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Applied and Environmental Microbiology, December 2002, p. 6220-6236, Vol. 68, No. 12
0099-2240/02/$04.00+0 DOI: 10.1128/AEM.68.12.6220-6236.2002
Copyright © 2002, American Society for Microbiology. All Rights Reserved.
Poultry Microbiological Safety Research Unit,1 Antimicrobial Resistance Research Unit, USDA Agricultural Research Service, Athens, Georgia2
Received 22 March 2002/ Accepted 23 August 2002
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Handling and consumption of poultry or poultry-related products are considered to be a primary source for Campylobacter-induced disease in humans (5, 18, 24). Campylobacter has been cultured from as many as 75% of the live broiler population and from as much as 80% of processed poultry meat samples sold commercially (13, 14, 19, 27). The high colonization prevalence of poultry and the resultant clinical infections in humans have prompted a number of investigations focused upon identifying and subsequently eliminating sources of Campylobacter contamination in chickens. However, the pathways involved in Campylobacter contamination of poultry flocks remain unclear. Several suspected sources or vectors of contamination have been studied and include transmission from parent to progeny through the egg, exposure of birds to contaminated water, a previously contaminated rearing environment, hatchery pads, litter, feed, personnel, small animals on the farm, flies, and rodents (10, 11, 16, 17, 20, 25, 26, 29).
In an effort to further elucidate the means by which poultry flocks are contaminated with Campylobacter, 16 flocks from four different farms, representing two broiler producers in the United States, were studied. Samples from both poultry production and poultry processing environments were collected and cultured for the presence of Campylobacter. All Campylobacter isolates obtained were genotyped by using flaA short variable region (SVR) DNA sequence analysis to determine the relationships between the isolates (22). The identification of critical sources of Campylobacter contamination in poultry will allow for the development of intervention strategies that aggressively target specific locations. These interventions will facilitate the delivery of pathogen-free birds to the abattoir and consequently should reduce the incidence of human exposure.
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Sample collection.
Samples were collected in both the production environment and the processing environment for each of the flocks. Production samples were taken prior to flock placement, at delivery (delivery tray liners), and at 2-week intervals until slaughter (at 6 or 8 weeks of age). Production samples taken inside of the rearing facility at each sampling period included samples from broiler feces (n = 25), water lines (n = 6), water cups (n = 6), litter (n = 6), feed from the feed hopper (n = 2), feed from the feeder (n = 2), drag swabs (n = 3), wall swabs (n = 2), fan swabs (n = 2), mouse intestines (collected as trapped), insects (collected as observed), fly strips (n = 2), and cecal droppings (n = 5). Production-associated samples taken from the exterior of the rearing facility included samples from wild bird feces (collected as observed), animal feces (collected as observed), dirt (n = 1), standing water (n = 1), and boot swabs (n = 3).
Samples collected in the processing environment included samples from carcass rinses (n = 25), prechill water (n = 5), postchill water (n = 5), prescald water (n = 5), postscald water (n = 5), pretransport crate swabs (n = 10), and post-transport crate swabs (n = 10). In general, samples were collected into sterile plastic bags and placed in insulated boxes containing ice packs for overnight transport to the laboratory.
Bacterial isolates.
Fecal samples were weighed and diluted 1:3 (wt/vol) with Difco buffered peptone water (Becton Dickinson, Sparks, Md.). Serial dilutions were prepared and plated onto Campy-Cefex agar which was incubated at 42°C for 36 to 48 h in a microaerobic atmosphere (5% O2, 10% CO2, 85% N2) (30). Following incubation, a representative number of presumptive Campylobacter colonies were confirmed by observation of the typical cellular morphology by using phase-contrast microscopy and with a commercial latex agglutination kit (Integrated Diagnostics, Inc., Baltimore, Md.).
Carcass rinse samples were taken as previously described (9). Briefly, carcasses were sampled as they exited the final chill tank. Each carcass was placed into a clean bag with 100 ml of sterile tap water and vigorously shaken for 1 min. A 0.1-ml aliquot was plated onto duplicate Campy-Cefex agar and incubated as described for fecal samples. In addition, a 10-ml aliquot was used to inoculate 90 ml of Campylobacter enrichment broth (Acumedia Manufacturers, Inc., Baltimore, Md.) plus Campylobacter-selective supplement (Bolton's; Medox Diagnostics, Ogdensburg, N.Y.) which was enriched at 37°C for 4 h followed by a 40-h incubation at 42°C. Following a total of 44 h of incubation, the enriched samples were plated onto Campy-Cefex agar plates and incubated as previously described (32). Confirmation procedures for carcass rinse isolates were identical to those used for fecal isolates. All other samples were placed in Campylobacter enrichment broth plus Campylobacter-selective supplement and incubated as previously described (32).
