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SouthAsianJExpBiol;1(3):xxx‐xxx;2011
ISSN:2230‐9799 Vol.1,Issue3,Pagexxx‐xxxhttp://www.sajeb.org
REGULARARTICLE
Antibioticsinaquaculture:Anoverview
R.Vignesha*,B.S.Karthikeyanb,N.PeriyasamyaandK.Devanathana
aCentreforAdvancedStudyinMarineBiology,FacultyofMarineSciences,AnnamalaiUniversity,Parangipettai
608502,Tamilnadu,India
bDepartmentofBioinformatics,SchoolofLifeSciences,BharathidasanUniversity,Tiruchirapalli620024,Tamilnadu,
India
ARTICLEINFO
ArticleHistory:
Received:24‐05‐2011
Revised:04‐06‐2011
Accepted:08‐06‐2011
*CorrespondingAuthor:
Email:vignesh144@gmail.com
Keywords:Antibiotics,Pollutants,
Aquaculture,Impacts,Ecosystems,
HumanHealth
ABSTRACT
Thepresenceofantibioticcompoundsinterrestrialandaquaticenvironment
isofhigherinterestworldwideduetotheemergenceasdangerouspollut‐
antsoftheenvironmentandtothehumanhealth.Fishandshrimpaquacul‐
tureisrecognizedasanimportantlivelihood,whichhasgoodeconomicre‐
turns.Thusvastarraysofantibioticsareappliedtotheaquacultureinabe‐
liefthatitwillenhancetheproductionandalsoinahopethatitwillimprove
thesocioeconomicprofileindevelopingcountries.Butthebaneofantibiot‐
icstothemarineandotheraquaticecosystemsisnotconsideredtoalarger
extent.Theaccessibilityofthegreatnumberofantibiotics,alreadystandard
forhumanuse,makesthemaprecioussourcefortreatmentofother,than
infectious,diseasesinhumansandanimals.Thisreviewpaperhighlightsthe
usageofantibioticsandtheirimpactsinaquacultureenvironment.
1.Introduction
Inmanycountriesaquacultureisamajorthrust
areawhichplaysvitalroleinimprovingcommunity
progress,foodsecurity,povertymitigation,em‐
ploymentandothereconomicactivities.World‐
wideproductionoffarmedaquaticanimalsand
plantshastobereachedtoseveralbillionsaccord‐
ingtotheFoodandAgriculturalOrganization
(FAO).Ashumanpopulationgrows,thedemand
andneedforfishwillgrowflankingit(FAO,2007).
Despitedevelopmentsinfishingtechnology,the
demandforfishwillalmostcertainlyexceedsus‐
tainablelevels.Aquacultureispoisedtofillthegap
betweenfishneedsandsustainablefishingand
needtobescalabletomeetfuturedemands(FAO,
2007).
India,acountrywithanareaof3.3millionsqkm
andapopulationofabout1.21billionpeopleis
artisticwithrichfreshwater,brackishwaterand
marineresources.Thecountryproducesabout5
millionmtoffishinwhichtotalaquaculturepro‐
ductionisabout1.6millionmt(FAO,2007).Aqua‐
cultureproductionhasincreasedthreetimesdur‐
ingthelasttenyears.Althoughaquaculturehas
madeverygoodprogressinthelastfivedecades,it
isstillaverysmallsub‐sectorofagriculture.Consid‐
eringthecountry’svastprospectiveforaquacul‐
ture(bothfreshwaterandcoastal),therecent
achievementsbyR&Donvariousaspectsofaqua‐
culture,inadditionwiththepublicandprivatesec‐
torsprospectaquaculturewithanoptimisticeco‐
nomicactivity.
2
Vigneshetal.,SouthAsianJExpBiol;1(3):xxx‐xxx;2011
Duringthelasttwo‐threedecades,therewasmas‐
sivegrowthoffishandshrimpculturingwhichobvi‐
ouslyimprovedcountry’sexportvalueandalsohas
unfortunatelyresultedinharmfulenvironmental
impacts.Theaccomplishmentinthemassproduc‐
tionofhatcherybredshrimpsandfishesalsolead
theroadtowardsinventionofadvancedculture
techniquestomeetitsdemand.Withthehelpof
advancedculturetechniquesevenwithlowinvest‐
menthighyieldwasobtained.Thisgrowthinvited
multinationalcompaniestoinitializebusinessand
theyestablishedtheircompaniesincoastaland
agriculturallandsinthe1990s.Themajoraquacul‐
tureshrimpproducingregionsandtheprogressin
aquacultureproductionofshrimpsinAsiafrom
2003‐2011isshowninTable1andTable2.Asa
sourceoflivelihoodcapturefisheriesandaquacul‐
tureemployed43.5millionpeoplein2006.Many
countriesareinvestingheavilyintheaquaculture
sectorexpectingthefuturedemandforhighquality
seafoodwillbemetbyfarmedfish(FAO2009).
