WO2001021736A1 - Process to remove solid slag particles from a mixture of solid slag particles and water - Google Patents
Process to remove solid slag particles from a mixture of solid slag particles and water Download PDFInfo
- Publication number
- WO2001021736A1 WO2001021736A1 PCT/EP2000/009254 EP0009254W WO0121736A1 WO 2001021736 A1 WO2001021736 A1 WO 2001021736A1 EP 0009254 W EP0009254 W EP 0009254W WO 0121736 A1 WO0121736 A1 WO 0121736A1
- Authority
- WO
- WIPO (PCT)
- Prior art keywords
- vessel
- slag
- water
- process according
- slag particles
- 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.)
- Ceased
Links
Classifications
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10J—PRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
- C10J3/00—Production of combustible gases containing carbon monoxide from solid carbonaceous fuels
- C10J3/46—Gasification of granular or pulverulent flues in suspension
- C10J3/48—Apparatus; Plants
- C10J3/52—Ash-removing devices
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10J—PRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
- C10J3/00—Production of combustible gases containing carbon monoxide from solid carbonaceous fuels
- C10J3/72—Other features
- C10J3/82—Gas withdrawal means
- C10J3/84—Gas withdrawal means with means for removing dust or tar from the gas
-
- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10J—PRODUCTION OF PRODUCER GAS, WATER-GAS, SYNTHESIS GAS FROM SOLID CARBONACEOUS MATERIAL, OR MIXTURES CONTAINING THESE GASES; CARBURETTING AIR OR OTHER GASES
- C10J2300/00—Details of gasification processes
- C10J2300/16—Integration of gasification processes with another plant or parts within the plant
- C10J2300/1625—Integration of gasification processes with another plant or parts within the plant with solids treatment
Definitions
- the present invention is directed to a process to remove solid slag from a mixture of solid slag and water present in a quench zone, which quench zone is part of a process for the preparation of synthesis gas by partial combustion of finely dispersed solid carbon-containing fuel with an oxygen-containing gas.
- a problem of this sluicing procedure is that, when the valve between the lockhopper and the quench vessel is closed, the slag accumulating up-stream this valve has a tendency for bridging at the narrow space just above the said valve. It has appeared very difficult to have the slag to fall into the lockhopper after reconnecting the lockhopper to the gasification system.
- This problem is solved by the process disclosed in EP-A-290087, wherein a permanent nitrogen-gas bubble or nitrogen-gas cap is maintained in the lockhopper.
- One disadvantage is the need to install additional equipment to supply nitrogen and the associated costs of the nitrogen consumption during every sluicing cycle.
- a further disadvantage is that together with the discharged mixture an amount of sulphur compounds, of which hydrogen sulphide is the most prominent, and other dissolved components, for example ammonia, chloride and carbon monoxide, are also discharged.
- Hydrogen sulphide is formed in the reactor from sulphur containing compounds which are present in the hydrocarbon feed. Part of the hydrogen sulphide will dissolve in the water present in the slag quench vessel and will thus be discharged together with the slag in the above described process.
- the object of the present invention is a simple process to quickly separate solid slag particles from a quench zone, containing a mixture of said slag particles and water, such that no or very little sulphur containing compounds are being removed with the slag from the quench zone.
- the present process is directed to separate slag particles from a process for the preparation of synthesis gas by partial combustion of finely dispersed solid carbon-containing fuel with an oxygen-containing gas.
- carbon-containing fuel are coal, peat, wood, coke, for example petroleum coke, soot, carbon containing waste, biomass and mixtures of these. Mixtures of the aforementioned feedstocks and metal containing waste streams can also be used as feed.
- the ratio of volume of water poor in slag, which is extracted from the second vessel, relative to the volume of solids passing conduit from the first vessel to the second vessel in the same time period is preferably between 0.7 and 1.5 and more preferably between 0.8 and 1.
- the volume of liquid extracted from the second vessel and supplied to the first vessel is about the same as the volume of solids passing from the first to the second vessel due to gravity.
- the liquid in the connecting conduit between first and second vessel will then be kept close to stagnant. This situation further reduces any sulphur compounds from entering the second vessel.
- the mass flux of the slag particles in the connecting conduit between the first and second vessel is between 100-150 kg slag particles per square meter of the cross sectional area of the conduit or valve, whatever the smallest, per second (kg/m ⁇ /s) .
