WO2006079931A1 - Vessel flushing system - Google Patents
Vessel flushing system Download PDFInfo
- Publication number
- WO2006079931A1 WO2006079931A1 PCT/IB2006/000685 IB2006000685W WO2006079931A1 WO 2006079931 A1 WO2006079931 A1 WO 2006079931A1 IB 2006000685 W IB2006000685 W IB 2006000685W WO 2006079931 A1 WO2006079931 A1 WO 2006079931A1
- Authority
- WO
- WIPO (PCT)
- Prior art keywords
- vessel
- nozzles
- base
- flushing system
- flow
- Prior art date
Links
- 238000011010 flushing procedure Methods 0.000 title claims abstract description 42
- 239000007787 solid Substances 0.000 claims abstract description 56
- 239000002245 particle Substances 0.000 claims abstract description 34
- 239000012530 fluid Substances 0.000 claims abstract description 31
- 238000000034 method Methods 0.000 claims description 37
- 239000007921 spray Substances 0.000 claims description 31
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 46
- 239000004576 sand Substances 0.000 description 45
- 238000005243 fluidization Methods 0.000 description 16
- 239000002002 slurry Substances 0.000 description 14
- 238000002474 experimental method Methods 0.000 description 9
- 238000013461 design Methods 0.000 description 5
- 239000000203 mixture Substances 0.000 description 4
- 238000012360 testing method Methods 0.000 description 4
- 230000000694 effects Effects 0.000 description 3
- 238000005406 washing Methods 0.000 description 3
- LYCAIKOWRPUZTN-UHFFFAOYSA-N Ethylene glycol Chemical compound OCCO LYCAIKOWRPUZTN-UHFFFAOYSA-N 0.000 description 2
- 238000004140 cleaning Methods 0.000 description 2
- 238000006073 displacement reaction Methods 0.000 description 2
- 238000004519 manufacturing process Methods 0.000 description 2
- 239000003921 oil Substances 0.000 description 2
- 230000002093 peripheral effect Effects 0.000 description 2
- 239000004215 Carbon black (E152) Substances 0.000 description 1
- 101000793686 Homo sapiens Azurocidin Proteins 0.000 description 1
- 230000000903 blocking effect Effects 0.000 description 1
- 230000002301 combined effect Effects 0.000 description 1
- 230000001627 detrimental effect Effects 0.000 description 1
- 238000011038 discontinuous diafiltration by volume reduction Methods 0.000 description 1
- 239000013505 freshwater Substances 0.000 description 1
- 229930195733 hydrocarbon Natural products 0.000 description 1
- 150000002430 hydrocarbons Chemical class 0.000 description 1
- 239000003112 inhibitor Substances 0.000 description 1
- 239000007788 liquid Substances 0.000 description 1
- 238000012545 processing Methods 0.000 description 1
- 235000013580 sausages Nutrition 0.000 description 1
- 238000003860 storage Methods 0.000 description 1
- 238000009827 uniform distribution Methods 0.000 description 1
Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B08—CLEANING
- B08B—CLEANING IN GENERAL; PREVENTION OF FOULING IN GENERAL
- B08B9/00—Cleaning hollow articles by methods or apparatus specially adapted thereto
- B08B9/08—Cleaning containers, e.g. tanks
- B08B9/093—Cleaning containers, e.g. tanks by the force of jets or sprays
- B08B9/0933—Removing sludge or the like from tank bottoms
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01F—MIXING, e.g. DISSOLVING, EMULSIFYING OR DISPERSING
- B01F25/00—Flow mixers; Mixers for falling materials, e.g. solid particles
- B01F25/20—Jet mixers, i.e. mixers using high-speed fluid streams
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B08—CLEANING
- B08B—CLEANING IN GENERAL; PREVENTION OF FOULING IN GENERAL
- B08B9/00—Cleaning hollow articles by methods or apparatus specially adapted thereto
- B08B9/08—Cleaning containers, e.g. tanks
- B08B9/093—Cleaning containers, e.g. tanks by the force of jets or sprays
Definitions
- the present invention relates to an apparatus and method for flushing solids in a vessel such as an accumulator vessel or flush tank.
- Accumulator vessels may be used for collection of solids, for example, in process plant where solids are separated from fluids. Examples include: a flushing system used in a hydrocarbon or produced water desander assembly; a sand washing system; solids cleaning as used in oil and gas well production and processes for recovering a hydrate inhibitor such as monoethylene glycol (MEG).
