GB2500685A - Steam plant with reverse osmosis unit - Google Patents
Steam plant with reverse osmosis unit Download PDFInfo
- Publication number
- GB2500685A GB2500685A GB1205631.3A GB201205631A GB2500685A GB 2500685 A GB2500685 A GB 2500685A GB 201205631 A GB201205631 A GB 201205631A GB 2500685 A GB2500685 A GB 2500685A
- Authority
- GB
- United Kingdom
- Prior art keywords
- concentrate
- water
- vessel
- processing unit
- boiler
- 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.)
- Withdrawn
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- 238000001223 reverse osmosis Methods 0.000 title claims abstract description 42
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 145
- 239000012141 concentrate Substances 0.000 claims abstract description 107
- 238000012545 processing Methods 0.000 claims abstract description 49
- 239000012466 permeate Substances 0.000 claims abstract description 32
- 239000012267 brine Substances 0.000 claims abstract description 28
- HPALAKNZSZLMCH-UHFFFAOYSA-M sodium;chloride;hydrate Chemical compound O.[Na+].[Cl-] HPALAKNZSZLMCH-UHFFFAOYSA-M 0.000 claims abstract description 28
- 238000000034 method Methods 0.000 claims abstract description 25
- 239000012530 fluid Substances 0.000 claims abstract description 15
- 238000004891 communication Methods 0.000 claims abstract description 12
- 238000011010 flushing procedure Methods 0.000 claims description 16
- 230000001172 regenerating effect Effects 0.000 claims description 3
- 238000002156 mixing Methods 0.000 claims description 2
- 239000012535 impurity Substances 0.000 description 18
- 239000011347 resin Substances 0.000 description 11
- 229920005989 resin Polymers 0.000 description 11
- 229910001415 sodium ion Inorganic materials 0.000 description 10
- FAPWRFPIFSIZLT-UHFFFAOYSA-M Sodium chloride Chemical compound [Na+].[Cl-] FAPWRFPIFSIZLT-UHFFFAOYSA-M 0.000 description 9
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 description 9
- 229910001425 magnesium ion Inorganic materials 0.000 description 9
- 229910001424 calcium ion Inorganic materials 0.000 description 8
- CDBYLPFSWZWCQE-UHFFFAOYSA-L Sodium Carbonate Chemical compound [Na+].[Na+].[O-]C([O-])=O CDBYLPFSWZWCQE-UHFFFAOYSA-L 0.000 description 7
- 235000002639 sodium chloride Nutrition 0.000 description 7
- 239000007787 solid Substances 0.000 description 7
- OYPRJOBELJOOCE-UHFFFAOYSA-N Calcium Chemical class [Ca] OYPRJOBELJOOCE-UHFFFAOYSA-N 0.000 description 6
- JLVVSXFLKOJNIY-UHFFFAOYSA-N Magnesium ion Chemical compound [Mg+2] JLVVSXFLKOJNIY-UHFFFAOYSA-N 0.000 description 6
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 description 6
- UIIMBOGNXHQVGW-UHFFFAOYSA-M Sodium bicarbonate Chemical compound [Na+].OC([O-])=O UIIMBOGNXHQVGW-UHFFFAOYSA-M 0.000 description 6
- 239000011575 calcium Substances 0.000 description 6
- 239000012528 membrane Substances 0.000 description 6
- 238000005260 corrosion Methods 0.000 description 5
- 230000007797 corrosion Effects 0.000 description 5
- 230000000694 effects Effects 0.000 description 5
- 239000011780 sodium chloride Substances 0.000 description 5
- VTYYLEPIZMXCLO-UHFFFAOYSA-L Calcium carbonate Chemical compound [Ca+2].[O-]C([O-])=O VTYYLEPIZMXCLO-UHFFFAOYSA-L 0.000 description 4
- FYYHWMGAXLPEAU-UHFFFAOYSA-N Magnesium Chemical class [Mg] FYYHWMGAXLPEAU-UHFFFAOYSA-N 0.000 description 4
- CSNNHWWHGAXBCP-UHFFFAOYSA-L Magnesium sulfate Chemical compound [Mg+2].[O-][S+2]([O-])([O-])[O-] CSNNHWWHGAXBCP-UHFFFAOYSA-L 0.000 description 4
- OSGAYBCDTDRGGQ-UHFFFAOYSA-L calcium sulfate Chemical compound [Ca+2].[O-]S([O-])(=O)=O OSGAYBCDTDRGGQ-UHFFFAOYSA-L 0.000 description 4
- 238000005187 foaming Methods 0.000 description 4
- 239000011777 magnesium Chemical class 0.000 description 4
- 238000004519 manufacturing process Methods 0.000 description 4
- 239000000243 solution Substances 0.000 description 4
- 238000012546 transfer Methods 0.000 description 4
- BHPQYMZQTOCNFJ-UHFFFAOYSA-N Calcium cation Chemical compound [Ca+2] BHPQYMZQTOCNFJ-UHFFFAOYSA-N 0.000 description 3
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 3
- 241001415288 Coccidae Species 0.000 description 3
- 229910052799 carbon Inorganic materials 0.000 description 3
- 230000007613 environmental effect Effects 0.000 description 3
- 239000006260 foam Substances 0.000 description 3
- ZLNQQNXFFQJAID-UHFFFAOYSA-L magnesium carbonate Chemical compound [Mg+2].[O-]C([O-])=O ZLNQQNXFFQJAID-UHFFFAOYSA-L 0.000 description 3
- 239000001095 magnesium carbonate Substances 0.000 description 3
- 235000014380 magnesium carbonate Nutrition 0.000 description 3
- 229910000021 magnesium carbonate Inorganic materials 0.000 description 3
- 230000037452 priming Effects 0.000 description 3
- 239000000377 silicon dioxide Substances 0.000 description 3
- 235000017557 sodium bicarbonate Nutrition 0.000 description 3
- 229910000030 sodium bicarbonate Inorganic materials 0.000 description 3
- 235000017550 sodium carbonate Nutrition 0.000 description 3
- 229910000029 sodium carbonate Inorganic materials 0.000 description 3
- 235000011121 sodium hydroxide Nutrition 0.000 description 3
- PMZURENOXWZQFD-UHFFFAOYSA-L Sodium Sulfate Chemical compound [Na+].[Na+].[O-]S([O-])(=O)=O PMZURENOXWZQFD-UHFFFAOYSA-L 0.000 description 2
- 230000015572 biosynthetic process Effects 0.000 description 2
