JP2010235382A - Method for operating sulfur recovery apparatus - Google Patents

Method for operating sulfur recovery apparatus Download PDF

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JP2010235382A
JP2010235382A JP2009084689A JP2009084689A JP2010235382A JP 2010235382 A JP2010235382 A JP 2010235382A JP 2009084689 A JP2009084689 A JP 2009084689A JP 2009084689 A JP2009084689 A JP 2009084689A JP 2010235382 A JP2010235382 A JP 2010235382A
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gas
sulfur
hydrogen sulfide
sulfur recovery
reactor
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JP5022401B2 (en
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Masao Arita
正雄 有田
Hideo Yamamoto
英雄 山本
Yasuhiro Yoshioka
泰裕 吉岡
Masahiro Moriya
正宏 守屋
Shigekazu Matsumoto
茂和 松本
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Eneos Corp
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JX Nippon Oil and Energy Corp
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Abstract

<P>PROBLEM TO BE SOLVED: To provide a method for operating a sulfur recovery apparatus, by which the discharge amount of air pollutants is sufficiently reduced when an operation is started. <P>SOLUTION: The method for operating the sulfur recovery apparatus includes: a temperature raising process comprising supplying a fuel gas and air in an air/fuel ratio of a theoretical air/fuel ratio or lower to a reaction furnace 12 and raising the temperature of a sulfur recovery part 10 by a combustion gas generated by the combustion of the fuel gas; and a reaction starting process comprising starting the supply of H<SB>2</SB>S to the reaction furnace 12 and burning a portion of the H<SB>2</SB>S when the operation of the sulfur recovery apparatus 1 is started. The sulfur recovery apparatus 1 includes: a sulfur recovery part 10 provided with the reaction furnace 12 for forming SO<SB>2</SB>by burning H<SB>2</SB>S and a first reactor 14 having a first catalyst for forming sulfur by subjecting SO<SB>2</SB>and H<SB>2</SB>S to a Claus reaction; and a gas absorption part 20 provided with a second reactor 34 having a second catalyst for hydrogenating SO<SB>2</SB>formed in the sulfur recovery part 10 and an absorption column 38 for absorbing H<SB>2</SB>S formed by the hydrogenation in an absorption liquid. <P>COPYRIGHT: (C)2011,JPO&INPIT

Description

本発明は、硫黄回収装置の運転方法に関する。   The present invention relates to a method for operating a sulfur recovery apparatus.

各種石油製品や石油化学製品の精製においては、製品安定性や臭気、腐食性等を改善するために、間接脱硫装置や直接脱硫装置などによって、硫黄成分を除去する工程を有する。通常、脱硫装置では、水素の存在下で、触媒を用いて、重油、重質軽油、軽質軽油、灯油、ナフサ等に含まれる硫黄成分を硫化水素に変換して除去する。生成した硫化水素ガスは、通常、硫黄回収装置において、一部が二酸化硫黄に変換された後、クラウス反応により硫黄として回収される。   In the refining of various petroleum products and petrochemical products, in order to improve product stability, odor, corrosiveness, etc., there is a step of removing sulfur components using an indirect desulfurization apparatus or a direct desulfurization apparatus. Usually, in a desulfurization apparatus, a sulfur component contained in heavy oil, heavy light oil, light light oil, kerosene, naphtha or the like is converted to hydrogen sulfide and removed using a catalyst in the presence of hydrogen. The produced hydrogen sulfide gas is usually converted into sulfur by a Claus reaction after being partially converted to sulfur dioxide in a sulfur recovery device.

硫黄回収装置における硫化水素ガスの具体的な処理方法としては、硫化水素ガスの一部を燃焼させて二酸化硫黄を生成させ、この二酸化硫黄と未燃焼の硫化水素とを触媒存在下、クラウス反応させて、硫黄と水を生成する方法が採用されている。このように硫化水素ガスの処理を行う硫黄回収装置は、通常、硫化水素を燃焼させて、クラウス反応を行い、硫黄を回収する硫黄回収部(クラウス系)と、硫黄回収部で発生した余剰の二酸化硫黄を加熱し、触媒存在下で水素により還元して硫化水素とし、当該硫化水素を吸収液で吸収させるガス吸収部と、硫化水素が除去されたオフガスを燃焼させる燃焼部とを有する。   As a specific treatment method of hydrogen sulfide gas in the sulfur recovery device, a part of the hydrogen sulfide gas is burned to produce sulfur dioxide, and this sulfur dioxide and unburned hydrogen sulfide are subjected to a Claus reaction in the presence of a catalyst. The method of producing sulfur and water is adopted. In this way, the sulfur recovery device that performs the treatment of hydrogen sulfide gas normally combusts hydrogen sulfide, performs a Claus reaction, and recovers sulfur, and a surplus generated in the sulfur recovery unit. Sulfur dioxide is heated and reduced with hydrogen in the presence of a catalyst to form hydrogen sulfide. The gas absorption part absorbs the hydrogen sulfide with an absorption liquid and the combustion part burns off-gas from which hydrogen sulfide has been removed.

図2は、硫黄回収装置の従来の運転方法を説明するための概略構成図である。硫黄回収装置3は、硫黄回収部100とガス吸収部200と燃焼部300とを備える。通常の運転状態では、反応炉112に、硫化水素ガス(アシッドガス)と空気とが所定の比率で供給され、硫化水素の一部が燃焼して酸化硫黄(二酸化硫黄)を生成する。生成した二酸化硫黄と未燃焼の硫化水素は、配管L102を通ってクラウス触媒を有する第1反応器114に導入される。第1反応器114では、クラウス反応が進行して硫化水素と二酸化硫黄とから硫黄が生成される。生成した硫黄は、二酸化硫黄及び硫化水素を含む未反応ガスとともに配管L104を通って、凝縮器116に導入され、凝縮器116より液状で回収される。   FIG. 2 is a schematic configuration diagram for explaining a conventional operation method of the sulfur recovery apparatus. The sulfur recovery device 3 includes a sulfur recovery unit 100, a gas absorption unit 200, and a combustion unit 300. In a normal operation state, hydrogen sulfide gas (acid gas) and air are supplied to the reaction furnace 112 at a predetermined ratio, and part of the hydrogen sulfide burns to generate sulfur oxide (sulfur dioxide). The produced sulfur dioxide and unburned hydrogen sulfide are introduced into the first reactor 114 having a Claus catalyst through the pipe L102. In the first reactor 114, the Claus reaction proceeds to generate sulfur from hydrogen sulfide and sulfur dioxide. The generated sulfur is introduced into the condenser 116 through the pipe L104 together with the unreacted gas containing sulfur dioxide and hydrogen sulfide, and is recovered in a liquid state from the condenser 116.

