Next Article in Journal
Harnessing the Potential of Walnut Leaves from Nerpio: Unveiling Extraction Techniques and Bioactivity Through Caenorhabditis elegans Studies
Previous Article in Journal
Metabolomic Analysis of Different Parts of Black Wax Gourd (Cucurbita pepo)
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

Explore the Contamination of Antibiotic Resistance Genes (ARGs) and Antibiotic-Resistant Bacteria (ARB) of the Processing Lines at Typical Broiler Slaughterhouse in China

1
Key Laboratory of Industrial Fermentation Microbiology of the Ministry of Education and Tianjin Key Laboratory of Industrial Microbiology, College of Biotechnology, Tianjin University of Science and Technology, Tianjin 300457, China
2
China Animal Disease Control Center, Slaughtering Technology Center, Ministry of Agriculture and Rural Affairs, Beijing 102600, China
*
Authors to whom correspondence should be addressed.
These authors contributed equally to this study.
Foods 2025, 14(6), 1047; https://doi.org/10.3390/foods14061047
Submission received: 19 February 2025 / Revised: 11 March 2025 / Accepted: 14 March 2025 / Published: 19 March 2025
(This article belongs to the Section Food Engineering and Technology)

Abstract

:
Farms are a major source of antibiotic resistance genes (ARGs) and antibiotic-resistant bacteria (ARB), and previous research mainly focuses on polluted soils and breeding environments. However, slaughtering is an important link in the transmission of ARGs and ARB from farmland to dining table. In this study, we aim to reveal the pollution of ARGs and ARB in the slaughter process of broilers. First, by qualitative and quantitative analysis of ARGs in samples collected from the broiler slaughtering and processing production chain, the contamination level of ARGs was reflected; secondly, potential hosts for ARGs and microbial community were analyzed to reflect the possible transmission rules; thirdly, through the antibiotic susceptibility spectrum analysis of four typical food-borne pathogens, the distribution of ARB was revealed. The results showed that 24 types of ARGs were detected positive on the broiler slaughter production line, and tetracycline-resistance genes (20.45%) were the most frequently detected. The types of ARGs vary with sampling process, and all sampling links contain high levels of sul2 and intI1. The most abundant ARGs were detected in chicken surface in the scalding stage and entrails surface in the evisceration stage. There was a significant correlation between intI1 and tetM, suggesting that tetM might be able to enter the human food chain through class-1 integrons. The host range of the oqxB gene is the most extensive, including Sphingobacterium, Bacteroidia unclassified, Rothia, Microbacterium, Algoriella, etc. In the relevant links of the slaughter production line, the microbial community structure is similar. Removing viscera may cause diffusion of ARGs carried by intestinal microorganisms and contaminate chicken and following processing production. The four food-borne pathogens we tested are widely present in all aspects of the slaughter process, and most of them have multi-drug resistance and even have a high degree of resistance to some veterinary drugs banned by the Ministry of Agriculture. Our study preliminarily revealed the pollution of ARGs and ARB in the slaughter process of broilers, and these results are helpful to carry out food safety risk assessment and formulate corresponding control measures.

1. Introduction

Antimicrobial resistance (AMR) has become a major public health crisis in recent years. It is estimated that deaths caused by AMR could climb from 700,000 annually in 2014 to 10 million by 2050 [1]. The use, misuse and abuse of antibiotics in veterinary, agriculture and clinical therapy for decades have increased the prevalence of antibiotics resistance genes (ARGs), especially the acquired resistance elements by horizontal gene transfer into the human and animal microbiomes [2]. ARGs can spread among the same or different species of bacteria through various molecular mechanisms, such as integrons, plasmids, transposons, etc., resulting in the emergence and rapid spread of antibiotic resistant bacteria (ARB) [3]. The long-term use of low-dose antimicrobials as growth promoters in animal production is still a common practice in many countries, which increases the economic benefits but also hides a great risk that the continuous use of antimicrobials promotes and exacerbates the emergence of drug-resistant bacteria [4,5]. Evaluating the impact of antimicrobial use in animal production on bacterial resistance in animals, humans and the environment remains a great challenge due to the interdependence and close interrelationship between humans, animals, and the environment [6,7]. Antibiotic abuse, misuse, or inappropriate prescribing can lead to the spread of AMR infections caused by pathogens that are first susceptible to antibiotics, after which the bacteria are able to acquire ARGs and act through a variety of mechanisms [8]. Bacteria with ARGs on transferable genetic elements have been identified in many microbial communities, including those associated with humans and countless communities associated with animals [9]. Unconventional use of antibiotics on food animal farms can accelerate the development and spread of bacterial resistance in ARB and ARGs, posing an increasing threat to human and animal health [10,11,12]. Farmed animals are an important source of antibiotic-resistant bacteria, and consumption of animal products has been associated with an increased risk of certain antibiotic-resistant infections [13,14,15].
Despite the increasing concerns over inappropriate use of antibiotics in veterinary medicine and food production, slaughterhouse and meat products remain potential reservoirs of ARGs and ARBs [16]. The prolonged and intensive use of antibiotics in food animal husbandry may lead to the accumulation of antibiotics in animal guts and the receiving environment, as well as sustained selective pressure on ARGs and ARBs [17,18]. ARGs in farm environments are widely distributed in soil, water, manure, and animal feces, primarily driven by factors such as antibiotic use, animal density, and waste management practices. The ARGs originating from farms can subsequently enter the food chain, particularly during animal transportation and processing in slaughterhouses. In slaughterhouse environments, ARGs are frequently detected in wastewater, surfaces, and animal carcasses, where their prevalence is often amplified due to the high concentration of microorganisms and the intensive processing activities. At the same time, factors such as contaminant exposure and horizontal genetic transfer (HGT) increase the risk of transmission of ARGs and ARBs from animal farms to the natural environment and humans [19]. This makes slaughterhouses a critical point for ARG dissemination and a key focus for research, as they represent a bridge between farm environments and human exposure through food products. Consequently, ARGs and ARB can spread to humans throughout the food-supply chain by exposure via contaminated animals, meat products, or natural environment (i.e., air, water, and soil) [20,21,22]. Unconventional use of antibiotics on food animal farms can accelerate the development and spread of bacterial resistance in ARB and ARGs, posing an increasing threat to human and animal health [23].
With the increase in global consumption of poultry meat, bacterial pathogens act as important factors affecting the safety of poultry and raw meat [24]. In recent years, the production and sales of chicken have shown rapid and steady growth in the world. According to the United States Department of Agriculture, world chicken production has maintained steady growth, increasing from 92.47 million tons in 2018 to 102.389 million tons in 2023 [25]. China is the world’s third largest producer of broiler chickens, with production reaching 14.30 million tons in 2023 [26]. Chicken meat products are rich in nutrients, as well as cross-contamination generated during processing in slaughterhouses; fresh chicken meat is susceptible to contamination by food-borne microorganisms and cross-contamination between carcasses, environmental hygiene, utensils, and staff operations during slaughter and processing increases the level of microbial contamination on the surface of carcasses, which directly affects the safety and hygiene of chicken meat [27,28,29]. Therefore, broiler slaughtering is one of the important links in the prevention and control of ARGs and ARB diffusion.
Most of the previous studies focused on the surrounding environment of the broiler slaughterhouse [30]. Actually, the slaughtering process could play crucial roles in the transmission of ARGs and ARB to humans via environmental interfaces and meat products. Bleeding, evisceration, and other related processes can contaminate broiler carcasses and equipment, leading to the spread of gut bacteria [31]. The gut microbiome often becomes particularly problematic since they represent a complex ecosystem and a epicenter of horizontally transferrable resistance traits between commensals and pathogens, and they cross-transmit resistant strains between animals and humans. Antibiotic resistance can be transmitted through vertical gene transfer (VGT) and HGT [32,33], and animal feces is an important reservoir and source of ARGs in the environment, creating favorable conditions for HGT events. HGT can be achieved by conjugation, transduction, and transformation [34]. In addition, these resistant bacteria continue to exist in the environment even after antibiotic selective pressure has been eliminated, resulting in persistent contamination effects [35]. Therefore, it is crucial to prioritize the exploration of the risk of antibiotic resistance distribution during slaughter.
Many studies have focused on MDR foodborne pathogens and commensal bacteria, mainly occurring in food and the food chain [31,36]. These results indicate that respective intervention measures along the slaughter processing line should aim at reducing the microbiological load on broiler carcasses as well as preventing cross-contamination. However, the data are insufficient on ARGs and ARB contamination in various stages of the processing lines of broiler slaughterhouse. In this study, we aimed to investigate the pollution of ARGs and ARBs in each key stages of the typical broiler slaughter production chain in order to achieve guidance on risk assessment in broiler slaughtering and processing in the future.

