Method and composition for cleaning and maintaining water delivery systems

Abstract

A sodium chlorite solution is admixed with a second solution containing an acid to make a reacted mixture. The reacted mixture is introduced into a water system, viz. a conduit in which water flows or a tank containing water. The reacted mixture is added to the water system to inhibit and/or eliminate bacterial fouling in the system, and/or inhibiting and/or removing mineral deposits from the system, and/or for reducing or eliminating microorganisms from the system. The second component is acidic enough to convert the sodium chlorite into chlorine dioxide while remaining unaffected in the reacted mixture and at the same time being a mineral antiscalant. Optimum conversion of the sodium chlorite component into active chlorine dioxide requires at least several minutes reaction time and, preferably, the use of a suitable catalyst, such as sodium molybdate.

Description

TECHNICAL FIELD

[0002] This invention relates to a method and composition for cleaning and maintaining water storage and/or distribution systems. More particularly, it relates to the use of a reacted mixture of a sodium chlorite solution and a second solution containing an acid for inhibiting and/or removing bacterial fouling an/or inhibiting and/or removing mineral deposits, and/or eliminating microorganisms from water storage and/or distribution systems.

BACKGROUND OF THE INVENTION

[0003] Water is stored in reservoirs and tanks and is delivered by conduits to places where the water is used. Water storage and delivery systems often become fouled and/or obstructed by mineral scale deposits and/or biological growths and/or bio-films. Irrigation systems used in the agricultural industry can experience fouling that is so severe that water flow is reduced to a level where valuable crops receive insufficient watering and perish from dehydration.

[0004] There is a need for compounds that can be added to water storage and delivery systems for eliminating the mineral and biological substances that cause the obstructions and comprise the systems. A principal object of this invention is to provide such a composition and a method of its use for cleaning and maintaining water delivery systems, including tanks, reservoirs and conduits.

[0005] There is also a need for an easily achieved on-site metering and mixing of the components of the composition and an easily achieved introduction of the composition into the water delivery system. Another object of the present invention is to fulfill this need.

BRIEF SUMMARY OF THE INVENTION

[0006] A basic aspect of the present invention is to admix a sodium chlorite solution with a second solution containing an acid to make a reacted mixture. A predetermined amount of this reacted mixture is then introduced into water in a water distribution system.

[0007] According to an aspect of the invention, the reacted mixture is introduced into a water system to inhibit and/or eliminate bacterial fouling in the system. Another aspect of the invention is to introduce the activated mixture into to the water for inhibiting and/or removing mineral deposits from the system. Yet another aspect of the invention is to introduce the activated mixture into the water for eliminating microorganisms from the system.

[0008] According to yet another aspect of the invention, the second component is acid enough to convert the sodium chlorite into chlorine dioxide while remaining unaffected in the reacted mixture and at the same time being a mineral antiscalant. The second solution may be formed by adding PBTC and sodium molybdate di-hydrate and water. The second compound may be a mixture of mineral acids and an antiscalant polymer. The antiscalant polymer may be polyacrylic acid or a polymeric compound.

[0009] According to an aspect of the invention, a catalyst is used to enhance conversion of the sodium chlorite into an active biocide, chlorine dioxide. By way of typical and therefore non limitive example, the catalyst may be sodium molybdate.

[0010] Other objects, advantages and features of the invention will become apparent from the description of the best mode set forth below, from the drawing, from the claims and from the principles that are embodied in the specific structures, compositions and method steps that have been illustrated and described.

BRIEF DESCRIPTION OF THE SEVERAL VIEWS OF THE DRAWING

[0011] The drawing is a flow diagram of a water distribution system and equipment for preparing the composition of the invention and introducing it into the water system.

DETAILED DESCRIPTION OF THE INVENTION

[0012] The drawing shows, by way of example, a portion of an irrigation system that includes a flow meter 10 in a conduit 12, e.g. an irrigation pipe. The flow meter 10 measures the flow in the conduit 12 and generates an electrical control signal that is proportional to the flow. The electrical signal may be electrical pulses that are sent to a pulse divider 14 which generates electrical control signals that are sent to controllers for two chemical feed pumps 16, 18. The electrical signals from pulse divider 14 may be electrical pulses which control the pumps 16, 18 for proportionally pumping the two components that are mixed. Preferably, the pumps 16, 18 are positive displacement pumps that include pistons. The control signals control the movement of the pistons. Each pumping stroke sends a predetermined volume of chemical into a conduit 20, 22 leading from a pump 16, 18 to a reaction chamber 24. Pump 16 pumps a first solution or component from its storage tank 26 to the reaction chamber 24. Pump 18 pumps a second solution or component from its storage tank 28 to the reaction chamber 24. The two solutions are precursor chemicals that are allowed to intermingle or react for the period of time, e.g. ten or more minutes, in the reaction chamber 24. The reacted mixture is removed through the top of the reaction chamber 24 and is delivered by a conduit 30 into the water conduit 12, into admixture with water that is flowing through the conduit 12. The admixture of the reacted solution in the water substantially instantly dilutes the reacted mixture to a desired working concentration for distribution by conduit 12 throughout the water system.

