JP2008277308A - Solid polymer electrolyte fuel cell power generating system and solid polymer electrolyte fuel cell power generating method - Google Patents

Solid polymer electrolyte fuel cell power generating system and solid polymer electrolyte fuel cell power generating method Download PDF

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JP2008277308A
JP2008277308A JP2008162851A JP2008162851A JP2008277308A JP 2008277308 A JP2008277308 A JP 2008277308A JP 2008162851 A JP2008162851 A JP 2008162851A JP 2008162851 A JP2008162851 A JP 2008162851A JP 2008277308 A JP2008277308 A JP 2008277308A
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Takeshi Tabata
健 田畑
Susumu Takami
晋 高見
Norihisa Kamiya
規寿 神家
Masataka Masuda
正孝 増田
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Osaka Gas Co Ltd
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Abstract

<P>PROBLEM TO BE SOLVED: To provide a small-sized, highly efficient and maintenance-free PEFC power generating system, realizing stable and highly-developed desulfurization with a small quantity of desulfurizing agent, which can afford a repeated start and stop with short starting time, and a PEFC (polymer electrolyte fuel cell) power generating method. <P>SOLUTION: The PEFC power generating system comprises the PEFC, and a fuel reforming system generating hydrogen-rich gas from raw fuel, of which, the fuel reforming system comprises at least a desulfurizer, a reforming reaction device, and a selective CO oxidizing reactor. The PEFC power generating system also comprises a vapor condensing and separating means condensing and separating vapor from at least a part of the reformed gas before being supplied to the selective CO oxidizing reactor, and a system of adding the gas with the vapor condensed, separated and removed by the vapor condensing and separating means to the raw fuel by recycling. A hydrogenation adsorptive desulfurizing agent, containing at least Cu, Zn and Ni or/and Fe, is used, as a desulfurizing agent of the desulfurizer. <P>COPYRIGHT: (C)2009,JPO&INPIT

Description

本発明は、固体高分子型燃料電池(PEFC:Polymer Electrolyte Fuel Cell)発電システム及びPEFC発電方法に関する。より詳細には、硫黄化合物を含有する原燃料を改質して燃料電池の燃料として供給する燃料改質システムを備えたPEFC発電システム及びPEFC発電方法に関する。   The present invention relates to a polymer electrolyte fuel cell (PEFC) power generation system and a PEFC power generation method. More specifically, the present invention relates to a PEFC power generation system and a PEFC power generation method including a fuel reforming system that reforms a raw fuel containing a sulfur compound and supplies it as fuel for a fuel cell.

炭化水素、アルコールなどを原燃料として用いるPEFC発電システムには、燃料改質システムが含まれている。燃料改質システムでは、原燃料から、燃料電池の燃料となる水素が多く含まれている水素リッチガスが製造される。原燃料から効率よく水素リッチガスを製造する方法として、触媒の存在下水蒸気と原燃料を反応させて改質ガスを得る水蒸気改質法が広く実用化され、燃料電池用の燃料改質システム、特に定置用燃料電池発電システムにおいて一般的に採用されている。水蒸気改質触媒は、硫黄被毒に弱いので、硫黄化合物を含む原燃料(例えば、都市ガス、LPG、ナフサなどの炭化水素系燃料など)を用いる場合には、原燃料は脱硫してから水蒸気改質に供される。   A PEFC power generation system that uses hydrocarbons, alcohol, or the like as a raw fuel includes a fuel reforming system. In a fuel reforming system, hydrogen-rich gas containing a large amount of hydrogen that is fuel for a fuel cell is produced from raw fuel. As a method for efficiently producing a hydrogen-rich gas from raw fuel, a steam reforming method in which reformed gas is obtained by reacting steam and raw fuel in the presence of a catalyst has been widely put into practical use. Generally used in stationary fuel cell power generation systems. Since steam reforming catalysts are vulnerable to sulfur poisoning, when using raw fuels containing sulfur compounds (for example, hydrocarbon fuels such as city gas, LPG, naphtha, etc.), the raw fuel must be desulfurized before steam. Used for reforming.

一方、PEFCの場合には、燃料となる水素リッチガス中にCOが高濃度に含まれていると電池の電極触媒が被毒されて発電性能が低下するので、水素リッチガス中のCO濃度は通常10ppm程度以下にする必要がある。   On the other hand, in the case of PEFC, if the concentration of CO in the hydrogen-rich gas used as fuel is high, the electrode catalyst of the battery is poisoned and the power generation performance decreases, so the CO concentration in the hydrogen-rich gas is usually 10 ppm. Must be less than or equal to

しかしながら、炭化水素、アルコールなどを水蒸気改質して得られる改質ガス中には、通常COが0.1%以上含まれているので、CO濃度を10ppm程度以下にするために、改質ガスに酸素(空気)を添加し、触媒の共存下COを選択的に酸化してCO2に変換するCO選択酸化プロセスが設けられる。 However, the reformed gas obtained by steam reforming hydrocarbons, alcohols, etc. usually contains 0.1% or more of CO. Therefore, in order to reduce the CO concentration to about 10 ppm or less, the reformed gas contains oxygen. (Air) is added, and a CO selective oxidation process is provided in which CO is selectively oxidized and converted to CO 2 in the presence of a catalyst.

即ち、一般的なPEFC発電システム用の燃料改質システムには、原燃料から硫黄化合物を除去する脱硫剤を充填した脱硫器と、脱硫された原燃料を水蒸気改質触媒の共存下水蒸気と反応させて改質ガスを生成する改質反応器と、改質ガスに含まれるCOをCO選択酸化触媒の共存下空気中の酸素で選択的に酸化してCO2に変換するCO選択酸化反応器とが含まれている。 That is, a general fuel reforming system for a PEFC power generation system includes a desulfurizer filled with a desulfurizing agent that removes sulfur compounds from raw fuel, and the desulfurized raw fuel reacts with steam in the presence of a steam reforming catalyst. Reforming reactor that generates reformed gas and CO selective oxidation reactor that selectively oxidizes CO contained in reformed gas with oxygen in the air in the presence of a CO selective oxidation catalyst and converts it to CO 2 And are included.

また、炭化水素のように低温で改質すると平衡などの制約から効率が低下する原燃料を用いる場合には、改質ガス中のCO濃度を0.1〜1%程度まで低減するために、一般に、改質ガス中のCOを触媒の共存下水蒸気と反応させてCO2に変換するCO変成器がCO選択酸化反応器に先立って設けられる。 In addition, when using raw fuel that reduces efficiency due to constraints such as equilibrium when reformed at low temperatures such as hydrocarbons, in order to reduce the CO concentration in the reformed gas to about 0.1 to 1%, in general, A CO converter that converts CO in the reformed gas into CO 2 by reacting with steam in the presence of a catalyst is provided prior to the CO selective oxidation reactor.

この様なPEFC発電システムにおける燃料改質システムでは、プロセスガスの流れは一方向で、改質ガスが原燃料に混合される事はない。   In such a fuel reforming system in the PEFC power generation system, the flow of the process gas is unidirectional, and the reformed gas is not mixed with the raw fuel.

また、脱硫器においては、吸着式脱硫剤が用いられ、常温で吸着脱硫を行う常温脱硫剤がしばしば用いられる。   In the desulfurizer, an adsorptive desulfurizing agent is used, and an ordinary temperature desulfurizing agent that performs adsorptive desulfurization at ordinary temperature is often used.

しかし、常温脱硫剤では、硫黄化合物のキャッチアップ量が少ないだけでなく、吸着の選択性が高くないので、硫黄化合物だけでなく炭化水素を幾分吸着する。このため、原燃料の組成や温度の変化によって硫黄のキャッチアップ量が変化する。更に、吸着していた炭化水素が運転条件の変化で脱着して改質反応器に高濃度で到達するために、改質触媒上でのカーボン析出を引き起こすという問題があった。   However, the room temperature desulfurization agent not only has a small catch amount of sulfur compounds, but also does not have a high adsorption selectivity, and therefore adsorbs some hydrocarbons as well as sulfur compounds. For this reason, the amount of sulfur catch-up varies depending on the composition and temperature of the raw fuel. Furthermore, since the adsorbed hydrocarbons are desorbed due to changes in operating conditions and reach the reforming reactor at a high concentration, there is a problem of causing carbon deposition on the reforming catalyst.

これらの問題点を解決できる脱硫剤として、特開平1-123627号公報及び特開平1-123628号公報には、銅−亜鉛系脱硫剤及び銅−亜鉛−アルミニウム系脱硫剤が開示されている。これらの脱硫剤を用いる場合には、原燃料中の硫黄を安定して1ppb以下に脱硫できる。   As a desulfurizing agent that can solve these problems, Japanese Patent Laid-Open Nos. 1-123627 and 1-123628 disclose copper-zinc-based desulfurizing agents and copper-zinc-aluminum-based desulfurizing agents. When these desulfurization agents are used, sulfur in the raw fuel can be stably desulfurized to 1 ppb or less.

しかしながら、これらの脱硫剤を使用する場合でも、高度の脱硫レベルを維持する場合には、脱硫剤の使用量を多くしなければならない。   However, even when these desulfurizing agents are used, the amount of the desulfurizing agent must be increased in order to maintain a high desulfurization level.

一方、一般に、脱硫剤の使用量を減らして安定した脱硫を行うには、水添脱硫プロセスが採用されている。水添脱硫は、硫化したNi-MoやCo-Mo系触媒を用い、水素の共存下250〜350℃で、有機硫黄を硫化水素に変換し、該硫化水素を吸着脱硫剤であるZnOと反応させ、ZnSとして脱硫する。水添用の水素源としては、通常、改質して得られる水素をリサイクルして原燃料に混合して用いる。   On the other hand, in general, a hydrodesulfurization process is employed in order to perform stable desulfurization by reducing the amount of desulfurizing agent used. Hydrodesulfurization uses sulfurized Ni-Mo and Co-Mo-based catalysts, converts organic sulfur to hydrogen sulfide in the presence of hydrogen in the presence of hydrogen at 250 to 350 ° C, and reacts this hydrogen sulfide with ZnO, an adsorptive desulfurization agent And desulfurized as ZnS. As a hydrogen source for hydrogenation, hydrogen obtained by reforming is usually recycled and mixed with raw fuel.

しかし、この方法では、脱硫レベルは通常0.1ppm程度で、微量の硫黄は改質プロセスにスリップしてしまうため、硫黄被毒により改質触媒の寿命が短縮すると共に、水蒸気改質プロセスでのS/C(水蒸気/原燃料中の炭素モル比)を低くした経済的な運転ができない。   However, in this method, the desulfurization level is usually about 0.1 ppm, and a small amount of sulfur slips into the reforming process. Therefore, sulfur poisoning shortens the life of the reforming catalyst, and S in the steam reforming process. Economical operation with low / C (steam / carbon ratio in raw fuel) is not possible.

また、250℃以上にならないと原燃料の投入ができないため、起動に時間がかかり、燃料電池などの用途には不向きである。実際に、かかる水添脱硫プロセスを採用しているオンサイトリン酸型燃料電池では、起動操作をしてから発電するまでに約3時間を要している。   Moreover, since raw fuel cannot be input unless the temperature exceeds 250 ° C., it takes a long time to start, and is not suitable for applications such as fuel cells. Actually, in an on-site phosphoric acid fuel cell employing such a hydrodesulfurization process, it takes about 3 hours from starting operation to generating power.

さらに、起動時には、水添用の水素がないため、触媒被毒を避けるためには水素を別途準備しておく必要があるが、家庭用など小型の発電システムとして応用が期待されているPEFCでは、水素を準備しておくことはコストやメンテナンス性などから考えがたい。また、家庭用途では起動停止が頻繁に行われるので、起動時の水添用水素の添加の省略は、直ちに改質触媒の劣化につながる。   Furthermore, since there is no hydrogen for hydrogenation at startup, it is necessary to prepare hydrogen separately to avoid catalyst poisoning, but PEFC is expected to be applied as a small power generation system for home use. Preparation of hydrogen is difficult to consider because of cost and maintainability. In addition, since start-up and stop-off are frequently performed for household use, omission of hydrogenation for hydrogenation during start-up immediately leads to deterioration of the reforming catalyst.