- 229910000020 calcium bicarbonate Inorganic materials 0.000 description 2
- 229910000019 calcium carbonate Inorganic materials 0.000 description 2
- 235000010216 calcium carbonate Nutrition 0.000 description 2
- 238000001816 cooling Methods 0.000 description 2
- 239000008233 hard water Substances 0.000 description 2
- 229910052500 inorganic mineral Inorganic materials 0.000 description 2
- 229910000022 magnesium bicarbonate Inorganic materials 0.000 description 2
- 235000014824 magnesium bicarbonate Nutrition 0.000 description 2
- 235000019341 magnesium sulphate Nutrition 0.000 description 2
- 229910052751 metal Inorganic materials 0.000 description 2
- 239000002184 metal Substances 0.000 description 2
- 235000010755 mineral Nutrition 0.000 description 2
- 239000011707 mineral Substances 0.000 description 2
- 230000000737 periodic effect Effects 0.000 description 2
- 230000000717 retained effect Effects 0.000 description 2
- 150000003839 salts Chemical class 0.000 description 2
- 235000012239 silicon dioxide Nutrition 0.000 description 2
- 239000000126 substance Substances 0.000 description 2
- UXVMQQNJUSDDNG-UHFFFAOYSA-L Calcium chloride Chemical compound [Cl-].[Cl-].[Ca+2] UXVMQQNJUSDDNG-UHFFFAOYSA-L 0.000 description 1
- DGAQECJNVWCQMB-PUAWFVPOSA-M Ilexoside XXIX Chemical group C[C@@H]1CC[C@@]2(CC[C@@]3(C(=CC[C@H]4[C@]3(CC[C@@H]5[C@@]4(CC[C@@H](C5(C)C)OS(=O)(=O)[O-])C)C)[C@@H]2[C@]1(C)O)C)C(=O)O[C@H]6[C@@H]([C@H]([C@@H]([C@H](O6)CO)O)O)O.[Na+] DGAQECJNVWCQMB-PUAWFVPOSA-M 0.000 description 1
- 235000019738 Limestone Nutrition 0.000 description 1
- 239000003929 acidic solution Substances 0.000 description 1
- 229910052925 anhydrite Inorganic materials 0.000 description 1
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 1
- 229910052791 calcium Inorganic materials 0.000 description 1
- NKWPZUCBCARRDP-UHFFFAOYSA-L calcium bicarbonate Chemical compound [Ca+2].OC([O-])=O.OC([O-])=O NKWPZUCBCARRDP-UHFFFAOYSA-L 0.000 description 1
- 239000001110 calcium chloride Substances 0.000 description 1
- 229910001628 calcium chloride Inorganic materials 0.000 description 1
- ZOMBKNNSYQHRCA-UHFFFAOYSA-J calcium sulfate hemihydrate Chemical compound O.[Ca+2].[Ca+2].[O-]S([O-])(=O)=O.[O-]S([O-])(=O)=O ZOMBKNNSYQHRCA-UHFFFAOYSA-J 0.000 description 1
- 239000001175 calcium sulphate Substances 0.000 description 1
- 235000011132 calcium sulphate Nutrition 0.000 description 1
- 229910052681 coesite Inorganic materials 0.000 description 1
- 238000011109 contamination Methods 0.000 description 1
- 229910052906 cristobalite Inorganic materials 0.000 description 1
- 238000013461 design Methods 0.000 description 1
- 238000007599 discharging Methods 0.000 description 1
- 238000005868 electrolysis reaction Methods 0.000 description 1
- 239000007789 gas Substances 0.000 description 1
- 229910052602 gypsum Inorganic materials 0.000 description 1
- 239000010440 gypsum Substances 0.000 description 1
- 239000011507 gypsum plaster Substances 0.000 description 1
- 238000010438 heat treatment Methods 0.000 description 1
- 239000006028 limestone Substances 0.000 description 1
- 229910052749 magnesium Chemical class 0.000 description 1
- QWDJLDTYWNBUKE-UHFFFAOYSA-L magnesium bicarbonate Chemical compound [Mg+2].OC([O-])=O.OC([O-])=O QWDJLDTYWNBUKE-UHFFFAOYSA-L 0.000 description 1
- 239000002370 magnesium bicarbonate Substances 0.000 description 1
- 229910052943 magnesium sulfate Inorganic materials 0.000 description 1
- 238000013021 overheating Methods 0.000 description 1
- 229910052760 oxygen Inorganic materials 0.000 description 1
- 239000001301 oxygen Substances 0.000 description 1
- 230000008929 regeneration Effects 0.000 description 1
- 238000011069 regeneration method Methods 0.000 description 1
- 239000011734 sodium Substances 0.000 description 1
- 229910052938 sodium sulfate Inorganic materials 0.000 description 1
- 235000011152 sodium sulphate Nutrition 0.000 description 1
- 239000008234 soft water Substances 0.000 description 1
- 238000004326 stimulated echo acquisition mode for imaging Methods 0.000 description 1
- 229910052682 stishovite Inorganic materials 0.000 description 1
- 229910052905 tridymite Inorganic materials 0.000 description 1
Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D61/00—Processes of separation using semi-permeable membranes, e.g. dialysis, osmosis or ultrafiltration; Apparatus, accessories or auxiliary operations specially adapted therefor
- B01D61/02—Reverse osmosis; Hyperfiltration ; Nanofiltration
-
- 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
- C02F1/44—Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis
- C02F1/441—Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis by reverse osmosis
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D61/00—Processes of separation using semi-permeable membranes, e.g. dialysis, osmosis or ultrafiltration; Apparatus, accessories or auxiliary operations specially adapted therefor
- B01D61/02—Reverse osmosis; Hyperfiltration ; Nanofiltration
- B01D61/025—Reverse osmosis; Hyperfiltration
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D61/00—Processes of separation using semi-permeable membranes, e.g. dialysis, osmosis or ultrafiltration; Apparatus, accessories or auxiliary operations specially adapted therefor
- B01D61/02—Reverse osmosis; Hyperfiltration ; Nanofiltration
