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TWI886552B - Circulating reduction system, iron ore reduction method and smelting furnace operating method - Google Patents

Circulating reduction system, iron ore reduction method and smelting furnace operating method Download PDF

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TWI886552B
TWI886552B TW112132363A TW112132363A TWI886552B TW I886552 B TWI886552 B TW I886552B TW 112132363 A TW112132363 A TW 112132363A TW 112132363 A TW112132363 A TW 112132363A TW I886552 B TWI886552 B TW I886552B
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gas
pipe
furnace
reduction
reduction system
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TW202426662A (en
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野呂寿人
瀬川浩司
久保貴哉
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日商杰富意礦物股份有限公司
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    • CCHEMISTRY; METALLURGY
    • C21METALLURGY OF IRON
    • C21BMANUFACTURE OF IRON OR STEEL
    • C21B5/00Making pig-iron in the blast furnace
    • C21B5/06Making pig-iron in the blast furnace using top gas in the blast furnace process
    • CCHEMISTRY; METALLURGY
    • C21METALLURGY OF IRON
    • C21BMANUFACTURE OF IRON OR STEEL
    • C21B11/00Making pig-iron other than in blast furnaces
    • CCHEMISTRY; METALLURGY
    • C21METALLURGY OF IRON
    • C21BMANUFACTURE OF IRON OR STEEL
    • C21B13/00Making spongy iron or liquid steel, by direct processes
    • C21B13/0073Selection or treatment of the reducing gases
    • CCHEMISTRY; METALLURGY
    • C21METALLURGY OF IRON
    • C21BMANUFACTURE OF IRON OR STEEL
    • C21B7/00Blast furnaces
    • C21B7/002Evacuating and treating of exhaust gases
    • CCHEMISTRY; METALLURGY
    • C21METALLURGY OF IRON
    • C21BMANUFACTURE OF IRON OR STEEL
    • C21B5/00Making pig-iron in the blast furnace
    • C21B5/001Injecting additional fuel or reducing agents
    • C21B2005/005Selection or treatment of the reducing gases
    • CCHEMISTRY; METALLURGY
    • C21METALLURGY OF IRON
    • C21BMANUFACTURE OF IRON OR STEEL
    • C21B2100/00Handling of exhaust gases produced during the manufacture of iron or steel
    • C21B2100/20Increasing the gas reduction potential of recycled exhaust gases
    • C21B2100/22Increasing the gas reduction potential of recycled exhaust gases by reforming
    • CCHEMISTRY; METALLURGY
    • C21METALLURGY OF IRON
    • C21BMANUFACTURE OF IRON OR STEEL
    • C21B2100/00Handling of exhaust gases produced during the manufacture of iron or steel
    • C21B2100/20Increasing the gas reduction potential of recycled exhaust gases
    • C21B2100/24Increasing the gas reduction potential of recycled exhaust gases by shift reactions
    • CCHEMISTRY; METALLURGY
    • C21METALLURGY OF IRON
    • C21BMANUFACTURE OF IRON OR STEEL
    • C21B2100/00Handling of exhaust gases produced during the manufacture of iron or steel
    • C21B2100/20Increasing the gas reduction potential of recycled exhaust gases
    • C21B2100/26Increasing the gas reduction potential of recycled exhaust gases by adding additional fuel in recirculation pipes
    • CCHEMISTRY; METALLURGY
    • C21METALLURGY OF IRON
    • C21BMANUFACTURE OF IRON OR STEEL
    • C21B2100/00Handling of exhaust gases produced during the manufacture of iron or steel
    • C21B2100/20Increasing the gas reduction potential of recycled exhaust gases
    • C21B2100/28Increasing the gas reduction potential of recycled exhaust gases by separation
    • C21B2100/282Increasing the gas reduction potential of recycled exhaust gases by separation of carbon dioxide
    • CCHEMISTRY; METALLURGY
    • C21METALLURGY OF IRON
    • C21BMANUFACTURE OF IRON OR STEEL
    • C21B2100/00Handling of exhaust gases produced during the manufacture of iron or steel
    • C21B2100/20Increasing the gas reduction potential of recycled exhaust gases
    • C21B2100/28Increasing the gas reduction potential of recycled exhaust gases by separation
    • C21B2100/284Increasing the gas reduction potential of recycled exhaust gases by separation of nitrogen
    • CCHEMISTRY; METALLURGY
    • C21METALLURGY OF IRON
    • C21BMANUFACTURE OF IRON OR STEEL
    • C21B2100/00Handling of exhaust gases produced during the manufacture of iron or steel
    • C21B2100/40Gas purification of exhaust gases to be recirculated or used in other metallurgical processes
    • C21B2100/44Removing particles, e.g. by scrubbing, dedusting
    • CCHEMISTRY; METALLURGY
    • C21METALLURGY OF IRON
    • C21BMANUFACTURE OF IRON OR STEEL
    • C21B2100/00Handling of exhaust gases produced during the manufacture of iron or steel
    • C21B2100/60Process control or energy utilisation in the manufacture of iron or steel
    • C21B2100/64Controlling the physical properties of the gas, e.g. pressure or temperature
    • CCHEMISTRY; METALLURGY
    • C21METALLURGY OF IRON
    • C21BMANUFACTURE OF IRON OR STEEL
    • C21B2100/00Handling of exhaust gases produced during the manufacture of iron or steel
    • C21B2100/60Process control or energy utilisation in the manufacture of iron or steel
    • C21B2100/66Heat exchange

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  • Engineering & Computer Science (AREA)
  • Chemical & Material Sciences (AREA)
  • Manufacturing & Machinery (AREA)
  • Materials Engineering (AREA)
  • Metallurgy (AREA)
  • Organic Chemistry (AREA)
  • Waste-Gas Treatment And Other Accessory Devices For Furnaces (AREA)
  • Manufacture Of Iron (AREA)

Abstract

本發明提供一種循環還原系統,其能夠將對自還原爐產生的包含CO 2的廢氣進行改質而獲得的富含CO的氣體作為還原氣體而有效率地進行循環利用。在本發明的循環還原系統100中,將在還原爐10中產生的包含CO 2的廢氣經由第一配管81而進行回收,自氫氣供給裝置30向廢氣中添加氫氣而製成氫化氣體。在觸媒裝置40中藉由逆水煤氣轉化反應將氫化氣體中的CO 2轉換為CO,從而成為CO濃度經提高的富含CO的氣體。富含CO的氣體經由第二配管82而作為還原氣體供給至還原爐10的內部。在第一配管81及第二配管82的中途不配置分離裝置,所述分離裝置自通過內部的氣體中分離水蒸氣以外的特定的氣體成分,並進行回收或去除。 The present invention provides a circulating reduction system that can efficiently circulate and utilize CO-rich gas obtained by reforming exhaust gas containing CO 2 generated from a reduction furnace as reducing gas. In the circulating reduction system 100 of the present invention, the exhaust gas containing CO 2 generated in the reduction furnace 10 is recovered through the first pipe 81, and hydrogen is added to the exhaust gas from the hydrogen supply device 30 to produce hydrogenated gas. In the catalyst device 40, CO 2 in the hydrogenated gas is converted into CO by a reverse water gas shift reaction, thereby becoming CO-rich gas with an increased CO concentration. The CO-rich gas is supplied to the inside of the reduction furnace 10 as reducing gas through the second pipe 82. A separation device for separating specific gas components other than water vapor from the gas passing through the inside and recovering or removing them is not arranged in the middle of the first pipe 81 and the second pipe 82.

Description

循環還原系統、鐵礦石還原方法以及熔礦爐操作方法Circulating reduction system, iron ore reduction method and smelting furnace operating method

本發明是有關於一種能夠根本性地削減促進全球變暖的CO 2的排出量的循環還原系統、鐵礦石還原方法以及熔礦爐操作方法。 The present invention relates to a circulation reduction system, an iron ore reduction method and a smelting furnace operating method capable of radically reducing the emission of CO2 which contributes to global warming.

在全球範圍內呼籲削減促進全球變暖的CO 2的排出量的過程中,佔日本國內的CO 2排出量的15%左右的該國內的鋼鐵業受政府方針影響並宣佈了2050年實現碳中和。為了實現這一點,需要開發出用於以接近現狀的水準的低成本製造粗鋼的鐵礦石還原製程及還原爐,但現狀是幾乎未確立該技術性的目標。 Amid calls for a reduction in CO2 emissions that contribute to global warming, Japan's steel industry, which accounts for about 15% of CO2 emissions in Japan, has been influenced by government policy and has announced that it will achieve carbon neutrality by 2050. To achieve this, it is necessary to develop an iron ore reduction process and reduction furnace that can produce crude steel at a low cost close to current levels, but the current technical goal has hardly been established.

此處,以氫作為鐵礦石的還原劑的氫還原製程視為不產生CO 2的理想的粗鋼生產技術而受到了全世界的關注。但是,若欲利用該方法維持國內每年約7500萬噸的鐵水的生產量,則需要大約750億Nm 3的氫。為了利用作為代表性的綠氫製造法的水電解法滿足該需求,即便忽略氫的輸送、液化、貯藏等所需的全部電力,亦估算每年需要0.34萬億kWh的電力。假設即便可解決電力成本高的課題,在年耗電量為1萬億kWh規模的日本,為國內的高爐製造商供應這麼多電力亦不得不說是極不現實的。 Here, the hydrogen reduction process, which uses hydrogen as a reducing agent for iron ore, has attracted worldwide attention as an ideal crude steel production technology that does not produce CO2 . However, if the domestic production of molten iron of about 75 million tons per year is to be maintained using this method, about 75 billion Nm3 of hydrogen is required. In order to meet this demand using water electrolysis, which is a representative green hydrogen production method, even if all the electricity required for hydrogen transportation, liquefaction, and storage is ignored, it is estimated that 0.34 trillion kWh of electricity is required per year. Even if the problem of high electricity costs can be solved, it is extremely unrealistic to supply such a large amount of electricity to domestic blast furnace manufacturers in Japan, where annual electricity consumption is 1 trillion kWh.

另一方面,亦正在進行自海外供應使用廉價的可再生能源而製造的大量的氫的各種嘗試。但是,即便可解決輸送成本高的課題,在煉鐵廠的周邊安全地大量貯藏爆炸濃度範圍廣的氫的技術性目標亦完全未確立。On the other hand, various attempts are being made to supply large quantities of hydrogen produced using cheap renewable energy from overseas. However, even if the problem of high transportation costs can be solved, the technical goal of safely storing large quantities of hydrogen with a wide range of explosive concentrations around steel smelters has not yet been established.

且說,國內的鋼鐵業排出國內的CO 2排出量的15%左右的CO 2的原因在於,主要利用使用焦炭對鐵礦石進行還原的高爐-轉爐法來生產高級鋼材。粗鋼的生產方法主要分類為高爐-轉爐法與電爐法,在高爐-轉爐法中,每1 t鋼材產生約2 t的CO 2,在電爐法中每1 t鋼材產生約0.5 t的CO 2。在可抑制CO 2的產生量的方面,電爐法更為優異。然而,汽車等中使用的高級鋼材由於銅等雜質容易對品質帶來不良影響,因此在以廢鐵為原料的電爐法中未批量生產。因此,國內的粗鋼的約75%利用高爐-轉爐法來生產。 The reason why the domestic steel industry emits about 15% of the country's CO2 emissions is that it mainly produces high-grade steel using the blast furnace-converter process, which uses coke to reduce iron ore. The production methods of crude steel are mainly classified into the blast furnace-converter process and the electric furnace process. In the blast furnace-converter process, about 2 tons of CO2 are generated for every ton of steel, and in the electric furnace process, about 0.5 tons of CO2 are generated for every ton of steel. The electric furnace process is superior in terms of suppressing the amount of CO2 generated. However, high-grade steel used in automobiles, etc., is easily adversely affected by impurities such as copper, so it is not mass-produced in the electric furnace process that uses scrap iron as raw materials. Therefore, about 75% of crude steel in the country is produced using the blast furnace-converter process.

對於CO 2的排出量特別多的高爐,例如在專利文獻1中,嘗試了藉由將自風口吹入的高溫空氣置換為氫或甲烷等還原氣體來削減焦炭的使用量。但是,焦炭不僅有作為還原劑的作用,亦有作為經由與自熱風爐吹入的氧的反應來對爐內進行加熱的加熱材的作用,以及作為確保爐內的通氣的通氣材的作用。因此,在找到用於維持爐內溫度、且不對鐵水的品質帶來不良影響地確保通氣性的(焦炭以外的)新手段之前,根本性地抑制焦炭的使用量極其困難。 For blast furnaces that emit a particularly high amount of CO 2 , for example, in Patent Document 1, attempts have been made to reduce the amount of coke used by replacing the high-temperature air blown in from the tuyere with a reducing gas such as hydrogen or methane. However, coke not only functions as a reducing agent, but also functions as a heating material for heating the furnace by reacting with oxygen blown in from the hot blast furnace, and as a ventilation material for ensuring ventilation in the furnace. Therefore, it is extremely difficult to fundamentally reduce the amount of coke used until a new means (other than coke) is found for maintaining the temperature in the furnace and ensuring ventilation without adversely affecting the quality of molten iron.

根據以上背景,日本的鋼鐵製造商的現狀是只能藉由削減高爐的作業台數來提高電爐的比率以應對當前局面。因此,電爐中使用的廢鐵的需求已經變得旺盛,預計為該供應而展開的激烈競爭今後將變得更加嚴峻。Against this backdrop, Japanese steelmakers are now forced to reduce the number of blast furnaces in operation and increase the ratio of electric furnaces to cope with the current situation. As a result, demand for scrap iron used in electric furnaces has become strong, and fierce competition for its supply is expected to become more severe in the future.