一方、第1反応器114で反応しなかった未反応ガス(硫化水素及び酸化硫黄を含む)は、配管L106及びバルブV104を通ってガス吸収部200の加熱器132に導入される。硫黄回収装置3の定常運転では、バルブV102は閉止されており、未反応ガスが燃焼器139で燃焼されて大気汚染物質が放出されることを防止している。未反応ガスは、加熱器132で導入される水素ガスとともに所定の温度に加熱され、配管L110を通って水素化触媒を有する第2反応器134に導入される。第2反応器134では、水素化触媒の作用により、未反応ガスに含まれる酸化硫黄が水素化されて硫化水素及び水を生成する。これらの硫化水素及び水は、他の副生ガスとともに配管L112を通ってクエンチャ136に導入され、硫化水素を含むガス留分と水とに分離される。クエンチャ136で分離されたガス留分は、配管L114及び配管L116を通ってガス吸収塔138に導入され、ガス留分に含まれる硫化水素が配管L124によって供給される吸収液で吸収される。硫化水素を吸収した吸収液は配管L126を通って排出され、他の装置でこの吸収液から分離される。分離された硫化水素は場合によって再び硫黄回収装置3の反応炉112に供給される。一方、ガス留分に含まれるオフガス(燃料ガス)は、配管L122を通って燃焼器139に導入され燃焼される。   On the other hand, unreacted gas (including hydrogen sulfide and sulfur oxide) that has not reacted in the first reactor 114 is introduced into the heater 132 of the gas absorption unit 200 through the pipe L106 and the valve V104. In the steady operation of the sulfur recovery device 3, the valve V102 is closed to prevent the unreacted gas from being combusted in the combustor 139 and releasing air pollutants. The unreacted gas is heated to a predetermined temperature together with the hydrogen gas introduced by the heater 132, and is introduced into the second reactor 134 having the hydrogenation catalyst through the pipe L110. In the second reactor 134, sulfur oxide contained in the unreacted gas is hydrogenated by the action of the hydrogenation catalyst to generate hydrogen sulfide and water. These hydrogen sulfide and water are introduced into the quencher 136 through the pipe L112 together with other by-product gases, and separated into a gas fraction containing hydrogen sulfide and water. The gas fraction separated by the quencher 136 is introduced into the gas absorption tower 138 through the pipe L114 and the pipe L116, and hydrogen sulfide contained in the gas fraction is absorbed by the absorbing liquid supplied through the pipe L124. The absorbing solution that has absorbed hydrogen sulfide is discharged through the pipe L126, and is separated from this absorbing solution by another device. The separated hydrogen sulfide is supplied again to the reaction furnace 112 of the sulfur recovery device 3 in some cases. On the other hand, off-gas (fuel gas) contained in the gas fraction is introduced into the combustor 139 through the pipe L122 and burned.

ところで、二酸化硫黄などの酸化硫黄ガス(SO)は、大気汚染物質として知られており、毒性も高いことから、大気中への放出量を極力低減することが求められている。このため、硫黄回収装置で発生する酸化硫黄ガスの大気中への放出量を極力低減することが求められる。 By the way, sulfur oxide gas (SO x ) such as sulfur dioxide is known as an air pollutant and has high toxicity. Therefore, it is required to reduce the amount released to the atmosphere as much as possible. For this reason, it is required to reduce as much as possible the amount of sulfur oxide gas generated in the sulfur recovery device to the atmosphere.

しかしながら、原料である硫化水素の量が変動して過剰または過少となった場合、硫黄回収装置の運転を停止する場合、あるいはその後運転を開始する場合には、硫黄回収装置にかかる負荷が変動して、運転を調整することが難しくなり、ガス吸収部で処理できない硫化水素を、配管L108を介して燃焼器139で燃焼せざるを得なくなってしまう。この場合、一時的に大気中に二酸化硫黄などの酸化硫黄ガスが燃焼器から排出されてしまうこととなる。このような負荷変動時において大気汚染物質の排出を抑制する運転方法として、燃焼性ガスを装置内に注入することが提案されている(例えば、特許文献1参照)。   However, when the amount of hydrogen sulfide as a raw material fluctuates and becomes excessive or insufficient, when the operation of the sulfur recovery device is stopped, or when the operation is started thereafter, the load on the sulfur recovery device fluctuates. Thus, it becomes difficult to adjust the operation, and hydrogen sulfide that cannot be processed by the gas absorption unit must be burned by the combustor 139 via the pipe L108. In this case, sulfur oxide gas such as sulfur dioxide is temporarily discharged from the combustor into the atmosphere. As an operation method for suppressing the discharge of air pollutants during such load fluctuations, it has been proposed to inject a combustible gas into the apparatus (see, for example, Patent Document 1).

特開平10−265204号公報Japanese Patent Laid-Open No. 10-265204

硫黄回収装置は、定期的に熱交換器や加熱炉などの各機器を開放してメンテナンスや修理を行う必要があり、その度に運転の停止操作及び開始操作が必要となる。特に硫黄回収装置の負荷が大きく変動する運転開始操作時においては、燃焼器から排出される酸化硫黄ガスの排出量が定常運転状態の時に比べて多くなる場合があった。このため、硫黄回収装置の運転開始操作時において、酸化硫黄ガスなどの大気汚染物質の排出量を安定的に低減することのできる運転方法が求められている。   The sulfur recovery device needs to periodically perform maintenance and repair by opening devices such as a heat exchanger and a heating furnace, and each time a stop operation and a start operation are required. In particular, at the time of an operation start operation in which the load of the sulfur recovery device fluctuates greatly, the amount of sulfur oxide gas discharged from the combustor may be larger than that in the steady operation state. Therefore, there is a need for an operation method that can stably reduce the amount of air pollutants discharged, such as sulfur oxide gas, at the start of operation of the sulfur recovery apparatus.

本発明は、かかる事情に鑑みてなされたものであり、硫黄回収装置の運転開始の際に、大気汚染物質の排出量を十分に低減することが可能な硫黄回収装置の運転方法を提供することを目的とする。   The present invention has been made in view of such circumstances, and provides a method for operating a sulfur recovery apparatus capable of sufficiently reducing the emission amount of air pollutants when the operation of the sulfur recovery apparatus is started. With the goal.

本発明では、硫化水素を燃焼させて二酸化硫黄を生成する反応炉と、二酸化硫黄及び硫化水素をクラウス反応させて硫黄を生成する第1触媒を有する第1反応器と、を備える硫黄回収部、並びに硫黄回収部で生成した二酸化硫黄を水素化反応させて硫化水素を生成する第2触媒を有する第2反応器と、第2反応器で生成した硫化水素を吸収液に吸収させる吸収塔を備えるガス吸収部、を具備する硫黄回収装置の運転方法であって、該硫黄回収装置の運転開始の際に、反応炉に水素を主成分とする燃料ガスとともに燃料ガスを燃焼させる空気を理論空燃比以下の空燃比で供給し、燃料ガスを燃焼させて生成する燃焼ガスにより硫黄回収部を昇温する昇温工程と、燃焼ガスをガス吸収部に流通させた状態で、反応炉への硫化水素の供給を開始して、該硫化水素の少なくとも一部を燃焼させる反応開始工程とを有する硫黄回収装置の運転方法を提供する。   In the present invention, a sulfur recovery unit comprising: a reaction furnace for burning hydrogen sulfide to produce sulfur dioxide; and a first reactor having a first catalyst for producing sulfur by causing a Claus reaction of sulfur dioxide and hydrogen sulfide. And a second reactor having a second catalyst for hydrogenating sulfur dioxide produced in the sulfur recovery unit to produce hydrogen sulfide, and an absorption tower for absorbing the hydrogen sulfide produced in the second reactor into the absorption liquid. A method for operating a sulfur recovery device comprising a gas absorption part, wherein when the operation of the sulfur recovery device is started, air that burns fuel gas together with fuel gas containing hydrogen as a main component in a reaction furnace is stoichiometric air-fuel ratio Hydrogen sulphide to the reactor in a state where the temperature is raised in the sulfur recovery part by the combustion gas generated by burning the fuel gas supplied at the following air-fuel ratio, and the combustion gas is circulated through the gas absorption part Started to supply It provides a method of operating Claus process having a reaction initiation step of combusting at least a portion of the sulfurized hydrocarbons.

