JP2013173878A - Method for converting organic substance into profitable material - Google Patents

Method for converting organic substance into profitable material Download PDF

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JP2013173878A
JP2013173878A JP2012040233A JP2012040233A JP2013173878A JP 2013173878 A JP2013173878 A JP 2013173878A JP 2012040233 A JP2012040233 A JP 2012040233A JP 2012040233 A JP2012040233 A JP 2012040233A JP 2013173878 A JP2013173878 A JP 2013173878A
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JP5835003B2 (en
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Katsuhiko Takagi
克彦 高木
Minoru Asanuma
稔 浅沼
Teruo Fujibayashi
晃夫 藤林
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JFE Steel Corp
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    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E50/00Technologies for the production of fuel of non-fossil origin
    • Y02E50/30Fuel from waste, e.g. synthetic alcohol or diesel
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P10/00Technologies related to metal processing
    • Y02P10/20Recycling
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P10/00Technologies related to metal processing
    • Y02P10/25Process efficiency
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P20/00Technologies relating to chemical industry
    • Y02P20/50Improvements relating to the production of bulk chemicals
    • Y02P20/52Improvements relating to the production of bulk chemicals using catalysts, e.g. selective catalysts
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/50Reuse, recycling or recovery technologies
    • Y02W30/62Plastics recycling; Rubber recycling

Abstract

PROBLEM TO BE SOLVED: To obtain a reformed product containing a large amount of light content while containing less amounts of heavy content and carbonaceous content, by efficiently reforming organic substances into low-molecular substances using stably available gas, when converting organic substances into low-molecular substances of gas products, liquid products or the like; and to make efficient use of solid residues generated in the molecular reduction reaction.SOLUTION: A method comprises steps of: adding excess steam to exhaust gas (g) containing carbon monoxide generated in a metallurgical furnace to perform a shift reaction; producing a mixed gas (g) including hydrogen and carbon dioxide generated in the shift reaction and steam not consumed in the shift reaction; bringing this mixed gas (g) into contact with an organic substance to cause a reaction of reforming the organic substance into low-molecular substances; recovering a low-molecular reformed product of the organic substance and a solid-state residue generated by the reaction; and utilizing the solid-state residue as a carbon material.

Description

本発明は、廃プラスチックなどの有機物質を改質して低分子化された改質物を得るとともに、低分子化反応で生じた固体状残渣を有効利用する有機物質の利材化方法に関する。   The present invention relates to a method for making an organic material that efficiently uses a solid residue generated by a low molecular weight reaction while modifying a low molecular weight material by modifying an organic material such as waste plastic.

一貫製鉄所において、コークスは鉄鉱石の還元剤として多量に使用されており、さらに、鉄鉱石焼結機の凝結材としてもコークスが使用されている。一方、コークスを製造するコークス炉からは多量のコークス炉ガスが発生し、また、コークスで鉄鉱石の還元を行う高炉からも多量の高炉ガスが発生し、これらの副生ガスは製鉄所の燃料や還元剤として活用されている。
近年、製鉄所では、炭酸ガスの排出削減という社会的要請や原料炭の高騰などの理由から、LNGなどの石炭以外の炭素源が燃料や還元剤の一部として利用されるようになってきた。しかし、さらなる炭酸ガス排出削減のために、LNGなどの化石燃料への依存を低下させることが求められている。
In integrated steelworks, coke is used in large quantities as a reducing agent for iron ore, and coke is also used as a coagulant for iron ore sintering machines. On the other hand, a large amount of coke oven gas is generated from the coke oven that produces coke, and a large amount of blast furnace gas is also generated from the blast furnace that reduces iron ore with coke. It is used as a reducing agent.
In recent years, carbon sources other than coal, such as LNG, have come to be used as part of fuels and reducing agents at steelworks due to social demands for reducing carbon dioxide emissions and soaring coking coal. . However, in order to further reduce carbon dioxide emissions, it is required to reduce the dependence on fossil fuels such as LNG.

ところで、廃プラスチック、含油スラッジ、廃油、バイオマスなどの多くは焼却処理されているのが現状である。しかし、焼却処理ではCO発生などの環境負荷が高く、また、焼却炉の熱的損傷の問題もあり、ケミカルリサイクル技術の確立が求められている。
ケミカルリサイクル技術のなかでも、有機物質を気体生成物や液体生成物に転換するための技術は、廃プラスチックを中心に従来から種々検討がなされ、例えば、以下のような提案がなされている。
By the way, the present situation is that most of waste plastic, oil-containing sludge, waste oil, biomass and the like are incinerated. However, the incineration process has a high environmental load such as CO 2 generation, and there is a problem of thermal damage of the incinerator, so that establishment of chemical recycling technology is required.
Among the chemical recycling technologies, technologies for converting an organic substance into a gas product or a liquid product have been variously studied mainly on waste plastics. For example, the following proposals have been made.

特許文献1には、水素濃度60vol%以上、好ましくは80vol%以上、温度600℃以上のコークス炉ガス(COG)を廃プラスチックなどの有機物質と反応させることにより、有機物質を高効率で水素化分解・ガス化し、COGを増熱化する方法が開示されている。
また、特許文献2には、石油の流動接触触媒(FCC)を熱媒体兼触媒として用い、温度350〜500℃で廃プラスチックを分解して液体燃料に変換する方法が開示されている。
また、特許文献3には、RDFや木材などを熱分解するにあたり、熱分解で生成したガスを水蒸気改質し、この水蒸気改質により水素濃度を高くしたガスを熱分解部に循環し、水素濃度を高くしたガス雰囲気で熱分解を行う方法が開示されている。
In Patent Document 1, a coke oven gas (COG) having a hydrogen concentration of 60 vol% or more, preferably 80 vol% or more and a temperature of 600 ° C or more is reacted with an organic material such as waste plastic, thereby hydrogenating the organic material with high efficiency. A method for increasing the heat of COG by decomposition and gasification is disclosed.
Further, Patent Document 2 discloses a method in which petroleum fluid contact catalyst (FCC) is used as a heat medium / catalyst and waste plastic is decomposed at a temperature of 350 to 500 ° C. to be converted into liquid fuel.
Further, in Patent Document 3, when pyrolyzing RDF, wood, etc., the gas generated by pyrolysis is steam reformed, and the gas having a high hydrogen concentration by this steam reforming is circulated to the pyrolysis section to generate hydrogen. A method of performing pyrolysis in a gas atmosphere with a high concentration is disclosed.

特開2007−224206号公報JP 2007-224206 A 特開2010−013657号公報JP 2010-013657 A 特開2001−131560号公報JP 2001-131560 A

しかしながら、上記従来技術には、以下のような問題がある。
まず、特許文献1に関しては、COG中の水素濃度が60vol%以上となるのは石炭乾留工程のうちでも乾留末期に限られるので、特許文献1の方法では、乾留末期のタイミングでガス流路を切替え、多量のダストを含む600℃以上のCOGを廃プラスッチク水素化分解反応器に供給する必要がある。しかし、このような過酷な条件で、流路切替弁を長期間安定して作動させ続けることは困難であり、この意味で実現性に乏しい技術であると言える。さらに、廃プラスチックの効率的なガス化のためには、60vol%以上の水素を含有するCOGを連続的に水素化分解反応器に供給することが必要であるが、このためには炭化室毎に水素濃度計と流路切替弁を設置する必要があり、設備コストが増大する。
However, the above prior art has the following problems.
First, regarding Patent Document 1, since the hydrogen concentration in COG is 60 vol% or more is limited to the end of the dry distillation in the coal dry distillation process, in the method of Patent Document 1, the gas flow path is opened at the end of the dry distillation. It is necessary to switch and supply COG of 600 ° C. or more containing a large amount of dust to a waste plastic hydrocracking reactor. However, it is difficult to stably operate the flow path switching valve for a long time under such a severe condition, and in this sense, it can be said that the technique is poor in feasibility. Furthermore, for efficient gasification of waste plastic, it is necessary to continuously supply COG containing 60 vol% or more of hydrogen to the hydrocracking reactor. In addition, it is necessary to install a hydrogen concentration meter and a flow path switching valve, which increases the equipment cost.

また、特許文献2の方法は、FCC触媒の添加によって接触分解と芳香族化が進むものの、不活性ガスフローで反応を行っているため、重油分とコークが合計で13質量%生成しており(実施例1)、軽質燃料の製造技術として満足できる水準とは言えない。
また、特許文献3の方法で生成するガスは、H、CO、COが主体で、燃焼熱が冶金炉発生排ガスのそれよりやや低い1800kcal/Nm程度のものであり、気体燃料としての価値は限定的なものとなる。
さらに、廃プラスチックなどの高分子量有機物質を分解して、気体生成物や液体生成物に転換するにあたり、固体状残渣の生成を完全に抑制することは困難である。しかしながら、固体状残渣を有効活用する方法は殆ど知られていないのが現状である。
Moreover, although the method of patent document 2 advances catalytic cracking and aromatization by addition of an FCC catalyst, since it reacts by an inert gas flow, 13 mass% of heavy oil components and coke are produced | generated in total. (Example 1) It cannot be said that it is a satisfactory level as a light fuel production technology.
Further, the gas generated by the method of Patent Document 3 is mainly H 2 , CO, and CO 2 , and the combustion heat is about 1800 kcal / Nm 3 that is slightly lower than that of the exhaust gas generated from the metallurgical furnace. The value is limited.
Furthermore, it is difficult to completely suppress the formation of a solid residue when decomposing a high molecular weight organic substance such as waste plastic to convert it into a gas product or a liquid product. However, at present, there are few known methods for effectively utilizing the solid residue.

したがって本発明の目的は、廃プラスチックなどの有機物質を低分子化して気体生成物や液体生成物などに転換する際に、安定的に供給可能なガスを用いて有機物質を効率的に改質して低分子化し、重質分や炭素質が少なく、軽質分を多量に含有する改質物を得ることができとともに、低分子化反応で生じた固体状残渣を有効利用することができる有機物質の利材化方法を提供することにある。   Accordingly, the object of the present invention is to efficiently reform organic substances using gases that can be stably supplied when converting organic substances such as waste plastics into gas products or liquid products by reducing the molecular weight. Organic substances that can be reduced in molecular weight, have a heavy or carbonaceous content, and can be modified to contain a large amount of light components, and can effectively use the solid residue generated in the molecular weight reduction reaction It is to provide a method for making a profit.

本発明者らは、上記課題を解決するため検討を重ねた結果、冶金炉で発生する一酸化炭素を含有する排ガスに過剰の水蒸気を添加してシフト反応を行わせ、このシフト反応後のガス、すなわちシフト反応で生成した水素および炭酸ガスと残存した水蒸気とを含む混合ガスを用い、高分子量の有機物質を改質して低分子化する方法によれば、安定的に供給可能なガスを用いて有機物質を効率的に改質して低分子化し、重質分や炭素質が少なく、軽質分を多量に含有する改質物を得ることができ、しかも、低分子化反応で生じた固体状残渣を、製鉄所などで行われる製造または処理プロセスにおいて、炭素材料として有効利用できることを見出した。また、有機物質の改質を鉄系触媒の存在下で行う場合には、低分子化反応で生じた固体状残渣を、製鉄所などで行われる製造または処理プロセスにおいて、鉄源を含有する炭素材料として有効利用できることを見出した。   As a result of repeated studies to solve the above-mentioned problems, the inventors of the present invention added an excessive water vapor to an exhaust gas containing carbon monoxide generated in a metallurgical furnace to cause a shift reaction, and a gas after the shift reaction. In other words, according to the method of reforming a high molecular weight organic substance and reducing the molecular weight using a mixed gas containing hydrogen and carbon dioxide generated by the shift reaction and the remaining water vapor, a gas that can be supplied stably can be obtained. It can be used to efficiently modify organic substances to lower the molecular weight, resulting in a modified product containing less heavy and carbon, and containing a large amount of lighter components, and solids generated by the lowering reaction. It has been found that the residue can be effectively used as a carbon material in a manufacturing or processing process performed at a steel mill or the like. In addition, when organic substances are reformed in the presence of an iron-based catalyst, the solid residue produced by the low molecular weight reaction is converted into carbon containing an iron source in a production or treatment process performed at a steel mill or the like. We found that it can be used effectively as a material.

本発明はこのような知見に基づきなされたもので、以下を要旨とするものである。
[1]冶金炉で発生した一酸化炭素を含有する排ガス(g)に過剰の水蒸気を添加してシフト反応を行わせることで、シフト反応で生成した水素および炭酸ガスと、シフト反応に消費されなかった水蒸気とを含む混合ガス(g)とし、この混合ガス(g)を有機物質に接触させることにより、有機物質を改質して低分子化する反応を生じさせ、該反応により生じた有機物質の低分子化改質物と固体状残渣を回収し、該固体状残渣を炭素材料として利材化することを特徴とする有機物質の利材化方法。
The present invention has been made on the basis of such findings and has the following gist.
[1] Addition of excess water vapor to the exhaust gas (g 0 ) containing carbon monoxide generated in the metallurgical furnace to cause the shift reaction to consume the hydrogen and carbon dioxide generated by the shift reaction and the shift reaction A mixed gas (g) containing water vapor that has not been produced is brought into contact with the organic substance to cause a reaction to modify the organic substance to reduce the molecular weight, and the reaction is caused by the reaction. A method for producing a material for an organic material, comprising recovering a low molecular weight modified product of the organic material and a solid residue, and using the solid residue as a carbon material.

