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JP2006016353A - Method for producing aromatic compound and hydrogen from lower hydrocarbon - Google Patents

Method for producing aromatic compound and hydrogen from lower hydrocarbon Download PDF

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JP2006016353A
JP2006016353A JP2004197126A JP2004197126A JP2006016353A JP 2006016353 A JP2006016353 A JP 2006016353A JP 2004197126 A JP2004197126 A JP 2004197126A JP 2004197126 A JP2004197126 A JP 2004197126A JP 2006016353 A JP2006016353 A JP 2006016353A
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hydrogen sulfide
hydrogen
biogas
catalyst
concentration
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Hironori Taki
寛則 瀧
Yuji Saito
祐二 斎藤
Masaru Ichikawa
勝 市川
Ayaichi Kojima
綾一 小島
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Taisei Corp
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    • 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
    • Y02CCAPTURE, STORAGE, SEQUESTRATION OR DISPOSAL OF GREENHOUSE GASES [GHG]
    • Y02C20/00Capture or disposal of greenhouse gases
    • Y02C20/20Capture or disposal of greenhouse gases of methane
    • 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
    • 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
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P20/00Technologies relating to chemical industry
    • Y02P20/50Improvements relating to the production of bulk chemicals
    • 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
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P20/00Technologies relating to chemical industry
    • Y02P20/50Improvements relating to the production of bulk chemicals
    • Y02P20/52Improvements relating to the production of bulk chemicals using catalysts, e.g. selective catalysts

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  • Exhaust Gas Treatment By Means Of Catalyst (AREA)
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  • Organic Low-Molecular-Weight Compounds And Preparation Thereof (AREA)
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Abstract

<P>PROBLEM TO BE SOLVED: To provide a method for efficiently producing aromatic hydrocarbons and hydrogen from a biogas. <P>SOLUTION: The method for producing the aromatic compounds and hydrogen comprises removing hydrogen sulfide in the biogas containing a lower hydrocarbon and hydrogen sulfide so that the remaining hydrogen sulfide content is a desired value, preferably, 1.25-10 ppm, and the obtained hydrogen sulfide-remaining biogas is treated in the presence of a catalyst. <P>COPYRIGHT: (C)2006,JPO&NCIPI

Description

本発明は、各種有機性廃棄物をメタン発酵により処理するときに発生するバイオガスから、触媒を用いて芳香族化合物及び水素を製造する方法に関する。   The present invention relates to a method for producing an aromatic compound and hydrogen from a biogas generated when various organic wastes are processed by methane fermentation using a catalyst.

近年、燃料電池技術の汎用化に伴い、水素エネルギーの重要性が認識されており、メタン等の低級炭化水素から芳香族化合物及び水素を得る方法等(特許文献1〜3参照)が開発されている。   In recent years, with the generalization of fuel cell technology, the importance of hydrogen energy has been recognized, and methods for obtaining aromatic compounds and hydrogen from lower hydrocarbons such as methane (see Patent Documents 1 to 3) have been developed. Yes.

一方、各種有機性廃棄物の処理方法の一つとして、微生物を用いたメタン発酵処理がある。この方法は、メタン菌等を用いて効率的に有機性廃棄物を処理する方法であり、同処理によってメタン等の低級炭化水素と二酸化炭素とを主成分とするガス(以下、「バイオガス」と称す。)を得ることができる。   On the other hand, there is a methane fermentation treatment using microorganisms as one of methods for treating various organic wastes. This method is an effective method for treating organic wastes using methane bacteria, etc., and a gas mainly composed of lower hydrocarbons such as methane and carbon dioxide (hereinafter referred to as “biogas”). Can be obtained.

バイオガスの利用方法としては、ガスタービン等で燃焼させて熱と電気エネルギーを得る方法のほかに、バイオガスを低級炭化水素源として触媒の存在下で芳香族炭化水素等の芳香族化合物及び水素を製造する方法(特許文献4参照)等がある。   In addition to a method of using a gas turbine or the like to obtain heat and electric energy, biogas can be used in addition to aromatic compounds such as aromatic hydrocarbons and hydrogen in the presence of a catalyst using biogas as a lower hydrocarbon source. (See Patent Document 4) and the like.

