GB1600289A - Sterilisation of water for nutrient film systems - Google Patents
Sterilisation of water for nutrient film systems Download PDFInfo
- Publication number
- GB1600289A GB1600289A GB35973/77A GB3597377A GB1600289A GB 1600289 A GB1600289 A GB 1600289A GB 35973/77 A GB35973/77 A GB 35973/77A GB 3597377 A GB3597377 A GB 3597377A GB 1600289 A GB1600289 A GB 1600289A
- Authority
- GB
- United Kingdom
- Prior art keywords
- water
- pathogenicide
- chlorine
- halogen
- fed
- 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.)
- Expired
Links
Classifications
-
- 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
- C02F1/50—Treatment of water, waste water, or sewage by addition or application of a germicide or by oligodynamic treatment
-
- A—HUMAN NECESSITIES
- A01—AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
- A01G—HORTICULTURE; CULTIVATION OF VEGETABLES, FLOWERS, RICE, FRUIT, VINES, HOPS OR SEAWEED; FORESTRY; WATERING
- A01G31/00—Soilless cultivation, e.g. hydroponics
-
- 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
- C02F1/72—Treatment of water, waste water, or sewage by oxidation
- C02F1/76—Treatment of water, waste water, or sewage by oxidation with halogens or compounds of halogens
Description
(54) STERILISATION OF WATER FOR NUTRIENT
FILM SYSTEMS
(71) We, FISONS LIMITED, a British
Company, of Fison House, 9 Grosvenor
Street, London WIX OAH, do hereby declare the invention, for which we pray that a patent may be granted to us, and the method by by which it is to be performed, to be particularly described in and by the following statement:- The present invention relates to a process and a composition for use therein.
It has been proposed to grow plants with their roots immersed in a flowing film of liquid containing plant nutrients. Typically, a shallow waterproof trough is formed and a film of aqueous nutrient solution flows through the trough, is collected, e.g. in a sump tank, and recycled, e.g. to a header tank, from whence it is fed back to the trough. During the cycle, water and nutrients are taken up by the plant and these require replacement before the nutrient solution is recycled. This is conveniently done in a mixing tank before the solution is recycled. Such a plant growth system is called hereinafter a nutrient film system.
However, problems are encountered with such a system in that bacterial and other infections are rapidly transmitted from one plant to another throughout the system. We have devised a method and composition for reducing the risk of infection.
The present invention provides a process for treating water fed to or circulating in a nutrient film system which comprises incorporating a plant physiologically acceptable amount of a pathogenicide into the water.
The term pathogenicide is used herein to denote materials which not only kill plant pathogens. e.g. bacteria, fungi, algae and/or viruses, outright but which also inhibit growth and/or development of the plant pathogens so as to minimise any increase in infection. Thus the term pathogenicide includes pathogenistat materials.
Suitable pathogenicides for present use include halogen (e.g. chlorine or bromine), halogen donors, permanganates. and benzimidazole and other fungicides (e.g.
carbendazim prothiocarb and etridiazole).
The use of halogen donors is particularly preferred since we have found that plants in general can tolerate high levels of halogen and the risk of damage due to errors in dosing halogen donors may be less than with other forms of pathogenicide.
The halogen donors for present use include hypohalites, e.g. sodium or calcium hypochlorite, and organic compounds, e.g.
halogenated alkylhydantoins, notably dibromo-dimethyl hydantoin, and sulphonchloramides, e.g. Chloramine T.
However, particularly preferred halogen donors for present use are those of the general formula:
and hydrates thereof wherein X is halogen, notable chlorine or bromine; and M is selected from halogen or an alkali-metal. It is preferred that X and at least one M be chlorine. Suitable halogen donors thus include trichloroisocyanuric acid, monosodium dichloroisocyanurate monopotassium dichloroisocyanurate; and hydrates thereof, notably the dihydrate of monosodium dichloroisocyanurate. The halogen donors may be used alone or in admixture with one another and may be used in their commercially available forms or purities. For example the donor may be used in association with cyanuric acid or a salt thereof.