- a gradient in the concentration of sulphur compounds will be present, wherein the concentration of sulphur compounds in the first vessel will be lower than in the quench zone.
- This concentration gradient is especially achieved when the height over diameter ratio of the first vessel is greater than three.
- the water poor in slag extracted from the second vessel is fed to the lower end of the first vessel to further increase this concentration gradient. This concentration gradient is advantageous because it further reduces the chances of any sulphur compounds entering the second vessel.
- the volume of the first vessel is preferably of the same size or larger than the second vessel.
- the additional volume acts as buffer capacity for problem solving and in addition reduces the chances of any sulphur compounds entering the second vessel.
- When closing the first vessel from the second vessel in step (c) preferable no or very few slag particles will be present in the connecting conduit, thereby reducing the chance that slag particles obstruct the valve present in said conduit, thereby reducing the change on damaging the valve, and keeping the buffer capacity available to anticipate for problems that may rise.
- the second vessel is preferably not too small because this will result in a too high sluicing frequency, resulting in a poor capacity of the process.
- the volume of the first vessel is between 2 and 3 times the volume of the second vessel .
- the volume of the second vessel will be determined by the required capacity to remove slag particles.
- One skilled in the art can easily determine the optimal volume taken into account the required time to conduct steps (a) -(e) and the desire to minimise the size of the vessels
- the first vessel is also provided with means to discharge water poor in slag.
- This water can advantageously be used as medium to cool the quench zone by extracting heat form this stream against cooling water, cooling air or another medium. Also it may be advantageously to use this water to destroy and/or clean deposits formed on the surface of the water layer present in the quench zone and deposits present on the quench zone construction itself. It may be advantageous to bleed some of this stream to prevent building up of contaminants.
- the preferred position at which the water poor in slag is discharged from the first vessel is the same as discussed for the second vessel.
- the present process is very advantageous to be used in a situation wherein the pressure in the first vessel is higher than the pressure of the environment into which the separated solids are discharged to from the second vessel.
- the pressure in the quench zone and the associated first vessel in the process according the invention is typically between 20 and 60 bars, while the solids are normally discharged at about ambient pressure from the second vessel, sometimes referred to as lockhopper vessel.
- the Figure represents an apparatus for performing the above described preferred embodiment of the process according to the present invention.
- the apparatus comprises a first vessel (1), a second vessel (2), preferably positioned below the first vessel, and a first (3) and second (4) conduit fluidly connecting the first and second vessel.
- the first conduit (3) is preferably located such that slag particles in step (b) can move by gravity from the first vessel (1) to the second vessel (2).
- Second conduit (4) is provided with pumping means (5) to transport water poor in slag particles from the second vessel to the first vessel. Suitable means to pump a liquid are for example a gear pump, a lobe pump, a rotary pump, a centrifugal pump or a riser.
- the inlet of second conduit (4) is located such that water which is poor in slag particles is pumped from the second vessel (2) into the first vessel (1) . Slag particles entering second vessel (2) via conduit (3) will accumulate in the lower part of the second vessel resulting in that the upper part of the second vessel is poor in slag particles relative to the lower part.
- conduit (4) is therefore located in the upper part of the second vessel (2) and away from the outlet opening (8) of the first conduit (3) entering the second vessel (2) .
- a tubular shield (7) is present around the outlet (8) of conduit
- the second vessel is furthermore provided with an outlet opening (9) through which solid particles can be discharged and the first vessel is provided with an inlet opening (10) for receiving the mixture from the quench zone (14) .
- the opening (10) may optionally be provided with a slag grinder to break large slag particles before entering the first vessel. If no slag grinder is present the opening (10) will typically be larger than the opening in the conduit connecting the first (1) and second (2) vessel, thereby enabling a trouble free flow of slag particles into the first vessel (1) from the quench zone (14).
- the Figure also shows valves (11, 13) present in conduits (3) and (9) in order to operate the process in a sluice mode according to the present invention.
- valve (13) is in a open position to discharge the slag particles from the second vessel (2) .
- the Figure also shows a discharge zone (12) .
- the Figure also shows a conduit (15) through which water poor in slag can be removed from the first vessel and a tubular shield (16) which has the same functionality as shield (7) described in the second vessel .