- a flushing system used in a hydrocarbon or produced water desander assembly
- a sand washing system solids cleaning as used in oil and gas well production and processes for recovering a hydrate inhibitor such as monoethylene glycol (MEG).
- solids e.g. sand
- Another similar operation where solids may be separated and removed is a solids cleaning system.
- solid particles e.g. sand
- the accumulated solids need to be removed from the vessel, either continuously or periodically in a batch emptying procedure, through an opening, which is usually located at the bottom of the vessel.
- a flushing system for an accumulator vessel comprising a plurality of nozzles disposed at intervals around a perimeter of the accumulator vessel and adjacent a base of the vessel, wherein the nozzles are arranged to direct a fluid supplied to the nozzle to create a rotational flow around the base of the accumulator vessel so as to fluidise solid particles in the base of the vessel.
- an outlet for removal of accumulated solids is provided in the base of the accumulator vessel.
- a method of emptying solids from an accumulator vessel comprising: directing a flow of a fluid through a plurality of nozzles into the base of the accumulator vessel so as to create a rotational flow around the base of the accumulator vessel, said rotational flow fluidising solid particles in the base of the accumulator vessel; and opening an outlet in the base of the accumulator vessel to allow the solid particles to be emptied.
- the outlet is arranged for the solids to flow downwards out of the vessel.
- the outlet may be arranged to provide an upward outflow of solids.
- the solids can be fluidised locally in a layer at the base of the vessel.
- the fluidising effect forms a localised slurry of particles, which are continuously moved within the fluidised layer so that the solids flow freely out of the vessel as it is emptied.
- the entire bed of particles is fluidised so as to be lifted up from the base.
- a certain minimum fluid flow rate is required to fluidise the solid particles and this has to be provided across substantially the entire cross-section of the vessel in order to lift the bed. This means that a relatively large fluid flow rate is required.
- effective emptying of solids can be achieved without fluidising or lifting the entire bed. As long as the fluid velocities are high enough to fluidise a layer of solids at the base of the vessel, highly effective emptying can be achieved.
- the vessel is an upright cylindrical vessel having a flat base or a semi-flat base (i.e. a base having a flat portion).
- the nozzles are mounted in the cylindrical side-wall a short distance (for example less than one fifth of a vessel diameter) above the base. More preferably, the nozzles are equi-spaced around the side-wall.
- the nozzles are preferably directed downwards towards the base at an angle to the vertical.
- the angle is preferably less than 45 degrees and more preferably is about 30 degrees.
- the nozzles should also be directed at an angle to the radius of the vessel so as to set up the rotational flow. A preferred angle to the radius is 60 degrees.
- the nozzles may be flat spray type nozzles.
- the flat spray type nozzles may provide a spray over an angle of about 100 degrees.
- nozzles may be provided in the base. These nozzles preferably produce a spray in the form of a flat disc.
- the arrangement of nozzles advantageously provides a fluidising flow covering a substantial portion of the area of the base of the vessel, and may in fact cover the entire base area of the vessel.
- the upright cylindrical vessel has a conical section at the base having a cone wall.
- some of the nozzles are mounted in the cylindrical side-wall a short distance (for example less than one fifth of a vessel diameter) above the top of the conical section.
- the nozzles are equi-spaced around the side- wall.
- Further nozzles may be provided in the cone wall. These further nozzles are preferably also flat spray type nozzles. The further nozzles are preferably directed downwards at an angle to the cone wall and at an angle to the radius of the vessel.
- the method of emptying the vessel may comprise supplying a fluid under pressure to any combination of nozzles.
- fluid may be provided under pressure through the outlet of the vessel prior to emptying. This provides the advantage of preventing or breaking down the bridging of solid particles above the outlet and is particularly suitable for use on a vessel having a conical section base.
- the vessel has a low-profile domed base.
- the base of the vessel may be "semi-flat" having a flat central portion and a conical outer portion.
- the nozzles are preferably arranged in a similar manner to that preferred for a flat base.
- the base may be a hemispherical domed end. This has many of the advantages of a conical section base in assisting the flow of solids during emptying, but has a considerably larger volume for a given vessel height, and is less prone to blockage due to bridging.
