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Article

Genetic Detection of Pseudomonas spp. in Commercial Amazonian Fish

by
Alba Ardura
1,*,
Ana R. Linde
2 and
Eva Garcia-Vazquez
1
1
Department of Functional Biology, University of Oviedo. C/Julian Claveria s/n, Oviedo 33006, Spain
2
Laboratory of Toxicology, National School of Public Health, Fundaçao Oswaldo Cruz, Rio de Janeiro 21041, Brazil
*
Author to whom correspondence should be addressed.
Int. J. Environ. Res. Public Health 2013, 10(9), 3954-3966; https://doi.org/10.3390/ijerph10093954
Submission received: 23 June 2013 / Revised: 23 July 2013 / Accepted: 15 August 2013 / Published: 29 August 2013
Browse Figures
Versions Notes

Abstract

:
Brazilian freshwater fish caught from large drainages like the River Amazon represent a million ton market in expansion, which is of enormous importance for export to other continents as exotic seafood. A guarantee of bacteriological safety is required for international exports that comprise a set of different bacteria but not any Pseudomonas. However, diarrhoea, infections and even septicaemia caused by some Pseudomonas species have been reported, especially in immune-depressed patients. In this work we have employed PCR-based methodology for identifying Pseudomonas species in commercial fish caught from two different areas within the Amazon basin. Most fish caught from the downstream tributary River Tapajòs were contaminated by five different Pseudomonas species. All fish samples obtained from the River Negro tributary (Manaus markets) contained Pseudomonas, but a less diverse community with only two species. The most dangerous Pseudomonas species for human health, P. aeruginosa, was not found and consumption of these fish (from their Pseudomonas content) can be considered safe for healthy consumers. As a precautionary approach we suggest considering Pseudomonas in routine bacteriological surveys of imported seafood.

