Patent Publication Number: US-10766797-B2

Title: Method and composition for use in the cyclic process for the efficient generation of chlorine dioxide in dilute solutions

Description:
BACKGROUND OF THE INVENTION 
     Field of Invention 
     This invention relates to a method for monitoring and controlling the relative concentration of activator used in the cyclic process for enhanced sanitation and oxidation of aqueous systems at aquatic facilities. 
     Background of the Technology 
     Aqueous systems that are exposed to various forms of oxidant demand as well as introduction of microbiological contamination must be effectively treated to control transfer of disease such as in the case of a swimming pool. 
     Chlorine dioxide has been proven very effective at inactivating microbiological organisms in such applications. However, generating chlorine dioxide can be hazardous due to the explosive nature of the gas as well as the potential for human exposure to toxic concentrations. Furthermore, chlorite anion concentrations must be held to a minimum in water that may be consumed due to toxicity concerns. The U.S. EPA has put a limit in drinking water at 1.0 ppm as chlorite anion. 
     Chlorine dioxide is typically produced in a chlorine dioxide generator where either acid or chlorine is combined with a chlorite donor to generate chlorine dioxide. In order to achieve efficient conversion of chlorite to chlorine dioxide, high concentrations are reacted thereby generating a high concentration of gas which is potentially dangerous. 
     Using these methods of chlorine dioxide generation also waste considerable amounts of reagents such as chlorite as well as elevate cost due to the inability to regenerate the chlorite ions that result from the reduction of the chlorine dioxide back to chlorite or the residual chlorite that was not activated during the initial formation of chlorine dioxide. 
     PRIOR ART 
     U.S. Pat. Nos. 7,922,933, 7,927,509, and 7,976,725 which are herein incorporated by reference, disclose a cyclic process for the in-situ generation of chlorine dioxide. The cyclic process utilizes bromide ions that are activated by an oxidant to produce free bromine. The free bromine oxidizes chlorite ions producing chlorine dioxide. Chlorine dioxide inactivates microbiological organisms (i.e.  Cryptosporidium ). During this process the free bromine and at least some portion of the chlorine dioxide are reduced back to bromide ions and chlorite ions respectively which are recycled back to free bromine and chlorine dioxide utilizing the cyclic process. 
     DISCUSSION OF PRIOR ART 
     The referenced patents demonstrate that free chlorine at near neutral pH does not convert chlorite ions into chlorine dioxide to an acceptable level to be useful in the cyclic process. More specifically, the pH range for aqueous systems at aquatic facilities based on Florida Department of Health guidelines is 7.2 to 7.8. Data from the referenced patents demonstrated that at pH 7.45 and 4.2 ppm free chlorine reported as Cl 2 , no detectable levels of chlorine dioxide was produced. However, when 5 ppm as bromide ions were added the chlorine dioxide was rapidly produced under the same conditions. 
     The data demonstrates how crucial the presence of bromide ions is to the successful implementation of the cyclic process and ultimately the microbiological efficacy of the treatment program. 
     Therefore, it is necessary to be able to determine the relative concentration of bromide ions in the aqueous system of an aquatic facility to ensure the cyclic process and subsequently the microbiological efficacy is achieved. 
     The measurement of bromide ion in the presence of other halide such as chloride is not an simple task. Ion Chromatography, titrimetric methods and ion selective probes can be used under certain test conditions. However, all of these methods are best suited for skilled laboratory technicians in a laboratory environment. 
     At aquatic facilities, it is common for maintenance workers or lifeguards to perform the water testing. 
     An easy to use method for determining the relative concentration of bromide ions is needed to ensure reliable and reproducible application of the cyclic process. 
     SUMMARY OF THE INVENTION 
     The disclosed invention comprises a method for determining and controlling the concentration of at least bromide ions in an aqueous system of an aquatic facility for the in-situ generation of chlorine dioxide using the cyclic process. 
     Disclosed is a method for determining the relative bromide ion concentration in an aqueous system of an aquatic facility using the cyclic process, the method comprising: a composition comprising a bromide donor and a tracer; the composition is applied to the aqueous system to sustain a bromide ion concentration ranging from 2 ppm to 5000 ppm; the tracer is monitored to determine the relative concentration of bromide ion, and the bromide ion concentration is sustained to ensure the cyclic process and subsequent microbiological efficacy is achieved. 
