GB1569639A - Process for the decomposition of ammonia vapours having a high content of hydrogen sulphide - Google Patents

Process for the decomposition of ammonia vapours having a high content of hydrogen sulphide Download PDF

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Publication number
GB1569639A
GB1569639A GB17086/77A GB1708677A GB1569639A GB 1569639 A GB1569639 A GB 1569639A GB 17086/77 A GB17086/77 A GB 17086/77A GB 1708677 A GB1708677 A GB 1708677A GB 1569639 A GB1569639 A GB 1569639A
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air
chamber
combustion
process according
vapours
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    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G7/00Incinerators or other apparatus for consuming industrial waste, e.g. chemicals
    • F23G7/06Incinerators or other apparatus for consuming industrial waste, e.g. chemicals of waste gases or noxious gases, e.g. exhaust gases
    • F23G7/07Incinerators or other apparatus for consuming industrial waste, e.g. chemicals of waste gases or noxious gases, e.g. exhaust gases in which combustion takes place in the presence of catalytic material
    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10KPURIFYING OR MODIFYING THE CHEMICAL COMPOSITION OF COMBUSTIBLE GASES CONTAINING CARBON MONOXIDE
    • C10K1/00Purifying combustible gases containing carbon monoxide
    • C10K1/08Purifying combustible gases containing carbon monoxide by washing with liquids; Reviving the used wash liquors
    • C10K1/10Purifying combustible gases containing carbon monoxide by washing with liquids; Reviving the used wash liquors with aqueous liquids
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G7/00Incinerators or other apparatus for consuming industrial waste, e.g. chemicals
    • F23G7/06Incinerators or other apparatus for consuming industrial waste, e.g. chemicals of waste gases or noxious gases, e.g. exhaust gases
    • F23G7/061Incinerators or other apparatus for consuming industrial waste, e.g. chemicals of waste gases or noxious gases, e.g. exhaust gases with supplementary heating
    • F23G7/065Incinerators or other apparatus for consuming industrial waste, e.g. chemicals of waste gases or noxious gases, e.g. exhaust gases with supplementary heating using gaseous or liquid fuel

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  • Engineering & Computer Science (AREA)
  • Chemical & Material Sciences (AREA)
  • Environmental & Geological Engineering (AREA)
  • Mechanical Engineering (AREA)
  • General Engineering & Computer Science (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Combustion & Propulsion (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • General Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Incineration Of Waste (AREA)
  • Exhaust Gas Treatment By Means Of Catalyst (AREA)
  • Catalysts (AREA)
  • Pre-Mixing And Non-Premixing Gas Burner (AREA)
  • Industrial Gases (AREA)
  • Treating Waste Gases (AREA)

