JPH0631350B2 - Solid-gas contact reactor - Google Patents
Solid-gas contact reactorInfo
- Publication number
- JPH0631350B2 JPH0631350B2 JP60024529A JP2452985A JPH0631350B2 JP H0631350 B2 JPH0631350 B2 JP H0631350B2 JP 60024529 A JP60024529 A JP 60024529A JP 2452985 A JP2452985 A JP 2452985A JP H0631350 B2 JPH0631350 B2 JP H0631350B2
- Authority
- JP
- Japan
- Prior art keywords
- gas
- adsorbent
- adsorption
- reaction
- solid
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Expired - Lifetime
Links
- 239000003463 adsorbent Substances 0.000 claims description 39
- 238000001179 sorption measurement Methods 0.000 claims description 18
- 230000008929 regeneration Effects 0.000 claims description 12
- 238000011069 regeneration method Methods 0.000 claims description 12
- 229910044991 metal oxide Inorganic materials 0.000 claims description 7
- 150000004706 metal oxides Chemical class 0.000 claims description 7
- 150000003464 sulfur compounds Chemical class 0.000 claims description 7
- 230000003197 catalytic effect Effects 0.000 claims description 3
- 239000007787 solid Substances 0.000 claims description 3
- 239000007789 gas Substances 0.000 description 56
- 238000006243 chemical reaction Methods 0.000 description 23
- 239000000428 dust Substances 0.000 description 14
- 238000002309 gasification Methods 0.000 description 13
- 239000003245 coal Substances 0.000 description 8
- RWSOTUBLDIXVET-UHFFFAOYSA-N Dihydrogen sulfide Chemical compound S RWSOTUBLDIXVET-UHFFFAOYSA-N 0.000 description 6
- 229910000037 hydrogen sulfide Inorganic materials 0.000 description 6
- 238000000034 method Methods 0.000 description 6
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 5
- 229910052760 oxygen Inorganic materials 0.000 description 5
- 239000001301 oxygen Substances 0.000 description 5
- 239000002994 raw material Substances 0.000 description 5
- 239000004071 soot Substances 0.000 description 4
- OKKJLVBELUTLKV-UHFFFAOYSA-N Methanol Chemical compound OC OKKJLVBELUTLKV-UHFFFAOYSA-N 0.000 description 3
- 239000002250 absorbent Substances 0.000 description 3
- 230000002745 absorbent Effects 0.000 description 3
- 239000003795 chemical substances by application Substances 0.000 description 3
- 239000000446 fuel Substances 0.000 description 3
- 239000000295 fuel oil Substances 0.000 description 3
- 229910052742 iron Inorganic materials 0.000 description 3
- 229910052725 zinc Inorganic materials 0.000 description 3
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 2
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 description 2
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 description 2
- UCKMPCXJQFINFW-UHFFFAOYSA-N Sulphide Chemical compound [S-2] UCKMPCXJQFINFW-UHFFFAOYSA-N 0.000 description 2
- GWEVSGVZZGPLCZ-UHFFFAOYSA-N Titan oxide Chemical compound O=[Ti]=O GWEVSGVZZGPLCZ-UHFFFAOYSA-N 0.000 description 2
- 230000015572 biosynthetic process Effects 0.000 description 2
- 230000000052 comparative effect Effects 0.000 description 2
- 229910052802 copper Inorganic materials 0.000 description 2
- 238000006477 desulfuration reaction Methods 0.000 description 2
- 230000023556 desulfurization Effects 0.000 description 2
- 230000020169 heat generation Effects 0.000 description 2
- 239000012535 impurity Substances 0.000 description 2
- 229910052748 manganese Inorganic materials 0.000 description 2
- VNWKTOKETHGBQD-UHFFFAOYSA-N methane Chemical compound C VNWKTOKETHGBQD-UHFFFAOYSA-N 0.000 description 2
- 229910052750 molybdenum Inorganic materials 0.000 description 2
- 239000011148 porous material Substances 0.000 description 2