- B01D61/12—Controlling or regulating
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J47/00—Ion-exchange processes in general; Apparatus therefor
- B01J47/02—Column or bed processes
- B01J47/022—Column or bed processes characterised by the construction of the column or container
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J49/00—Regeneration or reactivation of ion-exchangers; Apparatus therefor
- B01J49/05—Regeneration or reactivation of ion-exchangers; Apparatus therefor of fixed beds
- B01J49/06—Regeneration or reactivation of ion-exchangers; Apparatus therefor of fixed beds containing cationic exchangers
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J49/00—Regeneration or reactivation of ion-exchangers; Apparatus therefor
- B01J49/50—Regeneration or reactivation of ion-exchangers; Apparatus therefor characterised by the regeneration reagents
- B01J49/53—Regeneration or reactivation of ion-exchangers; Apparatus therefor characterised by the regeneration reagents for cationic exchangers
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J49/00—Regeneration or reactivation of ion-exchangers; Apparatus therefor
- B01J49/75—Regeneration or reactivation of ion-exchangers; Apparatus therefor of water softeners
-
- 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
- C02F1/42—Treatment of water, waste water, or sewage by ion-exchange
-
- 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
- C02F1/44—Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F01—MACHINES OR ENGINES IN GENERAL; ENGINE PLANTS IN GENERAL; STEAM ENGINES
- F01K—STEAM ENGINE PLANTS; STEAM ACCUMULATORS; ENGINE PLANTS NOT OTHERWISE PROVIDED FOR; ENGINES USING SPECIAL WORKING FLUIDS OR CYCLES
- F01K17/00—Using steam or condensate extracted or exhausted from steam engine plant
- F01K17/04—Using steam or condensate extracted or exhausted from steam engine plant for specific purposes other than heating
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F22—STEAM GENERATION
- F22B—METHODS OF STEAM GENERATION; STEAM BOILERS
- F22B33/00—Steam-generation plants, e.g. comprising steam boilers of different types in mutual association
- F22B33/18—Combinations of steam boilers with other apparatus
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F22—STEAM GENERATION
- F22D—PREHEATING, OR ACCUMULATING PREHEATED, FEED-WATER FOR STEAM GENERATION; FEED-WATER SUPPLY FOR STEAM GENERATION; CONTROLLING WATER LEVEL FOR STEAM GENERATION; AUXILIARY DEVICES FOR PROMOTING WATER CIRCULATION WITHIN STEAM BOILERS
- F22D11/00—Feed-water supply not provided for in other main groups
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2311/00—Details relating to membrane separation process operations and control
- B01D2311/04—Specific process operations in the feed stream; Feed pretreatment
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2311/00—Details relating to membrane separation process operations and control
- B01D2311/06—Specific process operations in the permeate stream
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2303/00—Specific treatment goals
- C02F2303/16—Regeneration of sorbents, filters
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2303/00—Specific treatment goals
- C02F2303/22—Eliminating or preventing deposits, scale removal, scale prevention
Landscapes
- Engineering & Computer Science (AREA)
- Chemical & Material Sciences (AREA)
- Water Supply & Treatment (AREA)
- Organic Chemistry (AREA)
- Chemical Kinetics & Catalysis (AREA)
- General Engineering & Computer Science (AREA)
- Life Sciences & Earth Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Environmental & Geological Engineering (AREA)
- Mechanical Engineering (AREA)
- Physics & Mathematics (AREA)
- Nanotechnology (AREA)
- Thermal Sciences (AREA)
- Combustion & Propulsion (AREA)
- Separation Using Semi-Permeable Membranes (AREA)
- Treatment Of Water By Ion Exchange (AREA)
Abstract
A steam plant 10 comprises a processing unit 12 arranged to treat raw water, a boiler 18 arranged to generate steam, a blowdown vessel 20 in fluid communication with the boiler so as to receive hot blowdown water from the boiler and a reverse osmosis unit 14. The reverse osmosis unit is in fluid communication with the processing unit through an inflow water line 24, with the boiler through a permeate line 60 and with the processing unit 12 and/or the blowdown vessel 20 through a concentrate line 74, 76, 78, 80, 82. In use, the reverse osmosis unit receives treated inflow water from the processing unit and generates permeate which is provided to the boiler through the permeate line and concentrate which is provided to the processing unit and/or the blowdown vessel through a concentrate line. Preferably, the processing unit comprises a softener vessel 30, 32 and a brine tank 34. There is also disclosed a method of operating a steam plant and a method of upgrading an existing steam plant.
Description
STEAM PLANT AND METHOD OF OPERATING THE SAME
The invention relates to a steam plant, a method of operating the same, and a method of upgrading an existing steam plant.
In an industrial and heating process utilising steam, steam is generated in a boiler and is transferred through pipework at high temperature and pressure to various industrial processes where the energy in the steam is utilised.
