WO2003037803A1 - Method and device for liquid treatment - Google Patents

Method and device for liquid treatment Download PDF

Info

Publication number
WO2003037803A1
WO2003037803A1 PCT/NO2002/000396 NO0200396W WO03037803A1 WO 2003037803 A1 WO2003037803 A1 WO 2003037803A1 NO 0200396 W NO0200396 W NO 0200396W WO 03037803 A1 WO03037803 A1 WO 03037803A1
Authority
WO
WIPO (PCT)
Prior art keywords
liquid
container
water
filter material
pipe
Prior art date
Application number
PCT/NO2002/000396
Other languages
French (fr)
Inventor
Svein Olav Risvold Stornes
Original Assignee
Wasto As
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by Wasto As filed Critical Wasto As
Publication of WO2003037803A1 publication Critical patent/WO2003037803A1/en

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/66Treatment of water, waste water, or sewage by neutralisation; pH adjustment
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/008Control or steering systems not provided for elsewhere in subclass C02F
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/68Treatment of water, waste water, or sewage by addition of specified substances, e.g. trace elements, for ameliorating potable water
    • C02F1/685Devices for dosing the additives
    • C02F1/688Devices in which the water progressively dissolves a solid compound
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2103/00Nature of the water, waste water, sewage or sludge to be treated
    • C02F2103/02Non-contaminated water, e.g. for industrial water supply
    • C02F2103/023Water in cooling circuits
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2209/00Controlling or monitoring parameters in water treatment
    • C02F2209/05Conductivity or salinity
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2209/00Controlling or monitoring parameters in water treatment
    • C02F2209/06Controlling or monitoring parameters in water treatment pH
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2209/00Controlling or monitoring parameters in water treatment
    • C02F2209/07Alkalinity
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2303/00Specific treatment goals
    • C02F2303/16Regeneration of sorbents, filters

