Induction of out-of-season spawning in Eurasian
perch Perca fluviatilis: effects of rates of cooling
and cooling durations on female gametogenesis
and spawning
Herve Migaud a, Pascal Fontaine a,*, Isdy Sulistyo a,Patrick Kestemont b, Jean-Noel Gardeur a
aLaboratoire de Sciences Animales, INPL-UHP, Nancy 1, MAN 34 rue Sainte Catherine,
54000 Nancy, FrancebUnite de Recherches en Biologie des Organismes, Facultes Universitaires Notre-Dame de la Paix,
61 rue de Bruxelles, B-5000 Namur, Belgium
Received 20 October 2000; accepted 12 May 2001
Abstract
This study was designed to determine the influence of different thermal conditions during an
out-of-season reproductive cycle on gonad recrudescence, plasma steroid levels (testosterone and
estradiol), vitellogenin (VTG) concentrations and spawning in Eurasian perch (Perca fluviatilis)
females. The experiment was performed in 450-l square polyester indoor tanks located in two
rooms equipped with controlled light and temperature devices. Four thermal regimes were tested
with two different rates of cooling from 21 to 6 �C, 3 weeks (3w) or 6 weeks (6w), and two
different durations at 6 �C, 3 months (3m) or 5 months (5m). The photoperiod was fixed at LD
12:12. A long cooling period (6w) resulted in greater gonadosomatic index (GSI) (3.6F 0.5%)
correlated with a larger oocyte diameter (787.9F 25.1 mm). The plasma levels of testosterone
(13.63F 1.18 ng ml � 1) in the former groups were higher than in the short cooling period groups
(6.82F 0.9 ng ml� 1). A longer duration at 6 �C (5m) resulted in higher GSI (14.8F 1%), plasma
testosterone levels (26.2F 0.4 ng ml � 1) and plasma protein phosphorus (PPP, 1.33F 0.3 mgml� 1). The fish from the 6w 5m batch showed the highest plasma estradiol and testosterone levels,
whereas the 3w 5m group showed the largest GSI. At the end of the experiment, several
spontaneous out-of-season spawnings were collected in batch 6w 5m. Biopsy showed that most
oocytes from groups 3w 5m and 6w 5m females were mature (migration of the germinal vesicle
0044-8486/02/$ - see front matter D 2002 Elsevier Science B.V. All rights reserved.
PII: S0044-8486 (01 )00675 -5
* Corresponding author. Tel.: +33-383-302-841; fax: +33-383-323-016.
E-mail addresses: [email protected] (H. Migaud),
[email protected] (P. Fontaine), [email protected] (P. Kestemont).
www.elsevier.com/locate/aqua-online
Aquaculture 205 (2002) 253–267
from central position), whereas few females showed a beginning of migration in groups 3w 3m and
6w 3m, suggesting that the gonad development and reproductive success of Eurasian perch mainly
depends on the chilling duration (long cold period) rather than on the cooling one, in order to
obtain out-of-season spawning. D 2002 Elsevier Science B.V. All rights reserved.
Keywords: Eurasian perch; Perca fluviatilis; Female; Reproductive cycle; Out-of-season spawning; Temperature;
Steroids
1. Introduction
The Eurasian perch, Perca fluviatilis, has been identified as the first species destined for
diversification of inland aquaculture (Fontaine et al., 1993; Kestemont and Dabrowski,
1996). In Northern and Western Europe, the aquaculture development is mainly linked
with its intensive rearing in recirculating systems. In order to satisfy the market require-
ments, reproduction cycles should be controlled to obtain out-of-season spawnings and
produce fingerlings throughout the year. At present, the production of percids relies mainly
on mature breeders captured in natural habitat just prior to spawning (Malison et al., 1994;
Malison and Held, 1996). The work published focused on extending spawning periods
(Tamazouzt et al., 1994; Dabrowski et al., 1996; Ciereszko et al., 1997a,b) and spawning
synchronisation (Kucharczyk et al., 1996; Kouril et al., 1997). Moreover, the reproduction
of the Eurasian perch received little attention compared to other North American percids,
such as yellow perch (P. flavescens) (Dabrowski et al., 1996) and walleye (Stizostedion
vitreum), and there are very few data dealing with the environmental control of the
Eurasian perch reproductive cycles. Some studies documented the influence of temper-
ature in the wild (Gillet et al., 1995; Sandstrom et al., 1995, 1997; Sulistyo et al., 1998,
2000).
Among the environmental factors, photoperiod and temperature are generally consid-
ered as the most important cues in the timing of gametogenesis and spawning in temperate
fish (Scott, 1979; Bromage, 1993). In the case of yellow perch, a period of low
temperature ( < 10 �C) in the winter is required to complete gonad maturation and
reproductive success (Hokanson 1977; Heidinger and Kayes, 1986). More recently, in
the case of Percids, several studies indicated that compressed photoperiods and temper-
ature regimes favoured maturation, such as in the yellow perch(Dabrowski et al., 1996;
Ciereszko et al., 1997a), white bass(Morone chrysops)(Kohler et al., 1994), striped
bass(M. saxatilis)(Blythe et al., 1994), sunshine bass(M. chrysops�M. saxatilis)(Tate
and Helfrich, 1998) and walleye(Malison et al., 1998). These two factors affect gonad
development through the action of steroid hormones (Borg 1994; Nagahama, 1994; Peter
and Yu, 1997). Works dealing with steroid variations (mainly estradiol and testosterone),
during a reproductive cycle, were conducted in several Percid fish, such as yellow perch
(Dabrowski et al., 1996), white perch (M. americana) (Jackson and Sullivan, 1994),
walleye (Malison et al., 1994; Malison and Held, 1996), white bass (Berlinsky et al., 1995)
and striped bass (Berlinsky and Specker, 1991; Woods and Sullivan, 1993).