Molecular subtype analysis.
One Campylobacter isolate originating from each positive sample type during each sampling period was chosen for subtype analysis. Isolated colonies of Campylobacter were resuspended in 300 µl of sterile H2O and placed at 100°C for 10 min. Ten microliters of each boiled cell suspension was used as the template for flaA SVR PCR with the primers FLA242FU (5'-CTA TGG ATG AGC AAT TWA AAA T-3') and FLA625RU (5'-CAA GWC CTG TTC CWA CTG AAG-3') (22). A 35-cycle reaction was used with 1 min of denaturing at 96°C, 1 min of annealing at 52°C, and a 1-min extension at 72°C. The resulting product was approximately 425 bp. Sequence data was generated by using either the FLA242FU primer or the FLA625RU primer with the Big Dye dye terminator cycle sequencing kit (Applied BioSystems Inc.-Perkin Elmer, Foster City, Calif.). Data were assembled with Sequencher version 4.1 (GeneCodes Corp., Ann Arbor, Mich.) and aligned by using ClustalX (34). The aligned sequences were compared, and dendrograms were generated by using the UPGMA algorithm with HKY85 distance measurements in version 4.0 of the Phylogenetic Analysis Using Parsimony (PAUP*) program (D. L. Swofford, Sinauer Associates, Sunderland, Mass., 1988).
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TABLE 1. Positive Campylobacter isolates from the producer A high-performance (AH) site
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TABLE 5. Percentage of Campylobacter-positive samples by sample type
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FIG. 1. Relationships derived from comparison of the SVR DNA sequences of the flaA genes from Campylobacter organisms isolated from the Arkansas low-performance farm in the fall. The dendrogram was generated as described in Materials and Methods, and the isolates are labeled as described in Results. The dates of isolation and the sources of the isolates are also provided.
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FIG. 2. Relationships derived from comparison of the SVR DNA sequences of the flaA genes from Campylobacter organisms isolated from the California high-performance farm in the winter. The dendrogram was generated as described in Materials and Methods, and the isolates are labeled as described in Results. The dates of isolation and the sources of the isolates are also provided. Asterisks denote isolates that were obtained prior to flock shedding.
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FIG. 3. Relationships derived from comparison of the SVR DNA sequences of the flaA genes from Campylobacter organisms isolated from the Arkansas high-performance farm in the spring. The dendrogram was generated as described in Materials and Methods, and the isolates are labeled as described in Results. The dates of isolation and the sources of the isolates are also provided.
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FIG. 4. Relationships derived from comparison of the SVR DNA sequences of the flaA genes from Campylobacter organisms isolated from the Arkansas low-performance farm in the spring. The dendrogram was generated as described in Materials and Methods, and the isolates are labeled as described in Results. The dates of isolation and the sources of the isolates are also provided.
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Four environmental samples associated with the CH-Winter sampling were Campylobacter positive. Of these samples, three were obtained prior to flock placement (one mouse sample, CH58, and two samples from wild bird feces, CH61 and CH62). The remaining environmental isolate (a sample from standing water, CH70) was positive 2 weeks later; however, flock shedding had not yet begun. Subtype analyses demonstrated that the three isolates obtained prior to flock placement were distinct from broiler-associated isolates (2.7 to 6.6% variability). The isolate from standing water, however, was identical to a fecal isolate.
In the seven remaining flocks where environmental samples were positive, three flocks were from the high-performance site of producer C (CH-Spring, CH-Summer, and CH-Fall) (Fig. 5, 6, and 7), three were from the producer A high-performance site (AH-Summer, AH-Fall, and AH-Winter) (Fig. 8, 9, and 10), and one was from the producer A low-performance site (AL-Winter) (Fig. 11). A total of four distinct Campylobacter clones were observed from the broiler-associated samples from the AL-Winter investigation (Fig. 11). One of the subtypes, comprising isolates AL01B, AL23B, and AL24B, was present only during week 6 of sampling; all other subtypes were present at both week 4 and week 6 of sampling. Eight Campylobacter-positive environmental samples were isolated from this flock; five were isolated in week 4, when flock shedding began (two are litter isolates, AL38 01/11/99 and AL40 01/11/99, and three are drag swab isolates, AL48 01/11/99, AL49A 01/11/99, and AL49B 01/11/99), while three were isolated in week 6 (two are drag swab isolates, AL49B 01/25/99 and AL50B 01/25/99, and one is an insect isolate, AL66 01/25/99). All eight of the environmental Campylobacter isolates matched broiler-associated isolates. Additionally, all environmental isolates were comprised of the four distinct subtypes associated with the broilers.