Definitions

  • This invention relates to a method and a device for treating liquids, especially for use in connection with an energy plant, in which water is used as an energy carrier, for example in a cooling and heating plant.
  • a plant in which water is used as an energy carrier, is operationally affected to a substantial degree by the chemical composition and particle content of the water used.
  • the hardness of the water normally indicated as °dH on a scale from 0 to 21, expressing the content of calcium and magnesium ions in the water, a low °dH-value indicating very soft water.
  • the acidity of the water normally indicated as pH on a scale from 0 to 14, expressing the content of hydrogen ions in the water, a low pH-value indicating acid water and pH 7 indicating neutral water.
  • the alkalinity of the water normally measured in milligrams of bicarbonate (HC0 3 ) per litre, which is a measurement of the sensitivity of the liquid to contamination, . that is, of a buffer capacity for acid additions.
  • the measurement indicates the ability of the liquid to neutralize acids, that is, the ability of the water to bear additions of hydrogen ions H+ without responding with a reduced pH.
  • Corrosion of the metals of the plant creates sludge.
  • the sludge preferably settles in areas with a low flow rate, such as heat exchangers and containers.
  • Corrosion is influenced by a number of factors, such as dissolved gases in the liquid, for example oxygen and carbon dioxide, too low a pH-value and alkalinity.
  • Impure water has a higher viscosity than pure water. The use of impure water thus results in a reduced flow rate in the plant.
  • a partial flow of the circulation water for example 10 %, is pumped through a purifying/treating device.
  • the water to be cleaned is pumped in at the top of a closed container containing several layers of different materials, through which the water is flowing down, then returning to the plant.
  • a tank of the kind mentioned contains a filter layer of granulated filter material at the top. Below the . filter material is disposed a layer of granulated magnesium oxide and calcium carbonate, under which is disposed filter sand. and, at the bottom, a layer of glass balls.
  • the filter sand is arranged to prevent the rest of the content within the tank, apart from the cleaned water, from sinking into the glass ball layer on the bottom of the tank.
  • the glass balls are arranged to form an insulating layer, in which a zinc ⁇ electrode is disposed, insulated from the container. The zinc electrode is connected through an ammeter to the container material.
  • the ammeter shows an amperage between the electrode and the container material, which varies depending on the pH- value of the water.
  • the liquid flow down through the material layers has turned out to compress the materials in such a way that there is an increased pressure fall through the container.
  • the compression of the material layers causes formation of flow channels, through which the liquid will flow, not having the desired surface of contact with the material layers. It has also proved difficult to maintain sufficient cleanliness in the glass ball layer, as fine material deposits on the balls. Such contamination interferes with the flow passage through the zinc electrode and results in the amperage of the ammeter not reflecting the pH-value of the water.
  • the invention has as its object to remedy the drawbacks of the prior art.
  • the liquid to be treated is first led down from the upper end portion of a first container into a granulated filter material and a sand filter layer below that, after which the liquid flows from the bottom of the first container to the bottom of a second container, where it flows up through layers consisting of granulated magnesium oxide and/or granulated calcium carbonate.
  • a zinc electrode which is electrically insulated from the container. The zinc electrode is connected through an ammeter to the material of the container.
  • the separated sludge and other contaminations may be flushed out of the filter material without any risk of the filter material and the other material layers becoming mixed up. It has also proved advantageous in normal operation to let the liquid flow upwards through the granulated magnesium oxide and calcium carbonate, whereby the layers maintain a relatively porous state compared to the conditions prevailing when the liquid is flowing downwards through said layers.
  • the method is highly suitable when it is relevant to circulate the liquid through materials with properties inhibiting bacterial growth.
  • Fig. 1 shows schematically an energy plant comprising a purifying-Vtreating plant in operation
  • Fig. 2 shows the plant of Fig. 1 during flushing of the first container
  • Fig. 3 shows the plant of Fig. 1 during flushing of the second container.
  • the reference numeral 1 identifies a purifying-/treating plant connected to an energy plant 2, like for example a cooling-, drying- or heating-plant.