- Example 1 In an experimental set-up as illustrated in Figure 2 vessel 1 was loaded with a mixture of water and 172 kg slag obtained from a coal gasification process having a density of 2335 kg/m ⁇ . Most slag particles were present at the bottom of vessel 1 near valve 11. Vessel 2 was loaded with clean water. After opening of valve 11, having a diameter of 10 cm, and after start-up of pump 5 a stable sluicing flow through the valve was observed. The pump flow rate was 15.5 litre/minute and the 172 kg of slag was sluiced out in 3.65 minutes. The ratio of volume of liquid which is transported from the second vessel to the first vessel via conduit (4) relative to the volume of solids passing conduit (3) in the same time period is in this example thus 0.75.
- Example 2 Example 2
- Example 1 was repeated except that the pump flow was 36.3 litre/minute. The same 172 kg of slag was sluiced out in 2.44 minutes. The ratio of volume of liquid which is transported from the second vessel to the first vessel via conduit (4) relative to the volume of solids passing conduit (3) in the same time period is in this example 1.18. Comparative experiment A
- Example 1 was repeated except that pump 5 was not used.
- the flow through valve 11 was very unstable and the experiment was repeated 15 times in order to obtain a reliable test result. On average it took the 172 kg of slag 5.6 minutes to pass valve 11.
Landscapes
- Chemical & Material Sciences (AREA)
- Engineering & Computer Science (AREA)
- Combustion & Propulsion (AREA)
- Oil, Petroleum & Natural Gas (AREA)
- Organic Chemistry (AREA)
- Processing Of Solid Wastes (AREA)
- Gasification And Melting Of Waste (AREA)
Abstract
Description
Claims
Priority Applications (4)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| US10/089,028 US6755980B1 (en) | 2000-09-20 | 2000-09-20 | Process to remove solid slag particles from a mixture of solid slag particles and water |
| EP00969277A EP1224246B1 (en) | 1999-09-21 | 2000-09-20 | Process to remove solid slag particles from a mixture of solid slag particles and water |
| AU79056/00A AU764501B2 (en) | 1999-09-21 | 2000-09-20 | Process to remove solid slag particles from a mixture of solid slag particles and water |
| DE60031875T DE60031875T2 (en) | 1999-09-21 | 2000-09-20 | METHOD FOR REMOVING FIXTURES FROM AN AQUEOUS MIXTURE |
Applications Claiming Priority (2)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| EP99307444 | 1999-09-21 | ||
| EP99307444.2 | 1999-09-21 |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| WO2001021736A1 true WO2001021736A1 (en) | 2001-03-29 |
Family
ID=8241629
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| PCT/EP2000/009254 Ceased WO2001021736A1 (en) | 1999-09-21 | 2000-09-20 | Process to remove solid slag particles from a mixture of solid slag particles and water |
Country Status (6)
| Country | Link |
|---|---|
| EP (1) | EP1224246B1 (en) |
| CN (1) | CN1220756C (en) |
| AU (1) | AU764501B2 (en) |
| DE (1) | DE60031875T2 (en) |
| ES (1) | ES2274808T3 (en) |
| WO (1) | WO2001021736A1 (en) |
Cited By (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| DE102006055050A1 (en) | 2006-11-22 | 2008-05-29 | Eos Gmbh Electro Optical Systems | Apparatus for layering a three-dimensional object and method for adjusting an optical system therefrom |
| WO2009092569A3 (en) * | 2008-01-24 | 2010-01-28 | Uhde Gmbh | Method and plant for removing accumulating slag from a slag bath |
| US8083815B2 (en) | 2008-12-22 | 2011-12-27 | Shell Oil Company | Process to prepare methanol and/or dimethylether |
| US8308983B2 (en) | 2008-10-08 | 2012-11-13 | Shell Oil Company | Process to prepare a gas mixture of hydrogen and carbon monoxide |
Families Citing this family (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US8349170B2 (en) * | 2008-05-14 | 2013-01-08 | Exxonmobil Research And Engineering Company | FCC reactor and riser design for short contact-time catalytic cracking of hydrocarbons |
