Process for recovering carbon monoxide from catalytic fast pyrolysis product
09845246 · 2017-12-19
Assignee
Inventors
- Eugene Schmelzer (Baltimore, MD, US)
- Charles Sorensen (Haverstraw, NY)
- Michael Tanzio (Cherry Hill, NJ, US)
Cpc classification
B01D2252/205
PERFORMING OPERATIONS; TRANSPORTING
Y02P20/151
GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
B01D2252/2026
PERFORMING OPERATIONS; TRANSPORTING
Y02C20/40
GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
Y02P30/20
GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
B01D2252/2028
PERFORMING OPERATIONS; TRANSPORTING
International classification
Abstract
The present invention provides an improved process for recovering CO from a catalytic fast pyrolysis (CFP) process product effluent. The process comprises the steps of: a) providing a first vapor phase stream resulting from a CFP process comprising, on a water-free and solids-free basis, from 25 to 80% CO and at least 15% CO.sub.2, b) mixing the first vapor phase stream of step a) with a particular solvent to make a mixed phase stream, c) separating the mixed phase stream of step b) into a second vapor phase stream comprising CO and a liquid phase stream, and d) recovering a product stream from the second vapor phase stream of step c) having a higher concentration of CO and a lower concentration of CO.sub.2 than the first vapor phase stream of step a).
Claims
1. An improved process for recovering CO from a catalytic fast pyrolysis process product effluent comprising steps of: a) providing a first vapor phase stream resulting from a catalytic fast pyrolysis process comprising, on a water-free and solids-free basis, from 25 to 80% CO and at least 15% CO.sub.2, b) mixing the first vapor phase stream of step a) with solvent having an absorption capacity for CO.sub.2 that is at least 5 times the absorption capacity of the solvent for CO to make a mixed phase stream, c) separating the mixed phase stream of step b) into a second vapor phase stream comprising CO and a liquid phase stream, and d) recovering a product stream from the second vapor phase stream of step c) having a higher concentration of CO and a lower concentration of CO.sub.2 than the first vapor phase stream of step a).
2. The process of claim 1 wherein the first vapor phase stream of step a) is produced by quenching a product effluent stream from a catalytic fast pyrolysis process, said product effluent stream comprising, on a water-free and solids-free basis, at least 20% CO, with water at conditions of −5 to 100° C. to produce a quench stream, and treating the quench stream to separate it into the first vapor phase stream and a liquid phase stream.
3. The process of claim 2 wherein the quench stream treating step comprises compressing the quench stream at conditions of 100 to 8000 kPa, and cooling the compressed stream at conditions of −30 to 60° C.
4. The process of claim 1 wherein the solvent of step b) comprises a dimethyl ether of polyethylene glycol of the general formula [CH.sub.3—O—(CH.sub.2—CH.sub.2—O).sub.n—CH.sub.3], where n ranges from 3 to 10.
5. The process of claim 1 wherein the solvent of step b) is selected form the group consisting of Selexol®, dialkylammonium dialkylcarbamates, polydimethyl siloxane (PDMS), polypropyleneglycol dimethylether (PPGDME), and combinations thereof.
6. The process of claim 5 wherein the solvent comprises Selexol®.
7. The process of claim 2 wherein the product effluent stream from a catalytic fast pyrolysis process comprises, on a water-free and solids-free basis, from 20 to 60% CO.
8. The process of claim 7 wherein the product effluent stream from a catalytic fast pyrolysis process comprises, on a water-free and solids-free basis, from 30 to 50% CO.
9. The process of claim 1 wherein the first vapor phase stream of step a) comprises from 35 to 70% CO and at least 20% CO.sub.2.
10. The process of claim 9 wherein the first vapor phase stream of step a) comprises from 40 to 65% CO and at least 25% CO.sub.2.
11. The process of claim 1 wherein the first vapor phase stream of step a) comprises from 15 to 60% CO.sub.2.
12. The process of claim 1 wherein the first vapor phase stream of step a) comprises a compound selected from the group consisting of methane, ethane, ethylene, propane, propylene, butanes, butenes, pentanes, pentenes, aromatics, phenols, cresols, naphthalenes, indole, and combinations thereof.