Aquacultureiswidelyusedasanimportantweapon
intheglobalfightagainstmalnutritionandpoverty,
particularlywithindevelopingcountrieswhereover
93%ofglobalproductioniscurrentlyproduced,pro‐
vidinginmostinstancesanaffordableandmuch
neededsourceofhighqualityanimalprotein,lipids
andotheressentialnutrients.(Alberttaconetal.,
2010).
2.AntibioticsandAquaculture
Alongwiththedevelopmentofaquaculture,dis‐
easescausedbyvariousetiologicalagentsfollowed
bymortalityofculturedstockhavebecomelimiting
factorsinproduction.Hence,thefarmersandthe
hatcheryoperatorshaveresortedtotheuseof
variousremedialmeasures,includinguseofantim‐
icrobialsanddrugsforcontrollingthedisease.The
frequencyofutilizingtheseantibioticsandother
chemicalsismoreinhatcheriesandscientificfarms
thanintraditionalfarms.
Amongthedrugsemployedinagriculture,antibiot‐
icsarethemostwidelyusedforanimalhealthand
management(Levey,1992).Accordancewitha
2008amendmenttotheAnimalDrugUserFeeAct,
theU.S.FoodandDrugAdministration(FDA)re‐
leasedanannualamountofantimicrobialdrugs
soldanddistributedforuseinfoodanimals.The
grandtotalfor2009is13.1millionkilogramsor
28.8millionpounds(USFDA,2008).Thetotal
amountofveterinaryantibioticsusedintherapeu‐
ticpurposesandasfeedingadditiveswereapproxi‐
mately1000tonsand500tonsin2005(KFDA,
2005).Theuseofantimicrobialsinaquacultureba‐
sicallystartedwiththeworkofGutsell(1946)who
recognizedtheprospectiveuseofantibiotics
(sulphanamidesforcombatingfurunculosis).Ac‐
cordingtoKummerer(2009a)antibioticsarenatu‐
rallyoccurringmanmadechemicalsthatcanbe
dividedintodifferentclassessuchasβ
‐lactams,
quinolonestetracyclines,macrolidsandsulfona‐
mides.Morenumberofantibioticslikechloram‐
phenicol,oxyteteracycline,kanamycin,nifurprazine,
Country200320042005200620072008200920102011
South‐
eastAsia
857,229993,5651,150,7141,333,6691,353,5541,382,6931,347,6981,362,4161,444,896
China789,373935,9441,064,9491,080,4791,265,6361,268,0741,252,7411,365,0691,512,877
India/
Bangla‐
desh
169,743191,064206,222209,047171,265291,890289,750331,250360,000
Americas296,461326,266379,363446,471449,099470,717495,033501,917523,550
Africa/
Mideast
25,25725,50026,77127,79026,64128,41028,25031,50038,500
Others7,7037,5859,96811,7519,50114,00015,00016,00016,000
Table1:Shrimpaquacultureproductionbymajorproducingregions(mt).
Sources:2003‐2007,FAO(2009);2008‐2011,GOALestimate(Jory,2010).
Country200320042005200620072008200920102011
China789,373935,9441,064,9491,242,3851,265,6361,268,0741,252,7411,365,0691,512,877
Thailand330,725360,292401,251500,800501,200473,622455,000420,000420,000
Vietnam231,717275,569327,200349,000376,700391,000418,148429,616475,946
Indonesia191,148238,567279,539339,803330,155315,050250,000275,000302,000
India113,240133,020143,170144,347107,665126,042106,000125,000135,000
Bangladesh56,50358,04463,05264,70063,600165,848183,750206,250225,000
Table2:ShrimpaquacultureproductioninAsia(mt).
Sources:2003‐2007,FAO(2009);2008‐2011,GOALestimate(Jory,2010).
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Vigneshetal.,SouthAsianJExpBiol;1(3):xxx‐xxx;2011
oxolinicacid,flumequin,ciproflaxinandothers
wereintroduced(AustinandAustin,1993).Later
theseantibioticswerefurtherclassifiedasantibac‐
terials,antivirals,antifungal,antiprotozoan,anti‐
metazoanpreparations,probiotics,immunostimu‐
lants,vaccines,bactecins,hormones,growthstimu‐
lants,anestheticsandbioremediatorsforbothbio‐
augmentorsandbiostimulators.
