African Journal of
Microbiology Research

  • Abbreviation: Afr. J. Microbiol. Res.
  • Language: English
  • ISSN: 1996-0808
  • DOI: 10.5897/AJMR
  • Start Year: 2007
  • Published Articles: 5233

Full Length Research Paper

Occurrence of multidrug-resistant bacteria in aquaculture farms in Côte d’Ivoire (West Africa)

Amian Aristide KOUDOU
  • Amian Aristide KOUDOU
  • Department of Natural Sciences, Centre of Ecology and Biodiversity, University Nanguis Abrogoua, 08 BP 109 Abidjan, Côte d’Ivoire.
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Solange KAKOU-NGAZOA
  • Solange KAKOU-NGAZOA
  • Platform of Molecular Biology, Pasteur Institute Cote d’Ivoire, Abidjan BP 490 Abidjan 01, Cote d’Ivoire.
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Kouadio Fernique KONAN
  • Kouadio Fernique KONAN
  • Platform of Molecular Biology, Pasteur Institute Cote d’Ivoire, Abidjan BP 490 Abidjan 01, Cote d’Ivoire.
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Edwige AKA
  • Edwige AKA
  • Platform of Molecular Biology, Pasteur Institute Cote d’Ivoire, Abidjan BP 490 Abidjan 01, Cote d’Ivoire.
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Audrey ADDABLAH
  • Audrey ADDABLAH
  • Platform of Molecular Biology, Pasteur Institute Cote d’Ivoire, Abidjan BP 490 Abidjan 01, Cote d’Ivoire.
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David COULIBALY N’GOLO
  • David COULIBALY N’GOLO
  • Platform of Molecular Biology, Pasteur Institute Cote d’Ivoire, Abidjan BP 490 Abidjan 01, Cote d’Ivoire.
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Stéphane KOUASSI
  • Stéphane KOUASSI
  • Platform of Molecular Biology, Pasteur Institute Cote d’Ivoire, Abidjan BP 490 Abidjan 01, Cote d’Ivoire.
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Mireille Kouamé SINA
  • Mireille Kouamé SINA
  • Platform of Molecular Biology, Pasteur Institute Cote d’Ivoire, Abidjan BP 490 Abidjan 01, Cote d’Ivoire.
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Hortense ATTA DIALLO
  • Hortense ATTA DIALLO
  • Department of Natural Sciences, Centre of Ecology and Biodiversity, University Nanguis Abrogoua, 08 BP 109 Abidjan, Côte d’Ivoire.
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Nathalie GUESSEND
  • Nathalie GUESSEND
  • Platform of Molecular Biology, Pasteur Institute Cote d’Ivoire, Abidjan BP 490 Abidjan 01, Cote d’Ivoire.
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Serge AHOUSSI
  • Serge AHOUSSI
  • Platform of Molecular Biology, Pasteur Institute Cote d’Ivoire, Abidjan BP 490 Abidjan 01, Cote d’Ivoire.
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Mireille DOSSO
  • Mireille DOSSO
  • Platform of Molecular Biology, Pasteur Institute Cote d’Ivoire, Abidjan BP 490 Abidjan 01, Cote d’Ivoire.
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  •  Received: 28 December 2019
  •  Accepted: 23 April 2020
  •  Published: 31 May 2020

 ABSTRACT

Aquaculture provides a significant proportion of the fish consumed around the world. In West Africa, aquaculture is an important economic sector. However, several diseases with high fish mortality are caused by bacterial infections.  Due to the lack of surveillance in aquaculture, this study investigated the presence of bacteria in fish farms. The purpose of the study was to isolate bacteria in aquaculture (Ivory Coast). Two hundred and forty fishes and water samples were collected from the pond of two fish farms. Fish was scraped, then, dissected to collect their gills and intestines. Bacterial culture was done for the detection of many species. Isolate identification was done using biochemical tests (API20E) and MALDI-TOF tests. Also, 1696 bacteria strains were isolated, 70.9% of strains were from the fish organs and 29,1% from the water samples. The higher colonization rate was observed in water and on fish’s surface. No statistical difference was observed between the two farms. Seven major species were isolated in both farms: Escherichia coli, Pseudomonas aeruginosa, Enterobacter hormaechei, Enterococcus faecalis, Citrobacter freundii, Morganella morganii and Bacillus cereus. The major isolated strains were Enterobacter hormachaei, Enterococcus faecalis and Escherichia coli. Multi-resistance for 3 classes of antibiotics was observed in some of those strains. This investigation shows microbiological risks for aquatic animals and humans who are in interaction with fish farms.
 