在此種狀況下,與高爐-轉爐法相比,CO 2排出量少的直接還原製程舉世矚目。在作為代表性的直接還原製程的所謂的米德萊克斯(Midrex)製程中,可利用改質天然氣將鐵礦石以固相的狀態進行還原而獲得直接還原鐵(DRI:Direct Reduced Iron)(參照引用文獻2)。由於在初期的米德萊克斯製程中僅可製造海綿狀的DRI,因此就氧化或起火的觀點而言,其處理或輸送一直困難。但是,在熱壓塊裝置經開發、工業化後,該些問題基本上被解決,藉由將DRI與廢鐵進行混合並投入至電爐中,削減投入廢鐵量而提高鋼材的品質的動向在世界範圍內逐漸擴展。進而,亦嘗試了藉由利用甲烷化反應(CO 2+4H 2→CH 4+2H 2O)而由CO 2與氫合成的甲烷來取代天然氣,或者取代為氫本身。 Under such circumstances, the direct reduction process, which has less CO 2 emissions than the blast furnace-converter process, has come to the fore. In the so-called Midrex process, which is a representative direct reduction process, iron ore is reduced in a solid phase using reformed natural gas to obtain direct reduced iron (DRI) (see reference 2). In the early days of the Midrex process, only spongy DRI could be produced, so it was difficult to handle or transport it from the perspective of oxidation or ignition. However, after the development and industrialization of hot-pressed equipment, these problems were basically solved, and the trend of reducing the amount of scrap iron input and improving the quality of steel by mixing DRI with scrap iron and feeding it into the electric furnace has gradually expanded around the world. Furthermore, attempts have been made to replace natural gas with methane synthesized from CO 2 and hydrogen by utilizing the methanation reaction (CO 2 +4H 2 →CH 4 +2H 2 O), or to replace it with hydrogen itself.

另一方面,在作為固相還原的直接還原製程中,若欲保持所製造的DRI的品位,則不得不使用對成本與供應有制約的高品位的鐵礦石作為原料。這一點相對於可將鐵礦石原料的約85%製成由低品位的微粉礦石或粉礦石製造出的球團或燒結礦的先前的高爐法而言成為大的缺點。On the other hand, in the direct reduction process as solid phase reduction, if the quality of the DRI produced is to be maintained, high-grade iron ore, which has cost and supply constraints, must be used as a raw material. This is a major disadvantage compared to the previous blast furnace method, which can produce about 85% of the iron ore raw material in the form of pellets or sintered ore made from low-grade fine ore or powder ore.

進而,在直接還原製程中,無法將粗鋼以鐵水的形式取出,因此無法沿用預處理爐或轉爐等先前的鋼鐵聯合製程的精煉設備。這一點亦成為日本的高爐製造商執著於高爐製程的一個原因。再者,推測直接還原製程停留在固相還原的原因在於,如上所述,無法根本性地解決維持通氣性與用於獲得鐵水的爐內溫度的課題。Furthermore, in the direct reduction process, crude steel cannot be taken out in the form of molten iron, so the refining equipment of the previous integrated steelmaking process, such as the pre-treatment furnace or converter, cannot be used. This is also one of the reasons why Japanese blast furnace manufacturers insist on the blast furnace process. Furthermore, it is speculated that the reason why the direct reduction process remains at solid phase reduction is that, as mentioned above, it is impossible to fundamentally solve the problem of maintaining the permeability and the temperature in the furnace for obtaining molten iron.

即,在高爐-轉爐法中,能夠代替焦炭的還原劑、加熱材及在不對鐵水的品質帶來不良影響的情況下確保通氣性的新手段成為主要的桎梏,根本性地削減焦炭使用量的目標尚未確立。另外,與高爐-轉爐法相比,CO 2排出量少的直接還原製程中有以下缺點:無法使用高爐中能夠使用的低成本且容易供應的低品位的微粉礦石或粉礦石,不將粗鋼作為鐵水取出,因此亦無法沿用先前的鋼鐵聯合製程的精煉設備。 That is, in the blast furnace-converter process, the main obstacles are the reducing agent that can replace coke, the heating material, and the new means to ensure the permeability without adversely affecting the quality of the molten iron, and the goal of fundamentally reducing the amount of coke used has not yet been established. In addition, compared with the blast furnace-converter process, the direct reduction process with less CO2 emissions has the following disadvantages: it cannot use the low-cost and easy-to-supply low-grade fine ores or powder ores that can be used in the blast furnace, and crude steel is not taken out as molten iron, so the refining equipment of the previous steelmaking process cannot be used.

根據此種背景,在專利文獻3中提出了一種利用來自高爐的廢氣中包含的CO 2的技術。即,提出了一種自高爐的廢氣中分離CO 2,並將回收的CO 2改質為CO,將該CO作為高爐的還原劑進行再利用。 [現有技術文獻] [專利文獻] Based on this background, Patent Document 3 proposes a technology for utilizing CO 2 contained in exhaust gas from a blast furnace. That is, it proposes a technology for separating CO 2 from the exhaust gas of a blast furnace, reforming the recovered CO 2 into CO, and reusing the CO as a reducing agent for the blast furnace. [Prior Art Document] [Patent Document]

[專利文獻1]國際公開第2021/220555號 [專利文獻2]日本專利特開2017-88912號公報 [專利文獻3]日本專利特開2011-225968號公報 [Patent Document 1] International Publication No. 2021/220555 [Patent Document 2] Japanese Patent Publication No. 2017-88912 [Patent Document 3] Japanese Patent Publication No. 2011-225968

[發明所欲解決之課題] 在所述專利文獻3所記載的技術中,將自高爐中產生的廢氣中分離回收的CO 2改質為CO進行再利用的結果,可抑制CO 2的產生量。然而,在該技術中,由於經過自廢氣中暫時分離回收CO 2並進行CO 2的改質的多個步驟,因此無法避免廢氣中的還原成分的循環效率的降低與各步驟的設備、運轉、維持所需的成本的負擔。因此,祈求使用更有效率的方法來對高爐等還原爐的廢氣中的還原成分進行循環利用。 [Problems to be Solved by the Invention] In the technology described in the aforementioned patent document 3, CO 2 separated and recovered from the exhaust gas generated in the blast furnace is reformed into CO for reuse, thereby suppressing the amount of CO 2 generated. However, in this technology, since CO 2 is temporarily separated and recovered from the exhaust gas and CO 2 is reformed through multiple steps, it is inevitable that the recycling efficiency of the reducing components in the exhaust gas is reduced and the cost of the equipment, operation, and maintenance of each step is incurred. Therefore, it is desired to use a more efficient method to recycle the reducing components in the exhaust gas of a reducing furnace such as a blast furnace.

鑒於所述課題,本發明的目的在於提供一種循環還原系統,其能夠將對自還原爐產生的包含CO 2的廢氣進行改質而獲得的富含CO的氣體作為還原氣體而有效率地進行循環利用。 In view of the above-mentioned subject, an object of the present invention is to provide a circulating reduction system which can efficiently circulate and utilize CO-rich gas obtained by reforming exhaust gas containing CO 2 generated from a reduction furnace as reducing gas.

另外,本發明的目的在於提供一種鐵礦石還原方法,其能夠將對自還原爐產生的包含CO 2的廢氣進行改質而獲得的富含CO的氣體作為還原氣體而有效率地進行循環利用,以進行鐵礦石的還原處理。 In addition, the object of the present invention is to provide an iron ore reduction method, which can efficiently circulate the CO-rich gas obtained by reforming the exhaust gas containing CO2 generated from the reduction furnace as reducing gas to carry out the reduction treatment of iron ore.

另外,本發明的目的在於提供一種熔礦爐操作方法,其能夠使用所述循環還原系統維持爐內溫度,且藉由焦炭以外的手段來確保通氣性。 [解決課題之手段] In addition, the object of the present invention is to provide a method for operating a smelting furnace, which is capable of maintaining the temperature in the furnace using the circulating reduction system and ensuring the permeability by means other than coke. [Means for Solving the Problem]

本發明者等對實現可將來自還原爐的廢氣作為還原劑的起始原料而循環利用該廢氣的有效率的還原製程的方法進行了努力研究,結果發現,藉由使用所謂的逆水煤氣轉化反應,可有效率地實現廢氣的循環再利用。The inventors of the present invention have conducted intensive research on a method for realizing an efficient reduction process that can circulate and utilize the exhaust gas from a reduction furnace as a starting material of a reducing agent, and have found that the exhaust gas can be efficiently circulated and reused by using the so-called reverse water gas shift reaction.

即,在鐵礦石的還原製程中產生的廢氣中一般而言不僅包含CO 2或源自大氣的氮,亦包含CO或H 2等剩餘的還原劑。例如,在高爐的廢氣中包含23體積%左右的CO 2、相同比例的CO、4體積%左右的H 2、以及50體積%左右的源自空氣的氮。本發明者等想到,在藉由向此種廢氣中加入氫並使該氣體與逆水煤氣轉化反應(RWGS:Reverse Water Gas Shift反應:CO 2+H 2→CO+H 2O)用的觸媒接觸,而將廢氣中的CO 2與CO的平衡大幅轉換為富CO後,與廢氣中原本包含的H 2及氮一起作為還原氣體進行循環利用。認識到,若此種循環利用成為可能,則可將先前使用的、例如焦炭等源自化石燃料的還原劑的投入量限於最小限度內。 That is, the exhaust gas generated in the reduction process of iron ore generally contains not only CO 2 and nitrogen from the atmosphere, but also residual reducing agents such as CO and H 2. For example, the exhaust gas from a blast furnace contains about 23% by volume of CO 2 , the same proportion of CO, about 4% by volume of H 2 , and about 50% by volume of nitrogen from the air. The inventors of the present invention have thought that by adding hydrogen to such exhaust gas and bringing the gas into contact with a catalyst for reverse water gas shift reaction (RWGS: Reverse Water Gas Shift reaction: CO 2 +H 2 →CO+H 2 O), the balance of CO 2 and CO in the exhaust gas is largely shifted to be rich in CO, and then recycled as reducing gas together with H 2 and nitrogen originally contained in the exhaust gas. The inventors have recognized that if such recycling is possible, the input amount of reducing agents derived from fossil fuels such as coke, which have been used in the past, can be limited to a minimum.

此處,將CO作為主要的還原劑進行循環利用的原因在於,利用H 2進行的鐵礦石的還原反應是吸熱反應,相對於此,利用CO進行的鐵礦石的還原反應是放熱反應,因此CO是可將還原爐內維持為高溫的最有效率的還原劑。另外,在利用CO的還原中,可直接利用由以焦炭作為還原劑時發現的碳引起的鐵的凝固點下降。藉此,在利用H 2的還原的情況下若並非1500℃以上則不熔融的還原鐵在利用CO的還原中在1200℃左右熔融。存在該約300℃的溫差的情況將大大減輕將還原鐵作為鐵水取出時的還原氣體的加熱爐的熱負荷。 Here, CO is circulated as the main reducing agent because the reduction reaction of iron ore by H2 is an endothermic reaction, while the reduction reaction of iron ore by CO is an exothermic reaction, so CO is the most efficient reducing agent that can maintain the temperature in the reduction furnace at a high temperature. In addition, in the reduction by CO, the freezing point of iron caused by carbon found when coke is used as a reducing agent can be directly utilized. Thereby, the reduced iron that does not melt unless it is 1500°C or above in the case of reduction by H2 melts at about 1200°C in the reduction by CO. The presence of this temperature difference of about 300°C greatly reduces the heat load of the heating furnace for the reducing gas when the reduced iron is taken out as molten iron.

另外,由富CO 2的廢氣合成的富CO的還原氣體主要供給至還原爐,但剩餘部分能夠進行排出、回收而轉用於各種用途。CO不僅有作為還原劑或燃料氣體的用途,亦是合成各種有機物時重要的費雪-闕布希(Fischer-Tropsch)反應(nCO+(2n+1)H 2→C nH 2n+2+nH 2O)的起始原料。因此,由富CO 2的廢氣合成的富CO的還原氣體並不限於還原劑,亦為能夠無剩餘地轉用為燃料氣體或各種有機化合物的原料的合成氣體。特別是若為了防止全球變暖而大幅削減化石燃料的使用量,則一直以其為原料的有機化學產業必須重新找到原料的供應商。該些產業成為所述合成氣體的接受體的意義重大。 In addition, the CO-rich reducing gas synthesized from CO2 -rich exhaust gas is mainly supplied to the reduction furnace, but the surplus can be discharged, recovered, and converted to various uses. CO is not only used as a reducing agent or fuel gas, but also an important starting material for the Fischer-Tropsch reaction (nCO+(2n+1) H2CnH2n +2 + nH2O ) in the synthesis of various organic substances. Therefore, the CO-rich reducing gas synthesized from CO2- rich exhaust gas is not limited to a reducing agent, but also a synthesis gas that can be converted to a fuel gas or a raw material for various organic compounds without surplus. In particular, if the use of fossil fuels is greatly reduced in order to prevent global warming, the organic chemical industry that has been using them as raw materials must find new suppliers of raw materials. It is of great significance for these industries to become acceptors of the synthesis gas.

如上所述般,投入至一般的高爐中的焦炭不僅有作為還原劑的作用,亦有作為加熱材與通氣材的作用。因此,在將還原鐵作為鐵水取出的情況下,即便可利用還原氣體中的CO的還原熱來維持爐內溫度,若將焦炭的投入量抑制至極限,則亦無法確保通氣性(無法維持穩定的還原環境)。As mentioned above, the coke put into a general blast furnace not only acts as a reducing agent, but also as a heating material and a ventilation material. Therefore, when the reduced iron is taken out as molten iron, even if the reduction heat of CO in the reducing gas can be used to maintain the temperature in the furnace, if the amount of coke put in is suppressed to the limit, ventilation cannot be ensured (a stable reducing environment cannot be maintained).

新認識到,該問題可藉由以下方式來解決:利用鑄模對與鐵水一起產生並自爐底排出的熔融爐渣的一部分進行緩冷、破碎,並將其作為通氣材混入焦炭中,自爐頂重新投入。即,高爐爐渣的熔點為約1400℃,因此,即便在高爐內因C而凝固點下降的鐵開始進行熔融的時點,該爐渣亦保持固體狀態而起到作為通氣材的作用。另外,由於該爐渣原本是熔礦爐中生成的物質,因此即便進行循環利用亦不會改變熔礦爐內的物質環境。It was newly recognized that this problem can be solved by using a mold to slowly cool and crush part of the molten slag that is produced with the molten iron and discharged from the bottom of the furnace, and then mixing it with the coke as a ventilation material and re-introducing it from the top of the furnace. That is, the melting point of blast furnace slag is about 1400℃, so even when the iron in the blast furnace, whose solidification point is lowered by C, begins to melt, the slag remains in a solid state and acts as a ventilation material. In addition, since the slag is originally a substance generated in the smelting furnace, even if it is recycled, it will not change the material environment in the smelting furnace.

