JP2016222781A - Hydrogen production method and system - Google Patents

Hydrogen production method and system Download PDF

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JP2016222781A
JP2016222781A JP2015108882A JP2015108882A JP2016222781A JP 2016222781 A JP2016222781 A JP 2016222781A JP 2015108882 A JP2015108882 A JP 2015108882A JP 2015108882 A JP2015108882 A JP 2015108882A JP 2016222781 A JP2016222781 A JP 2016222781A
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hydrogen
temperature
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calcium hydroxide
nickel hydroxide
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JP6570111B2 (en
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加納 純也
Junya Kano
純也 加納
章司 登家
Shoji Noboriya
章司 登家
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Tohoku University NUC
Yamato Sanko Manufacturing Co Ltd
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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
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Abstract

PROBLEM TO BE SOLVED: To provide a hydrogen production method and system which can highly efficiently produce high-purity hydrogen directly from cellulose or sewage sludge as a biomass resource.SOLUTION: Calcium hydroxide and nickel hydroxide are mixed with cellulose or sewage sludge as a biomass resource and the mixture is heated to produce hydrogen. In the case where the heat treatment temperature is 700-850°C, the biomass resource, calcium hydroxide and nickel hydroxide are mixed in the mixed molar ratio of 1:(0.01 (not zero) to 3.0):( 0.01 (not zero) to 1.0) and crushed and kneaded, the mixture is supplied to an external furnace and heat-exchanged with hot air to raise its temperature, and various produced gases produced by a heating reaction during temperature rising are decreased in temperature and dehumidified, and a part thereof is introduced into a continuous gas analyzer.SELECTED DRAWING: Figure 1

Description

本発明は、各種のエネルギー源として活用される水素ガスをバイオマス資源から製造するための水素製造方法及びそのシステムに関する。   The present invention relates to a hydrogen production method and system for producing hydrogen gas used as various energy sources from biomass resources.

東日本大震災以降、電力の供給不足により社会的・経済的に大きな打撃を受け、安全で安定供給可能なエネルギーの確保が強く望まれるようになった。一方、環境保全の観点から温暖化抑制のためには低炭素社会構築が強く望まれている。   Since the Great East Japan Earthquake, there has been a strong social and economic impact due to the shortage of power supply, and it has been strongly desired to secure safe and stable energy supply. On the other hand, the construction of a low-carbon society is strongly desired to prevent global warming from the viewpoint of environmental conservation.

そこで注目されているのが水素エネルギーである。水素から燃料電池により電気及び熱を取り出すことは普及技術であり、水素は重量当たりのエネルギー密度が高く、保管が可能なことからエネルギーキャリアとして有望である。また、純水素を燃料電池で使用する際には、大気汚染物質を排出しないことからクリーンな燃料である。   Therefore, hydrogen energy is attracting attention. Extraction of electricity and heat from hydrogen by a fuel cell is a popular technology, and hydrogen is promising as an energy carrier because it has a high energy density per weight and can be stored. Further, when pure hydrogen is used in a fuel cell, it is a clean fuel because it does not discharge air pollutants.

水素は、アンモニア製造、塩素ガスと混合して光照射により塩酸製造、油脂と共に二重結合を減らし固体化してトウモロコシ油やマーガリン製造等、多くの製品製造の原料として活用されている。また、具体的な例を挙げると、水素は、金属鉱石の還元、アニリンの製造におけるニトロベンゼンの還元、ナイロン66製造におけるベンゼンの触媒還元や、ロケット燃料や水素自動車等の内燃機関の燃料、各種燃料電池の供給ガスとしてのエネルギー源として活用されている。   Hydrogen is used as a raw material for many products such as ammonia production, hydrochloric acid production by mixing with chlorine gas, light irradiation, solidification by reducing double bonds together with fats and oils, and corn oil and margarine production. As specific examples, hydrogen is a reduction of metal ore, a reduction of nitrobenzene in the production of aniline, a catalytic reduction of benzene in the production of nylon 66, a fuel for internal combustion engines such as rocket fuel and hydrogen automobile, and various fuels. It is used as an energy source as battery supply gas.

従来の水素ガス製造方法としては、例えば、特許文献1に示すように、アルミニウム又はアルミニウム合金を水中で摩擦、粉砕し、50μm以下の微粒子にしてから当該微粒子に温度又は超音波の衝撃を加える活性化処理を行い、数日間の室温における熱処理を施した後、前記微粒子を5℃に冷却して保存状態に置いた微粒子を室温において水分子と反応させる方法が存在する。   As a conventional hydrogen gas production method, for example, as shown in Patent Document 1, aluminum or an aluminum alloy is rubbed and crushed in water to form fine particles of 50 μm or less, and then the temperature or ultrasonic impact is applied to the fine particles. There is a method in which after the heat treatment at room temperature for several days, the fine particles are cooled to 5 ° C. and placed in a storage state to react with water molecules at room temperature.

更に、特許文献2に開示されているように、バイオマスから水素ガスを製造する方法において、植物、植物から生産されたもの、古紙、家畜排せつ物、食品廃棄物、建築発生木材、又は、下水汚泥を含む廃棄物である高セルロース含有物の粉末と水酸化カルシウムの粉末と水酸化ニッケルの粉末とを所定量秤量し、該秤量物と複数の硬質ボールとを混合容器内に入れて所定時間混合粉砕した後、該混合粉砕物を密封容器内で、350℃以上、450℃以下の温度に加熱保持し、発生した水素ガスを導出するという特許技術が本出願人の先行技術となっている。   Furthermore, as disclosed in Patent Document 2, in the method for producing hydrogen gas from biomass, plants, those produced from plants, waste paper, livestock excrement, food waste, building generated wood, or sewage sludge A predetermined amount of high cellulose-containing powder, calcium hydroxide powder, and nickel hydroxide powder, which are waste materials, are weighed, and the weighed material and a plurality of hard balls are placed in a mixing container and mixed and pulverized for a predetermined time. Then, the prior art of the present applicant is that the mixed pulverized product is heated and held in a sealed container at a temperature of 350 ° C. or higher and 450 ° C. or lower to derive the generated hydrogen gas.