It is important to control the quality of the raw water fed to the boiler in order to prevent undesirable effects from occurring within the steam plant. These undesirable effects include corrosion of the metal components of the plant, such as pipework and valves, and the reduction of heat transfer rates which can lead to overheating and the loss of mechanical strength of components.
Water is referred to as being either "hard" or "soft". Hard water contains scale-forming impurities while soft water contains little or none. Hardness is caused by the presence of the mineral salts of calcium and magnesium and it is these minerals that encourage the formation of scale. If hard water is supplied to the boiler then scaling of the heat transfer surfaces will occur and this will reduce the heat transfer and efficiency of the boiler. Further, if the water supplied to the boiler contains dissolved gases, particularly oxygen, the corrosion of the boiler surfaces, pipework and other surfaces is likely to occur. If the pH value of the water is too low, the acidic solution will attack metal surfaces, and if the pH value is too high and the water is alkaline, other problems such as foaming may occur.
It is also desirable to prevent boiler water from being carried over from the boiler to the steam system as this can result in the contamination of control valves and heat transfer surfaces, and the restriction of steam trap orifices. Carryover is typically caused by either "priming" or "foaming". Priming is the ejection of boiler water into the steam take-off and is generally due to either operating the boiler with too high a water level, operating the boiler below its design pressure, or excessive steam demand. Foaming is the formation of foam in the space between the water surface and the steam take-off and is primarily due to a high-level of impurities in the boiler water.
As the boiler generates steam, any impurities which are in the boiler water and which do not boil off with the steam will concentrate in the boiler water. As the amount of total dissolved solids (TDS) become more and more concentrated, the steam bubbles tend to become more stable, failing to burst as they reach the water surface of the boiler.
Eventually, a substantial part of the steam space in the boiler becomes filled with bubbles and foam is carried over into the main part of the steam plant. It is therefore desirable to carefully control the amount of total dissolved solids (TDS) in the boiler water. The TDS value of the boiler water is monitored using a sensor and water known as blowdown water is discharged from the boiler to a blowdown vessel in order to maintain the TDS value within acceptable limits. Conventional boilers may be operated with the TDS in the range of 2000-3500 ppm. The blowdown water is mixed with colder water in the blowdown vessel and is then discharged to a drain.
Table 1 below shows the technical and commonly used names of some typical impurities in water, their chemical symbols, and their effects.
Name Symbol Common name Effect Calcium carbonate CaCO3 Chalk, limestone Soft scale Calcium bicarbonate Ca(HCO3)2 Soft scale + CO2 Calcium sulphate CaSO4 Gypsum, plaster of paris Hard scale Calcium chloride CaCI2 Corrosion Magnesium carbonate MgCO3 Soft scale Magnesium sulphate Mg504 Magnesite Corrosion Magnesium bicarbonate Mg(HCO3)2 Epsom salts Scale, corrosion Sodium chloride NaCI Common salt Electrolysis Sodium carbonate Na2CO3 Washing soda or soda Alkalinity Sodium bicarbonate NaHCO3 Baking soda Priming, foaming Sodium hydroxide NaOH Caustic soda Alkalinity, embrittlement Sodium sulphate Na2SO2 Glauber salts Alkalinity Silicon dioxide SiO2 Silica Hard scale
Table I
It is known to treat raw water by removing various impurities before providing it to the boiler as feedwater so as to minimise the undesirable effects described above. For example, if the water is too hard then scale forms in the boiler, and if the TDS value is too high then the blowdown rate of the boiler must be increased in order to prevent the TDS value in the boiler from becoming too high and leading to carryover.
The water treatment system of a steam plant typically comprises a filter unit, a softener unit and a reverse osmosis unit and raw water is passed through these units sequentially.
The filter unit is typically a carbon filter and acts to remove suspended solids trom the raw water. The filter must be periodically flushed in order to clean the filter and flush away debris that has built up in the filter.
The softener unit acts to reduce the hardness of the filtered water and typically comprises two softener vessels and a brine tank. Each softener vessel is provided with a resin to which sodium ions are bonded. As the filtered water is passed over the resin, the sodium ions bonded to the resin are displaced and exchanged for the calcium and magnesium ions in water, thus reducing the hardness of the water. After a period of time, all of the sodium ions will have been displaced from the resin and replaced with calcium and magnesium ions. Therefore, the softener vessel is regenerated by flushing the resin with a strong solution of sodium chloride from the brine tank. This causes the calcium and magnesium ions bonded to the resin to be replaced with sodium ions. The softener vessel is then flushed with water so as to remove the un-bonded calcium and magnesium ions from the softener vessel.
Typically, whilst one softener vessel is being used, the other is being regenerated so that water can be softened without interruption.
The reverse osmosis unit acts to reduce the TOS value of the softened water. The reverse osmosis unit comprises a semi-permeable membrane provided between two chambers. The softened water having a high TDS value is supplied to one of the chambers and pressure is applied. The applied pressure causes pure water, having a low TDS and known as permeate, to pass through the semi-permeable membrane to the other chamber. Concentrate containing a high concentration of impurities, and consequently having a high TOS value, is retained on the pressurized side of the semi-permeable membrane. The permeate is supplied to the boiler as feedwater via a feedtank, and the concentrate is discharged to a drain. The softened water supplied to the reverse osmosis unit may have a TDS value of 220 ppm and the permeate used as feedwater may have a TOS value of 23 ppm.
As should be appreciated from the above, a steam plant requires substantial volumes of water in order to operate. Specifically, raw water that is ultimately used to generate steam, cold water that can be mixed with the hot blowdown water, water for the brine tank of the softener unit, and flushing water for both the filter and the softener unit.
