Next Article in Journal
Fatty Acids Are Responsible for the Discrepancy of Key Aroma Compounds in Naturally Dried Red Goji Berries and Hot-Air-Dried Red Goji Berries
Previous Article in Journal
Nutritional and Antioxidant Valorization of Grape Pomace from Argentinian Vino De La Costa and Italian Cabernet Wines
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

Total Culturable Microbial Diversity of Food Contact Surfaces in Poultry and Fish Processing Industries After the Pre-Operational Cleaning Process

by
Luiz Gustavo Bach
1,
Gabriela Zarpelon Anhalt Braga
1,
Márcia Cristina Bedutti
1,
Layza Mylena Pardinho Dias
1,
Emanoelli Aparecida Rodrigues dos Santos
2,
Leonardo Ereno Tadielo
3,
Evelyn Cristine da Silva
2,
Jhennifer Arruda Schmiedt
1,
Virgínia Farias Alves
4,
Elaine Cristina Pereira De Martinis
5,*,
Fábio Sossai Possebon
2,
Vinicius Cunha Barcellos
1 and
Luciano dos Santos Bersot
1,*
1
Department of Veterinary Sciences, Palotina Campus, Federal University of Paraná (UFPR), Rua Pioneiro, 2153, Jardim Dallas, Palotina 85950-000, PR, Brazil
2
School of Veterinary Medicine and Animal Science, Botucatu Campus, São Paulo State University (UNESP), Distrito de Rubião Jr, SN, Botucatu 18618-681, SP, Brazil
3
Department of Animal Production and Food, State University of Santa Catarina, Lages 88040-900, SC, Brazil
4
Faculdade de Farmácia, Universidade Federal de Goiás, Goiânia 74605-170, GO, Brazil
5
Ribeirão Preto School of Pharmaceutical Sciences, University of São Paulo, Av. Prof. Dr. Zeferino Vaz, Vila Monte Alegre, Ribeirão Preto 14040-900, SP, Brazil
*
Authors to whom correspondence should be addressed.
Foods 2025, 14(13), 2387; https://doi.org/10.3390/foods14132387 (registering DOI)
Submission received: 11 April 2025 / Revised: 27 June 2025 / Accepted: 2 July 2025 / Published: 6 July 2025
(This article belongs to the Section Food Microbiology)

Abstract

This study assessed the viable and culturable microbial diversity that remained on equipment surfaces after hygiene procedures in Brazilian poultry and fish slaughterhouses. Food-contact surface samples were collected using sterile swabs in poultry (n = 50) and fish (Oreochromis niloticus, n = 50) slaughterhouses. The swab samples were used to prepare culture plates to recover viable and culturable cells. The grown plates were washed, and the total DNA of the cell suspension was extracted with a commercial kit. Sequencing of the total DNA extracted from cultures was targeted at the V3 and V4 regions of the 16S rRNA. DNA reads were analyzed by QIIME2 software, with results expressed in relative frequency (%RF). Alpha and beta diversity indexes were analyzed considering the spots of sample collection, type of industry, surfaces (smooth or modular), and materials (polypropylene, stainless steel, or polyurethane). The results showed that in the poultry slaughterhouse, the most abundant genera were Acinetobacter (27.4%), Staphylococcus (7.7%), and Pseudomonas (5.3%), while for the fish slaughterhouse, there was a higher abundance of Staphylococcus (27.7%), Acinetobacter (17.2%), and Bacillus (12.5%). Surface characteristics influenced the microbial diversity, with Acinetobacter spp. dominating modular surfaces and Staphylococcus spp. prevailing on smooth surfaces. The results obtained indicate there is an important resident microbiota that persists even after hygiene processes, and surface-specific cleaning strategies should be developed.

1. Introduction

Slaughterhouses are environments that need to be carefully monitored due to potential contamination by pathogenic and/or spoilage microorganisms, which represent a threat to public health and product quality [1,2,3].
To this end, Food Safety Management Systems (FSMSs) are applied, which are a set of processes, procedures, and tools, based on standards and regulations, developed to control hazards and ensure compliance with food safety requirements. These systems cover, among other things, prerequisite programs such as Good Hygiene Practices (GHPs) and Sanitation Standard Operating Procedures (SSOPs) [4,5].
In this scenario, the implementation of SSOPs is key to preventing foodborne diseases since it recommends routine pre-operational cleaning and sanitation [6,7]. Although these initial steps can significantly reduce microbial loads to acceptable levels, the total eradication of contaminants from processing environments is challenging due to several factors: (i) complex equipment design; (ii) different materials of food-contact and non-food-contact surfaces; (iii) extrinsic conditions, such as temperature and humidity; (iv) choice of sanitizers; (v) composition of food matrices or debris; and (vi) microbial diversity [8,9].
Industries usually assess the effectiveness of SSOPs by monitoring indicator microorganisms. This monitoring is performed by counting these microorganisms, which directly measures viable microbial cells, or using other techniques, such as bioluminescence assays, which indirectly detect their presence [10,11]. Although these methods are useful for routine monitoring, they provide a limited view of the whole microbial diversity in the processing environment. To more comprehensively characterize the bacterial diversity in different matrices, researchers have applied metagenomic approaches, which can be defined as DNA analysis of microbial communities in a sample without the need for prior culture [12]. Sequencing of the metagenomic DNA targeting the 16S rRNA gene is of great interest since it harbors both conserved and variable regions of the bacterial genome [13,14,15,16]. The DNA reads obtained can be compared with reference genetic databases to estimate the taxonomic profile of the environmental samples analyzed [17]. Furthermore, the metataxonomic results can be used to calculate the distribution of microbial populations within a single sample (alpha diversity) and among different samples (beta diversity) [18]. These indexes can help in understanding the microbial ecology of the slaughtering environment because they are supported by more robust data in comparison with traditional methods [19,20].
Despite these advantages, the analysis of metagenomic DNA does not precisely indicate whether the microorganism whose DNA was detected was dead or alive. It has been shown that the presence of an intrinsic microbiota in food industries is not uncommon, with transient and recalcitrant members in the environment [21,22]. However, studies are lacking to show the microbial diversity after pre-operational sanitation in chicken and fish slaughterhouses, especially in Brazil. This information is crucial to improving control strategies to eradicate viable microorganisms that survive SSOPs.
Based on these premises, the objective of the current study was to determine the profile of viable and cultivable microbial communities that survived pre-operational hygienic processes in Brazilian poultry and fish slaughterhouses, combining a culture approach with high-throughput DNA sequencing.

2. Materials and Methods

2.1. Sampling Procedures

Samplings were conducted in the cutting rooms of two food processing units located in the South and Midwest regions of Brazil. Both slaughterhouses had permission to export their products with official registration by the Brazilian Federal Inspection Service. The fish plant processed mainly Oreochromis niloticus (Nile tilapia) with the capacity to slaughter around 150,000 animals/day, and the poultry abattoir slaughtered up to 204,000 animals/day. The animals came from intensive farming systems in the region of the slaughterhouses. Tilapia were raised in excavated ponds, with slaughter conducted between 8 and 9 months of age at a weight of approximately 1 kg. Transport was carried out with the fish alive, in tanks containing potable water and an oxygen supply. Poultry were housed in climate-controlled sheds and slaughtered at approximately 42 days of age, with an average weight of 2.5 kg. Transport was carried out with the animals alive and placed in transport crates.
The temperatures of the cutting rooms were standardized at 12 °C throughout the study. The process of surface sanitization in the cutting rooms consisted of a pre-wash with pressurized water at a temperature of approximately 50 °C. After removing visible residual material, a neutral semi-pasty detergent was applied at a concentration of 3% to 6% using a foam generator. Next, manual scrubbing was performed on surfaces in direct contact with the product, using synthetic fibers and a chlorinated alkaline detergent solution at a concentration of 1% to 4%. After a minimum contact time of 10 min, a rinse with pressurized water at approximately 50 °C was carried out. Finally, a peracetic-acid-based sanitizer was applied at a concentration of 0.1%. Samplings were carried out over 10 consecutive weeks, from June to August 2023.
Samples were collected from food-contact surfaces composed of materials such as polypropylene, polyurethane, and stainless steel, commonly used in poultry and fish slaughterhouses. The points of collection are described in Table 1. These surfaces were selected because they were directly involved in the handling and transportation of food and were included in the SSOPs for routine cleaning and sanitation. In addition, their structural characteristics and the susceptibility to abrasion make them potential sites for the persistence of microorganisms and critical points for hygiene monitoring. To collect samples, surfaces of the poultry (n = 50) and fish (n = 50) slaughterhouses were swabbed with the aid of sterilized molds measuring 10 × 10 cm, totaling 400 cm2 for each sample [22,23]. The swabs collected were placed in 10 mL of saline solution composed of 0.85% sodium chloride (w/v), 0.1% bacteriological peptone (w/v), and 0.5% TweenTM 80 (v/v) from Sigma Aldrich (St. Louis, MO, USA) as a neutralizing agent [24].