- 229910052721 tungsten Inorganic materials 0.000 description 2
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 1
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 1
- MYMOFIZGZYHOMD-UHFFFAOYSA-N Dioxygen Chemical compound O=O MYMOFIZGZYHOMD-UHFFFAOYSA-N 0.000 description 1
- NINIDFKCEFEMDL-UHFFFAOYSA-N Sulfur Chemical compound [S] NINIDFKCEFEMDL-UHFFFAOYSA-N 0.000 description 1
- 229910021536 Zeolite Inorganic materials 0.000 description 1
- 238000005299 abrasion Methods 0.000 description 1
- 239000006096 absorbing agent Substances 0.000 description 1
- 230000003213 activating effect Effects 0.000 description 1
- PNEYBMLMFCGWSK-UHFFFAOYSA-N aluminium oxide Inorganic materials [O-2].[O-2].[O-2].[Al+3].[Al+3] PNEYBMLMFCGWSK-UHFFFAOYSA-N 0.000 description 1
- 229910021529 ammonia Inorganic materials 0.000 description 1
- 229910052799 carbon Inorganic materials 0.000 description 1
- 239000013043 chemical agent Substances 0.000 description 1
- 239000011362 coarse particle Substances 0.000 description 1
- 238000005536 corrosion prevention Methods 0.000 description 1
- 239000010779 crude oil Substances 0.000 description 1
- 239000013078 crystal Substances 0.000 description 1
- 230000006866 deterioration Effects 0.000 description 1
- 230000018109 developmental process Effects 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 229910001873 dinitrogen Inorganic materials 0.000 description 1
- HNPSIPDUKPIQMN-UHFFFAOYSA-N dioxosilane;oxo(oxoalumanyloxy)alumane Chemical compound O=[Si]=O.O=[Al]O[Al]=O HNPSIPDUKPIQMN-UHFFFAOYSA-N 0.000 description 1
- 229910001882 dioxygen Inorganic materials 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 238000010438 heat treatment Methods 0.000 description 1
- 230000007774 longterm Effects 0.000 description 1
- 239000002184 metal Substances 0.000 description 1
- 229910052751 metal Inorganic materials 0.000 description 1
- 239000000203 mixture Substances 0.000 description 1
- 239000003345 natural gas Substances 0.000 description 1
- 239000010742 number 1 fuel oil Substances 0.000 description 1
- 239000003921 oil Substances 0.000 description 1
- 239000003348 petrochemical agent Substances 0.000 description 1
- 239000003209 petroleum derivative Substances 0.000 description 1
- 238000010248 power generation Methods 0.000 description 1
- 230000002265 prevention Effects 0.000 description 1
- 230000001172 regenerating effect Effects 0.000 description 1
- 230000000630 rising effect Effects 0.000 description 1
- 238000010008 shearing Methods 0.000 description 1
- 239000000377 silicon dioxide Substances 0.000 description 1
- 238000003786 synthesis reaction Methods 0.000 description 1
- 239000010457 zeolite Substances 0.000 description 1
Landscapes
- Treating Waste Gases (AREA)
- Separation Of Gases By Adsorption (AREA)
- Physical Or Chemical Processes And Apparatus (AREA)
- Industrial Gases (AREA)
Description
【発明の詳細な説明】 (産業上の利用分野) 本発明は、たとえば石炭ガス化プロセスの生成ガスのよ
うなばいじんを含有する高温に還元性ガス混合物中に含
まれるイオウ化合物、特に硫化水素を吸着除去するに際
し、ばいじん付着による圧損上昇や閉塞がなく安定運転
が可能で、かつイオウ化合物を捕捉した該吸着剤の再生
反応を効率良く行うことが可能な固気接触反応装置に関
するものである。FIELD OF THE INVENTION The present invention relates to sulfur compounds, especially hydrogen sulfide, contained in a reducing gas mixture at elevated temperatures containing soot, such as the product gas of a coal gasification process. The present invention relates to a solid-gas contact reaction device capable of performing stable operation without pressure loss increase or blockage due to dust adhesion when adsorbing and removing, and capable of efficiently performing a regeneration reaction of the adsorbent that has captured a sulfur compound.
