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Applied and Environmental Microbiology, May 2006, p. 3314-3320, Vol. 72, No. 5
0099-2240/06/$08.00+0 doi:10.1128/AEM.72.5.3314-3320.2006
Copyright © 2006, American Society for Microbiology. All Rights Reserved.
Center for Food Safety, University of Georgia, Griffin, Georgia 30223,1 Ecolab Research Center, 655 Lone Oak Drive, St. Paul, Minnesota 55121,2 Gold Kist, 244 Perimeter Center Pkwy, N.E., Atlanta, Georgia 303463
Received 8 November 2005/ Accepted 27 February 2006
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Decontaminating floor drains of Listeria sp. is especially challenging because when entrapped in a biofilm, Listeria sp. is afforded unusual protection against disinfectants and treatments available to control pathogens on environmental surfaces (7, 9, 14, 17, 18). Once attached, the cells may produce multicellular biofilms that are resistant to disinfection and from which cells can become detached and contaminate food products. The establishment of biofilms by pathogenic bacteria in floor drains in food processing plants is believed to protect against effective cleaning regimens and to reduce or minimize the efficacy of bactericidal treatments. Studies have indicated that L. monocytogenes growing within mixed-microflora biofilms in food processing environments can be a major source of contamination (1, 9, 20).
Promising in vitro results have been obtained in previous studies with two competitive-exclusion bacteria (CE), Lactococcus lactis subsp. lactis C-1-92 and Enterococcus durans 152, for inhibition of the growth of L. monocytogenes in culture media and in biofilms at temperatures ranging from 4 to 37°C (22). The objective of this study was to evaluate the efficacy of these CE in controlling listerial growth and possibly eliminating the pathogen in floor drains at a wide range of temperatures in a facility in which fresh poultry is processed, including under refrigeration conditions.
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Floor drain selection.
Based on the direction of flow of the drains, the fluid flow rate, the fluid volume, the drain size, the temperatures of rooms, and the occurrence and persistence of Listeria sp., six floor drains for CE treatment and an untreated control were identified. Drains 1 and 2 were open trenches (height, 25 cm; width, 30 cm) and were comprised of concrete with fiberglass covers. These drains were located close to poultry meat cutting lines at mean temperatures of 16.8 and 11.5°C, respectively, and largely contained liquid drippings from meat, including meat that had fallen on the floor. Drains 1 and 2 were typically filled to 10 to 30% of capacity during operation. Drain 3 was an open trench (height, 25 cm; width, 30 cm) comprised of concrete with metal edging and a metal cover. This drain was located in the middle of a high-traffic area at a mean temperature of 15.1°C and was typically 20 to 40% full during operation. Drains 4 and 6 were open trenches (height, 20 cm; width, 30 cm) and were comprised of fiberglass. They were located near poultry meat packing areas at mean temperatures of 2.8 and 3.8°C, respectively, and were typically filled to 5 to 20% of capacity during operation. Drain 8 was an open trench (height, 150 cm; width, 90 cm) and was comprised of concrete with a fiberglass cover. This drain was near a liver and lung removal line at a mean temperature of 26.1°C and contained blood and meat debris. It was typically filled with liquid to 15 to 20% of capacity.
Sampling.
Using sterile gloves, an 18-oz. sterile "speci-sponge" (3.8 by 7.6 cm; Nasco Laboratory, Fort Atkinson, WI) was used to wipe an area that was ca. 10 by 10 cm at each sampling location. Five locations, including the inside (bottom) of the drain, the right side of the drain, the left side of the drain, the bottom side of the trench cover, and the floor within 30 cm of the drain, were sampled for each floor drain. Each sponge was placed in a Whirl-Pak bag and kept at 5°C for 2 to 14 h until the sample was assayed.
Enumeration of Listeria sp. and L. monocytogenes.