    
    
     
       BRIEF DESCRIPTION OF THE DRAWING 
         FIG. 1  illustrates the cyclic process where the bromide donor, bromide anion (Br−) and oxyhalogen surrogates (i.e. HOBr) of bromine are traced with an oxidizer inert tracer throughout the cyclic process. 
         FIG. 2  illustrates the stabilization of bromide ions and bromine&#39;s oxyhalogen surrogates (i.e. free bromine) by dialkylhydantoin in the presence of sunlight (UV). 
         FIG. 3  illustrates the improvement in chlorine dioxide generation when bromide ion is added to the aqueous system compared to free chlorine at near neutral pH. 
         FIG. 4  illustrates the microbiological efficacy of the cyclic process on inactivating  Cryptosporidium parvum  at two different chlorite concentrations using bromide ions activated by free chlorine at near neutral pH. The water chemistry and conditions applied in the test were consistent with water chemistry parameters used in aqueous systems at aquatic facilities. The data illustrates the microbiological efficacy of the cyclic process in achieving a 3-log and 4-log inactivation of  Cryptosporidium parvum.    
     
    
    
     DETAILED DESCRIPTION OF THE INVENTION 
     Various compositions and methods of the invention are described below. Although particular compositions and methods are exemplified herein, it is understood that any of a number of alternative compositions and methods are applicable and suitable for use in practicing the invention. 
     The practice of the present invention will employ, unless otherwise indicated, conventional techniques of water chemistry, which are known to those of skill in the art. Such techniques are explained fully in the literature. 
     Definitions: 
     As used herein, “molybdate donor” comprises a compound that when dissolved in water release molybdate having the general formula MoO 4   = . Non-limiting examples of molybdate donors include sodium molybdate, potassium molybdate, lithium molybdate and the like. 
     As used herein, the term “tracer” describes a chemical compound that is inert to the oxidizers used to treat the aqueous system of the aquatic facility and is combined with at least the bromide donor to form a composition. The composition can be in the form of a solid or liquid. The tracer can be detected and quantitatively measured. 
     As used herein, the term “oxidizing activator” is used with reference to an oxidizer selected from at least one of: free chlorine, peroxymonosulfate, alkali metal salts or ammonium salts of persulfates and electrolysis; wherein when the activating oxidizer is introduced to the aqueous system comprising bromide anions, the activating oxidizer reacts with bromide anion resulting in the formation of hypobromous acid. 
     As used herein, the term “free chlorine” is used with reference to a chlorine source that hydrolyses in the aqueous system to produce at least some portion of hypochlorous acid. 
     As used herein, the term “free bromine” is used with reference to the formation or presence of hypobromous acid and possibly some portion of hypobromite ions. 
     As used herein, the term “relative bromide ion concentration” is used with reference to the approximate concentration of bromide ion. The tracer is combined with the bromide donor at a known ratio. Since the tracer is not directly combined with the bromide ion and simply shadows the bromide ion, there is the potential for some variance between the actual concentration of bromide ion and measured tracer. For this reason, the measurement of tracer provides for the “relative bromide ion concentration”. 
     As used herein, the term “near neutral pH” is used with reference the pH of the aqueous system of between about 6.0 and 8.5. However, more preferred is a pH of about 6.8 to 8.0 where the ratio of hypobromous acid as compared to hypobromite ions is low, and the potential for formation of bromine gas is reduced. 
     As used herein, the term “inactivation” is used with reference to the ability to deactivate, kill, or destroy microbiological organisms. 
     As used herein, the term “microbiological organisms” is used with reference to all forms of microbiological life forms including: parasites, bacteria, viruses, algae, fungus, and organisms encased in biofilms. 
     As used herein, the term “free halogen donor” is used with reference to a halogen source which acts as an active oxidizer when dissolved in water. Chlorine based free halogen donors form at least one of Cl 2 , HOCl, and OCl −  (also referred to as free chlorine) when added to water, whereby the species formed is pH dependent. Bromine based free halogen donors form at least one of Br 2 , HOBr, and OBr −  (also referred to as free bromine), again the species being pH dependent. 
     As used herein, the term “peroxymonosulfate” encompasses the various species of the peracid chemistry and its various salts, whereby depending on the pH of the solution in which the peroxymonosulfate is added, the following species and combinations result: H 2 SO 5  (Caro&#39;s acid), HSO 5   − , SO 5   = . 