(従来の技術) 近年、原油価格の高騰や輸入原油の重質化への対策とし
て、劣質残渣あるいは石炭などの利用技術の開発が進め
られているが、これらを原料としてガス化を行い、得ら
れるガスを発電や燃料及び合成原料とする方法は、その
代表的な例である。(Prior art) In recent years, development of utilization technology of inferior residue or coal etc. has been promoted as measures against rising oil price and heavy imported crude oil. A typical example is a method in which the generated gas is used for power generation or as a fuel or a synthetic raw material.
しかし、このガス化生成ガスは、原料の石炭や重質油に
よつて違うが、数100〜数1000ppmの硫化水素を
含み、該硫化水素は公害防止、あるいは後流機器の腐食
防止のため、是非除去が必要である。However, this gasification product gas contains hydrogen sulfide of several hundreds to several thousand ppm, which varies depending on the raw material coal or heavy oil, and the hydrogen sulfide is for pollution prevention or corrosion prevention of downstream equipment, It needs to be removed.
この生成ガス中の硫化水素を乾式で除去する手段として
て、Fe,Zn,Mo,Cu,W等の金属酸化物の小球状吸着剤
を適用した固定床、移動床、流動床などの固気接触反応
器が使用されているが、ガス化生成ガス中には、未燃カ
ーボン(チヤー)、タールなどのばいじんを多量に含む
ため、従来の小球状吸着剤を適用した固定床において
は、飛散するばいじんによつて目塞りが生じ、圧力損失
が増大してガス化炉の運転に支障をきたすので好ましく
ない。又、吸着剤を移動させ圧力損失の増大を防止する
移動床においては、長時間の安定運転に問題があり、装
置が複雑となるなど欠点がある。更に、流動床において
は、吸着剤の摩耗、飛散等の欠点がある。そこで本発明
者らは上述した従来装置の欠点を克服し、経時的圧損上
昇がなく、かつコンパクト化された、経済的で、実用性
に富む固気接触反応装置として、管状構造体からなる吸
着剤を該吸着面がガス流れに対して平行になるように多
数個配置したことを特徴とする固気接触反応装置を既に
出願している(特願昭58−223250)。As a means for dryly removing hydrogen sulfide in the produced gas, solid gas such as a fixed bed, a moving bed or a fluidized bed to which a small spherical adsorbent of a metal oxide such as Fe, Zn, Mo, Cu or W is applied. Although a catalytic reactor is used, the gasification product gas contains a large amount of soot and dust such as unburned carbon (char) and tar. Therefore, in a fixed bed to which a conventional small spherical adsorbent is applied, it scatters. It is not preferable because clogging is caused by the dust and dirt, and the pressure loss increases, which hinders the operation of the gasification furnace. Further, in a moving bed in which the adsorbent is moved to prevent an increase in pressure loss, there is a problem in stable operation for a long time, which makes the device complicated. Further, in the fluidized bed, there are drawbacks such as abrasion and scattering of the adsorbent. Therefore, the present inventors have overcome the drawbacks of the above-mentioned conventional apparatus, have no increase in pressure loss over time, and have a compact size, which is economical, and has a high practicality. An application has already been filed for a solid-gas contact reaction device characterized in that a large number of agents are arranged such that the adsorption surface is parallel to the gas flow (Japanese Patent Application No. 58-223250).
(本発明が解決しようとする問題点) 本発明は上述の管状構造体からなる吸着剤に平行流で処
理ガスを通気させるようにした固気接触反応装置の特色
を生かすべく、イオウ化合物を捕捉した該吸着剤の再生
反応時の発熱を極力抑制し、吸着剤の局部加熱による性
能低下や損傷を防ぎ、安定した高温還元性ガスからの脱
硫方法を達成しうる固気接触反応装置を提供するもので
ある。(Problems to be Solved by the Present Invention) The present invention captures a sulfur compound in order to take advantage of the feature of the solid-gas contact reaction device in which the processing gas is passed through the adsorbent composed of the tubular structure in parallel flow. Provided is a solid-gas contact reaction apparatus capable of suppressing heat generation during regeneration reaction of the adsorbent as much as possible, preventing performance deterioration and damage due to local heating of the adsorbent, and achieving a stable desulfurization method from high-temperature reducing gas. It is a thing.