The present work, based on the hypothesis that temperature variations alone (fixed
photoperiod) could induce gonadal development and control the main phases of the
H. Migaud et al. / Aquaculture 205 (2002) 253–267254
Eurasian perch reproductive cycle (Sulistyo et al., 1997), was designed to (1) test the
effects of different rates of cooling and durations on the main female reproductive phases
and (2) to induce out-of-season spawnings.
2. Materials and methods
2.1. Facilities and fish
Eurasian perch broodstocks (age = 2 + , mean body weight: 364.0F 22.9 g, mean total
length: 25.1F 0.5 cm, n = 150) were reared from hatching at the laboratory in a constant
environment (T= 21 �C, photoperiod LD 12:12) and never spawned before the onset of the
experiment.
The experiment was conducted from November 1996 to August 1997. The fish were
transferred into 10, 450-l square polyester indoor tanks (14 fish tank � 1) in two rooms
equipped with controlled lights and temperature devices (six tanks in room A and four in
room B). The water-recirculated system was based on a fish-rearing process, which uses
simple aquariological techniques (Fontaine et al., 1994). Each room was lit by two
fluorescent tubes (200 lux at the water surface), at a constant photoperiod of LD 12:12.
Thermal regimes were tested, at two different cooling periods, from 21 to 6 �C, over 3(3w, room A) or 6 weeks (6w, room B), two chilling periods at 6 �C over 3 (3m) or 5
months (5m) and warming period over 2 weeks (Fig. 1). The water temperature profiles in
Fig. 1. Experiment design. The temperature variations applied in the experiment during the cooling (3w or 6w),
the chilling (3m or 5m) and the warming phases.
H. Migaud et al. / Aquaculture 205 (2002) 253–267 255
the different groups are shown in Fig. 1. The fish, first acclimated at 21 �C, were dividedinto four groups according to the different regimes. The perch were fed twice a day (at 9
a.m. and 4 p.m.) with commercial pellets (Biomar S.A., Ecolife, number 4.5), which are
composed of 46% proteins (DM), 15% fat, 8% ash and 1.7% cellulose. The feeding rate
was 0.5% of the biomass and the food excess was regularly removed.
The oxygen, the pH, the N–NH4+ and the N–NO2
� were measured twice weekly and
varied between 5 and 14, 5 and 7.9, 0.01 and 1.30, 0 and 1.78 mg l � 1, respectively.
2.2. Samplings of plasma and oocytes
At the beginning of the experiment and at the end of the cooling, chilling and warming
periods, three to five females from each group were anaesthetised in a 2-phenoxyethanol
solution (0.3 ml l� 1), then individually weighed (body weight BWF 0.1 g), measured for
standard length (SLF 1 mm), blood-sampled and dissected. A 1-ml blood sample was
taken from the heart (initial, during cooling and chilling periods and final) or the caudal
vessel (during warming period) using a heparinized syringe. The blood was then
centrifuged at 4000 rpm for 25 min and the plasma was stored in vials at � 25 �C until
assay. Biopsies were performed on each female in order to examine the germinal vesicle
position and check for ripeness. Approximately 20 oocytes were removed with a catheter,
soaked for 5 min in a clearing solution: methanol, formalin, acetic acid 1v, 1v, 1v
(Mylonas et al., 1997) and examined under a 40� magnifying glass. At the end of the
experiment, all the fish were killed for analysis.
2.3. Morphoanatomical parameters
The gonadosomatic (GSI), hepatosomatic (HSI) and viscerosomatic (VSI) indexes were
calculated as:
GSIð%Þ ¼ ðGW� 100Þ=BW,
HSIð%Þ ¼ ðLW� 100Þ=BW and VSIð%Þ ¼ ðVW� 100Þ=BW,
where BW=body weight, GW=weight of the gonads (g), LW=weight of the liver (g) and
VW=weight of the viscera (g). To determine the respective importance of the somatic and
gonad development in fish, the condition factors were determined with and without gonad
weights, as follow K1 = 100�BW/SL3 and K2 = 100� (BW�GW)/SL3, where SL= stan-
dard length (cm) (Le Cren, 1951).
2.4. Steroid assay and vitellogenin
Plasma concentrations of testosterone (T) and 17b-estradiol (E2) were determined using
RIA analysis, according to Fostier et al. (1983), after two extractions with cyclohexane/
ethylacetate (v/v). The extractions were performed on 50 ml of plasma for each steroid. The
samples were assayed in duplicate and the standards in triplicate. The vitellogenin (VTG)
was indirectly measured by the concentration of plasma protein phosphorus (PPP). The
H. Migaud et al. / Aquaculture 205 (2002) 253–267256
cross-reactivities of antisera with a variety of common steroids were described by Prat et
al. (1990).
