Email updates

Keep up to date with the latest news and content from BMC Veterinary Research and BioMed Central.

Open Access Research article

Occurrence of antibiotic resistance in bacteria isolated from seawater organisms caught in Campania Region: preliminary study

Giorgio Smaldone1, Raffaele Marrone1*, Silvia Cappiello2, Giuseppe A Martin1, Gaetano Oliva1, Maria L Cortesi1 and Aniello Anastasio1

Author Affiliations

1 Departement of Veterinary Medicine and Animal Production, University of Naples "Federico II", via F. Delpino 1, 80137 Naples, NA, Italy

2 Departement of Veterinary Medicine and Animal Production, Veterinary pharmacovigilance center, Campania region, via F. Delpino 1, 80137 Naples, NA, Italy

For all author emails, please log on.

BMC Veterinary Research 2014, 10:161  doi:10.1186/1746-6148-10-161

The electronic version of this article is the complete one and can be found online at: http://www.biomedcentral.com/1746-6148/10/161


Received:8 January 2014
Accepted:30 June 2014
Published:15 July 2014

© 2014 Smaldone et al.; licensee BioMed Central Ltd.

This is an Open Access article distributed under the terms of the Creative Commons Attribution License (http://creativecommons.org/licenses/by/2.0), which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly credited. The Creative Commons Public Domain Dedication waiver (http://creativecommons.org/publicdomain/zero/1.0/) applies to the data made available in this article, unless otherwise stated.

Abstract

Background

Environmental contamination by pharmaceuticals is a public health concern: drugs administered to humans and animals are excreted with urine or faeces and attend the sewage treatment. The main consequences of use and abuse of antibiotics is the development and diffusion of antibiotic resistance that has become a serious global problem. Aim of the study is to evaluate the presence of antimicrobial residues and to assess the antimicrobial resistance in bacteria species isolated from different wild caught seawater fish and fishery products.

Results

Three antibiotic substances (Oxytetracicline, Sulfamethoxazole and Trimethoprim) were detected (by screening and confirmatory methods) in Octopus vulgaris, Sepia officinalis and Thais haemastoma. All Vibrio strains isolated from fish were resistant to Vancomycin (VA) and Penicillin (P). In Vibrio alginolyticus, isolated in Octopus vulgaris, a resistance against 9 antibiotics was noted.

Conclusions

Wild caught seawater fish collected in Gulf of Salerno (Campania Region), especially in marine areas including mouths of streams, were contaminated with antibiotic-resistant bacteria strains and that they might play an important role in the spread of antibiotic-resistance.

Keywords:
Antibiotic resistance; Vibrio strains; Fish; Antibiotic residues

Background

Environmental contamination by pharmaceuticals is a public health concern. Medical substances may roughly be divided into medical substances used by human or veterinary medicine. The veterinary drugs may further be subdivided into substances used as growth promoters for livestock production, therapeutics in livestock productions, coccidiostatic used for poultry production, therapeutics for treatment of livestock on fields or as feed additives in fish farms.

Drugs administered to humans and animals are excreted with urine or faeces [1] and attend the sewage treatment plant [2]; successively if substances are hydrophilic or are metabolized to a more hydrophilic form of the parent lipophilic substance, will pass the waste water treatment plant and end up in the receiving waters where they may be are present at very low concentrations; it is important noted that several substances could stimulate a response in humans and animals also at low doses with a very specific target [3]. A recent study showed that a mixture of drugs at the concentrations actually found in the aquatic environment of some Italian areas is able to exert toxic effects on the proliferation of human and zebra fish (Danio rerio) cells cultures [4]. The main consequences of use and abuse of antibiotics is the development and diffusion of antibiotic resistance that represent a public health problem, with obvious consequences in human and veterinary medicine, since it affects animal therapy and food safety [5,6]. World wide there is growing concern about the increased prevalence of antibiotic resistance: the growing alarm related to the spreading of the resistance of antibiotics considered of first choice in the treatment of specific human infections prompted measures for antimicrobial resistance surveillance of bacteria circulating in humans, animals and food products. Aim of this study was to evaluate the presence of antimicrobial substances and to assess the antimicrobial resistance in bacteria species isolated from wild caught seawater fish and fishery products caught in Tyrrenian sea along the coast of Campania region (southern Italy). The antibiotics tested were Teicoplanin (TEC), Cephalexin (CN), Penicillin (P), Oxacillin (OX), Amoxicillin/Clavulanic Acid (AMC), Cefotaxime (CTX), Vancomycin (VA), Sulfamethoxazole (SXT), Rifampicin (RD), Cefoxitin (FOX), Plaritromicin (PRL), Ciprofloxacin (CIP), Chloramphenicol (C), Tobramicin (TOB), Tetracycline (TE), Tigecycline (TGC), Linezolid (LZD) and Fosfomycin (FOS).

