WO2015086418A1 - Method for reprocessing gas condensate - Google Patents
Method for reprocessing gas condensate Download PDFInfo
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- WO2015086418A1 WO2015086418A1 PCT/EP2014/076488 EP2014076488W WO2015086418A1 WO 2015086418 A1 WO2015086418 A1 WO 2015086418A1 EP 2014076488 W EP2014076488 W EP 2014076488W WO 2015086418 A1 WO2015086418 A1 WO 2015086418A1
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- Prior art keywords
- gas condensate
- gas
- carried out
- absorption
- condensate
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Classifications
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10K—PURIFYING OR MODIFYING THE CHEMICAL COMPOSITION OF COMBUSTIBLE GASES CONTAINING CARBON MONOXIDE
- C10K1/00—Purifying combustible gases containing carbon monoxide
- C10K1/001—Purifying combustible gases containing carbon monoxide working-up the condensates
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F9/00—Multistage treatment of water, waste water or sewage
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10K—PURIFYING OR MODIFYING THE CHEMICAL COMPOSITION OF COMBUSTIBLE GASES CONTAINING CARBON MONOXIDE
- C10K1/00—Purifying combustible gases containing carbon monoxide
- C10K1/002—Removal of contaminants
- C10K1/003—Removal of contaminants of acid contaminants, e.g. acid gas removal
- C10K1/004—Sulfur containing contaminants, e.g. hydrogen sulfide
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10K—PURIFYING OR MODIFYING THE CHEMICAL COMPOSITION OF COMBUSTIBLE GASES CONTAINING CARBON MONOXIDE
- C10K1/00—Purifying combustible gases containing carbon monoxide
- C10K1/002—Removal of contaminants
- C10K1/003—Removal of contaminants of acid contaminants, e.g. acid gas removal
- C10K1/005—Carbon dioxide
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10K—PURIFYING OR MODIFYING THE CHEMICAL COMPOSITION OF COMBUSTIBLE GASES CONTAINING CARBON MONOXIDE
- C10K1/00—Purifying combustible gases containing carbon monoxide
- C10K1/04—Purifying combustible gases containing carbon monoxide by cooling to condense non-gaseous materials
- C10K1/046—Reducing the tar content
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/001—Processes for the treatment of water whereby the filtration technique is of importance
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/26—Treatment of water, waste water, or sewage by extraction
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/28—Treatment of water, waste water, or sewage by sorption
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/30—Organic compounds
- C02F2101/32—Hydrocarbons, e.g. oil
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/30—Organic compounds
- C02F2101/34—Organic compounds containing oxygen
- C02F2101/345—Phenols
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/30—Organic compounds
- C02F2101/40—Organic compounds containing sulfur
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2103/00—Nature of the water, waste water, sewage or sludge to be treated
- C02F2103/34—Nature of the water, waste water, sewage or sludge to be treated from industrial activities not provided for in groups C02F2103/12 - C02F2103/32
- C02F2103/36—Nature of the water, waste water, sewage or sludge to be treated from industrial activities not provided for in groups C02F2103/12 - C02F2103/32 from the manufacture of organic compounds
- C02F2103/365—Nature of the water, waste water, sewage or sludge to be treated from industrial activities not provided for in groups C02F2103/12 - C02F2103/32 from the manufacture of organic compounds from petrochemical industry (e.g. refineries)
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2301/00—General aspects of water treatment
- C02F2301/06—Pressure conditions
- C02F2301/066—Overpressure, high pressure
Definitions
- This invention relates to a method for reprocessing a gas condensate which has been separated from raw synthesis gas produced by gasification of coke or coal in a fixed-bed pressure gasification reactor, for the further treatment, comprising the following method steps carried out one after the other:
- solid fuel such as coal, coke or other carbonaceous fuel
- a synthesis gas containing carbon monoxide and hydrogen wherein a solid ash is obtained, which is discharged from the reactor via an ash discharge grate which in many cases is formed as rotary grate.