特開平11−60514号公報Japanese Patent Laid-Open No. 11-60514 特開平10−272366号公報JP 10-272366 A 特開平11−47606号公報Japanese Patent Laid-Open No. 11-47606 特開2001−316302号公報JP 2001-316302 A

バイオガス中には主成分であるメタン等の低級炭化水素及び二酸化炭素のほかに、硫化水素、アンモニア等が含まれる。なかでも硫化水素は触媒を被毒して触媒活性を著しく失わせる場合があることが知られている。そこで従来は、触媒を用いてバイオガスから芳香族炭化水素等の芳香族化合物を得る場合には、硫化物を完全に除去することが行われていた(特許文献4)。一般的な硫化物の除去法としては物理的及び/又は化学的操作による方法、例えば、酸化鉄等を用いた化学処理、イオン酸化細菌を用いた生物脱硫法が挙げられる。しかしながら、化学処理法では硫化水素を完全に除去するには多大なエネルギーとコストが必要であるという問題がある。また生物脱硫法では処理が不安定であり硫化水素の完全除去が期待できないという問題がある。   Biogas contains hydrogen sulfide, ammonia and the like in addition to the main components of lower hydrocarbons such as methane and carbon dioxide. Among them, it is known that hydrogen sulfide may poison the catalyst and cause a significant loss of catalytic activity. Therefore, conventionally, when an aromatic compound such as an aromatic hydrocarbon is obtained from biogas using a catalyst, the sulfide has been completely removed (Patent Document 4). General methods for removing sulfides include physical and / or chemical operation methods, for example, chemical treatment using iron oxide or the like, and biological desulfurization method using ion-oxidizing bacteria. However, the chemical treatment method has a problem that enormous energy and cost are required to completely remove hydrogen sulfide. Further, the biological desulfurization method has a problem that the treatment is unstable and complete removal of hydrogen sulfide cannot be expected.

そこで本発明は、芳香族化合物及び水素をバイオガスから効率的に製造する方法を提供することを目的とする。   Then, an object of this invention is to provide the method of manufacturing an aromatic compound and hydrogen efficiently from biogas.

本発明は以下の発明を包含する。
(1)低級炭化水素及び硫化水素を含有するバイオガス中の硫化水素を、残存硫化水素濃度が所望の値となるように除去し、得られた硫化水素残存バイオガスを触媒の存在下で処理して芳香族化合物及び水素を製造する方法。
(2)残存硫化水素濃度が1.25〜10ppmとなるようにバイオガス中の硫化水素を除去することを特徴とする(1)に記載の方法。
(3)触媒が、モリブデンを担持させたメタロシリケートを還元性ガスにより炭化処理することにより得られたものであることを特徴とする(1)又は(2)に記載の方法。
The present invention includes the following inventions.
(1) Hydrogen sulfide in a biogas containing lower hydrocarbons and hydrogen sulfide is removed so that the residual hydrogen sulfide concentration becomes a desired value, and the obtained hydrogen sulfide residual biogas is treated in the presence of a catalyst. To produce an aromatic compound and hydrogen.
(2) The method according to (1), wherein hydrogen sulfide in the biogas is removed so that the residual hydrogen sulfide concentration is 1.25 to 10 ppm.
(3) The method according to (1) or (2), wherein the catalyst is obtained by carbonizing a metallosilicate supporting molybdenum with a reducing gas.

本発明により、バイオガスを触媒の存在下で処理して芳香族化合物及び水素を製造する方法において硫化水素濃度低減に要するエネルギー及びコストを低減することができる。また、同方法による芳香族化合物及び水素の製造全体に要するエネルギー及びコストを最少化することができる。   According to the present invention, energy and cost required for reducing the hydrogen sulfide concentration can be reduced in a method for producing an aromatic compound and hydrogen by treating biogas in the presence of a catalyst. In addition, the energy and cost required for the overall production of the aromatic compound and hydrogen by this method can be minimized.

本発明は、低級炭化水素及び硫化水素を含有するバイオガス中の硫化水素を、残存硫化水素濃度が所望の値となるように除去し、得られた硫化水素残存バイオガスを触媒の存在下で処理して芳香族化合物及び水素を製造する方法に関する。   The present invention removes hydrogen sulfide in a biogas containing lower hydrocarbons and hydrogen sulfide so that the residual hydrogen sulfide concentration has a desired value, and the obtained hydrogen sulfide residual biogas is removed in the presence of a catalyst. The present invention relates to a method for producing an aromatic compound and hydrogen by treatment.