Results and discussion

Microbial analysis and antibiogram

The microbial species isolated were Vibrio alginolyticus (Va), Vibrio parahaemolyticus (Vp), Shewanella putrefaciens (Sp) and Acromonas spp. (Ac) (Table 1); Vp is a bacteria naturally present in marine and estuarine aquatic environments and is part of the natural flora of fish and bivalve mollusks. Va, isolated from Sepia officinalis and Trachurus trachurus samples, is frequently detected from fin fish, shellfish, seawater, and sediment [7]. It has not been not widely recognized as a fish pathogen. Sp a microorganism common in marine environments as saprophytic is one of the major causes of spoilage of fish and fishery products [8]; Water bacteria might be indigenous to aquatic environments, or exogenous, transiently and occasionally present in the water as a result of shedding from animal, vegetal, or soil surfaces [9].

Table 1. Microbial species isolated in seawater fish and fishery products

The frequency of antibiotic resistance among microbial strains isolated was shown in Table 2 and Table 3. Although only 7 species of fish and 3 species of fishery products were studied to determine the incidence of antibiotic resistance, all the strains isolated were resistant to one or more of the antibiotics tested; the frequency of resistance varied from 16.6% to 50% in different samples; 69,45% of the microbial strains isolates showed resistance to more than 4 molecules tested. Va showed antimicrobial resistance against 9 antibiotics, Vp against 4 antibiotics, Sp against 6 antibiotics and Ac against 4 antibiotics tested. Accordinto to Martinez [9], more than 90% of bacterial strains originated in seawater are resistant to more than one antibiotic. Multiple antibiotic resistance has been reported in a wide range of human pathogenic or opportunistic bacteria such as Campylobacter spp. [10], Klebsiella pneumoniae[11], Salmonella sp.[12], Pseudomonas aeruginosa[13], E. coli[14] and also in fish pathogens [15]. In all bacterial strains resistance against TEC and VA, drugs belonging to the class of glycopeptides having similar mechanisms of action on bacterial cell wall synthesis, and against P and OX, drugs belonging to the class of β-lactam antibiotics, was observed. Spectra of activity of TEC and VA are limited to Gram–positive bacteria including methicillin–resistant strains of S. aureus and S. epidermidis and for this reason the resistant Gram–negative bacteria isolates could be not sensitive to mechanism of action of these molecules. VA has a shorter half–life than TEC and requires multiple dosing to maintain adequate serum levels. In contrast, the pharmacokinetics of TEC allow for once–daily dosing and it is a drug associated with a lower incidence of nephrotoxicity or ototoxicity. For these reasons TEC is more cost–effective and its role in hospitals is likely to increase. Resistance to VA could be related not only to the use of VA in human medicine but also to a cross-resistance due to the use of Avoparcin, a glycopeptides utilized to improve performance in poultry flocks [16], which are present in the area near to sampling zone. Resistance against P and OX could be related to the large use of β-lactam antibiotics in human and veterinary medicine. The sensitivity against C detected in all bacterial strains coupled with the absence of C residues in fish sampled, confirm the limited administration to humans and the compliance on the use of the drug for food producing animals, banned since 1995. However, according Kerry et al. [17], it is important to underline that resistance phenomena are not systematically correlated with the presence of the corresponding drugs.