[2]冶金炉で発生した一酸化炭素を含有する排ガス(g)に過剰の水蒸気を添加してシフト反応を行わせることで、シフト反応で生成した水素および炭酸ガスと、シフト反応に消費されなかった水蒸気とを含む混合ガス(g)とし、この混合ガス(g)を鉄系触媒の存在下、有機物質に接触させることにより、有機物質を改質して低分子化する反応を生じさせ、該反応により生じた有機物質の低分子化改質物と固体状残渣を回収し、該固体状残渣を鉄源を含有する炭素材料として利材化することを特徴とする有機物質の利材化方法。
[3]上記[2]の方法において、鉄系触媒が転炉ダストであることを特徴とする有機物質の利材化方法。
[2] Addition of excess water vapor to the exhaust gas (g 0 ) containing carbon monoxide generated in the metallurgical furnace to cause the shift reaction, and hydrogen and carbon dioxide generated by the shift reaction are consumed for the shift reaction. A mixed gas (g) containing water vapor that has not been produced is brought into contact with an organic substance in the presence of an iron-based catalyst, thereby causing a reaction that modifies the organic substance to lower its molecular weight. And recovering a low molecular weight modified product and a solid residue of the organic substance generated by the reaction, and using the solid residue as a carbon material containing an iron source. Method.
[3] A method for making an organic material into use in the method of [2] above, wherein the iron-based catalyst is converter dust.

[4]上記[1]〜[3]のいずれかの方法において、排ガス(g)が、冶金炉で発生した一酸化炭素と窒素を含有する排ガスから窒素の少なくとも一部を分離することで一酸化炭素濃度を高めた排ガスであることを特徴とする有機物質の利材化方法。
[5]上記[1]〜[4]のいずれかの方法において、混合ガス(g)の水蒸気濃度が5〜70vol%であることを特徴とする有機物質の利材化方法。
[6]上記[5]の方法において、混合ガス(g)は、水蒸気濃度が20〜70vol%、水素濃度が10〜40vol%、炭酸ガス濃度が10〜40vol%であることを特徴とする有機物質の利材化方法。
[7]上記[1]〜[6]のいずれかの方法において、改質される有機物質が、廃プラスチック、含油スラッジ、廃油、バイオマスの中から選ばれる1種以上であることを特徴とする有機物質の利材化方法。
[4] In any one of the above methods [1] to [3], the exhaust gas (g 0 ) separates at least a part of nitrogen from the exhaust gas containing carbon monoxide and nitrogen generated in the metallurgical furnace. A method for converting an organic substance into a material, characterized in that the exhaust gas has an increased carbon monoxide concentration.
[5] A method for producing an organic material, wherein the mixed gas (g) has a water vapor concentration of 5 to 70 vol% in any of the methods [1] to [4].
[6] In the method of [5] above, the mixed gas (g) is characterized in that the water vapor concentration is 20 to 70 vol%, the hydrogen concentration is 10 to 40 vol%, and the carbon dioxide concentration is 10 to 40 vol%. How to make a material profitable.
[7] The method according to any one of [1] to [6] above, wherein the organic substance to be modified is at least one selected from waste plastic, oil-containing sludge, waste oil, and biomass. How to make organic materials.

[8]上記[1]〜[7]のいずれかの方法において、固体状残渣を、製鉄所で行われる製造または処理プロセスにおいて炭素材料として利用することを特徴とする有機物質の利材化方法。
[9]上記[8]の方法において、製鉄所で行われる製造または処理プロセスが、焼結鉱製造プロセス、コークス製造プロセス、転炉脱炭プロセス、高炉プロセスのうちの1つ以上のプロセスであることを特徴とする有機物質の利材化方法。
[10]上記[1]〜[9]のいずれかの方法において、回収された有機物質の低分子化改質物を、製鉄所内で燃料および/または還元剤として利用することを特徴とする有機物質の利材化方法。
[11]上記[10]の方法において、回収された有機物質の低分子化改質物を高炉に吹き込むことを特徴とする有機物質の利材化方法。
[8] In the method according to any one of the above [1] to [7], the solid residue is used as a carbon material in a production or treatment process performed at a steel mill, .
[9] In the method of [8] above, the production or treatment process performed at the steel mill is one or more of a sintered ore production process, a coke production process, a converter decarburization process, and a blast furnace process. A method for converting an organic material into a material.
[10] The organic material according to any one of the above [1] to [9], wherein the low molecular weight reformed product of the recovered organic material is used as a fuel and / or a reducing agent in an ironworks. How to make a profit.
[11] A method for producing an organic material that is characterized in that, in the method of [10], the recovered low molecular weight modified product of the organic material is blown into a blast furnace.

本発明によれば、廃プラスチックなどの高分子量の有機物質を低分子化して気体生成物や液体生成物に転換する際に、安定的に供給可能なガスを用いて有機物質を効率的に改質して低分子化することで軽質分を多量に含有する高カロリーの改質物を得ることができるとともに、発生する少量の固体状残渣も炭素材料として、或いは鉄源を含有する炭素材料として、製鉄所などで行われる製造または処理プロセスにおいて有効利用することができる。このため廃プラスチックなどの高分子量有機物質を、エミッションレスでケミカルリサイクルすることが可能となる。
また、実施設備に関しても、特別な計測器や流路切替弁などが必要なく、しかも比較的低い反応温度でも有機物質の改質を行うことができるので、比較的簡易な設備で実施することができる。また、シフト反応によって生成するCOは、有機物質の改質中に炭酸ガス改質反応でCOに変化するため、有機物質のケミカルリサイクルをCO発生量を増加させることなく実施することが可能となる。
According to the present invention, when a high molecular weight organic substance such as waste plastic is reduced in molecular weight and converted into a gas product or a liquid product, the organic substance is efficiently modified using a gas that can be stably supplied. As a result, it is possible to obtain a high-calorie modified product containing a large amount of light components by reducing the molecular weight, and a small amount of solid residue generated as a carbon material or as a carbon material containing an iron source, It can be effectively used in manufacturing or processing processes performed at steelworks or the like. For this reason, it is possible to chemically recycle high molecular weight organic substances such as waste plastics without emission.
Also, with regard to the implementation equipment, there is no need for special measuring instruments or flow path switching valves, and the organic substance can be reformed even at a relatively low reaction temperature. it can. In addition, since CO 2 produced by the shift reaction changes to CO during the reforming of the organic material, it is possible to carry out chemical recycling of the organic material without increasing the amount of CO 2 generated. It becomes.

転炉ガスに水蒸気を添加して行うシフト反応において、水蒸気の添加量とシフト反応後のガスの組成(温度430℃における平衡組成計算値)との関係を示すグラフIn the shift reaction performed by adding water vapor to the converter gas, a graph showing the relationship between the amount of water vapor added and the composition of the gas after the shift reaction (calculated equilibrium composition at a temperature of 430 ° C.) 実施例において、シフト反応生成ガスの水蒸気濃度と、ポリエチレンの改質(低分子化)におけるガス化率および液化率との関係を示すグラフIn an Example, the graph which shows the relationship between the water vapor | steam density | concentration of shift reaction product gas, and the gasification rate and liquefaction rate in the modification | reformation (low molecular weight) of polyethylene 実施例において、シフト反応生成ガスの水蒸気濃度と、ポリエチレンの改質(低分子化)で得られた気体生成物および液体生成物のLHVとの関係を示すグラフIn an Example, the graph which shows the relationship between the water vapor | steam density | concentration of a shift reaction product gas, and LHV of the gas product obtained by the modification | reformation (low molecular weight reduction) of polyethylene. 実施例において、シフト反応生成ガスの水蒸気濃度と、ポリエチレンの改質(低分子化)におけるポリエチレン分解率との関係を示すグラフIn an Example, the graph which shows the relationship between the water vapor | steam density | concentration of shift reaction product gas, and the polyethylene decomposition rate in the modification | reformation (low molecular weight) of polyethylene 実施例において、シフト反応生成ガスの炭酸ガス濃度と、ポリエチレンの改質(低分子化)で得られた気体生成物の水素濃度との関係を示すグラフIn an Example, the graph which shows the relationship between the carbon dioxide gas concentration of shift reaction product gas, and the hydrogen concentration of the gas product obtained by the modification | reformation (low molecular weight reduction) of polyethylene 実施例において、シフト反応生成ガスの水素濃度と、ポリエチレンの改質(低分子化)で得られた気体生成物の炭酸ガス濃度との関係を示すグラフIn an Example, the graph which shows the relationship between the hydrogen concentration of shift reaction product gas, and the carbon dioxide gas concentration of the gas product obtained by the modification | reformation (low molecular weight reduction) of polyethylene 実施例(発明例11)で用いた設備を模式的に示す説明図Explanatory drawing which shows typically the equipment used in the Example (Invention Example 11)

本発明法では、冶金炉で発生した一酸化炭素を含有する排ガス(g)(以下、「冶金炉発生排ガス」という場合がある)に過剰の水蒸気を添加してシフト反応を行わせることで、シフト反応で生成した水素および炭酸ガスと、シフト反応に消費されなかった水蒸気とを含む混合ガス(g)とし、この混合ガス(g)(以下「シフト反応生成ガス」という場合がある。)を有機物質に接触させることにより、有機物質を改質して低分子化する反応を生じさせ、この反応により生じた有機物質の低分子化改質物と固体状残渣(少量)を回収し、この固体状残渣を、炭素材料として製鉄所などで行われる製造または処理プロセスにおいて利材化する。或いは、有機物質の低分子化反応を鉄系触媒の存在下で行い、この反応により生じた有機物質の低分子化改質物と固体状残渣(少量)を回収し、この固体状残渣を、鉄源を含有する炭素材料として、製鉄所などで行われる製造または処理プロセスにおいて利材化する。
なお、排ガス(g)に過剰の水蒸気を添加するとは、シフト反応で消費されない余剰の水蒸気が混合ガス(g)中に残存するように水蒸気を添加するという意味である。
In the method of the present invention, an excess water vapor is added to an exhaust gas (g 0 ) containing carbon monoxide generated in a metallurgical furnace (hereinafter sometimes referred to as “metallurgical furnace generated exhaust gas”) to cause a shift reaction. A mixed gas (g) containing hydrogen and carbon dioxide gas generated in the shift reaction and water vapor not consumed in the shift reaction, and this mixed gas (g) (hereinafter sometimes referred to as “shift reaction product gas”). Is brought into contact with an organic substance to cause a reaction to modify the organic substance to reduce the molecular weight, and the low molecular weight modified product of the organic substance and a solid residue (small amount) generated by this reaction are recovered. The solid residue is used as a carbon material in a manufacturing or processing process performed at a steel mill or the like. Alternatively, the molecular weight reduction reaction of the organic substance is performed in the presence of an iron-based catalyst, and the low molecular weight modified product of the organic substance and a solid residue (small amount) generated by this reaction are recovered. As a carbon material containing a source, it is used as a material in a manufacturing or processing process performed at a steel mill or the like.
Note that adding excess steam to the exhaust gas (g 0 ) means adding steam so that excess steam that is not consumed in the shift reaction remains in the mixed gas (g).

このような本発明法では、比較的低い反応温度でも効率的に有機物質の低分子化が促進され、水素消費量も少なく、且つ重質分や炭素質の生成もほとんど認められない。
一般に廃プラスチックなどの高分子量有機物質は、300〜400℃以上で加熱すると熱分解が始まることが知られているが、この時、軽質化とともに重質化も進行してしまう。熱分解時に水素を共存させると、炭化水素種への水素付加反応と水素化分解反応が進行するため、重質化抑制と低分子化に有効である。しかしながら、水素化分解に高温が必要であり、且つ水素消費量が多くなることが問題である。
In such a method of the present invention, the reduction of the molecular weight of the organic substance is efficiently promoted even at a relatively low reaction temperature, the hydrogen consumption is small, and the generation of heavy components and carbonaceous matter is hardly observed.
Generally, high molecular weight organic substances such as waste plastic are known to start thermal decomposition when heated at a temperature of 300 to 400 ° C. or higher, but at this time, they become lighter and heavier. Coexistence of hydrogen during thermal decomposition is effective in suppressing heavy formation and reducing the molecular weight because hydrogen addition reaction and hydrocracking reaction to hydrocarbon species proceed. However, the high temperature is required for hydrocracking, and the hydrogen consumption is a problem.

一方、水蒸気改質や炭酸ガス改質は、HOやCO分子中の酸素による炭化水素の酸化と看做すことができ、少ない水素添加量で低分子化と炭素質生成抑制が達成できる。さらに、水蒸気改質や炭酸ガス改質は、改質される有機分子の炭素鎖が長くなるにつれて反応温度が低下するという特徴を有する。本発明法において、比較的低い反応温度でも効率的に有機物質の低分子化が促進され、水素消費量も少なく、且つ重質分や炭素質の生成もほとんど認められないのは、上記混合ガス(g)を用いて有機物質の改質(低分子化)を行うことにより、水素化、水素化分解、水蒸気改質、炭酸ガス改質の4反応が同時に進行するためであると考えられる。
なお、前記水素化反応としては、炭化水素種への水素付加反応だけではなく、メタンなどの軽質炭化水素を生成するCOやCOへの水素付加反応も進行していることが気体生成物の分析結果から示唆される。本発明の説明では簡単のため、COやCOへの水素付加反応を炭化水素種への水素化反応と区別することなく、単に水素化(または水素化反応)として記述した。
On the other hand, steam reforming and carbon dioxide reforming can be regarded as oxidation of hydrocarbons by oxygen in H 2 O and CO 2 molecules, achieving low molecular weight and suppressing carbonaceous production with a small amount of hydrogen addition. it can. Furthermore, steam reforming and carbon dioxide reforming are characterized in that the reaction temperature decreases as the carbon chain of the organic molecule to be modified becomes longer. In the method of the present invention, the low molecular weight of an organic substance is efficiently promoted even at a relatively low reaction temperature, the amount of hydrogen consumption is small, and the generation of heavy components and carbonaceous matter is hardly recognized. It is considered that the four reactions of hydrogenation, hydrocracking, steam reforming, and carbon dioxide reforming proceed simultaneously by reforming (reducing molecular weight) the organic substance using (g).
Incidentally, as the hydrogenation reaction, not only hydrogenation reaction to hydrocarbon species, that is gaseous products that also proceed hydrogenation reaction to CO and CO 2 to produce a light hydrocarbon such as methane It is suggested from the analysis results. In the description of the present invention, for the sake of simplicity, the hydrogenation reaction to CO or CO 2 is simply described as hydrogenation (or hydrogenation reaction) without being distinguished from the hydrogenation reaction to hydrocarbon species.