Six samples of different concentrations were tested in each assay and were used as
quality controls for estimating intra- and inter-assay coefficients of variation (CV). As for
these two hormones, E2 and T, the sensitivity of measurement were 8 and 5 pg ml� 1,
respectively. The intra-assay CVs (n = 6) were 6.1% and 2.5%, respectively.
2.5. Statistical analysis
All quantitative data are expressed as meansF S.D. (standard deviation). As treatments
are not repeated (one experimental room/temperature regime), means data and individuals
data as well, which are not replications, but pseudoreplications (Hurlbert, 1984), cannot be
analysed by classical ANOVA. Also, the treatment effect can only be tested on individuals
data (n = 44) by a multivariate analysis. These measures correspond to three or five fish
sampled at the end of each period: initial, cooling (two levels), chilling (two levels) and
warming periods (one level).
The method used was a principal component analysis (PCA) and hierarchical
clustering with the aggregation criteria of Ward (Ward, 1963) with the SPAD 4.0
software (Lebart et al., 1996). It allows comparisons of subpopulations characterized by
a particular experimental treatment. The biometrical data (GSI, HIS, VSI, K1 and K2)
were used as active variables and the level of treatment were used as illustration
variables. Another PCA was used for hormonal data (plasma T, E2 and PPP concen-
trations) as active variables. The characteristics of the principal components and the
classes obtained by hierarchical clustering were tested with the value test. Values were
significantly different when the value test > 2, P < 0.05 (Morineau, 1984; Lebart et al.,
1996).
3. Results
3.1. Morphoanatomical parameters
At the end of the cooling period, the GSI were 2.50F 1.29% and 3.60F 0.55% in 3w
and 6w groups, respectively (Fig. 2). The period of 6 �C (3 or 5 months) induced a large
increase in the GSI. The largest GSI was found in females from groups 3w 5m and 6w
5m and reached 15.26% and 14.23%, respectively. The samples from the end of the
warming phase are not represented in Figs. 2 and 3, because perch spawned during the
increase of temperature before the sampling. The oocyte growth was affected by the
temperature profile (Fig. 3). The oocyte diameter (OD) in the initial sample averaged
358.1F 32.3 mm and increased to about 750–800 mm in all groups at the time of the
warming phase.
At the beginning of the experiment, the HIS of females was 2.40F 0.31% (n = 3). It
increased during the cooling phase and was 2.78F 0.40% and 3.32F 0.26% for group 3w
and 6w, respectively. At the end of the chilling phase, the HSI was about 2.4–2.8% in all
groups. The VSI was 8.92F 0.78% at the beginning of the experiment and decreased
H. Migaud et al. / Aquaculture 205 (2002) 253–267 257
during the cooling phase (6.80F 0.26% and 6.70F 0.40%, respectively, for group 3w and
6w). At the end of the period at 6 �C, the VSI ranged between 5% and 6% approximately,
without any group differences.
Fig. 3. Ovocyte diameter of female Eurasian perch, P. fluviatilis, during the experiment. Values represent
meanF S.D. with n= 5. Initial: initial values; Cool: end of cooling period values; Chill: end of cold chilling
period values. The different treatments tested are 3 or 6 weeks (3w or 6w) during the cooling period and the
interaction of the cooling and the chilling periods (3m or 5m): 3w 3m, 3w 5m, 6w 3m and 6w 5m.
Fig. 2. Gonadosomatic index (GSI) of female Eurasian perch, P. fluviatilis, during the experiment. GSIs values
represent meanF S.D. with n= 5. Initial: initial values; Cool: end of cooling period values; Chill: end of cold
chilling period values. The different treatments tested are 3 or 6 weeks (3w or 6w) during the cooling period and
the interaction of the cooling and the chilling periods (3m or 5m): 3w 3m, 3w 5m, 6w 3m and 6w 5m.
H. Migaud et al. / Aquaculture 205 (2002) 253–267258
The hierarchical clustering representation showed four classes drawn on the plane
defined by the two first axis on PCA, which represent 80% of global inertia (Fig. 4). The
first axis is significantly characterised by the initial and the cooling sampling periods, the
VSI, the K2 and the first class, in the left part (values test > 2). In opposition, the chilling
period, the GSI, the OD, the class 3 and the illustrative variables (the plasma T, E2 and
PPP levels), not represented in Fig. 4, characterise the right part of the axis (values
test > 2). Thus, the first axis confirms, significantly, the decrease of the VSI and the K2 and
the concomitance increase of the GSI, the OD and the plasma T, E2 and PPP levels over
the time. In class 3, as all the treatments were represented, the active variables which
characterised this class (GSI, OD, VSI and K2) were not significantly affected by the
treatment. The class 4, described by the second axis, is characterised by low HSI, K1 and
OD compared to the class 2 which is represented by higher HSI and OD.
