<?xml version="1.0" encoding="UTF-8"?><!DOCTYPE article  PUBLIC "-//NLM//DTD Journal Publishing DTD v3.0 20080202//EN" "http://dtd.nlm.nih.gov/publishing/3.0/journalpublishing3.dtd"><article xmlns:mml="http://www.w3.org/1998/Math/MathML" xmlns:xlink="http://www.w3.org/1999/xlink" dtd-version="3.0" xml:lang="en" article-type="research article"><front><journal-meta><journal-id journal-id-type="publisher-id">FNS</journal-id><journal-title-group><journal-title>Food and Nutrition Sciences</journal-title></journal-title-group><issn pub-type="epub">2157-944X</issn><publisher><publisher-name>Scientific Research Publishing</publisher-name></publisher></journal-meta><article-meta><article-id pub-id-type="doi">10.4236/fns.2012.36102</article-id><article-id pub-id-type="publisher-id">FNS-19918</article-id><article-categories><subj-group subj-group-type="heading"><subject>Articles</subject></subj-group><subj-group subj-group-type="Discipline-v2"><subject>Biomedical&amp;Life Sciences</subject></subj-group></article-categories><title-group><article-title>
 
 
  Electrolyzed Oxidized Water (EOW): Non-Thermal Approach for Decontamination of Food Borne Microorganisms in Food Industry
 
</article-title></title-group><contrib-group><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>ubrota</surname><given-names>Hati</given-names></name><xref ref-type="aff" rid="aff1"><sup>1</sup></xref><xref ref-type="corresp" rid="cor1"><sup>*</sup></xref></contrib><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Surajit</surname><given-names>Mandal</given-names></name><xref ref-type="aff" rid="aff1"><sup>1</sup></xref></contrib><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>P.</surname><given-names>S. Minz</given-names></name><xref ref-type="aff" rid="aff2"><sup>2</sup></xref></contrib><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Shilpa</surname><given-names>Vij</given-names></name><xref ref-type="aff" rid="aff1"><sup>1</sup></xref></contrib><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Yogesh</surname><given-names>Khetra</given-names></name><xref ref-type="aff" rid="aff3"><sup>3</sup></xref></contrib><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>B.</surname><given-names>P. Singh</given-names></name><xref ref-type="aff" rid="aff1"><sup>1</sup></xref></contrib><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Dipika</surname><given-names>Yadav</given-names></name><xref ref-type="aff" rid="aff1"><sup>1</sup></xref></contrib></contrib-group><aff id="aff2"><addr-line>Dairy Engineering Division, National Dairy Research Institute, Deemed University, Karnal, India</addr-line></aff><aff id="aff1"><addr-line>Dairy Microbiology Division, National Dairy Research Institute, Deemed University, Karnal, India</addr-line></aff><aff id="aff3"><addr-line>Dairy Technology Division, National Dairy Research Institute, Deemed University, Karnal, India.</addr-line></aff><author-notes><corresp id="cor1">* E-mail:<email>subrota_dt@yahoo.com(UH)</email>;</corresp></author-notes><pub-date pub-type="epub"><day>20</day><month>06</month><year>2012</year></pub-date><volume>03</volume><issue>06</issue><fpage>760</fpage><lpage>768</lpage><history><date date-type="received"><day>December</day>	<month>13th,</month>	<year>2011</year></date><date date-type="rev-recd"><day>April</day>	<month>11th,</month>	<year>2012</year>	</date><date date-type="accepted"><day>April</day>	<month>18th,</month>	<year>2012</year></date></history><permissions><copyright-statement>&#169; Copyright  2014 by authors and Scientific Research Publishing Inc. </copyright-statement><copyright-year>2014</copyright-year><license><license-p>This work is licensed under the Creative Commons Attribution International License (CC BY). http://creativecommons.org/licenses/by/4.0/</license-p></license></permissions><abstract><p>
 
 
  Electrolyzed Oxidized Water (EOW) is produced by passing a diluted salt solution through an electrolytic cell, having anode and cathode electrodes. The anode and cathode are separated by a bipolar membrane. Negatively charged ions—chloride and hydroxide in the diluted salt solution move to anode to give up electrons and become gas (O2, Cl2) and hypochlorous acid and having redox potential of +700 to +800 mV with pH 4.0. It has a strong oxidation potential and a shortage of electrons giving it the ability to oxidize and sterilize. In microbial inactivation process, oxidized water damage cell membranes, create disruption in cell metabolic processes and essentially kill the cell. EOW, also a strong acid, is different to hydrochloric acid or sulfuric acid in that it is not corrosive to skin, mucous membrane, or organic material. It is easy to handle and suitable for the sanitation of the plant and decontamination of foods. Electrolyzed water has been tested and used as a disinfectant in the food industry and other applications.