Key words: Aquaculture, multidrug-resistant strains, fish, West Africa.


 INTRODUCTION

Aquaculture belongs to the food industry with an average growth rate of 6.2% in the past years (FAO, 2016). It is an activity that contributes to the production of foods of high nutritional value, generating employment and economic income for the world population (Gabriel et  al., 2007). In addition, it strengthens the source of inputs for the food industry and foreign exchange for the country (Kouadio et al., 2019). In Africa, particularly in Côte d'Ivoire, aquaculture has an important place in the food industry   and   for    consumers   (Koumi  et    al.,    2017; Weichselbaum et al., 2013; Yao et al., 2017). In all aquaculture operations in the country, Tilapia is the major specie reared with frequencies depending on the system. One of the biggest threats to the aquaculture sector is infectious diseases (Abowei and Briyai, 2011). Antibiotics are used in aquatic ecosystems to control the bacteria responsible for infectious diseases (Watts et al., 2017; Ouattara et al., 2014; Salah and Aqel, 2014). Excessive use of antibiotics has led to the resistance of pathogenic bacteria. (Gao et al., 2012; Miller and Harbottle, 2017). Vibriosis, Photobacteriosis and Furunculosis are among other major diseases of marine and estuarine fish in natural and in aquaculture (Toranzo et al., 2005). The agents of Vibriosis are several species of V. anguillarium, V. vulnificus, V. alginolyticus and V. salmonicida. Photobacteriosis is caused by Photobacterium (Mookerjee et al., 2015). The surveillance of fish disease is under estimated in West Africa and the risk of dissemination is very high, as countries with limited resources do not have veterinary clinics providing clinical and biological diagnostics to monitor the use of antibiotics in animals (Ouedraogo et al., 2017). In West Africa, antibiotic resistance induces the emergence of resistant anterobacteria (Pitout and Laupland, 2008). Several studies have shown that 90% of bacterial strains in marine environment are resistant to more than one antibiotic and 20% are resistant to at least five antibiotics (Kouadio et al., 2017; Benie et al., 2017; Dib et al., 2018). Previous studies have demonstrated the extent of the circulation of bacterial multi resistance. It has been shown in certain animals such as chickens (Koga et al., 2015) in the natural environment and in artificial water systems. (Ouattara et al., 2014). In Côte d'Ivoire, few data are provided on the detection of bacterial multi resistance in aquaculture environments. Previous studies carried out in the DABOU area have focused more on pathogenic bacteria and less on those with antibiotic resistance (Kouadio-Ngbesso et al., 2019). However, surveillance of bacterial multi resistance has become a major concern throughout the world. this study investigated the presence of multi-drug resistant bacteria in two fish farms in Dabou, in the south of Abidjan.


 MATERIALS AND METHODS

Study area
 
Water and fish (Oreochromis niloticus) samples were collected from  two fish farms in Dabou, located in the South of Ivory Coast (fish farm 1 with GPS data: 5° 19’ 34,44’’ N, 4° 22’ 0.45’’ W; fish farm 2: 5°18’41.51’’ N, 4° 24’51.66’’ W). The study area is characterized by different aquatic ecosystem (lagoon and river) and with natural vegetation. Around these aquaculture zones, some human activities exist. Each fish farm area covers 1 hectare with 12 rectangular ponds (Figure 1).
 
Sampling in the aquaculture farm
 
Sampling was done during six months from November 2017 to April 2018 with five ponds per fish farm. Samples were collected once a month. During each visit four water and fish samples were collected from different points in each of the five ponds of the fish farms. Water samples were taken using sterile glass vials attached to a rope and fish samples were taken using mowing nets. Afterwards, 100 ml of water sample was taken from four different points in each pond. At each sampling period, Fish were sampled by rubbing its surface with swab. Next, the fish were dissected to remove their gills and intestines according to Adingra et al. (2010). A total of 240 were collected (Table 1). The water and fish samples were transported to the laboratory in a cooler containing (4° C) cold accumulator.
 