1. Introduction

Brazil contains a rich biodiversity of animal and plant taxa distributed at varied latitudes, and could open a new international market for high quality food products, perhaps targeting delicatessen shops and specialized restaurants. Such a market would be exclusive of Brazil because many species from some regions, like the Amazon, are unique and endemic. Due to their enormous diversity [1,2], Amazonian fishes represent a potentially interesting sector for export. Tools for labeling these fishes are currently being developed [3], aimed at enabling Amazonian fish introduction in demanding markets like the European one, where the normatives on traceability and food security control are strict (e.g., European Directives CE-178/2002; CE-1759/2006).
Introduction of exotic species in a new market encompasses some potential risks. One of them is introduction of parasites or pathogens endemic of their native region [4]. Control of such pathogens in the importer country may not be required if they are normally absent from local food. An example applicable to the fish trade could be Pseudomonas. These bacteria constitute a part of the normal fish microbiota, but are opportunistic and may become infectious and spread diseases in stressed fish [5]. Pseudomonas can be a problem for human consumers too. They appear in processes of seafood spoilage [6,7] and in ready-to-eat products [8]. In some conditions they can become human pathogens and cause infection. Many pathogeneses of Pseudomonas in humans, generally caused by only one species (most frequently P. aeruginosa), are health-care associated illnesses [9,10], and the risk of disease by ingestion in healthy consumers has been considered generally low in developed countries [11]. However, such risk exists and can be serious depending on the circumstances. Contamination with enterotoxigenic Pseudomonas has been reported from food and drinking water samples in some countries [12]. Jertborn and Svennerholm [13] have discovered enterotoxin-producing Pseudomonas in Swedish travellers with diarrhoea, somewhat more frequently in travellers visiting Africa, Asia and Latin America. In association with other bacteria they can cause severe cholera symptoms in healthy adults [14]. Even when their enterotoxigenic activity is weak they can still produce diarrhoea in immunodeficient individuals [15]. In addition they can cause skin problems; their presence in cosmetics is considered a health threat in the U.S. [16], and have produced outbreaks of skin infections [17]. Therefore there are infection risks when manipulating contaminated seafood.
Notwithstanding the information provided above, Pseudomonas species are not catalogued as a foodborne pathogen in Europe and other regions. Control tests of imported fish and shellfish include various bacterial species like Escherichia coli, C. botulinum, Listeria monocytogenes, Staphylococcus aureus, Enterobacter sakazakii and Salmonella sp., but not Pseudomonas spp. (e.g., European Council Directive 1991, 1995 and Council Directive 1998; Canadian Food Inspection Agency [18], European Comission [19], American Food Safety and Inspection Service (FSIS) [20].
The aim of this study was to investigate the presence of Pseudomonas spp. in samples of commercial fish sold in Brazilian markets from two different Amazonian states (Table 1): the River Tapajós (Para) and the River Negro (Amazonas). The results may inform about the convenience of including these bacteria in routine controls for Brazilian fish exports as well as in local markets. The molecular tools used in this study were PCR-amplification with Pseudomonas-specific primers and sequencing 16S rRNA genes. This type of methodology is highly sensitive and has been employed in other surveys of foodborne bacteria [21,22].
Table
Table 1. Samples analyzed, fish species with their common names and Pseudomonas species identified.
Table 1. Samples analyzed, fish species with their common names and Pseudomonas species identified.
SampleOriginFish spp.Common namePseudomonas species
T1TapajósProchilodus nigricansCurimatáPseudomonas psychrophila
T2TapajósCetopsis candiruCandiruPseudomonas spp.
T3TapajósLeporinus piauPiauPseudomonas psychrophila
T4TapajósLeporinus piauPiauPseudomonas syringae
T5TapajósSerrasalmus rhombeusPiranhaPseudomonas fragi
T6TapajósLeporinus piauPiauPseudomonas fluorescens
T7TapajósAgeneiosus brevifilisBocudoPseudomonas fluorescens
T8TapajósLeporinus piauPiauPseudomonas psychrophila
T9TapajósLeporinus piauPiauPseudomonas syringae
T10TapajósLeporinus piauPiauPseudomonas fluorescens
T11TapajósLeporinus piauPiauPseudomonas spp.
T12TapajósLeporinus piauPiauPseudomonas psychrophila
T13TapajósProchilodus nigricansCurimatáPseudomonas psychrophila
T14TapajósLeporinus piauPiauPseudomonas fragi
T15TapajósLeporinus piauPiauPseudomonas psychrophila
T16TapajósLeporinus piauPiauPseudomonas putida
T17TapajósLeporinus piauPiau-
T18TapajósLeporinus piauPiau-
M1NegroChaetobranchopsis orbicularisAcará brancoPseudomonas putida
M2NegroAstonotus ocellatusAcará-açúPseudomonas putida
M3NegroAstonotus ocellatusAcará-açúPseudomonas putida
M4NegroAstonotus ocellatusAcará-açúPseudomonas putida
M5NegroOsteoglossum bicirrhosumAruanàPseudomonas putida
M6NegroBrachypatystoma rousseauxiiDouradaPseudomonas putida
M7NegroSemaprochilodus insignisJaraquíPseudomonas putida
M8NegroPlagioscion squamosissimusPescadaPseudomonas putida
M9NegroPhractocephalus hemioliopterusPirararaPseudomonas psychrophila
M10NegroPseudoplatystoma fasciatumSurubimPseudomonas putida
M11NegroCichla temensisTucunaréPseudomonas putida
M12NegroCichla temensisTucunaréPseudomonas putida