The use of the dihydrate of monosodium dichloroiso cyanurate is especially preferred as this hydrate offers advantages in stability during storage and handling, notably when used in admixture with fertilizer salts. The use of trichloroisocyanuric acid offers the advantage of a sustained release of chlorine over a period of time.
Suitable permanganates for present use include alkali-metal, alkaline-earth metal and/or ammonium permanganates, notably potassium or calcium permanganate. The permanganates may be used in their commercially available forms and purity.
The presence of the permanganate in the circulating nutrient solution will cause the solution to have a purple colour. Where there is insufficient permanganate to destroy oxidisable organisms in the water, the solution will revert to is nonpermanganated colour (usually brownish).
Thus, the colour of the nutrient solution offers a clear warning that the permanganate has been consumed and that there is a risk of infection in the solution.
The fertilizer composition for present use is one containing N, P and K compounds and is characterised in that it is a water soluble composition. Preferably at least 80% by weight of a 10g sample of the fertilizer composition is dissolved after shaking with 1 litre of deionised water at 250C for 10 minutes. Thus, the fertilizer composition for present use typically contains ammonium, potassium and/or calcium nitrates, ammonium and/or potassium phosphate, magnesium sulphate and trace elements (e.g. copper sulphate, iron/ethylenediamine tetra-acetic acid complex, boric acid etc). If desired some of the fertilizer ingredients are added separately, e.g. as nitric acid and/or phosphoric acid feeds to the nutrient film system.
Where the fertilizer salts contain ammonia, this may combine with the available chlorine released by a halogen donor to form chloramines. We have found that chloramines provide a particularly preferred form of available chlorine for use in nutrient film systems since they have a slower action then uncombined available chlorine. Thus, chlorinating material persists in the water throughout its circulation without the need to add high initial levels of chlorine. Also, chloramines may cause less hardening of the plant cell structure than does uncombined chlorine.
Accordingly, the present invention provides a process for treating water in a nutrient film system which comprises incorporating chloramine into water fed to or circulating in the nutrient film system.
The chloramine is preferably monochloramine, although mixtures of mono and/or di-chloramine may be used.
The chloramine is conveniently formed in situ in the water or in a separate vessel from which it is dosed at the desired rate into the water. The chloramine is formed by the
reaction of chlorine of a chlorine donor
(notably a compound of formula 1) with
ammonia or an ammonium salt. The
ammonium salt is conveniently provided by
an ingredient in the fertilizer composition,
e.g. ammonium phosphate and/or
ammonium sulphate. It is preferred to
provide an excess of ammonium salt, e.g.
greater than 2, preferably at least 5, molar excess over that theoretically required to
convert the available chlorine to mono
chloramine. The excess of ammonium salt
also reduces the rate of decomposition of the chloramine and an excess of up to 500
molar percent of ammonium salt may be
used, if desired.
The amount of pathogenicide material
which is used will vary with the nature of the
material and the infection which is to be treated. Thus it will usually be desired to maintain from 0.2 to 10 parts per million of available halogen in the nutrient solution in the nutrient film system where a halogen or halogen donor is used, from 0.3 to 20 ppm of the chloramine (expressed as monochloromine equivalent) or from 1 to 10 ppm of Mn equivalent. In general satisfactory results may be achieved when from 0.2 to 30 ppm of the active component of the pathogenicide are maintained in the nutrient solution. In general the fertilizer mixtures will contain iron and the pathogenicide will usually be present in
from 50 to 2000to by weight of the iron. The iron is typically present in from 0.5 to 2 (; by weight (expressed as Fe) of the fertilizer.
Therefore the pathogenicide active ingredient will typically be present in from 0.25 to 4% by weight of total fertilizer composition.
The pathogenicide can be incorporated
into the water fed to or circulating in the
nutrient film system using a number of methods. Thus, it can be fed to the water separately from the fertilizer, e.g. by dosing the water with a suitable concentrate or by passing the water in contact with the solid pathogenicide. For example loose tablets of the pathogenicide can be placed in the sump tank of the nutrient film system, or a perforated net or tube containing the tablets can be suspended in the sump.