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FIG. 5. Relationships derived from comparison of the SVR DNA sequences of the flaA genes from Campylobacter organisms isolated from the California high-performance farm in the spring. The dendrogram was generated as described in Materials and Methods, and the isolates are labeled as described in Results. The dates of isolation and the sources of the isolates are also provided.
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FIG. 6. Relationships derived from comparison of the SVR DNA sequences of the flaA genes from Campylobacter organisms isolated from the California high-performance farm in the summer. The dendrogram was generated as described in Materials and Methods, and the isolates are labeled as described in Results. The dates of isolation and the sources of the isolates are also provided.
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FIG. 7. Relationships derived from comparison of the SVR DNA sequences of the flaA genes from Campylobacter organisms isolated from the California high-performance farm in the fall. The dendrogram was generated as described in Materials and Methods, and the isolates are labeled as described in Results. The dates of isolation and the sources of the isolates are also provided.
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FIG. 8. Relationships derived from comparison of the SVR DNA sequences of the flaA genes from Campylobacter organisms isolated from the Arkansas high-performance farm in the summer. The dendrogram was generated as described in Materials and Methods, and the isolates are labeled as described in Results. The dates of isolation and the sources of the isolates are also provided.
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FIG. 11. Relationships derived from comparison of the SVR DNA sequences of the flaA genes from Campylobacter organisms isolated from the Arkansas low-performance farm in the winter. The dendrogram was generated as described in Materials and Methods, and the isolates are labeled as described in Results. The dates of isolation and the sources of the isolates are also provided.
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FIG. 10. Relationships derived from comparison of the SVR DNA sequences of the flaA genes from Campylobacter organisms isolated from the Arkansas high-performance farm in the winter. The dendrogram was generated as described in Materials and Methods, and the isolates are labeled as described in Results. The dates of isolation and the sources of the isolates are also provided.
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FIG. 9. Relationships derived from comparison of the SVR DNA sequences of the flaA genes from Campylobacter organisms isolated from the Arkansas high-performance farm in the fall. The dendrogram was generated as described in Materials and Methods, and the isolates are labeled as described in Results. The dates of isolation and the sources of the isolates are also provided.
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FIG. 12. Relationships derived from comparison of the SVR DNA sequences of the flaA genes from Campylobacter organisms isolated from the Arkansas low-performance farm in the summer. The dendrogram was generated as described in Materials and Methods, and the isolates are labeled as described in Results. The dates of isolation and the sources of the isolates are also provided.
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Analysis of the remaining processing samples (from prescald water, postscald water, prechill water, and postchill water) revealed that a greater number of Campylobacter-positive samples were obtained from producer A than from producer C. Additionally, more Campylobacter isolates were collected from pre- and postscald water (14 isolates) than from pre- and postchill water (2 isolates). Molecular subtype analysis demonstrated that the prescald water isolates were comprised of both unique subtypes and subtypes that matched fecal isolates and carcass rinse isolates from the respective flocks. The postscald water isolates possessed flaA SVR DNA sequence subtypes that matched those of the respective production-associated isolates. The two prechill water isolates (CHP28 and CHP30) from CH-Fall had subtypes that matched carcass rinse isolates and pretransport crate isolates.
Molecular subtype analyses of Campylobacter isolates between flocks.
As stated previously, molecular subtype analysis of all Campylobacter isolates obtained from the producer C low-performance farm, regardless of season, had identical flaA SVR DNA sequences and were therefore considered to be clonal. Further analysis demonstrated that this subtype was also present in all flocks sampled from the high-performance farm of producer C; however, additional subtypes were also present. Analysis of all Campylobacter isolates obtained from the producer C high-performance farm during all seasons revealed that several of the same subtypes were present in different flocks. A similar observation, namely, that particular subtypes persist throughout the year on different farms, was made for producer A. Subtype analysis of all Campylobacter isolates obtained in this study from both producer A and producer C revealed that closely related subtypes were present within the operations of the two individual producers over all of the seasons investigated.
