JPS5912602B2 - Claus sulfur recovery equipment tail gas processing method - Google Patents
Claus sulfur recovery equipment tail gas processing methodInfo
- Publication number
- JPS5912602B2 JPS5912602B2 JP51031335A JP3133576A JPS5912602B2 JP S5912602 B2 JPS5912602 B2 JP S5912602B2 JP 51031335 A JP51031335 A JP 51031335A JP 3133576 A JP3133576 A JP 3133576A JP S5912602 B2 JPS5912602 B2 JP S5912602B2
- Authority
- JP
- Japan
- Prior art keywords
- sulfur
- catalyst
- gas
- claus
- tail gas
- 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
Links
- NINIDFKCEFEMDL-UHFFFAOYSA-N Sulfur Chemical compound [S] NINIDFKCEFEMDL-UHFFFAOYSA-N 0.000 title claims description 48
- 229910052717 sulfur Inorganic materials 0.000 title claims description 46
- 239000011593 sulfur Substances 0.000 title claims description 46
- 238000011084 recovery Methods 0.000 title claims description 20
- 238000003672 processing method Methods 0.000 title 1
- 239000007789 gas Substances 0.000 claims description 71
- 239000003054 catalyst Substances 0.000 claims description 64
- RAHZWNYVWXNFOC-UHFFFAOYSA-N Sulphur dioxide Chemical compound O=S=O RAHZWNYVWXNFOC-UHFFFAOYSA-N 0.000 claims description 41
- 238000000034 method Methods 0.000 claims description 35
- PXHVJJICTQNCMI-UHFFFAOYSA-N Nickel Chemical compound [Ni] PXHVJJICTQNCMI-UHFFFAOYSA-N 0.000 claims description 17
- 238000003795 desorption Methods 0.000 claims description 16
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 claims description 15
- RWSOTUBLDIXVET-UHFFFAOYSA-N Dihydrogen sulfide Chemical compound S RWSOTUBLDIXVET-UHFFFAOYSA-N 0.000 claims description 13
- 229910000037 hydrogen sulfide Inorganic materials 0.000 claims description 13
- 239000000203 mixture Substances 0.000 claims description 12
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 claims description 10
- 229910052759 nickel Inorganic materials 0.000 claims description 10
- 239000001301 oxygen Substances 0.000 claims description 10
- 229910052760 oxygen Inorganic materials 0.000 claims description 10
- GWEVSGVZZGPLCZ-UHFFFAOYSA-N Titan oxide Chemical compound O=[Ti]=O GWEVSGVZZGPLCZ-UHFFFAOYSA-N 0.000 claims description 8
- 238000001179 sorption measurement Methods 0.000 claims description 8
- OGIDPMRJRNCKJF-UHFFFAOYSA-N titanium oxide Inorganic materials [Ti]=O OGIDPMRJRNCKJF-UHFFFAOYSA-N 0.000 claims description 7
- 229910017052 cobalt Inorganic materials 0.000 claims description 6
- 239000010941 cobalt Substances 0.000 claims description 6
- GUTLYIVDDKVIGB-UHFFFAOYSA-N cobalt atom Chemical compound [Co] GUTLYIVDDKVIGB-UHFFFAOYSA-N 0.000 claims description 6
- 229910052742 iron Inorganic materials 0.000 claims description 6
- QPLDLSVMHZLSFG-UHFFFAOYSA-N Copper oxide Chemical class [Cu]=O QPLDLSVMHZLSFG-UHFFFAOYSA-N 0.000 claims description 4
- 239000011261 inert gas Substances 0.000 claims description 4
- 229910052751 metal Inorganic materials 0.000 claims description 2
- 239000002184 metal Substances 0.000 claims description 2
- 239000004480 active ingredient Substances 0.000 claims 1
- 238000006243 chemical reaction Methods 0.000 description 28
- 238000011069 regeneration method Methods 0.000 description 22
- 230000008929 regeneration Effects 0.000 description 21
- UQSXHKLRYXJYBZ-UHFFFAOYSA-N iron oxide Inorganic materials [Fe]=O UQSXHKLRYXJYBZ-UHFFFAOYSA-N 0.000 description 15
- 150000003464 sulfur compounds Chemical class 0.000 description 11
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 10
- 239000010949 copper Substances 0.000 description 10
- 235000013980 iron oxide Nutrition 0.000 description 8
- PNEYBMLMFCGWSK-UHFFFAOYSA-N aluminium oxide Inorganic materials [O-2].[O-2].[O-2].[Al+3].[Al+3] PNEYBMLMFCGWSK-UHFFFAOYSA-N 0.000 description 7
- BAUYGSIQEAFULO-UHFFFAOYSA-L iron(2+) sulfate (anhydrous) Chemical compound [Fe+2].[O-]S([O-])(=O)=O BAUYGSIQEAFULO-UHFFFAOYSA-L 0.000 description 7
- 229910052802 copper Inorganic materials 0.000 description 6
- 229910000359 iron(II) sulfate Inorganic materials 0.000 description 6
- 239000000243 solution Substances 0.000 description 6
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Chemical compound O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 6
- VHUUQVKOLVNVRT-UHFFFAOYSA-N Ammonium hydroxide Chemical compound [NH4+].[OH-] VHUUQVKOLVNVRT-UHFFFAOYSA-N 0.000 description 5
- 229910011212 Ti—Fe Inorganic materials 0.000 description 5
- 235000011114 ammonium hydroxide Nutrition 0.000 description 5
- 230000000694 effects Effects 0.000 description 5
- 235000003891 ferrous sulphate Nutrition 0.000 description 5
- 239000011790 ferrous sulphate Substances 0.000 description 5
- 239000002994 raw material Substances 0.000 description 5
- 229910001868 water Inorganic materials 0.000 description 5
- RYGMFSIKBFXOCR-UHFFFAOYSA-N Copper Chemical compound [Cu] RYGMFSIKBFXOCR-UHFFFAOYSA-N 0.000 description 4
- 239000007864 aqueous solution Substances 0.000 description 4
- 230000000052 comparative effect Effects 0.000 description 4
- 239000005751 Copper oxide Substances 0.000 description 3
- QGZKDVFQNNGYKY-UHFFFAOYSA-N ammonia Natural products N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 3
- IVMYJDGYRUAWML-UHFFFAOYSA-N cobalt(ii) oxide Chemical class [Co]=O IVMYJDGYRUAWML-UHFFFAOYSA-N 0.000 description 3
- 229910000431 copper oxide Inorganic materials 0.000 description 3
- XLYOFNOQVPJJNP-UHFFFAOYSA-M hydroxide Chemical compound [OH-] XLYOFNOQVPJJNP-UHFFFAOYSA-M 0.000 description 3
