CN103113010A - Method for synchronous implementation of methanation of coke oven gas and in-situ purification of marsh gas - Google Patents

Method for synchronous implementation of methanation of coke oven gas and in-situ purification of marsh gas Download PDF

Info

Publication number
CN103113010A
CN103113010A CN2013100418338A CN201310041833A CN103113010A CN 103113010 A CN103113010 A CN 103113010A CN 2013100418338 A CN2013100418338 A CN 2013100418338A CN 201310041833 A CN201310041833 A CN 201310041833A CN 103113010 A CN103113010 A CN 103113010A
Authority
CN
China
Prior art keywords
gas
coke
oven
anaerobic reactor
biogas
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
CN2013100418338A
Other languages
Chinese (zh)
Inventor
谢丽
王雯
罗刚
周琪
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Tongji University
Original Assignee
Tongji University
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Tongji University filed Critical Tongji University
Priority to CN2013100418338A priority Critical patent/CN103113010A/en
Publication of CN103113010A publication Critical patent/CN103113010A/en
Pending legal-status Critical Current

Links

Images

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E50/00Technologies for the production of fuel of non-fossil origin
    • Y02E50/30Fuel from waste, e.g. synthetic alcohol or diesel

Abstract

The invention relates to a method for synchronous implementation of methanation of coke oven gas and in-situ purification of marsh gas. The method comprises the following steps: (a) introducing the coke oven gas and organic wastes into an anaerobic reactor; (b) in the anaerobic reactor, degrading the organic wastes with microbes to generate CH4 and CO2, enabling produced CO2 to combine with H2 in the coke oven gas to generate CH4 under the action of the microbes, and reacting CO and CO2 in the coke oven gas with H2 to generate CH4 to get the marsh gas which mainly contains CH4; and (c) separating and removing impurities in the marsh gas obtained in the step (b) to get natural gas with high content of methane. Compared with the prior art, according to the method disclosed by the invention, a microbial process is adopted for introducing the coke oven gas into the anaerobic reactor, the in-situ purification of the marsh gas is simultaneously implemented during the preparation of the natural gas, a catalyst is not required, high temperature and high pressure are not required, and most of components except methane in the coke oven gas and the marsh gas can be converted to methane, so that the new method is provided for solving the problems of shortage of resources, environmental pollution, unreasonable energy structure and the like in the energy field in China.

