The
increase in intensive large-scale fish aquaculture has been linked to the
development of antibiotic resistance within some marine microbial communities.
In Italy, a number of environmentally different areas in the coastal North
Adriatic region have been established as semi-intensive and extensive fish
farms. These farms normally operate either with productive management of the
coastal environment (mostly lagoons) in marine and brackish water using
extensive and semi-intensive methods, or by intensively farming commercially
valuable fish and shellfish species in tanks and cages.
Several
environmental hazards can arise from these techniques, as the intensive
conditions can result in the spread of infectious diseases in the farmed fish
and shellfish species, which are caused by several types of Vibrio, Aeromonas and Photobacterium. The subsequent use of
the antibiotics tetracycline (TET) and oxytetracycline (OXTET), flumequine (FLU),
trimethoprim (TIM) and the association of trimethoprim with sulfadiazide (TIM-SUL),
which have been linked to the induction of antimicrobial resistance (AR) in
marine bacteria by horizontal gene transfer and mobile genetic elements. Pollution
in coastal areas causes significant problems in the marine environment, and can
result in contaminated water that used for drinking, irrigation and recreation,
and hence reduce health quality.
Fig. 1. Different incidences of antibiotic resistance strains in water, sediment and biofilm samples obtained from the aquaculture centres. |
This study measured the global incidence of antimicrobial resistance and the frequency of AR bacteria to either individual or multiple antibiotics commonly used in Italian fish farms at a number of different sites within each centre that are distributed along the Adriatic Sea between the Venetian Lagoon and the Gargano area in Puglia (Italy), as well as in a coastal site in the Veneto region. Samples were taken from sediment, biofilms and water from inlet water (Win) and outlet (Wout) entering and leaving the fish tank/ farm at each aquaculture centre.
Under the
selective pressure of the antibiotics used in fish farms, AR marine bacterial
strains can persist and form an environmental reservoir directly involved in
the seafood chain. AR bacteria exist in natural environments where antibiotics affect
bacterial metabolism, so comparisons were done between bacterial strains from
coastal aquaculture centres and those from an area 2 km away from the
coastline. This meant the data from the more intensively- and recently-treated
aquaculture centres could be compared to a baseline AR incidence. There was a
higher level of susceptibility to FLU, as the resistance frequency was <1%
(0.3%), compared to TET and OXTET, which averaged out at 20% resistance (but
ranged between 10 to 50%).
Veneto I is
a fish farm located in a small “valle di pesca”, (valley/ brackish lake) in the
north of the Adriatic region, where only experimental techniques to produce new
fish species are used. This experimental aquaculture approach seems to be
effective, as it is the centre with the lowest global incidence of AR strains
(24%). Veneto II is also a brackish lake where the fish are farmed in a semi-intensive
culture. In comparison with the first site within the same area, there was a
global incidence of 45% of AR strains to at least one antibiotic, but the most
significant result that has been found for Veneto II is the 18% of
multi-resistant strains in the centre. The authors suggest that this large
difference is because there is a more frequent use of antibiotics in the second
farm, whereas the first one had no records of usage in at least a year.
Gargano I
is an open-sea site located 2km away from the Puglia coastline that
sporadically used antibiotics for intensively-farmed fish in 35 cages up to
2009-2010, and the AR resistance incidence was similar to other centres, but
the level of multi-resistance was similar to that in the coastal sites. Finally,
Gargano II is located in a lagoon in the Gargano peninsula area. Horses and
sheep were being extensively bred in the surrounding area, and were also being
given TET; therefore this external source of TET-resistant bacteria could be
why 50% of strains were resistant to the antibiotic. This site was found to
have the highest incidence of AR, with 79% of strains showing resistance to at
least one antibiotic and a third with multiple resistances, but individually
were still all susceptible to TEM, TEM-SUL and FLU, which are only used in
aquaculture.
Further
research could look into more detail at how the community composition is
altered by the different aquaculture methods and the antibiotics used (i.e.
which microbial species are dominant when a certain antibiotic is introduced).
In addition, they could’ve also investigated whether some strains of the same
bacteria are resistant to at least one of the antibiotics at one site, but
still susceptible to the same ones at other sites, because some antibiotics
have been used for longer periods of time/ higher frequencies (i.e. so that
random mutations and/ or horizontal gene transfer can occur).
Labella, A., Gennari, M, Ghidini, Trento, I., Manfrin,
A., Berrego, J.J., and Lleo, M.M. (2013) High incidence of antibiotic
multi-resistant bacteria in coastal areas dedicated to fish farming. Marine Pollution Bulletin, 70: 197-203
Hello Eleanor, interesting review.
ReplyDeleteI have just reviewed a paper on AR genes in fish-farm in Gargano (Di Cesare et al. 2013). Although authors have worked on Enterococcus only, they cover some of the topics that you highlight. They exposed samples to different antibiotics showing different response in bacterial growth, also leading an idea of selection induced by the used antibiotic. In my opinion a good example of how fish-farm can represent reservoir for AR genes is that exposure to antibiotics can induce AR genes where these genes were absent (i.e. not detected) before as they showed. I hope the reduced use of antibiotics will be a common method in aquacolture not only in Italy.