- FBDB Fixed Bed Dry Bottom
- the gas condensate Before the gas condensate can be disposed of as waste water in a biological clarification plant, it must be reprocessed for reasons of environmental protection. In doing so, oils, tar and dust as well as phenols, ammonia and a so-called sour gas chiefly consisting of carbon dioxide and hydrogen sulfide are separated from the gas condensate.
- the separation of the phenols is carried out.
- This can be effected by an extraction process, such as the Lurgi Phenosolvan process, cf. Ullmann's Encyclopedia of Industrial Chemistry, Sixth Edition, Vol. 15, p. 433.
- the use of extractors of the mixer-settler type has proved successful.
- extracting agent diisopropyl ether frequently is used, and alternatively butyl acetate and methylisobutyl ketone can also be used.
- the Phenosolvan process proceeds continuously, with the extracting agent being circulated. It is liberated from its phenol load by distillation. After passing through the extraction step, the gas condensate as refined product is liberated from extracting agent residues by stripping e.g. with oxygen.
- the extraction of the phenols i.e. phenols passing over from the gas condensate into the extracting agent, is effected the more effectively the smaller the degree of dissociation of the phenols in the gas condensate. Since phenols react acidic in aqueous solution, but due to its ammonia content the gas condensate has a basic pH value of typically 9 to 10, the degree of dissociation of the phenols is comparatively high, whereby the effectiveness of the extraction is reduced. To effectively carry out the extraction of the phenols, the pH value of the gas condensate must be adjusted to a suitable value in dependence on the extracting agent used.
- step (d) separation of ammonia and, separately, of a sour gas chiefly consisting of H 2 S and C0 2 in a physical way, and at least partly recirculating the sour gas for use in step (b);
- step (b) characterized in that the absorption in step (b) is carried out under elevated pressure and the gas condensate subsequently is depressurized to the pressure existing in the extraction of step (b).
- the absorption of the sour gas is carried out under overpressure, as under this condition the absorption of gases such as C0 2 and H 2 S in the gas condensate is effected more quickly, whereby a shorter residence time and hence a smaller overall size of the absorption means is required.
- absorption columns have proved successful, which if necessary can be equipped with internal fittings and/or packings, in order to intensify the contact between the gas condensate and the sour gas.
- the gas condensate After performing the absorption, the gas condensate is depressurized to the pressure at which the extraction is carried out.
- the extraction frequently is carried out at atmospheric pressure.
- the depressurization can be carried out either in a separate tank or in the first fixing chamber of the mixer-settler in flow direction of the gas condensate. With the depressurization in the mixer-settler, the separate expansion tank is saved. It is, however, only possible when the gas evolution during the depressurization is limited such that the operation of the mixer-settler is not impaired.
- the pH value of the gas condensate is at least 6.5 and not more than 8.5 or most preferably at least 7.8 and not more than 8.2.
- the pH value is large enough to keep the acid corrosion on apparatuses and pipe conduits low.
- Another advantageous aspect of the invention consists in using diisopropyl ether or alternatively butyl acetate or methylisobutyl ketone as solvents for the extraction of the phenols.
- Fig. 1 shows an exemplary method flow diagram of the inventive reprocessing of gas condensate separated from synthesis gas produced in a fixed-bed pressure gasification reactor for the treatment in a biological clarification plant.
- the gas condensate 1 separated from the raw synthesis gas in a condensation means downstream of a fixed-bed pressure gasification reactor, cooled to 80 °C and depressurized to ambient pressure is introduced into a settling tank 2 referred to as tar separator.
- a settling tank 2 referred to as tar separator.
- an oil phase 3 and a tar and dust phase 4 here are separated from the gas condensate 1 .
- the gas condensate 5 prepurified in this way is introduced into a filter system 6, in which a residual phase 7 consisting of fine dust particles, oil and tar is separated from the gas condensate.
- the gas condensate 8 then is introduced into a pressure increasing means 9 and brought to a pressure of 5 bar.
- the gas condensate 10 treated in this way is introduced into an absorption means 1 1 in which it is brought in contact with sour gas 12. As absorption means, an absorption column is used.
