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Sister chromatid exchange test detection of
toxin-induced damage in cultured fish
J Lobillo, Jv Delgado, A Rodero
To cite this version:
Sister chromatid
exchange
test
detection
of toxin-induced
damage
in cultured fish
J Lobillo JV
Delgado
A
Rodero
Facultad de
I!eterinaria,
Universidad deC6rdoba,
DepartaTnento
deGen6tica,
Avda MedinaAzahara, 9, 14005 Cdrdoba, Spain
(Proceedings
of the 9thEuropean Colloquium
onCytogenetics
of DomesticAnimals;
Toulouse-Auzeville,
10-13July
1990)
sister chromatid exchange
(SCE) /
genotoxicity/
fishINTRODUCTION
In recent years, industrial and
agricultural
toxic wastes in waters from theGuadalquivir
Basin,
Gulf of Cadiz and the Strait of Gibraltar have increased. Thisgrowing
contamination has motivated our team todevelop
thecytogenetic
sister chromatidexchange
(SCE)
test,
with the aim ofdetecting
the effects of these wasteson the autochthonous cultured and wild fish
species
of the Southern Atlantic offthe coast of
Spain.
The SCE test consists of the detection of increases in the normal mean number
of sister chromatid
exchanges
inmetaphase
M2 cells. These cells are those whichhave
undergone
two rounds ofreplication
in the presence of5-bromodeoxyuridine
(BrdU).
The chromatic chromatid differentiation iseasily
detectedby
simple
acridine orange
staining
or with the fluorescenceplus
Giemsa(FPG)
technique.
MATERIALS AND METHODS
Fishes
belonging
to Rutilus alburnoides(Teleosteens
Cyprinidae)
and to Lizaaurata
(Teleosteens
Mugilidae)
species
were used in thisstudy
because of theirrepresentativeness
of the Southern AtlanticSpanish ichthyological
fauna.Four groups of individuals of these
species
were maintained in well-aeratedaquaria
at 25-27°C.Forty-eight
hours beforesacrifice,
they
wereinjected
ip
with0.5 mg of
phytohemagglutinin
(PHA-M)/
50
g of fishbody
weight.
One dose(0.8
mgof
BrdU/g
offish)
wasinjected directly
into thecephalic
kidney
24, 22, 20,
16 or12 h before
sacrifice,
in order to obtain the maximum M2 cell(cells
with sister chromatiddifferentiation)
yield.
Finally
0.3 ag of colchicine per gram of fish wasinjected
ip
2 h before sacrifice.After
sacrifice,
thekidney
was removed and macerated in 0.075 M KCl forAir-dried
preparations
were obtained and stained with acridine orange(Dutrillaux
andLejeune,
1973).
RESULTS
The BrdU treatment time which offered the maximum
yield
of M2 cells was 16 h for Rntilus alburnoides and 22 h for Liza aurata.Figure
1 shows an M2metaphase
cell with 4 SCE. Theimage
belongs
to the firstspecies
oftriploid
nature.Mean SCE values for 1VI2
metaphase
cells were 3.57 ! 0.59 in Rutilus alburnoides and 2.91 ! 0.43 in Liza aurata. Table I summarizes the results of the SCE assayDISCUSSION
Although
themeaning
and mechanism of SCE is stillunknown,
it has been demonstrated that most of thegenetically
active chemical toxins(mutagens and/or
carcinogens)
inducesignificant
increases in SCE whenthey
are tested in in vivo animalsystems
or in vitrosystems
with activation(Stetka
andWolff,
1976;
Carranoet
al,
1978;
Latt,
1982).
Atpresent,
the SCE test is a very sensitive andrapid
method fordetecting
chromosomemutagenicity
andprovides
apowerful
means ofdetecting
environmental
mutagens,
as acomplementary
test to other tests of the same nature.The
application
of BrdUincorporation
to the detection of SCE in fish was usedfor the first time
by
Klingerman
and Bloom(1976).
Since their
report,
other authors have used the detection of SCE as a sensitivecytogenetic
test fordetermining chemically
inducedgenetic
damage,
in in vivo(Alink
etal, 1980;
van der Hoeven etal,
1982;
van der Kerkhoff and van derGaag,
1985)
and in vitro(Barker
andRackhan,
1979)
systems.
In this
study
we established the mean number of SCE in fish maintained inhigh
quality
water,
in the absence of toxins. This value constitutes the infrastructure of the SCEgenotoxicity
test,
because any increase of this mean value in fishexposed
tocontaminated water indicates the presence in these waters of substances
producing
genetic
damage.
We are nowtesting
thegenotoxic activity
of severalagricultural
pesticides
whose results will bepresented
in the future.REFERENCES
Alink
GM,
Frederix-WoltersEMH,
van derGaag
MA,
van der KerkhoffJFJ,
Poels CLM(1980)
Induction of sister chromatidexchanges
in fishexposed
to Rhine water. Mutat Res78,
369-374Barker
EM,
Rackhan BD(1979)
The induction of sister chromatidexchanges
in cultured fish cells(A!aeca es!lenderes)
by carcinogenic
mutagens. Mutat Res68,
381-387Carrano
AV, Thompson LH,
LindlPA,
Minklre JL(1978)
Sister chromatidexchanges
as an indicator ofmutagenesis.
Nature 271, 551-553Dutrillaux
B, Lejeune
J(1973)
Coloration des chromosomes humains par 1’acridine orangeapr!s
traitement par le5-bromod6soxyuridine.
CR Acad Sci Paris Ser D 3179-3180Klingerman AD,
Bloom SE(1976)
Sister chromatid differentiation andexchanges
in adult mudminnow( U!rebra
lirni)
after in vivo exposure to 5-bromodeoxyuridine. Chromosoma56, 101-109
Latt SA
(1982)
Detection,significance
and mechanism of sister chromatidexchange
formation. Pastexperiments,
current concept, futurechallenges.
In: Sister ChromatidExciaange.
(Wolff
S,
ed)
JohnWiley
&Sons,
Inc, New YorkStetka
DG,
Wolff S(1976)
Sister chromatidexchange
as an assay forgenetic damage
in-duced
by mutagen-carcinogen.
I. In vivo test forcompound requiring
metabolic activation. MutatRes 41,
333-342van der Hoeven