Description

(54) PROCESS FOR THE DECOMPOSITION OF AMMONIA VAPOURS HAVING A HIGH CONTENT OF HYDROGEN SULPHIDE (71) We, FIRMA CARL STILL, a German Company, of 435 Recklinghausen, Postfach 1480, Germany, do hereby declare the invention, for which we pray that a patent may be granted to us, and the method by which it is to be performed, to be particularly described in and by the following state ment:- The invention relates to a process for the decomposition of ammonia vapours having a high content of hydrogen sulphide. The invention is especially but not exclusively applicable to deacidifier vapours from the NH3-H2S circulatory scrubbing of crude coke-oven ; the decomposition of gasses.
Processes fr the decomposition of deacidifier vapours are known, in which the vapours are heated by combustion of a heating medium with which the vapours are mixed, and the hot mixture is conveyed through a decomposition zone which may be empty or filled with packing material unaffected by temperature changes or with a catalyst of any type. In one process, the hot gases leaving the decomposition zone are completely combusted in a second stage by renewed addition of air.
It is also known - to Thtroduce into a decomposition zone vapours that are obtained without previous deaciditication by distillation from the gas scrubbing waters and condensates.
It is furthermore known to eliminate completely the entire amount of free ammonia in deacidifier vapours by combustion of the vapours in their entirety in- only one stage, wherein the combustion heat of the ammonia is obtained in the form of highly superheated steam, the condensate is separated off and the sulphur dioxide contained in the combustion gases is worked up to form sulphuric acid. With suitably restricted supply of air, it is thereby possible to obtain sulphur also in place of sulphuric acid.
The known processes for the two-stage combustion of the NH3 have the advantage that only traces of oxides of nitrogen are formed during the combustion of the NH3.
However, it has been shown that the twostage processes (when carried out not only thermally but also catalytically) lead to problems when the ammonia vapours to be decomposed have a high content of H25 as well as the HCN from the crude coke-oven gases. In this case, the H25 reacts, in the first stage of the combustion, with atmospheric oxygen to form elementary sulphur.
This amorphous sulphur settles not only in the direct condenser, which is connected after the waste-heat boiler of the decomposition stage, but is also carried by the decomposition stage, but is also carried by the decomposition gases into the subsequent gas pipes and apparatus, and deposits there as a pasty mass and leads to blockages. A small amount of the H3S is also oxidised further to form SO2 which dissolves in the condensates and also in cooling waters used in the circulation. These waters then take on an acid disposition and cause corrosion of the apparatus.
The task on which the invention is therefore based is to propose a method for the process defined at the beginning, in which the formation of elementary sulphur and the partial further oxidation to SO2 does not take place and therefore blockages and corrosions no longer occur.
The present invention provides a process for the decomposition of ammonia vapours containing hydrogen sulphide, in which gaseous fuel is burned by itself and the combustion gases therefrom are then mixed with the ammonia vapours to heat the latter, the hot mixture being conveyed through a decomposition zone. Advantageously, the mixture takes on a temperature in the range of from 1,000 to 1,200 C before it enters the decomposition zone.
Preferably, the decomposition zone - is filled with a catalyst, for example a nickel catalyst, for the ammonia decomposition.
However, as in the known process, it may alternatively be empty or filled with packing material unaffected by temperature changes.
Metallic nickel deposited on bodies, for example rings or balls, of magnesite or aluminium oxide as supports, have proved especially successful as catalyst.
If air is used for the combustion of the gaseous fuel, then a high discharge speed for the air from the port of any burner has a particularly favourable- effect; Air speeds in the range of from 6 to 12 m per second, especially 8 m per second, are advantageous.
It has also proved to be advantageous to the mixing of the combustion gases with the ammonia vapours to arrange a burner for the gaseous fuel and an inlet for the ammonia vapours at the head of the decomposition zone or of a decomposition reactor.
The gas stream is then forced, against its upward thrust, from top to bottom of the decomposition zone, which makes for a particularly intensive, thorough mixing.