2. Experimental Section

2.1. Sampling

The 30 fish samples analyzed (Table 1) were obtained from two different tributaries within the Amazon basin (Figure 1): the River Negro (Manaus markets; n = 12) and the River Tapajós (n = 18), and were directly purchased from fishermen in local harbors and markets. All fish specimens were morphologically identified in situ by visual inspection and taxonomically classified employing standard taxonomic guides. After cleaning the fish surface with ethanol, samples of muscle (the edible tissue) were excised in situ with sterilized blades and tweezers and immediately stored in absolute ethanol. Ethanol-preserved samples were transported in coolers to the laboratory for genetic analysis.
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Figure 1. A map with proportions of different Pseudomonas species found in each sampling site: Manaus and Tapajós.
Figure 1. A map with proportions of different Pseudomonas species found in each sampling site: Manaus and Tapajós.
Ijerph 10 03954 g001

2.2. Genetic Analyses

DNA extraction and PCR amplification were carried out in sterile conditions to prevent cross-contamination of samples during the process. Total DNA was extracted from a small piece (approximately 5 mg) of alcohol-preserved fish tissue by the standard protocol of Estoup et al. [23], using Chelex® resin (Bio-Rad Laboratories, Hercules, CA, USA). Chelex® is a chelating material used to purify other compounds from a tissue via ion exchange. It is often used for DNA extraction in preparation for PCR. Polar resin beads bind polar cellular components after breaking open cells, while DNA and RNA remain suspended in water solution above the Chelex®. The tissue was introduced in an Eppendorf tube with 500 µL of Chelex® resin (10%) and 7 µL of Proteinase K (20 mg/mL). It was incubated at 55 °C for 90 min. The DNA was dissolved in the aqueous solution. Finally, it was introduced in an oven at 100 °C during 20 min for inactivating the enzyme. The tube was stored at 4 °C or frozen at −20 °C for long-time preservation.
A fragment of the 16S rRNA gene was amplified by polymerase chain reaction (PCR), employing the Pseudomonas genus specific primers PA-GS-F (5′-GACGGGTGAGTAATGCCTA-3′) and PA-GS-R (5′-CACTGGTGTTCCTTCCTATA-3′) described by Spilker et al. [24] They amplify a DNA region of 618 nucleotides located between the sites 113 and 712, position and size relative to 16S rDNA sequence of Pseudomonas aeruginosa AT2 (AB091760) [24]. The amplification reaction was performed in a total volume of 40 µL, including Promega (Madison, WI, USA) Buffer 1X, 2.5 mM MgCl2, 0.25 mM dNTPs, 20 pmol of each primer, 20 ng of template DNA, and 1 U of DNA Taq polymerase (Promega). The PCR conditions were the following: an initial denaturation at 95 °C for 5 min, 10 cycles at 94 °C for 15 s, annealing at 53 °C for 30 s and elongation at 72 °C for 45 s. This was repeated for 25 cycles, increasing the elongation step at 72 °C by 5 s every cycle. The final extension phase was at 72 °C for 10 min.
PCR products were visualized in 2% agarose gels with 3 µL of 10 mg/mL ethidium bromide. Stained bands were excised from the gel, and DNA was purified with an Eppendorf PerfectPrep Gel CleanUp® kit prior to sequencing. After that, amplified and purified products were precipitated using standard 2-propanol precipitation and re-suspended in formamide.
Sequencing was performed in an ABI PRISM 3100 Genetic Analyzer (Applied Biosystems, Foster City, CA, USA) with BigDye 3.1 terminator system, at the Sequencing Unit of the University of Oviedo (Oviedo, Spain).

2.3. Sequence Edition and Phylogenetic Analysis

Sequences obtained from the 16S rRNA gene amplicons were visualized and edited employing the BioEdit Sequence Alignment Editor software [25]. Sequences were aligned with the ClustalW application [26] included in BioEdit.
The phylogenetic analysis was performed with the software MEGA 4.0 [27]. This software was employed to reconstruct the phylogenetic trees of the Pseudomonas species found in fish samples from 16S rDNA sequences. The methodology chosen was the neighbor-joining (NJ), the standard method of phylogenetic inference in DNA barcoding studies [28] because it allows to rapid analysis of large species assemblages [29]. The molecular substitution model was chosen using the software jModeltest [30] to determine the best suited model of sequence evolution and accompanying evolutionary parameter values for the data. Robustness of the NJ topology was assessed using 2,000 bootstrap replicates.
Pseudomonas species identification was made by comparing generated 16S rDNA sequences with reference sequences present in the GenBank database by means of BLAST online program [31].