Alternatively, the pathogenicide can be incorporated into the fertilizer formulation and this then dosed to the water, notably as a concentrate, optionally with one or more of the fertilizer ingredients being fed separately. In the case of chloramines these are most conveniently formed in situ in the
nutrient solution by the reaction of a chlorine donor with an ammonium salt.
Where an aqueous solution, suspension or emulsion of the pathogenicide and/or of fertilizer ingredients is being dosed, this may be dosed by any suitable means, e.g. by metering or proportionating pump or by feeding the concentrate or emulsion to the throat of a venturi in the water feed line or into the circulating nutrient solution in the nutrient film system. Preferably, the concentrate is fed to the sump tank or nutrient recycle line of the nutrient film system.
The pathogenicide can be admixed with a solid fertilizer composition, e.g. be included in granules or tablets containing the fertilizer ingredients. Such mixtures are preferably dry, but may contain up to 15% by weight overall of water of crystallisation and/or hydration. However, with some combinations of fertilizer salts and pathogenicides, it may be desired to isolate the salts from the pathogenicide. This may be achieved by providing the pathogenicide and/or the fertilizer salts with a coating, e.g.
of a dust, oil, wax and/or polymer. This may have the incidental effect of delaying or sustaining the release of the pathogenicide or the fertilizer into the water.
Alternatively, the fertilizer and pathogenicide can be put up in a multicompartment container having a partition separating the pathogenicide from the fertilizer ingredients. For example, the container takes the form of a cartridge to be inserted into a dispensing device, the cartridge having a transverse partition wall to separate the ingredients. which may be in tablet or granular form. The partition wall may be water soluble so as to permit intermingling of the water with all the contents of the cartridge to give a single outflow of nutrient solution containing pathogenicide. Alternatively, the partition may be water insoluble. In this case water will have to flow separately through each compartment of the cartridge. It may be possible to adjust the flow through each compartment separately and independently to achieve the desired dosage of pathogenicide and fertilizer nutrient into the water. It will be appreciated that the cartridge with a solid wall may be formed as two separate cartridges, one containing pathogenicide and the other containing fertilizer salts.
The term cartridge has been used herein to denote a container adapted to be mounted in a dispensing device and to release its contents to a stream of water flowing through or over the container. Thus, the cartridge may take the form of a metal or plastics mesh walled container to be immersed in a tank of water: a tubular member with water inlets and outlets: or other forms. The term cartridge is to be construed in the above description in this general sense. A typical cartridge and its use is illustrated in the accompanying drawings which are diagrammatic cross-sections through cartridges containing halogen donor and fertilizer ingredients.
The cartridge comprises a tubular metal or plastics body I as shown in Figure 1. The ends are closed with end caps 2. The tube or end caps are provided with apertures (temporarily sealed with tear off seals or by shrink wrapping the cartridge, to prevent escape of the contents). The cartridge is mounted in a suitable dispensing system for use. For example the cartridge may be suspended in a tank. e.g. in the sump tank or in a concentrate reservoir, where the apertures in the tube and end walls are sufficiently fine (e.g. less than 1 mm) for the rate of dissolution of the contents to be sustained over a period of time.
Alternatively, the cartridge may be mounted in a through-flow chamber as shown in Figure 2. Water flows through the cartridge either transversely or longitudinally (as shown) to dissolve the contents. The rate of flow of water may be adjusted by suitable valve or proportioning means to give a predetermined rate of release of solution. Alternatively, the rate of flow of water through the cartridge is related to the rate of flow of nutrient solution in the nutrient film system to which
the contents of the cartridge are to be added. For example the outlet of the chamber 3 is connected to a verturi section 4 in the recycle line of the nutrient film system. Make up water is drawn from the reservoir 5 via cartridge 1 into the verturi 4.
A typical mixture of plant nutrients and chlorine donor for use in the cartridge described above contains the following materials: potassium nitrate, calcium nitrate, potassium phosphate, magnesium nitrate, iron/ethylenediaminetetra-acetic acid complex, manganese sulphate, boric acid, copper sulphate and ammonium molybdate to provide 200 parts of nitrogen, 300 parts potassium, 60 parts phosphorus, 250 parts calcium, 50 parts magnesium, 12 parts of iron, 2 parts of manganese, 0.3 parts of boron, 0.1 parts of copper and 0.2 parts molybdenum: and 4 parts of the dihydrate of monosodium dichloroisocyanurate.