本発明の硫黄回収装置の運転方法では、運転開始時における硫黄回収部の昇温の際に、反応炉の空燃比を理論空燃比以下とした状態で燃料ガスを燃焼させている。このため、硫黄回収装置内の酸素濃度を十分に低減しつつ、装置内を昇温させることができる。このように装置内の酸素濃度が十分に低減されているため、硫黄回収装置に硫化水素を供給する前から硫黄回収部とガス吸収部とを流通させた状態で硫黄回収部を昇温しても、水素化反応用の第2触媒の損傷を抑制することできる。そして、硫化水素の供給を開始した当初から、硫黄回収部から排出される酸化硫黄及び硫化水素をガス吸収部において吸収することが可能となり、運転開始時における酸化硫黄ガスの大気中への排出量を十分に低減することができる。また、従来大気中に排出されていた酸化硫黄を、硫黄回収装置で処理できるようになるため、硫黄の回収量を増加させることができる。   In the operation method of the sulfur recovery apparatus of the present invention, the fuel gas is combusted in a state where the air-fuel ratio of the reactor is equal to or lower than the stoichiometric air-fuel ratio when the temperature of the sulfur recovery unit is raised at the start of operation. For this reason, the temperature in the apparatus can be raised while sufficiently reducing the oxygen concentration in the sulfur recovery apparatus. Since the oxygen concentration in the apparatus is sufficiently reduced in this way, the temperature of the sulfur recovery unit is raised while the sulfur recovery unit and the gas absorption unit are circulated before supplying hydrogen sulfide to the sulfur recovery unit. Also, damage to the second catalyst for the hydrogenation reaction can be suppressed. From the beginning of the supply of hydrogen sulfide, sulfur oxide and hydrogen sulfide discharged from the sulfur recovery unit can be absorbed by the gas absorption unit, and the amount of sulfur oxide gas discharged into the atmosphere at the start of operation Can be sufficiently reduced. Moreover, since sulfur oxide conventionally discharged into the atmosphere can be processed by the sulfur recovery device, the amount of recovered sulfur can be increased.

本発明では、昇温工程において、反応炉に燃料ガス及び空気とともにスチームを注入しながら昇温することが好ましい。   In the present invention, in the temperature raising step, it is preferable to raise the temperature while injecting steam together with fuel gas and air into the reactor.

これによって、硫黄回収部を徐々に昇温することが可能となり、硫黄回収装置の運転開始操作を一層円滑に行うことができる。   As a result, the temperature of the sulfur recovery unit can be gradually raised, and the operation of starting the operation of the sulfur recovery device can be performed more smoothly.

また、本発明の運転方法では、昇温工程の前に、硫黄回収部とガス吸収部とをそれぞれ個別に昇温させる予備工程を有することが好ましい。   Moreover, in the operating method of this invention, it is preferable to have a preliminary | backup process which heats up a sulfur collection | recovery part and a gas absorption part separately, respectively, before a temperature rising process.

これによって、運転開始操作に所要する作業及び時間を低減しつつ、硫黄回収部及びガス吸収部のそれぞれの温度調整作業を容易にすることができる。 Thereby, the temperature adjustment work of each of the sulfur recovery unit and the gas absorption unit can be facilitated while reducing the work and time required for the operation start operation.

本発明の硫黄回収装置の運転方法によれば、運転開始の際に、大気汚染物質の排出量を十分に低減することができる。   According to the operation method of the sulfur recovery apparatus of the present invention, the emission amount of air pollutants can be sufficiently reduced at the start of operation.

本発明の運転方法の好適な実施形態を説明するための硫黄回収装置の概略構成図である。It is a schematic block diagram of the sulfur collection | recovery apparatus for describing suitable embodiment of the operating method of this invention. 従来の運転方法を説明するための硫黄回収装置の概略構成図である。It is a schematic block diagram of the sulfur collection | recovery apparatus for demonstrating the conventional operating method.

以下、場合により図面を参照して、本発明の好適な実施形態について説明する。   In the following, preferred embodiments of the present invention will be described with reference to the drawings as the case may be.

図1は、本発明の運転方法の好適な実施形態を説明するための硫黄回収装置の概略構成図である。硫黄回収装置1は、硫黄回収部10とガス吸収部20と燃焼部30とを備える。本実施形態の運転方法は、ガス吸収部20の昇温と、燃料ガスを燃焼させて生成した燃焼ガスを用いて硫黄回収部10の昇温と、を行う昇温工程と、該燃焼ガスをガス吸収部20に流通させた状態で、反応炉12への硫化水素の供給を開始して、該硫化水素の少なくとも一部を燃焼させる反応開始工程とを有する。以下、工程毎に詳細に説明する。   FIG. 1 is a schematic configuration diagram of a sulfur recovery apparatus for explaining a preferred embodiment of the operation method of the present invention. The sulfur recovery device 1 includes a sulfur recovery unit 10, a gas absorption unit 20, and a combustion unit 30. The operation method of the present embodiment includes a temperature raising step for raising the temperature of the gas absorption unit 20 and raising the temperature of the sulfur recovery unit 10 using the combustion gas generated by burning the fuel gas. A reaction starting step of starting supply of hydrogen sulfide to the reaction furnace 12 and combusting at least a part of the hydrogen sulfide in a state of being circulated through the gas absorption unit 20. Hereinafter, it demonstrates in detail for every process.

(昇温工程)
昇温工程では、まずガス吸収部20の昇温を次の通りにして行う。加熱器32に燃料ガスとともに、該燃料ガスに対して空気を理論空燃比以下の空燃比で供給して燃料ガスを燃焼させ、燃焼ガスを生成する。ここで、理論空燃比とは、燃料ガスに対する、該燃料ガスを完全燃焼させるために必要な空気の質量比率をいい、空燃比は、燃料ガスに対する空気の質量比率をいう。昇温工程における燃料ガスに対する空気の量は、理論空燃比を基準(100質量%)として、80〜110質量%であることが好ましく、90〜100質量%であることが好ましい。加熱器に供給する空気の量が多すぎるとガス回収部20内における酸素濃度が上昇して第2反応器34に充填された水素化反応用の第2触媒が損傷し易くなる傾向がある。昇温工程においては、バルブV4が閉止されており、バルブV2が開放されている。加熱器32としては、通常のラインヒーターを用いることができる。
(Temperature raising process)
In the temperature raising step, first, the temperature of the gas absorption unit 20 is raised as follows. Along with the fuel gas to the heater 32, air is supplied to the fuel gas at an air-fuel ratio equal to or lower than the stoichiometric air-fuel ratio, and the fuel gas is combusted to generate combustion gas. Here, the stoichiometric air-fuel ratio refers to the mass ratio of air necessary for complete combustion of the fuel gas with respect to the fuel gas, and the air-fuel ratio refers to the mass ratio of air to the fuel gas. The amount of air with respect to the fuel gas in the temperature raising step is preferably 80 to 110% by mass, more preferably 90 to 100% by mass, based on the theoretical air / fuel ratio (100% by mass). If the amount of air supplied to the heater is too large, the oxygen concentration in the gas recovery unit 20 increases and the second catalyst for hydrogenation reaction charged in the second reactor 34 tends to be easily damaged. In the temperature raising step, the valve V4 is closed and the valve V2 is opened. A normal line heater can be used as the heater 32.

加熱器32を通過した燃焼ガスは、配管L10を通って、水素化用の第2触媒が充填された第2反応器34に導入される。これによって、第2反応器34が昇温される。昇温工程において、第2反応器34は、250〜300℃まで昇温されることが好ましい。昇温後の第2反応器34の温度が低すぎると、次の工程で反応炉12に硫化水素の供給を開始した場合に、二酸化硫黄の水素化が十分に進行せず、二酸化硫黄の排出量を十分に低減することができない傾向がある。一方、第2反応器34の温度が高すぎると、第2反応器34に充填された水素化用反応用の第2触媒の活性が低下する傾向がある。   The combustion gas that has passed through the heater 32 is introduced into the second reactor 34 filled with the second catalyst for hydrogenation through the pipe L10. Thereby, the temperature of the second reactor 34 is increased. In the temperature raising step, the second reactor 34 is preferably heated to 250 to 300 ° C. If the temperature of the second reactor 34 after the temperature rise is too low, when the supply of hydrogen sulfide to the reactor 12 is started in the next step, sulfur dioxide hydrogenation does not proceed sufficiently, and sulfur dioxide is discharged. There is a tendency that the amount cannot be reduced sufficiently. On the other hand, if the temperature of the second reactor 34 is too high, the activity of the second catalyst for the hydrogenation reaction charged in the second reactor 34 tends to decrease.

