Patent Application
20160184796
The present disclosure generally relates to processing of cellulosic biomass solids, and, more specifically, to methods and systems for processing a reaction product comprising lignin that may be obtained by a hydrothermal reaction of cellulosic biomass.
This section is intended to introduce various aspects of the art, which may be associated with exemplary embodiments of the present invention. This discussion is believed to assist in providing a framework to facilitate a better understanding of particular aspects of the present invention. Accordingly, it should be understood that this section should be read in this light, and not necessarily as admissions of any prior art.
A number of substances of commercial significance may be produced from natural sources, including biomass. Cellulosic biomass may be particularly advantageous in this regard due to the versatility of the abundant carbohydrates found therein in various forms. As used herein, the term “cellulosic biomass” refers to a living or formerly living biological material that contains cellulose. The lignocellulosic material found in the cell walls of higher plants is the world's largest source of carbohydrates. Materials commonly produced from cellulosic biomass may include, for example, paper and pulpwood via partial digestion, biofuels, including bioethanol by fermentation.
Development of fossil fuel alternatives derived from renewable resources have received recent attention. Cellulosic biomass has garnered particular attention in this regard due to its abundance and the versatility of the various constituents found therein, particularly cellulose and other carbohydrates. Despite promise and intense interest, the development and implementation of bio-based fuel technology has been slow. Existing technologies have heretofore produced fuels having a low energy density (e.g., bioethanol) and/or that are not fully compatible with existing engine designs and transportation infrastructure (e.g., methanol, biodiesel, Fischer-Tropsch diesel, hydrogen, and methane). Moreover, conventional bio-based processes have typically produced intermediates in dilute aqueous solutions (>50% water by weight) that are difficult to further process. Energy- and cost-efficient processes for processing cellulosic biomass into fuel blends having similar compositions to fossil fuels would be highly desirable to address the foregoing issues and others.
Further, in addition to the desired carbohydrates, other substances may be present within cellulosic biomass that can be especially problematic to deal with in an energy- and cost-efficient manner. For example, during cellulosic biomass processing, significant quantities of lignin present in cellulosic biomass may lead to fouling of processing equipment, potentially leading to costly system down time. The lignin can also lead to realization of a relatively low conversion of the cellulosic biomass into useable substances per unit weight of feedstock.
As evidenced by the foregoing, an efficient conversion of cellulosic biomass into fuel blends and other materials is a complex problem that presents immense engineering challenges. The present disclosure addresses these challenges and provides related advantages as well.
Recovery of various compounds from a product of reactions involving cellulosic biomass may be challenging due to the various components contained therein, including lignin. The present disclosure provides methods and systems for processing cellulosic biomass, particularly separation of a reaction product of a hydrothermal reaction containing lignin and lignin-derived products, where the reaction product is a mixture of various compounds and typically in more than one liquid phase. One phase of the reaction product is usually water. While feasible, distillation of a reaction product with multiple liquid phases that contains water into various product fractions can result in poor product separation and steam stripping, where water vapors carry heavier compounds, like phenols, into the overhead fraction. Although this may be addressed by conducting the distillation at higher pressure and temperature where multiple phases can be reduced or minimized, the higher pressure and temperature presents additional expenses including equipment costs, as well as risks to product from onset of undesired degradation reactions at higher temperatures. While the water in the reaction product can be removed through flashing prior to full distillation into product fractions, doing so can also result in steam stripping, thereby resulting in less efficient product separation in a subsequent distillation process.
The methods and systems provided in the present disclosure address the foregoing issues by providing liquid-liquid extraction to isolate the phases so that the phases can be further processed independent of each other. Once separated, the aqueous phase can be subject to flashing with reduced carryover of the less volatile organic components, including phenols and various oils, into the overhead distillate because a majority of the excess amount of these components which is not soluble in water has been removed. The remaining low concentration of organic components that is soluble in water is subject to a dilution effect that minimizes vaporization. Flashing of the aqueous phase can recover various light compounds that can be further processed into a fuel product. Light compounds can include those with a normal boiling point of less than about 150 degrees C., including but not limited to monohydric alcohols (e.g., mono-oxygenates), aldehydes, ketones, acids, and any combination thereof.
Flashing or distillation of a single phase of the non-aqueous phase(s) with reduced water concentration can achieve adequate product separation at a lower temperature whereas higher temperatures would be needed to obtain a single liquid phase at higher concentrations of water, to achieve similar efficient product separations in distillation The product fractions from distillation of the non-aqueous phase(s) can include at least an overhead fraction comprising light compounds, a middle fraction comprising lignin and lignin-derived products, including phenols, and a bottom fraction comprising heavy compounds with normal boiling points above about 350° C. The distillation can be performed to provide more than one middle fraction. For instance, distillation can be operated to provide a first middle fraction with a normal boiling point of about 150 to 250 degrees C. and a second middle fraction with a higher normal boiling point of 200 to 350 degrees C. Distillation can also be operated to provide a middle fraction with a normal boiling point of about 150 to 350 degrees C.
The light compounds recovered from the aqueous phase and the non-aqueous phase(s) can optionally be combined for further processing into a fuels product. A middle fraction recovered from the non-aqueous phase(s) can be recycled in the process in various manners, including for use as solvent or for further conversion to other intended products. For instance, a middle fraction can be provided to one or more hydrothermal reaction steps that generate the reaction product. In particular, a middle fraction comprising phenols can be used as a digestion solvent in a hydrothermal reaction. To improve product separation, the reaction product can be subject to a base-catalyzed depolymerization step prior to the liquid-liquid extraction or phase separation step to reduce the viscosity of the reaction product.
In particular, the present disclosure provides a method comprising: heating cellulosic biomass solids, molecular hydrogen, a catalyst capable of activating molecular hydrogen, and a digestion solvent in a reactor in a first reaction zone to form a first reaction product; subjecting the first reaction product to a base catalyzed depolymerization reaction to produce a depolymerized reaction product; providing at least a portion of the depolymerized reaction product to a separation zone comprising a liquid-liquid phase separation or extraction unit to obtain an aqueous stream and a non-aqueous stream, wherein the aqueous stream comprises a major portion of water in said portion of the depolymerized reaction product; providing at least a portion of the non-aqueous stream to a distillation unit to recover an overhead fraction, a middle fraction, and a bottom fraction.
In addition, the present disclosure provides another method comprising: heating cellulosic biomass solids, molecular hydrogen, a catalyst capable of activating molecular hydrogen, and a digestion solvent in a reactor in a first reaction zone to form a first reaction product; heating at least a portion of the first reaction product, molecular hydrogen, and a catalyst capable of activating molecular hydrogen in a reactor in a second reaction zone to form a second reaction product; subjecting at least one of the first reaction product and the second reaction product to a base catalyzed depolymerization reaction to produce a depolymerized reaction product; providing at least a portion of the depolymerized reaction product to a separation zone comprising a liquid-liquid phase separation or extraction unit to recover an aqueous stream and a non-aqueous stream, wherein the aqueous stream comprises a major portion of water in said portion of the second reaction product; providing at least a portion of the non-aqueous stream to a distillation unit to obtain an overhead fraction, a middle fraction, and a bottom fraction.
In addition, the present disclosure provides a system comprising: a first reaction zone comprising a reactor configured heat cellulosic biomass solids, molecular hydrogen, a catalyst capable of activating molecular hydrogen, and a digestion solvent to form a first reaction product; a base catalyzed depolymerization unit in fluid communication with an outlet of the reactor in the first reaction zone to receive the first reaction product, wherein the base catalyzed depolymerization unit is configured to produce a depolymerized reaction product; and a separation zone comprising: a liquid-liquid extraction or phase separation unit having an inlet in fluid communication with an outlet of the base catalyzed depolymerization unit to receive the depolymerized reaction product, wherein the liquid-liquid extraction or phase separation unit is configured to provide an aqueous stream and a non-aqueous stream, wherein the aqueous stream comprises a major portion of water in said portion of the first reaction product; and a distillation unit having an inlet in fluid communication with an outlet of the liquid-liquid phase separation or extraction unit to receive at least a portion of the non-aqueous stream, wherein the distillation unit is configured to provide at least an overhead fraction, a middle fraction, and a bottom fraction.
In addition, the present disclosure provides another system comprising: a first reaction zone comprising a reactor configured heat cellulosic biomass solids, molecular hydrogen, a catalyst capable of activating molecular hydrogen, and a digestion solvent to form a first reaction product; a second reaction zone comprising a reactor in fluid communication with an outlet of the reactor in the first reaction zone to receive the first reaction product, wherein the reactor in the second reaction zone is configured to heat a second reaction content comprising the first reaction product, molecular hydrogen, and a catalyst capable of activating molecular hydrogen to form a second reaction product; and a base catalyzed depolymerization unit in fluid communication with an outlet of the reactor in the second reaction zone to receive the second reaction product, wherein the base catalyzed depolymerization unit is configured to produce a depolymerized reaction product; and a separation zone comprising: a liquid-liquid extraction or phase separation unit having an inlet in fluid communication with an outlet of the base catalyzed depolymerization unit to receive the depolymerized reaction product, wherein the liquid-liquid extraction or phase separation unit is configured to provide an aqueous stream and a non-aqueous stream, wherein the aqueous phase comprises a major portion of water in said portion of the first reaction product; and a distillation unit having an inlet in fluid communication with an outlet of the liquid-liquid phase separation or extraction unit to receive at least a portion of the non-aqueous stream, wherein the distillation unit is configured to provide at least an overhead fraction, a middle fraction, and a bottom fraction.
The features and advantages of embodiments provided by the present disclosure will be readily apparent to one having ordinary skill in the art upon a reading of the description of the embodiments that follows.
The following figures are included to illustrate certain aspects of the present disclosure, and should not be viewed as an exclusive embodiment. The subject matter disclosed is capable of considerable modifications, alterations, combinations, and equivalents in form and function, as will occur to one having ordinary skill in the art and the benefit of this disclosure.
The present disclosure generally provides methods for processing cellulosic biomass into a fuel product, particularly processing of a reaction product obtained from hydrothermal digestion of cellulosic biomass solids. Cellulosic biomass is particularly advantageous because of the versatility of the abundant carbohydrates found therein in various forms. As used herein, the term “cellulosic biomass” refers to a living or formerly living biological material that contains cellulose. The lignocellulosic material found in the cell walls of higher plants is one of the world's largest sources of carbohydrates.
Unless otherwise specified, it is to be understood that use of the terms “biomass” or “cellulosic biomass” may be synonymous. The cellulosic biomass may be in any size, shape, or form. The cellulosic biomass may be natively present in any of these solid sizes, shapes, or forms, or they may be further processed prior to digestion. The cellulosic biomass may be chopped, ground, shredded, pulverized, and the like to produce a desired size prior to hydrothermal digestion. The cellulosic biomass may be washed (e.g., with water, an acid, a base, combinations thereof, and the like) prior to digestion taking place.
Any type of suitable cellulosic biomass source may be used. Suitable cellulosic biomass sources may include, for example, forestry residues, agricultural residues, herbaceous material, municipal solid wastes, waste and recycled paper, pulp and paper mill residues, and any combination thereof. Thus, in some embodiments, a suitable cellulosic biomass may include, for example, corn stover, straw, bagasse, miscanthus, sorghum residue, switch grass, bamboo, water hyacinth, hardwood, hardwood chips, hardwood pulp, softwood, softwood chips, softwood pulp, duckweed and any combination thereof. Leaves, roots, seeds, stalks, husks, and the like may be used as a source of the cellulosic biomass. Common sources of cellulosic biomass may include, for example, agricultural wastes (e.g., corn stalks, straw, seed hulls, sugarcane leavings, nut shells, and the like), wood materials (e.g., wood or bark, sawdust, timber slash, mill scrap, and the like), municipal waste (e.g., waste paper, yard clippings or debris, and the like), and energy crops (e.g., poplars, willows, switch grass, alfalfa, prairie bluestream, corn, soybeans, and the like). The cellulosic biomass may be chosen based upon considerations such as, for example, cellulose and/or hemicellulose content, lignin content, growing time/season, growing location/transportation cost, growing costs, harvesting costs, and the like.
Plants have primary cell walls and secondary cell walls. The primary cell wall contains three major polysaccharides (cellulose, pectin, and hemicellulose) and one group of glycoproteins. The secondary cell wall also contains polysaccharides polymeric lignin that is covalently crosslinked to hemicellulose. The complex mixture of constituents that is co-present with the cellulose can make its processing difficult, as discussed hereinafter. Lignin, in particular, may be an especially difficult constituent to deal with.
When converting cellulosic biomass into fuel blends and other materials, cellulose and other complex carbohydrates therein can be extracted and transformed into simpler organic molecules, which can be further processed thereafter. Digestion is one way in which cellulose and other complex carbohydrates may be converted into a more usable form. Digestion processes can break down cellulose and other complex carbohydrates within cellulosic biomass into simpler, soluble carbohydrates that are suitable for further transformation through downstream further processing reactions. As used herein, the term “soluble carbohydrates” refers to monosaccharides or polysaccharides that become solubilized in a digestion process. Illustrative carbohydrates that may be present in cellulosic biomass solids include, for example, sugars, sugar alcohols, celluloses, lignocelluloses, hemicelluloses, and any combination thereof.