- 229910000480 nickel oxide Inorganic materials 0.000 description 3
- GNRSAWUEBMWBQH-UHFFFAOYSA-N oxonickel Chemical compound [Ni]=O GNRSAWUEBMWBQH-UHFFFAOYSA-N 0.000 description 3
- 239000010936 titanium Substances 0.000 description 3
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 2
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 description 2
- BVKZGUZCCUSVTD-UHFFFAOYSA-L Carbonate Chemical compound [O-]C([O-])=O BVKZGUZCCUSVTD-UHFFFAOYSA-L 0.000 description 2
- CDBYLPFSWZWCQE-UHFFFAOYSA-L Sodium Carbonate Chemical compound [Na+].[Na+].[O-]C([O-])=O CDBYLPFSWZWCQE-UHFFFAOYSA-L 0.000 description 2
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 description 2
- 239000002253 acid Substances 0.000 description 2
- 239000003513 alkali Substances 0.000 description 2
- JJWKPURADFRFRB-UHFFFAOYSA-N carbonyl sulfide Chemical compound O=C=S JJWKPURADFRFRB-UHFFFAOYSA-N 0.000 description 2
- 150000001868 cobalt Chemical class 0.000 description 2
- 229910000428 cobalt oxide Inorganic materials 0.000 description 2
- 239000000306 component Substances 0.000 description 2
- 150000001879 copper Chemical class 0.000 description 2
- XTVVROIMIGLXTD-UHFFFAOYSA-N copper(II) nitrate Chemical compound [Cu+2].[O-][N+]([O-])=O.[O-][N+]([O-])=O XTVVROIMIGLXTD-UHFFFAOYSA-N 0.000 description 2
- 238000006477 desulfuration reaction Methods 0.000 description 2
- 230000023556 desulfurization Effects 0.000 description 2
- 239000003546 flue gas Substances 0.000 description 2
- 239000010439 graphite Substances 0.000 description 2
- 229910002804 graphite Inorganic materials 0.000 description 2
- 238000010438 heat treatment Methods 0.000 description 2
- 159000000014 iron salts Chemical class 0.000 description 2
- 238000004519 manufacturing process Methods 0.000 description 2
- 239000011259 mixed solution Substances 0.000 description 2
- 238000000465 moulding Methods 0.000 description 2
- 150000002815 nickel Chemical class 0.000 description 2
- 238000007254 oxidation reaction Methods 0.000 description 2
- 239000000047 product Substances 0.000 description 2
- 239000010453 quartz Substances 0.000 description 2
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N silicon dioxide Inorganic materials O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 description 2
- XJDNKRIXUMDJCW-UHFFFAOYSA-J titanium tetrachloride Chemical compound Cl[Ti](Cl)(Cl)Cl XJDNKRIXUMDJCW-UHFFFAOYSA-J 0.000 description 2
- BNGXYYYYKUGPPF-UHFFFAOYSA-M (3-methylphenyl)methyl-triphenylphosphanium;chloride Chemical compound [Cl-].CC1=CC=CC(C[P+](C=2C=CC=CC=2)(C=2C=CC=CC=2)C=2C=CC=CC=2)=C1 BNGXYYYYKUGPPF-UHFFFAOYSA-M 0.000 description 1
- QIVUCLWGARAQIO-OLIXTKCUSA-N (3s)-n-[(3s,5s,6r)-6-methyl-2-oxo-1-(2,2,2-trifluoroethyl)-5-(2,3,6-trifluorophenyl)piperidin-3-yl]-2-oxospiro[1h-pyrrolo[2,3-b]pyridine-3,6'-5,7-dihydrocyclopenta[b]pyridine]-3'-carboxamide Chemical compound C1([C@H]2[C@H](N(C(=O)[C@@H](NC(=O)C=3C=C4C[C@]5(CC4=NC=3)C3=CC=CN=C3NC5=O)C2)CC(F)(F)F)C)=C(F)C=CC(F)=C1F QIVUCLWGARAQIO-OLIXTKCUSA-N 0.000 description 1
- NLXLAEXVIDQMFP-UHFFFAOYSA-N Ammonium chloride Substances [NH4+].[Cl-] NLXLAEXVIDQMFP-UHFFFAOYSA-N 0.000 description 1
- 229910021503 Cobalt(II) hydroxide Inorganic materials 0.000 description 1
- JJLJMEJHUUYSSY-UHFFFAOYSA-L Copper hydroxide Chemical compound [OH-].[OH-].[Cu+2] JJLJMEJHUUYSSY-UHFFFAOYSA-L 0.000 description 1
- 239000005750 Copper hydroxide Substances 0.000 description 1
- MYMOFIZGZYHOMD-UHFFFAOYSA-N Dioxygen Chemical compound O=O MYMOFIZGZYHOMD-UHFFFAOYSA-N 0.000 description 1
- UFHFLCQGNIYNRP-UHFFFAOYSA-N Hydrogen Chemical compound [H][H] UFHFLCQGNIYNRP-UHFFFAOYSA-N 0.000 description 1
- 229910000831 Steel Inorganic materials 0.000 description 1
- RTAQQCXQSZGOHL-UHFFFAOYSA-N Titanium Chemical compound [Ti] RTAQQCXQSZGOHL-UHFFFAOYSA-N 0.000 description 1
- XSQUKJJJFZCRTK-UHFFFAOYSA-N Urea Chemical compound NC(N)=O XSQUKJJJFZCRTK-UHFFFAOYSA-N 0.000 description 1
- 238000010521 absorption reaction Methods 0.000 description 1
- 150000007513 acids Chemical class 0.000 description 1
- 238000003915 air pollution Methods 0.000 description 1
- 238000001354 calcination Methods 0.000 description 1
- 239000004202 carbamide Substances 0.000 description 1
- QGJOPFRUJISHPQ-NJFSPNSNSA-N carbon disulfide-14c Chemical compound S=[14C]=S QGJOPFRUJISHPQ-NJFSPNSNSA-N 0.000 description 1
- 230000003197 catalytic effect Effects 0.000 description 1
- UFMZWBIQTDUYBN-UHFFFAOYSA-N cobalt dinitrate Chemical compound [Co+2].[O-][N+]([O-])=O.[O-][N+]([O-])=O UFMZWBIQTDUYBN-UHFFFAOYSA-N 0.000 description 1
- 229910001981 cobalt nitrate Inorganic materials 0.000 description 1
- ASKVAEGIVYSGNY-UHFFFAOYSA-L cobalt(ii) hydroxide Chemical compound [OH-].[OH-].[Co+2] ASKVAEGIVYSGNY-UHFFFAOYSA-L 0.000 description 1
- 238000001816 cooling Methods 0.000 description 1
- 229910001956 copper hydroxide Inorganic materials 0.000 description 1
- 238000010908 decantation Methods 0.000 description 1
- 238000013461 design Methods 0.000 description 1
- 230000006866 deterioration Effects 0.000 description 1
- 229910001882 dioxygen Inorganic materials 0.000 description 1
- 239000012153 distilled water Substances 0.000 description 1
- 238000002474 experimental method Methods 0.000 description 1
- 238000001125 extrusion Methods 0.000 description 1
- VEPSWGHMGZQCIN-UHFFFAOYSA-H ferric oxalate Chemical compound [Fe+3].[Fe+3].[O-]C(=O)C([O-])=O.[O-]C(=O)C([O-])=O.[O-]C(=O)C([O-])=O VEPSWGHMGZQCIN-UHFFFAOYSA-H 0.000 description 1