2.4. Pseudomonas Diversity Estimates

Pseudomonas species diversity in each Amazonian location was estimated by means of ecological index (Shannon, H) using PRIMER 6 (Software package from the Plymouth Marine Laboratory, Lutton, Ivybridge, UK). The number of haplotypes (h) and nucleotide diversity (π) were calculated with the ARLEQUIN software [32,33].

2.5. Statistics

To compare the proportion of contaminated fish between locations, chi-square statistics was employed. Analysis was carried out using the SPSS 13.0 software (SPSS Inc., Chicago, IL, USA).

3. Results and Discussion

Positive PCR amplification was obtained with Pseudomonas specific primers for a fragment of the 16S rDNA [24] from 28 Amazonian fish out of 30 samples analyzed (93.3%): 16 from the River Tapajòs and 12 from the River Negro. Cross-contamination of samples during the process of DNA analysis can be reasonably excluded since the two samples from Tapajòs that did not provide positive PCR amplification (Table 1) could be considered Pseudomonas-free. Sequences were very clean (an example is in Figure 2) and mixture of species was not found for any sample. This does not exclude their presence but indicates that, if other Pseudomonas were present in a sample, they were likely in a lower concentration; the PCR primers would anneal preferentially with the most abundant target DNA. The sequences are available in the GenBank public database [31] under the accession numbers JF745541-JF745568.
Ijerph 10 03954 g002 1024
Figure 2. Chromatogram of a DNA sequence corresponding to the 16S rRNA gene fragment of a Pseudomonas putida (T16) found in Leporinus piau from Tapajós.
Figure 2. Chromatogram of a DNA sequence corresponding to the 16S rRNA gene fragment of a Pseudomonas putida (T16) found in Leporinus piau from Tapajós.
Ijerph 10 03954 g002
The 16S rDNA sequences obtained allowed to identifying five Pseudomonas species in Tapajós (Table 1): Pseudomonas pshychrophila, P. fragi, P. fluorescens, P. syringae and P. putida, based on 100% of similarity with other reference sequences of those species included in the GenBank. Two fish contained Pseudomonas but the species could not be identified because the alignment obtained did not yield 100% similarity with any other Pseudomonas species included in the GenBank, therefore they were classed as Pseudomonas sp. On the other hand, Manaus fish samples carried only two Pseudomonas species: P. putida and P. pshychrophila (Table 1).
For the fish carrier, Pseudomonas contamination affected different fish species (Table 1), but association fish-Pseudomonas species could not be properly tested due to reduced number of some fish species.
The Pseudomonas found in the two locations clustered in two main branches in a phylogenetic tree (Figure 3), supported by relatively low bootstrapping. One contained Pseudomonas putida and P. syringae and the other clustered the other three species and the unidentified sequences, which should logically correspond to species of the same group.
Although the proportion of contaminated fish was similar in the two locations analyzed, Tapajós fish samples contained more Pseudomonas sp. species and therefore higher bacterial diversity, both ecological and genetic, than Manaus commercial fish (Figure 4). The species composition of the Pseudomonas complex found in the two locations was significantly different (Chi-square value = 19.26, p < 0.001), clearly due to much higher proportion of P. putida and P. psychrophila in Manaus and Tapajós fish, respectively (Figure 1).
Ijerph 10 03954 g003 1024
Figure 3. Neighbour-Joining tree constructed based on 16S rDNA Pseudomonas sequences found in this survey. Bootstrap values (in percent).
Figure 3. Neighbour-Joining tree constructed based on 16S rDNA Pseudomonas sequences found in this survey. Bootstrap values (in percent).
Ijerph 10 03954 g003
Ijerph 10 03954 g004 1024
Figure 4. Diversity parameters of fishborne Pseudomonas communities from the Amazonian Tapajòs and Negro tributaries. Metagenetic h and π parameters, and Shannon index.
Figure 4. Diversity parameters of fishborne Pseudomonas communities from the Amazonian Tapajòs and Negro tributaries. Metagenetic h and π parameters, and Shannon index.
Ijerph 10 03954 g004
The results presented here, although based on small sample sizes, suggest that Pseudomonas are endemically present in Amazonian fish sold in local markets since most analyzed fish yielded positive PCR amplification for these bacteria. Pseudomonas aeruginosa, the most dangerous species for human health [9,10,17] and especially for consumers [13,15], was not detected. Therefore consumption of these fish can be considered generally safe for healthy people, at least from their Pseudomonas content.
The characteristics of the Pseudomonas species found from Brazilian fish samples (Table 2) may suggest the origin of the contamination. Fish infection in some Tapajós samples was suggested by the presence of the well-known fish pathogen P. fluorescens, which is considered as opportunistic pathogenic species in aquaculture [34,35], responsible for bacterial septicemia in fish. This species was present in three (16.7%) samples from Tapajós, but in none from Manaus (Figure 1). Pseudomonas infections in fish are promoted by different stressors [6,36]. Environmental stress produced by mining has been reported in the River Tapajós [37], and could contribute to facilitate fish infection by opportunistic Pseudomonas.