特許第4169197号公報Japanese Patent No. 4169197 特許第5170516号公報Japanese Patent No. 5170516

しかしながら、水素は、その約80%が石油や天然ガスを資源として水蒸気改質反応等により製造されている。この反応では、800〜1000℃程度の高温度が必要であり、また、生成するガスは、水素の他、一酸化炭素、二酸化炭素、メタン等を生成するため、その中から水素を選択的に回収するにはガス分離操作が必要である。水素源としてのこれら化石燃料は今後も永続的に採掘できることはなく、やがて枯渇する運命にある。   However, about 80% of hydrogen is produced by a steam reforming reaction using petroleum or natural gas as a resource. In this reaction, a high temperature of about 800 to 1000 ° C. is necessary, and the generated gas generates carbon monoxide, carbon dioxide, methane, etc. in addition to hydrogen. A gas separation operation is required for recovery. These fossil fuels as hydrogen sources will not be able to be mined permanently and will eventually be depleted.

近年、再生可能エネルギーの利用技術としては、太陽光発電や風力発電等の自然エネルギーが注目されているが、電力の安定供給面で課題が残っている。地域の木質バイオマスを活用した発電も順次導入は進んでいるが、原料となる木質バイオマスの収集・運搬を含むシステム構築が不可欠なため、数十年の事業期間における安定供給が課題となっている。   In recent years, natural energy such as solar power generation and wind power generation has attracted attention as a renewable energy utilization technology, but there remains a problem in terms of stable power supply. Power generation using local woody biomass is also being introduced gradually, but since it is essential to build a system that includes the collection and transportation of woody biomass as a raw material, stable supply during the decades of business has become an issue .

また、水素源としてプラスチックを用いる場合も、元々は化石燃料から製造されることを考えると、化石燃料資源の温存、地球温暖化防止の視点から、水素発生源の代替資源を開発することが急がれている。そのため、水素発生の源として、木質バイオマス、プラスチック廃棄物等に大いに期待が寄せられている。   Also, when plastic is used as the hydrogen source, considering that it is originally manufactured from fossil fuels, it is urgent to develop alternative resources for hydrogen sources from the perspective of preserving fossil fuel resources and preventing global warming. It is peeling off. Therefore, there are great expectations for woody biomass, plastic waste, etc. as a source of hydrogen generation.

また、上記した特許文献1においては、アルミニウム又はアルミニウム合金を水中で摩擦、粉砕するための大掛かりな切削装置が必要となってしまい、高効率、且つ、高純度の水素を製造するための連続稼動による水素ガス製造装置の実現が困難であるという問題点を有していた。   Moreover, in the above-mentioned Patent Document 1, a large-scale cutting device for rubbing and pulverizing aluminum or an aluminum alloy in water is necessary, and continuous operation for producing high-efficiency and high-purity hydrogen. It was difficult to realize a hydrogen gas production apparatus by

更に、上記した本出願人による特許文献2の場合、セルロースと水酸化カルシウムと水酸化ニッケルとの混合試料(重量3g)を、メカノケミカル処理として、遊星ミルとスチールボールとを用いて混合粉砕し、処理粉末を加熱し、質量分析装置により評価し、発生ガスの定性分析を行っているが、これもまた、バイオマス資源として例えば、セルロースや下水汚泥等から直接的に高効率、且つ、高純度の水素を連続製造するには、加熱処理温度が350℃以上、450℃以下の範囲であることを含めて、その連続稼働率が低いものとなってしまう虞があり、更なる改良の余地があった。   Furthermore, in the case of the above-mentioned Patent Document 2 by the present applicant, a mixed sample (weight 3 g) of cellulose, calcium hydroxide and nickel hydroxide is mixed and pulverized using a planetary mill and a steel ball as a mechanochemical treatment. The processed powder is heated, evaluated by a mass spectrometer, and the generated gas is qualitatively analyzed. This is also a high-efficiency and high-purity directly from, for example, cellulose or sewage sludge as a biomass resource. In order to continuously produce hydrogen, the heat treatment temperature may be 350 ° C. or higher and 450 ° C. or lower, and the continuous operation rate may be low, and there is room for further improvement. there were.

そこで、本発明は叙上のような従来存した諸事情に鑑み創出されたもので、従来のような化石燃料資源の改質反応等を使用しないで、バイオマス資源として例えば、セルロースや下水汚泥等から直接的に高効率、且つ、高純度の水素を連続製造することのできる水素製造方法及びそのシステムを提供することを目的とする。   Therefore, the present invention was created in view of the existing circumstances as described above, and without using a conventional fossil fuel resource reforming reaction, as a biomass resource, for example, cellulose, sewage sludge, etc. An object of the present invention is to provide a hydrogen production method and system capable of continuously producing high-efficiency and high-purity hydrogen directly from the above.

上述した課題を解決するために、本発明にあっては、バイオマス資源としてセルロースや下水汚泥(元素組成よりセルロースと同一の単位モル質量として扱う)に水酸化カルシウムと水酸化ニッケルを混合し、加熱することにより水素を生成することを特徴とした。   In order to solve the above-described problems, in the present invention, as a biomass resource, calcium hydroxide and nickel hydroxide are mixed with cellulose and sewage sludge (treated as the same unit molar mass as cellulose from the elemental composition) and heated. In this way, hydrogen is produced.