2.2. Sample Processing

The cell suspensions obtained from the swabs for each sampling point (400 cm2) were surface-plated (0.1 mL) on Plate Count Agar (PCA, Kasvi, São José dos Pinhais, Paraná, Brazil). After incubation at 36 ± 1 °C for 48 ± 2 h [25], the bacterial community that grew on each plate was harvested by washing with 3 mL of sterilized saline (sodium chloride 0.85 w/v) and transferred by pipette to 5 mL cryotubes to be kept frozen (−20 °C) for further analyses.

2.3. Identification of Microbial Diversity Through 16S rRNA Gene Sequencing

Sequencing of 16S rRNA genes for the culturable microbial community from agar plates was performed at the Institute of Biotechnology (IBTEC), São Paulo State University (UNESP), Botucatu Campus, São Paulo, Brazil. Genetic material was extracted using the commercial MagMAX CORE Nucleic Acid Purification Kit (Applied Biosystems™, Waltham, MA, USA) following the manufacturer’s instructions. Purity assessment was performed using the NanoDrop® ND-1000 UV–Vis (Thermo Fisher Scientific, Waltham, MA, USA) equipment. Extracted genetic material was quantified using a Qubit™ 2.0 fluorometer (Invitrogen, Waltham, MA, USA) and the Qubit™ 1X dsDNA High Sensitivity Kit (Invitrogen, Waltham, MA, USA). Considering the manufacturer’s recommendations, samples with 5 ng/µL of genomic DNA were considered for the sequencing step. The V3 and V4 regions of the 16S rRNA gene were used for sequencing on MiSeq equipment (Illumina Inc., San Diego, CA, USA) using the 600-cycle V3 kit. Library preparation consisted of amplification of primers for the V3–V4 region of the 16S rRNA gene (5′-TCGTCGGCAGCGTCAGATGTGTATAAGAGACAGCCTACGGGNGGCWGCAG-3′; 5′-TCTCGTGGGCTCGGAGATGTGTATAAGAGACAGGACTACHVGGGTATCTAATCC-3′; following Klindworth et al. [26] (Illumina Inc., San Diego, CA, USA)). The preparation steps followed the instructions of the 16S Metagenomic Sequencing Library Preparation protocol proposed by Illumina (Illumina Inc., San Diego, CA, USA). Bioinformatics analyses were conducted using QIIME2 software to process sequences and evaluate reads [27]. The DEBLUR program [28] was used to remove lower-quality reads and to categorize the reads into features. For alignment and phylogenetic analysis of the features, MAFFT (Multiple Alignment using Fast Fourier Transform) and FastTree v2.1.11 software were used. The features were taxonomically classified using the SILVA database [29].

2.4. Statistical Analysis

The results of 16S rRNA gene sequencing were expressed in operational taxonomic units (OTUs) to calculate the relative frequency (%RF) for phyla, orders, classes, families, genera, and species (whenever possible) for each slaughterhouse. Alpha diversity (Shannon’s diversity index, observed features, Faith’s phylogenetic diversity, and evenness) and beta diversity (Jaccard distance, Bray–Curtis distance, unweighted UniFrac distance, and weighted UniFrac distance) were compared between sample groups of collection points (different processing locations), origin (type of food—poultry or fish), surface (smooth and modular), and material (polypropylene, stainless steel, or polyurethane) using nonparametric tests. Alpha and beta diversity results were expressed graphically using principal coordinates analysis (PCoA). Differences in relative abundances of taxa were assessed by the ANCOM test [30]. A Venn diagram was constructed using Venny 2.1 (https://bioinfogp.cnb.csic.es/tools/venny/, accessed on 4 March 2025) to analyze and describe bacterial genera with RF > 1% for the smooth and modular surfaces.

3. Results

3.1. Description of Viable and Culturable Microbial Diversity in Poultry and Fish Slaughterhouses After Pre-Operational Sanitation Process

Microbial ecology was determined for 51 samples, 23 (46%) from the poultry slaughterhouse and 28 (56%) from the fish slaughterhouse (Table 2). The excluded samples from the poultry slaughterhouse included 20 (40%) samples with no colony growth on PCA plates and a further 7 (14%) samples, of which 6 had insufficient DNA for sequencing and 1 failed due to poor read quality. In the fish slaughterhouse, 22 (44%) samples were excluded due to the absence of colony growth. The absence of growth on some surfaces may be related to the effectiveness of the sanitization process. Bacterial growth was observed on culture plates regardless of surface type, with microorganisms recovered from both types. A total of 3,047,863 16S rRNA gene sequences were obtained, as follows: 1,817,491 reads from the poultry slaughterhouse (mean = 79,021; minimum = 31,455; maximum = 845,530) and 1,230,372 reads from the fish slaughterhouse (mean = 43,942; minimum = 31,988; maximum = 55,474).
With this approach that combined culture with high-throughput DNA sequencing, all detected taxa at the family, genus, and species levels were reported, with no relative abundance threshold applied. Considering both processing environments, 30 bacterial families were identified. In the poultry slaughterhouse, the highest RF rates comprised Moraxellaceae (29.8%), Microbacteriaceae (8.1%), Staphylococcaceae (7.7%), Pseudomonadaceae (5.3%), and Enterobacteriaceae (3.6%), as shown in Figure 1. In the fish slaughterhouse, the families Staphylococcaceae (18.8%), Moraxellaceae (16.9%), Microbacteriaceae (14%), Enterobacteriaceae (12.3%), and Bacillaceae (8.5%) prevailed (Figure 2).
Regarding genera, 35 were identified in both processing environments. In the poultry slaughterhouse, the most abundant ones were Acinetobacter (27.4%), Staphylococcus (7.7%), Pseudomonas (5.3%), Aeromonas (3.1%), and Streptomyces (3.1%), as shown in Figure 3. On the other hand, in the fish slaughterhouse, the most frequent genera identified were Staphylococcus (27.7%), Acinetobacter (17.2%), Bacillus (12.5%), Pseudomonas (9.6%), and Enterococcus (7.1%), as shown in Figure 4.
Due to 16S rRNA gene sequencing limitations, particularly regarding its resolution at the species level, only a few species could be identified. For the poultry slaughterhouse, sequencing analysis of viable and culturable microorganisms revealed the presence of five species, including Acinetobacter defluvii (1.5%), Microvirgula aerodenitrificans (0.01%), Sphingobacterium spiritivorum (0.008%), Bacteroidetes bacterium (0.005%), and Acinetobacter guillouiae (0.002%). In the fish slaughterhouse, four species were identified, as follows: Acinetobacter guillouiae (0.14%), Pseudomonas geniculata (0.04%), Bacteroidetes bacterium (0.006%), and Acinetobacter defluvii (0.005%).

