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WO1997007060A1 - Water treatment method - Google Patents

Water treatment method Download PDF

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Publication number
WO1997007060A1
WO1997007060A1 PCT/GB1996/001940 GB9601940W WO9707060A1 WO 1997007060 A1 WO1997007060 A1 WO 1997007060A1 GB 9601940 W GB9601940 W GB 9601940W WO 9707060 A1 WO9707060 A1 WO 9707060A1
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WO
WIPO (PCT)
Prior art keywords
water
biocidal
heat exchanger
cell
passed
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Ceased
Application number
PCT/GB1996/001940
Other languages
French (fr)
Inventor
Thomas Emlyn Gantert
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
KEM-FREE TECHNOLOGY Ltd
Original Assignee
KEM-FREE TECHNOLOGY Ltd
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 KEM-FREE TECHNOLOGY Ltd filed Critical KEM-FREE TECHNOLOGY Ltd
Priority to AU67064/96A priority Critical patent/AU6706496A/en
Publication of WO1997007060A1 publication Critical patent/WO1997007060A1/en
Anticipated expiration legal-status Critical
Ceased legal-status Critical Current

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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
    • C02F1/48Treatment of water, waste water, or sewage with magnetic or electric fields
    • 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
    • C02F1/46Treatment of water, waste water, or sewage by electrochemical methods
    • C02F1/4606Treatment of water, waste water, or sewage by electrochemical methods for producing oligodynamic substances to disinfect the water
    • 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
    • C02F2303/00Specific treatment goals
    • C02F2303/22Eliminating or preventing deposits, scale removal, scale prevention