本発明者らは、実施例に示す通り、芳香族化合物及び水素の生成反応速度(すなわち触媒活性)が、反応系中の硫化水素濃度に依存することを見出した。具体的には、共存する硫化水素濃度が高いほど、触媒活性は低下することを見出した。更にまた、反応時間(すなわち処理量)が増すに連れて触媒活性が低下することを見出した。   As shown in Examples, the present inventors have found that the reaction rate of production of aromatic compounds and hydrogen (that is, catalytic activity) depends on the concentration of hydrogen sulfide in the reaction system. Specifically, it has been found that the catalyst activity decreases as the concentration of coexisting hydrogen sulfide increases. Furthermore, it has been found that the catalytic activity decreases as the reaction time (ie, throughput) increases.

かかる知見から、硫化水素含有バイオガスを触媒の存在下で処理して芳香族化合物及び水素を製造する場合、硫化水素濃度及び処理量の増大に伴って触媒活性が低下することがわかる。そして、一定以上活性が低下した時点で触媒の再生処理が行われる必要がある。再生処理にはエネルギーとコストがかかるため、再生処理の回数は少なくしたほうがよい。そのためにはバイオガス中の硫化水素濃度を低減させる方法が有効である。しかしながら、硫化水素濃度を低減させるほど硫化水素低減に必要なエネルギーとコストが増大する。この関係を図1に模式的に示すので参照されたい。この知見を応用すれば、下記の通り、芳香族化合物及び水素の製造の効率的な運転が可能となる。   From this knowledge, it can be seen that when an aromatic compound and hydrogen are produced by treating a hydrogen sulfide-containing biogas in the presence of a catalyst, the catalytic activity decreases as the hydrogen sulfide concentration and the treatment amount increase. Then, it is necessary to regenerate the catalyst when the activity drops below a certain level. Since the regeneration process takes energy and cost, it is better to reduce the number of regeneration processes. For this purpose, a method of reducing the concentration of hydrogen sulfide in biogas is effective. However, the energy and cost required for hydrogen sulfide reduction increase as the hydrogen sulfide concentration is reduced. This relationship is schematically shown in FIG. If this knowledge is applied, an efficient operation of producing aromatic compounds and hydrogen can be performed as described below.

触媒再生処理に必要なエネルギー及びコストと、バイオガス中の硫化水素濃度を低減するために必要なエネルギー及びコストとを比較して、バイオガスから芳香族化合物及び水素を製造するために要するエネルギー及びコストの合計を最小化できる硫化水素濃度を算定し、算定値に従って硫化水素を除去して得られたバイオガスを用いて触媒反応を行えば、芳香族化合物及び水素を最も効率的に製造することができる。すなわち本発明は、予め求めた、残存硫化水素濃度(すなわち、硫化水素除去量)と芳香族化合物及び水素の製造工程全体に要するエネルギー及びコストとの関係に基づいて、同エネルギー及びコストが所望の程度に(通常は最小に)なる残存硫化水素濃度を決定し、決定された所望の残存硫化水素濃度が達成されるようにバイオガス中の硫化水素を除去し、得られた硫化水素残存バイオガスを触媒の存在下で処理して芳香族化合物及び水素を製造する方法に関する。なお本明細書において残存硫化水素濃度の「所望の値」とは、芳香族化合物及び水素の製造工程全体に要するエネルギー及びコストが所望の程度になるときの残存硫化水素濃度を意味する。   Compare the energy and cost required for the catalyst regeneration treatment with the energy and cost required to reduce the concentration of hydrogen sulfide in the biogas, and the energy and cost required to produce aromatic compounds and hydrogen from the biogas. The most efficient production of aromatic compounds and hydrogen is achieved by calculating the hydrogen sulfide concentration that can minimize the total cost and performing a catalytic reaction using the biogas obtained by removing hydrogen sulfide according to the calculated value. Can do. That is, the present invention is based on the relationship between the residual hydrogen sulfide concentration (that is, the amount of hydrogen sulfide removed) obtained in advance and the energy and cost required for the entire aromatic compound and hydrogen production process. Determine the residual hydrogen sulfide concentration to the extent (usually minimal), remove the hydrogen sulfide in the biogas so that the determined desired residual hydrogen sulfide concentration is achieved, and obtain the resulting hydrogen sulfide residual biogas In the presence of a catalyst to produce an aromatic compound and hydrogen. In the present specification, the “desired value” of the residual hydrogen sulfide concentration means the residual hydrogen sulfide concentration when the energy and cost required for the entire production process of the aromatic compound and hydrogen become a desired level.

