Abstract
Listeria monocytogenes is a foodborne pathogen of concern in dairy processing facilities, with the potential to cause human illness and trigger regulatory actions if found in the product. Monitoring for Listeria spp. through environmental sampling is recommended to prevent establishment of these microorganisms in dairy processing environments, thereby reducing the risk of product contamination. To inform on L. monocytogenes diversity and transmission, we analyzed genome sequences of L. monocytogenes strains (n = 88) obtained through the British Columbia Dairy Inspection Program. Strains were recovered from five different dairy processing facilities over a 10 year period (2007–2017). Analysis of whole genome sequences (WGS) grouped the isolates into nine sequence types and 11 cgMLST types (CT). The majority of isolates (93%) belonged to lineage II. Within each CT, single nucleotide polymorphism (SNP) differences ranged from 0 to 237 between isolates. A highly similar (0–16 SNPs) cluster of over 60 isolates, collected over 9 years within one facility (#71), was identified suggesting a possible persistent population. Analyses of genome content revealed a low frequency of genes associated with stress tolerance, with the exception of widely disseminated cadmium resistance genes cadA1 and cadA2. The distribution of virulence genes and mutations within internalin genes varied across the isolates and facilities. Further studies are needed to elucidate their phenotypic effect on pathogenicity and stress response. These findings demonstrate the diversity of L. monocytogenes isolates across dairy facilities in the same region. Findings also showed the utility of using WGS to discern potential persistence events within a single facility over time.
1 Introduction
Dairy product contamination with Listeria monocytogenes has led to numerous recalls and outbreaks worldwide (). Since listeriosis, the disease caused by L. monocytogenes, is attributed to high rates of morbidity (>90%) and mortality (18–30%), it is imperative to minimize the pathogen’s entry into the food system (Silk et al., 2013; ; Scobie et al., 2019). L. monocytogenes can be introduced into dairy foods and their associated environments through a variety of sources, including the farm/barn environments (; ), udder surfaces (), milking systems (Latorre et al., 2010; ), and milk (). For dairy products requiring extensive handling, the production environment (e.g., drains and floors), equipment, and continuous use systems (e.g., brines) can also serve as contamination sources (; ; ). Although pasteurization is an effective method to eliminate pathogens in these products, the presence of L. monocytogenes within the production environments presents a post-processing contamination risk to ready-to-eat (RTE) dairy products (Tompkin, 2002). To better understand the risk of product contamination within facilities, monitoring through environmental sampling is often used (Tompkin, 2002). This allows for the identification of contaminated areas and microbial niches that may be harboring L. monocytogenes, thereby providing opportunities for pathogen proliferation and continued introduction throughout the facility (Tompkin, 2002). Understanding contamination patterns helps prioritize and improve on existing cleaning and sanitation procedures and can indicate other systemic changes are warranted (e.g., review of employee practices and infrastructure modifications).
While prevalence within a facility is valuable information, leveraging these data with genetic information allows for a high level of discrimination between the recovered isolates. More specifically, these data can be used to further classify isolates into familial groupings (e.g., lineages and clonal complexes) that can be indicative of specific properties of these microorganisms (Orsi et al., 2011). At the broadest level, L. monocytogenes is grouped into four lineages, with most clinical and food-related isolates belonging to lineages I and II, respectively (Orsi et al., 2011). Although food-derived isolates are commonly associated with lineage II, sampling of dairy processing environments has shown the presence of both lineage I (Maury et al., 2019; Palacios-Gorba et al., 2021) and lineage II (; ; Stessl et al., 2014) strains.
Genetic information gathered from sequencing data has also allowed for more specific classifications of L. monocytogenes based on conserved genes (Ragon et al., 2008). For example, allelic differences in seven housekeeping genes are used to assign isolates to a multi-locus sequence type (ST), while STs consisting of one or fewer allelic differences are grouped into clonal complexes (CCs) (Ragon et al., 2008). Notably, one CC (CC1; lineage I) has been strongly associated with dairy products in France (Maury et al., 2019) and ruminants (; Palacios-Gorba et al., 2021).
Sequencing has also allowed for a better understanding of stress response mechanisms that may be indicative of persistence within the facility or survival in a food product (). Specifically, single-nucleotide polymorphism (SNP) analysis has been used to show isolate similarities within and between facilities (Stasiewicz et al., 2015; ). This analysis has also been used to differentiate between sporadic and potentially persistent L. monocytogenes strains in retail delis (Stasiewicz et al., 2015), produce environments (), patients, animals, and animal production environments (), meat and salmon raw materials, processed foods, and processing environments (), and dairy farms (). Analyzing specific genes/genetic elements that are potentially or positively linked to stress response and/or virulence (e.g., antimicrobial tolerance genes and elements associated with invasion, pathogenicity islands or stress survival islets) may also provide insights into L. monocytogenes survival advantages and genetic diversity.