Definitions

  • This invention relates to an improved method of treating water to eliminate undesired solutes and bioforms, and particularly to the treatment of cooling water.
  • the cooling of a great many devices involves transfer of heat from the device to a flow of water which is later cooled by a contraflowing stream of air. Cooling of the water often takes place in a so-called cooling tower in which the hot water from the device is sprayed or allowed to cascade in a manner that increases its surface area while it falls under the action of gravity into a sump. Cooling takes place through heat exchange with the contraflowing air and by evaporation. The cooled water that accumulates in the sump is subsequently re-used and pumped back into the device to be cooled. In factories and offices the ambient air is often maintained at a substantially constant temperature and humidity by a process called 'air conditioning'.
  • a further problem that occurs when treating cooling water is the build-up of solid residues on the interior surfaces of pipes, valves and other water carrying parts of the system.
  • the solids arise from precipitation of insoluble calcium and magnesium compounds which were present initially as soluble salts. Removal of these salts prior to use by ion exchange processes is expensive and increases the total volume of water consumed by the system due to the water used in the regeneration of the ion exchange medium.
  • the present invention provides a system for treating water which eliminates undesired solutes and bioforms without the use of chemical additives for either purpose and substantially eliminates the build up of solid residues in the system.
  • a method of treating water supplied to an evaporative cooler comprising subjecting the water to water conditioning treatment by the application of an electromagnetic radiat ⁇ ion field, passing the water through a heat exchanger in which it extracts thermal energy from the heat exchanger or fluid passing through it, passing the water to a first dispersion means whereby the water is formed into small droplets which fall under the action of gravity directly or through one or more baffles to a collection reservoir where the suspended solids are able to settle under the influence of gravity to a sump, returning the supernatant water from the reservoir to the water heat exchanger and passing the sump contents to a series of filters and through an electrolytic biocidal cell to a second dispersion means whereby the water is formed into small droplets which fall under the action of gravity directly or through one or more baffles to the collection reservoir.
  • the water conditioner is preferably one using an electromagnetic field in the radio frequency band.
  • the power may be varied in accordance with the rate of flow of the water being treated; such water conditioners are described in GB-A-2 246 725 or WO-A-92 00916.
  • the effect of such conditioners is to change certain salts in solution as ions in the water flowing through the conditioner field into colloidal suspensions. It is possible for the suspensions to re-dissolve however by careful manipulation of the conditioned water the suspended particles can be caused to agglomerate and precipitate. In the process of the present invention the solid suspended particles are removed by filtration prior to recirculation of the treated cooling water.
  • the water After the water has been conditioned it is passed through a heat exchanger in which the thermal energy from a hot fluid pas ⁇ ing through the heat exchanger is trans ⁇ ferred to the cooling water passing through it.
  • a heat exchanger in which the thermal energy from a hot fluid pas ⁇ ing through the heat exchanger is trans ⁇ ferred to the cooling water passing through it.
  • Such heat exchangers are well known and their design is dictated by the rate of flow of the two fluids, the contact surface area and the thickness and composition of the material, normally a metal or alloy, from which the exchanger is constructed.
  • the heated water leaving the heat exchanger is passed to a fir ⁇ t dispersion means whereby the water is formed into small droplets by spray jets or passage through a perforated pipe.
  • the droplets of heated water fall under the action of gravity directly or through one or more baffles to a collection reservoir.
  • the droplets lose thermal energy by direct transfer to the air and by partial evaporation.
  • the structure in which the droplets fall is formed with an outer shell which entraps the air entering at the lower end so that it rises at ever increasing velocity within a venturi.
  • Such cooling systems are well known and emit a mixture of heated air and water vapour at their upper end giving rise to visible vapour clouds when cooled by the external air.
  • the structure ⁇ are often referred to as 'cooling towers'.
  • the solids suspended Due to the evaporative lo ⁇ ses the solids suspended are concentrated and able to settle, without re-solution, in a sump located at the lower end of a cooling tower.
  • the supernatant water above the sump is passed through a series of filters and through an electrolytic biocidal cell before reuse by pumping to a second disper ⁇ ion mean ⁇ .
  • the water In the second dispersion means the water is formed into small droplets as described previously and allowed to fall as previously described through one or more baffles to the collection reservoir.
  • the first filter into which the supernatant water is passed has a coarse structure to remove debris, such as insects, leaves, etc., picked up by the water droplets as they fall through the cooling tower.
  • This is followed by a second filter which remove ⁇ smaller particle ⁇ such a ⁇ aggregated solids released from ⁇ olution initially by the water conditioner.
  • Such filter systems are known and in u ⁇ e with ⁇ wimming pool cleaning ⁇ ystem ⁇ .