2. Materials and Methods

2.1. Sample Collection

The samples of different stages of the broiler production processing were collected from a typical broilers slaughterhouse in Liaoning Dandong, China (Longitude 124°23′ E, Latitude 40°07′ N), which receives animals from multiple suppliers and all over the country. A total of 205 samples were collected. Ten representative links in the broiler slaughtering and processing chain were selected for sample collection, and the whole broiler slaughtering and processing chain was divided into the hanging link, electric anesthesia stabbing link, blood draining link, scalded link, pre-cooling link, dehairing and finishing link, offal removal link, splitting link, and packaging link. The selected representative links are scalded, cleaned, gutted, and split. A schematic diagram of the broiler-slaughtering and -processing production chain is shown in Figure 1. To ensure reproducibility and minimize contamination during sample collection and processing, strict quality control measures were implemented. Samples were collected under aseptic conditions in accordance with national standards (GB 4789.1-2016, GB/T 19480, and NY/T 541-2016). Sam pling personnel were trained in sterile techniques and wore protective equipment (e.g., gloves, masks, and sterile clothing) to prevent contamination.
With reference to GB/T 4789.17-2003’s non-destructive sampling methods, according to the special sampling conditions in the slaughtering production chain using 3M’s special sampling applicator stick, the head of the stick is aseptic sponges, and the head of the sponge is placed in 10 mL sterilized buffered peptone water (BPW) to seal [37]. In accordance with the stipulations of SN/T 4092-2015, “Carcass Sampling Methods for Microbiological Testing”, the sponge swab affixed to the sealed applicator stick was initially saturated with sterilized BPW. Subsequently, the designated specification plate was firmly pressed against the surface of the selected carcass. The sponge swab was then meticulously rubbed across the entire area delineated by the specification plate (measuring 10 cm by 10 cm), ensuring comprehensive coverage. This was achieved by maneuvering the swab in a horizontal motion, followed by flipping the sterilized sponge swab to guarantee that each facet of the swab made complete contact with the sampled carcass surface. Each side of the swab can fully contact the sampling surface, and the time of application of the wipe is controlled for a uniform time. The collection of clean cooling-water samples is conducted in the same way in the water and on the drainage surface; it is performed a certain period of time after the completion of the wipe sampling and is immediately placed in the preservation solution of the sterilized BPW stick, which is stored for preservation in a tube, which was screwed tightly and marked well. The collected samples were transported back to the laboratory at 4 °C.
The sampled swabs were fully shaken in the BPW preservation solution for about 5 min, and all the preservation solution after shaking was transferred to a sterilized 50 mL centrifuge tube and then centrifuged at a low speed of 1000 r/min for 15 min; then, the supernatant was poured off, and the precipitate was taken to extract the total genomic DNA of the samples.
The schematic diagram of the distribution of the ten sampling points and the number of samples collected at each point are illustrated in Figure 2 and Table 1.

2.2. DNA Extraction of Samples

Genomic DNA was extracted with TIANamp Micro DNA Kit (TianGen, Beijing, China) according to the manufacturer’s instruction. The concentrations and qualities of DNA extracted were determined with a NanoDrop ND-2000 (Thermo Scientific, Waltham, MA, USA). The DNA samples were stored at −20 °C until further analysis.

2.3. Qualitative and Quantitative PCR of ARGs and intI 1

Forty-three ARGs and a class I integron gene (intI 1) were tested via a PCR assay. The primers used are listed in Table 2. Furthermore, 11 ARGs (tetM, tetX, tetT, tetQ, sul2, mefA, blaTEM, floR, oqxB, aadA1, aac(6’)-ib-cr) and intI 1, as well as the 16S rRNA encoding gene, were quantified using the real-time PCR on an ABI StepOnePlus instrument (Applied Bio-systems, Foster City, CA, USA). The abundance of the above-listed genes was quantified via qPCR, targeting different fragments of ARGs that were cloned into plasmid vectors (pBackZero-T vector, Takara, Kyoto, Japan) and used as standards. A total of 2 mg of RNA was converted to cDNA using LunaScript RT SuperMix Kit (NEB, Ipswich, MA, USA) as per the manufacturer’s guidelines [38]. Gene expression analysis was performed by conducting RT-PCR with the SYBR Green Premix Pro Taq HS qPCR kit from Accurate Biotechnology in China. All gene expression levels were normalized to the levels of 16S rDNA. All primers used in this study were synthesized by GENEWIZ Biotechnology Co. (Tianjin, China). The relative mRNA levels of the PCR products were quantified using 16S rDNA as an internal standard and calculated with the 2−ΔΔCt method.

2.4. Microbial Community Analysis

High-throughput sequencing of the 16S rRNA gene was conducted by Shanghai Whaleboat Gene Technology Co., Ltd. (Shanghai, China) using the Illumina HiSeq platform. The variable V3 and V4 regions of the bacterial 16S rRNA gene were amplified using the primer pair 341F (5′-CCTAYGGGRBGCASCAG-3′) and 806R (5′-GGACTACHVGGGTWTCTAAT-3′). Raw sequencing data underwent a quality control process using UPARSE (version 7.0.1090). The PCR products were detected by agarose gel electrophoresis and cut and recovered for purification. The purified PCR products were subjected to secondary PCR and, at the same time, connected to the Hiseq2500 PE250 sequencing connector (Illumina, San Diego, CA, USA), and sequencing libraries were constructed for sequencing. Finally, clustering and species classification analyses were performed based on the effective sequencing results in terms of Operational Taxonomic Units (OTUs), α-diversity analysis, β-diversity analysis, Hierarchical clustering (Hierarchical clustering), Principal Coordinate Analysis (PCoA), and species difference analysis. Classification and abundance visualization were performed using Greengene database, Krona software package, etc. The analysis and visualization were performed using data-processing tools, including Origin 2017 and R (version 3.3.1). All raw sequence datasets obtained in this study have been deposited in the NCBI Sequence Read Archive (SRA) under the BioProject accession number PRJNA1218474.

2.5. Screening and Antibiotic Resistance Test of Foodborne Pathogens

From a total of 250 samples collected from the broiler slaughter and processing chain, foodborne pathogens, Listeria monocytogenes, Salmonella, Staphylococcus aureus, and Escherichia coli, were, respectively, screened according to National Standard of the People’s Republic of China GB 4789.30-2016, GB 4789.4-2016, GB 4789.10-2016 [39,40,41].
Escherichia coli (E. coli): The isolation and identification of E. coli were performed according to the national standard method GB 4789.30-2016. Samples were aseptically inoculated onto MacConkey and Erythromycin agar plates and incubated overnight. Typical colonies were selected and purified by streaking on the MacConkey agar. After a third purification, the colonies were inoculated onto a nutrient agar and incubated at 37 °C overnight. Suspected E. coli colonies were subjected to Gram staining and microscopic examination to confirm staining characteristics.
Salmonella: Samples were pre-enriched in BPW for 8 h, followed by enrichment in TTB (1:10 ratio) at 42 °C and SC (1:10 ratio) at 37 °C. Enriched cultures were streaked onto XLD and BS agar plates. XLD plates were incubated at 37 °C for 24 h, while BS plates were incubated at 37 °C for 48 h. Suspected colonies on the XLD agar appeared pink (with or without black centers), yellow, or as large black colonies. On the BS agar, the colonies were black with a metallic luster, brown, gray, or gray–green, with surrounding media potentially turning black, brown, or unchanged. Suspected Salmonella colonies were inoculated onto TSI slants and incubated at 37 °C for 24 h. Cultures exhibiting Salmonella-typical TSI biochemical characteristics were selected for PCR identification.
Single-enriched Listeria monocytogenes (L. monocytogenes): The isolation and identification of L. monocytogenes were conducted according to the national standard method GB 4789.30-2016. Aseptically, 25 g (mL) of the sample was homogenized with 225 mL of LB1 enrichment broth (1:10 ratio) and incubated at 30 ± 1 °C for 24 h. Subsequently, 0.1 mL of the enriched culture was transferred to 10 mL of LB2 enrichment broth and incubated at 30 °C for an additional 24 h. The LB2 culture was streaked onto PALCAM agar or L. monocytogenes chromogenic plates and incubated at 36 °C for 24–48 h. Typical or suspicious colonies were selected and inoculated into rhamnose and xylose fermentation tubes, followed by incubation at 36 ± 1 °C for 24 h. Simultaneously, colonies were streaked onto TSA-YE plates for purification and incubated at 36 ± 1 °C for 36 h. Rhamnose-positive and xylose-negative colonies were further purified and identified.
Campylobacter jejuni (C. jejuni): The swabs were vigorously mixed in BPW preservation solution, followed by low-speed centrifugation at 4000 r/min for 30 min. The supernatant was discarded, and the pellet was resuspended in 10 mL of Brinell’s broth (supplemented with additives and horse serum), then transferred to 90 mL of nutrient broth. The broth was placed in an anaerobic jar with microaerobic gas packs and indicators, creating a microaerobic environment (5% O2, 10% CO2, 85% N2), and incubated at 42 °C for 48 h. The enriched culture was streaked onto modified Skirrow’s agar plates and incubated under microaerobic conditions for 48 h. Single colonies were then streaked onto Columbia blood agar plates (containing 5% defibrinated sheep blood) for further cultivation.
Staphylococcus aureus: The sponge swab was vigorously shaken in the BPW preservation solution, and 1.5 mL of the solution was transferred into 10 mL of 7.5% NaCl nutrient broth, followed by incubation at 37 °C for 24 h. This process was repeated twice, with the final incubation lasting 20 min. The enriched culture was then streaked onto sheep blood agar plates and incubated at 37 °C for 24 h. Colonies exhibiting opaque, moist, glossy surfaces (yellow or white) with surrounding transparent hemolysis rings were selected for purification. Purified colonies were Gram-stained and examined microscopically for further identification.
Detection of various drugs commonly used in China’s poultry industry, such as macrolides, β-lactams, colchicine, aminoglycosides, aminoglycosides, aminoglycosides, and alcohols, as well as the current regulations of the Ministry of Agriculture, can no longer be used as veterinary therapeutic drugs. The broth dilution method was used to test a total of 26 antibiotics, including penicillin, ouaghmentine, erythromycin, clindamycin, enrofloxacin, ofloxacin, cefotifur, cefoxitin, sulphonylisoxazole, vancomycin, compound Neonormin, Doxycycline, Tamiflu, Fosfenicol, Tilmicin, Gentamicin, Linezolid, Ampicillin, Augmentin, Spectinomycin, Ceftazidime, Meropenem, Ampramycin, Mucomycin, Acetylmethoquine, and Tetracycline. The Minimum Inhibitory Concentration (MIC) was interpreted according to the guidelines of the Clinical and Laboratory Standards Institute (CLSI). Moreover, based on the corresponding standards of the American CLSI, the corresponding results of sensitive (S), moderately sensitive (I), and drug-resistant (R) were obtained.