3.2. Alpha and Beta Diversity

The microbial diversity of the slaughterhouses was assessed by cultures obtained from swabs, combined with high-throughput DNA sequencing. The results from alpha diversity (richness and uniformity within the sample) and beta diversity (dissimilarity comparing different samples) demonstrated that the type of equipment surface (smooth or modular) was the only factor that influenced alpha diversity, as indicated by the Shannon index (p = 0.026) and observed features (p = 0.036), shown in Table 3. The point of sampling, the type of material, and the type of food (poultry or fish) did not significantly influence the metrics evaluated.
Regarding beta diversity, the surface type was the only parameter that significantly influenced microbial dissimilarity, as evidenced by the Jaccard distance (p = 0.025) and PCoA graphic (shown in Table 3 and Figure 5, respectively).
Although no statistically significant difference was observed (p > 0,05) using ANCOM analysis to assess microbial diversity, considering the genera with RF > 1% on modular and smooth surfaces, a Venn diagram was created to better portray the occurrence of the groups of microorganisms observed (Figure 6). The comparative analysis revealed the presence of eight genera (53.3%) in both types of surfaces, while four genera (26.7%) were exclusive to the smooth surface, and three (20%) were exclusive to the modular surface. The Acinetobacter genus was the most abundant genus observed on the modular surface, representing 44.3%. On the other hand, on the smooth surface, Staphylococcus was the most predominant genus, corresponding to 28% of the observed microorganisms.

4. Discussion

It has been shown that the ecology of industrial food processing environments depends on various factors, such as animal microbiota, possible failures in the sanitation processes, the presence of organic residues, and the type of processing surface [19,22,31]. In this sense, it is very important to avoid cross-contamination between products and contact surfaces by implementing environmental monitoring programs [32]. This presumes the use of different techniques to evaluate the efficiency of pre-operational sanitation processes, such as visual inspection, bioluminescence, and microbiological analysis. However, none of these tests offer a detailed description of environmental microbial diversity, which is key information to combat bacterial contaminants.
This study was conducted to provide a clearer picture of the microbial profile found post-sanitation in fish and poultry processing environments. The experimental design proposed started with a culture step before the amplicon-based high-throughput DNA sequencing, which is key to demonstrating the presence of viable and culturable cells that are recalcitrant to the use of sanitizers. Moreover, this combined culture-dependent and culture-independent approach provides an opportunity for viable and culturable cells to produce more signals than the background dead cells [33]. Sequencing of the 16S rRNA gene has been used to evaluate the dynamics of microbial communities in animal product processing environments, as well as to assess factors that interfere with microbial colonization and persistence after pre-operational sanitation [34,35].
To our knowledge, this is the first study in Brazilian slaughterhouses to characterize the microbial diversity of poultry and fish cutting rooms after pre-operational sanitation using a combined approach of culture-dependent and high-throughput culture-independent techniques.
In this study, it was possible to characterize the bacterial diversity in poultry and fish slaughterhouses by sequencing the totality of 16S rRNA genes from cultures obtained from 51 samples, showing that both alpha and beta diversities were influenced by the type of surface (Table 3). Alpha diversity, assessed by the Shannon index (p = 0.026) and observed features (p = 0.036), revealed significant differences in both richness and uniformity within the samples. Furthermore, beta diversity was essential for comparing the microbial communities between the two industries, with the Jaccard distance showing a significant difference (p = 0.025) [18]. These results suggest bacterial colonization and survival were possibly influenced by the presence of irregular and recessed surfaces (such as in modular equipment), which may favor bacterial adherence and hinder the homogeneous dispersion of sanitizing agents, favoring biofilm formation [36]. Similarly, Tadielo et al. [37] also reported that modular-type polypropylene conveyors exhibited significantly greater microbial contamination than smooth-type polystyrene conveyors before the cleaning process, reinforcing that surface characteristics play a crucial role in microbial retention and contamination dynamics in food processing environments.
Moreover, the results of the present study revealed that the sample source did not significantly influence diversity indexes, and three genera were highly prevalent in the poultry and fish industry, namely Acinetobacter, Staphylococcus, and Pseudomonas (Figure 3 and Figure 4).
These results are consistent with those from Tadielo et al. [37], who reported increased RF of Acinetobacter sp. and Pseudomonas sp. in a chicken slaughterhouse after the pre-operational hygiene process in Brazil. These findings are corroborated by Sinlapapanya [38], who also found Acinetobacter sp. and Pseudomonas sp. after the cleaning and sanitation in a fish processing establishment located in Thailand. According to Møretrø & Langsrud [21], Acinetobacter sp. and Pseudomonas sp. are usually found in the same niches in food processing plants because they present similar growth and survival characteristics, with the ability to tolerate harsh conditions.
The Acinetobacter genus is commonly found both in chicken and fish meat [16,39], as well as on industrial surfaces used for food handling [40,41]. Its environmental prevalence may be related to the contamination of raw materials in contact with soil, water, and vegetation [42]. Moreover, it may tolerate low temperature, low availability of nutrients, cleaners/disinfectants, and shear forces [21], which may favor biofilm formation [38,43]. It is interesting to note that Acinetobacter sp. can dominate multispecies biofilms in vitro [44], which may partially explain its high prevalence (44.3%) on the surface of modular equipment observed in the present study. In addition, Acinetobacter spp. has been recognized for its ability to acquire and disseminate antimicrobial resistance genes, enabling the emergence of microorganisms with a multidrug-resistant phenotype [45,46]. This characteristic, combined with the potential for biofilm formation and the ability to persist in food processing environments, represents significant concerns for food safety, since it can contribute to the transmission of resistant or multidrug-resistant strains through cross-contamination along the food processing chain [47].
Pseudomonas spp. are psychrotrophic bacteria with a high ability to adapt to diverse environments, which can be attributed partially to the presence of many regulatory genes in their genome [48]. The ability of biofilm formation by Pseudomonas sp. is very important in food processing environments because it not only protects the bacterium against sanitizers, but this species has also been regarded as a primary colonizer that facilitates the adhesion of other bacteria [49,50,51]. This genus is recognized as a member of the natural microbiota of poultry [52] and fish [53], which helps to explain the high prevalence observed in this study. Other authors have reported that Pseudomonas sp. is a major contaminant in environments where the processing of animal products takes place [22,54].
On the other hand, in this study, the highest prevalence of Staphylococcus spp. was observed in the fish industry (27.7%). Considering that staphylococci are commonly found in skin and mucous tissues of humans and animals, the presence of this microorganism in food processing environments may suggest inadequate food handling practices [55]. Besler & Kılınç [56] evaluated the effect of various sanitizers on Staphylococcus sp. isolates from the fish slaughter industry, reporting that lower concentrations of the antimicrobial compounds tested did not present bactericidal action. In addition, those authors reported that staphylococci were highly prevalent (28%) on smooth surfaces (e.g., stainless steel), which may indicate their strong ability to form biofilms [57].
In the poultry abattoir investigated in this study, Aeromonas (3.1%) and Streptomyces (3.1%) were also highly abundant, which is consistent with their widespread presence as part of the microbiota of these animals [58,59]. Aeromonas sp. is a strong biofilm former [60], besides being tolerant of sanitizers in chicken slaughtering plants [37].
In the fish processing industry evaluated in this research, Bacillus (12.5%) and Enterococcus (7.1%) were also among the most prevalent genera. Bacillus sp. has a high ability to adapt to diverse environments, besides being able to form spores, presenting tolerance to very stressful conditions [38,61]. Concerning enterococci, Mendoza et al. [62] reported a high prevalence in several spots of a production chain of Nile tilapia, besides their presence in the water and healthy animals. The presence of enterococci in the fish processing chain is possibly an indicator of water contamination.
Considering that metagenomic DNA analysis does not distinguish between live and dead microorganisms, prior cultivation becomes a methodology that enables the exclusive evaluation of viable and culturable cells present in the samples. The use of prior cultivation followed by 16S rRNA gene sequencing has been employed to characterize the microbial diversity of food processing facilities [43,63]; milk, dairy products, and cheese [63,64]; plant-based products [65]; human milk [66]; as well as in the characterization of the microbiota of humans [67,68] and livestock animals [69]. However, this approach does not account for viable but non-culturable (VBNC) microorganisms, which also represent a challenge in assessing the effectiveness of sanitation procedures. These organisms remain metabolically active but lose the ability to grow on conventional culture media under laboratory conditions, making their detection difficult [70]. Nevertheless, the strategy adopted in our study focuses on the fraction of microorganisms with the greatest practical relevance to the food industry. These viable microorganisms are particularly important for evaluating the risk of cross-contamination and biofilm formation, both critical aspects in the control of industrial processes.
Peracetic acid is commonly used in the food industry because of its ability to inactivate microorganisms [71,72]. However, some bacteria may persist after the sanitization process, since several factors can compromise its effectiveness, including the concentration, time, and temperature of application [73], biofilm formation [74], and microbial interactions [51].
Therefore, the recovery of these viable isolates enables future studies aimed at identifying phenotypic and genetic factors associated with tolerance to sanitation programs, thereby enhancing the understanding of the mechanisms that favor microbial persistence in industrial environments and supporting the development of more effective and targeted control measures for food processing facilities [75,76].
In broad terms, the results of this study contributed to a better understanding of the resident microbial diversity of poultry and fish processing environments after pre-operation sanitation procedures. It was shown that the characteristics of the surfaces influenced the extent of microbial colonization, challenging the control strategies applied to control microbial contamination in different spots. The results also indicate the need for studies on microbial communities to evaluate the effectiveness of sanitizers and to develop novel strategies to combat microbial contamination in food processing plants.