When carrying out a process according to the invention on deacidifier vapours (which, compared with, say, distiller vapours have a higher content of H2S) the tendency to form organic sulphur compounds increases, As is known, the H2S from the deacidifier vapours reacts with the CO and CO2, which comes from the decomposition of the hydrogen cyanide contained in the deacidifier vapours and is contained in the combustion gases, to form COS and CS2. Water vapour in the reaction mixture promotes the decomposition of these substances and it has been shown to be an advantage to add water vapour to the gaseous fuel or to the air used for combustion or to both. COS and CS2 can, as is known, be eliminated from gases only by complex processes.Apart from this, by the addition of water vapour the tendency for carbon black to form is reduced.
A process in accordance with the invention is illustrated by way of the following comparative example.
1,250 m2n per hour of deacidifier vapours having a NH2 content of 20% by volume, a H2S content of 12% by volume and a HCN content of 2% by volume were mixed in accordance with a known process, with 375 m3n of cokeoven gas (Hu=4,300 Kcal/m3n), and the mixture was combusted with 1,000 m3n of air (deficiency relative to the total sum of combustible portions), the gas mixture taking on a temperature of 1,100"C. The gas mixture was passed over a nickel catalyst (metallic nickel on balls of inagnesiter, and then cooled in a direct condenser.There was still 0.1 g of NH2 per m3n present in the decomposition gas. 85 mg of elementary sulphur per litre were detected in the circulation of cooling water of the direct condenser, and the pH-valué of the cooling water dropped to 6. In addition to this, the decomposition gas contained 6 g of organic sulphur compounds {COS, CS2) per man.
After a few months' of operation, the plant had to be taken out of operation as the loss in pressure in the plant had become too high. During cleaning of the plant, pasty deposits, which had caused the loss in pressure, were found in the gas pipe behind the direct condenser. In addition to this, extensive visible corrosion had occurred.
92% of the dry substance obtained from the deposits consisted of elementary sulphur.
After these experiences, the operation was modified as follows: a water vapour content of 50% by volume was established in the air for combustion; a speed of 8 m per second was established for the mixture of air and water vapour at the burner ports the heating medium was first of all burned by itself and the deacidifier vapours contailing the NH2, HCN and H2S were mixed only thereafter with the combustion gases having a Iow content of oxygen. The mixture afterwards had a temperature of 1,100"C.
Further treatment was carried out as described above. In this case also, the composition gas still contained 0.1 g of NH2 per m3n. In the cooling water circulation no elementary sulphur could be detected and the pH value of the cooling water did not drop below 7. The content of organic sulphur compounds in the decomposition gas was 2 mg per m3n.
For putting the process into operation, apparatus comprising a special burner placed on the NH2 decomposition reactor, has proved particularly successful.
The present invention accordingly also provides apparatus for use in a process according to the present invention the apparatus comprising a burner having a fuel chamber which is connected to receive the gaseous fuel and through which pass a plurality of air distributor pipes from an air chamber which is connected to receive air for combustion of the gaseous fuel; the gaseous fuel chamber having a floor through which the distributor pipes pass and in which are formed bores for the passage of gaseous fuel, from the fuel chamber, for combustion; the wall of the fuel chamber projecting beyond the floor and the distributor pipes having ports lying within that projecting wall portion whereby air issuing from the ports mixes with gaseous fuel issuing from the bores in the fuel chamber floor, for combustion of the gaseous fuel; the burner having a casing which, with the wail of the fuel chamber, forms an annular space connected to supply the ammonia vapours for mixing with gases from the combustion of the gaseous fuel; the burner being located on the decomposition zone to supply thereto the hot mixture of ammonia vapours and combustion gases.
A burner for use in a process in accord ance- with the present invention will be described, by way of example, with reference to the accompanying drawings in which: Figure 1 illustrates a longitudinal crosssection through the burner.
Figure 2 is a cross-section through Figure 1 at the height of the line Il-Il.