P. putida was found in most Manaus samples (Figure 1) and in only one sample from Tapajós. Different Pseudomonas species have been associated with seafood (including chilled fish) spoilage, for example P. fragi [6], therefore the likely origin of contamination of these samples could be seafood manipulation, long time of storage before selling or simply opportunistic growth of these bacteria on fish exposed without protection in the open-door local markets. P. putida infections have also been reported in fish species, for example in farmed rainbow trout [38], also associated to stress, therefore this last possibility cannot be totally ruled out. P. psychrophila grows in cold conditions [39,40], unusual in the natural tropical Amazonian environment; they could be an opportunistic colonizer during the storage in cold rooms previous to selling in the market. Finally, P. syringae is a plant pathogen which can infect a wide range of plant species; more than any mineral or other organism is responsible for the surface frost damage in plants exposed to the environment [41]; like P. psychrophila tends to be favored by wet and cool conditions [41], being more probable that appear like an opportunistic colonizer during the storage in cool rooms.
Table
Table 2. Characteristics of the Pseudomonas species found from commercial Amazonian fish and potential risk for humans.
Table 2. Characteristics of the Pseudomonas species found from commercial Amazonian fish and potential risk for humans.
Pseudomonas speciesCharacteristicsPathogenesis reported for humans
P. fluorescensOpportunistic pathogen in fish [42]Oncology patients [43]
P. fragiSeafood spoilage [6,44]No published data about this
Opportunistic microbiota [6]
P. psychrophila No *
P. putidaSeafood spoilage [44]Immunodepressed patients [45]
Cosmopolitan opportunist [46]Nosocomial infections [47]
P. syringae No *
* They cannot survive at temperatures above 32 °C [39,41], and therefore cannot grow in humans where normal body temperature is 37 °C.
From the phylogenetic point of view, the tree obtained grouped the identified species consistently with previous phylogenetic studies of the genus [47,48]. The same marker, 16S rRNA gene, was used together with other three genes, since although this is a powerful tool for genus assignments, it does not discriminate sufficiently at the inter-species level [49]. In this case the discrimination level of 16S rRNA gene is enough to determine the contamination present in fishes with different species of Pseudomonas.
Although we have not found the most dangerous species, the Pseudomonas found in our study could be potentially harmful for vulnerable or immunodepressed consumers (Table 2). Infections by P. fluorescens and P. putida had been reported in old studies [43,44,45,50] (and references therein), and were confirmed later. P. fluorescens is a potential pathogen due to their capacity of adhesion to nerves [50], and outbreaks in oncology patients have been discovered [43]. On the other hand, P. putida bacteremia seemed to be infrequent and affect mainly immunocompromised patients, with a good prognosis since most cases were cured [45]; however, recent emergent multidrug-resistant and carbapenem-resistant. P. putida isolates cause difficult-to-treat nosocomial infections in seriously ill patients [51]. In brief, these species could cause problems in vulnerable people and do not represent a serious threat for healthy consumers [52], but using a precautionary approach it could be wise to start considering them for future seafood tests. The presence of these pathogens in the products tested here does not mean that they are a risk for consumers; in general Pseudomonas sp. represents a hazard for the health when its number exceeds 106–107 CFU/g of product [11,12,15,17] but CFU has not been quantified here. Rather these results could be considered an exploratory work on presence/absence of Pseudomonas. If routine surveys were undertaken they should include quantification of the bacteria concentration. RT-PCR based methods could be employed since they can estimate the number of DNA molecules present in a sample. These methods are relatively cheap nowadays and the sequencing cost per sample in our study was approximately 3€ (real cost). However, the analysis of foodborne bacteria is being revolutionized with new sequencing technologies such as NGS [53], and prospects are of better prices for large-scale analysis. On the other hand, this type of PCR-based methods allow to detecting extremely low number of microorganisms based on the production of specific gene copies of a microorganism in question, but it does not distinguish living bacteria from dead cells. Since PCR methodology is rapid (a few hours), additional tests based on the count of total viable microorganisms could be used after initial detection and identification by PCR. Examples are Standard Plate Count [54], determination of most probable number of viable bacteria [55], methods based on fluorescence techniques [56] or direct counting at the microscope [57].