一方、水素のリサイクルについても、大型の水素製造プラントでは、製品の水素をリサイクルして原燃料に添加するが、燃料電池発電システムに含まれる燃料改質システムなどでは、水素を精製しないので、改質ガスやアノードオフガスをリサイクルしている。200kWクラスのリン酸型燃料電池発電システムにおいては、リサイクルガスの流量も多く、電池の作動温度が180〜200℃程度と高いので、リサイクルガス中に水蒸気が凝縮することはないが、1〜数kWクラスの小型のPEFC発電システムの場合、電池の作動温度が80℃程度以下と低く、流量も極端に少なくなるので、リサイクルガスに含まれる水分がリサイクルライン中で凝縮して閉塞の問題をもたらす場合がある。   On the other hand, with regard to hydrogen recycling, large-scale hydrogen production plants recycle product hydrogen and add it to raw fuel. However, the fuel reforming system included in the fuel cell power generation system does not purify hydrogen, so it is improved. Quality gas and anode off-gas are recycled. In the 200kW class phosphoric acid fuel cell power generation system, the flow rate of the recycle gas is large and the battery operating temperature is as high as about 180-200 ° C, so that water vapor does not condense in the recycle gas. In the case of a small kW class PEFC power generation system, the operating temperature of the battery is as low as about 80 ° C or less, and the flow rate is extremely low, so the moisture contained in the recycle gas condenses in the recycle line, causing a blockage problem. There is a case.

さらに、PEFC発電システムの場合、CO選択酸化反応器で空気を添加するので、窒素が改質反応器に供給され、PEFCに悪影響を与えるアンモニアが生成してしまうという問題点があり、改質ガスやアノードオフガスをリサイクルすることができなかった。   Furthermore, in the case of a PEFC power generation system, since air is added in a CO selective oxidation reactor, there is a problem that nitrogen is supplied to the reforming reactor and ammonia that adversely affects PEFC is generated. And anode off-gas could not be recycled.

本発明は、特に小型のPEFCシステムに適用する際に問題となる改質ガスのリサイクルや、起動時の脱硫性能の確保を可能とすることにより、少量の脱硫剤で安定した高度な脱硫を実現し、小型で高効率、メンテナンスフリーでなおかつ、起動時間が短く起動停止頻度を多くできるPEFC発電システムおよびPEFC発電方法を提供することを目的とする。   The present invention realizes stable advanced desulfurization with a small amount of desulfurization agent by enabling the recycling of reformed gas, which is a problem especially when applied to small PEFC systems, and ensuring desulfurization performance at startup. Another object of the present invention is to provide a PEFC power generation system and a PEFC power generation method that are small in size, highly efficient, maintenance-free, and capable of increasing the frequency of start and stop with a short start time.

本発明者は、上記問題点に鑑み鋭意研究を重ねた結果、改質ガスのリサイクルの問題については、リサイクルガスをCO選択酸化反応器の上流側から分岐し、当該ガスから水分を凝縮分離することにより、アンモニアを生成せず、リサイクルライン内での水分の凝縮によるトラブルを発生させず、小型でも安定した運転が可能となることを見出した。   As a result of intensive studies in view of the above problems, the present inventors branch the recycle gas from the upstream side of the CO selective oxidation reactor to condense and separate moisture from the gas. As a result, it has been found that stable operation is possible even with a small size without generating ammonia and without causing trouble due to moisture condensation in the recycle line.

また、特定の水添吸着脱硫剤を用いた場合には、水添活性を有すると共に、水素が共存しない条件下でも、長期間連続でなければ吸着脱硫作用により原燃料中の有機硫黄化合物を1ppb以下のレベルまで除去できることを見いだした。   In addition, when a specific hydrogenated adsorptive desulfurization agent is used, it has hydrogenation activity, and even under conditions in which hydrogen does not coexist, if it is not continuous for a long period of time, 1 ppb of organic sulfur compounds in the raw fuel can be obtained by adsorptive desulfurization. We found that it can be removed to the following levels.

更に、短時間であれば、常温でも、硫黄化合物を吸着でき、原燃料中の硫黄化合物を1ppb以下のレベルまで除去でき、吸着された硫黄化合物は、好ましい運転温度である250℃程度まで脱硫剤が加熱された後には分解され、硫黄はバルクに吸収されるため、起動時に脱硫剤が十分に昇温していない状態で原燃料を投入しても、改質プロセスに触媒がスリップすることはないことも見いだした。   Furthermore, sulfur compounds can be adsorbed even at room temperature for a short time, and sulfur compounds in raw fuel can be removed to a level of 1 ppb or less, and the adsorbed sulfur compounds are desulfurizing agents up to about 250 ° C. which is a preferred operating temperature. After being heated, it is decomposed and sulfur is absorbed into the bulk. Therefore, even if the raw fuel is added when the desulfurizing agent is not sufficiently heated during startup, the catalyst will not slip into the reforming process. I found nothing.

即ち、本発明は、以下の固体高分子型燃料電池発電システムおよび固体高分子型燃料電子発電方法に係る。
1.原燃料を改質して水素リッチガスを生成する燃料改質システムと、水素リッチガスと酸素を固体高分子電解質を介して電気化学的に反応させて電気を発生する燃料電池とを少なくとも含む固体高分子型燃料電池発電システムであって、上記燃料改質システムが、原燃料から硫黄化合物を除去する脱硫剤を充填した脱硫器と、脱硫された原燃料を水蒸気改質触媒の共存下、水蒸気と反応させて改質ガスを生成する改質反応器と、改質ガスに含まれるCOをCO選択酸化触媒の共存下空気中の酸素で選択的に酸化してCO2に変換するCO選択酸化反応器とを少なくとも含む燃料改質システムであり、上記CO選択酸化反応器に供される前の改質ガスの少なくとも一部のガスから水蒸気を凝縮分離する水蒸気凝縮分離手段と、前記水蒸気凝縮分離手段により水蒸気が凝縮分離除去されたガスをリサイクルして原燃料に添加するシステムが設けられ、
上記脱硫器の脱硫剤として、CuとZnとNiまたは/及びFeとを少なくとも含有する水添吸着脱硫剤を用いて脱硫することを特徴とする固体高分子型燃料電池発電システム。
2.燃料改質システムが、改質反応器とCO選択酸化反応器の間に、改質ガス中のCOの大部分をCO変成触媒の共存下水蒸気と反応させてCO2に変換するCO変成器が設置されている上記1記載の固体高分子型燃料電池発電システム。
3.燃料改質システムが、気体状の原燃料を圧縮して供給する原燃料圧縮器を脱硫器よりも上流に備えており、CO選択酸化反応器に供される前の改質ガスの一部が、水蒸気を凝縮分離された後に原燃料圧縮器の吸入側に供給されることにより、原燃料に添加される手段が設けられている上記1または2記載の固体高分子型燃料電池発電システム。
4.水添吸着脱硫剤が、共沈法で得られたCu及びZnの酸化物を少なくとも含む混合物にNi及び/またはFeを含浸担持した組成物を水素還元して得られる水添吸着脱硫剤である上記1乃至3記載の固体高分子型燃料電池発電システム。
5.改質ガス中の水蒸気を凝縮分離する手段が、CO選択酸化反応器に供する直前に設けられ、全ての改質ガスが水蒸気凝縮分離手段に供され、水蒸気分離後であって、CO選択酸化用の空気を添加する前の改質ガスの一部をリサイクルして原燃料に添加する手段が設けられている上記1乃至4記載の固体高分子型燃料電池発電システム。
6.原燃料を改質して水素リッチガスを生成する燃料改質プロセスと、水素リッチガスと酸素を固体高分子電解質を介して電気化学的に反応させて電気を発生する燃料電池とを少なくとも含む固体高分子型燃料電池発電方法であって、原燃料から硫黄化合物を脱硫剤により除去する脱硫プロセスと、脱硫された原燃料を水蒸気改質触媒の共存下水蒸気と反応させて改質ガスを生成する改質プロセスと、改質ガスに含まれるCOをCO選択酸化触媒の共存下空気中の酸素で選択的に酸化してCO2に変換するCO選択酸化プロセスを少なくとも含む燃料改質プロセスにおいて、通常運転時、CO選択酸化プロセスに供される前の改質ガスの少なくとも一部のガスを水蒸気凝縮分離プロセスにより水蒸気を凝縮分離させ、前記水蒸気凝縮分離プロセスにより水蒸気を凝縮分離除去したガスをリサイクルして原燃料に添加し、上記脱硫プロセスにおいて、CuとZnとNiおよび/またはFeとを少なくとも含有する水添吸着脱硫剤を用いて脱硫することを特徴とする固体高分子型燃料電池発電方法。
7.燃料改質プロセスが、改質プロセスを出た改質ガス中のCOの大部分をCO変成触媒の共存下、水蒸気と反応させてCO2に変換するCO変成プロセスに供した後、通常運転時、CO選択酸化プロセスに供する前の改質ガスの少なくとも一部を水蒸気凝縮分離プロセスに供する燃料改質プロセスである上記6記載の固体高分子型燃料電池発電方法。
8.水添吸着脱硫剤が、共沈法で得られたCu及びZnの酸化物を少なくとも含む混合物にNi及び/またはFeを含浸担持した組成物を水素還元して得られる水添吸着脱硫剤である上記6または7記載の固体高分子型燃料電池発電方法。
9.原燃料が、炭素数4以下のアルカンを主成分とする気体状炭化水素である上記6乃至8記載の固体高分子型燃料電池発電方法。
10.水蒸気改質プロセスにおけるS/C(水蒸気/原燃料中の炭素モル比)が、2乃至3である上記9記載の固体高分子型燃料電池発電方法。
11.原燃料ガス流量に対するリサイクルに用いるガスの流量の体積比が、0.001乃至0.05である上記9または10記載の固体高分子型燃料電池発電方法。
12.起動時など改質ガスをリサイクルできない場合に、一時的に改質ガスのリサイクルを休止して脱硫プロセスを行い、その後、リサイクルを開始する上記6乃至10記載の固体高分子型燃料電池発電方法。
That is, the present invention relates to the following polymer electrolyte fuel cell power generation system and polymer electrolyte fuel electronic power generation method.
1. A solid polymer comprising at least a fuel reforming system that reforms raw fuel to generate a hydrogen-rich gas, and a fuel cell that generates electricity by electrochemically reacting the hydrogen-rich gas and oxygen via a solid polymer electrolyte Type fuel cell power generation system, wherein the fuel reforming system reacts with steam in the presence of a desulfurizer filled with a desulfurizing agent that removes sulfur compounds from the raw fuel and a steam reforming catalyst. Reforming reactor that generates reformed gas and CO selective oxidation reactor that selectively oxidizes CO contained in reformed gas with oxygen in the air in the presence of a CO selective oxidation catalyst and converts it to CO 2 A water vapor condensing / separating means for condensing and separating water vapor from at least a part of the reformed gas before being supplied to the CO selective oxidation reactor, and the water vapor condensing / separating means. Steamed There the system is provided to add by recycling condensed separated and removed gas to a raw fuel,
A solid polymer fuel cell power generation system characterized in that desulfurization is performed using a hydrogenated adsorption desulfurization agent containing at least Cu, Zn, Ni, and / or Fe as a desulfurization agent of the desulfurizer.
2. A CO reformer, in which the fuel reforming system, converts between the reforming reactor and the CO selective oxidation reactor to CO 2 by reacting most of the CO in the reformed gas with steam in the presence of the CO shift catalyst 2. The polymer electrolyte fuel cell power generation system according to 1 above, which is installed.
3. The fuel reforming system includes a raw fuel compressor that compresses and supplies gaseous raw fuel upstream of the desulfurizer, and a part of the reformed gas before being supplied to the CO selective oxidation reactor is provided. 3. The polymer electrolyte fuel cell power generation system according to the above 1 or 2, wherein means for adding to the raw fuel is provided by supplying water vapor to the suction side of the raw fuel compressor after being condensed and separated.
4). The hydrogenated adsorptive desulfurizing agent is a hydrogenated adsorptive desulfurizing agent obtained by hydrogen reduction of a composition obtained by impregnating and supporting Ni and / or Fe in a mixture containing at least Cu and Zn oxides obtained by a coprecipitation method. 4. The polymer electrolyte fuel cell power generation system as described in 1 to 3 above.
5. A means for condensing and separating water vapor in the reformed gas is provided immediately before being supplied to the CO selective oxidation reactor, and all the reformed gas is supplied to the water vapor condensing and separating means, and after steam separation, for CO selective oxidation. 5. The polymer electrolyte fuel cell power generation system according to any one of 1 to 4, wherein means for recycling a part of the reformed gas before adding the air is added to the raw fuel.
6). A solid polymer comprising at least a fuel reforming process for reforming raw fuel to generate a hydrogen-rich gas, and a fuel cell that generates electricity by electrochemically reacting the hydrogen-rich gas and oxygen via a solid polymer electrolyte Type fuel cell power generation method, a desulfurization process in which sulfur compounds are removed from raw fuel with a desulfurization agent, and reforming in which desulfurized raw fuel is reacted with steam in the presence of a steam reforming catalyst to generate reformed gas During normal operation in a fuel reforming process including at least a CO selective oxidation process that selectively oxidizes CO contained in reformed gas with oxygen in the air in the presence of a CO selective oxidation catalyst and converts it to CO 2 , At least a part of the reformed gas before being subjected to the CO selective oxidation process is condensed and separated by a steam condensation separation process, and the steam is separated by the steam condensation separation process. Recycled gas that has been condensed and removed, added to the raw fuel, and in the above desulfurization process, desulfurization using a hydrogenated desulfurization agent containing at least Cu, Zn, Ni and / or Fe Polymer fuel cell power generation method.
7). After the fuel reforming process, the presence of most of the CO shift catalyst in CO in the reformed gas leaving the reforming process, and subjected to CO conversion process of converting the CO 2 is reacted with steam, during normal operation 7. The polymer electrolyte fuel cell power generation method according to 6 above, which is a fuel reforming process in which at least a part of the reformed gas before being subjected to the CO selective oxidation process is subjected to a steam condensation separation process.
8). The hydrogenated adsorptive desulfurizing agent is a hydrogenated adsorptive desulfurizing agent obtained by hydrogen reduction of a composition obtained by impregnating and supporting Ni and / or Fe in a mixture containing at least Cu and Zn oxides obtained by a coprecipitation method. 8. The polymer electrolyte fuel cell power generation method according to 6 or 7 above.
9. 9. The polymer electrolyte fuel cell power generation method according to 6 to 8, wherein the raw fuel is a gaseous hydrocarbon mainly composed of alkane having 4 or less carbon atoms.
10. 10. The polymer electrolyte fuel cell power generation method according to 9 above, wherein S / C (steam / carbon molar ratio in raw fuel) in the steam reforming process is 2 to 3.
11. 11. The polymer electrolyte fuel cell power generation method according to 9 or 10 above, wherein the volume ratio of the flow rate of the gas used for recycling to the raw fuel gas flow rate is 0.001 to 0.05.
12 11. The polymer electrolyte fuel cell power generation method according to any one of 6 to 10 above, wherein when the reformed gas cannot be recycled, such as at the time of start-up, the reformed gas is temporarily suspended and the desulfurization process is performed, and then the recycling is started.