13. The process of claim 1 wherein the product stream of step d) comprises from 50 to 99% CO, from 0.00005 to 1% CO.sub.2, and less than 25% methane, wherein the concentration of CO is higher in the product stream of step d) than it is in the first vapor phase stream of step a), and the concentration of CO.sub.2 is lower in the product stream of step d) than it is in the first vapor phase stream of step a).
14. The process of claim 1 further comprising steps of: e) further separating the liquid phase stream of step c) to form a third vapor phase stream comprising CO.sub.2, and f) recovering a second product stream comprising at least 50% CO.sub.2 from the third vapor phase stream of step e).
15. The process of claim 14 wherein the second product stream of step f) comprises from 50 to 99% CO.sub.2, from 1 to 30% ethylene, and from 0.5 to 15% propylene.
16. The process of claim 14 further comprising the step of: g) recycling at least a portion of the second product stream of step f) to the catalytic fast pyrolysis process from which the first vapor phase stream of step a) results.
Description
BRIEF DESCRIPTION OF THE DRAWINGS
(1)
(2)
(3)
(4)
DETAILED DESCRIPTION OF THE INVENTION
(5) As a result of extensive research in view of the above, we have found that we can economically and effectively recover CO from a CFP process product effluent by separating and recovering at least a portion of the product of the CFP process into various phase fractions, and recovering CO by way of a series of sequential steps.
(6) The present improved process comprises steps of: a) providing a first vapor phase stream resulting from a CFP process comprising, on a water-free and solids-free basis, from 25 to 80% CO and at least 15% CO.sub.2, b) mixing the first vapor phase stream of step a) with solvent having an absorption capacity for CO.sub.2 that is at least 5 times the absorption capacity of the solvent for CO to make a mixed phase stream, c) separating the mixed phase stream of step b) into a second vapor phase stream comprising CO and a liquid phase stream, and d) recovering a product stream from the second vapor phase stream of step c) having a higher concentration of CO and a lower concentration of CO.sub.2 than the first vapor phase stream of step a); optionally followed by steps of: e) further separating the liquid phase stream of step c) to form a third vapor phase stream comprising CO.sub.2, and f) recovering a second product stream comprising at least 50% CO.sub.2 from the third vapor phase stream of step e); optionally followed by step: g) recycling at least a portion of the second product stream of step f) to the CFP process from which the first vapor phase stream comprising CO of step a) results.
(7) As used herein, the terms “aromatics” or “aromatic compound” refer to a hydrocarbon compound or compounds comprising one or more aromatic groups such as, for example, single aromatic ring systems (e.g., benzyl, phenyl, etc.) and fused polycyclic aromatic ring systems (e.g., naphthyl, 1,2,3,4-tetrahydronaphthyl, etc.). Examples of aromatic compounds include, but are not limited to, benzene, toluene, indane, indene, 2-ethyltoluene, 3-ethyltoluene, 4-ethyltoluene, trimethylbenzene (e.g., 1,3,5-trimethylbenzene, 1,2,4-trimethylbenzene, 1,2,3-trimethylbenzene, etc.), ethylbenzene, styrene, cumene, n-propylbenzene, xylenes (e.g., p-xylene, m-xylene, o-xylene), naphthalene, methylnaphthalene (e.g., 1-methylnaphthalene), anthracene, 9,10-dimethylanthracene, pyrene, phenanthrene, dimethyl naphthalene (e.g., 1,5-dimethylnaphthalene, 1,6-dimethylnaphthalene, 2,5-dimethylnaphthalene, etc.), ethyl naphthalene, hydrindene, methylhydrindene, and dimethylhydrindene. Single ring and/or higher ring aromatics may also be produced in some embodiments. Aromatics also include single and multiple ring compounds that contain heteroatom substituents, i.e., phenol, cresol, benzofuran, aniline, indole, etc.