The issues associated with converting cellulosic biomass into fuel blends (biofuels) in an energy- and cost-efficient manner using digestion are not only complex, but they are entirely different than those that are encountered in the digestion processes commonly used in the paper and pulpwood industry. Since the intent of cellulosic biomass digestion in the paper and pulpwood industry is to retain a solid material (e.g., wood pulp), incomplete digestion is usually performed at low temperatures (e.g., less than about 200° C.) for a fairly short period of time (e.g., between two to four hours). In contrast, digestion processes suitable for converting cellulosic biomass into fuel blends and other materials are ideally configured to maximize yields by solubilizing as much of the original cellulosic biomass charge as possible in a high-throughput manner. Paper and pulpwood digestion processes also typically remove lignin from the raw cellulosic biomass prior to pulp formation. Although digestion processes used in connection with forming fuel blends and other materials may likewise remove lignin prior to digestion, these extra process steps may impact the energy efficiency and cost of the biomass conversion process. The presence of lignin during high-conversion cellulosic biomass digestion may be particularly problematic.
Production of soluble carbohydrates for use in fuel blends and other materials via routine modification of paper and pulpwood digestion processes is not believed to be economically feasible for a number of reasons. Simply running the digestion processes of the paper and pulpwood industry for a longer period of time to produce more soluble carbohydrates is undesirable from a throughput standpoint. Use of digestion promoters such as strong alkalis, strong acids, or sulfites to accelerate the digestion rate can increase process costs and complexity due to post-processing separation steps and the possible need to protect downstream components from these agents. Accelerating the digestion rate by increasing the digestion temperature can actually reduce yields of biofuels due to thermal degradation of soluble carbohydrates that can occur at elevated digestion temperatures, particularly over extended periods of time. Once produced by digestion, soluble carbohydrates are very reactive and can rapidly degrade to produce caramelans and other heavy ends degradation products or byproducts, especially under higher temperature conditions, such as above about 150 degrees C. Use of higher digestion temperatures can also be undesirable from an energy efficiency standpoint. Any of these difficulties can defeat the economic viability of fuel blends derived from cellulosic biomass.
A particularly effective manner in which soluble carbohydrates may be formed is through hydrothermal digestion, and in which the soluble carbohydrates may be converted into more stable compounds is through subjecting them to one or more catalytic reductions, which may include hydrogenation and/or hydrogenolysis reactions. Stabilizing soluble carbohydrates through conducting one or more catalytic reduction reactions may allow digestion of cellulosic biomass to take place at higher temperatures than would otherwise be possible without unduly sacrificing yields. Depending on the reaction conditions and catalyst used, reaction products formed because of conducting one or more catalytic reduction reactions on soluble carbohydrates may comprise one or more alcohol functional groups, particularly including triols, glycol, monohydric alcohols, and any combination thereof, some of which may also include a residual carbonyl functionality (e.g., an aldehyde or a ketone). The compounds in the alcoholic component can be described as oxygenates where the compounds comprise one or more oxygen-containing functional groups, such as a hydroxyl group or a carbonyl group. Non-limiting examples of oxygenates include an aldehyde, a ketone, an alcohol, furan, an ether, or any combination thereof. Such reaction products are more thermally stable than soluble carbohydrates and may be readily transformable into fuel blends and other materials through conducting one or more downstream further processing reactions. In addition, the foregoing types of reaction products are good solvents in which a hydrothermal digestion may be performed, thereby promoting solubilization of soluble carbohydrates as their reaction products.
Hydrothermal digestion of a cellulosic biomass can include heating of the cellulosic biomass and a digestion solvent in the presence of molecular hydrogen and a catalyst capable of activating the molecular hydrogen (which can also be referred to herein as a “hydrogen-activating catalyst” or “hydrocatalytic catalyst”). In such approaches, the hydrothermal digestion of cellulosic biomass and the catalytic reduction of soluble carbohydrates produced therefrom may take place in the same vessel, which can be referred to as “in situ catalytic reduction reaction processes.” As such, digestion processes suitable for converting cellulosic biomass into fuel blends and other materials are preferably configured to maximize yields by solubilizing as much of the original cellulosic biomass charge as possible in a high-throughput manner. In situ catalytic reduction reaction processes may also be particularly advantageous from an energy efficiency standpoint, since hydrothermal digestion of cellulosic biomass is an endothermic process, whereas catalytic reduction reactions are exothermic. Thus, the excess heat generated by the in situ catalytic reduction reaction(s) may be utilized to drive the hydrothermal digestion with little opportunity for heat transfer loss to occur, thereby lowering the amount of additional heat energy input needed to conduct the digestion.
Typically, hydrothermal reactions of cellulosic biomass, including hydrothermal digestion and catalytic reduction, generates a reaction product that contains a variety of components, ranging from lighter compounds, such as an alcoholic component, to heavier compounds, including lignin and lignin-derived compounds, such as phenolics, and various compounds in between. The reaction product can also exist in more than one phase, depending on certain conditions, such as temperature and pressure. Because the reaction product is a mixture of compounds, further processing certain compounds to desired products can be challenging. For instance, further processing of certain light compounds in the reaction product to desired fuel products can be challenging, at least from an economics point of view, because other middle-boiling compounds, such as lignin and lignin-derived compounds also present, can limit further processing options of the components in the reaction product.
For example, the lignin present in the reaction product may lead to fouling of processing equipment, potentially leading to costly system down time. The reaction product is a mixture of various compounds and typically in more than one liquid phase. One phase of the reaction product is usually water. While feasible, distillation of a reaction product containing water into various product fractions typically requires higher temperatures and pressures compared to one with reduced water. The extra energy needed for the higher temperatures and pressures can translate into additional costs. While the water in the reaction product can be removed through flashing prior to distillation into product fractions, doing so can result in steam stripping where water vapors carry some phenols into the overhead fraction. Removal of phenols during flashing can result in less efficient product separation in a subsequent distillation process.
The methods and systems provided in the present disclosure address the foregoing issues by providing liquid-liquid extraction or phase separation to isolate the phases so that the phases can be further processed independent of each other. The reaction product can comprise an aqueous phase and one or more non-aqueous phases, which can be mixed with one another in an emulsion. Two streams that result from the liquid-liquid extraction or phase separation process include a non-aqueous stream that contains a major portion of the non-aqueous phase(s) and an aqueous stream that contains a major portion of the aqueous phase. Accordingly, the aqueous stream comprises a major portion of water present in the reaction product, while the non-aqueous stream comprises a minor portion of water present in the reaction product. The term “major” or grammatical equivalents thereof refers to greater than 50 wt %, including 55 wt % or greater, 60 wt % or greater, 70 wt % or greater, 75 wt % or greater, 80 wt % or greater, 85 wt % or greater, 90 wt % or greater, and 95 wt % or greater. The term “minor” or grammatical equivalents thereof means up to 50 wt %, including an amount in a range of 0.1 wt % and up to 50 wt %, up to 45 wt %, up to 40 wt %, up to 35 wt %, up to 30 wt %, up to 25 wt %, up to 20 wt %, up to 15 wt %, up to 10 wt %, or up to 5 wt %.
Liquid-liquid phase separation or liquid-liquid extraction can be used to generate the aqueous stream and non-aqueous stream. In general, liquid-liquid phase separation allows the reaction product to coalesce into the respective phases, which can then be isolated to the respective streams. Liquid-liquid extraction involves use of an extraction solvent to extract a substance from one liquid phase (e.g., an aqueous phase) into a different liquid phase (e.g., a non-aqueous phase) based on the relative solubility of the substance in each of the phases. Accordingly, liquid-liquid extraction can provide for a certain amount of extraction of various compounds from the aqueous phase, including various liquid compounds.
Selection of solvent, operating conditions, and the mechanism of contacting the solvent and reaction product permit control over the level or degree of compound extraction. In particular, the amount of extraction solvent added to the reaction product correlates to the amount of compounds extracted into the solvent phase from the aqueous phase. For instance, in a mixture of reaction product and extraction solvent that contains a relatively small amount of solvent, such as about 1 part solvent phase per 9 parts of aqueous phase, the extraction of compounds into the solvent is small as compared to when a larger amount of solvent is contacted with the aqueous phase, such as a mixture with about 9 parts solvent per one part of aqueous phase. That is, the degree of extraction increases with increasing amounts of extraction solvent used in the liquid-liquid extraction process. As such, it is possible to configure the liquid-liquid extraction process to extract a major portion of compounds from the aqueous phase to a degree where further handling of the aqueous phase for additional product recovery, such as flashing to recover light compounds, may not be needed. The addition of an extraction solvent can also facilitate coalescing of the phases of the reaction product by assisting with the breaking of the emulsion. At least a portion of the extraction solvent can come from a distillation product of the reaction product, such as a distillation product of at least one of the non-aqueous stream and a distillation product of a fuels product generated from further processing of the recovered light compounds.
Once separated, the aqueous stream can be subject to flashing with reduced steam stripping effect because it contains a reduced amount of non-water miscible compounds compared to the reaction product with multiple liquid phases because a major portion of the non-water miscible compounds, such as phenols, are in the non-aqueous stream. Flashing of the aqueous stream recovers various light compounds that can be further processed into a fuel product. As mentioned, light compounds can include those with a normal boiling point of less than about 150 degrees C., including but not limited to monohydric alcohols, aldehydes, ketones, acids, and any combination thereof. The terms “light,” “middle-boiling,” and “heavy,” or grammatical variations thereof, refer to various compounds relative to one another based on their normal boiling points.
The non-aqueous stream with reduced water can be subject to full distillation to obtain various product fractions with a similar degree of product separation at lower temperatures and pressures compared to distillation of the reaction product containing more water or one that has been subject to flashing prior to distillation. The product fractions from the non-aqueous stream can include at least an overhead fraction comprising light compounds, a middle fraction comprising lignin and lignin-derived products, including phenols, and a bottom fraction comprising waste. The non-aqueous stream can also comprise an amount of longer diols and mono-oxygenates (such as those with greater than C4) formed from carbohydrates, which can be recovered in the middle fraction. The distillation can be performed to provide more than one middle fractions. For instance, distillation can be operated to provide a first middle fraction with a normal boiling point of about 150 to 250 degrees C. and a second middle fraction with a higher normal boiling point of 200 to 350 degrees C. Distillation can also be operated to provide a middle fraction with a normal boiling point of about 150 to 350 degrees C.
As known to one of ordinary skill in the art, the overlap in the range of normal boiling point of the middle fractions is at least due to the distribution of compounds during the distillation process. For instance, trace amounts of light compounds may be found in a middle fraction and/or a bottom fraction, and vice versa, trace amounts of heavy compounds may be found in the overhead fraction and/or middle fraction. Likewise, there would be an overlap of compounds in the more than one middle fractions, if present, which leads to an overlap of normal boiling point of the middle fractions. In general, the first middle fraction may be referred to as the phenols fraction because it tends to capture compounds with normal boiling points around that of phenolic compounds. It is understood that the first middle fraction can contain other compounds from the second middle fraction as well as those with normal boiling points falling outside of about 150 to 250 degrees C. as discussed above. Similarly, the second middle fraction may be referred to as the lignin oligomers fraction because it tends to capture heavier compounds with normal boiling points around that of lignin oligomers. It is understood that the second middle fraction can contain other compounds from the first middle fraction as well as those with normal boiling points falling outside of about 200 to 350 degrees C. as discussed above. The middle fraction, whether or not it is in one fraction or more than one fractions, contains a major portion of the phenols in the reaction product fed to the distillation process.
The light compounds recovered from the aqueous stream and the non-aqueous stream can optionally be combined for further processing into a fuels product. The stream of fuels product can be subject to distillation to recover various fuels product fractions. At least a portion of the extraction solvent can come from at least one fuels product fraction. Similarly, a middle fraction recovered from the non-aqueous stream can be recycled in the process. For instance, additionally or alternatively, a middle fraction of the extraction solvent can come from a middle distillate fraction of the non-aqueous stream.
Additionally or alternatively, a middle distillate fraction of the non-aqueous stream can be provided to one or more hydrothermal reaction steps that generate the reaction product. In particular, a middle fraction can be used as a digestion solvent in a hydrothermal reaction. The middle fraction can comprise at least one of cyclohexanols, alkyl cyclohexanols, and phenols, particularly alkyl phenols, where at least a portion of the cyclohexanols is derived from sugars, at least a portion of the alkyl cyclohexanols is derived from lignin, and at least a portion of the alkyl phenols is derived from lignin. The middle fraction may further comprise lignin oligomers.
To improve product separation of the non-aqueous stream, the reaction product can be subject to a viscosity-reducing step, including base-catalyzed depolymerization prior to the liquid-liquid extraction or phase separation step. Base catalysis for the depolymerization of lignin can break down the lignin for the recovery of phenols and other aromatic compounds. Any suitable method and system of carrying out base-catalyzed depolymerization can be employed with the reaction product prior to the liquid-liquid phase separation or extraction step. Optionally, if additional lignin depolymerization is desired, the non-aqueous stream may be subject to an additional depolymerization step. Accordingly, the methods and systems described in the present disclosure can provide for improved yields and lower costs, including reducing or minimizing the need to employ expensive high pressure distillation and separations to process the reaction product.