3.2. Plasma steroid concentrations
The initial plasma T concentrations were 0.31F 0.01 ng ml� 1 (n = 4), then increased
during the cooling period to 13.23F 0.47 ng ml� 1 in group 3w and 6.82F 0.96 ng ml� 1
in group 6w (Fig. 5). It kept on increasing during the chilling phase and the plasma T
levels were 21.8F 0.6 and 27.5F 0.42 ng ml� 1 in group 3w 3m and 6w 3m, respectively,
and 24.27F 1.86 and 27.98F 0.71 ng ml� 1 in groups 3w 5m and 6w 5m, respectively.
Fig. 4. Hierarchical clustering representation for biometrical data, gonadosomatic (GSI), viscerosomatic (VSI) and
hepatosomatic (HIS) indexes, condition factors (K1 and K2) and oocyte diameter (OD). Three sampling periods
were tested (initial, cooling and chilling periods). The large symbols represent the four classes (C1, 2, 3 and 4)
and, the small one, individuals which belong to each class. The different treatments tested are 3 or 6 weeks (3w or
6w), 3 or 5 months (3m or 5m) corresponding to the cooling and the chilling periods, respectively, and the
interaction of the two periods (3w 3m, 3w 5m, 6w 3m and 6w 5m). The axis 1 and 2 represent 50% and 30% of
the global inertia, respectively.
H. Migaud et al. / Aquaculture 205 (2002) 253–267 259
After the 2-week water warming (from 6 to 14 �C), the plasma T concentrations decreased
in all four groups to about 14–19 ng ml � 1.
The initial E2 concentrations averaged 0.27F 0.01 ng ml � 1 (n= 4) (Fig. 6). At the end
of the cooling phase, the plasma E2 levels were 2.74F 0.10 and 2.06F 0.15 ng ml � 1 in
Fig. 5. Plasma concentrations of testosterone (T) in female Eurasian perch. Values represent meanF S.D. with
n= 5. Initial: initial values; Cool: end of cooling period values; Chill: end of cold chilling period values; Warm:
end of warming period values. The different treatments tested are 3 or 6 weeks (3w or 6w) during the cooling
period and the interaction of the cooling and the chilling periods (3m or 5m): 3w 3m, 3w 5m, 6w 3m and 6w 5m.
Fig. 6. Plasma concentrations of 17b-estradiol (E2) in female Eurasian perch. Values represent meanF S.D. with
n= 5. Initial: initial values; Cool: end of cooling period values; Chill: end of cold chilling period values; Warm:
end of warming period values. The different treatments tested are 3 or 6 weeks (3w or 6w) during the cooling
period and the interaction of the cooling and the chilling periods (3m or 5m): 3w 3m, 3w 5m, 6w 3m and 6w 5m.
H. Migaud et al. / Aquaculture 205 (2002) 253–267260
the females from group 3w and group 6w, respectively. At the end of the chilling period,
the plasma E2 levels averaged 4 ng ml� 1. Nevertheless, the females from group 6w 5m
achieves 5.56F 0.49 ng ml � 1. During the 2-week warming phase, the E2 concentrations
increased, particularly, in the 6w 5m group (up to 10.54F 0.45 ng ml� 1, n = 3) compared
to the others (about 6 ng ml� 1).
The initial PPP values were 0.07F 0.01 mg ml� 1 (n = 4, Fig. 7). They increased
during the cooling phase in the females from group 3w (0.52F 0.17 mg ml� 1) and
group 6w (0.49F 0.13 mg ml � 1). During the chilling period, the plasma PPP concen-
trations were 0.88 mg ml� 1 for the 3-month treatment and 1.33 mg ml� 1 for the 5-
month treatment. At the end of the warming phase, the PPP levels decreased (0.7 mgml� 1).
Through the multivariate study, different classes were identified and described with
the variables that contribute most to the drawing up of classes (Fig. 8). The initial
samples and samples done at the end of the cooling period, represented in the class 1,
are characterized by low plasma levels of T, E2 and PPP. As far as the samples
performed at the end of the chilling period are concerned, the PPP levels were
significantly higher in the class 4, mainly represented by the 5m treatment. The class
5 was characterized by significantly higher T levels, which was not linked to a treatment
effect since all the treatments were represented in this class (3w 3m, 3w 5m, 6w 3m and
6w 5m, Fig. 8). At the end of the warming phase, the class 3 confirmed that the plasma
E2 levels were significantly higher in the 6w 5m treatment compared to the other
treatments (class 2).
Fig. 7. Plasma concentrations of plasma protein phosphorus (PPP) in female Eurasian perch. Values represent
meanF S.D. with n= 5. Initial: initial values; Cool: end of cooling period values; Chill: end of cold chilling
period values; Warm: end of warming period values. The different treatments tested are 3 or 6 weeks (3w or 6w)
during the cooling period and the interaction of the cooling and the chilling periods (3m or 5m): 3w 3m, 3w 5m,
6w 3m and 6w 5m.
H. Migaud et al. / Aquaculture 205 (2002) 253–267 261
3.3. Spawning and observations
The biopsy performed 2 weeks after the warming phase showed that most of the oocytes
from the 3w 5m and 6w 5m groups were mature as the germinal vesicle migration were
observed in the sampled oocytes. The oocytes sampled from the 3w 3m and 6w 3m females
groups had still central germinal vesicle and only few of them showed a partial migration.