2.6. Data Analysis and Visualization

Quantitative information was presented as the average plus the standard error of the average (SEM). SPSS Statistics 23.0 was utilized to analyze the data through a one-way analysis of variance. Network analysis was conducted using R3.3.1 and the Gephi (0.9.2) platform.

3. Results and Discussion

3.1. Pollution of ARGs

According to the quantitative results of ARGs and intI1 (Figure 3), qualitative testing across eight major antibiotic types revealed the presence of ARGs in each category. Most ARGs were consistently detected across all sampling sessions, with tetQ, tetO, and tetW being particularly prominent. In contrast, blaSHV and oqxA were absent in most sessions and only detected in two instances, while tetT, mefA, and oqxB appeared in isolated sessions. Notably, intI1, a key integron gene facilitating ARGs transfer, was detected in all 10 sampling sessions.
Forty-three ARGs covering eight major types of antibiotic resistance and intI1 were tested in samples from broiler slaughter/processing chain, and twenty-three ARGs and intI1 were found to be positive. The ratio of detected links to ten total links is counted as the detection rate. Tetracycline-resistance genes (20.45%) were the most frequently detected, followed by macrolide resistance genes (6.82%) and quinolones resistance genes (6.82%), sulfonamide resistance genes (4.55%), β-lactam resistance genes (4.55%), chloramphenicol resistance genes (2.27%), and class I integron genes (2.27%), while peptide resistance genes were not detected. The kinds of ARGs detected in samples from each sampling points (X1–X10) are summarized in Figure 3. The highest diversity of ARGs was detected in sampling points X6 and X7 with a total of 18 kinds of ARGs; followed by X4, X5, X8, and X10 with sixteen kinds of ARGs; X1, X3, and X9 with fifteen kinds of ARGs; and X2 with fourteen kinds of ARGs. ARG spectrums for sampling points X1 and X2, X4 and X10, X5 and X8, X6 and X7 were similar. All parts of the slaughter chain were detected with positive ARGs, which suggested that the contamination of ARGs in the slaughter process of broilers was widespread.
Based on the qualitative results, ARGs heatmaps were produced, from which it can be seen clearly and intuitively that, among the forty-four ARGs and intI 1 detected qualitatively, the highest number of ARGs and intI 1 was detected on the surface of the X6 viscera and the surface of the meat in the X7 splitting session, with eighteen detected, followed by the surface of the X10 splitting conveyor belt, with seventeen; the same number of detections was found on the surfaces of the knives of the X5 clearing session and the knives of the X8 splitting session; the same number of detections was found on the surfaces of the knives of the X8 splitting session. Surface had the same number of detections at sixteen; X1 blanch fading session meat surface, X4 clean-ripping session meat surface, and X9 segmentation session worker’s hand surface had fifteen detections. X2 cooling water had fourteen detections, and X3 cooling session meat surface had the lowest number of detections, but the number of detections was as high as thirteen.
The clustering information shown in the heatmap indicated that the detection of ARGs and intI 1 were similar for X1 blanching and fading session meat surfaces and X2 cooling-session water, the detections of ARGs and intI 1 were similar for X4 clean-gutted-session meat surfaces and X10 segmentation session conveyor belt surfaces, and the similarity of detection of ARGs and intI 1 was high for X5 clean-gutted-session knife surfaces and X8 segmentation session knife surfaces. The detection of ARGs and intI 1 on the surface of the X6 offal and the surface of the meat in the X7 splitting session after removal of the offal were similar. X1 (scalding) and X6 (visceral removal) had the highest proportion of drug-resistant genes. X1 was the surface sample of chicken after scalding and alopecia, and the main drug-resistant gene was intI 1, indicating that broilers entering the slaughtering and processing chain from the outside would bring drug-resistant genes from the skin, feathers, or external environment. X6 is the sample collected during viscera extraction, and the main drug resistance gene is sul2, indicating that ARGs is likely to be contaminated by intestinal microorganisms due to viscera extraction.
Figure 4 illustrates which ARGs contribute most to these samples, and which sampling points they are distributed. The most abundant ARGs were detected in the samples from X1 and X6, followed by the sample from X4, X2, X5, and X10. A relatively less abundance of ARGs was detected in the samples from X3, X7, X8, X9. In general, intI1, sul2, tetX, blaTEM, and floR have the highest pollution levels, and tetM, tetT, tetQ, mefA, and oqxB have the lowest pollution levels. The most abundant intI1 is mainly derived from X1, X4, X2, and X10, and the second-highest abundance of sul2 is mainly derived from X6 and X5. The combined analysis of Figure 3 and Figure 4 indicates that the abundance of intI1 and sul2 is very high in the entire sampling chain. According to the analysis of qualitative results, eleven ARGs and intI 1, involving the eight major types of antibiotics that have research and analysis value, were selected for the quantitative analysis. The highest abundance levels of ARGs and intI 1 were detected on the meat surface of X1 scalded and faded session and on the surface of the viscera of X6. intI 1 abundance was very high in X1 (a sample of the chicken meat surface collected after scalded and dehairing). X6 was a sample collected during removal of viscera by rifling, and the ARGs with higher abundance were sul2 (0.446958626); most of sul2 was detected in chicken intestines and chicken feces in previous studies, so sul2 suggests to us that ARGs in this chain may originate from intestinal microbial contamination due to manipulation at the time of removal of viscera. The main types of ARGs causing contamination in the broiler slaughter chain were sul2, tetX, floR, and oqxB, whereas intI 1 was detected with a high detection rate and abundance, suggesting that the detected ARGs have a high risk of transmission.

3.2. Transmission Patterns of Antibiotic Resistance Genes in the Production Chain of Broiler Slaughtering and Processing

Among various genetic mechanisms that are involved in the dissemination of ARGs, integrons play a vital role [42]. Figure 5 demonstrated that there is a significant correlation between intI1 and tetM, which suggested tetM might have the potential to enter the human food chain via the Class-1 integrons. In addition, there is also a significant correlation between tetX, tetT, tetQ, sul2, mefA, and aadA1; a significant correlation between floR and aac(6′)-ib-cr; and a significant correlation between mefA and aadA1, which suggested that these ARGs have a joint relationship during diffusion.
A correlation analysis of the twelve quantitatively detected genes showed significant correlations greater than 0.7 at the Pearson 0.01 level and greater than 0.5 and less than 0.7 at the Pearson 0.05 level. The prevalence of significant correlations between ARGs and the type I integron gene intI 1 suggests that the ARGs detected in our broiler slaughter and processing chain have the ability to transfer horizontally.