- 238000005469 granulation Methods 0.000 description 1
- 230000003179 granulation Effects 0.000 description 1
- 239000010440 gypsum Substances 0.000 description 1
- 229910052602 gypsum Inorganic materials 0.000 description 1
- 239000001257 hydrogen Substances 0.000 description 1
- 229910052739 hydrogen Inorganic materials 0.000 description 1
- FBAFATDZDUQKNH-UHFFFAOYSA-M iron chloride Chemical compound [Cl-].[Fe] FBAFATDZDUQKNH-UHFFFAOYSA-M 0.000 description 1
- 229910000358 iron sulfate Inorganic materials 0.000 description 1
- MVFCKEFYUDZOCX-UHFFFAOYSA-N iron(2+);dinitrate Chemical compound [Fe+2].[O-][N+]([O-])=O.[O-][N+]([O-])=O MVFCKEFYUDZOCX-UHFFFAOYSA-N 0.000 description 1
- VBMVTYDPPZVILR-UHFFFAOYSA-N iron(2+);oxygen(2-) Chemical class [O-2].[Fe+2] VBMVTYDPPZVILR-UHFFFAOYSA-N 0.000 description 1
- PVFSDGKDKFSOTB-UHFFFAOYSA-K iron(3+);triacetate Chemical compound [Fe+3].CC([O-])=O.CC([O-])=O.CC([O-])=O PVFSDGKDKFSOTB-UHFFFAOYSA-K 0.000 description 1
- 230000004048 modification Effects 0.000 description 1
- 238000012986 modification Methods 0.000 description 1
- AYOOGWWGECJQPI-NSHDSACASA-N n-[(1s)-1-(5-fluoropyrimidin-2-yl)ethyl]-3-(3-propan-2-yloxy-1h-pyrazol-5-yl)imidazo[4,5-b]pyridin-5-amine Chemical compound N1C(OC(C)C)=CC(N2C3=NC(N[C@@H](C)C=4N=CC(F)=CN=4)=CC=C3N=C2)=N1 AYOOGWWGECJQPI-NSHDSACASA-N 0.000 description 1
- BFDHFSHZJLFAMC-UHFFFAOYSA-L nickel(ii) hydroxide Chemical compound [OH-].[OH-].[Ni+2] BFDHFSHZJLFAMC-UHFFFAOYSA-L 0.000 description 1
- KBJMLQFLOWQJNF-UHFFFAOYSA-N nickel(ii) nitrate Chemical compound [Ni+2].[O-][N+]([O-])=O.[O-][N+]([O-])=O KBJMLQFLOWQJNF-UHFFFAOYSA-N 0.000 description 1
- 229910052757 nitrogen Inorganic materials 0.000 description 1
- XULSCZPZVQIMFM-IPZQJPLYSA-N odevixibat Chemical compound C12=CC(SC)=C(OCC(=O)N[C@@H](C(=O)N[C@@H](CC)C(O)=O)C=3C=CC(O)=CC=3)C=C2S(=O)(=O)NC(CCCC)(CCCC)CN1C1=CC=CC=C1 XULSCZPZVQIMFM-IPZQJPLYSA-N 0.000 description 1
- 230000003647 oxidation Effects 0.000 description 1
- 230000001590 oxidative effect Effects 0.000 description 1
- SOQBVABWOPYFQZ-UHFFFAOYSA-N oxygen(2-);titanium(4+) Chemical class [O-2].[O-2].[Ti+4] SOQBVABWOPYFQZ-UHFFFAOYSA-N 0.000 description 1
- DCKVFVYPWDKYDN-UHFFFAOYSA-L oxygen(2-);titanium(4+);sulfate Chemical compound [O-2].[Ti+4].[O-]S([O-])(=O)=O DCKVFVYPWDKYDN-UHFFFAOYSA-L 0.000 description 1
- 238000011056 performance test Methods 0.000 description 1
- 239000000843 powder Substances 0.000 description 1
- 239000002244 precipitate Substances 0.000 description 1
- 238000002360 preparation method Methods 0.000 description 1
- 238000012545 processing Methods 0.000 description 1
- 239000012495 reaction gas Substances 0.000 description 1
- 230000001172 regenerating effect Effects 0.000 description 1
- 239000002002 slurry Substances 0.000 description 1
- 235000017550 sodium carbonate Nutrition 0.000 description 1
- 229910000029 sodium carbonate Inorganic materials 0.000 description 1
- 239000010959 steel Substances 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- 238000012360 testing method Methods 0.000 description 1
- 238000005979 thermal decomposition reaction Methods 0.000 description 1
- LLZRNZOLAXHGLL-UHFFFAOYSA-J titanic acid Chemical compound O[Ti](O)(O)O LLZRNZOLAXHGLL-UHFFFAOYSA-J 0.000 description 1
- 229910052719 titanium Inorganic materials 0.000 description 1
- 229910000349 titanium oxysulfate Inorganic materials 0.000 description 1
- 229910000348 titanium sulfate Inorganic materials 0.000 description 1
- 238000012546 transfer Methods 0.000 description 1
Classifications
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P20/00—Technologies relating to chemical industry
- Y02P20/50—Improvements relating to the production of bulk chemicals
- Y02P20/584—Recycling of catalysts
Landscapes
- Exhaust Gas Treatment By Means Of Catalyst (AREA)
- Solid-Sorbent Or Filter-Aiding Compositions (AREA)
- Catalysts (AREA)
Description
【発明の詳細な説明】
本発明は、クラウス硫黄回収装置テイルガス中に含有さ
れる硫黄化合物の減少方法に関する。DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for reducing sulfur compounds contained in Claus sulfur recovery apparatus tail gas.
さらに詳しく述べれば、クラウス硫黄回収装置テイルガ
ス中の硫化水素と二酸化硫黄を反応させて硫黄を生成す
るための触媒として、活性の第1成分として酸化チタン
、第2成分として鉄、コバルト、ニッケルおよび銅の酸
化物のうち少くとも1種類以上を加えたものを用いるこ
とを特徴とするクラウス硫黄回収装置テイルガスの処理
方法に関する。More specifically, as a catalyst for producing sulfur by reacting hydrogen sulfide and sulfur dioxide in the Claus sulfur recovery equipment tail gas, titanium oxide is used as the first active component, and iron, cobalt, nickel, and copper are used as the second active components. The present invention relates to a method for treating tail gas of a Claus sulfur recovery apparatus, characterized in that the present invention uses at least one type of oxides added thereto.
現在、高濃度の硫化水素を含有するガスの処理には、ク
ラウス硫黄回収装置が使用されている。Currently, Claus sulfur recovery equipment is used to treat gases containing high concentrations of hydrogen sulfide.
クラウス硫黄回収装置において硫化水素を部分酸化して
、単体硫黄とするものであるが、その反応は一般に以下
の式で表わされる。In the Claus sulfur recovery equipment, hydrogen sulfide is partially oxidized to form elemental sulfur, and the reaction is generally expressed by the following formula.
HO+−0=802+H20(1)
22
2 H2S +802= −Sx +2 H2O(2)
(1)式と2)式より、クラウス反応全体としては3
3 HS+−〇 =−8x+3HO(3)2 22 x
2
で表わすことができる。HO+-0=802+H20(1) 22 2 H2S +802= -Sx +2 H2O(2)
From equations (1) and 2), the overall Claus reaction is 3 3 HS+-〇 =-8x+3HO(3)2 22 x
It can be expressed as 2.
