Abstract
Background
Thermotolerant Campylobacter is among the more prevalent bacterial pathogens that cause foodborne diseases. This study aimed at evaluating the occurrence of thermotolerant Campylobacter contamination in chicken carcasses and processing plant stations (chilling water, scalding water, defeathering machinery, evisceration machine, and transport crates) in two of the Chilean main slaughterhouses. In addition, the isolation rates of thermotolerant Campylobacter during evisceration and following chiller processing were compared.
Results
The overall slaughterhouse contamination with thermotolerant Campylobacter was 54%. Differences were evident when the results from each plant were compared (plant A and plant B was 72% and 36%, respectively). The sampling points with the greatest contamination rates in both plants were after evisceration (90% and 54%, for plants A and B respectively). The decrease of thermotolerant Campylobacter contamination after chilling was significant (2 and 1.6 logs for plant A and B respectively P < 0.05).
Conclusion
Our findings indicate that chilling process has a limited effect in the final products Campylobacter contamination because poultry enter the slaughter processing with high counts of contamination. This may represent a health risk to consumers, if proper cooking practices are not employed. The levels and frequencies of Campylobacter found during the processing of Chilean poultry appear to be similar to those reported elsewhere in the world.
Background
Thermotolerant Campylobacter is a zoonotic bacteria and one of the main causes of gastroenteritis worldwide, including both developed and developing countries [1]. During 2006 Campylobacter jejuni was the second cause of sporadic gastroenteritis in the USA, with an incidence of 12.71 cases per 100.000 inhabitants [2]. It has also been reported that 80% of all Campylobacter related illnesses are transmitted through food and are responsible for no less than 5% of food-related deaths [3]. The two species commonly associated with enteric diseases are Campylobacter jejuni and Campylobacter coli, with C. jejuni being more frequent (80–90%) [1].
Campylobacter may be transferred to humans indirectly through the ingestion of contaminated water or food [4] and to a minor extent by direct contact with contaminated animals or animal carcasses. Despite the identification of numerous natural and artificial reservoirs for Campylobacter [5], most case-control studies seeking to identify the index source of infection, have identified poultry handling, processing, cooking, and/or preparation outside the home as significant contributing risk factors for disease [6,7]. C. jejuni infection typically results in an acute, self-limited gastrointestinal illness characterized by diarrhea, fever, and abdominal pain. The most significant post-infectious sequelae of C. jejuni infection is Guillain-Barre's syndrome (GBS). Occurrence data on Campylobacter positive chicken in Chilean processing plants is limited. The frequent presence of thermotolerant Campylobacter, and more specifically C. jejuni in broiler chickens, moved public health and international trade organizations to incorporate its control in the Hazard Analysis Critical Control Point (HACCP) system [8]. This strategy is aimed at identifying and controlling the presence of enteric pathogens in all stages of the food chain; particularly in the transport to and in the slaughterhouse processing [9,10]. FSIS recently proposed a new "risk-based inspection" approach supported by scientific risk assessment to provide the poultry industry with better options to control contamination in order to produce safe, unadulterated product [11]. To achieve these food safety objectives, more information of local origin about the epidemiology, physiology, and ecology of Campylobacter is urgently required.
This study was aimed to, a) identify thermotolerant Campylobacter contamination in broiler carcasses collected during poultry processing; b) identify thermotolerant Campylobacter contamination within poultry processing plants, c) compare the isolation rates of thermotolerant Campylobacter following the evisceration and chilling processes during commercial poultry preparation.
Our goals were to generate information to facilitate microbiological risk assessment studies necessary to reduce and control contamination by Campylobacter within the Chilean poultry industry and the development of interventional strategies in the approved HACCP plans.
Results
Of the 625 samples analyzed (whole chicken, processing plant environment and caecal samples), thermotolerant Campylobacter were cultured in 338 (54%). This includes both poultry processing plants (plants A and B). The overall occurrence of thermotolerant Campylobacter contamination was significantly higher (P < 0.05) in plant A (72%) than in plant B (36%).