例えば、転炉などの冶金炉から発生する排ガスには、通常、COが25〜80vol%程度含有されている。したがって、これに水蒸気を添加すると、下記のシフト反応(1)によってHとCOが生成する。
CO+HO→H+CO …(1)
本発明法では、排ガス(g)に過剰の水蒸気が添加されるので、シフト反応後の混合ガス(g)には、シフト反応により生成したH、COと過剰添加分のHOが含まれることになる。そして、このシフト反応生成ガス(g)による有機物質の改質(低分子化)では、各ガス成分による水素化、水素化分解、水蒸気改質、炭酸ガス改質の4反応が同時進行するものと考えられる。
For example, the exhaust gas generated from a metallurgical furnace such as a converter usually contains about 25 to 80 vol% of CO. Therefore, when water vapor is added thereto, H 2 and CO 2 are generated by the following shift reaction (1).
CO + H 2 O → H 2 + CO 2 (1)
In the method of the present invention, since excess water vapor is added to the exhaust gas (g 0 ), the mixed gas (g) after the shift reaction includes H 2 , CO 2 generated by the shift reaction, and H 2 O of excess addition. Will be included. In the reforming of organic substances (lower molecular weight) by this shift reaction product gas (g), four reactions of hydrogenation, hydrocracking, steam reforming, and carbon dioxide reforming by each gas component proceed simultaneously. it is conceivable that.

本発明では、排ガス(g)に対して過剰に添加する水蒸気の過剰割合やシフト反応の反応率を適宜制御することによって、ガス中の水蒸気、水素、炭酸ガスの各濃度を制御し、有機物質改質用の混合ガス(g)とすることができる。ただし、ガスホルダー(例えば、製鉄所内で使用されている一般的なガスホルダー)に貯蔵される冶金炉発生排ガスの一般的組成は、CO:50〜70vol%、CO:10〜20vol%、N:10〜20vol%、H:0〜5vol%(他に飽和水蒸気を含む)程度であるため、一般には、シフト反応の反応率制御まで行う必要はなく、水蒸気の過剰割合を調整するだけで、混合ガス(g)の水蒸気、水素、炭酸ガスの各濃度を所望のレベルに制御することができる。
なお、シフト反応の反応率は、シフト反応器内での滞留時間を調整することで制御することができる。例えば、滞留時間を短くするには、シフト反応器長さを小さくしたり、或いは触媒充填量を少なくする方法が一般的であり、その場合、シフト反応器長さや触媒充填量は、ほぼ平衡まで反応を進行させる場合の1/2〜1/4程度とすればよい。
In the present invention, the concentration of water vapor, hydrogen, and carbon dioxide in the gas is controlled by appropriately controlling the excess ratio of water vapor added excessively to the exhaust gas (g 0 ) and the reaction rate of the shift reaction. A mixed gas (g) for material modification can be obtained. However, the general composition of the metallurgical furnace generated exhaust gas stored in the gas holder (for example, a general gas holder used in a steelworks) is CO: 50 to 70 vol%, CO2: 10 to 20 vol%, N 2: 10~20vol%, H 2: because of the order 0~5vol% (including other saturated steam) generally is not necessary to carry out until the reaction rate control of the shift reaction, only by adjusting the excess percentage of water vapor Thus, each concentration of water vapor, hydrogen and carbon dioxide in the mixed gas (g) can be controlled to a desired level.
The reaction rate of the shift reaction can be controlled by adjusting the residence time in the shift reactor. For example, in order to shorten the residence time, a method in which the shift reactor length is reduced or the catalyst charge amount is reduced is generally used. In this case, the shift reactor length and the catalyst charge amount are almost until equilibrium. What is necessary is just to set it as about 1 / 2-1 / 4 in the case of advancing reaction.

一例として、CO:65vol%、CO:15vol%、N:18vol%、H:1vol%、HO:1vol%からなる組成の転炉ガス100kmol/h(=2240Nm/h)に、水蒸気の添加量を60kmol/h(=1340Nm/h)から540kmol/h(=12100Nm/h)まで変化させてシフト反応を行う場合について、水蒸気添加量とシフト反応後のガスの組成(温度430℃における平衡組成計算値)を図1に示す。これによれば、水蒸気添加量を調整するだけで、混合ガス(g)の水蒸気、水素、炭酸ガスの各濃度を制御でき、後述するような好ましいガス組成にできることが判る。なお、シフト反応は、通常、ほぼ平衡まで反応が進行することはよく知られている。 As an example, converter gas of 100 kmol / h (= 2240 Nm 3 / h) having a composition of CO: 65 vol%, CO 2 : 15 vol%, N 2 : 18 vol%, H 2 : 1 vol%, H 2 O: 1 vol% In the case of performing the shift reaction by changing the amount of water vapor added from 60 kmol / h (= 1340 Nm 3 / h) to 540 kmol / h (= 1100 Nm 3 / h), the amount of water vapor added and the composition of the gas after the shift reaction ( The calculated equilibrium composition at a temperature of 430 ° C. is shown in FIG. According to this, it can be seen that the concentration of water vapor, hydrogen, and carbon dioxide in the mixed gas (g) can be controlled only by adjusting the amount of water vapor added, and a preferable gas composition as described later can be obtained. In addition, it is well known that the shift reaction usually proceeds to almost equilibrium.

以下、本発明法の詳細と好ましい条件について説明する。
本発明において、シフト反応させる排ガス(g)として冶金炉発生排ガスを用いる理由は、冶金炉発生排ガスは比較的高濃度に一酸化炭素を含有し、且つ不要な窒素の濃度が低いためである。一酸化炭素を含有する冶金炉発生排ガス(g)としては、任意のものが使用できる。最も代表的なものは、鉄鋼製造プロセスの脱炭工程が行われる転炉から発生する転炉ガスであるが、それ以外にも、例えば、溶銑予備処理炉、溶融還元炉、シャフト炉などから発生する排ガスを例示することができ、これらの1種または2種以上の混合ガスを用いることができる。
冶金プロセスで生成する一酸化炭素が、さらに酸化されて二酸化炭素が生成する割合である二次燃焼率(CO/(CO+CO)×100)は、一般に10〜50%程度に過ぎない。また、排ガス(g)中には水素と窒素も含まれるが、H濃度は冶金プロセスに応じて変化し、0〜20vol%程度である。窒素は、炉内撹拌や煙道保安などのために供給されており、通常、排ガス(g)中の濃度は10〜30vol%程度である。
Hereinafter, details and preferred conditions of the method of the present invention will be described.
In the present invention, the reason why the metallurgical furnace generated exhaust gas is used as the exhaust gas (g 0 ) for the shift reaction is that the metallurgical furnace generated exhaust gas contains carbon monoxide at a relatively high concentration and the concentration of unnecessary nitrogen is low. . As the metallurgical furnace-generated exhaust gas (g 0 ) containing carbon monoxide, any one can be used. The most representative is the converter gas generated from the converter where the decarburization process of the steel manufacturing process is performed, but other than that, for example, it is generated from a hot metal pretreatment furnace, a smelting reduction furnace, a shaft furnace, etc. Exhaust gas to be used can be exemplified, and one kind or a mixture of two or more kinds thereof can be used.
The secondary combustion rate (CO 2 / (CO + CO 2 ) × 100), which is the rate at which carbon monoxide produced in the metallurgical process is further oxidized to produce carbon dioxide, is generally only about 10 to 50%. Also, in the exhaust gas (g 0) are also included hydrogen and nitrogen, H 2 concentration varies depending on the metallurgical process, it is about 0~20vol%. Nitrogen is supplied for in-furnace agitation and flue safety, and the concentration in the exhaust gas (g 0 ) is usually about 10 to 30 vol%.

以上の点から、一般的な冶金炉発生排ガス(g)の組成は、概ね以下のような範囲となる。
CO:80〜25vol%(二次燃焼率10〜50%に相当)
CO:10〜25vol%(二次燃焼率10〜50%に相当)
:10〜30vol%
:0〜20vol%
シフト反応には一酸化炭素が必要であるが、ガスの組成が上記の範囲であれば、排ガス(g)の組成に特段の問題はない。ここで、窒素は本発明で生じる化学反応(シフト反応、水素化、水素化分解、水蒸気改質、炭酸ガス改質)には何ら寄与せず、一方において、製造される気体生成物を希釈し、低位燃焼熱(以下、「LHV」という)を低下させる。特に、窒素濃度が50vol%を超えると、気体生成物のLHVの低下が顕著になるとともに、シフト反応速度も低下する傾向になる。このため窒素濃度は上記組成範囲内であることが好ましい。
From the above points, the composition of general metallurgical furnace-generated exhaust gas (g 0 ) is generally in the following range.
CO: 80-25 vol% (equivalent to 10-50% secondary combustion rate)
CO 2: 10~25vol% (corresponding to the secondary combustion rate 10-50%)
N 2: 10~30vol%
H2: 0 to 20 vol%
Although carbon monoxide is required for the shift reaction, there is no particular problem with the composition of the exhaust gas (g 0 ) as long as the gas composition is in the above range. Here, nitrogen does not contribute at all to the chemical reactions (shift reaction, hydrogenation, hydrocracking, steam reforming, carbon dioxide reforming) that occur in the present invention, while diluting the gas product produced. , Lower combustion heat (hereinafter referred to as “LHV”). In particular, when the nitrogen concentration exceeds 50 vol%, the LHV of the gas product is significantly reduced and the shift reaction rate tends to be reduced. Therefore, the nitrogen concentration is preferably within the above composition range.

さきに述べたように、ガスホルダー(例えば、製鉄所内で使用されている一般的なガスホルダー)に貯蔵される冶金炉発生排ガスの一般的組成は、CO:50〜70vol%、CO:10〜20vol%、N:10〜20vol%、H:0〜5vol%(他に飽和水蒸気を含む)程度であり、この組成は、上記の一般的な冶金炉発生排ガスの組成の中で高CO濃度組成に相当する。ガスホルダーに貯蔵されたガスは、製鉄所内の各工場で燃料ガスとして利用するため、利用先での燃焼効率の低下を防止する必要がある。そのため、ガス中CO濃度の下限値をガスホルダーへの貯蔵条件として設定しておくことが、高CO濃度組成になっている理由である。
本発明では、製鉄所内で使用されている一般的なガスホルダーに貯蔵されているような比較的CO濃度が高い排ガスであっても、上記のような一般的な冶金炉発生排ガスの組成であっても、排ガス(g)として利用することができる。
As mentioned earlier, gas holder (e.g., typical gas holder used in steelworks) General composition of metallurgical furnace generation exhaust gas to be stored in the, CO: 50~70vol%, CO 2 : 10 ˜20 vol%, N 2 : 10 to 20 vol%, H 2 : 0 to 5 vol% (including saturated steam in addition), and this composition is high in the composition of the above general metallurgical furnace generated exhaust gas. It corresponds to the CO concentration composition. Since the gas stored in the gas holder is used as fuel gas at each factory in the steelworks, it is necessary to prevent a decrease in combustion efficiency at the use destination. Therefore, setting the lower limit value of the CO concentration in the gas as a storage condition in the gas holder is the reason why the composition has a high CO concentration.
In the present invention, the composition of the exhaust gas generated in the general metallurgical furnace as described above is used even if the exhaust gas has a relatively high CO concentration as stored in a general gas holder used in a steelworks. However, it can be used as exhaust gas (g 0 ).

ところで、冶金炉発生排ガス(g)のなかには、一酸化炭素を含有するものの、窒素濃度が比較的高いものがあり、このような冶金炉発生排ガス(g)については、含有する窒素の少なくとも一部を分離(除去)して一酸化炭素濃度を高めた上で、過剰の水蒸気を添加してシフト反応を行わせるようにしてもよい。
窒素分離をするのが好ましい代表的な排ガスとしては、高炉ガスを挙げることができるが、この他にも電炉や窒素濃度が高くなる条件で操業しているシャフト炉の発生排ガスなどを挙げることができる。なお、転炉ガスなどのように、比較的高濃度の一酸化炭素を含有する排ガスについて窒素の分離を行い、一酸化炭素濃度をさらに高めた上で、シフト反応を行うこともできる。
By the way, some of the metallurgical furnace-generated exhaust gas (g 0 ) contains carbon monoxide but has a relatively high nitrogen concentration. Such a metallurgical furnace-generated exhaust gas (g 0 ) contains at least nitrogen contained therein. A part may be separated (removed) to increase the carbon monoxide concentration, and then an excess of water vapor may be added to cause the shift reaction.
As typical exhaust gas that is preferably subjected to nitrogen separation, blast furnace gas can be mentioned, but in addition to this, exhaust gas generated from an electric furnace or a shaft furnace operating under a condition where the nitrogen concentration becomes high can be mentioned. it can. In addition, the nitrogen gas is separated from an exhaust gas containing a relatively high concentration of carbon monoxide such as a converter gas, and the shift reaction can be performed after further increasing the carbon monoxide concentration.

排ガスから窒素を分離する方法に特別な制限はなく、吸着分離法、蒸留分離法など任意の方法を適用することができるが、窒素と一酸化炭素の沸点差が小さいことから、吸着分離法が特に好ましい。例えば、CO吸着剤として知られているCuを担持した活性炭はCOも吸着するため、Cu担持活性炭を吸着剤とするPSA法によって、高炉ガス(概略組成:N:50vol%、CO:25vol%、CO:25vol%)から脱着ガスとして概略組成がN:15vol%、CO:45vol%、CO:40vol%のガスを得ることができ、これは高炉ガス中の窒素を分離して一酸化炭素を濃縮したことになる。 There is no particular restriction on the method for separating nitrogen from exhaust gas, and any method such as adsorption separation method or distillation separation method can be applied. However, since the boiling point difference between nitrogen and carbon monoxide is small, the adsorption separation method is Particularly preferred. For example, since activated carbon supporting Cu + , which is known as a CO adsorbent, also adsorbs CO 2 , blast furnace gas (general composition: N 2 : 50 vol%, CO 2 ) is obtained by PSA method using Cu + supported activated carbon as an adsorbent. : 25vol%, CO 2: approximate composition as desorbed gas from 25 vol%) is N 2: 15vol%, CO: 45vol%, CO 2: it is possible to obtain a 40 vol% of the gas, which separates the nitrogen in the blast furnace gas Thus, the carbon monoxide is concentrated.