硫化水素と二酸化硫黄より硫黄を生成する反応(2)は
、化学平衡的には低温はど右辺に進行する。Reaction (2), which produces sulfur from hydrogen sulfide and sulfur dioxide, proceeds to the right at low temperatures in terms of chemical equilibrium.
したがって、クラウス反応は低温はど硫黄の生成率は高
くなる。Therefore, the lower the temperature in the Claus reaction, the higher the rate of sulfur production.
しかしながら、クラウス反応全体としては大きな発熱反
応であるから、通常反応は2ないし3段階で行われ、途
中に冷却工程がはいり、硫黄除去とガスの冷却が行われ
る。However, since the Claus reaction as a whole is a large exothermic reaction, the reaction is usually carried out in two or three stages, with a cooling step in the middle to remove sulfur and cool the gas.
クラウス硫黄回収装置において、クラウス反応を2〜3
段階に行った場合にも、そのテイルガス中には普通硫化
水素が0.2〜4%、二酸化イオウが0.1〜2,0%
、および少量の二硫化炭素、硫化カルボニル、硫黄が含
有されている。In the Claus sulfur recovery equipment, the Claus reaction is carried out by 2 to 3
Even when the stage is reached, the tail gas normally contains 0.2 to 4% hydrogen sulfide and 0.1 to 2.0% sulfur dioxide.
, and small amounts of carbon disulfide, carbonyl sulfide, and sulfur.
これら硫黄化合物を含むテイルガスの大気中への放出は
、大気汚染の原因となるので当然望ましいものではない
。Emission of tail gas containing these sulfur compounds into the atmosphere is naturally undesirable because it causes air pollution.
クラウス硫黄回収装置テイルガスの処理法としては各種
のものが開発あるいは提案されている。Various methods have been developed or proposed for processing the tail gas of Claus sulfur recovery equipment.
その一つはテイルガスを水素とともに高温でmと接触さ
せて、テイルガス中の硫黄化合物を硫化水素に変換して
から、硫化水素を溶液中で酸化、あるいは再生可能な溶
液に吸収除去するもので、ビーボン法(特公昭49−1
1142、特開昭48−55896)、スコツト法(特
開昭47−2908.47−6254)などが知られて
いる。One is to contact the tail gas with hydrogen at high temperature to convert the sulfur compounds in the tail gas to hydrogen sulfide, and then oxidize the hydrogen sulfide in a solution or remove it by absorption into a renewable solution. Bebon Law (Special Public Interest Act 1977-1)
1142, JP-A-48-55896), the Scott method (JP-A-47-2908, 47-6254), and the like are known.
テイルガスのその他の処理法としては、テイルガス中の
硫黄化合物を酸化して二酸化硫黄となし、その二酸化硫
黄を一般の排煙脱硫法(そのうち有名なのは二酸化硫黄
を石膏として固定する方法である)でもって処理するも
のがある。Other methods for treating tail gas include oxidizing the sulfur compounds in the tail gas to produce sulfur dioxide, and then converting the sulfur dioxide into general flue gas desulfurization (a well-known method is to fix sulfur dioxide as gypsum). There is something to process.
上記還元あるいは酸化工程を含む処理法に対しクラウス
反応を低温で行って、硫黄化合物の除去率を高める処理
方法がある。In contrast to the treatment method including the reduction or oxidation step described above, there is a treatment method in which a Claus reaction is performed at a low temperature to increase the removal rate of sulfur compounds.
先に述べたようにクラウス反応(式(2))は低温で行
われるほど硫黄化合物の除去率は高くなるが、硫黄の露
点が150〜250°Cであるから、硫黄の露点以下の
温度でクラウス反応を行えば、生成した硫黄は触媒上に
蓄積する。As mentioned earlier, the Claus reaction (Equation (2)) is carried out at a lower temperature, the higher the removal rate of sulfur compounds, but since the dew point of sulfur is 150 to 250°C, it is difficult to remove sulfur compounds at temperatures below the dew point of sulfur. When the Claus reaction is carried out, the sulfur produced accumulates on the catalyst.
硫黄の露点以下でクラウス反応を行わせて、触媒上に硫
黄を吸収させる低温クラウス法には、アルミナを用いる
方法(特公昭48−20999.50−21439,5
O−21440)あるいは活性炭を用いる方法(特公昭
46−22728)がすでに知られている。A method using alumina (Japanese Patent Publication No. 48-20999.50-21439, 5
A method using activated carbon (Japanese Patent Publication No. 46-22728) is already known.
低温クラウス法においては、触媒上に吸着した硫黄を再
生ガスでもって脱着する。In the low-temperature Claus process, sulfur adsorbed on the catalyst is desorbed using regeneration gas.
脱着ガスをクラウス硫黄回収装置に循環すればテイルガ
ス処理装置はクローズド化されることになり、これが低
温クラウス法の大きな特徴であり、有利な点でもある。If the desorbed gas is circulated to the Claus sulfur recovery unit, the tail gas treatment unit will be closed, which is a major feature and advantage of the low-temperature Claus process.
本発明者らは、上記のアルミナ、活性炭、および各種の
触媒のクラウス反応に対する活性を広い温度範囲におい
て研究した結果、活性の第1成分として酸化チタン、第
2成分として鉄、コバルト、ニッケル、および銅の酸化
物のうち少くとも1種以上を含む触媒が優れた性能を有
することを見出して、本発明に到達した。The present inventors studied the activity of the above-mentioned alumina, activated carbon, and various catalysts for the Claus reaction over a wide temperature range, and found that titanium oxide was the first active component, and iron, cobalt, nickel, and The present invention was achieved by discovering that a catalyst containing at least one type of copper oxide has excellent performance.
本発明の触媒(Ti−Fe、Co、Ni、Cu触媒)は
クラウス反応に対する活性が優れているばかりでなく、
脱着においても極めて優秀な性能を示すものである。The catalyst of the present invention (Ti-Fe, Co, Ni, Cu catalyst) not only has excellent activity for Claus reaction, but also
It also shows extremely excellent performance in attachment and detachment.
本発明の目的は、クラウス硫黄回収装置テイルガス中の
硫黄化合物を経済的に減少させる方法を提供することに
ある。It is an object of the present invention to provide a method for economically reducing sulfur compounds in Claus sulfur recovery unit tail gas.
また本発明の他の目的は、上記目的を達成させるための
新規な触媒を提供することである。Another object of the present invention is to provide a novel catalyst for achieving the above object.
本発明に従ってクラウス硫黄回収装置テイルガスを処理
するには、テイルガスを活性の第1成分として酸化チタ
ン、第2成分として鉄、コバルト、ニッケル、および銅
の酸化物のうち少くとも1種以上から成る触媒と接触さ
せ、反応(穴2))により生成した硫黄の少なくとも1
部を触媒に吸着させる。To treat Claus sulfur recovery apparatus tail gas in accordance with the present invention, the tail gas is treated with a catalyst comprising titanium oxide as an active first component and at least one of oxides of iron, cobalt, nickel, and copper as a second component. at least one of the sulfur produced by the reaction (hole 2))
part is adsorbed onto the catalyst.
この吸着工程を行う温度は触媒活性および硫黄の蒸気圧
等の面から80〜200℃が好ましく、120〜170
℃が特に好ましい。The temperature at which this adsorption step is carried out is preferably 80 to 200°C, and 120 to 170°C from the viewpoint of catalyst activity and sulfur vapor pressure.
