Quantification and characterization of Salmonella spp. isolates in sewage sludge with potential usage in agriculture

Abstract

Background

This study aims to scrutinize Salmonella spp. and its serotypes in sewage sludge samples from wastewater treatment plants, and assesses the presence of virulence genes and antibiotics resistant to the profile. Samples (n = 54) were collected and analyzed in accordance with the EPA Method 1682/2006. For positive serological reaction, 40 strains were selected for PCR analyses and detection of spvC, invA and sseL virulence genes, plasmid presence and resistance to antibiotics.

Results

Salmonella spp. was detected in 38.9% of the samples collected (<0.006473 to 12.19 MPN/gTS). The most prevalent serotype was Salmonella Infantis. All Salmonella spp. (n = 35) presented at least one of the three virulence genes mentioned above and 40% harboured plasmids. Salmonella Typhimurium strains were isolated harbouring at least one of the following virulence genes: spvC, invA or sseL. Four Salmonella spp. isolates were resistant to tetracycline; three were resistant to trimethoprim-sulfamethoxazole, and one isolate was resistant to ciprofloxacin. Two Salmonella spp. strains presented multi resistance to antimicrobial agents.

Conclusions

The results obtained demonstrated that Salmonella spp. have been found in sewage sludge, thus it is essential to set measures to mitigate human health risks when it is intended to be applied on agricultural soils.

Background

The employment of sewage sludge on agricultural fields has been recognized worldwide as a promising way to manage this kind of residue, as it can minimize environmental pollution, in addition to giving it useful destination, what is done at the Wastewater Treatment Plants (WWTP). None the less, careful consideration regarding its quality and impacts on human health ought to be given, since the presence of pathogens in sewage sludge, including Salmonella spp., have been documented in manifold studies [1-4].

In order to protect both human and environmental health, Brazilian legislation issued by Conselho Nacional do Meio Ambiente (Environmental National Council), which is a branch of the Federal Environmental Council, CONAMA N^o 375/2006 – has classified sewage sludge in two distinct classes: A (unrestricted application) and B (restricted application). For class A, the maximum values for thermotolerant coliforms is ≤10³ MPN/gTotal Solids (TS), the total absence of Salmonella spp. in 10 g of total solids, followed by <0.25 helminth viable ova/gTS and ≤0.25 enterovirus/g TS, while for class B the standards are ≤10⁶ MPN/gTS for thermotolerant coliforms and <10 helminth viable ova/gTS [5]. Some countries or some of their respective regions have been establishing microbiological and parasitological standards for biosolids, such as the USA legislation [6], the United Kingdom [7], Australia (South Australia, West Australia and EPA Victoria), Finland and New Zealand [8].

The employment of sewage sludge with no sanitary criteria or barriers, particularly in agricultural fields, intensifies the potential to disseminate such pathogen.

Of late, a worldwide increase in the number of outbreaks involving Salmonella spp. related to the fresh-cut produce industry and the consumption of fresh-cut vegetables has been observed. Such outbreaks are caused by a few Salmonella serotypes which have the capability to resist to environmental stresses, remaining viable for extended periods on field crops [9-11]. It has been observed that Salmonella can regrow in the soil and remain viable for more than two years after soil inoculation [12].

In a global survey conducted from 1990 to 1995, Salmonella Enteritidis, and Salmonella Typhimurium were considered to be the most isolated non-typhoid Salmonella in fifty-nine countries [13]. None of the less, in the city of São Paulo (Brazil), where surveillance studies indicated an increase in the prevalence of Salmonella Enteritidis both in clinical and environmental samples, whereas studies conducted in Agona, Ohio and Albany demonstrated the most isolated serotypes from sewage samples [14,15].