(8) As used herein, the term “biomass” has its conventional meaning in the art and refers to any organic source of energy or chemicals that is renewable. Its major components can be: (1) trees (wood) and all other vegetation; (2) agricultural products and wastes (corn, fruit, garbage ensilage, etc.); (3) algae and other marine plants; (4) metabolic wastes (manure, sewage), and (5) cellulosic urban waste. Examples of biomass materials are described, for example, in Huber, G. W. et al, “Synthesis of Transportation Fuels from Biomass: Chemistry, Catalysts, and Engineering,” Chem. Rev. 106, (2006), pp. 4044-4098.
(9) Biomass is conventionally defined as the living or recently dead biological material that can be converted for use as fuel or for industrial production. The criterion as biomass is that the material should be recently participating in the carbon cycle so that the release of carbon in the combustion process results in no net increase averaged over a reasonably short period of time (for this reason, fossil fuels such as peat, lignite and coal are not considered biomass by this definition as they contain carbon that has not participated in the carbon cycle for a long time so that their combustion results in a net increase in atmospheric carbon dioxide). Most commonly, biomass refers to plant matter grown for use as biofuel, but it also includes plant or animal matter used for production of fibers, chemicals or heat. Biomass may also include biodegradable wastes or byproducts that can be burned as fuel or converted to chemicals, including municipal wastes, green waste (the biodegradable waste comprised of garden or park waste, such as grass or flower cuttings and hedge trimmings), byproducts of farming including animal manures, food processing wastes, sewage sludge, and black liquor from wood pulp or algae. Biomass excludes organic material which has been transformed by geological processes into substances such as coal, oil shale or petroleum. Biomass is widely and typically grown from plants, including miscanthus, spurge, sunflower, switchgrass, hemp, corn (maize), poplar, willow, sugarcane, and oil palm (palm oil) with the roots, stems, leaves, seed husks and fruits all being potentially useful. Processing of the raw material for introduction to the processing unit may vary according to the needs of the unit and the form of the biomass.
(10) As used herein, the terms “olefin” or “olefin compound” (a.k.a. “alkenes”) have their ordinary meaning in the art, and refer to any unsaturated hydrocarbon containing one or more pairs of carbon atoms linked by a double bond. Olefins include both cyclic and acyclic (aliphatic) olefins, in which the double bond is located between carbon atoms forming part of a cyclic (closed ring) or of an open chain grouping, respectively. In addition, olefins may include any suitable number of double bonds (e.g., monoolefins, diolefins, triolefins, etc.). Examples of olefin compounds include, but are not limited to, ethene, propene, allene (propadiene), 1-butene, 2-butene, isobutene (2-methylpropene), butadiene, and isoprene, among others. Examples of cyclic olefins include cyclopentene, cyclohexene, and cycloheptene, among others. Aromatic compounds such as toluene are not considered olefins; however, olefins that include aromatic moieties are considered olefins, for example, benzyl acrylate or styrene.
(11) As used herein, the term ‘oxygenate” includes any organic compound that contains at least one atom of oxygen in its structure such as alcohols (e.g., methanol, ethanol, etc.), acids (e.g., acetic acid, propionic acid, etc.), aldehydes (e.g., formaldehyde, acetaldehyde, etc), esters (e.g., methyl acetate, ethyl acetate, etc.), ethers (e.g., dimethyl ether, diethyl ether, etc.), aromatics with oxygen containing substituents (e.g., phenol, cresol, benzoic acid etc.), cyclic ethers, acids, aldehydes, and esters (e.g. furan, furfural, etc.), and the like.