第2反応器34を通過した燃焼ガスは、配管L12を通ってクエンチャ36に導入される。クエンチャ36としては、通常の塔(タワー)や槽(ベッセル)を用いることができる。クエンチャ36では、燃焼ガスが冷却されることにより生成した水を分離して排出することができる。   The combustion gas that has passed through the second reactor 34 is introduced into the quencher 36 through the pipe L12. As the quencher 36, a normal tower or a vessel can be used. In the quencher 36, water generated by cooling the combustion gas can be separated and discharged.

クエンチャ36を通過した燃焼ガスの一部は、配管L14及びL16を経由してガス吸収塔38に導入される。また、クエンチャ36を通過した燃焼ガスの一部は、配管L18、ブロア37、及び配管L20を通過して加熱器32にリサイクルされる。ガス吸収塔38に導入された燃焼ガスは、配管L22を通って燃焼器39に導入され、その後大気中へ排出される。   Part of the combustion gas that has passed through the quencher 36 is introduced into the gas absorption tower 38 via the pipes L14 and L16. Further, part of the combustion gas that has passed through the quencher 36 passes through the pipe L18, the blower 37, and the pipe L20 and is recycled to the heater 32. The combustion gas introduced into the gas absorption tower 38 is introduced into the combustor 39 through the pipe L22 and then discharged into the atmosphere.

次に、硫黄回収部10の昇温を次の通りにして行う。反応炉12にスチーム(水蒸気)を注入しながら、燃料ガスとともに、該燃料ガスに対して空気を理論空燃比以下の空燃比で供給して燃料ガスを燃焼させ、燃焼ガスを生成する。ここで、理論空燃比とは、燃料ガスに対する、該燃料ガスを完全燃焼させるために必要な空気の質量比率をいい、空燃比は、燃料ガスに対する空気の質量比率をいう。昇温工程における燃料ガスに対する空気の量は、理論空燃比を基準(100質量%)として、80〜110質量%であることが好ましく、95〜105質量%であることが好ましい。反応炉12に供給する空気の量が多すぎると硫黄回収装置1内における酸素濃度が上昇し、硫黄回収装置1の内部に付着する硫黄や硫化鉄等の燃焼により発生する酸化硫黄等の大気汚染物質の排出量が多くなってしまう傾向がある。また、次工程で硫黄回収部10とガス吸収部20とを接続した際に、第2反応器34に充填された水素化反応用の第2触媒が損傷し易くなる傾向がある。   Next, the temperature of the sulfur recovery unit 10 is increased as follows. While injecting steam (water vapor) into the reaction furnace 12, together with the fuel gas, air is supplied to the fuel gas at an air / fuel ratio equal to or lower than the stoichiometric air / fuel ratio to burn the fuel gas to generate combustion gas. Here, the stoichiometric air-fuel ratio refers to the mass ratio of air necessary for complete combustion of the fuel gas with respect to the fuel gas, and the air-fuel ratio refers to the mass ratio of air to the fuel gas. The amount of air with respect to the fuel gas in the temperature raising step is preferably 80 to 110% by mass, and preferably 95 to 105% by mass based on the theoretical air-fuel ratio (100% by mass). If the amount of air supplied to the reaction furnace 12 is too large, the oxygen concentration in the sulfur recovery device 1 increases, and air pollution such as sulfur oxide generated by combustion of sulfur, iron sulfide, etc. adhering inside the sulfur recovery device 1 There is a tendency to increase the amount of substances discharged. Also, when the sulfur recovery unit 10 and the gas absorption unit 20 are connected in the next step, the second catalyst for hydrogenation reaction charged in the second reactor 34 tends to be easily damaged.

昇温工程においては、反応炉12出口の酸素濃度を、0.01〜1.0質量%に維持することが好ましい。該酸素濃度が1.0質量%を超えると、硫黄回収部10とガス吸収部20とを接続した際に第2反応器34に備えられる水素化反応用の第2触媒が損傷する傾向がある。また、硫黄回収装置1の内部に付着する硫黄や硫化鉄等が燃焼し、酸化硫黄等の大気汚染物質の排出量が多くなってしまう傾向がある。   In the temperature raising step, the oxygen concentration at the outlet of the reaction furnace 12 is preferably maintained at 0.01 to 1.0% by mass. When the oxygen concentration exceeds 1.0% by mass, the second catalyst for hydrogenation reaction provided in the second reactor 34 tends to be damaged when the sulfur recovery unit 10 and the gas absorption unit 20 are connected. . Moreover, sulfur, iron sulfide, etc. adhering to the inside of the sulfur recovery apparatus 1 are combusted, and there is a tendency that the amount of emission of air pollutants such as sulfur oxide increases.

燃料ガスとしては、水素ガスや各種炭化水素ガスを用いることが好ましく、水素ガスを用いることがより好ましい。水素ガスを用いることによって、硫黄回収装置1内への炭素の析出を十分に抑制することができる。   As the fuel gas, it is preferable to use hydrogen gas or various hydrocarbon gases, and it is more preferable to use hydrogen gas. By using hydrogen gas, the deposition of carbon into the sulfur recovery apparatus 1 can be sufficiently suppressed.

反応炉12で生成した燃焼ガスは、配管L2を通って、クラウス反応用の第1触媒が充填された第1反応器14に導入され、第1反応器14が昇温される。昇温工程において、反応炉12は1000℃、第1反応器14は200〜230℃に昇温されることが好ましい。第1反応器14の昇温温度が低すぎると、次の工程で硫化水素の供給を開始してもクラウス反応が十分に進行せず、多量の未反応硫化水素が下流側のガス吸収部20に流れて、ガス吸収部20の負荷が上昇してしまう傾向がある。一方、第1反応器14の昇温温度が高すぎると、クラウス反応用の第1触媒の活性が低下する傾向がある。   The combustion gas generated in the reaction furnace 12 is introduced into the first reactor 14 filled with the first catalyst for Claus reaction through the pipe L2, and the temperature of the first reactor 14 is increased. In the temperature raising step, the reactor 12 is preferably heated to 1000 ° C., and the first reactor 14 is heated to 200 to 230 ° C. If the temperature rise temperature of the first reactor 14 is too low, the Claus reaction will not proceed sufficiently even if the supply of hydrogen sulfide is started in the next step, and a large amount of unreacted hydrogen sulfide will be downstream. The load of the gas absorption unit 20 tends to increase. On the other hand, if the temperature rising temperature of the first reactor 14 is too high, the activity of the first catalyst for the Claus reaction tends to decrease.

第1反応器14を通過した燃焼ガスは、配管L4を通って、凝縮器16に導入される。凝縮器16としては通常の熱交換器を用いることができる。なお、通常の運転状態においては、凝縮器16には、冷媒(例えば水)を供給することができる。   The combustion gas that has passed through the first reactor 14 is introduced into the condenser 16 through the pipe L4. A normal heat exchanger can be used as the condenser 16. In a normal operation state, the condenser 16 can be supplied with a refrigerant (for example, water).

以上の工程によって、硫黄回収装置1全体が昇温される。昇温に伴って、各機器や配管の温度が上昇して熱膨張するため、機器破損や漏洩防止の観点から、硫黄回収装置1の昇温は徐々に行うことが好ましい。本実施形態では、反応炉12に燃料ガス及び空気とともに、スチームを供給することによって、反応炉12から排出される燃焼ガスの温度を調整している。これによって、硫黄回収装置1全体の昇温速度を円滑に制御することができる。   Through the above steps, the temperature of the entire sulfur recovery device 1 is increased. As the temperature rises, the temperature of each device and pipe rises and thermally expands. Therefore, it is preferable to gradually raise the temperature of the sulfur recovery device 1 from the viewpoint of preventing damage to the device and leakage. In the present embodiment, the temperature of the combustion gas discharged from the reaction furnace 12 is adjusted by supplying steam to the reaction furnace 12 together with the fuel gas and air. Thereby, the temperature increase rate of the entire sulfur recovery apparatus 1 can be controlled smoothly.

