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PROCESSING, PRODUCTS, AND FOOD SAFETY |
Agricultural Research Service, Poultry Processing Research Unit, Russell Research Center, USDA, Athens, GA 30605
1 Corresponding author: ahinton{at}saa.ars.usda.gov
| ABSTRACT |
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Key Words: spoilage microflora broiler carcass electrolyzed water chlorinated water inside-outside bird washer
| INTRODUCTION |
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Acidic and alkaline electrolyzed oxidizing (EO) water are produced in EO water generators by the electrolysis of dilute solutions of sodium chloride or other salts. The microbicidal activity of acidic EO water is due to the combination of the low pH, high oxidation-reduction potential (ORP), and elevated concentrations of hypochlorous acid (Kim et al., 2000b; Park et al., 2004) produced during electrolysis. Although alkaline EO water is not microbicidal, it can be used as a cleanser. The properties of EO water can be easily modified by altering the electrical amperage of the generator during electrolysis (Kim et al., 2000b). Salts, such as sodium chloride, are the only chemicals required during the production of EO water; therefore, the necessity of storing and handling large quantities of chlorine or other potentially dangerous chemicals is eliminated.
The microbicidal activity of acidic EO water has been successfully used in several fields to reduce microbial contamination of products. These applications include the use of EO water as a sanitizer during food preparation, as a disinfectant in medical operations, and as an antimicrobial agent to reduce contamination of agricultural crops (Wullaert, 1997). Acidic EO water has been reported to be microbicidal toward several pathogenic and indicator microorganisms associated with poultry processing (Kim et al., 2000a). Cultures of Escherichia coli O157:H7, Listeria monocytogenes (Park et al., 2004), and Salmonella enteritidis (Venkitanarayana et al., 1999a) can be completely inactivated by EO water in vitro and on cutting boards (Venkitanarayana et al., 1999b). Spraying contaminated eggs with EO water may reduce or eliminate Salmonella typhimurium, L. monocytogenes, Staphylococcus aureus, and E. coli on the surface of the eggs (Russell, 2003). Furthermore, EO water has been shown to be as effective as chlorinated water in reducing contamination of poultry meat by Campylobacter jejuni (Park et al., 2002a) and S. typhimurium. (Fabrizio et al., 2002). The purpose of the present study was to compare the ability of chlorinated and EO water to reduce the population of spoilage microorganisms on processed broiler carcasses.
| MATERIALS AND METHODS |
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Eviscerated broiler carcasses were collected from the processing line of a local commercial poultry processing facility before being sent into the final bird washer. Carcasses were placed on ice and immediately transported to a pilot plant scale poultry processing facility. For each of 3 experimental trials, carcasses were divided into 3 treatment groups of 24 carcasses each. Carcasses in each group were sprayed with tap water, a 50-ppm chlorine solution, or acidic EO water for 5 s at 80 psi in an inside-outside bird washer (IOBW). The pH of the tap water was 8.0, and the total chlorine concentration was 0.5 ppm. The 50 ppm of chlorinated water (pH 8.2) was prepared by mixing approximately 125 mL of 6.15% commercial bleach (The Clorox Co., Oakland, CA) in 150 L of tap water. Acidic EO water with a pH of 2.4, ORP of +1,180 mV, and 50 ppm of chlorine was produced with an EO water generator (Electric Aquagenics Unlimited Inc., Lindon, UT) filled with a 20% (wt/vol) solution of sodium chloride. The pH of the tap, chlorine, and EO water was measured using a handheld pH meter (model AP5, Denver Instrument, Denver, CO) before spraying the carcasses in the IOBW. The total chlorine concentration of the tap and chlorine water was also measured immediately before treating carcasses using a colorimetric reaction with N, N-diethyl-p-phenylenediamine from the CHEMetrics 2 SAM test kit (CHEMetrics Inc., Calverton, VA). The chlorine concentration of the EO water was determined using the iodometric titration method with the Hach hypochlorite test kit (model CN-HRDT, Hach Co., Loveland, CO).
Microbial Analyses
Treated carcasses were collected from the IOBW and placed in separate sterile plastic bags. Carcasses within each spray treatment group were divided into 4 smaller groups of 6 carcasses each in preparation for analysis or storage. One of the groups of 6 carcasses from each spray treatment was prepared for immediate microbial analysis, whereas the other 3 groups were placed in refrigerated storage at 4°C for 3, 7, or 14 d. The microbial flora of the carcasses was sampled using the whole carcass rinse procedure (Cox et al., 1981) by adding 100 mL of sterile neutralizing buffer (Difco Co., Detroit, MI) solution to the plastic bags containing the carcasses and shaking the carcasses on a mechanical shaker (Dickens et al., 1985) for 1 min. Carcass rinsates were decanted from the bags and serially diluted in sterile 0.1% bacto peptone solutions (Difco Co.).
