Methods for the Biomethanation of H2 and CO2
20190256872 ยท 2019-08-22
Inventors
Cpc classification
C12M23/58
CHEMISTRY; METALLURGY
Y02E50/30
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
International classification
C12M1/107
CHEMISTRY; METALLURGY
C12M1/12
CHEMISTRY; METALLURGY
Abstract
The invention relates to means and methods for the biomethanation of H.sub.2 and CO.sub.2. In particular, the invention relates to devices for producing methane by means of methanogenic microorganisms by converting H.sub.2 and CO.sub.2, wherein the devices comprise at least one reactor, an aqueous medium, which is provided in the at least one reactor, wherein the methanogenic microorganisms are contained in the aqueous medium, a feeding apparatus, which is designed to introduce H.sub.2 and CO.sub.2 into the at least one reactor, wherein H.sub.2 and CO.sub.2 form a gaseous mixture therein, and a reaction-increasing device, which is designed to enlarge the contact surface between the aqueous medium having the methanogenic microorganisms and the gaseous mixture. The invention further relates to methods for producing methane in a reactor device by means of methanogenic microorganisms.
Claims
1-29. (canceled)
20. Method for production of methane in a reactor device by means of methanogenic microorganisms, which are located in the reactor device in an aqueous medium, by conversion of H.sub.2 and CO.sub.2 as the reaction gas mixture, characterized in that the contact surface between the aqueous medium with the methanogenic microorganisms and the gaseous mixture is increased by means of a reaction boosting device during the conversion and further characterized in that by means of a return mechanism at least a portion of the gas, which accumulates in the reactor, is returned in the reactor device, wherein a return rate of the gas accumulating in the reactor is greater than a feed rate of the reaction mixture in the reactor.
21. Method according to claim 20, characterized in that the methanogenic microorganisms are a mixture of different microorganisms of the phylum Euryarchaeota.
22. Method according to claim 20, characterized in that the methanogenic microorganisms are supplied in the form of macroscopic colonies (pellets) to the aqueous medium.
23-25. (canceled)
26. Method according to claim 20, characterized in that the reactor device has: at least one reactor; an aqueous medium, which is prepared in the at least one reactor, the methanogenic microorganisms being located in the aqueous medium; a feed mechanism, which is designed to channel H.sub.2 and CO.sub.2 into the at least one reactor, wherein the H.sub.2 and CO.sub.2 form a gaseous mixture inside it; a reaction boosting device, which is designed to increase the contact surface between the aqueous medium with the methanogenic microorganisms and the gaseous mixture; a return mechanism, which is designed to return at least a portion of the gas, which accumulates in the reactor, wherein the return rate of the gas accumulating in the reactor is greater than the feed rate of the substrate gas in the reactor.
27. Method according to claim 26, characterized in that the reactor device further has a drainage mechanism, which is designed to drain a gas from the at least one reactor.
28. Method according to claim 27, characterized in that the gas has methane.
29. Method according to claim 28, characterized in that the quantitative fraction of methane in the gas is at least 50%.
30. Method according to claim 20, characterized in that the return rate of the gas accumulating in the reactor exceeds the feed rate of the substrate gas in the reactor by at least a factor of 100.
31. Method according to claim 20, characterized in that the return mechanism has a pump or a compressor.
32. Method according to claim 20, characterized in that the device further has a circulation mechanism, which is designed to circulate the aqueous medium through the at least one reactor.
33. Method according to claim 32, characterized in that the circulation mechanism has at least one pump.
34. Method according to claim 33, characterized in the pump is a driving jet pump.
35. Method according to claim 20, characterized in that the device is set up as stationary or nonstationary reactor.
36. Method according to claim 35, characterized in that the device is a solid state reactor or a submerse reactor.
37. Method according to claim 20, characterized in that the device is set up as continuous ideal stirred tank (CSTR), discontinuous ideal stirred tank (STR), tube reactor, loop reactor, reactors switched in series, or as cascade of reactors.
38. Method according to claim 20, characterized in that the reaction boosting device has at least one trickling bed, one spray tower, one in-line mixer or one pump.
39. Method according to claim 38, characterized in that the pump is a driving jet pump.
40. Method according to claim 26, characterized in that the feed mechanism further has: a device for enrichment of carbon dioxide from a gas mixture; and optionally a mechanism for electrolytic splitting of water; wherein the feed mechanism preferably is designed so that when the H.sub.2 and CO.sub.2 are channeled into the at least one reactor, the gaseous mixture forms a turbulent flow.