3.3. Correlation Analysis of Microbial Community at Different Slaughtering Links

The results of the PCoA (Figure 6A) showed that the community compositions in the slaughtering process were clustered into five groups: ironing (X1), cooling (X2, X3), eviscerating (X4, X5), removing viscera (X6), and segmenting (X7–X10). This result further indicates that the community composition of adjacent operation links was similar. X1 and X6 have unique community composition and differ significantly from the other links.
Based on the heat map results of the community analysis, the main microbial components were Pseudomonadaceae, Serrateae, Vaginococcus, Citrobacter, Aeromonas, Burkholderia and Larnella, among others. By analyzing the structure of the microbial community (Figure 6B), it is clear that X1 and X6 are representative of the structure of the two major groups of microbiomes or the starting point of contamination: the dominant microbial community in the X1 hot fading link was Rhizobium, Staphylococcus aureus, Rhizobium landis, Rhodococcus and Flavobacterium; these genera were mainly from the environment, suggesting that the microbial contamination in this link mainly came from the breeding environment; the structure of microbial community was significantly changed after X6, which mainly included Pseudomonadaceae, Serrateae, Vaginococcus, Citrobacter, Aeromonas, Burkholderia and Larnella, which are mainly of enteric origin. X6 net chamber session resulted in leakage of enteric microorganisms contaminating the subsequent sampling session. Meanwhile, Figure 6B showed that the microbial community structure was well correlated in the sampling session. The abundance of these bacteria could be effectively reduced by removing the division stage of the gut organs. Flavobacterium, Pseudomonadaceae and Sphingomonas were the main bacteria in chicken feces, and these bacteria may be carried into the breeding environment [43]. In addition, due to its low relative abundance, it is able to colonize retail-packaged meat kept at refrigerated temperatures, raising food safety concerns [44].
ARGs can persist in extracellular gene elements, such as plasmids and even naked DNA fragments, but their replications need to proceed intracellularly [45]. Thus, the change in bacterial communities is prone to affect the proliferation and behavior of ARGs [46]. The heat map results of the community analysis clearly showed the differences before and after sampling point X6. Microbial communities from sampling points X1-X5 clustered together, and high-abundance genera mainly include Acinetobacter, Stenotrophomonas, Rhizobiaceae-unclassified, Flavobacterium, Rhodococcus, etc., mainly belonging to environmental microorganisms. Meanwhile, microbial communities from sampling points X6–X10 clustered together, and the high-abundance genera mainly include Pseudodomonas, Serratia, Vagococcus, Citrobacter, Aeromonas, Burkholderiaceae, Janthinobacterium and Rahnella, etc., mainly belonging to intestinal microorganisms. It might be inferred that the X1 and follow-up links are polluted by bacteria from fur and breeding environments, while the X6 and follow-up links are contaminated by bacteria from internal organs. The ARGs that cause the contamination of the broiler chain mainly include intI 1, sul2, tetX, floR, oqxB, etc. X1 (scalding) and X6 (dirty removal) points caused significant changes in the community, and the community composition of the slaughter-related points was similar.

3.4. Analysis of Potential Hosts of ARGs and intI 1

Bacteria are the main carriers of resistance genes [47], and the correlation between genera with high abundance and ARGs was investigated using network analysis to identify potential host bacteria for ARGs. As shown in Figure 7, the correlation between genera with high abundance and ARGs was studied via network analysis to identify potential ARGs host bacteria. In total, 53 nodes and 255 edges were obtained. These edges indicated significant correlations (p < 0.01 and r > 0.80) between ARGs, between bacterial communities, and between ARGs and bacterial communities across the ten sampling sites, with a total of fifteen potential hosts of ARGs identified. oqxB’s potential host bacteria belonged to the Enterobacteriaceae, Rhizobia rhizobia, and Microbacteria Micro bacteria. Algle, Enterobacteriaceae, and Fragrance species were the potential host bacteria of mefA. aac(6)-ib-cr in Delftia was the only potential host bacteria. Network analyses also showed significant correlations (p < 0.01) between aac(6′)-ib-cr and tetX and between tetQ and mefA, but their potential host bacteria had lower abundance.
The correlations between the top bacterial genera and ARGs were studied with a network analysis in order to identify the potential host bacteria for ARGs. As shown in Figure 7, 53 nodes and 255 edges were obtained. These edges indicated that there were significant correlations between ARGs, between bacterial communities and between ARGs and bacterial communities in the ten sample points (p < 0.01 and r > 0.80). Fifteen potential hosts of ARGs were identified among the top 100 genera. The potential host bacteria for oqxB belonged to the Methylobacillus Acinetobacter, Enterobacteriaceae unclassified and Allorhizobium. Neorhizobium, Pararhizobium, Rhizobium, Taibaiella, Sphingobacterium, Mesorhizobium, Bacteroidia unclassified, Micrococcales unclassified, Bosea Rothia, Microbacterium, Algoriella, Enterobacteriaceae and Myroides are potential host bacteria for mefA. The only potential host bacteria for aac(6′)-ib-cr is Delftia. The network analysis also demonstrated that there were significant correlations between aac(6′)-ib-cr and tetX and between tetQ and mefA (p < 0.01), but their potential host bacteria did not have high abundances. Due to being influenced by several bacteria within the Enterobacteriaceae, several studies have indicated meat as a reservoir of ARGs and a potential source of the environmental contamination [48]. Because most environmental bacteria are still not culturable using current techniques, only a few ARG hosts were experimentally verified in previous studies [49]. Therefore, the co-occurrence patterns could provide a preliminary, albeit inconclusive, assessment for finding possible ARG hosts in complex environmental samples such as field environments.

3.5. Contamination with Food-Borne Antibiotic-Resistant Bacteria in the Production Chain of Broiler Slaughtering and Processing

A total of 205 samples were collected from the slaughter and processing production chain of broilers, and five foodborne pathogens were detected against the above samples, namely pathogenic E. coli, S. aureus, L. monocytogenes, Salmonella, and C. jejuni. The results showed (Figure 8A) that pathogenic E. coli were not detected in all samples; Salmonella was detected at the highest rate of 31.6% in X2 pre-cooled water; S. aureus was detected in all segments, with the highest rate of 92% on the surface of the meat after pre-cooling in X3; L. monocytogenes was detected only on the surface of the meat cut in the separator knives X9 and X8, with a detection rate of 6.7%; C. jejuni was not detected only in the organ excision section of X6 and in the segmented meat of X7, with the highest detection rate occurring on the surface of the organ meats, with a detection rate of 66.7%.
Typically, Staphylococcus aureus was common in the slaughter and processing chain of broilers, with the highest detection rate being in scalding water and Salmonella being detected at the highest rate in the pre-cooling area. Notably, L. monocytogenes was detected only during the splitting process. In previous studies, when broilers just entered the processing plant, the detection rate of Salmonella was 3–4%, and the positivity rate could reach 20–35% at the end of slaughtering and processing, which indicates that the slaughtering and processing of broilers is an important process in which Salmonella contamination occurs [50]. Salmonella in broiler slaughtering and processing mainly originates from cross-contamination between carcasses and environmental and equipment contamination, and scalding, depilation, gutting, and cooling are considered to be the main links of cross-contamination of broiler carcasses [51].
Antibiotic drug sensitivity test panels are divided into aerobic Gram-positive and Gram-negative bacterial tests. In this experiment, four aerobic foodborne pathogens with research value were detected: E. coli (virulence factor), Staphylococcus aureus, Salmonella, and L. monocytogenes, of which E. coli and Salmonella are Gram-negative, and L. monocytogenes and Staphylococcus aureus are Gram-positive. Figure 8B shows a drug sensitivity profile showing three results denoted as follows: drug-resistant (dark blue dots), drug moderately sensitive (light blue dots), and drug-sensitive (white dots). The E. coli screened at the surface of the scalded meat, at the surface of the clean rifted meat and at the surface of the cutter in the splitting process showed multi-drug resistance and high drug resistance. Salmonella spp. screened only in X2 cooled water, X3 cooled meat, and X6 offal removal sessions were also multi-drug-resistant. In the antibiotic sensitivity test, ampicillin, tetracycline, florfenicol, enrofloxacin, ofloxacin, and mucomycin were all banned veterinary drugs by the Ministry of Agriculture, but the results of the sensitivity test showed that the foodborne pathogens detected were still resistant to the antibiotics, and the follow-up sensitivity test for mucomycin revealed that E. coli detected at the X6 offal removal session was ultra-highly resistant to mucomycin. Gram-positive bacteria L. monocytogenes and Staphylococcus aureus, which can be detected at every step of the slaughter and processing chain of broiler chickens, were detected in the X6 removal of viscera link with a very high level of resistance to Staphylococcus aureus, with a total of 16 antibiotics detected out of 18 antibiotics tested, which is a high rate of detection of 89%, and the rest of the link also showed results of multi-resistance. L. monocytogenes was detected only in the hands of the X8 splitter and X9 splitter workers belonging to the splitting stage, and these two segments were multi-resistant and highly resistant to L. monocytogenes. Among the antibiotics banned by the Ministry of Agriculture, high levels of resistance were also detected, with enrofloxacin and ofloxacin being the most severe.
Although no pathogenic E. coli were detected, resistant contamination of E. coli remains a concern. The E. coli screened at X1, X4, and X8 sampling points showed multiple drug resistance and high drug resistance. It is worth noting that the E. coli screened at X1 and X6 sampling points were resistant to colistin to a high degree. Salmonella was only screened at X2, X3, and X6, but there were also cases of multiple drug resistance. In the antibiotic susceptibility test, ampicillin, tetracycline, flufenicol, enrofloxacin, ofloxacin and colistin are all veterinary drugs banned by the Ministry of Agriculture (2017. China) [52], but the susceptibility results show that the detected bacteria are still resistant. In the detection of Gram-positive bacteria L. monocytogenes and Staphylococcus aureus, Staphylococcus aureus can be detected at every step in the slaughtering and processing chain of broilers, and the resistance of Staphylococcus aureus in X6 exceptionally high, 16 antibiotics were detected in 18 antibiotics tested, the detection rate was as high as 89%, and other links also showed the results of multiple drug resistance. L. monocytogenes only detected in X8 and X9 links, which belong to the segmentation link. It also has multiple drug resistance and high drug resistance. Among the antibiotics banned by the Ministry of Agriculture, a high degree of resistance was also detected, with enrofloxacin and ofloxacin being the most severe. Overall, antimicrobial resistance showed an increasing trend along the slaughtering process. Based on the community analysis and the detection of drug-resistant food-borne pathogens, it is inferred that there is the possibility of cross-contamination in chicken slaughter and processing. Maintaining slaughter hygiene, regular microbiological monitoring of carcasses, implementing good production practices, and establishing a food safety system are necessary measures to minimize the risk to consumers and reduce the risk of food-borne pathogen infection [53]. Key points such as removal of internal organs and scalding and cooling points are refined and partitioned to prevent cross-infection [54].

