed by Tolero Energy LLC filed Critical Tolero Energy LLC
Publication of CA2913180A1 publication Critical patent/CA2913180A1/en
Abandoned legal-status Critical Current

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    • CCHEMISTRY; METALLURGY
    • C09DYES; PAINTS; POLISHES; NATURAL RESINS; ADHESIVES; COMPOSITIONS NOT OTHERWISE PROVIDED FOR; APPLICATIONS OF MATERIALS NOT OTHERWISE PROVIDED FOR
    • C09FNATURAL RESINS; FRENCH POLISH; DRYING-OILS; DRIERS (SICCATIVES); TURPENTINE
    • C09F1/00Obtaining purification, or chemical modification of natural resins, e.g. oleo-resins
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E50/00Technologies for the production of fuel of non-fossil origin
    • Y02E50/10Biofuels, e.g. bio-diesel

Abstract

A system is described that includes a pyrolyzer and a primary condenser. The primary condenser is coupled to the pyrolyzer and includes an input to receive pyrolytic vapors from the pyrolyzer and a solvent. The condenser is further configured to condense the pyrolytic vapors by contacting the pyrolytic vapors with the solvent to form a condensed liquid that exits the primary condenser via an output. A capture vessel receives the condensed liquid from the condenser output. A recirculator couples the capture vessel to the primary condenser input and is configured to receive the condensed liquid from the primary condenser, and to provide at least a portion of the condensed liquid as the solvent in the primary condenser. The solvent from the bio-oil component/solvent mixture is then extracted in a solvent extraction system and returned to the quenching system.

Description

PYROLYSIS SYSTEM AND METHOD FOR BIO-OIL COMPONENT
EXTRACTION
TECHNICAL FIELD
[0001] The disclosure herein relates to pyrolysis vapor condensation, and more specifically to bio-oil component extraction in a pyrolysis system.
BACKGROUND
[0002] Pyrolyzed vapors from "material" ("material" can consist of and/or contain petroleum compounds, plastics, tires, biomass (both vegetal and animal), solid wastes, extracts of liquid wastes, or a combination thereof) can, when condensed completely, produce a liquid known as bio-oil. The resulting raw bio-oil includes a high proportion of water and organic acids, and other thermal decomposition products from the pyrolized material. Raw bio-oil is often chemically unstable and typically rapidly polymerizes. Moreover the energy content or energy density of raw bio-oil is about half that of crude oil, due mostly from the amount of water and polar species contained within. Raw bio-oil is generally also very acidic and corrosive to some parts found in standard motors and turbines. Raw bio-oil often cannot be blended directly with other petroleum fuels due to its polarity as well as water content.
Upgrading and de-watering raw bio-oil has, to this point, been difficult and expensive, making conventionally produced bio-oil economically unattractive.
[0003] One method for processing bio-oil vapors obtained from a slow pyrolysis process involves quenching the vapors with biodiesel in a single-pass or stage. While this method may operate acceptably for some situations, continually feeding pure biodiesel into a quenching vessel to condense the bio-oil may prove costly for long-duration processes.
Further, significant volumes of biodiesel may prove impractical to employ for such a system. In addition, a slow pyrolysis technique often produces lower quantity bio-oil, therefore negatively affecting the economics of such a system. Moreover, resulting bio-oil/biodiesel fuel mixtures produced with bio-oil extracted via the single-pass process may have problems passing fuel combustion standards, such as ASTM D975 or D6751.
[0004] What is needed is a more economical and practical system and method to extract bio-oil components from pyrolyzed material.
BRIEF DESCRIPTION OF THE DRAWINGS
[0005] FIG. 1 illustrates a system for extracting bio-oil components from pyrolyzed material.
[0006] FIG. 2 illustrates a method for condensing bio-oil components from decomposed material fumes.
[0007] FIG. 3 illustrates further detail for one embodiment of the condensing of FIG. 2.
[0008] FIG. 4 illustrates one example of a system that employs fast pyrolysis for extracting bio-oil components from pyrolyzed material.
[0009] FIG. 5 illustrates one embodiment of a fast pyrolizer that may be used in the system of FIG. 4.
[0010] FIGs. 6A - 6H illustrate various specific embodiments of an elongated tubular housing capable of being used by the fast pyrolizer of FIG. 5.
[0011] FIG. 7 illustrates a close-up view of section 5-5 of the fast pyrolizer of FIG. 5 that employs an elevator according to one embodiment.
[0012] FIG. 8 illustrates a close-up view of section 4-4 of the fast pyrolizer of FIG. 5 that employs a heater according to one embodiment.
[0013] FIG. 9 illustrates a flow chart for one embodiment of a method of fast pyrolysis.
DETAILED DESCRIPTION
[0014] Examples of systems and methods are described below that provide for bio-oil component extraction from a material. In one embodiment, a system is described that includes a pyrolyzer and a primary condenser. The primary condenser is coupled to the pyrolyzer and includes an input to receive pyrolytic vapors from the pyrolyzer and a solvent. The condenser is further configured to condense the pyrolytic vapors by contacting the pyrolytic vapors with the solvent to form a condensed liquid that exits the primary condenser via an output. A
capture vessel receives the condensed liquid from the condenser output.
A recirculator couples the capture vessel to the primary condenser input and is configured to receive the condensed liquid from the primary condenser, and to provide at least a portion of the condensed liquid as part of or all of the solvent in the primary condenser.
[0015] Examples further provide for a method of extracting bio-oil components from vapors comprising: (a) pyrolyzing a material; (b) condensing a first amount of bio-oil component vapors produced by pyrolyzing the material with a solvent to produce a condensed liquid; and (c) recirculating at least a portion of the condensed liquid to condense a second amount of bio-oil component vapors.