本発明によれば、小型のPEFCシステムに適用する際に問題となる改質ガスのリサイクル時の水の凝縮によるトラブルやアンモニア生成を避けられる。本発明は、特に5kW程度以下(より好ましくは0.5〜2kW程度)の小型のPEFCを含む固体高分子型燃料電池発電システムに対して、好適に用いることができる。   According to the present invention, troubles due to water condensation and ammonia generation during recycling of reformed gas, which are problems when applied to a small PEFC system, can be avoided. The present invention can be suitably used particularly for a polymer electrolyte fuel cell power generation system including a small PEFC of about 5 kW or less (more preferably about 0.5 to 2 kW).

本発明では、定常時だけでなく水添用水素が供給されない起動時でも脱硫性能を確保できる。その結果、少量しか脱硫剤を用いていない場合であっても、安定した高度な脱硫を実現することができる。   In the present invention, the desulfurization performance can be ensured not only at the steady state but also at the start-up when the hydrogenation hydrogen is not supplied. As a result, even when only a small amount of the desulfurizing agent is used, stable and high-quality desulfurization can be realized.

本発明によると、小型で高効率、メンテナンスフリーでなおかつ、起動時間が短く起動停止頻度を多くできるPEFC発電システムを得ることができる。   According to the present invention, it is possible to obtain a PEFC power generation system that is small, highly efficient, maintenance-free, and has a short start-up time and a high start-stop frequency.

本発明によるPEFC発電システムには、原燃料を改質して水素リッチガスを生成する燃料改質システムと、水素リッチガスと酸素を固体高分子電解質を介して電気化学的に反応させて電気を発生する燃料電池とが少なくとも含まれる。   The PEFC power generation system according to the present invention includes a fuel reforming system that reforms raw fuel to generate a hydrogen-rich gas, and generates electricity by electrochemically reacting the hydrogen-rich gas and oxygen via a solid polymer electrolyte. And at least a fuel cell.

本発明で用いる燃料電池は、水素リッチガスと酸素または空気中の酸素を固体高分子電解質を介して電気化学的に反応させて電気を発生する燃料電池であるかぎり特に制約はない。また、本発明によるPEFC発電方法についても、燃料電池の運転方法については特に制約はない。本発明の効果が大きくなるのは、燃料電池を約100℃以下で動作させるいわゆるPEFCを用いる場合である。   The fuel cell used in the present invention is not particularly limited as long as it is a fuel cell that generates electricity by electrochemically reacting a hydrogen-rich gas and oxygen or oxygen in the air via a solid polymer electrolyte. Also, the PEFC power generation method according to the present invention is not particularly limited with respect to the fuel cell operation method. The effect of the present invention is enhanced when a so-called PEFC that operates the fuel cell at about 100 ° C. or less is used.

本発明で用いる燃料改質システムは、図1に例示するように、原燃料6から硫黄化合物を除去する脱硫剤を充填した脱硫器1と、脱硫された原燃料を水蒸気改質触媒の共存下水蒸気7と反応させて改質ガスを生成する改質反応器2と、改質ガスに含まれるCOをCO選択酸化触媒の共存下空気8中の酸素で選択的に酸化してCO2に変換するCO選択酸化反応器3とを少なくとも含み、上流側から脱硫器、改質反応器、CO選択酸化反応器の順に位置し、CO選択酸化反応器に供される前の改質ガスの少なくとも一部を、該改質ガス中に含まれる水蒸気を凝縮分離したのちリサイクルして原燃料に添加する手段が設けられている。 As illustrated in FIG. 1, the fuel reforming system used in the present invention includes a desulfurizer 1 filled with a desulfurizing agent that removes sulfur compounds from raw fuel 6 and the desulfurized raw fuel in the presence of a steam reforming catalyst. Reforming reactor 2 that reacts with water vapor 7 to generate reformed gas, and CO contained in the reformed gas is selectively oxidized with oxygen in air 8 in the presence of a CO selective oxidation catalyst and converted to CO 2 . At least one of the reformed gases before being supplied to the CO selective oxidation reactor, which is positioned in the order of the desulfurizer, the reforming reactor, and the CO selective oxidation reactor from the upstream side. There is provided means for condensing and separating the water vapor contained in the reformed gas and recycling it to the raw fuel.

以下、水蒸気を凝縮分離した後の改質ガスの一部であって、原燃料に添加されるガスをリサイクルガスという。また、リサイクルガスが流れるラインをリサイクルラインという。   Hereinafter, a part of the reformed gas after the water vapor is condensed and separated, and the gas added to the raw fuel is referred to as a recycle gas. A line through which recycled gas flows is called a recycling line.

CO選択酸化反応器を出た水素リッチガスは、PEFCに燃料として供給されるが、必要に応じて、水素リッチガスの流路途中に、遮断弁、逆止弁、流量調整弁、パージ用分岐ライン、加湿装置などを備えていても良い。   The hydrogen-rich gas exiting the CO selective oxidation reactor is supplied to the PEFC as fuel, but if necessary, a shut-off valve, check valve, flow control valve, purge branch line, A humidifier or the like may be provided.

CO選択酸化反応器に入る改質ガス中のCO濃度を低減するために、図2のように改質反応器2とCO選択酸化反応器3の間に、改質ガス中のCOの大部分をCO変成触媒の共存下水蒸気と反応させてCO2に変換するCO変成器11が設置されていてもよい。この場合、リサイクルライン5は、CO変成器11とCO選択酸化器3の間のガスを分岐する構造とすればよい。この時、CO選択酸化用空気を改質ガスに添加する前に、改質ガスをリサイクルラインとCO選択酸化反応器へのラインとに分岐する必要がある。 In order to reduce the CO concentration in the reformed gas entering the CO selective oxidation reactor, most of the CO in the reformed gas is placed between the reformer reactor 2 and the CO selective oxidation reactor 3 as shown in FIG. A CO converter 11 may be installed which reacts with water vapor in the presence of a CO conversion catalyst to convert to CO 2 . In this case, the recycle line 5 may be structured to branch the gas between the CO converter 11 and the CO selective oxidizer 3. At this time, before adding the CO selective oxidation air to the reformed gas, it is necessary to branch the reformed gas into a recycle line and a line to the CO selective oxidation reactor.

本発明に用いる脱硫器には、CuとZnとNiおよび/またはFeとを少なくとも含有する水添吸着脱硫剤が充填され、原燃料とCO選択酸化反応器に供される前の改質ガスの一部から改質ガス中に含まれる水蒸気を凝縮分離したリサイクルガスとの混合ガスが供給される構造となっている。   The desulfurizer used in the present invention is filled with a hydrogenated desulfurization agent containing at least Cu, Zn, Ni and / or Fe, and the reformed gas before being supplied to the raw fuel and the CO selective oxidation reactor. A mixed gas with a recycle gas obtained by condensing and separating water vapor contained in the reformed gas from a part is supplied.

脱硫器に供給する原燃料の圧力が不足する場合には、図3に示すように、原燃料を昇圧するための原燃料圧縮器12を脱硫器よりも上流に設置してもよい。また、リサイクルガスを原燃料圧縮器の吸入側に供給する構造としてもよく、この場合には、リサイクルガスを原燃料に混合するためのリサイクルガスブロアーを省略できる可能性があるという利点がある。   When the pressure of the raw fuel supplied to the desulfurizer is insufficient, a raw fuel compressor 12 for boosting the raw fuel may be installed upstream of the desulfurizer as shown in FIG. Further, a structure may be adopted in which the recycle gas is supplied to the intake side of the raw fuel compressor. In this case, there is an advantage that a recycle gas blower for mixing the recycle gas with the raw fuel may be omitted.

本発明に用いる改質反応器は、通常用いられる水蒸気改質反応器でよく、Ni系、Ru系などの水蒸気改質触媒が充填され、通常、水蒸気7を供給する手段と、反応に必要な熱を供給する手段が備えられている。また、水を蒸発させて改質用の水蒸気を発生させる水蒸気発生器を備えていてもよい。   The reforming reactor used in the present invention may be a commonly used steam reforming reactor, which is filled with a steam reforming catalyst such as Ni-based or Ru-based, and usually has a means for supplying steam 7 and is necessary for the reaction. Means for supplying heat are provided. Moreover, you may provide the water vapor generator which evaporates water and generate | occur | produces the water vapor | steam for reforming.

本発明に用いるCO選択酸化反応器は、通常用いられるCO選択酸化反応器でよく、Pt系、Ru系などのCO選択酸化触媒が充填され、通常空気8を供給する手段が備えられている。ただし、本発明においては、リサイクルラインは、空気を混合する前の改質ガスから分岐させる必要がある。   The CO selective oxidation reactor used in the present invention may be a commonly used CO selective oxidation reactor, which is filled with a CO selective oxidation catalyst such as Pt-based or Ru-based, and is provided with means for supplying normal air 8. However, in the present invention, the recycle line must be branched from the reformed gas before the air is mixed.

本発明で用いる改質ガスから水蒸気を凝縮分離する手段としては、その手段よりも後流側のラインで水蒸気が凝縮しないようにできれば、その構造等に特に制限はない。例えば、水冷式の凝縮器と気液分離器を組み合わせ、ドレインが抜き出されるものを例示できる。   As a means for condensing and separating water vapor from the reformed gas used in the present invention, there is no particular limitation on the structure or the like as long as the water vapor is not condensed in the line on the downstream side of the means. For example, a water-cooled condenser and a gas-liquid separator can be combined and the drain can be extracted.