The eggs were taken for number estimation and transferred for incubation. Only three
females naturally spawned in the 6w 5m group in July (the 15th, 20th and 22th) and one in
the 3w 3m group in May (20th), with an absolute fecundity ranging from 35000 to 53000
eggs/fish. When the experiment ended, 15 days after the warming period, another biopsy
was performed on non-ovulated females. The sampled oocytes contained central germinal
vesicle or had moved into an atretic stage.
4. Discussion
The present study provides new data on out-of-season spawning induction of Eurasian
perch by modification of the temperature profiles and complements existing data on
morphoanatomical indexes and sex steroids changes in this species.
Fig. 8. Hierarchical clustering representation for hormonal data, testosterone (T), estradiol (E2) and plasma protein
phosphorus (PPP), with four sampling periods tested (initial, cooling, chilling and warming periods). The large
symbols represent the five classes (C1, 2, 3, 4 and 5) and, the small one, individuals which belong to each class.
The different treatments tested are 3 or 6 weeks (3w or 6w), 3 or 5 months (3m or 5m) corresponding to the
cooling and the chilling periods, respectively, and the interaction of the two periods (3w 3m, 3w 5m, 6w 3m and
6w 5m). The axis 1 and 2 represent 69% and 22% of the global inertia, respectively.
H. Migaud et al. / Aquaculture 205 (2002) 253–267262
Adequate temperature profiles (a cooling period from 20 to 6 �C, a duration at 6 �C and
a warming period till 14 �C) successfully lead to the maturation of ovaries, with an average
GSI of 21%, thus higher than in the previous studies in which the GSI only reached
10.77F 1.79% (Tamazouzt et al., 1994) or 17–19% (Sulistyo et al., 1997). During this
study, the fish were under constant photoperiod and the GSI reached almost the same
values than in natural conditions (Sulistyo et al., 1998). Eurasian perch broodstocks, reared
from hatching in an artificial environment, under steady conditions (T > 20 �C, 14L/10D),are able to keep their reproduction ability.
This experiment confirms that a chilling period (maintaining water temperature at 6 �C)should be a crucial phase in the development of fish ovaries. Studies on yellow perch
showed that oogenesis requires a winter period to induce oocyte development and
maturation (Heidinger and Kayes, 1986). As far as this species is concerned, the water
temperature must be maintained under 10 �C for at least 160 days (Hokanson, 1977).
Contrary to many species reproducing during the spring, the photoperiod is probably not
the main factor to control the oocyte development and the maturation among Eurasian
perch. Similar conclusions were reported in yellow perch by Kayes and Calbert (1979) and
Dabrowski et al. (1994). These authors showed that spawning occurred during the same 4
days in April, as did the fish in the lake, whatever the photoperiodic regime applied in the
laboratory was (LD 13.5:10.5; 10.5:13.5; 6:18; 18:6). They also demonstrated that, when
transferred from the wild in April, yellow perch spawn in captivity either under long (LD
18:6) or short (LD 6:18) photoperiod if warmed to 12 �C. Dabrowski et al. (1996)
concluded that photothermal manipulations during the period of active ova growth and
vitellogenesis, as well as during the postvitellogenic phase of ovarian development, do not
lead to faster spawning among yellow perch. Thus, shifting the entire reproductive cycle,
instead of condensing or shortening reproductive phases (Blythe et al., 1994), seems to be
a more promising tool in order to accelerate spawning (Dabrowski et al., 1996; Tate and
Helfrich, 1998). In opposition, many studies showed that in Salmonid, the photoperiod is
the most important factor among the environmental cues, for synchronisation of the
reproductive cycle (Bromage, 1993).
Although the two cooling period tested from 22 to 6 �C did not show any difference in
the GSI (from 2.5% to 3.6%), a slight increase of oocyte diameter was observed from 450
to 700 mm for 3 and 6w, respectively. These differences might be related to steroids (E2
and T) and vitellogenin levels; however, according to the results of the principal
component analysis, only the T levels were significantly higher for the 6w treatment,
while the E2 and PPP concentrations were almost steady. So, a higher amount of T may be
due to a higher use of E2 by oocytes. No cooling period effect on oocyte diameter was
observed at the end of the chilling phase (duration at 6 �C). Oocyte growth was almost
completed during the cooling period for the 6w treatment, whereas it was only completed
during the chilling period in the 3w treatment.
The relation between the plasma steroids levels and the main reproductive phases often
seem to be unclear, because of the speed conversion of these steroids into other
compounds.
The chilling period at 6 �C is very important in the reproductive cycle of Eurasian
perch and the GSI increases to approximately 11–15% when fish were exposed to a 3- or
5-month chilling period, respectively (Fig. 2). This increase of the GSI is correlated with
H. Migaud et al. / Aquaculture 205 (2002) 253–267 263
the increase of the E2 (5.5 ng ml � 1 for group 6w 5m) and the vitellogenine, which
reached 0.9 and 1.3 ng ml� 1, after a chilling period of 3 or 5 months, respectively
(Fig. 7). This GSI difference is not related to the oocyte diameter, which is approximately
the same after the chilling durations at 6 �C, but probably to an increase in the number of
yolk oocytes.