本発明のより好適な形態は、上述の硫化水素含有バイオガス中の硫化水素を、残存硫化水素濃度が1.25〜10ppmとなるように除去する工程を含むことを特徴とする。本発明者らは驚くべきことに、残存硫化水素濃度がこれらの範囲内の値になるように除去されたバイオガスを低級炭化水素源として用いて触媒の存在下で芳香族化合物及び水素を製造した場合に、硫化水素が完全に除去された(すなわち、残存硫化水素濃度が0である)バイオガスを低級炭化水素源として用いた場合と同程度の芳香族化合物生成速度及び水素生成速度が達成されることを見出した。硫化水素を完全に除去するには多大なエネルギー及びコストを要するが、本発明のこの好適な形態によれば硫化水素低減に要するエネルギー及びコストを抑制しつつ同程度の反応速度を達成することができるためエネルギー及びコストの面から非常に有利である。本発明のこの形態において、残存硫化水素濃度の上限はより好ましくは3ppmであり、下限はより好ましくは1.50ppm、より好ましくは2.0ppm、より好ましくは2.7ppm、最も好ましくは3.0ppmである。残存硫化水素濃度の下限がこれらの範囲にある場合、硫化水素除去に要するエネルギー又はコストが比較的少なくなるためより有利である。   A more preferable embodiment of the present invention is characterized by including a step of removing hydrogen sulfide in the above-described hydrogen sulfide-containing biogas so that the residual hydrogen sulfide concentration is 1.25 to 10 ppm. The inventors have surprisingly produced aromatic compounds and hydrogen in the presence of a catalyst using biogas that has been removed so that the residual hydrogen sulfide concentration is within these ranges as a lower hydrocarbon source. In this case, the same aromatic compound production rate and hydrogen production rate can be achieved as when a biogas from which hydrogen sulfide has been completely removed (that is, the residual hydrogen sulfide concentration is 0) is used as the lower hydrocarbon source. I found out that Although a great deal of energy and cost is required to completely remove hydrogen sulfide, according to this preferred embodiment of the present invention, the same reaction rate can be achieved while suppressing the energy and cost required for hydrogen sulfide reduction. This is very advantageous in terms of energy and cost. In this form of the invention, the upper limit of residual hydrogen sulfide concentration is more preferably 3 ppm, and the lower limit is more preferably 1.50 ppm, more preferably 2.0 ppm, more preferably 2.7 ppm, most preferably 3.0 ppm. It is. When the lower limit of the residual hydrogen sulfide concentration is within these ranges, it is more advantageous because the energy or cost required for removing hydrogen sulfide is relatively small.

本発明に使用し得るバイオガスは、例えば、各種有機性廃棄物を微生物処理することにより得ることができる。また各種有機性廃棄物を含む埋立地で発生するバイオガスを使用することもできる。各種有機性廃棄物は有機物を含む廃棄物であれば特に限定されないが、例えば、家畜糞尿、生ゴミ、各種工場からの廃棄物・排水、下水、し尿、汚泥、雑草などが挙げられる。微生物処理方法は、微生物を利用して有機物をメタン等の低級炭化水素へ変換することができる方法であれば特に限定されないが、例えばUASB法(Upflow Anaerobic Sludge Blanket=上向流嫌気性スラッジブランケット法)、乾式メタン発酵法などが挙げられる。バイオガスの製造には通常、メタン発酵し得る嫌気性菌(メタン菌)が使用される。   The biogas that can be used in the present invention can be obtained, for example, by treating various organic wastes with microorganisms. Biogas generated in landfills containing various organic wastes can also be used. Various organic wastes are not particularly limited as long as they are organic wastes, and examples thereof include livestock manure, garbage, waste / drainage from various factories, sewage, human waste, sludge, weeds, and the like. The microorganism treatment method is not particularly limited as long as it is a method capable of converting an organic substance into a lower hydrocarbon such as methane using microorganisms. For example, the UASB method (Upflow Anaerobic Sludge Blanket = upflow anaerobic sludge blanket method) ), Dry methane fermentation and the like. For the production of biogas, anaerobic bacteria (methane bacteria) that can undergo methane fermentation are usually used.