4. Conclusions

In this study, we sampled ten key links in the production line of broiler slaughterhouses and qualitatively and quantitatively detected the ARGs associated with eight major classes of antibiotics and veterinary drugs banned by the Ministry of Agriculture, and the results showed that all types of antibiotic-associated ARGs were detected, among which tetracycline-resistant genes were detected at the highest rate, followed by macrolide-resistant genes and quinolone-resistant genes. The main ARGs and genes coding for actionable genetic factors detected in the broiler slaughter line included sul2, tetX, floR, oqxB, and intI 1. The highest abundance of ARGs and intI 1 was detected in the scalding and cleaning processes. The highest abundance of intI 1 was detected in the scalding session, suggesting that the contaminated ARGs in this session had a strong horizontal gene transfer ability; the highest abundance of ARGs in the gutting session was sul 2, suggesting that the ARGs in this session might come from gut microbial contamination due to offal extraction.
Microbial community structure correlated well with the sampling sessions. The scalding and offal picking sessions were representative of the structure of the two main types of microbiomes or the starting point of contamination, and the community compositions of the sessions following them were similar to these two sessions, respectively. oqxB’s potential host genus was Enterobacteriaceae. Algae, Enterobacteriaceae, and Bacteroidetes are potential host bacteria for mefA. The only aac(6′)-ib-cr potential host bacterium in Delftobacteria.
Foodborne pathogens were detected to varying degrees in all ten sampling sessions, with Staphylococcus aureus being the most prevalent; Salmonella was prevalent in sessions prior to gutting; L. monocytogenes was detected only on the surface of the parted meat and on the hands of the parted workers in the splitting session; and C. jejuni was detected very frequently in the scalded fading water and on the cleaned rifted meat. The results of drug sensitivity tests for E. coli, S. aureus, Salmonella, and L. monocytogenes detected at different stages of the process showed that most of them were highly resistant and multi-resistant. Among them, veterinary drugs that have been banned by the Ministry of Agriculture in China were detected in multiple links of drug resistance.
The main contamination of drug-resistant genes lies in the scalding water and gutting. It is recommended that slaughterhouses should reasonably handle the scalding water and replace it in time, and reasonably discharge it, and the gutting process should avoid scratching the viscera, which will cause drug-resistant contamination. The results preliminarily revealed the contamination of ARGs and ARBs in the slaughtering environment during broiler slaughtering. These data contribute to food safety risk assessment and the development of corresponding control measures. Although this study represents a survey of only one broiler slaughter-processing plant, it helps to provide information on the characteristics of the bacterial community in the chicken carcass and the contamination of ARGs and how it changes at various stages of processing. Similar surveys of multiple lines operating in different ways may help to better determine the nature and amount of contamination (especially pathogens) throughout the processing line. Future research will focus on developing alternatives to antibiotics for poultry farming, reducing the use of antibiotics and their accumulation in humans.

Author Contributions

Conceptualization, methodology, validation, H.Z. and Y.L.; formal analysis and investigation, L.R., Z.Y. and X.W.; resources, H.Z. and Y.L.; data curation, L.R.; writing—original draft preparation, L.R.; writing—review and editing, L.R., Y.L., X.L., F.L. and H.Z.; visualization, L.R. All authors have read and agreed to the published version of the manuscript.

Funding

This research received no external funding.

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

The original contributions presented in the study are included in the article, further inquiries can be directed to the corresponding authors.

Conflicts of Interest

The authors declare no conflicts of interest.