In general, the plasma sex steroid and the PPP levels observed during this experiment
were similar to those observed in natural environment (Sulistyo et al., 1998), with an
increase after the cooling period (autumnal decrease of water temperature) and during the
chilling phase, when oocytes develop. The thermophotoperiodic treatments, in closed
conditions, did not alter the endocrinological processes involved in oogenesis. Testoster-
one, which is involved mainly in estradiol production, could also play a role in oocyte
maintenance after vitellogenesis and until final maturation (Kime 1993). This could also
explain the high levels observed during the phase at 6 �C.At the end of this experiment, three spontaneous spawnings were collected from the 6w
5m group in July, whereas the natural spawning period in the east of France occurred in
April, probably in relation with the higher E2 and T levels during the reproductive cycle.
Among the three other groups, only one spontaneous spawning was observed (group 3w
3m), and the plasma E2 concentrations were significantly lower. Cierezsko et al. (1997a,b)
demonstrated that low E2 levels during vitellogenesis (winter period) led to disturbances in
ovarian development and also compromised egg quality. These results would suggest that
shifting the entire reproductive cycle is possible in Eurasian perch as it was observed in
yellow perch (Kolkovski and Dabrowski, 1998).
As for semen quality, 75% of the spermatozoa were moving for a period of only 30 s
and 60% for 35 s, after activation. This short motility duration requires males to be very
close to females at the spawning time. This result is in accordance with those observed by
Lahnsteiner et al. (1995), who showed that 80% of the spermatozoa among P. fluviatilis
are moving for only 20 s in distilled water. Different hypothesis could explain the lack of
egg fertilisation in this study. First of all, there was no enough male stimulation (female
pheromone lack). Vermeirssen et al. (1997) demonstrated that pheromone induce semen
outflow. Secondly, the storing conditions might have been unsuitable, with too few males.
Jones (1982) and Treasurer (1983) demonstrated that, in a natural habitat, at least two
males trail one female ready for spawning and are involved in egg ribbon fertilisation. The
stress induced by regular staff presence, especially at the spawning date, could be a
possible explanation, as it was observed in several studies (Kjorszvik et al., 1990). Other
factors could also explain this fertilisation problem, such as photoperiodic conditions
during the development of the male gonad. If the temperature effect on the reproductive
cycle have already been studied, the role of photoperiod on the different reproductive
stages (as gonadal development initiation, maturation or spawning) are still to be tested.
Another factor could also play an important part in successful spawning: broodstock age at
spawning time and especially the age at first maturation time, as well as the number of
previous reproductive cycle. The broodstock tested during this experiment were main-
tained under artificial conditions of temperature (22 �C) and photoperiod (12 h L/12 h D)
at the laboratory and, thus, never matured. Some studies showed that the number of fish,
which successfully reproduced during their first reproduction cycle, was lower compared
to the fish who had already spawned (Abi-Ayad, 1997).
H. Migaud et al. / Aquaculture 205 (2002) 253–267264
In conclusion, the cooling period of 6 weeks has given results with higher plasma E2
and protein–phosphorus levels. Cold chilling periods must be long. In fact, 5 months
allow normal gonad development, whereas 3 months seems to be insufficient. The present
study has shown that out-of-season spawning in Eurasian perch is possible by photo-
thermoperiodic manipulations. On the other hand, lots of atretic oocytes were observed.
When ovaries reach a mature state, the fact of maintaining females in waters at a
temperature of 14 �C for more than 2 weeks causes damage in ovaries, and oocytes
become atretic. The use of hormonal induction, such as luteinizing hormone-releasing
hormone (LHRH), could synchronize the ovulation and release the spawning in Eurasian
perch. Further researches are then necessary to determine the specific roles of the different
environmental factors during the final stages of the reproductive cycle (mainly final
maturation, ovulation and spawning), so as to better explain the atretic phenomenon.
Acknowledgements
We would like to thank all the members of the LSA laboratory staff for their active
collaboration in this study.
References
Abi-Ayad, A., 1997. Etude experimentale de la biologie de la reproduction de la perche fluviatile (P. fluviatilis).
Effet de la composition en acides gras de la serie (n-3) de l’alimentation des geniteurs sur la qualite des oeufs
et des larves. These de doctorat, Universite de Liege, Belgium, 147 pp.
Berlinsky, D.L., Specker, J.L., 1991. Changes in gonadal hormones during oocyte development of striped bass
(Morone saxatilis). Fish Physiol. Biochem. 9 (1), 51–62.
Berlinsky, D.L., Jackson, L.F., Smith, T.I.J., Sullivan, C.V., 1995. The annual reproductive cycle of the white bass
Morone chrysops. J. World Aquacult. Soc. 26 (3), 252–260.
Blythe, W.G., Helfrich, L.A., Sullivan, C.V., 1994. Sex steroid hormone and vitellogenine levels in striped bass
(Morone saxatilis) maturing under 6, 9 and 12 month photothermal cycles. Gen. Comp. Endocrinol. 94,
122–134.
Borg, B., 1994. Androgens in teleost fishes. Comp. Biochem. Physiol. 109C, 219–245.