  • the energy plant 2 is connected to a circulation pump 4 through pipes 6 and 8.
  • the liquid flows down at a relatively low rate through an upper filter layer 18 located in the first container 16 and then through a lower filter layer 20 to the bottom portion of the first container 16. From the bottom portion of the first container 16 the liquid flows through a pipe 22 to 5 the bottom portion of a second container 24.
  • the second container is filled with at least one layer of a reaction material 26. The liquid flows through the reaction material 26 to the upper portion of the second container 24, from where it flows through a pipe 28, a flow control valve 30 and a second shut-off valve 32, a pipe 34 and the pipe 6 back to the suction side of the circulation pump 4.
  • the upper portions of the containers 16, 24 are connected to a three-way valve 36 through pipes 38 and 40, respectively.
  • a pipe 42 connects the third passage of the three-way valve 36 to a drain 44.
  • a pipe 46 which may be connected to, for example, a water distribution system, not shown, carries clean flushing liquid through a third shut-off valve 48 to the pipe 22.
  • the filter material of the upper filter layer 18 of the container 16 may with advantage be formed by a granulated filter material, which may achieve, as the liquid flows down through the material, a removal of particles larger than 0,01 millimetres.
  • the height of the upper filter layer 18 must be at least 0,4 metres. With a smaller filter layer height the ability of the filter to remove small particles is reduced, and so is the ability of the filter to accumulate sludge without increasing the pressure fall across the filter.
  • the task of the lower filter layer 20 is to prevent sludge from flowing together with liquid through the pipe 22 into the lower portion of the second container 26.
  • the reaction material 26 of the second container 24 comprises granulated magnesium oxide and/or calcium carbonate. A possible mixture must be adapted to the liquid quality. When the liquid flows relatively slowly up through the reaction material 26, part of the reaction material is dissolved in the liquid, favourably influencing the pH-value and alkalinity of the liquid with respect to corrosion.
  • a zinc electrode 50 is installed in an insulated manner in the upper portion of the second container 24. Through an ammeter 52 and wires 54 and 56 the zinc electrode is connected to the material of the second container 24. The amperage through the ammeter 52 reflects the pH-value of the liquid.
  • the flow resistance in the first container 16 increases.
  • the filter material 18, 20 of the first container 16 is being filled up with sludge, the flow resistance in the first container 16 increases.
  • the filter material 18, 20 preferably with a sufficiently large quantity of liquid for the upper filter layer 18 and the lower filter layer 20 to be whirled up, the sludge present in the first container 16 is loosened, see Fig. 2.
  • the counter-flow flushing is carried out by closing the first shut-off valve 12 and the second shut-off valve 32, then opening of the three-way valve 36 to flow from the upper portion of the first container 16 through the pipes 38 and 42 to the drain 44.
  • the third shut-off valve 48 is opened and' clean liquid flows from the pipe 46 through the third shut- off valve 48, the pipe 22, the first container 16, the pipe 38, the three-way valve 36 and the pipe 42 to the drain 44.
  • the counter-flow flushing may be stopped when the exiting flushing liquid is clean. If desired, also the reaction material 26 may be flushed correspondingly in order for the granulated material to be loosened.
  • the flushing is carried out as described above, but the three-way valve 36 is turned in such a way that it opens to liquid flow from the upper portion of the second container 24 through the pipes 40 and 42 to the drain 44 while closing, at the same time, the pipe 38, see Fig. 3.
  • clean liquid flows from the pipe 46 through the third shut-off valve 48, the pipe 22, the second container 24, the pipe 40, the three- way valve 36 and the pipe 42 to the drain 44.
  • the counter- flow flushing is stopped after a predetermined flushing time.
  • the method and device according to the invention allows a granulated filter material 18, 20, which is cleaned by means of counter-flow flushing, to be kept separated from the reaction material 26, whereby the direction of flow through the reaction material may be an upward one.
  • a granulated filter material 18, 20 which is cleaned by means of counter-flow flushing, to be kept separated from the reaction material 26, whereby the direction of flow through the reaction material may be an upward one.
  • the upward flow through the reaction material 26 permits installation of the zinc electrode 50 in the upper end portion of the second container 24, where it is exposed to sludge only to an insignificant degree.