References

  1. WHO. Antimicrobial Resistance: Global Report on Surveillance. Available online: https://www.who.int/publications/i/item/9789241564748 (accessed on 21 September 2024).
  2. Fair, R.J.; Tor, Y. Antibiotics and Bacterial Resistance in the 21st Century. Perspect. Med. Chem. 2014, 6, S14459. [Google Scholar] [CrossRef] [PubMed]
  3. Jeon, J.H.; Jang, K.-M.; Lee, J.H.; Kang, L.-W.; Lee, S.H. Transmission of antibiotic resistance genes through mobile genetic elements in Acinetobacter baumannii and gene-transfer prevention. Sci. Total Environ. 2023, 857, 159497. [Google Scholar] [CrossRef] [PubMed]
  4. Zhang, A.-N.; Gaston, J.M.; Dai, C.L.; Zhao, S.; Poyet, M.; Groussin, M.; Yin, X.; Li, L.-G.; van Loosdrecht, M.C.M.; Topp, E.; et al. An omics-based framework for assessing the health risk of antimicrobial resistance genes. Nat. Commun. 2021, 12, 4765. [Google Scholar] [CrossRef]
  5. Bai, X.; Zhong, H.; Cui, X.; Wang, T.; Gu, Y.; Li, M.; Miao, X.; Li, J.; Lu, L.; Xu, W.; et al. Metagenomic profiling uncovers microbiota and antibiotic resistance patterns across human, chicken, pig fecal, and soil environments. Sci. Total Environ. 2024, 947, 174734. [Google Scholar] [CrossRef]
  6. Gao, X.-L.; Shao, M.-F.; Luo, Y.; Dong, Y.-F.; Ouyang, F.; Dong, W.-Y.; Li, J. Airborne bacterial contaminations in typical Chinese wet market with live poultry trade. Sci. Total Environ. 2016, 572, 681–687. [Google Scholar] [CrossRef]
  7. Theophilus, R.J.; Taft, D.H. Antimicrobial Resistance Genes (ARGs), the Gut Microbiome, and Infant Nutrition. Nutrients 2023, 15, 3177. [Google Scholar] [CrossRef]
  8. Ebmeyer, S.; Kristiansson, E.; Larsson, D.G.J. A framework for identifying the recent origins of mobile antibiotic resistance genes. Commun. Biol. 2021, 4, 8. [Google Scholar] [CrossRef]
  9. Peterson, E.; Kaur, P. Antibiotic Resistance Mechanisms in Bacteria: Relationships Between Resistance Determinants of Antibiotic Producers, Environmental Bacteria, and Clinical Pathogens. Front. Microbiol. 2018, 9, 2928. [Google Scholar] [CrossRef]
  10. Fang, H.; Han, L.; Zhang, H.; Long, Z.; Cai, L.; Yu, Y. Dissemination of antibiotic resistance genes and human pathogenic bacteria from a pig feedlot to the surrounding stream and agricultural soils. J. Hazard. Mater. 2018, 357, 53–62. [Google Scholar] [CrossRef]
  11. Weinroth, M.D.; Thomas, K.M.; Doster, E.; Vikram, A.; Schmidt, J.W.; Arthur, T.M.; Wheeler, T.L.; Parker, J.K.; Hanes, A.S.; Alekoza, N.; et al. Resistomes and microbiome of meat trimmings and colon content from culled cows raised in conventional and organic production systems. Anim. Microbiome 2022, 4, 21. [Google Scholar] [CrossRef]
  12. Liu, Z.; Klümper, U.; Shi, L.; Ye, L.; Li, M. From Pig Breeding Environment to Subsequently Produced Pork: Comparative Analysis of Antibiotic Resistance Genes and Bacterial Community Composition. Front. Microbiol. 2019, 10, 43. [Google Scholar] [CrossRef] [PubMed]
  13. Ben, W.; Wang, J.; Pan, X.; Qiang, Z. Dissemination of antibiotic resistance genes and their potential removal by on-farm treatment processes in nine swine feedlots in Shandong Province, China. Chemosphere 2017, 167, 262–268. [Google Scholar] [CrossRef] [PubMed]
  14. Xu, C.; Kong, L.; Gao, H.; Cheng, X.; Wang, X. A Review of Current Bacterial Resistance to Antibiotics in Food Animals. Front. Microbiol. 2022, 13, 822689. [Google Scholar] [CrossRef]
  15. Zhou, Z.-C.; Feng, W.-Q.; Han, Y.; Zheng, J.; Chen, T.; Wei, Y.-Y.; Gillings, M.; Zhu, Y.-G.; Chen, H. Prevalence and transmission of antibiotic resistance and microbiota between humans and water environments. Environ. Int. 2018, 121, 1155–1161. [Google Scholar] [CrossRef]
  16. Tu, Z.; Pang, L.; Lai, S.; Zhu, Y.; Wu, Y.; Zhou, Q.; Qi, H.; Zhang, Y.; Dong, Y.; Gan, Y.; et al. The hidden threat: Comprehensive assessment of antibiotic and disinfectant resistance in commercial pig slaughterhouses. Sci. Total Environ. 2024, 946, 174222. [Google Scholar] [CrossRef]
  17. Carlet, J. The gut is the epicentre of antibiotic resistance. Antimicrob. Resist. Infect. Control 2012, 1, 39. [Google Scholar] [CrossRef]
  18. Zhu, Y.; Lai, H.; Zou, L.; Yin, S.; Wang, C.; Han, X.; Xia, X.; Hu, K.; He, L.; Zhou, K.; et al. Antimicrobial resistance and resistance genes in Salmonella strains isolated from broiler chickens along the slaughtering process in China. Int. J. Food Microbiol. 2017, 259, 43–51. [Google Scholar] [CrossRef]
  19. Jia, S.; Zhang, X.-X.; Miao, Y.; Zhao, Y.; Ye, L.; Li, B.; Zhang, T. Fate of antibiotic resistance genes and their associations with bacterial community in livestock breeding wastewater and its receiving river water. Water Res. 2017, 124, 259–268. [Google Scholar] [CrossRef]
  20. Pu, C.; Yu, Y.; Diao, J.; Gong, X.; Li, J.; Sun, Y. Exploring the persistence and spreading of antibiotic resistance from manure to biocompost, soils and vegetables. Sci. Total Environ. 2019, 688, 262–269. [Google Scholar] [CrossRef]
  21. Wright, G.D. Antibiotic resistance in the environment: A link to the clinic? Curr. Opin. Microbiol. 2010, 13, 589–594. [Google Scholar] [CrossRef]
  22. Liu, J.; Zhao, Z.; Avillan, J.J.; Call, D.R.; Davis, M.; Sischo, W.M.; Zhang, A. Dairy farm soil presents distinct microbiota and varied prevalence of antibiotic resistance across housing areas. Environ. Pollut. 2019, 254, 113058. [Google Scholar] [CrossRef] [PubMed]
  23. Gaire, T.N.; Odland, C.; Zhang, B.; Slizovskiy, I.; Jorgenson, B.; Wehri, T.; Meneguzzi, M.; Wass, B.; Schuld, J.; Hanson, D.; et al. Slaughtering processes impact microbial communities and antimicrobial resistance genes of pig carcasses. Sci. Total Environ. 2024, 946, 174394. [Google Scholar] [CrossRef] [PubMed]
  24. Franz, E.; van der Fels-Klerx, H.J.; Thissen, J.; van Asselt, E.D. Farm and slaughterhouse characteristics affecting the occurrence of Salmonella and Campylobacter in the broiler supply chain. Poult. Sci. 2012, 91, 2376–2381. [Google Scholar] [CrossRef]
  25. Statista. Production of Poultry Meat Worldwide from 1990 to 2022. Available online: https://www.statista.com/statistics/237637/production-of-poultry-meat-worldwide-since-1990/ (accessed on 21 September 2024).
  26. USDA Foreign Agricultural Service. China—Poultry and Products Annual. Available online: https://fas.usda.gov/data/china-poultry-and-products-annual-7 (accessed on 21 September 2024).
  27. Pan, Y.; Zeng, J.; Zhang, L.; Hu, J.; Hao, H.; Zeng, Z.; Li, Y. The fate of antibiotics and antibiotic resistance genes in Large-Scale chicken farm Environments: Preliminary view of the performance of National veterinary Antimicrobial use reduction Action in Guangdong, China. Environ. Int. 2024, 191, 108974. [Google Scholar] [CrossRef]
  28. Yuan, Y.; Mo, C.; Huang, F.; Liao, X.; Yang, Y. Microbial metabolism affects the antibiotic resistome in the intestine of laying hens. Poult. Sci. 2024, 103, 104138. [Google Scholar] [CrossRef]
  29. Temmerman, R.; Ghanbari, M.; Antonissen, G.; Schatzmayr, G.; Duchateau, L.; Haesebrouck, F.; Garmyn, A.; Devreese, M. Dose-dependent impact of enrofloxacin on broiler chicken gut resistome is mitigated by synbiotic application. Front. Microbiol. 2022, 13, 869538. [Google Scholar] [CrossRef]
  30. Kpomasse, C.C.; Oke, O.E.; Houndonougbo, F.M.; Tona, K. Broiler production challenges in the tropics: A review. Vet. Med. Sci. 2021, 7, 831–842. [Google Scholar] [CrossRef]
  31. Chen, S.H.; Fegan, N.; Kocharunchitt, C.; Bowman, J.P.; Duffy, L.L. Changes of the bacterial community diversity on chicken carcasses through an Australian poultry processing line. Food Microbiol. 2020, 86, 103350. [Google Scholar] [CrossRef]
  32. Nguyen, A.Q.; Vu, H.P.; Nguyen, L.N.; Wang, Q.; Djordjevic, S.P.; Donner, E.; Yin, H.; Nghiem, L.D. Monitoring antibiotic resistance genes in wastewater treatment: Current strategies and future challenges. Sci. Total Environ. 2021, 783, 146964. [Google Scholar] [CrossRef]
  33. Tokuda, M.; Shintani, M. Microbial evolution through horizontal gene transfer by mobile genetic elements. Microb. Biotechnol. 2024, 17, e14408. [Google Scholar] [CrossRef]
  34. Yan, K.; Wei, M.; Li, F.; Wu, C.; Yi, S.; Tian, J.; Liu, Y.; Lu, H. Diffusion and enrichment of high-risk antibiotic resistance genes (ARGs) via the transmission chain (mulberry leave, guts and feces of silkworm, and soil) in an ecological restoration area of manganese mining, China: Role of heavy metals. Environ. Res. 2023, 225, 115616. [Google Scholar] [CrossRef] [PubMed]
  35. Lin, Z.; Yuan, T.; Zhou, L.; Cheng, S.; Qu, X.; Lu, P.; Feng, Q. Impact factors of the accumulation, migration and spread of antibiotic resistance in the environment. Environ. Geochem. Health 2020, 43, 1741–1758. [Google Scholar] [CrossRef] [PubMed]
  36. Campos Calero, G.; Caballero Gómez, N.; Benomar, N.; Pérez Montoro, B.; Knapp, C.W.; Gálvez, A.; Abriouel, H. Deciphering Resistome and Virulome Diversity in a Porcine Slaughterhouse and Pork Products Through Its Production Chain. Front. Microbiol. 2018, 9, 2099. [Google Scholar] [CrossRef]
  37. GB/T 4789.17-2003; Microbiology Inspection of Food Hygiene Inspection of Meat and Meat Products. Ministry of Health of China: Beijing, China, 2003.
  38. Scott, G.; Ryder, D.; Buckley, M.; Hill, R.; Treagus, S.; Stapleton, T.; Walker, D.I.; Lowther, J.; Batista, F.M. Long Amplicon Nanopore Sequencing for Dual-Typing RdRp and VP1 Genes of Norovirus Genogroups I and II in Wastewater. Food Environ. Virol. 2024, 16, 479–491. [Google Scholar] [CrossRef]
  39. GB 4789.30-2016; Food Safety National Standard Food Microbiology Test Listeria monocytogenes Test. State Food and Drug Administration: Beijing, China, 2016.
  40. GB 4789.4-2016; National Standard for Food Safety Microbiology Inspection of Food Salmonella Inspection. State Food and Drug Administration: Beijing, China, 2016.
  41. GB 4789.10-2016; National Standard for Food Safety Food Microbiological Test Staphylococcus aureus Test. State Food and Drug Administration: Beijing, China, 2016.
  42. Zhang, Y.; Yang, Z.; Xiang, Y.; Xu, R.; Zheng, Y.; Lu, Y.; Jia, M.; Sun, S.; Cao, J.; Xiong, W. Evolutions of antibiotic resistance genes (ARGs), class 1 integron-integrase (intI1) and potential hosts of ARGs during sludge anaerobic digestion with the iron nanoparticles addition. Sci. Total Environ. 2020, 724, 138248. [Google Scholar] [CrossRef]
  43. Yan, W.; Sun, C.; Zheng, J.; Wen, C.; Ji, C.; Zhang, D.; Chen, Y.; Hou, Z.; Yang, N. Efficacy of Fecal Sampling as a Gut Proxy in the Study of Chicken Gut Microbiota. Front. Microbiol. 2019, 10, 2126. [Google Scholar] [CrossRef]
  44. Pinto Jimenez, C.E.; Keestra, S.; Tandon, P.; Cumming, O.; Pickering, A.J.; Moodley, A.; Chandler, C.I.R. Biosecurity and water, sanitation, and hygiene (WASH) interventions in animal agricultural settings for reducing infection burden, antibiotic use, and antibiotic resistance: A One Health systematic review. Lancet Planet. Health 2023, 7, e418–e434. [Google Scholar] [CrossRef]
  45. Wang, Y.; Dagan, T. The evolution of antibiotic resistance islands occurs within the framework of plasmid lineages. Nat. Commun. 2024, 15, 4555. [Google Scholar] [CrossRef]
  46. Fang, P.; Peng, F.; Gao, X.; Xiao, P.; Yang, J. Decoupling the Dynamics of Bacterial Taxonomy and Antibiotic Resistance Function in a Subtropical Urban Reservoir as Revealed by High-Frequency Sampling. Front. Microbiol. 2019, 10, 1448. [Google Scholar] [CrossRef]
  47. Jian, Z.; Zeng, L.; Xu, T.; Sun, S.; Yan, S.; Yang, L.; Huang, Y.; Jia, J.; Dou, T. Antibiotic resistance genes in bacteria: Occurrence, spread, and control. J. Basic Microbiol. 2021, 61, 1049–1070. [Google Scholar] [CrossRef]
  48. Conceição, S.; Queiroga, M.C.; Laranjo, M. Antimicrobial Resistance in Bacteria from Meat and Meat Products: A One Health Perspective. Microorganisms 2023, 11, 2581. [Google Scholar] [CrossRef] [PubMed]
  49. Cheng, X.; Lu, Y.; Song, Y.; Zhang, R.; ShangGuan, X.; Xu, H.; Liu, C.; Liu, H. Analysis of Antibiotic Resistance Genes, Environmental Factors, and Microbial Community From Aquaculture Farms in Five Provinces, China. Front. Microbiol. 2021, 12, 679805. [Google Scholar] [CrossRef] [PubMed]
  50. Thames, H.T.; Fancher, C.A.; Colvin, M.G.; McAnally, M.; Tucker, E.; Zhang, L.; Kiess, A.S.; Dinh, T.T.N.; Sukumaran, A.T. The Prevalence of Salmonella and Campylobacter on Broiler Meat at Different Stages of Commercial Poultry Processing. Animals 2022, 12, 2460. [Google Scholar] [CrossRef] [PubMed]