本発明法でのシフト反応は公知の手法で行えばよく、特別な制限はない。一般的には、冶金炉発生排ガス(g)に事前に水蒸気を添加しておき、これを触媒が充填された固定床反応器に導入してシフト反応を行う。また、事前に添加する水蒸気を一部とし、反応器内に触媒を多段で充填し、触媒層と触媒層との間から残りの水蒸気を添加するようにしてもよい。
なお、本発明のようなシフト反応を行うことなく、冶金炉発生排ガス(g)に水蒸気、水素、炭酸ガスをそれぞれ添加すれば、本発明のシフト反応で得られる有機物質改質用の混合ガス(g)と同等の組成のガスを得ることはできるが、このような方法では、水蒸気に加えて、高価な水素ガスと炭酸ガスを添加しなければならず、コスト高となる。
The shift reaction in the method of the present invention may be carried out by a known method and is not particularly limited. Generally, water vapor is added to the metallurgical furnace-generated exhaust gas (g 0 ) in advance, and this is introduced into a fixed bed reactor filled with a catalyst to perform a shift reaction. Alternatively, the water vapor to be added in advance may be partially used, the catalyst may be packed in multiple stages in the reactor, and the remaining water vapor may be added between the catalyst layer and the catalyst layer.
If water vapor, hydrogen, and carbon dioxide are added to the metallurgical furnace-generated exhaust gas (g 0 ) without performing the shift reaction as in the present invention, the mixture for organic substance modification obtained by the shift reaction in the present invention is used. Although a gas having a composition equivalent to that of the gas (g) can be obtained, in such a method, in addition to water vapor, expensive hydrogen gas and carbon dioxide gas must be added, resulting in an increase in cost.

本発明において、シフト反応で得られる有機物質改質用の混合ガス(g)は、水蒸気、水素および炭酸ガスを含むものであり、それらの濃度に特別な制限はないが、以下のような理由から、水蒸気濃度は5〜70vol%であることが好ましい。すなわち、水蒸気濃度が低いと廃プラスチックなどの有機物質の分解率が低くなるが、水蒸気濃度を5vol%以上とすることにより、一定水準の有機物質の分解率を確保でき、気体生成物の生成率(ガス化率)・液体生成物の生成率(液化率)を一定の水準にできるとともに、発生する固体状残渣である重質分の生成量を少なくできる。一方、水蒸気濃度が高いと有機物質の改質反応生成ガス(有機物質の改質による低分子化で生成したガス。以下同様)中にCOが残留しやすくなるとともに、気体生成物・液体生成物のLHVが低下しやすくなるが、水蒸気濃度が70vol%以下であれば、改質反応生成ガス中でのCOの残留を抑えることができ、また、気体生成物・液体生成物のLHVの低下も抑えることができる。
また、有機物質の分解率を確保し、固体状残渣を少なくする観点から、混合ガス(g)の水素濃度および炭酸ガス濃度はともに5vol%以上が好ましい。
In the present invention, the mixed gas (g) for reforming the organic substance obtained by the shift reaction contains water vapor, hydrogen and carbon dioxide gas, and there is no particular limitation on the concentration thereof. Therefore, the water vapor concentration is preferably 5 to 70 vol%. In other words, when the water vapor concentration is low, the decomposition rate of organic substances such as waste plastics is low. However, by setting the water vapor concentration to 5 vol% or more, a certain level of organic material decomposition rate can be secured, and the rate of production of gas products. (Gasification rate)-The production rate (liquefaction rate) of the liquid product can be kept at a constant level, and the production amount of heavy components, which are solid residues, can be reduced. On the other hand, when the water vapor concentration is high, CO 2 tends to remain in the reforming reaction product gas of the organic substance (gas generated by low molecular weight reforming of the organic substance; the same applies hereinafter), and also a gas product / liquid production However, if the water vapor concentration is 70 vol% or less, the residual CO 2 in the reforming reaction product gas can be suppressed, and the LHV of the gas product / liquid product can be reduced. The decrease can also be suppressed.
Further, from the viewpoint of securing the decomposition rate of the organic substance and reducing the solid residue, both the hydrogen concentration and the carbon dioxide gas concentration of the mixed gas (g) are preferably 5 vol% or more.

また、以下のような理由から、有機物質改質用の混合ガス(g)のより好ましい組成は、水蒸気濃度:20〜70vol%、水素濃度:10〜40vol%、炭酸ガス濃度:10〜40vol%である。なお、この混合ガス(g)に、他のガス成分(例えば、窒素など)が含まれることは妨げない。水蒸気濃度を20vol%以上とすることにより、有機物質の分解率を十分に高めることができるとともに、気体生成物のLHVを高くすることができる。水蒸気濃度を70vol%以下とする理由は、さきに述べたとおりである。水素濃度を10vol%以上(より好ましくは12vol%以上)とすることにより、特に、比較的低温で有機物質の改質反応を行った場合でも、気体生成物中にCOが残留することを抑えることができる。炭酸ガス濃度を10vol%以上(より好ましくは13vol%以上)とすることにより、気体生成物中に炭化水素やCOに比べて低カロリーのガス成分であるHが残留しにくくなる。また、水素濃度や炭酸ガス濃度を40vol%以下とすることにより、廃プラスチックなどの有機物質の分解率を好ましいレベルにし、固体状残渣を少なくすることができる。また、以上のような観点から、混合ガス(g)のより好ましいガス組成は、水蒸気濃度:25〜65vol%、水素濃度:15〜35vol%、炭酸ガス濃度:15〜35vol%である。なお、この混合ガス(g)に、他のガス成分(例えば、窒素など)が含まれることは妨げない。 Moreover, for the following reasons, the more preferable composition of the mixed gas (g) for organic substance reforming is: water vapor concentration: 20 to 70 vol%, hydrogen concentration: 10 to 40 vol%, carbon dioxide concentration: 10 to 40 vol%. It is. In addition, it does not prevent that other gas components (for example, nitrogen etc.) are contained in this mixed gas (g). By setting the water vapor concentration to 20 vol% or more, the decomposition rate of the organic substance can be sufficiently increased, and the LHV of the gas product can be increased. The reason for setting the water vapor concentration to 70 vol% or less is as described above. By setting the hydrogen concentration to 10 vol% or more (more preferably 12 vol% or more), it is possible to suppress CO 2 from remaining in the gas product even when a reforming reaction of an organic substance is performed at a relatively low temperature. be able to. By setting the carbon dioxide gas concentration to 10 vol% or more (more preferably 13 vol% or more), H 2 that is a low-calorie gas component is less likely to remain in the gas product as compared to hydrocarbons and CO. Further, by setting the hydrogen concentration and the carbon dioxide gas concentration to 40 vol% or less, the decomposition rate of organic substances such as waste plastic can be set to a preferable level, and solid residue can be reduced. Moreover, from the above viewpoints, a more preferable gas composition of the mixed gas (g) is a water vapor concentration: 25 to 65 vol%, a hydrogen concentration: 15 to 35 vol%, and a carbon dioxide concentration: 15 to 35 vol%. In addition, it does not prevent that other gas components (for example, nitrogen etc.) are contained in this mixed gas (g).

また、本発明の特徴の一つとして、有機物質改質用の混合ガス(g)の水蒸気濃度によって、有機物質の改質における気体生成物生成量と液体生成物生成量との比を制御できることが挙げられる。すなわち、混合ガス(g)の水蒸気濃度を50vol%以上にすると気体生成物が主に生成し(すなわち、気体生成物生成量>液体生成物生成量)、水蒸気濃度を40vol%以下にすると液体生成物が主に生成する(すなわち、気体生成物生成量<液体生成物生成量)。なお、水素濃度、炭酸ガス濃度の影響は水蒸気濃度の影響ほど顕著ではないので、本発明の好適範囲内であればよい。   Further, as one of the features of the present invention, the ratio of the gas product generation amount and the liquid product generation amount in the reforming of the organic substance can be controlled by the water vapor concentration of the mixed gas (g) for the organic substance reforming. Is mentioned. That is, when the water vapor concentration of the mixed gas (g) is 50 vol% or more, a gas product is mainly generated (that is, when the gas product production amount> the liquid product production amount), and when the water vapor concentration is 40 vol% or less, liquid production is generated. The product is mainly produced (i.e., gas product yield <liquid product yield). In addition, since the influence of hydrogen concentration and carbon dioxide concentration is not as remarkable as the influence of water vapor concentration, it may be within the preferable range of the present invention.

次に、シフト反応で得られた混合ガス(g)による有機物質の改質(低分子化)条件について説明する。
本発明において、改質による低分子化の対象となる有機物質に特別な制限はないが、高分子量の有機物質が好適であり、例えば、廃プラスチック、含油スラッジ、廃油、バイオマスなどが挙げられ、これらの1種以上を対象とすることができる。
Next, conditions for modifying (lowering the molecular weight) of an organic substance with the mixed gas (g) obtained by the shift reaction will be described.
In the present invention, there is no particular limitation on the organic material to be reduced in molecular weight by modification, but high molecular weight organic material is suitable, for example, waste plastic, oil-containing sludge, waste oil, biomass, etc. One or more of these can be targeted.

対象とする廃プラスチックの種類に特別な制限はないが、例えば、産業廃棄物系、容器包装リサイクル法の対象プラスチックなどを挙げることができる。より具体的には、PEやPPなどのポリオレフィン類、PAやPETなどの熱可塑性ポリエステル類、PSなどのエラストマー類、熱硬化性樹脂類、合成ゴム類や発砲スチロールなどを挙げることができる。なお、多くのプラスチック類にはフィラーなどの無機物が添加されているが、本発明では、このような無機物は反応に関与しないので、固体状残渣として改質(低分子化)反応器(有機物質を改質して低分子化するための反応器。以下同様)から排出される。また、廃プラスチックは、必要に応じて適当なサイズに事前裁断された後、改質反応器に投入される。
また、廃プラスチックがポリ塩化ビニルなどの塩素含有樹脂を含んでいると、改質反応器内で塩素が発生し、この塩素が気体生成物や液体生成物中に含有されてしまう恐れがある。したがって、廃プラスチックが塩素含有樹脂を含む恐れがある場合には、改質反応器内にCaOなどのような塩素吸収剤を投入し、塩素分が生成する気体生成物や液体生成物中に含有されないようにすることが好ましい。
Although there is no special restriction | limiting in the kind of waste plastics made into object, For example, the object plastics etc. which are an industrial waste type | system | group and a container packaging recycling law can be mentioned. More specifically, polyolefins such as PE and PP, thermoplastic polyesters such as PA and PET, elastomers such as PS, thermosetting resins, synthetic rubbers, foamed polystyrene and the like can be mentioned. In addition, inorganic substances such as fillers are added to many plastics. However, in the present invention, such inorganic substances are not involved in the reaction, so that they are reformed (low molecular weight) reactors (organic substances) as solid residues. Is discharged from a reactor for reducing the molecular weight by modifying the same. In addition, the waste plastic is preliminarily cut to an appropriate size as required, and then charged into the reforming reactor.
Further, if the waste plastic contains a chlorine-containing resin such as polyvinyl chloride, chlorine is generated in the reforming reactor, and this chlorine may be contained in a gas product or a liquid product. Therefore, when there is a possibility that the waste plastic contains chlorine-containing resin, a chlorine absorbent such as CaO is introduced into the reforming reactor and contained in a gas product or liquid product that generates chlorine. It is preferable not to do so.

含油スラッジとは、含油廃液処理工程で発生する汚泥状の混合物のことであり、一般に30〜70質量%程度の水分を含んでいる。スラッジ中の油分としては、例えば、各種鉱物油、天然および/または合成油脂類、各種脂肪酸エステル類などが挙げられるが、これらに限定されるものではない。なお、改質反応器に含油スラッジを供給する際などのハンドリング性を向上させるために、遠心分離などの手法により、スラッジ中の水分を30〜50質量%程度まで低減させてもよい。   Oil-containing sludge is a sludge-like mixture generated in an oil-containing waste liquid treatment step, and generally contains about 30 to 70% by mass of water. Examples of the oil in the sludge include, but are not limited to, various mineral oils, natural and / or synthetic oils and fats, and various fatty acid esters. In addition, in order to improve handling property, such as when supplying oil-impregnated sludge to the reforming reactor, moisture in the sludge may be reduced to about 30 to 50% by mass by a method such as centrifugation.

廃油としては、例えば、使用済みの各種鉱物油、天然および/または合成油脂類、各種脂肪酸エステル類などが挙げられるが、これらに限定されるものではない。また、これら2種以上の廃油の混合物であってもよい。また、製鉄所の圧延工程で発生する廃油の場合、一般に多量(通常、80質量%超程度)の水分を含有しているが、この水分についても、比重分離などの手法によって事前に低減させておくことが、ハンドリング性の面で有利である。
有機物質が水を含んでいる場合には、改質反応器内で水蒸気が発生するので、その分を考慮してシフト反応で添加する水蒸気の過剰割合を決定する。
Examples of the waste oil include, but are not limited to, various used mineral oils, natural and / or synthetic fats and oils, and various fatty acid esters. Moreover, the mixture of these 2 or more types of waste oil may be sufficient. In addition, in the case of waste oil generated in the steel mill rolling process, it generally contains a large amount of water (usually more than about 80% by mass), but this water is also reduced in advance by a method such as specific gravity separation. It is advantageous in terms of handleability.
When the organic substance contains water, water vapor is generated in the reforming reactor. Therefore, the excess ratio of water vapor added in the shift reaction is determined in consideration of the amount.