 
</p></abstract><kwd-group><kwd>Electrolyzed; Oxidized; Anode; Disinfectant; Food; Microorganisms</kwd></kwd-group></article-meta></front><body><sec id="s1"><title>1. Introduction</title><p>Since the mid 1980’s, electrolyzed water has been certified for use in Japan as a medical product. The first form of electrolyzed water (EO) that was developed was the acidic type, and it was accepted quickly by the food industry in Japan. It was found to be useful at killing bacteria and parasites on raw fish without altering the sensory characteristics of the fish. Although Hazard Analysis Critical Control Point (HACCP) system has been implemented in many food processing establishments, most outbreaks of food-borne illnesses still occurred in foodservice sectors including institutions, fast food restaurants, and food stores, where food products had undergone various treatments and should have been rendered as safe [<xref ref-type="bibr" rid="scirp.19918-ref1">1</xref>]. This situation indicates that hazards might still exist in the food supply systems. Today, food chains are becoming complicated in handling, processing, transportation, and storage ensuring a safe food supply becomes a challenge task. Electrolyzed water definitely has a lot of potential uses for the food industry. Possibilities for the use of electrolyzed water are growing but one basic and proven application is using it as a disinfectant on food contact surfaces. This is advantageous to Industry because it involves on-site production of the disinfectant, which means there are no chemicals to store or handling costs of chemicals to deal with [<xref ref-type="bibr" rid="scirp.19918-ref2">2</xref>]. The major advantages of using EOW for inactivation of bacteria are less adverse environmental impacts and without the difficulties of transporting and storing potentially hazardous chemicals [<xref ref-type="bibr" rid="scirp.19918-ref3">3</xref>]. Another proven effective use is its application directly on fresh food products to reduce the number of microorganisms or pathogens present. It may even have the prospect of replacing the use of pesticides [<xref ref-type="bibr" rid="scirp.19918-ref2">2</xref>]. It also has possibilities in the area of specialized food products. There is potential use of electrolyzed water on food products that can be of benefit to people with diseases such as gout. It could be used to decrease the amount of purine in foods such as red meats and scallops, so people who suffer from gout are better able to consume the product and not suffer from the effects of that disease [<xref ref-type="bibr" rid="scirp.19918-ref4">4</xref>]. EO water is generated through the electrolysis of a dilute solution of NaCl and softened tap water passed through on electrolysis chamber. EO water is produced by passing a salt solution (12%) across a bipolar membrane, resulting in two solutions: an acidic solution that is characterized by a low pH, high oxidation-reduction potential (ORP), and a free chlorine concentration of approximately 50 ppm; the basic solution is composed of a high pH and low ORP [<xref ref-type="bibr" rid="scirp.19918-ref5">5</xref>]. The sodium ions are drawn to the cathode (NaOH) and the chlorine ions are drawn to the anode (HOCl). The alkaline EO water so collected has a pH of approximately 11.4 and ORP of 795 mV, while acidic EO water has a pH of approximately 2.6, ORP of 1150 mV and a chlorine concentration 40 and 90 ppm. EO water has been utilized to disinfect kitchen cutting boards, and other surfaces, fresh cut vegetables, alfalfa seeds and sprouts, broccoli, strawberry, lettuce, tomatoes, apple and poultry [6,7]. Electrolyzed oxidizing water (EOW) has been reported to have strong bactericidal effects on many pathogenic bacteria, such as Escherichia coli O157:H7 [<xref ref-type="bibr" rid="scirp.19918-ref8">8</xref>], Listeria monocytogenes [<xref ref-type="bibr" rid="scirp.19918-ref9">9</xref>], Bacillus cereus [<xref ref-type="bibr" rid="scirp.19918-ref10">10</xref>], and Salmonella sp. [<xref ref-type="bibr" rid="scirp.19918-ref11">11</xref>]. In addition, it could disinfect hepatitis B virus and human immunodeficiency virus [<xref ref-type="bibr" rid="scirp.19918-ref12">12</xref>] and reduce germinations of many fungal species [<xref ref-type="bibr" rid="scirp.19918-ref10">10</xref>]. EOW can also be used in agriculture for sterilization of fruits and vegetables [<xref ref-type="bibr" rid="scirp.19918-ref13">13</xref>], food materials and food processing materials [14,15] studied using acidic EO water to treat fresh-cut vegetables, and achieved up to a 2.6 log10 CFU/g reduction in bacterial population. In another study, EO water was used to disinfect plastic kitchen cutting board, which