JPH07102299B2 - Refining method for high temperature reducing gas - Google Patents
Refining method for high temperature reducing gasInfo
- Publication number
- JPH07102299B2 JPH07102299B2 JP62157849A JP15784987A JPH07102299B2 JP H07102299 B2 JPH07102299 B2 JP H07102299B2 JP 62157849 A JP62157849 A JP 62157849A JP 15784987 A JP15784987 A JP 15784987A JP H07102299 B2 JPH07102299 B2 JP H07102299B2
- Authority
- JP
- Japan
- Prior art keywords
- gas
- regeneration
- sulfur
- absorbent
- reactor
- 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
- 238000000034 method Methods 0.000 title claims description 90
- 238000007670 refining Methods 0.000 title claims description 10
- 239000007789 gas Substances 0.000 claims description 203
- 238000011069 regeneration method Methods 0.000 claims description 111
- 230000008929 regeneration Effects 0.000 claims description 110
- NINIDFKCEFEMDL-UHFFFAOYSA-N Sulfur Chemical compound [S] NINIDFKCEFEMDL-UHFFFAOYSA-N 0.000 claims description 69
- 239000002250 absorbent Substances 0.000 claims description 57
- 230000002745 absorbent Effects 0.000 claims description 57
- 229910052717 sulfur Inorganic materials 0.000 claims description 57
- 239000011593 sulfur Substances 0.000 claims description 57
- 238000010521 absorption reaction Methods 0.000 claims description 42
- 229910052760 oxygen Inorganic materials 0.000 claims description 23
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 claims description 21
- 239000001301 oxygen Substances 0.000 claims description 21
- 150000003464 sulfur compounds Chemical class 0.000 claims description 19
- JJWKPURADFRFRB-UHFFFAOYSA-N carbonyl sulfide Chemical compound O=C=S JJWKPURADFRFRB-UHFFFAOYSA-N 0.000 claims description 14
- 239000007788 liquid Substances 0.000 claims description 10
- RWSOTUBLDIXVET-UHFFFAOYSA-N Dihydrogen sulfide Chemical compound S RWSOTUBLDIXVET-UHFFFAOYSA-N 0.000 claims description 7
- 229910000037 hydrogen sulfide Inorganic materials 0.000 claims description 7
- 238000000746 purification Methods 0.000 claims description 4
- 238000002309 gasification Methods 0.000 description 42
- XEEYBQQBJWHFJM-UHFFFAOYSA-N iron Substances [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 description 17
- 238000006243 chemical reaction Methods 0.000 description 12
- 238000002485 combustion reaction Methods 0.000 description 9
- 229910002091 carbon monoxide Inorganic materials 0.000 description 6
- 230000003647 oxidation Effects 0.000 description 6
- 238000007254 oxidation reaction Methods 0.000 description 6
- 239000006227 byproduct Substances 0.000 description 5
- 238000004364 calculation method Methods 0.000 description 5
- 239000003054 catalyst Substances 0.000 description 5
- 239000003245 coal Substances 0.000 description 5
- 229910044991 metal oxide Inorganic materials 0.000 description 5
- 150000004706 metal oxides Chemical class 0.000 description 5
- 230000001172 regenerating effect Effects 0.000 description 5
- 230000006866 deterioration Effects 0.000 description 4
- 239000000295 fuel oil Substances 0.000 description 4
- 229910052739 hydrogen Inorganic materials 0.000 description 4
- 239000000203 mixture Substances 0.000 description 4
- 239000000047 product Substances 0.000 description 4
- 239000000428 dust Substances 0.000 description 3
- 230000000694 effects Effects 0.000 description 3
- 238000004519 manufacturing process Methods 0.000 description 3
- 239000010742 number 1 fuel oil Substances 0.000 description 3
- 239000003921 oil Substances 0.000 description 3
- 239000002994 raw material Substances 0.000 description 3
- UFWIBTONFRDIAS-UHFFFAOYSA-N Naphthalene Chemical compound C1=CC=CC2=CC=CC=C21 UFWIBTONFRDIAS-UHFFFAOYSA-N 0.000 description 2
- RAHZWNYVWXNFOC-UHFFFAOYSA-N Sulphur dioxide Chemical compound O=S=O RAHZWNYVWXNFOC-UHFFFAOYSA-N 0.000 description 2
- 238000001816 cooling Methods 0.000 description 2
- 239000000446 fuel Substances 0.000 description 2
- 238000010438 heat treatment Methods 0.000 description 2
- 230000001590 oxidative effect Effects 0.000 description 2
- 238000010926 purge Methods 0.000 description 2
- 238000011946 reduction process Methods 0.000 description 2
- 150000003467 sulfuric acid derivatives Chemical class 0.000 description 2
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 description 1
- -1 FeSO 4 Chemical class 0.000 description 1
- UFHFLCQGNIYNRP-UHFFFAOYSA-N Hydrogen Chemical compound [H][H] UFHFLCQGNIYNRP-UHFFFAOYSA-N 0.000 description 1
- LSNNMFCWUKXFEE-UHFFFAOYSA-N Sulfurous acid Chemical compound OS(O)=O LSNNMFCWUKXFEE-UHFFFAOYSA-N 0.000 description 1
- UCKMPCXJQFINFW-UHFFFAOYSA-N Sulphide Chemical compound [S-2] UCKMPCXJQFINFW-UHFFFAOYSA-N 0.000 description 1
- 229910052799 carbon Inorganic materials 0.000 description 1
- 239000003638 chemical reducing agent Substances 0.000 description 1
- 239000000571 coke Substances 0.000 description 1
- 238000011109 contamination Methods 0.000 description 1
- 238000007796 conventional method Methods 0.000 description 1
- 239000000498 cooling water Substances 0.000 description 1
- 229910052802 copper Inorganic materials 0.000 description 1
- 239000010779 crude oil Substances 0.000 description 1
- 230000007423 decrease Effects 0.000 description 1
- 230000002950 deficient Effects 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- JEIPFZHSYJVQDO-UHFFFAOYSA-N ferric oxide Chemical compound O=[Fe]O[Fe]=O JEIPFZHSYJVQDO-UHFFFAOYSA-N 0.000 description 1
- 229910052736 halogen Inorganic materials 0.000 description 1
- 150000002367 halogens Chemical class 0.000 description 1
- 239000001257 hydrogen Substances 0.000 description 1
- 238000002347 injection Methods 0.000 description 1
- 239000007924 injection Substances 0.000 description 1
- 229910052742 iron Inorganic materials 0.000 description 1
- 238000012423 maintenance Methods 0.000 description 1
- 229910052748 manganese Inorganic materials 0.000 description 1
- 229910052750 molybdenum Inorganic materials 0.000 description 1
- 239000004058 oil shale Substances 0.000 description 1
- 239000003208 petroleum Substances 0.000 description 1
- 231100000572 poisoning Toxicity 0.000 description 1
- 230000000607 poisoning effect Effects 0.000 description 1
- 239000011148 porous material Substances 0.000 description 1
- 238000010248 power generation Methods 0.000 description 1
- 230000002265 prevention Effects 0.000 description 1
- 238000011084 recovery Methods 0.000 description 1
- 238000004064 recycling Methods 0.000 description 1
- 239000004071 soot Substances 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- 239000013589 supplement Substances 0.000 description 1
- 230000001502 supplementing effect Effects 0.000 description 1
- 239000011269 tar Substances 0.000 description 1
- 239000011275 tar sand Substances 0.000 description 1
- 229910052721 tungsten Inorganic materials 0.000 description 1
- 238000004065 wastewater treatment Methods 0.000 description 1
- 229910052725 zinc Inorganic materials 0.000 description 1
Landscapes
- Industrial Gases (AREA)
- Treating Waste Gases (AREA)
- Gas Separation By Absorption (AREA)
Description
【発明の詳細な説明】 〔産業上の利用分野〕 本発明は、高温還元性ガスの精製方法に関し、例えば石
炭ガス化プロセスの生成ガスのような高温の還元性ガス
混合物中に含まれる硫化水素、硫化カルボニル等のイオ
ウ化合物を合理的に除去する方法に関する。Description: TECHNICAL FIELD The present invention relates to a method for refining a high-temperature reducing gas, for example, hydrogen sulfide contained in a high-temperature reducing gas mixture such as a product gas of a coal gasification process. , A method for rationally removing sulfur compounds such as carbonyl sulfide.