Description

A kind of method that realizes that synchronously coke-oven gas methanation and biogas original position are purified
Technical field
The present invention relates to the comprehensive utilization of coking industry byproduct and methane purification, especially relate to a kind of method that realizes that synchronously coke-oven gas methanation and biogas original position are purified.
Background technology
Anaerobic digestion process is widely used in the processing of high concentrated organic wastewater (vinasse, percolate etc.), organic waste (mud, cow dung, stalk etc.) due to advantages such as having high loading, less energy-consumption, low operating cost, the generation energy.The main component of the biogas that anaerobic digestion process produces is 50-70% methane (CH 4), 30-50% carbonic acid gas (CO 2) and a small amount of hydrogen sulfide (H 2S), water (H 2O), ammonia nitrogen (NH 3), hydrogen (H 2) and carbon monoxide (CO) etc., be a kind of continuable valuable energy derive.Undressed common biogas, energy density is low, and calorific value generally between 5200-6600 kilocalorie/cubic meter, uses as domestic energy for a long time, also is used at present generating.Yet along with the exhaustion of ore fuel, the demand of biogas utilization constantly increases, and is that the bio-natural gas of methane content more than 90% just paid close attention to widely because it utilizes efficiently with methane purification.Biogas calorific value high (8000-9000 kilocalorie/cubic meter) after purifying, but long distance transportation also can be used as vehicle fuel or inject gas distributing system replacement Sweet natural gas.Biogas is converted into the higher Sweet natural gas of calorific value mainly needs to remove wherein CO 2To improve CH 4Concentration, the biogas after purification also needs further to purify the impurity such as the hydrogen sulfide removed wherein, moisture.Methane purification is mainly realized CO by technology such as pressure-variable adsorption, washing, polyoxyethylene glycol washing or membrane sepn industrial at present 2Removal, above technology all need to be added extra equipment and be realized methane purification outside anaerobic reactor, these techniques are all to adopt physico-chemical process to realize methane purification in addition, need high pressure or add chemical substance just can carry out, thereby running cost are higher.The cost of methane purification is subjected to purification techniques, and the impact of biogas plant's scale etc. is at present at 0.18-0.70 dollar/m 3Between.In purification process, the CH of 2%-10% is arranged approximately 4Can lose, with CO 2Be discharged in air.Due to CH 4Greenhouse effect are CO 220 times, so this part CH 4The loss meeting impacts environment.
Coke(oven)gas refers to be mixed with coking coal with several bituminous coal, and through after high temperature carbonization, a kind of inflammable gas that produces in output coke and tar products is the byproduct of coking industry in pit kiln, but dry coal commercial coke oven gas 300-350m per ton 3Its chief component is: H 255%~60%, CH 423%~27%, CO5-8%, C 2Above unsaturated hydrocarbons 2%~4%, CO 21.5%~3%, O 20.3%~0.8%, H 2S0.01%, N 23%~7%.Utilize the coke(oven)gas synthetic natural gas to open up the efficient new way of utilizing of coke(oven)gas, can not only drive the technical progress of coking and energy industry, can also solve environmental pollution and wasting of resources problem that the coke(oven)gas discharging causes.The method of employing coke-oven gas for production of methane mainly comprises chemical process and physical method, wherein chemical process is to be the conversion of other except methane in coke(oven)gas methane, and physical method is to adopt the methods such as pressure-variable adsorption separation, low temperature separation process, membrane sepn, and methane is purified.Associated patent comprises CN191985A, CN101818087A, and CN101591578A, CN101607859A etc., however these methods all need to be in the situation that high temperature, high pressure and have catalyzer to exist to carry out, in addition to H in coke(oven)gas 2And CO 2Utilization also complete not, and the investment running cost all higher.
Summary of the invention
Purpose of the present invention is exactly to provide a kind of method that realizes that synchronously coke-oven gas methanation and biogas original position are purified for the defective that overcomes above-mentioned prior art existence.
Purpose of the present invention can be achieved through the following technical solutions:
A kind of method that realizes that synchronously coke-oven gas methanation and biogas original position are purified, the method comprises the following steps;
(a) coke(oven)gas and organic waste are passed in anaerobic reactor;
(b) in anaerobic reactor, organic waste is degraded by microorganisms and generates CH 4And CO 2, the CO of generation 2With the H in coke(oven)gas 2In conjunction with generating CH 4, under microbial process, the CO in coke(oven)gas and CO 2With H 2Generate CH 4, obtain with CH 4Be main biogas;
(c) separate the impurity of removing in step (b) gained biogas, obtain having the Sweet natural gas of high methane content.
The flow that passes into the coke(oven)gas of anaerobic reactor in step (a) is determined by the following method:
V Coke(oven)gas=4 * V CO2/ (P H2-3 * P CO-4 * P CO2)
Wherein, V Coke(oven)gasBe the flow of coke(oven)gas, V CO2CO for the anaerobic reactor generation 2Flow, P H2, P CO, P CO2Be respectively H 2, CO and CO 2Component in coke(oven)gas.
Temperature in step (a) or the described anaerobic reactor of step (b) is 30~40 ℃ or 50~60 ℃.
Step (a) or the described anaerobic reactor of step (b) are CSTR reactor or UASB reactor.
Microorganism mainly utilizes following reaction with CO 2Be converted into CH 4
4H 2+CO 2=CH 4+2H 2O ΔG 0=-1307KJ/mol
The described organic waste of step (b) is selected from sewage plant sludge, cow dung or pig manure.
In anaerobic reactor, mixing by mechanical stirring, gas stirring or hollow-fibre membrane aeration between organic waste and coke(oven)gas realizes.
The described pressure-variable adsorption that is separated into of step (c) separates or low temperature separation process, and these two kinds of separation methods are the now ripe technique of using.
The described impurity of step (c) comprises N 2, H 2, CO, H 2O, CO 2And H 2S, the total mass mark of impurity is less than 10%.
The described Sweet natural gas with high methane content of step (c) refers to that the massfraction of methane is the Sweet natural gas more than 98%.
The present invention proposes a kind of method of microorganism that utilizes and synchronously realize the method that coke-oven gas methanation and biogas original position are purified.Coke(oven)gas can directly pass into the anaerobic reactor of processing organic waste, and CO wherein can be converted into CH under the anaerobion effect 4, CO 2Can with H 2(can consume the H of 6-12% 2) generation CH 4, remaining approximately 50% H 2CO with the anaerobic reactor generation 2In conjunction with generating CH 4, this technique has not only realized the biogas original position purification of anaerobic reactor, also can realize the methanation of coke(oven)gas.
Compared with prior art, the present invention has the following advantages and beneficial effect:
(1) adopt microbiological processes that coke(oven)gas is passed into anaerobic reactor and realize the purification of biogas original position when producing Sweet natural gas, there is no precedent both at home and abroad, this technique to high-efficiency economy, need not to add catalyzer, need not High Temperature High Pressure, can be the most conversion except methane in coke(oven)gas and biogas methane, the shortage of resources that faces for solving China's energy field, environmental pollution, energy structure is unreasonable etc., and problem provides novel method.
(2) utilized greenhouse gases CO in technological process of the present invention 2, not only reduced CO 2Discharging, and with CO 2Be converted into the new energy, a kind of CO is provided 2Therefore the new way of recycling helps reduction of greenhouse gas discharge.
Description of drawings
Fig. 1 is process flow sheet of the present invention.
In figure, 1 is coke(oven)gas, and 2 is organic waste, and 3 is anaerobic reactor, and 4 is with CH 4Be main biogas, 5 for having the Sweet natural gas of high methane content.
Embodiment
The present invention is described in detail below in conjunction with the drawings and specific embodiments.
Embodiment 1
Take the anaerobism CSTR reactor of the plant excess sludge of disposing of sewage as example, reactor is 100m 3, biogas output is 1m 3/ L/d, CH in biogas 4Content is 60%, CO 2Content is 40%.Coke(oven)gas consists of H 2Content 65%, CO content 5%, CH 4Content 25%, CO 2Content 3%.The flow that coke(oven)gas passes into anaerobic reactor is 421m 3/ d, this reactor adopts mechanical stirring, and stirring velocity is 400rpm.The air-fuel mixture amount that produces is 200m approximately 3/ d, methane concentration are more than 90%, obtain the Sweet natural gas of 98% above methane content through further purifying.
Embodiment 2
A kind of method that realizes that synchronously coke-oven gas methanation and biogas original position are purified, its technique as shown in Figure 1, the method comprises the following steps:
(a) coke(oven)gas 1 is passed in the anaerobic reactor 3 of processing organic waste 2;
(b) in anaerobic reactor 3, organic waste 2 is degraded by microorganisms and produces CH 4And CO 2, the CO of generation 2Further with coke(oven)gas 1 in H 2In conjunction with generating CH 4, a small amount of CO and CO in coke(oven)gas 1 2Also utilized and H by microorganism 2Generate CH 4, obtain take CH4 as main biogas 4, wherein CH 4Massfraction be 91%;
(c) impurity in separating take CH4 as main biogas 4 by pressure-variable adsorption, acquisition has the Sweet natural gas 5 of high methane content (methane content is more than 98%).
Wherein, the flow that passes into the coke(oven)gas 1 of anaerobic reactor 3 in step (a) is determined by the following method:
V Coke(oven)gas 1=4 * V CO2/ (P H2-3 * P CO-4 * P CO2)
In formula, V Coke(oven)gas 1Be the flow of coke(oven)gas 1, V CO2CO for anaerobic reactor 3 generations 2Flow, P H2, P co, P CO2Be respectively H 2, CO and CO 2Component in coke(oven)gas 1.
The anaerobic reactor 3 of the present embodiment is the CSTR reactor, and the temperature in anaerobic reactor 3 is 30~40 ℃.Organic waste 2 in the present embodiment is sewage plant sludge.In anaerobic reactor 3, mixing between organic waste 2 and coke(oven)gas 1 realizes by mechanical stirring.Step (c) impurity comprises N 2, H 2, CO, H 2O, CO 2And H 2S, the total mass mark of impurity is 9%.
Embodiment 3
A kind of method that realizes that synchronously coke-oven gas methanation and biogas original position are purified, its technique as shown in Figure 1, the method comprises the following steps:
(a) coke(oven)gas 1 is passed in the anaerobic reactor 3 of processing organic waste 2;
(b) in anaerobic reactor 3, organic waste 2 is degraded by microorganisms and produces CH 4And CO 2, the CO of generation 2Further with coke(oven)gas 1 in H 2In conjunction with generating CH 4, a small amount of CO and CO in coke(oven)gas 1 2Also utilized and H by microorganism 2Generate CH 4, obtain take CH4 as main biogas 4, wherein CH 4Massfraction greater than 90%;
(c) impurity in take CH4 as main biogas 4 by low temperature separation process obtains to have the Sweet natural gas 5 of high methane content (methane content is more than 98%).
Wherein, the flow that passes into the coke(oven)gas 1 of anaerobic reactor 3 in step (a) is determined by the following method:
V Coke(oven)gas 1=4 * V CO2/ (P H2-3 * P CO-4 * P CO2)
In formula, V Coke(oven)gas 1Be the flow of coke(oven)gas 1, V CO2CO for anaerobic reactor 3 generations 2Flow, P H2, P co, P CO2Be respectively H 2, CO and CO 2Component in coke(oven)gas 1.
The anaerobic reactor 3 of the present embodiment is the UASB reactor, and the temperature in anaerobic reactor 3 is 50~60 ℃.Organic waste 2 in the present embodiment is cow dung.In anaerobic reactor 3, mixing by gas stirring between organic waste 2 and coke(oven)gas 1 realizes.Step (c) impurity comprises N 2, H 2, CO, H 2O, CO 2And H 2S, the total mass mark of impurity is less than 10%.
Embodiment 4
A kind of method that realizes that synchronously coke-oven gas methanation and biogas original position are purified, its technique as shown in Figure 1, the method comprises the following steps:
(a) coke(oven)gas 1 is passed in the anaerobic reactor 3 of processing organic waste 2;
(b) in anaerobic reactor 3, organic waste 2 is degraded by microorganisms and produces CH 4And CO 2, the CO of generation 2Further with coke(oven)gas 1 in H 2In conjunction with generating CH 4, a small amount of CO and CO in coke(oven)gas 1 2Also utilized and H by microorganism 2Generate CH 4, obtain take CH4 as main biogas 4, wherein CH 4Massfraction be 90%;
(c) impurity in take CH4 as main biogas 4 by low temperature separation process obtains to have the Sweet natural gas 5 of high methane content (methane content is more than 98%).
Wherein, the flow that passes into the coke(oven)gas 1 of anaerobic reactor 3 in step (a) is determined by the following method:
V Coke(oven)gas 1=4 * V CO2/ (P H2-3 * P CO-4 * P CO2)
In formula, V Coke(oven)gas 1Be the flow of coke(oven)gas 1, V CO2CO for anaerobic reactor 3 generations 2Flow, P H2, P CO, P CO2Be respectively H 2, CO and CO 2Component in coke(oven)gas 1.
The anaerobic reactor 3 of the present embodiment is the CSTR reactor, and the temperature in anaerobic reactor 3 is 30~40 ℃.Organic waste 2 in the present embodiment is pig manure.In anaerobic reactor 3, mixing by the hollow-fibre membrane aeration between organic waste 2 and coke(oven)gas 1 realizes.Step (c) impurity comprises N 2, H 2, CO, H 2O, CO 2And H 2S, the total mass mark of impurity is less than 10%.