The term “distillation” has its ordinary meaning, which refers to a method of recovering volatile compounds based on their normal boiling points. Distillation can be done in one stage or multiple stages. A one-stage of single stage distillation may be referred to as “flashing” or a grammatical equivalent, including “flash” or “flasher.” Flashing produces an overhead fraction and a bottom fraction and typically does not produce a middle product fraction. Multi-stage distillation produces various product fractions, including an overhead fraction and a bottom fraction, as well as one or more middle fractions. The manner in which flashing or multi-stage distillation can be carried out is known to one of ordinary skill in the art.
Unless otherwise specified, it is understood that the mention of various components, such as compounds, products, phases fractions, portions, streams, etc., in this disclosure refers to “at least a portion of” such component, whether or not the phrase “at least a portion of” is included therewith. The terms “hydrocarbon compounds,” “hydrocarbons,” or related terms refer to compounds comprising hydrogen and carbon atoms that do not have a phenolic functional group, which is a hydroxyl group (—OH) bonded to an aromatic hydrocarbon group. Illustrative, non-limiting hydrocarbon compounds include alkanes, alkenes, cycloalkanes and their alkyl substituents or derivatives, and cycloalkenes and their alkyl substituents or derivatives, which can be suitable for use in fuel composition, for instance gasoline or diesel. For instance, illustrative hydrocarbon compounds can include but are not limited to any one of cyclohexane, cyclohexene, propyl cyclopentane, propyl cyclopentene, propyl cyclohexane, propyl cyclohexene, anisole, propyl benzene, methyl propyl benzene, and oxygenated hydrocarbons such as cyclohexanone or methyl cyclohexanone.
Methods and systems described in this disclosure can provide for lignin reversion, e.g., reversion of lignin to phenols and conversion of phenolics derived from lignin to hydrocarbons. As mentioned, processing of cellulosic biomass can include hydrothermally digesting cellulosic biomass and carrying out a catalytic reduction reaction of soluble carbohydrates, including in one reactor. This can be achieved via in situ catalytic reduction reaction, which involves heating the cellulosic biomass and a digestion solvent in the presence of molecular hydrogen and a catalyst capable of activating molecular hydrogen. The hydrothermal digestion and catalytic reduction can generate a first reaction product comprising phenolics derived from lignin in the cellulosic biomass and an alcoholic component formed from a catalytic reduction reaction of soluble carbohydrates derived from the cellulosic biomass.
The term “alcoholic component” refers to an oxygenate where the oxygenate can be a monohydric alcohol, a glycol or diol, a triol, or any combination thereof. As used herein, the terms “glycol” or diol will refer to compounds containing two alcohol functional groups, two alcohol functional groups and a carbonyl functionality, or any combination thereof. It is understood that the alcoholic component also includes carbonyls that have carbonyl functionality. As used herein, the term “carbonyl functionality” will refer to an aldehyde functionality or a ketone functionality. In some embodiments, a glycol may comprise a significant fraction of the reaction product. Although a glycol may comprise a significant fraction of the reaction product, it is to be recognized that other alcohols, including triols and monohydric alcohols, for example, may also be present, as well as other oxygenates such as the ketone equivalent of the alcohol. Further, any of these alcohols may further include a carbonyl functionality.
As used herein, the term “triol” will refer to compounds containing three alcohol functional groups, three alcohol functional groups and a carbonyl functionality, and any combination thereof. As used herein, the term “monohydric alcohol” will refer to compounds containing one alcohol functional group, one alcohol functional group and a carbonyl functionality, and any combination thereof. The term “phenolics” or “phenols” has its ordinary meaning, which generally refers to a class of compounds that contain a hydroxyl group (—OH) bonded to an aromatic hydrocarbon group. The term “lignin oligomers” refers to a class of compounds with more than one lignin monomer, two or more aromatic rings, and a molecular weight of up to 300,000 Daltons. It is understood that lignin is a complex, amorphous, three-dimensional polymer having a structure based on phenylpropane. The molecular structure of lignin varies according to the source (e.g., type of plant) and is so complex and varied that its molecular structure has never been completely described. As such, lignin monomers and polymers can have various molecular structures. Commonly known lignin monomers include p-coumaryl alcohol, coniferyl alcohol, and sinapyl alcohol.
The in situ catalytic reduction reaction can be considered a first hydrothermal reaction step, which produces a first reaction product that may also be referred to as a digestion product. At least a portion of the phenolics in the first reaction product can optionally be converted to hydrocarbon compounds by a second hydrothermal reaction step where the first reaction product is heated in the presence of molecular hydrogen and catalyst capable activating molecular hydrogen. The reaction product from the second hydrothermal reaction step can be referred to as a second reaction product. Unless otherwise specified, the term “reaction product” can refer to the first reaction product or the second reaction product. Optionally, at least some of the alcoholic component in the first reaction product, such as glycol or triol, including carbonyls, can also be converted to monohydric alcohol in the second hydrothermal reaction step.
Unconverted phenolics—phenolics that have not been converted to hydrocarbons (meaning compounds that still contain a hydroxyl group bonded to an aromatic hydrocarbon group)—may be recycled or returned to at least one of the first hydrothermal reaction step and the second hydrothermal reaction step. The phenols may serve as part of the digestion solvent in the first hydrothermal reaction step, and/or the phenols may be further converted to hydrocarbons in the second hydrothermal reaction step. It has been found that, if employed, a second hydrothermal reaction step having a low phenolics concentration provides better yields of hydrocarbons from phenols, than one with a high concentration of phenolics, which limits the amount of water and other mono-oxygenated compounds available in the reaction. That is, lignin reversion is better when the concentration of phenolics in the reaction content of the second hydrothermal reaction step is low versus when the phenolics concentration is high. For instance, low phenolics concentration in the second hydrothermal reaction step is a concentration of up to 50% by weight based on the total weight of the content of the second hydrothermal reaction step. Non-limiting illustrative phenolics concentrations of the reaction content in the second hydrothermal reaction step can be in a range of about 0.1% and up to 50% by weight, and any amount in between, including up to 45%, up to 40%, up to 35%, up to 30%, up to 25%, up to 20%, up to 15%, up to 10%, or up to 5% by weight, based on the total content weight of the second hydrothermal reaction step. It is understood that the referenced any phenolics concentration amount in between 0.1 wt % to 50 wt % includes at least 5 wt %, at least 10 wt %, at least 15 wt %, at least 20 wt %, at least 25 wt %, at least 30 wt %, at least 35 wt %, at least 40 wt %, at least 45 wt %, or at least 50 wt %.
Lignin reversion, including conversion of lignin to phenols and/or conversion of phenolics to hydrocarbon compounds, can be improved if the conversion is accomplished in the presence of water. That is the overall phenolics concentration in the second hydrothermal reaction step of 50% or less by weight of the content of the second hydrothermal reaction step can be achieved at least in part with water. For instance, the concentration of water in the second hydrothermal reaction step can be at least 10% by weight based on the total weight of the content of the second hydrothermal reaction step. Non-limiting illustrative water concentration of the reaction content in the second hydrothermal reaction step can be at least 10%, at least 15%, at least 20%, at least 25%, at least 30%, at least 35%, or at least 40% by weight, based on the total content weight of the second hydrothermal reaction step. It is realized that the concentrations mentioned for the first or second hydrothermal reaction content are not limited to single liquid phase. Instead, the concentrations provided correspond to the concentrations of water averaged over all phases present in the respective reactor, where two or sometimes three or more liquid phases may be observed. Additional details regarding systems and methods related to lignin reversion can be found in U.S. application Ser. No. 14/868,426 filed on Sep. 29, 2015, claiming priority to application No. 62/058,440, filed on Oct. 1, 2014, entitled METHODS AND SYSTEMS FOR PROCESSING CELLULOSIC BIOMASS, the disclosure of which is incorporated by reference in its entirety.
At least one of the first reaction product and the second reaction product can be subject to a base catalyzed depolymerization step to generate a depolymerized reaction product where the lignin therein is at least partially depolymerized. Lignin depolymerization reduces the viscosity of the reaction product and thus, the non-aqueous stream, thereby improving the separation of the product fractions during distillation. In general, lignin depolymerization reactions revert high molecular weight lignin oligomers to lower molecular weight compounds, such as lighter lignin oligomers and/or lignin monomers, which results in viscosity reduction. Depolymerization of lignin in the reaction product provides lignin monomers that facilitate phenolics separation from the lignin oligomers and even heavier compounds. The lignin monomers can become a cutting agent to reduce the viscosity of the high molecular weight lignin oligomers.
In general, the base catalyzed depolymerization step may be carried out by contacting the reaction product with a base catalyst for an amount of time. Any suitable base catalyst may be used. Non-limiting suitable base catalysts include NaOH, KOH, Ca(OH)2, Mg(OH)2, solid base catalysts, and any combination thereof. The amount of base catalyst added may be in a range of about 0.5 wt % and 10 wt %, based on the weight of the reaction product. For instance, the amount may be about 0.5 wt %, 1.0 wt %, 1.5 wt %, 2.0 wt %, 2.5 wt %, 3.0 wt %, 3.5 wt %, 4.0 wt %, 4.5 wt %, 5.0 wt %, 5.5 wt %, 6.0 wt %, 6.5 wt %, 7.0 wt %, 7.5 wt %, 8.0 wt %, 8.5 wt %, 9.0 wt %, 9.5 wt %, 10.0 wt %, and any combination thereof. The base catalyst and reaction product is provided a minimum resident time for contact at a certain temperature before the reaction product proceeds to the next step in the process, including a second hydrothermal reaction step or a liquid-liquid phase separation or extraction step. In general, the resident time for contact can be at least about 5 minutes and can be up to about 240 minutes. For instance, non-limiting resident time for contact before the reaction product proceeds to the next step in the process includes at least 15 minutes, at least 30 minutes, at least 45 minutes, at least 60 minutes, at least 75 minutes, at least 90 minutes, at least 105 minutes, at least 120 minutes, at least 135 minutes, at least 150 minutes, at least 165 minutes, at least 180 minutes, at least 195 minutes, at least 210 minutes, at least 225 minutes, at least 240 minutes, and any combination thereof. In general, the resident temperature can be greater than 100 degrees C. and can be up to about 275 degrees C. For instance, non-limiting resident temperature is at least 110 degrees C., at least 120 degrees C., at least 130 degrees C., at least 140 degrees C., at least 150 degrees C., at least 160 degrees C., at least 170 degrees C., at least 180 degrees C., at least 190 degrees C., at least 200 degrees C., at least 210 degrees C., at least 220 degrees C., at least 230 degrees C., at least 240 degrees C., at least 250 degrees C., at least 260 degrees C., at least 270 degrees C., at least 275 degrees C. and any combination thereof. Additional information regarding base catalyzed depolymerization using a solid catalyst (or insoluble catalysts) are described in U.S. Application Publication No. 2012/0302796, the disclosures of which are incorporated by reference in its entirety. Additional details regarding base catalyzed depolymerization using soluble base catalysts can be found in Pandey & Kim, “Lignin Depolymerization and Conversion: A Review of Thermochemical Methods,” Chem. Eng. Technol., 2011, No. 1, 29-41, the disclosure of which is incorporated by reference in its entirety.
At least a portion of the first and/or second reaction product, with the lignin at least partially depolymerized, can be provided to a separation zone that provides for liquid-liquid extraction or phase separation of the reaction product and product recovery of the phases independent of each other. Optionally, prior to being provided to the separation zone, excess gas in the reaction product can be removed. Liquid-liquid extraction or phase separation involves coalescing of the respective phases of the reaction product and isolation of those phases from each other. The liquid-liquid extraction or phase separation can provide an aqueous stream and a non-aqueous stream that can contain one or more non-aqueous phases. The aqueous stream comprises a major portion of the water present in the reaction product. The non-aqueous stream comprises the remaining portion of the reaction product not in the aqueous stream, which contains a minor portion of the water in the reaction product.
Any suitable liquid-liquid extraction or phase separation methods and systems can be used to provide the aqueous stream and non-aqueous stream. These methods can be operated in batch mode, semi-batch mode, continuous mode, or any combination thereof. Non-limiting, illustrative methods and systems include a horizontal settling tank, one or more weirs, centrifuge- or hydroclone-type device, and devices that facilitate coalescing, including a fiber coalesce mat or a packed bed coalescer. Optionally, if liquid-liquid phase separation is employed, a portion of the non-aqueous stream can be recycled to the reaction product provided to the separation zone to improve the efficiency of the liquid-liquid phase separation.
If liquid-liquid extraction is used, at least a portion of the extraction solvent used in the liquid-liquid extraction comes from the reaction product itself. Any suitable liquid-liquid extraction methods and systems capable of partitioning the reaction product into the aqueous stream and the non-aqueous stream can be used. Suitable types of apparatus that can be employed in the liquid-liquid extraction include stage-type extractors or differential extractors. An example of a stage-type extractor is a mixer-settler apparatus that typically includes a mixing tank coupled to a settling vessel to allow the phases to coalesce. In general, a mixer-settler apparatus can be used in batch mode, or a plurality of mixer-settler apparatus can be staged to operate in a continuous or semi-continuous mode. Another stage-type extractor is a centrifugal contactor. Various types of differential extractors (also known as “continuous contact extractors,”) that are also suitable include, but are not limited to, centrifugal contactors and contacting columns such as tray columns, spray columns, packed towers, rotating disc contactors and pulse columns. The liquid-liquid extraction process can also involve apparatus that allows or facilitates coalescing of the phases, including a horizontal settling tank, one or more weirs, centrifuge- or hydroclone-type device, a fiber coalesce mat or a packed bed coalescer.