- the sour gas 12 chiefly consisting of carbon dioxide and hydrogen sulfide for one part is absorbed by the gas condensate 10, for the other part 13 discharged from the absorption means, and supplied to the further treatment (not shown). Due to the absorption of the sour gas, the pH value of the gas condensate is lowered from 9 to 8.
- the gas condensate 14 treated in this way is introduced into a depressurizing means 15. Here, it is depressurized to atmospheric pressure, at which the succeeding phenol extraction is carried out in the mixer-settler.
- the gas 16 released during depressurization is supplied to the waste disposal (not shown).
- the gas condensate 17 treated in this way subsequently is introduced into an extraction plant 18 for separating the phenols.
- the gas condensate is brought in contact with a suitable extracting agent, with the phenols passing over from the gas condensate into the extracting agent.
- the extraction is carried out in an extraction plant of the mixer-settler type.
- extracting agent diisopropyl ether is used.
- the phenols are absorbed the better by the extracting agent used, the less they are dissociated, which is why the degree of dissociation of the phenols has been reduced by the preceding decrease of the pH value.
- a phenol phase 19 is separated from the extracting agent by distillation and passed over to the further treatment (not shown).
- extracting agent residues are separated from the gas condensate liberated from phenols and added to the extracting agent circulating within the extraction plant 18.
- the dephenolized gas condensate 20 then is passed over to a plant 21 operating by the CLL process, for separating ammonia and sour gas.
- a plant 21 operating by the CLL process, for separating ammonia and sour gas.
- first ammonia and then the so-called sour gas 23 chiefly consisting of carbon dioxide and hydrogen sulfide is stripped out of the gas condensate at atmospheric pressure by means of steam in separate steps.
- the separated ammonia 22 is passed over to the further treatment (not shown).
- the gas condensate 24 now is reprocessed to such an extent that it can be transferred into a biological clarification plant (not shown).
- the sour gas 23 leaves the CLL plant 21 with 4 bar and in a pressure increasing means 25 is brought to the pressure existing in the absorption means 1 1 , in this case 5 bar, and introduced into the absorption means 1 1 as sour gas stream 12, in order to lower the pH value of the gas condensate.
- the invention improves the economy of the method for reprocessing gas condensate in that it provides for smaller overall sizes for the absorption means serving for the absorption of sour gas, and hence for the adjustment of the pH value.
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- Chemical & Material Sciences (AREA)
- Engineering & Computer Science (AREA)
- Combustion & Propulsion (AREA)
- Organic Chemistry (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Oil, Petroleum & Natural Gas (AREA)
- General Chemical & Material Sciences (AREA)
- Life Sciences & Earth Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Industrial Gases (AREA)
- Organic Low-Molecular-Weight Compounds And Preparation Thereof (AREA)
Abstract
A method for reprocessing a gas condensate which has been separated from raw synthesis gas produced by gasification of coke or coal in a fixed-bed pressure gasification reactor, for the further treatment, comprising the following method steps carried out one after the other: - separation of oils and tar by mechanical methods, - adjustment of the pH value of the gas condensate by absorption of sour gas obtained process-internally, - extraction of the phenols from the gas condensate by a solvent, - separation of ammonia and, separately, of a sour gas chiefly consisting of H2S and C02 in a physical way, wherein the absorption of the sour gas is carried out under elevated pressure and the gas condensate subsequently is depressurized to the pressure existing in the extraction.
Description
Method for Reprocessing Gas Condensate
Field of the Invention
This invention relates to a method for reprocessing a gas condensate which has been separated from raw synthesis gas produced by gasification of coke or coal in a fixed-bed pressure gasification reactor, for the further treatment, comprising the following method steps carried out one after the other:
- separation of oils, tar and dust by mechanical methods,
- adjustment of the pH value of the gas condensate
- extraction of the phenols from the gas condensate by a solvent,
- separation of ammonia and, separately, of a sour gas chiefly consisting of H2S and C02 in a physical way.