Landscapes

  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Removal Of Specific Substances (AREA)

Abstract

A method and device for the purification and treatment of a liquid, wherein the liquid is purified by flowing through a filter material (18, 20), the filter material being arranged to be cleaned by means of counter-flow flushing, and wherein, with the aim of changing the pH-value and alkalinity of the liquid, the liquid flows through a reaction material (26) in the form of magnesium oxide and/or calcium carbonate, the liquid flowing in a falling manner through the filter material, and flowing in an ascending manner through the reaction material.

Description

METHOD AND DEVICE FOR LIQUID TREATMENT
This invention relates to a method and a device for treating liquids, especially for use in connection with an energy plant, in which water is used as an energy carrier, for example in a cooling and heating plant.
A plant, in which water is used as an energy carrier, is operationally affected to a substantial degree by the chemical composition and particle content of the water used. Apart from the content of the water of particles in the form of organic and/or inorganic material, three conditions, in particular, are of importance and have to be controlled to maintain high efficiency and reliability in a plant of the kind in question:
- the hardness of the water, normally indicated as °dH on a scale from 0 to 21, expressing the content of calcium and magnesium ions in the water, a low °dH-value indicating very soft water. - the acidity of the water, normally indicated as pH on a scale from 0 to 14, expressing the content of hydrogen ions in the water, a low pH-value indicating acid water and pH 7 indicating neutral water.
- the alkalinity of the water, normally measured in milligrams of bicarbonate (HC03) per litre, which is a measurement of the sensitivity of the liquid to contamination, . that is, of a buffer capacity for acid additions. The measurement indicates the ability of the liquid to neutralize acids, that is, the ability of the water to bear additions of hydrogen ions H+ without responding with a reduced pH.
Experience tells that content from hard water (Ca, Mg) deposits on the warmest places in a plant, which are often the places where good heat transmission is important, such as heating elements and heat exchangers.
Corrosion of the metals of the plant creates sludge. The sludge preferably settles in areas with a low flow rate, such as heat exchangers and containers.
Corrosion is influenced by a number of factors, such as dissolved gases in the liquid, for example oxygen and carbon dioxide, too low a pH-value and alkalinity.
The use of different metals as the material in a plant, such as copper and steel, causes galvanic corrosion, increasing substantially at low pH-values. Corroding steel is converted into decomposed iron and carbon. Carbon is a very good insulator when deposited on walls and, in addition, causes abrasion in movable parts like pumps and valves.
When replenishing water is heated, oxygen separates and reacts with decomposed iron (bivalent), forming rust (trivalent). Rust precipitates from the water in areas of a relatively small water flow rate. When the oxygen reacts with other substances, the pH-value of the water falls further, leading to increased corrosion.
Impure water has a higher viscosity than pure water. The use of impure water thus results in a reduced flow rate in the plant.
To prevent corrosion in a plant of the kind in question, the relationship between pH-value and alkalinity has proved to be important. In the Baylis equilibrium curve, see graph 1, the area above the curve "A" represents values, in which the formation of a calcium carbonate coating can be expected, the curve "B" indicates carbon equilibrium, whereas the area below the curve "C" indicates that corrosion will occur.
Graph 1, Baylis equilibrium curve 10
pH-value
Figure imgf000005_0001
0 50 100 150 200 250 300 350
Due to the conditions mentioned above, the use of purifying and treating plants in installations where water/liquid is used as an energy carrier, is increasing.
According to the prior art, for example Norwegian patent 303968, a partial flow of the circulation water, for example 10 %, is pumped through a purifying/treating device. The water to be cleaned, is pumped in at the top of a closed container containing several layers of different materials, through which the water is flowing down, then returning to the plant.
Typically, a tank of the kind mentioned contains a filter layer of granulated filter material at the top. Below the. filter material is disposed a layer of granulated magnesium oxide and calcium carbonate, under which is disposed filter sand. and, at the bottom, a layer of glass balls.
When the water flows down through the filter material, free particles, if any, will bind to the filter material. The cleaned water flows through the layers of granulated magnesium oxide and calcium carbonate, in which the pH-value and alkalinity of the water are affected in such a manner, that the corrosiveness of the water is reduced. The filter sand is arranged to prevent the rest of the content within the tank, apart from the cleaned water, from sinking into the glass ball layer on the bottom of the tank. The glass balls are arranged to form an insulating layer, in which a zinc ■ electrode is disposed, insulated from the container. The zinc electrode is connected through an ammeter to the container material. The ammeter shows an amperage between the electrode and the container material, which varies depending on the pH- value of the water. When, after some time in operation, the container is to be cleaned, the flow lines to the plant are shut off, and liquid flows from below up through the layers, after which the liquid flows to a drain. In order to achieve satisfactory cleaning, it is necessary for the flow rate of the water through the container to be high enough to whirl up the layered materials of the container. Due to different specific weights, the layers will settle back into their correct relative positions within the container. However, practice has shown that, after cleaning, the desired separation of materials does not always occur to the degree desired.
The liquid flow down through the material layers has turned out to compress the materials in such a way that there is an increased pressure fall through the container. The compression of the material layers causes formation of flow channels, through which the liquid will flow, not having the desired surface of contact with the material layers. It has also proved difficult to maintain sufficient cleanliness in the glass ball layer, as fine material deposits on the balls. Such contamination interferes with the flow passage through the zinc electrode and results in the amperage of the ammeter not reflecting the pH-value of the water.
The invention has as its object to remedy the drawbacks of the prior art.
The object is realized, according to the invention, through the features specified in the description below and the following Claims.
It has proved convenient to separate the cleaning layer and the pH- and alkalinity controlling layers in two separate containers .