The content of the aqueous stream (which may also be referred to as the raffinate) exiting the liquid-liquid extraction depends on whether liquid-liquid phase separation or extraction is used. If liquid-liquid extraction is employed, the content of the aqueous stream depends at least on the level or degree of extraction, ranging from low to high. It is understood that the level of extraction can range anywhere between the low and high extremes. If the level of extraction is relatively low or if liquid-liquid phase separation is employed, the aqueous stream can comprise compounds that have some miscibility with water, including light compounds, middle-boiling compounds, and heavy compounds, as well as water-soluble salts, ash, tar, and other waste. Light compounds include those with a normal boiling point of less than 150 degrees C., including monohydric alcohols, aldehydes, ketones, acids, and any combination thereof. Middle-boiling compounds, such as those with a normal boiling point of 150 to 350 degrees C., which can be present in the aqueous stream include glycol and phenols. Heavy compounds include those with a normal boiling point of greater than 350 degrees C. The light compounds and middle-boiling compounds can be recovered from the aqueous stream for further handling, including further processing of light compounds into a fuels product and recycling of middle-boiling compounds as a solvent.
Liquid-liquid extraction typically does not provide sharp cut-offs between the water-miscible compounds in the aqueous stream and non-water miscible compounds in the non-aqueous stream. The amount of compounds extracted from the aqueous phase depends on various factors as will be apparent to one of ordinary skill in the art, including the type of extraction and the type of extractor apparatus, the type of solvent and the solvent ratio.
If the level of extraction is relatively high, the aqueous stream may comprise only trace amounts of these compounds because the compounds have been extracted from the aqueous phase, and they exit the liquid-liquid extraction in the non-aqueous stream. As such, the extracted compounds may be recovered in subsequent handling of the non-aqueous stream, such as distillation. In such a circumstance, it may not be cost effective to subject the aqueous phase to a product recovery step, such as flashing.
Non-limiting illustrative methods include one or more flashing steps. For instance, the aqueous stream can be subject to a first flashing step that recovers the light compounds and other desired compounds in the overhead fraction while the bottom fraction, which contains water-soluble salts, ash, tar, and other waste, can be discarded as waste or processed as a byproduct stream for use in biogas generation, or as fuel for a utility boiler. An option of processing such waste or byproduct includes burning the material after removal of a portion of the water. Additionally or alternatively, instead of becoming waste, the bottom fraction of the first flashing step can be subject to a second flashing step to produce an overhead fraction that comprises middle-boiling compounds like glycols and phenols. The overhead fraction of the second flashing step comprising the middle-boiling compounds can be recovered and provided elsewhere in the process, such as in the first and/or second hydrothermal reaction step. The middle boiling compounds in the aqueous stream can serve as a solvent and/or be further reacted in the first and/or second hydrothermal reaction step. The bottom fraction of the second flashing step containing water-soluble salts, ash, tar, and other waste can be discarded, burned as fuel after partial water removal, or further processed to convert carboxylic acid salts to desirable byproducts. Separation of the reaction product into an aqueous stream and a non-aqueous stream also removes a portion of water-miscible waste or byproducts, including salts, ash, and tar, from the non-aqueous phase(s), which can provide for improved yields and reduced fouling and costs because the water-miscible waste would not be present during distillation of the non-aqueous stream.
The non-aqueous stream comprises a minor portion of water in the reaction product in the liquid-liquid extraction or phase separation unit. While the non-aqueous stream can still contain some water, it is referred to as “non-aqueous” to distinguish it from the aqueous stream that contains substantially more water. In addition to the small amount of water, the non-aqueous stream also comprises a major portion of middle-boiling compounds and a smaller amount of light compounds due to the miscibility of certain light compounds with the non-aqueous phase(s). After liquid-liquid extraction or phase separation, the non-aqueous stream can be distilled into various product fractions, including an overhead fraction comprising light compounds, a middle fraction comprising middle-boiling compounds, including phenols and lignin oligomers, and a bottom fraction comprising the heaviest of compounds in the reaction product, which are often regarded as waste or used as utility fuel. Additionally or alternatively, the non-aqueous stream can be distilled into more than one middle fraction.
Similar to the light compounds recovered from the aqueous fraction, the light compounds recovered from the distillation of the non-aqueous stream can be further processed into a fuels product, a portion of which can serve as part of the extraction solvent. The light compounds recovered from each phase can be optionally combined prior to further processing. Similar to the middle-boiling compounds recovered from the aqueous fraction, the middle-boiling compounds recovered from the non-aqueous stream can be provided to the first and/or second hydrothermal reaction step. For instance, various compounds in the middle fraction(s), including phenols, can serve as solvent in the first hydrothermal reaction step. Additionally or alternatively, various compounds in the middle fraction(s), including phenols and lignin oligomers, can be further hydrotreated in the second hydrothermal reaction step. For instance, phenols in the middle fraction(s) can be converted to hydrocarbons in the second hydrothermal reaction step, and lignin oligomers in the middle fraction(s) can be further reverted to phenols in the second hydrothermal reaction step, particularly in the presence of water. While lignin oligomers can be provided to the first hydrothermal reaction step, it is not preferred. A middle distillate fraction of the non-aqueous stream can also serve as an extraction solvent in the liquid-liquid extraction step.
As described, phenols serving as solvent in the first hydrothermal reaction step can come from products recovered from the aqueous stream and/or non-aqueous stream. Any suitable amount of recycled phenols—phenols coming from the reaction product—can be provided. In some circumstances, the amount of phenols provided to the first hydrothermal reaction step is a ratio of the amount of lignin provided thereto. For instance, phenols can be provided at a ratio of at least 1 part phenols to 2 parts lignin (1:2), including a ratio in a range of 1 part phenols to 2 parts lignin (1:2) to 10 parts phenols to 1 part lignin (10:1), or any ratio in between. Non-limiting illustrative ratios include at least 1 part phenols to 1 part lignin (1:1), 2 parts phenols to 1 part lignin (2:1), 3 parts phenols to 1 part lignin (3:1), 4 parts phenols to 1 part lignin (4:1), 5 parts phenols to 1 part lignin (5:1), 6 parts phenols to 1 part lignin (6:1), 7 parts phenols to 1 part lignin (7:1), 8 parts phenols to 1 part lignin (8:1), 9 parts phenols to 1 part lignin (9:1), 10 parts phenols to 1 part lignin (10:1), and any combination thereof. It is understood that lignin is provided as a component of the biomass feed, or via recycle of a process stream containing lignin.
If a second hydrothermal reaction step is present, glycols, phenols, and/or lignin oligomers can be provided to it. The glycols and phenols can be products recovered from the aqueous stream. The phenols and lignin oligomers can come from a middle fraction distilled from the non-aqueous stream. Any suitable amount of recycled phenols and/or lignin oligomers can be provided consistent with the low phenolics concentration of up to 50% by weight based on the total weight of the content of the second hydrothermal reaction step discussed above. The term “recycled” refers to compounds recovered from the reaction product.
Optionally, if further lignin depolymerization is desired, the non-aqueous stream can be subject to one or more lignin depolymerization reactions prior to full distillation. Any suitable lignin depolymerization reaction can be used. The middle fraction comprising phenols and/or lignin oligomers distilled from the non-aqueous stream can also be provided to the lignin depolymerization reactions to further reduce the viscosity of the feed into the distillation unit, thereby enhancing product separation. It is recognized that this step may necessarily involve use of less water and optionally can be conducted in the absence of catalyst, such that higher temperatures (in excess of 300° C.) may be required for effective conversion of lignin to smaller fragments of lower viscosity via this step. It is also understood that the step of lignin depolymerization of the non-aqueous stream prior to full distillation may be omitted. If lignin is still present in the non-aqueous stream prior to full distillation, it may become precipitated and form a slurry of lignin. In this circumstance, optionally, a filter may be provided to capture at least a portion of this lignin in the non-aqueous stream prior to full distillation. The lignin captured by the filter may be provided to at least one of any of the base catalyzed depolymerization step and the optional lignin depolymerization of the non-aqueous stream.
The following paragraphs provide additional details of the provided methods and systems for processing cellulosic biomass into a fuel product, particularly processing of a reaction product obtained from hydrothermal reaction of cellulosic biomass solids. As mentioned above, hydrothermal reaction of a cellulosic biomass can include in situ catalytic reduction, which involves heating of the cellulosic biomass and a digestion solvent in the presence of molecular hydrogen and a catalyst capable of activating the molecular hydrogen. Any type of suitable catalyst capable of activating hydrogen can be used in any reactor suitable for use with the selected catalyst(s) for the first and/or second hydrothermal reaction step. For example, at least one of the first and second hydrothermal reaction steps can be carried out using fluidly mobile catalyst particles that can be at least partially suspended in a fluid phase via gas flow, liquid flow, mechanical agitation, or any combination thereof in a reactor. Various conditions can be implemented so that the fluidly mobile catalyst particles are not carried out of the reactor by the fluid flowing through the reactor. A reactor operating under these circumstances can be called an ebullating bed reactor in part because the catalyst particles remain in the reactor to form a catalytic bed. It is understood that one of ordinary skill in the art can select the various conditions to achieve an ebullating bed reactor. For instance, a suitable concentration of catalyst and/or catalyst size can be selected to obtain the desired reactor conditions.
On the other hand, the conditions can be modified so that the fluidly mobile catalyst particles flow with the biomass solids through the reactor. A reactor operating under these circumstances can be called a slurry reactor. Adequate catalyst distribution is desirable in a slurry reactor so that soluble carbohydrates formed during hydrothermal digestion may be intercepted and converted into more stable compounds before they have had an opportunity to significantly degrade, even under thermal conditions that otherwise promote their degradation.
If present, the second hydrothermal reaction step can also be carried out using a catalyst that does not comprise fluidly mobile catalyst particles. For example, the second hydrothermal reaction step can be carried out in a fixed bed reactor or a trickle bed reactor, which are known by one of ordinary skill in the art. For instance, during operation of a fixed bed or trickle bed reactor and fluid is flowing through the reactor, the height of the bed does not increase to greater than 10% as compared to when fluid is not flowing through the reactor.
If a reactor with a catalyst that does not comprise fluidly mobile catalyst particles is used in the second hydrothermal reaction step, a possible issue may be clogging of the bed by cellulosic particulates in the first reaction product from the digestion. As cellulosic biomass breaks apart during digestion, smaller and smaller particulates may be produced until only insoluble materials remain. Cellulosic particulates may also be present in native cellulosic biomass before digestion takes place. One way of handling cellulosic particulates can be use of a screen at a fluid outlet of the hydrothermal digestion unit to assist in maintaining the cellulosic fines therein. Periodic backflow or “backflush” of liquid or gas may be necessary to flush solids from this screen, to maintain fluid outflow. At a certain size, the cellulosic particulates may pass through the screen of the hydrothermal digestion unit and enter at least the reactor in the second reaction zone.
Another way to address cellulosic particulates, particularly ones that are sufficiently small to pass through screens, is the methods and systems disclosed in commonly owned U.S. Application Publication No. 2013/0152456 (“the '456 publication”), the disclosure of which is incorporated herein in its entirety. In general, the '456 publication discloses a solids separation unit to which the first reaction product can be routed to have at least a portion of the cellulosic particulates removed before it enters a reactor in the second reaction zone. The solids separation unit can comprise one or more filters, where at least one of the filters can be backflushed to remove cellulosic fines therefrom, while one or more of the other filters remain in fluid communication with an inlet of the reactor in the second reaction zone.
In some embodiments, catalysts capable of activating molecular hydrogen may comprise a metal such as, for example, Cr, Mo, W, Re, Mn, Cu, Cd, Fe, Co, Ni, Pt, Pd, Rh, Ru, Ir, Os, and alloys or any combination thereof, either alone or with promoters such as Au, Ag, Cr, Zn, Mn, Sn, Bi, B, O, and alloys or any combination thereof. In some embodiments, the catalysts and promoters may allow for various hydrothermal reactions, such as hydrogenation and hydrogenolysis reactions, to occur at the same time or in succession of one another. In some embodiments, such catalysts may also comprise a carbonaceous pyropolymer catalyst containing transition metals (e.g., Cr, Mo, W, Re, Mn, Cu, and Cd) or Group VIII metals (e.g., Fe, Co, Ni, Pt, Pd, Rh, Ru, Ir, and Os). In some embodiments, the foregoing catalysts may be combined with an alkaline earth metal oxide or adhered to a catalytically active support. In some or other embodiments, the catalyst capable of activating molecular hydrogen may be deposited on a catalyst support that is not itself catalytically active.