Preferably this latter is used in the form of a tablet or as granules.
Where it is necessary to separate the chlorine donor from the fertilizer salts (notably where ammonium salts are present in the fertilizer salts) cartridge 1 may have a transverse wall 6 as shown dotted. This wall may be water soluble or readily disintegrated when wet (e.g. made from paper) or may be water resistant (e.g. made from metal or plastics).
Whilst the invention has been described above in terms of the use of a single pathogenicide. it is within the scope of the present invention to use mixtures of pathogenicides. Thus a halogen donor can be used to sanitize the water in combination with a fungicide, e.g. that sold under the
Trade Mark Benlate.
The invention will now be illustrated by the following Examples in which all parts and percentages are given by weight unless stated otherwise.
Example 1
An NFT system comprises nutrient solution being circulated through a trough from a header tank to a sump tank from whence it is pumped to the header tank. A nutrient solution and water are fed to the sump tank to make up the nutrients and water consumed by the plants growing in the trough. A perforated plastics tube is suspended in the sump tank so that solution flows through the perforations of the tube.
Within the tube is held a tablet containing trichloroisocyanic acid and available under the Registered Trade Mark of FITAB.
During the period of operation the available chlorine in the circulating nutrient solution varies between 5 ppm when a new tablet is put into the tube and less than 1 ppm when the tablet is largely consumed. In order to maintain the sanitising effect of the tablet, a new tablet is inserted into the tube when the available chlorine level falls below 1 ppm.
Example 2
The process of Example 1 is repeated except that the chlorine donor is sodium dichloroisocyanurate and this is dissolved in water to give a concentrate. This aqueous concentrate is drip fed to the sump tank at such a rate as is required to maintain from 1 to 3 ppm of available chlorine in the circulating nutrient solution.
WHAT WE CLAIM IS:
1. A process for treating water fed to or
circulating in a nutrient film system which
comprises incorporating a plant physiologically acceptable amount of a pathogenicide into the water.
2. A process as claimed in claim I wherein the pathogenicide is selected from halogens; halogen donors; permanganates; benzimidazoles and other fungicides.
3. A process as claimed in either of claims
1 or 2 wherein the pathogenicide is selected from those of the formula:
and hydrates thereof wherein X is halogen and each M is selected from halogen or an alkali-metal 4. A process as claimed in any one of claims I to 3 wherein the halogen donor is selected from trichloroisocyanuric acid.
monosodium dichlorp isocyanurate.
monopotassium dichloroisocyanurate and hydrates thereof.
5. A process as claimed in either of claims 1 or 2 wherein the pathogenicide is a chloramine.
6. A process as claimed in claim 5 wherein the chloramine is produced in situ by the reaction of chlorine or a chlorine donor with ammonia or an ammonium salt.
7. A process as claimed in claim 6 wherein the ammonium salt is used in an excess of from 2 to 500 molar percent over that theoretically required to convert the available chlorine into mono-chloramine.
8. A process as claimed in any one of the preceding claims wherein from 0.2 to 30 ppm of the active component of the pathogenicide are maintained in the water.
9. A process as claimed in any one of claims 1 to 7 wherein iron is also being incorporated into the water and the active component of the pathogenicide is incorporated at from 50 to 200% by weight of the iron expressed as Fe.
10. A process as claimed in any one of the preceding claims wherein the pathogenicide is fed to the water as a fluid concentrate.
11. A process as claimed in any one of claims 1 to 9 wherein the water is contacted with the pathogenicide in solid form.
12. A process as claimed in any one of the preceding claims wherein the pathogenicide is fed to the water in association with one or more fertilizer ingredients.
13. A process as claimed in any one of the preceding claims wherein the pathogenicide is incorporated into the nutrient solution circulating in the nutrient film system in the sump tank of the system or in the solution recycle line.
14. A process as claimed in claim I substantially as hereinbefore described.
15. A process as claimed in claim I substantially as hereinbefore described in any one of the Examples or as described with respect to the accompanying drawings.