Water is financially an expensive resource and contributes to a large proportion of the running costs of a steam plant. Further, a large proportion of this water is ultimately discharged to a drain and water authorities typically levy a charge for this. Water is a finite resource and demand on water supplies is increasing.
Therefore, from both a financial and an environmental point of view it is desirable to reduce the water consumption of a steam plant.
According to an aspect of the invention there is provided a steam plant, comprising: a processing unit arranged to treat raw water; a boiler arranged to generate steam; a blowdown vessel in fluid communication with the boiler so as to receive hot blowdown water from the boiler; and a reverse osmosis unit in fluid communication with the processing unit though an inflow water line, the boiler through a permeate line, and the processing unit and/or the blowdown vessel through a concentrate line; wherein in use, the reverse osmosis unit receives treated inflow water from the processing unit and generates permeate which is provided to the boiler through the permeate line and concentrate which is provided to the processing unit and/or the blowdown vessel through the concentrate line. In other aspects of the invention, the concentrate may be provided to the boiler, via a feedtank (otherwise known as a hotwell), and/or the RO inlet of the reverse osmosis unit instead of, or in addition to, the processing unit and/or the blowdown vessel.
By using concentrate from the reverse osmosis unit in the processing unit and/or the blowdown vessel, the water consumption of the steam plant may be reduced, thereby reducing the operating costs of the steam plant and reducing the environmental impact of the steam plant.
The processing unit may comprise a softener unit including at least one softener vessel and a brine tank. The concentrate may be provided to the brine tank and may be subsequently used to regenerate the at least one softener vessel. By using the concentrate to fill the brine tank, the use of raw water typically used to fill the brine tank may be reduced. The concentrate may be provided to at least one softener vessel so as to flush the softener vessel. By using the concentrate to flush the softener vessel, the use of raw water typically used to flush the softener vessel may be reduced.
The processing unit may comprise a filter, such as a carbon filter. The concentrate may be provided to the filter so as to flush the filter. By using the concentrate to flush the filter, the use of raw water typically used to flush the filter may be reduced. The concentrate may be provided to the blowdown vessel where it is mixed with hot blowdown water so as to cool the blowdown water. By using the concentrate to cool the hot blowdown water, the use of raw water typically used to cool hot blowdown water may be reduced.
The steam plant may further comprise a concentrate tank arranged to receive and temporarily store concentrate from the reverse osmosis unit.
According to another aspect of the invention there is provided a method of operating a steam plant, comprising: providing raw water to a processing unit which genelates treated inflow water; providing the treated inflow water to a reverse osmosis unit which generates permeate and concentrate; providing the permeate to a boiler; and providing the concentrate to the processing unit and/or a blowdown vessel.
The processing unit may comprise a softener unit including at least one softener vessel and a brine tank. The concentrate may be provided to the brine tank; and the method may further comprise: regenerating the at least one softener vessel using concentrate from the brine tank. The method may further comprise flushing the at least one softener vessel with the concentrate.
The processing unit may comprise a filter. The method may further comprise flushing the filter with the concentrate.
The method may further comprise providing the concentrate to the blowdown vessel and mixing with hot blowdown water so as to cool the blowdown water.
The method may further comprise temporarily storing the concentrate in a concentrate storage tank, and subsequently providing the concentrate to the processing unit and/or blowdown vessel.
According to another aspect of the invention there is provided a method of modifying an existing steam plant complising a processing unit arianged to treat iaw watel; a boiler arranged to generate steam; a blowdown vessel in fluid communication with the boiler so as to receive hot blowdown water from the boiler; and a reverse osmosis unit in fluid communication with the piocessing unit though an inflow water line and the boiler through a permeate line and having a concentrate output, the method complising: fluidically connecting the concentiate output of the ieverse osmosis unit with the processing unit and/or the blowdown vessel through a concentrate line, such that during use of the steam plant, concentrate can be provided to the processing unit and/or the blowdown vessel through the concentrate line.
The invention may comprise any combination of the features and/or limitations referred to herein, except combinations of such features as are mutually exclusive.
Embodiments of the present invention will now be described, by way of example, with reference to the accompanying Figure 1 which schematically shows part of a steam plant.
Figure 1 schematically shows part of a steam plant 10 comprising a processing unit 12, a reverse osmosis unit 14, a feedtank (hotwell) 16, a boiler 18, and a blowdown vessel 20. In use, the processing unit 12 and reveise osmosis 14 treat raw water which is supplied to the boiler 18 via the feedtank 16 to generate steam. The steam generated by the boiler 18 is transferred through pipework at high temperature and pressure to various industrial processes where the energy in the steam is utilised (not shown). At periodic inteivals, blowdown water is discharged fiom the boiler 18 to the blowdown vessel 20 where it is cooled and discharged. Although not shown in the schematic of Figure 1, various pumps, valves and sensors may be provided to control the flow of water and steam around the system.
The processing unit 12 has an inlet 22 for receiving raw water, and an outlet 24 for discharging treated water. The processing unit 12 comprises a filter 26, in the form of a caibon filter, and a softenei unit 28 that aie fluidically connected in series. The filter 26 is arranged to remove suspended solids from the raw water and the softener unit 28 is arranged to reduce the hardness of the water. The filter 26 is also provided with a flushing water line 36 and a drain line 38. The softener unit 28 includes first and second softener vessels 30, 32, each containing a resin to which sodium ions are bonded, and a brine tank 34 for regenerating the softener vessels 30, 32. The softener unit 28 is also provided with control valves that allow filtered water to flow through one softener vessel 30, 32 whilst the other softener vessel 30, 32 is being regenerated.
This allows the softener unit 28 to be continuously used. The softener unit 28 is also provided with a brine tank fill line 40, a flushing water line 42, and drain lines 44.