再者,僅將緩冷、破碎後的爐渣作為通氣材,僅將還原氣體作為還原劑來啟動熔礦爐操作並不容易。因此,與通常的高爐同樣地,在高爐內交替地積層還原劑兼通氣材的焦炭與鐵源之後,在吹入利用熱風爐加熱後的高溫空氣的「高爐模式」下首先啟動熔礦爐。然後,階段性地切換為在焦炭中緩緩混合爐渣,同時向吹入至熔礦爐中的空氣中緩緩加入還原氣體的「無焦炭模式」。在使熔礦爐休止的情況下,若按照該相反的順序在無焦炭模式後在高爐模式下結束操作,則重新啟動會變得容易。Furthermore, it is not easy to start the melting furnace operation using only the slowly cooled and crushed slag as the ventilation material and only the reducing gas as the reducing agent. Therefore, as with a normal blast furnace, the melting furnace is first started in the "blast furnace mode" where high-temperature air heated by a hot blast furnace is blown in after alternating layers of coke and iron source, which are both reducing agents and ventilation materials, in the blast furnace. Then, the melting furnace is gradually switched to the "coke-free mode" where the slag is gradually mixed with the coke and the reducing gas is gradually added to the air blown into the melting furnace. When the melting furnace is shut down, restarting becomes easy if the operation is terminated in the blast furnace mode after the coke-free mode in the reverse order.

本發明是基於以上見解而成者,其主旨如以下所述。 [1]一種循環還原系統,具有:還原爐,對收容於內部的氧化物進行還原; 第一配管,自所述還原爐回收在所述還原爐中產生且包含CO 2的廢氣並使其通過; 氫氣供給裝置,連接於所述第一配管的中途,向所述廢氣中添加氫氣而製成氫化氣體; 觸媒裝置,與所述第一配管的終端連接,具有收容逆水煤氣轉化反應用的觸媒的反應室,自所述第一配管導入至所述反應室中的所述氫化氣體與所述觸媒接觸,利用逆水煤氣轉化反應將所述氫化氣體中的CO 2轉換為CO,從而製成CO濃度經提高的富含CO的氣體;以及 第二配管,自所述觸媒裝置延伸,與所述還原爐連接,使所述富含CO的氣體通過,將所述富含CO的氣體作為還原氣體供給至所述還原爐的內部, 在所述第一配管及所述第二配管的中途不配置分離裝置,所述分離裝置自通過內部的氣體中分離水蒸氣以外的特定的氣體成分,並進行回收或去除。 The present invention is based on the above findings, and its main purpose is as follows. [1] A circulating reduction system, comprising: a reduction furnace, which reduces oxides contained therein; a first pipe, which recovers exhaust gas containing CO2 generated in the reduction furnace from the reduction furnace and passes the exhaust gas through the reduction furnace; a hydrogen supply device, which is connected to the middle of the first pipe and adds hydrogen to the exhaust gas to produce hydrogenated gas; a catalyst device, which is connected to the end of the first pipe and has a reaction chamber for containing a catalyst for a reverse water gas shift reaction, wherein the hydrogenated gas introduced into the reaction chamber from the first pipe contacts the catalyst, and the CO2 in the hydrogenated gas is reduced by the reverse water gas shift reaction. 2 is converted into CO, thereby producing a CO-rich gas with an increased CO concentration; and a second pipe extending from the catalyst device and connected to the reduction furnace, allowing the CO-rich gas to pass through, and supplying the CO-rich gas to the interior of the reduction furnace as a reducing gas, and no separation device is arranged in the middle of the first pipe and the second pipe, and the separation device separates specific gas components other than water vapor from the gas passing through the interior and recovers or removes them.

[2]如所述[1]所述的循環還原系統,具有氣體加熱裝置,所述氣體加熱裝置配置於所述第二配管的中途,對所述富含CO的氣體進行加熱。[2] The circulating reduction system described in [1] above, further comprising a gas heating device, wherein the gas heating device is disposed in the middle of the second pipe and heats the CO-rich gas.

[3]如所述[2]所述的循環還原系統,具有第三配管,所述第三配管在所述第二配管的中途自較所述氣體加熱裝置更靠上游的位置分支並與所述氣體加熱裝置連接,經由所述第三配管而將所述富含CO的氣體的一部分作為燃燒氣體而供給至所述氣體加熱裝置。[3] The circulating reduction system as described in [2] has a third pipe, which branches from the second pipe at a position upstream of the gas heating device and is connected to the gas heating device, and a portion of the CO-rich gas is supplied to the gas heating device as combustion gas through the third pipe.

[4]如所述[2]或[3]所述的循環還原系統,具有第四配管,所述第四配管自所述氣體加熱裝置延伸並連接於所述第一配管的中途,經由所述第四配管而使自所述氣體加熱裝置產生的燃燒廢氣與所述第一配管內的所述廢氣合流。[4] The circulation reduction system as described in [2] or [3] has a fourth pipe, which extends from the gas heating device and is connected to the middle of the first pipe, so that the combustion exhaust gas generated from the gas heating device is combined with the exhaust gas in the first pipe through the fourth pipe.

[5]如所述[1]至[4]中任一項所述的循環還原系統,其中,所述觸媒裝置具有對所述反應室進行加熱的加熱裝置, 所述循環還原系統具有第五配管,所述第五配管自所述第二配管分支並與所述加熱裝置連接,經由所述第五配管而將所述富含CO的氣體的一部分作為燃燒氣體而供給至所述加熱裝置。 [5] A circulating reduction system as described in any one of [1] to [4], wherein the catalyst device has a heating device for heating the reaction chamber, and the circulating reduction system has a fifth pipe, the fifth pipe is branched from the second pipe and connected to the heating device, and a portion of the CO-rich gas is supplied to the heating device as combustion gas through the fifth pipe.

[6]如所述[5]所述的循環還原系統,具有第六配管,所述第六配管自所述加熱裝置延伸並連接於所述第一配管的中途,經由所述第六配管而使自所述加熱裝置產生的燃燒廢氣與所述第一配管內的所述廢氣合流。[6] The circulation reduction system described in [5] has a sixth pipe extending from the heating device and connected to the middle of the first pipe, and the combustion exhaust gas generated from the heating device is combined with the exhaust gas in the first pipe through the sixth pipe.

[7]如所述[1]至[6]中任一項所述的循環還原系統,具有第一除濕器,所述第一除濕器在所述第一配管的中途配置於較供所述氫氣供給裝置連接的部位更靠上游處,自所述廢氣中去除水蒸氣。[7] The circulation reduction system described in any one of [1] to [6] has a first dehumidifier, which is arranged in the middle of the first pipe and upstream of the position connected to the hydrogen supply device, and removes water vapor from the exhaust gas.

[8]如所述[1]至[7]中任一項所述的循環還原系統,具有第二除濕器,所述第二除濕器配置於所述第二配管的中途,自所述富含CO的氣體中去除水蒸氣。[8] The recycling reduction system described in any one of [1] to [7] has a second dehumidifier, which is arranged in the middle of the second pipe and removes water vapor from the CO2-rich gas.

[9]如所述[1至[8]中任一項所述的循環還原系統,具有:切換閥,配置於所述第二配管的中途;以及第七配管,自所述切換閥延伸, 經由所述第七配管而回收所述富含CO的氣體的一部分。 [9] A circulation reduction system as described in any one of [1 to [8], comprising: a switching valve disposed in the middle of the second pipe; and a seventh pipe extending from the switching valve, and recovering a portion of the CO-rich gas through the seventh pipe.

[10]如所述[9]所述的循環還原系統,具有第三除濕器,所述第三除濕器配置於所述第七配管的中途,自通過所述第七配管的所述富含CO的氣體中去除水蒸氣。[10] The recycling reduction system described in [9] has a third dehumidifier, which is arranged in the middle of the seventh pipe and removes water vapor from the CO-rich gas passing through the seventh pipe.

[11]如所述[1]至[10]中任一項所述的循環還原系統,其中,所述還原爐為熔礦爐,所述氧化物為鐵礦石。[11] The circulating reduction system as described in any one of [1] to [10], wherein the reduction furnace is a smelting furnace and the oxide is iron ore.

[12]如所述[11]所述的循環還原系統,其中,所述熔礦爐為高爐。[12] The circulating reduction system as described in [11], wherein the smelting furnace is a blast furnace.

[13]一種鐵礦石還原方法,使用如所述[1]至[12]中任一項所述的循環還原系統,將對所述廢氣進行改質而獲得的所述富含CO的氣體作為所述還原氣體進行循環利用,進行作為所述氧化物的鐵礦石的還原處理。[13] A method for reducing iron ore, using the circulating reduction system as described in any one of [1] to [12], wherein the CO-rich gas obtained by reforming the exhaust gas is circulated as the reducing gas to reduce the iron ore as the oxide.

[14]一種熔礦爐操作方法,為使用如所述[11]或[12]所述的循環還原系統的熔礦爐操作方法,其中, 自所述熔礦爐的爐頂將(I)作為所述鐵礦石且選自燒結礦、塊礦石、鐵礦石球團及粉礦石中的至少一種、及(II)將對自所述熔礦爐的底部排出的熔融爐渣進行緩冷而獲得的凝固爐渣破碎後的破碎爐渣、或者包含所述破碎爐渣與焦炭的混合物的通氣材交替地呈層狀裝入至所述熔礦爐內,從而確保所述還原氣體的爐內通氣性。 [14] A method for operating a smelting furnace using the circulating reduction system described in [11] or [12], wherein: (I) at least one of the iron ore selected from sintered ore, lump ore, iron ore pellets and powdered ore, and (II) crushed slag obtained by crushing solidified slag obtained by slowly cooling molten slag discharged from the bottom of the smelting furnace, or a mixture of the crushed slag and coke are alternately loaded into the smelting furnace in layers from the top of the smelting furnace, thereby ensuring the in-furnace permeability of the reducing gas.

[15]如所述[14]所述的熔礦爐操作方法,其中,自位於所述熔礦爐的下部的風口將所述還原氣體與空氣作為吹入氣體而供給至所述熔礦爐的內部, 使所述通氣材中的所述破碎爐渣相對於所述焦炭的比例與所述吹入氣體中的所述還原氣體相對於所述空氣的比例階段性地增加,以階段性地抑制所述焦炭的使用量。 [發明的效果] [15] A method for operating a melting furnace as described in [14], wherein the reducing gas and air are supplied as injection gas to the interior of the melting furnace from a tuyere located at the bottom of the melting furnace, so that the ratio of the crushed slag to the coke in the ventilation material and the ratio of the reducing gas to the air in the injection gas are increased in stages, thereby gradually suppressing the amount of coke used. [Effect of the invention]

藉由本發明的循環還原系統,可將對自還原爐產生的包含CO 2的廢氣進行改質而獲得的富含CO的氣體作為還原氣體而有效率地進行循環利用。 According to the circulating reduction system of the present invention, CO-rich gas obtained by reforming exhaust gas containing CO 2 generated from a reduction furnace can be efficiently circulated and utilized as reducing gas.

藉由本發明的鐵礦石的還原方法,可將對自還原爐產生的包含CO 2的廢氣進行改質而獲得的富含CO的氣體作為還原氣體而有效率地進行循環利用,以進行鐵礦石的還原處理。 According to the iron ore reduction method of the present invention, CO-rich gas obtained by reforming CO2- containing exhaust gas generated from a reduction furnace can be efficiently circulated as reducing gas to carry out the reduction treatment of iron ore.

藉由本發明的熔礦爐操作方法,可使用所述循環還原系統,維持爐內溫度,且藉由焦炭以外的手段來確保通氣性。According to the smelting furnace operating method of the present invention, the circulating reduction system can be used to maintain the temperature in the furnace and ensure the permeability by means other than coke.

[循環還原系統] 參照圖1對基於本發明的一實施形態的循環還原系統100進行說明。循環還原系統100具有還原爐10、第一除濕器20、氫氣供給裝置30、觸媒裝置40、第二除濕器50、及氣體加熱裝置60,作為配管設備而具有第一配管81、第二配管82、第三配管83、第四配管84、第五配管85、第六配管86、第七配管87、及切換閥90。 [Circulation reduction system] Referring to FIG. 1 , a circulation reduction system 100 according to an embodiment of the present invention is described. The circulation reduction system 100 has a reduction furnace 10, a first dehumidifier 20, a hydrogen supply device 30, a catalyst device 40, a second dehumidifier 50, and a gas heating device 60, and as piping equipment, has a first piping 81, a second piping 82, a third piping 83, a fourth piping 84, a fifth piping 85, a sixth piping 86, a seventh piping 87, and a switching valve 90.

還原爐10例如可為高爐等熔礦爐。在還原爐10為熔礦爐的情況下,自爐頂12向還原爐10內裝入鐵礦石及焦炭,自位於還原爐10的下部的風口14向還原爐10內吹入高溫的還原氣體,藉此在還原爐10內進行鐵礦石的還原。The reduction furnace 10 may be, for example, a molten metal furnace such as a blast furnace. When the reduction furnace 10 is a molten metal furnace, iron ore and coke are charged into the reduction furnace 10 from the furnace top 12, and a high-temperature reducing gas is blown into the reduction furnace 10 from a tuyere 14 located at the bottom of the reduction furnace 10, thereby reducing the iron ore in the reduction furnace 10.

第一配管81是自還原爐10回收在還原爐10中產生的包含CO 2的廢氣並使其通過的配管設備。第一配管81的始端與還原爐10(在一例中為爐頂12)連接,終端與觸媒裝置40連接。在第一配管81的中途連接氫氣供給裝置30。另外,在第一配管81的中途,在較連接氫氣供給裝置30的部位更靠上游處配置第一除濕器20。第一配管81具有自還原爐10延伸並與第一除濕器20連接的配管81A、以及自第一除濕器20延伸並與觸媒裝置40連接的配管81B。再者,在本說明書中,所謂與配管相關的「上游」或「下游」,設為與配管內的氣體流通方向相關者。 The first piping 81 is a piping device for recovering the exhaust gas containing CO2 generated in the reducing furnace 10 from the reducing furnace 10 and passing it. The starting end of the first piping 81 is connected to the reducing furnace 10 (in one example, the furnace top 12), and the terminal end is connected to the catalyst device 40. The hydrogen supply device 30 is connected in the middle of the first piping 81. In addition, the first dehumidifier 20 is arranged in the middle of the first piping 81 at a position upstream of the portion connected to the hydrogen supply device 30. The first piping 81 has a piping 81A extending from the reducing furnace 10 and connected to the first dehumidifier 20, and a piping 81B extending from the first dehumidifier 20 and connected to the catalyst device 40. In this specification, the term "upstream" or "downstream" in relation to piping refers to the term in relation to the direction in which gas flows in the piping.