(12) As used herein, the terms “pyrolysis” and “pyrolyzing” have their conventional meaning in the art and refer to the transformation of a compound, e.g., a solid hydrocarbonaceous material, into one or more other substances, e.g., volatile organic compounds, gases and coke, by heat, preferably without the addition of, or in the absence of, oxygen. Preferably, the volume fraction of oxygen present in a pyrolysis reaction chamber is 0.5% or less. Pyrolysis may take place with or without the use of a catalyst. “Catalytic pyrolysis” refers to pyrolysis performed in the presence of a catalyst, and may involve steps as described in more detail below. Catalytic fast pyrolysis (CFP) that involves the conversion of biomass in a catalytic fluid bed reactor to produce a mixture of aromatics, olefins, and a variety of other materials is a particularly beneficial pyrolysis process. Examples of catalytic pyrolysis processes are outlined, for example, in Huber, G. W. et al, “Synthesis of Transportation Fuels from Biomass: Chemistry, Catalysts, and Engineering,” Chem. Rev. 106, (2006), pp. 4044-4098, incorporated herein by reference.
(13) As used herein, the term “recovery” of a component is the fraction (or percent) of that component that is present in the recovered product stream(s) compared to the amount of that component that is present in the reactor effluent stream. For example if 10 grams of “A” is present in the reactor effluent and 8.5 grams of “A” is present in the recovered product stream, then the recovery of “A” is 8.5/10 or 0.85 (85%). All percentages provided herein are by mass unless otherwise indicated.
(14) The catalyst useful in the CFP process includes those containing internal porosity selected according to pore size (e.g., mesoporous and pore sizes typically associated with zeolites), e.g., average pore sizes of less than about 100 Angstroms (Å), for example, less than about 10 Å, such as less than about 5 Å, or smaller. In some embodiments, catalysts with average pore sizes of from about 5 to about 100 Å may be used. In some embodiments, catalysts with average pore sizes of between about 5.5 and about 6.5 Å, or between about 5.9 and about 6.3 Å may be used. In some embodiments, catalysts with average pore sizes of between about 7 and about 8 Å, or between about 7.2 and about 7.8 Å may be used.
(15) In preferred embodiments of the CFP process, the catalyst may be selected from naturally occurring zeolites, synthetic zeolites and combinations thereof. In certain embodiments, the catalyst may have the structure of ZSM-5, as would be understood by those skilled in the art. Optionally, such a catalyst can comprise acidic sites. Other types of zeolite catalysts include those having the structure of ferrierite, zeolite Y, zeolite Beta, mordenite, MCM-22, ZSM-23, ZSM-57, SUZ-4, EU-1, ZSM-11, SAPO-31, SSZ-23, among others. In other embodiments, non-zeolitic catalysts may be used; for example, WOx/ZrO2, aluminum phosphates, etc. In some embodiments, the catalyst may comprise a metal and/or a metal oxide. Suitable metals and/or oxides include, for example, nickel, palladium, platinum, titanium, vanadium, chromium, manganese, iron, cobalt, zinc, copper, gallium, and/or any of their oxides, among others. In some embodiments promoter elements chosen from among the rare earth elements, i.e., elements 57-71, cerium, zirconium or their oxides or combinations thereof may be included to modify activity or structure of the catalyst. In addition, in some cases, properties of the catalysts (e.g., pore structure, type and/or number of acid sites, etc.) may be chosen to selectively produce a desired product.
(16) Examples of apparatus and process conditions suitable for the CFP process are described in U.S. Pat. No. 8,277,643 and in US Patent Application 2013/0060070A1, each incorporated herein by reference. Conditions for CFP of biomass may include one or a combination of the following features (which are not intended to limit the broader aspects of the invention): a zeolite catalyst such as one having the structure of ZSM-5; a zeolite catalyst comprising a metal selected from the group consisting of titanium, vanadium, chromium, manganese, iron, cobalt, nickel, copper, zinc, gallium, platinum, palladium, silver, phosphorus, sodium, potassium, magnesium, calcium, tungsten, zirconium, cerium, lanthanum, and combinations thereof; a fluidized bed, circulating bed, or riser reactor; an operating temperature in the range of 300 to 1000° C.; and a solid catalyst-to-biomass mass ratio of from 0.1 to 40.