The presence of virulence genes such as invA and sseL, which are located, respectively, on the pathogenicity island I (SPI-1) and II (SPI-2), has been used as evidence of pathogenicity [16]. The virulence genes which compose SPI Pathogenicity Island are responsible for the entry of Salmonella spp. into host epithelial cells. The pathogenic genes presented in SPI-2 are related to modifications in host cell functions, being thus essential for survival and replication of Salmonella Enterica within host macrophages [17]. The spvC virulence gene, present in plasmids and/or chromosomes, strengthens the systemic proliferation of the pathogen and, furthermore, contributes to its replication in extra-intestinal sites [18]. The presence of these three virulence genes predicts overall pathogenicity, invasiveness and replication capabilities of Salmonella species.

Antimicrobial resistance patterns for typhoidal and non-typhoidal Salmonella are constantly changing, and the treatment of infections caused by multidrug resistant strains (MDR) poses a serious public health concern. A study conducted in Brazil with Salmonella spp. strains isolated from clinical specimens which were collected in each of the five Brazilian regions, detected that this microorganism presented low resistance to all antibiotics tested, except for cloranfenicol [19]. Later on, a study conducted by Medeiros et al. [20] with the participation of several Brazilian states, pointed out to the fact that all the 250 Salmonella strains which were previously isolated from chicken carcasses were resistant to at least one antibiotic, and that 53.2% of the samples assessed were MDR.

In the light of the fact that the use of sewage sludge on agricultural fields can be considered a way to spread such pathogen, and therefore risk the health of the population exposed, the aim of this study was to survey Salmonella spp. and its serotypes in sewage sludge samples from five WWTPs located in São Paulo metropolitan region (MRSP). In addition to so, we intended to search for the presence of virulence genes, plasmids, and antimicrobial resistance/resistant profiles in the isolated strains.

Results

In total, 54 samples were collected from the five WWTP sites throughout the 12 months of 2011, and analysed in order to observe Salmonella spp. presence. Table 1 shows Salmonella concentrations in sludge samples from each WWTP studied from January to December 2011. This bacterium was detected in 38.9% (21/54) of all samples analysed. Bacteria concentration above <0.006473 MPN/g TS (Detection Limit - DL) was detected in 38.9% (21/54) of all samples analysed. The highest concentration of Salmonella spp. was found in WWTP 2, where counts ranged from DL (<0.006473 MPN/g TS) to 12.19 MPN/g. The lowest Salmonella spp. concentration was found in WWTP 1 (0.75 MPN/g) and WWTP 5 (0.43 MPN/g), and no Salmonella spp. was isolated in WWTP 3.

Table 1.

Concentration of Salmonella spp. (MPN/g TS) in sewage sludge samples collected from the five WWTPs in 2011

Date	WWTP 1	WWTP 2	WWTP 3	WWTP 4	WWTP 5
Jan	<0.006473	<0.006473	<0.006473	0.43	<0.006473
Feb	<0.006473	1.74	<0.006473	0.49	0.43
Mar	<0.006473	3.72	NP	<0.006473	<0.006473
Apr	<0.006473	6.03	<0.006473	0.21	<0.006473
May	<0.006473	4.81	<0.006473	<0.006473	<0.006473
Jun	<0.006473	5.63	<0.006473	NP	<0.006473
Jul	<0.006473	2.28	NP	1.32	<0.006473
Aug	<0.006473	12.20	NP	<0.006473	<0.006473
Sep	<0.006473	3.29	NP	0.69	<0.006473
Oct	<0.006473	1.66	<0.006473	0.76	<0.006473
Nov	0.75	5.74	NP	0.85	<0.006473
Dec	<0.006473	4.45	<0.006473	1.86	<0.006473

NP = Not Performed.

Table 2 summarizes the results obtained via serology identification. Such results indicate the presence of virulence genes, plasmids, and antibiotic resistance in Salmonella strains which were previously isolated from sewage sludge. Out of the 307 isolations, 40 were selected and subjected to serological typing. Five strains could not be serotyped. The most prevalent serotype among the strains which were submitted to serotype procedure was Salmonella Infantis, where 6 out of the 35 strains analysed could be classified as such, followed by S. Agona with 14.3% (5/35), and 8.6% (3/35) in regard to S. Anatum, S. Corvallis, S. Mbandaka, and S. Typhimurium; 5.7% (2/35) in regard to S. Müchen, S. Salamae, and 2.8% (1/35) in regard to S. Give, S. Javiana, S. Minnesota, S. Molade, S. Newport, S. Ohio, S. Oranienburg, and S. Ouakam.