- Figure IA is a cross-sectional elevation of the bottom of an accumulator vessel, showing flow directions of fluid supplied to nozzles;
- Figure IB is a plan view of the bottom of the accumulator vessel of figure IA, showing a rotational flow pattern
- Figures 2A and 2B are plan views similar to that of Figure IB, but showing a flow coverage area of a single nozzle (Figure 2A) and overlapping coverage areas of three nozzles (Figure 2B);
- Figure 3 is a sectional elevation of a model of an accumulator vessel used for experimental tests
- Figure 4 is a plan view of the accumulator vessel of Figure 3, showing flow coverage areas for selected nozzles
- Figure 5 is a sectional elevation of the accumulator vessel model of Figure 3 having a conical base section
- Figures 6A and 6B show two alternative arrangements for the outlet of an accumulator vessel.
- the bottom part 10 of an accumulator vessel has a domed end 12 with a central, downwardly oriented outlet 14 for emptying the vessel.
- Nozzles 16a, 16b protrude through a peripheral wall 18 of the bottom part 10 and are directed downwards at an angle (in this case of about 30 degrees) to the vertical, so that a flow of fluid supplied to the nozzles is directed downwards into the domed end 12, as shown by the arrows 20a.
- FIG. IB three nozzles 16a, 16b, 16c are shown equi-spaced at angles of 120 degrees around the peripheral wall 18.
- the nozzles are not only directed at a downward angle as shown in Figure IA, but, as shown by the arrows 20b, are arranged to set up a rotational flow around the vessel when fluid is supplied simultaneously to all three nozzles 16a, 16b, 16c.
- a coverage area 22b is shown for one nozzle 16b.
- the nozzle 16b is shaped to provide a flat spray pattern, radiating outwardly over a certain angle (in this case of about 100 degrees).
- the flat spray pattern of the nozzle 16b has a central spray direction 24b, which is directed at an angle to the radius of the vessel. This results in the coverage area 22.
- the coverage area is the area, in plan view, of fluidisation of solid particles in the vessel bottom 10.
- coverage areas 22a, 22b, 22c are shown for the three nozzles 16a, 16b, 16c.
- the combined coverage of the three nozzles covers the entire cross- section area of the vessel bottom 10.
- the momentum of the flow from nozzle 16b is centred on the central direction 24b, which is at an angle of about 60 degrees to the radius of the vessel.
- FIG. 3 shows a lower portion of a model of a cylindrical accumulator vessel 30 used for experiments with sand and water.
- the accumulator vessel 30 has a flat end cup 32 at its base.
- the inner diameter of the vessel 30 is 500 mm while its total height is 1000 mm.
- Three flat spray sidewall nozzles 34a, 34b, 34c are fixed in a sidewall 35 around the lower part of the accumulator vessel 30, and three further nozzles 36a, 36b (not shown), 36c are fixed in a bottom end wall 38.
- a central outlet 40 is provided for emptying the vessel and a valve 42 allows the outlet 40 to be opened and closed.
- a separate side entry 44 with a valve 46 is also provided to enable water under pressure to be supplied to the vessel through the outlet 40.
- the flat spray sidewall nozzles 34a, 34b, 34c are disposed around the sidewall 35 with a 120° displacement with respect to each other.
- the further nozzles 36a, 36b, 36c are disposed in the bottom end wall 38 with a displacement of 120° with respect to each other.
- the disposition of the further nozzles is rotated 45° with respect to the sidewall nozzles.
- the sidewall nozzles 34a, 34b, 34c are mounted "almost tangentially" (i.e. so that they only protrude a very short distance into the vessel 30) and pointing down towards the bottom end wall 38.
- the flushing coverage area for each nozzle is mainly in front of it along the bottom end wall 38 and the sidewall 35. Using this configuration provides a rotational flow of flushing water in the core region of the vessel.
- the sidewall 35 is subject to continuous washing.
- the further nozzles 36a, 36b, 36c are full spray deflector type nozzles creating a flat spray disc just above the bottom end wall 38.
- Each further nozzle has a deflector cap 37 having the two main functions of creating a flat spray disc and preventing sand particles from entering and blocking the nozzle.
- the sidewall nozzles 34a, 34b, 34c are angled downwards at about 30 degrees with respect to the vertical sidewall 35.