Due to decreasing costs and turn-around time for results, whole genome sequencing (WGS) is becoming a more viable option for use within multiple sectors of the food system (). In recent years, North American agencies such as the Centers for Disease Control and Prevention, the Canadian Food Inspection Agency, and the Food and Drug Administration have transitioned to using WGS to identify and characterize pathogens of concern isolated from foods and food processing environments (Rantsiou et al., 2018; ). While zero tolerance for L. monocytogenes in all RTE foods is enforced in the U.S., in Canada, a tiered risk-based system is used for determining allowable limits (). Specifically, zero tolerance is practiced for RTE foods that support the growth of L. monocytogenes and any RTE foods produced for vulnerable populations (). For RTE products that do not support pathogen growth or have limited potential for growth (i.e., not exceeding 100 CFU/g), up to 100 CFU/g are allowed ().
In 2002, two separate listeriosis outbreaks in British Columbia (BC), Canada were linked to the consumption of soft cheese, resulting in 134 illnesses (McIntyre et al., 2015). These outbreaks triggered the introduction of a voluntary monthly testing program of certain soft cheeses and collection of environmental samples by the industry and British Columbia Centre for Disease Control (BCCDC) inspectors (McIntyre et al., 2015). In this retrospective study, WGS was used to characterize L. monocytogenes isolates obtained through the BC Dairy Inspection Program over 10 years to better understand the diversity of L. monocytogenes isolates encountered in the dairy sector in BC.
2 Materials and methods
2.1 Whole genome sequencing and data assembly
Listeria monocytogenes isolates (n = 88) were previously isolated as part of provincial dairy inspection activities in BC, Canada, from 2007 to 2017. As part of inspectional activities, 87 finished product (food) and 195 environmental samples were collected from the five dairy facilities. Nine food product and 39 environmental samples were positive for L. monocytogenes. From these positive samples, 54 isolates from food samples and 34 isolates from environmental swab samples were selected for further analyses (Table 1). Isolates were stored at −80°C in tryptic soy broth (TSB; Neogen, Lansing, MI, United States) supplemented with 25% (w/v) glycerol. Prior to use, isolates were resuscitated by streaking onto tryptic soy agar (TSA; Neogen) supplemented with 0.6% yeast extract (YE; Fisher, Hampton, NH, United States), followed by 24 h incubation at 37°C. An isolated colony was transferred to 3 mL of TSB and incubated at 37°C for 18 h (TSB; Neogen). Genomic DNA was extracted using Qiagen DNeasy Blood and Tissue kits (Qiagen, Hilden, Germany) according to the manufacturer’s instructions for Gram-positive bacterial DNA. Quality and quantity of DNA was assessed using dsDNA broad range assay kit for DeNovix DS-11 Spectrophotometer/Fluorometer (DeNovix, Wilmington, DE, United States). DNA libraries were prepared at Oregon State University’s Center for Quantitative Life Sciences (Corvallis, OR, United States) using the PlexWell kit (seqWell, Beverly, MA, United States) according to the manufacturer’s instructions, followed by 2×150-bp paired-end sequencing using Illumina HiSeq (Illumina, San Diego, CA, United States). Resulting raw reads were quality checked with FastQC (v 0.11.9) and trimmed using Trimmomatic (v 0.39) (). Trimmed reads were de novo assembled using SPAdes (v 3.14.1) (Prjibelski et al., 2020) and optimized with Unicycler (v 0.4.8) (Wick et al., 2017). Resulting assembly files were assessed for quality (Supplementary Table S1) and annotated with Prokka (v 1.14.6) (Seemann, 2014).