  • the filtered water After the filtered water leaves the filter system it enters an electrolytic biocidal cell in which biocidal metal ion ⁇ are released into the water.
  • Cells of thi ⁇ nature are known in which the electrode ⁇ are formed from an alloy compri ⁇ ing copper and ⁇ ilver; the ratio of the metals preferably lies in the range 90/10 to 70/30.
  • electrodes of different compositions may be used according to the history of the cooling water in the system.
  • By appropriate construction of the electrode system and control of the magnitude and polarity of the potential applied to the electrodes even wear can be achieved a ⁇ the metal ⁇ are relea ⁇ ed into the water passing through. It is possible to monitor the level of released ions downstream of the electrode system and ensure that the concentration is maintained at the desired level.
  • a self- compen ⁇ ating system providing a regular reversal of electr ⁇ ode polarity is preferred in which the electrodes are maintained at a preset con ⁇ tant potential.
  • Both copper and ⁇ ilver are toxic to mo ⁇ t bacteria and fungal species so that any such undesirable life forms picked up during the passage of the water through the cooling tower will be inactivated and, provided sufficient ion ⁇ are released into the ⁇ ystem, bacterial and fungal growth in the exposed areas of the cooling tower and within the fluid system will be prevented.
  • FIG. 1 is a schematic diagram of a water treatment system according to the invention.
  • FIG 2 is a cross- ⁇ ectional view of a biocidal electrode used in the system of Figure 1.
  • An evaporative cooling system incorporating the water treatment method of the present invention see Figure 1, consists of a heat exchanger l which is supplied with heated fluid, such as steam or refrigerant condensate, from a thermal engine, not shown.
  • heated fluid such as steam or refrigerant condensate
  • the heated fluid flows through tubes 2 in thermal contact with coolant water in a manifold 3.
  • the coolant water is supplied to the heat exchanger 1 from a reservoir 4 by means of a pump 5.
  • the pumped water passes through a pipe 6 which is fitted with a water conditioner 7.
  • a first dispersion means 8 consisting of a pipe 9 carrying a series of dispersion roses 11 placed at the top of an enclosed cooling tower 12.
  • the water leaves the roses 11 in the form of fine droplets which fall on a series of baffles 13 so as to increase the effective path through the cooling area.
  • the droplets accumulate in the reservoir 4.
  • the air that enters the lower end of the tower through apertures 14 is drawn upwards by means of a fan 15 located at the upper end of the tower.
  • a baffle 16 acts as a drift suppressor and prevents water droplets being sucked out of the cooling system.
  • the reservoir 4 is kept at a steady level by the addition of further water from a mains supply controlled by a float valve 17.
  • the lower portion of the reservoir 4 forms a sump 18 where a mixture of water and solids accumulate.
  • the residue in the sump 18 is sucked through a coarse filter 19 by means of a second pump 21.
  • the output of the pump 21 is directed into a sand filter 22 where the majority of solid particles are removed from the water passing through it.
  • the pump 21 and filter 22 are fitted with a control system, not shown, which causes an intermittent reversal of flow to prevent the filter 22 becoming clogged.
  • the effluent from the filter 22 flows through an electrolytic biocidal cell 23 which releases copper and silver ions into the water.
  • the water enters a second dispersion means 24 con ⁇ i ⁇ ting of a pipe 25 carrying a series of disper ⁇ ion roses 26 placed above the first dipersion mean ⁇ 8.
  • the water leaves the roses and pas ⁇ es through the cooling tower 12, in the manner previously described, and accumulate ⁇ in the reservoir 4.
  • any 'hardness' or dissolved metals, such as calcium and magnesium, from the mains supply water used to top up the reservoir 4 will be converted to a solid suspension before entering the heat exchanger 1 so that the build-up of scale deposits will be prevented.
  • a ⁇ the water i ⁇ re-cycled and after filtration any bioform ⁇ picked up from the air entering the cooling ⁇ y ⁇ tem or from other ⁇ ources are killed or rendered impotent by the copper and ⁇ ilver ion ⁇ from the electro ⁇ lytic cell 23.
  • a ⁇ ociated with the water treatment ⁇ ystem described will be control system ⁇ .
  • the water conditioner 7 will require a control system to alter the magnetic field in accordance with the turbulence of the water pas ⁇ ing through it if it is of the type de ⁇ cribed in EP-0 493 559.
  • the electrolytic cell require ⁇ a control ⁇ ystem to ensure the correct level of biocidal ions is maintained.
  • Further control systems are required to control the water flow and filtration in accordance with the thermal load placed on the cooling system. The design and operation of such systems is known and the control features may be conven ⁇ iently incorporated in a suitably programmed microprocessor controller.
  • the biocidal electrode comprises a pipe 31 having a constriction 32 which, in conjunction with a deflector plate 33, ensures that water flowing through the pipe circulates around the electrode ⁇ tructure 34.
  • the electrode structure is formed from a number of electrodes of an alloy in which the ratio of copper to silver i ⁇ 80 to 20.
  • the electrode ⁇ tructure i ⁇ held in a branch pipe 35 by mean ⁇ of a screw fitted plug 36 sealed with an 'O'ring 37.
  • the rear of the electrode 34 is attached to the plug 36 by means of bolts 38 which also act as terminals for connecting the nece ⁇ sary electrical supply to the electr- ode ⁇ .
  • the electrolytic sy ⁇ tem operate ⁇ the electrode ⁇ dissolve and must be replaced at infrequent interval ⁇ . Replacement is carried out simply by unscrewing the plug 36 and the bolts 38.