C is particularly preferred.
吸着工程におけるテイルガスの空間速度(標準状態換算
)は、経済的な触媒使用量および硫黄化合物の除去効率
の面から200〜IQ 、ooov/ v / hが好
ましく、200〜5,000■/v/hが特に好ましい
。The space velocity of the tail gas in the adsorption step (converted to standard conditions) is preferably 200 to IQ, ooov/v/h, and 200 to 5,000/v/h from the viewpoint of economical catalyst usage and removal efficiency of sulfur compounds. h is particularly preferred.
触媒上に硫黄が吸着して、ある一定値以上に達すると、
硫黄化合物の除去率が低下しはじめるる。When sulfur is adsorbed on the catalyst and reaches a certain value or more,
The removal rate of sulfur compounds begins to decrease.
したがって、硫黄化合物の除去率が望まれる値より低く
なれば、触媒上の硫黄を脱着した、触媒を再生しなけれ
ばならない。Therefore, if the removal rate of sulfur compounds becomes lower than the desired value, the catalyst that has desorbed the sulfur on the catalyst must be regenerated.
触媒上から硫黄を脱着して触媒を再生させるためには2
種類の方法がある。In order to desorb sulfur from the catalyst and regenerate the catalyst, 2.
There are different methods.
その一つの方法では、酸素を含有するガスを再生ガスと
して用いて、吸着している硫黄を酸化して、二酸化硫黄
として脱着させる。In one method, an oxygen-containing gas is used as a regeneration gas to oxidize the adsorbed sulfur and desorb it as sulfur dioxide.
もう一つの方法では、高温の不活性ガスを再生ガスとし
て用いて、硫黄の露点以上の温度で硫黄を蒸発させて脱
着する。Another method uses a hot inert gas as a regeneration gas to evaporate and desorb sulfur at temperatures above the sulfur dew point.
吸着した硫黄を酸素含有ガスでもって脱着する場合には
、反応(4)が起る。When adsorbed sulfur is desorbed with oxygen-containing gas, reaction (4) occurs.
S+0□=SO□ Δ、H= −70K cal /
mole(4)本発明のTi−Fe 、Co 、Ni
)Cu触媒を用いた場合には、反応(4)は100℃以
上の温度で充分に実用的な速さで進行する。S+0□=SO□ Δ, H= -70K cal /
mole (4) Ti-Fe, Co, Ni of the present invention
) When a Cu catalyst is used, reaction (4) proceeds at a sufficiently practical rate at a temperature of 100° C. or higher.
反応(4)は70Kcal/moleの非常な発熱反応
であるので、脱着ガスは非常な高温に達する。Since reaction (4) is a very exothermic reaction of 70 Kcal/mole, the desorption gas reaches a very high temperature.
例えば、再生ガスに空気を用いた場合には、脱着ガスが
二酸化硫黄約20楚を含有するが、その温度は1,00
0℃を越える。For example, when air is used as the regeneration gas, the desorption gas contains about 20 °C of sulfur dioxide, but the temperature is 1,00 °C.
Exceeds 0℃.
このような高温においてはTi −Fe 、 Co 、
Ni 。At such high temperatures, Ti-Fe, Co,
Ni.
Cu触媒は活性を失うので、再生ガス中の酸素濃度を低
くするか、或は脱着ガスを冷却後、再生ガスに混合して
触媒層に循環させる。Since the Cu catalyst loses its activity, either the oxygen concentration in the regeneration gas is lowered, or the desorbed gas is cooled and then mixed with the regeneration gas and circulated to the catalyst layer.
この脱着ガスを循環させる方法では、脱着ガス中の二酸
化硫黄の濃度を高くできるので有利である。This method of circulating the desorption gas is advantageous because it allows the concentration of sulfur dioxide in the desorption gas to be increased.
再生ガスに空気を用いれば、二酸化硫黄を約20%含有
する脱着ガスが得られ、また再生ガスに酸素ガスを用い
れば、はぼ100%二酸化硫黄を含むガスを得ることが
できる。If air is used as the regeneration gas, a desorption gas containing about 20% sulfur dioxide can be obtained, and if oxygen gas is used as the regeneration gas, a gas containing almost 100% sulfur dioxide can be obtained.
脱着ガスの循環率(全脱着ガスに対する循環される脱着
ガスの割合)は、触媒の耐熱性を考えて選べば良いわけ
であるが、本発明のTi −Fe 、 Co 、 Ni
、 Cu触媒を用いる場合には、触媒層の温度を約6
00℃以下にするように循環率を決める。The circulation rate of the desorption gas (ratio of the desorption gas circulated to the total desorption gas) can be selected by considering the heat resistance of the catalyst, but the Ti-Fe, Co, Ni of the present invention
, When using a Cu catalyst, the temperature of the catalyst layer is about 6
Decide the circulation rate to keep it below 00℃.
例えば、空気を再生ガスとして使用する場合には、循環
率をおおむね75%以上とすればよいわけである。For example, when air is used as the regeneration gas, the circulation rate may be approximately 75% or more.
この脱着工程における再生ガスの供給速度、あるいは空
間速度は吸着工程のそれとほぼ同じ程度でよい。The supply rate or space velocity of the regeneration gas in this desorption step may be approximately the same as that in the adsorption step.
このように再生ガスの供給速度を適当に選ぶことにより
、脱着ガス中の酸素濃度は痕跡程度とすることができる
。By appropriately selecting the supply rate of the regeneration gas in this manner, the oxygen concentration in the desorption gas can be reduced to a trace level.
上記のように酸素含有ガスを再生ガスとして用いた場合
には、比較的高濃度の二酸化硫黄(および高温で気化し
た硫黄)を含む脱着ガスが得られる。When an oxygen-containing gas is used as the regeneration gas as described above, a desorption gas containing a relatively high concentration of sulfur dioxide (and sulfur vaporized at high temperature) is obtained.
この二酸化硫黄を含む脱着ガスは公知の乾式あるいは湿
式の排煙脱硫法、あるいは硫酸を製造するプロセスで処
理しても良く、またクラウス硫黄回収装置へ循環しても
良い。This desorption gas containing sulfur dioxide may be treated by a known dry or wet flue gas desulfurization method or a process for producing sulfuric acid, or may be circulated to a Claus sulfur recovery device.
脱着ガスをクラウス硫黄回収装置へ循環する場合には、
テイルガス処理がクローズドシステムとなるので特に好
ましい。When circulating the desorption gas to the Claus sulfur recovery device,
This is particularly preferred since the tail gas treatment becomes a closed system.
本発明の特徴は、硫化水素と二酸化硫黄の反応を促進さ
せる触媒に低温で高活性なTi−Fe。The present invention is characterized by the use of Ti-Fe, which is highly active at low temperatures, as a catalyst that promotes the reaction between hydrogen sulfide and sulfur dioxide.
Co 、 Ni 、 Cu触媒を用いることがあるが、
本発明のもう一つの特徴は、硫黄を吸着した触媒の再生
を酸素含有ガスで行うことができ、かつそれを100°
Cという非常な低温で行えるということである。Co, Ni, Cu catalysts may be used,
Another feature of the invention is that the regeneration of the sulfur-adsorbed catalyst can be carried out with an oxygen-containing gas and that it can be
This means that it can be done at a very low temperature of C.