 
Bacteriological examination
 
Isolation and biochemical identification
 
Fishes were skinned and gills and intestines were removed. A small portion of the organs and the swabs were transferred into sterile 3 ml of PBS1X (pH= 7.2). The solution was mixed and 100 µl were inoculated into 3 ml of Luria Bertani broth and incubated at 37°C for 24 h.  After 24 h cultures were inoculated on different media: trypticase soy agar (TSA) for Enterobacteriaceae, Thiosulfate Citrate Bile Salts Sucrose Agar (TCBS) for Vibrio isolation, Eosin Methyl Blue Agar (EMB) for Gram negative bacteria and selective media for Pseudomonas group Cetrimide Agar (biolab, cab. 20500, lot: cab 090419072). After 18-24 h of incubation at 37°C, bacteria colonies were selected to perform Gram staining (Saleh et al., 2017). Bacterial identification was done by API 20E kits (BioMerieux, France).
 
MALDITOF analysis
 
Bacteria strains were identified by MALDI-TOF (Biomerieux, VITEK MS) according to the principle described by Carbonnelle and Nassif (2011). The bacterial strains to be analyzed were cultured on microbiological agar and incubated at 37°C for 24 h. the colonies obtained were used for analysis with MALDITOF. The method is based on the ionization of bacterial proteins by a laser beam and the creation of characteristic peaks (spectrum). The preparations were made in "sandwich" form: the sample is deposited on a matrix film before being covered by a final matrix layer. The plate carrying the samples is placed in the spectrometer where they are subjected to the laser beam. From a database of spectra, the software searches for the corresponding species of bacteria according to a reliability index between two spectra. The confirmation of the strains is data based (VITEK MS 3.1).
 
Antibiotic susceptibility of strains
 
Fresh bacterial colonies were added to 2 ml of physiological saline. The density of the bacterial suspension was adjusted to 0.5 Mc Farland it was inoculated onto the surface of Mueller Hinton agar (OXOID, CM: 0337). Selected antibiotic discs (Table 3) were placed on the agar and incubated at 37°C for 24 h.  The diameter interpretation was based on the EUCAST 2019 (European Committee on Antimicrobial Susceptibility Testing V.1.0) recommendations. The sensitivity or resistance of bacteria to antibiotics is evaluated by comparing the inhibition diameters to the minimum inhibition concentration of the discs. If the measured inhibition diameter on the agar is greater than the minimum inhibition concentration of the disc, the bacterium is sensitive to the antibiotic; otherwise it is resistant (Guessennd et al., 2013). 


 RESULTS

Bacterial dissemination in fishes and in water samples
 
Seven bacterial species were isolated from water and in fish organs collected from two aquaculture farms.  Enterobater hormaechei (hor), Enterococcus faecalis (fac), Citrobacter freundii (cit), Bacillus cereus (bac), Pseudomonas aeruginosa (psd), Escherichia coli (col) and Morganella morganii (mor) were isolated and confirmed by biochemical tests and by MALDI-TOF analysis. The strains showed resistance to antibiotics. These isolated strains represent potential sources of pathogenicity for humans. Swab and water samples have similar colonization rates with 29.7 (504/1696) and 29.12% (494/1696), respectively; whereas intestine and gills showed a lower colonization rate by 15% (Table 2). Bacterial species in the aquaculture farms were: Enterobacter hormachaei, E.coli, B. cereus, Enterococcus faecalis and M. morganii with presence of 16, 15.9, 14.9, 14.2, and 14% of the samples, respectively (Table 2). The ANOVA 1 test showed no significant difference between the two farms for the presence of bacterial strains.
 
Antibiotic susceptibility testing
 
Isolated bacterial strains were tested for sensitivity to different families of antibiotics (Table 3). The bacteria E. coli, Citrobacter freundii M. morganii E. faecalis and E. hormachei are subjected to the same antibiotics. On the other hand, strains of Pseudomonas aeruginosa were tested with another group of antibiotics. The results showed that 44.9% (31/69) of the strains were resistant to tested antibiotics and 55.9% were susceptible to  those antibiotics (Table 3). E. coli,  M. morganii and P. aeruginosa strains showed resistance against  3 different antibiotics families (Figure 2A, D, E); while E. hormachei and E. faecalis for 2 antibiotics (Figure 2B and F) and C. freundii strains have multiple resistance against five antibiotics (Figure 2C). Multi-drug resistance for 3 classes of antibiotics is observed in some strains (Figure 2A to F).
 


 DISCUSSION

The bacteriological evaluation of fish and  water  samples  collected from two farms revealed different species of bacteria. The bacterial colonization rate showed that E. coli was the most isolated bacteria followed by P. aeruginosa and E. faecalis. The presence of these bacteria has been shown in other studies that also reported the presence of Bacillus cereus with multi-resistance in aquaculture tanks (Gao et al., 2012).
 