4. Conclusions

The possible presence of Pseudomonas in fish and seafood should be considered when food imports arrive from countries or areas with Pseudomonas endemism and high prevalence of enterotoxigenic-derived diseases. We suggest that routine tests for Pseudomonas could be included in the battery of tests aimed at controlling the bacteriological quality of imported fish. PCR-based methodologies, like those employed in this study, are easy and fast and could be considered as a complementary tool to bacterial cultivation.

Acknowledgments

This study has been funded by the Spanish Agency of International Cooperation for Development (AECID) Project D/023514/09. We are grateful to Vanessa Gomes, Ione Ginuino, Gema E. Adan and Eduardo del Rosal for collaboration in sampling. Ivan G. Pola helped with laboratory work.

Conflicts of Interest

The authors declare no conflict of interest.

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MDPI and ACS Style

Ardura, A.; Linde, A.R.; Garcia-Vazquez, E. Genetic Detection of Pseudomonas spp. in Commercial Amazonian Fish. Int. J. Environ. Res. Public Health 2013, 10, 3954-3966. https://doi.org/10.3390/ijerph10093954

AMA Style

Ardura A, Linde AR, Garcia-Vazquez E. Genetic Detection of Pseudomonas spp. in Commercial Amazonian Fish. International Journal of Environmental Research and Public Health. 2013; 10(9):3954-3966. https://doi.org/10.3390/ijerph10093954

Chicago/Turabian Style

Ardura, Alba, Ana R. Linde, and Eva Garcia-Vazquez. 2013. "Genetic Detection of Pseudomonas spp. in Commercial Amazonian Fish" International Journal of Environmental Research and Public Health 10, no. 9: 3954-3966. https://doi.org/10.3390/ijerph10093954

APA Style

Ardura, A., Linde, A. R., & Garcia-Vazquez, E. (2013). Genetic Detection of Pseudomonas spp. in Commercial Amazonian Fish. International Journal of Environmental Research and Public Health, 10(9), 3954-3966. https://doi.org/10.3390/ijerph10093954

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