反応炉12に供給するスチームの温度及び圧力に特に制限はなく、例えば、100〜1000kPa、130〜250℃のものを用いることができる。スチームは、ボイラー等から供給される。スチームはボイラーでの調整や圧力調節弁によって所望の圧力及び温度に調整される。   There is no restriction | limiting in particular in the temperature and pressure of the steam supplied to the reaction furnace 12, For example, the thing of 100-1000 kPa and 130-250 degreeC can be used. Steam is supplied from a boiler or the like. The steam is adjusted to a desired pressure and temperature by adjustment with a boiler or a pressure control valve.

ガス吸収部20を昇温した後、硫黄回収部10とガス吸収部20との接続を行う。この際、反応炉12出口における燃焼ガスの酸素濃度を、0.01〜1.0質量%に維持することが好ましい。該酸素濃度が1.0質量%を超えると第2反応器34に備えられる水素化反応用の第2触媒が損傷する傾向がある。また、硫黄回収部10とガス吸収部20との接続は、バルブV4を開放し、バルブV2を閉止することによって行う。反応開始工程における硫化水素の供給開始前に、硫黄回収部10とガス回収部20とを接続することで、硫化水素の供給を開始した当初から、硫黄回収部10で生成する酸化硫黄及び硫化水素をガス吸収部20において吸収することが可能となる。これによって、硫黄回収装置1の運転開始時における酸化硫黄ガスの大気中への排出量を十分に低減することができる。また、従来大気中に排出されていた酸化硫黄を、硫黄回収装置1で処理できるようになるため、硫黄の回収量を増加させることができる。   After raising the temperature of the gas absorption unit 20, the sulfur recovery unit 10 and the gas absorption unit 20 are connected. At this time, it is preferable to maintain the oxygen concentration of the combustion gas at the outlet of the reaction furnace 12 at 0.01 to 1.0 mass%. When the oxygen concentration exceeds 1.0% by mass, the second catalyst for hydrogenation reaction provided in the second reactor 34 tends to be damaged. The sulfur recovery unit 10 and the gas absorption unit 20 are connected by opening the valve V4 and closing the valve V2. By connecting the sulfur recovery unit 10 and the gas recovery unit 20 before starting the supply of hydrogen sulfide in the reaction start process, sulfur oxide and hydrogen sulfide generated in the sulfur recovery unit 10 from the beginning of the supply of hydrogen sulfide. Can be absorbed in the gas absorption part 20. Thereby, the amount of sulfur oxide gas discharged into the atmosphere at the start of operation of the sulfur recovery apparatus 1 can be sufficiently reduced. Moreover, since sulfur oxide conventionally discharged into the atmosphere can be processed by the sulfur recovery device 1, the amount of sulfur recovered can be increased.

(反応開始工程)
反応開始工程は、反応炉への硫化水素ガス(アシッドガス)の供給を開始して、該硫化水素の少なくとも一部を燃焼させる工程であり、定常運転への移行工程である。
(Reaction start process)
The reaction start step is a step of starting the supply of hydrogen sulfide gas (acid gas) to the reaction furnace and combusting at least a part of the hydrogen sulfide, and is a transition step to a steady operation.

昇温工程によって、例えば、反応炉12を1000℃、第1反応器14を200〜230℃にまで昇温したら、反応炉12に硫化水素ガスの供給を開始することにより、反応開始工程を開始する。クラウス反応用の第1触媒の損傷を十分に抑制する観点、及び運転開始操作を円滑に行う観点から、硫化水素ガスの供給は徐々に増やすことが好ましい。   For example, when the temperature of the reaction furnace 12 is increased to 1000 ° C. and the temperature of the first reactor 14 is increased to 200 to 230 ° C., the reaction start process is started by starting the supply of hydrogen sulfide gas to the reaction furnace 12. To do. It is preferable that the supply of hydrogen sulfide gas is gradually increased from the viewpoint of sufficiently suppressing the damage of the first catalyst for the Claus reaction and smoothly performing the operation start operation.

反応炉12には、燃料ガスを燃焼させるために供給される所定量の空気に加えて、硫化水素ガスの供給開始と同時に、該硫化水素ガスの少なくとも一部を燃焼させる空気を供給することが好ましい。硫化水素ガスを燃焼させるための空気の量は、該空気に含まれる酸素によって該硫化水素ガスの供給量全体の1/3が下記式(1)で反応する量とすることが好ましい。これによって、硫黄回収部10からガス吸収部20に導入される硫化水素及び二酸化硫黄の量を十分に低減することができる。   In addition to a predetermined amount of air supplied to burn the fuel gas, the reactor 12 is supplied with air for burning at least a part of the hydrogen sulfide gas at the same time as the supply of the hydrogen sulfide gas is started. preferable. The amount of air for burning the hydrogen sulfide gas is preferably an amount such that 1/3 of the total supply amount of the hydrogen sulfide gas reacts by the following formula (1) by oxygen contained in the air. Thereby, the amount of hydrogen sulfide and sulfur dioxide introduced from the sulfur recovery unit 10 to the gas absorption unit 20 can be sufficiently reduced.

S+3/2O → SO+HO ・・・(1) H 2 S + 3 / 2O 2 → SO 2 + H 2 O (1)

運転開始操作時における運転状態の変動を十分抑制する観点から、反応炉12への硫化水素ガスの供給を増やしながら、それに対応して燃料ガスの供給を徐々に減らすことが好ましい。この際、水素化反応用の第2触媒の損傷を防止するため、燃料ガスの供給量の減少量に見合うように、燃料ガス燃焼用の空気の供給量も減らすことが好ましい。   From the viewpoint of sufficiently suppressing fluctuations in the operating state at the start of operation, it is preferable to gradually reduce the supply of fuel gas correspondingly while increasing the supply of hydrogen sulfide gas to the reaction furnace 12. At this time, in order to prevent damage to the second catalyst for the hydrogenation reaction, it is preferable to reduce the amount of air supplied for fuel gas combustion to match the amount of decrease in the amount of fuel gas supplied.

上記式(1)の反応によって生成した二酸化硫黄は、未反応の硫化水素と共に配管L2を通ってクラウス反応用の第1触媒を有する第1反応器14に導入される。第1反応器14では、下記式(2)で表されるクラウス反応が進行し、硫黄の生成量が増加する。第1反応器14で生成した硫黄は、燃焼ガスや未反応の硫化水素ガス及び二酸化硫黄ガスとともに、配管L4を通って凝縮器16に導入される。生成した硫黄は凝縮器16で、例えば190℃以下に冷却され、液状の状態で硫黄回数装置1から排出される。   Sulfur dioxide generated by the reaction of the above formula (1) is introduced into the first reactor 14 having the first catalyst for Claus reaction through the pipe L2 together with unreacted hydrogen sulfide. In the first reactor 14, the Claus reaction represented by the following formula (2) proceeds, and the amount of sulfur produced increases. Sulfur produced in the first reactor 14 is introduced into the condenser 16 through the pipe L4 together with combustion gas, unreacted hydrogen sulfide gas, and sulfur dioxide gas. The produced sulfur is cooled to, for example, 190 ° C. or less by the condenser 16 and is discharged from the sulfur counter 1 in a liquid state.