加熱処理温度を700℃〜850℃とした場合において、前記バイオマス資源と水酸化カルシウムと水酸化ニッケルの配合モル比率を1:(0.01(ゼロではない)〜3.0):(0.01(ゼロではない)〜1.0)とした。   When the heat treatment temperature is 700 ° C. to 850 ° C., the mixing molar ratio of the biomass resource, calcium hydroxide, and nickel hydroxide is 1: (0.01 (not zero) to 3.0) :( 0. 01 (not zero) to 1.0).

バイオマス資源としてセルロースや下水汚泥(元素組成よりセルロースと同一の単位モル質量として扱う)に水酸化カルシウムと水酸化ニッケルを所定のモル比率で混合し、解砕・混練する混合手段と、前記解砕・混練された混合物を外熱炉へ供給して熱風と熱交換し昇温させる加熱処理手段と、前記昇温時の加熱反応によって発生した各種生成ガスを減温除湿してその一部を連続ガス分析計へ導入させる減温除湿手段と、を有する水素製造装置により水素を生成することを特徴とする。   Mixing means for mixing calcium hydroxide and nickel hydroxide in a predetermined molar ratio to cellulose and sewage sludge (treated as the same unit molar mass as cellulose from the elemental composition) as a biomass resource, and crushing and kneading, and said crushing・ A heat treatment means for supplying the kneaded mixture to an external heating furnace and exchanging heat with hot air to raise the temperature, and reducing and dehumidifying various product gases generated by the heating reaction at the time of the temperature rise, and a part thereof Hydrogen is produced by a hydrogen production apparatus having a dehumidifying and dehumidifying means to be introduced into the gas analyzer.

本発明では、バイオマス資源に水酸化カルシウムと水酸化ニッケルを混合し、加熱することにより水素の直接製造技術を開発した。一方、下水道は社会インフラに組み込まれており、下水汚泥は永続的に発生するバイオマス資源であることに着目し、様々な変換技術の開発が報告されている。そこでこれらの開発技術を応用し、下水汚泥からバッチ式水素製造を試み、通常の化石燃料資源の改質反応等を使用しないで直接的に下水汚泥から高純度水素を製造することに成功した。この技術を応用し、高効率に高純度な水素を製造する実用プラントの導入に向けて、実験室レベルの連続式の水素製造試験機でスケールアップ因子を把握し、実証プラントの基本概念、設計につなげたものである。   In the present invention, a technique for directly producing hydrogen has been developed by mixing biomass resources with calcium hydroxide and nickel hydroxide and heating them. On the other hand, the development of various conversion technologies has been reported, focusing on the fact that sewage is built into social infrastructure and sewage sludge is a permanently generated biomass resource. Therefore, by applying these development technologies, we attempted batch-type hydrogen production from sewage sludge, and succeeded in producing high-purity hydrogen directly from sewage sludge without using the usual reforming reaction of fossil fuel resources. Applying this technology, in order to introduce a practical plant that produces high-purity hydrogen with high efficiency, the basic concept and design of the demonstration plant are ascertained with a laboratory-level continuous hydrogen production tester to understand the scale-up factors. It is connected.

本発明によれば、従来のような化石燃料資源の改質反応等を使用しないで、バイオマス資源として例えば、セルロースや下水汚泥等から直接的に高効率、且つ、高純度の水素を連続製造することができる。   According to the present invention, without using a conventional fossil fuel resource reforming reaction or the like, high-efficiency, high-purity hydrogen is continuously produced directly from, for example, cellulose or sewage sludge as a biomass resource. be able to.

本発明を実施するための一形態を示す水素製造試験装置の概略構成における処理の流れを示すフロー構成図である。It is a flow block diagram which shows the flow of a process in schematic structure of the hydrogen production test apparatus which shows one form for implementing this invention. 水酸化カルシウムと水酸化ニッケルの混合量が水素発生量に与える影響の実験結果をグラフで示した説明図である。It is explanatory drawing which showed the experimental result of the influence which the mixing amount of calcium hydroxide and nickel hydroxide has on the amount of hydrogen generation. 処理温度を700〜850℃で一定とし、合計供給量を12kg/hで一定とした時の、出口堰の有無による下水汚泥滞留量の影響下での水素発生量の試験結果を示す説明図である。It is explanatory drawing which shows the test result of the hydrogen generation amount under the influence of the amount of sewage sludge retention by the presence or absence of an exit weir when processing temperature is made constant at 700-850 degreeC, and a total supply amount is made constant at 12 kg / h. is there. 処理温度を700〜850℃で一定とし、汚泥を1とした時の配合比率と合計供給量を変化させて行った水素発生量の試験結果を示す説明図である。It is explanatory drawing which shows the test result of the amount of hydrogen generation performed by making process temperature constant at 700-850 degreeC and changing the mixture ratio and total supply amount when sludge is set to 1. FIG. 混練部の手前に水を滴下する装置を設けて定量供給を行った場合であって、(a)はその実験条件を説明する説明図、(b)は実験結果を示すグラフ図である。It is a case where a device for dropping water is provided in front of the kneading section and quantitative supply is performed, (a) is an explanatory diagram for explaining the experimental conditions, and (b) is a graph showing the experimental results. 混練部の手前に水を滴下する装置を設け、定量供給量を半分に下げて行った場合であって、(a)はその実験条件を説明する説明図、(b)は実験結果を示すグラフ図である。This is a case where a device for dropping water is provided in front of the kneading section, and the quantitative supply amount is lowered by half, (a) is an explanatory diagram for explaining the experimental conditions, and (b) is a graph showing the experimental results FIG. 処理温度を700〜850℃、合計供給量を6kg/h、堰有を基準として連続式水素発生反応の最適化を行った場合の実験結果を示す説明図である。It is explanatory drawing which shows the experimental result at the time of optimizing a continuous hydrogen generation reaction on the basis of 700-850 degreeC of process temperature, a total supply amount of 6 kg / h, and having a weir. 実用プラントの導入効果検討からの結論を表としてまとめた説明図である。It is explanatory drawing which put together the conclusion from the introduction effect examination of a practical plant as a table | surface.