自還原爐10的爐頂12排出的廢氣在第一配管81中流動的過程中,在藉由第一除濕器20實施了除濕處理後,自氫氣供給裝置30補給氫氣(H 2)氣體,從而成為氫化氣體。為了抑制水煤氣轉化反應以促進逆水煤氣轉化反應,較佳為進行除濕處理。廢氣的組成並無特別限定,但典型而言,具有如下組成:除水蒸氣外,含有CO 2:13體積%~24體積%、CO:21體積%~31體積%、及H 2:3體積%~15體積%,剩餘部分包含源自空氣的N 2。氫化氣體的組成並無特別限定,但典型而言,具有如下組成:除水蒸氣外,含有CO 2:13體積%~24體積%、CO:21體積%~31體積%、及H 2:10體積%~30體積%,剩餘部分包含源自空氣的N 2。自氫氣供給裝置30供給的氫理想的是藉由利用了可再生能源的水電解法而獲得的綠氫,但在藉由將本發明的循環還原系統應用於高爐操作而使焦炭的使用量成為零之前,可利用由焦爐煤氣精製而得的氫來代替。 The exhaust gas discharged from the top 12 of the reduction furnace 10 flows in the first pipe 81, and after being dehumidified by the first dehumidifier 20, hydrogen (H 2 ) gas is supplied from the hydrogen supply device 30, thereby becoming hydrogenated gas. In order to suppress the water gas shift reaction and promote the reverse water gas shift reaction, it is preferable to perform the dehumidification treatment. The composition of the exhaust gas is not particularly limited, but typically has the following composition: except for water vapor, it contains CO 2 : 13 volume % to 24 volume %, CO: 21 volume % to 31 volume %, and H 2 : 3 volume % to 15 volume %, and the remainder contains N 2 derived from air. The composition of the hydrogenated gas is not particularly limited, but typically has the following composition: in addition to water vapor, it contains CO 2 : 13 volume % to 24 volume %, CO: 21 volume % to 31 volume %, and H 2 : 10 volume % to 30 volume %, and the remainder contains N 2 from air. The hydrogen supplied from the hydrogen gas supply device 30 is ideally green hydrogen obtained by water electrolysis using renewable energy, but before the use of coke is reduced to zero by applying the circulating reduction system of the present invention to blast furnace operation, hydrogen purified from coke furnace gas can be used instead.

再者,較佳為,在第一配管81的中途,在較第一除濕器20更靠上游處,或者在較第一除濕器20更靠下游且較與氫氣供給裝置30連接的部位更靠上游處設置除塵裝置(未圖示),對廢氣實施除塵處理,從而將源自原料的粉塵自廢氣中除去。Furthermore, it is preferable to install a dust removal device (not shown) in the middle of the first piping 81, upstream of the first dehumidifier 20, or downstream of the first dehumidifier 20 and upstream of the portion connected to the hydrogen gas supply device 30, to perform dust removal treatment on the exhaust gas, thereby removing dust originating from the raw materials from the exhaust gas.

觸媒裝置(逆轉化型重組器)40與第一配管81的終端連接,且具有:反應室42,收容逆水煤氣轉化反應用的觸媒;以及加熱裝置44,對該反應室42進行加熱。在觸媒裝置40中,自第一配管81導入至反應室42中的氫化氣體與觸媒接觸,在逆水煤氣轉化反應中將氫化氣體中的CO 2轉換為CO,從而成為CO濃度經提高的富含CO的氣體。逆水煤氣轉化反應後的富含CO的氣體的組成並無特別限定,典型而言,具有如下組成,除水蒸氣外,含有CO 2:6體積%~20體積%、CO:24體積%~40體積%、及H 2:5體積%~24體積%、剩餘部分包含源自空氣的N 2。能夠用於逆水煤氣轉化反應的觸媒已知有鎳基體或貴金屬基體等多種,但本發明中使用的觸媒可為其任一種。 The catalyst device (reversal reformer) 40 is connected to the terminal of the first pipe 81 and includes: a reaction chamber 42 for accommodating a catalyst for the reverse water gas shift reaction; and a heating device 44 for heating the reaction chamber 42. In the catalyst device 40, the hydrogenated gas introduced into the reaction chamber 42 from the first pipe 81 contacts the catalyst, and CO2 in the hydrogenated gas is converted into CO in the reverse water gas shift reaction, thereby becoming a CO-rich gas with an increased CO concentration. The composition of the CO-rich gas after the reverse water gas shift reaction is not particularly limited, and typically has the following composition: in addition to water vapor, it contains CO 2 : 6 vol% to 20 vol%, CO: 24 vol% to 40 vol%, and H 2 : 5 vol% to 24 vol%, and the remainder contains N 2 from air. There are many known catalysts that can be used for the reverse water gas shift reaction, such as nickel substrates or precious metal substrates, but the catalyst used in the present invention may be any of them.

在使氫化氣體與觸媒裝置40內的觸媒接觸時,就作為吸熱反應的逆水煤氣轉化反應的轉換效率的觀點而言,理想的是在觸媒不易劣化的溫度範圍內,將所導入的氫化氣體的溫度盡可能設定為高溫。具體而言,較佳為藉由加熱裝置44預先對反應室42內進行加熱,以使觸媒周邊的反應氣體(氫化氣體)的溫度成為800℃以上且1200℃以下。When the hydrogenated gas is brought into contact with the catalyst in the catalyst device 40, from the viewpoint of the conversion efficiency of the reverse water gas shift reaction, which is an endothermic reaction, it is desirable to set the temperature of the introduced hydrogenated gas as high as possible within a temperature range in which the catalyst is not easily degraded. Specifically, it is preferred to preheat the reaction chamber 42 by the heating device 44 so that the temperature of the reaction gas (hydrogenated gas) around the catalyst is 800° C. or higher and 1200° C. or lower.

第二配管82是自觸媒裝置40延伸並與還原爐10(在一例中為風口14)連接,使富含CO的氣體通過,將富含CO的氣體作為還原氣體(在一例中經由風口14)供給至還原爐10的內部的配管設備。較佳為在第二配管82的中途配置自富含CO的氣體中去除水蒸氣的第二除濕器50、以及對富含CO的氣體進行加熱的氣體加熱裝置60。在該情況下,較佳為在第二除濕器50的下游配置氣體加熱裝置60。在該情況下,第二配管82具有自觸媒裝置40延伸並與第二除濕器50連接的配管82A、自第二除濕器50延伸並與氣體加熱裝置60連接的配管82B、自氣體加熱裝置60延伸並與還原爐10(在一例中為風口14)連接的配管82C。The second pipe 82 is a pipe device extending from the catalyst device 40 and connected to the reduction furnace 10 (in one example, the tuyere 14), allowing the CO-rich gas to pass through, and supplying the CO-rich gas as reducing gas (in one example, through the tuyere 14) to the inside of the reduction furnace 10. It is preferable to arrange the second dehumidifier 50 for removing water vapor from the CO-rich gas and the gas heating device 60 for heating the CO-rich gas in the middle of the second pipe 82. In this case, it is preferable to arrange the gas heating device 60 downstream of the second dehumidifier 50. In this case, the second piping 82 includes a piping 82A extending from the catalyst device 40 and connected to the second dehumidifier 50, a piping 82B extending from the second dehumidifier 50 and connected to the gas heating device 60, and a piping 82C extending from the gas heating device 60 and connected to the reduction furnace 10 (in one example, the tuyere 14).

通過了觸媒裝置40的富含CO的氣體在第二配管82中流動的過程中,在藉由第二除濕器50實施了除濕處理後,藉由氣體加熱裝置60進行加熱,然後作為還原氣體被吹入至還原爐10內。The CO-rich gas that has passed through the catalyst device 40 is dehumidified by the second dehumidifier 50 while flowing in the second pipe 82. Thereafter, the gas is heated by the gas heating device 60 and then blown into the reduction furnace 10 as reducing gas.

即,理想的是在利用所述觸媒的反應後,利用氣體加熱裝置60對要吹入至還原爐10中的富含CO的氣體(還原氣體)的溫度進行調整。關於還原爐10中的鐵礦石的還原效率,還原氣體越高溫越有優勢,但在進行鐵礦石的固相還原的情況下,理想的是將吹入至還原爐10內的還原氣體的溫度設為900℃以上。另外,在將還原鐵作為1500℃的鐵水取出時,需要將形成於還原爐10的下方區域的鐵源與爐渣的熔融區域的溫度維持為1650℃以上,因此理想的是,若焦炭的投入量達到先前的高爐的50%左右,則以還原氣體的溫度成為1200℃以上的方式對還原氣體進行加熱之後進行吹入,若焦炭的投入量小於先前的高爐的20%,則以還原氣體的溫度成為1500℃以上的方式對還原氣體進行加熱之後進行吹入。That is, it is desirable to adjust the temperature of the CO-rich gas (reducing gas) to be blown into the reduction furnace 10 by the gas heating device 60 after the reaction using the catalyst. Regarding the reduction efficiency of the iron ore in the reduction furnace 10, the higher the temperature of the reducing gas, the more advantageous it is. However, in the case of solid phase reduction of the iron ore, it is desirable to set the temperature of the reducing gas blown into the reduction furnace 10 to 900° C. or higher. In addition, when the reduced iron is taken out as molten iron at 1500°C, the temperature of the molten zone of the iron source and slag formed in the lower area of the reduction furnace 10 needs to be maintained at above 1650°C. Therefore, it is ideal that if the amount of coke input reaches about 50% of the previous blast furnace, the reducing gas is heated in such a way that the temperature of the reducing gas becomes above 1200°C and then blown in. If the amount of coke input is less than 20% of the previous blast furnace, the reducing gas is heated in such a way that the temperature of the reducing gas becomes above 1500°C and then blown in.

氣體加熱裝置60的較佳的操作如以下所述。本實施形態的循環還原系統100較佳為具有第三配管83,所述第三配管83在第二配管82的中途自較氣體加熱裝置60更靠上游且較第二除濕器50更靠下游的位置分支並與氣體加熱裝置60連接。並且,較佳為經由第三配管83將在第二配管82中流動的富含CO的氣體的一部分作為燃燒氣體供給至氣體加熱裝置60中。如此,藉由在氣體加熱裝置60中將富含CO的氣體的一部分作為燃料氣體而使其燃燒,可將還原氣體的溫度提高至所述所期望的溫度。雖在圖1中省略,但為了使燃燒氣體燃燒而向氣體加熱裝置60供給的含氧的氣體較佳為(不包含未經消耗的氮的)氧氣。The preferred operation of the gas heating device 60 is as follows. The circulation reduction system 100 of the present embodiment preferably has a third pipe 83, which branches from a position more upstream than the gas heating device 60 and more downstream than the second dehumidifier 50 in the middle of the second pipe 82 and is connected to the gas heating device 60. Furthermore, it is preferred to supply a portion of the CO-rich gas flowing in the second pipe 82 as a combustion gas to the gas heating device 60 via the third pipe 83. In this way, by burning a portion of the CO-rich gas as a fuel gas in the gas heating device 60, the temperature of the reduction gas can be increased to the desired temperature. Although omitted in FIG. 1 , the oxygen-containing gas supplied to the gas heating device 60 for burning the combustion gas is preferably oxygen gas (not containing unconsumed nitrogen).

循環還原系統100較佳為具有第四配管84,所述第四配管84自氣體加熱裝置60延伸並連接於第一配管81的中途。第四配管84具有上游部分84A及下游部分84B。並且,較佳為經由第四配管84而使自氣體加熱裝置60產生的燃燒廢氣與第一配管81內的廢氣合流,並進行再利用。第四配管84較佳為在第一配管81的中途連接於較第一除濕器20更靠上游的位置。當在使自氣體加熱裝置60產生的燃燒廢氣與(1)觸媒裝置40和氣體加熱裝置60之間的還原氣體配管、(2)氫氣供給裝置30和觸媒裝置40之間的氫化氣體配管進行熱交換之後,在第一除濕器20的上游與第一配管81內的廢氣合流時,亦可對還原氣體與氫化氣體進行預熱。The circulation reduction system 100 preferably has a fourth pipe 84 extending from the gas heating device 60 and connected to the middle of the first pipe 81. The fourth pipe 84 has an upstream portion 84A and a downstream portion 84B. Furthermore, it is preferred that the combustion exhaust gas generated from the gas heating device 60 is merged with the exhaust gas in the first pipe 81 through the fourth pipe 84 and reused. The fourth pipe 84 is preferably connected to a position upstream of the first dehumidifier 20 in the middle of the first pipe 81. When the combustion exhaust gas generated from the gas heating device 60 is subjected to heat exchange with (1) the reducing gas piping between the catalyst device 40 and the gas heating device 60 and (2) the hydrogenated gas piping between the hydrogen supply device 30 and the catalyst device 40, and then merges with the exhaust gas in the first piping 81 upstream of the first dehumidifier 20, the reducing gas and the hydrogenated gas can be preheated.

再者,在如圖1所例示般的、利用間接加熱式的氣體加熱裝置60無法將還原氣體完全提高至所期望的溫度的情況下,亦可自氣體加熱裝置60的前端附近添加氧等,使還原氣體中包含的CO或H 2的一部分直接燃燒。另外,若在高爐模式下在啟動時,向還原爐10內吹入的熱風中使用利用深冷分離法等形成為富氧的空氣,則由於被氮的加熱奪走的氣體加熱裝置60的熱負荷下降,因此容易提高還原氣體的溫度。 Furthermore, when the reducing gas cannot be completely raised to the desired temperature by the indirect heating type gas heating device 60 as shown in FIG1 , oxygen or the like may be added near the front end of the gas heating device 60 to directly burn a portion of CO or H2 contained in the reducing gas. In addition, when the hot air blown into the reducing furnace 10 at the time of startup in the blast furnace mode is oxygen-enriched air made by cryogenic separation or the like, the heat load of the gas heating device 60 taken away by the heating of nitrogen is reduced, so that the temperature of the reducing gas can be easily raised.