Table 1
| Facility/year | No. of samples (n = facility total) | No. of isolates | No. sequence types (ST) | No. clonal complexes (CC) | No. cgMLST types (CT) | No. sigB allelic types (AT) |
|---|---|---|---|---|---|---|
| Facility #14 | n = 2 | |||||
| 2016 | 1 | 1 | 1 | 1 | 1 | 1 |
| 2017 | 1 | 1 | 1 | 1 | 1 | 1 |
| Facility #71 | n = 72 | |||||
| 2007 | 2 | 2 | 1 | 1 | 1 | 1 |
| 2009 | 3 | 9 | 2 | 2 | 2 | 2 |
| 2010 | 7 | 7 | 1 | 1 | 1 | 1 |
| 2012 | 12 | 45 | 2 | 2 | 2 | 2 |
| 2015 | 3 | 3 | 3 | 3 | 3 | 3 |
| 2016 | 6 | 6 | 2 | 2 | 2 | 2 |
| Facility #106 | n = 1 | |||||
| 2015 | 1 | 1 | 1 | 1 | 1 | 1 |
| Facility #122 | n = 12 | |||||
| 2017 | 12 | 12 | 1 | 1 | 1 | 1 |
| Facility #131 | n = 1 | |||||
| 2016 | 1 | 1 | 1 | 1 | 1 | 1 |
Number of samples and distribution of L. monocytogenes isolates, sequence types, clonal complexes, cgMLST types, sigB allelic profiles, and years of isolate recovery within each facility.
2.2 Multi-locus sequence typing, core genome MLST, and sigB allelic typing
Multi-locus sequence type (ST), clonal complex (CC), cgMLST, and sigB allelic profiles were assigned using the Listeria Pasteur database, BIGSdb-Lm (Moura et al., 2016). cgMLST was performed using a scheme consisting of 1,748 conserved core genes; assemblies were submitted to the BIGSdb-Lm to receive cgMLST type (CT) assignments.
2.3 Screening for virulence and stress response related genes
Isolates were screened for presence and absence of relevant virulence and stress response genetic markers according to , with minor modifications. Briefly, the BIGSdb-Lm virulence scheme (92 loci) was used to assess virulence gene presence/absence. The presence of stress response genes, including antimicrobial resistance and tolerance genes (tetR, tnpABC, qacH, qacC, emrE, emrC, and bcrABC) and heavy metal genes (cadA1, cadA2, cadA4, arsA1, arsA2, arsB1, arsB2, arsD1, arsD2, arsR1, and arsR2) were screened using NCBI BLASTN, with a minimum nucleotide identity and alignment length coverage of 80%. Genetic mutations were identified by aligning genes of interest to a reference sequence using the MUSCLE algorithm in MEGAX (v 10.2.6) (). Accession numbers for reference strains used for genetic element screening and alignments are provided in the Supplementary Table S2.
2.4 Whole genome SNP analysis
Single nucleotide polymorphisms (SNPs) were assessed according to Weisberg et al. (2020), with slight modifications described by . Briefly, the pairwise average nucleotide identity (ANI) among isolates and confirmation of species-level grouping (i.e., L. monocytogenes; >95% ANI) was performed using FastANI (v 1.1) (). Raw reads were mapped to a representative reference sequence within the group (WRLP15) using BWA mem (v 0.7.17) (Li and Durbin, 2009). Alignments were annotated and sorted, and duplicate reads were identified using Picard tools (v 2.0.1). Graphtyper (v 2.6.2) was run with the default parameters (). The algorithm Graphtyper identifies sequence variants by aligning short read sequence data to a pangenome (). SNPs were filtered using vcffilter in vcflib (v 1.0.0) with the options -f “ABHet <0.0 | ABHet >0.33” -f “ABHom <0.0 | ABHom >0.97” -f “MaxAASR >0.4” -f “MQ > 30” (). SNP calls annotated as “FAIL” or “heterozygous” were filtered to “no-call.” Filtered SNP calls were converted to fasta format using BCFtools (v 1.3) (Li et al., 2009). The bitwise. Dist function within the R package poppr (v 2.9.2) was used to construct pairwise SNP distance tables from the fasta alignments (). Poppr was then used to construct and visualize a minimum spanning network (MSN). The phylogenetic tree based on the SNP data was made using IQ-TREE version 1.6.12, with parameters -bb 1000 -alrt 1000 (Nguyen et al., 2015).
3 Results
3.1 General genome characteristics and isolate grouping
The majority of the isolates (n = 82) belonged to lineage II and only six isolates were lineage I. Lineage II isolates were recovered from foods (n = 51), food contact surfaces (FCS; n = 6) and non-food contact surfaces (NFCS; n = 25), whereas lineage I isolates were recovered from foods (n = 3) and NFCS (n = 3) (Figure 1). Classification information including isolate source, lineage, ST, CC, and CT is summarized in Tables 1, 2.