Prior art
By means of fixed-bed pressure gasification reactors solid fuel, such as coal, coke or other carbonaceous fuel, is gasified with steam and oxygen as gasification medium at elevated temperature and, in most cases, under overpressure to obtain a synthesis gas containing carbon monoxide and hydrogen, wherein a solid ash is obtained, which is discharged from the reactor via an ash discharge grate which in many cases is formed as rotary grate. This type of reactor frequently also is referred to as FBDB (= Fixed Bed Dry Bottom) pressure gasifier.
When cooling synthesis gas obtained by the gasification of carbonaceous solids, a carbonaceous waste water referred to as gas condensate is obtained. Before the gas condensate can be disposed of as waste water in a biological clarification plant, it must be reprocessed for reasons of environmental protection. In doing so, oils, tar and dust as well as phenols, ammonia and a so-called sour gas chiefly consisting of carbon dioxide and hydrogen sulfide are separated from the gas condensate.
When reprocessing the gas condensate, solids such as tar and dust as well as oil first are separated mechanically. The greatest part of these constituents is separated in a settling tank called tar separator by mechanical separation methods, for example by sedimentation. Fine cleaning subsequently is effected by filtration, cf. Ullmann's Encyclopedia of Industrial Chemistry, Sixth Edition, Vol. 15, p. 369 and p. 437, Fig. 75.
As next reprocessing step the separation of the phenols is carried out. This can be effected by an extraction process, such as the Lurgi Phenosolvan process, cf. Ullmann's Encyclopedia of Industrial Chemistry, Sixth Edition, Vol. 15, p. 433. The use of extractors of the mixer-settler type has proved successful. As extracting agent diisopropyl ether frequently is used, and alternatively butyl acetate and methylisobutyl ketone can also be used.
The Phenosolvan process proceeds continuously, with the extracting agent being circulated. It is liberated from its phenol load by distillation. After passing through the extraction step, the gas condensate as refined product is liberated from extracting agent residues by stripping e.g. with oxygen.
The extraction of the phenols, i.e. phenols passing over from the gas condensate into the extracting agent, is effected the more effectively the smaller the degree of dissociation of the phenols in the gas condensate. Since phenols react acidic in aqueous solution, but due to its ammonia content the gas condensate has a basic pH value of typically 9 to 10, the degree of dissociation of the phenols is
comparatively high, whereby the effectiveness of the extraction is reduced. To effectively carry out the extraction of the phenols, the pH value of the gas condensate must be adjusted to a suitable value in dependence on the extracting agent used.
From the Chinese Patent Applications CN 102241453 A and CN 102674608 A it is known that lowering the pH value of the gas condensate can be effected by absorption of sour gas. Since this absorption is a process proceeding slowly, large and hence expensive tanks, such as absorption columns of correspondingly large design, are required.
After the separation of the phenols, hydrogen sulfide, carbon dioxide and ammonia still are to be separated from the gas condensate. For this task, for example, the so-called Chemie Linz-Lurgi (CLL) process can be used, cf. Ullmann's Encyclopedia of Industrial Chemistry, Sixth Edition, Vol. 15, p. 435. The separation here is effected in a physical way, by stripping with steam, and by distillation. In one process step, hydrogen sulfide and carbon dioxide are jointly removed by distillation, as so-called sour gas. In a separate process step, ammonia is separated from the gas condensate by distillation and stripping.
It is the object of the present invention to provide an improved method for separating phenols, sour gas and ammonia from gas condensate, which can do with small dimensions of the pipe conduits and apparatuses used, whereby the investment costs are kept low.
Description of the Invention
This object is solved by a method for reprocessing a gas condensate which has been separated from raw synthesis gas produced by gasification of coke or coal in a fixed-bed pressure gasification reactor, for the further treatment, comprising the following method steps carried out one after the other:
(a) separation of oils and tar by mechanical methods,
(b) adjustment of the pH value of the gas condensate by absorption of sour gas separated from the gas condensate in step (d),
(c) extraction of the phenols from the gas condensate,
(d) separation of ammonia and, separately, of a sour gas chiefly consisting of H2S and C02 in a physical way, and at least partly recirculating the sour gas for use in step (b);
characterized in that the absorption in step (b) is carried out under elevated pressure and the gas condensate subsequently is depressurized to the pressure existing in the extraction of step (b).