Claims (9)

1. a method that realizes that synchronously coke-oven gas methanation and biogas original position are purified, is characterized in that, the method comprises the following steps:
(a) coke(oven)gas and organic waste are passed in anaerobic reactor;
(b) in anaerobic reactor, organic waste is degraded by microorganisms and generates CH 4And CO 2, the CO of generation 2With the H in coke(oven)gas 2In conjunction with generating CH 4, under microbial process, the CO in coke(oven)gas and CO 2With H 2Generate CH 4, obtain with CH 4Be main biogas;
(c) separate the impurity of removing in step (b) gained biogas, obtain having the Sweet natural gas of high methane content.
2. a kind of method that realizes that synchronously coke-oven gas methanation and biogas original position are purified according to claim 1, is characterized in that, the flow that passes into the coke(oven)gas of anaerobic reactor in step (a) is determined by the following method:
V Coke(oven)gas=4 * V CO2/ (P H2-3 * P CO-4 * P CO2)
Wherein, V Coke(oven)gasBe the flow of coke(oven)gas, V CO2CO for the anaerobic reactor generation 2Flow, P H2, P co, P CO2Be respectively H 2, CO and CO 2Component in coke(oven)gas.
3. a kind of method that realizes that synchronously coke-oven gas methanation and biogas original position are purified according to claim 1, is characterized in that, the temperature in step (a) or the described anaerobic reactor of step (b) is 30~40 ℃ or 50~60 ℃.
4. a kind of method that realizes that synchronously coke-oven gas methanation and biogas original position are purified according to claim 1, is characterized in that, step (a) or the described anaerobic reactor of step (b) are CSTR reactor or UASB reactor.
5. a kind of method that realizes that synchronously coke-oven gas methanation and biogas original position are purified according to claim 1, is characterized in that, the described organic waste of step (b) is selected from sewage plant sludge, cow dung or pig manure.
6. a kind of method that realizes that synchronously coke-oven gas methanation and biogas original position are purified according to claim 1, it is characterized in that, in anaerobic reactor, mixing by mechanical stirring, gas stirring or hollow-fibre membrane aeration between organic waste and coke(oven)gas realizes.
7. a kind of method that realizes that synchronously coke-oven gas methanation and biogas original position are purified according to claim 1, is characterized in that, the described pressure-variable adsorption that is separated into of step (c) separates or low temperature separation process.
8. a kind of method that realizes that synchronously coke-oven gas methanation and biogas original position are purified according to claim 1, is characterized in that, the described impurity of step (c) comprises N 2, H 2, CO, H 2O, CO 2And H 2S, the total mass mark of impurity is less than 10%.
9. a kind of method that realizes that synchronously coke-oven gas methanation and biogas original position are purified according to claim 1, is characterized in that, the described Sweet natural gas with high methane content of step (c) refers to that the massfraction of methane is the Sweet natural gas more than 98%.
CN2013100418338A 2013-02-01 2013-02-01 Method for synchronous implementation of methanation of coke oven gas and in-situ purification of marsh gas Pending CN103113010A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN2013100418338A CN103113010A (en) 2013-02-01 2013-02-01 Method for synchronous implementation of methanation of coke oven gas and in-situ purification of marsh gas

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN2013100418338A CN103113010A (en) 2013-02-01 2013-02-01 Method for synchronous implementation of methanation of coke oven gas and in-situ purification of marsh gas

Publications (1)

Publication Number Publication Date
CN103113010A true CN103113010A (en) 2013-05-22

Family

ID=48411424

Family Applications (1)

Application Number Title Priority Date Filing Date
CN2013100418338A Pending CN103113010A (en) 2013-02-01 2013-02-01 Method for synchronous implementation of methanation of coke oven gas and in-situ purification of marsh gas

Country Status (1)

Country Link
CN (1) CN103113010A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104926062A (en) * 2015-07-07 2015-09-23 云南师范大学 Enrichment and domestication method of hydrogen nutrition type bacteria groups producing methane
CN105463048A (en) * 2015-03-26 2016-04-06 高节义 Method for preparing methane from coal combustion exhaust and device thereof
CN105602999A (en) * 2015-11-13 2016-05-25 中国石油大学(北京) System and method used for producing high-quality biological methane gas from biomass

Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CA999437A (en) * 1973-02-28 1976-11-09 Herman F. Feldmann Process for converting solid wastes to pipeline gas
CN102492506A (en) * 2011-12-12 2012-06-13 中国科学院广州能源研究所 Method and device for removing carbon dioxide in methane by organic waste water
CN102585950A (en) * 2012-02-27 2012-07-18 四川亚连科技有限责任公司 Method for preparing synthetic natural gas by coke oven gas in combination with straw gas
EP2479246A1 (en) * 2011-01-22 2012-07-25 Karlsruher Institut für Technologie Methane synthesis from synthesis gas in a bubble column reactor
CN102614887A (en) * 2012-02-27 2012-08-01 四川亚连科技有限责任公司 Catalytic agent and preparation method for preparing natural gas by mixing coke-oven gas and straw gas
CN102796765A (en) * 2012-08-06 2012-11-28 北京化工大学常州先进材料研究院 Method for treating easily-degradable organic waste in two-phase hydrogen-production methane-production coupling reaction