reduced E. coli O157:H7 populations more than 5.0 log CFU/100 cm<sup>2</sup> [<xref ref-type="bibr" rid="scirp.19918-ref16">16</xref>]. Using acidic EO water against pure cultures of Enterobacter aerogenes and Staphylococcus aureus yielded 9 log10 CFU/g reduction after 30 s treatment [<xref ref-type="bibr" rid="scirp.19918-ref16">16</xref>]. EO water also has the potential to be more cost effective than traditional disinfectants. Electrolyzed oxidizing (EO) water is a relatively new disinfecting compound that has shown promise against cells suspendsions of Escherichia coli (EC) O157:H7, Salmonella enteritidis, and Listeria monocytogenes [<xref ref-type="bibr" rid="scirp.19918-ref16">16</xref>], E. coli O157:H7 and L. monocytogenes attached to cutting boards [<xref ref-type="bibr" rid="scirp.19918-ref17">17</xref>], spoilage organisms associated with vegetables, pathogens in solution, or pathogens attached to poultry surfaces. It is less dangerous and less expensive than most traditional preservation methods.</p></sec><sec id="s2"><title>2. Basic Principle and EO Water Generation Process</title><p>EO water was initially developed in Japan [<xref ref-type="bibr" rid="scirp.19918-ref18">18</xref>]. It has been reported to have strong bactericidal effects on most pathogenic bacteria that are important to food safety. EO water is produced by passing a diluted salt solution through an electrolytic cell, within which the anode and cathode are separated by a membrane. Generation of EO water involved electrolysis of sodium chloride in a cell containing inert positively charged and negatively charged platinum electrodes separated by a bipolar membrane. A salt solution (12% NaCl) and deionized water were pumped into the EO water generator (ROX Water Electrolyzer, Hoshizaki America, Inc., Peachtree City, GA). By subjecting the electrodes to direct current voltage, two types of water possessing different characteristics were produced: an electrolyzed basic aqueous solution (EOB; pH of 11.6 and oxidation-reduction potential [ORP] of 795 mV) and an electrolyzed acidic solution (EOA; pH range of 2.3 - 2.7, 1150 mV ORP, and approximately 50 ppm free chlorine). Amperage for generation of EO water can be adjusted manually with this system. Two types of water are produced simultaneously. EO water, with low pH (2.3 - 2.7), high oxidation-reduction potential (ORP, &gt;1000 mV), high dissolved oxygen and contains free chlorine (concentration depends on the EO water machine setting), is produced from anode side. However, electrolyzed reduced (ER) water, with high pH (10.0 - 11.5), high dissolved hydrogen, and low ORP (800 to 900 mV), is produced from the cathode side. ER water with strong reducing potential can be used to remove dirt and grease from items such as cutting boards and other kitchen utensils [<xref ref-type="bibr" rid="scirp.19918-ref19">19</xref>].</p><p>The principle of producing electrolyzed water is shown in the following (<xref ref-type="fig" rid="fig1">Figure 1</xref>):</p><sec id="s3_0_1"><title>Positivepole:</title><p><img src="7-2700351\3b7b85e7-ba9d-4fdc-bd07-191cdc038eb0.jpg" /></p></sec><sec id="s3_0_2"><title>Negativepole:</title><p><img src="7-2700351\477447bd-d431-42bf-827d-7f84ac65e861.jpg" /></p></sec><sec id="s3_1"><title>2.1. Substances Generated at Anode</title><p>1) Hypochlorous acid (HClO)</p><p>2) Chlorine gas (Cl<sub>2</sub>)</p><p>Chlorine changes its existence form depending on the pH of the solution. As the pH of electrolyzed acidic water is around 2.5, it consists of 85% of hypochlorous acid and 15% of chlorine gas. Therefore, the available chlorine in electrolyzed acidic water refers to a combination of hypochlorous acid and chlorine gas. The amount of chlorine gas production is as little as 0.012 ml/min (15 A, 2.5 L/min). In contrast, sodium hypochlorite (ClO-, hypochlorite ion) widely used in the market has a pH of</p><p>around 10.</p><p>3) Hydrochloric acid (HCl)</p><p>The pH 2.5 of electrolyzed acidic water is due to the generation of extremely dilute hydrochloric acid. The Poisonous Material Control Law specifies a minimum of 10%. But the concentration of hydrochloric acid in acidic water is around 0.01%, which is about 1/1000 of the specified level.</p><p>4) Oxygen gas (O<sub>2</sub>)</p><p>More than 99.9% of generated gas is oxygen. Its generation rate is about 24 ml/min (15 A, 2.5 L/min).</p></sec><sec id="s3_2"><title>2.2. Substances Generated in Alkaline Water</title><p>1) Sodium hydroxide The pH 11.5 of electrolyzed alkaline water is due to the generation of extremely dilute sodium hydroxide. The Poisonous Material Control Law specifies a minimum of 5%. But the concentration of sodium hydroxide in acidic water is around 0.013%, which is about 1/400 of the specified level.