以下、本発明の実施の形態を詳細に説明する。   Hereinafter, embodiments of the present invention will be described in detail.

以下、本発明の実施の形態を詳細に説明する。本実施形態では、図1のフロー構成に示すような外熱式連続稼動の水素製造試験装置Pを設計・製作し、各種諸条件における実験を行った。すなわち、本装置Pは、図1に示すように、水酸化カルシウムCa(OH)を投入する第1定量供給ホッパ1、脱水汚泥を投入する第2定量供給ホッパ2、水酸化ニッケルNi(OH)を投入する第3定量供給ホッパ3、と各定量供給ホッパ1,2,3から水酸化カルシウム、脱水汚泥、水酸化ニッケル各々が充填される二軸混練スクリュー4(混合手段)、該二軸混練スクリュー4から入口シール5及び窒素投入機6を介して、前記水酸化カルシウム、脱水汚泥、水酸化ニッケル各々が投入されて加熱処理するためのジャケット・シェル構造の外熱炉7(加熱処理手段)とを備えている。 Hereinafter, embodiments of the present invention will be described in detail. In the present embodiment, an external heating type continuous operation hydrogen production test apparatus P as shown in the flow configuration of FIG. 1 was designed and manufactured, and experiments were performed under various conditions. That is, as shown in FIG. 1, the apparatus P includes a first fixed supply hopper 1 for feeding calcium hydroxide Ca (OH) 2 , a second fixed supply hopper 2 for feeding dehydrated sludge, and nickel hydroxide Ni (OH ) 2 3 metering hopper 3 for introducing a calcium hydroxide from the metering hopper 1, 2, 3, dewatered sludge, biaxial kneading screw 4 (mixing means nickel hydroxide, each of which is filled), the two- An external heating furnace 7 (heat treatment) having a jacket / shell structure for heat treatment in which calcium hydroxide, dehydrated sludge and nickel hydroxide are introduced from the shaft kneading screw 4 through an inlet seal 5 and a nitrogen feeder 6. Means).

外熱炉7は、外気とLPGによって熱風を発生させる熱風発生炉8に接続され、更に、外熱炉7は、散水スプレー式で、且つ、冷却水循環式の凝縮器9(減温除湿手段)及び排気ファン10に接続されている。また、外熱炉7は、出口シール11を介して、燃焼後の処理物をサンプルとして回収する。前記凝縮器9は、炭化炉排気ダンパ14及び水エゼクタ15を介して、排気と排水が可能な循環水槽13に接続され、また、凝縮器9は、生成ガスの排気と分析を同時に行うための調整ポンプ12に接続されている。   The external heating furnace 7 is connected to a hot air generation furnace 8 that generates hot air using outside air and LPG. Further, the external heating furnace 7 is a water spray type condenser and a cooling water circulation type condenser 9 (temperature reduction and dehumidification means). And an exhaust fan 10. Further, the external heating furnace 7 collects the processed material after combustion as a sample via the outlet seal 11. The condenser 9 is connected to a circulating water tank 13 capable of exhausting and draining through a carbonization furnace exhaust damper 14 and a water ejector 15, and the condenser 9 is for exhausting and analyzing the generated gas at the same time. It is connected to the regulating pump 12.

<処理物の流れ>
原料となる水酸化カルシウム、脱水汚泥、水酸化ニッケルは、それぞれの定量供給ホッパ1,2,3に充填され、不図示の切出し機にて実験条件のモル比率になる重量となって切出され、二軸混練スクリュー4に充填される。原料は二軸混練スクリュー4にて順に運ばれ、ピンスクリュー部分4aにて解砕・混練され、良く混練された状態で外熱炉へ供給される。外熱炉7へ供給された原料は当該外熱炉7のジャケットの熱風と熱交換して昇温され、反応が進み水素ガス(H)・メタンガス(CH)・一酸化炭素(CO)・二酸化炭素(CO)・酸素(O)等の各種ガスを発生させる。処理後、サンプルは処理品として回収される。
<Flow of processed material>
Calcium hydroxide, dehydrated sludge, and nickel hydroxide as raw materials are filled in the respective quantitative supply hoppers 1, 2, and 3, and are cut out by a cutting machine (not shown) to a weight that provides the molar ratio of the experimental conditions. The biaxial kneading screw 4 is filled. The raw materials are sequentially conveyed by the twin-screw kneading screw 4, crushed and kneaded by the pin screw portion 4a, and supplied to the external heating furnace in a well kneaded state. The raw material supplied to the external heating furnace 7 is heated up by exchanging heat with the hot air in the jacket of the external heating furnace 7, and the reaction proceeds and hydrogen gas (H 2 ), methane gas (CH 4 ), carbon monoxide (CO) Generate various gases such as carbon dioxide (CO 2 ) and oxygen (O 2 ). After processing, the sample is recovered as a processed product.