Table 2. Frequency of antibiotic resistance among the bacteria isolated

Table 3. Frequency of antibiotic resistance among the bacteria isolated

Antibiotic resistance profiles among bacterial strains isolates (% resistant strains) were presented in Table 4. As a whole, as supported by statistical analysis, all culturable bacteria were significantly (P < 0.001) affected by the presence of the tested antibiotic molecules. In particular, for seven molecules (FOS, FOX, AMC, PRL, TOB, TE and LZD) for the four different bacteria strains isolated a statistically significant (P < 0.05) effect (resistance or sensibility) was observed. The other molecules showed any statistically significant effect (P > 0.05) among the different isolated microbial strains; in particular, four of them showed very high resistance (mean values: VA: 100%, OX: 98.9%, TEC: 97.7%, P: 85.7%).

Table 4. Antibiotic resistance profiles among bacterial strains isolates (% resistant strains)

The study of antibiotic resistance in indigenous water organisms is important, as it might indicate the extent of alteration of water ecosystems by human action. The spread of strains with antibiotic resistance from animal to animal does not meet the minimum barrier in the marine environment and resistance evolves as a consequence of promiscuous exchange and shuffling of genes, genetic platforms, and genetic vectors. Several pollutants in seawater might exert selective activities, as well as ecological damage in water environment, resulting in antibiotic resistance: Baquero et al. [18] noted that resistance profiles of aquatic pseudomonads depend on the species composition, but also from the site in which they were isolated, being more antibiotic-resistant along shorelines and in sheltered bays than in the open water, indicating the influence of nonaquatic organisms or pollutants.

Detection of residues of antibiotics

Residues of antibacterial substances were detected in common octopus, european cuttlefish and red-mouthed rock shell. At the confirmatory analysis only two of the examined drugs were detected. Oxytetracycline and Sulfamethoxazole were quantified with 3.62 μg/kg and 0.48 μg/kg respectively. Levels detected were in compliance with LMR established by UE Reg. 37/2010. The presence of antibiotics might be due to the increased possibility of accumulation in fishery products that, for a period of their life cycle, remain for a long time in the same fishing area. In our study, the sampling area is within a stretch of coastline that spans the mouth of one river and several streams that cross a lot of livestock and agricultural fields.

Studies on residues of pharmacologically active molecules have shown elimination rates in the aquatic environment after the depuration treatment generally between 60 and 90%, for a wide variety of polar drugs [19]. The elimination of drugs in common sewage treatment plants is often incomplete and recent works demonstrates the presence of antimicrobial residues in river waters [20]. Polar antibiotics cannot be eliminated effectively as much of the process of elimination is based on absorption on activated sludge and so ultimately on hydrophobic interactions. Another route of elimination of drugs in the aquatic waste water is connected to the dispersion of manure "contaminated" on the fields as fertilizer through runoff into streams of wastewater and those used for irrigation. It was showed that sulfa drugs, such as sulfadimethoxine, are sufficiently stable in the manure as to maintain a significant residual activity up when the manure is used for fertilizing [21,22] and that some of the metabolites of antibiotics excreted may also be retransformed into the active drug progenitor; such as the glucuronide dicloramphenicol or the N-4-acetyl sulfamethazine converted into the manure in Chloramphenicol and Sulfamethazine respectively [23].

Conclusions

The risk of antibiotic resistance was considered significantly more serious than the risk associated with the presence of antibiotic residues in food [24]. Results presented in this study provide evidence that seawater fishes collected in some area of Campania Region, especially in marine areas including mouths of streams, were contaminated by residues of antibiotic and antibiotic-resistant bacteria strains and that they might play an important role in the spread of antibiotic-resistance. The resistance of 97.7% of isolated strains against TEC might suggest that the main sources of contamination were hospital discharges.

Future prediction and prevention of antibiotic resistance depends on the research investments in the development of microbial source tracking as well as in the ecology, including water ecology, of antibiotic-resistant microorganisms.

Methods

Sampling

Samples were collected always in the same area of the gulf of Salerno (Campania Region, Southern Italy) with the support of the mobile station of the Fish Research Laboratory of the Department of Veterinary Medicine and Animal Production, University of Naples “Federico II”. The sampling area was chosen because it is close to sewers conveying hospital wastewater. This study has been reviewed by Ethical Animal Care and Use Committee, University of Naples “Federico II”, Department of Veterinary Medicine and Animal Production and received institutional approval.

