1. Field of the Invention
The present invention relates to a system for additions of solid chemicals to liquid systems. More particularly, the present invention is directed to a method and apparatus to slug feed solid chemicals into a system.
2. Background of the Prior Art
Evaporative cooling equipment dissipates heat by evaporation of some of the recirculated cooling water. The water in the recirculated-loop is warm and open to the atmosphere. One issue with such systems is the tendency for biological growth to occur. This biological growth can impede heat transfer, aggravate corrosion, and may even harbor human pathogens. To control biological growth in cooling equipment, liquid biocides are often pumped into the recirculating loop.
Using liquid biocides increases the potential for environmental accidents. Spills and leaks can occur while handling and pumping the toxic biocides resulting in contamination of the environment. Solid biocides are preferred to liquids since the chance for a concentrated liquid spills is eliminated and handling of solids is usually easier than handling concentrated liquids. There are several ways in the prior art to use solid biocides with an automatic feed. The simplest consists of placing soluble tablets in a floating device with a mesh bottom and placing the float into a basin. U.S. Pat. Nos. 3,792,979 and 4,241,025 are two examples of this type of device. An alternative method is described in U.S. Pat. Nos. 4,858,449 and 5,928,608 where the tablets are placed in a canister and a spray is directed at the tablets to slowly dissolve the chemical. Yet another method is described in U.S. Pat. No. 6,739,351 where the chemical is placed in a holding vessel and a controlled flow of liquid is passed through the chemicals. All of these devices attempt to control the release of solid chemicals by controlling the kinetics of dissolution, i.e., the length of time that the water is flowing through the feeder and the water velocity. The release from this type of equipment will be variable unless the equipment is very carefully controlled. A modification of these devices is found in U.S. Pat. No. 6,418,958 where the spray containing the dissolved liquid is collected in a tank. The spray is recirculated until the liquid reaches a pre-set conductivity limit. The concentrated liquid is then pumped into the system like any other concentrated liquid chemical.
When feeding a solid chemical using the prior art, the dissolution of the solid chemical relies on the kinetics of the dissolution process. Thus, if the feed is controlled by an erosion process, in which the rate at which chemical is released is based on the flow rate and the diminishing surface area of the chemical block, the flow rate and surface area of the chemical will determine how fast the chemical is released. Other devices use different techniques, such as conductivity controllers, to attempt to control this variable release but the equipment is complex and prone to breakdown. The chemical itself can clump and bridge which also affects the dissolution rate of the chemical.
In general, these prior-art systems are suited for a continuous or semi-continuous release of chemical in which the chemical is released over an extended period of time. However, many biocides are most effective when a high dose is slug-fed for a short period of time. To administer such biocides under current (prior art) systems, blowdown of the system is stopped and a high quantity of biocide is fed to the system. The blowdown is kept off for a short period of time allowing the biocide to work. After the biocide is allowed to work, blowdown is resumed, and the biocide will slowly bleed from the system. Besides the biocides being more effective in a high dose for a short period of time, overall less biocide is used under such a slug-feed program than with a continuous-release program. Thus using a slug-feed program will result in less biocide being used and eventually being released into the environment. Because of the slow release rate of the prior art techniques, solid biocides cannot easily be used for automatic slug feeding.
The present invention relates to a saturation limited feed system for automated or semi-automated additions of solid chemicals to liquid systems. More particularly, the present invention is directed to a method and apparatus to slug-feed solid chemicals into a circulating liquid system. The method and apparatus can be used to add any suitable chemical to any suitable system, but the invention is described specifically for the addition of a biocide to the recirculating water of a cooling system.
The present invention does not use kinetics to control the dissolution of the solid chemical; instead the invention relies on the solubility of the solid chemical in the liquid. The solubility limit of a chemical in a solution is defined as the maximum amount of chemical that can be dissolved in that solution at a specific temperature. The solubility limit is usually given as a percentage (e.g., 1%) or as grams of chemicals that can be dissolved in a liter of solution (e.g., 1%=10 g/liter). Once a solution is at its solubility limit, additional solid chemicals added to the solution will not dissolve. In accordance with a preferred arrangement of the invention, a basket constructed from a plastic mesh is located inside a water impermeable container. For simplicity the water impermeable container will be referred to herein alternatively as slug pipe, a holding tube, or as PVC pipe, though any water impermeable container made from an appropriate plastic, metal, fiberglass, or other material will be suitable. Nor does the container need to be in the shape of a pipe or tube as any shape container will also be suitable. Likewise the basket mesh will be referred to as a basket fabricated from some suitable plastic such as polypropylene; however, any appropriate material can be used for the basket.