<熱源ガスの流れ>
供給される熱風は熱風発生炉8に外気が取込まれ、LPGにより所定の温度まで昇温される。昇温後、外熱炉7のジャケットに供給され、外熱炉7のシェルと熱交換し、温度の下がった熱風が排気ファン10により排気される。
<Flow of heat source gas>
The supplied hot air is taken into the hot air generating furnace 8 and is heated to a predetermined temperature by LPG. After the temperature rise, the air is supplied to the jacket of the external heating furnace 7, exchanges heat with the shell of the external heating furnace 7, and the hot air whose temperature has dropped is exhausted by the exhaust fan 10.

<生成ガスの流れ>
外熱炉7内で反応により生成したガスは多量の水蒸気を含んでいるため、凝縮器9で減温除湿後、水エゼクター15により吸引され水を潜った後、大気解放される。また、生成ガスの一部を調整ポンプ12で吸出し分析計へ導入し、連続的にガス分析を行う。
<Flow of generated gas>
Since the gas generated by the reaction in the external heating furnace 7 contains a large amount of water vapor, it is dehumidified by the condenser 9 and then sucked by the water ejector 15 and submerged in water, and then released to the atmosphere. A part of the product gas is introduced into the suction analyzer by the adjusting pump 12, and the gas analysis is continuously performed.

<生成物の評価>
図2には、水酸化カルシウムと水酸化ニッケルの混合量が水素発生量に与える影響が示されている。水酸化カルシウムの混合量において、水酸化ニッケルの混合量を0molから、0.1mol、1molと増加させると、水素発生量も増加する。また、水酸化ニッケルを入れない0molの時は、水酸化カルシウムの混合比を増加させると水素発生量は単調に増加する。一方、水酸化ニッケルを0.1molと1mol混合したときは、水酸化カルシウムが各々1mol、3molで水素の発生量が単位当たり38g/kg、74g/kgと最大になり、水酸化ニッケルの混合量に対して、最適な水酸化カルシウムの混合量が存在することが解った。
<Evaluation of product>
FIG. 2 shows the influence of the mixing amount of calcium hydroxide and nickel hydroxide on the hydrogen generation amount. When the mixing amount of nickel hydroxide is increased from 0 mol to 0.1 mol and 1 mol in the mixing amount of calcium hydroxide, the amount of hydrogen generation also increases. In addition, at 0 mol without nickel hydroxide, the amount of hydrogen generation increases monotonously when the mixing ratio of calcium hydroxide is increased. On the other hand, when 0.1 mol and 1 mol of nickel hydroxide are mixed, the amount of hydrogen generated is maximum at 38 g / kg and 74 g / kg per unit when calcium hydroxide is 1 mol and 3 mol, respectively. On the other hand, it was found that there was an optimum mixing amount of calcium hydroxide.

<乾燥汚泥を使用した場合の生成物の評価>
図3に示すように、出口堰を設けたことにより、滞留量が増えたため、機内での処理時間が延び、発生ガス量に大幅な改善が見られた。すなわち、加熱処理温度700〜850℃、合計供給量12kg/hの時、堰無では、発生ガス量7.0L/min、単位当たりの水素発生量が12.9g/kg、水素ガス濃度61.35vol%であったのに対して、堰有では、発生ガス量23.1L/min、単位当たりの水素発生量が42.7g/kg、水素ガス濃度61.37vol%であった。よって、以後の試験は堰を付けて行った。また、ガス中の水素濃度には大きな差が見られなかったので、ガス中の水素濃度は処理温度に依存すると考えられる。
<Evaluation of product when dry sludge is used>
As shown in FIG. 3, since the amount of stay increased due to the provision of the outlet weir, the processing time in the machine was extended, and the amount of generated gas was greatly improved. That is, when the heat treatment temperature is 700 to 850 ° C. and the total supply amount is 12 kg / h, the generated gas amount is 7.0 L / min, the hydrogen generation amount per unit is 12.9 g / kg, the hydrogen gas concentration is 61. Whereas it was 35 vol%, in the presence of weirs, the generated gas amount was 23.1 L / min, the hydrogen generation amount per unit was 42.7 g / kg, and the hydrogen gas concentration was 61.37 vol%. Therefore, the subsequent tests were conducted with a weir. Further, since there was no significant difference in the hydrogen concentration in the gas, the hydrogen concentration in the gas is considered to depend on the processing temperature.

<各原料の配合比率の影響の明確化>
処理温度を700〜850℃とし、汚泥を1molとした時の配合比率と合計供給量を変化させて試験を行った。その結果、図4に示すように、水酸化カルシウムが1mol、又は、水酸化ニッケルが0.01molの時は水素発生量が大幅に下がっており、水酸化カルシウムが2mol程度、水酸化ニッケルは0.5mol程度必要だということが判明した。しかし、単位当たりの水素発生量としてはまだ低く、更なる操作が必要である。
<Clarification of the effect of the mixing ratio of each raw material>
The test was conducted by changing the blending ratio and the total supply amount when the treatment temperature was 700 to 850 ° C. and the sludge was 1 mol. As a result, as shown in FIG. 4, when calcium hydroxide is 1 mol or nickel hydroxide is 0.01 mol, the amount of hydrogen generation is greatly reduced, calcium hydroxide is about 2 mol, and nickel hydroxide is 0 It was found that about 5 mol was necessary. However, the amount of hydrogen generated per unit is still low and further operation is required.

<原料への水添加の影響の明確化>
基礎試験では水の添加により、水素発生量が2.5倍程度になるという結果があったことから、本試験機に置いても、二軸混練スクリュー4の混練部の手前、又は、側近(例えばピンスクリュー部分4a)に水滴下装置(図1参照)を設け、定量供給を行った。
<Clarification of the effect of water addition to raw materials>
In the basic test, there was a result that the amount of hydrogen generation was increased by about 2.5 times by adding water. Therefore, even in this testing machine, before or near the kneading part of the biaxial kneading screw 4 ( For example, a water dripping device (see FIG. 1) was provided in the pin screw portion 4a), and a fixed amount was supplied.