本発明に使用し得るバイオガスはメタン等の低級炭化水素及び硫化水素を含有する。より具体的には、本発明に使用されるバイオガスは通常、容量%で少なくとも40%、好ましくは60%以上のメタンガス、容量%で55%以下、好ましくは35%以下の二酸化炭素、及び容量%で0.01〜1%の硫化水素を含有する。   The biogas that can be used in the present invention contains lower hydrocarbons such as methane and hydrogen sulfide. More specifically, the biogas used in the present invention is usually at least 40% by volume, preferably 60% or more methane gas, 55% or less, preferably 35% or less carbon dioxide, and volume by volume. % Contains 0.01 to 1% hydrogen sulfide.

バイオガス中の硫化水素を除去する方法としては、硫化水素を所定の濃度にまで低下させ得る方法であれば特に限定されず、通常の物理的及び/又は化学的方法を採用することができる。例えば酸化鉄を用いる方法(乾式脱硫法)や、バイオガスを炭酸ソーダ水溶液又は水に流通させる方法(湿式脱硫法)や、微生物を用いて硫化水素を硫酸イオンに変換して除去する方法が例示できる。   The method for removing hydrogen sulfide in the biogas is not particularly limited as long as hydrogen sulfide can be reduced to a predetermined concentration, and normal physical and / or chemical methods can be employed. For example, a method using iron oxide (dry desulfurization method), a method of circulating biogas in a sodium carbonate aqueous solution or water (wet desulfurization method), and a method of converting hydrogen sulfide into sulfate ions using microorganisms and removing them are exemplified. it can.

なお、バイオガス中には数ppmのアンモニアが含まれる場合がある。しかしながら、実施例3で明らかにされる通り、100ppm以下のアンモニア含量であれば芳香族化合物及び水素の生成速度に影響がないとわかっていることから、アンモニアについては特段除去する必要はない。   Biogas may contain several ppm of ammonia. However, as is clear from Example 3, it is known that if the ammonia content is 100 ppm or less, the production rate of the aromatic compound and hydrogen is not affected, and therefore, it is not necessary to remove ammonia.

また、上記の通りバイオガス中には二酸化炭素が相当量含まれている。バイオガスに含まれる二酸化炭素が高濃度又は低濃度である場合には、芳香族化合物及び水素の生成速度が低下することがある。そのような場合には、必要に応じて、バイオガス中の二酸化炭素濃度を容積%で0.01〜10%、好ましくは1〜3%に制御することもできる。調節方法としては二酸化炭素濃度を制御する方法であれば特に限定されないが例えばアルカリ吸着剤を用いる方法や、PSA法(Pressure Swing Adsorption:圧力スイング吸着法)等を用いることができる。   Further, as described above, the biogas contains a considerable amount of carbon dioxide. When the carbon dioxide contained in the biogas has a high concentration or a low concentration, the production rate of the aromatic compound and hydrogen may decrease. In such a case, the carbon dioxide concentration in the biogas can be controlled to 0.01 to 10% by volume, preferably 1 to 3%, as necessary. The adjustment method is not particularly limited as long as it is a method for controlling the carbon dioxide concentration. For example, a method using an alkali adsorbent, a PSA method (Pressure Swing Adsorption), or the like can be used.

本発明において「バイオガスを触媒の存在下で処理する」とは、バイオガスに含まれるメタン等の低級炭化水素を芳香族化合物及び水素に変換する反応を触媒の存在下で行うことを意味する。   In the present invention, “treating biogas in the presence of a catalyst” means that a reaction for converting a lower hydrocarbon such as methane contained in the biogas into an aromatic compound and hydrogen is performed in the presence of the catalyst. .