Although it has been described that there is a filter 26 and a softener unit, in other embodiments only one may be present. Further, additional water treatment devices or units may be incorporated into the processing unit 12 as necessary.
The outlet 24 of the processing unit 12 is fluidically connected to the RD inlet 46 of the reverse osmosis unit 14 with an inflow water line 48. This allows raw water treated by the processing unit 12 to be supplied to the reverse osmosis unit 14. The reverse osmosis unit 14 is arranged to reduce the total dissolved solids (TDS) value of treated inflow water provided from the processing unit 12. As schematically shown in Figure 1, the reverse osmosis unit 14 comprises an inflow chamber 50 and a permeate chamber 52 separated by a semi-permeable membrane 54. The RO inlet 46 opens into the inflow chamber 50 which is further provided with a concentrate outlet 56 from which concentrate, having a high TDS value, can be discharged. The permeate chamber 52 is provided with a permeate outlet 58 from which permeate, having a low TDS value, can be discharged. In use, the inflow chamber 50 is maintained under pressure and inflow water is provided to this chamber through the RD inlet 46. Pure water, known as permeate and low in impurities, passes through the membrane 54 where it can be discharged from the permeate outlet 58, whilst concentrate, high in impurities, can be drawn from the concentrate outlet 56.
The permeate outlet 58 of the reverse osmosis unit 14 is connected to a permeate line which is configured to supply the permeate generated by the reverse osmosis unit 14 to the feedtank 16. In turn, the feedtank 16 is fluidically connected to the boiler 18 by a feedwater supply line 62 so that feedwater in the feedtank 16 can be supplied to the boiler 18. The boiler 62 is configured to generate steam from the feedwater and is provided with a steam supply line 64 for delivering and transferring the steam to various processes (not shown) within the steam plant.
The boiler 18 is also provided with a blowdown outlet 66 towards the bottom of the boiler to which a blowdown line 68 is attached. The blowdown line 68 connects the boiler 18 to the blowdown vessel 20 such that hot blowdown water can be discharged from the boiler 18 to the blowdown vessel 20. The blowdown vessel 20 is further provided with a drain line 70 which allows cooled blowdown water to be discharged to a drain.
In addition to the components described above, the steam plant 10 is further provided with a concentrate storage tank 72 that is fluidically connected to the concentrate outlet 56 of the reverse osmosis unit 14 by a concentrate line 74. This allows concentrate generated by the reverse osmosis unit 14 to be fed to and stored by the concentrate tank. The concentrate storage tank 72 is connected to various other components of the steam plant 10 with various concentrate lines. Specifically, in this embodiment the concentrate storage tank 72 is connected to the blowdown vessel 20 with a line 76, the flushing line 36 of the filter 26 with a line 78, the brine tank fill line 40 of the brine tank 34 with a line 80 and the flushing line 42 of the softener unit 28 with a line 82. This allows concentrate from the reverse osmosis unit 14, temporarily stored in the concentrate storage tank 72, to be supplied to these various components.
In use, raw water is provided to the inlet 22 of the processing vessel 12 and is passed through the carbon filter 26 to remove any suspended particulate in the water. The filtered water is then passed through the softener unit 28 to reduce the hardness of the water. The softener unit 28 comprises two softener vessels 30. 32 and the filtered water is passed through one of these vessels 30, 32 whilst the other vessel is being regenerated (as will be explained below). As the filtered water is passed over the resin in the softener vessel 30, 32, the magnesium or calcium ions in the water displace and replace the sodium ions bonded to the resin. This therefore reduces the hardness of the water by replacing the magnesium and calcium ions with sodium ions. The filtered and softened water is then fed to the RO inlet 46 of the reverse osmosis unit 14 as treated inflow water through the inflow water line 48. The treated inflow water enters the inflow chamber 50 of the reverse osmosis unit 14 and is subjected to a high pressure. Permeate that is low in impurities, and which consequently has a low TDS value, passes through the membrane 54 to the permeate chamber 52, whilst concentrate high in impurities, and which consequently has a high TDS value, is retained in the inflow chamber 50. The concentrate is drawn through the concentrate outlet 56 of the reverse osmosis unit 14 at a known rate and is fed to the concentrate storage tank 72 through the concentrate line 74. The permeate, which is relatively soft and which has a relatively low TOS value, is fed to the feedtank 16 through the permeate line 60. Various chemicals are supplied to the feedwater in the feedtank 16.
Boiler feedwater is fed to the boiler 18 through the feedwater supply line 62 where it is heated to generate steam. The steam is transferred to various industrial processes in the steam plant 10 through the steam supply line 64.
The impurities in the boiler water within the boiler 18 concentrate as they do not boil off and the TDS value of the boiler water therefore increases. As previously discussed, if the TDS value is too high then foam forms within the boiler which may be carried over into the remainder of the steam system. Therefore, at periodic intervals, blowdown water having a high TDS value is discharged from the boiler 18 through the blowdown outlet 66 to the blowdown vessel 20 via the blowdown water line 68. The temperature of the blowdown water is too high for it to be immediately discharged to a drain.
Therefore, the hot blowdown water supplied to the blowdown vessel 20 is mixed with cooler water within the blowdown vessel 20 before it is discharged through the drain 70. In this embodiment, the concentrate generated by the reverse osmosis unit 14 and stored in the storage tank 72 is supplied to the blowdown vessel 20 through the line 76.
The concentrate is at approximately ambient temperature and therefore can be used to cool the hot blowdown water. If there is insufficient concentrate available to sufficiently cool the hot blowdown water, then water from another source, such as raw water, can be used in addition. Since the concentrate is only being used to cool hot blowdown water, it does not matter that it is high in impurities.