図5(a)に水添加の影響の明確化の実験条件を示す。すなわち、その条件とは、加熱処理温度が700〜850℃、汚泥:水酸化カルシウム:水酸化ニッケル=1:2:0.5(モル比率)、合計供給量が12kg/h、堰有、水供給量が1.25kg/h(水添加率50%)及び0.6kg/h(水添加率25%)である。   FIG. 5A shows experimental conditions for clarifying the influence of water addition. That is, the heat treatment temperature is 700 to 850 ° C., sludge: calcium hydroxide: nickel hydroxide = 1: 2: 0.5 (molar ratio), total supply amount is 12 kg / h, weir, water The supply amounts are 1.25 kg / h (water addition rate 50%) and 0.6 kg / h (water addition rate 25%).

その結果、図5(b)に示すように、時刻14:20より汚泥無水分重量の50%に相当する1.25kg/hの水を供給し変化を見たが、急激な水分蒸発量の増加のためか、機内の圧力バランスを崩し、リーク空気が増えた。そのため、分析計入口排気流量の増加が見られたが、それに伴い酸素濃度の上昇を招き、分析計で危険域のガスをサンプリングしたため、窒素パージを繰り返すこととなった。その後、時刻15:43に水の供給量を汚泥無水分重量の25%に相当する0.6kg/hに下げたが、崩れた圧力バランスは復旧できなかった。水を供給したことによる圧力バランスの変化は蒸発水分量の増加に伴い増加する必要供給熱量に試験機の供給熱量が対応できていない可能性があるため、供給量を半分に下げ、図6(a)に示す水添加の影響の明確化実験条件にて試験を行った。すなわち、その条件とは、加熱処理温度が700〜850℃、汚泥:水酸化カルシウム:水酸化ニッケル=1:2:0.5(モル比率)、合計供給量が6kg/h、堰有、水供給量が0.16kg/h(水添加率15%)及び0.52kg/h(水添加率50%)である。   As a result, as shown in FIG. 5 (b), 1.25 kg / h of water corresponding to 50% of the sludge anhydrous weight was supplied and the change was observed at time 14:20. Because of the increase, the pressure balance inside the aircraft was lost and leaked air increased. As a result, an increase in the flow rate at the inlet of the analyzer was observed, but this caused an increase in the oxygen concentration, and because the gas in the hazardous area was sampled by the analyzer, the nitrogen purge was repeated. Thereafter, at time 15:43, the water supply amount was lowered to 0.6 kg / h corresponding to 25% of the sludge anhydrous weight, but the collapsed pressure balance could not be recovered. Since the change in pressure balance due to the supply of water may not be able to cope with the required supply heat quantity that increases with the increase in the amount of evaporated water, the supply quantity of the tester is reduced to half, and FIG. The test was conducted under the experimental conditions for clarifying the influence of water addition shown in a). That is, the heat treatment temperature is 700 to 850 ° C., sludge: calcium hydroxide: nickel hydroxide = 1: 2: 0.5 (molar ratio), the total supply amount is 6 kg / h, weir, water The supply amounts are 0.16 kg / h (water addition rate 15%) and 0.52 kg / h (water addition rate 50%).

その結果、図6(b)に示すように、時刻13:23より汚泥無水分重量の15%に相当する0.16kg/hの水を供給し変化を見たが、一時的に排気流量は上がったが、水素濃度が下がり、時刻16:00頃には変化が収まり、未供給時と同程度の分析入口排気流量及び水素濃度となった。よって、時刻16:14より水の供給量を汚泥無水分重量の50%に相当する0.52kg/hに上げたが、同じく一時的に流量の増加及び水素濃度の低下が起こった。その後、圧力バランスを崩し、暫く窒素パージによるハンチングを起こした後、持ち直したが、未供給時と同程度の数値で収まった。   As a result, as shown in FIG. 6 (b), water was supplied at 0.16 kg / h corresponding to 15% of the sludge anhydrous weight from time 13:23, and the change was observed. Although the hydrogen concentration increased, the hydrogen concentration decreased, and the change stopped at around 16:00, and the analysis inlet exhaust flow rate and hydrogen concentration were about the same as when the gas was not supplied. Therefore, although the supply amount of water was increased to 0.52 kg / h corresponding to 50% of the sludge anhydrous weight from time 16:14, the flow rate increased and the hydrogen concentration decreased temporarily. After that, the pressure balance was lost, hunting by nitrogen purge was caused for a while, and then it was picked up, but it stayed at the same value as when not supplied.

これにより、連続式の反応においては水の供給による水素発生量の増加は確認できなかった。これは、常に供給される脱水汚泥より発生する多量の蒸気が基礎研究での水滴下に相当する効果を発揮しており、それ以上の水の供給は反応に寄与しないためと考えられる。   As a result, in the continuous reaction, an increase in the amount of hydrogen generated due to the supply of water could not be confirmed. This is probably because the large amount of steam generated from the constantly supplied dewatered sludge has an effect equivalent to the dripping of water in basic research, and the supply of more water does not contribute to the reaction.

<連続式における反応の最適化>
上記した原料への水添加の影響の明確化において、反応に必要な熱量が当初想定していた熱量より多く必要としている可能性が見受けられた。よって、本実施形態においては、加熱処理温度700〜850℃、合計供給量6kg/h、堰有を基準とし、基礎研究にてランニングコストに関して最も安価な触媒使用量の配合比率は、汚泥:水酸化カルシウム:水酸化ニッケル=1:2:0.5(モル比率)と示されたので、これを基に最適化を行った。
<Optimization of reaction in continuous system>
In the clarification of the influence of water addition to the raw materials described above, there was a possibility that the amount of heat required for the reaction was more than the amount of heat originally assumed. Therefore, in this embodiment, based on the heat treatment temperature of 700 to 850 ° C., the total supply amount of 6 kg / h, and the presence of the weir, the mixing ratio of the catalyst usage amount that is the cheapest in terms of running cost in basic research is Since it was shown that calcium oxide: nickel hydroxide = 1: 2: 0.5 (molar ratio), optimization was performed based on this.