3.ImpactsofAntibiotics
Antibioticsaredesignedtoinhibitthegrowthand
tokillpathogenicbacteria.Theygenerallyactin
oneofthethreeways:Bydisruptingcellmem‐
branes,bydisruptingproteinorDNAsynthesisor
byinhibitingenzymeactivity.Compoundswithan‐
tibioticactivityareselectedforuseinhumanand
veterinarymedicinebecauseoftheirselectivetox‐
icitytocellmembranes,ribosomalactivityoren‐
zymeactivityinprokaryoticcells.Despitetheirlow
toxicity,therearesignificantenvironmentalcon‐
cernswithwidespreaduseofantibiotics.Manyan‐
tibioticsarestablechemicalcompoundsthatare
notbrokendowninthebody,butremainactive
longafterbeingexcreted.Atpresent,antibiotics
makeaconsiderablecontributiontothegrowing
problemofactivemedicalsubstancescirculatingin
theenvironment.Thecommonpracticesthatoccur
inthefishindustry,particularlyindevelopingcoun‐
tries,wherelargeamountsofantibioticsareused
toavoidinfection.(Cabelloetal.,2006).
Thecontinuousandheavyuseofantibioticsinthe
aquacultureenvironmentscouldleadtovarious
hazardswithconcerntothehealthofaquaticor‐
ganismsaswellastothehumansonconsumption
offishesandshrimps.Theantibioticsusedinaqua‐
culture,eitherforprophylacticorremedialpur‐
posesoftenmountupinthetissueofaquaticani‐
mals.Presenceofanti‐microbialdrugresiduesin
theedibletissuescancauseallergies,toxiceffects,
changesintheintestinalmicrobialfaunaandacqui‐
sitionofdrug‐resistance.Remainsofchlorampheni‐
colinfoodconsumedbyhumanscanevenresultin
aplasticanemia,whichleadstoverybrutalbone
marrowdiseases.Nitrofuranantibioticsareknown
tocausecancerandsomanyotherdiseases.
Antibioticscanevenbeconsideredasamajorfac‐
torthatisresponsibleforaffectingthemicrobial
communityintheenvironment.Butthestudieson
theantibioticsanditseffectsonaquaticfarmsare
lessandthereasonforthisobservablefactisvery
wellexplainedbyKummerrer(2009b),whostated
thattheconcentrationofantibioticswereinmono‐
gramsandlowermicrogramsperlitersrangeand
thislowerconcentrationmakesitdifficulttostudy
theeffects.Alsothemicrobesarepresentinmuch
lowerdensitieswhichmakefurthercomplications
indeterminingthemicrobialcommunitystructure.
Antibioticsactasanecologicalbarrierintheenvi‐
ronmentthatcouldpotentiallyaffectmicrobial
communities.TheeffectsincludePhylogenetic
structurealteration,resistanceexpansionandeco‐
logicalfunctiondisturbanceinthemicroecosystem
(ChanDing,2010).
Antibioticswhichhaveanaffinityforabsorbing
ontoaparticulatematter,especiallyinthemarine
environmentmaypersistandremainactivefor
muchlongerintheenvironment(Halling‐Sorenson
etal.,1998).Anoxicsedimentsarecommoninthe
aquaticenvironmentandmostantibioticcom‐
poundspersistmuchlongerintheseanoxiccondi‐
tions.Hektoenetal.(1995)showedthatantibiotics
buriedinsedimentsasshallowas1‐7cmhavehalf
livesofmorethan300days.Thisemphasizesthat
theantibioticscanbuildupintheaquaticenviron‐
menttodangerouslevelsthatmayeffectbenthic
communitiesandcontinueupthroughthefood
chain.
Researchhasprovedthatmanychemicalsmanu‐
facturedandusedtodayentertheenvironment,
disperseandpersistintheenvironmentformuch
longeroriginallyexpected(Kolpin,2002).Theusage
ofantibioticsinthefishandshrimpaquaculture
hasbecomeamajorproblemwhichseepages
throughpondbottomanddischargesaswastesand
effluentsmixingintorunoffwaterandcovering
coastalmangrovesdestroyingimportantnatural
habitatsforshrimps,fishesandtohumans
(Jatindraetal.,2009).Thestudiesoffishfarms
haveshownthatthemajorityofantibioticsadded
infeedarenotassimilatedbyfishbutgointothe
environments(Weston,1996).LeandMunekage
(2004)alsoreportedthatantibioticsresiduesmay
causeharmfuleffectonecosystems.Thustheaccu‐
mulationoftheseantibioticsinsedimentswilldefi‐
nitelyalterthenaturalfunctionsthatmighttake
placeintheenvironment.Itisforthisreason,that
mostoftheimportingcountrieshavecompletely
bannedtheuseofcertainantibiotics.Thelistof
bannedantibioticsbymarineproductsexportde‐
velopmentauthorityofIndia(MPEDA)isgivenin
Table3.