The use of concentrate, that would ordinarily be directly discharged to a drain due to its high level of impurities, to cool hot blowdown water eliminates, or at least reduces, the amount of raw water that is required in the blowdown vessel. There is therefore a financial saving as the cost of raw water to cool the hot blowdown water is eliminated (or at least reduced), and the cost of disposing of the concentrate is also eliminated (or at least reduced).
After a period of time, the filter 26 will become blocked with the suspended solids which it has removed from the raw water. It is therefore necessary to periodically flush the filter 26 with flushing water. In this embodiment, concentrate generated by the reverse osmosis unit 14 and stored in the storage tank 72 is supplied to the filter flushing line 36 and is used to flush the filter 26 so as to remove any debris. The concentrate used to flush the filter 26 is then discharged through the drain 38. If there is insufficient concentrate available to flush the filter 26, then water from another source, such as raw watel, can be used in addition. Since the concentiate is only being used to flush the filter, it does not matter that it is high in impurities.
The use of concentrate, that would ordinarily be diiectly dischaiged to a drain due to its high level of impurities, to flush the filter 26 eliminates, or at least reduces, the amount of raw watel that is iequired for flushing. Theie is therefore a financial saving as the cost of raw water to flush the filter 26 is eliminated (or at least reduced), and the cost of disposing of the concentrate is also eliminated (or at least reduced).
After a period of time, all of the sodium ions bonded to the resin of the softener vessel 30, 32 being used will have been replaced with calcium and magnesium ions, and therefore the softenei vessel 30, 32 must be regeneiated. In order to do this, a series of valves are actuated so that the filtered water is directed to the other softener vessel 30, 32 to ensure continuous operation of the softener unit 28. The softener vessel 30, 32 is regenerated by filling the vessel 30, 32 with a stiong solution of sodium chloride supplied fiom the brine tank 34. This causes the sodium and magnesium ions bonded to the lesin to be displaced and ieplaced with sodium ions. In this embodiment, the concentrate generated by the reverse osmosis unit 14 and stored in the storage tank 72 is supplied to the brine tank 34 through the line 80 where it is mixed with solid sodium chloride so as to form a strong brine solution. If there is insufficient concentiate available to generate sufficient brine, then water from another source, such as raw water, can be used in addition. Since the concentrate is only being used to form brine solution, it does not matter that it is high in impurities. Once the regeneration of the resin has taken place, the softener vessel 30, 32 is flushed so as to remove the magnesium and calcium ions from the vessel 30, 32. In this embodiment, concentrate generated by the reverse osmosis unit 14 and stored in the storage tank 72 is supplied to the softener unit flushing line 42 and is used to flush the softener vessel 30, 32. The concentrate used to flush the softener vessel 30, 32 is then discharged thiough the drain 44. If there is insufficient concentrate available to flush the softener vessel 30, 32, then water from another source, such as raw water, can be used in addition. Since the concentrate is only being used to flush the softener unit 28, it does not matter that it is high in impurities.
The use of concentrate, that would ordinarily be directly discharged to a drain due to its high level of impurities, to fill the brine tank 34 and flush the softener vessel 30, 32 eliminates, or at least reduces, the amount of raw water that is required. There is therefore a financial saving as the cost of raw water to fill the brine tank 34 and flush the softener vessel 30, 32 is eliminated (or at least reduced), and the cost of disposing of the concentrate is also eliminated (or at least reduced).
As can be seen from the above, using the concentrate from the reverse osmosis unit 14 in other areas of the steam plant where water quality is not as important results in both financial and environmental benefits. Although it has been described that the concentrate is used for flushing the filter, filling the brine tank, flushing the softener vessel and cooling blowdown water, it should be appreciated that a particular steam plant may not implement all of these uses. For example, in a particular steam plant the concentrate may only be used for cooling blowdown water, or may only be used to flush the filter. Also, depending on the particular requirements, it is not essential that a concentrate storage tank is provided if the concentrate can be used "on-the-fly".
As shown in Figure 1 in dotted lines, instead of providing concentrate to the blowdown vessel 20 and/or the processing unit 12, concentrate may be supplied to the feedtank (hotwell) 16 and/or the RO inlet 46 of the reverse osmosis unit 14. However, due to the quality of the concentrate, in particular the high TDS value, any such supply must be carefully controlled.
Sortie of the components of the steam plant 10 described above with reference to Figure 1 may already be present in an existing steam plant 10; although configured entirely differently. Therefore, it may be possible to upgrade or modify an existing steam plant 10 to use concentrate from a reverse osmosis unit 14 in other parts of the plant 10, thereby making the steam plant 10 more efficient and environmentally friendly.
Where it has been described that a particular component is in fluid communication with another component by a particular line, it should be appreciated that this may be directly, or indirectly, and other components may be disposed in the fluid path between the two. For example, in the above described embodiment the reverse osmosis unit 14 is in fluid communication with the boiler 18 through the permeate line 60. However, a feedtank 16 is disposed in the fluid path between the two, and a further fluid line 62from the feedtank 16 to the boiler 18 is provided.
Claims (18)
- CLAIMS: 1. A steam plant, comprising: a processing unit arranged to treat raw water; a boiler arranged to generate steam; a blowdown vessel in fluid communication with the boiler so as to receive hot blowdown water from the boiler; and a reverse osmosis unit in fluid communication with the processing unit though an inflow water line, the boiler through a permeate line, and the processing unit and/or the blowdown vessel through a concentrate line; wherein in use, the reverse osmosis unit receives treated inflow water from the processing unit and generates permeate which is provided to the boiler through the permeate line and concentrate which is provided to the processing unit and/or the blowdown vessel through a concentrate line.
- 2. A steam plant according to claim 1, wherein the processing unit comprises a softener unit including at least one softener vessel and a brine tank.
- 3. A steam plant according to claim 2, wherein in use the concentrate is provided to the brine tank and is subsequently used to regenerate the at least one softener vessel.