本発明では触媒として、触媒材料を担体に担持させたものを用いることができる。好ましくは、この触媒は更に還元性ガスを混合させて炭化処理されたものである。触媒の担体としてはHZSM−5やMCM−22などのオングストロームスケールの細孔径を有する多孔質のメタロシリケートが好ましいが、触媒材料を担持できるものであれば特に限定されない。触媒材料としてはモリブデン、レニウム、タングステン、コバルト、ロジウム等の金属及びそれらの化合物並びにそれらの炭化物からなる群から選択される少なくとも1種を用いることができるがこれらに限定されない。触媒材料の担持量は、全重量の6〜20重量%程度が適当である。これらの触媒材料の担体への担持は通常の方法で行うことができ、例えば、触媒材料となる金属の水溶性無機塩を前駆体として含浸法にて担体に担持させる方法、又は、揮発性を有する触媒材料となる金属の有機金属錯体を用いて化学気相成長法(Chemical vapor desposition)にて行うことが好ましい。還元性ガスとしてはメタン、水素、メタン水素混合ガス等を使用することができるがこれらに限定されない。また本発明において「炭化処理」とは、触媒材料またはその前駆体を、上記還元性ガス流通下にて、昇温速度を一定にしながら加熱・還元し、炭化物を得る処理を意味する。また炭化処理は、触媒材料またはその前駆体を担体に担持させたものに対して行うこともできる。触媒材料の前駆体の例としては酸化物が挙げられる。   In the present invention, a catalyst having a catalyst material supported on a carrier can be used. Preferably, the catalyst is further carbonized by mixing a reducing gas. The catalyst carrier is preferably a porous metallosilicate having an angstrom-scale pore size such as HZSM-5 or MCM-22, but is not particularly limited as long as it can support a catalyst material. As the catalyst material, at least one selected from the group consisting of metals such as molybdenum, rhenium, tungsten, cobalt, rhodium, compounds thereof, and carbides thereof can be used, but is not limited thereto. The amount of catalyst material supported is suitably about 6 to 20% by weight of the total weight. These catalyst materials can be supported on a carrier by a usual method. For example, a method in which a water-soluble inorganic salt of a metal serving as a catalyst material is supported on a carrier by an impregnation method, or volatility can be achieved. It is preferable to carry out by a chemical vapor deposition method using an organometallic complex of a metal as a catalyst material. As the reducing gas, methane, hydrogen, methane-hydrogen mixed gas, or the like can be used, but is not limited thereto. Further, in the present invention, “carbonization treatment” means a treatment for obtaining a carbide by heating / reducing the catalyst material or its precursor under a flow of the reducing gas while keeping the temperature rising rate constant. The carbonization treatment can also be performed on a catalyst material or a precursor thereof supported on a carrier. Examples of the precursor of the catalyst material include oxides.

バイオガス中の低級炭化水素から芳香族化合物及び水素を得る反応処理は、通常は回分式又は流通式の反応形式で実施されるが、固定床、移動床又は流動化床等の流通式反応形式で実施することが好ましい。反応は、例えば触媒を固定床流通式反応管(例えば石英製)に充填し、好ましくは600〜850℃、より好ましくは700〜750℃の温度で、好ましくは1〜10atm、より好ましくは3〜5atmの圧力で、所定のバイオガスを好ましくはSV(重量時間空間速度)1000〜10000、より好ましくは3000〜5000で供給することによって行う。   The reaction treatment for obtaining aromatic compounds and hydrogen from lower hydrocarbons in biogas is usually carried out in a batch or flow type reaction mode, but a flow type reaction mode such as a fixed bed, moving bed or fluidized bed. It is preferable to carry out. In the reaction, for example, a catalyst is filled in a fixed bed flow type reaction tube (for example, made of quartz), preferably at a temperature of 600 to 850 ° C, more preferably 700 to 750 ° C, preferably 1 to 10 atm, more preferably 3 to 3. It is carried out by supplying a predetermined biogas at a pressure of 5 atm, preferably at SV (weight hourly space velocity) 1000-10000, more preferably 3000-5000.

上記反応により、ベンゼン、トルエン等の芳香族炭化水素を主成分とする芳香族化合物が得られる。なお、得られる芳香族化合物の種類や比率は原料に応じて変動し得る。また、この反応に伴って高純度の水素が得られる。   By the above reaction, an aromatic compound mainly containing an aromatic hydrocarbon such as benzene and toluene can be obtained. In addition, the kind and ratio of the aromatic compound obtained can be changed according to the raw material. In addition, high-purity hydrogen is obtained with this reaction.