接著,對於觸媒裝置40的較佳的操作,亦同樣較佳為使用富含CO的氣體的一部分作為燃燒氣體。即,本實施形態的循環還原系統100較佳為具有第五配管85,所述第五配管85自第二配管82分支並與觸媒裝置40的加熱裝置44連接。第五配管85較佳為在第二配管82的中途,自較氣體加熱裝置60更靠上游且較第二除濕器50更靠下游的位置分支。並且,較佳為經由第五配管85將富含CO的氣體的一部分作為燃燒氣體而供給至加熱裝置44中。雖在圖1中省略,但為了使燃燒氣體燃燒而供給至加熱裝置44中的含氧的氣體較佳為(不包含未經消耗的氮的)氧氣。Next, for the preferred operation of the catalyst device 40, it is also preferred to use a part of the CO-rich gas as the combustion gas. That is, the circulation reduction system 100 of the present embodiment preferably has a fifth pipe 85, which branches from the second pipe 82 and is connected to the heating device 44 of the catalyst device 40. The fifth pipe 85 is preferably branched from the middle of the second pipe 82, from a position more upstream than the gas heating device 60 and more downstream than the second dehumidifier 50. And, it is preferred to supply a part of the CO-rich gas as the combustion gas to the heating device 44 through the fifth pipe 85. Although omitted in FIG. 1 , the oxygen-containing gas supplied to the heating device 44 for burning the combustion gas is preferably oxygen gas (not containing unconsumed nitrogen).

循環還原系統100較佳為具有第六配管86,所述第六配管86自加熱裝置44延伸並連接於第一配管81的中途。並且,較佳為經由第六配管86而使自加熱裝置44產生的燃燒廢氣與第一配管81內的廢氣合流,並進行再利用。再者,在本實施形態中,由於將第六配管86的上游部分86A連接於作為來自氣體加熱裝置60的燃料廢氣流路的第四配管84的中途,因此第六配管86的下游部分86B兼作第四配管84的下游部分84B。但是,本發明並不限定於此,當然亦可與第四配管84獨立地將第六配管86直接連接於第一配管81。當在使自加熱裝置44產生的燃燒廢氣與氫氣供給裝置30和觸媒裝置40之間的氫化氣體配管進行熱交換之後,在第一除濕器20的上游與第一配管81內的廢氣合流時,亦可對氫化氣體進行預熱。The circulation reduction system 100 preferably has a sixth pipe 86 extending from the heating device 44 and connected to the middle of the first pipe 81. Furthermore, it is preferred that the combustion exhaust gas generated from the heating device 44 is merged with the exhaust gas in the first pipe 81 through the sixth pipe 86 and reused. Furthermore, in the present embodiment, since the upstream portion 86A of the sixth pipe 86 is connected to the middle of the fourth pipe 84 which is the fuel exhaust gas flow path from the gas heating device 60, the downstream portion 86B of the sixth pipe 86 also serves as the downstream portion 84B of the fourth pipe 84. However, the present invention is not limited thereto, and of course the sixth pipe 86 may be directly connected to the first pipe 81 independently of the fourth pipe 84. When the combustion exhaust gas generated from the heating device 44 is heat-exchanged with the hydrogen gas piping between the hydrogen gas supply device 30 and the catalyst device 40 and then merges with the exhaust gas in the first piping 81 upstream of the first dehumidifier 20, the hydrogen gas can be preheated.

在以上所說明的本實施形態中,藉由反復進行如下步驟,即利用還原氣體的吹入的鐵礦石的還原步驟、來自還原爐的廢氣的回收步驟、廢氣的除塵及除濕步驟(任意步驟)、對廢氣的氫化步驟、藉由逆水煤氣轉化反應而自氫化氣體生成富含CO的氣體的步驟、富含CO的氣體的除濕步驟(任意步驟)、富含CO的氣體的加熱步驟(任意步驟)及富含CO的氣體作為還原氣體的吹入步驟,而實現將來自還原爐10的廢氣在封閉的循環系統中進行再利用的循環製程。In the present embodiment described above, by repeatedly performing the following steps, namely, a reduction step of iron ore by blowing in reducing gas, a recovery step of exhaust gas from the reduction furnace, a dust removal and dehumidification step of the exhaust gas (optional step), a hydrogenation step of the exhaust gas, a step of generating a CO-rich gas from the hydrogenated gas by a reverse water gas shift reaction, a dehumidification step of the CO-rich gas (optional step), a heating step of the CO-rich gas (optional step) and a blowing step of the CO-rich gas as reducing gas, a circulation process for reusing the exhaust gas from the reduction furnace 10 in a closed circulation system is realized.

作為還原氣體的富含CO的氣體中殘留的未轉換的CO 2在循環製程的過程中總歸會成為CO源,因此無需自還原氣體中分離。即,在本實施形態中,重要的是在第一配管81及第二配管82的中途不配置分離裝置,所述分離裝置自通過內部的氣體中分離水蒸氣以外的特定的氣體成分,並進行回收或去除。在本實施形態中,除可應用現有技術的除塵及除濕以外,不需要新的分離濃縮過程,因此還原氣體的循環效率高。 The unconverted CO2 remaining in the CO-rich gas as the reducing gas will always become a CO source during the circulation process, so it does not need to be separated from the reducing gas. That is, in this embodiment, it is important that a separation device is not arranged in the middle of the first pipe 81 and the second pipe 82, and the separation device separates specific gas components other than water vapor from the gas passing through the inside and recovers or removes them. In this embodiment, in addition to the dust removal and dehumidification of the existing technology, no new separation and concentration process is required, so the circulation efficiency of the reducing gas is high.

在本實施形態中,由於利用以等莫耳的氫將CO 2轉換為CO的逆水煤氣轉化反應,因此與將利用需要CO 2的4倍莫耳的氫的甲烷化反應生成的甲烷作為還原劑的所述先前還原法相比,可將每CO 2的氫的供應量抑制為約1/4。 In this embodiment, since the reverse water gas shift reaction is used to convert CO2 into CO with equimolar hydrogen, the supply amount of hydrogen per CO2 can be suppressed to about 1/4 compared to the previous reduction method that uses methane generated by a methanation reaction requiring 4 times the molar amount of hydrogen as CO2 as a reducing agent.

在本實施形態中,將自廢氣改質後的以CO為主體的還原氣體以高溫供給至還原爐10內,可將鐵礦石中的雜質作為熔融爐渣而自鐵水中分離,因此與一般的高爐相同,可將在成本方面有利且供應亦容易的低品位的微粉礦石或粉礦石用作球團或燒結礦。In the present embodiment, reducing gas mainly composed of CO after reforming the exhaust gas is supplied to the reduction furnace 10 at a high temperature, and impurities in the iron ore can be separated from the molten iron as molten slag. Therefore, as with a general blast furnace, low-grade fine powder ore or powder ore, which is cost-effective and easy to supply, can be used as pellets or sintered ore.

再者,富含CO的氣體的剩餘部分(在本實施形態中為還原氣體、氣體加熱裝置60的燃燒氣體、及作為加熱裝置44的燃燒氣體而使用的富含CO的氣體的殘留部分)可進行回收。即,循環還原系統100具有配置於第二配管82的中途的切換閥90、以及自該切換閥90延伸的第七配管87,可經由該第七配管87而回收富含CO的氣體的一部分。所回收的富含CO的氣體例如可用作成為有機化合物的原料的合成氣體。在本實施形態中,實現將自還原爐10排出的富CO 2的廢氣轉換為富CO的還原氣體並進行循環利用的系統,因此藉由將富含CO的氣體的剩餘部分作為合成氣體而在有機化學產業等中有效利用,可將對大氣的CO 2排出量抑制至零水準。 Furthermore, the remaining portion of the CO-rich gas (in this embodiment, the reduced gas, the combustion gas of the gas heating device 60, and the residual portion of the CO-rich gas used as the combustion gas of the heating device 44) can be recovered. That is, the recycling reduction system 100 has a switching valve 90 disposed in the middle of the second pipe 82 and a seventh pipe 87 extending from the switching valve 90, and a portion of the CO-rich gas can be recovered through the seventh pipe 87. The recovered CO-rich gas can be used as a synthesis gas that becomes a raw material of an organic compound, for example. In this embodiment, a system is realized that converts the CO2 -rich exhaust gas discharged from the reduction furnace 10 into a CO-rich reducing gas and circulates it for utilization. Therefore, by effectively utilizing the remaining CO-rich gas as synthesis gas in the organic chemical industry, etc., the CO2 emission to the atmosphere can be suppressed to zero level.

另外,利用鑄模對自鐵水分離出的熔融爐渣進行緩冷而製成凝固爐渣,對該凝固爐渣進行破碎而製成破碎爐渣,可將其作為透氣材進行再利用。在源自該爐渣的通氣材附著有自還原爐(熔礦爐)排出的生鐵的一部分的情況下,可經由該通氣材而將作為鐵源的生鐵返回至還原爐。In addition, the molten slag separated from the iron water is slowly cooled in a casting mold to form solidified slag, and the solidified slag is crushed to form crushed slag, which can be reused as a breathable material. If a part of the pig iron discharged from the reduction furnace (melting furnace) is attached to the breathable material derived from the slag, the pig iron as an iron source can be returned to the reduction furnace through the breathable material.

再者,熔融爐渣根據比重差自動地排出至鐵水的表面,因此即便進行循環利用亦幾乎不會對鐵水的品質帶來不良影響。另外,循環利用後的熔融爐渣具有與通常的高爐爐渣同等的品質,因此可作為高爐水泥等的原料進行工業利用。Furthermore, the molten slag is automatically discharged to the surface of the molten iron due to the difference in specific gravity, so even if it is recycled, it will hardly have any adverse effect on the quality of the molten iron. In addition, the recycled molten slag has the same quality as ordinary blast furnace slag, so it can be used industrially as a raw material for blast furnace cement, etc.

參照圖2對基於本發明的另一實施形態的循環還原系統200進行說明。循環還原系統200不具有第二除濕器50,取而代之,在第七配管87的中途配置有第三除濕器70,除此以外,具有與循環還原系統100相同的結構。即,在本發明中第二除濕器50並非必需的結構。較佳為,在不配置第二除濕器50的情況下,藉由第三除濕器70自通過第七配管87的富含CO的氣體中去除水蒸氣。Referring to FIG. 2 , a recycling reduction system 200 according to another embodiment of the present invention is described. The recycling reduction system 200 does not have the second dehumidifier 50, but instead, a third dehumidifier 70 is arranged in the middle of the seventh piping 87. In other respects, the recycling reduction system 200 has the same structure as the recycling reduction system 100. That is, the second dehumidifier 50 is not an essential structure in the present invention. Preferably, when the second dehumidifier 50 is not arranged, water vapor is removed from the CO-rich gas passing through the seventh piping 87 by the third dehumidifier 70.

上述內容中,主要對還原爐10為高爐等熔礦爐,還原對象物為鐵礦石的情況進行了說明,但本發明並不限定於此。還原爐10亦可為固體還原爐。另外,若還原對象物為氧化物則並不限定於鐵礦石,例如亦可為作為錳鐵或矽錳的原料的錳礦石。In the above description, the reduction furnace 10 is mainly a melting furnace such as a blast furnace, and the reduction object is iron ore. However, the present invention is not limited to this. The reduction furnace 10 may also be a solid reduction furnace. In addition, if the reduction object is an oxide, it is not limited to iron ore, and for example, it may be manganese ore as a raw material of iron manganese or silicon manganese.

[鐵礦石還原方法] 基於本發明的一實施形態的鐵礦石還原方法使用所述循環還原系統100、循環還原系統200,將對廢氣進行改質而獲得的富含CO的氣體作為還原氣體進行循環利用,從而進行作為氧化物的鐵礦石的還原處理。藉此,可將對自還原爐10產生的包含CO 2的廢氣進行改質而獲得的富含CO的氣體作為還原氣體而有效率地進行循環利用,以進行鐵礦石的還原處理。 [Iron Ore Reduction Method] The iron ore reduction method according to one embodiment of the present invention uses the above-mentioned circulating reduction system 100 and circulating reduction system 200 to circulate the CO-rich gas obtained by reforming the exhaust gas as a reducing gas, thereby reducing the iron ore as an oxide. In this way, the CO-rich gas obtained by reforming the exhaust gas containing CO2 generated from the reduction furnace 10 can be efficiently circulated as a reducing gas to reduce the iron ore.

另外,藉由本實施形態的還原方法,實現可將來自還原爐10的廢氣作為還原劑的起始原料而循環利用該廢氣的有效率的還原製程,因此可顯著地減少CO 2產生量。進而,能夠根本性地抑制在鐵礦石還原製程中先前使用的焦炭等源自化石燃料的還原劑的投入量。 In addition, the reduction method of this embodiment realizes an efficient reduction process that can circulate the exhaust gas from the reduction furnace 10 as a starting material of the reducing agent, thereby significantly reducing the amount of CO2 generated. Furthermore, the input amount of reducing agents such as coke derived from fossil fuels that have been used in the iron ore reduction process can be fundamentally suppressed.

[熔礦爐操作方法] 基於本發明的一實施形態的熔礦爐操作方法使用所述循環還原系統100、循環還原系統200來進行。並且,重要的是,自還原爐(熔礦爐)10的爐頂,將(I)作為鐵礦石且選自燒結礦、塊礦石、鐵礦石球團及粉礦石中的至少一種(鐵源)、及(II)將對自熔礦爐的底部排出的熔融爐渣進行緩冷而獲得的凝固爐渣破碎後的破碎爐渣、或者包含所述破碎爐渣與焦炭的混合物的通氣材交替地呈層狀裝入至熔礦爐內,從而確保所述還原氣體的爐內通氣性。藉此,可使用所述循環還原系統100、循環還原系統200來維持爐內溫度,且藉由焦炭以外的手段來確保通氣性。 [Method for operating a smelting furnace] A method for operating a smelting furnace according to an embodiment of the present invention is performed using the circulating reduction system 100 and the circulating reduction system 200. Furthermore, it is important that (I) at least one of iron ore selected from sintered ore, lump ore, iron ore pellets and powdered ore (iron source) and (II) crushed slag obtained by slowly cooling molten slag discharged from the bottom of the molten furnace or a mixture of the crushed slag and coke are alternately charged into the molten furnace in layers at the top of the reduction furnace (melting furnace) 10, thereby ensuring the in-furnace permeability of the reducing gas. In this way, the circulating reduction system 100 and the circulating reduction system 200 can be used to maintain the furnace temperature and ensure the permeability by means other than coke.

在基於本實施形態的操作中,將還原氣體與空氣作為吹入氣體自風口14供給至熔礦爐的內部。此時,較佳為使通氣材中的破碎爐渣相對於焦炭的比例與吹入氣體中的還原氣體相對於空氣的比例階段性地增加,從而階段性地抑制焦炭的使用量。In the operation based on this embodiment, reducing gas and air are supplied as injection gas into the melting furnace from the tuyere 14. At this time, it is preferable to increase the ratio of crushed slag to coke in the ventilation material and the ratio of reducing gas to air in the injection gas in stages, thereby gradually reducing the amount of coke used.