Ten milliliters of 0.1% peptone was added to each bag, and the sponge and peptone were blended with a stomacher blender (Seward Medical, London, United Kingdom) at 150 rpm for 1 min. The fluid was serially diluted (1:10) in 0.1% peptone (Becton Dickinson Microbiology Systems, Sparks, MD), and 0.1 ml from each dilution tube was plated in duplicate on the surface of modified Oxford medium (MOX) (Oxoid, Ogdensburg, NY) plates. When Listeria sp. was not detected by the direct plating method, the broth plus the sponge was selectively enriched in 225 ml Fraser broth (Becton Dickinson Microbiology Systems) for 24 h at 37°C. Then 1 ml of the broth was serially diluted (1:10) in 0.1% peptone to obtain 108 CFU/ml, and 0.1 ml of each dilution was surface plated on MOX plates in duplicate. The MOX plates were incubated at 37°C for 48 h, and typical black colonies were counted as presumptive Listeria sp. colonies. Colonies counted as Listeria sp. colonies were randomly selected and transferred to MOX plates, and they were confirmed to be Listeria sp. by biochemical tests (API 20I miniaturized diagnostic test; bioMérieux Vitek, Hazelwood, MO) and a lateral flow latex agglutination assay (Listeria Rapid Test; Oxoid, Ogdensburg, NY) and to be L. monocytogenes by an enzyme-linked fluorescent immunoassay with an automated VIDAS instrument (miniVIDAS; bioMérieux Vitek, Hazelwood, MO) and by a PCR assay (Qualicon BAX system; DuPont, Wilmington, DE).
Determination of aerobic plate counts (APCs).
Serial dilutions (duplicate 0.1-ml portions of each dilution) of the samples described above were surface plated on plate count agar plates (Becton Dickinson Microbiology Systems) and incubated at 30°C for 72 h for enumeration.
Preparation of competitive-exclusion bacteria.
Each CE strain, L. lactis subsp. lactis C-1-92 or E. durans 152, was grown individually in 250 ml of Lactobacillus MRS broth (Becton Dickinson Microbiology Systems) at 32°C for 24 h. Cells were sedimented by centrifugation at 10,000 x g for 20 min at 4°C. The bacteria were resuspended in 25 ml of MRS broth at a density of ca. 109 CFU/ml, serially diluted (1:10) in 0.1% peptone, and plated on MRS agar and tryptic soy agar in duplicate for bacterial counting.
Application of competitive-exclusion bacteria to floor drains.
The CE treatment was performed within 20 min after routine sanitation procedures in the plant were completed. Two enzyme-based cleaning products, DY-GEST I (Ecolab, St. Paul, MN) and DY-GEST II (Ecolab), were used to apply the CE treatment. This treatment was routinely used with the cleaning products as part of the plant's routine sanitation procedures; however, the drains were not included as part of the daily routine sanitation procedures. When used under pressure, the cleaning agents formed a foam that remained for about 15 min. The DY-GEST preparation was prepared by mixing in a bottle 20 ml of each product with 3.78 liters of tap water. The two CE isolates (25 ml each) were added to a tank foaming dispenser (model 925916; Lafferty Equipment Manufacturing Co., North Little Rock, AR), followed by the ca. 4 liters of diluted DY-GEST preparation. The tank foaming dispenser was connected to pressurized air, and foam was applied to each floor drain. Approximately 107 CE/ml in the foam formula was applied in order to cover all locations in the floor drain following sanitation four times during the first week of application (Monday through Thursday). After this, the CE treatment was applied twice a week (Tuesday and Thursday) for the following 3 weeks. Samples were collected once a week during the 5 weeks after the CE treatment was initiated. After this, samples were collected every other week or once a month for up to 18 weeks following the last CE treatment.
Statistical analysis.
The least-square means of Listeria sp. counts and APCs at each sampling location before and after CE treatment in each floor drain were determined using the general linear model of the Statistical Analyses System procedure (SAS Institute, Cary, NC). The values used for statistical analysis when bacteria were detected and not detected by selective enrichment in each floor drain were 1.6 and 0 log10 CFU/100 cm2, respectively. The criterion used for significance for differences was P < 0.05 for all assays.
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View this table: [in a new window] |
TABLE 1. Listeria sp. counts for floor drain samples collected before and after CE treatment
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FIG. 1. Listeria sp. counts in concrete, open-trench floor drain 1, which was located near poultry meat cutting lines and contained liquid drippings from meat, including meat that had fallen on the floor. The drain was typically filled to 10 to 30% of capacity during operation. , bottom side of cover; , floor within ca. 30 cm of the drain. (T), CE treatment applied.