</p><p>2) Hydrogen gas Almost 100% of generated gas is hydrogen. Its generation rate is about 112 ml/min (15 A, 2.5 L/min). The explosive limit (maximum volume concentration) in the air is 4% - 75%. But generated gas is exhausted outdoors and causes no problem. For example, in a totally enclosed 5 &#215; 5 &#215; 3 m (75 m<sup>3</sup>) room, hydrogen gas concentration will not reach the explosive limit of 4% unless the unit is continuously operated for more than 440 hours. The main advantage of EO water is its safety. EO water which is also a strong acid is different to hydrochloric acid or sulfuric acid in that it is not corrosive to skin, mucous membrane, or organic material. On the other hand, sodium hypochlorite was proved to have a strong toxicity, such as skin irritation, membrane irritation, acute toxicity, and so on [<xref ref-type="bibr" rid="scirp.19918-ref20">20</xref>]. Currently used hatchery sanitizers (formaldehyde gas and glutaraldehyde) are noxious to humans and chicks, and may pose a serious health risk [<xref ref-type="bibr" rid="scirp.19918-ref21">21</xref>]. Furthermore, the use of formaldehyde gas and glutaraldehyde are gradually being limited because of the adverse effects this chemical has on the environment [<xref ref-type="bibr" rid="scirp.19918-ref22">22</xref>] also stated that EO water provides a useful means of cleaning and disinfecting digestive endoscopes between patients. It is safe for the human body and for the environment. In addition, the cost of using EO water is much less expensive (5.3 yen/L) compared with glutaraldehyde (1200 yen/L) [<xref ref-type="bibr" rid="scirp.19918-ref22">22</xref>]. When EO water comes into contact with organic matter, or is diluted by tap water or reverse osmosis (RO) water, it becomes ordinary water again. Thus, it’s less adverse impact on the environment as well as users’ health. Moreover, compared with other conventional disinfecting techniques, EO water reduces cleaning times, is easy to handle, has very few side effects, and is relative cheap [<xref ref-type="bibr" rid="scirp.19918-ref23">23</xref>]. Chemicals used for cleaning and disinfection are expensive and represent an operating expense for the dairy producer. Once the initial capital investment is made to purchase an EO water generator, the only operating expenses are water, salts and electricity to run the unit [<xref ref-type="bibr" rid="scirp.19918-ref24">24</xref>] The main disadvantage of EO water is that the solution rapidly loses its antimicrobial activity if EO water is not continuously supplied with H<sup>+</sup>, HOCl and Cl<sub>2</sub> by electrolysis [<xref ref-type="bibr" rid="scirp.19918-ref25">25</xref>]. EO water is gaining a reputation in various fields as a more capable disinfectant than conventional chemical disinfectants. However, problems, such as chlorine gas emission, metal corrosion, and synthetic resin degradation, due to its strong acidity and free chlorine content have been a matter of concern. Although metal corrosion and synthetic resin degradation occurred, they were not serious on hemodialysis equipment [23,26] also indicated that EO water did not have any adverse effect on stainless steel, it can still be safely used as a sanitizer to inactivate bacteria on food contact surfaces made from stainless steel in food processing. After disinfection, washing food equipment with sterile water can completely avoid metal corrosion. During the EO water generation process, chlorine ions are generated, and thus chlorine gas is emitted. This necessitates the use of standard-type extractor fan.</p></sec></sec><sec id="s4"><title>3. Inactivation of Microbes Using EO Water</title><p>EO water may inactivate both vegetative cells and bacterial endospores. Three basic mechanisms have been attributed to the inactivation of microbial spores during EO water treatment. These include destruction of DNA by UV irradiation, volatilization of compounds from the spore surface by UV-photons and erosion or so called “etching” of the spore surface by adsorption of reactive species like free radicals. Many studies have been conducted in evaluating the bactericidal activity of EO water. EO water possess antimicrobial activity on a variety of microorganisms including Pseudomonas aeruginosa [25, 27] Staphylococcus aureus [<xref ref-type="bibr" rid="scirp.19918-ref27">27</xref>], S. epidermidis, E. coli O157:H7 [17,28,29], Salmonella enteritidis [<xref ref-type="bibr" rid="scirp.19918-ref17">17</xref>], Salmonella Typhimurium [<xref ref-type="bibr" rid="scirp.19918-ref11">11</xref>], Bacillus cereus [27,30,31], Listeria monocytogenes [11,27,29], Campylobacter jejuni [<xref ref-type="bibr" rid="scirp.19918-ref18">18</xref>], Enterobacter