近年、石油資源の枯渇、価格の高騰から、燃料(又は原
料)の多様化が叫ばれ、石炭や重質油(タールサンド
油、オイルシエール油、大慶重油、マヤ原油、或いは減
圧残油など)の利用技術の開発が進められている。石炭
や重質油をガス化して発電に利用したり或いは燃料及び
合成原料とする方法はその代表的な一例である。In recent years, due to depletion of petroleum resources and soaring prices, diversification of fuels (or raw materials) has been called for, and coal and heavy oil (tar sand oil, oil shale oil, Daqing heavy oil, Maya crude oil, vacuum residual oil, etc.) Is being developed. A typical example is a method in which coal or heavy oil is gasified and used for power generation or used as a fuel and a synthetic raw material.
しかし、このガス化生成ガスには原料の石炭や重質油に
よつて違うが数100〜数1000ppmの硫化水素や硫化カルボ
ニル等のイオウ化合物を含み、公害防止上或いは後流機
器の腐食や触媒の被毒防止のため除去する必要がある。However, this gasification product gas contains sulfur compounds such as hydrogen sulfide and carbonyl sulfide in the range of several hundreds to several thousand ppm, though it depends on the raw material coal or heavy oil. Must be removed to prevent poisoning.
この除去方法としては湿式法と乾式法があるが、湿式法
は処理ガスを冷却しなければならず熱経済上不利であ
り、かつ共存成分(タール、ナフタリン、ハロゲン、NH
3、HCN、煤塵など)の除去あるいは吸収液の汚染、劣化
防止のための前処理や廃水処理のための設備が必要とな
り、プロセスが複雑になる。There are a wet method and a dry method as the removal method, but the wet method is disadvantageous in terms of thermal economy because the processing gas must be cooled, and coexisting components (tar, naphthalene, halogen, NH 3
(3 , HCN, soot, etc.) removal or contamination of absorption liquid, equipment for pretreatment and wastewater treatment to prevent deterioration is required, which complicates the process.
一方、乾式法は熱経済的にも有利で、プロセス構成も簡
素なことから、金属酸化物を主成分とする吸収剤を高温
で硫化物として吸収除去する方法が一般的になつてい
る。吸収剤としてはFe、Zn、Mo、Mn、Cu、Wなどの金属
酸化物が使用され、250〜500℃でH2SやCOSと反応させる
が、Fe2O3の場合を例に採つて説明すると、吸収反応は
(1)〜(7)式に示すように進むとされている。On the other hand, the dry method is also advantageous in terms of thermo-economics and has a simple process structure. Therefore, a method of absorbing and removing an absorbent containing a metal oxide as a main component as a sulfide at a high temperature is generally used. As the absorbent, metal oxides such as Fe, Zn, Mo, Mn, Cu, W are used and reacted with H 2 S and COS at 250 to 500 ° C. Taking Fe 2 O 3 as an example, To explain, it is said that the absorption reaction proceeds as shown in equations (1) to (7).
Fe2O3+H2→2FeO+H2O ……(1) 3Fe2O3+H2→2Fe3O4+H2O ……(2) Fe2O3+CO→2FeO+CO2 ……(3) 3Fe2O3+CO→2Fe3O4+CO2 ……(4) FeO+H2S→FeS+H2O ……(5) Fe3O4+H2+3H2S→3FeS+4H2O ……(6) Fe3O4+CO+3H2S→3FeS+3H2O+CO2 ……(7) 次いで、吸収反応後の吸収剤は酸素含有ガスで(8)式
に示すように金属酸化物に再生され、この吸収、再生反
応の繰返しで高温還元性ガス中のイオウ化合物は亜硫酸
ガスとして回収除去される。Fe 2 O 3 + H 2 → 2FeO + H 2 O …… (1) 3Fe 2 O 3 + H 2 → 2Fe 3 O 4 + H 2 O …… (2) Fe 2 O 3 + CO → 2FeO + CO 2 …… (3) 3Fe 2 O 3 + CO → 2Fe 3 O 4 + CO 2 ...... (4) FeO + H 2 S → FeS + H 2 O ...... (5) Fe 3 O 4 + H 2 + 3H 2 S → 3FeS + 4H 2 O ...... (6) Fe 3 O 4 + CO + 3H 2 S → 3FeS + 3H 2 O + CO 2 (7) Then, the absorbent after the absorption reaction is regenerated into a metal oxide by the oxygen-containing gas as shown in the formula (8), and the absorption and regeneration reactions are repeated to obtain high-temperature reducibility. The sulfur compound in the gas is recovered and removed as sulfurous acid gas.
4FeS+7O2→2Fe2O3+4SO2 ……(8) このプロセスで使用される吸収剤は、前述の金属酸化物
を単独あるいは耐熱性の多孔質物質に担持したものを、
移動床方式の場合は球状あるいは円柱状に成形したもの
が、固定床方式の場合は、ハニカム状に成形したものが
一般に使用されている。4FeS + 7O 2 → 2Fe 2 O 3 + 4SO 2 (8) The absorbent used in this process is the above-mentioned metal oxide, either alone or supported on a heat-resistant porous material.
In the case of the moving bed system, a spherical or cylindrical molded product is generally used, and in the case of the fixed bed system, a honeycomb molded product is generally used.
石炭ガス化ガスのような還元性ガスからイオウ化合物を
除去して精製されたガスはエネルギー源として利用され
るので、CO、H2濃度を安定して製造するプロセスにする
のが好ましく、(1)〜(4)式の反応を極力抑制しな
ければならない。移動床方式では吸収工程と再生工程が
連続的に繰返されるので、上記の技術的課題は克服しや
すいが、固定床方式では吸収工程と再生工程を断続的に
繰返すので、吸収剤再生後の吸収反応開始時には、精製
ガス中のCO、H2濃度が一時的に低下するので、高温還元
性ガスの精製方法としては実用上好ましくない。Since a gas purified by removing sulfur compounds from a reducing gas such as coal gasification gas is used as an energy source, it is preferable to use a process for producing stable CO and H 2 concentrations. )-(4) reactions must be suppressed as much as possible. In the moving bed system, the absorption process and the regeneration process are continuously repeated, so it is easy to overcome the above technical problems, but in the fixed bed system, the absorption process and the regeneration process are repeated intermittently. At the start of the reaction, the concentration of CO and H 2 in the purified gas temporarily decreases, which is not practically preferable as a method for purifying the high-temperature reducing gas.
そこで、本発明者らは固定床反応器を三塔順次切替え
て、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収剤で吸着除去する方法におい
て、該イオウ化合物を吸収した吸収剤を酸素含有ガスで
再生する工程、次いで再生された吸収剤を高温還元性ガ
スで該吸収剤前後の精製の対象となる還元性ガス濃度が
同一になるまで還元する工程、次いで該高温還元性ガス
を通気して該吸収剤で該イオウ化合物を吸収除去する工
程を連続的に繰り返すことにより、精製ガス中の還元性
ガス濃度を安定化させる高温還元性ガスの精製法を提案
した(特願昭60−85412号)。Therefore, the inventors of the present invention switched the fixed bed reactor to three towers in sequence and adsorbed and removed the sulfur compound contained in the high-temperature reducing gas with an absorbent containing a metal oxide as a main component. A step of regenerating the absorbed absorbent with an oxygen-containing gas, then a step of reducing the regenerated absorbent with a high-temperature reducing gas until the reducing gas concentration to be purified before and after the absorbent becomes the same, and then A method for refining a high-temperature reducing gas has been proposed, which stabilizes the concentration of the reducing gas in the purified gas by continuously repeating the step of aerating a high-temperature reducing gas and absorbing and removing the sulfur compound with the absorbent. (Japanese Patent Application No. 60-85412).