また、当該水蒸気を凝縮分離する手段は、図1乃至3に示すようにリサイクルライン上に取り付けてもよく、図4に示すように、改質ガスの全量を通過させて水蒸気を凝縮分離できるように取り付けてもよい。後者の場合には、水蒸気を凝縮分離した後、CO選択酸化反応器において空気を添加する前にリサイクルラインを分岐してもよい。この場合、CO選択酸化反応器に入る改質ガスは、水蒸気が分離されているので、CO選択酸化反応器の運転温度範囲が広がるとともに、低温での運転が可能になる。したがって、PEFC発電システムの燃料改質システムの運転で問題となるCO選択酸化反応器の制御性や安定性が向上するというメリットがある。図4の様なフローとした上で、必要があれば、さらにリサイクルライン上に水蒸気を凝縮分離する手段を設けてもよい。   Further, the means for condensing and separating the water vapor may be mounted on the recycle line as shown in FIGS. 1 to 3, and as shown in FIG. 4, the water can be condensed and separated by allowing the entire reformed gas to pass therethrough. You may attach to. In the latter case, after the water vapor is condensed and separated, the recycle line may be branched before adding air in the CO selective oxidation reactor. In this case, since the reformed gas entering the CO selective oxidation reactor is separated from water vapor, the operating temperature range of the CO selective oxidation reactor is widened and operation at a low temperature is possible. Therefore, there is an advantage that the controllability and stability of the CO selective oxidation reactor, which is a problem in the operation of the fuel reforming system of the PEFC power generation system, is improved. In the flow shown in FIG. 4, if necessary, means for condensing and separating water vapor may be further provided on the recycle line.

本発明で用いるリサイクルラインには、図示していないが、必要に応じて、遮断弁、調節弁、逆止弁、ブロアー、定量ポンプなどを設置してもよい。但し、本発明による水添吸着脱硫剤を用いる場合には、必ずしもリサイクルガス量を原燃料の流量に合わせて厳密に制御する必要はない。また、ゲージ圧2kPa程度の日本の低圧の都市ガスを原燃料として、原燃料圧縮器を用いて原燃料を圧縮し、原燃料圧縮器の吸入側にリサイクルガスを添加するシステムにおいては、CO選択酸化反応器以降のプロセスガスの背圧が、通常、2kPaよりは遙かに大きいので、リサイクルライン上に逆止弁を設けなくとも、逆流することはない。   Although not shown in the figure, the recycle line used in the present invention may be provided with a shut-off valve, a control valve, a check valve, a blower, a metering pump, etc., if necessary. However, when the hydrogenated adsorptive desulfurization agent according to the present invention is used, it is not always necessary to strictly control the amount of the recycle gas according to the flow rate of the raw fuel. In addition, CO is selected for a system that uses low-pressure city gas in Japan with a gauge pressure of about 2 kPa as raw fuel, compresses raw fuel using a raw fuel compressor, and adds recycle gas to the intake side of the raw fuel compressor. Since the back pressure of the process gas after the oxidation reactor is usually much higher than 2 kPa, there is no back flow even if a check valve is not provided on the recycle line.

本発明において用いるCuとZnとNiおよび/またはFeとを少なくとも含有する水添吸着脱硫剤は、特に制限はないが、幅広い条件で使用可能とするためには、共沈法で得られたCu及びZnの酸化物にNiおよび/またはFeを含浸担持した組成物を水素還元して得られる水添吸着脱硫剤であることが望ましい。   The hydrogenated desulfurization agent containing at least Cu, Zn, Ni and / or Fe used in the present invention is not particularly limited, but in order to be usable under a wide range of conditions, Cu obtained by a coprecipitation method is used. Further, it is desirable to be a hydrogenated adsorptive desulfurization agent obtained by hydrogen reduction of a composition obtained by impregnating and supporting Ni and / or Fe on an oxide of Zn.

かかる水添吸着脱硫剤は、共沈法で得られたCu及びZnの酸化物にNi及び/またはFeを含浸担持した組成物を水素還元して得られる限り、特に制限はないが、例えば、以下のような製造法で製造できる。   The hydrogenated adsorptive desulfurization agent is not particularly limited as long as it is obtained by hydrogen reduction of a composition obtained by impregnating and supporting Ni and / or Fe on Cu and Zn oxides obtained by a coprecipitation method. It can be manufactured by the following manufacturing method.

まず、硝酸銅、酢酸銅などの水溶性銅化合物、および硝酸亜鉛、酢酸亜鉛などの水溶性亜鉛化合物を溶解する水溶液と、炭酸ナトリウムなどのアルカリ性水溶液とを混合・攪拌して沈殿を生じさせる。生成した沈殿を水洗、ろ過し、乾燥したのち、空気などの酸化雰囲気下、270〜400℃程度において焼成し、さらに水を加えてスラリーとした後、ろ別、成形、乾燥して酸化銅−酸化亜鉛の混合成形体を得る。なお、共沈時にAlを含有せしめ、酸化銅−酸化亜鉛−酸化アルミニウムの混合成形体とすることにより、耐熱性を向上させてもよい。   First, an aqueous solution that dissolves a water-soluble copper compound such as copper nitrate and copper acetate, and a water-soluble zinc compound such as zinc nitrate and zinc acetate, and an alkaline aqueous solution such as sodium carbonate are mixed and stirred to cause precipitation. The produced precipitate is washed with water, filtered and dried, then calcined in an oxidizing atmosphere such as air at about 270 to 400 ° C., further added with water to form a slurry, filtered, molded and dried to obtain copper oxide- A mixed molded body of zinc oxide is obtained. In addition, you may improve heat resistance by containing Al at the time of coprecipitation, and setting it as the mixed molded object of a copper oxide-zinc oxide-aluminum oxide.

該酸化銅−酸化亜鉛の混合成形体中の銅と亜鉛の比は特に限定されるものではないが、原子比で1:0.3〜10程度、好ましくは1:0.5〜3程度、より好ましくは1:1〜2.3程度となるようにする。混合成形体の寸法等は特に制限されないが、小さすぎるとプロセスの圧損が大きくなり、大きすぎると硫黄のキャッチアップ量が減るおそれがあるので、通常2〜6mm程度の大きさが好ましい。   The ratio of copper and zinc in the copper oxide-zinc oxide mixed molded body is not particularly limited, but the atomic ratio is about 1: 0.3 to 10, preferably about 1: 0.5 to 3, more preferably 1 : 1 to 2.3. The size of the mixed molded body is not particularly limited, but if it is too small, the pressure loss of the process becomes large, and if it is too large, the amount of sulfur catch-up may be reduced. Therefore, a size of about 2 to 6 mm is usually preferable.

次いで、上記のようにして得られた酸化銅−酸化亜鉛の混合成形体を、Ni及び/またはFeの硝酸塩、酢酸塩など水溶性塩を溶解する水溶液中に浸漬し、Ni及び/またはFeを含浸させ、乾燥した後、空気などの酸化雰囲気下、通常270〜400℃程度において焼成し、水添吸着脱硫剤前駆体を得る。このときの該前駆体中のNi及び/またはFeの含有量は、1〜10重量%程度となるように調整することが好ましい。   Next, the copper oxide-zinc oxide mixed molded body obtained as described above is immersed in an aqueous solution in which water-soluble salts such as nitrates and acetates of Ni and / or Fe are dissolved, and Ni and / or Fe is added. After impregnating and drying, firing is usually performed at about 270 to 400 ° C. in an oxidizing atmosphere such as air to obtain a hydrogenated adsorptive desulfurizing agent precursor. At this time, the content of Ni and / or Fe in the precursor is preferably adjusted to be about 1 to 10% by weight.

次に、上記で得られた前駆体を、水素を6体積%程度以下、好ましくは0.5〜4体積%程度含む水素と不活性ガスとの混合ガスの存在下に、150〜350℃程度で還元処理することにより、所望の水添吸着脱硫剤が得られる。   Next, the precursor obtained above is reduced at about 150 to 350 ° C. in the presence of a mixed gas of hydrogen and inert gas containing about 6% by volume or less, preferably about 0.5 to 4% by volume of hydrogen. By processing, a desired hydrogenated adsorptive desulfurization agent can be obtained.

本発明のPEFC発電システムに供給される原燃料としては、炭化水素、アルコールなどがあげられる。硫黄化合物を全く含まない合成燃料である場合には、本発明によるシステムは利用できるが、効果はあまりない。硫黄化合物を含む原燃料としては、例えば、都市ガスとして供給されている天然ガス、プロパンガス、ブタンガス等のLPG、ナフサなどを例示できる。天然ガス、LPGなどの炭素数4以下のアルカンを主成分とする気体状の炭化水素がより好ましい。このようなアルカンを主成分とする気体炭化水素を用いた場合には、本発明の効果がより安定して幅広い運転条件で得られる。   Examples of the raw fuel supplied to the PEFC power generation system of the present invention include hydrocarbons and alcohols. In the case of a synthetic fuel that does not contain any sulfur compounds, the system according to the invention can be used but is not very effective. Examples of raw fuels containing sulfur compounds include LPG such as natural gas, propane gas, and butane gas supplied as city gas, naphtha, and the like. Gaseous hydrocarbons mainly composed of alkanes having 4 or less carbon atoms such as natural gas and LPG are more preferred. When such a gaseous hydrocarbon containing alkane as a main component is used, the effects of the present invention can be obtained more stably and under a wide range of operating conditions.

本発明によるPEFC発電方法では、原燃料をまず脱硫プロセスで脱硫する。通常の運転においては、CO選択酸化プロセスに供される前の改質ガスから水蒸気を凝縮分離したリサイクルガスを脱硫前の原燃料に混合し、これをCuとZnとNiおよび/またはFeとを少なくとも含有する水添吸着脱硫剤に接触されることにより脱硫する。このときの脱硫剤の温度は、好ましくは100〜400℃程度、より好ましくは200〜300℃程度である。   In the PEFC power generation method according to the present invention, the raw fuel is first desulfurized by a desulfurization process. In normal operation, recycle gas obtained by condensing and separating water vapor from reformed gas before being subjected to the CO selective oxidation process is mixed with raw fuel before desulfurization, and this is mixed with Cu, Zn, Ni and / or Fe. It desulfurizes by contacting with the hydrogenated adsorption desulfurizing agent contained at least. The temperature of the desulfurizing agent at this time is preferably about 100 to 400 ° C, more preferably about 200 to 300 ° C.

添加すべきリサイクルガスの流量は、原燃料中の硫黄化合物の種類と濃度、リサイクルガスと原燃料の組成などに応じて適宜設定することができる。例えば、硫黄含有量がppmオーダーであり、容易に水素化されるアルケンが原燃料中に含まれていない限り、水素が、原燃料に対して体積比で0.0005程度以上であれば十分であり、より好ましくは0.005程度以上である。本発明におけるリサイクルガスは、通常水素濃度が50%程度以上となっているので、リサイクルガスの流量としては、原燃料に対する体積比で0.001程度以上、より好ましくは0.01程度以上である。   The flow rate of the recycle gas to be added can be appropriately set according to the type and concentration of the sulfur compound in the raw fuel, the composition of the recycle gas and the raw fuel, and the like. For example, as long as the sulfur content is on the order of ppm and the alkene that is easily hydrogenated is not contained in the raw fuel, it is sufficient that the hydrogen is about 0.0005 or more by volume with respect to the raw fuel, More preferably, it is about 0.005 or more. Since the recycle gas in the present invention usually has a hydrogen concentration of about 50% or more, the flow rate of the recycle gas is about 0.001 or more, more preferably about 0.01 or more by volume ratio to the raw fuel.

一方、本発明による脱硫プロセスでは、水素が過剰に存在しても、脱硫性能には実質的に影響を与えない。しかし、リサイクルガスの添加割合が増えると、リサイクルガス中に含まれるCO2やCOと水素が脱硫剤上で反応し、メタンを生成する副反応が起こった場合、温度上昇が大きくなるというリスクがある。従って、原燃料中に特に硫黄濃度が高くなく、容易に水素化されるアルケン類が顕著に含まれない限り、リサイクルガス流量は、原燃料に対して体積比で0.05程度以下とすることが好ましい。リサイクルガスが完全にメタン化した場合でも、脱硫プロセスでの温度上昇は数十℃程度に止まるので、より好ましい温度範囲で運転している限り、実質的な問題は生じない。従って、発電量に合わせて原燃料の流量を変える場合も、原燃料の全流量範囲で、リサイクルガスの体積比が成り行きで好ましい範囲である0.001乃至0.05程度となる場合には、特にリサイクルガスの流量を制御する必要はない。 On the other hand, in the desulfurization process according to the present invention, even if hydrogen is present in excess, the desulfurization performance is not substantially affected. However, as the proportion of recycled gas added increases, there is a risk that the temperature rise will increase if a side reaction occurs in which CO 2 or CO and hydrogen contained in the recycled gas react on the desulfurization agent to produce methane. is there. Therefore, unless the raw fuel has a particularly high sulfur concentration and alkenes that are easily hydrogenated are not significantly contained, the recycle gas flow rate should be about 0.05 or less by volume with respect to the raw fuel. Is preferred. Even when the recycle gas is completely methanated, the temperature rise in the desulfurization process is only tens of degrees Celsius, so that no substantial problem occurs as long as the operation is performed in a more preferable temperature range. Therefore, even when the flow rate of the raw fuel is changed in accordance with the power generation amount, when the volume ratio of the recycle gas is about 0.001 to 0.05 which is a preferable range in the entire flow rate range of the raw fuel, In particular, it is not necessary to control the flow rate of the recycled gas.