Inhatcheries,itisthecommonpracticetouseanti‐
bioticsasaprophylactic/therapeutic,measurees‐
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Vigneshetal.,SouthAsianJExpBiol;1(3):xxx‐xxx;2011
peciallywhenlarvaldevelopmentishindered.This
isalsomeanttotreatthemicrobialinfectionsin
storedwaterinhatcherytanks,whilelarvaland
postlarvaldevelopmentcontinues.Thepractice
canbereplacedbyusingprobiotics(helpfulmi‐
crobes).Enrichmentoflivelarvalfeedswithantibi‐
oticstoenhancequality(bio‐encapsulation)can
alsoleadtoilleffectsofantibioticsuse.Allthese
measureswillleaveantibioticresidueinthecul‐
turedstock.Thustheapplicationofantibioticsand
otherchemicalsintheaquaculturefarmsto
achievehighproductioncauseddiseaseproblems
andcoastalenvironmentalpollution.
4.Antibioticresistance
Theaquaticenvironmenthasmoredirectandinti‐
matecontactwithhumanlifeduetothewidecon‐
sumptionoffishandshrimps.Thusitmaytransfer
antibioticresistanceposingthreattopublichealth
andecosystems.Theantibioticsusedareoftennon
‐biodegradableandremainintheaquacultureenvi‐
ronmentforlongperiodsoftime.Thisencourages
thegrowthofbacteria,whichcansurviveinthe
presenceoftheseantibiotics,acquiringaresistance
thatispassedontoconsequentgenerations.The
dangeris,thesebacteriacanbetransferredtohu‐
manandanimalpathogens,leadingtoincreased
infectiousdiseaseinfish,animalsandhumans
alike.
Antibioticusagehasreceivedalotattentioninthe
mediaforthepastfewyearsduetotheincreasing
numberofdiseasesbecomingresistanttotradi‐
tionaltreatments.Thecontinuousandindiscrimi‐
nateusageofantibioticsintheaquaculturefarms
hasledveryseriousconsequences.Itpavedwayfor
theoutbreakofmutagenic,multidrugresistantmi‐
crobialstrainswhichcancauseinfectiousdiseases.
Marinefishfarmsaresurroundedbyawiderange
ofmarineecosystemlikefishing,andothermarine
foodprocessingunits.Someofthewildfishesfeed
fromleftoverfoodpelletswhicharemedicated
withantibioticsandobviouslyitpassestothe
fishesandaresearchhasconfirmedthatwildfishes
capturearoundaquacultureareasingestthepel‐
lets.Residuesoftetracyclineandquinoloneswere
reportedinwildfishescapturedintheseaquacul‐
tureareas(Tendenciaetal.,2001).Apartfrom
antibioticresistance,theseantibioticsgetaccumu‐
latedinthetissuesofthefishesandshrimps.
Theevolutionofresistanceisaninevitableconse‐
quenceofantibioticuse(Stokes,2001)andthis
consequenceisperhapsthemostimportantimpli‐
cationofantibioticuseinaquacultureforavariety
ofreason(Salyersetal.,2002).TheuseofOxytet‐
racycline(OTC)inaquaculturehasbeenshownto
causeaseasonalshiftinbacterialspeciestowards
enterobacteriaceaeandisassociatedwithantibi‐
oticresistance(Guardabaasietal.,1999;Wollen‐
bergeretal.,2000)samplestakenfromgillsand
intestinesofwildandcommercialfishescaptured
nearfishfarmingactivitieshaveshownhighfre‐
quenciesofmultipleantibioticresistance(Rhodes
etal2000,Guardabassietal.,1999).Alsotheresis‐
tantstrainsofbacteriarequireevenhigherlevelsof
dosingtotreatdiseasesleadingtomoreantibiotic
reachingthenaturalenvironment(Bruunetal.,
2003).
Thescientificevidenceisthatuseofantibioticsin
foodproducinganimalscanleadtoresistancein
intestinalbacteriaandthisresistancecanthenbe
transmittedtothegeneralpopulationcausing
treatment‐resistantillness.Infishfarmingaquacul‐
turemariculturethewidespreaduseofantibiotics
fortreatingbacterialdiseaseshasbeenassociated
withthedevelopmentofantibioticsresistancein
Aeromonashydrophila,A.salomonicida,Edward
siellatarda,E.icttaluri,Vibrioanguillarum,
V.salmonicida,Pasteurellapiscida(Hernandezser‐
vanop,2005).