一方、従来の高温還元性ガスの精製法においては、再生
SO2ガスからのイオウ回収は、その還元剤として石炭、
コークス等を使用するか或は還元性ガス(CO、H2等)と
還元触媒(Co−Mo系等)やクラウス触媒等を使用してお
り、システムが複雑となる為、運転保守が容易ではな
い。On the other hand, in the conventional high-temperature reducing gas purification method,
Sulfur recovery from SO 2 gas uses coal as its reducing agent,
Since coke is used or reducing gas (CO, H 2 etc.) and reducing catalyst (Co-Mo system etc.) and Claus catalyst etc. are used, the system becomes complicated, so operation and maintenance is not easy. Absent.
また、吸収、再生時の処理ガス温度は、一般に夫々300
〜500℃、500〜900℃で、大きな差異があるので、従来
の固定床方式の場合、吸収→再生の工程切替開始時に処
理温度まで立上る間は、再生温度が不十分となる。これ
は結果として吸収性能及び吸収剤に悪影響を及ぼし、長
期的には吸収剤の劣化につながる。In addition, the process gas temperature during absorption and regeneration is generally 300 for each.
Since there is a large difference between ~ 500 ° C and 500 ~ 900 ° C, in the case of the conventional fixed bed system, the regeneration temperature becomes insufficient while the temperature rises up to the treatment temperature at the start of the process switching from absorption to regeneration. This results in a negative impact on the absorbent performance and the absorbent and leads to deterioration of the absorbent in the long run.
更に、吸収→再生の工程切替毎に、脱圧ステップ及び再
生後の反応器からのSO2ガスの混入防止が必要である。
従つて、再生→還元の工程切替開始前に、再生系のSO2
ガスをパージする為に、減圧運転を一定時間行わねばな
らず、綿密な運転制御が必須であり、運転がかなり面倒
になつていた。Further, it is necessary to prevent the mixture of SO 2 gas from the reactor after the depressurization step and regeneration every time the process of absorption → regeneration is switched.
Therefore, before starting the process switching from regeneration to reduction, the SO 2
In order to purge the gas, the depressurization operation had to be performed for a certain period of time, and careful operation control was essential, which made the operation considerably troublesome.
そこで本発明者らは、 (1) 高温還元性ガス中に含まれる硫化水素、硫化カ
ルボニル等のイオウ化合物を吸収除去する方法で、再生
された吸収剤を高温還元性ガスで該吸収剤前後の対象と
なる還元性ガス濃度が一定となるまで還元後、イオウ化
合物を吸収除去する工程を連続的に繰り返す高温還元性
ガスの精製方法において、吸収剤を充填した反応器を少
なくとも三塔使用し、還元、吸収、SO2還元、再生の四
工程により構成し、該SO2還元工程に再生工程からの循
環ガスを供給し、再生工程及びSO2還元工程で生成する
亜硫酸ガスを単体イオウに転化させて液体イオウとして
回収除去後、その生成ガスの一部を還元工程に導入し、
残部を再生工程に戻すことを特徴とする高温還元性ガス
の精製方法、並びに (2) 上記(1)の方法において、SO2還元工程への
再生工程からの循環ガスに前記高温還元性ガスを添加
し、該循環ガス中の酸素との燃焼反応で該SO2還元工程
に必要な温度に昇温させることを特徴とする高温還元性
ガスの精製方法、 を特願昭62−56776号として提案し、更に、 (3) 高温還元性ガス中に含まれる硫化水素、硫化カ
ルボニル等のイオウ化合物を吸収剤で吸収除去する方法
で、再生された吸収剤を用いてイオウ化合物を吸収除去
する工程を連続的に繰り返す高温還元性ガスの精製方法
において、吸収剤を充填した少なくとも三塔の反応器と
クラウス触媒を充填した少なくとも一塔の反応器を使用
し、吸収、予備再生、再生及び硫黄回収の四工程により
構成し、該再生工程の循環ガス中に前記還元性ガス及び
回収イオウの一部を添加し、酸素の存在下で、該還元性
ガス及び回収イオウを燃焼又は反応させ、必要再生温度
とSO2濃度を確保することによつて、再生工程で単体イ
オウ及びイオウ化合物を生成させ、再生用反応器出口循
環ガス中の単体イオウを液体イオウとして回収分離後、
該循環ガスを前記クラウス触媒を充填した反応器に通し
て該循環ガス中のイオウ化合物を単体イオウに転化さ
せ、液体イオウとして回収除去すると共に、単体イオウ
除去後の該循環ガスの一部を吸収工程に導入し、残部を
再生工程に戻すことを特徴とする高温還元性ガスの精製
方法 を特願昭62−95213号として提案した。Therefore, the inventors of the present invention (1) absorb and remove sulfur compounds such as hydrogen sulfide and carbonyl sulfide contained in the high temperature reducing gas by absorbing the regenerated absorbent with the high temperature reducing gas before and after the absorbent. After reducing until the target reducing gas concentration becomes constant, in a method for refining a high temperature reducing gas that continuously repeats the step of absorbing and removing the sulfur compound, at least three reactors filled with an absorbent are used, reduction, absorption, SO 2 reduction, constituted by the four steps of reproduction, supplying circulating gas from the regeneration step to the SO 2 reduction step to convert the sulfur dioxide to elemental sulfur produced in the regeneration step and SO 2 reduction step After recovering and removing as liquid sulfur, a part of the produced gas is introduced into the reduction process,
A method for purifying a high-temperature reducing gas, characterized in that the rest is returned to the regeneration step, and (2) In the method of (1) above, the high-temperature reducing gas is added to the circulating gas from the regeneration step to the SO 2 reduction step. Proposed as Japanese Patent Application No. 62-56776, a method for refining a high-temperature reducing gas, which is characterized in that the temperature is raised to a temperature necessary for the SO 2 reduction step by a combustion reaction with oxygen in the circulating gas. In addition, (3) a method of absorbing and removing a sulfur compound such as hydrogen sulfide and carbonyl sulfide contained in the high-temperature reducing gas with an absorbent by a method of absorbing and removing the sulfur compound using a regenerated absorbent. In the method of continuously refining a high temperature reducing gas, at least three reactors packed with an absorbent and at least one reactor packed with a Claus catalyst are used to absorb, pre-regenerate, regenerate and recover sulfur. By four steps Form, it was added a portion of the reducing gas and recovering sulfur circulating gas regeneration step, in the presence of oxygen, is combusted or reacting said reducing gas and recovering sulfur, required regeneration temperature and SO 2 By ensuring the concentration, simple sulfur and sulfur compounds are generated in the regeneration step, and the simple sulfur in the recycling reactor outlet circulation gas is recovered and separated as liquid sulfur,
The circulating gas is passed through a reactor filled with the Claus catalyst to convert the sulfur compound in the circulating gas into elemental sulfur, which is recovered and removed as liquid sulfur, and at the same time, a part of the circulating gas after removal of the elemental sulfur is absorbed. A method for refining a high-temperature reducing gas, which is characterized in that it is introduced into the process and the rest is returned to the regeneration process, was proposed as Japanese Patent Application No. 62-95213.
本発明は、上記先願方法より更に経済性を向上させるた
めに、再生工程での性能向上、すなわち単体イオウの効
率的な回収を行うことのできる高温還元性ガスの精製方
法を提供するものである。The present invention provides a method for refining a high-temperature reducing gas capable of improving the performance in the regeneration step, that is, efficiently recovering elemental sulfur in order to further improve the economical efficiency as compared with the above-mentioned prior application method. is there.
本発明は、高温還元性ガス中に含まれる硫化水素、硫化
カルボニル等のイオウ化合物を吸収剤で吸収除去する方
法で、再生された吸収剤を用いてイオウ化合物を吸収除
去する工程を連続的に繰り返す高温還元性ガスの精製方
法において、吸収剤を充填した少なくとも三塔の反応器
を使用し、吸収、予備再生及び再生の三工程により構成
し、該再生工程の循環ガス中に上記還元性ガス及び/又
は系内での回収イオウの一部を添加し酸素の存在下で、
該還元性ガス及び/又は該回収イオウを反応(或いは燃
焼させて必要再生温度とSO2濃度を確保することによ
り、再生工程で単体イオウを生成させ、再生用反応器出
口循環ガス中の単体イオウを液体イオウとして回収除去
後、該循環ガスの一部を吸収工程に導入し、残部を再生
工程に戻すことを特徴とする高温還元性ガスの精製方法
に関する。The present invention is a method of absorbing and removing a sulfur compound such as hydrogen sulfide and carbonyl sulfide contained in a high temperature reducing gas with an absorbent, and a step of continuously absorbing and removing a sulfur compound using a regenerated absorbent. In the repeated refining method of a high temperature reducing gas, at least three reactors packed with an absorbent are used, and the three steps of absorption, preliminary regeneration and regeneration are used, and the reducing gas is contained in the circulating gas of the regeneration step. And / or in the presence of oxygen by adding a portion of the recovered sulfur in the system,
By reacting (or burning) the reducing gas and / or the recovered sulfur to secure a required regeneration temperature and SO 2 concentration, elemental sulfur is generated in the regeneration step, and elemental sulfur in the recycle reactor outlet circulation gas is generated. The present invention relates to a method for purifying a high-temperature reducing gas, which comprises recovering and removing as a liquid sulfur, introducing a part of the circulating gas into an absorption step, and returning the remaining part to a regeneration step.