41. Method according to claim 26, characterized in that the feed mechanism is further designed so that, in operation, the volume of introduced H.sub.2 and CO.sub.2 per hour exceeds the volume capacity of the at least one reactor by at least the factor of 2, wherein the pressure in the reactor is optionally greater than or equal to 0.1 bar.
42. Method according to claim 20, characterized in that the methanogenic microorganisms are not immobilized in the aqueous medium.
Description
BRIEF DESCRIPTION OF THE FIGURES
Nonlimiting Examples and Figures
[0083] With the aid of the enclosed representations (figures) and sample embodiments, the invention shall be explained more closely.
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LIST OF REFERENCES FOR FIGS. 1 TO 6
[0094] 100 Device for production of methane with a tube reactor [0095] 102 Inlet line [0096] 104 First valve [0097] 106 Nozzle [0098] 108 Reactor (designed as a tube reactor) [0099] 110 Gas separation device [0100] 112 Second valve [0101] 114 First outlet [0102] 116 Aqueous medium [0103] 118 First return branch [0104] 120 Pump [0105] 122 Second return branch [0106] 124 Mixing element [0107] 126 Feed mechanism [0108] 128 Liquid surface [0109] 200 Device for production of methane with a stirred tank [0110] 202 Reactor (designed as a stirred tank) [0111] 204 Stirrer [0112] 300 Device for production of methane with a submerse reactor [0113] 302 Reactor (designed as a submerse reactor) [0114] 400 Device for production of methane with a spray tower [0115] 402 Reactor (designed as a spray tower) [0116] 404 Dispersion device [0117] 500 Device for production of methane with a trickle-bed reactor [0118] 502 Reactor (designed as a trickle-bed reactor) [0119] 504 Matrix [0120] 600 Device for production of methane with a trickle-bed reactor [0121] 602 Reactor (designed as a driving jet reactor)
LIST OF REFERENCES FOR FIG. 7 TO 10
[0122] (A) Gasified reactor part with up flow [0123] (B) Nongasified reactor part with down flow [0124] (C) Water body by which several reactors can be tempered [0125] (1) Primarily water filled volume fraction of the reactor [0126] (2) Primarily gas filled volume fraction of the reactor [0127] (3) Gas supply [0128] (4) Gas recirculation [0129] (5) Inlet for nutrient and bacteria supply, pH adjustment, taking samples, etc. [0130] (6) Defoamer dosage [0131] (7) Defoaming device, foam trap [0132] (8) Drainage of solid, liquid and dissolved products from (1) [0133] (9) Drainage of gaseous products from (2) [0134] (10) Gas recirculation pump [0135] (11) Shutoff element [0136] (12) Pressure sustaining valve
DETAILED DESCRIPTION OF SPECIFIC SAMPLE EMBODIMENTS OF THE INVENTION
[0137]
[0138] In the sample embodiment represented in
[0139] By means of the first return branch 118 the gaseous phase from the gas separation device 110 can be fed to the nozzle 106 and thus recycled. The gaseous phase taken away by means of the first return branch 118 can involve predominantly components of the substrate gas which have not been converted to methane in the reactor 108. These unreacted residues can be so to speak recycled in this way and are again available to the microbial reaction. The first return branch 118 can be omitted in very long tube reactors 108, since the substrate gas introduced at the inlet of such a tube reactor 108 is converted with high probability by the end of the reactor 108. In other words, it can be assumed that with increasing length of the tube reactor 108 the portion of the unreacted substrate gas at the end of such a reactor becomes increasingly smaller.
[0140] The nozzle 106 arranged between the first valve 104 and the reactor 108 serves to introduce at least the substrate gas into the reactor 108 such that at the same time a recirculation or throughput of the liquid medium 116 with the substrate gas so introduced takes place. By means of the nozzle 106 the kinetic energy of the substrate gas can be increased before it is introduced into the reactor 108. In this way, the substrate gas introduced can be as it were blown into the aqueous medium containing the methanogenic microorganisms, producing a strong recirculation of the aqueous medium 116. In other words, by introducing the substrate gas into the reactor 108 by means of the nozzle 106 one can produce numerous gas bubbles which push the aqueous phase 116 through (hereinafter called the dynamic case). In this way, the reaction surface between the substrate gas and the aqueous medium 116 is drastically increased as compared to the case (hereinafter called the static case) when the substrate gas is introduced into a tube reactor 108 without the above-described recirculation of the aqueous phase 116.