**WARNING** end of DESC field may overlap start of CLMS **.
Claims (15)
1. A process for treating water fed to or
circulating in a nutrient film system which
comprises incorporating a plant physiologically acceptable amount of a pathogenicide into the water.
2. A process as claimed in claim I wherein the pathogenicide is selected from halogens; halogen donors; permanganates; benzimidazoles and other fungicides.
3. A process as claimed in either of claims
1 or 2 wherein the pathogenicide is selected from those of the formula:
and hydrates thereof wherein X is halogen and each M is selected from halogen or an alkali-metal
4. A process as claimed in any one of claims I to 3 wherein the halogen donor is selected from trichloroisocyanuric acid.
monosodium dichlorp isocyanurate.
monopotassium dichloroisocyanurate and hydrates thereof.
5. A process as claimed in either of claims 1 or 2 wherein the pathogenicide is a chloramine.
6. A process as claimed in claim 5 wherein the chloramine is produced in situ by the reaction of chlorine or a chlorine donor with ammonia or an ammonium salt.
7. A process as claimed in claim 6 wherein the ammonium salt is used in an excess of from 2 to 500 molar percent over that theoretically required to convert the available chlorine into mono-chloramine.
8. A process as claimed in any one of the preceding claims wherein from 0.2 to 30 ppm of the active component of the pathogenicide are maintained in the water.
9. A process as claimed in any one of claims 1 to 7 wherein iron is also being incorporated into the water and the active component of the pathogenicide is incorporated at from 50 to 200% by weight of the iron expressed as Fe.
10. A process as claimed in any one of the preceding claims wherein the pathogenicide is fed to the water as a fluid concentrate.
11. A process as claimed in any one of claims 1 to 9 wherein the water is contacted with the pathogenicide in solid form.
12. A process as claimed in any one of the preceding claims wherein the pathogenicide is fed to the water in association with one or more fertilizer ingredients.
13. A process as claimed in any one of the preceding claims wherein the pathogenicide is incorporated into the nutrient solution circulating in the nutrient film system in the sump tank of the system or in the solution recycle line.
14. A process as claimed in claim I substantially as hereinbefore described.
15. A process as claimed in claim I substantially as hereinbefore described in any one of the Examples or as described with respect to the accompanying drawings.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
GB35973/77A GB1600289A (en) | 1978-05-31 | 1978-05-31 | Sterilisation of water for nutrient film systems |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
GB35973/77A GB1600289A (en) | 1978-05-31 | 1978-05-31 | Sterilisation of water for nutrient film systems |
Publications (1)
Publication Number | Publication Date |
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GB1600289A true GB1600289A (en) | 1981-10-14 |
Family
ID=10383551
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
GB35973/77A Expired GB1600289A (en) | 1978-05-31 | 1978-05-31 | Sterilisation of water for nutrient film systems |
Country Status (1)
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GB (1) | GB1600289A (en) |
Cited By (25)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
EP0293400A1 (en) * | 1986-10-31 | 1988-12-07 | Great Lakes Chemical Corporation | Method for controlling plant diseases and microorganisms in the presence of plants |
FR2618137A1 (en) * | 1987-07-17 | 1989-01-20 | Elf Aquitaine | CHLORINATION SYSTEM FOR WATER TREATING |
EP0361955A2 (en) * | 1988-09-29 | 1990-04-04 | Albright & Wilson Limited | Hydroponic crop production |