  51. Boubendir, S.; Arsenault, J.; Quessy, S.; Thibodeau, A.; Fravalo, P.; Thériault, W.P.; Fournaise, S.; Gaucher, M.-L. Salmonella Contamination of Broiler Chicken Carcasses at Critical Steps of the Slaughter Process and in the Environment of Two Slaughter Plants: Prevalence, Genetic Profiles, and Association with the Final Carcass Status. J. Food Prot. 2021, 84, 321–332. [Google Scholar] [CrossRef]
  52. Ministry of Agriculture. Announcement No. 2513, Ministry of Agriculture of the People’s Republic of China. Available online: https://www.moa.gov.cn/xw/bmdt/201704/t20170414_5560977.htm (accessed on 26 September 2024).
  53. Warmate, D.; Onarinde, B.A. Food safety incidents in the red meat industry: A review of foodborne disease outbreaks linked to the consumption of red meat and its products, 1991 to 2021. Int. J. Food Microbiol. 2023, 398, 110240. [Google Scholar] [CrossRef]
  54. Pasquali, F.; Klaharn, K.; Pichpol, D.; Meeyam, T.; Harintharanon, T.; Lohaanukul, P.; Punyapornwithaya, V. Bacterial contamination of chicken meat in slaughterhouses and the associated risk factors: A nationwide study in Thailand. PLoS ONE 2022, 17, e0269416. [Google Scholar] [CrossRef]
Figure 1. Broiler slaughter process and location distribution of sampling sites. (Pictures were collected from http://image.baidu.com; accessed on 21 September 2024).
Figure 1. Broiler slaughter process and location distribution of sampling sites. (Pictures were collected from http://image.baidu.com; accessed on 21 September 2024).
Foods 14 01047 g001
Figure 2. Simplified diagram of the broiler-slaughtering and -processing production chain and sampling points. Note: The dotted line represents meat sampled, the dotted solid line represents water sampled, the solid line with a slash represents the surface of a knife sampled, the solid line with a hollow rhombus represents the surface of an operator’s hand sampled, and the solid line with a solid rhombus represents the surface of a conveyor belt sampled.
Figure 2. Simplified diagram of the broiler-slaughtering and -processing production chain and sampling points. Note: The dotted line represents meat sampled, the dotted solid line represents water sampled, the solid line with a slash represents the surface of a knife sampled, the solid line with a hollow rhombus represents the surface of an operator’s hand sampled, and the solid line with a solid rhombus represents the surface of a conveyor belt sampled.
Foods 14 01047 g002
Figure 3. Qualitative test results of ARGs at ten sampling points in the broiler slaughter and processing chain. Note: Red represents the target gene detected positively, white represents the target gene detected negatively; X1: carcasses surface, X2: cooling pool water, X3: carcasses surface after washing with cooling water, X4: carcasses surface, X5: knife surface, X6: entrails surface, X7: carcasses surface, X8: knife surface, X9: hand surface, X10: conveyor surface.
Figure 3. Qualitative test results of ARGs at ten sampling points in the broiler slaughter and processing chain. Note: Red represents the target gene detected positively, white represents the target gene detected negatively; X1: carcasses surface, X2: cooling pool water, X3: carcasses surface after washing with cooling water, X4: carcasses surface, X5: knife surface, X6: entrails surface, X7: carcasses surface, X8: knife surface, X9: hand surface, X10: conveyor surface.
Foods 14 01047 g003
Figure 4. Types of ARGs and their abundance distribution (visualized by Circos) from ten sampling points in the broiler slaughter processing chain. Note: The length of the outer ring bar represents the percentage of ARGs in each sample. Each ARG and sampling point is represented by a specific ribbon color, and the width of each ribbon indicates the abundance of ARGs. X1: carcasses surface, X2: cooling pool water, X3: carcasses surface after washing with cooling water, X4: carcasses surface, X5: knife surface, X6: entrails surface, X7: carcasses surface, X8: knife surface, X9: hand surface, X10: conveyor surface.
Figure 4. Types of ARGs and their abundance distribution (visualized by Circos) from ten sampling points in the broiler slaughter processing chain. Note: The length of the outer ring bar represents the percentage of ARGs in each sample. Each ARG and sampling point is represented by a specific ribbon color, and the width of each ribbon indicates the abundance of ARGs. X1: carcasses surface, X2: cooling pool water, X3: carcasses surface after washing with cooling water, X4: carcasses surface, X5: knife surface, X6: entrails surface, X7: carcasses surface, X8: knife surface, X9: hand surface, X10: conveyor surface.
Foods 14 01047 g004
Figure 5. Correlation analysis of twelve quantitatively detected genes.
Figure 5. Correlation analysis of twelve quantitatively detected genes.
Foods 14 01047 g005
Figure 6. (A) PCoA analysis shows correlation between ten sampling points in the broiler slaughter and processing chain. (B) Heat map analysis of the most common genera in samples from ten sampling points on the broiler slaughter and processing process. Clustering using Spearman rank correlation. Different colors indicate the relative abundance of each genus. The sample name indicates the sampling location. Note: X1: carcasses surface, X2: cooling pool water, X3: carcasses surface after washing with cooling water, X4: carcasses surface, X5: knife surface, X6: entrails surface, X7: carcasses surface, X8: knife surface, X9: hand surface, X10: conveyor surface.
Figure 6. (A) PCoA analysis shows correlation between ten sampling points in the broiler slaughter and processing chain. (B) Heat map analysis of the most common genera in samples from ten sampling points on the broiler slaughter and processing process. Clustering using Spearman rank correlation. Different colors indicate the relative abundance of each genus. The sample name indicates the sampling location. Note: X1: carcasses surface, X2: cooling pool water, X3: carcasses surface after washing with cooling water, X4: carcasses surface, X5: knife surface, X6: entrails surface, X7: carcasses surface, X8: knife surface, X9: hand surface, X10: conveyor surface.
Foods 14 01047 g006
Figure 7. Network analysis of cooccurring ARGs and potential host bacteria (top 30 genera) based on Pearson’s correlation coefficients (p < 0.01, r > 0.80). Note: Bold fonts represent antibiotic resistance genes, and the nodes with different colors represent the related bacteria genus. The node size is proportional to the number of connections (degree). An edge represents a significant and strong correlation, where the edge thickness is proportional to the Pearson’s correlation coefficient.
Figure 7. Network analysis of cooccurring ARGs and potential host bacteria (top 30 genera) based on Pearson’s correlation coefficients (p < 0.01, r > 0.80). Note: Bold fonts represent antibiotic resistance genes, and the nodes with different colors represent the related bacteria genus. The node size is proportional to the number of connections (degree). An edge represents a significant and strong correlation, where the edge thickness is proportional to the Pearson’s correlation coefficient.
Foods 14 01047 g007
Figure 8. (A) Proportion of four foodborne pathogens, Salmonella, Staphylococcus aureus, Listeria monocytogenes, and Campylobacter jejuni, detected at ten sampling sites. (B) The results of susceptibility tests. Note: Escherichia coli (E. coli), Salmonella (SE), Staphylococcus aureus (S. aureus), and Listeria monocytogenes (LM) screened at different stages. The test results showed three types of resistance ( dark blue dots), poisoning sensitivity ( light blue dots), and sensitivity (○ white dots); X1: carcasses surface, X2: cooling pool water, X3: carcasses surface after washing with cooling water, X4: carcasses surface, X5: knife surface, X6: entrails surface, X7: carcasses surface, X8: knife surface, X9: hand surface, X10: conveyor surface.
Figure 8. (A) Proportion of four foodborne pathogens, Salmonella, Staphylococcus aureus, Listeria monocytogenes, and Campylobacter jejuni, detected at ten sampling sites. (B) The results of susceptibility tests. Note: Escherichia coli (E. coli), Salmonella (SE), Staphylococcus aureus (S. aureus), and Listeria monocytogenes (LM) screened at different stages. The test results showed three types of resistance ( dark blue dots), poisoning sensitivity ( light blue dots), and sensitivity (○ white dots); X1: carcasses surface, X2: cooling pool water, X3: carcasses surface after washing with cooling water, X4: carcasses surface, X5: knife surface, X6: entrails surface, X7: carcasses surface, X8: knife surface, X9: hand surface, X10: conveyor surface.
Foods 14 01047 g008
Table 1. Information of samples collected.
Table 1. Information of samples collected.
Sample NameSampling StageSampling PointNumber of Samples Collected
X1scaldingcarcasses surface25
X2cooling pool water25
X3carcasses surface after washing with cooling water25
X4disembowelingcarcasses surface25
X5knife surface25
X6evisceratingentrails surface25
X7fragmentingcarcasses surface25
X8knife surface25
X9hand surface25
X10conveyor surface25
total/250
Table 2. Primers of qualitative detection.
Table 2. Primers of qualitative detection.
Target GenesAntibioticPrimer Sequence
(5′–3′)
Product Length
(bp)
tetAtetracyclinesGCGCGATCTGGTTCACTCG164
AGTCGACAGYRGCGCCGGC
tetCtetracyclinesCTTGAGAGCCTTCAACCCAG418
ATGGTCGTCATCTACCTGCC
tetGtetracyclinesGTCGATTACACGATTATGGC432
CACTTGGCCGATCAGTTGA
tetMtetracyclinesACAGAAAGCTTATTATATAAC171
GGCGTGTCTATGATGTTCAC
tetOtetracyclinesACGGARAGTTTATTGTATACC171
TGGCGTATCTATAATGTTGAC
tetQtetracyclinesAGAATCTGCTGTTTGCCAGTG169
CGGAGTGTCAATGATATTGCA
tetTtetracyclinesAAGGTTTATTATATAAAAGTG169
AGGTGTATCTATGATATTTAC
tetWtetracyclinesAGGTGTATCTATGATATTTAC168
GGGCGTATCCACAATGTTAAC
tetXtetracyclinesGACCCGTTGGACTGACTATGG168
CTTCCTGACCTGAACCTTTGTG
sul1sulfonamidesCGCACCGGAAACATCGCTGCAC163
TGAAGTTCCGCCGCAAGGCTCG
sul2sulfonamidesTCCGGTGGAGGCCGGTATCTGG191
CGGGAATGCCATCTGCCTTGAG
Sul IIIsulfonamidesTCCGTTCAGCGAATTGGTGCAG128
TTCGTTCACGCCTTACACCAGC
ermBmacrolidesCCGATACCGTTTACGAAATTGG190
TAGCAAACCCGTATTCCACG
mefAmacrolidesAGTATCATTAATCACTAGTGC186
TTCTTCTGGTACTAAAAGTGG
blaTEMβ-lactamsGCATCTTACGGATGGCATGA99
CCTCCGATCGTTGTCAGAAGT
blaSHVβ-lactamsGGTTATGCGTTATATTCGCCTGTG861
TTAGCGTTGCCAGTGCTCGATCA
oqxA4-quinolonesGATCAGTCAGTGGGATAGTTT627
TACTCGGCGTTAACTGATTA
oqxB4-quinolonesTCCTGATCTCCATTAACGCCCA131
ACCGGAACCCATCTCGATGC
qnrD4-quinolonesACGACAGGAATAGCTTGGAAGG465
TCAGCCAAAGACCAATCAAACG
floRFlorfenicolCGGTCGGTATTGTCTTCACG171
TCACGGGCCACGCTGTAT
aadA1aminoglycosidesAGCTAAGCGCGAACTGCAAT195
TGGCTCGAAGATACCTGCAA
aac(6′)-ib-craminoglycosidesGCTCTATGAGTGGCTAAATCGATC182
GCAATGTATGGAGTGACGGAC
intI1class I integronsCCTCCCGCACGATGATC280
TCCACGCATCGTCAGGC
mcr-1polymyxinsATGATGCAGCATACTTCTGTG1626
TCAGCGGATGAATGCGGTG
mcr-2polymyxinsGATGGCGGTCTATCCTGTAT715
AAGGCTGACACCCCATGTCAT
mcr-3polymyxinsACCAGTAAATCTGGTGGCGT929
AGGACAACCTCGTCATAGCA
mcr-4polymyxinsTTGCAGACGCCCATGGAATA1116
GCCGCATGAGCTAGTATCGT
mcr-5polymyxinsGGACGCGACTCCCTAACTTC1644
ACAACCAGTACGAGAGCACG
mcr-6polymyxinsGTCCGGTCAATCCCTATCTGT556
ATCACGGGATTGACATAGCTAC
mcr-7polymyxinsAGGGGATAAACCGACCCTGA335
TGATCTCGATGTTGGGCACC
mcr-8polymyxinsAACCGCCAGAGCACAGAATT667
TTCCCCCAGCGATTCTCCAT
mcr-9polymyxinsGGTAGTTATTCCGCTGG1572
TCGCGGTCAGGATTAAC
tetStetracyclinesGGTCAACGGCTTGTCTATGTA667
CCAGGCTCTCATACTGAATGC
tetBtetracyclinesAAAACTTATTATATTATAGTG169
TGGAGTATCAATAATATTCAC
tetHtetracyclinesCAGTGAAAATTCACTGGCAAC185
ATCCAAAGTGTGGTTGAGAAT
qnrS4-quinolonesGCAAGTTCATTGAACAGGGT428
TCTAAACCGTCGAGTTCGGCG
qnrA4-quinolonesAGGATTTCTCACGCCAGGATT124
CCGCTTTCAATGAAACTGCAA
depA4-quinolonesCCAGCTCGGCAACTTGATAC570
ATGCTCGCCTTCCAGAAAA
gyrA4-quinolonesCAAGAATCGTGGGTGATG351
GTGGAATATTTGTCGCCA
ermCmacrolidesGAAATCGGCTCAGGAAAAGG293
TAGCAAACCCGTATTCCACG
ermFmacrolidesTCTAGCAATGAGAATGAAGGT309
ACTATAACGTGATGGTTGGGAGGGA
ermAmacrolidesAAGCGGTAAACCCCTCTGA190
TTCGCAAATCCCTTCTCAAC
ereAmacrolidesCCTTCACATCCGGATTCGCTCGA420
CTTCACATCCGGATTCGCTCGA
CatA1chloram phenicolsGGGTGAGTTTCACCAGTTTTGATT101
CACCTTGTCGCCTTGCGTATA
16S rDNA-TGTGTAGCGGTGAAATGCG140
CATCGTTTACGGCGTGGAC
Disclaimer/Publisher’s Note: The statements, opinions and data contained in all publications are solely those of the individual author(s) and contributor(s) and not of MDPI and/or the editor(s). MDPI and/or the editor(s) disclaim responsibility for any injury to people or property resulting from any ideas, methods, instructions or products referred to in the content.