本発明では、再生工程の循環ガス中で高温還元性ガス
(H2,CO等を含有した可燃ガス)及び系内で回収したイ
オウ(以下、回収イオウ)の一部を燃焼させ、再生用反
応器入口を600〜1000℃、該循環ガス中のSO2濃度を0.1
〜5vol%に維持することによつて、該再生用反応器内を
酸素の存在しない状態の下で、該循環ガス中のSO2,H2O
及びCO2ガス等の一部が、(9)〜(15)式に示すよう
に、該吸収剤(FeS)と反応し、或はガス相互間で反応
して、夫々、単体イオウ(S2)、硫化水素、硫化カルボ
ニル、水素及び一酸化炭素等を生成する。In the present invention, a high-temperature reducing gas (combustible gas containing H 2 , CO, etc.) and a part of sulfur recovered in the system (hereinafter, recovered sulfur) is burned in the circulation gas of the regeneration process to generate a reaction for regeneration. The inlet of the vessel is 600 to 1000 ° C, and the concentration of SO 2 in the circulating gas is 0.1.
By maintaining the content in the recycle reactor in the absence of oxygen, the SO 2 and H 2 O in the circulating gas can be maintained by maintaining the amount of SO 5 to 5 vol%.
And a part of the CO 2 gas or the like reacts with the absorbent (FeS) or between the gases as shown in the formulas (9) to (15), respectively, so that the elemental sulfur (S 2 ), Hydrogen sulfide, carbonyl sulfide, hydrogen and carbon monoxide.
4FeS+2SO2→4FeO+3S2 ……(9) 6FeS+4SO2→2Fe3O4+5S2 ……(10) 8FeS+6SO2→4Fe2O3+7S2 ……(11) FeS+H2O→FeO+H2S ……(12) 3FeS+4H2O→Fe3O4+3H2S+H2 ……(13) 3FeS+4CO2→Fe3O4+3COS+CO ……(14) 2H2S+SO2→3/xSx+2H2O ……(15) (但し、x=2〜8) COS+H2O→H2S+CO2 ……(16) 上記単体イオウ(生成イオウ)を液体イオウとして回収
除去後、該循環ガスの一部を吸収工程に導入し、残部を
再生工程に戻す。4FeS + 2SO 2 → 4FeO + 3S 2 …… (9) 6FeS + 4SO 2 → 2Fe 3 O 4 + 5S 2 …… (10) 8FeS + 6SO 2 → 4Fe 2 O 3 + 7S 2 …… (11) FeS + H 2 O → FeO + H 2 S …… (12) 3FeS + 4H 2 O → Fe 3 O 4 + 3H 2 S + H 2 …… (13) 3FeS + 4CO 2 → Fe 3 O 4 + 3COS + CO …… (14) 2H 2 S + SO 2 → 3 / xSx + 2H 2 O …… (15) (however, x = 2-8) COS + H 2 O → H 2 S + CO 2 (16) After recovering and removing the above elemental sulfur as liquid sulfur, a part of the circulating gas is introduced into the absorption process, and the rest is used in the regeneration process. return.
再生工程への循環ガス中には、一部のガス状イオウ並び
に副生H2S,COS,H2及びCO等の可燃ガスが含有されてお
り、これらは高温還元性ガス及び回収イオウの一部を循
環ガス中で燃焼させる時、共に燃焼し、再生工程の補熱
に役立つ。また、回収イオウの一部を燃焼させることに
よつて、再生循環ガス中のSO2ガスを所定濃度に維持す
るのみならず、再生工程の補熱にも役立つ。The circulating gas to the regeneration process contains some gaseous sulfur and combustible gases such as by-products H 2 S, COS, H 2 and CO, which are one of high-temperature reducing gas and recovered sulfur. When the parts are burnt in the circulating gas, they burn together and serve to supplement heat in the regeneration process. In addition, by burning a part of the recovered sulfur, not only is the SO 2 gas in the recycle gas maintained at a predetermined concentration, but it is also useful for supplementing heat in the regeneration process.
従つて、以上の補助作用により、燃焼用高温還元性ガス
及び回収イオウの使用量をかなり低減し得るので、より
効果的なシステムとなる。即ち、高温還元性ガス及び回
収イオウの反応(燃焼)は、再生工程の補熱並びに再生
工程での単体イオウ生成の性能向上に寄与する。Therefore, the amount of the high-temperature reducing gas for combustion and the amount of recovered sulfur used can be considerably reduced by the above-mentioned auxiliary action, resulting in a more effective system. That is, the reaction (combustion) of the high-temperature reducing gas and the recovered sulfur contributes to the supplementary heat of the regeneration process and the performance improvement of the simple sulfur production in the regeneration process.
以下本発明方法の実施態様を添付図面により詳細に説明
する。Hereinafter, embodiments of the method of the present invention will be described in detail with reference to the accompanying drawings.
第1図において、石炭1は、少量の空気又は酸素2で、
ガス化炉3において部分燃焼、ガス化され、H2及びCOを
主成分とするガス化粗ガス(還元性ガス)4が得られ
る。この粗ガス4は集塵装置5でガス中のダストを10mg
/Nm3程度まで充分除去後、脱塵ガス化ガス6となつてラ
イン7及び流路切替バルブ9を介して吸収工程中にある
例えば反応器16に供給される。In FIG. 1, coal 1 is a small amount of air or oxygen 2,
Partial combustion and gasification are performed in the gasification furnace 3 to obtain a gasified crude gas (reducing gas) 4 containing H 2 and CO as main components. This crude gas 4 is 10 mg of dust in the gas in the dust collector 5.
After being sufficiently removed to about / Nm 3 , it is supplied to the dedusting gasified gas 6 through a line 7 and a flow path switching valve 9 to, for example, the reactor 16 in the absorption step.
この脱塵ガス化ガス(以下、ガス化ガス)6は石炭の種
類やガス化条件によつて異なるが、ダスト以外に、数10
〜数1000ppmのH2S,COS,NH3及び極く微量のHF,HCl等を含
み、ガス温度は、ガス化炉3出口のスチームヒータなど
で熱回収され、250〜500℃、圧力はガス化炉3の形式に
より異なるが、常圧〜25kg/cm2Gである。This dedusting gasification gas (hereinafter, gasification gas) 6 differs depending on the type of coal and gasification conditions, but in addition to dust,
~ Contains several 1000ppm of H 2 S, COS, NH 3 and a very small amount of HF, HCl, etc., the gas temperature is recovered by the steam heater at the outlet of the gasification furnace 3, 250 ~ 500 ℃, the pressure is gas The pressure is from normal pressure to 25 kg / cm 2 G, though it depends on the type of the chemical conversion furnace 3.
第1図では、吸収剤19が充填された同一構造の反応器1
6,17,18を(1)〜(7)式による吸収工程、(9)〜
(14)式による再生工程と順次切替えていく固定床式の
実施態様を示しているが、本発明は固定床式に限定され
るものではなく、還元性ガス中のH2S,COS等のイオウ化
合物を吸収剤で吸収除去後、(9)〜(14)式による再
生を繰り返すプロセスなら、流動床式、移動床式を問わ
ず適用できる。また、ガス流路切替の固定床式三塔切替
以外の多塔固定床式にも適用できるのはいうまでもな
い。In FIG. 1, a reactor 1 of identical structure filled with absorbent 19 is shown.