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  • Chemical & Material Sciences (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Organic Chemistry (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Electrochemistry (AREA)
  • General Chemical & Material Sciences (AREA)
  • Water Treatment By Electricity Or Magnetism (AREA)

Abstract

Water supplied to an evaporative cooler is treated by a number of successive steps, comprising (1) water conditioning by an electromagnetic radiation field, preferably in the radio frequency band; (2) the conditioned water is passed through a heat exchanger; (3) the water is passed to a first dispersion means whereby the water is formed into small droplets which fall, under the action of gravity directly or through one or more baffles, to a collection reservoir where the suspended solids are able to settle under the influence of gravity to a sump; (4) the supernatant water is returned from the reservoir to the water heat exchanger; (5) the sump contents is passed to a series of filters and through an electrolytic biocidal cell to a second dispersion means operating as described previously.

Description

WATER TREATMENT METHOD
This invention relates to an improved method of treating water to eliminate undesired solutes and bioforms, and particularly to the treatment of cooling water.
The cooling of a great many devices involves transfer of heat from the device to a flow of water which is later cooled by a contraflowing stream of air. Cooling of the water often takes place in a so-called cooling tower in which the hot water from the device is sprayed or allowed to cascade in a manner that increases its surface area while it falls under the action of gravity into a sump. Cooling takes place through heat exchange with the contraflowing air and by evaporation. The cooled water that accumulates in the sump is subsequently re-used and pumped back into the device to be cooled. In factories and offices the ambient air is often maintained at a substantially constant temperature and humidity by a process called 'air conditioning'. The necessary cooling of ambient air to remove moisture and, when necessary, lower temperature requires a refrigeration plant which cannot operate without cooling for the refrigerant. Except in the case of very small plants external water cooling is used. The temperature of the water used for cooling is often ideal for the growth of bacteria and other bioforms. Sufficient nutrients are usually present for large colonies of pathogenic bacteria to be created and inevitably dispersed in droplets of cooling water. In the event that εuch droplets are ingested through the lungs of humans or animals serious and even fatal infections may result.
It has been proposed that the growth of bacteria and other unwanted bioforms may be eliminated by the addition of biocidal chemicals to cooling water. This solution to the problem is not totally satisfactory as there is consid¬ erable cost involved. Careful monitoring must be carried out to ensure adequate amounts of biocide are present in the cooling water to prevent bacterial build-up avoiding excessive usage. Many of the biocidal chemicals are highly toxic in their undiluted form, hazardous to handle and their residueε are environmentally undesirable.
A further problem that occurs when treating cooling water is the build-up of solid residues on the interior surfaces of pipes, valves and other water carrying parts of the system. The solids arise from precipitation of insoluble calcium and magnesium compounds which were present initially as soluble salts. Removal of these salts prior to use by ion exchange processes is expensive and increases the total volume of water consumed by the system due to the water used in the regeneration of the ion exchange medium.
The present invention provides a system for treating water which eliminates undesired solutes and bioforms without the use of chemical additives for either purpose and substantially eliminates the build up of solid residues in the system.
According to the present invention there is provided a method of treating water supplied to an evaporative cooler comprising subjecting the water to water conditioning treatment by the application of an electromagnetic radiat¬ ion field, passing the water through a heat exchanger in which it extracts thermal energy from the heat exchanger or fluid passing through it, passing the water to a first dispersion means whereby the water is formed into small droplets which fall under the action of gravity directly or through one or more baffles to a collection reservoir where the suspended solids are able to settle under the influence of gravity to a sump, returning the supernatant water from the reservoir to the water heat exchanger and passing the sump contents to a series of filters and through an electrolytic biocidal cell to a second dispersion means whereby the water is formed into small droplets which fall under the action of gravity directly or through one or more baffles to the collection reservoir.