汚泥:水酸化カルシウム:水酸化ニッケル=1:2:0.5(モル比率)の時、二酸化炭素濃度が高い結果となったので、反応を促進させるために、水酸化カルシウムを2.5molの配合比率になるように切出し量を調整した。しかし、汚泥の切出し量に変動があり、供給量が増えてしまったため、図7に記載されたように、汚泥が増えた時の配合比率で最適化を行った。この時、反応が促進され、水素濃度の上昇が見られた。すなわち、汚泥:水酸化カルシウム:水酸化ニッケル=1:2.2:0.45(モル比率)で、合計供給量6.82kg/h、発生ガス量14.1L/minの時、単位当たりの水素発生量が43.3g/kg、水素ガス濃度66.2vol%となった。また、汚泥供給量が増えたために発生ガス量が増えたことも考えられるが、水素発生量が増加しているので、反応が促進されたといえる。   When sludge: calcium hydroxide: nickel hydroxide = 1: 2: 0.5 (molar ratio), the carbon dioxide concentration was high, so that 2.5 mol of calcium hydroxide was added to promote the reaction. The cut-out amount was adjusted so as to obtain a blending ratio. However, since the amount of sludge cut out fluctuated and the supply amount increased, as shown in FIG. 7, optimization was performed with the blending ratio when sludge increased. At this time, the reaction was accelerated and an increase in the hydrogen concentration was observed. That is, sludge: calcium hydroxide: nickel hydroxide = 1: 2.2: 0.45 (molar ratio), total supply amount 6.82 kg / h, generated gas amount 14.1 L / min, per unit The hydrogen generation amount was 43.3 g / kg, and the hydrogen gas concentration was 66.2 vol%. In addition, the amount of generated gas may have increased due to an increase in the amount of sludge supplied, but it can be said that the reaction was promoted because the amount of hydrogen generated increased.

次に、水酸化カルシウムを3.0molの配合比率になるように切出し量を調整したが、上記と同様に汚泥の供給量が増えていたため、低い比率となった。しかしながら、配合比率を上げたことにより、二酸化炭の濃度の減少は見られたが、水素発生量に関しては微減しており、この範囲で発生のピークがあると考えられる。これは基礎研究に用いられた固定層反応器の傾向が、連続試験機で同様に確認されたので、今後も固定層反応器と同様の結果を実機へと繋げて行くことが可能であるという証左が得られた。この結果により、得られた配合比率と水素発生量を基に実用プラントの設計を行うことが可能となる。   Next, the amount of cutting out was adjusted so that the mixing ratio of calcium hydroxide was 3.0 mol. However, since the amount of sludge supplied was increased in the same manner as described above, the ratio was low. However, although the concentration of coal dioxide was decreased by increasing the blending ratio, the amount of hydrogen generation was slightly decreased, and it is considered that there is a generation peak in this range. This is because the tendency of the fixed bed reactor used in the basic research was confirmed in a continuous test machine as well, so it is possible to connect the same results to the actual machine in the future. The proof was obtained. As a result, it is possible to design a practical plant based on the obtained blending ratio and the amount of hydrogen generation.

<連続試験からの主な結論>
本実施形態では、処理温度700〜850℃、配合比率が汚泥:水酸化カルシウム:水酸化ニッケル=1:2.2:0.45(モル比率)の時、水素発生量43.3g/kgの結果が得られた。但し、小型試験機のため、外乱(リーク空気等)による影響が大きく、外気の流入により窒素濃度が上がり、水素濃度が下がった。このため、上記した水素製造試験装置Pにおいて、外乱の影響を抑えるために装置P全体のシール性の更なる改良を行うことにより、高効率で高純度な水素を製造する実用プラントの導入(連続稼動による水素製造装置の製造)が可能となる。
<Main conclusions from continuous tests>
In this embodiment, when the treatment temperature is 700 to 850 ° C. and the blending ratio is sludge: calcium hydroxide: nickel hydroxide = 1: 2.2: 0.45 (molar ratio), the hydrogen generation amount is 43.3 g / kg. Results were obtained. However, because of the small tester, it was greatly affected by disturbance (leakage air, etc.), and the nitrogen concentration increased and the hydrogen concentration decreased due to the inflow of outside air. For this reason, in the hydrogen production test apparatus P described above, introduction of a practical plant for producing high-efficiency and high-purity hydrogen by further improving the sealing performance of the entire apparatus P in order to suppress the influence of disturbance (continuous) Production of hydrogen production equipment by operation) becomes possible.

<実用プラントの導入効果検討からの結論>
従来の化石燃料からの副生水素を地域のバイオマス資源である下水汚泥から製造した水素に転換することは、エネルギー・セキュリティや地域のエネルギーの自立や雇用創出の点から重要である。因みに、弘前市から採取した下水汚泥は、炭素44.62%、水素6.69%、窒素4.80%、酸素30.10%、硫黄0.49%、の固形分の組成に、含水率が75.1%というようにセルロースの組成に近い分子量であることから、これを基準として水酸化カルシウムと水酸化ニッケルの混合比率を決定することが可能である。
<Conclusion from study of introduction effect of practical plant>
Converting by-product hydrogen from conventional fossil fuels into hydrogen produced from sewage sludge, which is a local biomass resource, is important in terms of energy security, local energy independence and job creation. By the way, the sewage sludge collected from Hirosaki city has a solid content of 44.62% carbon, 6.69% hydrogen, 4.80% nitrogen, 30.10% oxygen, 0.49% sulfur, and water content. Since the molecular weight is close to the cellulose composition, such as 75.1%, the mixing ratio of calcium hydroxide and nickel hydroxide can be determined based on this.