純メタンガスに対して、二酸化炭素を1容量%、硫化水素を0〜100ppm添加したガスを用いて芳香族化合物及び水素を製造したときのベンゼン生成速度の経時的変化を図2に、水素生成速度の経時的変化を図3に示す。用いた触媒は6重量%のモリブデンをHZSM−5に担持させた触媒である。この触媒を反応容器に充填し、上記ガスをSV(重量時間空間速度)=3000(mL/(g・h))で通気し、反応温度750℃、3atmで反応させた。図2及び3から明らかな通り、ベンゼン生成速度及び水素生成速度の経時的変化は硫化水素が10ppmまで混合されている場合であっても、硫化水素が0ppmの場合と殆ど差異がなかった。このことから、二酸化炭素が1%存在する条件では硫化水素を10ppm以下とすることで硫化水素を完全に除去した場合と同程度のベンゼン生成速度及び水素生成速度を達成できることが明らかとなった。   Figure 2 shows the change in benzene production rate over time when an aromatic compound and hydrogen are produced using a gas containing 1% by volume of carbon dioxide and 0-100 ppm of hydrogen sulfide with respect to pure methane gas. The change with time is shown in FIG. The catalyst used was a catalyst in which 6% by weight of molybdenum was supported on HZSM-5. This catalyst was filled in a reaction vessel, and the gas was passed through with SV (weight hourly space velocity) = 3000 (mL / (g · h)), and reacted at a reaction temperature of 750 ° C. and 3 atm. As is clear from FIGS. 2 and 3, the time-dependent changes in the benzene production rate and the hydrogen production rate were almost the same as when hydrogen sulfide was 0 ppm even when hydrogen sulfide was mixed up to 10 ppm. From this, it has been clarified that under the condition where carbon dioxide is present at 1%, the benzene production rate and the hydrogen production rate comparable to those obtained when hydrogen sulfide is completely removed can be achieved by setting hydrogen sulfide to 10 ppm or less.

純メタンガスに対して、水素を6容量%、硫化水素を0〜100ppm添加したガスを用いて芳香族化合物及び水素を製造したときのベンゼン生成速度の経時的変化を図4に、水素生成速度の経時的変化を図5に示す。用いた触媒は6重量%のモリブデンをHZSM−5に担持させた触媒である。この触媒を反応容器に充填し、上記ガスをSV(重量時間空間速度)=3000(mL/(g・h))で通気し、反応温度750℃、3atmで反応させた。図4及び5から明らかな通り、ベンゼン生成速度及び水素生成速度の経時的変化は硫化水素が3ppmまで混合されている場合であっても、硫化水素が0ppmの場合と殆ど差異がなかった。このことから、水素が6%存在する条件では硫化水素を3ppm以下とすることで硫化水素を完全に除去した場合と同程度のベンゼン生成速度及び水素生成速度を達成できることが明らかとなった。   FIG. 4 shows the change over time in the benzene production rate when an aromatic compound and hydrogen are produced using a gas in which 6% by volume of hydrogen and 0 to 100 ppm of hydrogen sulfide are added to pure methane gas. The change over time is shown in FIG. The catalyst used was a catalyst in which 6% by weight of molybdenum was supported on HZSM-5. This catalyst was filled in a reaction vessel, and the gas was passed through with SV (weight hourly space velocity) = 3000 (mL / (g · h)), and reacted at a reaction temperature of 750 ° C. and 3 atm. As apparent from FIGS. 4 and 5, the benzene production rate and the hydrogen production rate over time were almost the same as those when hydrogen sulfide was 0 ppm even when hydrogen sulfide was mixed up to 3 ppm. From this, it has been clarified that under the condition where 6% hydrogen is present, by setting the hydrogen sulfide to 3 ppm or less, it is possible to achieve the same benzene production rate and hydrogen production rate as when hydrogen sulfide is completely removed.