脱硫プロセスの圧力としては、常圧付近がより好ましいが、上記記載の製造方法によってえられた水添吸着脱硫剤を用いれば、ゲージ圧で1MPa程度まで上昇させることができる。   The pressure in the desulfurization process is more preferably around normal pressure, but if a hydrogenated desulfurization agent obtained by the production method described above is used, the pressure can be increased to about 1 MPa with a gauge pressure.

脱硫プロセスのGHSV(ガス時間当たり空間速度)は、原燃料中の硫黄化合物の種類及び濃度、使用時間などにより、適宜設計されるが、硫黄含有量がppmオーダーであり、容易に水素化されるアルケンが原燃料中に含まれていない限り、GHSVが100乃至5000h-1程度、好ましくは200乃至2000 h-1程度となるように定めればよい。 The GHSV (space velocity per gas hour) of the desulfurization process is designed as appropriate depending on the type and concentration of sulfur compounds in the raw fuel, operating time, etc., but the sulfur content is on the order of ppm and is easily hydrogenated. Unless alkene is contained in the raw fuel, GHSV may be determined to be about 100 to 5000 h −1 , preferably about 200 to 2000 h −1 .

脱硫プロセスがかかる運転条件で運転される場合、原燃料中の硫黄濃度を容易に1ppbレベル以下とすることができる。   When the desulfurization process is operated under such operating conditions, the sulfur concentration in the raw fuel can be easily reduced to 1 ppb level or less.

一方、起動時など改質ガスをリサイクルできない運転状態においては、改質ガスをリサイクルせずに、原燃料をそのまま水添吸着脱硫剤に接触させて脱硫してもよい。起動時など改質ガスをリサイクルできない場合とは、例えば、リサイクルガスの水素濃度が低すぎる場合(通常50%程度以下)、リサイクルガスのCO濃度が高すぎる場合(通常2%程度以上)などの場合である。   On the other hand, in an operating state where the reformed gas cannot be recycled, such as at the time of startup, the raw fuel may be directly desulfurized by contacting the hydrogenated adsorbent desulfurizing agent without recycling the reformed gas. Cases where the reformed gas cannot be recycled, such as when starting, include when the hydrogen concentration of the recycled gas is too low (usually around 50% or less), or when the CO concentration of the recycled gas is too high (usually around 2% or more) Is the case.

リサイクルを行わない状態で、十分な脱硫性能が得られる時間は、原燃料の組成、硫黄化合物の種類及び濃度、脱硫剤の使用経過時間などに依存するが、リサイクルガス添加前の原燃料の硫黄含有量がppmオーダーであり、容易に水素化されるアルケンが原燃料中に含まれていおらず、好ましい温度範囲で適正に設計されたGHSVで運転されている限り、10時間〜100時間程度は連続で脱硫性能を維持することができる。その後、改質ガスをリサイクルすれば、脱硫剤に新鮮な水素が供給されるので、再びリサイクルを停止しても、やはり10〜100時間程度は連続で脱硫性能を維持することができる。   The time during which sufficient desulfurization performance can be obtained without recycling is dependent on the composition of the raw fuel, the type and concentration of sulfur compounds, the elapsed time of use of the desulfurizing agent, etc. As long as the content is on the order of ppm, alkene that is easily hydrogenated is not contained in the raw fuel, and is operated with a properly designed GHSV in the preferred temperature range, about 10 to 100 hours Desulfurization performance can be maintained continuously. Thereafter, if the reformed gas is recycled, fresh hydrogen is supplied to the desulfurization agent. Therefore, even if the recycle is stopped again, the desulfurization performance can be maintained continuously for about 10 to 100 hours.

さらに、起動時、脱硫剤が好ましい温度域に到達していない段階において、リサイクルガスを添加せず、原燃料をそのまま水添吸着脱硫剤に接触させて脱硫することも可能である。この状態で、十分な脱硫性能が得られる時間は、原燃料の組成、硫黄化合物の種類及び濃度、脱硫剤の使用経過時間などに依存するが、硫黄含有量がppmオーダーであり、容易に水素化されるアルケンが原燃料中に含まれておらず、好ましいGHSVで運転されている限り、1〜3時間程度は連続で脱硫性能を維持することができる。その後、脱硫剤を昇温し、改質ガスをリサイクルすれば、脱硫剤に吸着した有機硫黄が分解すると共に、新鮮な水素が供給されるので、再びリサイクルを停止し、温度が好ましい温度より低くなっても、やはり1〜3時間程度は連続で脱硫性能を維持することができる。   Further, at the time of start-up, when the desulfurizing agent has not reached the preferred temperature range, it is possible to desulfurize the raw fuel by directly contacting the hydrogenated adsorbing desulfurizing agent without adding the recycle gas. The time during which sufficient desulfurization performance is obtained in this state depends on the composition of raw fuel, the type and concentration of sulfur compounds, the elapsed time of use of the desulfurization agent, etc., but the sulfur content is on the order of ppm, and hydrogen As long as the alkene to be converted is not contained in the raw fuel and is operated at the preferred GHSV, the desulfurization performance can be maintained continuously for about 1 to 3 hours. Then, if the temperature of the desulfurizing agent is raised and the reformed gas is recycled, the organic sulfur adsorbed on the desulfurizing agent is decomposed and fresh hydrogen is supplied. Therefore, the recycling is stopped again, and the temperature is lower than the preferred temperature. Even so, the desulfurization performance can be maintained continuously for about 1 to 3 hours.

また、原燃料中の硫黄濃度が高い場合には、水添吸着脱硫剤の使用量を大幅に削減するため、原燃料を、既知のZnO等吸着脱硫剤に接触させて大部分の硫黄を吸着除去した後、水添吸着脱硫剤に接触させてもよい。   In addition, when the sulfur concentration in the raw fuel is high, the raw fuel is brought into contact with a known adsorbing desulfurizing agent such as ZnO to greatly reduce the amount of hydrogenated adsorbing desulfurizing agent used. After removing, it may be brought into contact with a hydrogenated adsorption desulfurizing agent.

さらに、原燃料中に難分解性の有機硫黄化合物が高濃度で含まれる場合や容易に水素化されるアルケンが顕著に含まれる場合には、まず、原燃料にリサイクルガスを添加し、Ni-Mo系、Co-Mo系などの既知の水添脱硫触媒に接触させて有機硫黄やアルケンを水素化したのち、上記吸着脱硫剤に接触させて大部分の硫黄を吸着除去し、水添吸着脱硫剤に接触させてもよい。この場合、リサイクルガスの体積比は、既知の水添脱硫触媒の使用条件に合わせて、水添吸着脱硫剤のみで脱硫する場合に比べて大きく設定する必要があり、また、上記製造方法による水添吸着脱硫剤を使用することが望ましい。   Furthermore, if the raw fuel contains a highly decomposable organic sulfur compound at a high concentration, or if the alkene that is easily hydrogenated is noticeably contained, first add a recycle gas to the raw fuel, then add Ni- Hydrogenate organic sulfur and alkenes by contacting with known hydrodesulfurization catalysts such as Mo-based and Co-Mo-based, then contact with the above-mentioned adsorptive desulfurizing agent to adsorb and remove most of the sulfur, and then hydrogenated adsorptive desulfurization. You may make it contact an agent. In this case, the volume ratio of the recycle gas needs to be set to be larger than that in the case of desulfurization only with the hydrogen adsorption desulfurization agent in accordance with the use conditions of the known hydrodesulfurization catalyst. It is desirable to use an adsorbed desulfurizing agent.

上記脱硫プロセスにより脱硫された原燃料は、水蒸気と混合して水蒸気改質プロセスに供される。PEFC発電システムにおいては、PEFCの運転温度が低いためにPEFCの排熱を利用して改質用の水蒸気を発生できず、燃料を余分に消費して水蒸気を発生する必要があるので、燃料改質システムの熱効率を高め、PEFC発電システムの発電効率を向上させるには、低いS/C比(水蒸気/原燃料中の炭素モル比)で運転すればよい。本発明においては、水蒸気改質プロセスで使用する水蒸気改質触媒や反応条件は既知の方法でよいが、本発明によるPEFC発電方法であれば、原燃料中の硫黄が安定して1ppbレベル以下となっているので、S/C<3の低S/C運転が可能である。原燃料として、天然ガスやLPGなどを用いる場合には、発電効率が極大となるS/C=2乃至3程度、好ましくは2.2乃至2.8程度で運転することが好ましい。   The raw fuel desulfurized by the desulfurization process is mixed with steam and used for the steam reforming process. In the PEFC power generation system, since the operating temperature of the PEFC is low, it is not possible to generate steam for reforming using the exhaust heat of the PEFC, and it is necessary to consume excess fuel to generate steam. In order to increase the thermal efficiency of the quality system and improve the power generation efficiency of the PEFC power generation system, it is only necessary to operate at a low S / C ratio (steam / carbon ratio in raw fuel). In the present invention, the steam reforming catalyst used in the steam reforming process and the reaction conditions may be known methods, but with the PEFC power generation method according to the present invention, the sulfur in the raw fuel is stable and below 1 ppb level. Therefore, low S / C operation with S / C <3 is possible. When natural gas, LPG, or the like is used as the raw fuel, it is preferable to operate at S / C of about 2 to 3, preferably about 2.2 to 2.8, at which power generation efficiency is maximized.

上記水蒸気改質プロセスにより生成した改質ガス中のCO濃度が1%程度以上と高い場合には、該改質ガスは、CO変成プロセスに供されることが好ましい。本発明においては、CO変成プロセスで使用するCO変成触媒はCu-Zn系触媒など既知のCO変成触媒でよく、反応条件は既知の条件でよいが、CO選択酸化プロセスでのCO低減性能と耐久性、並びにCO選択酸化反応の制御性を向上する上で、CO変成プロセスにおいてできる限りCO濃度を低減することが好ましく、CO変成出口の改質ガス中のCO濃度が、ドライベースで好ましくは1%以下程度、より好ましくは0.5%以下程度となるよう、CO変成プロセスの反応条件を選ぶことが望ましい。   When the CO concentration in the reformed gas produced by the steam reforming process is as high as about 1% or more, the reformed gas is preferably subjected to a CO shift process. In the present invention, the CO conversion catalyst used in the CO conversion process may be a known CO conversion catalyst such as a Cu-Zn-based catalyst, and the reaction conditions may be known conditions, but the CO reduction performance and durability in the CO selective oxidation process. It is preferable to reduce the CO concentration as much as possible in the CO conversion process, and the CO concentration in the reformed gas at the CO conversion outlet is preferably 1 on a dry basis. It is desirable to select the reaction conditions for the CO shift process so that it is about% or less, more preferably about 0.5% or less.

上記水蒸気改質プロセスにより生成した改質ガス、または、上記CO変成プロセスでCOを低減した改質ガスは、酸化用の空気を添加してからCO選択酸化プロセスに供される。本発明においては、CO選択酸化プロセスで使用するCO選択酸化触媒や反応条件は既知の方法でよいが、酸化用の空気を添加する前の改質ガスをリサイクル用に分岐する。   The reformed gas generated by the steam reforming process or the reformed gas in which CO has been reduced by the CO conversion process is subjected to a CO selective oxidation process after adding air for oxidation. In the present invention, the CO selective oxidation catalyst and reaction conditions used in the CO selective oxidation process may be known methods, but the reformed gas before adding the oxidation air is branched for recycling.