Thermotolerant Campylobacter in chicken carcasses during processing
The data obtained from both plants are shown in Table 1. The whole chicken contamination rate with thermotolerant Campylobacter at plant A was 80%. This rate was significantly lower in the plant B (41%). The greatest contamination rate in both plants was after evisceration (90% and 54%, for plants A and B respectively) (Table 1).
Table 1.
Plant | Reception | After defeathering | After evisceration | After chilling | Total |
---|---|---|---|---|---|
A | 35/44 (80) | 46/62 (74)a | 61/68 (90)b | 46/62 (68)c | 188/236 (80) |
B | 22/48 (46)a | 15/62 (24)b | 37/68 (54)c | 23/61 (38) | 97/239 (41) |
n° of sample positive/n° examined (%).
Within each row, letters indicates statistically significantly different (P < 0.05, Test of proportion)
The overall contamination rate (plants A and B) with thermotolerant Campylobacter in the chicken carcasses following evisceration was 72%; this rate decreased significantly (P < 0.05) after the carcasses were chilled in the water tanks (56%). The detection of thermotolerant Campylobacter after evisceration was 90% in plant A. This rate decreased significantly after chilling (68%) (P < 0.05, Chi-square test). In contrast, there was no decrease in plant B.
In an attempt to ascertain the pre-processing baseline thermotolerant Campylobacter microbial status, the caecal content of 40 chickens were analyzed. This analysis identified Campylobacter jejuni in 85% (17/20) and 25% (5/20) in plants A and B, respectively.
Occurrence of thermotolerant Campylobacter contamination in processing plant environment samples
As shown in Table 2, the rates of thermotolerant Campylobacter present in chicken in each processing environment sample analyzed as a whole varied between 35% and 22% for plants A and B respectively. Otherwise, in both plants, the highest isolation rate of thermotolerant Campylobacter was found in the evisceration machine. This coincides with the greatest contamination rates observed after evisceration, as described earlier. Thermotolerant Campylobacter was isolated in only one sample of chilling water from a total of 22 samples analyzed (plant B).
Table 2.
Plant | Defeathering machine | Evisceration machine | Scalding water | Chilling water | Transport crates | Total |
---|---|---|---|---|---|---|
A | 4/11 (36) | 7/11 (64) | 2/11 (18) | 0/11 (0) | 6/11 (55) | 19/55 (35) |
B | 3/11 (27) | 4/11 (36) | 1/11 (9) | 1/11 (9) | 3/11 (27) | 12/55 (22) |
n° of sample positive/n° examined (%)
Enumeration of thermotolerant Campylobacter
To perform the bacterial counts only the positive samples were taken into account. The thermotolerant Campylobacter contamination found in carcasses collected after evisceration and after chilling is shown in Table 3. Overall, C. jejuni contamination, ranged from 3.3 log10 up to 7.7 log10 cfu/carcass. As expected, the plant that had carcasses with the highest numbers after evisceration also had carcasses with the highest numbers after chilling. The decreased of thermotolerant Campylobacter contamination following the chilling process was significant, 2 and 1.6 log10 for plants A and B respectively (P < 0.05, Kruskal-Wallis test). Despite this, samples collected after chilling with counts as high as 6.4 log10 cfu/carcass were observed in both plants.
Table 3.
Median (log cfu/carcass) | ||||
---|---|---|---|---|
Plant | n | After evisceration | n | After chilling |
A | 68 | 5.2 ± 1.1a | 62 | 3.3 ± 0.9b |
B | 68 | 6.1 ± 1.2a | 61 | 4.5 ± 0.9b |
Within each row, letters indicates statistically significantly different (P < 0,05 Kruskal-Wallis test)
Thermotolerant Campylobacter species and biotypes
Table 4 shows the biotypes of thermotolerant Campylobacter recovered from plants A and B for all the sampling points tested. C. jejuni was the species most frequently isolated (627/645, 97%), whereas C. coli accounted for 18/645 (3%) of the strains collected. C. jejuni biotyping tests showed that biotype II was by far most prevalent in both plants (573/645, 89%). The remaining strains belonged to biotypes IV (30/645, 5%), and I (24/645, 4%). Biotype C. jejuni II was most frequently isolated from carcasses, processing plant environment, and caecal contents during processing. Additionally, only a few strains were C. coli biotypes II (2%) and I (1%).