Thegeneralpremiseofmanystudiesexamining
resistanceisthatasmoreantibioticisintroduced
intotheenvironmentthegreaterwillbetheinci‐
denceofantibioticresistanceinthebacterialflora
(Smithetal.,1994a;Halling‐sorensonetal.,
1998).Whenantibioticsarepresent,resistant
strainshaveanadvantageovernon‐ resistant
strainsandpredominateinthepopulation.Antibi‐
oticresistancebacteriaandtheirresistancegenes
areoftendetectedinaquaticecosystems(Esiobuet
1 Chloramphenicol 11 Dimetridazole
2 Nitrofurans 12 Metronidazole
3 Neomycin 13 Onidazole
4 NalidixicAcid 14 Ipronidazole
5 Sulphamethoxazole 15 Nitroimidazoles
6 Aristolochia 16 Clenbuterol
7 Chlorprpmazine 17 Diethylstilbestrol
8 Colchicine 18 Sulfonamide
9 Apsone 19 Floroquinolones
10 Chloroform 20 Glycopeptides
Table3:ListofAntibioticsandPharmacologicallyActive
SubstancesBannedForUseinIndianAquaculture.
Source:Marineproductexportdevelopmentauthority
(MPEDA,2001).
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Vigneshetal.,SouthAsianJExpBiol;1(3):xxx‐xxx;2011
al.,2002;Schwartzetal.,2003;Biyelaetal.,2004).
Tendenciaanddelapena(2001)foundthatantibi‐
oticresistancewasassociatedwithhistoricaland
currentuseofantimicrobialswhichwasfoundto
behighinshrimppondsusingoxolinicacidinfeed.
Anotherstudyshowedthatthereisanincreasein
tetracyclineresistancegenesabundance,
(comparedto16srRNAgenes)atlowleveloxytet‐
racyclineexposureinaquaticsystems(Knappetal.,
2008).Phylogeneticanalysisofseveralgroupsof
antibioticresistancegeneshassuggestedthatge‐
neticmaterialforpresent‐dayantibioticresistance
hashadalonghistoryofselectionanddiversifica‐
tionwellbeforethecurrent‘antibioticera’(Aminov
andMackie,2007).
Ithasbeenextensivelyshownthatexcessiveand
prophylacticuseofantibioticsinanimalshasa
negativeinfluenceonantibiotictherapyofanimal
andhumanbacterialinfectionsbecause1)zoonotic
antibioticresistantbacteriaareabletoinfecthu‐
manbeings;and2)animalandhumanpathogens
cansharegeneticdeterminantsforantibioticresis‐
tanceastheresultofhorizontalexchangeofge‐
neticinformation(HarrisonandLederberg1998;
Teuber2001;Cabello,2003;Anguloetal.,2004;
Cabello2004;Molbak,2004;Wassenaar,2005).
Becauseoftheirtoxicitytomicroorganisms,antibi‐
oticsmayalsoaffectthecompositionofthephyto‐
planktoncommunity,thezooplanktoncommunity
andeventhediversityofpopulationsoflargerani‐
mals.Inthismanner,potentialalterationsofthe
diversityofthemarinemicrobiotaproducedby
antibioticsmayalterthehomeostasisofthemarine
environmentandaffectcomplexformsoflifein‐
cludingfish,shellfish,marinemammals,andhuman
beings.Forallthesereasons,extremeantibiotic
useinaquacultureshouldbeofhighconcerntothe
aquacultureindustryanditsregulators,topublic
officialsdealingwithhumanandveterinaryhealth
andwiththesafeguardingoftheenvironment,and
tonon‐governmentalorganizationsdealingwith
theseissues.
Itisnowgenerallyrenownedthatthenaturalenvi‐
ronmentharboursanenormousdiversityofantibi‐
oticresistancegenesandsomesoilbacteriamay
evensurviveonantibioticsusingthemastheirsole
sourceofcarbon(D’Costaetal.,2006;2007;
Wright,2007;Martínez,2008;Dantasetal.,2008).
Theprincipalpollutanttransformationprocesses,
microbialdegradationorbiotransformationmaybe
themostefficientwayforremovalofchemicalpol‐
lutantsandtheirtoxicityfromtheenvironments
(Srinivasanetal2001).Antibioticshavenotalways
beenusedinaresponsiblemannerinaquaculture
and,inanumberofreportedsituations;controlof
theuseofantibioticshasnotprovidedaproper
assuranceofthepreventionofriskstohumans.
FAO,theWorldHealthOrganization(WHO),the
InternationalOfficeofEpizootics(OIE)andanum‐
berofnationalgovernmentshavealreadyraised
theissueofirresponsibleuseofantibioticsinall
productionsectors,withparticularconcernforthe
potentialriskstopublichealth.Manygovernments
aroundtheworldhaveintroduced,changedor
tightenednationalregulationsontheuseofantibi‐
otics,ingeneralandwithintheaquaculturesector.