Table 2.

Serological identification, presence of virulence genes, plasmids, and resistance to antibiotics regarding Salmonella strains

Sample source	Serovars	Presence of virulence genes			Plasmid	Antibiotic resistence
		invA	sseL	spvC
WWTP 2	Infantis	+	+	-	+	S
WWTP 2	Infantis	+	+	-	-	S
WWTP 2	Infantis	+	+	-	-	S
WWTP 2	Infantis	+	+	-	-	S
WWTP 4	Infantis	+	+	-	-	S
WWTP 4	Infantis	+	+	-	-	S
WWTP 2	Agona	+	+	-	-	S
WWTP 2	Agona	+	+	-	-	AMP,CIP
WWTP 2	Agona	+	+	-	-	S
WWTP 2	Agona	+	+	-	-	S
WWTP 4	Agona	+	+	-	-	S
WWTP 2	Anatum	+	+	-	+	TET,SUT
WWTP 2	Anatum	+	+	-	+	TET,SUT
WWTP 2	Anatum	+	+	-	-	S
WWTP 4	Corvalis	+	+	-	+	S
WWTP 4	Corvalis	+	+	-	+	S
WWTP 4	Corvalis	+	+	-	+	S
WWTP 2	Mbandaka	+	+	-	-	S
WWTP 4	Mbandaka	+	+	-	-	S
WWTP 4	Mbandaka	+	+	-	-	S
WWTP 4	Typhimurium	+	+	-	+	TET, AMP, SUT
WWTP 5	Typhimurium	+	+	+	+	S
WWTP 5	Typhimurium	+	+	+	+	S
WWTP 1	München	+	+	-	+	CAZ, TET, ATM, CTT, COM
WWTP 2	München	-	+	-	+	S
WWTP 4	Salamae	+	+	-	-	S
WWTP 4	Salamae	+	+	-	-	S
WWTP 4	Give	+	+	-	-	S
WWTP 4	Javiana	+	+	-	-	S
WWTP 2	Minnesota	+	+	-	-	S
WWTP 2	Molade	-	+	-	+	S
WWTP 4	Newport	+	+	-	-	S
WWTP 2	Ohio	+	+	-	+	S
WWTP 2	Oranienburg	+	+	-	-	S
WWTP 2	Ouakan	+	+	-	+	S

(+) presence, (-) absence; S-susceptible; AMP: ampicillin; CTT: cefotetan; TET: tetracycline; CIP: ciprofloxacin; SUT: sulfametoxazol; CAZ: ceftazidime; ATM: aztreonam; COM: cefepime.

The results referring to the detection of virulence genes revealed that all Salmonella spp. isolated strains previously analysed presented at least one of the spvC, invA, and sseL genes. Two strains (Salmonella Molade and Salmonella Muechen) presented negative results for invA gene, and two strains of Salmonella Typhimurium present at the spvC gene. From the 35 isolates subjected to plasmid extraction, 14 (40%) presented at least one plasmid.

Antimicrobial susceptibility tests revealed that 14.2% (3/35) of the strains were resistant to two antimicrobial agents, and just two strains 2/35 (5.7%) were MDR. All isolates were susceptible to cefotetan, imipenem, meropenem, and ertapenem (Table 2).

Figure 1 presents the image of agarose gels for PCR identification of Salmonella spp. previously isolated which were obtained from sewage sludge. In these strains, the presence of virulence genes and plasmidial profile were analysed. The identification of 40 isolates by PCR resulted in 36 strains containing the 429 bp band expected for all organisms identified as Salmonella spp. Three presented the 429 bp band in addition to the 620 bp band expected for Salmonella Typhimurium. Salmonella Enteritidis was not identified in this study, and four isolates were not identified as belonging to Salmonella group. As for plasmids, these extracromossomal elements were observed in 14 (40%) of the Salmonella strains subjected to serotyping, including Salmonella Typhimurium.