The research concerned 56 samples: 33 fish (7 species), 13 cephalopods (2 species) and 10 gasteropods (1 specie) present in the sampling zone in that season; fish species, collected at a depth of 5–7 meters and at a distance of about 50 meters from the coast, were: red scorpionfish (Scorpaena scrofa, 6 samples), giant goby (Gobius cobitis, 7 samples), atlantic horse mackerel (Trachurus trachurus, 4 samples), brown meagre (Sciaena umbra, 3 samples), white seabream (Diplodus sargus, 6 samples), fathead mullet (Mugil cephalus, 5 samples), green wrasse (Labrus viridis, 2 samples), common octopus (Octopus vulgaris, 7 samples), european cuttlefish (Sepia officinalis, 6 samples) and red-mouthed rock shell (Thais haemastoma, 10 samples) respectively. Samples after capture were immediately transported on ice to the lab “Prof.ssa Teresa Antonietta Sarli” of the Department of Veterinary Medicine and Animal Production, University of Naples "Federico II”. An aliquot was subjected to microbiological analysis and the other was frozen at -80°C until analyzed.

Microbial analysis and antibiogram

All samples were analyzed for the presence of microbial species of the genus "Vibrio" according to recognized ISO methods. Briefly all samples were scrubbed and analytical portions (25 g) were aseptically removed and collected in a sterile bag with 225 ml of alkaline saline peptone water (ASPW). According to ISO/TS 21872–1:2007 [25] and ISO/TS 21872–2:2007 [26] indications for fresh products, the samples were homogenized using a stomacher (PBI International, Milan, Italy) at 11000 rev min-1 for 3 min and incubated at 37°C [26] and 42°C [25] for 6 h. A further enrichment was performed employing 1 ml of the first enrichment and 9 ml of ASPW. This broth culture was incubated at 37°C and 42°C for 18 h. The enrichment cultures from incubation were plated onto thiosulphate-citrate-bile salt sucrose (TCBS) (Oxoid, Hampshire, UK) agar and incubated at 37°C for 24 h. Typical colonies were transferred into Nutrient Agar plates (Oxoid, Hampshire, UK) added to 5 g/l NaCl to bring it to a final concentration of 1% and incubated at 37°C for 24 h according to ISO/TS method. After incubation at 37°C for 24 h, the isolates were subjected to the Gram stain, the oxidase test using Oxidase Sticks (Oxoid, Hampshire, UK), Triple-Sugar-Iron (TSI) (Oxoid, Hampshire, UK) and biochemical identification with API 20E (bioMérieux, Marcy l’Étoile, France) according to Di Pinto et al.[27]. The identification profiles were obtained by the APIweb software (bioMérieux, Marcy l’Étoile, France) according to to the instructions of the manufacturer.

The strains isolated were subjected to the antibiotic resistance test using standard methods. Antibiotic susceptibility was determined by the agar diffusion method according to French national guidelines [28]. Bacterial suspensions prepared in sterile 0.85% saline matching an optical density of 0.5 McFarland standard corresponding to 108 cfu/ml and diluted 1:100 in physiological saline were inoculated by lawn onto Muller-Hinton agar (Difco, Le Pont de Claix, France). Each antibiotic test was run in duplicate on freshly prepared agar plates. After incubation for 24 h at 37°C, organisms were classified as sensitive (S), intermediate (I) or resistant (R) according to the inhibition zone diameter [28].

Detection of residues of antibiotics

Analysis were performed on fish muscle. Each sample analyzed consisted of a pool of fish and fishery products grouped by species (i.e. sample of red scorpionfish consisted of a pool of six red scorpionfish caught). The detection of antibiotics residues was carried out using the kit “Premi® Test” (Biopharm, Darmstadt, Germany), as a screening method, according manufacturer's instructions. The kit is based on the growth inhibition of Bacillus stearothermophilus, a microorganism sensible to the residues of different antibiotics. This test is able to detect residues of β-lactam antibiotics, cephalosporins, macrolides, tetracyclines, sulfonamides, aminoglycosides, quinolones, amphenicols and polypeptides. The principle on which is based the test is the following: a standard number of spores is embedded in an agar medium with selected nutrients. When Premi® Test is heated to 64°C, spores can germinate. If antimicrobial substances are absent, spores germinated producing hydrogen and a clear color change from purple to yellow occurs. When anti-microbial compounds are present above limit of detection, spores will not be able to germinate and there will be no colour change.