リサイクルする改質ガスから水蒸気を凝縮分離するプロセスは、リサイクルガスを分岐したあと原燃料に混入するまでの間に行っても良く、または、改質ガス全量から水蒸気を凝縮分離したのちリサイクルガスを分岐し、原燃料に添加しても良い。   The process of condensing and separating water vapor from the reformed gas to be recycled may be performed after the recycle gas is branched and mixed into the raw fuel, or after the water vapor is condensed and separated from the entire reformed gas, the recycle gas is removed. It may be branched and added to the raw fuel.

改質ガスからの水蒸気の凝縮分離に際しては、必ずしも水蒸気を完全凝縮分離する必要はなく、リサイクルラインから原燃料にリサイクルガスを添加するまでに水蒸気が凝縮することのないように、条件、手法などを適宜設定するればよい。例えば、水冷式の水蒸気凝縮器に常温(10〜25℃程度)の水を流通させることにより、水蒸気を凝縮させて、気水分離器でドレインを抜き出す方法を例示できる。   When condensing and separating water vapor from reformed gas, it is not always necessary to completely condense and separate water vapor, and conditions, methods, etc. so that water vapor does not condense before the recycle gas is added to the raw fuel from the recycle line. May be set as appropriate. For example, it is possible to exemplify a method in which water at normal temperature (about 10 to 25 ° C.) is circulated through a water-cooled water vapor condenser to condense the water vapor and extract the drain with a steam-water separator.

上記CO選択酸化反応器を出た水素リッチガスは、PEFCに供給され、酸素または空気との電気化学的反応により、電力を生成する。該水素リッチガスを燃料としてPEFCで発電する方法は、特に制限されず、既知の水素リッチガスを燃料にしてPEFCで発電する方法を適用することができる。   The hydrogen-rich gas exiting the CO selective oxidation reactor is supplied to the PEFC and generates electric power through an electrochemical reaction with oxygen or air. A method for generating electricity with PEFC using the hydrogen-rich gas as a fuel is not particularly limited, and a method for generating electricity with PEFC using a known hydrogen-rich gas as a fuel can be applied.

また、起動時など、水素リッチガスの組成がPEFCでの発電に適当でない場合は、PEFCには供給せず、そのまま燃焼するなどして処理しても良い。   In addition, when the composition of the hydrogen-rich gas is not suitable for power generation by PEFC, such as at the time of startup, it may be processed by burning it as it is without supplying it to PEFC.

システムの停止時においては、燃料改質システムに空気が混入しないような措置がとられる限り、特に制約はない。リサイクルを停止してからも短時間(定格ガス流量として1〜3時間程度)であれば原燃料を投入できるので、原燃料が気体であれば、原燃料での燃料改質システムのパージを行うこともできる。PEFCの停止操作は、常法に従って行えばよい。   When the system is shut down, there is no particular limitation as long as measures are taken to prevent air from entering the fuel reforming system. Since the raw fuel can be input within a short time (about 1 to 3 hours as the rated gas flow rate) after the recycling is stopped, if the raw fuel is a gas, the fuel reforming system is purged with the raw fuel. You can also. The PEFC stop operation may be performed according to a conventional method.

以下、参考例、実施例、比較例を用いて本発明を詳細に説明するが、本発明は、実施例に限定されるものではない。   EXAMPLES Hereinafter, although this invention is demonstrated in detail using a reference example, an Example, and a comparative example, this invention is not limited to an Example.

参考例1
硝酸銅、硝酸亜鉛及び水酸化アルミニウムを1:1:0.3のモル比で含有する混合水溶液を、攪拌しながら約60℃に保った炭酸ナトリウム水溶液に滴下し、沈澱を生じさせた。得られた沈澱を水洗、濾過、乾燥の後、直径1/8インチ×長さ1/8インチに打錠成形し、約300℃で焼成して酸化銅−酸化亜鉛−酸化アルミニウム混合物成形体を得た。
Reference example 1
A mixed aqueous solution containing copper nitrate, zinc nitrate and aluminum hydroxide in a molar ratio of 1: 1: 0.3 was added dropwise to an aqueous sodium carbonate solution maintained at about 60 ° C. with stirring to cause precipitation. The resulting precipitate was washed with water, filtered and dried, then tableted into a 1/8 inch diameter x 1/8 inch length and fired at about 300 ° C. to form a copper oxide-zinc oxide-aluminum oxide mixture molded body. Obtained.

次いで、得られた混合物成形体を硝酸ニッケル水溶液中に浸漬してニッケルを含浸せしめ、乾燥の後、約300℃で焼成して脱硫剤前駆体を得た。得られた脱硫剤前駆体中のニッケル濃度は、5重量%であった。   Subsequently, the obtained mixture molded body was immersed in an aqueous nickel nitrate solution so as to be impregnated with nickel, dried, and then fired at about 300 ° C. to obtain a desulfurizing agent precursor. The nickel concentration in the obtained desulfurizing agent precursor was 5% by weight.

上記で得られた脱硫剤前駆体を、水素を2容量%含有する水素−窒素混合ガス気流中で、約200℃で還元することにより、Cu-Zn-Al-Ni系水添吸着脱硫剤を得た。   By reducing the desulfurization agent precursor obtained above at about 200 ° C. in a hydrogen-nitrogen mixed gas stream containing 2% by volume of hydrogen, a Cu—Zn—Al—Ni hydrogenated adsorption desulfurization agent was obtained. Obtained.

参考例2
参考例1で得られたCu-Zn-Al-Ni系水添吸着脱硫剤を充填したSUS製反応管(触媒層長30cm)に、表1に示される組成の都市ガス(13Aガス)を、GHSV=2000h-1、水素/都市ガス=0.01(モル比)、圧力0.02kg/cm2-G、温度250℃の条件で脱硫した。脱硫後のガス中の硫黄含有量は、5000時間にわたって0.1ppb以下であった。
Reference example 2
To the SUS reaction tube (catalyst layer length 30 cm) filled with the Cu—Zn—Al—Ni hydrogenated adsorption desulfurization agent obtained in Reference Example 1, the city gas (13A gas) having the composition shown in Table 1 was added. Desulfurization was performed under the conditions of GHSV = 2000 h −1 , hydrogen / city gas = 0.01 (molar ratio), pressure 0.02 kg / cm 2 -G, temperature 250 ° C. The sulfur content in the gas after desulfurization was 0.1 ppb or less over 5000 hours.

表1
メタン 88%
エタン 6%
プロパン 3%
ブタン 3%
ジメチルサルファイド 3mg-S/Nm3
t-ブチルメルカプタン 2mg-S/Nm3
参考例3
参考例1で得られたCu-Zn-Al-Ni系水添吸着脱硫剤を用い、水素を添加しない以外は参考例2と同様にして都市ガスを脱硫した。脱硫後のガス中の硫黄含有量は、200時間にわたって0.1ppb以下であった。
Table 1
Methane 88%
Ethane 6%
Propane 3%
Butane 3%
Dimethyl sulfide 3mg-S / Nm 3
t-Butyl mercaptan 2mg-S / Nm 3
Reference example 3
The city gas was desulfurized in the same manner as in Reference Example 2 except that the Cu—Zn—Al—Ni hydrogenated adsorption desulfurization agent obtained in Reference Example 1 was used and hydrogen was not added. The sulfur content in the gas after desulfurization was 0.1 ppb or less over 200 hours.

参考例4
参考例1で得られたCu-Zn-Al-Ni系水添吸着脱硫剤を用い、温度を室温(約25℃)とする以外は参考例2と同様にして都市ガスを脱硫した。脱硫後のガス中の硫黄含有量は、20時間にわたって0.1ppb以下であった。
Reference example 4
The city gas was desulfurized in the same manner as in Reference Example 2 except that the Cu—Zn—Al—Ni-based hydrogenated adsorptive desulfurization agent obtained in Reference Example 1 was used and the temperature was set to room temperature (about 25 ° C.). The sulfur content in the gas after desulfurization was 0.1 ppb or less over 20 hours.

実施例1
基本的なフローが、図2であるPEFC発電システムを構成した。すなわち、参考例1で得られたCu-Zn-Al-Ni系水添吸着脱硫剤100mlを充填したSUS製脱硫器1と、Ru系水蒸気改質触媒200mlを充填した外熱式水蒸気改質反応器2と、Cu-Zn系CO変成触媒800mlを充填した熱交換型CO変成器11と、Ru系CO選択酸化触媒200mlを充填したCO選択酸化反応器3と、1kW級の常圧作動のPEFCスタック9を図2のようなフローで組み合わせた。さらに、CO変成器出口の改質ガスを一部分岐し、水冷式の凝縮器と気水分離器からなる水蒸気凝縮分離器に導入した後、定量ポンプで原燃料ガスに添加できるリサイクルラインを設けた。
Example 1
The basic flow constituted the PEFC power generation system shown in FIG. In other words, the SUS desulfurizer 1 filled with 100 ml of the Cu-Zn-Al-Ni hydrogenated adsorptive desulfurization agent obtained in Reference Example 1 and the external heating steam reforming reaction filled with 200 ml of the Ru-based steam reforming catalyst. , A heat exchange type CO converter 11 charged with 800 ml of a Cu-Zn-based CO shift catalyst, a CO selective oxidation reactor 3 charged with 200 ml of a Ru-based CO selective oxidation catalyst, and a 1 kW-class atmospheric pressure PEFC The stacks 9 were combined according to the flow shown in FIG. In addition, a part of the reformed gas at the outlet of the CO converter was branched and introduced into a steam condenser consisting of a water-cooled condenser and a steam / water separator. .

実施例2
実施例1のPEFC発電システムを用いて、発電試験を行った。原燃料として、表1記載の都市ガス4.2 l/min(標準状態)を用いた。これに水蒸気を凝縮分離することによって露点が20℃以下となったリサイクルガス50 ml/min(標準状態)を加えて、混合後の燃料ガスを250℃に予熱し、脱硫器で脱硫した。脱硫した原燃料にS/C=2.5となるように水蒸気を加えて、入口約450℃、出口約650℃に保たれた外熱式水蒸気改質反応器に供し、改質ガスを得た。得られた改質ガスを約250℃まで冷却し、CO変成器に供給することによって、残存する水蒸気で大部分のCOを
CO2に変換した。このガスの一部を分岐し、水蒸気を凝縮分離してリサイクルガスとした。残りの改質ガスは、入口温度を90℃に保ち、触媒層の温度が180℃を越えないように温度制御されたCO選択酸化反応器に空気0.8l/min(標準状態)を添加した上で導入され、COを10ppm以下に低減した。こうして得られた水素リッチガスを燃料とし、空気を酸化剤としてPEFCスタックで水素利用率約70%で定電流で発電し、約1.1kWの直流電力を得た。
Example 2
A power generation test was conducted using the PEFC power generation system of Example 1. As raw fuel, city gas 4.2 l / min (standard state) shown in Table 1 was used. Recycled gas 50 ml / min (standard state) with a dew point of 20 ° C. or less by condensing and separating water vapor was added thereto, and the mixed fuel gas was preheated to 250 ° C. and desulfurized with a desulfurizer. Steam was added to the desulfurized raw fuel so that S / C = 2.5, and the raw fuel was supplied to an external heat steam reforming reactor maintained at an inlet of about 450 ° C. and an outlet of about 650 ° C. to obtain a reformed gas. The resulting reformed gas is cooled to about 250 ° C and supplied to a CO converter, so that most of the CO is removed with the remaining steam.
Converted to CO 2 . A part of this gas was branched, and water vapor was condensed and separated into a recycled gas. For the remaining reformed gas, 0.8 l / min (standard condition) of air was added to a CO selective oxidation reactor whose temperature was controlled so that the inlet temperature was maintained at 90 ° C and the temperature of the catalyst layer did not exceed 180 ° C. CO was reduced to 10ppm or less. Using the hydrogen-rich gas thus obtained as fuel and air as an oxidant, the PEFC stack generated electricity at a constant current at a hydrogen utilization rate of approximately 70%, and a DC power of approximately 1.1 kW was obtained.

この時の脱硫後の原燃料中の硫黄濃度は0.1ppb以下であった。また、PEFCに供給される水素リッチガス中のメタン濃度は1.8%、CO濃度は1ppm未満であった。一方、リサイクルガス中の水素濃度は約75%であった。   At this time, the sulfur concentration in the raw fuel after desulfurization was 0.1 ppb or less. The methane concentration in the hydrogen-rich gas supplied to PEFC was 1.8%, and the CO concentration was less than 1 ppm. On the other hand, the hydrogen concentration in the recycled gas was about 75%.