aerogenes [<xref ref-type="bibr" rid="scirp.19918-ref32">32</xref>] and Vibrio parahaemolyticus [<xref ref-type="bibr" rid="scirp.19918-ref33">33</xref>]. EO water can also reduce germination of many fungal species, such as Alternaria spp., Bortrytis spp., Cladosporium spp., Colletotrichum spp., Curvularia lunata, Didymella bryonaie, Epicoccum nigrum, Fusarium spp., Helminthosporium spp., Pestalotia spp., Phomopsis longicolla, Rhodosporidium toruloides, Stagonospora nodorum, Thielaviopsis basicola, Trichoderma spirale, Acidovorax avenae subsp., Erwinia chrysanthemi, Pantoea ananatis, Pseudomonas syringae [<xref ref-type="bibr" rid="scirp.19918-ref10">10</xref>], Aspergillus spp. [<xref ref-type="bibr" rid="scirp.19918-ref10">10</xref>], Botryosphaeria berengeriana (AlHaq et al., 2002), Monilinia fructicola (Al-Haq et al., 2001; 10], Penicillium expansum and Tilletia indica. In general, bacteria generally grow in a pH range of 4 - 9. Aerobic bacteria grow mostly at ORP range +200 to 800 mV, while anaerobic bacteria grow well at +700 to +200 mV. High ORP in the EO water cause the modification of metabolic fluxes and ATP production, probably due to the change in the electron flow in cells. Low pH may sensitize the outer membrane of bacterial cells to the entry of HOCl into bacterial cells. HOCl, the most active of the chlorine compounds, appears to kill the microbial cell through inhibiting glucose oxidation by chlorine-oxidizing sulfhydryl groups of certain enzymes important in carbohydrate metabolism. Other modes of chlorine action that have been proposed are: 1) disruption of protein synthesis; 2) oxidative decarboxylation of amino acids to nitrites and aldehydes; 3) reactions with nucleic acids, purines, and pyrimidines; 4) unbalanced metabolism after the destruction of key enzymes; 5) induction of deoxyribonucleic acid (DNA) lesions with using a scanning electron microscope. The cells treated with electrolyzed acidic water had wrinkled cell wall with round pores in which the cytoplasmic structures were flushed out (<xref ref-type="fig" rid="fig2">Figure 2</xref>). [<xref ref-type="bibr" rid="scirp.19918-ref28">28</xref>] has developed chemically modified water from deionized water with the same properties (i.e., pH, chlorine and ORP) as EO water without using electrolysis. Their results suggested that ORP of EO water might be the primary factor responsible for the bactericidal effect. However, ORP is not the main factor of antimicrobial activity because the higher ORP of ozonated water did not show higher disinfectant effect than lower ORP of EO water. They further defined that free chlorine of EO water, mainly hypochlorous acid (HOCl), produces hydroxyl radical (OH<sup>−</sup>) that acts on microorganisms. Ozone solution produces OH, too. The higher OH produced by higher HOCl concentration in EO water means the better the disinfectant efficacy than ozone solution. The relative concentrations of aqueous molecular chlorine, HOCl, hypochlorite ion (OCl) and chlorine gas (Cl<sub>2</sub>) were also the factors that accounted for the bactericidal potency. At pH 4, EO water with the maximum concentration of HOCl had the maximum microbiocidal activity. [<xref ref-type="bibr" rid="scirp.19918-ref29">29</xref>] investigated the effects of chlorine and pH on efficacy of EO water for inactivating E. coli O157:H7 and L. monocytogenes. EO water is very effective for inactivating E. coli O157:H7 and L. monocytogenes in a wide pH range (between 2.6 and 7.0), if sufficient free chlorine (&gt;2 mg/L) is present. For each chlorine content, bactericidal activity and ORP increased with decreasing pH. Based on fluorescent and spectroscopic measurements, [<xref ref-type="bibr" rid="scirp.19918-ref34">34</xref>] reported that the ORP of EO water could damage the outer and inner membranes of E. coli O157:H7. The redox state of the glutathione disulfide-glutathione couple (GSSG/2GSH) can serve as an important indicator of redox environment. There are many redox couples in a cell that work together to maintain the redox environment. The inactivation mechanism hypothesized was that</p><p>ORP could damage the redox state of GSSG/2GSH and then penetrate the outer and inner membranes of cell, giving rise to the release of intracellular components and finally cause the necrosis of E. coli O157:H7. Thus, the antimicrobial effect of EO water derives from the combined action of the hydrogen ion concentration, oxidation-reduction potential and free chlorine. Storage conditions can affect chemical and physical properties of EO water. When stored under an open, agitated and diffused light condition the EO water had the highest chlorine loss rate. Under open condition, chlorine loss