Samples positive to Premi® Test were analyzed by the mean of HPLC-DAD method suggested by Fernandez-Torres et al. [29] for the following compounds (97–99.9% purity, Sigma-Aldrich - USA): Sulfadiazine (SDI), Trimetroprim (TMP), Oxytetracycline (OXT), C and SXT. HPLC-UV method proposed by De Jesùs Valle et al. [30], was used for VA detection. Antibiotic selection was made considering drugs commonly used in farms in the Campania region [31]. All reagents used were of analytical grade. Measurements were made with a Jasco (Mary's Court, Easton, MD, USA) liquid chromatograph equipped with UV and diode array (DAD) detector, an injector with a loop of 50 μL, a quaternary pump, a vacuum degasser an a thermostated column compartment. For first method the separation of the analyzed compounds was conducted by means of a Phenomenex C18 (150 mm × 4.6 mm I.D., particle size 5 μm) analytical column with a C18 (4 mm × 4 mm, particle size 5 μm) guard-column. The mobile phase consisted of a mixture of 0.1% (v/v) formic acid in water pH 2.6 (phase A) and acetonitrile (phase B). A gradient eluition program at 1 mL/m-1 flow rate was used. After a step of 8 min with 99% (phase A) a linear elution gradient to 65% in 25 min was performed. The column effluent was monitored by DAD detector in the range of 200–400 nm. The sample extraction was conducted as follows: After homogenization of sample (2 g of lyophilized tissue + 5 of deionized water) 50 μL of Proteinase-K solution was added; to the mixture, centrifuged for 2.5 hours, 100 μL of formic acid was then added. Finally the samples was treated three times with 5 mL of dichloromethane and the extracts were evaporated under nitrogen. 50 μL of the residue, reconstituted with 1 mL of deionized water, were injected.

For the vancomycin detection method [30], chromatographic separation was carried out by the means of a Nucleosil 120 C18 5 μm column (length, 15 cm; inner diameter, 0.4 cm) using a mixture of 50 mM NH4H2PO4 (pH 4)–acetonitrile (92:8, v/v) as the mobile phase at a flow rate 1 mL/min and a column temperature of 40°C with UV detection at 220 nm. Regarding extraction procedure briefly: a mixture of 500 μg of sample with 20 μL of 60% perchloric acid was vortexed for 30 s, followed by centrifugation at 10,900 rpm, after the supernatant was collected and an aliquot of 50 μL was injected into the chromatographic system.

Statistical analysis

The χ2 test performed with the Epi-Info statistical program (version 6.0; Centers for Diseases Control and Prevention, Atlanta, GA, USA) was used to test the effect of the antibiotics on the bacteria growth and to assess the effect type (resistance or sensibility) of each molecule among the different isolated microbial strain.

Competing interests

The authors declare that they have no competing interests.

Authors’ contributions

GS, RM, and SC conceived and designed the experiments; GS and GAM performer the experiments; All authors contributed in the writing of the paper. GO, MLC and AA summarized and analized the data, reviewed and commented the manuscript. All authors read and approved the final manuscript.

Acknowledgements

The authors acknowledge Veterinary Pharmacovigilance Center of Campania region for study management.

References

  1. Forth W, Henschler D, Rummel W, Starke K: Allgemeine und spezielle. In Pharmakologie und Toxikologie. 6th edition. Vienna, Zurich: Wissenschaftsverlag, Mannheim, Leipzig; 1996. OpenURL

  2. Stumpf M, Ternes T, Haberer K, Seel P, Baumann W: Nachweis von Arzneimittelrückständen in Kläranlagen und Fließgewässern.