- the flat spray sidewall nozzles 34a, 34b, 34c used in this study have a spray angle of 102°.
- Figure 4 illustrates the coverage area 48 of a flat spray sidewall nozzle 34b and the coverage area 49 a full spray deflector type further nozzle 36a.
- Figure 5 shows an alternative design of a model of an accumulator vessel 50 for use in the experiments having a conical section end cup 52, which has a cone wall 57.
- the inner diameter of the vessel 50 is 500 mm while its height is 1000 mm.
- the angle of the cone is 45°.
- Three flat spray sidewall nozzles 54a, 54b, 54c are fixed in a sidewall 55 around the lower part of the cylinder and 100 mm above the top of the conical section 52.
- Three cone nozzles 56a, 56b, 56c are disposed around the middle region of the conical section 52.
- the same outlet arrangement is provided for as for the flat end cup vessel 30 of Figure 3 - including the central outlet 40, valve 42, side entry 44, and side entry valve 46.
- the sidewall nozzles 54a, 54b, 54c are disposed at 120° with respect to each other around the sidewall 55.
- the further flat spray nozzles 56a, 56b, 56c are also disposed at 120° with respect to each other and rotated 45° with respect to the sidewall nozzles.
- Both the sidewall nozzles 54a, 54b, 54c and the cone nozzles 56a, 56b, 56c are mounted "almost tangential" to the sidewall 55 and cone wall 57 and pointing downward and to one side.
- the configuration of nozzles results in an effective rotational flow around the base of the vessel.
- the sidewall 55 is subjected to continuous washing and lifting up of adjacent solid particles.
- the flushing coverage area for each nozzle is mainly in front of it along the cone wall 57 and the sidewall 55.
- the cone nozzles 56a, 56b, 56c are fixed with a 90° bend at the cone wall and are directed downwards at 60° with respect to the vertical axis of the tank.
- the sidewall nozzles 54a, 54b, 54c are angled downwards at 30° with respect to the sidewall 55. All the flat spray nozzles have a spray angle of 102°.
- the outlet 40 is shown disposed below the vessel base for downward flow of solids during the emptying procedure.
- Figure 6A an alternative outlet arrangement is shown with an outlet pipe 60a aligned axially within the vessel 10 and having an opening 62a located a short distance above the centre of the vessel base. By providing a pressure difference between the vessel 10 and the outlet of pipe 60a the solids are removed by means of an upward flow.
- Figure 6B A similar arrangement is shown in Figure 6B, but here the outlet pipe 60b has a bend 64 so that it passes through a side wall of the vessel 10 from where the solids are removed.
- the experiment was carried out with 100 ⁇ m sand particles in the vessel 30 and fresh water supplied to all three flat spray nozzles 34a, 34b, 34c and all three further nozzles 36a, 36b, 36c.
- the pressure of the water supplied to all the nozzles was kept constant at 3 bar.
- the initial height of the sand bed was 35 cm.
- the sand was packed in 2 hours before the start of fluidisation.
- the whole bed was fluidised after 5 minutes.
- Sand concentration out of the tank at the start of the emptying process was measured at 48 vol%.
- Sand concentration in the slurry after 10 minutes was 13 vol% and after 20 minutes about 1 vol%.
- the level in the vessel was kept constant.
- the accumulator vessel 30 was filled with 20 cm of 100 ⁇ m sand, and water to a height of 80 cm. Both the sidewall nozzles 34a, 34b, 34c and the further nozzles 36a, 36b, 36c were used.
- the bed had been at rest for 30 minutes fore the start of the fluidisation process.
- the water pressure behind all the nozzles was kept constant at 3 bar.
- the content of the bed was mostly fluidised after 10 minutes, but it was first fully fluidised after 20 minutes.
- the fluidised bed height at 3 bar after 20 minutes was 95 cm. There was a quiet zone with clear water at the top of the bed. The height of this zone was about 10 cm. Case 3
- the accumulator vessel 30 was filled with 20 cm of 100 ⁇ m sand, and water to a height of 80 cm. Only the sidewall nozzles 34a, 34b, 34c were used. The bed had been at rest for 30 minutes before the start of fluidisation. The water pressure behind all nozzles was kept constant at 4 bar. The content of the bed was mostly fluidised after 10 minutes. The fluidised bed height at after 10 minutes was 50 cm. There was a quiet zone with clear water at the top of the bed. The height of this zone was about 40 cm. The bed was almost fully fluidised after 20 minutes. The fluidised bed height after 20 minutes was 57 cm. Whole bed content was moving except a small region at the bottom centre. The vessel 30 was emptied in 6 minutes. There were no particles left at the bottom or inside the vessel after emptying. It was an effective and good sand removal operation.