2HS+SO → 2HO+3S ・・・・(2) 2H 2 S + SO 2 → 2H 2 O + 3S (2)

反応開始工程において、第1反応器14の運転状態は、最終的に200〜350℃の温度に到達することが好ましい。このような温度条件とすることによって、上記式(2)のクラウス反応が安定的に進行し、酸化硫黄の排出量を十分に低減しつつガス吸収部20の硫化水素ガスの吸収負荷を十分に低減することができる。   In the reaction start step, it is preferable that the operation state of the first reactor 14 finally reaches a temperature of 200 to 350 ° C. By setting such a temperature condition, the Claus reaction of the above formula (2) proceeds stably, and the absorption load of the hydrogen sulfide gas in the gas absorption unit 20 is sufficiently reduced while sufficiently reducing the amount of sulfur oxide discharged. Can be reduced.

凝縮器16で冷却された硫化水素ガス及び二酸化硫黄ガスは、燃焼ガスとともに配管L6を通ってガス吸収部20に設けられる加熱器32に導入され、270〜300℃に加熱される。加熱された硫化水素ガス及び酸化硫黄ガスは、燃焼ガス及び加熱器32に供給される水素ガスとともに水素化反応用の第2触媒を備える第2反応器34に導入される。ここで、第2反応器34では、水素化反応用の第2触媒の作用によって、二酸化硫黄及び水素が下記式(3)に示すように反応して、硫化水素及び水を生成する。なお、加熱器32としては通常のラインヒーターを用いることができる。   The hydrogen sulfide gas and the sulfur dioxide gas cooled by the condenser 16 are introduced into the heater 32 provided in the gas absorption unit 20 through the pipe L6 together with the combustion gas, and are heated to 270 to 300 ° C. The heated hydrogen sulfide gas and sulfur oxide gas are introduced into a second reactor 34 having a second catalyst for hydrogenation reaction together with the combustion gas and the hydrogen gas supplied to the heater 32. Here, in the second reactor 34, sulfur dioxide and hydrogen react as shown in the following formula (3) by the action of the second catalyst for hydrogenation reaction to generate hydrogen sulfide and water. Note that a normal line heater can be used as the heater 32.

SO+3H → HS+2HO ・・・(3) SO 2 + 3H 2 → H 2 S + 2H 2 O (3)

第2反応器34に収容される水素化反応用の第2触媒としては、通常の触媒を用いることができる。   As the second catalyst for the hydrogenation reaction accommodated in the second reactor 34, a normal catalyst can be used.

上記式(3)の反応によって生成した硫化水素及び水は、燃焼ガスとともに、配管L12を通ってクエンチャ36に導入されて、水と硫化水素及び燃焼ガスとに分離される。分離された水はクエンチャ36の底部から硫黄回収装置1の外部に排出される。   The hydrogen sulfide and water generated by the reaction of the above formula (3) are introduced into the quencher 36 through the pipe L12 together with the combustion gas, and separated into water, hydrogen sulfide and the combustion gas. The separated water is discharged from the bottom of the quencher 36 to the outside of the sulfur recovery apparatus 1.

クエンチャ36で分離された硫化水素及び燃焼ガスは、配管L14及びL16を通ってガス吸収塔38に導入され、配管L24を通ってガス吸収塔38に供給される吸収液と接触する。硫化水素は吸収液に吸収され、硫化水素を吸収した吸収液は、配管L26を通って排出される。硫化水素濃度が十分に低減された燃焼ガスは、配管L22を通って燃焼部30に備えられる燃焼器39に導入される。該燃焼ガスは、硫化水素ガス及び酸化硫黄ガス濃度が十分に低減されているため、燃焼器39から排出される排出ガス中の酸化硫黄ガスなどの大気汚染物質の濃度は十分に低減されている。   The hydrogen sulfide and the combustion gas separated by the quencher 36 are introduced into the gas absorption tower 38 through the pipes L14 and L16, and come into contact with the absorption liquid supplied to the gas absorption tower 38 through the pipe L24. The hydrogen sulfide is absorbed by the absorption liquid, and the absorption liquid that has absorbed the hydrogen sulfide is discharged through the pipe L26. The combustion gas in which the hydrogen sulfide concentration is sufficiently reduced is introduced into the combustor 39 provided in the combustion unit 30 through the pipe L22. Since the combustion gas has sufficiently reduced hydrogen sulfide gas and sulfur oxide gas concentrations, the concentration of air pollutants such as sulfur oxide gas in the exhaust gas discharged from the combustor 39 is sufficiently reduced. .

なお、ガス吸収塔38の負荷を調整するため、及びガス吸収部20全体のバランスを保つために、硫化水素ガス及び燃焼ガスの一部は、配管L18、ブロア37及び配管L20を介してリサイクルされる場合がある。   In order to adjust the load of the gas absorption tower 38 and to maintain the balance of the entire gas absorption unit 20, part of the hydrogen sulfide gas and the combustion gas is recycled through the pipe L18, the blower 37, and the pipe L20. There is a case.

反応開始工程においては、反応炉12への硫化水素の供給量を徐々に増やしつつ燃料ガスの供給量を徐々に減らすことが好ましい。最終的に、反応炉12への燃料ガスの供給を止めて反応開始工程を終了し、反応炉12に硫化水素ガスのみを供給する定常運転に移行することができる。反応炉12へのスチームの供給は、反応開始工程中に停止してもよく、定常運転まで継続的に供給してもよい。   In the reaction start step, it is preferable to gradually decrease the supply amount of the fuel gas while gradually increasing the supply amount of hydrogen sulfide to the reaction furnace 12. Finally, the supply of the fuel gas to the reaction furnace 12 is stopped, the reaction start process is terminated, and a steady operation for supplying only the hydrogen sulfide gas to the reaction furnace 12 can be performed. The supply of steam to the reaction furnace 12 may be stopped during the reaction start process, or may be continuously supplied until steady operation.

反応開始工程終了後、定常運転とすることができる。定常運転では、硫黄回収部10の反応炉12に、硫化水素ガスと空気とが所定の比率で供給され、硫化水素ガスの一部が燃焼して二酸化硫黄を生成する(上記式(1))。反応炉12に供給される硫化水素ガスと空気との比率は、硫化水素ガスの供給量全体の1/3が上記式(1)で燃焼する比率とする。この比率に調製することによって、後述するクラウス反応が効率的に進行し、未反応の硫化水素及び二酸化硫黄の発生を十分に抑制することができる。また、硫黄回収装置1における硫黄の回収量を増加することができる。   After the reaction start step is completed, a steady operation can be performed. In steady operation, hydrogen sulfide gas and air are supplied to the reaction furnace 12 of the sulfur recovery unit 10 at a predetermined ratio, and a part of the hydrogen sulfide gas burns to generate sulfur dioxide (the above formula (1)). . The ratio of the hydrogen sulfide gas and air supplied to the reaction furnace 12 is a ratio at which 1/3 of the total supply amount of hydrogen sulfide gas burns according to the above equation (1). By adjusting to this ratio, the Claus reaction described later proceeds efficiently, and generation of unreacted hydrogen sulfide and sulfur dioxide can be sufficiently suppressed. Further, the amount of sulfur recovered in the sulfur recovery device 1 can be increased.

上記実施形態による硫黄回収装置の運転方法によれば、凝縮器16から排出される酸化硫黄含有ガスを、配管L8を介して燃焼器39へ排出させずに、運転の開始操作を行うことができる。したがって、酸化硫黄ガスなどの大気汚染物質の大気排出を十分に低減することができる。   According to the operation method of the sulfur recovery device according to the above embodiment, the operation for starting operation can be performed without discharging the sulfur oxide-containing gas discharged from the condenser 16 to the combustor 39 via the pipe L8. . Therefore, atmospheric emissions of air pollutants such as sulfur oxide gas can be sufficiently reduced.

以上、本発明の好適な実施形態について説明したが、本発明は上記実施形態に何ら限定されるものではない。   The preferred embodiment of the present invention has been described above, but the present invention is not limited to the above embodiment.