The water conditioner is preferably one using an electromagnetic field in the radio frequency band. The power may be varied in accordance with the rate of flow of the water being treated; such water conditioners are described in GB-A-2 246 725 or WO-A-92 00916. The effect of such conditioners is to change certain salts in solution as ions in the water flowing through the conditioner field into colloidal suspensions. It is possible for the suspensions to re-dissolve however by careful manipulation of the conditioned water the suspended particles can be caused to agglomerate and precipitate. In the process of the present invention the solid suspended particles are removed by filtration prior to recirculation of the treated cooling water.
After the water has been conditioned it is passed through a heat exchanger in which the thermal energy from a hot fluid pasεing through the heat exchanger is trans¬ ferred to the cooling water passing through it. Such heat exchangers are well known and their design is dictated by the rate of flow of the two fluids, the contact surface area and the thickness and composition of the material, normally a metal or alloy, from which the exchanger is constructed. The heated water leaving the heat exchanger is passed to a firεt dispersion means whereby the water is formed into small droplets by spray jets or passage through a perforated pipe. The droplets of heated water fall under the action of gravity directly or through one or more baffles to a collection reservoir. During their fall the droplets lose thermal energy by direct transfer to the air and by partial evaporation. To assist the thermal energy loss the structure in which the droplets fall is formed with an outer shell which entraps the air entering at the lower end so that it rises at ever increasing velocity within a venturi. Such cooling systems are well known and emit a mixture of heated air and water vapour at their upper end giving rise to visible vapour clouds when cooled by the external air. The structureε are often referred to as 'cooling towers'.
Due to the evaporative loεses the solids suspended are concentrated and able to settle, without re-solution, in a sump located at the lower end of a cooling tower. The supernatant water above the sump is passed through a series of filters and through an electrolytic biocidal cell before reuse by pumping to a second disperεion meanε. In the second dispersion means the water is formed into small droplets as described previously and allowed to fall as previously described through one or more baffles to the collection reservoir.
The first filter into which the supernatant water is passed has a coarse structure to remove debris, such as insects, leaves, etc., picked up by the water droplets as they fall through the cooling tower. This is followed by a second filter which removeε smaller particleε such aε aggregated solids released from εolution initially by the water conditioner. Such filter systems are known and in uεe with εwimming pool cleaning εystemε.
After the filtered water leaves the filter system it enters an electrolytic biocidal cell in which biocidal metal ionε are released into the water. Cells of thiε nature are known in which the electrodeε are formed from an alloy compriεing copper and εilver; the ratio of the metals preferably lies in the range 90/10 to 70/30. In a given installation electrodes of different compositions may be used according to the history of the cooling water in the system. By appropriate construction of the electrode system and control of the magnitude and polarity of the potential applied to the electrodes even wear can be achieved aε the metalε are releaεed into the water passing through. It is possible to monitor the level of released ions downstream of the electrode system and ensure that the concentration is maintained at the desired level. A self- compenεating system providing a regular reversal of electr¬ ode polarity is preferred in which the electrodes are maintained at a preset conεtant potential. Both copper and εilver are toxic to moεt bacteria and fungal species so that any such undesirable life forms picked up during the passage of the water through the cooling tower will be inactivated and, provided sufficient ionε are released into the εystem, bacterial and fungal growth in the exposed areas of the cooling tower and within the fluid system will be prevented.
In order that the invention may be clearly understood, one form thereof will be described with reference to the accompanying drawings in which:
Figure 1 is a schematic diagram of a water treatment system according to the invention, and