純メタンガスに対して、二酸化炭素を容量1%、アンモニアを0〜100ppm添加したガスを用いて水素及び芳香族化合物を製造したときのベンゼン生成速度の経時的変化を図6に、水素生成速度の経時的変化を図7に示す。用いた触媒は6重量%のモリブデンをHZSM−5に担持させた触媒である。この触媒を反応容器に充填し、上記ガスをSV(重量時間空間速度)=3000(mL/(g・h))で通気し、反応温度750℃、3atmで反応させた。図6及び7から明らかな通り、ベンゼン生成速度及び水素生成速度の経時的変化は硫化水素が100ppmまで混合されている場合であっても、硫化水素が0ppmの場合と殆ど差異がなかった。バイオガス中のアンモニア濃度は通常は数ppm程度であることに鑑みれば、バイオガスを原料として芳香族化合物及び水素を製造する場合にはアンモニア除去工程を設けなくても、アンモニアを完全に除去した場合と同程度に芳香族化合物及び水素を製造することが可能となることが分った。   FIG. 6 shows changes over time in the benzene production rate when hydrogen and an aromatic compound are produced using a gas in which carbon dioxide is added at a volume of 1% and ammonia is added at 0 to 100 ppm with respect to pure methane gas. The change over time is shown in FIG. The catalyst used was a catalyst in which 6% by weight of molybdenum was supported on HZSM-5. This catalyst was filled in a reaction vessel, and the gas was passed through with SV (weight hourly space velocity) = 3000 (mL / (g · h)), and reacted at a reaction temperature of 750 ° C. and 3 atm. As apparent from FIGS. 6 and 7, the benzene production rate and the hydrogen production rate over time were almost the same as those when hydrogen sulfide was 0 ppm even when hydrogen sulfide was mixed up to 100 ppm. In view of the fact that the ammonia concentration in the biogas is usually about several ppm, when the aromatic compound and hydrogen are produced from the biogas as a raw material, the ammonia is completely removed without providing an ammonia removal step. It has been found that aromatic compounds and hydrogen can be produced to the same extent as in the case.

残存硫化水素濃度と、触媒再生及び硫化水素濃度低減に要するエネルギー及びコストとの関係を示す概念図である。It is a conceptual diagram which shows the relationship between residual hydrogen sulfide concentration, energy and cost which are required for catalyst regeneration and hydrogen sulfide concentration reduction. 二酸化炭素が1%存在するときの、ベンゼン生成速度に対する硫化水素濃度の影響を示した図である。It is the figure which showed the influence of the hydrogen sulfide density | concentration with respect to a benzene production | generation rate when carbon dioxide exists 1%. 二酸化炭素が1%存在するときの、水素生成速度に対する硫化水素濃度の影響を示した図である。It is the figure which showed the influence of the hydrogen sulfide density | concentration with respect to a hydrogen production rate when a carbon dioxide exists. 水素が6%存在するときの、ベンゼン生成速度に対する硫化水素濃度の影響を示した図である。It is the figure which showed the influence of the hydrogen sulfide density | concentration with respect to benzene production | generation speed | velocity when hydrogen exists 6%. 水素が6%存在するときの、水素生成速度に対する硫化水素濃度の影響を示した図である。It is the figure which showed the influence of the hydrogen sulfide density | concentration with respect to a hydrogen production | generation rate when hydrogen exists 6%. 二酸化炭素が1%存在するときの、ベンゼン生成速度に対するアンモニア濃度の影響を示した図である。It is the figure which showed the influence of ammonia concentration with respect to benzene production | generation speed | velocity when carbon dioxide exists 1%. 二酸化炭素が1%存在するときの、水素生成速度に対するアンモニア濃度の影響を示した図である。It is the figure which showed the influence of the ammonia concentration with respect to the hydrogen production | generation speed | velocity when carbon dioxide exists 1%.

Claims (3)

低級炭化水素及び硫化水素を含有するバイオガス中の硫化水素を、残存硫化水素濃度が所望の値となるように除去し、得られた硫化水素残存バイオガスを触媒の存在下で処理して芳香族化合物及び水素を製造する方法。   Hydrogen sulfide in the biogas containing lower hydrocarbons and hydrogen sulfide is removed so that the residual hydrogen sulfide concentration becomes a desired value, and the resulting hydrogen sulfide residual biogas is treated in the presence of a catalyst to produce an aroma. Group compounds and methods for producing hydrogen. 残存硫化水素濃度が1.25〜10ppmとなるようにバイオガス中の硫化水素を除去することを特徴とする請求項1に記載の方法。   The method according to claim 1, wherein hydrogen sulfide in the biogas is removed so that the residual hydrogen sulfide concentration is 1.25 to 10 ppm. 触媒が、モリブデンを担持させたメタロシリケートを還元性ガスにより炭化処理することにより得られたものであることを特徴とする請求項1又は2に記載の方法。   The method according to claim 1 or 2, wherein the catalyst is obtained by carbonizing a metallosilicate supporting molybdenum with a reducing gas.
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