(問題点を解決するための手段) 本発明は、石炭や重質油などのガス化によつて得られる
高温還元性ガス中に含まれるイオウ化合物を、金属酸化
物を主成分とする吸着剤で吸着除去し、該吸着剤を再生
して繰り返し使用する脱硫方法を管状、ハニカム状、板
状構造体から成る該吸着剤をガス流れに対して平行にな
るように多数個配置した固気接触反応装置で行うととも
に、吸着と再生反応のガス流れ方向を切替ることで再生
反応時の局部的な発熱を抑制して吸着剤の性能維持を図
るものである。(Means for Solving Problems) The present invention relates to a sulfur compound contained in a high-temperature reducing gas obtained by gasification of coal, heavy oil, or the like as an adsorbent containing a metal oxide as a main component. Desulfurization method in which the adsorbent is adsorbed and removed by reusing the adsorbent repeatedly, and the adsorbent consisting of tubular, honeycomb, and plate-like structures is arranged in parallel so as to be parallel to the gas flow. This is carried out in a reactor, and by switching the gas flow directions of the adsorption and regeneration reactions, local heat generation during the regeneration reaction is suppressed and the performance of the adsorbent is maintained.
すなわち本発明は、高温還元性ガス中に含まれるイオウ
化合物を、金属酸化物を主成分とする吸着剤で吸着除去
し、該吸着剤を再生して繰り返し使用するようにした装
置において、管状構造体からなる吸着剤を該吸着面がガ
ス流れに対して平行になるように多数個配置するととも
に、吸着時と再生時のガス流れ方向を逆向きにしうるよ
うにしたことを特徴とする固気接触反応装置である。That is, the present invention provides a device having a tubular structure in which a sulfur compound contained in a high-temperature reducing gas is adsorbed and removed by an adsorbent containing a metal oxide as a main component, and the adsorbent is regenerated for repeated use. Solid gas characterized by arranging a large number of adsorbents composed of a body so that the adsorption surface is parallel to the gas flow, and enabling the gas flow directions during adsorption and regeneration to be opposite. It is a catalytic reactor.
本発明においては、石炭や重質油などのガス化によつて
得られる高温還元性ガス中のイオウ化合物、特に硫化水
素をFe,Zn,Mo,Mn,Cu,Wなどの金属酸化物を吸着剤
として、250〜450℃で接触反応させ、硫化物とし
て吸着剤内部に捕捉し、また不純物のCOSがHCNも
一部反応し除去するもので、Feの場合のH2ガスによる
反応式は次の通りである。In the present invention, sulfur compounds in a high-temperature reducing gas obtained by gasification of coal, heavy oil, etc., particularly hydrogen sulfide, are adsorbed on metal oxides such as Fe, Zn, Mo, Mn, Cu, W. As a chemical agent, the reaction is carried out at 250 to 450 ° C., the sulfide is trapped inside the adsorbent, and COS as an impurity also partially reacts and removes HCN. The reaction formula by H 2 gas for Fe is as follows. Is the street.