- 4. A steam plant according to claim 2 or 3, wherein in use the concentrate is provided to at least one softener vessel so as to flush the softener vessel.
- 5. A steam plant according to any preceding claim, wherein the processing unit comprises a filter.
- 6. A steam plant according to claim 5, wherein in use the concentrate is provided to the filter so as to flush the filter.
- 7. A steam plant according to any preceding claim, wherein in use the concentrate is provided to the blowdown vessel where it is mixed with hot blowdown water so as to cool the blowdown water.
- 8. A steam plant according to any preceding claim, further comprising a concentrate tank arranged to receive and temporarily store concentrate from the reverse osmosis unit.
- 9. A method of operating a steam plant, comprising: providing raw water to a processing unit which generates treated inflow water; providing the treated inflow water to a reverse osmosis unit which generates permeate and concentrate; providing the permeate to a boiler; and providing the concentrate to the processing unit and/or a blowdown vessel.
- 10. A method according to claim 9, wherein the processing unit comprises a softener unit including at least one softener vessel and a brine tank.
- 11. A method according to claim 10, wherein the concentrate is provided to the brine tank; and wherein the method further comprises: regenerating the at least one softener vessel using concentrate from the brine tank.
- 12. A method according to claim 10 or 11, further comprising flushing the at least one softener vessel with the concentrate.
- 13. A method according to any of claims 9-12, wherein the processing unit comprises a filter.
- 14. A method according to claim 13, further comprising flushing the filter with the concentrate.
- 15. A method according to any of claims 9-14, further comprising providing the concentrate to the blowdown vessel and mixing with hot blowdown water so as to cool the blowdown water.
- 16. A method according to any preceding claim, further comprising temporarily storing the concentrate in a concentrate storage tank, and subsequently providing the concentrate to the processing unit and/or blowdown vessel.
- 17. A method of modifying an existing steam plant comprising a processing unit arranged to treat raw water; a boiler arranged to generate steam; a blowdown vessel in fluid communication with the boiler so as to receive blowdown water from the boiler; and a reverse osmosis unit in fluid communication with the processing unit though an inflow water line and the boiler through a permeate line and having a concentrate output, the method comprising: fluidically connecting the concentrate output of the reverse osmosis unit with the processing unit and/or the blowdown vessel through a concentrate line, such that during use of the steam plant, concentrate can be provided to the processing unit and/or the blowdown vessel through the concentrate line.
- 18. A steam plant substantially as described herein with reference to the accompanying drawings.
Priority Applications (6)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| GB1205631.3A GB2500685A (en) | 2012-03-30 | 2012-03-30 | Steam plant with reverse osmosis unit |
| EP13160939.8A EP2644572B1 (en) | 2012-03-30 | 2013-03-25 | Steam plant and method of operating the same |
| ES13160939.8T ES2568609T3 (en) | 2012-03-30 | 2013-03-25 | Steam plant and method to operate it |
| JP2013073629A JP6182342B2 (en) | 2012-03-30 | 2013-03-29 | Steam plant and operating method thereof |
| KR1020130034635A KR102073063B1 (en) | 2012-03-30 | 2013-03-29 | Steam plant, method of operating the same and method of modifying an existing steam plant |
| CN2013101851088A CN103438423A (en) | 2012-03-30 | 2013-03-29 | Steam plant and method of operating the same |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| GB1205631.3A GB2500685A (en) | 2012-03-30 | 2012-03-30 | Steam plant with reverse osmosis unit |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| GB201205631D0 GB201205631D0 (en) | 2012-05-16 |
| GB2500685A true GB2500685A (en) | 2013-10-02 |
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Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| GB1205631.3A Withdrawn GB2500685A (en) | 2012-03-30 | 2012-03-30 | Steam plant with reverse osmosis unit |
Country Status (6)
| Country | Link |
|---|---|
| EP (1) | EP2644572B1 (en) |
| JP (1) | JP6182342B2 (en) |
| KR (1) | KR102073063B1 (en) |
| CN (1) | CN103438423A (en) |
| ES (1) | ES2568609T3 (en) |
| GB (1) | GB2500685A (en) |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US10399870B2 (en) * | 2017-03-06 | 2019-09-03 | B. Braun Avitum Ag | Water treatment system |
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| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| DE202014101587U1 (en) * | 2014-04-03 | 2014-06-12 | Zeosys Gmbh | Apparatus for the recovery of halogenated hydrocarbons |
| GB2537678A (en) * | 2015-04-24 | 2016-10-26 | Linde Ag | Scale removal system |
| EP3130391B1 (en) * | 2015-08-14 | 2019-05-22 | fluvicon GmbH | Fluid purification by forward osmosis, ion exchange and re-concentration |
| JP6764686B2 (en) * | 2016-05-18 | 2020-10-07 | オルガノ株式会社 | Water treatment method and equipment and ion exchange resin regeneration method |
| KR102028859B1 (en) | 2019-04-04 | 2019-10-04 | 오기성 | Energy recovery system using blowdown water for total dissolved solids controlling of boiler |
| JP2021007927A (en) * | 2019-07-02 | 2021-01-28 | 栗田工業株式会社 | Regeneration process of water softener, and manufacturing apparatus of desalted water |
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Also Published As
| Publication number | Publication date |
|---|---|
| KR20130111455A (en) | 2013-10-10 |
| CN103438423A (en) | 2013-12-11 |
| JP2013212504A (en) | 2013-10-17 |
| KR102073063B1 (en) | 2020-02-04 |
| ES2568609T3 (en) | 2016-05-03 |
| GB201205631D0 (en) | 2012-05-16 |
| EP2644572A1 (en) | 2013-10-02 |
| JP6182342B2 (en) | 2017-08-16 |
| EP2644572B1 (en) | 2016-03-23 |
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