5. Conclusions

This study revealed the presence of viable and culturable microbial diversity after the cleaning process, highlighting that surface characteristics influence the diversity observed. Acinetobacter was predominant on modular surfaces, while Staphylococcus prevailed on smooth surfaces. These results suggest that the type of equipment surface plays a critical role in shaping microbial communities in the food industry. Understanding this influence can support the development of more effective hygiene strategies, reinforcing food quality and safety.

Author Contributions

L.d.S.B., L.G.B., and G.Z.A.B.: conceptualization; L.d.S.B.: supervision; L.G.B., G.Z.A.B., M.C.B., L.M.P.D., E.A.R.d.S., L.E.T., E.C.d.S., J.A.S., V.F.A., E.C.P.D.M., F.S.P., V.C.B., and L.d.S.B.: methodology, investigation, formal analysis, and writing—original draft preparation; V.F.A., E.C.P.D.M., L.E.T., and L.d.S.B.: writing—review and editing. All authors have read and agreed to the published version of the manuscript.

Funding

This study was financed in part by the Coordination for the Improvement of Higher Education Personnel–Brazil (CAPES) Finance Code 001 for the scholarship of L.G.B., G.Z.A.B., and J.A.S.

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 author.

Acknowledgments

ECPDM and LSB are PQ-2 fellows from CNPq, Brazil (processes #306998/2022-0 and #308547/2021-7, respectively). ECPDM is also grateful to CNPq for a research grant (#407025/2021-9).

Conflicts of Interest

The authors declare that they have no actual or potential conflicts of interest, including any financial, personal, or other relationships with other people or organizations, that could have inappropriately influenced or be perceived to have influenced this work.