Fe2O3+H2→2FeO+H2O FeO+H2S→FeS+H2O MCN+H2O→NH3+CO COS+H2O→CO2+H2S 本発明では、これら吸着剤をガス通過面がガス流れと平
行になるように管状、ハニカム状、板状構造体を配置
し、吸着時のガス流れ方向とは逆の方向から含酸素ガス
を流すことで、該吸着剤の性能維持と反応器内部の均一
な熱分布を保持することを特徴とし、吸着剤の金属酸化
物を形成するにあたつては、該酸化物自体の形成による
か、またはチタニア、シリカ、アルミナやゼオライトな
どの耐熱性多孔質物質に金属酸化物を担持して、ガス流
れが平行流となるように構造体を形成するなどの各種方
法で行うことができる。Fe 2 O 3 + H 2 → 2 FeO + H 2 O FeO + H 2 S → FeS + H 2 O MCN + H 2 O → NH 3 + CO COS + H 2 O → CO 2 + H 2 S By arranging the tubular, honeycomb, or plate-like structure so that the oxygen-containing gas flows from the direction opposite to the gas flow direction during adsorption, the performance of the adsorbent is maintained and uniform heat is generated inside the reactor. Characterized by maintaining the distribution, in forming the metal oxide of the adsorbent, the formation of the oxide itself, or the metal in the heat-resistant porous material such as titania, silica, alumina or zeolite. It can be carried out by various methods such as supporting an oxide and forming a structure so that the gas flows are parallel flows.
以下、実施態様を示す第1図に基づいて本発明装置を詳
細に説明する。Hereinafter, the device of the present invention will be described in detail based on FIG. 1 showing an embodiment.
第1図において、石炭1は小量の空気又は酸素2でガス
炉3内で部分燃焼ガス化され、H2及びCOを主成分とする
ガス化ガス4が得られる。これは石油や天然ガスの代替
として、コンパインドガスタービンや、都市ガス等の燃
料に、或いはメタノールやアンモニア又は石油化学の合
成原料に使用される。In FIG. 1, coal 1 is partially combusted and gasified in a gas furnace 3 with a small amount of air or oxygen 2 to obtain a gasified gas 4 containing H 2 and CO as main components. It is used as a substitute for petroleum or natural gas, as a fuel for companion gas turbines, city gas, etc., or as a synthetic raw material for methanol, ammonia, or petrochemicals.
このガス化ガス4は石炭の種類やガス化条件に依つて異
なるが、数10〜数1000ppmのH2SやCOS,NH4や、2
0〜40g/Nm3のばいじんを含み、温度はガス化炉
3出口のスチームヒータ等で熱回収され、250〜50
0℃、圧力はガス炉3の形式によつて異なるが、常圧〜
25ataである。The gasification gas 4 varies depending on the type of coal and the gasification conditions, but is several tens to several thousand ppm of H 2 S, COS, NH 4 , and 2
It contains 0 to 40 g / Nm 3 of soot and dust, and the temperature is 250 to 50 because heat is recovered by a steam heater at the outlet of the gasification furnace 3.
0 ℃, the pressure depends on the type of gas furnace 3, but normal pressure ~
25 ata.
本発明では、先ず、サイクロン等の除じん装置5で粗粒
ばいじん17を除き、ガス化ガス6は次にFe,Zn,Mo,
Mn,Cu,W等の金属酸化物からなる吸着剤8を充填した
反応器7でH2Sを硫化物として吸着除去する。In the present invention, first, the dust removal device 5 such as a cyclone is used to remove the coarse particle dust 17, and the gasification gas 6 is fed to Fe, Zn, Mo,
H 2 S is adsorbed and removed as a sulfide in a reactor 7 filled with an adsorbent 8 made of a metal oxide such as Mn, Cu or W.
Fe酸化物を吸収剤とした場合の反応式は下記のとおりで
あり、 3Fe2O3+H2→2Fe3O4+H2O 3H2S+Fe3O4+H2→3FeS+4H2O HCN+H2O→NH3+CO COS+H2O→CO2+H2S 不純物のHCNやCOSも一部反応し除去される。The reaction formula when Fe oxide is used as the absorber is as follows: 3Fe 2 O 3 + H 2 → 2Fe 3 O 4 + H 2 O 3H 2 S + Fe 3 O 4 + H 2 → 3FeS + 4H 2 O HCN + H 2 O → NH 3 + CO COS + H 2 O → CO 2 + H 2 S Impurities such as HCN and COS are also partially reacted and removed.