藉由基於本實施形態的熔礦爐操作方法,能夠使用低成本且容易供應的低品位的微粉礦石或粉礦石以鐵水的形式獲得還原鐵,因此可在下一步驟以後直接轉用先前的鋼鐵聯合製程。By using the smelting furnace operation method according to the present embodiment, it is possible to obtain reduced iron in the form of molten iron using low-grade micro-powder ore or powder ore that is low-cost and easily available, so that the previous steelmaking integrated process can be directly switched to after the next step.

高爐的通氣程度能夠以破碎爐渣的粒度進行調整,例如以添加通氣口的形式對緩冷爐渣進行澆鑄,則進一步容易確保通氣。再者,即便在通氣材中使用一般的熔礦爐爐渣亦沒有特別的問題。The ventilation level of the blast furnace can be adjusted by the particle size of the crushed slag. For example, by adding vents to the slowly cooled slag for casting, ventilation can be further ensured. Furthermore, there are no special problems even if ordinary molten furnace slag is used as the ventilation material.

在基於本實施形態的熔礦爐操作方法中,在循環熔礦爐100、循環熔礦爐200中產生的熔融爐渣的量較通常的高爐多出自爐頂12再投入的爐渣在融合帶以後再熔融的量。另外,若投入的爐渣變多,則作為爐渣的熔化熱而被奪走的熱量亦增加。因此,在高爐模式下啟動操作時,理想的是預先對鐵源層與通氣層的層厚比進行調整,以使鐵源層較一般的高爐更富集。 [實施例] In the smelting furnace operation method based on this embodiment, the amount of molten slag produced in the circulating smelting furnace 100 and the circulating smelting furnace 200 is greater than that in a conventional blast furnace because the slag re-injected from the furnace top 12 is re-melted after the fusion zone. In addition, if more slag is added, the amount of heat taken away as the melting heat of the slag also increases. Therefore, when starting the operation in the blast furnace mode, it is ideal to adjust the layer thickness ratio of the iron source layer and the ventilation layer in advance so that the iron source layer is more enriched than that of a conventional blast furnace. [Example]

[實施例1] 如以下所述,作為發明例1、發明例2及比較例,進行了用於對本發明的還原方法的效果進行確認的平衡計算。 [Example 1] As described below, as Invention Example 1, Invention Example 2, and Comparative Example, a balance calculation was performed to confirm the effect of the reduction method of the present invention.

(發明例1) 將基於發明例1的循環還原系統的平衡計算模型示於圖3中。作為初始狀態,設想如下狀態:裝有25莫耳的氧化鐵(III)(Fe 2O 3)的還原爐10與裝有包含CO:22莫耳、CO 2:22.8莫耳、H 2:4.2莫耳、N 2:51莫耳的總計100莫耳的相當於高爐廢氣的混合氣體的作為觸媒裝置40的逆轉化型重組器(以下,簡稱為「重組器40」)連接。在重組器的入側設置第一除濕器20,在重組器的出側設置第二除濕器50,在第一除濕器與重組器之間設置將重組器內的H 2莫耳數維持為22.8莫耳(相當於高爐廢氣中的CO 2濃度)的氫氣供給裝置30。若自氫氣供給裝置供給的H 2與被第一除濕器及第二除濕器去除的H 2O以外的氣體相對於還原爐及重組器無出入,則由於所有的H 2O自經消耗的H 2生成,因此可認為在重組器與還原爐中循環的混合氣體的總計莫耳數不變化。 (Invention Example 1) The equilibrium calculation model of the cyclic reduction system based on Invention Example 1 is shown in FIG3. As an initial state, the following state is assumed: a reduction furnace 10 charged with 25 mol of iron (III) oxide ( Fe2O3 ) is connected to a reverse conversion type reformer (hereinafter referred to as "reformer 40 " ) as a catalyst device 40 charged with a mixed gas equivalent to blast furnace exhaust gas containing 100 mol in total of CO: 22 mol, CO2 : 22.8 mol, H2: 4.2 mol, and N2: 51 mol. A first dehumidifier 20 is provided at the inlet side of the reformer, a second dehumidifier 50 is provided at the outlet side of the reformer, and a hydrogen supply device 30 is provided between the first dehumidifier and the reformer to maintain the H2 molar number in the reformer at 22.8 moles (equivalent to the CO2 concentration in the blast furnace exhaust gas). If the H2 supplied from the hydrogen supply device and the gas other than the H2O removed by the first dehumidifier and the second dehumidifier do not enter or exit the reduction furnace and the reformer, since all the H2O is generated from the consumed H2 , it can be considered that the total molar number of the mixed gas circulating in the reformer and the reduction furnace does not change.

在本發明例1中,還原爐與重組器內的溫度均設為藉由自外部供給的熱量而保持為900℃的狀態。實際上,在還原爐與重組器之間進行氣體循環時需要氣體輸送系統,但出於確認原理的目的,忽略被其消耗的能量。同樣地,亦忽略第一除濕器、第二除濕器、及氫氣供給裝置的驅動所消耗的能量。由於重組器中的逆水煤氣轉化反應有時達不到平衡狀態,因此會受所使用的觸媒性能左右,但假設達到了平衡反應。In Example 1 of the present invention, the temperature in the reduction furnace and the reformer is maintained at 900°C by heat supplied from the outside. In fact, a gas transport system is required for gas circulation between the reduction furnace and the reformer, but for the purpose of confirming the principle, the energy consumed by it is ignored. Similarly, the energy consumed by driving the first dehumidifier, the second dehumidifier, and the hydrogen supply device is also ignored. Since the reverse water gas shift reaction in the reformer sometimes cannot reach a balanced state, it will be affected by the performance of the catalyst used, but it is assumed that a balanced reaction is achieved.

此處,考慮以如下操作作為一個循環,並反復進行所述操作的循環製程:將氫化氣體在重組器內迎來穩定狀態時生成的還原氣體全部送出至還原爐中,將還原反應迎來穩定狀態時的還原爐內氣體作為廢氣而取出,向其中添加達到一定水準的氫至再次製成氫化氣體為止。利用計算力學研究中心股份有限公司製造的熱力學平衡計算軟體&熱力學資料庫Fact Sage 8.1算出自重組器向還原爐送出還原氣體的每個循環中所發生的重組器內及還原爐內的氣體成分及鐵源的平衡狀態。將其結果示於圖4中。再者,在重組器與還原爐中生成的化合物中亦包含甲烷等,但忽略了0.005莫耳以下的微量成分。Here, a cyclic process is considered in which the following operation is repeated as one cycle: all the reducing gas generated when the hydrogenated gas reaches a stable state in the reformer is sent to the reducing furnace, the gas in the reducing furnace when the reduction reaction reaches a stable state is taken out as waste gas, and a certain level of hydrogen is added to it until hydrogenated gas is produced again. The thermodynamic balance calculation software & thermodynamic database Fact Sage 8.1 manufactured by the Computational Mechanics Research Center Co., Ltd. is used to calculate the gas composition and iron source equilibrium state in the reformer and the reducing furnace in each cycle of sending reducing gas from the reformer to the reducing furnace. The results are shown in Figure 4. Furthermore, the compounds generated in the reformer and the reducer also include methane, etc., but trace components below 0.005 mol are ignored.

在所述還原爐內,藉由自重組器供給的CO與未被逆水煤氣轉化反應消耗的剩餘的H 2進行鐵源的還原。作為鐵源而投入的固相的Fe 2O 3在第一個循環中變化為2倍莫耳的FeO(固相),在第二個循環以後,FeO逐漸被還原而變化為α-Fe(固相),同時在第七個循環中還原完成。主要的還原反應是自FeO向α-Fe的反應,這一點與高爐中已知的見解相符。該鐵源的還原所消耗的H 2量為89莫耳。 In the reduction furnace, the iron source is reduced by CO supplied from the reformer and the remaining H2 not consumed by the reverse water gas shift reaction. The solid Fe2O3 introduced as the iron source is converted into 2 times the mole of FeO (solid phase) in the first cycle. After the second cycle, FeO is gradually reduced and converted into α-Fe (solid phase), and the reduction is completed in the seventh cycle. The main reduction reaction is the reaction from FeO to α-Fe, which is consistent with the known view in the blast furnace. The amount of H2 consumed in the reduction of the iron source is 89 moles.

(發明例2) 將基於發明例2的循環還原系統的平衡計算模型示於圖5中。除在重組器的出側不設置第二除濕器這一點外,其與圖3所示的基於發明例1的循環還原系統的平衡計算模型相同。計算條件亦與發明例1同樣地算出重組器內及還原爐內的氣體成分及鐵源的平衡狀態。將其結果示於圖6中。 (Invention Example 2) The equilibrium calculation model of the circulation reduction system based on Invention Example 2 is shown in FIG5. It is the same as the equilibrium calculation model of the circulation reduction system based on Invention Example 1 shown in FIG3, except that the second dehumidifier is not provided on the outlet side of the reformer. The calculation conditions are also the same as those of Invention Example 1, and the equilibrium state of the gas composition and the iron source in the reformer and the reduction furnace are calculated. The result is shown in FIG6.

作為鐵源而投入的固相的Fe 2O 3在第一個循環中變化為2倍莫耳的FeO(固相),在第三個循環以後,FeO逐漸被還原而變化為α-Fe(固相),同時在第九個循環中還原完成。主要的還原反應是自FeO向α-Fe的反應,這一點與在高爐中已知的見解相符。該鐵源的還原所消耗的H 2量為85莫耳。 The solid Fe2O3 introduced as the iron source changes to 2 moles of FeO (solid phase) in the first cycle. After the third cycle, FeO is gradually reduced to α-Fe (solid phase), and the reduction is completed in the ninth cycle. The main reduction reaction is from FeO to α-Fe, which is consistent with the known view in the blast furnace. The amount of H2 consumed for the reduction of this iron source is 85 moles.

(比較例) 將基於比較例的循環還原系統的平衡計算模型示於圖7中。除不設置重組器及第二除濕器這一點外,其與圖3所示的基於發明例1的循環還原系統的平衡計算模型相同。計算條件亦與發明例1同樣地算出重組器內及還原爐內的氣體成分及鐵源的平衡狀態。將其結果示於圖8中。 (Comparative Example) The equilibrium calculation model of the circulation reduction system based on the comparative example is shown in FIG7. It is the same as the equilibrium calculation model of the circulation reduction system based on the inventive example 1 shown in FIG3 except that the reformer and the second dehumidifier are not provided. The calculation conditions are also the same as those of the inventive example 1 to calculate the equilibrium state of the gas composition and the iron source in the reformer and the reduction furnace. The result is shown in FIG8.

在比較例的還原爐內,僅利用自氫氣供給裝置直接投入至還原爐中的H 2進行鐵源的還原。作為鐵源而投入的25莫耳的Fe 2O 3(固相)在第一個循環中變化為8.2莫耳的Fe 3O 4(固相)與22.5莫耳的FeO(固相),在第二個循環以後,FeO逐漸被還原而變化為α-Fe(固相),同時與發明例2相同,在第九個循環中還原完成。主要的還原反應是自FeO向α-Fe的反應,這一點與發明例1、發明例2相同。該鐵源的還原所消耗的H 2量為較發明例2少10莫耳的75莫耳。 In the reduction furnace of the comparative example, the iron source is reduced only by using H2 directly fed into the reduction furnace from the hydrogen gas supply device. 25 mol of Fe2O3 (solid phase) fed as the iron source changes to 8.2 mol of Fe3O4 (solid phase) and 22.5 mol of FeO (solid phase) in the first cycle. After the second cycle, FeO is gradually reduced and changes to α-Fe (solid phase). At the same time, as in Invention Example 2, the reduction is completed in the ninth cycle. The main reduction reaction is the reaction from FeO to α-Fe, which is the same as Invention Example 1 and Invention Example 2. The amount of H2 consumed in the reduction of the iron source is 75 mol, which is 10 mol less than that of Invention Example 2.

(還原爐內的吸熱量) 發明例1、發明例2與比較例的大的不同在於在還原爐內的吸熱量。將根據利用Fact Sage 8.1算出的各反應的反應熱計算出的還原爐內的反應熱(吸熱量)示於圖9及圖10中。 (Heat absorption in the reduction furnace) The biggest difference between Invention Example 1 and Invention Example 2 and the comparative example is the heat absorption in the reduction furnace. The heat of reaction (heat absorption) in the reduction furnace calculated based on the heat of reaction of each reaction calculated using Fact Sage 8.1 is shown in Figures 9 and 10.

關於利用H 2的鐵源的直接還原,若除初期完成的自Fe 2O 3向Fe 3O 4的反應外,均為吸熱反應。相對於此,在發明例1的利用CO與剩餘H 2的鐵源的還原中,基於CO還原的發熱量補充基於H 2還原的吸熱量,因此可大幅抑制總計的吸熱量(參照圖9)。另外,在發明例2中,在FeO的還原區域,基於CO還原的發熱量超過基於H 2還原的吸熱量,因此FeO的還原溫度自發地維持為高溫(參照圖9)。若鐵源投入量增加,則FeO的還原階段進一步延長。通常,對需要將內部維持為高溫的還原爐自風口與爐頂以外供給熱極其困難。因此,若考慮到需要以投入至還原爐中的焦炭的燃燒熱來補充該吸收熱,則本發明例的優越性顯而易見。 Regarding the direct reduction of the iron source using H2 , except for the reaction from Fe2O3 to Fe3O4 that is completed in the initial stage, all reactions are endothermic reactions. In contrast, in the reduction of the iron source using CO and excess H2 in Invention Example 1, the heat generated by CO reduction supplements the heat absorbed by H2 reduction, so the total heat absorbed can be greatly suppressed (see Figure 9). In addition, in Invention Example 2, in the reduction area of FeO, the heat generated by CO reduction exceeds the heat absorbed by H2 reduction, so the reduction temperature of FeO is spontaneously maintained at a high temperature (see Figure 9). If the amount of iron source input increases, the reduction stage of FeO is further extended. Generally, it is extremely difficult to supply heat from outside the tuyere and the furnace top to a reduction furnace that needs to maintain a high temperature inside. Therefore, considering that the absorption heat must be supplemented by the combustion heat of the coke fed into the reduction furnace, the superiority of the present invention is obvious.