Figure 3 illustrates the inclination of the ports of the air distributor pipes.
Figure 4 indicates the direction of the inclinations of the air distributor pipes of.
Figure 3.
Air for combustion flows into the burner through a connecting pipe 1 into an air chamber 2 having a circular cross-section, and is distributed to air distributor pipes 3 which are arranged in concentric circles and are firmly and tightly set into the separating floor 2a of the air chamber 2. The air flows through the pipes 3, which extend through a fuel gas chamber 4, likewise of circular cross-section, as far as their inclined ports 8. The arrows 9 indicate the direction of inclination and show that, in the outer circle of pipes, the ports 8 are directed inwardly.
The air distributor pipes 3 arranged on the inner circles have ports with inclinations alternately in a clockwise and anti-clockwise direction.
Coke-oven gas is introduced through a connecting pipe 5 into the space of the fuel gas chamber 4 remaining between the air distributor pipes 3, and leaves through circular bores 10, which may also be specially equipped, in the floor 10a of the fuel gas chamber 4. The coke-oven gas mixes with the air issuing from the ports 8 and is combusted.
The casing 3a of the fuel gas chamber 4 projects beyond the floor 10a by about 0.2 m, and is partially surrounded by a casing 7b which carries a fastening flange ring 3b and which, together with the outer wall 3a of the combustion chamber 4, forms a space 7 between the casings. Deacidifier vapours are introduced into this space 7 through a connecting pipe 6 and they leave at port 7a and are then on the periphery of the flame of the coke-oven gas.
Before entering the decomposition reactor (not shown) which is connected subsequently, the coke oven gas which is already combusted and contains only a little 02, is now intensively mixed with the deacidifier vapours from port 7a and the mixture, takes on a temperature of 1,100"C. In this state, the mixed gases are passed over the nickel catalyst in the decomposition zone.
WHAT WE CLAIM IS: 1. A process for the decomposition of ammonia vapours containing hydrogen sul - - phide, in which gaseous fuel is burned by itself and the combustion gases therefrom are then mixed with the ammonia vapours to heat the latter, the hot mixture being conveyed through a decomposition zone.
2. A process according to claim 1, in which the ammonia vapours containing hydrogen sulphide are deacidifier vapours from the NH3-H2S circulatory. scrubbing of crude coke-oven gas.
3. A process according to claim 1 or claim 2 in which the mixture enters the decomposition zone with a temperature in.
the range of from 1,000 to 1,200"C.
4. A process according to any one of claims 1 to 3, in which the decomposiXtion zone is filled with a catalyst for the ammonia decomposition.
5. A process according to claim 4, in which the catalyst is a nickel catalyst.
6. A process according to claim 4 or claim 5, in which metallic nickel deposited on bodies of magnesite or aluminium oxide is used as catalyst.
7. A process according to any one of claims 1 to 6, in which an air current flowing out of a burner port at a speed in the range of from 6 to 12 m per second is used for the combustion of the gaseous fuel.
8. A process according to claim 7, in which the current of air leaves the burner port at a speed of 8 m per second.
9. A process according to any one of claims 1 to 8, in which the combustion gases and the ammonia vapours are passed from top to bottom through the decomposition zone.
10. A process according to any one of claims 1 to 9, in which water vapour is added to the gaseous fuel or to air used for combustion of the gaseous fuel or to both.
11. Apparatus for use in a process according to any one of claims 1 to 10, comprising a burner having a fuel chamber which is connected to receive the gaseous fuel and through which pass a plurality of air distributor pipes from an air chamber which is connected to receive air for combustion of the gaseous fuel; the gaseous fuel chamber having a floor through which the distributor pipes pass and in which are formed bores for the passage of gaseous fuel, from the fuel chamber, for combustion; the wall of the fuel chamber projecting beyond the floor, and the distributor pipes having ports lying within that projecting wall portion whereby air issuing from the ports mixes with gaseous fuel issuing from the bores in the fuel chamber floor, for oom- bastion of the gaseous fuel; the burner having a casing which, with the wall of the fuel chamber, forms an annular space connected to supply the ammonia vapours for mixing with gases from the combustion of the gaseous fuel; the burner being located
**WARNING** end of DESC field may overlap start of CLMS **.