    Vom Wasser 1996, 86:291-303. OpenURL

  3. Jobling S, Williams R, Johnson A, Taylor A, Gross-Sorokin M, Nolan M, Tyler C, Van Aerle R, Santos E, Brighty G: Predicted exposures to steroid estrogens in U.K. rivers correlate with widespread sexual disruption in wild fish populations.

    Environ Health Perspect 2006, 114(Suppl 1):32-39. PubMed Abstract | PubMed Central Full Text OpenURL

  4. Pomati F, Castiglioni S, Zuccato E, Fanelli R, Rossetti C, Calamari D: Effects of environmental contamination by therapeutic drugs on human embryonic cells.

    Environ Sci Technol 2006, 40:2442-2447. PubMed Abstract | Publisher Full Text OpenURL

  5. Kummerer K: Resistance in the environment.

    J Antimicrob Chemother 2004, 54:311-320. PubMed Abstract | Publisher Full Text OpenURL

  6. Miranda JM, Vázquez BI, Fente CA, Barros-Velázquez J, Cepeda A, Franco CM: Evolution of resistance in poultry intestinal Escherichia coli during three commonly used antimicrobial therapeutic treatments in poultry.

    Poult Sci 2008, 87:1643-1648. PubMed Abstract | Publisher Full Text OpenURL

  7. Gjerde J, Boe B: Isolation and characterization of Vibrio alginolyticus and Vibrio parahaemolyticus from the Norwegian coastal environment.

    Acta Vet Scand 1981, 22:331-343. PubMed Abstract OpenURL

  8. Jergensen BR, Huss HH: Growth and activity of Shewanella putrefaciens isolated from spoiling fish.

    Int J Food Microbiol 1989, 9:51-62. PubMed Abstract | Publisher Full Text OpenURL

  9. Martinez JL: Recent advances on antibiotic resistance genes.

    In Recent Advances in Marine Biotechnology. Molecular Genetics of Marine Organisms, Volume 10 Edited by Fingerman N. 2003, pp13-pp32. OpenURL

  10. Randall LP, Ridley AM, Cooles SW, Sharma M, Sayers AR, Pumbwe L, Newell DG, Piddock LJV, Woodward MJ: Prevalence of multiple antibiotic resistance in 443 Campylobacter spp. isolated from humans and animals.

    J Antimic Chemot 2003, 52:507-510. Publisher Full Text OpenURL

  11. Carneiro LAM, Silva APS, Merquior VLC, Queiroz MLP: Antimicrobial resistance in Gram-negative bacilli isolated from infant formulas.

    FEMS Microbiol Lett 2003, 228:175-179. PubMed Abstract | Publisher Full Text OpenURL

  12. Randall LP, Cooles SW, Osborn MK, Piddock LJV, Woodward MJ: Antibiotic resistance genes, integrons and multiple antibiotic resistance in thirty-Wve serotypes of Salmonella enterica isolated from humans and animals in the UK.

    J Antimicrob Chemother 2004, 53:208-216. PubMed Abstract | Publisher Full Text OpenURL

  13. Ziha-Zari WI, Llanes C, Köhler T, Pechere JC, Plesiat P: In vivo emergence of multidrug-resistant mutants of Pseudomonas aeruginosa overexpressing the active eZux system MexA-MexB-OprM.

    Antimicrob Agents Ch 1999, 43(2):287-291. OpenURL

  14. Miranda JM, Vázquez BI, Fente CA, Barros-Velázquez J, Cepeda A, Franco Abuín CM: Antimicrobial resistance in Escherichia coli strains isolated from organic and conventional pork meat: a comparative survey.

    Eur Food Res Technol 2008, 226:371-375. Publisher Full Text OpenURL

  15. Schmidt AS, Bruun MS, Dalsgaard I, Pedersen K, Larsen JL: Occurrence of antimicrobial resistance in fish pathogenic and environmental bacteria associated with four Danish rainbow trout farms.

    Appl Environ Microb 2000, 66:4908-4915. Publisher Full Text OpenURL

  16. Bager F, Madsen M, Christensen J, Aerestrup FM: Avoparcin used as a growth promoter is associated with the occurrence of vancomycin – resistant Enterococcus faecium on Danish poultry and pig farms.