[0016] In a specific example, a non-polar high boiling point solvent is used to quench bio-oil components from a material or waste material pyrolysis vapor stream. The resulting liquid is returned to the quenching zone to quench more pyrolysis vapors and load the solvent with more bio-oil components. During the quenching process, an injection rate and temperature of the quenching solution are controlled to obtain a particular quantity and quality of the resulting loaded solution. Moreover, in some embodiments, chemical species such as acetone, acetaldehyde, water and acetic acid may be separated in situ by controlling the temperature.
[0017] In another example, a bio-oil component solution is further concentrated by extracting the solvent mixed with bio-oil components and returning the solvent to the quenching system loop. A small proportion of solvent may be preserved to improve some characteristics like viscosity and solubility, for example, of the final liquid.
[0018] In a third example, a liquid is produced from pyrolysis vapors which can be used directly in conjunction with a wide variety of fuels.
[0019] SYSTEM DESCRIPTION
[0020] Although illustrative embodiments are described in detail herein with reference to the accompanying drawings, variations to specific embodiments and details are encompassed by this disclosure. It is intended that the scope of embodiments described herein be defined by claims and their equivalents. Furthermore, it is contemplated that a particular feature described, either individually or as part of an embodiment, can be combined with other individually described features, or parts of other embodiments.
[0021] FIG. 1 illustrates a system, generally designated 100, for extracting bio-oil components from pyrolyzed material. The system 100 includes a pyrolizer 110 where a material 120 is exposed to heat with little or no oxygen present. Embodiments recognize that fast and flash pyrolysis (e.g. greater than 1000 'DC/min heating rates) may provide, for example, generation of higher liquid yields of better quality of bio-oil component/solvent solution 140. The material 120 fed to the pyrolizer can consist of and/or contain petroleum compounds, plastics, tires, biomass (both vegetal and animal), solid wastes, extracts of liquid wastes, or a combination thereof, and the like.
[0022] Gases 112 generated by the pyrolysis of the material 120 are directed from the pyrolyzer 110 to an input of a primary condenser 130.
The condenser causes bio-oil component vapor to condense to a liquid form of bio-oil components. In one embodiment, the primary condenser takes the form of a quenching chamber. Other embodiments may employ non-quenching techniques. In a specific quenching embodiment, a second input to the condenser receives a condensing solvent 132. The solvent is generally sprayed onto the gases (pyrolysis vapors) to form a bio-oil component/solvent mixture that is stored in a bio-oil component/solvent mixture tank 140.
[0023] Further referring to FIG. 1, for one embodiment, a recirculator 142 couples the inlet to the condenser 130 to an outlet of the mixture tank 140 to feed at least a portion of the bio-oil component/solvent mixture back to the condenser 130. The fed back mixture is then used to quench additional bio-oil component vapors as more fully explained below. In some embodiments, a temperature controller 144 may be employed to control the temperature of the mixture going into the condenser to extract an optimal percentage of bio-oil components from the vapor stream.
[0024] With continued reference to FIG. 1, bio-oil component vapors that fail to condense in the primary condenser 130 may be directed to an input of a secondary condenser 134 along a secondary path 136. A
condensing process similar to that of the primary condenser 130 is carried out in the secondary condenser 134. A resulting liquid bio-oil component/solvent mixture from the secondary condenser is fed from an outlet to the mixture tank 140. A secondary recirculator extends from the mixture tank 140 back to the secondary condenser 134 to feed the bio-oil component/solvent mixture as the quenching agent in the secondary condenser.
[0025] The bio-oil component/solvent mixture tank 140 may maintain a consistent volume, and includes a third outlet that feeds a solvent extraction tank or vessel 150. As more fully explained below, the solvent component of the bio-oil component/solvent mixture may be separated from the mixture, and returned to the mixture tank 140. The solvent extracted from the mixture can also be returned to the line going from the bio-oil component/solvent mixture tank to the condenser 130.
The resulting bio-oil component liquid may then be fed to a solute solution tank 160, where further purification or refining may take place.
[0026] For some embodiments, the characteristics of the condensing solvent can be selected to improve the component separation of the pyrolytic gases 112. For example, the solvent polarity may provide better separation of chemicals of interest, and as such may be selected based on the intended end use. For example, in the case of a fuel compatible mixture, a non-polar or substantially non-polar solvent may be used to capture non-polar chemical species from the bio-oil components which are miscible in standard petroleum fuels.
[0027] Polar solvents can also be used as the condensing solvent. For example, use of a polar solvent as condensing solvent can cause polar compounds to be trapped, causing the non-polar species to separate in a different layer from the polar solvent. The non-polar species can then be separated. Ionic solvents can also be used and similarly removed, recycled and reused.
[0028] The primary condenser 130 may further be injected with reagents, such as, for example, steam, hydrogen, or other catalysts. The reagents can be injected into the condenser 130 or blended with the condensing solvent when applicable. The heat present in the pyrolysis vapors or condenser 130 can then be utilized to activate a chemical reaction.
[0029] The boiling and melting points of the solvent can also be varied. In an example, the solvent can be selected to have a melting point lower than that of room temperature to avoid mechanical issues, such as clogging of the condensation and transfer systems. The solvent may also be selected to have a low melting point to avoid freezing during normal ambient storage. Additionally, the boiling point of the solvent can be selected based on the use of the condenser 130 and solvent, for purpose of condensation. The solvent can further be selected to have a minimum of decomposition during condensation.