6,17,18 absorption process according to formulas (1) to (7), (9) to
Although a fixed bed type embodiment in which the regeneration step according to the equation (14) and the regeneration step are sequentially switched is shown, the present invention is not limited to the fixed bed type, and H 2 S, COS, etc. in a reducing gas can be used. A process of repeating regeneration by the formulas (9) to (14) after absorbing and removing the sulfur compound with an absorbent can be applied to both fluidized bed type and moving bed type. Further, needless to say, the present invention can be applied to a multi-column fixed bed type other than the fixed bed type three tower switching for gas flow path switching.
更に、吸収剤の組成、形状に何ら限定されるものではな
い。Furthermore, the composition and shape of the absorbent are not limited in any way.
ここでは、反応器16で吸収工程を、反応器17で予備再生
工程を、そして反応器18で再生工程を行つている状態で
説明する。Here, a state where the absorption process is performed in the reactor 16, the preliminary regeneration process is performed in the reactor 17, and the regeneration process is performed in the reactor 18 will be described.
ガス化ガス6は、一部再生用にライン8を介して使用
し、残り全量をライン7及び流路切替バルブ9を介し
て、反応器16に導入することで、そのイオウ化合物は通
常、反応温度300〜500℃で、(1)〜(7)式によつ
て、吸収剤19に吸収除去され、流路切替バルブ43を介し
て、精製ガス50として後流のガスタービン(図示省略)
に供給される。The gasification gas 6 is used for partial regeneration through the line 8, and the remaining whole amount is introduced into the reactor 16 through the line 7 and the flow path switching valve 9, so that the sulfur compound is usually reacted. At a temperature of 300 to 500 ° C., the gas is absorbed and removed by the absorbent 19 according to the equations (1) to (7), and the gas turbine is used as a purified gas 50 via the flow path switching valve 43 (not shown).
Is supplied to.
予備再生工程は、吸収工程終了後の系内のガス温度を再
生反応に必要な温度まで上げるためのものであり、基本
的には再生工程と同じ循環系となつている。The pre-regeneration step is to raise the temperature of the gas in the system after the absorption step to the temperature required for the regeneration reaction, and is basically the same circulation system as the regeneration step.
即ち、予備再生工程においては、反応器17に再生循環ガ
スの一部を導入し、そのガス中にガス化ガス6の一部を
ライン8を経て熱交換器12で加熱後のガス化ガス65及び
空気又は酸素含有ガス30を熱交換器31で加熱後のガス66
の必要量を、夫々流路切替バルブ14,33を介して供給
し、該再生循環ガス中でガス化ガス65を燃焼させ該反応
器17の予熱を行う。該反応器17の出口ガス36は、熱交換
器39で冷却後、流路切替バルブ44を介して再生工程出口
循環ガス51と合流して、イオウ凝縮器53に導入される。
予備再生工程及び再生工程を出た循環ガス51から、イオ
ウ凝縮器53及びイオウ分離器57で単体イオウを回収除去
した後の処理ガスは、ブロア58で昇圧し、一部を吸収工
程へ供給し、残りを流路切替バルブ48を介して熱交換器
40で加熱後、ライン64を経て反応器18及び反応器17に夫
々導入して循環させる。That is, in the preliminary regeneration step, a part of the regenerated circulation gas is introduced into the reactor 17, and a part of the gasification gas 6 is heated in the heat exchanger 12 via the line 8 into the gas. And the gas after heating the air- or oxygen-containing gas 30 in the heat exchanger 31 66
Are supplied through the flow path switching valves 14 and 33, respectively, and the gasification gas 65 is burned in the regenerated circulation gas to preheat the reactor 17. The outlet gas 36 of the reactor 17 is cooled by the heat exchanger 39, merges with the regeneration process outlet circulation gas 51 through the flow path switching valve 44, and is introduced into the sulfur condenser 53.
From the circulating gas 51 that has exited the preliminary regeneration step and the regeneration step, the treated gas after the sulfur condenser 53 and the sulfur separator 57 collects and removes the elemental sulfur, and the blower 58 boosts the pressure, and a part of it is supplied to the absorption step. , The rest through the flow path switching valve 48, heat exchanger
After heating at 40, they are introduced into the reactor 18 and the reactor 17 via line 64 and circulated.
なお、反応器17が所定温度まで昇温された時、流路切替
バルブ45を開にして、再生循環ガス61の一部を導入す
る。When the reactor 17 is heated to a predetermined temperature, the flow path switching valve 45 is opened and a part of the recycle gas 61 is introduced.
このような方法をとることにより、反応器18が再生工程
を終了する前に、該反応器17の内部温度を再生必要温度
迄上げることができる。該反応器17が必要温度に到達し
たら、再生を一部行いながら再生工程待機状態にしてお
く。By adopting such a method, the internal temperature of the reactor 17 can be raised to the temperature required for regeneration before the reactor 18 finishes the regeneration process. When the reactor 17 reaches the required temperature, it is put in a standby state for the regeneration process while partially performing regeneration.
なお、この予備再生工程を設けることによつて、固定床
方式における吸収→再生及び再生→吸収の工程切替時の
ガス流れの断続性が緩衝され、その連続性が維持できる
ので、吸収剤の吸収性能及び再生性能が安定化される。In addition, by providing this preliminary regeneration step, the intermittentness of the gas flow at the time of switching the steps of absorption → regeneration and regeneration → absorption in the fixed bed system is buffered and its continuity can be maintained, so that absorption of the absorbent can be maintained. Performance and reproduction performance are stabilized.
再生工程においては、ガス化ガス65、回収イオウ26及び
空気又は酸素含有ガス66を、夫々流路切替バルブ15,29
及び34を介して、再生循環ガス64ラインに供給し、該ガ
ス化ガス65、回収イオウ26並びに該循環ガス64中の副生
H2S,COS,H2,CO及びガス状イオウ(S2)等を反応器18入
口で反応(燃焼)させることによつて、所定の再生温度
及び該循環ガス64中のSO2濃度を維持し、該反応器18で
吸収剤19が(9)〜(14)式によつて再生される。In the regeneration process, the gasification gas 65, the recovered sulfur 26 and the air or oxygen-containing gas 66 are supplied to the flow path switching valves 15 and 29, respectively.
And a recycle gas 64 line, and the gasification gas 65, recovered sulfur 26, and by-products in the circulation gas 64 are supplied.
By reacting (combusting) H 2 S, COS, H 2 , CO and gaseous sulfur (S 2 ) at the inlet of the reactor 18, the predetermined regeneration temperature and the SO 2 concentration in the circulating gas 64 can be adjusted. Maintaining and regenerating the absorbent 19 in the reactor 18 according to equations (9)-(14).
上記の回収イオウ26としては、上記の循環ガス51から抜
出したものや、後述のイオウ分離器57からライン83に抜
出される液体イオウをガス化したものが使用される。As the recovered sulfur 26, the one extracted from the circulating gas 51 or the one obtained by gasifying the liquid sulfur extracted from the later-described sulfur separator 57 to the line 83 is used.
上記可燃分がガス温度が低いために万一燃焼しにくい場
合には、例えば吸収剤19のような助燃剤又は触媒等を使
用し、十分な燃焼を行なわせることができる。If the combustible component is difficult to burn due to the low gas temperature, a combustor such as the absorbent 19 or a catalyst may be used to perform sufficient combustion.
また、再生は、圧力が常圧〜40kg/cm2G、反応温度が600
〜1000℃、SV値(ガス流量Nm3/h/吸収剤容量m3)が100
〜20001/h、及び循環ガス中SO2濃度が0.1〜5vol%で、
(9)〜(14)式によつて行われ、吸収剤19が再生され
る。上記条件において、経済性の観点から、圧力15〜30
kg/cm2、反応温度700〜850℃、SV値200〜8001/h及び循
環ガス中SO2濃度1〜4vol%にする方が好ましい。In addition, the regeneration is carried out at a pressure of normal pressure to 40 kg / cm 2 G and a reaction temperature of 600.