     As used herein, the term “aquatic facility” is used with reference to all structural components and equipment comprising an aqueous system used by humans for exercise, sports and/or recreation. Examples of aquatic facilities include but are not limited to: water parks, theme parks, swimming pools, spas, mammal habits at zoos, therapy pools, hot tubs and the like. 
     As used herein, the term “aqueous system” describes that portion of the aquatic facility comprising water (also referred to as the “aqueous solution”) used by visitors of the aquatic facility for recreation, sports and exercise. Non-limiting examples include: swimming, water rides, water sports, physical therapy and the like. 
     As used herein, the term “recreational water” is defined as the water contained in the swimming pool, hot tub, feature pool, water park etc. used by people visiting the aquatic facility. 
     As used herein, the term “cyclic process” relates to the recycling of substantially inert anions comprising bromide and chlorite into their oxyhalogen surrogates, exemplified by hypobromous acid and chlorine dioxide respectfully followed by reduction back to their respective anions, and where the process is repeated. 
     As used herein, the term “chlorite anion donor” is a compound that comprises an alkali metal salt comprising chlorite anions ClO 2   − , chlorine dioxide, or any convenient direct or indirect source of chlorite anions. For example, chlorine dioxide can indirectly produce chlorite due to reduction in an aqueous system. Sodium chlorite directly supplies chlorite anions. Regardless of whether the chlorite anion is provided by a direct or indirect chlorite anion donor, any chlorite anions in the aqueous system implementing the disclosed cyclic process of the invention will be regenerated to chlorine dioxide in the disclosed cyclic process. 
     As used herein, the term “chlorite anion” is comprises chlorite having the general formula ClO 2   − . 
     As used herein, the term “recycled” also “recycling” means at least some portion of the recovered bromide anions and chlorite anions are regenerated to their respective oxyhalogen compounds, followed by reduction back to their respective anions, and where the process is repeated. 
     As used herein, the term “ Cryptosporidium ” is used to represent any form of parasitic microbiological organism from the family of  cryptosporidium . An example of  Cryptosporidium  is  Cryptosporidium parvum  (often referred to as  C. parvum ). Other examples of  Cryptosporidium  include but are not limited to:  C. hominis, C. canis, C. felis, C. meleagridis , and  C. muris.    
     The disclosed invention comprises a method for determining and controlling the concentration of at least bromide ions in an aqueous system of an aquatic facility for the in-situ generation of chlorine dioxide using the cyclic process. 
     Disclosed is a method for determining the relative bromide ion concentration in an aqueous system of an aquatic facility using the cyclic process, the method comprising: a composition comprising a bromide donor and a tracer; the composition is applied to the aqueous system to sustain a bromide ion concentration ranging from 2 ppm to 5000 ppm; the tracer is monitored to determine the relative concentration of bromide ion, and the bromide ion concentration is sustained to ensure the cyclic process and subsequent microbiological efficacy is achieved. 
     The microbiological efficacy of the cyclic process is preferably measured by achieving a 3-log inactivation of  Cryptosporidium , more preferred achieving a 4-log inactivation of  Cryptosporidium.    
     The tracer should be inert to the oxidizers used to treat the aqueous system of the aquatic facility. Furthermore the tracer should be non-toxic and environmentally benign. Examples of suitable tracers include but are not limited to molybdate donor(s) and cyanurate(s). The preferred tracer is a molybdate donor. 
     Molybdate (i.e. sodium molybdate) is an oxoanion of molybdenium in its highest oxidation state of 6. This makes molybdate ideal for use in applications such as the cyclic process as it is stable from further oxidation and precipitation. 
     Molybdate is easily tested using colorimetric methods like those used at aquatic facilities. Companies such as PalinTest® and Hach® provide easy to use test kits for determining low level molybdate (i.e. 0.02 ppm) concentrations without interference from other metals at typical concentrations found in aquatic facilities. 
     Sodium molybdate (Na 2 MoO 4 ) is one non-limiting example of preferred molybdate donor suitable for use as a tracer. Other non-limiting examples include: lithium, potassium and ammonium molybdates to name a few. 