- the accumulator vessel 30 was filled with 35 cm of 100 ⁇ m sand, and water to a height of 80 cm. Both the sidewall nozzles 34a, 34b, 34c and the further nozzles 36a, 36b, 36c were used. The bed had been at rest for 30 minutes before the start of fluidisation. Then, all the nozzles were closed. The water above the sand bed was removed from the top of the tank. Two litres of Nome oil was added to the bed. The bed was then fluidised again using the bottom and the side nozzles. To mix the oil into the sand/water slurry a pump was used. The oil was sucked from the top layer through a recycle tube and then injected to the bed at the bottom of the tank.
- the recycle tube was moved around the bed to achieve a more efficient mixing. This process was continued for 45 minutes. After mixing the oil into the sand/water slurry the mixture was left to rest for 10 days. During this time the oil/water height in the tank was 95 cm while the height of the wet oily sand bed was 35 cm. All the nozzles were closed and the water flow behind them was shut down.
- the bed was then fluidised using both the sidewall nozzles 34a, 34b, 34c and the further nozzles 36a, 36b, 36c.
- the water pressure behind all the nozzles was kept constant at 3.7 bar during the test.
- the bed started to fluidise after about one minute and it was fully fluidised after about 5 minutes.
- the bed height after 5 minutes was 50 cm.
- the boundary between the fluidised region with sand particles and clear water above it was very clear.
- the interface between the fluidised bed of particles and the water above it was also quite clear with a wavy form interface.
- the vessel 30 was emptied 10 minutes after the start of fluidisation. During the emptying process all the nozzles were operating at reduced capacity. The pressure behind the further nozzles 36a, 36b, 36c was 2.5 bar and the pressure behind the sidewall nozzles 34a, 34b, 34c was 3.5 bar. During the last 2 minutes of the emptying process the pressure was further reduced to approximately 0.5 and 2.5 bar respectively. When the slurry level was about 10 cm above the bottom the water flow to all nozzles was closed down. The vessel 30 was successfully emptied with both the bottom end and the sidewalls free of sand.
- the accumulator vessel 50 was filled with lOO ⁇ m dry sand. The water height was 70 cm. It was left to settle and rest for two days. AU six nozzles 54a, 54b, 54c, 56a, 56b, 56c were used. The water pressure behind all the nozzles was kept constant at 3.7bar. The bed was fluidised after 4 minutes with a height of 60 cm. The whole bed was fluidised and everything was moving. The fluidised bed height after 10 minutes was 85 cm.
- the accumulator vessel 50 was filled with 80 kg of 100 ⁇ m dry sand and water. The water height in the bed was 80 cm. The bed was left to settle and rest for 30 minutes. The bed was the fluidised and emptied. All six nozzles 54a, 54b, 54c, 56a, 56b, 56c were used. The water pressure behind all the nozzles was kept constant at 3 bar. Particles started to move around after about 30 seconds. The bed was fluidised after 3 minutes.
- the accumulator vessel 50 was filled with sand, water and oil. Two litres of Nome oil was filled into the tank. The fluidisation water was then started using the cone nozzles 56a, 56b, 56c. The water pressure behind the nozzles was kept constant at 1 bar. 100 ⁇ m sand was then gradually added to the bed while it was moving. The fluidisation water helped to mix and lift up the bed level. When the bed height passed the sidewall nozzles 54a, 54b, 54c they were also opened to help the fluidisation. The water pressure behind them was also kept constant at 1 bar. Five additional litres of oil was added to keep the bed oil-rich. 80 kg of dry sand was filled into the vessel 50 while it was fluidising. The bed was allowed to rest for about one hour before the water above the sand bed and below the oil layer was removed. The bed was then fluidised again using all the nozzles 54a, 54b, 54c, 56a, 56b, 56c.
- a slurry a pump was used to mix the oil into the sand/water.