Table 4.
Plant A | Plant B | |||||||
---|---|---|---|---|---|---|---|---|
Strains | Chicken carcasses | Environment | Caecal contents | Total | Chicken carcasses | Environment | Caecal contents | Total |
C. coli biotype I | 6 | 1 | 1 | 8 | ||||
C. coli biotype II | 8 | 8 | 2 | 4 | ||||
C. jejuni biotype I | 14 | 14 | 9 | 1 | 10 | |||
C. jejuni biotype II | 305 | 26 | 25 | 356 | 187 | 22 | 8 | 217 |
C. jejuni biotype IV | 18 | 2 | 4 | 24 | 4 | 2 | 6 | |
Total | 410 | 235 |
Discussion
In this study, as showed in table 1 and 2 thermotolerant Campylobacter contamination is widespread in caecal contents, processing plant environment and the poultry carcasses that reach the retailers stores. In pioneering initial studies conducted in 1982, Figueroa et al. [12], found that the C. jejuni bacterial load in the cloacal contents of 51 chickens (21 processed and 26 live birds) was fairly high: 46 specimens (90%); 25 (96%) in live birds and 21 (84%) in processed birds. Recent studies (Figueroa A., unpublished results) revealed much lower prevalence rates (12%) in some processed birds analyzed with a similar methodology, suggesting that carcasses decontamination can be reached. Despite this C. jejuni is sought as the most frequent pathogen isolated from poultry meats in Chile [13].
Microbiological analysis during poultry processing in slaughterhouses confirmed previous reports by Stern et al. [14] and Arsenault et al. [15] who observed a positive correlation between the contamination of carcasses and the high positivity rates for Campylobacter of flocks at the farm level. The recovery rates of Campylobacter in plant B represent lower contamination rates in both cloacal swabs and caecal content samples at plant A. This disparity in the intestinal tract colonization in live birds may explain the differences in the positive rates found in poultry carcasses and the environment samples between both plants resulting in an increased cross contamination risk during slaughter and processing.
The proportion of carcasses contaminated with Campylobacter increase during evisceration steps. This findings was corroborated by the fact that the number of positive carcasses increased significantly (P < 0.05) after evisceration. Rosenquist et al. [16] observed that as an average the evisceration process led to a significant increase in the numbers of Campylobacter by 0.5 log10 CFU/g of neck skin. The increase in contaminated carcasses is a result of viscera rupture, inevitably leading to the contamination of equipment, working surfaces, process water, and air and increasing the opportunities for cross contamination of Campylobacter-free carcasses during processing [5]. As the machinery used cannot adapt to the natural variation in the size of the carcasses being processed, the rupture of the intestines and the leak of fecal material is not uncommon in the slaughter plants [16,17]. Based on the results presented here, we may conclude as previously reported, that evisceration is a critical step in carcass contamination [5,16,18].
The immersion chilling procedure has been identified as a critical control point (CCP) in a generic Hazard Analysis Critical Control Points (HACCP) study of poultry contamination by all pathogens [19]. In both plants, the chilling process with water containing 0.5 to 0.75 ppm of free chlorine was significantly (P < 0.05) associated with an important reduction in Campylobacter counts in broilers carcasses. Both, the washing process and the application of chlorinated water during carcass chilling must contribute to these results. Decreases in Campylobacter counts associated with chilling operations have also been reported previously, indicating that it is possible to achieve reductions of up to 2 log10 CFU of Campylobacter on carcasses during processing with chlorinated water [3,20-22]. The results presented here agree with these findings when comparing the median CFU counts per carcass before and after chiller treatment in both plants. Like in the data reported by Stern et al. [22], we found a significant reduction (P < 0.05) not only in the number of Campylobacter-positive carcasses but also in the bacterial counts per carcasses, underlining the benefits of an effective washing process of appropriate chlorine concentrations and low temperatures used on a continuous basis in the chiller tanks. The use of chlorinated water during carcass chilling reduced the populations of Campylobacter, but this practice, as confirmed in this study, has limited effect in the final magnitude of the Campylobacter contamination, because the poultry enter the slaughter processing with a high counts of contamination that the chilling stage is not capable of reducing.