(17) Referring more particularly to
(18) The CFP reactor 100 may be operated at a temperature from 300 to 1000° C., and the product stream from reactor 100 is typically at a temperature of 300 to 620° C., such as 400 to 575° C., for example 500 to 550° C., and a pressure of 100 kPa to 1500 kPa, such as 200 kPa to 1000 kPa, for example 300 kPa to 700 kPa (pressures expressed as absolute pressures). The raw product stream from reactor 100 comprises aromatics, olefins, oxygenates, paraffins, H.sub.2, CH.sub.4, CO, CO.sub.2, water, char, ash, coke, catalyst fines, and a host of other components. The raw product stream can comprise 20 to 60%, such as 25 to 55%, for example 30 to 50% CO; 10 to 50%, such as 15 to 40%, for example 20 to 35% CO.sub.2; 0.1 to 10%, such as 0.2 to 5%, for example 0.3 to 1.0% H.sub.2; 2 to 15%, such as 3 to 10%, for example 4 to 8% CH.sub.4; 2 to 40%, such as 3 to 35%, for example 4 to 30%, BTX; 0.1 to 10%, such as 0.2 to 5%, for example 0.3 to 3% oxygenates; and 1 to 15%, such as 2 to 10%, for example 3 to 6% C.sub.2-C.sub.4 olefins. The raw product stream can comprise a vapor mixture where the sum of CO and CO.sub.2 is 30 to 90%, such as 40 to 85%, for example 50 to 80%. These values are on a water- and solids-free basis.
(19) Referring more particularly to
(20) The quenching with water in the quench system may be conducted at conditions of temperature from −5 to 200° C., such as from 10 to 100° C., for example from 40 to 80° C., and pressure of 150 to 1500 kPa, for example from 300 to 700 kPa. The quench stream treating step comprises compressing the quench stream at conditions of 100 to 8000 kPa, for example 600 to 2000 kPa, and cooling the compressed stream at conditions of −30 to 60° C., for example 5 to 30° C.
(21) Referring more particularly to
(22) Referring more particularly to
(23) The solvent required in the process of the present invention must be selective for CO.sub.2, aromatics, and olefins absorption in mixtures with CO and H.sub.2. This required solvent has an absorption capacity for CO.sub.2 that is at least 5 times, or at least 10 times, the absorption capacity of the solvent for CO. Examples of such solvent include Selexol®, dialkylammonium dialkylcarbamates, polydimethyl siloxane (PDMS), polypropyleneglycol dimethylether (PPGDME), and combinations thereof. Selexol®, sold by The Dow Chemical Company and its affiliates, is a dimethyl ether of polyethylene glycol of the general formula [CH.sub.3—O—(CH.sub.2—CH.sub.2—O).sub.n—CH.sub.3], where n ranges from 3 to 10, or mixture thereof. The published primary use for Selexol® is to remove acid gases and other contaminants from various gas streams by physical absorption, not chemical reaction typical of amine solvents. A benefit of this process is that the energy required to regenerate a physical solvent such as Selexol® is significantly less than the energy needed to regenerate a chemical (amine) solvent. In addition, since the acid gas removal capacity of Selexol® is only dependent on physical absorption, it is possible to achieve much higher amounts of acid gas absorbed in the solvent, as compared to amines. The relative absorption capacities of Selexol® for various components compared to CH.sub.4 are presented in Table 1. Data in Table 1 are from “Using physical solvent in multiple applications”—Jack Mcjannett—DOW—digital refining 2012 (http://www.digitalrefining.com/data/articles/file/1312419751.pdf).