Figure 1.

Image of agarose gels for PCR identification of Salmonella spp. isolates from sewage sludge, presence of virulence genes and plasmidial profile. A- Identification of Salmonella spp. and serotypes Salmonella Typhimurium e Salmonella Enteriditis; B- Detection of virulence genes; C- Plasmidial profile; Strains 397 and 398: positive control for Salmonella Enteriditis and Salmonella Typhimurium, respectively; M- molecular weight markers.

Discussion

This study aims to present the level of Salmonella contamination in sewage sludge from WWTPs located in the most populated Brazilian metropolitan area. Data concerning the presence and concentration of such pathogen in sewage sludge are scarce in Brazil. Thus, the results herein reported could constitute an informational dataset, which would be used in order to give further support to interventional measures developed by sanitary authorities and also to the process of establishing guidelines for sludge usage on agricultural fields.

None of the less, we have also observed a huge difference in Salmonella spp. concentration amongst the five WWTPs assessed. In WWTP 1, WWTP 3, and WWTP 5, lime stabilizations were performed, which, according to Bean et al. [21], increases pH values up to 13, thus possibly eliminating all bacteria. In WWTP 2 and 4 where lime stabilization was not performed, Salmonella spp. concentration was higher if in comparison with WWTP 1, 3, and 5.

It is quite common to find such differences among results concerning the presence or concentration of Salmonella spp. in sewage sludge worldwide, even in those which undergo the same treatment process (mesophilic anaerobic digestion). In the present study, the frequency of positive samples were above DL (<0.006473 MNP/g) in 38.9% (21/54) of the samples analyzed, which was below the figures derived from other studies [22] and [23], which registered 92 - 100% (n =91) and 58% (n =24), respectively. The highest concentration of Salmonella spp. was found in WWTP 2 (1.2 × 10¹ MPN/g), which is in agreement with the review previously carried out by Sidhu and Toze [3], wherein the concentration usually varied from 1.1 × 10¹ to 5.9 × 10³ MPN/g TS. Wong et al. [24], on the contrary, found lower concentrations than the ones from the above mentioned studies, that is, ranging from 0.487 MPN/4 g to 0.954 MPN/4 g (0.122 – 0.238 MPN/g) in sludge from a WWTP in Michigan (USA). Such differences may be explained by the complex chemical sludge composition which differs from one country to another, type of treatment applied, regrowth or the presence of growth inhibitory factors, and population epidemiological profile [23]. Although distinct epidemiological studies have indicated the presence of Salmonella Enteritidis in sewage sludge, in the present study such serotype has not been detected. The absence of such specific serotype could be explained due to the limited number of strains serotyped. Similar results were noticed in Sweden [23]. Salström, in 2006, stated that such results could be due to the fact that this serotype is best adapted to human and animal hosts rather than to stressful environmental conditions [23]. None of the less, the presence of several serotypes in sewage sludge after outbreaks related to the ingestion of raw fruits and vegetables, such as S. Infantis, S. Newport, S. Javiana, S. Oranienburg, S. Mbandaka, S. Anatum, S. Müenchen, and S. Typhimurium [9,25-27], was observed. Furthermore, serotypes S. Newport and S. Typhimurium have a remarkable capacity to form a biofilm on leaves [28] and then to invade various tissues of plants [29].

The presence of spvC gene was found in only two out of the three Salmonella Typhimurium isolated strains, harbouring also invA and sseL genes. Peterson et al. [30] reported that up to that moment, the spvC gene had been found only in five Salmonella strains: S. Cholerasuis, S. Dublin, S. Enteritidis, and S. Typhimurium. Thus, the Salmonella Typhimurium strains mentioned in this study could represent a threat, as three virulence genes were detected even after the sewage sludge treatment.