5.PossibleActions
Naturalbiodegradationofantibioticsintheenvi‐
ronmentmaynotbeanadequateoptionfortheir
eradication.Someoftheseproducts,suchasqui‐
nolones,takeseveralmonthstodegrade.Theup‐
shotisthatduringthattime,antimicrobialsare
drawnintheselectionforresistanceanditsgenetic
transfertootherbacteriaandappearanceofviru‐
lencefactors.Drugresistanceisamultifacetedcon‐
cernthathaslittlechancetoimprove,forresis‐
tanceisnotreversible.Therefore,thereisanur‐
gentneedtoembarkuponitinadeterminedman‐
ner.Someofthemostinstantaneousactionscould
be:
1.Synchronizationbetweenhuman,veterinary
andenvironmentalsectorstorecognizethe
magnitudeoftherelationshipsamongthe
occurrencesofantimicrobialresistancein
humans,animalsandtheenvironment.
2.Enforcementofexistinglegislation.Approxi‐
mately80%oftheworld’saquaculturepro‐
ductionoriginatesincountrieswitheither
scarceboundariesonantimicrobialuseor
negligentenforcement.
3.Themosteffectivemeanstoforestallthe
developmentandextendofantimicrobial
resistanceistoreducetheneedforantibiotic
treatment.
4.Impartingeducationaboutthesensibleuse
ofantibioticstotheaquaculturesectorsis
needful.
6
Vigneshetal.,SouthAsianJExpBiol;1(3):xxx‐xxx;2011
6.Conclusion
Researchmustcontinueintothedevelopmentof
safeandeffectivevaccinesagainstbacteria.Safe
andeffectivevaccineseliminatetheneedtoapply
antibiotics.Thepresenceofresidualantibiotics/
antibioticresidues,antibioticresistanceinmarine
bacteriaandinfishpathogens,andeffectsonthe
diversityofphytoplanktonandzooplanktoninar‐
eassurroundingaquaculturesitesshouldalsobe
ascertained.Investigationofthepresenceofresid‐
ualantibiotics/antibioticresiduesinfree‐ranging
(wild)fishandshellfisharoundaquaculturesites
andinthemeatofmarketablesalmonisnecessary.
Thepassageofantibioticresistancedeterminants
frombacteriainthemarineenvironmenttohuman
andterrestrialanimalpathogensshouldalsobe
investigated.Centralizedepidemiologicalstudiesof
fishinfectionsshouldbeimplementedandtheir
resultsrelatedtoantibioticusageandantibiotic
resistanceshouldbejustified.Thepotentialforex‐
posureofaquacultureworkerstoantibioticsshould
bedeterminedandthepotentialeffectsofthisex‐
posureshouldbeascertained.
Medicineshaveanimportantroleinthetreatment
andpreventionofdiseaseinbothhumansandani‐
mals.Althoughthesideeffectsonhumanandani‐
malhealthareusuallyinvestigatedinthorough
safetyandtoxicologystudies,thepotentialenvi‐
ronmentalimpactsofthemanufactureanduseof
medicinesarelesswellunderstoodandhaveonly
recentlybecomeatopicofresearchinterest.
Theaccessibilityofthegreatnumberofantibiotics,
alreadystandardforhumanuse,makesthema
precioussourcefortreatmentofother,thaninfec‐
tiousdiseasesinhumansandanimals.Almostnoth‐
ingisknownabouttheeffectsofsubinhibitoryan‐
tibioticsonarchaeainspiteofthattheyarewell‐
knownmembersinmicrobialcommunities.
Broaderandwelldefinedstudyintheseareaswill
helpinunderstandingtheantibioticsandresistance
mechanismsdevelopedbynaturalecosystems.This
willalsoassistinmakingliablechoiceswheninter‐
actingwiththeseecosystemsintherouteofclinical
oragriculturaluseofantibiotics.
References
AlbertTaconGJ,MarcMetian,GiovanniM,Turchini,SenaDeSilva
S(2010)Responsibleaquacultureandtrophiclevelimplicationsto
globalfishsupply.Reviewsinfisheriesscience18:94‐105.
AminovRI,MackieRI(2007)Evolutionandecologyofantibiotic
resistancegenes.FEMSMicrobiologyLetters271:147–161.
AnguloFJ,Nargund,VN,ChillerTC(2004)Evidenceofanassocia‐
tionbetweenuseofanti‐microbialagentsinfoodanimalsandanti
‐microbialresistanceamongbacteriaisolatedfromhumansand
thehumanhealthconsequencesofsuchresistance.Journalof
VeterinaryMedicine51:374–379.
AustinB,AustinDA(1993)BacterialFishPathogens:Diseaseif
FarmedandWildFishEllisHarwood,NewYork2:384.