Figure 1
Table 2
| Facility/isolate ID | Year isolated | Source | Lineage | ST | CC | cgMLST | bcrABC | cadA genes |
|---|---|---|---|---|---|---|---|---|
| Facility #14 | ||||||||
| WRLP94 | 2016 | Environment | II | 2803 | 226 | 10475 | − | − |
| WRLP95 | 2017 | Environment | II | 11 | 11 | 10087 | + | A1 |
| Facility #71 | ||||||||
| WRLP16-17 | 2007 | Environment | II | 11 | 11 | 6558 | − | A1 |
| DE25-1a, WRLP8-9 | 2009 | Environment | II | 7 | 7 | 10086 | − | − |
| DE26-1a, DE27-1a | 2009 | Environment | II | 11 | 11 | 6558 | − | A1 |
| WRLP11-12, WRLP14-15 | 2009 | Environment | II | 11 | 11 | 6558 | − | A1 |
| WRLP18-24 | 2010 | Environment | II | 11 | 11 | 6558 | − | A1 |
| WRLP26-68 | 2012 | Food | II | 11 | 11 | 6558 | − | A1 |
| WRLP69 | 2012 | Environment | II | 11 | 11 | 6558 | − | A1 |
| WRLP70 | 2012 | Food | I | 224 | 224 | 6679 | − | − |
| WRLP71 | 2015 | Environment | II | 11 | 11 | 6558 | − | A1 |
| WRLP73 | 2015 | Food | I | 1 | 1 | 6441 | − | − |
| WRLP74 | 2015 | Food | I | 397 | 4 | 6720 | − | − |
| WRLP75-79 | 2016 | Environment | II | 11 | 11 | 6558 | − | A1 |
| WRLP80 | 2016 | Environment | I | 1 | 1 | 252 | − | − |
| Facility #106 | ||||||||
| WRLP81 | 2015 | Environment | I | 288 | 288 | 6544 | − | A2 |
| Facility #122 | ||||||||
| WRLP82-83 | 2017 | Environment | II | 399 | 14 | 10088 | − | − |
| WRLP84-87 | 2017 | Food | II | 399 | 14 | 10088 | − | − |
| WRLP88-89 | 2017 | Environment | II | 399 | 14 | 10088 | − | − |
| WRLP90-93 | 2017 | Food | II | 399 | 14 | 10088 | − | − |
| Facility #131 | ||||||||
| WRLP96 | 2016 | Environment | I | 6 | 6 | 10,089 | − | − |
L. monocytogenes isolate characterization and distribution of heavy metal and antimicrobial tolerance-related genes.
Isolates described by , .
There was a total of nine STs, belonging to nine CCs (Table 1). The majority (n = 66) of isolates were ST/CC11, followed by ST399/CC14 (n = 12), ST/CC7 (n = 3), ST/CC224 (n = 1), ST2803/CC226 (n = 1), ST/CC288 (n = 1) and the previously described hypervirulent ST/CC1 (n = 2; WRLP73 and WRLP80), ST397/CC4 (n = 1; WRLP74), and ST/CC6 (n = 1; WRLP96) (Maury et al., 2016) (Figure 1; Table 2). One ST was identified as novel: ST2803, belonging to CC226. Based on the cgMLST data, there were 11 CTs identified within this sample set, with CT6558 (ST/CC11) isolated at the highest frequency (n = 65), including isolates from food, FCS, and NFCS sources (Figure 1). Less commonly, isolates belonged to CT10088 (ST399, CC14; n = 12) and CT10086 (ST/CC7; n = 3), while only one isolate was seen in each CT252 (ST/CC1), CT6441 (ST/CC1), CT6544 (ST/CC288), CT6679 (ST/CC224), CT6720 (ST397, CC4), CT10087 (ST/CC11), CT10089 (ST/CC6), and CT10475 (ST2803, CC226) (Figure 1; Table 2). Based on sigB profiling, six different allelic types (ATs) were also identified, with the most common being AT 6 (n = 78), followed by AT 1 (n = 4), AT 2, and AT 4 (each n = 2), and single isolates belonging to each AT 3 and AT 13 (Table 1).
Isolate diversity varied between facilities. Two facilities (#106 and #131) each had only one isolate recovered, limiting analyses within the facility (Table 1). Facility #14 had two isolates recovered, in different years, both with distinct ST, CC, CT, and sigB AT profiles (Table 1). In contrast, 12 isolates recovered in facility #122 in the same year all had the same ST, CC, CT, and sigB AT profiles (Table 1). The majority of the analyzed isolates came from facility #71, recovered from 2007 to 2016. This facility also had the highest isolate diversity, with 72 isolates belonging to five ST, CC, and sigB AT profiles and six CTs (Table 1). Novel CTs were recovered from four of the five facilities sampled. Specifically, five novel CTs were discovered, including two novel CTs recovered from facility #14 (CT10475 and CT10087), and one novel CT isolated from each of these facilities #71 (CT10086), #122 (CT10088), and #131 (CT10089) (Table 2).