The invention functions by loading an excess of chemical into the mesh basket and placing the mesh basket into the PVC pipe. The PVC pipe is filled with a specific volume of water and the chemical and water are allowed to stay in contact for a period of time. During this time, the chemical dissolves until it approaches its solubility limit. At this point, no additional chemical will dissolve into the water. When there is a need for a slug of chemical, a valve or series of valves is opened and water flows through the slug pipe displacing the chemical-saturated water with unsaturated water. The flush typical lasts for only a few minutes; little additional chemical is dissolved by the small amount of excess flush water. The dosage of the chemical is accordingly determined by the volume of the water in the slug pipe times the solubility of the chemical. With this invention, the dosage of the solid chemical is controlled by the chemical's solubility equilibrium rather than the kinetics of dissolution as used in the prior art. The control mechanism for opening the valve for biocide addition to a cooling tower is preferably a timer-controlled valve; however, other methods to control the chemical release are known, and are also considered part of the invention. Some of these alternative-means to activate the flush are:
Another advantage of the present invention is its ease of scale-up from adding a small amount of chemicals to adding a very large amount of chemicals. The quantity of chemicals contained in a flush is simply the solubility of the chemical times the volume of the slug pipe. If a small amount of chemical is needed, the invention can be configured to place only a small volume of water in contact with the chemical. If a larger quantity of chemical per dose is needed then the only required change is that a larger volume of water is maintained in contact with the chemical, i.e., a larger slug pipe is used. Besides varying the size of the container, the varying quantity of chemical dosing can be achieved by configuring the system with a large volume slug pipe, and using inert objects to displace water in the container, using various liquid heights in a container by varying the height of the output connection, or by other methods and systems known to persons having ordinary skill in the art.
Referring to
As the invention relies on the solubility limit of the chemical, and the addition of different amounts of chemical to the circulating system 2 may be desired under different various conditions, and different chemicals have different solubility limits, the invention provides a simple method for adjusting the amount of chemical added in a single slug feed. As shown in
DBNPA is a non-oxidizing biocide that is commonly used to control microbiological activity in cooling towers. DBNPA has a solubility limit in room-temperature water of about 1.0%. DBNPA is preferably slug-fed at a dosage of about 10 ppm based on the water volume of the system. A typical treatment program consists of dosing DBNPA 3 times per week (13 times per month). On a monthly basis the chemical feed system is inspected and the chemicals in the feeder are recharged. A water system having a volume of 1000 gallons requires a dose of 37.8 grams of DBNPA to be treated at the 10 ppm level. This treatment is accomplished by slug feeding 3.8 liters of water saturated (1.0%) with DBNPA. This dosage is administered as a slug feed over the course of a few minutes.
A 4″ diameter pipe holds approximately 200 ml of water per inch, thus a water-filled length of pipe that is about 19 inches long holds 3.8 liters. The actual device would be somewhat larger to include additional volume for holding at least 13×37.8=491 grams of DBNPA. A 2′/2″ diameter mesh pipe 13 inches in length holds over 1000 grams of DBNPA, sufficient for 13 slug feeds at 37.8 grams with 100% excess.
DBNPA has close to an ideal solubility for this invention. The chemical is soluble enough that a very large water volume and hence a large pipe is not required for a typical dose. Yet, at 1.0% solubility, it is not so soluble that the dissolving of the chemical with each dose would dramatically increase the volume of water and thus increase subsequent dosages. This allows a large number of doses to be done from a single charge. If the density of the DBNPA is equal to that of water, the variation in volume of saturated water with each dose over the period of a month will be less than 10% of nominal.
A more soluble chemical can also be used with this invention; however the number of doses will be limited. Likewise a less soluble chemical could be used but the water volume of the feeder would need to be increased to get a similar dose.
Table 1 illustrates the consistency of results that was obtained from testing with a small scale device. The device consisted of a 3.0 liter plastic container surrounding a tube fabricated from 400-mesh polypropylene. 600 grams of DBNPA powder were added to the mesh-tube. After various soak times, 1 gpm of water was flushed through the feeder for 2 minutes. The total amount of DBNPA was then measured.