This high prevalence of these three bacteria could be linked to contamination of the feeding sources of fish ponds. Several human activities (farming, laundry, fecal matter, market gardening) around aquaculture areas contaminate natural waters such as rivers and lagoons. These waters, which are prone to microbial contamination, are used as a source of water for ponds and are sometimes untreated (Gabriel et al., 2007; Benie et al., 2017). Rasool et al. (2017) reported the presence of B. cereus in fishes in India, suggesting that the detection   of  bacteria  in  water  and  farmed  fish  is  not limited to a single bacterial species.
 
E. faecalis, which showed a high colonization rate in this study, preferentially this bacterium is found in the intestines of warm-blooded animals. Finding these bacteria in fish that is a cold-blooded animal (poikilotherm), could be explained by human contamination. The presence of E. coli in the fish indicates fecal contamination of the biotope. Saeidi et al. (2018) have reported that the presence of E. coli and other enteric bacteria indicate fecal contamination. Bacillus cereus is one of the bacteria responsible for food poisoning. The presence in aquaculture suggests the persistence of this bacterium in the environment. Different genes responsible for enterotoxin production in B. cereus have been characterized (Ehling-Schulz et al., 2019). So far, no study has been carried out to relate the presence of virulent genes and enterotoxin production in case of isolates of B. cereus from fish.
 
Environmental factors can influence the bacterial colonization of pond water and fish (Fister et al., 2016). The detection of pathogenic bacteria in fish farms could reflect the list of pathogens in fishes (Toranzo et al., 2005; Soto-Rodriguez et al., 2013) and their geographical distribution of diseases and particularly in sub-Saharan Africa with countries with similar fish farming practices. Some studies have reported identical results for bacterial diseases in fishes (Abowei and Briyai, 2011; Eshetu et al., 2014). The detection of multi-resistant strains in this study correlates with the findings of Ouattara et al. (2016) with the dissemination in the aquaculture environment in Cote d’Ivoire. As a consequence of abusive and uncontrolled use of antibiotics for medical, veterinarian and food production, the increase of MDR is a general treat in West Africa (Gao et al., 2012; Devarajan et al., 2015). The rate of bacterial colonization in fish farms could influence yield (Bentzon et al., 2016) as it would result in a loss through fish mortality. It would be necessary to ensure the quality of the water used in the ponds or their source. In fact, there is no boundary between the different environments (industrial, hospital agricultural, animal) and the populations (Rajani et al., 2016; Toule et al., 2017). The results confirm the presence of MDR strains in aquaculture and show the need to investigate  the occurrence of enterotoxigenic B. cereus, E. coli and other bacteria and to study the relationship between their presence and the presence of diarrheal enterotoxin.  


 CONCLUSION

The importance of aquaculture production to provide future fish demands for human consumption is evident. One of the biggest challenges is the surveillance and control of fish production. In Africa, there is lack of surveillance in the food production system. There is a need to correlate human, animal and environment health surveillances. The presence of potential pathogens which are multidrug-resistant in aquaculture farms poses a considerable threat to public hygiene. The distribution of bacteria strains in water and in fish organs correlated in both farms. This study has demonstrated the presence of resistant strains in aquaculture farms and suggests the transmission of bacteria from nearby environments to the fish farms. 


 CONFLICT OF INTERESTS

The authors have not declared any conflict of interests.

 



 REFERENCES

Abowei JFN, Briyai OF (2011). A Review of Some Bacteria Diseases in Africa Culture Fisheries. Asian Journal of Medical Sciences 3(5):206-217.
 

Abowei JFN, Briyai OF (2011). A Review of Some Bacteria Diseases in Africa Culture Fisheries. Asian Journal of Medical Sciences 3(5):206-217.

  
 

Adingra AA, Gore Bi, Ble TM, Dosso M (2010). Evaluation of the bacterial load in tilapia oreochromis niloticus (Linné 1758) sold on the steps of abidjan (Ivory Coast). Agronomie Africaine 22(3):217-225.

  
 

Benie CK, Nathalie G, Adjéhi D, Solange A, Fernique konan K, Desire K, Bourahima B, Marcellin DK, Mireille D (2017). Prevalence and Antibiotic Resistance of Pseudomonas aeruginosa Isolated from Bovine Meat, Fresh Fish and Smoked Fish. Archives of Clinical Microbiology 8(3).