In some embodiments, the catalyst used in the first and/or second hydrothermal reaction step may comprise a poison-tolerant catalyst. As used herein the term “poison-tolerant catalyst” refers to a catalyst that is capable of activating molecular hydrogen without needing to be regenerated or replaced due to low catalytic activity for at least about 12 hours of continuous operation. Use of a poison-tolerant catalyst may be particularly desirable when reacting soluble carbohydrates derived from cellulosic biomass solids that have not had catalyst poisons removed therefrom. Catalysts that are not poison tolerant may also be used to achieve a similar result, but they may need to be regenerated or replaced more frequently than does a poison-tolerant catalyst.
Suitable poison-tolerant catalysts may include, for example, sulfided catalysts. In some or other embodiments, nitrided catalysts may be used as poison-tolerant catalysts. Sulfided catalysts suitable for activating molecular hydrogen are described in commonly owned U.S. patent application Ser. No. 13/495,785, and 61/553,591, each of which is incorporated herein by reference in its entirety.
The catalyst particles may have a particulate size of about 250 microns or less, about 100 microns or less, or about 10 microns or less. The minimum particulate size of the catalyst particles may be about 1 micron. The catalyst particles may comprise catalyst fines. As used herein, the term “catalyst fines” refers to solid catalysts having a nominal particulate size of about 100 microns or less. Catalyst fines may be generated from catalyst production processes, for example, during extrusion of solid catalysts. Catalyst fines may also be produced by grinding larger catalyst solids or during regeneration of catalyst solids. Suitable methods for producing catalyst fines are described in U.S. Pat. Nos. 6,030,915 and 6,127,229, each of which is incorporated herein by reference in its entirety. In some instances, catalyst fines may be intentionally removed from a solid catalyst production run, since they may be difficult to sequester in some catalytic processes. Techniques for removing catalyst fines from larger catalyst solids may include, for example, sieving or like size separation processes. When conducting in situ catalytic reduction reaction processes, such as those described herein, catalyst fines may be particularly well suited, since they can be easily fluidized and distributed in the interstitial pore space of the digesting cellulosic biomass solids.
Catalysts that are not particularly poison-tolerant may also be used in conjunction with the techniques described herein. Such catalysts may include, for example, Ru, Pt, Pd, or compounds thereof disposed on a solid support such as, for example, Ru on titanium dioxide or Ru on carbon. Although such catalysts may not have particular poison tolerance, they may be regenerable, such as through exposure of the catalyst to water at elevated temperatures, which may be in either a subcritical state or a supercritical state.
The catalysts used in conjunction with the processes described herein may be operable to generate molecular hydrogen. For example, in some embodiments, catalysts suitable for aqueous phase reforming (i.e., APR catalysts) may be used. Suitable APR catalysts may include, for example, catalysts comprising Pt, Pd, Ru, Ni, Co, or other Group VIII metals alloyed or modified with Re, Mo, Sn, or other metals. Thus, in some embodiments described herein, an external hydrogen feed may not be needed in order to effectively carry out the stabilization of soluble carbohydrates by a catalytic reduction reaction. However, in other embodiments, an external hydrogen feed may be used, optionally in combination with internally generated hydrogen. In yet other embodiments, the molecular hydrogen needed may be externally supplied to the cellulosic biomass solids. If external hydrogen is provided, the molecular hydrogen may be supplied as an upwardly directed fluid stream. Benefits of supplying an upwardly directed fluid stream are described herein.
The digestion solvent provided to the first reaction zone may comprise an organic solvent. In various embodiments, the digestion solvent may comprise an organic solvent and water. Although any organic solvent that is at least partially miscible with water may be used in the digestion solvent, particularly advantageous organic solvents are those that can be directly converted into fuel blends and other materials without being separated from the alcoholic component. That is, particularly advantageous organic solvents are those that may be co-processed during downstream further processing reactions with the alcoholic component being produced. Suitable organic solvents in this regard may include, for example, ethanol, ethylene glycol, propylene glycol, glycerol, phenols, and any combination thereof. Other suitable organic solvents may include sugar alcohols, for example.
In some embodiments, the digestion solvent may further comprise a small amount of a monohydric alcohol. The presence of at least some monohydric alcohols in the digestion solvent may desirably enhance the digestion and/or the catalytic reduction reactions being conducted therein. For example, inclusion of about 1% to about 5% by weight monohydric alcohols in the digestion solvent may desirably maintain catalyst activity due to a surface cleaning effect. At higher concentrations of monohydric alcohols, bulk solvent effects may begin to predominate. In some embodiments, the digestion solvent may comprise about 10 wt. % or less monohydric alcohols, with the balance of the digestion solvent comprising water and another organic solvent. In some embodiments, the digestion solvent may comprise about 5 wt. % or less monohydric alcohols, or about 4% or less monohydric alcohols, or about 3% or less monohydric alcohols, or about 2% of less monohydric alcohols, or about 1% or less monohydric alcohols. Monohydric alcohols present in the digestion solvent may arise from any source. In some embodiments, the monohydric alcohols may be formed as a co-product with the alcoholic component being formed by the catalytic reduction reaction. In some or other embodiments, the monohydric alcohols may be formed by a subsequent catalytic reduction of the initially produced alcoholic component and thereafter returned to the cellulosic biomass solids. In still other embodiments, the monohydric alcohols may be sourced from an external feed that is in flow communication with the cellulosic biomass solids.
In some embodiments, the digestion solvent may comprise between about 1% water and about 99% water, with the organic solvent comprising the balance of the digestion solvent composition. Although higher percentages of water may be more favorable from an environmental standpoint, higher quantities of organic solvent may more effectively promote hydrothermal digestion due to the organic solvent's greater propensity to solubilize carbohydrates and promote catalytic reduction of the soluble carbohydrates. In some embodiments, the digestion solvent may comprise about 90% or less water by weight. In other embodiments, the digestion solvent may comprise about 80% or less water by weight, or about 70% or less water by weight, or about 60% or less water by weight, or about 50% or less water by weight, or about 40% or less water by weight, or about 30% or less water by weight, or about 20% or less water by weight, or about 10% or less water by weight, or about 5% or less water by weight.
Various illustrative embodiments will be further described with reference to
Referring to
The reaction content in hydrothermal digestion unit 2 is heated to form a first reaction product comprising phenols and an alcoholic component. The phenols are derived from lignin in the cellulosic biomass, and the alcoholic component is formed from soluble carbohydrates derived from cellulosic biomass. Heating of the first reaction content provides for in situ catalytic reduction where digestion of the cellulosic biomass and catalytic reduction of soluble carbohydrates takes place in the same reactor. The reaction content in hydrothermal digestion unit 2 is heated to a temperature that may be in a range of about 190 to 260 degrees C., such as in a range of about 225 to 245 degrees C. For instance, the reaction content in hydrothermal digestion unit 2 can be heated to about 190, 195, 200, 205, 210, 215, 220, 225, 230, 235, 240, 245, 250, 255, or 260 degrees C.
The heating of the first reaction content in hydrothermal digestion unit 2 is preferably performed under a pressurized state. As used herein, the term “pressurized state” refers to a pressure that is greater than atmospheric pressure (1 bar). For example, hydrothermal digestion unit 2 may have a pressure of at least about 30 bar, such as at least about 45 bar, at least about 60 bar, at least about 75 bar, at least about 90 bar, at least about 100 bar, at least about 110 bar, at least about 120 bar, or at least about 130. Hydrothermal digestion unit 2 may have a pressure of at most about 450 bar, such as at most about 330 bar, at most about 200 bar, at most about 175 bar, at most about 150 bar, or at most about 130 bar. As such, hydrothermal digestion unit 2 may have a pressure in a range of about 30 to 450 bar, such as a range of about 45 and 330 bar or in a range of about 75 to 130 bar. Hydrogen is preferably added to achieve the desired total pressure of hydrothermal digestion unit 2. For instance, hydrogen partial pressure of greater than 5 bar, greater than 10, or greater than 25 bar can be provided to hydrothermal digestion unit 2 to achieve the desired total pressure. Additional pressure may occur from vaporization of a portion of the water and volatile compounds of the reaction content. Heating of the digestion solvent in hydrothermal digestion unit 2 in a pressurized state may allow the normal boiling point of various compounds of the digestion solvent to be exceeded, thus allowing a predominately liquid state to be maintained, thereby allowing the rate of hydrothermal digestion to be increased relative to lower temperature digestion processes.
The reaction content in hydrothermal digestion unit 2 may be heated for at least 30 minutes and up to 10 hours, most typically between 120 minutes to 300 minutes. For example, digestion may be carried out for at least 30 minutes, at least 60 minutes, at least 120 minutes, at least 180 minutes, at least 240 minutes, at least 300 minutes, at least 360 minutes, at least 420 minutes, at least 480 minutes, at least 540 minutes, or at least 600 minutes. Digestion may be carried out at most 600 minutes, at most 540 minutes, at most 480 minutes, at most 420 minutes, at most 360 minutes, at most 300 minutes, at most 240 minutes, at most 180 minutes, at most 120 minutes, at most 60 minutes, or at most 30 minutes.
Referring to
Solids introduction mechanism 4 may comprise loading mechanism 6 and pressure transition zone 8, which may continuously or periodically elevate the cellulosic biomass from atmospheric pressure to a pressure near that of the operating pressure of hydrothermal digestion unit 2, particularly when hydrothermal digestion unit 2 is in a pressurized state. This allows for continuous or semi-continuous introduction of cellulosic biomass to take place without fully depressurizing hydrothermal digestion unit 2. That is, the cellulosic biomass solids may be continuously or semi-continuously added to the hydrothermal digestion unit while the hydrothermal digestion unit is in a pressurized state. Without the ability to introduce fresh cellulosic biomass to a pressurized hydrothermal digestion unit, depressurization and cooling of the hydrothermal digestion unit may take place during biomass addition, significantly reducing the energy- and cost-efficiency of the biomass conversion process.
Pressure transition zone 8 may comprise one or more suitable pressurization zones for pressurizing and introducing cellulosic biomass solids to hydrothermal digestion unit 2. Such suitable pressurization zones are described in more detail in commonly owned United States Patent Application Publications 2013/0152457 and 2013/0152458, and incorporated herein by reference in their entirety. Another suitable example of an illustrative pressure transition zone is described in more detail in commonly owned U.S. patent application Ser. No. 14/868,448, which claims priority to Application No. 62/058,177, filed on Oct. 1, 2014, entitled SYSTEMS AND METHODS FOR PROVIDING FEED MATERIAL TO A PRESSURIZED SYSTEM, which is incorporated herein by reference in its entirety. Suitable pressurization zones described therein may include, for example, pressure vessels, pressurized screw feeders, one or more pumps capable of pumping solids and solids slurries, and the like. Multiple pressurization zones may be connected in series to increase the pressure of the cellulosic biomass solids in a stepwise manner.
In various embodiments, soluble carbohydrates produced from cellulosic biomass solids may be converted into a reaction product comprising a glycol via a catalytic reduction reaction mediated by a catalyst that is capable of activating molecular hydrogen. As described in commonly owned U.S. Patent Applications 61/720,704 and 61/720,714, entitled “Methods for Production and Processing of a Glycol Reaction Product Obtained from Hydrothermal Digestion of Cellulosic Biomass Solids” and “Methods for Conversion of a Glycol Reaction Product Obtained from Hydrothermal Digestion of Cellulosic Biomass Solids Into a Dried Monohydric Alcohol Feed,” each filed Oct. 31, 2012 and incorporated herein by reference in its entirety, production of glycols may present several process advantages, particularly with regard to downstream further processing reactions. In other aspects, formation of monohydric alcohols may be more desirable.
Referring to
Catalyst particulates 10 may be conveyed into the cellulosic biomass solids in hydrothermal digestion unit 2 for distribution using fluid flow from any direction. In particular, at least a portion of catalyst particulates 10 may be conveyed by upwardly directed fluid flow, or at least that upwardly directed fluid flow be present. For instance, catalyst particulates 10 may be supplied through fluid inlet line 9 as shown in
Suitable techniques for using fluid flow to distribute catalyst particulates 10 within cellulosic biomass solids are described in commonly owned U.S. Patent Applications 61/665,727 and 61/665,627, each filed on Jun. 28, 2012 (PCT/US2013/048239 and PCT/US2013/048248) and incorporated herein by reference in its entirety. As described therein, cellulosic biomass solids may have at least some innate propensity for retaining catalyst particulates 10 being conveyed by fluid flow, and at least a portion of the cellulosic biomass solids may be sized to better promote such retention. In addition, using fluid flow, particularly upwardly directed fluid flow, to force catalyst particulates 10 to actively circulate through a charge of digesting cellulosic biomass solids may ensure adequate catalyst distribution as well as advantageously reduce thermal gradients that may occur during hydrothermal digestion. As a further advantage, active circulation of catalyst particulates 10 may address the problem created by the production of cellulosic biomass fines, since they may be co-circulated with catalyst particulates for continued digestion to take place in hydrothermal digestion unit 2.
The upwardly directed fluid flow may comprise a gas stream, a liquid stream, or any combination thereof. Also, the upwardly directed fluid flow may comprise one upwardly directed fluid stream, or two upwardly directed fluid streams, or three upwardly directed fluid streams, or four upwardly directed fluid streams, or five upwardly directed fluid streams.