(24) TABLE-US-00001 TABLE 1 Component R = K′Component/K′CH.sub.4 H.sub.2 0.2 N.sub.2 0.3 CO 0.43 CH.sub.4 1 C.sub.2H.sub.6 7.2 CO.sub.2 15.2 C.sub.3H.sub.8 15.4 n-C.sub.4H.sub.10 36 COS 35 NH.sub.3 73 n-C.sub.5H.sub.12 83 H.sub.2S 134 C.sub.6H.sub.14 167 CH.sub.3SH 340 C.sub.7H.sub.16 360 CS.sub.2 360 C.sub.6H.sub.6 3,800 C.sub.2H.sub.5OH 3,900 C.sub.4H.sub.4S 8,200 H.sub.2O 11,000 HCN 19,000
(25) The vapor phase stream 14 of
(26) Stream 17 from separator 170 of
(27) Stream 19 from separator 170 of
(28) Stream 20 from phase separator 140 of
(29) Stream 24 from selective absorber 190 or 390 of
(30) The steps of the improved process of the present invention may be conducted at conditions of temperature, pressure and flow rate depending on the composition of the process stream and the desired recovery of the various products. For example, the pressure of the selective solvent absorber 190 or 390 can range from 100 kPa to 10,000 kPa (1 to 100 bara), such as from 200 kPa to 5,000 kPa (2 to 50 bara), for example from 500 kPa to 2,000 kPa (5 to 20 bara). The temperature in the selective solvent absorber 190 or 390 can range from −10 to 100° C., such as from 0 to 50° C., for example from 3 to 25° C.
(31) The flash drum 191 or 391 of
(32) The solvent stripper 395 of
(33) The novel arrangement of unit operations and process conditions required of the present process facilitates the separation and recovery of a valuable CO stream from a biomass upgrading process. This reduces the volume of vapor that must be separated in the aromatics separation scheme, thus reducing costs and sizes of equipment and improving efficiency. This also reduces the volume of the gases that are recycled to the process thus providing enhanced process flexibility. The inventive process increases the concentration of CO.sub.2 and olefins in the gas stream that is available for recycle, thus increasing olefin conversion and improving aromatics productivity. An unexpected benefit of the present process is the potential for eliminating the xylenes absorber to collect the aromatics that are present in the vapors from the phase separator, thus reducing the number of unit operations in a CFP product purification process.
(34) The following Example demonstrates the present invention and its capability for use. The invention is capable of other and different embodiments, and its several details are capable of modifications in various apparent respects, without departing from the spirit and scope of the invention. Accordingly, the Example is to be regarded as illustrative in nature and not as restrictive. All percentages are by mass unless otherwise indicated.
EXAMPLE
(35) A model was constructed to calculate the separation of a CO-rich stream from a CFP product mixture in a single pass. A model of the vapor composition that exits the primary phase separator was entered into an Aspen® simulation of the CO separation process as depicted in
(36) TABLE-US-00002 TABLE 2 14 23 24 25 26 Separator CO.sub.2-rich CO-rich Spent Bottoms Stream Outlet Solvent Stream Stream Solvent Solvent T, ° C. 5 8 105 8.7 105 13.2 P, bar 9.013 9.013 1.513 9.013 1.513 9.013 Flow, kg/hr 145,074 3.2 × 10.sup.6 39,915 78,022 3,227,140 3,267,050 Fractions H.sub.2 0.006 743 ppb 0.011 Trace 9 ppb N.sub.2 Trace Trace Trace CO 0.516 0.095 0.908 48 ppm 0.001 CO.sub.2 0.354 0.741 295 ppm 0.007 0.016 Methane 0.071 0.079 0.08 258 ppm 0.001 Propane 0.001 0.002 4 ppm 26 ppm 46 ppm Ethylene 0.029 0.058 785 ppm 585 ppm 0.001 Propylene 0.013 0.022 20 ppm 332 ppm 594 ppm 1-Butene 563 ppm 720 ppm 12 ppb 16 ppm 25 ppm n-Butane 725 ppm 879 ppm 55 ppb 22 ppm 32 ppm n-Pentane 111 ppm 83 ppm Trace 4 ppm 5 ppm Pentene 173 ppm 140 ppm Trace 6 ppm 8 ppm n-Hexane 36 ppm 15 ppm Trace 1 ppm 2 ppm 1-Hexene 80 ppm 37 ppm Trace 3 ppm 4 ppm n-Octane 