[0141] The driving jet can be formed by the nozzle 106 with the help of the liquid phase which is drained off from the gas separation device 110. The nozzle 106 can be, for example, a jet pump in which, depending on the design of the device, the gaseous medium or the liquid phase drained away from the gas separation device 110 can be used. The liquid phase drained away through the second return branch 122 is the aqueous medium 116 from the reactor 108. The gas separation device 110 can be seen functionally as a settling or separation device. In the reactor 108, due to the turbulent mixing processes, the aqueous medium 116 can be present as a foamy gas/water mixture. In other words, the liquid containing the methanogenic microorganisms is heavily enriched with the gaseous phasemethane and residues of the substrate gas. In this state, the aqueous medium 116 is transferred to the gas separation device 110 and a separation of the gaseous phase from the liquid phase occurs there, while the aqueous medium 116 can still be foamy. This gas separation process can naturally occur by uplifting of the gaseous phase (unreacted residues of the substrate gas and methane) from the mixture 116 of liquid and gas. The liquid essentially cleansed of the gaseous phase together with the methanogenic microorganisms can then, as shown in
[0142] The gas which can be drained away at the second outlet of the gas separation device 110 and which can be fed to the nozzle 106 by means of the optional first return branch 118 contains essentially only methane in the optimal case, and possibly slight residues of the unreacted substrate gas. The recirculation rate of the gaseous phase from the gas separation device 110 can be adapted to the length of the reactor 108 and, as already mentioned, will tend toward zero in sufficiently long reactors 108, in which the recirculated gaseous phase from the gas separation device 110 consists essentially of methane. Since the production method presented here is very efficient, i.e., thanks to the strong mixing of the aqueous medium 116 in the reactor 108 with the substrate gas, conversion rates of more than 90% for example, more than 95% for example, practically 100% for example can be achieved. When the first recirculation branch 118 is present, the recirculation rate of the gaseous phase from the gas separation device 110 can always be larger than the feed rate of the substrate gas into the reactor 108 by means of the inlet line 102, for example by factors on the order of 1 to 100, for example, to 200 for example, to 500 for example, to 1000 or more, for example. With very long tube reactors 108, as mentioned above, almost the entire substrate gas is converted to methane. An appropriately designed return branch 118 can also be provided in this case, despite a vanishingly small fraction of the substrate gas residue in the recirculated gas. Regardless of the conversion rate inside the reactor 108, with the help of a high gas recirculation rate by means of the first return branch 118, which thus corresponds functionally to a recirculation branch, the gas fraction in the gas/water mixture inside the reactor 108 and thus the degree of turbulence can be increased. By means of the gas recirculation, the mixing of the gas/water mixture inside the reactor 108, i.e., the contact time and contact surface between these two phases, can thus be increased.
[0143] The gas mixture located above the liquid surface 128 in the gas separation device 110 during the operation of the device 100 contains the product gas and, depending on the efficiency of the conversion, small to vanishingly slight residues of unreacted substrate gas. This gas mixture can be drained off entirely or partially at the first outlet 114 from the device 100 and optionally recirculated by means of the first return branch 118 to the reactor 108. In other words, a gaseous phase of identical composition is drained off at the first outlet 112 and at the second outlet (belonging to the optional first return branch 118).
[0144] Equilibrium generally obtains for a particular H.sub.2/CO.sub.2 ratio in the reactor 108 or in the gas separation device 110: a CO.sub.2 concentration in the gas corresponds to a CO.sub.2 concentration in the aqueous medium 116. If the entire CO.sub.2 is converted, the pH value in the aqueous medium 116 will rise, which may be undesirable. Therefore, the feeding of the substrate gas at the inlet line 102 can be adjusted so that both in the gas phase drained off at the first outlet 114 and thus also at the second outlet a residue of CO.sub.2 always remains, for example around 1% to around 2%. A total conversion of H.sub.2 on the other hand does not result in shifting of the pH value. In order to stabilize the pH value it can thus be beneficial to supply the substrate gas to the device 100 by means of the inlet line 102 in a ratio of around 4:1 (H.sub.2 to CO.sub.2) or less.
[0145] The introducing of the substrate gas into the reactor 108 by means of the nozzle 106, resulting in the mixing of the aqueous medium 116 with the substrate gas, ensures that a much larger number of the methanogenic organisms per unit of time come into contact with the substrate gas in the dynamic case and therefore a larger number of the methanogenic organisms can produce methane per unit of time than in the static case. Approximately speaking, the reaction or contact surface between an aqueous medium 116 present in the reactor and the substrate gas corresponds in the static case to the surface of the medium. In the dynamic case, however, or according to the teaching of the invention as explained in this specification, this surface is much larger, since there must be added to the already roughened and thus larger surface of the aqueous medium 116 in the reactor 108 (indicated by the wavy line inside the reactor 108) the sum of the surfaces of the gas bubbles permeating the aqueous medium 116, wherein the gas bubbles at the beginning of the tube reactor 108 tend to have only substrate gas, and at its end the gas bubbles ideally can have only the end product methane and in between the gas forming the bubbles can have any given mix ratio of substrate gas and methane.