References

  1. Conter, M.; Rega, M.; Lamperti, L.; Andriani, L.; Bacci, C.; Bonardi, S. Comparing non-compliances and non-conformities: The different points of view of pig slaughterhouse operator, competent authority and customers. Food Control 2024, 160, 110366. [Google Scholar] [CrossRef]
  2. Reta, G.G.; Lopes, S.M.; Martins De Aquino, N.S.; Tondo, E.C. Quantification of Salmonella transfer in cross-contamination scenarios found in chicken slaughterhouses. Food Microbiol. 2023, 116, 104347. [Google Scholar] [CrossRef] [PubMed]
  3. Sui, L.; Yi, Z.; Xiao, X.; Ma, J.; Huang, H.; Xu, C.; Wang, W.; Qu, X. Investigation of microbial communities across swine slaughter stages and disinfection efficacy assessment in a pig slaughterhouse. LWT 2023, 187, 115334. [Google Scholar] [CrossRef]
  4. Huss, H.H.; Ryder, J. Assessment and Management of Seafood Safety and Quality. Available online: https://www.fao.org/4/y4743e/y4743e0h.htm (accessed on 13 June 2025).
  5. Rincon-Ballesteros, L.; Lannelongue, G.; González-Benito, J. Cross-continental insights: Comparing food safety management systems in Europe and Latin America. Food Control 2024, 164, 110552. [Google Scholar] [CrossRef]
  6. Antoci, S.; Iannetti, L.; Centorotola, G.; Acciari, V.A.; Pomilio, F.; Daminelli, P.; Romanelli, C.; Ciorba, A.B.; Santini, N.; Torresi, M.; et al. Monitoring Italian establishments exporting food of animal origin to third countries: SSOP compliance and Listeria monocytogenes and Salmonella spp. contamination. Food Control 2021, 121, 107584. [Google Scholar] [CrossRef]
  7. Alves, V.F.; Tadielo, L.E.; Pires, A.C.M.S.; Pereira, M.G.; Bersot, L.S.; De Martinis, E.C.P. Hidden places for foodborne bacterial pathogens and novel approaches to control biofilms in the meat industry. Foods 2024, 13, 3994. [Google Scholar] [CrossRef]
  8. Bernardes, P.C.; Araújo, E.A.; Pires, A.C.D.S.; Fialho Júnior, J.F.Q.; Lelis, C.A.; Andrade, N.J.D. Work of adhesion of dairy products on stainless steel surface. Braz. J. Microbiol. 2012, 43, 1261–1268. [Google Scholar] [CrossRef]
  9. Tang, X.; Flint, S.H.; Brooks, J.D.; Bennett, R.J. Factors affecting the attachment of micro-organisms isolated from ultrafiltration and reverse osmosis membranes in dairy processing plants. J. Appl. Microbiol. 2009, 107, 443–451. [Google Scholar] [CrossRef]
  10. Moazzami, M.; Bergenkvist, E.; Boqvist, S.; Frosth, S.; Langsrud, S.; Møretrø, T.; Vågsholm, I.; Hansson, I. Assessment of ATP-bioluminescence and dipslide sampling to determine the efficacy of slaughterhouse cleaning and disinfection compared with total aerobic and Enterobacterales counts. J. Food Prot. 2023, 86, 100155. [Google Scholar] [CrossRef]
  11. Corbitt, A.J.; Bennion, N.; Forsythe, S.J. Adenylate kinase amplification of ATP bioluminescence for hygiene monitoring in the food and beverage industry. Lett. Appl. Microbiol. 2000, 30, 443–447. [Google Scholar] [CrossRef]
  12. Almeida, O.G.G.; De Martinis, E.C.P. Bioinformatics tools to assess metagenomic data for applied microbiology. Appl. Microbiol. Biotechnol. 2019, 103, 69–82. [Google Scholar] [CrossRef] [PubMed]
  13. Kim, Y.; Ban, G.-H.; Hong, Y.W.; Jeong, K.C.; Bae, D.; Kim, S.A. Bacterial profile of pork from production to retail based on high-throughput sequencing. Food Res. Int. 2024, 176, 113745. [Google Scholar] [CrossRef] [PubMed]
  14. Yeom, J.; Bae, D.; Kim, S.A. Microbial dynamics of South Korean beef and surroundings along the supply chain based on high-throughput sequencing. Meat Sci. 2024, 214, 109520. [Google Scholar] [CrossRef] [PubMed]
  15. Zagdoun, M.; Coeuret, G.; N’Dione, M.; Champomier-Vergès, M.-C.; Chaillou, S. Large microbiota survey reveals how the microbial ecology of cooked ham is shaped by different processing steps. Food Microbiol. 2020, 91, 103547. [Google Scholar] [CrossRef]
  16. Zhang, J.; Ding, X.; Guan, R.; Zhu, C.; Xu, C.; Zhu, B.; Zhang, H.; Xiong, Z.; Xue, Y.; Tu, J.; et al. Evaluation of different 16S rRNA gene V regions for exploring bacterial diversity in a eutrophic freshwater lake. Sci. Total Environ. 2018, 618, 1254–1267. [Google Scholar] [CrossRef]
  17. De Filippis, F.; Parente, E.; Ercolini, D. Recent past, present, and future of the food microbiome. Annu. Rev. Food Sci. Technol. 2018, 9, 589–608. [Google Scholar] [CrossRef]
  18. Daly, A.J.; Baetens, J.M.; De Baets, B. Ecological diversity: Measuring the unmeasurable. Mathematics 2018, 6, 119. [Google Scholar] [CrossRef]
  19. De Filippis, F.; Valentino, V.; Alvarez-Ordóñez, A.; Cotter, P.D.; Ercolini, D. Environmental microbiome mapping as a strategy to improve quality and safety in the food industry. Curr. Opin. Food Sci. 2021, 38, 168–176. [Google Scholar] [CrossRef]
  20. Sequino, G.; Valentino, V.; Villani, F.; De Filippis, F. Omics-based monitoring of microbial dynamics across the food chain for the improvement of food safety and quality. Food Res. Int. 2022, 157, 111242. [Google Scholar] [CrossRef]
  21. Møretrø, T.; Langsrud, S. Residential bacteria on surfaces in the food industry and their implications for food safety and quality. Compr. Rev. Food Sci. Food Saf. 2017, 16, 1022–1041. [Google Scholar] [CrossRef]
  22. Tadielo, L.E.; Dos Santos, E.A.R.; Possebon, F.S.; Schmiedt, J.A.; Juliano, L.C.B.; Cerqueira-Cézar, C.K.; De Oliveira, J.P.; Sampaio, A.N.D.C.E.; Melo, P.R.L.; Caron, E.F.F.; et al. Characterization of microbial ecology, Listeria monocytogenes, and Salmonella sp. on equipment and utensil surfaces in Brazilian poultry, pork, and dairy industries. Food Res. Int. 2023, 173, 113422. [Google Scholar] [CrossRef] [PubMed]
  23. Soares, V.M.; Viana, C.; Pereira, J.G.; Destro, M.T.; Nero, L.A.; Bersot, L.D.S.; Paes De Almeida Nogueira Pinto, J. Absence of a continuous water spray system does not influence the microbiological contamination of the conveyor belts in chicken slaughterhouses. LWT 2018, 97, 414–418. [Google Scholar] [CrossRef]
  24. Beltrame, C.A.; Martelo, E.B.; Mesquita, R.A.; Barbosa, J.; Steffens, C.; Toniazzo, G.; Valduga, E.; Cansian, R.L. Adhesion of Listeria monocytogenes to cutting board surfaces and removal by different sanitizers. J. Verbr. Lebensm. 2015, 10, 41–47. [Google Scholar] [CrossRef]
  25. Ryser, E.T.; Schuman, J.D. 8. Mesophilic Aerobic Plate Count. In Compendium of Methods for the Microbiological Examination of Foods; APHA Press: Washington, DC, USA, 2013; pp. 95–101. [Google Scholar] [CrossRef]
  26. Klindworth, A.; Pruesse, E.; Schweer, T.; Peplies, J.; Quast, C.; Horn, M.; Glöckner, F.O. Evaluation of general 16S ribosomal RNA gene PCR primers for classical and next-generation sequencing-based diversity studies. Nucleic Acids Res. 2013, 41, e1. [Google Scholar] [CrossRef]
  27. Bolyen, E.; Rideout, J.R.; Dillon, M.R.; Bokulich, N.A.; Abnet, C.C.; Al-Ghalith, G.A.; Alexander, H.; Alm, E.J.; Arumugam, M.; Asnicar, F.; et al. Reproducible, interactive, scalable and extensible microbiome data science using QIIME 2. Nat. Biotechnol. 2019, 37, 852–857. [Google Scholar] [CrossRef]
  28. Amir, A.; McDonald, D.; Navas-Molina, J.A.; Kopylova, E.; Morton, J.T.; Xu, Z.Z.; Kightley, E.P.; Thompson, L.R.; Hyde, E.R.; Gonzalez, A.; et al. Deblur rapidly resolves single-nucleotide community sequence patterns. mSystems 2017, 2, e00191-16. [Google Scholar] [CrossRef]
  29. Quast, C.; Pruesse, E.; Yilmaz, P.; Gerken, J.; Schweer, T.; Yarza, P.; Peplies, J.; Glöckner, F.O. The SILVA ribosomal RNA gene database project: Improved data processing and web-based tools. Nucleic Acids Res. 2012, 41, D590–D596. [Google Scholar] [CrossRef] [PubMed]
  30. Mandal, S.; Van Treuren, W.; White, R.A.; Eggesbø, M.; Knight, R.; Peddada, S.D. Analysis of composition of microbiomes: A novel method for studying microbial composition. Microb. Ecol. Health Dis. 2015, 26, 27663. [Google Scholar] [CrossRef]
  31. Maes, S.; Heyndrickx, M.; Vackier, T.; Steenackers, H.; Verplaetse, A.; Reu, K.D. Identification and spoilage potential of the remaining dominant microbiota on food contact surfaces after cleaning and disinfection in different food industries. J. Food Prot. 2019, 82, 262–275. [Google Scholar] [CrossRef]
  32. Wiedmann, M.; Belias, A.; Sullivan, G.; David, J. Food and Beverage Environmental Monitoring Handbook. Available online: https://www.neogen.com/en/usac/neocenter/resources/food-beverage-environmental-monitoring-handbook/?utm_medium=SocialShare (accessed on 25 May 2025).
  33. De Martinis, E.C.P.; Duvall, R.E.; Hitchins, A.D. Real-Time PCR detection of 16S rRNA genes speeds most-probable-number enumeration of foodborne Listeria monocytogenes. J. Food Prot. 2007, 70, 1650–1655. [Google Scholar] [CrossRef]
  34. Doyle, C.J.; O’Toole, P.W.; Cotter, P.D. Metagenome-based surveillance and diagnostic approaches to studying the microbial ecology of food production and processing environments. Environ. Microbiol. 2017, 19, 4382–4391. [Google Scholar] [CrossRef] [PubMed]
  35. Hascoët, A.-S.; Ripolles-Avila, C.; Guerrero-Navarro, A.E.; Rodríguez-Jerez, J.J. Microbial ecology evaluation of an Iberian pig processing plant through implementing SCH sensors and the influence of the resident microbiota on Listeria monocytogenes. Appl. Sci. 2019, 9, 4611. [Google Scholar] [CrossRef]
  36. Verran, J.; Redfern, J.; Smith, L.A.; Whitehead, K.A. A critical evaluation of sampling methods used for assessing microorganisms on surfaces. Food Bioprod. Process. 2010, 88, 335–340. [Google Scholar] [CrossRef]