[0030] The solvent can be selected to have a boiling temperature low enough to be distilled under normal or reduced pressure while maintaining captured bio-oil components. For example the solvent can be selected from the following chemical groups; alkanes, alkenes, aromatics, alcohols, ketones, aldehydes, fatty acids, fatty esters, triglycerides, esters, their derivatives, and a combination thereof. The solvent can also include a pure solvent mixture. More complex mixtures like biodiesel, vegetable oil, motor oil, and hydrocarbon distillation cuts can also be used. Alternatively the solvent can also be ionic liquids some of which can be recycled via atmospheric or vacuum distillation.
[0031] After gases 112 are quenched by condensing solvent, a bio-oil component/solvent solution is formed and contained by the bio-oil component/solvent solution mixture tank 140. The bio-oil component/solvent solution includes components from the gases 112, particularly bio-oil components. The bio-oil component/solvent solution can be captured for a maximum recycling yield as well as minimizing the losses downstream and avoid contamination in the rest of the system.
[0032] The removal of heat by condensation is obtained when the heat of the gases 112 is transferred to the solvent. For example this can be accomplished by rapidly contacting the pyrolysis gases 112 with the solvent in the primary condenser 130. In such examples the solvent can be sprayed in the direct path of the pyrolysis gases in a quenching process. In another example, the solvent may be introduced as a falling film with the gases 112.
[0033] As noted above, in the example of FIG. 1, the bio-oil component/solvent solution contained in the bio-oil component/solvent solution mixture tank 140 is further used as the condensing solvent. To do this, the bio-oil component/solvent solution is directed back to the primary condenser 130 via the recirculator 142 as the condensing solvent for further condensation. Examples provide for the system to be operated, among other possibilities, as a batch or a continuous process. In a batch process, the bio-oil component/solvent solution mixture tank 140 is filled with the pure solvent to a level corresponding to the fraction of solvent in the final bio-oil component/solvent solution mixture. A portion of the solvent is transferred to the primary condenser 130 to condense a first portion of bio-oil components. The resulting bio-oil component/solvent solution is continually transferred back to the primary condenser 130 until the liquid level in the bio-oil component/solvent solution mixture tank has reached the filled mark, giving a final bio-oil component/solvent solution mixture with an optimum bio-oil component/solvent ratio. The recirculator is stopped and the final bio-oil component/solvent solution is entirely transferred to solvent extraction tank 150. In a continuous process, the bio-oil component/solvent solution may be slowly bled to the solvent extraction tank 150 while fresh or recycled condensing solvent is mixed with the bio-oil component/solvent solution, and this mixture is then introduced to the condensation system. For one embodiment, during a continuous process, a volume level and concentration of the mixture is kept constant.
[0034] Embodiments recognize that, after condensation by condensing solvent, desirable components (e.g. bio-oil components) or undesirable components (e.g. impurities) may still be present in gaseous, liquid or other forms. As such, the embodiment of FIG. 1 includes the secondary condenser 134 to receive a secondary stream from the primary condenser 130 for further condensation. Small quantities of the solvent may be present in the secondary stream 136 where, for example, a solvent has a relatively high boiling point. The solvent can be separated or extracted from the secondary condenser 134 by the solvent extraction system and then returned to the quenching process.
[0035] By adjusting the exit temperature of the primary condenser 130 it is possible to selectively extract bio-oil components from the bio-oil component/solvent solution. For example, by controlling a gas outlet exit temperature of the primary condenser 130 to about 125 degrees C, it is possible to remove the acetic acid, water, methanol, and all other light chemical species having a boiling point inferior to the set temperature.
This results in an anhydrous bio-oil component/solvent solution containing little organic acids which can be stripped during the solvent recycling step.
[0036] When the bio-oil component/solvent solution is directed into the solvent extractor 150, the condensing solvent can be removed by heating and condensing the vapors either by atmospheric or reduced pressure distillation, evaporation, and flash evaporation, or other methods. The bio-oil component/solvent solution can be cooled or the heat absorbed from the primary condenser 130 can be used beneficially to help in solvent extraction 150. The solvent is then usually, but not necessarily, purified further before being sent back to the primary condenser 130. Although the solvent can be extracted in its totality, the resulting bio-oil components solution can also contain a fraction of the condensing solvent in order to improve its physicochemical characteristics, like viscosity. Alternatively, another solvent can also be added to improve the characteristics of the bio-oil component solution.
This resulting bio-oil component solution or concentrate is chemically and physically stable and can be stored, blended or further processed while maintaining chemical properties.
[0037] METHOD DESCRIPTION
[0038] FIG. 2 illustrates a method for using a solvent to obtain bio-oil components from thermally decomposed material fumes. Reference is made to the embodiment of FIG. 1 in describing elements of FIG. 2.
[0039] At (210), a material is thermally decomposed to produce vapors. As described regarding FIG. 1, the vapors may include components which, when condensed (e.g. quenched), produce bio-oil components. For example, with reference to FIG. 1, a pyrolyzer may be used to decompose the material in the absence of oxygen to produce the vapors. In an example, the vapors produced in (210) can be obtained by heating the material (e.g. by exposure to a heating rate of 10,000 degrees Celsius/minute) without oxygen so that the material decomposes, producing gases.
[0040] At (220), the vapors are provided to a condenser, such as a quenching reactor. The quenching reactor cools the gases from (210) by, for example, exposure to a quenching solution. Examples of quenching reactors include a condenser, such as described in FIG. 1, provided with a solvent. Among other forms, the quenching solution may be a pure solvent (e.g. substantially of a single kind of compound), a mixture of different compounds, or a loaded solvent (e.g. including having been exposed to, and loaded, with bio-oil components as more fully described below in (230) and (240)).