From the 35 strains tested, 33 harboured sseL as well as the invA virulence genes, however two strains (Salmonella Molade and Salmonella München), did not harbour the latter virulence gene. The invA gene is widely recognised as a genetic marker for Salmonella enterica strains, as so can be found in almost all strains, being even used for PCR identification in this group [31]. Instead, upon assessing 630 different Salmonella enterica strains, Rahn et al. [32], found that 99.4% of those strains harboured the invA gene. Therefore, although found in the group related to the present study, the presence of invA gene is not universal.

Forty per cent of the 35 strains identified in this study presented plasmids (Table 2). According to Rychlik et al.[33], high molecular weight plasmids (above 20 Kb) are usually related to virulence genes or as resistance to antimicrobial agents; and low weight plasmids have not yet been fully comprehended, however, some of them could be related as resistant to heavy metals and also to other substances found in the environment. Although the isolation techniques performed in our study do not distinguish between high and low molecular weight plasmids, it was possible to observe the presence of such elements in 40% of the strains, including two Salmonella Typhimurium, which presented the spvC gene. The existence of plasmids in Salmonella strains in this study might come as a result in regard to the presence of heavy metals and high sulphur concentrations that are commonly present in São Paulo wastewaters and sewage sludge [34,35].

Concerning antimicrobial resistance, out of the five strains which were resistant to two or more drugs, four harboured plasmids, and one Salmonella Agona strain was resistant to two antimicrobial agents, presenting no plasmid at all (Table 2). Singh et al. [36] perceived that the presence of plasmids is not mandatory for the occurrence of antimicrobial drug resistance in Salmonella Enterica strains, once such resistant genes can also be found in chromosomes.

The results demonstrated in this research show that 14.2% (3/35) of the strains were resistant to two antimicrobial agents, and 5.7% (2/35) were MDR. Similar results were found by Sahlström et al. [23] – where 12% (12/101) of Salmonella isolates were resistant to at least one antimicrobial agent, and 7% (7/101) were MDR strains. Such results are quite different from those related to other studies previously conducted in Brazil, where Salmonella strains from human and non-human sources presented higher resistance to antimicrobial agents. In Rio de Janeiro, Fonseca et al. [37] isolated 35 Salmonella Infantis samples derived from stools of hospitalized children and found that 34 strains were resistant to at least two antimicrobial agents.

Studies conducted by Oliveira et al. [38] and Medeiros et al. [20] found in a farm strains of Salmonella in animal waste which were resistant to antibiotics, hence demonstrating that such kind of strain is circulating freely in the environment, and such fact can be considered as a crucial concern in case sewage sludge is used in agriculture.

Although the present study demonstrates a vast number of susceptible strains, the presence of an ESBL-producing and ciprofloxacin-resistant Salmonella (Agona) is worrisome. Since resistance to this antibiotic has increased and so has the production of ESBL [39], and also seeing that such is the alternative antibiotic with the aim of controlling MDR strains, treatment options are now limited.

Eventually, we also ought to take into account that some studies have presented the ability Salmonella spp. presents when it comes to regrowth in soil, internalization phenomena and its growth within plants tissues, as well as its capacity to survive for long periods in soil and crops [40-42]. Therefore, its presence must be considered as a major concern, even if such is found in low concentrations.

Conclusions

The results obtained in this study demonstrate that several genres of Salmonella are circulating in the environment, including MDR strains, therefore they can easily be found in sewage sludge. Although Salmonella Enteritidis strains were not isolated in this study, the serotypes herein mentioned are implicated in several worldwide outbreaks related to these bacteria. Moreover, certain virulence factors were found in three samples of Salmonella Typhimurium which harboured invA, sseL and spvC. Therefore in order to avoid the spreading of such bacteria through the consumption of fresh products the application of sewage sludge in agricultural soils should only be allowed with the implementation of sanitary barriers, under the supervision of environmental and health authorities, such as different types of sewage sludge stabilizations, already present in other countries.