According to the invention, the absorption of the sour gas is carried out under overpressure, as under this condition the absorption of gases such as C02 and H2S in the gas condensate is effected more quickly, whereby a shorter residence time and hence a smaller overall size of the absorption means is required.
Preferred Aspects of the Invention
As absorption means absorption columns have proved successful, which if necessary can be equipped with internal fittings and/or packings, in order to intensify the contact between the gas condensate and the sour gas.
After performing the absorption, the gas condensate is depressurized to the pressure at which the extraction is carried out. The extraction frequently is carried out at atmospheric pressure. The depressurization can be carried out either in a separate tank or in the first fixing chamber of the mixer-settler in flow direction of the gas condensate. With the depressurization in the mixer-settler, the separate expansion tank is saved. It is, however, only possible when the gas evolution during the depressurization is limited such that the operation of the mixer-settler is not impaired.
It is particularly advantageous when the absorption is carried out in the pressure range of 1 .5 to 10 bar. This range constitutes the optimum compromise between
the increased effectiveness of the absorption due to the overpressure and the equipment expenditure for pressure increase.
For the effectiveness of the phenol extraction process it is particularly advantageous to adjust the pH value of the gas condensate by means of the absorption of the sour gas such that after the depressurization it preferably is at least 6.5 and not more than 8.5 or most preferably at least 7.8 and not more than 8.2. In these preferred or most preferred ranges, by far the largest part of the phenols is neutralized and thus can be removed from the gas condensate with high effectiveness by the downstream phenol removal process. On the other hand, the pH value is large enough to keep the acid corrosion on apparatuses and pipe conduits low.
Another advantageous aspect of the invention consists in using diisopropyl ether or alternatively butyl acetate or methylisobutyl ketone as solvents for the extraction of the phenols.
Exemplary Embodiments
Further developments, advantages and possible applications of the invention can also be taken from the following description of non-limiting exemplary embodiments and numerical examples as well as the drawing. All features described and/or illustrated form the invention per se or in any combination, independent of their inclusion in the claims or their back-reference. With reference to the drawing, Fig. 1 , the invention will now be explained in detail.
Fig. 1 shows an exemplary method flow diagram of the inventive reprocessing of gas condensate separated from synthesis gas produced in a fixed-bed pressure gasification reactor for the treatment in a biological clarification plant.
The gas condensate 1 separated from the raw synthesis gas in a condensation means downstream of a fixed-bed pressure gasification reactor, cooled to 80 °C
and depressurized to ambient pressure is introduced into a settling tank 2 referred to as tar separator. By phase separation and sedimentation, an oil phase 3 and a tar and dust phase 4 here are separated from the gas condensate 1 . The gas condensate 5 prepurified in this way is introduced into a filter system 6, in which a residual phase 7 consisting of fine dust particles, oil and tar is separated from the gas condensate. The gas condensate 8 then is introduced into a pressure increasing means 9 and brought to a pressure of 5 bar. The gas condensate 10 treated in this way is introduced into an absorption means 1 1 in which it is brought in contact with sour gas 12. As absorption means, an absorption column is used.
The sour gas 12 chiefly consisting of carbon dioxide and hydrogen sulfide for one part is absorbed by the gas condensate 10, for the other part 13 discharged from the absorption means, and supplied to the further treatment (not shown). Due to the absorption of the sour gas, the pH value of the gas condensate is lowered from 9 to 8. The gas condensate 14 treated in this way is introduced into a depressurizing means 15. Here, it is depressurized to atmospheric pressure, at which the succeeding phenol extraction is carried out in the mixer-settler. The gas 16 released during depressurization is supplied to the waste disposal (not shown). The gas condensate 17 treated in this way subsequently is introduced into an extraction plant 18 for separating the phenols. Here, the gas condensate is brought in contact with a suitable extracting agent, with the phenols passing over from the gas condensate into the extracting agent. The extraction is carried out in an extraction plant of the mixer-settler type. As extracting agent diisopropyl ether is used. The phenols are absorbed the better by the extracting agent used, the less they are dissociated, which is why the degree of dissociation of the phenols has been reduced by the preceding decrease of the pH value. Within the extraction plant 18 a phenol phase 19 is separated from the extracting agent by distillation and passed over to the further treatment (not shown). Within the extraction plant 18, by stripping with nitrogen, extracting agent residues are separated from the gas condensate liberated from phenols and added to the extracting agent circulating within the extraction plant 18.