3.2 SNP analysis
The pairwise SNP differences among the isolates ranged from 0 to 103,956 (Supplementary Figure S1). As expected from the genetic distance between lineages, the largest SNP difference was seen between a lineage I strain, WRLP74 (ST397/CC4), and a lineage II strain, WRLP94 (ST2803/CC226), recovered from facilities #71 and #14, respectively (Figure 2; Supplementary Figure S1). For the CTs containing more than one isolate, pairwise SNP differences varied from 0–33 (CT6558) and 92–139 (CT10086) to 9–237 (CT10088) (Supplementary Figure S1). We next mapped facility information onto the MSN to infer transmission patterns and potential for persistent populations. The most remarkable pattern was observed for facility #71. It had a diversity of isolates from both lineages I and II, consistent with multiple, separate introductions. However, the majority of isolates (n = 63) grouped into a single genotype (ST/CC11; Figure 2). Given that members of this genotype were collected throughout the 9 years of sampling (Table 2), this pattern is less likely explained by introduction of a large population and more consistent with the presence of a persistent population. Facility #122 also had numerous isolates, and all but one pair were categorized into unique genotypes, with SNP differences ranging from 36 to 159 (Figure 2). When compared to isolates from other facilities, isolates from facility #122 had a minimum of 9,314 and a maximum of 100,056 SNP differences (Figure 2; Supplementary Figure S1). Facility #14 had two isolates (WRLP94 and WRLP95; ST2803/CC226 and ST/CC11, respectively) recovered, and they had 31,881 pairwise SNP differences (Supplementary Figure S1). Though ST11 was observed in more than one facility, the isolate collected from facility #14 (WRLP95) and a cluster of 65 ST11 isolates from facility #71 differed by 744–778 pairwise SNP differences (Figure 2; Supplementary Figure S1).
Figure 2
3.3 Genetic elements associated with stress tolerance
A low frequency of genes and genetic elements associated with stress tolerance and antimicrobial resistance (AMR) was seen among the isolates (Table 2; Figure 3). Importantly, genes and genetic elements present in more than one isolate were also seen in other isolates belonging to the same ST/CC. The bcrABC cassette, associated with tolerance to quaternary ammonium compounds, was identified in the genome sequence of only one isolate (WRLP95; ST/CC11) (Table 2). Other genes associated with AMR and stress tolerance (e.g., tetR, qacC, qacH, tnpABC, and emrC) were not identified in any genome sequences examined. Also, none of the genomes possessed the Listeria genomic island (LGI) 1, cadA4, emrE, or the arsenic resistance gene cassette located in the LGI2. However, genetic determinants associated with the tolerance to the heavy metal cadmium (cadA1 or cadA2) were detected in the genome sequences of isolates recovered from three facilities (#14, #71, and #106) (Table 2). Specifically, cadA1 was found in 75% (66/88) of isolates, whereas the cadA2 gene was only identified in WRLP81 (ST/CC288). Notably, the cadA1 gene was identified in 65 (91%) isolates from facility #71, and one of two isolates recovered from facility #14 (all ST/CC11).
Figure 3

Presence of genetic elements associated with virulence and stress response in L. monocytogenes isolates recovered from dairy facilities. The phylogenetic tree, based on SNP data, was obtained using IQ-TREE version 1.6.12 with the parameters -bb 1000 and -alrt 1000. Shaded boxes indicate the presence of the genetic element; white boxes indicate the absence of the genetic element; x indicates insertion(s) or deletion(s) identified within the respective gene or genetic element. No premature stop codons (PMSCs) were identified in any genes containing insertions or deletions. Genetic elements with different colored boxes have differing genetic functions.
The stress survival islet (SSI-1) was only identified in isolates within facility #71, including isolates recovered in 2009 (DE25-1, WRLP8, and WRLP9; ST/CC7) and 2012 (WRLP70; ST/CC224) (Figure 3). When comparing the SSI-1 genes of these four isolates, three isolates recovered in 2009 (DE25-1, WRLP8, and WRLP9; ST/CC7) had no SNP differences across all five genes in SSI-1. The isolate that was recovered in 2012, WRLP70 (ST/CC224), had two SNP differences in lmo0447, three SNP differences in lmo0445, four SNP differences in lmo0446 and lmo0448, and 11 SNP differences in lmo0444 gene as compared to the SSI-1 genes from the 2009 isolates.