バイオマスとしては、例えば、下水汚泥、紙、建設廃材、間伐材などの他、ゴミ固形燃料(RDF)などの加工されたバイオマスなどが挙げられるが、これらに限定されるものではない。バイオマスには、通常、多量の水分が含有されているので、事前に乾燥させておくことがエネルギー効率の点から好ましい。また、ナトリウムやカリウムなどのアルカリ金属を比較的高濃度に含むバイオマスの場合、改質反応器内でアルカリ金属が析出する可能性があるので、水洗などの方法によって事前にアルカリ金属を溶出させておくことが好ましい。なお、建設廃材などの大型のバイオマスは、事前に裁断して改質反応器に投入される。   Examples of biomass include, but are not limited to, sewage sludge, paper, construction waste, thinned wood, and other processed biomass such as waste solid fuel (RDF). Since biomass usually contains a large amount of water, it is preferable to dry it beforehand in view of energy efficiency. In addition, in the case of biomass containing relatively high concentrations of alkali metals such as sodium and potassium, alkali metals may be deposited in the reforming reactor. It is preferable to keep it. In addition, large biomass such as construction waste is cut in advance and charged into the reforming reactor.

有機物質改質時の反応温度は、有機物質の種類に応じて、以下のようにすることが好ましい。廃プラスチックやバイオマスの場合には、反応温度は400〜900℃程度が適当である。反応温度が400℃未満では廃プラスチックやバイオマスの分解率が低く、一方、900℃を超えると炭素質の生成が多くなる。また、含油スラッジや廃油の場合には、反応温度は300〜800℃程度が適当である。反応温度が300℃未満では含油スラッジや廃油の分解率が低くなる。一方、反応温度が800℃を超えても含油スラッジや廃油の改質(低分子化)特性に影響はないが、必要以上の高温であるため、経済的でない。   The reaction temperature during organic substance modification is preferably as follows according to the type of organic substance. In the case of waste plastic or biomass, a reaction temperature of about 400 to 900 ° C. is appropriate. When the reaction temperature is less than 400 ° C, the decomposition rate of waste plastics and biomass is low. On the other hand, when the reaction temperature exceeds 900 ° C, the production of carbonaceous matter increases. In the case of oil-containing sludge or waste oil, the reaction temperature is suitably about 300 to 800 ° C. When the reaction temperature is less than 300 ° C., the decomposition rate of oil-containing sludge and waste oil becomes low. On the other hand, even if the reaction temperature exceeds 800 ° C., there is no effect on the reforming (lower molecular weight) characteristics of the oil-containing sludge or waste oil, but it is not economical because the temperature is higher than necessary.

また、廃プラスチックおよび/またはバイオマスと含油スラッジおよび/または廃油からなる混合物を対象とする場合には、上述した点から、反応温度は400〜800℃程度が適当である。なお、気体生成物生成量と液体生成物生成量との比に対する反応温度の影響はほとんど見られない。また、圧力の影響もほとんど認められないので、常圧または数kg/cm程度の微加圧で改質反応器を運転することが経済的である。
改質反応器の種類は特に限定されないが、反応器内で廃プラスチックなどの有機物質が円滑に移動し、且つ有機物質改質用の混合ガス(g)と効率的に接触でき、さらに、固体状残渣を連続的に排出できるという点から、ロータリーキルンのような横型の移動床方式反応器が好ましい。
Moreover, when the mixture which consists of waste plastics and / or biomass and oil-containing sludge and / or waste oil is made into object, about 400-800 degreeC is suitable for reaction temperature from the point mentioned above. In addition, the influence of reaction temperature with respect to the ratio of a gaseous product production amount and a liquid product production amount is hardly seen. In addition, since the influence of pressure is hardly observed, it is economical to operate the reforming reactor at normal pressure or at a slight pressure of about several kg / cm 2 .
The type of reforming reactor is not particularly limited, but organic substances such as waste plastic can move smoothly in the reactor, and can be efficiently contacted with the mixed gas (g) for organic substance reforming. A horizontal moving bed type reactor such as a rotary kiln is preferable because the residue can be continuously discharged.

本発明では有機物質の改質に特に触媒を必要としないので、触媒を用いない場合に発生する固体状残渣は、製鉄所などで行われる製造または処理プロセスにおいて炭素材料として利用される。また、本発明では、Ni系改質触媒、Ni系水素化触媒、Pt/ゼオライト系石油精製触媒などの水蒸気改質活性、炭酸ガス改質活性、水素化活性、水素化分解活性をそれぞれ有する1種または2種以上の触媒を用いて改質反応を行うこともでき、その場合に発生する固体状残渣は、触媒と分離した後、製鉄所などで行われる製造または処理プロセスにおいて炭素材料として利用される。触媒の分離方法は特に制限がないが、遠心分離やサイクロンなどの比重差を利用した分離方法の他、目視による分離など任意の方法が採用できる。   In the present invention, since a catalyst is not particularly required for reforming the organic substance, the solid residue generated when the catalyst is not used is used as a carbon material in a production or treatment process performed at a steel mill or the like. In the present invention, a Ni-based reforming catalyst, a Ni-based hydrogenation catalyst, a Pt / zeolite-based petroleum refining catalyst, etc. each have steam reforming activity, carbon dioxide reforming activity, hydrogenation activity, and hydrocracking activity. The reforming reaction can also be carried out using a seed or two or more kinds of catalysts, and the solid residue generated in that case is used as a carbon material in a manufacturing or processing process carried out at an ironworks after separation from the catalyst. Is done. The method for separating the catalyst is not particularly limited, but any method such as separation by visual observation can be adopted in addition to a separation method using a specific gravity difference such as centrifugal separation or cyclone.

一方、鉄系触媒を用いて有機物質の改質反応を行う場合には、発生する固体状残渣は鉄源(鉄系触媒由来の鉄源)を含有する炭素材料として利用される。鉄系触媒としては、転炉で発生する転炉ダスト、Fe−Cr系などの高温用シフト触媒、アルミナやゼオライトなどの各種担体に担持した鉄系触媒が好ましい。特に、転炉ダストは微細な鉄粒子であり、有機物質の改質反応に高い活性を示すだけでなく、転炉脱燐などの溶銑予備処理プロセスや転炉脱炭プロセスの副生物であり安価であるため、使い捨てとすることも可能であるため特に好ましい。一方、エチルベンゼン脱水素触媒(例えば、Fe−K系)のような脱水素活性を有する触媒は、改質反応で発生する炭素質を増加させるため、好ましくない。   On the other hand, when an organic material reforming reaction is performed using an iron-based catalyst, the generated solid residue is used as a carbon material containing an iron source (an iron source derived from an iron-based catalyst). As the iron-based catalyst, converter dust generated in the converter, a high-temperature shift catalyst such as Fe-Cr, and iron-based catalysts supported on various carriers such as alumina and zeolite are preferable. In particular, converter dust is a fine iron particle that not only exhibits high activity in organic material reforming reactions, but also is a byproduct of hot metal pretreatment processes such as converter dephosphorization and converter decarburization processes, and is inexpensive. Therefore, it is particularly preferable because it can be disposable. On the other hand, a catalyst having dehydrogenation activity such as an ethylbenzene dehydrogenation catalyst (for example, Fe-K system) is not preferable because it increases carbonaceous matter generated in the reforming reaction.

触媒を充填する場合には、廃プラスチックなどの有機物質と触媒との接触が良好となることから、ロータリーキルンのような横型の移動床式改質反応器ではなく、縦型の改質反応器を採用してもよい。この場合、シフト反応で得られた混合ガス(g)は、改質反応器の上部よりも、下部および/または側部から供給する方が、混合ガス(g)と有機物質や触媒との接触が良好となり好ましい。
縦型の改質反応器としては、化学工業で用いられる一般的な固定床反応器を用いることができるが、特に、混合ガス(g)を改質反応器下部から供給する方式を採用する場合には、製鉄設備である高炉やシャフト炉、或いは転炉を改質反応器として利用することもできる。高炉やシャフト炉を改質反応器として利用する場合は、炉上部から有機物質と触媒を、炉下部から混合ガス(g)を、それぞれ連続的に供給して向流接触させ、炉上部から気体生成物を、炉下部から液体生成物と固体状残渣および触媒を連続的に抜き出す移動床式とすると、反応効率が高くなり好ましい。また、転炉を改質反応器として利用する場合は、有機物質と触媒を炉に投入した後、炉下部から混合ガス(g)を連続的に供給し、気体生成物は炉上部から連続的に抜き出し、液体生成物と固体状残渣および触媒は一定時間の反応後に炉を傾けて抜き出すという、吹錬と同様の回分式反応形式とすることができる。いずれの場合も、固体状残渣と触媒は液体生成物と分離され、触媒が鉄系触媒である場合には、通常、製鉄所などで行われる製造または処理プロセスにおいて鉄源を含有する炭素材料として利用される。また、触媒が非鉄系触媒である場合には、固体状残渣と触媒は分離され、固体状残渣が製鉄所などで行われる製造または処理プロセスにおいて炭素材料として利用される。
When packing the catalyst, contact between the organic material such as waste plastic and the catalyst is good, so a vertical reforming reactor is used instead of a horizontal moving bed reforming reactor such as a rotary kiln. It may be adopted. In this case, the mixed gas (g) obtained by the shift reaction is supplied from the lower part and / or the side part rather than the upper part of the reforming reactor. Is preferable.
As a vertical reforming reactor, a general fixed bed reactor used in the chemical industry can be used, but in particular, when a method of supplying a mixed gas (g) from the lower part of the reforming reactor is employed. In addition, a blast furnace, a shaft furnace, or a converter, which is an iron manufacturing facility, can be used as a reforming reactor. When a blast furnace or shaft furnace is used as a reforming reactor, an organic substance and a catalyst are supplied continuously from the top of the furnace, and a mixed gas (g) is continuously supplied from the bottom of the furnace to counter-current contact, and gas is supplied from the top of the furnace. It is preferable that the product is a moving bed type in which the liquid product, the solid residue, and the catalyst are continuously extracted from the lower part of the furnace because the reaction efficiency becomes high. When a converter is used as a reforming reactor, an organic substance and a catalyst are introduced into the furnace, then a mixed gas (g) is continuously supplied from the lower part of the furnace, and a gas product is continuously supplied from the upper part of the furnace. The liquid product, the solid residue, and the catalyst can be extracted in a batch reaction mode similar to blowing, in which the furnace is tilted after the reaction for a certain time. In either case, the solid residue and the catalyst are separated from the liquid product, and when the catalyst is an iron-based catalyst, it is usually used as a carbon material containing an iron source in a production or treatment process performed at a steel mill or the like. Used. Further, when the catalyst is a non-ferrous catalyst, the solid residue and the catalyst are separated, and the solid residue is used as a carbon material in a production or treatment process performed in an ironworks or the like.

特に、転炉ダストを触媒とする場合、転炉ダストが安価で使い捨てとすることが可能なため、ロータリーキルンのような横型の移動床式反応器とすることも好ましい。この場合、炉前部から有機物質と触媒を、炉後部から混合ガス(g)を、それぞれ連続的に供給して向流接触させ、炉前部から気体と液体生成物を、炉後部から固体状残渣と触媒を連続的に抜き出す移動床式とすると、反応効率が高くなり好ましい。固体状残渣と触媒は、何ら分離工程を経ることなく、鉄源を含有する炭素材料として、製鉄所などで行われる製造または処理プロセスにおいて利用できる。   In particular, when converter dust is used as a catalyst, it is also preferable to use a horizontal moving bed reactor such as a rotary kiln because the converter dust is inexpensive and can be made disposable. In this case, an organic substance and a catalyst are continuously supplied from the front of the furnace, and a mixed gas (g) is continuously supplied from the rear of the furnace to be brought into countercurrent contact, and a gas and a liquid product are supplied from the front of the furnace and a solid is supplied from the rear of the furnace. It is preferable to use a moving bed type in which the solid residue and the catalyst are continuously extracted, since the reaction efficiency becomes high. The solid residue and the catalyst can be used in a production or treatment process performed at a steel mill or the like as a carbon material containing an iron source without any separation step.

本発明法で得られる有機物質の改質物は、改質反応生成ガスを冷却した後、気液分離することによって、それぞれ気体生成物と液体生成物に分離することができる。また、必要に応じて蒸留分離することによって、液体生成物からナフサ相当留分、灯油相当留分、軽油相当留分などに分離することができる。改質反応生成ガスの冷却方法、気液分離方法、並びに蒸留分離方法は公知の方法で行うことができ、特別な制限はない。
気体生成物中の可燃成分は一酸化炭素とC1〜C4の炭化水素から成り、そのLHVは約6〜10Mcal/Nmである。このように、天然ガス並みのLHVであるにも拘わらず、一酸化炭素濃度が高いので、天然ガスよりも燃焼性が高いことが特徴である。一酸化炭素濃度が高く且つ燃焼性が高いことから、一貫製鉄所の主要な燃料であるコークス炉ガスの代替燃料として用いることができる。また、COと軽質炭化水素からなる混合ガスであるので、天然ガス代替として高炉内に吹きこむこともできる。
The reformed product of the organic substance obtained by the method of the present invention can be separated into a gas product and a liquid product, respectively, by cooling the reforming reaction product gas and then performing gas-liquid separation. In addition, the liquid product can be separated into a naphtha-equivalent fraction, a kerosene-equivalent fraction, a light oil-equivalent fraction, and the like by distillation separation as necessary. The cooling method, the gas-liquid separation method, and the distillation separation method of the reforming reaction product gas can be performed by known methods, and there is no particular limitation.
Combustible components of the gas product consists hydrocarbons of carbon monoxide and C1 -C4, the LHV of about 6~10Mcal / Nm 3. Thus, although it is LHV comparable to natural gas, since carbon monoxide concentration is high, it is characterized by higher combustibility than natural gas. Since it has a high carbon monoxide concentration and high combustibility, it can be used as an alternative fuel for coke oven gas, which is the main fuel of integrated steelworks. Moreover, since it is a mixed gas consisting of CO and light hydrocarbons, it can be blown into the blast furnace as an alternative to natural gas.