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CA999437A (en) * 1973-02-28 1976-11-09 Herman F. Feldmann Process for converting solid wastes to pipeline gas
EP2479246A1 (en) * 2011-01-22 2012-07-25 Karlsruher Institut für Technologie Methane synthesis from synthesis gas in a bubble column reactor
CN102492506A (en) * 2011-12-12 2012-06-13 中国科学院广州能源研究所 Method and device for removing carbon dioxide in methane by organic waste water
CN102585950A (en) * 2012-02-27 2012-07-18 四川亚连科技有限责任公司 Method for preparing synthetic natural gas by coke oven gas in combination with straw gas
CN102614887A (en) * 2012-02-27 2012-08-01 四川亚连科技有限责任公司 Catalytic agent and preparation method for preparing natural gas by mixing coke-oven gas and straw gas
CN102796765A (en) * 2012-08-06 2012-11-28 北京化工大学常州先进材料研究院 Method for treating easily-degradable organic waste in two-phase hydrogen-production methane-production coupling reaction

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
张新波等: "焦炉气甲烷化制天然气技术开发", 《化工进展》, vol. 31, 31 December 2012 (2012-12-31), pages 1 - 9 *
杜雄伟: "国内焦炉气制天然气专利技术发展现状", 《现代化工》, vol. 32, no. 01, 31 January 2012 (2012-01-31), pages 19 - 22 *

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN105463048A (en) * 2015-03-26 2016-04-06 高节义 Method for preparing methane from coal combustion exhaust and device thereof
CN104926062A (en) * 2015-07-07 2015-09-23 云南师范大学 Enrichment and domestication method of hydrogen nutrition type bacteria groups producing methane
CN105602999A (en) * 2015-11-13 2016-05-25 中国石油大学(北京) System and method used for producing high-quality biological methane gas from biomass

Similar Documents

Publication Publication Date Title
Bi et al. Improved high solid anaerobic digestion of chicken manure by moderate in situ ammonia stripping and its relation to metabolic pathway
CN101245262B (en) Gas-steam combined cycle system and technique based on coal gasification and methanation
CN103898265B (en) A kind of coke-oven gas upgrading direct-reduction iron ore system and device and method
CN101638670A (en) Method for co-producing hydrogen and methane by utilizing dry anaerobic fermentation of solid organic wastes
CN111547678B (en) Method and system for preparing methanol by full-component thermal catalysis of marsh gas
Zhang et al. A mini-review on in situ biogas upgrading technologies via enhanced hydrogenotrophic methanogenesis to improve the quality of biogas from anaerobic digesters
WO2016077577A1 (en) Method for generating methane from a carbonaceous feedstock
CN104531186A (en) Method for producing tar and hydrocarbon fuel products with coal
Kigozi et al. Biogas technology: Current trends, opportunities and challenges
CN102181486B (en) Method for promoting rapid preparation of methane from organic waste by utilizing exogenous hydrogen
CN103555566A (en) Novel external electrolysis device for promoting anaerobic digestion to produce methane
CN103087793A (en) Process for realizing natural gas preparation with coke oven gas by using anaerobic microbes
CN113966387B (en) Method and device for producing methane
Xie et al. Biogas upgrading
CN103113010A (en) Method for synchronous implementation of methanation of coke oven gas and in-situ purification of marsh gas
CN105623761A (en) Method for biologically synthesizing natural gas from coke oven gas
CN101607859A (en) A kind of technology of employing coke-oven gas for production of methane
CN111171848B (en) System and method for producing high-purity steel and hydrogen
CN209854029U (en) Device for preparing methanol from synthesis gas without conversion system
CN105316052A (en) Method for preparing natural gas by using coke oven gas
CN105645581B (en) It is a kind of synchronously to realize organic waste treatment and the system and device and method of synthesis gas upgrading
CN1782038A (en) Process of co-producing high clean fuel by adding hydrogen to coal gasifying, power plant or other industrial waste gas
CN115698308A (en) Process for the biological production of hydrogen and/or methane by absorption and bioconversion of carbon dioxide
CN103074134A (en) Method for preparing biogas and carbonate by straw wastes
JP2018126090A (en) Process gas modification method and process gas modification device

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
C12 Rejection of a patent application after its publication
RJ01 Rejection of invention patent application after publication

Application publication date: 20130522