以下、実施例及び比較例に基づき本発明をさらに具体的に説明するが、本発明は以下の実施例に何ら限定されるものではない。   EXAMPLES Hereinafter, although this invention is demonstrated more concretely based on an Example and a comparative example, this invention is not limited to a following example at all.

(実施例1)
図1に示す硫黄回収装置1の運転開始操作を以下の通り行った。
Example 1
Operation start operation of the sulfur collection | recovery apparatus 1 shown in FIG. 1 was performed as follows.

まず、加熱器32に、燃料ガスとともに、該燃料ガスに対して空気を理論空燃比以下の空燃比で供給して燃料ガスを燃焼させ、燃焼ガスを生成させた。この燃焼ガスを、第2反応器34、クエンチャ36及びブロア37の順で循環させた。これによって、ガス吸収部20を、第2反応器34の温度が270℃になるまで昇温した。このとき、硫黄回収装置1におけるバルブV2を開放し、バルブV4を閉止していた。   First, together with the fuel gas, air was supplied to the heater 32 at an air / fuel ratio equal to or lower than the stoichiometric air / fuel ratio to burn the fuel gas to generate combustion gas. This combustion gas was circulated in the order of the second reactor 34, the quencher 36 and the blower 37. Thereby, the gas absorption part 20 was heated up until the temperature of the 2nd reactor 34 became 270 degreeC. At this time, the valve V2 in the sulfur recovery apparatus 1 was opened and the valve V4 was closed.

次に、水素ガス、空気及びスチームを反応炉12に導入して、水素ガスを燃焼させ、発生した燃焼ガス(水)によって、硫黄回収部10全体を昇温した。この際、スチームの注入量を調整することによって、硫黄回収部10の昇温速度を30〜50℃/時間に制御した。   Next, hydrogen gas, air, and steam were introduced into the reaction furnace 12 to burn the hydrogen gas, and the temperature of the entire sulfur recovery unit 10 was increased by the generated combustion gas (water). Under the present circumstances, the temperature increase rate of the sulfur collection | recovery part 10 was controlled to 30-50 degreeC / hour by adjusting the injection amount of steam.

反応炉12に供給する水素に対する空気の比率を、理論空燃比を基準として、90〜100質量%となるように調整した。そして、硫黄回収装置1内の酸素濃度を1体積%以下とした。なお、酸素濃度測定は、凝縮器16の出口にて行い、市販のガスセンサーを用いて行った。   The ratio of air to hydrogen supplied to the reaction furnace 12 was adjusted to 90 to 100% by mass based on the theoretical air-fuel ratio. And the oxygen concentration in the sulfur collection | recovery apparatus 1 was 1 volume% or less. The oxygen concentration measurement was performed at the outlet of the condenser 16 and was performed using a commercially available gas sensor.

次に、バルブV4を開放するとともに、バルブV2を閉止して、凝縮器16から排出される燃焼ガスが、配管L8を通って燃焼器39に排出されないようにした。   Next, the valve V4 was opened and the valve V2 was closed so that the combustion gas discharged from the condenser 16 was not discharged to the combustor 39 through the pipe L8.

反応炉12が1000℃、第1反応器14が200〜230℃に到達した後、反応炉12に硫化水素ガス(アシッドガス)を導入して、反応開始工程を開始した。硫化水素ガスは、反応炉12に導入する燃料ガスを減らしながら、徐々に増やした。この際、反応炉12への空気の導入量は、水素ガスを理論燃焼させるために必要な空気量の90〜100質量%に相当する空気量と、硫化水素の総量の1/3を燃焼させるために必要な空気量との合計量とした。   After the reaction furnace 12 reached 1000 ° C. and the first reactor 14 reached 200 to 230 ° C., hydrogen sulfide gas (acid gas) was introduced into the reaction furnace 12 to start the reaction start process. The hydrogen sulfide gas was gradually increased while reducing the fuel gas introduced into the reactor 12. At this time, the amount of air introduced into the reaction furnace 12 burns 1/3 of the air amount corresponding to 90 to 100% by mass of the air amount necessary for theoretically burning hydrogen gas and the total amount of hydrogen sulfide. Therefore, the total amount with the amount of air required for this purpose was used.

反応炉12に導入した硫化水素の一部は上記式(1)によって二酸化硫黄となり、当該二酸化硫黄は未反応の硫化水素と上記式(2)によって反応(クラウス反応)して、硫黄を生成した。この硫黄は、凝縮器16から回収された。   Part of the hydrogen sulfide introduced into the reaction furnace 12 becomes sulfur dioxide by the above formula (1), and the sulfur dioxide reacts with the unreacted hydrogen sulfide by the above formula (2) (Klaus reaction) to generate sulfur. . This sulfur was recovered from the condenser 16.

第1反応器14から排出された未反応の二酸化硫黄ガスは、凝縮器16を通過して、加熱器32に導入され270〜300℃に昇温された後、水素ガスとともに第2反応器34に導入され、上記式(3)の反応によって硫化水素と水とに変換された。   The unreacted sulfur dioxide gas discharged from the first reactor 14 passes through the condenser 16, is introduced into the heater 32, and is heated to 270 to 300 ° C. Then, the second reactor 34 together with the hydrogen gas is used. And converted into hydrogen sulfide and water by the reaction of the above formula (3).

硫化水素は、クエンチャ36によって水と分離された後、ガス吸収塔38に導入され、吸収液(ジイソプロパノールアミン)に吸収された。硫化水素が除去された燃焼ガス(オフガス)は、配管L22を通って燃焼器39に導入された。燃焼器39から排出される排出ガス中の二酸化硫黄濃度を市販のガス濃度計測器を用いて測定した。運転開始操作時における排出ガス中の二酸化硫黄の濃度は、数10〜数100ppmで推移した。   The hydrogen sulfide was separated from water by the quencher 36 and then introduced into the gas absorption tower 38 and absorbed by the absorption liquid (diisopropanolamine). The combustion gas (off gas) from which hydrogen sulfide was removed was introduced into the combustor 39 through the pipe L22. The sulfur dioxide concentration in the exhaust gas discharged from the combustor 39 was measured using a commercially available gas concentration measuring device. The concentration of sulfur dioxide in the exhaust gas at the start of operation changed from several tens to several hundred ppm.

反応炉12への水素ガスの供給を停止して、定常運転に移行した。運転開始操作(予備工程)の開始から、第1反応器14及び第2反応器34が所定の温度に到達して反応炉12への水素ガスの供給を停止するまで、すなわち定常運転状態となるまでに所要した時間は48時間であった。   The supply of hydrogen gas to the reaction furnace 12 was stopped, and a steady operation was started. From the start of the operation start operation (preliminary process) until the first reactor 14 and the second reactor 34 reach a predetermined temperature and stop the supply of hydrogen gas to the reaction furnace 12, that is, a steady operation state is established. It took 48 hours to complete.

(比較例1)
図2に示す硫黄回収装置3の運転開始操作を以下の通り行った。
(Comparative Example 1)
Operation start operation of the sulfur collection | recovery apparatus 3 shown in FIG. 2 was performed as follows.

水素ガス、空気及びスチームを反応炉112に導入して燃焼させ、発生した燃焼ガス(水)によって、硫黄回収部100全体を昇温した。硫黄回収部100の昇温速度は、昇温速度を30〜50℃/時間に調整した。   Hydrogen gas, air, and steam were introduced into the reaction furnace 112 for combustion, and the temperature of the entire sulfur recovery unit 100 was increased by the generated combustion gas (water). The temperature increase rate of the sulfur recovery unit 100 was adjusted to 30 to 50 ° C./hour.