At least some of the one or more upwardly directed fluid streams may contain catalyst particulates at its source. That is, the fluid stream(s) may comprise a stream of catalyst particulates. The one or more upwardly directed fluid streams may convey catalyst particulates therein. In other circumstances, the one or more upwardly directed fluid streams may not contain catalyst particulates at its source, but they may still fluidize catalyst particulates located in or near the cellulosic biomass solids.
The one or more upwardly directed fluid streams may comprise a gas stream. For example, a gas stream being used for upwardly directed fluid flow may comprise a stream of molecular hydrogen. Steam, or an inert gas such as nitrogen, for example, may be used in place of or in addition to a stream of molecular hydrogen. Up to about 40% steam may be present in the fluid stream.
The one or more upwardly directed fluid streams may comprise a liquid stream, particularly when it is not necessarily desired to maintain catalyst particulates in the cellulosic biomass solids and/or a gas stream alone is insufficient to distribute catalyst particulates, for example. Unlike a gas stream, a liquid stream may convey catalyst particulates through the cellulosic biomass solids, add to the liquid head surrounding the cellulosic biomass solids, and eventually spill over. In other circumstances, catalyst fluidization may be incomplete, and a liquid stream may still not convey catalyst particulates completely through the cellulosic biomass solids before the liquid head spills over.
As such, in certain instances, at least a portion of the liquid head may be circulated through the cellulosic biomass solids. Suitable hydrothermal digestion units configured for circulating a liquid phase therethrough, such as hydrothermal digestion unit 2 depicted in
Another way to distribute catalyst particulates 10 is to convey at least a portion comprising phenols in hydrothermal digestion unit 2 to a point above at least a portion of the cellulosic biomass solids and release that portion. Catalyst particulates 10 can have the tendency to accumulate and agglomerate in larger particles in presence of phenols, particularly if the phenols aggregate to form a phenols-rich liquid phase, which contains a major portion of the phenols in unit 2. The formation of the phenols-rich liquid phase provides a catalyst-rich fraction, which contains a major portion of catalyst in unit 2, above cellulosic biomass solids in hydrothermal digestion unit 2, which can act to release catalyst particulates for downward percolation through the cellulosic biomass solids. Techniques for downward percolation of catalyst particulates and phenols are described in commonly owned U.S. Patent Application No. 61/720,757 filed Oct. 31, 2012, entitled “Methods and Systems for Distributing a Slurry Catalyst in Cellulosic Biomass Solids” and U.S. Patent Publication No. 20140174432, filed on Dec. 17, 2013, the disclosures of which are incorporated herein by reference in their entirety.
In the embodiment of system 1 shown in
As shown in
Referring to
In
Referring to
The hydrothermal reaction carried out in phenolics conversion unit 16 can provide for conversion of lignin-derived phenolics into desirable hydrocarbons that can be used in a fuel blends, such as gasoline. Illustrative, non-limiting hydrocarbon compounds include alkanes, alkenes, cycloalkanes and their alkyl substituents or derivatives, and cycloalkenes and their alkyl substituents or derivatives, which can be suitable for use in fuel composition, for instance gasoline or diesel. For instance, illustrative hydrocarbon compounds can include but are not limited to any one of cyclohexane, cyclohexene, propyl cyclopentane, propyl cyclopentene, propyl cyclohexane, propyl cyclohexene, anisole, propyl benzene, oxygenated hydrocarbons cyclohexanone or methyl cyclohexanone, and methyl propyl benzene. The conversion of lignin derived phenolics into desirable hydrocarbons may not be complete, which can leave unconverted phenolics still remaining in the second reaction product. Optionally, the hydrothermal reaction carried out in phenolics conversion unit 16 can also provide for hydrodeoxygenation where triols and glycol of the alcoholic component are converted to monohydric alcohol. The hydrodeoxygenation may not be complete, which can leave triols and glycol still remaining in the second reaction product. As such, the second reaction product can comprise unconverted phenolics, hydrocarbons converted from phenolics, and at least a portion of the alcoholic component.
In phenolics conversion unit 16, phenols can also be converted to a cyclic alcohol, including at least one of alkyl cyclohexanols and alkyl cyclopentanols. Operating conditions of phenolics conversion unit 16 can be selected to generate relatively more of certain phenols-derived cyclic alcohols, thereby leaving less phenols in the second reaction content in unit 16. At least one of cyclohexanol and cyclopentanol can also be formed from carbohydrates in hydrothermal digestion unit 2 and phenolics conversion unit 16, if present, via hydrodeoxygenation reactions in the presence of a catalyst capable of activating molecular hydrogen.
As mentioned, it has been found that a second hydrothermal reaction step, which takes in reaction zone 17, such as in phenolics conversion unit 16 of
Also mentioned was that conversion of lignin to phenols and/or conversion of phenolics to hydrocarbon compounds can be improved if the conversion is accomplished in the presence of water. Referring to
Similarly in
Base catalyzed depolymerization step 50 may be carried out by contacting the reaction product with a base catalyst for an amount of time. Any suitable base catalyst may be used. Non-limiting suitable base catalysts include NaOH, KOH, Ca(OH)2, Mg(OH)2, solid base catalysts, and any combination thereof. The amount of base catalyst added may be in a range of about 0.5 wt % and 10 wt %, based on the weight of the reaction product. For instance, the amount may be about 0.5 wt %, 1.0 wt %, 1.5 wt %, 2.0 wt %, 2.5 wt %, 3.0 wt %, 3.5 wt %, 4.0 wt %, 4.5 wt %, 5.0 wt %, 5.5 wt %, 6.0 wt %, 6.5 wt %, 7.0 wt %, 7.5 wt %, 8.0 wt %, 8.5 wt %, 9.0 wt %, 9.5 wt %, 10.0 wt %, and any combination thereof. The base catalyst and reaction product is provided a minimum resident time for contact at a certain temperature before the reaction product proceeds to the next step in the process, including a second hydrothermal reaction step or a liquid-liquid phase separation or extraction step. In general, the resident time for contact can be at least about 5 minutes and can be up to about 240 minutes. For instance, non-limiting resident time for contact before the reaction product proceeds to the next step in the process includes at least 15 minutes, at least 30 minutes, at least 45 minutes, at least 60 minutes, at least 75 minutes, at least 90 minutes, at least 105 minutes, at least 120 minutes, at least 135 minutes, at least 150 minutes, at least 165 minutes, at least 180 minutes, at least 195 minutes, at least 210 minutes, at least 225 minutes, at least 240 minutes, and any combination thereof. In general, the resident temperature can be greater than 100 degrees C. and can be up to about 275 degrees C. For instance, non-limiting resident temperature is at least 110 degrees C., at least 120 degrees C., at least 130 degrees C., at least 140 degrees C., at least 150 degrees C., at least 160 degrees C., at least 170 degrees C., at least 180 degrees C., at least 190 degrees C., at least 200 degrees C., at least 210 degrees C., at least 220 degrees C., at least 230 degrees C., at least 240 degrees C., at least 250 degrees C., at least 260 degrees C., at least 270 degrees C., at least 275 degrees C. and any combination thereof.
As mentioned, gas separator unit 18 is optional so the first reaction product or the second reaction product can be provided to separation zone 13 from hydrothermal digestion unit 2 or phenolics conversion unit 16, respectively, without going through gas separator unit 18. Referring to
Liquid-liquid extraction or phase separation unit 20 can employ phase separation or extraction to isolate the aqueous stream and the non-aqueous stream. The reaction product generally has an aqueous phase and at least one non-aqueous phase. Under certain conditions, the aqueous phase and the non-aqueous phase(s) coalesce into two layers. Under other conditions, the aqueous phase and the non-aqueous phase(s) can coalesce into three layers. In particular, there can be an aromatics layer on top of an aqueous layer, which is on top of another non-aqueous layer. One illustrative condition includes a temperature of the reaction product above about 150 degrees C., the non-aqueous phase(s) may be on top of the aqueous layer. When the temperature of the reaction product is below about 150 degrees, at least one non-aqueous layer may become denser than the aqueous phase and sinks below. If mono-oxygenated aromatics or other non-water miscible compounds are present, the aromatics may tend to coalesce above the aqueous layer to form another non-aqueous layer, which can result in the mentioned three layers.
The reaction product entering liquid-liquid extraction or phase separation unit 20 is an emulsion where there is at least some mixing of the phases with one another. If liquid-liquid phase separation is employed, the reaction product is allowed to coalesce into the respective phases, which can then be separated from one another. One illustrative way to allow the phases and/or layers to coalesce is to reduce the temperature of the reaction product. The temperature reduction can be at least 20 degrees C. For instance, a temperature of the reaction product in liquid-liquid extraction or phase separation unit 20 can be in a range of 20 to 150 degrees C., or any range therein, lower than a temperature of the reaction product exiting hydrothermal digestion unit 2 in
Additionally or alternatively, another way to allow the phases and/or layers to coalesce is to provide resident time in liquid-liquid extraction or phase separation unit 20 so gravity can act upon the difference in density between the phases and/or layers. The resident time in unit 20 can be at least 5 minutes. For instance, the reaction product can spend in a range of 5 to 30 minutes in liquid-liquid extraction or phase separation unit 20 or any range therein. Non-limiting illustrative resident times can be 5 minutes, 10 minutes, 15 minutes, 20 minutes, 25 minutes, 30 minutes or any time in between.
Additionally or alternatively, another way to allow the phases and/or layers to coalesce is to provide resident time in liquid-liquid extraction or phase separation unit 20 is to augment gravitational force with a centripetal force, such as through use of a centrifuge or hydroclone device.
In liquid-liquid extraction or phase separation, the settling into the different phases is optimal when the amount of each phase present in the emulsion is roughly equal to one another, for example, 1:1. As mentioned, the reaction product generated by either hydrothermal digester 2 in
One way to enhance the liquid-liquid phase separation is to provide a portion of the non-aqueous stream coming out of unit 20 to the reaction product entering liquid-liquid extraction or phase separation unit 20 via line 26. Supplementing the reaction product with the non-aqueous stream increases the non-aqueous phase(s) concentration in liquid-liquid extraction or phase separation unit 20, which can enhance coalescing of the phases. This is still considered to be liquid-liquid phase separation where an extraction solvent is not added as compared to liquid-liquid extraction where an extraction solvent is added, whereby extraction solvent is a solvent mixture of different composition from the liquid phase being separated. The non-aqueous stream in line 31 is therefore not considered an extraction solvent because it has a similar composition as the non-aqueous phase(s) in the reaction product in line 26, and its composition has not been altered to become a solvent.
Referring to
If liquid-liquid extraction is employed, unit 20 can allow for extraction of various compounds from the aqueous phase of the reaction product by an extraction solvent. This may be achieved by using an extraction solvent in which the compounds targeted for extraction have a higher solubility than in the aqueous phase. At least a portion of the extraction solvent comes from the reaction product, particularly a distillate fraction of the non-aqueous stream, particularly a distillate fraction that comprises phenols, including methoxypropylphenol. U.S. Provisional Application Nos. 62/097,728 and 62/097,919 provide disclosures regarding an extraction solvent comprising a distillate fraction of the non-aqueous stream, the disclosures of which are incorporated by reference herein in their entirety. An extraction solvent can also comprise a product from further processing of light compounds recovered from the reaction product, including the aqueous stream and/or non-aqueous stream. U.S. Provisional Application No. 62/097,683 provides disclosures regarding an extraction solvent comprising such product from further processing of recovered light compounds, the disclosure of which is incorporated by reference in its entirety.
As shown in
The extraction solvent can be provided at a ratio in a range of 1 part solvent in line 45 to 9 parts reaction product in line 26 to 9 parts solvent in line 45 to 1 part reaction product in line 26. Non-limiting illustrative ratios include 1 part solvent to 9 parts reaction product (1:9), 1 part solvent to 8 parts reaction product (1:8), 1 part solvent to 7 parts reaction product (1:7), 1 part solvent to 6 parts reaction product (1:6), 1 part solvent to 5 parts reaction product (1:5), 1 part solvent to 4 parts reaction product (1:4), 1 part solvent to 3 parts reaction product (1:3), 1 part solvent to 2 parts reaction product (1:2), 1 part solvent to 1 part reaction product (1:1), 2 parts solvent to 1 part reaction product (2:1), 3 parts solvent to 1 part reaction product (3:1), 4 parts solvent to 1 part reaction product (4:1), 5 parts solvent to 1 part reaction product (5:1), 6 parts solvent to 1 part reaction product (6:1), 7 parts solvent to 1 part reaction product (7:1), 8 parts solvent to 1 part reaction product (8:1), 9 parts solvent to 1 part reaction product (9:1), 10 parts solvent to 1 part reaction product (10:1), and any combination thereof.
The reaction product generated by either hydrothermal digester 2 in
Referring to
Suitable types of apparatus that can be employed in the liquid-liquid extraction include stage-type extractors or differential extractors. An example of a stage-type extractor is a mixer-settler apparatus that typically includes a mixing tank coupled to a settling vessel to allow the phases to coalesce. In general, a mixer-settler apparatus can be used in batch mode, or a plurality of mixer-settler apparatus can be staged to operate in a continuous or semi-continuous mode. Another stage-type extractor is a centrifugal contactor. Various types of differential extractors (also known as “continuous contact extractors,”) that are also suitable include, but are not limited to, centrifugal contactors and contacting columns such as tray columns, spray columns, packed towers, rotating disc contactors and pulse columns.