3.4 Presence of virulence genes
A select number (n = 92) of genes and genetic elements known to confer virulence were investigated in all isolates, with the results indicating a high level of variability in their presence/absence and sequence similarity (Figure 3). Overall, there were 50 virulence genes present in all isolates, 16 virulence genes absent in all isolates, and 26 genes present within a subset of the isolates. Premature stop codons (PMSCs) were not observed in any of the inlA and inlB genes. However, a 9-bp internal deletion within inlA was found in WRLP96 (nt 2212 to 2220; ST/CC6). Other internalin genes were observed in all or a subset of isolates. Specifically, inlC, inlC2, inlD, inlE, inlH, inlJ, and inlK were present in all 88 tested isolates, whereas the presence of other internalins was dependent on lineage and clonal complex. Specifically, inlF was present in all lineage I isolates and 4/82 (5%) lineage II isolates (ST/CC7: DE25-1, WRLP8, and WRLP9; and ST2803/CC226: WRLP94). With the exception of WRLP96 (ST/CC6), all lineage I isolates, and one lineage II isolate (WRLP94) had a 6-bp insertion at nt 999 within inlF. Similarly, inlG was found in five isolates, belonging to ST/CC7, ST2803/CC226, and ST/CC6. Three isolates from facility #71, belonging to ST/CC7, harbored inlL, whereas inlI was present in most of the tested isolates, with the exception of ST399/CC14 (WRLP82-93) and ST2803/CC226 (WRLP94) isolates. For all lineage I isolates, indel mutations were present in the inlI gene. Similarly, a 3-bp insertion (nt 87) was present in the inlD gene of all lineage I isolates. Several isolates contained a 210-bp insertion (at nt 1830; n = 18) and some isolates exhibited a 15 bp deletion (at nt 2607; n = 6) in inlJ; whereas the majority of isolates (n = 85) possessed insertions within inlK when aligned to a reference strain (EGDe; accession no. NC_003210) (Supplementary Table S2).
The presence of other virulence genes varied depending on lineage, CC, and facility of isolate origin (Figure 3). The adhesion gene ami was absent in all lineage I isolates from facility #71, one isolate from facility #122 (WRLP88; lineage II; ST399/CC14), and one isolate from facility #131 (WRLP96; lineage I; ST/CC6). Conversely, vip was absent from most of the facility #71 isolates, with the exception of the four lineage I isolates (WRLP70, WRLP73, WRLP74, and WRLP80), which all had nucleotide insertions within the gene. The vip gene was also found in isolates recovered from facility #106 (WRLP81; lineage I; ST/CC288), facility #122 (WRLP82-WRLP93; lineage II; ST399/CC14) and facility #131 (WRLP96; lineage I; ST/CC6). A gene associated with vacuolar escape, comK, was present in all lineage I isolates and two lineage II isolates from facility #71, all isolates from facility #122, and one isolate in each facility #14 and #131. Genes lapB, lntA, oatA, and svpA were present in all isolates. However, insertions were identified in the lapB and oatA genes of all lineage I isolates, and 6 bp and 15 bp insertions were identified in the lntA and svpA genes, respectively, within WRLP70 (ST/CC224). For the teichoic acid synthesis genes, all isolates either contained gltA and gltB or tagB. Specifically, gltA and gltB were present in 4/6 lineage I isolates (WRLP73, WRLP74, WRLP80, and WRLP96), whereas tagB was present in all other isolates. The invasion gene aut, or its allelic form aut_IVb, was present in all isolates within this dataset, with a 18 bp deletion noted at nt 261 in WRLP96 (ST/CC6). For the iap (also known as chwA) gene, indel mutations were present in all isolates except those belonging to ST/CC7 (DE25-1, WRLP8, and WRLP9).
For the Listeria pathogenicity islands, all six LIPI-1 genes (prfA, plcA, hlyA, mpl, actA, and plcB) were present in all the L. monocytogenes isolates examined (Figure 3). However, a 105 bp internal deletion in actA was observed in the isolates belonging to ST/CC1, ST397/CC4, and ST/CC288 (WRLP73 and WRLP80, WRLP74, and WRLP81, respectively) at nt position 793. LIPI-2 was not detected in any of the isolates, while LIPI-3 and LIPI-4 were only found among lineage I isolates. All six lineage I isolates possessed LIPI-3 genes (llsG, llsH, llsX, llsB, llsY, llsD, llsP, and llsA), while WRLP74, belonging to ST397/CC4, was the only isolate possessing LIPI-4.
4 Discussion
Understanding the population dynamics and diversity of L. monocytogenes found in frequently consumed food commodities within a region is essential for effective public health risk management, disease surveillance and prevention of food contamination. The L. monocytogenes isolate set recovered through the BC Dairy Inspection Program provided the opportunity to use whole genome sequencing information to investigate population diversity of isolates recovered in dairy facilities located within the same geographic region over a long period of time, improving our understanding of L. monocytogenes genotypes within and across facilities, their virulence potential, and contamination and persistence events.
