Aquaculture Europe 2023

September 18 - 21, 2023

Vienna,Austria

Add To Calendar 21/09/2023 09:45:0021/09/2023 10:00:00Europe/ViennaAquaculture Europe 2023IMPACT OF OXYTETRACYCLINE EXPOSURE ON FISH SKIN MICROBIOMES IN AN EARTHEN POND POLYCULTURE SYSTEMStolz 0The European Aquaculture Societywebmaster@aquaeas.orgfalseDD/MM/YYYYaaVZHLXMfzTRLzDrHmAi181982

IMPACT OF OXYTETRACYCLINE EXPOSURE ON FISH SKIN MICROBIOMES IN AN EARTHEN POND POLYCULTURE SYSTEM

J. McMurtrie a,b*, S.C. Debnath a,b, E. Vaughan c, R.B. Shahid d, K. Khatun d, B. Kasprzyk-Hordern c , D. Bass e, J. Cable f, B. Temperton a , J .  Delamare-Deboutteville g , C.V. Mohan g, M.G .  Sarower d , M.A. Rouf d, C.R. Tyler a,b

a) Biosciences, University of Exeter, EX4 4HB, UK
b) Sustainable Aquaculture Futures, University of Exeter, EX4 4QD, UK
c) Department of Chemistry, University of Bath, BA2 7AY, UK
d) Fisheries and Marine Resource Technology Discipline, Khulna University, 9208, Bangladesh
e) Centre for Environment, Fisheries and Aquaculture Science, Weymouth, DT4 8UB, UK
f) Schoo l of Biosciences, Cardiff University, CF10 3AX
g) WorldFish, Bayan Lepas, Penang, Malaysia
Email: jm1106@exeter.ac.uk

 



Introduction

 Fish farming is striving to maximise sustainable production to meet the needs of a growing global  human popula tion, however, disease is a major barrier to achieving this

 .  To  address the problem of disease in a quaculture there has been, and continues to be, widespread  use (and misuse) of antibiotics for  both disease treatment and prevention

 . Globally, antibiotic use is particularly prevalent in freshwater finfish culture

, however, it is unclear what influence antibiotic exposure may have on the fish microbiome under normal culture conditions , which is a critical component  for maintaining health and resilience against disease. Here we assessed the effects of exposure to oxytetracycline (OTC) on the fish skin  and pond water microbiomes; antibiotic residue fate; and  development of antimicrobial resistance. This was performed as a mesocosm study in Khulna, Bangladesh to provide realistic environmental and microbial conditions that directly translate to aquaculture practices.

Materials and methods

Tilapia and carp (Oreochromis niloticus  and Labeo rohita)  were  polycultured  in  earthen aquaculture ponds  (3x control and 3x treatment ponds) and exposed  to a  typical  medical  treatment dose (100 mg/kg )  of OTC  via the diet for five days . Sampling of water and fish skin swabs were collected prior to treatment ,  and subsequently at 2 , 9 and 23 days following  the 5 day antibiotic exposure. To characterise the prokaryotic and microeukaryotic communities, amplicon sequencing libraries of pond water filters and fish skin swabs were prepared as previously described

 . PCR-free metagenomes of pond water were also prepared to characterise the diversity of antimicrobial resistance genes selected in the resistome following antibiotic exposure. Sequencing of  16S  V4  amplicons,  metagenomes and 18S V9 amplicons was performed on the Illumina Novaseq SP- 250, S1-150 and Illumina MiSeq V2-150 respectively. To assess antibiotic residue fate, pond water was concentrated by Solid Phase Extraction and quantified by the multi- residue UPLC-MS/MS validated methodology of Holton and Kasprzyk-Hordern

 . Generalised l inear mixed effects modelling  was performed to statistically assess OTC residue fate and fish growth.

Results and discussion

T ilapia grew over the experimental period by 0.61 ± 0.31 g (95%-CI)  < 0.001 per day, with no observed difference between control and treatment groups  p = 0.756, illustrating no toxic or beneficial effects of the antibiotic treatment on growth (Fig. 1A) . Throughout the experimental period, concentrations of OTC in water of control  ponds remained low at 0.045 ± 0.018 µg/L (95%-CI) (Fig 1B) . Two days after the completion of exposure, OTC concentration reached 9.6 ± 2.11 µg/L (95%-CI) in  dosed  pond water, and  the  overall concentration of OTC in treatment ponds was significantly elevated compared to control ponds  p < 0.001. At the final sampling point, 23 days post-exposure, the concentration of oxytetracycline in treatment ponds had returned to  pre-exposure levels.

Ultra-deep sequencing  of  16S V4 amplicons for 384 samples of fish skin and pond water yielded a median sequencing depth of 168,440 paired- end reads per sample. Additionally, 104 samples of pond water were sequenced as 18S V9 amplicons, resulting in a median sequencing depth of 56,184 paired-end reads. We will report the impact of antibiotic exposure on fish skin microbiome community structure and will correlate specific taxonomic shifts to measured oxytetracycline concentrations.  In parallel, to assess the development of antimicrobial resistance following therapeutic use of antibiotics in aquaculture we performed shotgun metagenomic sequencing on 12 pond water metagenomes of control and treatment ponds. Sequencing generated a total of 750 million paired-end reads.  Ongoing analysis  is exploring the diversity and abundance of antimicrobial resistance genes, in addition to mobile genetic elements selected in the resistome, that will be reported upon at the meeting.

 By characterizing animal and environmental health, as well as the development and spread of antimicrobial disease resistance, these analyses aim to provide a comprehensive understanding of the implications for antibiotic (mis)use in aquaculture within the one health framework.

References