[0146] Moreover, for further increasing of the contact surface between the substrate gas and the aqueous medium 116 the reactor 108 can optionally have at least one mixing element 124. The at least one mixing element 124 can be at least one element which is suitable to mix the substrate gas present in the reactor 108 with the aqueous medium 116. The at least one mixing element 124 can be, for example, a mechanically dynamic element and be designed for example as a rotating water wheel, a jet stream mixer, a turbine stirrer, a propeller stirrer, or perhaps an in-line mixer, this being by no means considered to be an exhaustive listing of possible mixing elements. But the at least one mixing element 124 can also be a mechanically static element, such as an atomization screen, which converts larger substrate gas bubbles into smaller substrate gas bubbles. The at least one mixing element 124 can also have at least one of both a mechanically dynamic and a mechanically static element.
[0147] As shown moreover in
[0148] The effective conversion of the substrate gas by means of the methanogenic microorganisms into the product gas methane is based on a highly turbulent gas/water/bacteria mixing inside the tube reactor 108 with an adequate flow rate of the aqueous medium 116, which when using static in-line mixers can be for example in the range of around 3 m/s to around 10 m/s, for example in the range of around 3 m/s to around 5 m/s. When using dynamic in-line mixers with independent motor drive unit, no flow rate is dictated.
[0149] The boosted reaction rate inside the reactor 108 can be accomplished by a highly turbulent mixing of the aqueous medium 116 with the substrate gas. Preferably, the gas volume introduced into the reactor 108 per hour is greater than the volume capacity of the tube reactor 108 itself. The ratio of the gas volume introduced into the reactor 108 per hour to its volume capacity can be for example around 5:1 or more, for example around 10:1, for example around 25:1, for example 50:1 or more. These values pertain to the gas feed at the feed mechanism 102.
[0150] Based on these figures, a little mathematical estimate shall be made to demonstrate the possible capability of the concept presented here. If one starts from a ratio of the gas volume introduced into the reactor 108 per hour to its volume capacity of 5:1, for each cubic meter of reactor volume with an almost complete conversion of the substrate gas according to the teaching of this specification 1 m.sup.3 of methane can be formed per hour. 1 m.sup.3 of methane has an energy content of around 10 kWh. It follows from the development of 1 m.sup.3 methane per hour per 1 m.sup.3 of reactor volume, at complete conversion of the substrate gases to methane, that a corresponding reactor will have a power of around 10 kW per cubic meter. Thus, a reactor 100 m.sup.3 in size would have a power of 1 MW. If one increases the gas throughput ratio to 25:1 per hour, with complete conversion of the substrate gases to methane one can realize a reactor plant with 1 MW power with only 20 m.sup.3 of reactor volume. However, it must be stressed that this is a sample calculation, which is meant to illustrate quantitatively a possible operating scenario of the device for production of methane by means of methanogenic microorganisms as an estimation and should in no way be taken as limiting the power spectrum of the concept presented here.
[0151] The highly turbulent mixing of the aqueous medium 116 with the substrate gas inside the reactor 116by whatever means this is brought aboutensures a distinct increasing of the contact surface between the aqueous medium 116 with the methanogenic microorganisms and the substrate gas, which in turn ensures a distinctly higher reaction rate inside the reactor 108 as compared to the static case mentioned above. In view of the intense mixing of the aqueous medium 116, one can speak in the present case of a rather atypical operation of the tube reactor 108 of the sample device 100 for the production of methane by means of methanogenic microorganisms, since tube reactors of this kind used in chemistry usually have a negligible axial mixing in operation. But in the case presented here of the production method for methane by means of the 100 from
[0152] The sample embodiment of the device 100 for production of methane described thus far and represented in
[0153] Another sample embodiment of a device 200 for the production of methane by means of methanogenic microorganisms is represented in
[0154] By means of the first return branch 118 the gaseous phase, possibly containing unreacted substrate gas which collects above the surface of the aqueous medium 116 inside the stirred tank 202, can be taken away and mixed in with the substrate gas supplied at the inlet line 102 by means of a compressor 206 and thus ensure a boosted turbulent mixing of the phases inside the stirred tank 202.