The dephenolized gas condensate 20 then is passed over to a plant 21 operating by the CLL process, for separating ammonia and sour gas. Here, first ammonia and then the so-called sour gas 23 chiefly consisting of carbon dioxide and hydrogen sulfide is stripped out of the gas condensate at atmospheric pressure by means of steam in separate steps. The separated ammonia 22 is passed over to the further treatment (not shown). The gas condensate 24 now is reprocessed to such an extent that it can be transferred into a biological clarification plant (not shown). The sour gas 23 leaves the CLL plant 21 with 4 bar and in a pressure increasing means 25 is brought to the pressure existing in the absorption means 1 1 , in this case 5 bar, and introduced into the absorption means 1 1 as sour gas stream 12, in order to lower the pH value of the gas condensate.
Industrial Applicability
The invention improves the economy of the method for reprocessing gas condensate in that it provides for smaller overall sizes for the absorption means serving for the absorption of sour gas, and hence for the adjustment of the pH value.
List of Reference Numerals
1 gas condensate
2 settling tank
3 oil phase
4 tar and dust phase
5 gas condensate
6 filter system
7 tar and dust phase
8 gas condensate
9 pressure increasing means
10 gas condensate
1 1 absorption means
12 sour gas
13 sour gas
14 gas condensate
15 depressurizing means
16 sour gas
17 gas condensate
18 extraction plant for phenol separation
19 phenol phase
20 gas condensate
21 plant for separating ammonia and sour gas (CLL process)
22 ammonia
23 sour gas
24 gas condensate
25 pressure increasing means
Claims
1 . A method for reprocessing a gas condensate which has been separated from raw synthesis gas produced by gasification of coke or coal in a fixed-bed pressure gasification reactor, for the further treatment, comprising the following method steps carried out one after the other:
(a) separation of oils and tar by mechanical methods,
(b) adjustment of the pH value of the gas condensate by absorption of sour gas separated from the gas condensate in step (d),
(c) extraction of the phenols from the gas condensate,
(d) separation of ammonia and, separately, of a sour gas chiefly consisting of H2S and C02 in a physical way and at least partly recirculating the sour gas for use in step (b);
characterized in that the absorption in step (b) is carried out under elevated pressure and the gas condensate subsequently is depressurized to the pressure existing in the extraction of step (b).
2. The method according to claim 1 , characterized in that the absorption carried out in step (b) of claim 1 is carried out in an absorption column.
3. The method according to any of the preceding claims, characterized in that the depressurization of the gas condensate is carried out in a separate expansion tank.
4. The method according to any of the preceding claims, characterized in that for carrying out the extraction in step (c) a mixer-settler comprising at least one mixing chamber is used.
5. The method according to any of the preceding claims, characterized in that the depressurization of the gas condensate is carried out in the first mixing chamber of the mixer-settler in flow direction of the gas condensate.
6. The method according to any of the preceding claims, characterized in that the absorption in step (b) is carried out at a pressure of at least 1 .5 and not more than 10 bar.
7. The method according to any of the preceding claims, characterized in that after the depressurization the pH value of the gas condensate is at least 6.5 and not more than 8.5.
8. The method according to any of the preceding claims, characterized in that after the depressurization the pH value of the gas condensate is at least 7.8 and not more than 8.2.