The liquid to be treated is first led down from the upper end portion of a first container into a granulated filter material and a sand filter layer below that, after which the liquid flows from the bottom of the first container to the bottom of a second container, where it flows up through layers consisting of granulated magnesium oxide and/or granulated calcium carbonate. At the upper portion of the second container the treated liquid flows past a zinc electrode, which is electrically insulated from the container. The zinc electrode is connected through an ammeter to the material of the container.
By the use of two discrete containers, the separated sludge and other contaminations may be flushed out of the filter material without any risk of the filter material and the other material layers becoming mixed up. It has also proved advantageous in normal operation to let the liquid flow upwards through the granulated magnesium oxide and calcium carbonate, whereby the layers maintain a relatively porous state compared to the conditions prevailing when the liquid is flowing downwards through said layers.
The method is highly suitable when it is relevant to circulate the liquid through materials with properties inhibiting bacterial growth.
In the method according to the invention it is unnecessary to use a layer of glass balls to keep the area at the zinc electrode clean.
In the following will be described a non-limiting example of a preferred method and embodiment which is visualized in the accompanying drawings, in which:
Fig. 1 shows schematically an energy plant comprising a purifying-Vtreating plant in operation;
Fig. 2 shows the plant of Fig. 1 during flushing of the first container; and
Fig. 3 shows the plant of Fig. 1 during flushing of the second container.
In the drawings the reference numeral 1 identifies a purifying-/treating plant connected to an energy plant 2, like for example a cooling-, drying- or heating-plant. The energy plant 2 is connected to a circulation pump 4 through pipes 6 and 8.
From the pipe 8, which is connected to the pressure side of s the circulation pump 4, a partial flow of liquid flows, in normal operation, through a pipe 10, a first shut-off valve 12 and a pipe 14 to the upper portion of a first container ' 16. In the drawings arrows indicate the flow direction of the liquid.
o Then, the liquid flows down at a relatively low rate through an upper filter layer 18 located in the first container 16 and then through a lower filter layer 20 to the bottom portion of the first container 16. From the bottom portion of the first container 16 the liquid flows through a pipe 22 to 5 the bottom portion of a second container 24. The second container is filled with at least one layer of a reaction material 26. The liquid flows through the reaction material 26 to the upper portion of the second container 24, from where it flows through a pipe 28, a flow control valve 30 and a second shut-off valve 32, a pipe 34 and the pipe 6 back to the suction side of the circulation pump 4.
The upper portions of the containers 16, 24 are connected to a three-way valve 36 through pipes 38 and 40, respectively. A pipe 42 connects the third passage of the three-way valve 36 to a drain 44.
A pipe 46, which may be connected to, for example, a water distribution system, not shown, carries clean flushing liquid through a third shut-off valve 48 to the pipe 22.
The filter material of the upper filter layer 18 of the container 16 may with advantage be formed by a granulated filter material, which may achieve, as the liquid flows down through the material, a removal of particles larger than 0,01 millimetres. To achieve adequate purification, the height of the upper filter layer 18 must be at least 0,4 metres. With a smaller filter layer height the ability of the filter to remove small particles is reduced, and so is the ability of the filter to accumulate sludge without increasing the pressure fall across the filter.
As the lower filter layer 20 of the first container 16 relatively fine sand is used with advantage. The task of the lower filter layer 20 is to prevent sludge from flowing together with liquid through the pipe 22 into the lower portion of the second container 26.
The reaction material 26 of the second container 24 comprises granulated magnesium oxide and/or calcium carbonate. A possible mixture must be adapted to the liquid quality. When the liquid flows relatively slowly up through the reaction material 26, part of the reaction material is dissolved in the liquid, favourably influencing the pH-value and alkalinity of the liquid with respect to corrosion.
A zinc electrode 50 is installed in an insulated manner in the upper portion of the second container 24. Through an ammeter 52 and wires 54 and 56 the zinc electrode is connected to the material of the second container 24. The amperage through the ammeter 52 reflects the pH-value of the liquid.
As the filter material 18, 20 of the first container 16 is being filled up with sludge, the flow resistance in the first container 16 increases. By counter-flow flushing through the filter material 18, 20, preferably with a sufficiently large quantity of liquid for the upper filter layer 18 and the lower filter layer 20 to be whirled up, the sludge present in the first container 16 is loosened, see Fig. 2.
The counter-flow flushing is carried out by closing the first shut-off valve 12 and the second shut-off valve 32, then opening of the three-way valve 36 to flow from the upper portion of the first container 16 through the pipes 38 and 42 to the drain 44. The third shut-off valve 48 is opened and' clean liquid flows from the pipe 46 through the third shut- off valve 48, the pipe 22, the first container 16, the pipe 38, the three-way valve 36 and the pipe 42 to the drain 44. The counter-flow flushing may be stopped when the exiting flushing liquid is clean. If desired, also the reaction material 26 may be flushed correspondingly in order for the granulated material to be loosened. The flushing is carried out as described above, but the three-way valve 36 is turned in such a way that it opens to liquid flow from the upper portion of the second container 24 through the pipes 40 and 42 to the drain 44 while closing, at the same time, the pipe 38, see Fig. 3. Thus, clean liquid flows from the pipe 46 through the third shut-off valve 48, the pipe 22, the second container 24, the pipe 40, the three- way valve 36 and the pipe 42 to the drain 44. The counter- flow flushing is stopped after a predetermined flushing time.
The method and device according to the invention allows a granulated filter material 18, 20, which is cleaned by means of counter-flow flushing, to be kept separated from the reaction material 26, whereby the direction of flow through the reaction material may be an upward one. By an upward flow, undue packing of the reaction material 26 is prevented, whereby the formation of channels with a subsequently reduced treating effect is essentially avoided.
The upward flow through the reaction material 26 permits installation of the zinc electrode 50 in the upper end portion of the second container 24, where it is exposed to sludge only to an insignificant degree.