従来知られているように、活性炭を低温クラウス反応の
触媒に使用する場合には再生に酸素含有ガスを用いるこ
とはできない。As is known in the art, when activated carbon is used as a catalyst for low-temperature Claus reactions, oxygen-containing gas cannot be used for regeneration.
なぜならば、活性炭の一部が酸素と反応して失われるか
らである。This is because some of the activated carbon reacts with oxygen and is lost.
アルミナを触媒として用いた場合、酸素を含有するガス
を再生ガスとして使用できるが、アルミナ触媒の反応(
4)に対する活性は低く、本発明者らの試験では200
℃以上の温度にならないと進行しない。When alumina is used as a catalyst, oxygen-containing gas can be used as a regeneration gas, but the reaction of the alumina catalyst (
The activity against 4) is low, and in our tests, 200
It will not progress unless the temperature reaches ℃ or higher.
触媒の再生法のもう一つは、高温の不活性ガスを用いる
方法である。Another method for regenerating the catalyst is to use a high temperature inert gas.
不活性ガスには、窒素、水蒸気、クラウス回収装置テイ
ルガス等が挙げられるが、この場合にはこれら再生ガス
を硫黄の露点以上の温度で触媒層に通ずれば良い。Examples of the inert gas include nitrogen, water vapor, Claus recovery device tail gas, etc. In this case, these regeneration gases may be passed through the catalyst layer at a temperature equal to or higher than the dew point of sulfur.
脱着ガスは冷却して硫黄を凝縮除去するか、クラウス炉
へ再循環しても良い。The desorbed gas may be cooled to condense out the sulfur or recycled to the Claus reactor.
本発明のクラウス回収装置テイルガスの処理においては
、活性の第1成分として酸化チタン、第2成分として鉄
、コバルト、ニッケル および銅の酸化物のうち少くと
も1種以上とから成る触媒を用いる。In the treatment of the Claus recovery apparatus tail gas of the present invention, a catalyst is used which comprises titanium oxide as the active first component and at least one of oxides of iron, cobalt, nickel, and copper as the second component.
これら活性成分の割合は、触媒活性および価格の面から
、第1成分と第2成分の金属成分の原子比が50 :
50〜99:1が好ましく、特に70:30〜98:2
とするのが好ましい。From the viewpoint of catalytic activity and cost, the ratio of these active components is such that the atomic ratio of the metal components of the first component and the second component is 50:
50-99:1 is preferred, especially 70:30-98:2
It is preferable that
本発明の触媒を得るためのチタンの原料としては、各種
の酸化チタン、チタン酸、四塩化チタン、硫酸チタン、
硫酸チタニルなどを使用し得る。Titanium raw materials for obtaining the catalyst of the present invention include various titanium oxides, titanic acids, titanium tetrachloride, titanium sulfate,
Titanyl sulfate and the like may be used.
鉄の原料としては、各種の酸化鉄、また加熱することに
より酸化鉄を生成する含水酸化鉄、硝酸鉄、硫酸鉄、塩
化鉄、酢酸鉄、シュウ酸鉄などの有機、無機の各種鉄塩
を使用し得る。Raw materials for iron include various iron oxides, as well as various organic and inorganic iron salts such as hydrated iron oxide, iron nitrate, iron sulfate, iron chloride, iron acetate, and iron oxalate, which produce iron oxide when heated. Can be used.
また触媒調製法として汎用される上記の各種鉄塩の水溶
液をアンモニア水、力性アルカリ、炭酸アルカリ、炭酸
アルカリ、尿素などで沈殿し、加熱分解により酸化鉄を
生成せしめる方法も好ましい。It is also preferable to precipitate an aqueous solution of the above-mentioned various iron salts with aqueous ammonia, alkali carbonate, alkali carbonate, urea, etc., which is commonly used as a catalyst preparation method, and generate iron oxide by thermal decomposition.
コバルトの原料としても、各種の酸化コバルト、また加
熱することにより酸化コバルトを生成する水酸化コバル
ト、その他有機、無機の各種コバルト塩を使用し得る。As a raw material for cobalt, various cobalt oxides, cobalt hydroxide which produces cobalt oxide by heating, and various other organic and inorganic cobalt salts can be used.
また各種のコバルト塩の水溶液に沈殿剤を加え、生成し
た水酸化物を加熱分解することにより酸化コバルトを生
成せしめる方法も好ましい。Also preferred is a method in which cobalt oxide is produced by adding a precipitant to an aqueous solution of various cobalt salts and thermally decomposing the produced hydroxide.
ニツケルの原料としても、酸化ニッケル、また加熱する
ことにより酸化ニッケルを生成する水酸化ニッケル、そ
の他有機、無機の各種ニッケル塩を使用し得る。As raw materials for nickel, nickel oxide, nickel hydroxide which produces nickel oxide when heated, and various other organic and inorganic nickel salts can be used.
また各種のニッケル塩の水溶液に沈殿剤を加え、生成し
た水酸化物を加熱分解することにより酸化ニッケルを生
成せしめる方法も好ましい。Also preferred is a method in which nickel oxide is produced by adding a precipitant to an aqueous solution of various nickel salts and thermally decomposing the produced hydroxide.
銅の原料としても、酸化銅、または加熱することにより
酸化銅を生成する水酸化銅、その他有機、無機の各種銅
塩を使用し得る。As a raw material for copper, copper oxide, copper hydroxide which produces copper oxide upon heating, and various other organic and inorganic copper salts can be used.
またこれらの銅塩の水溶液に沈殿剤を加え、生成した水
酸化物を加熱分解することにより酸化鋼を得るのも良い
方法である。It is also a good method to obtain oxidized steel by adding a precipitant to an aqueous solution of these copper salts and thermally decomposing the generated hydroxide.
また本発明の触媒を製造するには、触媒の製造に通常用
いられている打錠成型法、押出し成型法転勤造粒法など
いずれも使用し得る。Further, in order to produce the catalyst of the present invention, any of the tableting method, extrusion molding, transfer granulation method, etc. commonly used in the production of catalysts can be used.
なお、本発明はクララステイルガスの処理のみに限定さ
れるものではなく、これに類似の各種ガスにも、通常の
設計変更程度の修正によって適用しつるものである。It should be noted that the present invention is not limited only to the treatment of Clarastail gas, but can also be applied to various gases similar to this by making modifications to the extent of ordinary design changes.
以下に実施例を示して本発明をより具体的に説明する。EXAMPLES The present invention will be explained in more detail with reference to Examples below.
実施例−1
四塩化チタン(T t C14)溶液500gを水11
に溶解する。Example-1 500 g of titanium tetrachloride (T t C14) solution was added to 11 parts of water.
dissolve in
この溶液に硫酸第1鉄(FeSO4・7H20)811
を加えて溶解する。Ferrous sulfate (FeSO4・7H20) 811
Add and dissolve.
この混合溶液をアンモニア水中に徐々に滴下すれば、チ
タン酸と含水酸化鉄の共沈殿物が生成する。When this mixed solution is gradually dropped into aqueous ammonia, a coprecipitate of titanic acid and hydrated iron oxide is generated.