[0155] A further sample embodiment of a device 300 for the production of methane by means of methanogenic microorganisms is shown in
[0156] Yet another sample embodiment of a device 400 for the production of methane by means of methanogenic microorganisms is shown in
[0157]
[0158] Yet another embodiment of the device for the production of methane by means of methanogenic microorganisms is shown in
[0159]
[0160] Several such submerse reactors (R.sub.1 to R.sub.n) can be operated in series as a cascade one after another (see
In all the embodiments presented here of the device for production of methane by means of methanogenic microorganisms the CO.sub.2 can be obtained from a smoke gas, such as a trash incinerator or a power plant, such as a coal-fired power plant. For this, the device according to the invention can have a concentration device, having for example a pressurized tank filled with water, through which smoke gas is taken. Since CO.sub.2 has better solubility as compared to N.sub.2 and O.sub.2, the water can become enriched with CO.sub.2 under pressure. Then, by reducing the pressure, the smoke gas can at first be removed from the concentration device. By a further pressure reduction the CO.sub.2 can then be released from the water and supplied as substrate gas to the nozzle 106 and used, for example, together with the recirculated aqueous medium 116 to form the driving jet. Oxygen residues can be removed chemically or biologically before feeding to the nozzle 106.
[0161] As compared to chemical methods using catalysis, the method according to the invention can also be carried out with gases that are not pure. Steps to purify the gases are done away with. As compared to other methods of biomethanization, defined biomass densities can be established here and reproduced as needed. Furthermore, a good gas supply of the organisms is assured by the internal recirculation of the gas.
Sample Embodiment 1
[0162] Load water in reactor with nutrient salts for freshwater medium per Widdel (1980) as well as permillage trace elements per Immhoff-Stuckle et al. (1983). Heat water in the reactor to around 60-70 C., drive out the atmosphere with N.sub.2. Close reactor. Let water cool down under N.sub.2 atmosphere to around 40 C. and add N.sub.2 up to a pressure of around 0.2 bar. Add a permillage vitamin solution per Balch et al. (1979). Reduce with NaS to <0.2 V. Add active methanogenic bacterial macrocolonies, so-called pellets, from an anaerobic industrial wastewater treatment plant (such as a pulp plant or the food industry) in sufficient concentration (around 1% dry substance). Adjust temperature from 35 to 38 C. and pH to around 7. Start mixing of the reactor. Charge reactor with a defined quantity of substrate gases (H.sub.2/CO.sub.2) per unit of time in a ratio of around 4:1 with a pressure of 0.2 bar. Maintain a pressure in the reactor of 0.2-0.1 bar. Release the resulting gas mixture from the reactor at a pressure of >0.2-0.1 bar.
LITERATURE
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(1984): Anaerobic degradation of 3-chlor-benzoic acid to methane in a defined medium, IAWPRC Symposium on Forest Industry Waste Water, Tamper [0186] Schoberth, S. M., Brunner, M., Sahm, H. (1988): Anaerobic decomposition of halogen aromatics, Gas-Wasser-Fach 129, (1), 32-34 [0187] Sterner, M. (2009): Dynamic Simulation of the Electricity Supply in Germany by the Decomposition Scenario of the Renewable Energy Industry, final report, Fraunhofer IWES, 2009 [0188] Sterner, M. (2009): Bioenergy and renewable power methane in integrated 100% renewable energy systems, Limiting global warming by transforming energy systems, dissertation, University of Kassel, Fraunhofer IWES, 2009 [0189] Sterner, M.; Specht, M. (2010): Renewable methane. A solution for the integration and storage of renewable energies and a path to full regenerative supply, In Solarzeitalter January 2010 [0190] Sterner, M. (2011): Energy-economic and ecological evaluation of the wind gas supply, Fraunhofer IWES, February 2011 [0191] Tom Smolinka et al. (2011): NOW Study, current state and development potential of water electrolysis for the production of hydrogen from regenerative energies, summary of the final report, 2011 [0192] Vereijken, T., Brunner, M. (1989): New developments in brewery water treatment, Brauindustrie June 1989, 653-656 [0193] Association of the Swiss Gas Industry (VSG), Agency for Renewable Energies and Energy Efficiency (A EE): Swiss Renewable Power-to-GasRenewable gas from electricity for Switzerland, Bern, June 2012 [0194] Widdel, F. (1980): Anaerobic decomposition of fatty acids and benzoic acid by newly isolated sulfate-reducing bacteria, dissertation, University of Gttingen