FR2649090A1 (en) * | 1989-06-30 | 1991-01-04 | Barvil Sarl | Cartridge for disinfecting water, especially in a swimming pool |
EP0517102A1 (en) * | 1991-06-03 | 1992-12-09 | Bromine Compounds Ltd. | Process and compositions for the disinfection of waters |
US5976386A (en) * | 1994-10-03 | 1999-11-02 | A.Y. Laboratories Ltd. | Method and apparatus for treating liquids to inhibit growth of living organisms |
WO2001053209A2 (en) * | 2000-01-18 | 2001-07-26 | Albemarle Corporation | Methods for microbiological control in aqueous systems |
US6448410B1 (en) | 2000-01-18 | 2002-09-10 | Albemarle Corporation | Production of compacted biocidal agent from particulate biocidal agent without using a binder |
US6495698B1 (en) | 2000-01-18 | 2002-12-17 | Albemarle Corporation | Binder-free compacted forms of 1,3-dihalo-5,5-dimethylhydantoins |
US6508954B1 (en) | 2000-01-18 | 2003-01-21 | Albemarle Corporation | 1,3-dibromo-5,5-dimethylhydantoin of enhanced properties |
US6680070B1 (en) | 2000-01-18 | 2004-01-20 | Albemarle Corporation | Particulate blends and compacted products formed therefrom, and the preparation thereof |
US6809205B1 (en) | 2000-01-18 | 2004-10-26 | Albemarle Corporation | Process for producing N-halogenated organic compounds |
US6965035B1 (en) | 2002-07-25 | 2005-11-15 | Albemarle Corp | Compacted forms of halogenated hydantoins |
US7008545B2 (en) | 2002-08-22 | 2006-03-07 | Hercules Incorporated | Synergistic biocidal mixtures |
WO2007134388A1 (en) | 2006-05-18 | 2007-11-29 | Wobelea Pty. Limited | Treatment of edible crops |
WO2008083896A1 (en) * | 2007-01-12 | 2008-07-17 | Unilever N.V. | Gravity-fed water purification apparatus with venturi dosing device |
US7579018B2 (en) | 2000-01-18 | 2009-08-25 | Albemarle Corporation | Microbiological control in aqueous systems |
US7767240B2 (en) | 2001-06-28 | 2010-08-03 | Albemarle Corporation | Microbiological control in poultry processing |
US7837883B2 (en) | 2004-01-14 | 2010-11-23 | A. Y Laboratories Ltd. | Biocides and apparatus |
US7901276B2 (en) | 2003-06-24 | 2011-03-08 | Albemarle Corporation | Microbiocidal control in the processing of meat-producing four-legged animals |
US7914365B2 (en) | 2005-12-01 | 2011-03-29 | Albemarle Corporation | Microbiocidal control in the processing of meat-producing four-legged animals |
US7999118B2 (en) | 2000-01-18 | 2011-08-16 | Albemarle Corporation | Process for producing N-halogenated hydantoins |
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-
1978
- 1978-05-31 GB GB35973/77A patent/GB1600289A/en not_active Expired
Cited By (53)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
EP0293400A1 (en) * | 1986-10-31 | 1988-12-07 | Great Lakes Chemical Corporation | Method for controlling plant diseases and microorganisms in the presence of plants |
EP0293400A4 (en) * | 1986-10-31 | 1991-09-11 | Great Lakes Chemical Corporation | Method for controlling plant diseases and microorganisms in the presence of plants |
FR2618137A1 (en) * | 1987-07-17 | 1989-01-20 | Elf Aquitaine | CHLORINATION SYSTEM FOR WATER TREATING |
WO1989000546A1 (en) * | 1987-07-17 | 1989-01-26 | Societe Nationale Elf Aquitaine (Production) | System for treating water by chlorination |
US4986902A (en) * | 1987-07-17 | 1991-01-22 | Societe Nationale Elf Aquitaine (Production) | Chlorination system for a water to be treated |
EP0361955A2 (en) * | 1988-09-29 | 1990-04-04 | Albright & Wilson Limited | Hydroponic crop production |
EP0361955A3 (en) * | 1988-09-29 | 1991-10-09 | Albright & Wilson Limited | Hydroponic crop production |
FR2649090A1 (en) * | 1989-06-30 | 1991-01-04 | Barvil Sarl | Cartridge for disinfecting water, especially in a swimming pool |
EP0517102A1 (en) * | 1991-06-03 | 1992-12-09 | Bromine Compounds Ltd. | Process and compositions for the disinfection of waters |