BruunMS,MadsenL,DalsgaardI(2003)Efficiencyofoxytetracy‐
clinetreatmentinrainbowtroutexperimentallyinfectedwith
Flavobacteriumpsychrophilumstrainshavingdifferentinvitro
antibioticsusceptibilities.Aquaculture215:11–20.
BiyelaPT,LinJBezuidenhoutCC(2004)theroleofaquaticecosys‐
temsasreservoirsofantibioticresistantbacteriaandantibiotic
resistancegenes.WaterScienceTechnology50:45‐50.
ChanDing,JianzhongHe(2010)Effectofantibioticsinthe
environmentonmicrobialpopulations.AppliedMicrobiologyand
Biotechnology87(3):925‐41.
CabelloFC(2003)Antibioticsandaquaculture.Ananalysisoftheir
potentialimpactupontheenvironment,humanandanimalhealth
inChile.FundacionTerram.AnalisisdePoliticasPublicas17:1–16.
CabelloFC(2004)AntibioticsandaquacultureinChile:implications
forhumanandanimalhealth.ReviewMedicineChile132:1001–
1006.
CabelloFC(2006)Heavyuseofprophylacticantibioticsinaquacul‐
ture:agrowingproblemforhumanandanimalhealthandforthe
environment.EnvironmentalMicrobiology8:1137‐‐1144.
CodexCodeofPracticetoMinimizeandContainAntimicrobial
Resistance(2002)TheStateofWorldFisheriesandAquaculture
report,FAO.
DantasG,SommerMO,OluwasegunRD,ChurchGM(2008)Bacte‐
riasubsistingonantibioticsScience320:100–103.
D’CostaVM,McGrannKM,HughesDW,WrightGD(2006)Sam‐
plingtheantibioticresistomeScience311:374–377.
D’CostaVM,GriffithsE,WrightGD(2007)Expandingthesoilanti‐
bioticresistome:exploringenvironmentaldiversity.CurrentOpin‐
ioninMicrobiology10:481–489.
EsiobuN,ArmentaLIkeJ(2002)Antibioticresistanceinsoiland
waterenvironments.InternationalJournalofEnvironmental
Health12:133‐144.
FAO/SEAFDEC/CIDA(1996,1997,2000)Useofchemicalsinaqua‐
cultureinAsia,ProceedingsoftheMeetingontheUseofChemi‐
calsinAquacultureinAsia,Iloilo,thePhilippines.
FAO(2009)WorldAgriculture:towards2030‐2050anFAOPer‐
spective,Rome,Italy.
GuidelinesfortheResponsibleandPrudentUseofAntimicrobial
AgentsinVeterinaryMedicine,OIETerrestrialInternationalAnimal
HealthCode(2006).
GuardabassiL,DalsgaardA,RaffatelluM,OlsenJE(2000)Increase
intheprevalenceofoxolinicacidresistantAcinetobacterspp.
observedinastreamreceivingtheeffluentfromafreshwater
troutfarmfollowingthetreatmentwithoxolinicacid‐medicated
feed.Aquaculture188:205–218.
Gutsell,J(1946)Sulfadrugsandthetreatmentoffurunculosisin
trout.Science104:85‐86.
7
Vigneshetal.,SouthAsianJExpBiol;1(3):xxx‐xxx;2011
Halling‐SorensonB,NorsNielsesS,LanzkyPF,IngerslevF,
lutzhoftHCH,JorgensenSE(1998)occurrencefateandeffectsof
pharmaceuticalsubstancesintheenvironment‐areview.Chemos‐
phere36:357‐394.
HektoenH,BergeJA,HormazabalV,Yndestad,M(1995)Persis‐
tenceofantibacterialagentsinmarinesediments.Aquaculture
133:175–184.
HernandezGC,UlloaPJ,VergaraOJA,EspejoTR,CabelloCF(2005)
Vibrioparahaemolyticusinfectionsandalgalintoxicationsasemer‐
gentpublichealthproblemsinChile.ReviewMedicineChile133:
1081–1088.
HarrisonPFJ,LederbergJ(1998)AntimicrobialResistance:Issues
andOptions.WorkshopReport.NationalAcademyPress,Washing‐
ton,DC.
Jatindra(2009)Degradationofantibiotics(Trimethoprimand
Sulphamethoxazole)pollutantsusingUVandTiO2inaqueous
medium.Modernappliedscience3:2.
JoryDE(2010)GOALProductionDataProjectsTemperedAquacul‐
tureGrowth:TheGlobalAquacultureAdvocate:8‐11.
KolpinDW,FurlongET,MeyerMT,ThurmanEM,ZauggSD,Barber
LB,BuxtonHT(2002)Pharmaceuticals,hormones,andotheror‐
ganicwastewatercontaminantsinUSstreams1999–2000.Ana‐
tionalreconnaissance.EnvironmentScienceandTechnology
36:1202–1211.