In general, a mixer-settler apparatus useful in liquid-liquid extraction unit 20 includes a mixer vessel with an agitator to provide mixing of the solvent provided by line 45 and reaction product provided by line 26. The mixed contents can be provided to a settling tank where the phases can coalesce and separate so an aqueous stream can be withdrawn via line 28 and a non-aqueous stream can be withdrawn via line 24.
In general, centrifugal contactors are high-speed, rotary machines characterized by relatively low resident time. The number of stages in a centrifugal device is usually one, however, centrifugal contactors with multiple stages can also be used. Centrifugal contactors utilize mechanical devices to agitate the mixture to increase the interfacial area and decrease the mass transfer resistance. Various types of differential extractors (also known as “continuous contact extractors,”) that are also suitable for use as unit 20 include, but are not limited to, centrifugal contactors and contacting columns such as tray columns, spray columns, packed towers, rotating disc contactors and pulse columns.
Contacting columns are suitable for various liquid-liquid extraction operations. Packing, trays, spray or other droplet-formation mechanisms or other apparatus are used to increase the surface area in which the two liquid phases (i.e., a solvent phase and a hydrocarbon phase) contact, which also increases the effective length of the flow path. Changes in flows and physical properties along the length of an extractor can also be considered in selecting the type of extractor and/or the specific configuration, materials or construction, and packing material type and characteristics (i.e., average particle size, shape, density, surface area, and the like). For instance, the extraction solvent in line 45 may be provided in unit 20 in a counter-current flow direction relative to the flow of reaction product in line 26.
It is understood that liquid-liquid extraction or phase separation unit 20 can comprise more than device to provide the necessary and/or desired separation. Liquid-liquid extraction or phase separation unit 20 can be operated in batch mode, semi-batch mode, continuous mode, or any combination thereof.
As mentioned, the aqueous stream comprises a major portion of the water present in the reaction product provided to liquid-liquid extraction or phase separation unit 20. For instance, the aqueous stream comprises greater than 50 wt %, including 55 wt % or greater, 60 wt % or greater, 70 wt % or greater, particularly 75 wt % or greater, 80 wt % or greater, 85 wt % or greater, 90 wt % or greater, and 95 wt % or greater of the water in the reaction product in unit 20. Correspondingly, the non-aqueous stream comprises a minor portion of the water in the reaction product provided to liquid-liquid extraction or phase separation unit 20. For instance, the non-aqueous stream comprises up to 50 wt %, including an amount in a range of 0.1 wt % and up to 50 wt %, up to 45 wt %, up to 40 wt %, up to 35 wt %, up to 30 wt %, up to 25 wt %, up to 20 wt %, up to 15 wt %, up to 10 wt %, or up to 5 wt % of water in the reaction product in unit 20. The non-aqueous stream comprises the remaining portion of the reaction product not in the aqueous stream. For instance, if the reaction product coalesces into three layers, and the aqueous phase is the middle layer, separation of the aqueous phase leaves the remaining two layers as the non-aqueous stream. Additionally or alternatively, the layers can be individually recovered and the non-aqueous layers can be combined as the non-aqueous stream.
In addition to water, the aqueous stream further comprises compounds that are miscible with water. These include light compounds, middle-boiling compounds, heavy compounds, water-soluble salts, and ash. The light compounds include those that have a normal boiling point of less than 150 degrees C. Non-limiting illustrative examples of light compounds include monohydric alcohols, aldehydes, ketones, acids, and any combination thereof. The middle-boiling compounds present in the aqueous stream include those that have a normal boiling point in a range of 150 to 350 degrees C. or greater, which can include glycols and phenols. The heavy compounds include those that have a normal boiling point of greater than 350 degrees C.
If relative amount of extraction solvent employed is low, such as when the extraction solvent is provided at less than 50% by weight relative to the reaction product in line 26, the extent of the extraction may be minimal so the aqueous stream can also comprise a major portion of compounds at least partially miscible with water in the reaction product line 26 and provided to unit 20, including light compounds, middle-boiling compounds, heavy compounds, in addition to water-soluble salts, and ash. The light compounds include those that have a normal boiling point of less than 150 degrees C. Non-limiting illustrative examples of light compounds include monohydric alcohols, aldehydes, ketones, acids, and any combination thereof. The middle-boiling compounds present in the aqueous stream include those that have a normal boiling point in a range of 150 to 350 degrees C. or greater, which can include glycols and phenols. The heavy compounds include those that have a normal boiling point of greater than 350 degrees C.
If the relative amount of extraction solvent provided is high, such as when the extraction solvent is provided at greater than 50% by weight relative to the reaction product in line 26, the aqueous stream may be largely depleted of light compounds targeted for extraction, including at least one of mono-oxygenates (such as C1-C4), certain diols, and free acids (such as acetic acid or higher). That is, in these circumstances, the aqueous stream may contain a minor portion of light compounds targeted for extraction in the reaction product in line 26 and provided to unit 20, where these light compounds include at least one of mono-oxygenates (such as C1-C4), certain diols, and free acids (such as acetic acid or higher). In these circumstances, the aqueous stream may still comprise glycols, including ethylene glycol and propylene glycol, as well as some amount of the extraction solvent. The aqueous stream also contains water soluble salts, including acid salts and ash.
Referring to
Referring to
Aqueous separation zone 25 can comprise any suitable method known to one of ordinary skill in the art used to separate these light compounds. For instance, zone 25 can comprise one or more flashers. In one circumstance, which is not shown, zone 25 can comprise one flasher to flash the aqueous stream to recover light compounds in the overhead fraction while the bottom fraction containing water-soluble salts and ash can be discarded as waste. The bottom fraction from a single flash, however, can also contain other valuable heavier compounds, such as phenols and glycols.
Referring
If the relative amount of extraction solvent supplied to unit 20 is high, such as greater than 1 part extraction solvent to 2 parts reaction product in line 26, recovery of light compounds in the aqueous stream in line 28 may not be necessary or desirable. As such, the aqueous stream may not be processed in aqueous separation zone 25 as described, thereby rendering zone 25 optional. Additionally or alternatively, the handling of the aqueous stream in zone 25 may be configured to provide the heavier compounds like phenols and glycols instead of the light compounds, thereby rendering line 32 optional.
Suitable lignin depolymerization reactions are known in the art. Non-limiting illustrative lignin depolymerization reactions include thermal reactions, which can be performed with or without catalysts. Generally, thermal lignin depolymerization reactions performed without catalysts typically take place in a temperature of greater than 300 degrees C. Catalysts and hydrogen can be added to reduce the reaction to below 300 degrees C. Any suitable catalyst can be employed, including acid or basic catalysts, in solid or liquid form. For example, methods relating to lignin depolymerization catalysts using a solid catalyst are described in U.S. Application Publication No. 2012/0302796, the disclosures of which are incorporated by reference in its entirety. Other disclosures relating to using catalysts in lignin depolymerization include U.S. Pat. Nos. 6,100,385 and 7,964,761, the disclosures of which are incorporated by reference in their entirety. Other methods to depolymerize lignin in the non-aqueous stream include pyrolysis (thermolysis), gasification, hydrogenolysis, chemical oxidation, and hydrolysis under supercritical conditions. Additional details regarding these methods can be found in Pandey & Kim, “Lignin Depolymerization and Conversion: A Review of Thermochemical Methods,” Chem. Eng. Technol., 2011, No. 1, 29-41, the disclosure of which is incorporated by reference in its entirety.
Referring to
An overhead fraction separated from the non-aqueous stream, which is depicted as line 38, includes a major portion of light compounds in the non-aqueous stream in distillation unit 27. For instance, more than 50 wt %, particularly at least 75 wt %, at least 80 wt %, at least 85 wt %, at least 90 wt %, or at least 95 wt % of compounds with a normal boiling point of less than 150 degrees C. present in the non-aqueous stream in distillation unit 27 is in overhead fraction in line 38.
The middle fraction can comprise compounds heavier than the light compounds, particularly those with a normal boiling point of 150 degrees C. or greater. Distillation unit 27 can be operated to provide more than one middle fraction. For instance, distillation can be operated to provide a first middle fraction, depicted as line 39, with a normal boiling point of about 150 to 250 degrees C., which typically captures phenolic compounds, and a second middle fraction, depicted as line 40, with a higher normal boiling point of 200 to 350 degrees C., which typically captures lignin oligomers. Distillation can also be operated to provide a middle fraction with a normal boiling point of about 150 to 350 degrees C. As mentioned above, there is an overlap in the normal boiling point of the middle fractions, which is at least due to the distribution of compounds during the distillation process. Accordingly, the first middle fraction in line 39 can include compounds with a normal boiling point in a range of about 150 to 300 degrees C. The second middle fraction, which is depicted as line 40, can include compounds with a normal boiling point of 200 to 350 degrees C., which typically captures lignin oligomers. The bottom fraction depicted as line 41 has compounds with a normal boiling point of greater than 350 degrees C., which typically capture the heaviest of compounds regarded as waste or byproducts, such as caramel and/or tar. While the first middle fraction may be referred to as the phenols fraction and the second middle fraction may be referred to as the lignin oligomers fraction, it is understood that the phenols fraction may contain lignin oligomers, and the lignin oligomers may contain phenols. It is understood that a middle fraction distilled from the non-aqueous stream can be the phenols fraction, the lignin oligomers fraction, or a combination thereof. As described, separation zone 13 provides one or more middle fraction that contains a major portion of phenolics in the reaction product provided to separation zone 13.
Referring to
Referring to
Referring to
Additionally or alternatively, in
Referring to
As shown in
Some or all of material in at least one of line 39 and line 40 may be provided to lignin depolymerization unit 29. For instance, at least 10 wt % of the material in a middle fraction distilled from the non-aqueous stream is provided to lignin depolymerization unit 29, particularly, at least 20 wt %, at least 30 wt %, at least 40 wt %, at least 50 wt %, at least 60 wt %, at least 70 wt %, at least 80 wt %, or at least 90 wt %. The amount may be selected by one of ordinary skill in the art by balancing different factors, including the use of phenols as solvent in liquid-liquid extraction unit 20, hydrothermal digestion unit 2, and further lignin reversion and conversion to hydrocarbons in phenolics conversion unit 16. Recycling more material to one location leaves less material for recycling to other locations. It is understood that an external solvent may be used in system 1. For instance, an external extraction solvent (i.e., one that is not recycled) may be provided to liquid-liquid extraction unit 20 and/or an external digestion solvent may be provided to hydrothermal digestion unit 2. In particular, external solvent(s) may be needed at start up when system 1 has not produced any product fractions that can be recycled as described herein. External solvent(s) may also be used after start up to supplement as needed or desired.
Referring to
Referring to
Although a number of different types of catalysts may be used for mediating condensation reactions, zeolite catalysts also may be particularly advantageous in this regard. One zeolite catalyst that may be particularly well suited for mediating condensation reactions of alcohols is ZSM-5 (Zeolite Socony Mobil 5), a pentasil aluminosilicate zeolite having a composition of NanAlnSi96-nO192.16H2O (0<n<27), which may transform an alcohol feed into a condensation product. Other suitable zeolite catalysts may include, for example, ZSM-12, ZSM-22, ZSM-23, SAPO-11, and SAPO-41.
In various embodiments, the condensation reaction may take place at a temperature ranging between about 275 degrees C. and about 450 degrees C. The condensation reaction may take place in a condensed phase (e.g., a liquor phase) or in a vapor phase. For condensation reactions taking place in a vapor phase, the temperature may range between about 300 degrees C. and about 400 degrees C., such as 350 degrees C. or above. The condensation reaction may take place at a pressure in a range of about 5 bar to 50 bar, such as 10 bar to 30 bar, including about 15 bar to 20 bar.
The alcoholic component, particularly when it includes methanol and an oxygenate, such as such as at least one of ketones, aldehydes, furans, and ethers, can provide for improved conversion of methanol over to a fuel compound, such as gasoline or diesel, as compared to other conventional methanol conversion processes. An example of such a conventional methanol conversion process is the methanol-to-gasoline process.
The higher molecular weight compound produced by the condensation reaction may comprise >C4 hydrocarbons, such as C4-C30 hydrocarbons, C4-C24 hydrocarbons, C4-C18 hydrocarbons, or C4-C12 hydrocarbons; or >C6 hydrocarbons, such as C6-C30 hydrocarbons, C6-C24 hydrocarbons, C6-C18 hydrocarbons, or C6-C12 hydrocarbons. As used herein, the term “hydrocarbons” refers to compounds containing both carbon and hydrogen without reference to other elements that may be present. Thus, heteroatom-substituted compounds are also described herein by the term “hydrocarbons.” The particular composition of the higher molecular weight compound produced by the condensation reaction may vary depending on the catalyst(s) and temperatures used for both the catalytic reduction reaction and the condensation reaction, as well as other parameters such as pressure.