2 ppm 262 ppb Trace 103 ppb 105 ppb 1-Heptene 0.002 525 ppm Trace 91 ppm 96 ppm Benzene 0.004 0.001 Trace 168 ppm 181 ppm Toluene 0.002 268 ppm Trace 77 ppm 79 ppm p-Xylene 53 ppm 4 ppm Trace 2 ppm 2 ppm m-Xylene 88 ppm 7 ppm Trace 4 ppm 4 ppm o-Xylene 15 ppm 997 ppb Trace 679 ppb 683 ppb Ethylbenzene 9 ppm 713 ppb Trace 391 ppb 395 ppb n-Propylbenzene 49 ppb 2 ppb Trace 2 ppb 2 ppb Cumene 3 ppm 167 ppb Trace 137 ppb 137 ppb 1,2,3- 281 ppb 7 ppb Trace 13 ppb 12 ppb Trimethylphenol Styrene 3 ppm 189 ppb Trace 140 ppb 140 ppb Benzofuran 71 ppb 2 ppb Trace 3 ppb 3 ppb Aniline 20 ppb Trace Trace Trace Trace Indole Trace Trace Trace Trace Trace Indene 9 ppb Trace Trace Trace Trace Naphthalene 3 ppb Trace Trace Trace Trace 2- 4 ppb Trace Trace Trace Trace Methylnaphthalene Phenol 1 ppb Trace Trace Trace Trace m-Cresol 6 ppb Trace Trace Trace Trace H.sub.2O 653 ppm 103 ppm Trace 28 ppm 29 ppm Solvent 1.000 39 ppb 7 ppb 0.992 0.979
(37) TABLE-US-00003 TABLE 3 Fraction of component recovered CO-rich Stream CO.sub.2-rich Stream Component Stream 24 Stream 23 Hydrogen 1.0000 0.0000 CO 0.9472 0.0507 CO.sub.2 0.0004 0.5760 Methane 0.6113 0.3073 Propane 0.0021 0.4403 Ethylene 0.0144 0.5438 Propylene 0.0008 0.4467 1-Butene 0.0000 0.3521 n-Butane 0.0000 0.3336 n-Pentane 0.0000 0.2053 Pentene 0.0000 0.2222 n-Hexane 0.0000 0.1140 1-Hexene 0.0000 0.1278 n-Octane 0.0000 0.0291 1-Heptene 0.0000 0.0665 Benzene 0.0000 0.0797 Toluene 0.0000 0.0415 p-Xylene 0.0000 0.0213 m-Xylene 0.0000 0.0207 o-Xylene 0.0000 0.0179 Ethylbenzene 0.0000 0.0217 Cumene 0.0000 0.0156 Styrene 0.0000 0.0174
(38) The results of this example unexpectedly show that a very high fraction of the CO in the product gases can be recovered by way of the present process. Furthermore, it is surprising that a stream with higher concentrations of CO.sub.2, ethylene, and propylene that is a very valuable recycle stream can be produced by the present process. It is an unexpected benefit that the CO.sub.2-rich stream produced by the process of this invention is suitable for recycle and can eliminate the need for recovering aromatics from this stream as the aromatics will return to the CFP reactor. Separation of a CO-rich stream reduces the volume of vapor that must be separated in the aromatics separation scheme, thus reducing costs and sizes of equipment and improving efficiency. This also reduces the volume of the gases that are recycled to the process thus providing enhanced process flexibility. The inventive process increases the concentration of CO.sub.2 and olefins in the gas stream that is available for recycle, thus increasing olefin conversion and improving aromatics productivity.
(39) All patents, patent applications, test procedures, priority documents, articles, publications, manuals, and other documents cited herein are fully incorporated by reference to the extent such disclosure is not inconsistent with this invention and for all jurisdictions in which such incorporation is permitted.
(40) When numerical lower limits and numerical upper limits are listed herein, ranges from any lower limit to any upper limit are contemplated.
(41) While the illustrative embodiments of the invention have been described with particularity, it will be understood that various other modifications will be apparent to and may be readily made by those skilled in the art without departing from the spirit and scope of the invention. Accordingly, it is not intended that the scope of the claims hereof be limited to the examples and descriptions set forth herein but rather that the claims be construed as encompassing all the features of patentable novelty which reside in the present invention, including all features which would be treated as equivalents thereof by those skilled in the art to which the invention pertains.