Although some of the dairy isolates characterized in this study belonged to hypervirulent CCs within lineage I and possessed unique virulence elements (Table 2), the majority (93%) of isolates belonged to lineage II. This is in contrast to findings from a large longitudinal study from France, which reported that lineage I strains were strongly associated with dairy products (Maury et al., 2019), and a large-scale longitudinal study of dairy farms in Spain, where lineage I accounted for 69% of isolates (Palacios-Gorba et al., 2021). While some studies have suggested that lineage II isolates are more often associated with foods and environments than clinical cases (Orsi et al., 2011; Maury et al., 2016), in Canada lineage II isolates, especially strains belonging to CC8, have been predominantly associated with outbreaks and sporadic cases of listeriosis for more than two decades (
When comparing isolates by CCs across the five dairy processing facilities, only ST/CC11 was found in more than one facility (facilities #71 and #14) (Table 2). This is not surprising, as previous studies in cheese processing (
These findings highlight the importance of using whole genome sequences and more discriminatory analyses, such as SNPs, to better understand potential contamination and persistence events and genetic diversity of L. monocytogenes contaminants within a facility (Figure 2). Within the BC isolate set, the group of 12 ST399/CC14/CT10088 isolates within facility #122 were clearly differentiated based on SNP differences (39–159 SNPs), suggesting highly similar but unique isolates. These genetic similarities could be the result of the same original contamination source, or less likely, they could be from separate contamination events. The group of 65 CT6558 isolates (ST/CC11), however, was less clearly separated, with isolates being indistinguishable or closely related based on SNP differences (0–33) (Figure 2). This highly similar group of isolates from the same facility (#71) suggests a potential harborage site and/or dispersal throughout the facility. Since these isolates were collected over multiple years (2007–2016), this further suggests persistence (Kwong et al., 2016) of a specific genotype occurring within facility #71.
While persistence has been speculated to be associated with stress response genes, such as genes associated with antimicrobial resistance and tolerance (e.g., bcrABC, qacC, or emrE) (
Genetic determinants for heavy metal resistance, however, were widely observed in BC isolates (Table 2). Similar results have been reported in other studies that examined dairy isolates, with resistance to heavy metal cadmium commonly seen (
Similarly, the presence of stress survival islet 1 (SSI-1), consisting of five genes that assist in L. monocytogenes survival under stress conditions, especially in acidic and elevated salt environments (Ryan et al., 2010), has been suggested to increase survival of L. monocytogenes in food industry environments. Since organic acids can be naturally found or added to fermented dairy products, it is likely that this islet is beneficial for L. monocytogenes survival in dairy facilities. However, SSI-1 was not highly prevalent among BC isolates, with only four isolates from the same facility (#71) possessing full length SSI-1 (Figure 3). Of particular interest, three of these isolates belonged to CC7, which has previously been shown to have a significantly higher tolerance to lactic acid compared to 14 other CCs studied by Myintzaw et al. (2022). Other studies have also proposed the presence of SSI-1 aiding in biofilm formation and increased adherence (
Studies have also suggested that in some L. monocytogenes strains the comK gene and prophage gene insertions can be used as markers to differentiate outbreak strains (
When classical markers associated with adhesion and invasion properties, such as internalins inlA and inlB, were examined, there were no PMSCs observed to suggest reduced invasion capacity (Nightingale et al., 2008;
Although the role of other internalins in virulence has not been clearly established, considering the presence, absence and mutations in these genes may offer a greater level of discrimination among L. monocytogenes strains. This has been suggested to be helpful in partial profiling to discriminate between suspected transient and persistent contamination events within a facility (
In the set of isolates analyzed in our study, mutations were identified in inlD, inlF, inlI, inlJ, and inlK (Figure 3). Most of these mutations were present in the lineage I isolates, except for inlJ mutations, which were also found in lineage II isolates from facility #122. In contrast to our findings, others have reported intact inlJ genes in L. monocytogenes isolates recovered from raw milk (
Similar to internalins, Listeria pathogenicity islands (LIPIs) have been traditionally used to further screen L. monocytogenes virulence potential (
When examining other pathogenicity islands, no isolates possessed LIPI-2. LIPI-3 was present in six isolates all belonging to lineage I, whereas LIPI-4 was seen in one isolate only, also belonging to lineage I (Figure 3). LIPI-3 genes encode for the hemolytic, cytotoxic virulence factor listeriolysin S (
Other virulence factors, such as vip and ami, have been explored in some studies as additional markers of virulence (Milohanic et al., 2001;