The populations of psychrotrophic bacteria and yeasts in the carcass rinsates were enumerated. Psychrotrophic bacteria were enumerated on plate count agar (Difco Co.), incubated at 4°C for 10 d, and yeasts were enumerated on acidified potato dextrose agar incubated at 28°C for 3 d. Morphologically distinct colonies on each media were selected, and isolates were identified using the MIDI Sherlock Microbial Identification System (MIDI Inc., Newark, DE; Operating Manual, M. I. S., 2002; Hinton et al., 2004a).
Statistical Analysis
Data from the 3 trials were combined for statistical analyses due to insignificant trial differences or interactions. Group means of data for the number of microorganisms recovered from the carcasses were compared to determine significant differences in the size of microbial populations recovered from carcasses sprayed with tap, chlorinated, or EO water in the IOBW. Data were also analyzed to determine significant differences in the number of microorganisms recovered from the carcasses sprayed with the same solution and stored at 4°C for 0, 3, 7, 14 d. The lower limit of detection of the plating procedures used was 10 cfu/mL. For purposes of statistical analyses, a value of log10 0.99 cfu/mL was assigned to samples in which no microorganisms were recovered. Data were analyzed using GraphPad InStat version 3.05, 32 Bit for Windows 95/NT (GraphPad Software, San Diego, CA) to perform one-way ANOVA. When the AN-OVA detected significant differences in group means, the Tukey-Kramer multiple comparisons test was used to determine if treatment groups differed significantly. All significant differences were determined at P
0.05.
| RESULTS AND DISCUSSION |
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Significantly fewer psychrotrophic bacteria were recovered from carcasses after spraying with EO or chlorinated water than from carcasses sprayed with tap water (Table 1
). Chlorination of water used to spray carcasses in IOBW has been reported to reduce the population of total bacteria on poultry carcasses (Northcutt et al., 2003). Although forcing EO water through spray nozzles may reduce the chlorine concentration of the water, the residual chlorine in the water can still reduce bacterial contamination of the carcasses (Hsu et al., 2004).
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Although no psychrotrophs were recovered from carcasses immediately after washing with chlorinated or EO water, Pseudomonas spp. were the predominant psychrotrophs isolated from all carcasses refrigerated for 7 to 14 d (Table 2
). Psychrotrophic bacteria generally comprise a minor portion of the microflora of fresh poultry, but some pseudomonads are capable of growing on poultry meat during refrigerated storage (McMeekin, 1977; Gallo et al., 1988; Sundheim et al., 1988). Even though commercial poultry processing operations reduce the number of pseudomonads on broiler carcasses, the population of these bacteria on carcasses increases during refrigerated storage (Hinton et al., 2004b). During changes in the size and composition of the native microflora of fresh poultry during refrigeration (Barnes and Thornley, 1966; Russell et al., 1996), the population of psychrotrophic pseudomonads increases until these bacteria become the dominant flora of spoiled, refrigerated poultry (Arnaut-Rollier et al., 1999). Pseudomonas putida was recovered from carcasses washed with chlorinated water, whereas Pseudomonas chloroaphis was isolated from carcasses washed with tap, chlorinated, or EO water.
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Findings indicated that yeasts on poultry carcasses are also susceptible to the antimicrobial activity of EO and chlorinated water used in an IOBW (Table 3
). The number of yeasts recovered from carcasses sprayed with chlorine water was significantly lower than the number of yeasts recovered from carcasses sprayed with tap water, and significantly fewer yeasts were recovered from carcasses sprayed with EO water than from carcasses sprayed with chlorine water or tap water. Between d 7 and 14 of refrigerated storage, there was a significant increase in the number of yeasts recovered from carcasses washed with tap water, whereas the number of yeasts recovered from carcasses sprayed with chlorine water increased significantly between d 3 and 14. After 14 d of refrigeration, however, there was no significant increase in the population of yeasts recovered from carcasses sprayed with EO water. Although commercial processing generally also reduces contamination of poultry carcasses by yeasts, the population of these psychrotrophic microorganisms in the microflora increases during refrigerated storage (Hinton et al., 2002). Candida spp. are among the most prevalent yeast species of isolated from commercially processed carcasses, and these yeasts were isolated from carcasses washed with tap, chlorinated, or EO water (Table 4
).
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| ACKNOWLEDGMENTS |
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Received for publication December 20, 2005. Accepted for publication March 13, 2006.
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