  
 

Bentzon-Tilia M, Sonnenschein Eva C, Gram L (2016). Monitoring and managing microbes in aquaculture -Towards a sustainable industry. Microbial Biotechnology 9:576-584.
Crossref

  
 

Carbonnelle E, Nassif X (2011). Routine use of MALDI-TOF-MS for pathogen identification in medical microbiology. Medical Sciences (Paris) 27(10):882-888.
Crossref

  
 

Devarajan N, Laffite A, Graham ND, Meijer M, Prabakar K, Mubedi JI, Elongo V, Mpiana PT, Ibelings BW, Wildi W, Poté J (2015). Accumulation of clinically relevant antibiotic-resistance genes, bacterial load, and metals in freshwater lake sediments in central Europe. Environmental Science and Technology 49:6528-6537.
Crossref

  
 

Dib AL, Agabou A, Chahed A, Kurekci C, Moreno E, Espigares M, Espigares E (2018). Isolation, molecular characterization and antimicrobial resistance of Enterobacteriaceae isolated from fish and seafood. Food Control 88:54-60.
Crossref

  
 

Ehling-Shulz M, Theresa MK, Didier L (2019). The Bacillus cereus Group: Bacillus species with Pathogenic Potential. Microbiology Spectrometry 7(3):0032-2018.
Crossref

  
 

Eshetu YA, Alemnesh W, Tafesse K, Geraud L (2014). Yersiniosis outbreak in rainbow trout at fish farm in Oromia Regional State, Ethiopia. Ethiopian Veterinary Journal 18(2):35-49.

  
 

FAO (2016). Food and Agriculture Organization of the United Nations. The State of World Fisheries and Aquaculture. Contribution to food security and nutrition for all P. 23.

  
 

Fister S, Robben C, Witte AK, Schoder D, Wagner M, Rossmanith P (2016). Influence of Environmental Factors on Phage-Bacteria Interaction and on the Efficacy and Infectivity of Phage P100. Frontiers Microbiology 7:1152.
Crossref

  
 

Gabriel UU, Akinrotimi OA, Bekibele DO, Onunkwoand DN, Anyanwu PEJ (2007). Locally produced fish feed: potentials for aquaculture development in subsaharan Africa. African Journal of Agricultural Research 2(7):287-295.

  
 

Gao P, Daqing M, Yi L, Limei W, Bingjie X, Lin X (2012). Occurrence of sulfonamide and tetracycline-resistant bacteria and resistance genes in aquaculture environment. Water Research 46(7):2355-2364.
Crossref

  
 

Guessennd NK, Ouattara MB, Ouattara ND, Nevry RK, Gbonon V, Tiekoura KB, Dosso M (2013). Study of multi-resistant bacteria in hospital effluents from a hospital and university centre (CHU) in the city of Abidjan (Côte d'Ivoire). Journal of Applied Biosciences 69:5456-5464.
Crossref

  
 

Koga Vanessa L, Gabriela RR, Sara S, Eliana CV, Alexandre O, Benito Gde-B, Kelly CTde-B, Gerson N, Renata KTK (2015). Evaluation of the Antibiotic Resistance and Virulence of Escherichia coli Strains Isolated from Chicken Carcasses in 2007 and 2013 from Parana', Brazil. Foodborne Pathogens and Disease 12(6):479-485.
Crossref

  
 

Kouadio E, Larissa K, Ahou RK, Tia JG, Boua CA, Lucien PK (2019). Comparative study of three locally available feeds on the growth and nutritional quality of Oreochromis niloticus juveniles. Journal of Applied Biology and Biotechnology 7(05):83-91.
Crossref

  
 

Kouadio IK, Guessennd N, Dadié A, Gbonon V, Tiékoura B, Ouattara MB, Konan F, Dje M, Dosso M (2017). Occurrence and antimicrobial resistance of Enterococcus spp. isolated from lettuce and irrigation water in Abidjan, Côte d'Ivoire. Journal of Food Quality and Hazards Control 4:20-23.