Claims

C L A I M S
1. A method for the purification and treatment of liquid, wherein the liquid is purified by flowing through a filter material (18, 20), the filter material being arranged to be cleaned by means of counter-flow flushing, and wherein, with the aim of changing the pH- value and alkalinity of the liquid, the liquid flows through a reaction material (26) in the form of magnesium oxide and/or calcium carbonate, c h a r a c - teri z ed in that the liquid flows in a descending manner through the filter material, and flows in an ascending manner through the reaction material.
2. A device in purifying and treating equipment for a liquid, wherein the liquid is purified by flowing through a filter material (18, 20), the filter material being arranged to be cleaned by means of counter-flow flushing, and wherein, with the aim of changing the pH- value and alkalinity of the liquid, the liquid flows through a reaction material (26) in the form of magnesium oxide and/or calcium carbonate, c harac ter i z ed i n that a first container (16) containing the filter material (18, 20) is connected at its lower end portion through a pipe (22), in a communicating manner, to a second container (24) containing the reaction material (26).
3. A device according to claim 2, c haracteri z ed i n that the second container (24) is provided, at its upper end portion, with a zinc electrode (50) electrically insulated from the second container (24), the zinc electrode (50) being connected through an ammeter (52) and associated wires (54, 56) to the material of the second container (24).
PCT/NO2002/000396 2001-11-01 2002-10-31 Method and device for liquid treatment WO2003037803A1 (en)

Applications Claiming Priority (2)

Application Number Priority Date Filing Date Title
NO20015354A NO20015354L (en) 2001-11-01 2001-11-01 Liquid treatment method and apparatus
NO20015354 2001-11-01

Publications (1)

Publication Number Publication Date
WO2003037803A1 true WO2003037803A1 (en) 2003-05-08

Family

ID=19912980

Family Applications (1)

Application Number Title Priority Date Filing Date
PCT/NO2002/000396 WO2003037803A1 (en) 2001-11-01 2002-10-31 Method and device for liquid treatment

Country Status (2)

Country Link
NO (1) NO20015354L (en)
WO (1) WO2003037803A1 (en)

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
DK81963C (en) * 1950-12-15 1957-01-28 Magno Syn Werk G M B H Procedure for deacidifying drinking and drinking water.
DE3631218A1 (en) * 1986-09-13 1988-03-24 Dvgw Forschungsstelle Am Engle Process for treating acidic, heavy metal-containing and/or aluminium-containing raw waters
CH666474A5 (en) * 1985-09-18 1988-07-29 Peter Gysi System to neutralise condensate from heating boiler flue gas - has vessel contg permeable horizontal partition carrying neutralising granulate with condensate inlet and outlet above granulate
NO303968B1 (en) * 1996-06-07 1998-10-05 Rc Enwa As Process and liquid purification and treatment plant for purification of liquids
DE20102875U1 (en) * 2001-02-19 2002-06-20 Viessmann Werke GmbH & Co., 35108 Allendorf Device for neutralizing condensate water in boiler systems