Figure 2 is a cross-εectional view of a biocidal electrode used in the system of Figure 1. An evaporative cooling system incorporating the water treatment method of the present invention, see Figure 1, consists of a heat exchanger l which is supplied with heated fluid, such as steam or refrigerant condensate, from a thermal engine, not shown. The heated fluid flows through tubes 2 in thermal contact with coolant water in a manifold 3. The coolant water is supplied to the heat exchanger 1 from a reservoir 4 by means of a pump 5. The pumped water passes through a pipe 6 which is fitted with a water conditioner 7. Af er passage through the heat exchanger 1 the water enters a first dispersion means 8 consisting of a pipe 9 carrying a series of dispersion roses 11 placed at the top of an enclosed cooling tower 12. The water leaves the roses 11 in the form of fine droplets which fall on a series of baffles 13 so as to increase the effective path through the cooling area. At the bottom of the tower the droplets accumulate in the reservoir 4.
In order to ensure a steady and rapid air flow through the tower 12 the air that enters the lower end of the tower through apertures 14 is drawn upwards by means of a fan 15 located at the upper end of the tower. A baffle 16 acts as a drift suppressor and prevents water droplets being sucked out of the cooling system. The reservoir 4 is kept at a steady level by the addition of further water from a mains supply controlled by a float valve 17. The lower portion of the reservoir 4 forms a sump 18 where a mixture of water and solids accumulate.
The residue in the sump 18 is sucked through a coarse filter 19 by means of a second pump 21. The output of the pump 21 is directed into a sand filter 22 where the majority of solid particles are removed from the water passing through it. The pump 21 and filter 22 are fitted with a control system, not shown, which causes an intermittent reversal of flow to prevent the filter 22 becoming clogged. The effluent from the filter 22 flows through an electrolytic biocidal cell 23 which releases copper and silver ions into the water. After the biocidal treatment the water enters a second dispersion means 24 conεiεting of a pipe 25 carrying a series of disperεion roses 26 placed above the first dipersion meanε 8. The water leaves the roses and pasεes through the cooling tower 12, in the manner previously described, and accumulateε in the reservoir 4.
It will be seen that any 'hardness' or dissolved metals, such as calcium and magnesium, from the mains supply water used to top up the reservoir 4 will be converted to a solid suspension before entering the heat exchanger 1 so that the build-up of scale deposits will be prevented. Aε the water iε re-cycled and after filtration any bioformε picked up from the air entering the cooling εyεtem or from other εources are killed or rendered impotent by the copper and εilver ionε from the electro¬ lytic cell 23.
Aεεociated with the water treatment εystem described will be control systemε. The water conditioner 7 will require a control system to alter the magnetic field in accordance with the turbulence of the water pasεing through it if it is of the type deεcribed in EP-0 493 559. The electrolytic cell requireε a control εystem to ensure the correct level of biocidal ions is maintained. Further control systems are required to control the water flow and filtration in accordance with the thermal load placed on the cooling system. The design and operation of such systems is known and the control features may be conven¬ iently incorporated in a suitably programmed microprocessor controller. The biocidal electrode, see Figure 2, comprises a pipe 31 having a constriction 32 which, in conjunction with a deflector plate 33, ensures that water flowing through the pipe circulates around the electrode εtructure 34. The electrode structure is formed from a number of electrodes of an alloy in which the ratio of copper to silver iε 80 to 20. The electrode εtructure iε held in a branch pipe 35 by meanε of a screw fitted plug 36 sealed with an 'O'ring 37. The rear of the electrode 34 is attached to the plug 36 by means of bolts 38 which also act as terminals for connecting the neceεsary electrical supply to the electr- odeε. As the electrolytic syεtem operateε the electrodeε dissolve and must be replaced at infrequent intervalε. Replacement is carried out simply by unscrewing the plug 36 and the bolts 38.
In a practical test a water treatment installation operating in accordance with the invention was fitted to a cooling tower having a flow rate of approximately 2000 litres per minute and a sump or reservoir of approximately 2000 litres. The water inlet temperature was about 35 degrees Celcius which dropped to 24 degrees on cooling. In spite of the ideal conditions for forming scale in the heat exchanger and for the growth of bioforms neither occurred.