Methods

Sampling

Sludge samples were collected from five Wastewater Treatment Plants (WWTP) located in a Brazilian densely populated metropolitan region. The treatment process which was used in all WWTPs was activated sludge with mesophilic anaerobic sludge digestion. Table 3 shows the operational characteristics of each WWTP provided by Sabesp [43], such as sewage flow rates (L/s), generated sludge (Ton/d), and chemical conditioning.

Table 3.

Sewage flow rates (L/s), generated sludge (Ton/d), and chemical conditioning applied to the five WWTPs

WWTP	Sewage flow (L/s)	Generated sludge (Ton/d)	Chemical conditioning
1	1.89	69.0	Lime + Ferric chloride
2	10.19	316.0	Ferric chloride + polymers
3	2.48	73.7	Lime + Ferric chloride + Polymers
4	0.80	14.3	Ferric chloride + polymers
5	0.85	41.0	Lime + Ferric chloride

Sampling was performed monthly in each WWTP in accordance with EPA’s recommendations [44] from January 2011 to December 2011. Samples (n = 54) were collected from a sludge pile after the dewatering process and stored in sterile plastic bottles which were kept chilled during transportation and analyzed within a 24-hour period.

Salmonella spp. isolation

Salmonella spp. isolation and enumeration were performed according to the EPA Method 1682 [44]: Salmonella in Sewage Sludge (Biosolids) Modified Semisolid Rappaport-Vassiliadis (MSRV). This method is based on “the most probable number technique” (MPN). Briefly, prior to inoculation, 30 g of sewage sludge was diluted with buffered water and homogenized in a mixer for two minutes. Subsequently, volumes of 20, 10, and 1 mL were inoculated in three series of five tubes containing Tryptic Soy Broth Medium (TSB) (Difco®, Detroit, MI,USA) and incubated at 36°C for 24 hours.

Subsequent to incubation, six drops (30 μL) from each tube were transferred to selective MSRV medium (Difco®, Detroit, MI, USA) added with novobiocin (Difco®, Sparks, MD, USA) and malachite green in order to inhibit non-Salmonella species while permitting most Salmonella species to grow. MSRV plates were incubated at 42°C for 18 hours. Thereafter, colonies with “whitish halo” were transferred to Xylose-Lysine Desoxycholate agar (XLD) (Difco®, Detroit, MI, USA) and incubated at 36°C for 24 hours. The existence of typical colonies could be confirmed by the usage of Lysine-Iron agar (LIA) (Difco®, Detroit, MI, USA), Triple Sugar iron agar (TSI) (Difco®, Detroit, MI, USA), and of urea broth, followed by positive serological typing through the usage of poly O and poly H antisera. Determination of total solids (% dry weight) was performed according to USEPA [44] and used to calculate MPN/g dry weight. Salmonella spp. density was reported in MPN/4 g of dry weight.

In order to determine circulating serotypes, 40 Salmonella spp isolated strains representing all samples previously examined were selected from both lowest and highest dilution of all positive samples from the five WWTPs. For serotyping, the strains were sent to the Enteropathogens Laboratory from “Instituto Adolfo Lutz”, which is a branch of São Paulo State Department of Health.

Salmonella spp. PCR identification

From the 307 isolates with positive serological reaction, 40 were further tested through PCR. DNA was extracted according to the method described by Chapman et al. [45] and amplification was performed with the set of primers described by Soumet et al. [46].

Briefly, amplifications were performed on 5 μl of the DNA samples which were previously extracted. Those samples were added to a mix (20 μl) consisting of 5 μl of 5× Gotaq buffer, 0.6 μmol of each primer (Invitrogen Corp – California USA), 200 μmol of dNTP (Thermo Fisher Scientific Inc.), and 1U of GOTaq Polymerase (Promega Inc.- Madinson, WI). Three sets of primers were used: ST11-ST15, specific for genus Salmonella; S1-S4 specific for Salmonella Enteritidis virulence genes; and Fli15-Typ04, which is a specific primer used to identify fliC genes only found in Salmonella Typhimurium. PCR reactions were carried out in a Mastercycler Thermocycler (Eppendorf - Hamburg, Germany). Primer sequences are described in Table 4.