through evaporation followed first-order kinetics. The rate of chlorine loss was increased around 5-fold with agitation, but it was not significantly affected by diffused light [<xref ref-type="bibr" rid="scirp.19918-ref35">35</xref>]. EO water exposed to the atmosphere could reduce more chlorine and oxygen than that kept to a closed systems for a longer time [11,36] reported that EO water stored at 4˚C was more stable than stored at 25˚C. The effectiveness of chlorine as a bactericidal agent is reduced in the presence of organic matter due to the formation of combined available chlorines. At an identical chlorine concentration, the combined available chlorines had much lower bactericidal activity than the free form [<xref ref-type="bibr" rid="scirp.19918-ref37">37</xref>]. The accompanying loss of DNA-transforming ability; 6) inhibition of oxygen uptake and oxidative phosphorylation, coupled with leakage of some macromolecules; 7) formation of toxic N-chlorine derivatives of cytosine; and 8) creation of chromosomal aberrations [<xref ref-type="bibr" rid="scirp.19918-ref38">38</xref>]. A theory for inactivation of bacteria based on the high oxidation potential of EO water causing damage of cell membranes was reported by [<xref ref-type="bibr" rid="scirp.19918-ref34">34</xref>]. The chemical process of oxidation occurs when oxygen contacts with other compounds causing them to lose electrons and further causing the compounds to break down and change functions. In the case of microbes, oxidation could damage cell membranes, create disruption in cell metabolic processes and essentially kill the cell.</p></sec><sec id="s5"><title>4. Potential Application of EOW in Food Processing</title><p>Application of electrolyzed oxidizing water to reduce Listeria monocytogenes on ready-to-eat meats [<xref ref-type="bibr" rid="scirp.19918-ref11">11</xref>]. Experiments were conducted to determine the effectiveness of acidic (EOA) or basic electrolyzed oxidizing (EOB) water, alone or in combination, on ready-to-eat (RTE) meats to reduce Listeria monocytogenes. The Centers for Disease Control and Prevention (CDC) considers E. coli O157:H7 and L. monocytogenes to be of great concern because of the severity and number of illnesses they cause [<xref ref-type="bibr" rid="scirp.19918-ref39">39</xref>]. Frankfurters or ham surfaces were experimentally inoculated with L. monocytogenes and subjected to dipping or spraying treatments (25˚C or 4˚C for up to 30 min) with EOA, EOB, and other food grade compounds. L. monocytogenes was reduced the greatest when frankfurters were treated with EOA and dipped at 25˚C for 15 min. Reductions greater than 1 log CFU/g were not observed for the duration of the study. Even with a prolonged contact time, treatments with EOA or EOB were not enough to meet regulatory requirements for control of LM on RTE meats. Additional studies required to identify food grade antimicrobials to control the pathogen on RTE meats are warranted.</p><p>EO water has been used as a disinfectant for food processing equipment. EO water (pH of 2.53, ORP of 1178 mV and chlorine of 53 mg/L) could also reduce Enterobacter aerogenes and S. aureus on glass, stainless steel, glazed ceramic tile, unglazed ceramic tile and vitreous china surfaces. Immersion of these surfaces in EO water for 5 min with agitation (50 rpm) reduced populations of E. aerogenes and S. aureus on the tested surfaces to &lt;1 CFU/cm<sup>2</sup> [<xref ref-type="bibr" rid="scirp.19918-ref32">32</xref>]. Listeria monocytogenes is a foodborne pathogen that can lead to potentially life-threatening listeriosis in high-risk populations. [<xref ref-type="bibr" rid="scirp.19918-ref8">8</xref>] investigated the resistance of L. monocytogenes biofilms on stainless steel surfaces to EO water (pH of 2.60, ORP of 1160 mV and chlorine of 56 mg/L) and found that a 300 s treatment on a stainless steel surface, could reduce the L. monocytogenes from 1.9 &#215; 10<sup>10</sup> CFU/82.5 cm<sup>2</sup> to below detection levels. However, it took 300 s of exposure to 200 mg/L chlorine solution to achieve the same result.</p><p>Fresh-cut apples (approx. 