US7651622B2 (en) | 1991-06-03 | 2010-01-26 | Bromine Compounds Limited | Process and compositions for the disinfection of waters |
US7449120B2 (en) | 1991-06-03 | 2008-11-11 | Bromine Compounds Limited | Process and compositions for the disinfection of waters |
US7067063B2 (en) | 1991-06-03 | 2006-06-27 | Bromine Compounds Limited | Process and compositions for the disinfection of waters |
EP1734008A3 (en) * | 1991-06-03 | 2008-04-09 | Bromine Compounds Ltd. | Process for the disinfection of waters |
US7285224B2 (en) | 1991-06-03 | 2007-10-23 | Bromine Compounds Limited | Process and compositions for the disinfection of waters |
EP1293482A1 (en) * | 1991-06-03 | 2003-03-19 | Bromine Compounds Ltd. | Process for the disinfection of waters |
EP1734008A2 (en) * | 1991-06-03 | 2006-12-20 | Bromine Compounds Ltd. | Process for the disinfection of waters |
US6132628A (en) * | 1994-10-02 | 2000-10-17 | A.Y. Laboratories Ltd. | Method of treating liquids to inhibit growth of living organisms |
US5976386A (en) * | 1994-10-03 | 1999-11-02 | A.Y. Laboratories Ltd. | Method and apparatus for treating liquids to inhibit growth of living organisms |
US6448410B1 (en) | 2000-01-18 | 2002-09-10 | Albemarle Corporation | Production of compacted biocidal agent from particulate biocidal agent without using a binder |
US8586763B2 (en) | 2000-01-18 | 2013-11-19 | Albemarle Corporation | Process for producing N-halogenated hydantoins |
US6809205B1 (en) | 2000-01-18 | 2004-10-26 | Albemarle Corporation | Process for producing N-halogenated organic compounds |
US9029562B2 (en) | 2000-01-18 | 2015-05-12 | Albemarle Corporation | Process for producing N-halogenated hydantoins |
US6680070B1 (en) | 2000-01-18 | 2004-01-20 | Albemarle Corporation | Particulate blends and compacted products formed therefrom, and the preparation thereof |
US6641828B1 (en) | 2000-01-18 | 2003-11-04 | Albemarle Corporation | Methods for microbiological control in aqueous systems |
US6565868B1 (en) | 2000-01-18 | 2003-05-20 | Albemarle Corporation | Methods for microbiological control in aqueous systems |
US6508954B1 (en) | 2000-01-18 | 2003-01-21 | Albemarle Corporation | 1,3-dibromo-5,5-dimethylhydantoin of enhanced properties |
US7999118B2 (en) | 2000-01-18 | 2011-08-16 | Albemarle Corporation | Process for producing N-halogenated hydantoins |
US6495698B1 (en) | 2000-01-18 | 2002-12-17 | Albemarle Corporation | Binder-free compacted forms of 1,3-dihalo-5,5-dimethylhydantoins |
US7985413B2 (en) | 2000-01-18 | 2011-07-26 | Albemarle Corporation | Microbiological control in aqueous systems |
WO2001053209A3 (en) * | 2000-01-18 | 2002-03-28 | Albemarle Corp | Methods for microbiological control in aqueous systems |
WO2001053209A2 (en) * | 2000-01-18 | 2001-07-26 | Albemarle Corporation | Methods for microbiological control in aqueous systems |
US7579018B2 (en) | 2000-01-18 | 2009-08-25 | Albemarle Corporation | Microbiological control in aqueous systems |
US7767240B2 (en) | 2001-06-28 | 2010-08-03 | Albemarle Corporation | Microbiological control in poultry processing |
US6965035B1 (en) | 2002-07-25 | 2005-11-15 | Albemarle Corp | Compacted forms of halogenated hydantoins |
US7008545B2 (en) | 2002-08-22 | 2006-03-07 | Hercules Incorporated | Synergistic biocidal mixtures |
US7901276B2 (en) | 2003-06-24 | 2011-03-08 | Albemarle Corporation | Microbiocidal control in the processing of meat-producing four-legged animals |
US8632794B2 (en) | 2004-01-14 | 2014-01-21 | A.Y. Laboratories Ltd. | Biocides and apparatus |
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US8211318B2 (en) | 2004-01-14 | 2012-07-03 | A. Y. Laboratories Ltd | Biocides and apparatus |
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