9. The method according to any of the preceding claims, characterized in that as extracting agent in step (c) of claim 1 there is alternatively used diisopropyl ether, butyl acetate or methylisobutyl ketone.
Applications Claiming Priority (2)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| DE102013114002 | 2013-12-13 | ||
| DE102013114002.5 | 2013-12-13 |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| WO2015086418A1 true WO2015086418A1 (en) | 2015-06-18 |
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Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| PCT/EP2014/076488 Ceased WO2015086418A1 (en) | 2013-12-13 | 2014-12-04 | Method for reprocessing gas condensate |
Country Status (1)
| Country | Link |
|---|---|
| WO (1) | WO2015086418A1 (en) |
Cited By (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN105668678A (en) * | 2016-03-31 | 2016-06-15 | 陕西煤业化工集团神木天元化工有限公司 | Wastewater pretreatment system, wastewater treatment system and wastewater treatment method |
| CN108659892A (en) * | 2017-03-28 | 2018-10-16 | 上海宝钢化工有限公司 | Coke oven gas blast condensation area tank waste gas recovery system and recovery method |
| CN108773979A (en) * | 2018-06-28 | 2018-11-09 | 上海力脉环保设备有限公司 | A kind of Environmentally-frielow-energy-consumptipolycarboxylic low-energy-consumptipolycarboxylic tar refining processing method of sodium sulfate wastewater containing phenol |
| CN109942136A (en) * | 2019-04-16 | 2019-06-28 | 河北丰源环保科技股份有限公司 | The processing system and technique of UTILIZATION OF VESIDUAL HEAT IN after the gas-fired of a kind of pair of semi-coke wastewater and coal gas power plant |
Citations (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US3711402A (en) * | 1971-05-13 | 1973-01-16 | Air Liquide | Process for the treatment of phenolated industrial effluent |
| US4097539A (en) * | 1973-12-28 | 1978-06-27 | Metallgesellschaft Aktiengesellschaft | Process of scrubbing polyhydroxy phenols from gas |
| CN102241453A (en) * | 2010-09-25 | 2011-11-16 | 仲恺农业工程学院 | Method for treating coal gasification wastewater containing phenol and ammonia |
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|---|---|---|---|---|
| US3711402A (en) * | 1971-05-13 | 1973-01-16 | Air Liquide | Process for the treatment of phenolated industrial effluent |
| US4097539A (en) * | 1973-12-28 | 1978-06-27 | Metallgesellschaft Aktiengesellschaft | Process of scrubbing polyhydroxy phenols from gas |
| CN102241453A (en) * | 2010-09-25 | 2011-11-16 | 仲恺农业工程学院 | Method for treating coal gasification wastewater containing phenol and ammonia |
Cited By (6)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN105668678A (en) * | 2016-03-31 | 2016-06-15 | 陕西煤业化工集团神木天元化工有限公司 | Wastewater pretreatment system, wastewater treatment system and wastewater treatment method |
| CN108659892A (en) * | 2017-03-28 | 2018-10-16 | 上海宝钢化工有限公司 | Coke oven gas blast condensation area tank waste gas recovery system and recovery method |
| CN108659892B (en) * | 2017-03-28 | 2020-12-08 | 宝武炭材料科技有限公司 | Coke oven gas blast condensation area tank waste gas recovery system and recovery method |
| CN108773979A (en) * | 2018-06-28 | 2018-11-09 | 上海力脉环保设备有限公司 | A kind of Environmentally-frielow-energy-consumptipolycarboxylic low-energy-consumptipolycarboxylic tar refining processing method of sodium sulfate wastewater containing phenol |
| CN108773979B (en) * | 2018-06-28 | 2021-06-29 | 上海力脉环保设备有限公司 | Environment-friendly low-energy-consumption treatment method for wastewater containing sodium phenolate refined from tar |
| CN109942136A (en) * | 2019-04-16 | 2019-06-28 | 河北丰源环保科技股份有限公司 | The processing system and technique of UTILIZATION OF VESIDUAL HEAT IN after the gas-fired of a kind of pair of semi-coke wastewater and coal gas power plant |
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