反応温度は250〜450℃、SV値(ガス流量Nm3
/h/吸着剤容量m3)は1000〜20,0001/
h程度で、ガス中のH2Sの90〜95%以上が除去され
る。The reaction temperature is 250 to 450 ° C., SV value (gas flow rate Nm 3
/ H / adsorbent capacity m 3 ) is 1000 to 20,0001 /
At about h, 90 to 95% or more of H 2 S in the gas is removed.
本発明においては、上記の吸収剤の形状は、管状構造体
を採用し、この吸着剤をガス流れに対して平行になるよ
うに多数個配置しており、これによつて従来の小球状吸
着剤を適用した固定床、移動床、反応装置にみられたば
いじんによる圧損上昇もなく、安定した運転が可能とな
り、また従来の流動床反応装置にみられた摩耗損失も少
なく、経済的にも有利なものとすることができる。In the present invention, as the shape of the absorbent, a tubular structure is adopted, and a large number of the absorbents are arranged in parallel to the gas flow. There is no pressure drop increase due to soot and dust found in fixed beds, moving beds and reactors where agents are applied, stable operation is possible, and the wear loss found in conventional fluidized bed reactors is also small, economically Can be advantageous.
反応器7は第1図では多塔方式を採用しているが、これ
は一方でH2Sの吸着等で劣化した吸着剤を切替え方式に
より再生賦活させるためのものである。The reactor 7 adopts the multi-column system in FIG. 1, but this is for regenerating and activating the adsorbent deteriorated by the adsorption of H 2 S and the like by the switching system.
次に、処理ガス9はグラニユラーベツド方式等の精密除
じん装置10で微細ばいじん11を除き、クリーンガス
12にしてガスタービン燃料や合成ガス原料に供され
る。Next, the treated gas 9 is subjected to a fine dust removal device 10 such as a Granular bed method to remove fine dust 11 and converted into a clean gas 12 to be used as a gas turbine fuel or a raw material for synthesis gas.
一方、反応器7内の充填吸着剤が吸着H2Sによつて飽和
に達してくると、該反応器に空気又は酸素13を供給
し、次式に示すような焙焼反応を行い、吸着剤を再生さ
せると同時に、濃厚なSO2ガス14を得る。On the other hand, when the packed adsorbent in the reactor 7 reaches saturation due to the adsorbed H 2 S, air or oxygen 13 is supplied to the reactor to perform a roasting reaction as shown in the following formula, At the same time that the agent is regenerated, a rich SO 2 gas 14 is obtained.
4FeS+7O2→2Fe2O3+4SO2 4Fe3O4+O2→6Fe2O3 上記反応は発熱反応であり、空気又は(及び)酸素13
の供給に応じ急激に起るので、第1図に示すように出口
ガス14を経路15で循環しながら、必要量の空気又は
(及び)酸素を低濃度で全体に一様に供給するなどによ
り、温度をコントロールするとともに、ガス流れ方向を
吸着反応とは逆にしてH2S吸着量の少ない方から再生反
応をゆつくり進行させることを特徴とするものである。4FeS + 7O 2 → 2Fe 2 O 3 + 4SO 2 4Fe 3 O 4 + O 2 → 6Fe 2 O 3 The above reaction is an exothermic reaction, and air or (and) oxygen 13
As shown in FIG. 1, the outlet gas 14 is circulated in the path 15 while the required amount of air or / and oxygen is uniformly supplied to the whole at a low concentration. In addition to controlling the temperature, the gas flow direction is opposite to that of the adsorption reaction, and the regeneration reaction proceeds slowly from the side with the smaller H 2 S adsorption amount.