液体生成物はC5〜C24の炭化水素から成っていることから、ナフサ(C5〜C8)、灯油(C9〜C12)、軽油(C13〜C24)の混合物であり、重油相当(C25以上)をほとんど含まない良質の軽質油である。この液体生成物は、蒸留分離によって、ナフサ、灯油、軽油として別々に利用してもよいが、混合物のまま、製鉄所などのような冶金炉を有する工場の燃料や溶鉱炉の重油代替還元剤として利用することができる。
なお、ナフサ(C5〜C8)の含有率が多いことから、ナフサ分は蒸留分離して化学工業原料として活用し、ナフサ分離後の蒸留残渣(灯油、軽油の混合物)だけを製鉄所で重油代替還元剤として利用してもよい。
Since the liquid product consists of C5 to C24 hydrocarbons, it is a mixture of naphtha (C5 to C8), kerosene (C9 to C12), and light oil (C13 to C24). High quality light oil not included. This liquid product may be used separately as naphtha, kerosene, or light oil by distillation separation, but as a mixture, it can be used as a reducing agent instead of heavy oil in blast furnaces and fuels in factories with metallurgical furnaces such as ironworks. Can be used.
Since the content of naphtha (C5 to C8) is high, the naphtha is separated by distillation and used as a raw material for chemical industry, and only the distillation residue (mixture of kerosene and light oil) after separation of naphtha is replaced with heavy oil at the steelworks. It may be used as a reducing agent.

以上のように本発明法において、有機物質の低分子化反応で生成し、回収された低分子化改質物(気体生成物、液体生成物)は、必要に応じて蒸留分離などの工程を経た後、それぞれ気体燃料や液体燃料などとして有効利用することができる。特に、製鉄所内で燃料および/または還元剤として利用し、また、熱源および還元剤として高炉内に吹き込むことができるので、高炉や製鉄所において安価で且つ高品質の燃料や還元剤を安定的に確保することができる。気体生成物(ガス)の高炉内への吹き込みは、通常、羽口を通じて行うが、これに限られるものではない。気体生成物を羽口から吹き込む場合、羽口に吹込みランスを設置し、この吹込みランスから吹き込むのが一般的である。   As described above, in the method of the present invention, the low molecular weight reformed product (gas product, liquid product) produced and recovered by the low molecular weight reaction of the organic substance is subjected to steps such as distillation separation as necessary. Thereafter, they can be effectively used as gaseous fuel, liquid fuel, and the like. In particular, it can be used as fuel and / or reducing agent in steelworks and can be blown into the blast furnace as a heat source and reducing agent. Can be secured. The gas product (gas) is usually blown into the blast furnace through a tuyere, but is not limited thereto. When blowing a gaseous product from a tuyere, it is common to install a blowing lance in the tuyere and to blow from this blowing lance.

一方、有機物質の低分子化反応で発生し、回収された固体状残渣は、炭素材料(「鉄源を含有する炭素材料」の場合を含む。以下同様)として、製鉄所などで行われる製造または処理プロセスにおいて有効利用することができる。製鉄所で行われる製造または処理プロセスとしては、例えば、焼結鉱製造プロセス、コークス製造プロセス、転炉脱炭プロセス、高炉プロセスなどが挙げられ、これらの1つ以上のプロセスにおいて、炭素材料として利用することができる。また、製鉄所以外の製造または処理プロセスにおいて、炭素材料として利用してもよい。具体的には、活性炭や黒鉛電極などの炭素材料製造プロセスにおける代替炭素源としての利用などを例示することができる。   On the other hand, the solid residue generated and recovered by the low molecular weight reaction of the organic substance is produced at a steel mill or the like as a carbon material (including the case of “carbon material containing an iron source”). Alternatively, it can be used effectively in the processing process. Examples of production or treatment processes performed at steelworks include sinter production processes, coke production processes, converter decarburization processes, blast furnace processes, and the like, and are used as carbon materials in one or more of these processes. can do. Moreover, you may utilize as a carbon material in manufacture or a process other than a steelworks. Specifically, use as an alternative carbon source in a carbon material manufacturing process such as activated carbon or graphite electrode can be exemplified.

焼結鉱製造プロセス(焼結機)では粉状のコークスを鉄鉱石の凝結材として利用しており、この粉コークスの一部を上記固体状残渣で代替できる。固体状残渣が鉄源を含んでいる場合には、その鉄源は鉄鉱石とともに凝結し、塊鉱石を形成する。
また、コークス製造プロセス(コークス炉)では、原料炭の一部代替材料として上記固体状残渣を利用することができる。なお、コークス炉では原料炭の一部代替として廃プラスチックを投入しているので、この廃プラスチックの代替とすることもできる。
In the sintered ore production process (sintering machine), powdered coke is used as a coagulating material for iron ore, and a part of the powdered coke can be replaced with the solid residue. When the solid residue contains an iron source, the iron source condenses with the iron ore to form a massive ore.
In the coke production process (coke oven), the solid residue can be used as a partial substitute material for raw coal. Since coke ovens use waste plastic as a partial substitute for coking coal, it can be used as a substitute for this waste plastic.

転炉脱炭プロセス(転炉)では、土状黒鉛などの転炉加炭材の代替材料として上記固体状残渣を利用することができる。特に、転炉ダストを触媒として有機物質の改質反応を行った後の転炉ダストを含有する固体状残渣は、転炉から発生したダストを鉄源とした炭素材料であるため、転炉の操業に何ら影響を与えることがないので、好ましい。
高炉プロセスでの上記固体状残渣の利用については、焼結鉱製造プロセスやコークス製造プロセスにおいて上記固体状残渣を利用して製造した塊鉱石やコークスを高炉原料とすること自体が、高炉での上記固体状残渣の利用に相当する。また、上記固体状残渣を成型したものをそのまま高炉原料(炭材)として利用することもでき、特に、鉄系触媒(なかでも転炉ダスト)用いて有機物質の改質反応を行った後の固体状残渣を成型したものは、鉄源(鉄系触媒由来の鉄源)+炭材からなる高炉原料として利用することができる。
In the converter decarburization process (converter), the solid residue can be used as an alternative material for converter carburized material such as earth graphite. In particular, the solid residue containing the converter dust after the organic substance reforming reaction using the converter dust as a catalyst is a carbon material using the dust generated from the converter as an iron source. This is preferable because it does not affect the operation.
Regarding the use of the solid residue in the blast furnace process, the fact that the block ore and coke produced by using the solid residue in the sinter ore production process is used as the blast furnace raw material itself, This corresponds to the use of a solid residue. In addition, the molded solid residue can be used as a blast furnace raw material (carbon material) as it is, especially after an organic substance reforming reaction using an iron-based catalyst (especially converter dust). What formed the solid residue can be used as a blast furnace raw material consisting of iron source (iron source derived from iron-based catalyst) + carbon material.

なお、以上述べた点からして、本発明で得られる混合ガス(g)と同等の組成の混合ガスを用いれば、有機物質を効率的に分解し、低分子化することができる。特に、水蒸気濃度:20〜70vol%、水素濃度:10〜40vol%、炭酸ガス濃度:10〜40vol%、より好ましくは水蒸気濃度:25〜65vol%、水素濃度:15〜35vol%、炭酸ガス濃度:15〜35vol%である混合ガスを用いることにより、有機物質の分解率を十分に高めることができるとともに、気体生成物のLHVを高くすることができる。なお、この混合ガスに、他のガス成分(例えば、窒素など)が含まれることは妨げない。
このようなガス組成の限定理由は、さきに述べた本発明法における限定理由と同様である。本発明法以外でこのような組成の混合ガスを得るには、例えば、ベースとなるガスに水蒸気、水素、炭酸ガスの1種以上を添加する。
この混合ガスによる有機物質の改質(低分子化)条件は、さきに述べた本発明法における改質(低分子化)条件と同様である。
In addition, from the point mentioned above, if the mixed gas of the composition equivalent to the mixed gas (g) obtained by this invention is used, an organic substance can be decomposed | disassembled efficiently and a molecular weight can be reduced. In particular, water vapor concentration: 20-70 vol%, hydrogen concentration: 10-40 vol%, carbon dioxide concentration: 10-40 vol%, more preferably water vapor concentration: 25-65 vol%, hydrogen concentration: 15-35 vol%, carbon dioxide concentration: By using a mixed gas of 15 to 35 vol%, the decomposition rate of the organic substance can be sufficiently increased, and the LHV of the gas product can be increased. In addition, it does not prevent that other gas components (for example, nitrogen etc.) are contained in this mixed gas.
The reason for limiting the gas composition is the same as the reason for limitation in the method of the present invention described above. In order to obtain a mixed gas having such a composition other than the method of the present invention, for example, one or more of water vapor, hydrogen, and carbon dioxide gas is added to the base gas.
The conditions for modifying (decreasing the molecular weight) of the organic substance by the mixed gas are the same as the conditions for modifying (decreasing the molecular weight) in the method of the present invention described above.

したがって、その方法の要旨は下記[i]〜[viii]の通りであり、後述する本発明の実施例は、下記[i]〜[viii]の方法の実施例でもある。
[i]水蒸気濃度が20〜70vol%、水素濃度が10〜40vol%、炭酸ガス濃度が10〜40vol%である混合ガスを有機物質に接触させることにより、有機物質を改質して低分子化する反応を生じさせ、該反応により生じた有機物質の低分子化改質物と固体状残渣を回収し、該固体状残渣を炭素材料として利材化することを特徴とする有機物質の利材化方法。
[ii]水蒸気濃度が20〜70vol%、水素濃度が10〜40vol%、炭酸ガス濃度が10〜40vol%である混合ガスを鉄系触媒の存在下、有機物質に接触させることにより、有機物質を改質して低分子化する反応を生じさせ、該反応により生じた有機物質の低分子化改質物と固体状残渣を回収し、該固体状残渣を鉄源を含有する炭素材料として利材化することを特徴とする有機物質の利材化方法。
[iii]上記[i]または[ii]の方法において、混合ガスは、水蒸気濃度が25〜65vol%、水素濃度が15〜35vol%、炭酸ガス濃度が15〜35vol%であることを特徴とする有機物質の利材化方法。
Therefore, the gist of the method is as follows [i] to [viii], and the examples of the present invention described later are also examples of the methods [i] to [viii] below.
[I] Reducing the molecular weight of the organic material by modifying the organic material by bringing a mixed gas having a water vapor concentration of 20 to 70 vol%, a hydrogen concentration of 10 to 40 vol%, and a carbon dioxide gas concentration of 10 to 40 vol% into contact with the organic material. The organic substance produced by the reaction is recovered, the low molecular weight modified product of the organic substance and the solid residue are collected, and the solid residue is used as a carbon material. Method.
[Ii] By bringing a mixed gas having a water vapor concentration of 20 to 70 vol%, a hydrogen concentration of 10 to 40 vol%, and a carbon dioxide gas concentration of 10 to 40 vol% into contact with the organic material in the presence of an iron-based catalyst, Reducing the molecular weight by reforming, recovering the low molecular weight modified product and solid residue of the organic substance generated by the reaction, and using the solid residue as a carbon material containing an iron source A method for making organic materials into a material.
[Iii] In the method [i] or [ii] above, the mixed gas has a water vapor concentration of 25 to 65 vol%, a hydrogen concentration of 15 to 35 vol%, and a carbon dioxide concentration of 15 to 35 vol%. How to make organic materials.

[iv]上記[i]〜[iii]のいずれかの方法において、改質される有機物質が、廃プラスチック、含油スラッジ、廃油、バイオマスの中から選ばれる1種以上であることを特徴とする記載の有機物質の利材化方法。
[v]上記[i]〜[iv]のいずれかの方法において、固体状残渣を、製鉄所で行われる製造または処理プロセスにおいて炭素材料として利用することを特徴とする有機物質の利材化方法。
[vi]上記[v]の方法において、製鉄所で行われる製造または処理プロセスが、焼結鉱製造プロセス、コークス製造プロセス、転炉脱炭プロセス、高炉プロセスのうちの1つ以上のプロセスであることを特徴とする有機物質の利材化方法。
[vii]上記[i]〜[vi]のいずれかの方法において、回収された有機物質の低分子化改質物を、製鉄所内で燃料および/または還元剤として利用することを特徴とする有機物質の利材化方法。
[viii]上記[vii]の方法において、回収された有機物質の低分子化改質物を高炉に吹き込むことを特徴とする有機物質の利材化方法。
[Iv] The method according to any one of [i] to [iii] above, wherein the organic substance to be modified is at least one selected from waste plastic, oil-containing sludge, waste oil, and biomass. A method for making the organic substance described in the above.
[V] In the method according to any one of [i] to [iv] above, the solid residue is used as a carbon material in a production or treatment process performed at a steel mill, .
[Vi] In the method of [v] above, the production or treatment process performed at the steel mill is one or more of a sintered ore production process, a coke production process, a converter decarburization process, and a blast furnace process. A method for converting an organic material into a material.
[Vii] The organic material according to any one of the above [i] to [vi], wherein the recovered low molecular weight reformed organic material is used as a fuel and / or a reducing agent in a steel mill. How to make a profit.
[Viii] In the method of [vii] above, a method for converting an organic substance into a profitable material is characterized in that the low molecular weight modified product of the recovered organic substance is blown into a blast furnace.