さらに、運転を約1000時間継続したところ、PEFCの電圧が若干低下したものの、約1.1kWの直流電力は引き続き得られた。このときの脱硫後の原燃料ガス中の硫黄濃度は0.1ppb以下であった。また、PEFCに供給される水素リッチガス中のメタン濃度は1.8%、CO濃度は1ppm未満であった。   Furthermore, when the operation was continued for about 1000 hours, the DC power of about 1.1 kW was continuously obtained although the PEFC voltage dropped slightly. At this time, the sulfur concentration in the raw fuel gas after desulfurization was 0.1 ppb or less. The methane concentration in the hydrogen-rich gas supplied to PEFC was 1.8%, and the CO concentration was less than 1 ppm.

比較例1
CO選択酸化反応器出口ガスの一部をリサイクルガスとして用いる以外は、実施例2と同様にして発電を行った。ごく初期においては、約1.1kWの直流電力が得られたが、その後徐々に電圧が低下し、約300時間後には発電電力が1kWを切ってしまった。さらに約200時間経過後には電圧が急激に低下したため、発電を中止した。
Comparative Example 1
Electricity was generated in the same manner as in Example 2 except that a part of the CO selective oxidation reactor outlet gas was used as the recycle gas. In the very beginning, DC power of about 1.1 kW was obtained, but then the voltage gradually decreased, and after about 300 hours, the generated power was cut below 1 kW. Furthermore, after about 200 hours, the voltage dropped sharply and power generation was stopped.

CO選択酸化反応器出口ガスを分析したところ、アンモニアが約0.1ppm検出された。   When the CO selective oxidation reactor outlet gas was analyzed, about 0.1 ppm of ammonia was detected.

実施例3
各反応器及び水蒸気凝縮分離用熱交換器を除く熱交換器が同一形状のプレート型エレメントで構成され、該プレート型エレメントを積層して一体化した図5に示すフローの燃料改質システムを製作した。図5の装置は、PEFCセルスタックを除いて、蒸気発生器を内蔵する以外の基本的なフローは、図4と同様である。CO選択酸化反応器を出た水素リッチガスは、PEFCスタックに燃料として供給されるように接続し、PEFC発電システムを構成した。
Example 3
The heat exchanger excluding each reactor and the heat exchanger for steam condensation separation is composed of plate-shaped elements with the same shape, and the fuel reforming system with the flow shown in Fig. 5 is manufactured by stacking and integrating these plate-shaped elements. did. The basic flow of the apparatus of FIG. 5 is the same as that of FIG. 4 except for the built-in steam generator except for the PEFC cell stack. The hydrogen-rich gas exiting the CO selective oxidation reactor was connected to be supplied as fuel to the PEFC stack, and a PEFC power generation system was configured.

CO変成器を出たガスは、全量水冷式の水蒸気凝縮分離器に導入されて水蒸気を凝縮分離したあと、一部はリサイクルガスとして、原燃料圧縮器の吸入側に添加され、残りは、CO選択酸化反応に供した。   The gas exiting the CO converter is introduced into the water-cooled water vapor condensing separator to condense and separate the water vapor, and part of it is added as recycled gas to the intake side of the raw fuel compressor. It used for the selective oxidation reaction.

ここで、表1に示す組成の都市ガス4.2 l/min(標準状態)に、水蒸気を凝縮分離し、露点が20℃以下となったリサイクルガス50 ml/min(標準状態)を加えて燃料圧縮器で0.2kg/cm2程度に昇圧し、熱交換の後、参考例1で得られたCu-Zn-Al-Ni系水添吸着脱硫剤100mlを充填した脱硫器で約250℃で脱硫した。脱硫後の原燃料をS/C=2.5で水蒸気改質したのち、CO変成を行い、水蒸気を凝縮分離後、空気0.8l/min(標準状態)を加えてCO選択酸化反応に供した。この時の改質反応器出口改質ガス温度は約620℃に制御し、CO変成器出口は約150℃、CO選択酸化反応器入口は約25℃となり、CO選択酸化反応器の触媒層の温度は、160℃を越えないように温度制御した。 Here, the fuel gas is compressed by adding 50 ml / min (standard state) of the recycle gas with dew point of 20 ℃ or less to the city gas of 4.2 l / min (standard state) with the composition shown in Table 1. The pressure was increased to about 0.2 kg / cm 2 with a heat exchanger, and after heat exchange, desulfurization was performed at about 250 ° C. with a desulfurizer filled with 100 ml of the Cu—Zn—Al—Ni hydrogen adsorption desulfurization agent obtained in Reference Example 1. . The raw fuel after desulfurization was steam reformed at S / C = 2.5, and then CO conversion was performed. After condensing and separating the steam, 0.8 l / min (standard state) of air was added and subjected to CO selective oxidation reaction. At this time, the reforming gas outlet reformed gas temperature is controlled to about 620 ° C, the CO converter outlet is about 150 ° C, the CO selective oxidation reactor inlet is about 25 ° C, and the catalyst layer of the CO selective oxidation reactor is The temperature was controlled so as not to exceed 160 ° C.

このとき、リサイクルガス中の水素濃度は約75%、得られた水素リッチガス中のメタン濃度は2.5%、CO濃度は3ppm未満であり、PEFCからは約1.1kWの電力が得られた。   At this time, the hydrogen concentration in the recycled gas was about 75%, the methane concentration in the obtained hydrogen-rich gas was 2.5%, the CO concentration was less than 3 ppm, and about 1.1 kW of electric power was obtained from PEFC.

さらに、1000時間にわたって、このシステムを運転し続けたが、得られた水素リッチガス中のメタン濃度、CO濃度には変化がなく、PEFCからも、ほぼ1.1kWの電力が継続的に得られた。   Furthermore, the system was continuously operated for 1000 hours, but the methane concentration and CO concentration in the obtained hydrogen-rich gas remained unchanged, and approximately 1.1 kW of electric power was continuously obtained from PEFC.

比較例2
改質ガスのリサイクルを中断し、原燃料圧縮器と脱硫器の間に市販の酸化マンガン系常温脱硫剤を100ml充填した常温脱硫器を配し、脱硫器の中は空洞とする以外は実施例3と同様にして、PEFC発電システムを構成した。
Comparative Example 2
Example except that the recycle of reformed gas was interrupted, and a room temperature desulfurizer filled with 100 ml of commercially available manganese oxide-based room temperature desulfurization agent was placed between the raw fuel compressor and the desulfurizer, and the desulfurizer was made hollow. The PEFC power generation system was configured in the same way as in Section 3.

脱硫を常温脱硫器を用いて常温で行う以外は実施例3と同様にして、発電試験を行った。その結果、初期においては、得られた水素リッチガス中のメタン濃度は2.5%、CO濃度は3ppm未満であり、PEFCからは約1.1kWの電力が得られた。   A power generation test was conducted in the same manner as in Example 3 except that desulfurization was performed at room temperature using a room temperature desulfurizer. As a result, in the initial stage, the methane concentration in the obtained hydrogen-rich gas was 2.5%, the CO concentration was less than 3 ppm, and about 1.1 kW of power was obtained from PEFC.

さらに、運転を継続したところ、約600時間経過した頃からPEFCの電圧が顕著に低下し始めた。さらに、約100時間運転を継続したが、ついに電池電圧が危険な領域まで低下したので、運転を中止した。   Furthermore, when the operation was continued, the PEFC voltage began to drop significantly after about 600 hours. Furthermore, the operation was continued for about 100 hours, but the operation was stopped because the battery voltage finally dropped to a dangerous area.

このときの水素リッチガス中のメタン濃度は8.2%であり、CO濃度は1ppm未満であった。これは、改質触媒が硫黄被毒により劣化し、改質性能が低下して水素の流量が低下し、PEFCでの水素利用率が上がったためであると考えられる。   At this time, the methane concentration in the hydrogen-rich gas was 8.2%, and the CO concentration was less than 1 ppm. This is thought to be because the reforming catalyst was deteriorated by sulfur poisoning, the reforming performance was lowered, the flow rate of hydrogen was lowered, and the hydrogen utilization rate in PEFC was increased.

実施例4
水添吸着脱硫剤を400ml充填した以外は、実施例3で用いたPEFC発電システムと同様のシステムを使用し、実施例3と同様の条件において発電を行った。
Example 4
A system similar to the PEFC power generation system used in Example 3 was used except that 400 ml of the hydrogenated adsorptive desulfurization agent was charged, and power generation was performed under the same conditions as in Example 3.

1000時間経過後も得られる水素リッチガス中のメタン濃度およびCO濃度には変化がなく、PEFCの出力は、約1.1kWを保っていた。   The methane concentration and CO concentration in the hydrogen-rich gas obtained after 1000 hours did not change, and the PEFC output was maintained at about 1.1 kW.

引き続き、以下のような負荷変動を与えながら燃料改質システム単独で運転を継続した。まず50%負荷相当で1時間運転し、次に100%負荷相当で1時間運転することを1サイクルとして、合計2900サイクル(条件変更などの時間を含めた運転時間:6100時間)の負荷変動を与えた。なお、50%負荷相当の運転条件としては、原燃料として、表1記載の都市ガス2.52 l/min(標準状態)を使用し、これにリサイクルガス30 ml/min(標準状態)を添加した。100%負荷相当の運転条件は、実施例3における運転条件と同一である。   Subsequently, the fuel reforming system alone was operated while giving the following load fluctuations. First, run for 1 hour at 50% load, then run for 1 hour at 100% load as one cycle, and load fluctuations totaling 2900 cycles (running time including condition change time: 6100 hours) Gave. As operating conditions corresponding to 50% load, city gas 2.52 l / min (standard state) shown in Table 1 was used as raw fuel, and 30 ml / min (standard state) of recycle gas was added thereto. The operating conditions corresponding to 100% load are the same as the operating conditions in Example 3.

得られた水素リッチガス中のメタン濃度およびCO濃度は、負荷変動を与える前と同様であった。   The methane concentration and CO concentration in the obtained hydrogen-rich gas were the same as before the load fluctuation was given.

負荷変動を与えた後、再度燃料改質システムをPEFCに再度接続し、100%負荷を与えながら発電を行った。PEFCの出力は、約1.1kWであった。   After the load change was applied, the fuel reforming system was connected again to the PEFC, and power was generated while applying a 100% load. The PEFC output was about 1.1kW.

以上のことから、負荷変動により脱硫器へ流入するガスの流速が変化しても、全く問題なく脱硫が行われていることが明らかである。   From the above, it is clear that desulfurization is performed without any problem even if the flow rate of the gas flowing into the desulfurizer changes due to load fluctuation.

実施例5
実施例3で用いたPEFC発電システムを用い、停止時窒素を用いて燃料改質システムをパージした。再度起動する際、プロセスガスは流通せずに改質炉燃料を送り込んで改質反応器を昇温すると共に、起動用ヒーターを作動させて水蒸気発生器、脱硫器、CO変成器を昇温し、水蒸気発生器とプロセスガスの通る反応器全ての温度が120℃を越えたときに、水蒸気発生器に原水を供給し始めた。そして、リサイクルラインを閉じた状態で都市ガスの供給を開始した。このときの脱硫器の温度は約180℃、改質器出口のプロセスガス温度は450℃であった。このまま約20分間昇温を続けたのち、CO選択酸化反応用の空気を導入すると共に、リサイクルラインを開とした。このあと、各部の温度が安定するまで約20分保持した後、水素リッチガスをPEFCに供給し、発電を開始した。
Example 5
Using the PEFC power generation system used in Example 3, the fuel reforming system was purged with nitrogen during shutdown. When starting up again, process gas is not circulated and the reforming reactor fuel is sent to raise the temperature of the reforming reactor, and the starting heater is activated to raise the temperature of the steam generator, desulfurizer, and CO converter. When the temperature of all the reactors through which the steam generator and process gas pass exceeded 120 ° C, raw water was started to be supplied to the steam generator. The city gas supply was started with the recycle line closed. At this time, the temperature of the desulfurizer was about 180 ° C., and the process gas temperature at the reformer outlet was 450 ° C. After continuing the temperature increase for about 20 minutes, air for CO selective oxidation reaction was introduced and the recycle line was opened. After that, after holding for about 20 minutes until the temperature of each part was stabilized, hydrogen-rich gas was supplied to PEFC, and power generation was started.

この様な停止・起動操作50回を含む1000時間の運転を行ったが、得られた水素リッチガス中のメタン濃度は2.4%、CO濃度は3ppm未満であり、PEFCからは約1.1kWの電力が継続的に得られた。   The operation for 1000 hours including 50 stop / start operations was performed, but the resulting hydrogen-rich gas had a methane concentration of 2.4% and a CO concentration of less than 3 ppm. Obtained continuously.