另外,根據圖10,預計用於使FeO在還原區域中的發熱量最大的對重組器的H 2補給量與廢氣中的CO 2的莫耳量為相同程度。可認為若抑制對重組器的H 2的補給量,則還原速度亦會下降,因此實際上是根據還原爐內的溫度與還原速度的平衡對H 2補給量進行調整。 In addition, according to Figure 10, the amount of H2 supplied to the reformer to maximize the calorific value of FeO in the reduction zone is expected to be about the same as the molar amount of CO2 in the exhaust gas. It is considered that if the amount of H2 supplied to the reformer is suppressed, the reduction rate will also decrease, so the amount of H2 supplied is actually adjusted based on the balance between the temperature in the reduction furnace and the reduction rate .

[實施例2] 如以下所述,作為發明例3、發明例4,進行使用了實驗用的循環還原系統的鐵礦石的還原。 [Example 2] As described below, as Invention Examples 3 and 4, reduction of iron ore was performed using an experimental cycle reduction system.

(發明例3) 將基於發明例3的實驗用的循環還原系統的結構示於圖11中。在圖11中,在將設置於重量計上的作為實驗用還原爐的BF模擬器(以下,稱為「還原爐10」)的爐底部隔開的鎢網上,形成了交替積層有粉碎為5 mm左右的焦炭2.2 kg與粉碎為3 mm左右的塊礦石5.0 kg而得的原料塊A。 (Invention Example 3) The structure of the experimental cyclic reduction system based on Invention Example 3 is shown in FIG11. In FIG11, raw material blocks A obtained by alternating layers of 2.2 kg of coke crushed to about 5 mm and 5.0 kg of lump ore crushed to about 3 mm are formed on a tungsten mesh that separates the furnace bottom of a BF simulator (hereinafter referred to as "reduction furnace 10") set on a weighing scale as an experimental reduction furnace.

進而,在原料塊A上形成了原料塊B,所述原料塊B是將在所述焦炭1.1 kg中均勻地混合有粉碎為5 mm左右的高爐緩冷爐渣2.8 kg而成者與粉碎為3 mm左右的塊礦石5.0 kg交替積層而得。Furthermore, on the raw material block A, a raw material block B was formed. The raw material block B was obtained by uniformly mixing 2.8 kg of blast furnace slow-cooling slag crushed to about 5 mm in 1.1 kg of the above coke and 5.0 kg of lump ore crushed to about 3 mm, and stacking them alternately.

自爐頂部排出的廢氣經過除塵裝置、除濕器20、第一套電管狀爐40、除濕器、第二套電管狀爐40、除濕器50、及蓄熱型的氣體加熱裝置60後,經由切換閥91,一方面與廢氣處理裝置連接,另一方面與還原爐下部的噴嘴92連接。兩套電管狀爐40是在中心部設置了保持有鉑觸媒51 g的石英製反應管的陶瓷電管狀爐。The exhaust gas discharged from the top of the furnace passes through the dust removal device, the dehumidifier 20, the first set of electric tube-shaped furnaces 40, the dehumidifier, the second set of electric tube-shaped furnaces 40, the dehumidifier 50, and the heat storage type gas heating device 60, and is connected to the exhaust gas treatment device through the switching valve 91 on the one hand, and is connected to the nozzle 92 at the bottom of the reduction furnace on the other hand. The two sets of electric tube-shaped furnaces 40 are ceramic electric tube-shaped furnaces with a quartz reaction tube holding a platinum catalyst 51 g set in the center.

在第一套電管狀爐40的跟前、以及第二套電管狀爐40與除濕器50之間的兩個部位設置氣體組成分析用的採樣管並與微氣相層析分析裝置(微GC(Gas Chromatograph))連接。另外,在除濕器20與第一套電管狀爐40之間經由切換閥93及質量流量控制器(Mass Flow Controller,MFC)94而連接有氫配管30。Sampling tubes for gas composition analysis are provided in front of the first electric tubular furnace 40 and between the second electric tubular furnace 40 and the dehumidifier 50 and are connected to a micro gas chromatography analysis device (micro GC (Gas Chromatograph)). In addition, a hydrogen pipe 30 is connected between the dehumidifier 20 and the first electric tubular furnace 40 via a switching valve 93 and a mass flow controller (MFC) 94.

在還原爐10下部的噴嘴92的相反側設置有經由蓄熱型的氣體加熱爐95而送入2.3%富氧空氣的噴嘴96。自噴嘴96導入的空氣的流量由質量流量控制器(MFC)97進行控制。A nozzle 96 for introducing 2.3% oxygen-enriched air via a regenerative gas heating furnace 95 is provided on the opposite side of the nozzle 92 at the lower portion of the reduction furnace 10. The flow rate of the air introduced from the nozzle 96 is controlled by a mass flow controller (MFC) 97.

為了完全對在還原實驗結束後殘留於還原爐10內的廢氣進行排氣處理,在除濕器20與切換閥93之間經由切換閥98而連接有吹掃用氮氣配管。In order to completely exhaust the waste gas remaining in the reduction furnace 10 after the reduction experiment, a nitrogen purge pipe is connected between the dehumidifier 20 and the switch valve 93 via the switch valve 98.

首先,將切換閥91設定於廢氣處理裝置側並將廢氣自還原爐10分離。然後,自還原爐10的噴嘴96利用MFC 97將加熱至1200℃的空氣以17 L/分鐘的流速導入至還原爐10內。兩套電管狀爐40均利用設置於觸媒周邊的熱電偶(thermocouple,TC),將內部溫度設定為800℃。First, the switching valve 91 is set on the exhaust gas treatment device side to separate the exhaust gas from the reduction furnace 10. Then, the air heated to 1200°C is introduced into the reduction furnace 10 at a flow rate of 17 L/min from the nozzle 96 of the reduction furnace 10 using the MFC 97. Both sets of electric tubular furnaces 40 use thermocouples (TC) set around the catalyst to set the internal temperature to 800°C.

在原料塊A中塊礦石被還原而產生的廢氣與通過第二套電管狀爐40後的混合氣體的代表組成(在第一套電管狀爐40的入側無氫補充的情況)如表1所記載般。可知,通過第二套電管狀爐40後,在由廢氣中的剩餘H 2引起的逆水煤氣轉化反應中CO增加了2.7%,CO 2與H 2分別減少了2.7%。 The representative composition of the exhaust gas generated by the reduction of the ore in the raw material block A and the mixed gas after passing through the second set of electric tubular furnace 40 (in the case of no hydrogen supplementation at the inlet side of the first set of electric tubular furnace 40) is shown in Table 1. It can be seen that after passing through the second set of electric tubular furnace 40, CO increased by 2.7% in the reverse water gas shift reaction caused by the residual H2 in the exhaust gas, and CO2 and H2 decreased by 2.7% respectively.

在原料塊A中的焦炭2.2 kg作為廢氣被全部消耗的時點,利用MFC 97將自噴嘴96導入的空氣的流量變更為8.5 L/分鐘。與此同時,將切換閥93切換至氫配管30側並導入氫氣,利用MFC 94進行調整以使進入第一套電管狀爐40前的混合氣體中的H 2濃度(與初始排氣中的CO 2濃度相同)成為22.8%。然後,將切換閥91切換至還原爐10側並自噴嘴92導入還原氣體。再者,原料塊A中的焦炭被全部消耗是根據還原爐10的重量變化進行判斷。 When 2.2 kg of coke in the raw material block A is completely consumed as exhaust gas, the flow rate of air introduced from the nozzle 96 is changed to 8.5 L/min by using the MFC 97. At the same time, the switching valve 93 is switched to the hydrogen distribution pipe 30 side and hydrogen is introduced, and the MFC 94 is adjusted so that the H 2 concentration in the mixed gas before entering the first set of electric tubular furnaces 40 (the same as the CO 2 concentration in the initial exhaust gas) becomes 22.8%. Then, the switching valve 91 is switched to the reduction furnace 10 side and the reducing gas is introduced from the nozzle 92. In addition, the complete consumption of the coke in the raw material block A is determined based on the weight change of the reduction furnace 10.

在該狀態下,等待原料塊B中的焦炭1.1 kg被全部消耗,停止自噴嘴96導入的空氣,停止兩套電管狀爐與兩套燃氣加熱爐。然後,等待水冷套內的水溫成為30℃,利用切換閥93遮斷氫氣,將切換閥91切換至廢氣處理裝置側,將切換閥98切換至氮氣導入側而將殘留於還原爐10內的廢氣全部排出至廢氣處理裝置中。之後,將還原爐10解體並確認爐內的狀況。In this state, wait until 1.1 kg of coke in the raw material block B is completely consumed, stop the air introduced from the nozzle 96, stop the two sets of electric tube furnaces and the two sets of gas heating furnaces. Then, wait until the water temperature in the water cooling jacket reaches 30°C, use the switching valve 93 to shut off the hydrogen gas, switch the switching valve 91 to the exhaust gas treatment device side, switch the switching valve 98 to the nitrogen introduction side, and discharge all the exhaust gas remaining in the reduction furnace 10 to the exhaust gas treatment device. After that, dismantle the reduction furnace 10 and confirm the condition inside the furnace.

原料塊A、原料B中的合計10 kg的塊礦石、焦炭3.3 kg、高爐緩冷爐渣2.8 kg均幾乎未在鎢網上確認到。在被鎢網隔開的爐底確認到鐵氧體(α-Fe)與滲碳體(Fe 3C)的混合物以及堆積於其上的爐渣。利用X射線繞射確認到混合物包含鐵氧體與滲碳體。再者,利用燃燒型的碳-硫分析裝置測定出的該混合物中的碳大致為4.3質量%左右,在混合物的上部與下部進行比較的情況下,在下部碳顯示出提高0.3質量%左右的傾向。 A total of 10 kg of lump ore, 3.3 kg of coke, and 2.8 kg of blast furnace slow cooling slag in raw material lump A and raw material B were almost not confirmed on the tungsten mesh. A mixture of ferrite (α-Fe) and cementite (Fe 3 C) and slag accumulated on it were confirmed at the bottom of the furnace separated by the tungsten mesh. X-ray diffraction confirmed that the mixture contained ferrite and cementite. Furthermore, the carbon in the mixture measured by a combustion-type carbon-sulfur analyzer was approximately 4.3 mass%. When comparing the upper and lower parts of the mixture, the carbon in the lower part showed a tendency to increase by about 0.3 mass%.

藉由以上實驗,確認到在與高爐模式相當的原料塊A的總量被還原之後的、和以爐渣作為通氣材的減碳50%的操作相當的原料塊B的還原步驟中,亦可將作為原料投入的塊礦石全部還原。Through the above experiments, it was confirmed that after the total amount of raw material block A equivalent to the blast furnace mode was reduced, in the reduction step of raw material block B equivalent to the operation of 50% carbon reduction using slag as a ventilation material, the lump ore input as raw material can also be completely reduced.

(發明例4) 將基於發明例4的實驗用的循環還原系統的結構示於圖12中。除將電管狀爐40設為一套,在電管狀爐40的下游不配置除濕器以外,其與圖11所示的發明例3的循環還原系統相同。電管狀爐40利用設置於觸媒周邊的熱電偶(TC),將內部溫度設定為900℃。除此以外的條件設為與發明例3相同而進行了試驗。 (Invention Example 4) The structure of the experimental circulation reduction system based on Invention Example 4 is shown in FIG12. It is the same as the circulation reduction system of Invention Example 3 shown in FIG11, except that the electric tubular furnace 40 is set as one set and no dehumidifier is arranged downstream of the electric tubular furnace 40. The electric tubular furnace 40 uses a thermocouple (TC) arranged around the catalyst to set the internal temperature to 900°C. The test was conducted under the same conditions as Invention Example 3.

在原料塊A中塊礦石被還原而產生的廢氣與通過電管狀爐40後的混合氣體的代表組成(在電管狀爐40的入側無氫補充的情況)如表1所記載般。可知,在通過電管狀爐40後,在由廢氣中的剩餘H 2引起的逆水煤氣轉化反應中CO增加了1.8%,CO 2與H 2分別減少了1.8%。 The representative composition of the exhaust gas generated by the reduction of the ore in the raw material block A and the mixed gas after passing through the electric tubular furnace 40 (in the case of no hydrogen supplementation at the inlet side of the electric tubular furnace 40) is shown in Table 1. It can be seen that after passing through the electric tubular furnace 40, CO increased by 1.8% in the reverse water gas shift reaction caused by the residual H2 in the exhaust gas, and CO2 and H2 decreased by 1.8% respectively.

試驗結束後,與發明例3同樣地,塊礦石、焦炭及高爐緩冷爐渣均幾乎未在鎢網上確認到。在被鎢網隔開的爐底確認到鐵氧體(α-Fe)與滲碳體(Fe 3C)的混合物以及堆積於其上的爐渣。利用X射線繞射確認到混合物包含鐵氧體與滲碳體。再者,利用燃燒型的碳-硫分析裝置測定出的該混合物中的碳大致為4.3質量%左右,在混合物的上部與下部進行比較的情況下,在下部碳顯示出提高0.3質量%左右的傾向。 After the test, similar to Invention Example 3, almost no lump ore, coke, and blast furnace slow cooling slag were confirmed on the tungsten mesh. A mixture of ferrite (α-Fe) and cementite (Fe 3 C) and slag deposited thereon were confirmed at the furnace bottom separated by the tungsten mesh. X-ray diffraction confirmed that the mixture contained ferrite and cementite. Furthermore, the carbon in the mixture measured by a combustion-type carbon-sulfur analyzer was approximately 4.3 mass %, and when comparing the upper and lower parts of the mixture, the carbon in the lower part showed a tendency to increase by about 0.3 mass %.

藉由以上實驗,確認到在與高爐模式相當的原料塊A的總量被還原之後的、和以爐渣作為通氣材的減碳50%的操作相當的原料塊B的還原步驟中,亦可將作為原料投入的塊狀礦石全部還原。Through the above experiments, it was confirmed that after the total amount of raw material block A equivalent to the blast furnace mode was reduced, in the reduction step of raw material block B equivalent to the operation of 50% carbon reduction using slag as a ventilation material, all the lump ore input as raw material can be reduced.