この場合、アンモニア溶液のPHが7以下にならないよ
うに適宜アンモニア水を添加する。In this case, ammonia water is added as appropriate so that the pH of the ammonia solution does not become 7 or less.
生じた沈殿をデカンテーションにより蒸留水でよく洗浄
したのち沢過し、120℃で1昼夜乾燥する。The resulting precipitate is thoroughly washed with distilled water by decantation, filtered, and dried at 120°C for one day and night.
乾燥後の粉末にグラファイトを3重量受加え充分に混合
し、成型圧力500に9/cI?Lで直径6mrn、厚
さ6朋の大きさに打錠成型する。Add 3 weights of graphite to the dried powder, mix thoroughly, and set the molding pressure to 500 to 9/cI? Compress and mold into a L size with a diameter of 6 mrn and a thickness of 6 mm.
得られた成型品を5000Cで4時間焼成する。The obtained molded product is fired at 5000C for 4 hours.
かくして得られた触媒は原子比でTi : Fe=9
: 1の組成を有する。The catalyst thus obtained had an atomic ratio of Ti:Fe=9
: It has a composition of 1.
触媒の性能試験は次のように行なった。The catalyst performance test was conducted as follows.
反応管は内径17朋の石英製で内部に外径5朋の石英製
の熱電対保護管を有している。The reaction tube was made of quartz and had an inner diameter of 17 mm, and contained therein a thermocouple protection tube made of quartz and had an outer diameter of 5 mm.
この反応管を電気炉で加熱して反応温度を設定する。This reaction tube is heated in an electric furnace to set the reaction temperature.
反応管の中央部に10〜20メツシユに破砕された触媒
を8d充填し、下記組成のガスを801/hの流速(空
間速度10,000h−”)で流した。The center of the reaction tube was filled with 8 d of catalyst crushed into 10 to 20 meshes, and a gas having the following composition was flowed at a flow rate of 801/h (space velocity 10,000 h-'').
ガス組成 H2S 1.0±0.05% S02 0.5±0.025% N2 残部 得られた結果を表1に示す。gas composition H2S 1.0±0.05% S02 0.5±0.025% N2 remainder The results obtained are shown in Table 1.
比較例−1
硝酸アルミニウム(AA(NOs)3・9H20)50
0gと硫酸第1鉄41gを水11に溶かす。Comparative example-1 Aluminum nitrate (AA(NOs)3.9H20) 50
0g and 41g of ferrous sulfate are dissolved in 11g of water.
この混合溶液をアンモニア水中に徐々に滴下すればアル
ミナゾルと含水酸化鉄の共沈殿物が生成する。If this mixed solution is gradually dropped into aqueous ammonia, a coprecipitate of alumina sol and hydrated iron oxide is generated.
以下実施例−1に示したのと同様の方法でA 1203
−Fe203触媒(Al: Fe=9 : 1、原子比
)を調製した。A 1203 was prepared in the same manner as shown in Example-1.
-Fe203 catalyst (Al:Fe=9:1, atomic ratio) was prepared.
得られた触媒の性能を実施例−1に示したのと同様の実
験条件で測定して、表1に示す結果を得た。The performance of the obtained catalyst was measured under the same experimental conditions as shown in Example-1, and the results shown in Table 1 were obtained.
比較例−2
市販のクラウス反応用アルミナ触媒を用いて、実施例−
1に示したのと同様の実験条件で性能を測定し、表1に
示す結果を得た。Comparative Example-2 Using a commercially available alumina catalyst for Claus reaction, Example-
Performance was measured under the same experimental conditions as shown in Table 1, and the results shown in Table 1 were obtained.
実施例−2
酸化チタンと酸化鉄の割合を変化させた以外は実施例1
と同様の調製法でTi 二Fe=9.8 : 0.2゜
8:2,7:3の割合で含有する触媒を製造した。Example-2 Example 1 except that the ratio of titanium oxide and iron oxide was changed
A catalyst containing Ti2Fe in a ratio of 9.8:0.2°8:2, 7:3 was prepared using the same method as above.
これら触媒の性能を実施例−1に示したのと同様の実験
条件で測定し、表2に示す結果を得た。The performance of these catalysts was measured under the same experimental conditions as shown in Example-1, and the results shown in Table 2 were obtained.
実施例−3
硫酸第1鉄のかわりに硝酸コバルトを用いた以外は実施
例−1と同様の方法でTi02−Co0触媒を調製した
。Example-3 A Ti02-Co0 catalyst was prepared in the same manner as in Example-1 except that cobalt nitrate was used instead of ferrous sulfate.
なおこの場合沈殿剤としてはN a 2 C03溶液を
用いた。In this case, a Na 2 C03 solution was used as a precipitant.
触媒の組成を種々変えて、その性能を実施例−1に示し
たのと同様の実験条件で測定し、表3に示す結果を得た
。The composition of the catalyst was varied and its performance was measured under the same experimental conditions as shown in Example 1, and the results shown in Table 3 were obtained.
実施例−4
硫酸第1鉄のかわりに硝酸ニッケルを用いた以外は実施
例−1と同様の方法でT 102 N t O触媒を
調製した。Example-4 A T 102 N t O catalyst was prepared in the same manner as in Example-1 except that nickel nitrate was used instead of ferrous sulfate.
なおこの場合沈殿剤としてはNa2CO3溶液を用いた
。In this case, a Na2CO3 solution was used as a precipitant.
触媒の組成を種々変えて、その性能を実施例−1に示し
たのと同様の実験条件で測定し、表4に示す結果を得た
。The composition of the catalyst was varied and its performance was measured under the same experimental conditions as shown in Example-1, and the results shown in Table 4 were obtained.
実施例−5
硫酸第1鉄のかわりに硝酸銅を用いた以外は実施例−1
と同様の方法でT 102 Cu O触媒を調製した
。Example-5 Example-1 except that copper nitrate was used instead of ferrous sulfate
A T 102 Cu O catalyst was prepared in a similar manner.
なおこの場合沈殿剤としてはN a 2 C03溶液を
用いた。In this case, a Na 2 C03 solution was used as a precipitant.
触媒の組成を種々変えて、その性能を実施例−1に示し
たのと同様の実験条件で測定し、表5に示す結果を得た
。The composition of the catalyst was varied and its performance was measured under the same experimental conditions as shown in Example 1, and the results shown in Table 5 were obtained.
実施例−6 本実施例では3残分系触媒の性能について述べる。Example-6 In this example, the performance of a three-residue catalyst will be described.
メタチタン酸スラリー500gをとり(TiO2として
150.!i’)、これに硝酸銅25.2.9および酸
化鉄8.3gを加える。Take 500 g of metatitanic acid slurry (150.!i' as TiO2) and add 25.2.9 g of copper nitrate and 8.3 g of iron oxide.
更に水5001rLlを加え、この混合物をニーダ−に
て充分混練する。Furthermore, 5001 rLl of water was added, and the mixture was thoroughly kneaded in a kneader.
得られたペースト状の混合物を300℃で5時間予備焼
成した後に、グラファイトを3重量係加え、成型圧力約
500 fQ9/crAで直径6群、厚さ6間の大きさ
に打錠成型する。After preliminarily calcining the resulting paste-like mixture at 300° C. for 5 hours, 3 weights of graphite are added and the mixture is compressed into tablets with a diameter of 6 and a thickness of 6 at a molding pressure of about 500 fQ9/crA.