KummerrerK(2009a)Antibioticsintheaquaticenvironmenta
reviewpart1.Chemosphere75:417‐434.
KummerrerK(2009b)Antibioticsintheaquaticenvironmenta
reviewpart11.Chemosphere75:435‐441.
KnappCW,EngemannCA,HansonML,KeenPL,HallKJ,Graham
DW(2008)indirectevidenceoftransposon‐mediatedselectionof
antibioticresistancegenesinaquaticsystemsatlow‐leveloxytet‐
racyclineexposures.EnvironmentalScienceandTechnology42:
5348–5353.
LeveySB(1992)theantibioticparadox,howmiracledrugsare
destroyingthemiracle.PlenumPublication,NewYork.
LeTX,MunekageY(2004)Residuesofselectedantibioticsinwater
andmudfromshrimppondsinmangroveareasinVietNam.Ma‐
rinePollutionBulletin49:922‐929.
MartínezJL(2008)Antibioticsandantibioticresistancegenesin
naturalenvironments.Science321:365–367.
MPEDA(2001)Notificationofbanonuseofantibiotics/drugsetc.
inaquaculture.DeputyDirector(Aqua.),MPEDA,MinistryofCom‐
merce,Govt.ofIndia.
MolbakK(2004)spreadofresistantbacteriaandresistancegenes
fromanimalstohumansthepublichealthconsequences.Journal
ofVeterinaryMedicine51:364‐369.
NawazMS,EricksonBD,KhanAA,KhanSA,PothuluriJV,RafiiF,
SutherlandJB,WagnerD,CernigliaCE(2001)Humanhealthimpact
andregulatoryissuesinvolvingantimicrobialresistanceinthefood
animalproductionenvironment.RegulationResolutionPerspec‐
tives1:1–10.
RhodesG,HuysG,SwingsJ,McGannP,HineyM,SmithP,Pickup
R.W(2000a)Distributionofoxytetracyclineresistanceplasmids
betweenaeromonadsinhospitalandaquacultureenvironments:
implicationofTn1721indisseminationofthetetracyclineresis‐
tancedeterminantTetA.AppliedandEnvironmentalMicrobiology
66:3883–3890.
ResponsibleUseofAntibioticsinAquaculture(2005)FAOTechni‐
calFisheriespaper469.
SalyersAA,GuptaA,WangY(2004)Humanintestinalbacteriaas
reservoirsforantibioticresistancegenesTrendsinMicrobiology
12:412‐416.
SrinivasanM,BragadeeswaranSandRajaramR(2001)Roleof
NeemCake,NeempowderinAquacultureVol.IV.
SrinivasanM,BalachandarSandBragadeeswaranS(1999)Mud
Crabculture.AgriGoldSwarnaSedyamVolII.(5).
StokesHW,HolmesAJ,NieldBS,HolleyMP,NevalainenKMH,
MabbuttBC,GillingsMR(2001)GenecassettePCR:sequence‐
independentrecoveryofentiregenesfromenvironmentalDNA.
AppliedandEnvironmentalMicrobiology67:5240–5246.
SmithP,HineyMP,SamuelsenOB(1994)Bacterialresistanceto
antimicrobialagentsusedinfishfarmingacriticalevaluationof
methodandmeaning.SchwartzT,KohnenW,JaansenB,ObstU
(2003)Detectionofantibioticresistantbacteriaandtheirresis‐
tancegenesinwastewatersurfacewateranddrinkingwater
biofilms.FEMSMicrobiologyEcology43:325‐335.
Towardssafeandeffectiveuseofchemicalsincoastalaquacul‐
ture.FAO(1997)ReportsandStudies,GESAMPRome65:40
WestonDP(1996)Environmentalconsiderationsintheuseof
antibacterialdrugsinaqua‐culture.AquacultureandWaterRe‐
sourceManagement.BlackwellScience,Oxford140–165.
Tendencia,delaPena(2001)Antibioticresistanceofbacteria
fromshrimpponds.Aquaculture195:193‐204.
TeuberM(2001)Veterinaryuseandantibioticresistance.Current
OpinioninMicrobiology4:493‐499.
WrightGD(2007)theantibioticresistomethenexusofchemical
andgeneticdiversity.NatureReviewMicrobiology5:175–186.
WassenaarTM(2005)Useofantimicrobialagentsinveterinary
medicineandimplicationsforhumanhealth.CriticalReviewsin
Microbiology31:155‐169.
WollenbergerL,HallingSorensenB,KuskKO(2000)Acuteand
chronictoxicityofveterinaryantibioticsofDaphniamagna.
Chemosphere40:723‐730.