Claims (14)

**WARNING** start of CLMS field may overlap end of DESC **. the hot mixture of ammonia vapours and combustion gases. A burner for use in a process in accord ance- with the present invention will be described, by way of example, with reference to the accompanying drawings in which: Figure 1 illustrates a longitudinal crosssection through the burner. Figure 2 is a cross-section through Figure 1 at the height of the line Il-Il. Figure 3 illustrates the inclination of the ports of the air distributor pipes. Figure 4 indicates the direction of the inclinations of the air distributor pipes of. Figure 3. Air for combustion flows into the burner through a connecting pipe 1 into an air chamber 2 having a circular cross-section, and is distributed to air distributor pipes 3 which are arranged in concentric circles and are firmly and tightly set into the separating floor 2a of the air chamber 2. The air flows through the pipes 3, which extend through a fuel gas chamber 4, likewise of circular cross-section, as far as their inclined ports 8. The arrows 9 indicate the direction of inclination and show that, in the outer circle of pipes, the ports 8 are directed inwardly. The air distributor pipes 3 arranged on the inner circles have ports with inclinations alternately in a clockwise and anti-clockwise direction. Coke-oven gas is introduced through a connecting pipe 5 into the space of the fuel gas chamber 4 remaining between the air distributor pipes 3, and leaves through circular bores 10, which may also be specially equipped, in the floor 10a of the fuel gas chamber 4. The coke-oven gas mixes with the air issuing from the ports 8 and is combusted. The casing 3a of the fuel gas chamber 4 projects beyond the floor 10a by about 0.2 m, and is partially surrounded by a casing 7b which carries a fastening flange ring 3b and which, together with the outer wall 3a of the combustion chamber 4, forms a space 7 between the casings. Deacidifier vapours are introduced into this space 7 through a connecting pipe 6 and they leave at port 7a and are then on the periphery of the flame of the coke-oven gas. Before entering the decomposition reactor (not shown) which is connected subsequently, the coke oven gas which is already combusted and contains only a little 02, is now intensively mixed with the deacidifier vapours from port 7a and the mixture, takes on a temperature of 1,100"C. In this state, the mixed gases are passed over the nickel catalyst in the decomposition zone. WHAT WE CLAIM IS:
1. A process for the decomposition of ammonia vapours containing hydrogen sul - - phide, in which gaseous fuel is burned by itself and the combustion gases therefrom are then mixed with the ammonia vapours to heat the latter, the hot mixture being conveyed through a decomposition zone.
2. A process according to claim 1, in which the ammonia vapours containing hydrogen sulphide are deacidifier vapours from the NH3-H2S circulatory. scrubbing of crude coke-oven gas.
3. A process according to claim 1 or claim 2 in which the mixture enters the decomposition zone with a temperature in.
the range of from 1,000 to 1,200"C.
4. A process according to any one of claims 1 to 3, in which the decomposiXtion zone is filled with a catalyst for the ammonia decomposition.
5. A process according to claim 4, in which the catalyst is a nickel catalyst.
6. A process according to claim 4 or claim 5, in which metallic nickel deposited on bodies of magnesite or aluminium oxide is used as catalyst.
7. A process according to any one of claims 1 to 6, in which an air current flowing out of a burner port at a speed in the range of from 6 to 12 m per second is used for the combustion of the gaseous fuel.
8. A process according to claim 7, in which the current of air leaves the burner port at a speed of 8 m per second.
9. A process according to any one of claims 1 to 8, in which the combustion gases and the ammonia vapours are passed from top to bottom through the decomposition zone.
10. A process according to any one of claims 1 to 9, in which water vapour is added to the gaseous fuel or to air used for combustion of the gaseous fuel or to both.
11. Apparatus for use in a process according to any one of claims 1 to 10, comprising a burner having a fuel chamber which is connected to receive the gaseous fuel and through which pass a plurality of air distributor pipes from an air chamber which is connected to receive air for combustion of the gaseous fuel; the gaseous fuel chamber having a floor through which the distributor pipes pass and in which are formed bores for the passage of gaseous fuel, from the fuel chamber, for combustion; the wall of the fuel chamber projecting beyond the floor, and the distributor pipes having ports lying within that projecting wall portion whereby air issuing from the ports mixes with gaseous fuel issuing from the bores in the fuel chamber floor, for oom- bastion of the gaseous fuel; the burner having a casing which, with the wall of the fuel chamber, forms an annular space connected to supply the ammonia vapours for mixing with gases from the combustion of the gaseous fuel; the burner being located
on the decomposition zone to supply thereto the hot mixture of ammonia vapours and combustion gases.
12. Apparatus according to claim 11, in which the air chamber and the fuel chamber both having a circular cross-section and the air distributor pipes are arranged on concentric cirles, wherein the ports of the air distributor pipes arranged on the outer circle are inclined inwardly and those of the pipes arranged on the inner circles are inclined alternately in a clockwise direction and an anticlockwise direction.
13. A process according to any one of claims 1 to 10, substantially as herein described,
14. Apparatus for use in the decomposition of ammonia vapours, substantially as described herein with reference to, and as shown in, the accompanying drawings.
GB17086/77A 1976-04-24 1977-04-25 Process for the decomposition of ammonia vapours having a high content of hydrogen sulphide Expired GB1569639A (en)