Share and Cite

MDPI and ACS Style

Ren, L.; Li, Y.; Ye, Z.; Wang, X.; Luo, X.; Lu, F.; Zhao, H. Explore the Contamination of Antibiotic Resistance Genes (ARGs) and Antibiotic-Resistant Bacteria (ARB) of the Processing Lines at Typical Broiler Slaughterhouse in China. Foods 2025, 14, 1047. https://doi.org/10.3390/foods14061047

AMA Style

Ren L, Li Y, Ye Z, Wang X, Luo X, Lu F, Zhao H. Explore the Contamination of Antibiotic Resistance Genes (ARGs) and Antibiotic-Resistant Bacteria (ARB) of the Processing Lines at Typical Broiler Slaughterhouse in China. Foods. 2025; 14(6):1047. https://doi.org/10.3390/foods14061047

Chicago/Turabian Style

Ren, Lu, Ying Li, Ziyu Ye, Xixi Wang, Xuegang Luo, Fuping Lu, and Huabing Zhao. 2025. "Explore the Contamination of Antibiotic Resistance Genes (ARGs) and Antibiotic-Resistant Bacteria (ARB) of the Processing Lines at Typical Broiler Slaughterhouse in China" Foods 14, no. 6: 1047. https://doi.org/10.3390/foods14061047

APA Style

Ren, L., Li, Y., Ye, Z., Wang, X., Luo, X., Lu, F., & Zhao, H. (2025). Explore the Contamination of Antibiotic Resistance Genes (ARGs) and Antibiotic-Resistant Bacteria (ARB) of the Processing Lines at Typical Broiler Slaughterhouse in China. Foods, 14(6), 1047. https://doi.org/10.3390/foods14061047

Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.

Article Metrics

Back to TopTop