[0041] Further referring to FIG. 2, after being provided to the quenching reactor, the heated vapors are quenched at (230) by exposure to the quenching solution, and the quenching solution is loaded with bio-oil components from the heated vapors at (240). The quenching solution, material and condenser may be selected or configured so that particular components are loaded into the solvent. For example, aspects of the steps described above at (210) through (230) can be varied for production of a particular solvent at (240). By way of example, at (210) the injection rate of the solvent and temperature of the quenching solution may be manipulated by the temperature controller to control the quantity and quality of the resulting loaded solution. Moreover, the temperature can be controlled to separate undesired chemical species.
[0042] At (250) the loaded solvent having bio-oil components is recirculated to further quench vapors. Examples provide for (230)-(250) to be performed, among other possibilities, as a batch or a continuous process. In a batch process, once a target concentration of chemical species is attained, the loaded solvent is transferred to the solvent extraction tank or system. In a continuous process, the loaded solvent is slowly bled to the solvent extraction tank or system while fresh or recycled solvent is mixed with the loaded solvent, and this mixture is then introduced to the quenching system. During a continuous process a level and concentration of the mixture is kept constant.
[0043] The solvent can then be separated from the bio-oil components for reuse, and for use of the bio-oil components, at (260).
[0044] FIG. 3 illustrates further detail for one specific quenching method corresponding to the condensing step 230 described above in FIG. 2. The quenching process involves introducing bio-oil component gases into a quenching reactor, at 302, at a temperature selected between 350-750 degrees. Solvent may then be introduced into the reactor, at 304, at a temperature that may be based on a temperature of captured bio-oil components from the quenching process, more fully explained below. The solvent may then be sprayed or otherwise rapidly drawn into contact with the bio-oil component vapor, at 306. The resulting exchange of heat results in the condensation of a large portion of the bio-oil component vapor to bio-oil components liquid.
[0045] Further referring to FIG. 3, once the bio-oil components condense into liquid, it is then captured, at 308, and the resulting temperature monitored, at 310. For some embodiments, a resulting temperature of about 125 degrees C results in an optimal extraction of desired bio-oil components liquid from the vapor. A determination is carried out, at 312, as to whether the captured liquid is approximately 125 degrees C. If so, then no temperature adjustments are carried out on newly fed solvent into the quenching reactor. Should the temperature not be approximately 125 degrees C, then a temperature adjustment is made, at 314, to increase the temperature of the solvent (if the resulting captured liquid is less than 125 degrees) or reduce the temperature of the solvent (if the resulting captured liquid is higher than 125 degrees C).
This temperature control mechanism optimizes the volume and quality of bio-oil components liquid extracted during each quenching operation.
[0046] EXAMPLE
[0047] For one specific example of system operation consistent with the disclosure above, a material in the form of waste wood was directed into a flash pyrolysis oven where it was rapidly heated at a rate in excess of 10,000 'DC/min up to about 500-550 C. The pyrolysis gases generated were rapidly removed and separated from hot biochars and directed, through a heated duct kept near 500 C, to the quencher. There, the pyrolysis vapors were sprayed-in-flight with a relatively cold mixture of condensed/quenched bio-oil components in undecane. The condensed/quenched resulting liquid dropped into the primary quencher tank and was kept at about 125 0C, while the unquenched chemical species having a boiling point inferior to 125 0C went through the quencher tank to exit to a secondary quencher/condenser for collection.
From the secondary quencher/condenser, the non-condensable gases were directed to a thermal oxidizer, returned to the process for heat generation, for the generation of other chemicals from catalysts, used elsewhere in the plant operation or transported off plant for other usage.
The resulting concentration in the primary quencher tank was maintained at about 50% bio-oil components/undecane.
[0048] At the same rate that the 50% bio-oil components/undecane solution was removed from the quencher tank, pure undecane was mixed with the 50% bio-oil components/undecane before introduction to the quenching zone. The liquid level in the quencher tank was kept constant.
The 50% bio-oil components/undecane solution removed from the quenching tank was directed to the solvent extraction system while keeping it at 125 0C. The solvent extraction system was maintained at a constant temperature for the undecane to evaporate at about 190-2000C.
Alternatively, a vacuum system could be used to extract the undecane and possibly use less energy than normal distillation at ambient pressure.
The totality of the undecane was extracted. The resulting bio-oil components were cooled and stored for future blending or transformation.
The undecane extracted could be further purified and then stored or returned for further quenching.
[0049] In such an embodiment, undecane is a pure solvent so its extraction can be done at a single temperature which is better for process control. When the process uses a pure solvent, no residues are left to accumulate in the system and the final product.
[0050] The utilization of an alkane as a co-solvent precipitates chemical species responsible for unacceptable levels of micro-carbon residues in the final blend. Moreover, in cases where a small quantity of solvent is still present in the final product, the gel point of undecane is significantly low (-25 0C) to make the product compatible in environments with sub-zero temperatures.
[0051] The system, apparatus, and methods described above lend themselves well to extracting a purified form of bio-oil components liquid that may be mixed with, for example, diesel at fairly high mixture percentages. This is due in large part on the purity of the bio-oil components via the system and methods described herein, which results in lower residues forming during combustion of a purified bio-oil component/diesel fuel mixture. As a result, diesel mixed with a high percentage of bio-oil components may pass standards mandated by diesel fuel standards such as ASTM D975.
[0052] FIG. 4 illustrates a system, generally designated 400, that employs fast pyrolysis in an application for extracting bio-oil components.
It is but one example of an application for fast pyrolysis. The system 400 includes a pyrolizer 402 where material is exposed to heat with little or no oxygen present. The pyrolized material is then fed to a condenser 404 where, for example, bio oil may be condensed from the gases generated by the pyrolizer. An oil extractor 406 may then extract the condensed bio oil for use as a fuel. The material fed to the pyrolizer 402 may contain petroleum compounds, plastics, tires, biomass (both vegetal and animal), solid wastes, extracts of liquid wastes, or a combination thereof, and the like. The material is usually solid, but can also be or contain liquids.