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FIG. 5. Listeria sp. counts in concrete, open-trench floor drain 8, which was located near a liver and lung removal line at a mean temperature of 26.1°C and contained blood and meat debris. This drain was typically filled with liquid to 15 to 20% of capacity. , bottom side of cover; , floor within ca. 30 cm of the drain. (T), CE treatment applied.
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A significant reduction in Listeria sp. counts was also observed for drain 3 in the second week after CE treatment, and Listeria sp. was not detectable by a direct plating method at all sites. The mean Listeria sp. count at weeks 12 to 16 was 2.2 log10 CFU/100 cm2, which indicated that there was a 2.7-log10 CFU/100 cm2 reduction after the CE treatments (P < 0.05) (Table 1). However, the Listeria sp. counts in some locations of drain 3 were highly variable at later sampling times (Fig. 2).
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FIG. 2. Listeria sp. counts in concrete, open-trench floor drain 3, which was located in the middle of a high-traffic area and was typically filled to 20 to 40% of capacity during operation. , bottom side of cover; , floor within ca. 30 cm of the drain. (T), CE treatment applied.
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FIG. 3. Listeria sp. counts in fiberglass, open-trench floor drain 4, which was located near a poultry meat packing area and was typically filled to 5 to 20% of capacity during operation. , bottom side of cover; , floor within ca. 30 cm of the drain. (T), CE treatment applied.
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The mean Listeria sp. count for drain 6 at weeks 12 to 16 was 2.0 log10 CFU/100 cm2 after CE treatment, which indicated that there was a 1.6-log10 CFU/100 cm2 reduction after CE treatment (P < 0.05) (Table 1). Following CE treatment either the Listeria sp. counts at most locations in the drain were substantially reduced or Listeria sp. was undetectable, and this response continued for at least 18 weeks after the last treatment (Fig. 4).
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FIG. 4. Listeria sp. counts in fiberglass, open-trench floor drain 6, which was located near a poultry meat packing area and was typically filled to 5 to 20% of capacity during operation. , bottom side of cover; , floor within ca. 30 cm of the drain. (T), CE treatment applied.
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View this table: [in a new window] |
TABLE 2. Aerobic plate counts for drain samples collected before, during, and after CE treatment
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We used an enzyme-foam-based cleaner to apply the CE to the drains. The advantage of the foam cleaner was that it provided more exposure time (minimum, 15 min) for CE to be in contact with the drain surface. Data obtained from inoculation studies revealed that CE strains survived well in the foam cleaner and that there was no change in CE counts during 24 h of exposure (data not shown).
Our results revealed that application of the two CE strains in the floor drains did not substantially change the total countable bacterial population during or after the treatment compared with the APCs of samples collected before CE treatment. However in some locations (especially drains 3 and 4) the APCs were less during and after treatment than before treatment. CE may have colonized the drains and not only reduced Listeria sp. populations but also subsequently formed their own biofilms and controlled bacterial populations that were sensitive to the antagonistic metabolites of the CE (1, 2, 6, 19).
The mechanism by which the CE reduce Listeria sp. counts has not been elucidated; however, we have previously reported that both CE isolates produce antimicrobials that are active against L. monocytogenes (22). L. lactis subsp. lactis C-1-92 possesses genes for nisin expression. Nisin is approved as a food preservative in many countries and has antimicrobial activity against L. monocytogenes. Direct use of nisin in food products for control of Listeria may increase the likelihood of Listeria adaptation to nisin and subsequent tolerance to this bacteriocin. Although there is a possibility that listeriae in floor drains could develop tolerance to nisin following repeated exposure to L. lactis C-1-92, the likelihood is reduced by the inclusion of E. durans 152, which produces a different antimicrobial(s) than nisin (22).
The antimicrobial activity of lactic acid bacteria and their metabolites against L. monocytogenes has been well documented (3-5, 8, 10-13, 21). However, the application of these bacteria to floor drains in food processing facilities to control L. monocytogenes has not been reported previously. Our study revealed that application of two CE isolates can greatly reduce the numbers of Listeria sp. and L. monocytogenes cells in floor drains at 3 to 26°C in a facility in which fresh poultry is processed.
This study was supported in part by grants from the State of Georgia's Traditional Industries Program for Food Processing and the American Meat Institute Foundation.
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