この再生温度は250〜600℃で行われ、吸着したS
の殆んどが放散されるが、再生反応初期は高濃度のSO2
ガスが放散され、急激な発熱反応を生起させると吸着剤
の耐熱温度以上に加熱され、吸着剤の結晶構造変質によ
る性能失活があるので上記のような配慮は不可欠であ
る。濃厚SO2ガスは経路16を経て、そのまま硫酸製造
原料などに利用するか、あるいは単体硫黄として回収す
る工程へ導かれる。The regeneration temperature is 250 to 600 ° C, and the adsorbed S
Most of the CO 2 is emitted, but high concentration of SO 2
When the gas is diffused and a rapid exothermic reaction occurs, the gas is heated above the heat resistant temperature of the adsorbent and the performance is deactivated due to the change in the crystal structure of the adsorbent. The concentrated SO 2 gas is passed through the route 16 and used as it is as a raw material for producing sulfuric acid or the like, or is guided to a step of recovering it as elemental sulfur.
以下、実施例をあげて本発明の効果を具体的に説明す
る。Hereinafter, the effects of the present invention will be specifically described with reference to examples.
(実施例1) 石炭のガス化によつて得られた3000ppmのH2Sを含む
ガス化ガスを多段サイクロンを通して、ばいじんを約3
00mg/Nm3とし、温度400℃で、以下に説明する
本発明の反応器に導きH2Sの吸着試験を行つた。(Example 1) A gasified gas containing 3000 ppm of H 2 S obtained by gasification of coal was passed through a multi-stage cyclone to remove about 3 parts of dust.
The adsorption test of H 2 S was carried out at a temperature of 400 ° C. with the amount of 00 mg / Nm 3 introduced into the reactor of the present invention described below.
第2図はこの実施例1で使用した反応器及び吸着剤の構
造を示す。FIG. 2 shows the structures of the reactor and adsorbent used in this Example 1.
図中1は管状構造体の吸着剤を充填した反応装置であ
り、内部に管状吸着剤2が2段に充填されている。ガス
化ガス3はこの吸着層の一方から入り、内部で硫化水素
が吸着層で吸着され、浄化ガス4として系外に排出され
る。In the figure, reference numeral 1 is a reaction device filled with an adsorbent for a tubular structure, and the tubular adsorbent 2 is filled in two stages inside. The gasification gas 3 enters from one side of the adsorption layer, hydrogen sulfide is adsorbed inside the adsorption layer, and is discharged out of the system as a purified gas 4.
この管状吸着剤2は四角型、六角型、三角型などの形状
をしており、本実施例では四角型(格子状)の孔径(ピ
ツチ)4.5mm、壁厚1.2mmのFe2O3系吸着剤を組合
せて第2図中21,22,23……で示す各1本の管状
吸着剤の寸法を150口×500L(mm)としたものを
2段に配置したものである。The tubular adsorbent 2 has a shape such as a square shape, a hexagonal shape, and a triangular shape. In this embodiment, Fe 2 O having a square (lattice) pore diameter (pitch) of 4.5 mm and a wall thickness of 1.2 mm. A combination of 3 type adsorbents, each of which has a tubular adsorbent size of 1 , 2, 2 2 , 2 3, ... Is.
このような管状の吸着剤ではガス流れは吸着面に対して
平行であり、吸着面に対してばいじんを押しつけるガス
流れがないため、たとえばいじんが表面に付着した場合
でも、ガス流れの剪断力のため再飛散し、ばいじん付着
の経時増加は見られず、圧力損失の増大はほとんどな
く、プラントの安定運転が可能となる。又、複雑な吸着
剤の移動操作がなく、摩耗も少なく、経済的に有利であ
る。In such a tubular adsorbent, the gas flow is parallel to the adsorption surface, and there is no gas flow that presses dust against the adsorption surface, so even if dust adheres to the surface, the shearing force of the gas flow Therefore, it is re-scattered, no increase in the adhesion of dust and dust is observed, the pressure loss is hardly increased, and the stable operation of the plant becomes possible. Further, there is no complicated operation for moving the adsorbent, and there is little wear, which is economically advantageous.