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
DK81963C (en) * 1950-12-15 1957-01-28 Magno Syn Werk G M B H Procedure for deacidifying drinking and drinking water.
CH666474A5 (en) * 1985-09-18 1988-07-29 Peter Gysi System to neutralise condensate from heating boiler flue gas - has vessel contg permeable horizontal partition carrying neutralising granulate with condensate inlet and outlet above granulate
DE3631218A1 (en) * 1986-09-13 1988-03-24 Dvgw Forschungsstelle Am Engle Process for treating acidic, heavy metal-containing and/or aluminium-containing raw waters
NO303968B1 (en) * 1996-06-07 1998-10-05 Rc Enwa As Process and liquid purification and treatment plant for purification of liquids
DE20102875U1 (en) * 2001-02-19 2002-06-20 Viessmann Werke GmbH & Co., 35108 Allendorf Device for neutralizing condensate water in boiler systems

Also Published As

Publication number Publication date
NO20015354D0 (en) 2001-11-01
NO20015354L (en) 2003-05-02

Similar Documents

Publication Publication Date Title
Larson Corrosion by domestic waters
Cornwell et al. Pitting corrosion in copper tubes in cold water service
EP0912451B1 (en) A method and a device for the purification of fluids
CN110002661A (en) Method for treating desulfurized wastewater and utilization wet slag removal evaporation disposition desulfurization wastewater device
Larson Deterioration of water quality in distribution systems
US6416672B1 (en) Removal of dissolved and colloidal silica
WO2003037803A1 (en) Method and device for liquid treatment
Andritsos et al. Sulfide scale formation and control: the case of lead sulfide
US5522992A (en) Solution treatment device
Larson Chemical control of corrosion
Boffardi Corrosion inhibitors in the water treatment industry
US8075766B2 (en) Liquid filtration system
Robinette A novel adaptation of 1950 vintage technology to prevent pitting of copper heat exchanger tubes in a hydronic system infected by corrosive bacteria
Geesey et al. Unusual types of pitting corrosion of copper tubes in potable water systems
Stetter et al. Pilot scale studies on the removal of trace metal contaminations in drinking water treatment using chelating ion-exchange resins
Benjamin et al. Pilot testing a limestone contactor in British Columbia
CN217578537U (en) Coal gas water cleaning system
RU2150433C1 (en) Chemical water treatment process
US10717663B2 (en) Chemical denitrification of contaminated water
El Din The problem of “red waters”: A new approach to its solution
Pryor et al. Practical guidelines for safe operation of cooling tower water ozonation systems
Vaughan Aeration for carbon dioxide removal from water supply of Sioux Falls, South Dakota
CN117185402A (en) Desulfurization wastewater treatment system and method
Bhalerao et al. Application of corrosion control techniques in municipal water and waste water engineering
JP3190463U (en) Water reforming tools

Legal Events

Date Code Title Description
AK Designated states

Kind code of ref document: A1

Designated state(s): AE AG AL AM AT AU AZ BA BB BG BR BY BZ CA CH CN CO CR CU CZ DE DK DM DZ EC EE ES FI GB GD GE GH GM HR HU ID IL IN IS JP KE KG KP KR KZ LC LK LR LS LT LU LV MA MD MG MK MN MW MX MZ NO NZ OM PH PL PT RO RU SD SE SG SI SK SL TJ TM TN TR TT TZ UA UG US UZ VC VN YU ZA ZM ZW

AL Designated countries for regional patents

Kind code of ref document: A1

Designated state(s): GH GM KE LS MW MZ SD SL SZ TZ UG ZM ZW AM AZ BY KG KZ MD RU TJ TM AT BE BG CH CY CZ DE DK EE ES FI FR GB GR IE IT LU MC NL PT SE SK TR BF BJ CF CG CI CM GA GN GQ GW ML MR NE SN TD TG

121 Ep: the epo has been informed by wipo that ep was designated in this application
122 Ep: pct application non-entry in european phase
NENP Non-entry into the national phase

Ref country code: JP

WWW Wipo information: withdrawn in national office

Country of ref document: JP