  37. Tadielo, L.E.; Dos Santos, E.A.E.; Possebon, F.S.; Schmiedt, J.A.; Orisio, P.H.S.; Juliano, L.C.B.; Cerqueira-Cézar, C.K.; Pinto, J.P.A.N.; Pereira, J.G.; Bersot, L.D.S. Preoperational cleaning processes interfere with microbial ecology and presence of Listeria monocytogenes and Salmonella spp. on food conveyor belts of a poultry slaughterhouse in Brazil. LWT 2023, 184, 115037. [Google Scholar] [CrossRef]
  38. Sinlapapanya, P.; Pelyuntha, W.; Vongkamjan, K. Diversity of sanitizer-resistant bacteria on food contact surface and handling equipment in squid sushi production line. Food Res. Int. 2025, 203, 115837. [Google Scholar] [CrossRef]
  39. Ghaffoori Kanaan, M.H.; Al-Shadeedi, S.M.J.; Al-Massody, A.J.; Ghasemian, A. Drug resistance and virulence traits of Acinetobacter baumannii from turkey and chicken raw meat. Comp. Immunol. Microbiol. Infect. Dis. 2020, 70, 101451. [Google Scholar] [CrossRef] [PubMed]
  40. Wagner, E.M.; Pracser, N.; Thalguter, S.; Fischel, K.; Rammer, N.; Pospíšilová, L.; Alispahic, M.; Wagner, M.; Rychli, K. Identification of biofilm hotspots in a meat processing environment: Detection of spoilage bacteria in multi-species biofilms. Int. J. Food Microbiol. 2020, 328, 108668. [Google Scholar] [CrossRef]
  41. Cherifi, T.; Arsenault, J.; Quessy, S.; Fravalo, P. Co-occurrence of L. monocytogenes with other bacterial genera and bacterial diversity on cleaned conveyor surfaces in a swine slaughterhouse. Microorganisms 2022, 10, 613. [Google Scholar] [CrossRef]
  42. Choi, J.-Y.; Kim, Y.; Ko, E.A.; Park, Y.K.; Jheong, W.-H.; Ko, G.; Ko, K.S. Acinetobacter species isolates from a range of environments: Species survey and observations of antimicrobial resistance. Diagn. Microbiol. Infect. Dis. 2012, 74, 177–180. [Google Scholar] [CrossRef]
  43. Naim, W.; Manetsberger, J.; Lavilla Lerma, L.; Benomar, N.; Caballero Gómez, N.; Cuesta-Bertomeu, I.S.; Gata Díaz, J.Á.; Abriouel, H. Impact of disinfection methods used in the slaughterhouse environment on microbiome diversity throughout the meat production chain. Curr. Res. Microb. Sci. 2025, 8, 100336. [Google Scholar] [CrossRef]
  44. Fagerlund, A.; Møretrø, T.; Heir, E.; Briandet, R.; Langsrud, S. Cleaning and disinfection of biofilms composed of Listeria monocytogenes and background microbiota from meat processing surfaces. Appl. Environ. Microbiol. 2017, 83, e01046-17. [Google Scholar] [CrossRef] [PubMed]
  45. Mahamat, A.; Bertrand, X.; Moreau, B.; Hommel, D.; Couppie, P.; Simonnet, C.; Kallel, H.; Demar, M.; Djossou, F.; Nacher, M. Clinical epidemiology and resistance mechanisms of carbapenem-resistant Acinetobacter baumannii, French Guiana, 2008–2014. Int. J. Antimicrob. Agents 2016, 48, 51–55. [Google Scholar] [CrossRef]
  46. Tsitsos, A.; Damianos, A.; Tsiouris, V.; Papapanagiotou, E.; Soultos, N.; Papa, A.; Tyrodimos, I.; Economou, V. Prevalence, seasonal variation, and proteomic relationship of β-lactamase-producing Escherichia coli, Klebsiella pneumoniae, and Acinetobacter spp. in poultry meat at the abattoir level in Greece. Food Microbiol. 2025, 128, 104709. [Google Scholar] [CrossRef]
  47. Malta, R.C.R.; Ramos, G.L.D.P.A.; Nascimento, J.D.S. From food to hospital: We need to talk about Acinetobacter spp. Germs 2020, 10, 210–217. [Google Scholar] [CrossRef] [PubMed]
  48. Gula, G.; Dorotkiewicz-Jach, A.; Korzekwa, K.; Valvano, M.A.; Drulis-Kawa, Z. Complex signaling networks controlling dynamic molecular changes in Pseudomonas aeruginosa biofilm. Curr. Med. Chem. 2019, 26, 1979–1993. [Google Scholar] [CrossRef] [PubMed]
  49. Pang, X.Y.; Yang, Y.S.; Yuk, H.G. Biofilm formation and disinfectant resistance of Salmonella sp. in mono- and dual-species with Pseudomonas aeruginosa. J. Appl. Microbiol. 2017, 123, 651–660. [Google Scholar] [CrossRef]
  50. Sterniša, M.; Gradišar Centa, U.; Drnovšek, A.; Remškar, M.; Smole Možina, S. Pseudomonas fragi biofilm on stainless steel (at low temperatures) affects the survival of Campylobacter jejuni and Listeria monocytogenes and their control by a polymer molybdenum oxide nanocomposite coating. Int. J. Food Microbiol. 2023, 394, 110159. [Google Scholar] [CrossRef]
  51. Voloshchuk, O.; Rolon, M.L.; Bartlett, K.V.; Mendez Acevedo, M.; LaBorde, L.F.; Kovac, J. Pseudomonadaceae increased the tolerance of Listeria monocytogenes to sanitizers in multi-species biofilms. Food Microbiol. 2025, 128, 104687. [Google Scholar] [CrossRef]
  52. Rychlik, I.; Karasova, D.; Crhanova, M. Microbiota of chickens and their environment in commercial production. Avian Dis. 2023, 67, 1–9. [Google Scholar] [CrossRef]
  53. Abril, A.G.; Calo-Mata, P.; Böhme, K.; Villa, T.G.; Barros-Velázquez, J.; Sánchez-Pérez, Á.; Pazos, M.; Carrera, M. Shotgun proteomic analyses of Pseudomonas species isolated from fish products. Food Chem. 2024, 450, 139342. [Google Scholar] [CrossRef]
  54. Barcenilla, C.; Cobo-Díaz, J.F.; Puente, A.; Valentino, V.; De Filippis, F.; Ercolini, D.; Carlino, N.; Pinto, F.; Segata, N.; Prieto, M.; et al. In-depth characterization of food and environmental microbiomes across different meat processing plants. Microbiome 2024, 12, 199. [Google Scholar] [CrossRef]
  55. Xu, X.; Rothrock, M.J.; Mishra, A.; Kumar, G.D.; Mishra, A. Relationship of the poultry microbiome to pathogen colonization, farm management, poultry production, and foodborne illness risk assessment. J. Food Prot. 2023, 86, 100169. [Google Scholar] [CrossRef] [PubMed]
  56. Besler, A.; Kılınç, B. An investigation of the efficacy of different disinfectants on Staphylococcus aureus and Pseudomonas fluorescens isolated from fish processing plant. Ege J. Fish. Aquat. Sci. 2023, 40, 228–234. [Google Scholar] [CrossRef]
  57. Da Silva Meira, Q.G.; De Medeiros Barbosa, I.; Alves Aguiar Athayde, A.J.; De Siqueira-Júnior, J.P.; De Souza, E.L. Influence of temperature and surface kind on biofilm formation by Staphylococcus aureus from food-contact surfaces and sensitivity to sanitizers. Food Control 2012, 25, 469–475. [Google Scholar] [CrossRef]
  58. Igbinosa, I.H. Antibiogram profiling and pathogenic status of Aeromonas species recovered from chicken. Saudi J. Biol. Sci. 2014, 21, 481–485. [Google Scholar] [CrossRef] [PubMed]
  59. Marmion, M.; Ferone, M.T.; Whyte, P.; Scannell, A.G.M. The changing microbiome of poultry meat; from farm to fridge. Food Microbiol. 2021, 99, 103823. [Google Scholar] [CrossRef]
  60. Rahman, M.A.; Akter, S.; Ashrafudoulla, M.; Rapak, M.T.; Lee, K.O.; Ha, S.D. Targeted insights into Aeromonas hydrophila biofilms: Surface preferences, resistance mechanisms, and gene expression. Poult. Sci. 2025, 104, 104851. [Google Scholar] [CrossRef]
  61. Reich, C.; Wenning, M.; Dettling, A.; Luma, K.E.; Scherer, S.; Hinrichs, J. Thermal resistance of vegetative thermophilic spore forming bacilli in skim milk isolated from dairy environments. Food Control 2017, 82, 114–120. [Google Scholar] [CrossRef]
  62. Mendoza, D.M.; Aquino, M.G.B.; Reyes, A.T. Assessment of Enterococcus in fish and its environment: A study in tilapia farms operating in the Budamasa areas of Minalin, Pampanga, Philippines. AACL Bioflux 2023, 16, 1007–1024. [Google Scholar]
  63. Frazilio, D.A.; De Almeida, O.G.G.; Niño-Arias, F.C.; De Martinis, E.C.P. Finding a common core microbiota in two Brazilian dairies through culture and DNA metabarcoding studies. J. Food Sci. Technol. 2019, 56, 5326–5335. [Google Scholar] [CrossRef]
  64. Li, Y.; Guo, X.; Peng, Q.; Shen, T.; Yao, J.; Wei, Y.; Duan, H.; Liu, W. Culturomics: A promising approach for exploring bacterial diversity in natural fermented milk. Food Biosci. 2024, 62, 105383. [Google Scholar] [CrossRef]
  65. Hong, J.H.; Jin, Y.H.; Pawluk, A.M.; Mah, J.-H. Metagenomic and culturomic analyses of bacterial species contributing to tyramine formation in Cheonggukjang. LWT 2024, 201, 116265. [Google Scholar] [CrossRef]
  66. Cheema, S.K.; Li, R.; Cameron, S.J.S. Culturomics as a tool to better understand the human milk microbiota and host–microbiota interactions. Microbiota Host 2023, 1, e230001. [Google Scholar] [CrossRef]
  67. Gong, L.; Li, X.; Ji, L.; Chen, G.; Han, Z.; Su, L.; Wu, D. Characterization and comparison of gut microbiota in patients with acute pancreatitis by metagenomics and culturomics. Heliyon 2025, 11, e42243. [Google Scholar] [CrossRef]
  68. Sun, Y.; Liu, Y.; Li, J.; Tan, Y.; An, T.; Zhuo, M.; Pan, Z.; Ma, M.; Jia, B.; Zhang, H.; et al. Characterization of lung and oral microbiomes in lung cancer patients using culturomics and 16s rRNA gene sequencing. Microbiol. Spectr. 2023, 11, e00314-23. [Google Scholar] [CrossRef]
  69. Moote, P.E.; Zaytsoff, S.J.M.; Ortega Polo, R.; Abbott, D.W.; Uwiera, R.R.E.; Inglis, G.D. Application of culturomics to characterize diverse anaerobic bacteria from the gastrointestinal tract of broiler chickens in relation to environmental reservoirs. Can. J. Microbiol. 2020, 66, 288–302. [Google Scholar] [CrossRef]
  70. Chen, S.; Li, X.; Wang, Y.; Zeng, J.; Ye, C.; Li, X.; Guo, L.; Zhang, S.; Yu, X. Induction of Escherichia coli into a VBNC state through chlorination/chloramination and differences in characteristics of the bacterium between states. Water Res. 2018, 142, 279–288. [Google Scholar] [CrossRef] [PubMed]
  71. Pacheappan, G.D.; Samsudin, N.I.P.; Hasan, H. The effects of different disinfectants and application conditions on microbial contaminants at dairy processing line. Food Process. Preserv. 2022, 46, e16172. [Google Scholar] [CrossRef]
  72. György, É.; Unguran, K.A.; Laslo, É. Biocide tolerance and impact of sanitizer concentrations on the antibiotic resistance of bacteria originating from cheese. Foods 2023, 12, 3937. [Google Scholar] [CrossRef]