~ 1000 ℃, SV value (gas flow Nm 3 / h / absorbent capacity m 3 ) is 100
~20001 / h, and the circulating gas SO 2 concentration is 0.1~5vol%,
The absorbent 19 is regenerated by using the equations (9) to (14). Under the above conditions, from the viewpoint of economy, the pressure is 15-30
It is preferable to set kg / cm 2 , reaction temperature of 700 to 850 ° C., SV value of 200 to 8001 / h, and SO 2 concentration of 1 to 4 vol% in the circulating gas.
また、再生循環ガス量(反応器18出口基準)は吸収工程
への受入ガス化ガス6の量の5〜60%、再生工程への回
収イオウ26の注入量は全回収イオウ量の0〜30%にす
る。予備再生工程及び再生工程へのガス化ガス65の供給
量については、以下の関係式により算出される。In addition, the amount of recycle gas (based on the outlet of the reactor 18) is 5 to 60% of the amount of the gasification gas 6 received in the absorption process, and the amount of the recovered sulfur 26 injected into the regeneration process is 0 to 30% of the total amount of the recovered sulfur. %. The supply amount of the gasification gas 65 to the preliminary regeneration process and the regeneration process is calculated by the following relational expression.
VRe/(VCg×CS)=0.5〜10 ……(17) ここで、VRe:予備再生工程及び再生工程への供給ガス化
ガス量(Nm3/h) VCg:吸収工程への受入ガス化ガス量(Nm3/h) CS :受入ガス化ガス中の(H2S+COS)のmol
分率(−) 上記ガス化ガス65の供給量は、(17)式で求めた数値の
範囲外であると効果的でなくなる。V Re / (V Cg × C S ) = 0.5〜10 ・ ・ ・ (17) Where, V Re is the amount of gasification gas supplied to the preliminary regeneration process and regeneration process (Nm 3 / h) V Cg : To the absorption process Received gasification gas amount (Nm 3 / h) C S : mol of (H 2 S + COS) in the received gasification gas
Fraction (-) If the supply amount of the gasification gas 65 is out of the range of the numerical value obtained by the equation (17), it becomes ineffective.
なお、本発明では、吸収工程終了後の吸収剤19、即ち硫
化された吸収剤19(主としてFeSになつている)は、予
備再生及び再生時に殆んど四三酸化鉄(Fe3O4)になる
ので、例えば先に提案した特願昭62−56776号明細書に
記載の再生済み吸収剤の還元工程(Fe2O3をガス化ガス
でFe3O4に還元する)は不要であり、再生後、該反応器
内の冷却及びSO2ガス等のパージ後、すぐに吸収工程に
切替えることができる。Incidentally, in the present invention, the absorbent 19 after the absorption step, that is, the sulfurized absorbent 19 (mainly FeS) is almost iron trioxide (Fe 3 O 4 ) during pre-regeneration and regeneration. Therefore, for example, the step of reducing the regenerated absorbent (reducing Fe 2 O 3 to Fe 3 O 4 with a gasification gas) described in Japanese Patent Application No. 62-56776 previously proposed is unnecessary. After the regeneration, the absorption step can be immediately switched to after cooling the inside of the reactor and purging SO 2 gas and the like.
さて、再生工程中の反応器18出口の循環ガス37は、熱交
換器40にて冷却後、単体イオウ(生成イオウ)が回収さ
れる。先ず循環ガス51は、イオウ凝縮器53で130〜250℃
に冷却され、循環ガス中の単体イオウは液体イオウ81と
して回収され、イオウ分離器57に貯蔵されて、液体イオ
ウ83ラインを通して抜き出される。By the way, the circulating gas 37 at the outlet of the reactor 18 in the regeneration step is cooled by the heat exchanger 40, and then elemental sulfur (produced sulfur) is recovered. First, the circulating gas 51 is stored in the sulfur condenser 53 at 130 to 250 ° C.
The sulfur in the circulating gas is recovered as liquid sulfur 81, stored in the sulfur separator 57, and extracted through the liquid sulfur 83 line.
単体イオウが回収除去された循環ガスは、ブロア58によ
つて昇圧され、そのガスのうち再生工程において注入さ
れたガス化ガス65、回収イオウ26及び空気又は酸素含有
ガス66に見合う量が、流路切替バルブ20を介して吸収工
程中にある反応器16の入口に供給される。The circulating gas from which the elemental sulfur has been recovered and removed is pressurized by the blower 58, and the amount of the gas, which is commensurate with the gasification gas 65, the recovered sulfur 26 and the air- or oxygen-containing gas 66 injected in the regeneration process, flows. It is fed via the path switching valve 20 to the inlet of the reactor 16 during the absorption process.
即ち、第1図で分るとおり、再生工程においては、取扱
うガスが循環系になつているので、系外から再生工程へ
ガス化ガス65、回収イオウ26及び空気又は酸素含有ガス
66を注入すると、その中でガス化ガス65、回収イオウ26
並びに循環ガス59中の副生H2S,COS,H2,CO,及びガス状イ
オウ(S2)等の燃焼反応に消費されたO2ガス以外のN2,H
2O,CO2等は、この循環系に蓄積されるので、循環系のガ
ス量バランスをとるために、ガス化ガス65、回収イオウ
26及び空気又は酸素含有ガス66の注入に見合う分だけ、
この循環系外(吸収工程)に抜き出してやる必要があ
る。That is, as can be seen in FIG. 1, in the regeneration process, the gas to be handled is in the circulation system, so the gasification gas 65, the recovered sulfur 26 and the air or oxygen-containing gas from the outside of the system to the regeneration process.
When 66 is injected, gasified gas 65, recovered sulfur 26
And N 2 and H other than O 2 gas consumed in the combustion reaction of by-products H 2 S, COS, H 2 and CO in the circulating gas 59 and gaseous sulfur (S 2 ).
2 O, CO 2, etc. are accumulated in this circulation system, so in order to balance the gas amount in the circulation system, gasification gas 65, recovered sulfur
26 and the amount of air or oxygen-containing gas 66 injected,
It is necessary to extract it outside the circulation system (absorption process).
また、残りの循環ガス61(イオウ凝縮器53で単体イオウ
を除去後の循環ガス59から一部吸収工程へ供給したガス
60を差引いた残りの循環ガス)は、流路切替バルブ48を
介して熱交換器40にて加熱後、反応器18及び反応器17に
夫々供給され、循環される。In addition, the remaining circulating gas 61 (the gas that was supplied to the partial absorption process from the circulating gas 59 after the simple sulfur was removed by the sulfur condenser 53)
The remaining circulating gas from which 60 is subtracted) is heated in the heat exchanger 40 via the flow path switching valve 48, and then supplied to the reactor 18 and the reactor 17 and circulated.
ここで、吸収工程へ供給されるガス60は、ガス化ガス7
と混合されるので、そのガス中の残余SO2及びガス状イ
オウ等は、吸収工程中の反応器16内の前部で、吸収剤19
の下において、以下の(18)〜(20)式によつてH2Sガ
スに転化される。Here, the gas 60 supplied to the absorption step is the gasification gas 7
As a result, the residual SO 2 and gaseous sulfur, etc. in the gas are mixed with the absorbent 19 at the front of the reactor 16 during the absorption process.
Is converted to H 2 S gas by the following equations (18) to (20).
SO2+3H2→H2S+2H2O ……(18) SO2+3CO+H2O→H2S+3CO2 ……(19) 1/xSx+H2→H2S ……(20) (但し、x=2〜8) この生成H2Sと該ガス中の残余H2S,COS等は、SV値500〜4
0001/hの下で、反応器16を通過する間に、ガス化ガス7
中のイオウ化合物と共に吸収除去される。SO 2 + 3H 2 → H 2 S + 2H 2 O (18) SO 2 + 3CO + H 2 O → H 2 S + 3CO 2 ... (19) 1 / xSx + H 2 → H 2 S ... (20) (However, x = 2 8) The generated H 2 S and the residual H 2 S, COS, etc. in the gas have an SV value of 500 to 4
While passing through the reactor 16 under 0001 / h, the gasification gas 7
It is absorbed and removed together with the sulfur compounds therein.
反応器18の再生工程が終了すると、反応器17は予備再生
→再生工程に切替えられ、反応器18は、その後器内の冷
却が行われる。When the regeneration step of the reactor 18 is completed, the reactor 17 is switched from the pre-regeneration step to the regeneration step, and the inside of the reactor 18 is then cooled.