[0053] One specific embodiment of a pyrolysis reactor, or pyrolizer, generally designated 500, is shown in FIG. 5. The pyrolizer includes an elongated hollow tube or reactor 502 formed of metal with a feed inlet 504 and an outlet 506. To minimize complexity, the interior of the tube forms an unobstructed flow path, and includes no moving parts. The flow path includes at least one interior surface 508 that forms a contact surface for material progressing through the tube.
[0054] The elongated hollow tube, or reactor 502, may be formed from different alloys of stainless steel to avoid oxidation. However, a proper selection will often depend on the mechanical, electrical and magnetic properties of the metal. Carbon steel can also be used. Although the corrosion resistance of carbon steel is much less than that of stainless steel, considering that the inside of the reactor is usually not exposed to oxygen, and also its price, electrical properties and magnetic properties, standard carbon steel may be very attractive to use for an economical reactor. The magnetic properties are important depending on the selection of the heat generation device, as is explained below. Aluminum and aluminum alloys can also be used as building materials for the reactor. Any metal cladding can also be used for improved passivation to the harsh conditions the reactor can be subjected to. Electro-deposition, anodizing are also other methods to passivate the metal on its surface to avoid oxidation or reduction of the ramp reactor. These coating techniques can be very attractive to keep the costs low while still using the core material's characteristics.
[0055] Various alternative embodiments for the shape of the elongated reactor 502 are shown in FIGs 6A - 6H. The reactor could basically have any cross-sectional shape, but those offering the best material-surface contact are those with a flat bottom. This optimizes the conduction mode of heating. Moreover, the opposite wall of the contact surface must also not be placed too far from the material falling through it, in order to take advantage of radiation heating. Square, rectangular, or half-circle reactors are preferable. However, other cross-section configurations could also be used, like triangular or trapezoidal. It is also possible to transit to other cross-sectional shapes and thicknesses along the tube length.
[0056] In its most straightforward form, the reactor is a straight tubular element from the feed inlet to the outlet, and shown in FIG. 6A, at 602. In this case, and if the coefficient of friction is neglected (since the material is degassing rapidly), the material entering the tube will have a constant acceleration. In other words, the speed of the material sliding through the reactor will constantly increase, until it exits the outlet.
[0057] FIG. 6B illustrates an alternative tube construction that maintains the rectangular cross section, but curves the tube, at 604. This results in the flowing material decreasing its acceleration, but at a constant speed. FIG. 6C illustrates an embodiment where the tube curves laterally back and forth (zigzagged), at 606, to increase path and residence time, and also to increase the mixing of the material falling through the flow path. To further mix the material as it flows through the tube, plural fixed transverse mixing elements 608 may be employed throughout the length of the tube, as shown in FIG. 6D.
[0058] For many applications, a straight elongated hollow tube works well for its straightforward nature and robustness during operation.
However, in some situations, space is limited. FIG.s 6E - 6G illustrate tube constructions that employ a coiled configuration to minimize space, yet maximize surface area contact for pyrolysis. It is possible to twist the tube while maintaining the optimum free-sliding angle for the material to flow through to be optimally thermally treated. The general material properties will help determine the slopes (elevation angle of tube) for optimum spread and speed for thermal treatment.
[0059] FIG. 6E shows a high coil tube, at 610. For this configuration, gravity is still the main drive force to move the material through the length of the tube. In FIG. 6F, at 612, a more compact form of the coiled tube is shown that cannot rely on gravity alone to move the material. For such a construction, a mechanical device such as a vibration mechanism or pressure device may be employed to cooperate with gravity in moving the material through the flow path.
[0060] For relatively long residence times, the tube may be relatively flat, such as that shown in FIG. 6G, at 614. For even longer residence times, it is possible to force the substance to be treated upwards the reactor ramp. In such case, when a vibration device is attached to the reactor, a mesh or rough reactor floor will help prevent the substance from flowing back downward to the inlet. Moreover, such a compact coiled reactor can alternatively use an open top, or U-shaped ramp, to rapidly remove the gases generated during thermal treatment. In this case, an outer shell surrounding the whole coil may be used. However, the radiative mode of heat transfer can still be used but only when the coil is with a very low profile. The heat from the coil floor above will serve to heat the material by radiation. Alternatively, an enclosed coil could also have a series of holes along its side walls to rapidly remove the gases in the same manner as the topless ramp. In this later design detail, as shown in FIG. 6H, an outer shell 616 may be utilized to contain the gases.
[0061] Other variations in the reactor shape are possible. Because the organic particles lose weight and volume during their thermal treatment, in regards to the optimization of the conduction mode of heat transfer as well as optimization of the heating source, it is possible that the reactor width could be reduced along the path of the material falling through. Furthermore, the width reduction would also reduce the overall weight and cost of the reactor. The reactor ramp may also be constructed of separate longitudinal elements joined together, instead of one large tube. In some cases, the joining mechanism is preferred to be non-electrically conductive, with a non-electrically conductive joint.
[0062] Referring back to FIG. 5, the elongated hollow tube is oriented such that the feed inlet 504 is elevated relative to the outlet 506. Where the relative elevation is at or greater than a critical free-sliding angle, the force of gravity directs the material downwardly through the tube. In some situations, the relative elevation angle may be less than the critical free-sliding angle. In such circumstances, an additional driving force such as the vibration or pressure device noted above may be used to assist gravity in drawing the material through the tube. Generally speaking, the critical free-sliding angle depends on the characteristics of the material, its density, its weight, particle size, etc. Injection of high velocity oxygen-less gas would help move the organic material through the reactor but would also disturb the material bed and most likely lift if from the bottom, thus breaking the heat conduction efficiency. For this reason, a mechanical means, such as through vibration, to move the material along the reactor is preferred.