  73. Beltrame, C.A.; Kubiak, G.B.; Lerin, L.A.; Rottava, I.; Mossi, A.J.; Oliveira, D.D.; Cansian, R.L.; Treichel, H.; Toniazzo, G. Influence of different sanitizers on food contaminant bacteria: Effect of exposure temperature, contact time, and product concentration. Food Sci. Technol. 2012, 32, 228–232. [Google Scholar] [CrossRef]
  74. Akinbobola, A.B.; Sherry, L.; Mckay, W.G.; Ramage, G.; Williams, C. Tolerance of Pseudomonas aeruginosa in in-vitro biofilms to high-level peracetic acid disinfection. J. Hosp. Infect. 2017, 97, 162–168. [Google Scholar] [CrossRef] [PubMed]
  75. Dos Santos, E.A.R.; Tadielo, L.E.; Schmiedt, J.A.; Orisio, P.H.S.; Brugeff, E.C.L.; Possebon, F.S.; Pereira, M.O.; Pereira, J.G.; Bersot, L.S. Inhibitory effects of piperine and black pepper essential oil on multispecies biofilm formation by Listeria monocytogenes, Salmonella Typhimurium, and Pseudomonas aeruginosa. LWT 2023, 182, 114851. [Google Scholar] [CrossRef]
  76. Tadielo, L.E.; Bellé, T.H.; Dos Santos, E.A.R.; Schmiedt, J.A.; Cerqueira-Cézar, C.K.; Nero, L.A.; Yamatogi, R.S.; Pereira, J.G.; Bersot, L.D.S. Pure and mixed biofilms formation of Listeria monocytogenes and Salmonella Typhimurium on polypropylene surfaces. LWT 2022, 162, 113469. [Google Scholar] [CrossRef]
Figure 1. Diversity of bacterial families identified on smooth and modular surfaces after the pre-operational sanitation process in a Brazilian poultry slaughterhouse. Swabs from the surfaces were cultured on Plate Count Agar, total DNA was extracted from the grown microbial communities, and the V3 and V4 regions of 16S rRNA genes were amplified and sequenced with high-throughput technology. All identified bacterial families are shown, with no abundance threshold applied.
Figure 1. Diversity of bacterial families identified on smooth and modular surfaces after the pre-operational sanitation process in a Brazilian poultry slaughterhouse. Swabs from the surfaces were cultured on Plate Count Agar, total DNA was extracted from the grown microbial communities, and the V3 and V4 regions of 16S rRNA genes were amplified and sequenced with high-throughput technology. All identified bacterial families are shown, with no abundance threshold applied.
Foods 14 02387 g001
Figure 2. Diversity of bacterial families identified on smooth and modular surfaces after the pre-operational sanitation process in a Brazilian fish slaughterhouse. Swabs from the surfaces were cultured on Plate Count Agar, total DNA was extracted from the grown microbial communities, and the V3 and V4 regions of 16S rRNA genes were amplified and sequenced with high-throughput technology. All identified bacterial families are shown, with no abundance threshold applied.
Figure 2. Diversity of bacterial families identified on smooth and modular surfaces after the pre-operational sanitation process in a Brazilian fish slaughterhouse. Swabs from the surfaces were cultured on Plate Count Agar, total DNA was extracted from the grown microbial communities, and the V3 and V4 regions of 16S rRNA genes were amplified and sequenced with high-throughput technology. All identified bacterial families are shown, with no abundance threshold applied.
Foods 14 02387 g002
Figure 3. Diversity of bacterial genera identified on smooth and modular surfaces after the pre-operational sanitation process in a Brazilian poultry slaughterhouse. Swabs from the surfaces were cultured on Plate Count Agar, total DNA was extracted from the grown microbial communities, and the V3 and V4 regions of 16S rRNA genes were amplified and sequenced with high-throughput technology. All identified bacterial genera are shown, with no abundance threshold applied.
Figure 3. Diversity of bacterial genera identified on smooth and modular surfaces after the pre-operational sanitation process in a Brazilian poultry slaughterhouse. Swabs from the surfaces were cultured on Plate Count Agar, total DNA was extracted from the grown microbial communities, and the V3 and V4 regions of 16S rRNA genes were amplified and sequenced with high-throughput technology. All identified bacterial genera are shown, with no abundance threshold applied.
Foods 14 02387 g003
Figure 4. Diversity of bacterial genera identified on smooth and modular surfaces after the pre-operational sanitation process in a Brazilian fish slaughterhouse. Swabs from the surfaces were cultured on Plate Count Agar, total DNA was extracted from the grown microbial communities, and the V3 and V4 regions of 16S rRNA genes were amplified and sequenced with high-throughput technology. All identified bacterial genera are shown, with no abundance threshold applied.
Figure 4. Diversity of bacterial genera identified on smooth and modular surfaces after the pre-operational sanitation process in a Brazilian fish slaughterhouse. Swabs from the surfaces were cultured on Plate Count Agar, total DNA was extracted from the grown microbial communities, and the V3 and V4 regions of 16S rRNA genes were amplified and sequenced with high-throughput technology. All identified bacterial genera are shown, with no abundance threshold applied.
Foods 14 02387 g004
Figure 5. Principal coordinates analysis (PCoA) based on Jaccard dissimilarity of bacterial communities from modular (blue) and smooth (red) surfaces after pre-operational sanitation in Brazilian poultry and fish slaughterhouses. Axes 1, 2, and 3 explain 9.461%, 5.425%, and 4.839% of the variation, respectively. The distribution of samples shows a partial separation by surface type, suggesting that surface characteristics may influence bacterial composition after cleaning.
Figure 5. Principal coordinates analysis (PCoA) based on Jaccard dissimilarity of bacterial communities from modular (blue) and smooth (red) surfaces after pre-operational sanitation in Brazilian poultry and fish slaughterhouses. Axes 1, 2, and 3 explain 9.461%, 5.425%, and 4.839% of the variation, respectively. The distribution of samples shows a partial separation by surface type, suggesting that surface characteristics may influence bacterial composition after cleaning.
Foods 14 02387 g005
Figure 6. Venn diagram based on bacterial genera with relative frequency (RF) > 1% identified after pre-operational sanitation on modular and smooth surfaces, respectively, from Brazilian fish and poultry slaughterhouses.
Figure 6. Venn diagram based on bacterial genera with relative frequency (RF) > 1% identified after pre-operational sanitation on modular and smooth surfaces, respectively, from Brazilian fish and poultry slaughterhouses.
Foods 14 02387 g006
Table 1. Location and quantity of samples evaluated on different equipment surfaces in Brazilian poultry and fish slaughterhouses.
Table 1. Location and quantity of samples evaluated on different equipment surfaces in Brazilian poultry and fish slaughterhouses.
Collection PointsN%
Poultry slaughterhouse (n = 50)   
  Modular polypropylene conveyor belt1020
  Modular polypropylene conveyor belt1020
  Stainless steel table1020
  Smooth polyurethane conveyor belt1020
  Modular polypropylene conveyor belt1020
Fish slaughterhouse (n = 50)  
  Modular polypropylene conveyor belt1020
  Smooth polypropylene cutting board1020
  Skin machine (stainless steel)1020
  Modular polypropylene conveyor belt1020
  Modular polypropylene conveyor belt1020
Table 2. Presence and absence of bacterial growth on PCA plates from samples evaluated on equipment surfaces in Brazilian poultry and fish slaughterhouses.
Table 2. Presence and absence of bacterial growth on PCA plates from samples evaluated on equipment surfaces in Brazilian poultry and fish slaughterhouses.
Collection PointsN +%N −%
Poultry slaughterhouse (n = 50)     
  Modular polypropylene conveyor belt48612
  Modular polypropylene conveyor belt71436
  Stainless steel table61248
  Smooth polyurethane conveyor belt71436
  Modular polypropylene conveyor belt61248
Fish slaughterhouse (n = 50)    
  Modular polypropylene conveyor belt61248
  Smooth polypropylene cutting board510510
  Skin machine (stainless steel)48612
  Modular polypropylene conveyor belt510510
  Modular polypropylene conveyor belt81624
(+) indicates the number and percentage of samples with bacterial growth on PCA plates. (−) indicates the number and percentage of samples with no bacterial growth on PCA plates.
Table 3. Alpha and beta diversity parameters of culturable microbial communities observed on surfaces of poultry and fish slaughterhouses after pre-operational sanitation, considering different parameters (type of meat product, collection site, type of surface, and surface material).
Table 3. Alpha and beta diversity parameters of culturable microbial communities observed on surfaces of poultry and fish slaughterhouses after pre-operational sanitation, considering different parameters (type of meat product, collection site, type of surface, and surface material).
CategoriesAlpha Diversity *Beta Diversity **
Shannon’s Diversity IndexObserved FeaturesFaith’s Phylogenetic DiversityEvennessJaccard DistanceBray–Curtis distanceUnweighted UniFrac DistanceWeighted UniFrac Distance
Type of food0.2830.3110.1940.7320.0670.1090.1220.621
Sampling point0.3040.3690.6100.504
Type of surface0.0260.0360.1100.1450.0250.0820.2270.215
Type of material0.3640.5840.4550.2040.7590.7210.7600.950
* Kruskal–Wallis test, with statistical significance defined by p < 0.05. ** Pseudo-F test, with statistical significance defined by p < 0.05.
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