The data presented here confirmed that in our setting a high percentage of commercial chickens are positive for Campylobacter at the time of slaughter. As a result, there is a high incidence of Campylobacter spp. in retail establishments, this constitute a serious hazard for public health [5,23]. In Chile, Figueroa et al. [24] reported a prevalence of 45% (50/90) of Campylobacter contamination in fresh poultry meats. Therefore, reducing the incidence and numbers of Campylobacter contamination during the processing of broilers is needed to achieve a safer final product.
Conclusion
This study has generated data on the high frequency rate of Campylobacter contamination in live broiler. This phenomenon derives in high contamination of carcasses and the processing equipment in two Chilean poultry slaughterhouses. According to the data obtained the high rates of cecal carriage at the time of slaughtering is a key factor in the occurrence of Campylobacter on both, chicken carcasses and the processing environments. Special attention should be given to the identification of critical control points of potential contamination at the grange level. Also in the processing, such as the plucking and evisceration steps in order to reduce cross contamination with fecal contents during subsequent processes. The data obtained have also shown that the chilling step is a critical control point to reduce carcass contamination but also to reduce the total counts per carcass. With regard to the international importance of the Chilean poultry industry, specially now when chicken exports have experimented strong growth, reaching highly demanding markets such as Mexico, the European Union, China and Japan, among others, information generated by this study may be used as a reference when setting food safety targets, in evaluating individual producers and food safety programs "from the farm to the fork", when HACCP program needs to be scientifically validated and applied more consistently at all stages of poultry production or when designing risk assessment actions. Emphasis should be given to the consumers to cook chicken thoroughly and handle this product carefully as a potential source of Campylobacter spp. in order to avoid illness and cross contamination to other food items.
Methods
Experimental design
The occurrence of thermotolerant Campylobacter contamination in poultry carcasses was evaluated in consecutive samplings in two processing plants (A and B). The samples were randomly collected between January 2006 and January 2007. Each chicken processing plant, located in Santiago Metropolitan Area, was visited on 11 occasions. Plants A and B had processing capacities of 120.000 and 70.000 birds per day, respectively. Both plants have some differences in the processes applied: plant A's chilling process utilizes a dual water tank system with NaClO added followed by air chilling. Plant B's chilling process relies on carcass cooling through water chilling exclusively with NaClO also added. The second difference noted was the timing of the chicken carcasses marinade (salt injection). Plant A marinated the carcasses prior to the chilling process, while plant B marinated them after the chilling process.
Sample collection
At each sampling, thermotolerant Campylobacter contamination was evaluated in four steps during poultry processing: reception (n = 92), after defeathering (n = 124), after evisceration (n = 136) and after chilling (n = 123). Broilers were 42 days old at slaughter and their live weight was 2.5 and 3.5 kg. When carcasses were received, samples were obtained by means of cloacal swabs which were immersed in sterile tubes with 1 ml of 0.1% peptone water. For the remaining 3 stages of bird processing (after defeathering, evisceration and chilling), carcasses were removed from the line at random using a clean pair of latex gloves for each specimen and immediately placed in a sterile plastic bag. On every occasion, broiler carcasses were taken from the same production lot (i.e. birds from the same origin, transported in the same truck and processed in the same conditions). Furthermore, from each plant 20 caecal samples were collected from the evisceration line in sterile plastic bags. To evaluate the possible environment contamination at the processing plant, we analyzed 110 samples directly collected by immersing 500 ml sterile bottles in the scald and in the chill tanks (n = 22 samples), respectively. We also analyzed swab samples from obvious fecal contaminations of the transport crates (n = 22), evisceration machines (n = 22) and defeathering machines (n = 22). In each case, samples were obtained prior to site washing by the plant personnel. All swab samples were placed in sterile tubes containing 1 ml of 0.1% peptone water before inoculation to an appropriate selective culture media.
Following collection, samples were transported at 4°C in refrigerated boxes within 1 h to the Microbiology and Probiotics Laboratory, INTA, University of Chile. The isolation and identification of thermotolerant Campylobacter was performed through a validated FSIS method [25]. Bacterial analysis was initiated upon arrival in the laboratory.