    Prev Vet Med 1997, 95:112. OpenURL

  17. Kerry J, Coyne R, Gilroy D, Hiney M, Smith P: Spatial distribution of oxytetracycline and elevated frequencies of oxytetracycline resistance in sediments beneath salmon farm following oxytetracycline therapy.

    Aquaculture 1996, 145:31-39. Publisher Full Text OpenURL

  18. Baquero F, Martinez JL, Canton R: Antibiotics and antibiotic resistance in water environments.

    Curr Opin Biotechnol 2008, 19:260-265. PubMed Abstract | Publisher Full Text OpenURL

  19. Ternes TA: Occurrence of drugs in sewage treatment plants and rivers.

    In Water Res 1998, 32:3245-3260. Publisher Full Text OpenURL

  20. Iglesias A, Nebot C, Miranda JM, Vazquez BI, Cepeda A: Detection and quantitative analysis of 21 veterinary drugs in river water using high-pressure liquid chromatography coupled to tandem mass spectrometry.

    Environ Sci Pollut R 2012, 19:3235-3249. Publisher Full Text OpenURL

  21. Migliore L, Brambilla G, Cozzolino S, Gaudio L: Effect on plants of sulphadimethoxine used in intensive farming Panicum miliaceum, Pisum sativum and Zea mays.

    Agric Ecosys Environ 1995, 52:103-110. Publisher Full Text OpenURL

  22. Boehm R: Effects of residues of antiinfectives in animal excrements upon slurry management and upon soil.

    Dtsch tierärztl Wschr 1996, 103:264-268. OpenURL

  23. Berger K, Petersen B, Buening-Pfaue H: Persistence of drugs occurring in liquid manure in the food chain.

    Arch Lebensmittelhyg 1986, 37:99-102. OpenURL

  24. Joint FAO/OIE/WHO: Expert Workshop on Non-Human Antimicrobial Usage and Antimicrobial Resistance: Scientific assessment, Geneva, December 1 – 5, 2003. Databasehttp://www.who.int/foodsafety/micro/meetings/nov2003/en/ webcite

  25. ISO/TS 21872–1:2007: Microbiology of food and animal feeding stuffs – Horizontal method for the detection of potentially enteropathogenic Vibrio spp. – Part 1: Detection of Vibrio parahaemolyticus and Vibrio cholerae. Databasehttp://www.iso.org/iso/catalogue_detail.htm?csnumber=38278 webcite

  26. ISO/TS 21872–2:2007: Microbiology of food and animal feeding stuffs -- Horizontal method for the detection of potentially enteropathogenic Vibrio spp. -- Part 2: Detection of species other than Vibrio parahaemolyticus and Vibrio cholerae. Databasehttp://www.iso.org/iso/catalogue_detail.htm?csnumber=38279 webcite

  27. Di Pinto A, Ciccarese G, De Corato R, Novello L, Terio V: Detection of pathogenic Vibrio parahaemolyticus in southern Italian shellfish.

    Food Control 2008, 19:1037-1041. Publisher Full Text OpenURL

  28. Comité de l’antibiogramme de la Société Française de Microbiologie Database [http://www.sfm-microbiologie.org webcite]

  29. Fernandez-Torres R, Bello Lopez MA, Olias Consentino M, Callejon Mochon M: Simultaneous determination of selected antibiotics and their main metabolites in fish and mussel samples by high-performance liquid chromatography with diode array-fluorescence (HPLC-DAD-FLD) detection.

    Anal Lett 2011, 44:2357-2372. Publisher Full Text OpenURL

  30. De Jesús Valle MJ, López FG, Navarro AS: Development and validation of an HPLC method for vancomycin and its application to a pharmacokinetic study.

    J Pharmaceut Biomed 2008, 48:835-839. Publisher Full Text OpenURL

  31. Rapporto 2012 sulle antibiotico resistenze e sull’uso di antibiotici rilevati nelle strutture ospedaliere della Campania Databasehttp://resources.regione.campania.it/slide/files/Assessori/sanita/OER/file_13594_GNR.pdf webcite