A single catalyst may mediate the transformation of the alcoholic component into a form suitable for undergoing a condensation reaction as well as mediating the condensation reaction itself. Zeolite catalysts are one type of catalyst suitable for directly converting alcohols to condensation products in such a manner. A particularly suitable zeolite catalyst in this regard may be ZSM-5, although other zeolite catalysts may also be suitable.
On the other hand, a first catalyst may be used to mediate the transformation of the alcoholic component into a form suitable for undergoing a condensation reaction, and a second catalyst may be used to mediate the condensation reaction. Unless otherwise specified, it is to be understood that reference herein to a condensation reaction and condensation catalyst refers to either type of condensation process. Further disclosure of suitable condensation catalysts now follows. Zeolite catalysts may be used as either the first catalyst or the second catalyst. Again, a particularly suitable zeolite catalyst in this regard may be ZSM-5, although other zeolite catalysts may also be suitable.
Various catalytic processes may be used to form higher molecular weight compounds by a condensation reaction. In some embodiments, the catalyst used for mediating a condensation reaction may comprise a basic site, or both an acidic site and a basic site. Catalysts comprising both an acidic site and a basic site will be referred to herein as multi-functional catalysts. In some or other embodiments, a catalyst used for mediating a condensation reaction may comprise one or more metal atoms. Any of the condensation catalysts may also optionally be disposed on a solid support, if desired. Additional details regarding suitable catalysts are described in commonly owned U.S. patent application Ser. No. 14/067,330, filed Oct. 30, 2013, and entitled Methods and Systems for Processing Lignin During Hydrothermal Digestion of Cellulosic Biomass Solids,” the entire disclosure of which is incorporated herein by reference.
For example, the condensation catalyst may also include a zeolite and other microporous supports that contain Group IA compounds, such as Li, Na, K, Cs and Rb. Preferably, the Group IA material may be present in an amount less than that required to neutralize the acidic nature of the support. A metal function may also be provided by the addition of group VIIIB metals, or Cu, Ga, In, Zn or Sn. In some embodiments, the condensation catalyst may be derived from the combination of MgO and Al2O3 to form a hydrotalcite material. Another condensation catalyst may comprise a combination of MgO and ZrO2, or a combination of ZnO and Al2O3. Each of these materials may also contain an additional metal function provided by copper or a Group VIIIB metal, such as Ni, Pd, Pt, or combinations of the foregoing.
The condensation reaction mediated by the condensation catalyst may be carried out in any reactor of suitable design, including continuous-flow, batch, semi-batch or multi-system reactors, without limitation as to design, size, geometry, flow rates, and the like. The reactor system may also use a fluidized catalytic bed system, a swing bed system, fixed bed system, a moving bed system, or a combination of the above. In some embodiments, bi-phasic (e.g., liquid-liquid) and tri-phasic (e.g., liquid-liquid-solid) reactors may be used to carry out the condensation reaction.
To facilitate a better understanding of the present invention, the following examples of preferred embodiments are given. In no way should the following examples be read to limit, or to define, the scope of the invention.
A 450-ml Parr reactor with 35.00 grams of 2,6-dimethylphenol, 11.68 grams of methylisobutylcarbinol (MIBC) and 163.33 grams of deionized water as solvent, 0.1066 grams of potassium hydroxide buffer, and 2.98 grams of Raney Cobalt 2724 catalyst (WR Grace). 14.0 grams of southern pine wood at nominal 10% moisture were added for reaction cycles again conducted under 52 bar of H2, with heating to 190 C for 1 hour, followed by 245° C. for 3 hours.
After 6 cycles of wood addition, the reactor contents was deinventoried by pipet removal from the top, leaving only an approximate 10-grams of liquid plus catalyst as residue on the bottom of the reactor, for recycle and use in further reaction cycles.
A sample of the aqueous layer product was analyzed by gas chromatography using a 60-m×0.32 mm ID DB-5 column of 1 μm thickness, with 50:1 split ratio, 2 ml/min helium flow, and column oven at 40° C. for 8 minutes, followed by ramp to 285° C. at 10° C./min, and a hold time of 53.5 minutes. The injector temperature was set at 250° C., and the detector temperature was set at 300° C. Gas Chromatographic-Mass Spec (GCMS) was effected using the same protocol.
Principal products were ethylene glycol at 1.8 weight percent, and 1,2-proplene glycol at 2.0 wt. %, along with light monooxygenates C1-C3, intermediates C4-C6 monooxygenates (ketones, alcohols) and diols. Numerous phenolic components were formed (methoxypropylphenol, propylphenol) and observed in addition to the 2,6-dimethylphenol solvent. pH of the final reaction aqueous phase was 4.93. The digester intermediate products can be considered the first reaction product formed in a hydrothermal digestion unit as described in the present disclosure.
The reaction mixture from Example 1 was rigorously shaken using mechanical shaker, and sampled into four nominal 20-gram aliquots.
For Example 2A, the mixed 20.02 gram sample was added to a Parr 50-ml reactor along with 14.99 grams of toluene. The reactor was pressured to 20 bar with hydrogen, and heated to 180° C. for 1 hour with stirring, to extract lipophilic components into the upper toluene phase.
For example 2B, 20.03 grams of the digester intermediate mixture from Example 1 were added to a second 50-ml Parr reactor, along with 0.4025 grams of Raney Cobalt catalyst (WR Grace 2724). The reactor was pressured with 52 bar of hydrogen, and heated to 270° C. for 5 hours, before cooling and depressuring for addition of 15.03 grams of toluene extractant. The reactor was then reheated under 20 bar of hydrogen, and heated to 180° C. for 1 hour with stirring, to extract lipophilic components into the upper toluene phase.
For example 2C, 0.7524 grams of KOH were added to 20.01 grams of the mixed intermediate from Example 1, in a third 50-ml Parr reactor. The reactor was pressured with 20 bar of hydrogen, and heated to 270° C. for only 0.5 hours, before cooling and depressuring for addition of 15.03 grams of toluene extractant. The reactor was then reheated under 20 bar of hydrogen, and heated to 180° C. for 1 hour with stirring, to extract lipophilic components into the upper toluene phase.
For example 2D, 0.2541 grams of KOH were added with 0.4044 grams of Raney Cobalt (WR Grace 2724) along with 20.00 grams of digester intermediate from Example 1, to a fourth 50-ml Parr reactor. The reactor was pressured with 52 bar of hydrogen, and heated to 270° C. for 5 hours, before cooling and depressuring for addition of 15.02 grams of toluene extractant. The reactor was then reheated under 20 bar of hydrogen, and heated to 180° C. for 1 hour with stirring, to extract lipophilic components into the upper toluene phase.
After depressurizing and opening for analysis, Reactor 2A was sampled warm (nominal 80-85° C.), and after full cooling to room temperature (less than 30° C.). Presence of ethylene and propylene glycols in the upper toluene phase was less than 0.05 wt. % regardless of whether sampled warm, or with full cooling. Methoxypropylphenol was present in the upper toluene layer at 0.36 wt. % warm, vs. 0.34 wt. % after fully cooling to room temperature. Monooxygenates lighter than 1-propanol were 0.21 wt. % when sampled warm, vs. 0.17 wt. % upon cooling. These results indicated minimal changes in composition from separations at 80° C. (indicative of a commercial process) vs. room temperature used for standard lab sample analyses. pH of the lower layer was measured as 4.72.
All the upper layers from all examples exhibited similar compositions. For Example 2B, the monooxygenates C1-C3 were more than 7-fold increased relative to those observed in the toluene extract layer from Example 1. This result demonstrates use of a high temperature hydrodeoxygenation reaction step with a catalyst capable of activating molecular hydrogen, to convert diols and glycols present (primarily in the aqueous layer), to monooxygenates. pH of the aqueous phase from this reactor was 4.86 at the end of the reaction cycle.
Example 2D where a catalyst capable of activating molecular hydrogen was employed, the monooxygenates concentration in the upper toluene extract phase was increased by nearly threefold relative to Example 2A. pH of the aqueous layer was 5.38, indicative of moderate KOH addition to the Example 1 intermediate.
For Example 2C with base addition but no addition of catalyst capable of activating molecular hydrogen, the nominal 36% increase in light monooxygenates was not significant, and mostly attributable to an increase in methanol concentration which likely occurred via noncatalytic pathways via thermal decomposition of lignin-derived species. pH for the aqueous layer was 11.78, resulting from the relatively large addition of KOH.
All reactors showed separation of droplets of a phenolic-rich third phase upon cooling. Phenolic components were therefore underrepresented in the GC analyses for all Examples 2A-2D.
Upper layer extracts from Examples 2A through 2D were separately transferred to a 25-ml 2-necked 14/20 flask for microscale distillation using a short path vacuum distillation head adapter (ACE glass). Distillations were conducted first at atmospheric pressure under nitrogen until water and light ends were no longer produced, then switching to vacuum distillation at a nominal 100 Torr with ramp of bottoms temperature to 250° C. using a fixed protocol, for removal of a vacuum distillation fraction.
GC analyses were performed on the vacuum distillation cuts, while the amount of heavy residue remaining in the distillation flask was assessed by weighing.
For Example 3A (distillation of upper layer extract 2A with toluene extraction only), the amount of residue remaining was 6.62% of the total mixture charged to distillation. Of this, vacuum cut was produced that was 9.98% of the amount charged, and contained a concentration of components in the phenolics range of retention time greater than 2,6-dimethylphenol starting solvent of 6.5 wt. %.
For Example 3B (distillation of upper layer extract 2B with 270° C. reversion for 5 hours in the presence of a hydrodeoxygenation catalyst capable of reverting molecular), the amount of residue remaining was 7.42% of the total mixture charged to distillation. Of this, vacuum cut was produced that was 11.35% of the amount charged, and contained a concentration of components in the phenolics range of retention time greater than 2,6-dimethylphenol starting solvent of 6.5 wt. %.
For Example 3C with base addition to obtain high pH for 0.5 hours, the amount of residue remaining was only 2.16% of the total mixture charged to distillation. Of this, vacuum cut was produced that was 9.0% of the amount charged, and contained a concentration of components in the phenolics range of retention time greater than 2,6-dimethylphenol starting solvent of 12.8 wt. %.
Comparison with Example 3A, base addition to obtain pH 11.78 prior to extraction and distillation provided three-fold less heavy ends residue, and a more than doubling of the concentration of components in the phenolics range (formed from wood charged), with retention time greater than 2,6-dimethylphenol starting solvent.
For Example 3D with partial base addition and the addition of hydrodeoxygenation catalyst for 5 hours of treatment at 270° C. under hydrogen, the amount of residue remaining was 6.38% of the total mixture charged to distillation. Of this, vacuum cut was produced that was 8.2% of the amount charged, and contained a concentration of components in the phenolics range of retention time greater than 2,6-dimethylphenol starting solvent of 10.5%, representing a 60% increase in formation of these components compared to Example 3A with no reactive treatment. The amount of residue reduction with lower base addition to obtain pH of only 5.32, was lower than that observed in Example 3C where a pH of 11.78 was obtained via three-fold greater base addition. However, a measureable increase in phenolics formation was apparent in the GC analysis despite the small amount of base addition, with use of longer reaction time at 270° C.
These results show that base addition to obtain pH greater than 7, or 9 or preferably greater than 11, is effective in reducing the heavy ends fraction in intermediate reaction product, and in converting into components in the phenolics solvent ranges of the GC analysis trace.
Note: Literature value for solubility of 2,6-dimethyl phenol in water is 10 g/L (1%). Dan Goodwin
Therefore, the present invention is well adapted to attain the ends and advantages mentioned as well as those that are inherent therein. The particular embodiments disclosed above are illustrative only, as the present invention may be modified and practiced in different but equivalent manners apparent to those skilled in the art having the benefit of the teachings herein. Furthermore, no limitations are intended to the details of construction or design herein shown, other than as described in the claims below. It is therefore evident that the particular illustrative embodiments disclosed above may be altered, combined, or modified and all such variations are considered within the scope and spirit of the present invention. The invention illustratively disclosed herein suitably may be practiced in the absence of any element that is not specifically disclosed herein and/or any optional element disclosed herein. While compositions and methods are described in terms of “comprising,” “containing,” or “including” various components or steps, the compositions and methods may also “consist essentially of” or “consist of” the various components and steps. All numbers and ranges disclosed above may vary by some amount. Whenever a numerical range with a lower limit and an upper limit is disclosed, any number and any included range falling within the range is specifically disclosed. In particular, every range of values (of the form, “from about a to about b,” or, equivalently, “from approximately a to b,” or, equivalently, “from approximately a-b”) disclosed herein is to be understood to set forth every number and range encompassed within the broader range of values. Also, the terms in the claims have their plain, ordinary meaning unless otherwise explicitly and clearly defined by the patentee. Moreover, the indefinite articles “a” or “an,” as used in the claims, are defined herein to mean one or more than one of the elements that it introduces. If there is any conflict in the usages of a word or term in this specification and one or more patent or other documents that may be incorporated herein by reference, the definitions that are consistent with this specification should be adopted.
This present application claims the benefit of U.S. Provisional Application No. 62/098,004 filed Dec. 30, 2014, the disclosures of which are incorporated herein by reference.
| Number | Date | Country | |
|---|---|---|---|
| 62098004 | Dec 2014 | US |