Claims

1. A method of treating water supplied to an evaporative cooler comprising the stepε of (1) subjecting the water to water conditioning treatment by the application of an electromagnetic radiation field, (2) pasεing the water through a heat exchanger in which it extracts thermal energy from the heat exchanger or fluid passing through it, (3) passing the water to a firεt diεperεion meanε whereby the water iε formed into small dropletε which fall under the action of gravity directly or through one or more baffleε to a collection reεervoir where the suspended εolidε are able to εettle under the influence of gravity to a sump, (4) returning the supernatant water from the reservoir to the water heat exchanger and (5) pasεing the sump contents to a series of filters and through an electrolytic biocidal cell to a second dispersion means whereby the water is formed into small droplets which fall under the action of gravity directly or through one or more baffles to the collection reservoir.
2. The method according to claim 1 wherein the water conditioner useε an electromagnetic field in the radio frequency band.
3. The method according to either claim 1 or claim 2 wherein the power supplied to the water conditioner iε varied in accordance with the rate of flow of the water being treated.
4. The method according to any of the preceding claimε, wherein any solid suspended particles are removed by filtration prior to recirculation of the treated cooling water.
5. The method according to any of the preceding claims, wherein after the water has been conditioned it is passed through a heat exchanger in which the thermal energy from a hot fluid passing through the heat exchanger is trans- ferred to the water paεεing through it.
6. The method according to any of the preceding claims, wherein the heated water leaving the heat exchanger is passed to a first dispersion means whereby the water is formed into small droplets by spray jets or passage through a perforated pipe.
7. The method according to any of the preceding claims, wherein the supernatant water above the sump is passed through a series of filters and through an electrolytic biocidal cell before reuse by pumping to the second dispersion means.
8. The method according to claim 7, wherein there are two filters, a first filter into which the supernatant water is passed having a coarse structure followed by a second filter which having a finer structure to remove particles, such as aggregated solids, released from solution by the water conditioner.
9. The method according to claims 7 or 8, wherein after the filtered water leaves the filter system it enters the electrolytic biocidal cell in which biocidal metal ions are released into the water.
10. The method according to claim 9, wherein the level of released biocidal ions downstream of the electrode εystem iε monitored to enεure that the concentration iε maintained at a deεired level .
11. The method according to claims 9 or 10, wherein the polarity of the electrodes in the biocidal cell is regularly reversed and wherein the electrodes are maintained at a preset constant potential.
12. The method according to claims 9 to 11, wherein the electrodes in the biocidal cell are formed from a subεtantially copper and silver alloy.
13. The method according to claims 9 or 10, wherein the polarity of the electrodes in the biocidal cell is regularly reversed and wherein the electrodes are maintained at a preset constant potential.
14. Methods of treating water supplied to an evaporative cooler according to claim 1 and as herein described.
15. Methods of treating water supplied to an evaporative cooler as herein described with reference to the accompanying drawings.
PCT/GB1996/001940 1995-08-18 1996-08-09 Water treatment method Ceased WO1997007060A1 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
AU67064/96A AU6706496A (en) 1995-08-18 1996-08-09 Water treatment method

Applications Claiming Priority (2)

Application Number Priority Date Filing Date Title
GB9516980.1 1995-08-18
GB9516980A GB2304338A (en) 1995-08-18 1995-08-18 Water treatment method

Publications (1)

Publication Number Publication Date
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GB (1) GB2304338A (en)
WO (1) WO1997007060A1 (en)
ZA (1) ZA966970B (en)

Cited By (3)

* Cited by examiner, † Cited by third party
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WO2001090001A1 (en) * 2000-05-19 2001-11-29 Watermaid Pty. Ltd. Cooling tower maintenance
AU2001252029B2 (en) * 2000-05-19 2004-09-23 Watermaid Pty. Ltd. Cooling tower maintenance
WO2024022853A3 (en) * 2022-07-29 2024-08-15 Skirde Mark Oliver Device and method for disinfecting and cleaning room air and for disinfecting surfaces

Families Citing this family (3)

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WO2001019736A1 (en) * 1999-09-15 2001-03-22 Everclear Environmental Technologies Corporation Water-treatment system for heating, ventilation and air conditioning system
CN100501291C (en) * 2006-01-18 2009-06-17 金兴才 Closed cooling tower
CN103411444A (en) * 2013-07-31 2013-11-27 南京威安新材料科技有限公司 Dry type convective cooling tower

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Publication number Priority date Publication date Assignee Title
WO1992000916A1 (en) * 1990-07-11 1992-01-23 Daniel Stefanini Water conditioners

Patent Citations (2)

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Publication number Priority date Publication date Assignee Title
WO1992000916A1 (en) * 1990-07-11 1992-01-23 Daniel Stefanini Water conditioners
GB2246725A (en) * 1990-07-11 1992-02-12 Daniel Stefanini Electrical water conditioner

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2001090001A1 (en) * 2000-05-19 2001-11-29 Watermaid Pty. Ltd. Cooling tower maintenance
AU2001252029B2 (en) * 2000-05-19 2004-09-23 Watermaid Pty. Ltd. Cooling tower maintenance
WO2024022853A3 (en) * 2022-07-29 2024-08-15 Skirde Mark Oliver Device and method for disinfecting and cleaning room air and for disinfecting surfaces

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GB9516980D0 (en) 1995-10-18
AU6706496A (en) 1997-03-12
GB2304338A (en) 1997-03-19
ZA966970B (en) 1997-10-31

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