  
 

Kouadio-Ngbesso N, Kouamé-Sina SM, Koffi AR, Toulé AC, Adingra AA, Dadié AT (2019). Shiga toxigenic, enteroinvasive and enteropathogenic Escherichia coli in fish from experimental fish farm (Layo), Côte d'Ivoire. African Journal of Microbiological Research 13(23):369-375.
Crossref

  
 

Koumi RA, Kimou NB, Ouattara IN, Atsé CB, Kouamé PL (2017). Utilization of fish feeds by Côte d'Ivoire fish farmers and its influence on the quantitative competitive commercial fish production. International Journal of Biochemical Reseach Review 19(3):1-13.
Crossref

  
 

Miller RA, Harbottle H (2017). Antimicrobial drug resistance in fish pathogens. Microbiol Spectrum 6(1):ARBA-0017-2017.
Crossref

  
 

Mookerjee S, Batabyal P, Sarkar MH, Palit A (2015). Seasonal Prevalence of Enteropathogenic Vibrio and Their Phages in the Riverine Estuarine Ecosystem of South Bengal. PLoS ONE 10(9):e0137338.
Crossref

  
 

Ouattara MB, Guessennd KN, Coulibaly ND, Saraka ND, Coulibaly KJ, Koffi NR, Ouattara GD, Gbonon V, Tiekoura KB, Dosso M (2014). First Report of Qnr Genes in Multidrugs Resistant Enterobacteria Isolated from Different Ecosystems in Abidjan, Ivory Coast. International Journal of Biological Sciences and Applications 1(4):170-175.

  
 

Ouedraogo AS, Jean Pierre H, Ban˜ uls AL, Oue'draogo R, Godreuil S (2017). Emergence and spread of antibiotic resistance in West Africa: contributing factors and threat assessment. Tropical Health and Medicine 27:147-154.
Crossref

  
 

Pitout JD, Laupland KB (2008). Extended-spectrum beta-lactamase-producing Enterobacteriaceae: an emerging public-health concern. The Lancet Infectious Diseases 8:159-166.
Crossref

  
 

Rajani CSR, Chaudhary A, Swarna A, Puniya AK (2016). Identification and Virulence of Enterobacter sakazakii. Journal of Food Industrial Microbiology 2:108.
Crossref

  
 

Rasool U, Ajaz A, Badroo GA, Mir M, Fayaz S, Mustafa R (2017). Isolation and Identification of Bacillus cereus from Fish and their Handlers from Jammu. India. International Journal of Current Microbiology and Applied Sciences 6(8):441-447.
Crossref

  
 

Saeidi N, Gu X, Tran NH, Goh SG, Kitajima M, Kushmaro A, Schmitz BW, Gin KY-H (2018). Occurrence of traditional and alternative fecal indicators in tropical urban environments under different land use patterns. Applied Environmental Microbiology 84:e00287-18.
Crossref

  
 

Salah MA, Aqel A (2014). Antimicrobials Use in Aquaculture and their Public Health Impact. Journal of Aquaculture Research and Development 5(4):2155-9546.
Crossref

  
 

Saleh BAA, Moussa SMG, Nejdet G (2017). Pathogenic Bacteria for Human and Fish Isolated from Fish Farm in Kastamonu, Turkey. Journal of Aquaculture and Marine Biology 6(3):00157.
Crossref

  
 

Soto-Rodriguez SA, Cabanillas-Ramos J, Alcaraz U, Gómez-Gil B, Romalde JL (2013). Identification and virulence of Aeromonas dhakensis, Pseudomonas mosselii and Microbacterium paraoxydans isolated from Nile tilapia. Oreochromis niloticus, cultivated in Mexico. Journal Applied of Microbiology 1(15):654-662.
Crossref

  
 

Toranzo AE, Magarin˜os B, Romalde JL (2005). A review of the main bacterial fish diseases in mariculture systems. Aquaculture e 246:37-61.
Crossref

  
 

Toulé AC, Adingra A, Kouadio-N'gbesso N, Kambire O, Koffi-Nevry R, Koussemon M (2017). Physicochemical and bacteriological characterization of waters in Layo and Jacqueville aquaculture stations (Ebrié lagoon, Côte d'Ivoire). International Journal of Biological and Chemical Sciences 11(6):2842-2855.
Crossref

  
 

Watts J, Harold S, Lauma L, Michelle H (2017). The Rising Tide of Antimicrobial Resistance in Aquaculture: Sources, Sinks and Solutions. Marine drugs 15:158.
Crossref

  
 

Weichselbaum E, Coe S, Buttriss J, Stanner S (2013). Fish in the diet: a review. Nutrition Bulletin 3(8):128-177.
Crossref

  
 

Yao H, Rachel AK, Célestin BA, Paul EK, Patrice LK (2017). Côte d'Ivoire aquaculture systems perception: Characteristics and influence on national fish production. International Journal of Fisheries and Aquaculture 9(11):108-118.
Crossref

  

 




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