The average quantity of chemicals released was 34.6 grams with a standard deviation of 3.1 grams. Depending on the arrangement of a specific feeder and density of the dissolved chemical, the feeder may perform more consistently with the basket elevated and containing a mesh bottom and/or with the sides of the basket masked to allow a more consistent water/chemical interface regardless of the quantity of chemical in the feeder.
The invention as shown and described with respect to
The invention also does not require an internal basket as the chemical can simply sit in the slug pipe so long as the configuration of the slug-pipe and flow of the saturated liquid inhibits solid chemicals from leaving the container. Having a mesh basket allows equilibrium to be reached faster and limits the amount of solid chemical carryout when flushing over a large range of flushing velocities.
This invention can be combined with a kinetic feeding step to provide additional dosing, if necessary. This part of the treatment will have the same issues as prior art devices, particularly the control of release rate. However, much of the required dose will be accurately provided by the saturation dosing therefore the impact of the variability of the kinetic dosing will be less. Making the device into a combination saturation and kinetic feeder could simply be done by allowing the purge water to flow for a controlled length of time at a specific flow rate for more than required to purge the system of saturated chemicals. The amount of the additional kinetic-dose can be controlled by adjusting either the flow rate, the length of time of the kinetic-feed flow, or both. In addition, since much of the dose is provided with the first flush, the time required to supply the full dosage is short enough to allow slug feeding of the chemical.
By adding this kinetic step, a single feeder size could treat a broad range of systems. A specific feeder will have a specific volume of water and thus release a specific amount of chemical when the water becomes saturated. That amount of chemical will be appropriate for a specific size of cooling system. For smaller systems, inert material can be added to the feeder. This inert material will reduce the volume of water in the feeder and hence the amount of chemical released. For larger systems, a kinetic release step can be added. By controlling the length of time and the water velocity for this step, larger systems can be adequately treated. Thus a broad range of chemical dosing can be done from a single feeder.
As an example, tests were run using a 6″ diameter feeder containing 20 liters of water and the release rate, without any soak time, was measured. Operating for 30 minutes at a 4-gpm rate through the feeder (displacing 23 times the water volume of the feeder) 130 grams of chemical were released. This kinetically-controlled release is in addition to the chemical that would be released had the feeder been allowed to soak. A purely saturation-based release would result in the dissolution of 10 grams per liter of DBNPA or a 200 gram dosage. The kinetic addition step thus increases the dose of chemical for a single release to 330 grams. A 200 gram dose of DBNPA will treat 5,280 gallons at a 10 ppm level; a 330 gram dose will treat 8,700 gallons. Using the rule of thumb that the water volume of an evaporative cooling system is equal to 10× the tonnage, a purely saturation limited feeder with a 20 liter volume can treat up to a 500-ton system. The addition of the kinetic release step above increases the size of the system that can be treated with a single feeder from 500 tons to over 800 tons.
This invention could, in addition, be used for a monthly single-shot dose of a different, compatible, and highly-soluble chemical. For example, by adding a quantity of a compatible, highly-soluble biocide or biodispersant to the invention when it is being refilled with a biocide, the first release will contain both the multiple-slug-fed biocide and the highly-soluble biocide or biodispersant. Such dosing can be effective at preventing bacteria resistant to the primary biocide from becoming established or aiding in the removal of biofilm. As an example, if the multiple-slug-fed chemical is DBNPA the highly-soluble chemical could be isothiazoline. Isothiazoline is available as a solid, is highly soluble, and is compatible with DBNPA. The exact amount of isothiazoline required for a single dose could be added to the feeder once per month when the feeder is being refilled. The isothiazoline would completely dissolve during the first holding period and that dose would be released along with the DBNPA the first time that the system is slug-fed.
This application claims the priority benefit under 35 U.S.C. §119(e) of U.S. Provisional Application Ser. No. 61/723,926, entitled “SATURATION LIMITED FEEDER FOR CHEMICAL ADDITIONS,” filed Nov. 8, 2012, and U.S. Provisional Application Ser. No. 61/828,824, entitled “SATURATION LIMITED FEEDER FOR CHEMICAL ADDITIONS,” filed May 30, 2013, both of which are incorporated herein by reference in their entirety.
Number | Date | Country | |
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61723926 | Nov 2012 | US | |
61828824 | May 2013 | US |