・発明例1
転炉ガスを一時貯留するガスホルダーのガス払出し配管に分岐管を設け、この分岐管を通じて転炉ガスの一部を抜き出すことができるようにした。この分岐管の下流側には流量調節弁、スチーム混合器、予熱器(転炉ガスとスチームの混合ガス用)、シフト反応器(円筒竪型)、改質反応器(外熱式ロータリーキルン)、液体生成物捕集器を備えた改質反応生成ガス冷却用のガス冷却器を、この順に配置した。前記改質反応器の入側には、スクリューコンベア方式の廃プラスチック定量投入装置を設置した。また、シフト反応器の出側配管とガス冷却器の冷却後ガスの出側配管には、サンプリングポートと流量計を設置した。
・ Invention Example 1
A branch pipe is provided in the gas discharge pipe of the gas holder for temporarily storing the converter gas, and a part of the converter gas can be extracted through the branch pipe. Downstream of this branch pipe is a flow control valve, steam mixer, preheater (for converter gas and steam mixed gas), shift reactor (cylindrical vertical type), reforming reactor (externally heated rotary kiln), A gas cooler for cooling the reforming reaction product gas equipped with a liquid product collector was arranged in this order. On the inlet side of the reforming reactor, a screw conveyor type waste plastic quantitative charging device was installed. A sampling port and a flow meter were installed in the outlet piping of the shift reactor and the outlet piping of the gas after cooling of the gas cooler.

ガスホルダー中の転炉ガスの平均組成は、H:12vol%、CO:54vol%、CO:17vol%、HO:1vol%、N:16vol%であった。スチーム混合器に対して転炉ガスを74Nm/h、水蒸気として圧力10kg/cmGのスチームを100Nm/h供給し、予熱器で320℃まで昇温した後、シフト反応器(Fe−Cr系高温シフト触媒充填)に導入した。シフト反応器でのシフト反応によって、ガス組成がH:26vol%、CO:2vol%、CO:28vol%、HO:37vol%、N:7vol%のガス(シフト反応生成ガス)が得られた。このシフト反応生成ガスは、流量が172Nm/h(質量流量では170kg/h)、反応器出口ガス温度が430℃であった。 The average composition of the converter gas in the gas holder, H 2: 12vol%, CO : 54vol%, CO 2: 17vol%, H 2 O: 1vol%, N 2: was 16 vol%. The converter gas 74 nm 3 / h, a steam pressure 10 kg / cm 2 G and 100 Nm 3 / h supplied as steam against a steam mixer, after raising the temperature to 320 ° C. in the preheater, the shift reactor (Fe- (Cr-based high temperature shift catalyst filling). Due to the shift reaction in the shift reactor, gas having a gas composition of H 2 : 26 vol%, CO: 2 vol%, CO 2 : 28 vol%, H 2 O: 37 vol%, N 2 : 7 vol% (shift reaction product gas) Obtained. This shift reaction product gas had a flow rate of 172 Nm 3 / h (170 kg / h in mass flow rate) and a reactor outlet gas temperature of 430 ° C.

改質反応器である外熱式ロータリーキルンは予め500℃に予熱されており、この改質反応器に、シフト反応生成ガスを導入するとともに、廃プラスチックのモデル物質として粒状に破砕処理したポリエチレンを880kg/hで供給し、計画反応温度である800℃まで昇温させた。800℃に到達後、液体生成物捕集器に捕集されていた液体生成物を払い出し、その後1時間、廃プラスチックの改質反応を継続した。
気体生成物分はガス冷却器による冷却後のガス分析結果から、また、液体生成物分は液体生成物捕集器に捕集された液体生成物の分析結果から、それぞれ生成量と組成を求め、また、気体生成物についてはLHVを求めた。それらの結果を表1に示す。
The externally heated rotary kiln, which is a reforming reactor, is preheated to 500 ° C. in advance, and 880 kg of polyethylene that has been crushed into granules as a model material of waste plastic is introduced into this reforming reactor while introducing a shift reaction product gas. / H, and the temperature was raised to 800 ° C., which is the planned reaction temperature. After reaching 800 ° C., the liquid product collected in the liquid product collector was discharged, and then the reforming reaction of the waste plastic was continued for 1 hour.
The amount and composition of the gas product are determined from the gas analysis results after cooling by the gas cooler, and the liquid product content is determined from the analysis results of the liquid product collected in the liquid product collector. Moreover, LHV was calculated | required about the gaseous product. The results are shown in Table 1.

原料として供給したシフト反応生成ガスとポリエチレンの合計量は1050kg/hであるので、供給原料総量に対する生成率は、気体生成物が36%、液体生成物が62%であった。未反応ポリエチレン量を直接計量することは困難なので、供給したシフト反応生成ガスとポリエチレンの合計量(1050kg/h)に対する、気体生成物(380kg/h)と液体生成物(650kg/h)の合計収率をポリエチレン分解率と定義すると、この発明例1では、ポリエチレン分解率が98%と十分に高い値であること、C25以上の炭化水素の生成がほとんど認められないことから、ポリエチレンは効率的に低分子化されたことは明らかである。有機物質の改質反応によりHO、CO、Hは完全に消費されており、水蒸気改質、炭酸ガス改質、水素化、水素化分解の4反応が同時に進行したものと考えられる。生成した気体生成物のLHVは8.9Mcal/Nmと、転炉ガス(1.9Mcal/Nm)の4.7倍に増熱していた。 Since the total amount of shift reaction product gas and polyethylene supplied as raw materials was 1050 kg / h, the production rate relative to the total amount of the feed materials was 36% for gas products and 62% for liquid products. Since it is difficult to directly measure the amount of unreacted polyethylene, the sum of the gas product (380 kg / h) and the liquid product (650 kg / h) relative to the total amount of shift reaction product gas and polyethylene (1050 kg / h) supplied. When the yield is defined as the polyethylene decomposition rate, in Example 1, the polyethylene decomposition rate is 98%, which is a sufficiently high value, and the production of hydrocarbons of C25 or higher is hardly observed. It is clear that the molecular weight was reduced. H 2 O, CO 2 and H 2 are completely consumed by the reforming reaction of the organic substance, and it is considered that four reactions of steam reforming, carbon dioxide reforming, hydrogenation, and hydrocracking proceeded simultaneously. . The LHV of the produced gas product was 8.9 Mcal / Nm 3 and increased to 4.7 times that of the converter gas (1.9 Mcal / Nm 3 ).

Figure 2013173878
Figure 2013173878

ポリエチレンは効率的に低分子化されたものの、上記の気体生成物と液体生成物のほかに、2質量%(20kg/h)と僅かではあるが、固体状残渣が発生した。改質反応を無触媒で行ったので、この残渣は鉄源を含有しない炭素材料に相当する。この残渣をコークス炉で利用する実験を行った。固体状残渣を1トンと原料炭19トンを事前に混合し、これを一つの炭化室に装入した。乾留は通常通りの工程で進行し、何ら問題なくコークスを製造できた。このコークス炉の炭化室あたりの原料炭装入量は20トンなので、原料炭を5%削減できたことになる。   Polyethylene was efficiently reduced in molecular weight, but in addition to the above gas product and liquid product, a solid residue was generated although it was a little 2 mass% (20 kg / h). Since the reforming reaction was carried out without a catalyst, this residue corresponds to a carbon material containing no iron source. An experiment was conducted in which this residue was used in a coke oven. 1 ton of solid residue and 19 ton of coking coal were mixed in advance and charged in one carbonization chamber. Carbonization proceeded in the usual process, and coke could be produced without any problems. Since the coking coal charge amount per coking chamber of the coke oven is 20 tons, the coking coal can be reduced by 5%.

・発明例2〜10
発明例1と同様の設備において、シフト反応器に供給するスチーム流量を種々変化させたこと、並びに改質反応温度を800℃と500℃の2水準とした以外は発明例1と同様にして、転炉ガスのシフト反応とシフト反応生成ガスによるポリエチレンの改質反応実験を行った。その結果を表2と図2〜図6に示す。
Inventive examples 2 to 10
In the same equipment as Invention Example 1, except that the steam flow rate supplied to the shift reactor was variously changed and the reforming reaction temperature was set at two levels of 800 ° C. and 500 ° C., the same as in Invention Example 1, Experiments were carried out on the shift reaction of the converter gas and the reforming reaction of polyethylene with the shift reaction product gas. The results are shown in Table 2 and FIGS.

図2は、シフト反応生成ガスの水蒸気濃度と、ポリエチレンの改質(反応温度:800℃)におけるガス化率および液化率との関係を示したものである。ここで、ガス化率とは、供給したシフト反応生成ガスとポリエチレンの合計量(kg/h)に対する気体生成物の生成量(kg/h)の割合であり、気体生成物の定義は表1に示すようにHからC4までとした。同様に、液化率とは、供給したシフト反応生成ガスとポリエチレンの合計量(kg/h)に対する液体生成物の生成量(kg/h)の割合であり、液体生成物の定義は表1に示すようにC5からC24までとした。図3は、シフト反応生成ガスの水蒸気濃度と、ポリエチレンの改質(反応温度:800℃)で得られた気体生成物および液体生成物のLHVとの関係を示したものである。ここで、液体生成物のLHVは、液体生成物の気体換算の標準状態における体積当たりのLHVで表した。図4は、シフト反応生成ガスの水蒸気濃度と、ポリエチレンの改質によるポリエチレン分解率との関係を示したもので、特に、反応温度500℃と800℃においてポリエチレン分解率が同等であることを示したものである。図5は、シフト反応生成ガスの炭酸ガス濃度と、ポリエチレンの改質(反応温度:800℃)で得られた気体生成物の水素濃度との関係を示したものである。図6は、シフト反応生成ガスの水素濃度と、ポリエチレンの改質(反応温度:500℃)で得られた気体生成物の炭酸ガス濃度との関係を示したものである。 FIG. 2 shows the relationship between the water vapor concentration of the shift reaction product gas and the gasification rate and liquefaction rate in the reforming of polyethylene (reaction temperature: 800 ° C.). Here, the gasification rate is a ratio of the production amount (kg / h) of the gas product to the total amount (kg / h) of the supplied shift reaction product gas and polyethylene, and the definition of the gas product is shown in Table 1. From H 2 to C 4 as shown in FIG. Similarly, the liquefaction rate is a ratio of the production amount (kg / h) of the liquid product to the total amount (kg / h) of the supplied shift reaction product gas and polyethylene, and the definition of the liquid product is shown in Table 1. As shown, it was from C5 to C24. FIG. 3 shows the relationship between the water vapor concentration of the shift reaction product gas and the LHV of the gas product and liquid product obtained by the modification of polyethylene (reaction temperature: 800 ° C.). Here, the LHV of the liquid product was expressed as LHV per volume in the standard state in terms of gas of the liquid product. FIG. 4 shows the relationship between the water vapor concentration of the shift reaction product gas and the polyethylene decomposition rate due to the modification of polyethylene, and in particular, shows that the polyethylene decomposition rate is equivalent at reaction temperatures of 500 ° C. and 800 ° C. It is a thing. FIG. 5 shows the relationship between the carbon dioxide concentration of the shift reaction product gas and the hydrogen concentration of the gas product obtained by the reforming of polyethylene (reaction temperature: 800 ° C.). FIG. 6 shows the relationship between the hydrogen concentration of the shift reaction product gas and the carbon dioxide concentration of the gas product obtained by the reforming of polyethylene (reaction temperature: 500 ° C.).

Figure 2013173878
Figure 2013173878

・発明例11
この実施例で使用した設備の概略を図7に示す。この設備は、底部にガス分散板20を有する縦型の改質反応器2(内容積:約3m)を備えており、この改質反応器2内には、最下層に粒状に破砕処理したポリエチレンaを880kg充填し、その上部に金属製の網b(10メッシュ)を乗せ、さらにその上部にNi触媒c(Ni担持率:10質量%、担体:α−Al)を800kg充填した。シフト反応器1で生成したシフト反応生成ガスは改質反応器2の底部に導入され、ガス分散板20を通じて反応器内に供給され、反応器内を上昇する。改質生成物は改質反応器2の上部から排出され、液体生成物捕集器3にて気体生成物と液体生成物に分離される。分離された気体生成物はガス冷却器4で冷却される。なお、転炉ガスを一時貯留するガスホルダーからシフト反応器1に至るまでの設備構成は、発明例1と同様とした。
-Invention Example 11
An outline of the equipment used in this example is shown in FIG. This equipment is provided with a vertical reforming reactor 2 (internal volume: about 3 m 3 ) having a gas dispersion plate 20 at the bottom, and in this reforming reactor 2, the lowermost layer is crushed into granules. Was filled with 880 kg of the polyethylene a, and a metal net b (10 mesh) was placed on the top, and further Ni catalyst c (Ni loading: 10% by mass, support: α-Al 2 O 3 ) was placed on the top 800 kg. Filled. The shift reaction product gas generated in the shift reactor 1 is introduced into the bottom of the reforming reactor 2, and is supplied into the reactor through the gas dispersion plate 20, and ascends in the reactor. The reformed product is discharged from the upper part of the reforming reactor 2 and separated into a gas product and a liquid product by the liquid product collector 3. The separated gas product is cooled by the gas cooler 4. The equipment configuration from the gas holder for temporarily storing the converter gas to the shift reactor 1 was the same as that of Invention Example 1.

以上のような設備を用い、改質反応器2での計画反応温度を750℃とした以外は、発明例1と同様の条件(転炉ガス組成、シフト反応生成ガスを得るまでの条件、シフト反応生成ガス組成・温度・流量など)にしてポリエチレンの改質反応実験を行った。
気体生成物と液体生成物の生成量と組成などを、発明例1と同様の方法で求めた。その結果を表3に示す。発明例1とほぼ同等の反応結果であり、改質反応器2での反応温度を750℃と、発明例1よりも50℃低くできたのは触媒添加の効果であると考えられる。
Except for using the above equipment and setting the planned reaction temperature in the reforming reactor 2 to 750 ° C., the same conditions as in Invention Example 1 (conditions for obtaining the converter gas composition, shift reaction product gas, shift The reaction reaction gas composition, temperature, flow rate, etc.) were used to conduct experiments on the reforming of polyethylene.
The production amount and composition of the gas product and the liquid product were determined in the same manner as in Invention Example 1. The results are shown in Table 3. The reaction results were almost the same as those of Invention Example 1, and it was considered that the reaction temperature in the reforming reactor 2 was 750 ° C., which was 50 ° C. lower than that of Invention Example 1, due to the effect of catalyst addition.