Bromage, N., 1993. Environmental control of reproduction in salmonids. Recent Adv. Aquacult. IV, 55–65.
Ciereszko, R.E., Dabrowski, K., Ciereszko, A., Ottobre, J., 1997a. Plasma concentrations of steroid hormones in
male yellow perch Perca flavescens: the effect of age and photothermal manipulation. Environ. Biol. Fishes,
1–9.
Ciereszko, R.E., Dabrowski, K., Ciereszko, A., 1997b. Effects of temperature and photoperiod on reproduction of
female yellow perch Perca flavescens: plasma concentrations of steroid hormone, spontaneous and induced
ovulation, and quality of eggs. J. World Aquacult. Soc. 28 (4), 344–356.
Dabrowski, K., Ciereszko, A., Ramseyer, L., Culver, D., Kestemont, P., 1994. Effects of hormonal treatment on
induced spermiation and ovulation in the yellow perch (Perca flavescens). Aquaculture 120, 171–180.
Dabrowski, K., Ciereszko, R.E., Ciereszko, A., Toth, G.P., Christ, S.A., El-Saidy, D., Ottobre, J.S., 1996.
Reproductive physiology of yellow perch (Perca flavescens): environmental and endocrinological cues. J.
Appl. Ichthyol. 12, 139–148.
Fontaine, P., Tamazouzt, L., Terver, D., Georges, A., 1993. Actual state of production of perch: problems and
prospects: I. Mass rearing potentialities of the common perch under controlled conditions. In: Kestemont, P.,
Billard, R. (Eds.), Aquaculture of Freshwater Species (except Salmonids), vol. 20. European Aquaculture
Society, pp. 46–48, Spec. Publ.
H. Migaud et al. / Aquaculture 205 (2002) 253–267 265
Fontaine, P., Vlavlonou, R., Tamazouzt, L., Terver, D., Masson, G., 1994. Elevage de perches sevrees en eau
recyclee: resultats preliminaire. Cah. Ethol. Appl. 13, 411–420.
Fostier, A., Jalabert, B., Billard, R., Breton, B., Zohar, Y., 1983. The gonadal steroids. In: Hoar, W.S.,
Randall, D.J., Onaldson, E.M. (Eds.), Fish Physiology, vol. IXA. Academic Press, pp. 227–372.
Gillet, C., Dubois, J.P., Bonnet, S., 1995. Influence of temperature and size of females on the timing of
spawning of perch, Perca fluviatilis in lake Geneva from 1984 to 1993. Environ. Biol. Fishes 42,
355–363.
Heidinger, R.C., Kayes, T.B., 1986. Yellow perch. In: Stickney, R.R. (Ed.), Culture of Non Salmonid
Freshwater Fish: Yellow Perch. CRC Press, Boca Raton, FL, pp. 103–113.
Hokanson, K.E.F., 1977. Temperature requirements of some percids and adaptations to the seasonal temperature
cycle. J. Fish. Res. Board Can. 34, 1524–1550.
Hurlbert, S.H., 1984. Pseudoreplication and the design of ecological field experiments. Ecol. Monogr. 54,
187–211.
Jackson, L.F., Sullivan, C.V., 1994. Reproduction of white perch: the annual gametogenic cycle. Trans. Am.
Fish. Soc. 124, 563–577.
Jones, D.H., 1982. The spawning of perch (Perca fluviatilis L.) in Loch Leven, Kinross, Scotland. Aquacult.
Fish. Manage. 13, 139–151.
Kayes, T.B., Calbert, H.E., 1979. Effects of photoperiod and temperature on the spawning of yellow perch
(Perca flavescens). Proc. World Maric. Soc. 10, 306–316.
Kestemont, P., Dabrowski, K. (Eds.), 1996. Recent advances in the aquaculture of percid fish. J. Appl. Ichthyol.
12 (3–4), 137–200.
Kime, D.E., 1993. Classical and non-classical reproductive steroids in fish. Rev. Fish Biol. Fish. 3, 160–180.
Kjorszvik, E., Mangor-Jensen, Holmefjord, I., 1990. Egg quality in fishes. Adv. Mar. Biol. 26, 71–113.
Kohler, C.C., Sheehan, R.J., Habicht, C., Malison, J.A., 1994. Habituation to captivity and controlled spawning of
white bass. Trans. Am. Fish. Soc. 123, 964–974.
Kolkovski, S., Dabrowski, K., 1998. Off-season spawning of yellow perch. Prog. Fish-Cult. 60, 133–136.
Kouril, J., Linhart, O., Relot, P., 1997. Induced spawning of perch by means of a GnRH analogue. Aquacult. Int.
5, 375–377.
Kucharczyk, D., Kujawa, R., Mamcarz, A., Skrzypczak, A., 1996. Induced spawning in perch, Perca fluviatilis L.
using carp pituitary extract and HCG. Aquacult. Res. 27, 847–852.
Lahnsteiner, F., Berger, B., Weismann, T., Patzner, R., 1995. Fine structure and mobility of spermatozoa and
composition of the seminal plasma in the perch. J. Fish Biol. 47, 492–508.
