CN1024524C - Method for operation of claus-apparatus - Google Patents

Method for operation of claus-apparatus Download PDF

Info

Publication number
CN1024524C
CN1024524C CN 90102210 CN90102210A CN1024524C CN 1024524 C CN1024524 C CN 1024524C CN 90102210 CN90102210 CN 90102210 CN 90102210 A CN90102210 A CN 90102210A CN 1024524 C CN1024524 C CN 1024524C
Authority
CN
China
Prior art keywords
gas
unstripped
hydrogen
managing
waste
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 - Fee Related
Application number
CN 90102210
Other languages
Chinese (zh)
Other versions
CN1048201A (en
Inventor
乌尔里希·梅斯尔
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Krupp Koppers GmbH
Original Assignee
Krupp Koppers GmbH
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Priority claimed from DE19893919908 external-priority patent/DE3919908A1/en
Application filed by Krupp Koppers GmbH filed Critical Krupp Koppers GmbH
Publication of CN1048201A publication Critical patent/CN1048201A/en
Application granted granted Critical
Publication of CN1024524C publication Critical patent/CN1024524C/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

Links

Images

Landscapes

  • Treating Waste Gases (AREA)
  • Exhaust Gas Treatment By Means Of Catalyst (AREA)
  • Incineration Of Waste (AREA)

Abstract

The invention concerns a manner of execution of the procedure according to main patent no.P3843295. In this case it is provided that an exhaust gas containing ammonia is added to the original gas, prior to its introduction into the combustion furnaces.