[0013] By way of example, the flow sensor may be a Module IP115 hot-tap insertion flow sensor, manufactured by Sea Metrics, Inc., having a business address of 20419 80th Ave.S., Kent, 98032. The pulse divider may be a model PD10 pulse divider, also manufactured by Sea Metrics, Inc. The pumps may be model B711-392SI pumps manufactured by LMI Milton Roy, having a business address of 8 Post Office Square, Acton Mass. 01720. The reaction chamber 24 may be an off the shelf item. It may be what is known as a reaction column that is made from schedule 80PVC pipe, measuring two inches in diameter, and twelve inches long, with end caps and tubing fittings.

[0014] The pumps 16, 18 force the reactants into the bottom of the reaction chamber or column. The pressure of the pumps 16, 18 forces the reacted mixture up out of the top of the reaction chamber 24, following between ten to twenty minutes admixing time of the reactants in the reaction chamber 24. The pumps 16, 18 are 1.6 gallon per hour capacity pumps.

[0015] The following are some examples that are submitted for the purpose of making it easier to understand the invention.

EXAMPLE 1

[0016] A solution containing 17.5% wt/wt of PBTC, 0.1% wt/wt sodium molybdate di-hydrate (Na2MoO4:2H2O) in water was added to an equal volume of 7.5% wt/wt sodium chlorite (NaCIO2) in water. After allowing the mixture to react for ten minutes, small aliquots were added to a liter of stirred irrigation water from a berry farm until the chlorine dioxide level reached 0.5 parts per million. After fifteen minutes, samples were taken for enumeration of bacteria on aerobic plate count agar. Approximately a 10,000 fold reduction in bacteria was achieved based on the initial bacterial content of the untreated irrigation water. Water samples treated with only the PBTC solution showed no decrease in bacterial counts.

EXAMPLE 2

[0017] An irrigation system at a California vineyard carrying 1500 gallons per minute of water was treated with the chemical composition in Example 1 resulting in a final concentration of 0.2 ppm chlorine dioxide and 0.8 ppm PBTC. After several days, the bacterial counts increased due to dispersion and dislodging of established biofilms in the system. However, within a week of continuous treatment, the bacterial counts decreased 100 fold from the initial level of approximately 1000 organisms per ml to less than 10.

EXAMPLE 3

[0018] A sample of irrigation water heavily contaminated with iron related bacteria (IRB), a major source of bio-fouling was treated with the solution of Example 1 to achieve a chlorine dioxide residual of 0.25 ppm. After a fifteen minute contact time, the treated water was analyzed for IRB using the BART (Biological Activity Reaction Test) test kit sold by Droycon Bioconcepts, Inc., Regina, Saskatchewan, Canada. All traces of IRB were eliminated vs. the control untreated water, which contained an estimated IRB level of 1,000 per ml.

[0019] One component of the reacted mixture may be sodium chlorite. Under acidic conditions this compound spontaneously forms chlorine dioxide, a powerful antimicrobial. Salts of hypochlorite or chlorine gas may be used in place of the sodium chlorite. This compound may be used to prepare hypochlorous acid in the reaction chamber 24. This reacted mixture is also a powerful antimicrobial. The second component may be an organophosphorate compound such as 2-phosphonobutane-1,2,4-tricaboxylic acid (PBTC), CAS Registry No. 37971-36-1. Alternatively, the second component may be a mixture of mineral acids and antiscalant polymers such as polyacrylic acid or other polymeric compounds. The second component has the attributes of being acidic enough to convert sodium chlorite into chlorine dioxide while remaining unaffected in the reaction mixture. At the same time it is an excellent mineral antiscalant.

[0020] Very few chelants and/or antiscaling compounds remain unaffected in the presence of even dilute amounts of oxidizing compounds. PBTC is one of the very few chelants that demonstrates acceptable stability in the presence of strong oxidizers. Furthermore, the reaction of PBTC with sodium chlorite might be greatly accelerated and reaction time greatly reduced, by the inclusion of small amounts of a catalyst such as, but not limited to, sodium molybdate in the PBTC component prior to admixing it with the sodium chlorite component.