- the oil was sucked from the top layer through a recycle tube and then injected to the bed at the bottom of the vessel 50.
- the recycle tube was moved around the bed to achieve a more efficient mixing. This process was continued for 30 minutes.
- After mixing the oil into the sand/water slurry the mixture was left to rest for 11 days.
- the oil/water height in the tank was 95 cm and the wet oily sand bed height was 17 cm above the top of the conical section 52. AU the nozzles were closed and the water flow behind them was cut off.
- the bed was fluidised after 11 days of storage. AU six nozzles 54a, 54b, 54c, 56a, 56b, 56c were used. The water pressure behind all the nozzles was kept at a constant 3 bar. The bed was fluidised after 2-3 minutes. The height of the fluidised bed after 3 minutes was 36 cm. Sand particles started to move around just after the start of fluidisation. The whole bed was fluidised and everything was moving after about 3 minutes. Fluidised bed height after 6 minutes was 45 cm above the top of the conical section 52.
- the flushing arrangement fluidises the tank content rapidly and efficiently creating a rotating core region inside the vessel.
- a flat end cup or a semi flat, domed end cup, with the flushing arrangement described has many advantages. It provides a more uniform operating condition both inside the vessel and for the downstream equipment and process. It is less prone to blockage of the outlet due to the high sand concentration at the start of the emptying process. Such a design also results in a larger effective vessel volume, lower total height and weight.
- the fluidised slurry will be in a continuous rotational movement, resulting in a more uniform distribution of particles in the vessel. The more uniformly distributed slurry will flow continuously towards the outlet.
- the outflow will have a uniform solids concentration, which results in a more stable operation and a more robust system.
- a flattened dome shaped end cup is almost like a flat dish while a conical end cup, to provide a natural fall for the solids, must have a minimum cone angle of 45°, resulting in a cone height of at least one radius. This is significant in relation to the total height of an accumulator. Another important issue is the available useful volume in the vessel. This volume is much bigger in a vessel with a flattened dome shaped end cup than for a conical end cup with the same total height. Using a flattened dome shaped end cup may also result in a lower total weight of the accumulator vessel.
- a conical shape end cup will result in a shorter emptying time period and no particles will remain in the vessel. Due to the natural fall of particles in a conical end cup one does not need to fluidise the bed with the same intensity as for a flat end cup during the emptying period.
- a hemispherical end cup may provide a better performance by using the best aspects of the conical and flat end cups. Because of the larger volume above the outlet in a hemispherical end cup there will be no bridging or clogging around the outlet (as occurs in a conical end cup). There will also be a more uniformly distributed solid/liquid slurry leaving the vessel similar to that in a flat end cup. Due to the larger angle of the inclination in a half spherical end cup the tank will empty faster than in the case with a flat end cup and no particles will be left behind. These effects result in a more stable and robust system.
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- Engineering & Computer Science (AREA)
- Mechanical Engineering (AREA)
- Chemical & Material Sciences (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Devices And Processes Conducted In The Presence Of Fluids And Solid Particles (AREA)
- Nozzles (AREA)
- Feeding, Discharge, Calcimining, Fusing, And Gas-Generation Devices (AREA)
- Auxiliary Methods And Devices For Loading And Unloading (AREA)
Abstract
Description
Claims
Priority Applications (3)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
AU2006208968A AU2006208968A1 (en) | 2005-01-25 | 2006-01-18 | Vessel flushing system |
GB0716071A GB2437231A (en) | 2005-01-25 | 2006-01-18 | Vessel flushing system |
NO20074298A NO20074298L (en) | 2005-01-25 | 2007-08-22 | Flushing system for thoughts |