| DE102008033095A1 (en) * | 2008-07-15 | 2010-01-28 | Uhde Gmbh | Apparatus for slag removal from a coal gasification reactor |
| DE102008035386A1 (en) | 2008-07-29 | 2010-02-11 | Uhde Gmbh | Slag discharge from reactor for syngas recovery |
Citations (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| GB2026145A (en) * | 1978-07-06 | 1980-01-30 | Ruhrchemie Ag | Sluicing of residues from the pressure system of a pressure gasification plant |
| GB2086931A (en) * | 1980-11-12 | 1982-05-19 | Texaco Development Corp | Ash removal and synthesis gas generation from coal |
| EP0113469A2 (en) * | 1983-01-10 | 1984-07-18 | Texaco Development Corporation | A method for removal of sour water from coal gasification slag |
| EP0290087A2 (en) * | 1987-05-05 | 1988-11-09 | Shell Internationale Researchmaatschappij B.V. | Process and apparatus for the preparation of synthesis gas |
| JPH10287886A (en) * | 1997-04-11 | 1998-10-27 | Babcock Hitachi Kk | Discharging method of slag and apparatus by using the same |
-
2000
- 2000-09-20 WO PCT/EP2000/009254 patent/WO2001021736A1/en not_active Ceased
- 2000-09-20 ES ES00969277T patent/ES2274808T3/en not_active Expired - Lifetime
- 2000-09-20 DE DE60031875T patent/DE60031875T2/en not_active Expired - Lifetime
- 2000-09-20 EP EP00969277A patent/EP1224246B1/en not_active Expired - Lifetime
- 2000-09-20 CN CN 00813191 patent/CN1220756C/en not_active Expired - Lifetime
- 2000-09-20 AU AU79056/00A patent/AU764501B2/en not_active Expired
Patent Citations (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| GB2026145A (en) * | 1978-07-06 | 1980-01-30 | Ruhrchemie Ag | Sluicing of residues from the pressure system of a pressure gasification plant |
| GB2086931A (en) * | 1980-11-12 | 1982-05-19 | Texaco Development Corp | Ash removal and synthesis gas generation from coal |
| EP0113469A2 (en) * | 1983-01-10 | 1984-07-18 | Texaco Development Corporation | A method for removal of sour water from coal gasification slag |
| EP0290087A2 (en) * | 1987-05-05 | 1988-11-09 | Shell Internationale Researchmaatschappij B.V. | Process and apparatus for the preparation of synthesis gas |
| JPH10287886A (en) * | 1997-04-11 | 1998-10-27 | Babcock Hitachi Kk | Discharging method of slag and apparatus by using the same |
Non-Patent Citations (1)
| Title |
|---|
| PATENT ABSTRACTS OF JAPAN vol. 1999, no. 01 29 January 1999 (1999-01-29) * |
Cited By (6)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| DE102006055050A1 (en) | 2006-11-22 | 2008-05-29 | Eos Gmbh Electro Optical Systems | Apparatus for layering a three-dimensional object and method for adjusting an optical system therefrom |
| WO2009092569A3 (en) * | 2008-01-24 | 2010-01-28 | Uhde Gmbh | Method and plant for removing accumulating slag from a slag bath |
| US8414780B2 (en) | 2008-01-24 | 2013-04-09 | Thyssenkrupp Uhde Gmbh | Method and system for removing slag, particularly slag that occurs during synthesis gas extraction, from a slag bath container |
| US8308983B2 (en) | 2008-10-08 | 2012-11-13 | Shell Oil Company | Process to prepare a gas mixture of hydrogen and carbon monoxide |
| US8470291B2 (en) | 2008-10-08 | 2013-06-25 | Shell Oil Company | Process to prepare a gas mixture of hydrogen and carbon monoxide |
| US8083815B2 (en) | 2008-12-22 | 2011-12-27 | Shell Oil Company | Process to prepare methanol and/or dimethylether |
Also Published As
| Publication number | Publication date |
|---|---|
| AU764501B2 (en) | 2003-08-21 |
| CN1376190A (en) | 2002-10-23 |
| EP1224246B1 (en) | 2006-11-15 |
| DE60031875T2 (en) | 2007-04-05 |
| AU7905600A (en) | 2001-04-24 |
| EP1224246A1 (en) | 2002-07-24 |
| DE60031875D1 (en) | 2006-12-28 |
| CN1220756C (en) | 2005-09-28 |
| ES2274808T3 (en) | 2007-06-01 |
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