Description

Method for operation of Claus-apparatus
The present invention relates to a kind of working method of Cross unit, particularly a kind of composition-formed of this method.
In coking industry, utilize Crouse's method to produce sulphur and be widely used.US4 for example, 143,122 have described a kind of circulation cleaning equipment that cleans coke oven gas, equipment is in the front of a clustered aggregates, the latter is by the reactor of decompose nitrogen, refrigeration cycle recovery indirectly, and alkalization washing (extraction element), the claus oven that waste heat boiler is housed and two claus reaction devices are formed.This clustered aggregates is used for producing sulphur in the waste gas from the circulation cleaning equipment of front, produces the bottom heat supply gas of sulfur-bearing hardly and steam simultaneously as its byproduct.Crouse's residual gas then goes back in the reactor front delivery that is used for decompose nitrogen.
This device can only the cycle of treatment washing plant waste gas, as its raw material of determining, and the partial combustion of the decomposition of nitrogen compound and sulphur compound is to carry out in two different equipment, these two equipment configurations air feeder and waste heat boiler.
In the working method of Cross unit of the present invention, make earlier to contain H 2The unstripped gas partial combustion of S, in a two-stage or multistage claus reaction device, continue reaction then, wherein, in the roasting kiln of the band waste heat boiler of on or two, installing side by side, the flow that depends on the hydrogen sulfide that adds with unstripped gas is realized the prime burning of unstripped gas, after this gas is further handled in an one claus reaction device, and the throughput of this reactor is by the maximum sulphur flow set of expecting.
In described method, be defined in the residual gas that forms behind the claus reaction device and will carry out shortening, the sulfide that all still are contained in the residual gas becomes hydrogen sulfide.Wherein with the heating hydrogen carrier of coal gas as hydrogenation.In addition, also use the hydrogen in the residual gas together, this hydrogen produces in the catalyst layer at roasting kiln when the generation catalytic decomposition of nitrogenize contained in the unstripped gas.Generally speaking, the hydrogen content in the residual gas is not enough to make the complete hydrogenation of contained sulfide, therefore, in the method, introduces heated air and is absolutely necessary as hydrogen carrier.
Therefore, the present invention relates to a kind of composition-formed of described method, on the one hand, can make the shortening of residual gas worthwhile more economically, can solve the environmental protection problem of ammonia-contaminated gas on the other hand simultaneously by this method.
According to the present invention,, can finish above-mentioned task by before entering roasting kiln, sneaking into a kind of ammoniated waste gas in the unstripped gas of back.
The ammonia-contaminated gas that mixes to unstripped gas can be a kind of waste gas from any source, for example is from the steam stripped ammonia vapour mixture that contains of waste water.Depend on its ammonia content, every Nm with raw material gas phase blended exhausted air quantity 3(standard cubic meter) unstripped gas can mix a Nm at most 3Waste gas.The ammonia contained nitride in unstripped gas that is added by this mode carries out catalytic decomposition at the catalyst layer of roasting kiln, has correspondingly improved the amounts of hydrogen that is produced in this way thus.Thereby the amounts of hydrogen of this raising can be used for the residual gas shortening, therefore, and the hydrogen that can corresponding minimizing adds from other source for this purpose, perhaps in case of necessity even can stop fully.
Further specify other details of the inventive method below by means of schema shown in the drawings.
In this schema, enter at pipeline 1 before the burner 2 and 5 of roasting kiln 3 and 6, in unstripped gas, sneak into a kind of ammoniated waste gas through managing 42.If the hydrogen sulfide flow that unstripped gas is brought into greater than the predetermined volumes of burning disconnected 3, will be shunted the gas mixture of a part of unstripped gas and ammonia-contaminated gas by pipe 1, through managing 4 burners 5 of sending into second roasting kiln 6.Supply with required combustion air by pipe 7 and 8 to burner 2 and 5, be used for to burner 2 and the necessary burning gas of 5 supplies, for example coke(oven)gas or partial oxygen gasification by pipe 9 pipes of telling 10 and 11.All be provided with catalyst layer 3a and 6a in the roasting kiln 3 and 6, be used for decomposing nitride that exists in the unstripped gas and the nitrogen of bringing into by waste gas.Catalyst layer 3a here and 6a are equipped with the commercial catalyst that this is suitable for, and they for example contain nickel is catalytic active substance.
The hydrogen that ammonia and all the other nitride catalysts generate when decomposing is stayed in the gas.Through after the roasting kiln 3, the gas of this heat enters waste heat boiler 13 via pipe 12, is 270 ℃ in this gas cooling to temperature, so that then enter collection tube 15 through managing 14, pipe 15 is sent to gas the first step of claus reaction device 16.If started second roasting kiln 6 equally, the gas shunting that handle the there is extracted out by pipe 17, correspondingly cooling in affiliated waste heat boiler 18, and this is after manage the 19 same collection tubes 15 of introducing, like this, two stock streams of gas lump together and send into claus reaction device 16.Gas is extracted out by the first step of claus reaction device 16 through managing 20, and arrives first flue of waste heat boilers 22 through interchanger 21, and being cooled to temperature at this is 154 ℃.Then, through managing 23 gas sent into the second stage of claus reaction device 16.Wherein, obtaining a little in the interchanger 21 that gas connects betwixt reheats.Gas is drawn by claus reaction device 16 through managing 24 again, is sent to second flue of waste heat boiler 122, and being cooled to temperature again at this is 154 ℃.Because most sulphur are removed from the gas of waste heat boiler 22 back, so this gas that repeatedly is also referred to as Crouse's residual gas only contains a small amount of unconverted H 2S and SO 2Because these impurity, this residual gas can't directly enter atmosphere.Thereby, at first it is sent into interchanger 26 through managing 25, arrive hydrogenation reactors 29 through managing 27 then, wherein, be heated to about 280 ℃ in the well heater 28 that gas connects earlier betwixt.In hydrogenation reactor 29, all sulfide that are contained in the residual gas all become hydrogen sulfide through shortening.Wherein, the hydrogen carrier that at first is used for hydrogenation with the contained hydrogen conduct of residual gas itself.Because the present invention sneaks into unstripped gas with ammonia-contaminated gas, has correspondingly improved the hydrogen content in the residual gas.If so also deficiency is so that the complete hydrogenation of all sulfide that residual gas still exists, can add other hydrogen-containing gas, for example combustion gas to hydrogen reactor 29 through managing 9.For the shortening of sulfide, use commercially available hydrogenation catalyst here, they for example contain that nickel is activeconstituents.Residual gas behind the hydrogenation is extracted out by hydrogenator through managing 30.As previously mentioned, because this residual gas only contains H 2S is as sulfur component, and available one goes on foot H 2The S washing continues to handle to it.If Cross unit and gasification or the coupling of coal tar equipment, the raw gas that this residual gas for example can be produced with the there is at H 2Mix mutually before the S washing step.
The isolating sulphur of gas cooling time institute is extracted out through managing 31,32,33 and 34 in waste heat boiler 13,18 and 22, and each manifold goes into to collect house steward 35, by pipe 35 sulphur is sent to further processing treatment.Pipe 36 is used for to waste heat boiler 22 provides boiler water storage, and the steam that the there produces is then extracted out by pipe 37.Waste heat boiler 13 is supplied with necessary boiler water storage by pipe 38.Tell arm 39 by this pipe, supply with boiler water storage to waste heat boiler 18.Extract the steam that produces out by managing 40 and 41 in waste heat boiler 13 and 18, the steam of wherein managing in 41 merges with the vapor phase of managing in 40.
Illustrate that with embodiment the mode of operation of the inventive method contains 53%(Vol below) H 2The unstripped gas of S is with 1210Nm 3The flow of/h enters technology by pipe 1.To sneak into flow to this air-flow be 240Nm through managing 42 3/ h contains 18%(Vol) NH 3Waste gas.It is very high to handle in the residual gas that this mixed gas forms hydrogen richness under the condition of having stated in front then, so that only need import only 59Nm to hydrogenator 29 through managing 9 3Combustion gas.Compare with preceding method, saved 79% expense during the residual gas hydrogenation.Solved the problem of environmental pollution of the ammonia-contaminated gas that adds simultaneously.