[0063] Further referring to FIG. 5, and in particular section 4-4 (shown close-up in FIG. 7), the angle of the reactor can be fixed for a given process but the system can also incorporate mechanical elements permitting for the reactor angle to be changed for optimization of the process. To allow for adjusting the elevation angle, a pivot 702 may be employed for raising and lowering the tube. While FIG. 7 shows a half-pivot, which enables for easy removal of the ramp, various other shapes may also be employed. A support (not shown) at the other end of the tube keeps the feed inlet at the desired height.
[0064] FIG. 8 illustrates a close-up view of section 5-5 of FIG. 5, and shows one specific embodiment of a heater 802 that employs strip heater elements 804 that are held against the periphery of the reactor by a removable clip 806. Instead of a removable clip, permanent mounting materials may be used to secure the heater elements to the tube. As seen in FIG. 5, multiple heaters are distributed along the length of the reactor to optimize the heating. Heating rods, strips, or other types of Joule or infrared heaters can be attached or be part of the reactor faces. As a minimum, only the contact (bottom) face should be heated. With proper insulation the other faces could reach a temperature sufficient enough to help the fast heating process. Ultimately, all faces should be heated in this fashion for optimal heat transfer to the substance flowing through the reactor. Another advantage of such system is the possibility of heating different zones to different temperatures.
[0065] As alternatives to the strip heaters described above, various other heating methods could be used to heat the reactor. For example, gas burners are maybe the most well developed methods for heating processes. However, their efficiencies are not as good as some other methods. The efficiency can be improved when integrated with other processes from a pyrolysis plant, like using syngas from pyrolysis. In order to use gas burners with the present ramp reactor, it will be important to use a shell on the ramp to contain the combustion gases, such as that shown in FIG. 6H. A layer of high efficiency thermal insulator significantly reduces heat loss. The burners can be installed inside the outer shell of the ramp or produced separately in a burner box. The hot combustion gases can then be directed inside the ramp reactor outer shell to heat the ramp uniformly.
[0066] Heat transfer fluid (i.e. air, combustion gases, syngas, thermal oil, ionic or liquid salts, fluidized solid particulates, etc.) can be heated remotely using gas burners or via electrical heating and subsequently transferred to a shell built around the reactor where the heat will be transferred to all faces of the reactor. The fluid may be returned to the heating box to be reheated or discarded appropriately.
[0067] The reactor ramp could also be heated directly using the Joule heating effect by an electrical current passing through it. In this case, the ramp should be completely isolated electrically from all other equipment attached to it, including sensors. When the ramp includes more than one electrically insulated section, it is possible to heat each section independently to different temperatures.
[0068] Induction heating can also be used to heat the reactor. A
single induction coil can be placed around a straight reactor. It is also possible to use multiple coils. The multiple coils can be controlled individually by one or more induction generators. A single induction generator can also be used in a switching mode using an internal or external switcher to alternatively turn on and off each coil. In this manner, a smaller induction generator can be used to heat a very long section of reactor. Two spiral induction coils can also be used to heat a spiral reactor. A series of spiral reactors can be heated by a series of spiral coils. As is often the case, standard water cooled induction coils must be thermally insulated from the heated ramp as not to cool down the ramp reactor. However, it is also possible to use wire coils, but in this case there would be advantages to include the heat generated by the current going through the wires by installing them in close physical proximity to the ramp element, inside the insulation layer.
[0069] In the case of induction heating, a ferro-magnetic construction material for the ramp also offers an added advantage of adding magnetic and electrical hysteresis effects to the standard Eddie current induction heating, increasing the overall induction effect which results in a more efficient heating of the ramp reactor. Moreover, in the case of pyrolysis of material, given a high enough induction current, it is also possible to turn the charred layer on the material being pyrolyzed into a heating device. It is known that graphite like material can heat up when submitted to an electrical induction field. Induction heating can also be used to generate heat directly in the bulk of the material particles being pyrolyzed, always in close proximity to the unpyrolyzed material, inducing a very high heating rate, but also high liquid yields. This latest phenomenon can also be extended to other applications, including catalysis, cracking, etc.
[0070] The rate of heating is important for complete thermal treatment within the time of flight inside the reactor, as well as obtaining maximum liquid yield. Although a single method for heating the reactor ramp could be used, it could be advantageous to use different heating devices to heat different zones along the path of the ramp reactor. The following is simply one example but many cross features can be used consistent with this idea. A thin section for the first section could be used along with induction heating to have a very rapid heat transfer/generation as fresh and relatively cold material comes in through the ramp reactor entrance, the ramp could then transition to a thicker construction material and be heated using electrical heating strips. The heat generation/transfer in that reactor zone does not need rapid response but a sustained temperature since the material was already preheated in the first zone.
These changes in thickness and heating zones can help maximize the thermal treatment efficiencies while reducing equipment and operation costs.
[0071] The fast thermal treatment apparatus described herein can be used for many different applications, including thermal treatment of solids, liquids and gases. It can be used for drying or evaporation. It can be used as a fast chemical reactor. It can also be used for fast pyrolysis and gasification. It can also be used in many different applications where a control of the atmosphere is necessary.
[0072] FIG. 9 illustrates high-level steps for a method of pyrolizing a material. Reference is made to the embodiment of FIG. 5 in describing elements of FIG. 9.