更に、停止・起動操作が合計135回となり、運転時間の合計が1100時間となるまで運転を継続した。得られた水素リッチガス中のメタン濃度は、変化がなく、PEFCからは約1.1kWの電力が継続的に得られた。   Furthermore, the operation was continued until the total number of stop / start operations was 135 and the total operation time was 1100 hours. There was no change in the methane concentration in the obtained hydrogen-rich gas, and approximately 1.1 kW of electric power was continuously obtained from PEFC.

比較例3
脱硫器にNi-Mo系水添脱硫触媒50mlとZnO吸着脱硫剤50mlを充填し、リサイクルガスの流量を500mlとする以外は実施例5と同様にして起動停止を含む発電試験を行った。
Comparative Example 3
A power generation test including start and stop was performed in the same manner as in Example 5 except that 50 ml of Ni-Mo hydrodesulfurization catalyst and 50 ml of ZnO adsorption desulfurization agent were charged in the desulfurizer and the flow rate of the recycle gas was 500 ml.

途中で徐々にPEFCの電圧が低下し始め、最終的には1kWを切ってしまった。このとき、水素リッチガス中のメタン濃度は5.7%まで上昇していた。   On the way, the PEFC voltage gradually began to drop, and eventually dropped to 1kW. At this time, the methane concentration in the hydrogen-rich gas increased to 5.7%.

比較例4
CO変成器出口のガスの一部について、水蒸気を凝縮分離せずにリサイクルする以外は、実施例2と同様にして発電を行った。
Comparative Example 4
Electric power was generated in the same manner as in Example 2 except that a part of the gas at the CO transformer outlet was recycled without condensing and separating water vapor.

発電開始2時間後からしばしば電圧が低下し、3時間後には運転できなくなった。原燃料のラインに水が混入し、流量が不安定化したのが原因であると考えられる。   The voltage often decreased after 2 hours from the start of power generation, and operation became impossible after 3 hours. This is probably due to water mixing in the raw fuel line and the flow becoming unstable.

図1は、本発明によるPEFC発電システムの一態様を示すフロー図である。FIG. 1 is a flowchart showing one embodiment of a PEFC power generation system according to the present invention. 図2は、本発明によるPEFC発電システムの別の態様を示すフロー図である。FIG. 2 is a flowchart showing another embodiment of the PEFC power generation system according to the present invention. 図3は、本発明によるPEFC発電システムの第三の態様を示すフロー図である。FIG. 3 is a flowchart showing a third embodiment of the PEFC power generation system according to the present invention. 図4は、本発明によるPEFC発電システムの第四の態様を示すフロー図である。FIG. 4 is a flowchart showing a fourth embodiment of the PEFC power generation system according to the present invention. 図5は、実施例において用いたPEFC発電システムの構成とフローを示す図である。FIG. 5 is a diagram illustrating a configuration and a flow of the PEFC power generation system used in the example.

符号の説明Explanation of symbols

1…脱硫器
2…改質反応器
3…CO選択酸化反応器
4…水蒸気凝縮分離器
5…リサイクルライン
6…原燃料
7…プロセス水蒸気
8…CO選択酸化用空気
9…固体高分子型燃料電池
10…ドレイン
11…CO変成器
12…原燃料圧縮器
13…水蒸気発生器
14…改質ガス冷却用熱交換器
15…気水分離器
16…起動用ヒーター
17…CO選択酸化反応器用冷却ファン
18…水蒸気発生用原水
19…改質炉用燃料
20…燃焼空気
21…断熱材
22…燃焼排ガス
DESCRIPTION OF SYMBOLS 1 ... Desulfurizer 2 ... Reforming reactor 3 ... CO selective oxidation reactor 4 ... Steam condensing separator 5 ... Recycle line 6 ... Raw fuel 7 ... Process steam 8 ... CO selective oxidation air 9 ... Solid polymer fuel cell DESCRIPTION OF SYMBOLS 10 ... Drain 11 ... CO converter 12 ... Raw fuel compressor 13 ... Steam generator 14 ... Reformed gas cooling heat exchanger 15 ... Steam separator 16 ... Startup heater 17 ... CO selective oxidation reactor cooling fan 18 ... Raw water for steam generation 19 ... Fuel for reforming furnace 20 ... Combustion air 21 ... Heat insulating material 22 ... Combustion exhaust gas

Claims (6)

原燃料を改質して水素リッチガスを生成する燃料改質プロセスと、水素リッチガスと酸素を固体高分子電解質を介して電気化学的に反応させて電気を発生する燃料電池とを少なくとも含む固体高分子型燃料電池発電方法であって、原燃料から硫黄化合物を脱硫剤により除去する脱硫プロセスと、脱硫された原燃料を水蒸気改質触媒の共存下水蒸気と反応させて改質ガスを生成する改質プロセスと、改質ガスに含まれるCOをCO選択酸化触媒の共存下空気中の酸素で選択的に酸化してCO2に変換するCO選択酸化プロセスを少なくとも含む燃料改質プロセスにおいて、通常運転時、CO選択酸化プロセスに供される前であってCO選択酸化用空気を改質ガスに添加する前に、改質ガスの少なくとも一部のガスを水蒸気凝縮分離プロセスにより水蒸気を凝縮分離させ、前記水蒸気凝縮分離プロセスにより水蒸気を凝縮分離除去したガスをリサイクルして原燃料に添加し、上記脱硫プロセスにおいて、CuとZnとNiおよび/またはFeとを少なくとも含有する水添吸着脱硫剤を用いて脱硫し、起動時など改質ガスをリサイクルできない場合に、一時的に改質ガスのリサイクルを休止して脱硫プロセスを行い、その後、リサイクルを開始することを特徴とする固体高分子型燃料電池発電方法。 A solid polymer comprising at least a fuel reforming process for reforming raw fuel to generate a hydrogen-rich gas, and a fuel cell that generates electricity by electrochemically reacting the hydrogen-rich gas and oxygen via a solid polymer electrolyte Type fuel cell power generation method, a desulfurization process in which sulfur compounds are removed from raw fuel with a desulfurization agent, and reforming in which desulfurized raw fuel is reacted with steam in the presence of a steam reforming catalyst to generate reformed gas During normal operation in a fuel reforming process including at least a CO selective oxidation process that selectively oxidizes CO contained in reformed gas with oxygen in the air in the presence of a CO selective oxidation catalyst and converts it to CO 2 , Before being subjected to the CO selective oxidation process and before adding the CO selective oxidation air to the reformed gas, at least a part of the reformed gas is condensed with steam by a steam condensation separation process. A hydrogenated adsorbing desulfurization agent containing at least Cu, Zn, Ni and / or Fe in the desulfurization process, wherein the gas obtained by condensing and separating the water vapor by the water vapor condensation process is recycled and added to the raw fuel. If the reformed gas cannot be recycled at the time of start-up, etc., it is temporarily decommissioned and the desulfurization process is stopped, and then the recycling is started. Fuel cell power generation method. 燃料改質プロセスが、改質プロセスを出た改質ガス中のCOの大部分をCO変成触媒の共存下、水蒸気と反応させてCO2に変換するCO変成プロセスに供した後、通常運転時、CO選択酸化プロセスに供する前の改質ガスの少なくとも一部を水蒸気凝縮分離プロセスに供する燃料改質プロセスである請求項1記載の固体高分子型燃料電池発電方法。 After the fuel reforming process, the presence of most of the CO shift catalyst in CO in the reformed gas leaving the reforming process, and subjected to CO conversion process of converting the CO 2 is reacted with steam, during normal operation 2. The solid polymer fuel cell power generation method according to claim 1, wherein the method is a fuel reforming process in which at least a part of the reformed gas before being subjected to the CO selective oxidation process is subjected to a steam condensation separation process. 水添吸着脱硫剤が、共沈法で得られたCu及びZnの酸化物を少なくとも含む混合物にNi及び/またはFeを含浸担持した組成物を水素還元して得られる水添吸着脱硫剤である請求項1または2記載の固体高分子型燃料電池発電方法。 The hydrogenated adsorptive desulfurizing agent is a hydrogenated adsorptive desulfurizing agent obtained by hydrogen reduction of a composition obtained by impregnating and supporting Ni and / or Fe in a mixture containing at least Cu and Zn oxides obtained by a coprecipitation method. The solid polymer fuel cell power generation method according to claim 1 or 2. 原燃料が、炭素数4以下のアルカンを主成分とする気体状炭化水素である請求項1〜3のいずれかに記載の固体高分子型燃料電池発電方法。 The solid polymer fuel cell power generation method according to any one of claims 1 to 3, wherein the raw fuel is a gaseous hydrocarbon mainly composed of alkane having 4 or less carbon atoms. 水蒸気改質プロセスにおけるS/C(水蒸気/原燃料中の炭素モル比)が、2乃至3である請求項4記載の固体高分子型燃料電池発電方法。 5. The polymer electrolyte fuel cell power generation method according to claim 4, wherein S / C (steam / carbon molar ratio in raw fuel) in the steam reforming process is 2 to 3. 原燃料ガス流量に対するリサイクルに用いるガスの流量の体積比が、0.001乃至0.05である請求項4または5記載の固体高分子型燃料電池発電方法。 6. The polymer electrolyte fuel cell power generation method according to claim 4, wherein a volume ratio of a flow rate of a gas used for recycling to a raw fuel gas flow rate is 0.001 to 0.05.
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Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2010231903A (en) * 2009-03-26 2010-10-14 Toshiba Home Technology Corp Fuel cell device
JP2012169044A (en) * 2011-02-10 2012-09-06 Aisin Seiki Co Ltd Fuel cell system
JP2012204331A (en) * 2011-03-28 2012-10-22 Toshiba Fuel Cell Power Systems Corp Impurity removal device, fuel reforming system including the same, driving method thereof, and fuel cell system
JPWO2012128369A1 (en) * 2011-03-24 2014-07-24 Jx日鉱日石エネルギー株式会社 Fuel cell system
US9461322B2 (en) 2012-11-27 2016-10-04 Panasonic Intellectual Property Management Co., Ltd. Hydrogen generation apparatus and fuel cell system

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH02188405A (en) * 1989-01-13 1990-07-24 Fuji Electric Co Ltd Water cooled carbon monoxide conversion reactor of fuel cell
JPH06228570A (en) * 1993-02-01 1994-08-16 Idemitsu Kosan Co Ltd Desulfurization of feedstock hydrocarbon for fuel cell
JPH07320761A (en) * 1994-05-25 1995-12-08 Toshiba Corp Fuel cell power generation plant
JPH1161154A (en) * 1997-08-21 1999-03-05 Osaka Gas Co Ltd Production of desulfurizing agent and desulfurization of hydrocarbon
JP2000285948A (en) * 1999-03-30 2000-10-13 Osaka Gas Co Ltd Solid polymer fuel cell system

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH02188405A (en) * 1989-01-13 1990-07-24 Fuji Electric Co Ltd Water cooled carbon monoxide conversion reactor of fuel cell
JPH06228570A (en) * 1993-02-01 1994-08-16 Idemitsu Kosan Co Ltd Desulfurization of feedstock hydrocarbon for fuel cell
JPH07320761A (en) * 1994-05-25 1995-12-08 Toshiba Corp Fuel cell power generation plant
JPH1161154A (en) * 1997-08-21 1999-03-05 Osaka Gas Co Ltd Production of desulfurizing agent and desulfurization of hydrocarbon
JP2000285948A (en) * 1999-03-30 2000-10-13 Osaka Gas Co Ltd Solid polymer fuel cell system

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2010231903A (en) * 2009-03-26 2010-10-14 Toshiba Home Technology Corp Fuel cell device
JP2012169044A (en) * 2011-02-10 2012-09-06 Aisin Seiki Co Ltd Fuel cell system
JPWO2012128369A1 (en) * 2011-03-24 2014-07-24 Jx日鉱日石エネルギー株式会社 Fuel cell system
JP2012204331A (en) * 2011-03-28 2012-10-22 Toshiba Fuel Cell Power Systems Corp Impurity removal device, fuel reforming system including the same, driving method thereof, and fuel cell system
US9461322B2 (en) 2012-11-27 2016-10-04 Panasonic Intellectual Property Management Co., Ltd. Hydrogen generation apparatus and fuel cell system

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