得られた成型品を500℃で4時間焼成した。The obtained molded product was fired at 500° C. for 4 hours.
かくして得られた触媒は原子比で、Ti : Fe :
Cu=9 : 0.5 : 0.5の組成を有する。The catalyst thus obtained has an atomic ratio of Ti:Fe:
It has a composition of Cu=9:0.5:0.5.
その性能を実施例−1に示したのと同様の実験条件で測
定し、表6に示す結果を得た。Its performance was measured under the same experimental conditions as shown in Example-1, and the results shown in Table 6 were obtained.
実施例−7
本実施例においては、実施例−1の触媒を用い、吸着工
程と再生工程を行った結果について述べる。Example 7 In this example, the results of an adsorption step and a regeneration step using the catalyst of Example 1 will be described.
(a) 吸着工程:
反応ガス(E(、、S 1.0±0.05%、502
0.5±0.025%、N2020%、N2残)のガス
を空間速度2,000h−1で3時間流通した。(a) Adsorption step: Reaction gas (E(,,S 1.0±0.05%, 502
0.5±0.025%, N2020%, N2 remainder) gas was passed through the tube at a space velocity of 2,000 h-1 for 3 hours.
(b) 再生工程:
再生ガス(024%、N2 残)のガスを空間速度1,
000 h−”で流通した。(b) Regeneration process: Regeneration gas (024%, remaining N2) at a space velocity of 1,
000 h-''.
以下のような結果を得た。The following results were obtained.
吸着工程を130°Cで行ったところ、H2SとSO2
の除去率は3時間の間のいずれも95%以上であった。When the adsorption process was carried out at 130°C, H2S and SO2
The removal rate was 95% or more for all three hours.
再生工程も、触媒層入口温度130°Cで行ったところ
、脱着ガスはS02を4%含有していた。When the regeneration step was also carried out at a catalyst bed inlet temperature of 130°C, the desorption gas contained 4% S02.
触媒上の硫黄がSO2に酸化される時に、反応熱により
触媒層中央部の温度は最高430℃まで上昇することが
認められた。It was observed that when the sulfur on the catalyst was oxidized to SO2, the temperature at the center of the catalyst layer rose to a maximum of 430°C due to the heat of reaction.
温度上昇の結果、触媒上に吸着した硫黄の一部は蒸発し
て脱着することが、反応管下部に硫黄が付着したのを観
察することにより確認できた。It was confirmed by observing that sulfur adhered to the lower part of the reaction tube that as a result of the temperature increase, some of the sulfur adsorbed on the catalyst evaporated and was desorbed.
上記吸着−再生工程を10回繰返し行ったが、触媒の性
能低下はなかった。Although the above adsorption-regeneration step was repeated 10 times, there was no deterioration in the performance of the catalyst.
比較例−3
比較例−2に示したアルミナ触媒を用い、実施例−7と
同様の実験を行い、次のような結果を得た。Comparative Example 3 Using the alumina catalyst shown in Comparative Example 2, an experiment similar to Example 7 was conducted, and the following results were obtained.
吸着工程を130℃で行ったところ、H2SとS02の
除去率は3時間の問いずれも95%以上であった。When the adsorption step was carried out at 130° C., the removal rate of H2S and S02 was 95% or more for 3 hours.
再生工程は130,150,170°Gで試みたが硫黄
のSO2への酸化反応は進行せず、脱着ガスにはSO2
が含まれていなかった。The regeneration process was attempted at 130, 150, and 170°G, but the oxidation reaction of sulfur to SO2 did not proceed, and the desorption gas contained SO2.
was not included.
Claims (1)
、第1成分として酸化チタン、第2成分として鉄、コバ
ルト、ニッケルおよび銅の酸化物のうち少なくとも1種
類以上を加えたものを活性成分とする触媒と接触させ、
生成した硫黄を該触媒に吸着させる工程、および硫黄を
吸着した触媒から硫黄を脱着させる工程とから成ること
を特徴とするクラウス硫黄回収装置ティルガスの処理方
法。 2 着脱工程において、酸素含有ガスを用いる特許請求
の範囲第1項記載のクラウス硫黄回収装置テイルガスの
処理方法。 3 着脱工程において、不活性ガスを硫黄の露点以上の
温度で触媒層に通過させる特許請求の範囲第1項記載の
クラウス硫黄回収装置テイルガスの処理方法。 4 吸着工程を80〜200℃で行なう特許請求の範囲
第1項の記載のクラウス硫黄回収装置テイルガスの処理
方法。 5 触媒の第1成分と第2成分の組成比が金属成分の原
子比で99:1〜50 : 50である特許請求の範囲
第1項記載のクラクス硫黄回収装置テイルガスの処理方
法。[Claims] 1. A gas containing at least hydrogen sulfide and sulfur dioxide, with titanium oxide as the first component and at least one of iron, cobalt, nickel, and copper oxides as the second component. in contact with a catalyst containing as an active ingredient,
A method for treating till gas from a Claus sulfur recovery apparatus, comprising the steps of: adsorbing generated sulfur onto the catalyst; and desorbing sulfur from the catalyst that has adsorbed sulfur. 2. A method for treating tail gas from a Claus sulfur recovery apparatus according to claim 1, in which an oxygen-containing gas is used in the attaching and detaching step. 3. A method for treating tail gas from a Claus sulfur recovery apparatus according to claim 1, wherein in the attachment/desorption step, an inert gas is passed through the catalyst layer at a temperature equal to or higher than the dew point of sulfur. 4. A method for treating tail gas from a Claus sulfur recovery device according to claim 1, wherein the adsorption step is carried out at 80 to 200°C. 5. The method for treating tail gas of a KRAKS sulfur recovery device according to claim 1, wherein the composition ratio of the first component and the second component of the catalyst is 99:1 to 50:50 in terms of atomic ratio of metal components.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP51031335A JPS5912602B2 (en) | 1976-03-24 | 1976-03-24 | Claus sulfur recovery equipment tail gas processing method |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP51031335A JPS5912602B2 (en) | 1976-03-24 | 1976-03-24 | Claus sulfur recovery equipment tail gas processing method |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS52114593A JPS52114593A (en) | 1977-09-26 |
| JPS5912602B2 true JPS5912602B2 (en) | 1984-03-24 |
Family
ID=12328372
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP51031335A Expired JPS5912602B2 (en) | 1976-03-24 | 1976-03-24 | Claus sulfur recovery equipment tail gas processing method |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS5912602B2 (en) |
Families Citing this family (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| DE3332563A1 (en) * | 1983-09-09 | 1985-03-28 | Basf Ag, 6700 Ludwigshafen | METHOD FOR DESULFURING H (ARROW DOWN) 2 (ARROW DOWN) GASES |
| JPH0832548B2 (en) * | 1985-10-25 | 1996-03-29 | ソシエテ・ナシオナル・エルフ・アキテ−ヌ (プロデユクシオン) | Method for removing sulfur compounds contained in residual gas |
-
1976
- 1976-03-24 JP JP51031335A patent/JPS5912602B2/en not_active Expired
Also Published As
| Publication number | Publication date |
|---|---|
| JPS52114593A (en) | 1977-09-26 |
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