[0021] According to an aspect of the invention, the generation and delivery of antiscalant, antimicrobial mixture is easily achieved on-site by metering the individual component solutions into the reaction vessel 24, either by positive pumping or by vacuum eduction, and introducing the resultant reaction mixture into the water stream or volume. In some installations, the reaction mixture may be introduced into a body of water in a tank as opposed to flowing water in a conduit.

[0022] The process of generating and delivering the reaction mixture may be conducted intermittently by use of timer controlled chemical feed pumps, or can be conducted continuously, by flow controlled pumping or eduction. Optimum conversion of the sodium chlorite compound into active chlorine dioxide requires at least several minutes of reaction time and, preferably, the use of a suitable catalyst, such as sodium molybdate. Accordingly, the reaction or mixing chamber 24 should be of a suitable volume to allow the two solutions or components to co-mingle and react for the desired length of time before exiting the reaction chamber 24, into the conduit 12 or a water tank.

[0023] The illustrated embodiment is only a single example of the present invention and, therefore, is non-limitive. It is to be understood that many changes in the particular structure, materials and features of the invention may be made without departing from the spirit and scope of the invention. Therefore, it is our intention that our patent rights not be limited by the particular embodiment that is illustrated and described herein, but rather is to be determined by the following claims, interpreted according to accepted doctrines of claim interpretation, including use of the doctrine of equivalents.

Claims

1. A method of treating water in a water distribution system, comprising: admixing a sodium chlorite solution with a second solution containing an acid to make a reacted mixture; and introducing a predetermined amount of the reacted mixture into a water system.

2. The method of claim 1, comprising introducing the reacted mixture into the water to inhibit and/or eliminate bacterial fouling in the system.

3. The method of claim 1, comprising introducing the activated mixture into the water for inhibiting and/or removing mineral deposits from the system.

4. The method of claim 2, comprising introducing the activated mixture into the water for inhibiting and/or removing mineral deposits from the system.

5. The method of claim 1, comprising introducing the activated mixture into the water for reducing or eliminating microorganisms from the system.

6. The method of claim 2, comprising introducing the activated mixture into the water for reducing or eliminating microorganisms from the system.

7. The method of claim 3, comprising introducing the activated mixture into the water for reducing or eliminating microorganisms from the system.

8. The method of claim 4, comprising introducing the activated mixture for reducing or eliminating microorganisms from the system.

9. The method of claim 1, wherein the second component is acidic enough to convert the sodium chlorite into chlorine dioxide while remaining unaffected in the reacted mixture and at the same time being a mineral antiscalant.

10. The method of claim 1, wherein the second solution is formed by adding 2-phosphonobutane-1,2,4-tricarboxylic acid (PBTC) and sodium molybdate di-hydrate and water.

11. The method of claim 1, wherein the second compound contains PBTC.

12. The method of claim 1, wherein the second compound is a mixture of mineral acids and antiscalant polymers.

13. The method of claim 12, wherein the antiscalant polymer is polyacrylic acid.

14. The method of claim 12, wherein the anticscalant polymer is a polymeric compound.

15. The method of claim 1, wherein the second compound has the attributes of being acidic enough to convert sodium chlorite into chlorine dioxide while remaining unaffected in the reaction mixture.

16. The method of claim 1, further comprising using an antiscalant, dispersant compound, as an acid activator, to enhance the properties of the reacted mixture towards controlling mineral deposits in the water system.

17. The method of claim 16, further comprising using a catalyst to enhance conversion of the sodium chlorite into an active biocide, chlorine dioxide.

18. The method of claim 17, wherein the catalyst is sodium molybdate.

19. A reacted mixture resulting from admixing a sodium chlorite solution with a second solution containing an acid to make the reacted mixture.

20. The composition of claim 19, wherein the composition will inhibit and/or eliminate bacterial fouling introduced into a water system.

21. The composition of claim 19, wherein the composition will inhibit and/or remove mineral deposits from the water system.

22. The composition of claim 19, wherein the composition will inhibit and/or remove mineral deposits when introduced into a water system.

23. The composition of claim 19, wherein the composition will reduce and/or eliminate microorganisms from a water system when introduced into the water system.

24. The composition of claim 19, wherein the second component is acidic enough that it will convert the sodium chlorite into chlorine dioxide while remaining unaffected in the reacted mixture and at the same time will be a mineral antiscalant.