     The concentration of molybdate can range from 0.02-2 ppm reported as molybdate (MoO 4   2− ). The measured result of the test can also be reported as molybdenium (Mo) by multiplying the molybdate concentration by a factor of 0.6. For example, a molybdate concentration of 0.02 ppm (reported MoO 4   2− ) is equivalent to 0.012 ppm (reported as Mo). 
     Another non-limiting example of a suitable tracer comprises cyanurates exemplified by cyanuric acid, sodium cyanurate, potassium cyanurate and the like. 
     The tracer is combined with the bromide donor by mixing the tracer and bromide donor together at a known ratio to form a composition. The composition can be in the form of a solid or liquid. 
     The solid composition can be further formed into any number of non-limiting geometric shapes such as a tablet, pellet or puck. 
     The weight percent ratio of tracer to bromide donor can vary based on which tracer and donor are used. For example, sodium molybdate has a different formula weight than potassium molybdate and therefore to obtain the same molybdate concentration, more potassium molybdate is required in the composition to compensate for the higher formula weight. 
     The composition can further include other additives that can be monitored for their relative concentration by measuring the tracer. For example, dialkylhydantoins are effective UV stabilizers of free bromine. The UV stabilization of free bromine inhibits the formation to bromate when exposed to sunlight (UV). Non-limiting examples of suitable dialkylhydantoins include: 5,5-dimethylhydantoin and 5-ethyl-5-methylhydantoin. 
     The tracer concentration in the aqueous system ranges from 0.02 to 2.0 ppm reported as molybdate. Preferably the tracer concentration ranges from 0.05 to 1.0 ppm as molybdate, and most preferred from 0.10 to 0.80 ppm as molybdate. 
     The bromide ion concentration ranges from 2 to 5000 ppm as bromide. The preferred bromide concentration ranges from 2 to 500 ppm as bromide and the most preferred bromide concentration ranges from 5 to 100 ppm as bromide. 
     The composition comprising a molybdate donor and bromide donor has a weight percent ratio of molybdate (MoO 4   2− ) to bromide (Br − ) ranging from 1:25000 to 1:5000, more preferably 1:5000 to 1:1000, and most preferred between 1:1000 and 1:10. 
     The oxidizer inert tracer shadows the bromide ions in the aqueous system. When water is lost due to filter backwash, splashing or draining, both the tracer and bromide ion concentration decrease. When the tracer concentration reaches or drops below the desired minimum concentration, additional composition can be applied to the aqueous system to sustain the bromide concentration. 
     EXAMPLE 
     Sodium molybdate was obtained from Sigma Aldrich, sodium bromide was obtained from Albemarle Corporation and 25 wt % active sodium chlorite was obtained from OxyChem Corporation. 
     An 18′×33′ oval shaped pool with approximately 4′ of water was treated with a composition comprising 14 g of Na 2 MoO 4  and 2400 g of NaBr. The composition was produced by combining both ingredients and mixing. The pool was treated with trichloroisocyanuric acid to sustain between 2 mg/l to 3 mg/l chlorine (as Cl 2 ). 
     The composition was added directly to the pool water and allowed to dissolve and dissipate in the pool water for several hours. A sample of pool water was collected and tested using a Hach® DR2800 spectrophotometer using low range molybdenum reagents. The pH was measured at 7.57. 
     The molybdenum (as Mo) measured 0.09 mg/l. The molybdate (as MoO 4   2− ) concentration was obtained by multiplying the molybdenum concentration by 1.67 resulting in a molybdate concentration of 0.15 mg/l. Based on the amount of sodium molybdate added to the pool and the result of the molybdate test, the pool volume was calculated to be 71,795 gallons. 
     Based on the pool volume, the bromide ion (as Br − ) concentration is calculated to be 6.86 mg/l (as Br − ). 
     During evening hours (after dusk), 490 g of 25 wt % active sodium chlorite was added to the pool. The treatment was allowed to circulate for approximately 1 hour. A sample was collected and a lissamine green test was performed using a PalinTest® spectrophotometer with low range lissamine green reagent. The lissamine green treated sample was allowed to react for 20 minutes before measuring the chlorine dioxide concentration. The result of the lissamine green test was 0.25 mg/l as ClO 2 . 
     The example illustrates that the method and composition of the disclosed invention for monitoring and controlling the relative concentration of bromide ion used in the cyclic process is effective.