また、硫黄回収部100の昇温と同時に、加熱器132に、燃料ガスとともに、該燃料ガスに対して空気を理論空燃比以下の空燃比で供給して燃料ガスを燃焼させ、燃焼ガスを生成させた。この燃焼ガスを、第2反応器134、クエンチャ136及びブロア137の順で循環させた。これによって、ガス吸収部200を第2反応器134の温度が270℃になるまで昇温した。このとき、硫黄回収装置3におけるバルブV102を開放し、バルブV104を閉止していた。   Simultaneously with the temperature rise of the sulfur recovery unit 100, the fuel gas is supplied to the heater 132 together with the fuel gas at an air / fuel ratio equal to or lower than the stoichiometric air / fuel ratio to burn the fuel gas, thereby generating combustion gas. I let you. This combustion gas was circulated in the order of the second reactor 134, the quencher 136, and the blower 137. Thereby, the gas absorption part 200 was heated up until the temperature of the 2nd reactor 134 became 270 degreeC. At this time, the valve V102 in the sulfur recovery device 3 was opened and the valve V104 was closed.

反応炉112が1000℃、第1反応器114が200〜230℃に到達した後、バルブV102を開放し、バルブV104を閉止したまま、反応炉112に硫化水素ガス(アシッドガス)を導入して、反応開始工程を開始した。硫化水素ガスは、反応炉112に導入する燃料ガスを減らしながら、徐々に増やした。この際、反応炉112への空気の導入量は、水素ガスを理論燃焼させるために必要な空気量と、硫化水素の総量の1/3を燃焼させるために必要な空気量との合計量以上とした。   After the reactor 112 reaches 1000 ° C. and the first reactor 114 reaches 200 to 230 ° C., the valve V102 is opened, and the hydrogen sulfide gas (acid gas) is introduced into the reactor 112 with the valve V104 closed. The reaction start process was started. The hydrogen sulfide gas was gradually increased while reducing the fuel gas introduced into the reaction furnace 112. At this time, the amount of air introduced into the reaction furnace 112 is equal to or greater than the total amount of the air amount necessary for theoretically burning hydrogen gas and the air amount necessary for burning one third of the total amount of hydrogen sulfide. It was.

反応炉112に導入した硫化水素の一部は上記式(1)によって二酸化硫黄となり、当該二酸化硫黄は未反応の硫化水素と上記式(2)によって反応(クラウス反応)して、硫黄を生成した。この硫黄は、凝縮器116から回収された。   Part of the hydrogen sulfide introduced into the reaction furnace 112 becomes sulfur dioxide by the above formula (1), and the sulfur dioxide reacts with the unreacted hydrogen sulfide by the above formula (2) (Klaus reaction) to generate sulfur. . This sulfur was recovered from the condenser 116.

第1反応器114から排出された未反応の二酸化硫黄ガス及び硫化水素ガスは、凝縮器116を通過して、バルブV102、配管L108を通って、燃焼器139に導入された。燃焼器139から排出される排出ガスの二酸化硫黄濃度を市販のガス濃度計測器を用いて測定した。運転開始操作時における排出ガスの二酸化硫黄の濃度は、実施例1の数十〜数百倍であった。   The unreacted sulfur dioxide gas and hydrogen sulfide gas discharged from the first reactor 114 passed through the condenser 116 and were introduced into the combustor 139 through the valve V102 and the pipe L108. The sulfur dioxide concentration of the exhaust gas discharged from the combustor 139 was measured using a commercially available gas concentration meter. The concentration of sulfur dioxide in the exhaust gas at the start of operation was several tens to several hundred times that in Example 1.

反応炉112への水素ガスの供給を停止した後、バルブV102を閉止し、バルブV104を開放することによって、硫黄回収部100とガス吸収部200との繋ぎこみを行い、硫黄回収装置の定常運転に移行した。運転開始操作の開始から、定常運転に移行するまでに所要した時間は48時間であった。   After the supply of hydrogen gas to the reaction furnace 112 is stopped, the valve V102 is closed and the valve V104 is opened, so that the sulfur recovery unit 100 and the gas absorption unit 200 are connected to each other, and the sulfur recovery device is operated in a steady state. It moved to. The time required from the start of the operation start operation to the transition to the steady operation was 48 hours.

1,3…硫黄回収装置、10,100…硫黄回収部、12,112…反応炉、14,114…第1反応器、16,116…凝縮器、20,200…ガス吸収部、30,300…燃焼部、32,132…加熱器、34,134…第2反応器、36,136…クエンチャ、37,137…ブロア、38,138…ガス吸収塔、39,139…燃焼器。   DESCRIPTION OF SYMBOLS 1,3 ... Sulfur recovery apparatus, 10,100 ... Sulfur recovery part, 12,112 ... Reactor, 14,114 ... 1st reactor, 16,116 ... Condenser, 20,200 ... Gas absorption part, 30,300 ... Combustion section, 32, 132 ... Heater, 34, 134 ... Second reactor, 36, 136 ... Quencher, 37, 137 ... Blower, 38, 138 ... Gas absorption tower, 39, 139 ... Combustor.

Claims (3)

硫化水素を燃焼させて二酸化硫黄を生成する反応炉と、前記二酸化硫黄及び硫化水素をクラウス反応させて硫黄を生成する第1触媒を有する第1反応器と、を備える硫黄回収部、並びに、
前記硫黄回収部で生成した二酸化硫黄を水素化反応させて硫化水素を生成する第2触媒を有する第2反応器と、前記第2反応器で生成した前記硫化水素を吸収液に吸収させる吸収塔と、を備えるガス吸収部、を具備する硫黄回収装置の運転方法であって、
該硫黄回収装置の運転開始の際に、
前記反応炉に水素を主成分とする燃料ガスとともに前記燃料ガスを燃焼させる空気を理論空燃比以下の空燃比で供給し、前記燃料ガスを燃焼させて生成する燃焼ガスにより前記硫黄回収部を昇温する昇温工程と、
前記燃焼ガスを前記ガス吸収部に流通させた状態で、前記反応炉への硫化水素の供給を開始して、該硫化水素の少なくとも一部を燃焼させる反応開始工程と、を有する硫黄回収装置の運転方法。
A sulfur recovery unit comprising: a reaction furnace that burns hydrogen sulfide to generate sulfur dioxide; and a first reactor that has a first catalyst that generates sulfur by causing a Claus reaction between the sulfur dioxide and hydrogen sulfide; and
A second reactor having a second catalyst for hydrogenating sulfur dioxide produced in the sulfur recovery section to produce hydrogen sulfide; and an absorption tower for absorbing the hydrogen sulfide produced in the second reactor into an absorbent. And a method for operating a sulfur recovery device comprising a gas absorption part comprising:
At the start of operation of the sulfur recovery device,
Air for burning the fuel gas together with a fuel gas containing hydrogen as a main component is supplied to the reactor at an air-fuel ratio equal to or lower than the stoichiometric air-fuel ratio, and the sulfur recovery unit is elevated by the combustion gas generated by burning the fuel gas. A heating step for heating;
A reaction start step of starting supply of hydrogen sulfide to the reaction furnace and combusting at least a part of the hydrogen sulfide in a state where the combustion gas is circulated through the gas absorption part. how to drive.
前記昇温工程では、前記反応炉に前記燃料ガス及び前記空気とともにスチームを注入しながら昇温する請求項1記載の硫黄回収装置の運転方法。   The operation method of a sulfur recovery apparatus according to claim 1, wherein in the temperature raising step, the temperature is raised while injecting steam together with the fuel gas and the air into the reactor. 前記昇温工程の前に、前記硫黄回収部と前記ガス吸収部とをそれぞれ個別に昇温させる予備工程を有する請求項1または2記載の硫黄回収装置の運転方法。   The method for operating a sulfur recovery apparatus according to claim 1 or 2, further comprising a preliminary step of individually heating the sulfur recovery unit and the gas absorption unit before the temperature increase step.
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CN109019524A (en) * 2018-08-30 2018-12-18 山东迅达化工集团有限公司 A kind of recovery technology of sulfur of middle low concentration sour gas

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