Claims (2)

1, a kind of working method of Cross unit wherein makes earlier to contain H 2The unstripped gas of S is in the roasting kiln of one or two band waste heat boiler of installing side by side, the flow that depends on the hydrogen sulfide that adds with unstripped gas is realized the prime burning of unstripped gas, it is characterized in that: before entering roasting kiln, in unstripped gas, sneak into a kind of ammoniated waste gas, after the burning, gas is further handled in an independent claus reaction device.
2, the described method of claim 1 is characterized in that, mostly is every Nm most with the amount of the ammonia-contaminated gas of original mixed gases 3Raw material mixes 1Nm 3Waste gas.
CN 90102210 1989-06-19 1990-06-10 Method for operation of claus-apparatus Expired - Fee Related CN1024524C (en)

Applications Claiming Priority (3)

Application Number Priority Date Filing Date Title
DE19893919908 DE3919908A1 (en) 1988-12-22 1989-06-19 Improving claus reactor output - by adding ammonia to hydrogen sulphide feed gas before initial partial combustion stage
DEP3919908.8 1989-06-19
DE3919908.8 1989-06-19

Publications (2)

Publication Number Publication Date
CN1048201A CN1048201A (en) 1991-01-02
CN1024524C true CN1024524C (en) 1994-05-18

Family

ID=6383001

Family Applications (1)

Application Number Title Priority Date Filing Date
CN 90102210 Expired - Fee Related CN1024524C (en) 1989-06-19 1990-06-10 Method for operation of claus-apparatus

Country Status (5)

Country Link
CN (1) CN1024524C (en)
DD (1) DD300097A5 (en)
ES (1) ES2024191A6 (en)
PL (1) PL165217B3 (en)
ZA (1) ZA902342B (en)

Families Citing this family (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
DE10233818B4 (en) * 2002-07-25 2007-05-24 Uhde Gmbh Waste heat boiler for a Claus plant
CN100430315C (en) * 2006-09-18 2008-11-05 孔庆然 Equipment and method for treating exhaust gas for carbon bisulfide preparing process
CN101274750B (en) * 2007-12-29 2010-06-30 江苏晟宜环保科技有限公司 Tail gas-recycled sulfur recovery method
CN102381686A (en) * 2011-07-29 2012-03-21 山东三维石化工程股份有限公司 Treatment process of high-ammonia and low-sulfur gas

Also Published As

Publication number Publication date
ES2024191A6 (en) 1992-02-16
PL165217B3 (en) 1994-11-30
ZA902342B (en) 1990-12-28
CN1048201A (en) 1991-01-02
DD300097A5 (en) 1992-05-21
PL284933A3 (en) 1991-09-09

Similar Documents

Publication Publication Date Title
CN101910381B (en) Method and apparatus to facilitate substitute natural gas production
CN100475313C (en) Device for the recovery and diffluence of sulfur dioxide and the system and method thereof
CN101244805B (en) Method for producing methanol synthesis gas by oven gas non-catalytic pure oxygen-steam conversion
CN105567898A (en) Reformed gas-based reduction method with return of the waste reduction gases and decarbonisation of the waste gas component used as combustion gas for the reformer
CN101801842A (en) Be used for from the method and apparatus of biogas production synthetic gas
CN1100721C (en) Steam reforming process
US4447333A (en) Process for the elimination of ammonia in coke plant waste waters
CN101391746A (en) Small-sized coal gasification hydrogen making method
RU2199486C2 (en) Process of production of synthesis gas used for synthesis of gasoline, kerosene, and gas oil (versions)
CN102256895B (en) Method for the upgrading of the gas mixture from a deaerator associated with the production of a synthesis gas, and plant for implementing same
CN1024524C (en) Method for operation of claus-apparatus
CN1025020C (en) Process for producting rich hydrogen gas
CN101155753B (en) Combustion device that produces hydrogen with re-use of captured Co2
CN205347482U (en) System for still crude gas direct reduction is metallurgical to utilize carbide stove tail gas system
CN100412173C (en) Process for pretreatment of coke oven gas and partial oxidation preparation of synthetic raw gas
EP0157917A2 (en) Reduction of metal compounds
US5100640A (en) Method of operating a claus-plant
CA2493286A1 (en) Method for isolating hydrogen sulphide from coke oven gas with the subsequent recovery of elemental sulphur in a claus plant
CN215917413U (en) Active carbon preparation combustible gas cyclic utilization device
CN205170754U (en) Pyrolysis of coal gas and mixed methanation system of carbide tail gas
CN113060704B (en) Organic solid clean high-efficiency hydrogen production device and method
CN111234850B (en) Calcium-based biomass chemical chain pyrolysis system
CN1073374A (en) Remove the method for the hydrogen sulfide in the gas
CN114657304B (en) Device and method for preparing gas-based shaft furnace reducing gas by purifying biomass gas
CN109593580A (en) A kind of semi-coke furnace tail gas fine de-sulfur and adiabatic methanation process

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
C14 Grant of patent or utility model
GR01 Patent grant
C19 Lapse of patent right due to non-payment of the annual fee
CF01 Termination of patent right due to non-payment of annual fee