600 g) were disinfected by sodium hypochlorite (pH 9.3, available chlorine 200 mg/ kg) or electrolyzed acidic water (pH 2.6, available chlorine 30 mg/kg), rinsed thoroughly with tap water for 15 seconds and checked with chlorine test paper for residual chlorine [<xref ref-type="bibr" rid="scirp.19918-ref40">40</xref>]. EO water containing 50 mg/L chlorine had a stronger bactericidal effect than that containing 15 or 30 mg/L chlorine. The treatment did not cause discoloration of fresh-cut produces. Rinsing EO water (50 mg/L) treated fresh-cut produces with fresh water did not increase the bacterial reduction due to the additive effects of the sequential treatment. [<xref ref-type="bibr" rid="scirp.19918-ref41">41</xref>] reported that cucumbers washed with ER water (pH of 11.3, ORP of −870 mV) for 5 min and then soaked in EO water (pH of 2.6, ORP of 1130 mV and free chlorine of 30 mg/L) for 5 min showed a reduction in aerobic mesophiles. Lettuce with smooth surfaces have been used for the investigation of the effectiveness of EO water on bacterial reduction. [<xref ref-type="bibr" rid="scirp.19918-ref42">42</xref>] observed that shaking lettuce with EO water (45 mg/L free chlorine) at 100 rpm for 3 min significantly decreased mean populations of E. coli O157:H7 and L. monocytogenes by 2.41 and 2.65 logCFU per lettuce leaf, respectively, when compared with sterile H<sub>2</sub>O<sub>2</sub> treatment. The result was in agreement with that of [<xref ref-type="bibr" rid="scirp.19918-ref15">15</xref>] who pointed out that EO water (50 mg/L of free chlorine) treatment of shredded lettuce did not significantly affect the quality characteristics such as color and general appearance.</p><p>Electrolyzed alkaline water contains a small amount of sodium hydroxide which is a material of soap, and is effective in washing away proteins, fats and oils which are hard to wash by water. [<xref ref-type="bibr" rid="scirp.19918-ref33">33</xref>] also reported that EO water was a very effective sanitizer used for cleaning fish contacting surfaces in traditional grocery stores and fish markets, so that secondary bacterial contamination could be prevented. EO water was especially effective in reducing the population of E. coli and V. parahaemolyticus contamination on tilapia.</p><p>[<xref ref-type="bibr" rid="scirp.19918-ref43">43</xref>] found that treating raw salmon with EO water (pH of 2.6, ORP of 1150 mV and free chlorine of 90 mg/L) at 35˚C for 64 min resulted in a 1.07 logCFU/g (91.1%) and 1.12 logCFU/g (92.3%) reduction in E. coli O157:H7 and L. monocytogenes, respectively. [<xref ref-type="bibr" rid="scirp.19918-ref44">44</xref>] stated that gloves used in handling food for protection of the worker and seller could become a carrier of pathogens through the contact of raw materials or contaminated surfaces. However, applications of EO water following a thorough cleaning greatly reduced L. monocytogenes population on gloves and seafood processing plants. Soaking inoculated gloves in EO water (pH of 2.6, ORP of 1125 mV and free chlorine of 40 mg/L) at room temperature for 5 min completely eliminated L. monocytogenes on gloves (&gt; 4.46 logCFU/cm<sup>2</sup>) [<xref ref-type="bibr" rid="scirp.19918-ref44">44</xref>]. The treatment by immersion in EO water containing 50 mg/L chlorine for 5 min significantly reduced L. monocytogenes on tested surfaces (3.73 log/25cm<sup>2</sup> on stainless steel sheet, 4.24 log/25 cm<sup>2</sup> on ceramic tile and 1.52 log/25cm<sup>2</sup> on floor tile) [<xref ref-type="bibr" rid="scirp.19918-ref45">45</xref>].</p></sec><sec id="s6"><title>5. Safety Concern of EOW</title><p>Use of EO water in different ways such as cleaning, sanitation on the surfaces of food processing equipments, decontamination or inactivation of food borne microorganisms present in fruits, vegetables or meat, sea foods etc. raise an issue of food safety. Different testings for EO water related to food safety has been followed [<xref ref-type="bibr" rid="scirp.19918-ref46">46</xref>].</p><sec id="s6_1"><title>5.1. Cytotoxicity Test</title><p>The number of colonies showed no significant difference between incubation with electrolyzed acidic water and incubation with distilled water for injection as a negative control.</p></sec><sec id="s6_2"><title>5.2. Reverse Mutation Test (Ames Test)</title><p>No reverse mutation occurred in any bacterial species cultured with electrolyzed acidic water, showing its nonmutagenicity.</p></sec><sec id="s6_3"><title>5.3. Chromosomal Aberration Test</title><p>Both direct and metabolic activation methods resulted in no significant difference from the control.</p></sec><sec id="s6_4"><title>5.4. Hemolysis Test</title><p>In erythrocyte fragility test, electrolyzed acidic water provided higher hemolytic activity than distilled water.</p></sec><sec id="s6_5"><title>5.5. Single Dose Toxicity Test</title><p>Mice dosed with electrolyzed acidic water showed no abnormality in body weight, general symptoms and macroscopic findings.</p></sec><sec id="s6_6"><title>5.6. Skin Toxicity Test by Repeated Immersion</title><p>Rats immersed in electrolyzed acidic water demonstrated no adverse effect in skin, body weight, food intake, blood, biochemical, and pathological examinations.</p></sec><sec id="s6_7"><title>5.7. Antigenicity Test</title><p>Guinea pigs sensitized to electrolyzed acidic water showed no anaphylactic symptoms.