ここで、図8において、製造コスト1=(水酸化カルシウムと水酸化ニッケル原料購入費用+投入一次エネルギーコスト)/水素回収量、製造コスト2=(水酸化カルシウムと水酸化ニッケル原料購入+投入一次エネルギーコスト+50tプラントの運転管理費・修繕費・焼去灰処分費・減価償去費(35年均等))/水素回収量、エネルギー収支=(水素の高位発熱量×水素回収量)/投入一次エネルギー、エネルギー回収率=(水素の高位発熱量×水素回収量)/(下水汚泥の有機成分のもつエネルギー+投入一次エネルギー)、下水汚泥処理コスト1=(水酸化カルシウムと水酸化ニッケル原料購入+投入一次エネルギーコスト)/処理する下水汚泥量、下水汚泥処理コスト2=(水酸化カルシウムと水酸化ニッケル原料購入+投入一次エネルギーコスト+50t/日プラントの運転管理費・修繕費・焼去灰処分費・減価償却費(35年均等))/処理する下水汚泥量、である。   Here, in FIG. 8, production cost 1 = (calcium hydroxide and nickel hydroxide raw material purchase cost + input primary energy cost) / hydrogen recovery amount, production cost 2 = (calcium hydroxide and nickel hydroxide raw material purchase + input primary) Energy cost + 50t plant operation management costs, repair costs, burned ash disposal costs, depreciation costs (equal to 35 years)) / hydrogen recovery, energy balance = (higher heating value of hydrogen x hydrogen recovery) / input Primary energy, energy recovery rate = (higher heating value of hydrogen x hydrogen recovery amount) / (energy of organic components of sewage sludge + input primary energy), sewage sludge treatment cost 1 = (purchased calcium hydroxide and nickel hydroxide raw material) + Primary energy cost input) / Amount of sewage sludge to be treated, Sewage sludge treatment cost 2 = (Purchased calcium hydroxide and nickel hydroxide raw materials + Input primary energy cost) + 50t / day operation and management costs, repair costs and baked Sahai disposal costs, depreciation and amortization of plant (35 years equally)) / processing sewage sludge amount, it is.

P 水素製造試験装置
1 第1定量供給ホッパ
2 第2定量供給ホッパ
3 第3定量供給ホッパ
4 二軸混練スクリュー(混合手段)
4a ピンスクリュー部分
5 入口シール
6 窒素投入機
7 外熱炉(加熱処理手段)
8 熱風発生炉
9 凝縮器(減温除湿手段)
10 排気ファン
11 出口シール
12 調整ポンプ
13 循環水槽
14 炭化炉排気ダンパ
15 水エゼクタ
P Hydrogen production test apparatus 1 First fixed supply hopper 2 Second fixed supply hopper 3 Third fixed supply hopper 4 Twin screw kneading screw (mixing means)
4a Pin screw part 5 Inlet seal 6 Nitrogen charging machine 7 External heating furnace (heating treatment means)
8 Hot-air generator 9 Condenser (Temperature reduction and dehumidification means)
DESCRIPTION OF SYMBOLS 10 Exhaust fan 11 Outlet seal 12 Adjustment pump 13 Circulating water tank 14 Carbonization furnace exhaust damper 15 Water ejector

Claims (3)

バイオマス資源としてセルロースや下水汚泥に水酸化カルシウムと水酸化ニッケルを混合し、加熱することにより水素を生成することを特徴とした水素製造方法。   A hydrogen production method characterized in that as a biomass resource, calcium hydroxide and nickel hydroxide are mixed in cellulose or sewage sludge and heated to produce hydrogen. 加熱処理温度を700℃〜850℃とした場合において、前記バイオマス資源と水酸化カルシウムと水酸化ニッケルの配合モル比率を1:(0.01(ゼロではない)〜3.0):(0.01(ゼロではない)〜1.0)とした請求項1記載の水素製造方法。   When the heat treatment temperature is 700 ° C. to 850 ° C., the mixing molar ratio of the biomass resource, calcium hydroxide, and nickel hydroxide is 1: (0.01 (not zero) to 3.0) :( 0. The hydrogen production method according to claim 1, wherein 01 (not zero) to 1.0). バイオマス資源としてセルロースや下水汚泥に水酸化カルシウムと水酸化ニッケルを所定のモル比率で混合し、解砕・混練する混合手段と、前記解砕・混練された混合物を外熱炉へ供給して熱風と熱交換し昇温させる加熱処理手段と、前記昇温時の加熱反応によって発生した各種生成ガスを減温除湿してその一部を連続ガス分析計へ導入させる減温除湿手段と、を有する水素製造装置により水素を生成することを特徴とする水素製造システム。   As a biomass resource, mixing means for mixing calcium hydroxide and nickel hydroxide in cellulose and sewage sludge at a predetermined molar ratio, crushing and kneading, and supplying the pulverized and kneaded mixture to an external heating furnace Heat treatment means for exchanging heat and raising the temperature, and dehumidifying and dehumidifying means for reducing the temperature and dehumidifying various product gases generated by the heating reaction at the time of raising the temperature and introducing a part thereof into a continuous gas analyzer. A hydrogen production system characterized in that hydrogen is produced by a hydrogen production apparatus.
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