To assess the presence of active chlorine in the cooling tanks, free chlorine concentrations were determined "in situ" with a chlorimeter.
Isolation and identification of thermotolerant Campylobacter
Whole chicken carcass
To each raw whole chicken carcass 200 ml of 0.1% peptone water were added on arrival laboratory. Carcass rinses were performed by hand shaking for 60 seconds in each of two directions to ensure that the water came into contact with all surfaces. Then, 10 ml of the total volume were centrifuged at 5000 rpm for 5 minutes, and two loops of the centrifugate was streaked on modified Charcoal Cefoperazone Deoxycholate Agar (mCCDA) containing cefoperazone, amphotericin B and rifampicin. The plates were incubated at 42°C for 48 h in gas jars with a microaerobic atmosphere. As an additional enrichment step, 10 ml of each rinse fluid were transferred to 90 ml of Hunt Enrichment Broth (HEB) an incubated at 37°C for 48 h in gas jars with a microaerobic atmosphere (5% O2, 10% CO2 and 85% N2). After incubation, all plates were inspected for suspicious colonies, which were Gram-stained and cell compatible with Campylobacter were sub-cultured onto Skirrow agar and incubated for 48 h–5 days at 42°C under microaerobic conditions. All colony types were further identified as C. jejuni, C. coli, or C. lari using the extended biotyping scheme of Lior [26].
Caecal Contents
Thermotolerant Campylobacter contamination was evaluated by analyzing approximately 3 cm of the caecal mucosae. The tissue was maintained in a sterile container, inoculated aseptically onto mCCDA plates and incubated under microaerobic conditions at 42°C for 48 h.
Processing Plant Environment samples
Swab samples of the transport crates and the defeathering and evisceration machines were examined for Campylobacter by direct plating onto mCCDA agar. The plates were then incubated as described above. As for the tank water samples, 10 ml from the scalding and chilling water tanks were transferred to 90 ml HEB enrichment broth and incubated at 37°C for 48 h in gas jars with a microaerobic atmosphere. After enrichment, three loops of the enrichment broth were streaked onto mCCDA and incubated as previously described.
Enumeration of thermotolerant Campylobacter
Contamination rates with thermotolerant Campylobacter after evisceration and chilling were quantified as described by Stern and Pretanik [27]. Briefly, 0.1-ml aliquots of each dilution of the rinse water was plated directly onto duplicate mCCDA agar plates and incubated at 42°C for 48 h under microaerobic atmosphere. All colony types were further confirmed as previously described. Since 0.1 ml of rinse suspension from the total rinse volume of 200 ml was plated, the sensitivity of the method to detect the organism represented an estimated 2,000 CFU per carcass. Counts of CFU at each dilution were averaged, and estimations of Campylobacter concentrations per carcass were calculated.
Statistical analysis
Analysis of differences in the Campylobacter culture counts in the different steps during poultry processing was performed using a test of proportion. Campylobacter mean counts per carcass following the evisceration and the chilling steps were compared applying the Kruskal-Wallis test. P < 0.05 was considered statistically significant.
Authors' contributions
GOF conceived the study, participated in its design and approved the final manuscript.
MRT participated in its design, microbiological assays, performed statistical analysis and reviewed the paper. CEL carried out the sample collection, microbiological assays, assisted with the development of methods and wrote first drafts of the manuscript. PCR assisted with the development of methods, microbiological assays and reviewed the paper. MAT performed microbiological assays and statistical analysis.
Contributor Information
Guillermo Figueroa, Email: gfiguero@uchile.cl.
Miriam Troncoso, Email: mtronco@inta.cl.
Cristián López, Email: clopez@inta.cl.
Patricia Rivas, Email: patriciacrivas@gmail.com.
Magaly Toro, Email: mtoro@inta.cl.
Acknowledgements
The authors gratefully acknowledge Loki Skylizard and Oscar Brunser for critical reading of the manuscript and comments. Further, we thank the financial assistance of FONDECYT 1061150 Grant, and the cooperation provided by the management and employees of plants A and B.
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