発明例1と同様、2質量%(20kg/h)と僅かではあるが、固体状残渣が発生した。本発明例ではNi触媒を充填しているので、遠心分離によって固体状残渣と触媒の一次分離を行い、さらに目視によって固体状残渣のみを分離した。したがって、この回収残渣は鉄源を含有しない炭素材料に相当する。なお、固体状残渣の回収率は90%(回収量:0.9トン)であった。発明例1と同様、この残渣をコークス炉で利用する実験を行った。固体状残渣を0.9トンと原料炭19.1トンを事前に混合し、これを一つの炭化室に装入した。乾留は通常通りの工程で進行し、何ら問題なくコークスを製造できた。このコークス炉の炭化室あたりの原料炭装入量は20トンなので、原料炭を4.5%削減できたことになる。   Similar to Invention Example 1, a solid residue was generated although it was a little 2 mass% (20 kg / h). In the example of the present invention, since the Ni catalyst was filled, the solid residue and the catalyst were primarily separated by centrifugal separation, and only the solid residue was separated visually. Therefore, this recovered residue corresponds to a carbon material that does not contain an iron source. The solid residue recovery rate was 90% (recovery amount: 0.9 tons). Similar to Invention Example 1, an experiment was conducted in which this residue was used in a coke oven. 0.9 tons of solid residue and 19.1 tons of coking coal were mixed in advance and charged into one carbonization chamber. Carbonization proceeded in the usual process, and coke could be produced without any problems. Since the coking coal charge per coking chamber of this coke oven is 20 tons, the coking coal was reduced by 4.5%.

Figure 2013173878
Figure 2013173878

・比較例1
水蒸気と水素濃度がともに低いガスによるポリエチレンの改質反応効率を調べるために、H:1vol%、CO:61vol%、CO:19vol%、HO:1vol%、N:18vol%なる組成の標準ガスを作り、このガスによりポリエチレンの改質反応実験を行った。その結果、温度800℃においてもポリエチレン分解率は16%、ガス化率10%、液化率5%に過ぎず、低分子化はほとんど進行しなかった。
Comparative example 1
In order to examine the reforming reaction efficiency of polyethylene with a gas having a low water vapor and hydrogen concentration, H 2 : 1 vol%, CO: 61 vol%, CO 2 : 19 vol%, H 2 O: 1 vol%, N 2 : 18 vol% A standard gas of composition was made, and a polyethylene reforming reaction experiment was conducted with this gas. As a result, even at a temperature of 800 ° C., the polyethylene degradation rate was only 16%, the gasification rate was 10%, and the liquefaction rate was only 5%.

・発明例12
一酸化炭素を含有する冶金炉発生排ガスとして高炉ガスを用いた。高炉ガスの脱硫・乾燥処理後の組成は、H:3vol%、CO:23vol%、CO:21vol%、N:53vol%であったので、以下に述べるPSA法によって窒素分離を行い、一酸化炭素の濃度を高めた。
PSA法による窒素分離では、吸着剤としてCu担持活性炭を400kg充填した吸着塔に、上記高炉ガスを常圧で136Nm/h供給した。脱着は7kPa(絶対圧)で行い、脱着ガス(=一酸化炭素を濃縮した高炉ガス)の組成はH<1vol%、CO:47vol%、CO:37vol%、N:16vol%、流量は58Nm/hであった。この一酸化炭素を濃縮した高炉ガス58Nm/hと水蒸気として圧力10kg/cmGのスチーム73Nm/hをスチーム混合器に供給し、発明例1と同様にしてシフト反応を行った。その結果、ガス組成がH:19vol%、CO:2vol%、CO:35vol%、HO:37vol%、N:7vol%のガス(シフト反応生成ガス)が得られた。このシフト反応生成ガスは、流量が130Nm/h(質量流量では146kg/h)、反応器出口ガス温度が430℃であった。
Invention Example 12
Blast furnace gas was used as an exhaust gas generated from a metallurgical furnace containing carbon monoxide. The composition of the blast furnace gas after desulfurization / drying treatment was H 2 : 3 vol%, CO: 23 vol%, CO 2 : 21 vol%, N 2 : 53 vol%, so that nitrogen separation was performed by the PSA method described below, Increased concentration of carbon monoxide.
In nitrogen separation by the PSA method, the above blast furnace gas was supplied at 136 Nm 3 / h at normal pressure to an adsorption tower packed with 400 kg of Cu + supported activated carbon as an adsorbent. Desorption is performed at 7 kPa (absolute pressure), and the composition of the desorption gas (= blast furnace gas enriched with carbon monoxide) is H 2 <1 vol%, CO: 47 vol%, CO 2 : 37 vol%, N 2 : 16 vol%, flow rate Was 58 Nm 3 / h. The carbon monoxide and steam 73 nm 3 / h a pressure 10 kg / cm 2 G was supplied to the steam mixer as blast furnace gas 58 nm 3 / h and steam were concentrated and subjected to a shift reaction in the same manner as in Invention Example 1. As a result, a gas (shift reaction product gas) having a gas composition of H 2 : 19 vol%, CO: 2 vol%, CO 2 : 35 vol%, H 2 O: 37 vol%, and N 2 : 7 vol% was obtained. This shift reaction product gas had a flow rate of 130 Nm 3 / h (146 kg / h in mass flow rate) and a reactor outlet gas temperature of 430 ° C.

発明例1と同様の装置を用い、触媒として脱水・乾燥した転炉ダストを50kg/h、発明例1と同様に破砕処理したポリエチレンを880kg/hを供給し、上記のシフト反応生成ガス(146kg/h)により、反応温度を600℃でポリエチレンの低分子化反応を行った。反応結果は、気体生成物の生成量320kg/h(LHV:7.5Mcal/Nm)、液体生成物の生成量650kg/h、ポリエチレン分解率95%であった。 Using the same apparatus as in Invention Example 1, 50 kg / h of the converter dust dehydrated and dried as a catalyst and 880 kg / h of polyethylene crushed in the same manner as in Invention Example 1 were supplied, and the shift reaction product gas (146 kg) was supplied. / H), a reaction for reducing the molecular weight of polyethylene was carried out at a reaction temperature of 600 ° C. As a result of the reaction, the production amount of gas product was 320 kg / h (LHV: 7.5 Mcal / Nm 3 ), the production amount of liquid product was 650 kg / h, and the polyethylene degradation rate was 95%.

発生した固体状残渣は110kg/hであったが、これには触媒である転炉ダスト(50kg/h)が含まれている。転炉ダスト中の鉄分含有量はFeとして50〜80質量%程度である。計算上、本実施例の固体状残渣は、金属鉄換算で鉄源を23〜36質量%含む炭素材料に相当するが、簡単のため30質量%の金属鉄と70質量%の炭素から成るとした。
この残渣を転炉加炭材として利用する実験を行った。この転炉では加炭材として土状黒鉛を5kg/t-steel使用しているが、実験では4kg/t-steelの土状黒鉛に固体状残渣を1.4kg/t-steel(炭素分として1kg/t-steel)混合したものを加炭材とした。その結果、通常と何ら変わりがなく、問題なく吹錬することができた。
The generated solid residue was 110 kg / h, which includes converter dust (50 kg / h) as a catalyst. The iron content in the converter dust is about 50 to 80% by mass as Fe. In calculation, the solid residue of this example corresponds to a carbon material containing 23 to 36% by mass of an iron source in terms of metallic iron, but for simplicity, it is composed of 30% by mass of metallic iron and 70% by mass of carbon. did.
An experiment was conducted in which this residue was used as a converter carburizing material. In this converter, 5 kg / t-steel of earth graphite is used as a carburizing material. In the experiment, a solid residue of 1.4 kg / t-steel (carbon content) is added to 4 kg / t-steel earth graphite. A mixture of 1 kg / t-steel) was used as a carburized material. As a result, there was no change from usual and it was possible to blow without problems.

1 シフト反応器
2 改質反応器
3 液体生成物捕集器
4 ガス冷却器
20 ガス分散板
a ポリエチレン
b 網
c Ni触媒
DESCRIPTION OF SYMBOLS 1 Shift reactor 2 Reforming reactor 3 Liquid product collector 4 Gas cooler 20 Gas dispersion plate a Polyethylene b Net c Ni catalyst

Claims (11)

冶金炉で発生した一酸化炭素を含有する排ガス(g)に過剰の水蒸気を添加してシフト反応を行わせることで、シフト反応で生成した水素および炭酸ガスと、シフト反応に消費されなかった水蒸気とを含む混合ガス(g)とし、この混合ガス(g)を有機物質に接触させることにより、有機物質を改質して低分子化する反応を生じさせ、該反応により生じた有機物質の低分子化改質物と固体状残渣を回収し、該固体状残渣を炭素材料として利材化することを特徴とする有機物質の利材化方法。 By adding excess water vapor to the exhaust gas (g 0 ) containing carbon monoxide generated in the metallurgical furnace to cause the shift reaction, hydrogen and carbon dioxide generated by the shift reaction were not consumed in the shift reaction. A mixed gas (g) containing water vapor is brought into contact with the organic substance to cause a reaction that modifies the organic substance and lowers the molecular weight. A method for producing an organic material, which comprises recovering a low molecular weight modified product and a solid residue, and using the solid residue as a carbon material. 冶金炉で発生した一酸化炭素を含有する排ガス(g)に過剰の水蒸気を添加してシフト反応を行わせることで、シフト反応で生成した水素および炭酸ガスと、シフト反応に消費されなかった水蒸気とを含む混合ガス(g)とし、この混合ガス(g)を鉄系触媒の存在下、有機物質に接触させることにより、有機物質を改質して低分子化する反応を生じさせ、該反応により生じた有機物質の低分子化改質物と固体状残渣を回収し、該固体状残渣を鉄源を含有する炭素材料として利材化することを特徴とする有機物質の利材化方法。 By adding excess water vapor to the exhaust gas (g 0 ) containing carbon monoxide generated in the metallurgical furnace to cause the shift reaction, hydrogen and carbon dioxide generated by the shift reaction were not consumed in the shift reaction. A mixed gas (g) containing water vapor is brought into contact with the organic substance in the presence of an iron-based catalyst to cause a reaction to modify the organic substance to reduce the molecular weight, A method for producing an organic material comprising collecting a low molecular weight modified product and a solid residue of an organic substance generated by the reaction, and using the solid residue as a carbon material containing an iron source. 鉄系触媒が転炉ダストであることを特徴とする請求項2に記載の有機物質の利材化方法。   The method for converting an organic substance into a material according to claim 2, wherein the iron-based catalyst is converter dust. 排ガス(g)が、冶金炉で発生した一酸化炭素と窒素を含有する排ガスから窒素の少なくとも一部を分離することで一酸化炭素濃度を高めた排ガスであることを特徴とする請求項1〜3のいずれかに記載の有機物質の利材化方法。 The exhaust gas (g 0 ) is an exhaust gas whose carbon monoxide concentration is increased by separating at least a part of nitrogen from exhaust gas containing carbon monoxide and nitrogen generated in a metallurgical furnace. A method for converting an organic substance into a material according to any one of? 混合ガス(g)の水蒸気濃度が5〜70vol%であることを特徴とする請求項1〜4のいずれかに記載の有機物質の利材化方法。   The method for converting an organic substance into a material according to any one of claims 1 to 4, wherein the mixed gas (g) has a water vapor concentration of 5 to 70 vol%. 混合ガス(g)は、水蒸気濃度が20〜70vol%、水素濃度が10〜40vol%、炭酸ガス濃度が10〜40vol%であることを特徴とする請求項5に記載の有機物質の利材化方法。   The mixed gas (g) has a water vapor concentration of 20 to 70 vol%, a hydrogen concentration of 10 to 40 vol%, and a carbon dioxide gas concentration of 10 to 40 vol%. Method. 改質される有機物質が、廃プラスチック、含油スラッジ、廃油、バイオマスの中から選ばれる1種以上であることを特徴とする請求項1〜6のいずれかに記載の有機物質の利材化方法。   The organic material to be reformed is one or more kinds selected from waste plastic, oil-containing sludge, waste oil, and biomass. . 固体状残渣を、製鉄所で行われる製造または処理プロセスにおいて炭素材料として利用することを特徴とする請求項1〜7のいずれかに記載の有機物質の利材化方法。   The solid residue is used as a carbon material in a manufacturing or treatment process performed at a steel mill, The organic material utilization method according to any one of claims 1 to 7. 製鉄所で行われる製造または処理プロセスが、焼結鉱製造プロセス、コークス製造プロセス、転炉脱炭プロセス、高炉プロセスのうちの1つ以上のプロセスであることを特徴とする請求項8に記載の有機物質の利材化方法。   9. The manufacturing or processing process performed at a steel mill is one or more of a sinter ore manufacturing process, a coke manufacturing process, a converter decarburization process, and a blast furnace process. How to make organic materials. 回収された有機物質の低分子化改質物を、製鉄所内で燃料および/または還元剤として利用することを特徴とする請求項1〜9のいずれかに記載の有機物質の利材化方法。   10. The method for converting an organic substance into a profitable material according to any one of claims 1 to 9, wherein the recovered low molecular weight modified product of the organic substance is used as a fuel and / or a reducing agent in an ironworks. 回収された有機物質の低分子化改質物を高炉に吹き込むことを特徴とする請求項10に記載の有機物質の利材化方法。   The method for making a material for an organic material according to claim 10, wherein the low molecular weight modified product of the recovered organic material is blown into a blast furnace.
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