即ち、流路切替バルブ15,25,29及び34を閉にして、130
〜250℃の再生循環ガス61の一部を流路切替バルブ48を
介して該反応器18に導入することによつて、該反応器18
内をガス化ガス7の温度に合わせるべく300〜500℃に冷
却する。その冷却後、該反応器18前後の流路切替バルブ
11,69を開にし、且つ流路切替バルブ47,48を閉にし、ガ
ス化ガス7の一部を該反応器18に導入し、該反応器18内
のガスパージを行う。即ち、再生工程終了直後は、反応
器18内にSO2ガス、ガス状イオウ等が残存しているた
め、該反応器18出口ガス37を循環ガス63ラインに導入し
て予備再生→再生工程に切替えられた反応器17へ送られ
る。That is, the flow path switching valves 15, 25, 29 and 34 are closed to
By introducing a part of the recycle gas 61 at a temperature of ~ 250 ° C into the reactor 18 via the flow path switching valve 48, the reactor 18
The inside is cooled to 300 to 500 ° C. so as to match the temperature of the gasification gas 7. After the cooling, the flow path switching valve before and after the reactor 18
11, 69 are opened and the flow path switching valves 47, 48 are closed, a part of the gasification gas 7 is introduced into the reactor 18, and the gas in the reactor 18 is purged. That is, immediately after the completion of the regeneration step, SO 2 gas, gaseous sulfur, etc. remain in the reactor 18, so the reactor 18 outlet gas 37 is introduced into the circulation gas 63 line to perform the preliminary regeneration → regeneration step. It is sent to the switched reactor 17.
この反応器18内のSO2ガス、ガス状イオウ等がパージさ
れた後、流路切替バルブ22,49を開及び流路切替バルブ6
9を閉にして、本来の吸収工程を開始する。なお、反応
器18及び反応器17の工程切替については、その工程切替
時のガス流れの連続性を持たせるために、夫々、再生→
吸収及び予備再生→再生の工程切替が同時になされる。
その後、反応器16が吸収→予備再生工程に切替えられ
る。After the SO 2 gas, gaseous sulfur, etc. in the reactor 18 have been purged, the flow path switching valves 22 and 49 are opened and the flow path switching valve 6
Close 9 and start the actual absorption process. Regarding the process switching of the reactor 18 and the reactor 17, in order to maintain continuity of the gas flow at the time of the process switching, regeneration is performed →
Absorption and pre-regeneration → regeneration process switching is done at the same time.
Then, the reactor 16 is switched to the absorption → preliminary regeneration process.
また、再生工程においては、吸収剤19の空気又は酸素含
有ガス66による通常の直接酸化の再生は行わず、(9)
〜(14)式の反応による吸収剤19の再生を行うため、吸
収剤19の再生用空気又は酸素含有ガス66の流量は大巾に
低減できる。通常の直接酸化で吸収剤19を再生する場合
と比較して、空気量として2〜5割程度低減できるの
で、高温還元性ガス精製プロセスの電力消費量低減に大
きく寄与する。Further, in the regeneration step, the normal direct oxidation of the absorbent 19 by the air or the oxygen-containing gas 66 is not performed, and (9)
Since the absorbent 19 is regenerated by the reaction of equations (14) to (14), the flow rate of the air for regenerating the absorbent 19 or the oxygen-containing gas 66 can be greatly reduced. Compared with the case where the absorbent 19 is regenerated by normal direct oxidation, the amount of air can be reduced by about 20 to 50%, which greatly contributes to the reduction of power consumption in the high temperature reducing gas purification process.
また、燃焼用ガス化ガス65及び回収イオウ26等の注入量
は理論燃焼酸素(O2)量よりやゝ多目に供給すること、
及び吸収剤19の直接酸化による再生を行わないことによ
り、再生工程内でのSO3生成を抑制し得るので、吸収剤1
9の活性劣化の原因となるFeSO4,Fe2(SO4)3等の硫酸
塩の副生を防止できる。Also, the injection amount of the combustion gasification gas 65 and the recovered sulfur 26, etc. should be supplied slightly larger than the theoretical combustion oxygen (O 2 ) amount,
Also, since the generation of SO 3 in the regeneration process can be suppressed by not regenerating the absorbent 19 by direct oxidation, the absorbent 1
It is possible to prevent by-production of sulfates such as FeSO 4 , Fe 2 (SO 4 ) 3 and the like, which cause activity deterioration of 9.
更に、再生工程中の反応器内でのH2SとCOSの生成は、循
環ガス中のH2O及びCO2濃度及び温度等に左右されるが、
経済性の観点からの再生条件下(圧力:15〜30kg/cm2G、
温度:700〜850℃、SV値:200〜8001/h)で、該反応器出
口循環ガス中の濃度として100〜5000ppm程度になる。Furthermore, the production of H 2 S and COS in the reactor during the regeneration process depends on the concentrations of H 2 O and CO 2 in the circulating gas, the temperature, etc.
Regeneration conditions from the economical point of view (pressure: 15-30 kg / cm 2 G,
At a temperature of 700 to 850 ° C. and an SV value of 200 to 8001 / h), the concentration in the circulating gas at the outlet of the reactor becomes about 100 to 5000 ppm.
なお、経時的に、或は運転操作ミス等の何らかの原因
で、吸収剤19の再生が不十分になり吸収性能が低下した
ような場合は、再生温度を750℃以上に保持し、且つ従
来法のO2ガスによる吸収剤の直接酸化〔吸収剤中のFe分
を完全酸化(Fe2O3)状態にすること〕によつて再生を
行わせ、該吸収剤の吸収、再生性能の回復を期待するこ
とができる。この場合は、特願昭62−56776号明細書)
に記載のように1塔で再生及び還元工程を行わせ、吸収
工程に移行させるようにする。In addition, when the regeneration of the absorbent 19 is insufficient and the absorption performance is deteriorated due to some reason such as a lapse of time or an operation error, the regeneration temperature is kept at 750 ° C. or higher and the conventional method is used. Regeneration is carried out by direct oxidation of the absorbent by O 2 gas [making the Fe content in the absorbent completely oxidized (Fe 2 O 3 ) state] to recover the absorption and regeneration performance of the absorbent. Can be expected. In this case, the specification of Japanese Patent Application No. 62-56776)
The regeneration and reduction steps are carried out in one column as described in 1, and the absorption step is performed.
本発明方法における再生の計算例を以下に記述する。A calculation example of reproduction in the method of the present invention will be described below.
計算条件: (1)ガス化ガス6の条件 ガス化ガス流量=800,000Nm3/h ガス化ガス組成(vol%) ガス化ガス圧力=20kg/cm2G ガス化ガス温度=400℃ (2)吸収工程出口ガス中H2S濃度=100ppm以下 計算例 再生圧力=20kg/cm2G 再生循環ガス64温度(熱交換器40出口)=650℃ 再生用反応器18出口ガス温度=750℃ 再生循環ガス中SO2濃度=3vol% として、再生循環ガス64量、再生に必要なガス化ガス8
量、再生用空気30量及び再生循環ガスからの吸収用反応
器16への抜出しガス60量等の主要事項についての計算結
果は以下のとおりである。Calculation conditions: (1) Gasification gas 6 conditions Gasification gas flow rate = 800,000 Nm 3 / h Gasification gas composition (vol%) Gasification gas pressure = 20kg / cm 2 G Gasification gas temperature = 400 ° C (2) Absorption process outlet gas H 2 S concentration = 100ppm or less Calculation example Regeneration pressure = 20kg / cm 2 G Regeneration circulation gas 64 Temperature (heat exchange Reactor 18 outlet gas temperature = 750 ° C SO 2 concentration = 3vol% in the recycle gas, recycle gas 64, gasification gas required for regeneration 8
The calculation results for the main items such as the amount, the amount of regeneration air 30 and the amount of regeneration gas from the regeneration circulation gas 60 to the absorption reactor 16 are as follows.