[0073] At 902, a fast pyrolysis reactor is provided that includes an feed inlet, an outlet, and internal walls. The reactor inlet is oriented to a non-vertical elevation with respect to the outlet for gravity feed flow, at 904. A user may then feed material into the reactor inlet, at 906. As the material progresses through the reactor, it is heated via direct heat transfer between the material and at least one of the internal walls, at 908. The resulting pyrolized material and gases may then be further processed, depending on the application, at 910.
[0074] Those skilled in the art will appreciate the benefits and advantages afforded by the embodiments disclosed herein. By providing a recirculator to recycle a bio-oil component solvent mixture in a condensing process as well as extracting and recycling the solvent, significant logistical and cost savings may be realized in the extraction of bio-oil components in a pyrolysis system. Further, by controlling the temperature of the solvent based on a desired end-temperature, an optimal extraction during condensation may be attained.
[0075] It is contemplated for examples described herein to extend to individual elements and concepts described herein, independently of other concepts, ideas or system, as well as for examples to include combinations of elements recited anywhere in this application. Although examples are described in detail herein with reference to the accompanying drawings, it is to be understood that the invention is not limited to those precise examples. As such, many modifications and variations will be apparent to practitioners skilled in this art. Accordingly, it is intended that the scope of the invention be defined by the following claims and their equivalents. Furthermore, it is contemplated that a particular feature described either individually or as part of an example can be combined with other individually described features, or parts of other examples, even if the other features and examples make no mentioned of the particular feature. Thus, the absence of describing combinations should not preclude the inventor from claiming rights to such combinations.

Claims (25)

1. A system for pyrolyzing material, the system comprising:
a pyrolyzer;
a primary condenser, coupled to the pyrolyzer and configured to receive pyrolytic vapors from the pyrolyzer, and further configured to condense the pyrolytic vapors by contacting the pyrolytic vapors with a solvent, to form a condensed liquid, the condensed liquid being separated into at least one bio-oil component and a solvent component to form a bio-oil component/solvent mixture;
a capture vessel to receive the condensed liquid; and a recirculator coupled to the capture vessel and the primary condenser, the recirculator configured to provide at least a portion of the solvent component as the solvent used in the primary condenser.
2. (Canceled) 3. The system according to Claim 1, further comprising:
an extraction system to extract the solvent component from the bio-oil component/solvent mixture.
4. The system according to Claim 3, wherein the extracted solvent component or bio-oil component/solvent mixture is recycled for use in the primary condenser.
5. The system according to Claim 3, wherein the extraction system operates to extract the solvent component from the mixture in a batch or continuous basis.
6. The system according to Claim 3, wherein the extraction system comprises one from the group of an atmospheric or reduced pressure distiller, evaporator, flash evaporator, or others.
7. The system according to Claim 3, wherein the extracted solvent component can be returned directly to the primary condenser or temporarily stored for future use.

8. The system according to Claim 3, wherein the extracted solvent component can be replaced partially or in totality by another solvent or solvents.
9. The system of Claim 1, wherein the solvent comprises one or more from the group including alkanes, alkenes, aromatics, alcohols, ketones, aldehydes, fatty acids, fatty esters, triglycerides, esters, their derivatives, and a combination thereof.
10. The system of Claim 1, further comprising a temperature controller coupled to the primary condenser to control at least one of (i) a temperature of the solvent and (ii) a temperature of the vapors.
11. The system of claim 10, wherein the temperature of the solvent introduced to the primary condenser is adjusted based on a threshold temperature of the bio-oil component/solvent mixture 12. The system of claim 1, wherein the primary condenser comprises a quenching reactor.
13. The system of Claim 1, further comprising a processor to process uncondensed gases.
14. The system of Claim 1, further including a secondary condenser coupled to the primary condenser to receive uncondensed bio-oil component vapors from the primary condenser, the secondary condenser having an output coupled to the capture vessel.
15. The system of Claim 14, wherein a secondary recirculator feeds back a portion of the condensed liquid from the capture vessel to the secondary condenser to condense the uncondensed bio-oil component vapors.
16. A method of extracting bio-oil components from a bio-oil vapor, the method comprising;
(a) pyrolyzing a material 10 generate a bio-oil vapor stream;

(b) condensing a first amount of the bio-oil vapor stream with a solvent to produce a condensed liquid, the condensed liquid being separated into at least one bio-oil component and a solvent component to form a bio-oil component/solvent mixture;
and (c) recirculating at least a portion of the solvent component to further condense a second amount of bio-oil component vapor 17. (Canceled) 18. The method of Claim 16, further comprising controlling at least one of (i) a temperature of the solvent and (ii) a temperature of the bio-oil component vapor stream.
19. The method of Claim 18, wherein the controlling of the temperature of the solvent is based on a desired temperature of the condensed liquid.
20. The method of Claim 16, wherein the condensing comprises quenching.
21. The method of Claim 16, further comprising processing of non-condensable gases 22. The method of Claim 16, further comprising extracting the solvent component from the bio-oil component/solvent mixtures.
23. The method of Claim 22, further comprising reusing the extracted solvent component for use in the condensing.
24. The method of Claim 22, wherein the extracting extracts at least a portion of the solvent component from the mixture in a batch or continuous basis.
25. The method of Claim 22, wherein the extracting comprises at least one of mechanical, chemical, physical or physicochemical methods.
26. The method of Claim 22, wherein the extracting further comprises returning the extracted solvent component directly for condensing or storing for future use.