このようにして吸着出口のH2S濃度が100ppmとなり、
破過に達するまで吸着反応を行つた後、反応器入口温度
500℃でガス化ガス流れと逆方向から再生ガス(酸素
ガス1%、窒素ガス99%)を流した場合と、同方向で
流した場合の吸着剤の温度分布を、再生ガスの流れ方向
と断面部につき測定した結果を第3図に示す。In this way, the H 2 S concentration at the adsorption outlet becomes 100 ppm,
After performing the adsorption reaction until the breakthrough is reached, the regeneration gas (oxygen gas 1%, nitrogen gas 99%) flows in the same direction as the gasification gas flow at the reactor inlet temperature of 500 ° C. FIG. 3 shows the results of measuring the temperature distribution of the adsorbent in the case of the above, in the flow direction of the regeneration gas and in the cross section.
再生反応時のガス流れ方向を吸着反応と逆にする本実施
例は同一方向にする比較例より吸収剤長さ方向、断面部
とも再生反応熱による発熱量も少なくなつており、吸着
剤の耐熱性の観点からも失活しにくいことから長期間の
使用に耐える利点がある。In the present example, in which the gas flow direction during the regeneration reaction is opposite to that in the adsorption reaction, the calorific value due to the heat of the regeneration reaction is smaller in both the absorbent length direction and the cross section than in the comparative example in which the same direction is used, and the heat resistance of the adsorbent is reduced. From the standpoint of sex, since it is hard to deactivate, it has the advantage of withstanding long-term use.
第1,2図は本発明装置の一実施態様例の説明図で、第
1図は本発明装置を石炭ガス化装置に組込んだ場合の全
フローを示しており、第2図は吸着剤を充填した反応器
の構造を示している。 第3図は本発明の実施例と比較例の反応器内部の温度分
布測定結果を示す図である。1 and 2 are explanatory views of an embodiment of the apparatus of the present invention, FIG. 1 shows the entire flow when the apparatus of the present invention is incorporated into a coal gasifier, and FIG. 2 shows an adsorbent. 1 shows the structure of a reactor filled with. FIG. 3 is a diagram showing the results of measuring the temperature distribution inside the reactors of Examples of the present invention and Comparative Examples.
Claims (1)
を、金属酸化物を主成分とする吸着剤で吸着除去し、該
吸着剤を再生して繰り返し使用するようにした装置にお
いて、管状構造体からなる吸着剤を該吸着面がガス流れ
に対して平行になるように多数個配置するとともに、吸
着時と再生時のガス流れ方向を逆向きにしうるようにし
たことを特徴とする固気接触反応装置。1. A tubular structure in a device in which a sulfur compound contained in a high-temperature reducing gas is adsorbed and removed by an adsorbent containing a metal oxide as a main component, and the adsorbent is regenerated for repeated use. Solid gas characterized by arranging a large number of adsorbents composed of a body so that the adsorption surface is parallel to the gas flow, and enabling the gas flow directions during adsorption and regeneration to be opposite. Catalytic reactor.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP60024529A JPH0631350B2 (en) | 1985-02-13 | 1985-02-13 | Solid-gas contact reactor |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP60024529A JPH0631350B2 (en) | 1985-02-13 | 1985-02-13 | Solid-gas contact reactor |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS61185592A JPS61185592A (en) | 1986-08-19 |
| JPH0631350B2 true JPH0631350B2 (en) | 1994-04-27 |
Family
ID=12140679
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP60024529A Expired - Lifetime JPH0631350B2 (en) | 1985-02-13 | 1985-02-13 | Solid-gas contact reactor |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH0631350B2 (en) |
Families Citing this family (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN101235324B (en) | 2007-11-13 | 2011-06-08 | 沈阳航空工业学院 | High-temperature coal gas desulfurizer using coal ash as carrier |
| JP2015010211A (en) * | 2013-07-01 | 2015-01-19 | 一般財団法人電力中央研究所 | Impurity removal method and desulfurization method |
-
1985
- 1985-02-13 JP JP60024529A patent/JPH0631350B2/en not_active Expired - Lifetime
Also Published As
| Publication number | Publication date |
|---|---|
| JPS61185592A (en) | 1986-08-19 |
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