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Our findings also demonstrate that closely related clones are present throughout the poultry industry, regardless of the producer and location. It is not believed that this observation is a result of a media preference, because direct plating, rather than enrichment, was used for the recovery of Campylobacter from broiler fecal samples. However, it should be noted that all culture methodologies possess an inherent bias in that only a finite number of colonies can be picked and subsequently typed. Consequently, this limitation allows for only the most predominant clones to be detected. A second explanation is that some subtypes of Campylobacter may be better adapted for survival in different niches than are others. It may well be that the environmental stresses associated with having a chicken as a niche have led to the preferential survival of specific Campylobacter clones. A third, but related, explanation may be the transmission of Campylobacter from breeder hens to the broiler offspring (7-9, 12, 15, 20). A limited number of Campylobacter clones may be present within the population of breeder grandparents as well as the subsequent breeder hens and roosters. These clones may be passed on to the broiler offspring, where they proliferate and become the predominant clones. Should either of the two scenarios occur, new intervention strategies directed against the predominant clones or focused on the breeder hens and roosters will need to be developed.
Production-associated environmental samples were positive in 12 of the 16 flocks sampled. In 10 of these 12 flocks, environmental samples turned positive during the same week in which flock shedding began. In general, environmental isolates obtained from within the rearing facility (samples from drag swabs, litter, water line swabs, and fan swabs) possessed subtypes identical to those of the fecal and cecal isolates from the respective flocks. Considering that most of these samples were negative for Campylobacter prior to flock shedding, it is likely that shedding of Campylobacter from the broilers led to the contamination of the rearing-facility samples rather than the reverse. Analyses of external environmental isolates demonstrated varied results. In four of the five flocks where samples from the external environment of the rearing facility turned positive with flock shedding, environmental isolates had flaA SVR DNA sequences identical to those of the fecal and cecal isolates of the broilers. The exception, AL-Spring, revealed that some environmental isolates possessed genotypes identical to those of isolates originating from the flock, while other environmental isolates possessed genotypes that were distantly related to isolates obtained from the flock. Considering the free access that some vectors (mice, insects, and wild birds) have inside and outside of the rearing facility, coupled with the fact that positive isolates were obtained concurrently from all samples, it is difficult to determine which vector, poultry or environment, served as the source of the observed Campylobacter contamination.
Analysis of Campylobacter isolates from the two investigations where positive samples were obtained prior to flock shedding, namely, the AL-Fall and CH-Winter investigations, demonstrated that particular Campylobacter subtypes from these previously isolated environmental samples were identical to some of the Campylobacter subtypes observed within the flocks once shedding began. An isolate originating from a wild bird, AL61, had a flaA SVR DNA sequence identical to that of a subset of isolates collected from the broiler-associated samples. Additional subtypes were also present within this flock. A standing-water isolate, CH70, obtained from the CH-Winter investigation, had a subtype identical to that of a subsequently isolated broiler isolate. It should be noted that the number of Campylobacter-positive isolates obtained from this particular investigation was quite low. The above observations suggest that the environment can be a contributing factor to Campylobacter contamination of broiler flocks. Certain husbandry practices, such as opening the rearing facility to the outside environment for cooling, may lead to this contamination. Conversely, practices such as the reuse of litter and limited disinfection of the rearing facility between flocks appeared to have little effect on contamination of flocks. The presence of additional subtypes within broiler flocks, coupled with the previous observation that environmental samples are rarely positive prior to flock shedding, indicates, however, that the environment may not be the sole source for Campylobacter contamination of broiler flocks. Alternatively, Campylobacter organisms that were sublethally injured from environmental exposure may not have been adequately recovered in this investigation. Improved methods of culture and molecular detection would greatly facilitate epidemiologic investigations.
Analysis of Campylobacter isolates recovered from the processing environment revealed that contamination of the final product (carcass) originated primarily from the intestinal contents of the broiler flock. This may have occurred during processing or, more likely, transpired during transport of the birds (31). However, additional sources within the processing environment, such as pretransport crates and residual Campylobacter from previously processed flocks, also contributed to contamination of the final product. These observations suggest that more robust cleaning of crates and of the processing facilities may result in a further decline of Campylobacter contamination of the final market product. Improved detection methods and additional epidemiologic investigations are needed to further elucidate the means by which broiler flocks become contaminated with Campylobacter.
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TABLE 2. Positive Campylobacter isolates from the producer A low-performance (AL) site
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TABLE 3. Positive Campylobacter isolates from the producer C high-performance (CH) site
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TABLE 4. Positive Campylobacter isolates from the producer C low-performance (CL) site
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We also acknowledge the participating companies and the technical support of Aphrodite Douris, Susan Brooks, Latoya Wiggins, and Debbie Posey.
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