27. A system comprising:
a fast pyrolizer to pyrolize material;
a condenser coupled to the fast pyrolizer to receive the pyrolized material and condense pyrolized gas into a liquid;
an oil extractor to extract bio-oil from the condensed liquid; and wherein the fast pyrolizer includes an elongated tubular housing having a feed inlet to receive material, an outlet, and a flow path with an internal contact surface extending from the inlet to the outlet, the feed inlet oriented to a non-vertical relative elevation with respect to the outlet to allow a flow of the material via gravity and/or vibration, at least a portion of the internal contact surface to directly contact the material; and a heater to heat the internal contact surface such that the material is heated via direct thermal transfer from the internal contact surface such that pyrolysis occurs in the flow path.
1. A system for pyrolyzing material, the system comprising:
a pyrolyzer;
a primary condenser, coupled to the pyrolyzer and configured to receive pyrolytic vapors from the pyrolyzer, and further configured to condense the pyrolytic vapors by contacting the pyrolytic vapors with a solvent, to form a condensed liquid, the condensed liquid being separated into at least one bio-oil component and a solvent component to form a bio-oil component/solvent mixture;
a capture vessel to receive the condensed liquid; and a recirculator coupled to the capture vessel and the primary condenser, the recirculator configured to provide at least a portion of the solvent component as the solvent used in the primary condenser.
2. The system according to Claim 1, further comprising:
an extraction system to extract the solvent component from the bio-oil component/solvent mixture.
3. The system according to Claim 2, wherein the extracted solvent component or bio-oil component/solvent mixture is recycled for use in the primary condenser.
4. The system according to Claim 2, wherein the extraction system operates to extract the solvent component from the mixture in a batch or continuous basis.
5. The system according to Claim 2, wherein the extraction system comprises one from the group of an atmospheric or reduced pressure distiller, evaporator, flash evaporator, or others.
6. The system according to Claim 2, wherein the extracted solvent component can be returned directly to the primary condenser or temporarily stored for future use.
7. The system according to Claim 2, wherein the extracted solvent component can be replaced partially or in totality by another solvent or solvents.
8. The system of Claim 1, wherein the solvent comprises one or more from the group including alkanes, alkenes, aromatics, alcohols, ketones, aldehydes, fatty acids, fatty esters, triglycerides, esters, their derivatives, and a combination thereof.
9. The system of Claim 1, further comprising a temperature controller coupled to the primary condenser to control at least one of (i) a temperature of the solvent and (ii) a temperature of the vapors.
10. The system of claim 9, wherein the temperature of the solvent introduced to the primary condenser is adjusted based on a threshold temperature of the bio-oil component/solvent mixture.
11. The system of claim 1, wherein the primary condenser comprises a quenching reactor.
12. The system of Claim 1, further comprising a processor to process uncondensed gases.
13. The system of Claim 1, further including a secondary condenser coupled to the primary condenser to receive uncondensed bio-oil component vapors from the primary condenser, the secondary condenser having an output coupled to the capture vessel.
14. The system of Claim 13, wherein a secondary recirculator feeds back a portion of the condensed liquid from the capture vessel to the secondary condenser to condense the uncondensed bio-oil component vapors.
15. A method of extracting bio-oil components from a bio-oil vapor, the method comprising:
(a) pyrolyzing a material to generate a bio-oil vapor stream;

(b) condensing a first amount of the bio-oil vapor stream with a solvent to produce a condensed liquid, the condensed liquid being separated into at least one bio-oil component and a solvent component to form a bio-oil component/solvent mixture;
and (c) recirculating at least a portion of the solvent component to further condense a second amount of bio-oil component vapor.
16. The method of Claim 15, further comprising controlling at least one of (i) a temperature of the solvent and (ii) a temperature of the bio-oil component vapor stream.
17. The method of Claim 16, wherein the controlling of the temperature of the solvent is based on a desired temperature of the condensed liquid.
18. The method of Claim 15, wherein the condensing comprises quenching.
19. The method of Claim 15, further comprising processing of non-condensable gases.
20. The method of Claim 15, further comprising extracting the solvent component from the bio-oil component/solvent mixtures.
21. The method of Claim 20, further comprising reusing the extracted solvent component for use in the condensing.
22. The method of Claim 20, wherein the extracting extracts at least a portion of the solvent component from the mixture in a batch or continuous basis.
23. The method of Claim 20, wherein the extracting comprises at least one of mechanical, chemical, physical or physicochemical methods.
24. The method of Claim 20, wherein the extracting further comprises returning the extracted solvent component directly for condensing or storing for future use.
25. A system comprising:
a fast pyrolizer to pyrolize material;
a condenser coupled to the fast pyrolizer to receive the pyrolized material and condense pyrolized gas into a liquid;
an oil extractor to extract bio-oil from the condensed liquid; and wherein the fast pyrolizer includes an elongated tubular housing having a feed inlet to receive material, an outlet, and a flow path with an internal contact surface extending from the inlet to the outlet, the feed inlet oriented to a non-vertical relative elevation with respect to the outlet to allow a flow of the material via gravity and/or vibration, at least a portion of the internal contact surface to directly contact the material; and a heater to heat the internal contact surface such that the material is heated via direct thermal transfer from the internal contact surface such that pyrolysis occurs in the flow path.
CA2913180A 2013-05-31 2014-05-28 Pyrolysis system and method for bio-oil component extraction Abandoned CA2913180A1 (en)

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US13/907,494 2013-05-31
US13/907,494 US10589187B2 (en) 2013-05-31 2013-05-31 Pyrolysis system for bio-oil component extraction
US14/046,883 US20150096879A1 (en) 2013-10-04 2013-10-04 Fast pyrolysis apparatus and method
US14/046,883 2013-10-04
PCT/US2014/039853 WO2014193997A1 (en) 2013-05-31 2014-05-28 Pyrolysis system and method for bio-oil component extraction

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