Similarly, the role of ami in L. monocytogenes virulence is not clear. While this gene has been found in other, nonpathogenic Listeria spp. including L. innocua and L. welshimeri (
5 Conclusion
By evaluating L. monocytogenes isolates obtained from dairy processing facilities across BC, insights were gained into the diversity of isolates within and across these facilities. Even though samples were collected based on a regulatory sampling assignment (i.e., not a predetermined experimental design), and not all samples yielded L. monocytogenes positive results, analyzing the collected isolates and conditions in the facility at the time of sampling can be useful in understanding population dynamics within facilities producing similar commodities in the region as well as in providing information about potential strain persistence within dairy environments. Outside of regulatory activities, the sporadic finding of positive samples in dairy environments highlights the importance of routine sampling with the intent to find the pathogen as part of an environmental monitoring program or other sampling plan within facilities to help reduce the risk of product contamination and illness risk to the consumer. Whole genome sequencing helped identify isolate similarities and differences, and several virulence and stress tolerance genetic markers that could be used by facilities to differentiate L. monocytogenes within their food production environment(s). These data also highlight that different lineages, clonal complexes and sequence types are dominant in dairy environments in different regions, especially between North American and European studies, cautioning researchers and authorities not to rely on studies from limited regions, whether longitudinal or short term, in risk assessment studies and models.
Statements
Data availability statement
The datasets presented in this study can be found in online repositories. The names of the repository/repositories and accession number(s) can be found at: Bioproject accession PRJNA998448.
Author contributions
SB: Data curation, Formal analysis, Methodology, Visualization, Writing – original draft, Writing – review & editing. RB: Data curation, Formal analysis, Visualization, Writing – review & editing. LM: Conceptualization, Writing – review & editing. SS: Conceptualization, Writing – review & editing. AW: Formal analysis, Methodology, Supervision, Validation, Visualization, Writing – review & editing. ER: Data curation, Writing – review & editing. JC: Supervision, Validation, Writing – review & editing. JK: Conceptualization, Formal analysis, Funding acquisition, Methodology, Project administration, Supervision, Visualization, Writing – original draft, Writing – review & editing.
Funding
The author(s) declare that financial support was received for the research, authorship, and/or publication of this article. The research was funded in part by the OSU Agricultural Research Foundation grant (ARF#9256A).
Acknowledgments
This research was supported in part by the OSU Agricultural Research Foundation grant (ARF#9256A), for which we are grateful. We extend our thanks to the Center for Quantitative Life Sciences at Oregon State University for WGS services and the Institute Pasteur teams for the curation and maintenance of the BIGSdb-Pasteur databases. We also thank the Department of Botany and Plant Pathology for its support of the computational infrastructure, and Andrea Domen and Joy Waite-Cusic for technical assistance and constructive feedback regarding this work.
Conflict of interest
The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.
Publisher’s note
All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations, or those of the publisher, the editors and the reviewers. Any product that may be evaluated in this article, or claim that may be made by its manufacturer, is not guaranteed or endorsed by the publisher.
Supplementary material
The Supplementary material for this article can be found online at: https://www.frontiersin.org/articles/10.3389/fmicb.2024.1304734/full#supplementary-material
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Summary
Keywords
Listeria monocytogenes, dairy environments, whole genome sequencing, genomic diversity, persistence
Citation
Brown SRB, Bland R, McIntyre L, Shyng S, Weisberg AJ, Riutta ER, Chang JH and Kovacevic J (2024) Genomic characterization of Listeria monocytogenes recovered from dairy facilities in British Columbia, Canada from 2007 to 2017. Front. Microbiol. 15:1304734. doi: 10.3389/fmicb.2024.1304734
Received
29 September 2023
Accepted
11 March 2024
Published
22 March 2024
Volume
15 - 2024
Edited by
Alexandre Lamas, University of Santiago de Compostela, Spain
Reviewed by
Jose Roberto Aguirre Sanchez, National Council of Science and Technology (CONACYT), Mexico
Sangmi Lee, Chungbuk National University, Republic of Korea
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© 2024 Brown, Bland, McIntyre, Shyng, Weisberg, Riutta, Chang and Kovacevic.
This is an open-access article distributed under the terms of the Creative Commons Attribution License (CC BY). The use, distribution or reproduction in other forums is permitted, provided the original author(s) and the copyright owner(s) are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms.
*Correspondence: Jovana Kovacevic, jovana.kovacevic@oregonstate.edu
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