[表1] 表1 區分 氣體 CO CO 2 H 2 N 2 H 2O vol% vol% vol% vol% vol% 發明例3 廢氣 22.0 22.8 4.2 51.0 - 混合氣體 24.7 20.1 1.5 51.0 0.8 發明例4 廢氣 22.0 22.8 4.2 51.0 - 混合氣體 23.8 21.0 2.4 51.0 1.8 [Table 1] Table 1 Differentiation Gas CO CO 2 H2 N 2 H2O vol% vol% vol% vol% vol% Invention Example 3 Exhaust gas 22.0 22.8 4.2 51.0 - Mixed gas 24.7 20.1 1.5 51.0 0.8 Invention Example 4 Exhaust gas 22.0 22.8 4.2 51.0 - Mixed gas 23.8 21.0 2.4 51.0 1.8

10:還原爐 12:爐頂 14:風口 20:第一除濕器/除濕器 30:氫氣供給裝置/氫配管 40:觸媒裝置(逆轉化型重組器)/電管狀爐 42:反應室 44:加熱裝置 50:第二除濕器/除濕器 60:氣體加熱裝置 70:第三除濕器 81:第一配管 81A、81B、82A、82B、82C:配管 82:第二配管 83:第三配管 84:第四配管 85:第五配管 86:第六配管 84A、86A:上游部分 84B、86B:下游部分 87:第七配管 90、91、93、98:切換閥 92、96:噴嘴 94、97:MFC 95:氣體加熱爐 100、200:循環還原系統/循環熔礦爐 A、B:原料塊 10: Reduction furnace 12: Furnace top 14: Tuyere 20: First dehumidifier/dehumidifier 30: Hydrogen supply device/hydrogen piping 40: Catalyst device (reversing reformer)/electrode furnace 42: Reaction chamber 44: Heating device 50: Second dehumidifier/dehumidifier 60: Gas heating device 70: Third dehumidifier 81: First piping 81A, 81B, 82A, 82B, 82C: Piping 82: Second piping 83: Third piping 84: Fourth piping 85: Fifth piping 86: Sixth piping 84A, 86A: Upstream part 84B, 86B: Downstream part 87: Seventh pipe 90, 91, 93, 98: Switch valve 92, 96: Nozzle 94, 97: MFC 95: Gas heating furnace 100, 200: Circulating reduction system/circulating smelting furnace A, B: Raw material block

圖1是表示基於本發明的一實施形態的循環還原系統100的結構的示意圖。 圖2是表示基於本發明的另一實施形態的循環還原系統200的結構的示意圖。 圖3是表示基於發明例1的循環還原系統的平衡計算模型的示意圖。 圖4是表示圖3的模型(發明例1)中的還原狀況的圖表。 圖5是表示基於發明例2的循環還原系統的平衡計算模型的示意圖。 圖6是表示圖5的模型(發明例2)中的還原狀況的圖表。 圖7是表示基於比較例的循環還原系統的平衡計算模型的示意圖。 圖8是表示圖7的模型(比較例)中的還原狀況的圖表。 圖9是表示發明例1、發明例2及比較例中的還原爐內的吸熱量相對於循環數的變化的圖表。 圖10是表示發明例1、發明例2及比較例中的FeO還原區域中的還原爐內吸熱量相對於氫化氣體中的氫量的變化的圖表。 圖11是表示基於發明例3的實驗用的循環還原系統的結構的示意圖。 圖12是表示基於發明例4的實驗用的循環還原系統的結構的示意圖。 FIG. 1 is a schematic diagram showing the structure of a recycling reduction system 100 according to an embodiment of the present invention. FIG. 2 is a schematic diagram showing the structure of a recycling reduction system 200 according to another embodiment of the present invention. FIG. 3 is a schematic diagram showing a balance calculation model of a recycling reduction system according to Invention Example 1. FIG. 4 is a graph showing the reduction state in the model of FIG. 3 (Invention Example 1). FIG. 5 is a schematic diagram showing a balance calculation model of a recycling reduction system according to Invention Example 2. FIG. 6 is a graph showing the reduction state in the model of FIG. 5 (Invention Example 2). FIG. 7 is a schematic diagram showing a balance calculation model of a recycling reduction system according to a comparative example. FIG8 is a graph showing the reduction state in the model (comparative example) of FIG7. FIG9 is a graph showing the change in the heat absorption in the reduction furnace relative to the number of cycles in Invention Example 1, Invention Example 2 and the comparative example. FIG10 is a graph showing the change in the heat absorption in the reduction furnace in the FeO reduction zone relative to the amount of hydrogen in the hydrogenation gas in Invention Example 1, Invention Example 2 and the comparative example. FIG11 is a schematic diagram showing the structure of the experimental cyclic reduction system based on Invention Example 3. FIG12 is a schematic diagram showing the structure of the experimental cyclic reduction system based on Invention Example 4.

10:還原爐 10: Reduction furnace

12:爐頂 12: stove top

14:風口 14: Wind outlet

20:第一除濕器/除濕器 20: First dehumidifier/dehumidifier

30:氫氣供給裝置/氫配管 30: Hydrogen supply device/hydrogen piping

40:觸媒裝置(逆轉化型重組器)/電管狀爐 40: Catalyst device (reversing reformer)/tube furnace

42:反應室 42: Reaction room

44:加熱裝置 44: Heating device

50:第二除濕器/除濕器 50: Second dehumidifier/dehumidifier

60:氣體加熱裝置 60: Gas heating device

81:第一配管 81: First piping

81A、81B、82A、82B、82C:配管 81A, 81B, 82A, 82B, 82C: piping

82:第二配管 82: Second piping

83:第三配管 83: Third piping

84:第四配管 84: Fourth pipe

85:第五配管 85: Fifth pipe

86:第六配管 86: Sixth pipe

84A、86A:上游部分 84A, 86A: Upstream part

84B、86B:下游部分 84B, 86B: Downstream part

87:第七配管 87: Seventh pipe

90:切換閥 90: Switching valve

100:循環還原系統/循環熔礦爐 100: Circulating reduction system/circulating smelting furnace

Claims (15)

一種循環還原系統,具有: 還原爐,對收容於內部的氧化物進行還原; 第一配管,自所述還原爐回收在所述還原爐中產生且包含CO 2的廢氣並使其通過; 氫氣供給裝置,連接於所述第一配管的中途,向所述廢氣中添加氫氣而製成氫化氣體; 觸媒裝置,連接著所述第一配管的終端,具有收容逆水煤氣轉化反應用的觸媒的反應室,使自所述第一配管導入至所述反應室中的所述氫化氣體與所述觸媒接觸,利用逆水煤氣轉化反應將所述氫化氣體中的CO 2轉換為CO,從而製成CO濃度經提高的富含CO的氣體;以及 第二配管,自所述觸媒裝置延伸,與所述還原爐連接,使所述富含CO的氣體通過,將所述富含CO的氣體作為還原氣體供給至所述還原爐的內部, 在所述第一配管及所述第二配管的中途未配置分離裝置,所述分離裝置自通過內部的氣體中分離水蒸氣以外的特定的氣體成分,並進行回收或去除。 A circulating reduction system comprises: a reduction furnace for reducing oxides contained therein; a first pipe for recovering exhaust gas containing CO2 generated in the reduction furnace from the reduction furnace and passing the exhaust gas; a hydrogen supply device connected to the middle of the first pipe for adding hydrogen to the exhaust gas to produce hydrogenated gas; a catalyst device connected to the end of the first pipe and having a reaction chamber for containing a catalyst for a reverse water gas shift reaction, so that the hydrogenated gas introduced into the reaction chamber from the first pipe contacts the catalyst, and CO2 in the hydrogenated gas is reduced by the reverse water gas shift reaction. 2 is converted into CO, thereby producing a CO-rich gas with an increased CO concentration; and a second pipe extending from the catalyst device and connected to the reduction furnace, allowing the CO-rich gas to pass through, and supplying the CO-rich gas to the interior of the reduction furnace as a reducing gas, and no separation device is arranged in the middle of the first pipe and the second pipe, and the separation device separates specific gas components other than water vapor from the gas passing through the interior and recovers or removes them. 如請求項1所述的循環還原系統,具有氣體加熱裝置,所述氣體加熱裝置配置於所述第二配管的中途,對所述富含CO的氣體進行加熱。The circulation reduction system as described in claim 1 has a gas heating device, which is arranged in the middle of the second pipe to heat the CO-rich gas. 如請求項2所述的循環還原系統,具有第三配管,所述第三配管自所述第二配管的中途且為較所述氣體加熱裝置更靠上游的位置分支並與所述氣體加熱裝置連接,經由所述第三配管而將所述富含CO的氣體的一部分作為燃燒氣體而供給至所述氣體加熱裝置。The circulating reduction system as described in claim 2 has a third pipe, which branches from the middle of the second pipe and is further upstream than the gas heating device and is connected to the gas heating device, and a portion of the CO-rich gas is supplied to the gas heating device as combustion gas through the third pipe. 如請求項2或3所述的循環還原系統,具有第四配管,所述第四配管自所述氣體加熱裝置延伸並連接於所述第一配管的中途,經由所述第四配管而使自所述氣體加熱裝置產生的燃燒廢氣與所述第一配管內的所述廢氣合流。The circulation reduction system as described in claim 2 or 3 has a fourth pipe, which extends from the gas heating device and is connected to the middle of the first pipe, so that the combustion exhaust gas generated from the gas heating device and the exhaust gas in the first pipe are combined through the fourth pipe. 如請求項1至3中任一項所述的循環還原系統,其中,所述觸媒裝置具有對所述反應室進行加熱的加熱裝置, 所述循環還原系統具有第五配管,所述第五配管自所述第二配管分支並與所述加熱裝置連接,經由所述第五配管而將所述富含CO的氣體的一部分作為燃燒氣體而供給至所述加熱裝置。 A circulation reduction system as described in any one of claims 1 to 3, wherein the catalyst device has a heating device for heating the reaction chamber, and the circulation reduction system has a fifth pipe, the fifth pipe is branched from the second pipe and connected to the heating device, and a part of the CO-rich gas is supplied to the heating device as a combustion gas through the fifth pipe. 如請求項5所述的循環還原系統,具有第六配管,所述第六配管自所述加熱裝置延伸並連接於所述第一配管的中途,經由所述第六配管而使自所述加熱裝置產生的燃燒廢氣與所述第一配管內的所述廢氣合流。The circulation reduction system as described in claim 5 includes a sixth pipe extending from the heating device and connected to the middle of the first pipe, and the combustion exhaust gas generated from the heating device is merged with the exhaust gas in the first pipe through the sixth pipe. 如請求項1至3中任一項所述的循環還原系統,具有第一除濕器,所述第一除濕器配置於所述第一配管的中途且為較供所述氫氣供給裝置連接的部位更靠上游處,自所述廢氣中去除水蒸氣。The circulation reduction system as described in any one of claims 1 to 3 has a first dehumidifier, which is arranged in the middle of the first pipe and upstream of the position connected to the hydrogen supply device, and removes water vapor from the exhaust gas. 如請求項1至3中任一項所述的循環還原系統,具有第二除濕器,所述第二除濕器配置於所述第二配管的中途,自所述富含CO的氣體中去除水蒸氣。The recycling reduction system as described in any one of claims 1 to 3 has a second dehumidifier, which is arranged in the middle of the second pipe and removes water vapor from the CO-rich gas. 如請求項1至3中任一項所述的循環還原系統,具有:切換閥,配置於所述第二配管的中途;以及第七配管,自所述切換閥延伸, 經由所述第七配管而回收所述富含CO的氣體的一部分。 The circulation reduction system as described in any one of claims 1 to 3 comprises: a switching valve disposed in the middle of the second piping; and a seventh piping extending from the switching valve, and recovering a portion of the CO-rich gas through the seventh piping. 如請求項9所述的循環還原系統,具有第三除濕器,所述第三除濕器配置於所述第七配管的中途,自通過所述第七配管的所述富含CO的氣體中去除水蒸氣。The circulation reduction system as described in claim 9 has a third dehumidifier, which is arranged in the middle of the seventh pipe and removes water vapor from the CO-rich gas passing through the seventh pipe. 如請求項1至3中任一項所述的循環還原系統,其中,所述還原爐為熔礦爐,所述氧化物為鐵礦石。A circulating reduction system as described in any one of claims 1 to 3, wherein the reduction furnace is a smelting furnace and the oxide is iron ore. 如請求項11所述的循環還原系統,其中,所述熔礦爐為高爐。A circulating reduction system as described in claim 11, wherein the smelting furnace is a blast furnace. 一種鐵礦石還原方法,使用如請求項1至12中任一項所述的循環還原系統,將對所述廢氣進行改質而獲得的所述富含CO的氣體作為所述還原氣體進行循環利用,進行作為所述氧化物的鐵礦石的還原處理。A method for reducing iron ore, using the circulating reduction system as described in any one of claims 1 to 12, wherein the CO-rich gas obtained by reforming the exhaust gas is circulated as the reducing gas to reduce the iron ore as the oxide. 一種熔礦爐操作方法,為使用如請求項11或12所述的循環還原系統的熔礦爐操作方法,其中, 自所述熔礦爐的爐頂將(I)作為所述鐵礦石的選自燒結礦、塊礦石、鐵礦石球團及粉礦石中的至少一種、及(II)將對自所述熔礦爐的底部排出的熔融爐渣進行緩冷而獲得的凝固爐渣破碎後的破碎爐渣、或者包含所述破碎爐渣與焦炭的混合物的通氣材交替地呈層狀裝入至所述熔礦爐內,從而確保所述還原氣體的爐內通氣性。 A method for operating a smelting furnace using a circulating reduction system as described in claim 11 or 12, wherein: (I) at least one of sintered ore, lump ore, iron ore pellets and powdered ore as the iron ore, and (II) crushed slag obtained by crushing solidified slag obtained by slowly cooling molten slag discharged from the bottom of the smelting furnace, or a ventilation material containing a mixture of the crushed slag and coke are alternately loaded into the smelting furnace in layers from the top of the smelting furnace, thereby ensuring the in-furnace permeability of the reducing gas. 如請求項14所述的熔礦爐操作方法,其中,自位於所述熔礦爐的下部的風口將所述還原氣體與空氣作為吹入氣體而供給至所述熔礦爐的內部, 使所述通氣材中的所述破碎爐渣相對於所述焦炭的比例與所述吹入氣體中的所述還原氣體相對於所述空氣的比例階段性地增加,以階段性地抑制所述焦炭的使用量。 A method for operating a melting furnace as described in claim 14, wherein the reducing gas and air are supplied as injection gas to the interior of the melting furnace from a tuyere located at the bottom of the melting furnace, so that the ratio of the crushed slag to the coke in the ventilation material and the ratio of the reducing gas to the air in the injection gas are increased in stages, so as to gradually suppress the use of the coke.
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