Applications Claiming Priority (2)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
GBGB0501442.8A GB0501442D0 (en) | 2005-01-25 | 2005-01-25 | Vessel flushing system |
GB0501442.8 | 2005-01-25 |
Publications (1)
Publication Number | Publication Date |
---|---|
WO2006079931A1 true WO2006079931A1 (en) | 2006-08-03 |
Family
ID=34259581
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
PCT/IB2006/000685 WO2006079931A1 (en) | 2005-01-25 | 2006-01-18 | Vessel flushing system |
Country Status (4)
Country | Link |
---|---|
AU (1) | AU2006208968A1 (en) |
GB (2) | GB0501442D0 (en) |
NO (1) | NO20074298L (en) |
WO (1) | WO2006079931A1 (en) |
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
WO2010024692A1 (en) * | 2008-08-29 | 2010-03-04 | Tool-Tech As | Method of using new flushing ports during cleaning of a piston accumulator |
WO2019211084A1 (en) * | 2018-05-04 | 2019-11-07 | Hydac Technology Gmbh | Damping device |
Citations (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
BE525444A (en) * | ||||
US1978015A (en) * | 1930-06-30 | 1934-10-23 | Peter M Erdman | Apparatus and method of cleaning tanks containing fluid |
US3586294A (en) * | 1969-02-20 | 1971-06-22 | James J Strong | Method and apparatus for creating a suspension of fine particles in a liquid |
DE2902983B1 (en) * | 1979-01-26 | 1980-01-24 | Franz-Josef Dipl-Ing Baum | Water storage basin |
EP0779111A2 (en) * | 1995-12-11 | 1997-06-18 | TAIHO INDUSTRIES Co., LTD. | Method for treating liquid in a tank and liquid jetting device used in the method |
CA2230306A1 (en) * | 1998-02-23 | 1999-08-23 | Canadian Environmental Equipment & Engineering Technologies Inc. | Desanding system for oil tanks |
US20040226587A1 (en) * | 2003-05-16 | 2004-11-18 | Michel Lemire | Sand removal system |
-
2005
- 2005-01-25 GB GBGB0501442.8A patent/GB0501442D0/en not_active Ceased
-
2006
- 2006-01-18 WO PCT/IB2006/000685 patent/WO2006079931A1/en not_active Application Discontinuation
- 2006-01-18 GB GB0716071A patent/GB2437231A/en not_active Withdrawn
- 2006-01-18 AU AU2006208968A patent/AU2006208968A1/en not_active Abandoned
-
2007
- 2007-08-22 NO NO20074298A patent/NO20074298L/en not_active Application Discontinuation
Patent Citations (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
BE525444A (en) * | ||||
US1978015A (en) * | 1930-06-30 | 1934-10-23 | Peter M Erdman | Apparatus and method of cleaning tanks containing fluid |
US3586294A (en) * | 1969-02-20 | 1971-06-22 | James J Strong | Method and apparatus for creating a suspension of fine particles in a liquid |
DE2902983B1 (en) * | 1979-01-26 | 1980-01-24 | Franz-Josef Dipl-Ing Baum | Water storage basin |
EP0779111A2 (en) * | 1995-12-11 | 1997-06-18 | TAIHO INDUSTRIES Co., LTD. | Method for treating liquid in a tank and liquid jetting device used in the method |
CA2230306A1 (en) * | 1998-02-23 | 1999-08-23 | Canadian Environmental Equipment & Engineering Technologies Inc. | Desanding system for oil tanks |
US20040226587A1 (en) * | 2003-05-16 | 2004-11-18 | Michel Lemire | Sand removal system |
Cited By (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
WO2010024692A1 (en) * | 2008-08-29 | 2010-03-04 | Tool-Tech As | Method of using new flushing ports during cleaning of a piston accumulator |
EP2315951A1 (en) * | 2008-08-29 | 2011-05-04 | Tool Tech As | Method of using new flushing ports during cleaning of a piston accumulator |
AU2009286190B2 (en) * | 2008-08-29 | 2011-12-08 | Tool-Tech As | Method of using new flushing ports during cleaning of a piston accumulator |
EP2315951A4 (en) * | 2008-08-29 | 2013-12-04 | Tool Tech As | Method of using new flushing ports during cleaning of a piston accumulator |
US8602046B2 (en) | 2008-08-29 | 2013-12-10 | Tool-Tech As | Method and a device for the cleaning of a piston-based hydraulic accumulator |
WO2019211084A1 (en) * | 2018-05-04 | 2019-11-07 | Hydac Technology Gmbh | Damping device |
US11480198B2 (en) | 2018-05-04 | 2022-10-25 | Hydac Technology Gmbh | Damping device |
Also Published As
Publication number | Publication date |
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GB2437231A (en) | 2007-10-17 |
GB0501442D0 (en) | 2005-03-02 |
GB0716071D0 (en) | 2007-09-26 |
NO20074298L (en) | 2007-08-22 |
AU2006208968A1 (en) | 2006-08-03 |
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