Lebart L., Morineau, A., Lambert, T., Pleuvret, P., SPADR Version 4. System pour l’analyse de donnees. Manuel
de reference. Launay, Paris, 1996.
Le Cren, E.D., 1951. The length-weight relationship and seasonal cycle in gonad weight and condition in the
perch (Perca fluviatilis). J. Anim. Ecol. 20, 201–219.
Malison, J.A., Held, J.A., 1996. Reproductive biology and spawning. In: Summerfelf, R.C. (Ed.), Walleye
Culture Manual. NCRAC Culture Series 101. North Central Regional Aquaculture Center Publications
Office, Iowa State University, USA, pp. 11–18.
Malison, J.A., Procarione, L.S., Barry, T.P., Kapuscinski, A.R., Kayes, T.B., 1994. Endocrine and gonadal
changes during the annual reproductive cycle of the freshwater teleost fish, Stizostedion vitreum. Fish Physiol.
Biochem. 13, 473–484.
Malison, J.A., Procarione, L.S., Kayes, T.B., Hansen, J.F., Held, J.A., 1998. Induction of out-of-season
spawning in walleye (Stizostedion vitreum). Aquaculture 163, 151–161.
Morineau, A., 1984. Note sur la caracterisation statistique d’une classe et les valeurs-tests. Bulletin Technique
Centre International de Statistique et d’Informatique Appliquees 2 (1–2), 20–27.
Mylonas, C.C., Magnust, Y., Klebanov, Y., Gissis, A., Zohar, Y., 1997. Reproductive biology and endocrine
regulation of final oocyte maturation of captive white bass. J. Fish Biol. 51, 234–250.
Nagahama, Y., 1994. Endocrine control of gametogenesis. Int. J. Dev. Biol. 38, 217–229.
Peter, R.E., Yu, K.L., 1997. Neuroendocrine regulation of ovulation in fishes: basic and applied aspects. Rev.
Fish Biol. Fish. 7, 173–197.
Prat, F., Zanuy, S., Carillo, M., De Mones, A., Fostier, A., 1990. Seasonal changes in plasma levels of gonadal
steroids of sea bass, Dicentrarchus labrax L. Gen. Comp. Endocrinol. 78, 361–373.
H. Migaud et al. / Aquaculture 205 (2002) 253–267266
Sandstrom, O., Neuman, E., Thoresson, G., 1995. Effects of temperature on life history variables in perch. J. Fish
Biol. 47, 652–670.
Sandstrom, O., Abrahamsson, I., Andersson, J., Vetemaa, M., 1997. Temperature effects on spawning and egg
development in Eurasian perch. J. Fish Biol. 51, 1015–1024.
Scott, D.B.C., 1979. Environmental timing and the control of reproduction in teleost fish. Symp. Zool. Soc.
London 44, 105–132.
Sulistyo, I., Fontaine, P., Kestemont, P., Gardeur, J.N., Capdeville, B., Georges, A., 1997. Effect of thermopho-
toperiod regimes on reproductive response in perch P.fluviatilis L. In: Creswell, L., Harache, Y. (Eds.), 2nd
International Workshop on Aquaculture of Percid Fish. Martinique, May 4. European Aquaculture Society,
pp. 349–350.
Sulistyo, I., Rinchard, J., Fontaine, P., Gardeur, J.N., Capdeville, B., Kestemont, P., 1998. Reproductive cycle
and plasma levels of sex steroids in female Eurasian perch Perca fluviatilis. Aquat. Living Resour. 11 (2),
101–110.
Sulistyo, I., Fontaine, P., Rinchard, J., Gardeur, J.N., Migaud, H., Capdeville, B., Kestemont, P., 2000. Repro-
ductive cycle and plasma levels steroids in male Eurasian perch Perca fluviatilis. Aquat. Living Resour. 13
(2), 99–106.
Tamazouzt, L., Fontaine, P., Terver, D., 1994. Decalage de la periode de reproduction de la perche commune
(Perca fluviatilis) en eau recyclee. Ichtyophysiol. Acta 17, 29–40.
Tate, A.E., Helfrich, L.A., 1998. Off season spawning of sunshine bass (Morone chrysops�M. saxatilis)
exposed to 6 or 9 month phase shifted photothermal cycles. Aquaculture 167, 67–83.
Treasurer, J.W., 1983. Estimates of egg and viable embryo production in a lacustrine perch, Perca fluviatilis.
Environ. Biol. Fishes 8, 3–16.
Vermeirssen, E.L.M., Scott, A.P., Liley, N.R., 1997. Female rainbow trout urine contains a pheromone which
causes a rapid rise in plasma 17,20b-dihydroxy-4-pregnen-3-one levels and milt amounts in males. J. Fish
Biol. 50, 107–119.
Ward, J.H., 1963. Hierarchical grouping to optimise an objective function. J. Am. Stat. Assoc. 58, 224–236.
Woods, L.C., Sullivan, C.V., 1993. Reproduction of stripped bass (Morone saxatilis) broodstock: monitoring
maturation and hormonal induction of spawning. Aquacult. Fish. Manage. 24, 211–222.
H. Migaud et al. / Aquaculture 205 (2002) 253–267 267