<計算結果> 1) 再生循環ガス量=約185,000Nm3/h(再生用反応器
出口では約200,000Nm3/h) 2) ガス化ガス量=約7000Nm3/h 3) 再生用空気量=約9400Nm3/h 4) 吸収用反応器への抜出しガス量=約14800Nm3/h 以上から、ガス化ガス使用量は受入ガス化ガス6に対し
約0.9%と極めて少なく、再生用空気量は従来の再生法
(O2による吸収剤の直接酸化、再生用空気量=約15000N
m3/h)より35%以上少ないことが分る。<Calculation Results> 1) regeneration recycle gas amount = In about 185,000Nm 3 / h (regeneration reactor outlet of about 200,000 3 / h) 2) gasification gas amount = about 7000Nm 3 / h 3) regeneration air quantity = About 9400 Nm 3 / h 4) The amount of gas discharged to the absorption reactor = about 14800 Nm 3 / h or more, so the amount of gasification gas used is extremely small, about 0.9% of the amount of gasification gas 6 received, and the amount of regeneration air is Conventional regeneration method (direct oxidation of absorbent with O 2 , amount of regeneration air = about 15000N
It turns out that it is more than 35% less than m 3 / h).
なお、第1図において、説明されていない流路切替バル
ブ10,13,21,23,24,27,28,32,41,42,46,67,68は、反応器
16が吸収工程を、反応器17が予備再生工程を、そして反
応器18が再生工程を実行している時は、通常、閉の状態
になつている。また、ガス化ガス8ライン及び空気又は
酸素含有ガス30ラインの熱交換器12,31の高温ガス源71,
72、並びにイオウ凝縮器53の冷却水91は、熱交換条件を
満足するものなら何ら制限されない。In addition, in FIG. 1, the flow path switching valves 10, 13, 21, 23, 24, 27, 28, 32, 41, 42, 46, 67, 68 which are not described are reactors.
It is normally closed when 16 is performing the absorption step, reactor 17 is performing the pre-regeneration step, and reactor 18 is performing the regeneration step. Also, the high temperature gas source 71, of the heat exchangers 12, 31 of 8 lines of gasification gas and 30 lines of air or oxygen-containing gas
72 and the cooling water 91 of the sulfur condenser 53 are not limited as long as they satisfy the heat exchange conditions.
本発明の高温還元性ガスの精製方法は、次のような効果
を有する。The high-temperature reducing gas purification method of the present invention has the following effects.
(1) ガス化炉の実用的なあらゆる運転負荷範囲に対
応できる。(1) It can handle all practical operating load ranges of gasifiers.
(2) 再生工程において、再生用反応器に循環ガスを
導入する前に、該循環ガス中にガス化ガス、回収イオウ
の一部を供給し、それらを該循環ガス中の副生H2S,COS,
H2,CO及びガス状イオウ等と共に空気又は酸素含有ガス
で以て燃焼し、必要再生温度及びSO2濃度を確保し、且
つ該吸収剤の酸素(O2)による直接酸化を行わせない方
法で該吸収剤を再生する、ことによつて、再生工程で使
用する再生空気量を、通常の再生工程(吸収剤のO2によ
る直接酸化)で該吸収剤を再生する場合と比較して、2
〜5割程度低減し得るので、電力消費の大巾な節減を計
ることができる。(2) In the regeneration step, before introducing the circulation gas into the regeneration reactor, a part of the gasification gas and the recovered sulfur are supplied into the circulation gas, and H 2 S as a by-product in the circulation gas is supplied to them. , COS,
A method of burning with H 2 CO, gaseous sulfur, etc. with air or an oxygen-containing gas to secure the required regeneration temperature and SO 2 concentration, and not directly oxidizing the absorbent with oxygen (O 2 ). In order to regenerate the absorbent by, in comparison with the case of regenerating the absorbent in a normal regeneration step (direct oxidation of the absorbent with O 2 ), Two
Since it can be reduced by about 50%, it is possible to greatly reduce the power consumption.
(3) 従来の再生済み吸収剤の還元工程(Fe2O3をガ
ス化ガスでFe3O4に還元する)及びクラウス反応工程が
不要であり、反応工程が2工程削減できるので、運転操
作が非常に簡素化される。(3) There is no need for the conventional reduction process of regenerated absorbent (reduction of Fe 2 O 3 to Fe 3 O 4 with gasification gas) and Claus reaction process, and the reaction process can be reduced by 2 processes, so operation Is greatly simplified.
(4) 再生循環ガス中において、理論燃焼酸素不足域
でガス化ガス、回収イオウの一部等を燃焼させ、且つ吸
収剤の酸素による直接酸化を行わせない方法によつて、
該吸収剤からのFeSO4,Fe2(SO4)3等の硫酸塩の副生率
を小さく抑えることができるので、該吸収剤の性能劣化
防止に対し、寄与効果がある。(4) By a method of burning a gasification gas, a part of recovered sulfur, etc. in a theoretical combustion oxygen deficient region in a recycle gas and not directly oxidizing the absorbent with oxygen,
Since the by-product rate of sulfates such as FeSO 4 and Fe 2 (SO 4 ) 3 from the absorbent can be suppressed to a small level, it contributes to the prevention of performance deterioration of the absorbent.
第1図は本発明の一実施例を説明するための図である。 FIG. 1 is a diagram for explaining one embodiment of the present invention.
───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.6 識別記号 庁内整理番号 FI 技術表示箇所 C10K 1/34 ─────────────────────────────────────────────────── ─── Continuation of the front page (51) Int.Cl. 6 Identification code Internal reference number FI technical display location C10K 1/34
Claims (1)
化カルボニル等のイオウ化合物を吸収剤で吸収除去する
方法で、再生された吸収剤を用いてイオウ化合物を吸収
除去する工程を連続的に繰り返す高温還元性ガスの精製
方法において、吸収剤を充填した少なくとも三塔の反応
器を使用し、吸収、予備再生及び再生の三工程により構
成し、該再生工程の循環ガス中に前記還元性ガス及び/
又は系内での回収イオウの一部を添加し酸素の存在下で
該還元性ガス及び/又は該回収イオウを反応させて必要
再生温度とSO2濃度を確保することにより、再生工程で
単体イオウを生成させ、再生用反応器出口循環ガス中の
単体イオウを液体イオウとして回収除去後、該循環ガス
の一部を吸収工程に導入し、残部を再生工程に戻すこと
を特徴とする高温還元性ガスの精製方法。1. A method of absorbing and removing a sulfur compound such as hydrogen sulfide and carbonyl sulfide contained in a high-temperature reducing gas by an absorbent, and continuously removing the sulfur compound by using a regenerated absorbent. In the method for refining a high-temperature reducing gas that is repeated as described above, at least three reactors packed with an absorbent are used, and the three steps of absorption, preliminary regeneration and regeneration are used, and the reducing gas is added to the circulating gas in the regeneration step. Gas and /
Alternatively, by adding a part of the sulfur recovered in the system and reacting the reducing gas and / or the recovered sulfur in the presence of oxygen to secure the necessary regeneration temperature and SO 2 concentration, the sulfur in the regeneration step Is produced, and after recovering and removing the elemental sulfur in the circulation gas at the outlet of the regeneration reactor as liquid sulfur, a part of the circulation gas is introduced into the absorption step, and the rest is returned to the regeneration step. Gas purification method.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP62157849A JPH07102299B2 (en) | 1987-06-26 | 1987-06-26 | Refining method for high temperature reducing gas |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP62157849A JPH07102299B2 (en) | 1987-06-26 | 1987-06-26 | Refining method for high temperature reducing gas |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS644215A JPS644215A (en) | 1989-01-09 |
| JPH07102299B2 true JPH07102299B2 (en) | 1995-11-08 |
Family
ID=15658707
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP62157849A Expired - Lifetime JPH07102299B2 (en) | 1987-06-26 | 1987-06-26 | Refining method for high temperature reducing gas |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH07102299B2 (en) |
Families Citing this family (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2865845B2 (en) * | 1990-10-08 | 1999-03-08 | 三菱重工業株式会社 | Purification method of high-temperature reducing gas |
-
1987
- 1987-06-26 JP JP62157849A patent/JPH07102299B2/en not_active Expired - Lifetime
Also Published As
| Publication number | Publication date |
|---|---|
| JPS644215A (en) | 1989-01-09 |
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