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
DE2618027A DE2618027C2 (en) 1976-04-24 1976-04-24 Use of a burner for the decomposition of ammonia vapor containing hydrogen sulphide

Publications (1)

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GB1569639A true GB1569639A (en) 1980-06-18

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JP (1) JPS52130475A (en)
BE (1) BE853897A (en)
DE (1) DE2618027C2 (en)
ES (1) ES457960A1 (en)
FR (1) FR2348961A1 (en)
GB (1) GB1569639A (en)
IT (1) IT1075144B (en)
SE (1) SE434221B (en)

Families Citing this family (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
DE2920691C2 (en) * 1979-05-22 1986-08-07 Vereinigte Elektrizitätswerke Westfalen AG, 4600 Dortmund Process for the preparation of pollutant compounds
JP5700914B2 (en) * 2009-04-03 2015-04-15 光洋サーモシステム株式会社 Exhaust gas treatment apparatus and exhaust gas treatment equipment provided with the same
CN103398377A (en) * 2013-08-22 2013-11-20 重庆紫光新科化工开发有限公司 Tail gas burner and tail gas boiler as well as tail gas heat energy recovery method
CN111649343B (en) * 2020-06-22 2022-05-24 四川铭能科技开发有限公司 Efficient low-nitrogen VOC waste gas incinerator and incineration method

Family Cites Families (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
DE1202772B (en) * 1963-01-25 1965-10-14 Still Fa Carl Process for the incineration of the ammonia produced during the processing of coke oven or gas works
FR1601667A (en) * 1968-12-18 1970-09-07
DE1926629C3 (en) * 1969-05-24 1979-04-26 Guenter Dr. 4250 Bottrop Wunderlich Process for removing ammonia separated from coke oven gases and their condensates
DE2044813C3 (en) * 1970-09-10 1978-04-06 Ofu Ofenbau-Union Gmbh, 4000 Duesseldorf Gas burner with a large number of channels arranged in a burner nozzle made of refractory material for the supply of gas and air to the combustion participants
DE2218629C2 (en) * 1972-04-18 1982-10-21 Krupp-Koppers Gmbh, 4300 Essen Process for the incineration of Claus residual gas
DE2241891C3 (en) * 1972-08-25 1980-04-03 Didier-Engineering Gmbh, 4300 Essen Method and device for incinerating ammonia plumes resulting from the cleaning of coke oven gases
DE2410411C2 (en) * 1974-03-05 1981-12-10 Krupp-Koppers Gmbh, 4300 Essen Process for the elimination of ammonia, in particular coking ammonia
DE2537451C2 (en) * 1975-08-22 1987-05-27 Carl Still Gmbh & Co Kg, 4350 Recklinghausen Process for converting the ammonia contained in coke oven gases into nitrogen and water and the hydrogen sulfide into sulfur

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Publication number Publication date
SE434221B (en) 1984-07-16
FR2348961A1 (en) 1977-11-18
FR2348961B1 (en) 1982-05-07
IT1075144B (en) 1985-04-22
ES457960A1 (en) 1978-02-01
DE2618027C2 (en) 1982-06-09
JPS5520131B2 (en) 1980-05-31
BE853897A (en) 1977-10-24
JPS52130475A (en) 1977-11-01
DE2618027A1 (en) 1977-11-10
SE7704614L (en) 1977-10-25

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PS Patent sealed [section 19, patents act 1949]
PCNP Patent ceased through non-payment of renewal fee