Bach, L.G.; Braga, G.Z.A.; Bedutti, M.C.; Dias, L.M.P.; dos Santos, E.A.R.; Tadielo, L.E.; Silva, E.C.d.; Schmiedt, J.A.; Alves, V.F.; De Martinis, E.C.P.; et al. Total Culturable Microbial Diversity of Food Contact Surfaces in Poultry and Fish Processing Industries After the Pre-Operational Cleaning Process. Foods 2025, 14, 2387. https://doi.org/10.3390/foods14132387

AMA Style

Bach LG, Braga GZA, Bedutti MC, Dias LMP, dos Santos EAR, Tadielo LE, Silva ECd, Schmiedt JA, Alves VF, De Martinis ECP, et al. Total Culturable Microbial Diversity of Food Contact Surfaces in Poultry and Fish Processing Industries After the Pre-Operational Cleaning Process. Foods. 2025; 14(13):2387. https://doi.org/10.3390/foods14132387

Chicago/Turabian Style

Bach, Luiz Gustavo, Gabriela Zarpelon Anhalt Braga, Márcia Cristina Bedutti, Layza Mylena Pardinho Dias, Emanoelli Aparecida Rodrigues dos Santos, Leonardo Ereno Tadielo, Evelyn Cristine da Silva, Jhennifer Arruda Schmiedt, Virgínia Farias Alves, Elaine Cristina Pereira De Martinis, and et al. 2025. "Total Culturable Microbial Diversity of Food Contact Surfaces in Poultry and Fish Processing Industries After the Pre-Operational Cleaning Process" Foods 14, no. 13: 2387. https://doi.org/10.3390/foods14132387

APA Style

Bach, L. G., Braga, G. Z. A., Bedutti, M. C., Dias, L. M. P., dos Santos, E. A. R., Tadielo, L. E., Silva, E. C. d., Schmiedt, J. A., Alves, V. F., De Martinis, E. C. P., Possebon, F. S., Barcellos, V. C., & Bersot, L. d. S. (2025). Total Culturable Microbial Diversity of Food Contact Surfaces in Poultry and Fish Processing Industries After the Pre-Operational Cleaning Process. Foods, 14(13), 2387. https://doi.org/10.3390/foods14132387

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