</p></sec><sec id="s6_8"><title>5.8. Cumulative Skin Irritation Test</title><p>No change was observed in any rabbit skins treated with electrolyzed acidic water, demonstrating no skin irritancy.</p></sec><sec id="s6_9"><title>5.9. Primary Eye Mucosa Irritation Test</title><p>After administration of eye drops of electrolyzed acidic water, no change was found in either non-eye washed, 2-second or 4-second eye washed rabbit group.</p></sec><sec id="s6_10"><title>5.10. Oral Mucosa Irritation Test</title><p>Electrolyzed acidic water was flowed into the oral cavity of hamsters at 1 ml/min for 10, 20 or 30 minutes. The 10-minute or 20-minute flow caused no disorder. But the 30-minute flow resulted in mild histopathological degeneration of oral mucosa.</p></sec><sec id="s6_11"><title>5.11. Inhalation Toxicity Test</title><p>The treated rats had no general symptoms and showed no change in body weight, food intake, blood, biochemical, and pathological examinations.</p></sec><sec id="s6_12"><title>5.12. Sensitization Test</title><p>No sensitization was observed by hypodermic injection and induction of electrolyzed acidic water.</p></sec><sec id="s6_13"><title>5.13. Primary Skin Irritation Test on Rabbits</title><p>The primary irritation index (P.I.I.) required in accordance with the Federal Register (1972) was 0.4 which falls within the non-irritating category.</p></sec><sec id="s6_14"><title>5.14. Colony Formation Inhibition Test with Cultured Cells</title><p>In the direct exposure method, the 50% inhibitory concentration (IC50) by concentration-dependant inhibition of colony formation resulted in around 94.8%. But in the culture medium mixture method, the analyte solution did not inhibit colony formation. These results showed that the direct exposure of cells to electrolyzed alkaline water obtained from the analyte caused slight cytotoxicity, but the exposure to alkaline water mixed with culture medium had no such effect.</p></sec><sec id="s6_15"><title>5.15. Marmot Skin Sensitization Test by Maximization Method</title><p>Electrolyzed alkaline water was determined to have no skin sensitization potential.</p></sec><sec id="s6_16"><title>5.16. Acute Eye Mucosa Irritation Test</title><p>After 1 hour from administration of eye drops containing 0.1 mol/L sodium hydroxide solution, all samples showed conjunctival swelling (Grade 1) and increased ocular discharge (Grade 2). After 24 hours from administration, no conjunctival swelling was observed on any sample.</p></sec><sec id="s6_17"><title>5.17. Shelf Life of EOW</title><p>When stored in an open container or direct sunlight, electrolyzed acidic water will rapidly lose available chlorine and should be used as soon as possible. But it will have a shelf life for several weeks when stored in shade in a sealed container [<xref ref-type="bibr" rid="scirp.19918-ref46">46</xref>].</p></sec></sec><sec id="s7"><title>6. Conclusion</title><p>EO water has great potential to compete with current methods. Need to optimize the process for individual applications. EOW treatment may be used as an effective method for reducing microbial contamination not only on food processing surfaces but also on non-food-contact surfaces such as ceramic tiles, floors, stainless steel, laboratory glassware, or medical or dental facilities and raw fruits or vegetables for pretreatment with EOW to reduce microbial load. Reduction of S. aureus, E. aerogenes and L. monocytogenes after treatment with EOW indicated that EOW can also prevent cross contamination from treatment solutions. As EOW is produced on-site and on demand for direct use, it can also reduce health hazards for workers by eliminating the need to handle concentrated chemicals. It may be useful as a food safety agent. EOW are useful in food manufacturing, depending on the food being produced. The use of EOW is an emerging technology and huge scope to further research and development to compete with current practices.</p></sec><sec id="s8"><title>REFERENCES</title></sec><sec id="s9"><title>NOTES</title></sec></body><back><ref-list><title>References</title><ref id="scirp.19918-ref1"><label>1</label><mixed-citation publication-type="other" xlink:type="simple">P. C. Chang, “HACCP Update in Fish Process in Taiwan,” In: D. F. Hwang and T. Noguchi, Eds., Proceedings of International Scientific Symposium on Marine Toxins and Marine Food Safety, National Taiwan Ocean University, Keelung, 2003, pp. 137-141.</mixed-citation></ref><ref id="scirp.19918-ref2"><label>2</label><mixed-citation publication-type="other" xlink:type="simple">Science and Education Impact, “Detecting Food Borne Enemies,” 2001. 
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