Table 4.

PCR Primers were used for Salmonella spp. identification and virulence genes detection

Target	Primers	Primers sequence	Band size	Reference
Identification	ST11	GCCAACCATTGCTAAATTGGCGCA	429 pb	[38]
	ST15	GGTAGAAATTCCCAGCGGGTACTGG
	Fli15	CGGTGTTGCCCAGGTTGGTAAT	620 pb
	Typ04	ACTCTTGCTGGCGGTGCGACTT
	S1	GCCGTACACGAGCTTATAGA	250 pb
	S4	ACCTACAGGGGCACAATAAC
Virulence	SPVC-1	ACTCCTTGCACAACCAAATGCGGA	571 pb	[25]
	SPVC-2	TGTCTTCTGCATTTCGCCACCATCA
	INVA-1	ACAGTGCTCGTTTACGACCTGAAT	244 pb
	INVA-2	AGACGACTGGTACTGATCGATAAT
	sseL F	TTCCGCGACAACCGACCTTTCTAA	169 pb
	sseL R	TTCTTGAACCAGACCTTGCGTTGC

ST11/ST15-amplifying sequences of Salmonella sp; S1/S4-amplifying sequences of a Salmonella Enteritidis phage type 4 strain; Fli15/Typ04-amplifying sequences of Salmonella Typhimurium strain.

Detection of virulence genes

The 40 previously selected isolates were tested in order to find the presence of spvC, invA, and sseL virulence genes, which are in accordance to Peterson et al. [30]. Within a 25 μl reaction volume, the following quantities were added: 5 μl of DNA template, 5 μl of 5× Gotaq buffer, 0.3 μmol of each primer (Bioneer Oligo Synthesis Report - Korea), 200 μmol of dNTP (Thermo Fisher Scientific Inc.), and 1U of GOTaq Polymerase (Promega Inc.- Wisconsin -USA) (Table 4).

Electrophoresis

PCR products were performed by electrophoresis using a 3.0% agarose gel prepared with 1× TAE buffer and stained with ethidium bromide. A 100 bp DNA Ladder Plus (Thermo Fisher Scientific Inc.) was included as a size marker. Gel images were obtained via UV transillumination and captured by a gel documentation system (Epi Chemi II Darkroom and Software Labworks – UVP).

Plasmid detection

Plasmid extraction was carried out by using a Wizard PlusSV Minipreps DNA Purification System commercial kit (Promega Inc.- Wisconsin -USA) using 2 mL of overnight culture according to the manufacturer’s instructions. Plasmids were recovered in 100 μL of nuclease-free water and stored at 20°C. Prior to plasmid separation by electrophoresis, the material was heated for 15 minutes at 65°C and then maintained in ice bath for five minutes. The same process was conducted with a Hind III marker.

Plasmids were undergone electrophoresis in 1.0% agarose gel for 3 hours at 3.0 V/cm along with a molecular Hind III weight marker (Thermo Fisher Scientific Inc.). The gel was stained by using ethidium bromide (10 mg/ml), visualised under ultraviolet light and captured by Epi Chemi II Darkroom, and UVP BioImaging Systems.

Antimicrobial susceptibility testing

The 40 selected Salmonella spp. isolates were submitted to antimicrobial susceptibility tests by using the Kirby-Bauer disk-diffusion technique according to CLSI [47] recommendations. The antibiotics used were as follows: ciprofloxacin (5 μg); tetracycline (30 μg); trimethoprim-sulfamethoxazole (25 μg); cefotetan (30 μg); cefotaxime (30 μg); ceftazidime (30 μg); cefepime (30 μg); aztreonam (30 μg); imipenem (10 μg); meropenem (10 μg); and ertapenem (10 μg). In the case of resistance to β-lactams, further tests for enzyme production were performed [48]. Interpretation of inhibition zones was carried out by using CLSI [49] criteria.