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www.elsevier.com/locate/jembe
Journal of Experimental Marine Biolo
Domestication reduces the capacity to escape from predators
Katherina B. Brokordt a,*, Miriam Fernandez b, Carlos F. Gaymer a
a Center for Advanced Studies in Arid Zones (CEAZA), Departamento de Biologıa Marina, Universidad Catolica del Norte, Larrondo 1281,
Coquimbo, Chileb Center for Advanced Studies in Ecology and Biodiversity (CASEB), Estacion Costera de Investigaciones Marinas, Departamento de Ecologıa,
Pontificia Universidad Catolica de Chile, Chile
Received 2 May 2005; received in revised form 23 May 2005; accepted 8 August 2005
Abstract
Phenotypic plasticity in response to variations in predatory pressure frequently occurs in wild populations, but it may be more
evident and critical in species subjected to high exploitation rates and aquaculture. The Chilean scallop Argopecten purpuratus is
becoming a domesticated species and the production of hatchery-reared scallops (closed environment), has implied the develop-
ment of successive generations of individuals deprived of several stimuli normally present in their natural habitats (e.g. predators).
We compared the escape capacities between wild and cultured A. purpuratus and also evaluated the effect of reproductive
investment on the escape response capacities. Wild and cultured scallops, at different reproductive stages (maturing, mature and
spawned), were stimulated to escape with the predatory sea star Meyenaster gelatinosus. We recorded: (1) the time to reaction, (2)
the total number of claps, the duration of the clapping response and the clapping rate until exhaustion, (3) the time they spent closed
after exhaustion, and (4) the proportion of claps recovered, the duration of the clapping response and the clapping rate after 20 min
of recuperation. We found that wild A. purpuratus (1) reacted earlier when contacted by their natural predator, (2) escaped faster
(greater clapping rates), (3) spent less time with their valves closed when exhausted, and (4) most of their escape capacities (i.e.
claps number; clapping time; capacity of recuperation) were less affected by the energetic requirements imposed by gonad
maturation and/or spawning than in cultured scallops. We considered that all these aspects of the escape response would make wild
scallops less vulnerable to predation than cultured scallops, thus decreasing predation risk. Given the reduction of escape
performance in cultured scallops, we suggest that this aspect should be considered for the success of culture-based restocking
programs.
D 2005 Elsevier B.V. All rights reserved.
Keywords: Argopecten purpuratus; Cultured scallops; Escape response; Reproductive cost; Restocking; Wild scallops
1. Introduction
Predation is a major factor causing mortality in wild
populations, and consequently species have evolved a
varied set of response mechanisms to avoid or decrease
predation pressure (Sih, 1987). Passive defensive
mechanisms (e.g. morphological traits) as well as active
0022-0981/$ - see front matter D 2005 Elsevier B.V. All rights reserved.
doi:10.1016/j.jembe.2005.08.007
* Corresponding author. Tel.: +56 51 209929; fax: +56 51 209812.
E-mail address: [email protected] (K.B. Brokordt).
responses (e.g. escape behaviours) often have direct
energetic costs (Sih, 1987; Kleinman et al., 1996) and
consequently, many animals have evolved flexible
mechanisms that may be developed or lost over short
periods, depending on the predation risk (Havel, 1987;
Legault and Himmelman, 1993; Reimer et al., 1995;
Reimer and Tedengren, 1996; Rochette et al., 1998).
Morphological, physiological and behavioural respon-
ses to predation seem to be attenuated in culture-reared
fishes in comparison to wild populations (Huntingford,
gy and Ecology 329 (2006) 11–19
K.B. Brokordt et al. / J. Exp. Mar. Biol. Ecol. 329 (2006) 11–1912
2004). This suggests the important selective pressure
of predation, but also suggests that changes in the
genetic structure, and in the phenotypic response of
individuals to predation, may occur in species subjected
to high exploitation rate and aquaculture (Huntingford,
2004).
Comparisons of responses to predators between cul-
tured and wild animals show differences in both juve-
nile and adult stages in species of different taxa
(Haugum et al., 1999; Alvarez and Nicieza, 2003;
Lafrance et al., 2003). Hatchery reared juvenile brown
trout (Salmo trutta) approached dummy predators more
frequently than wild juveniles, and this bnaivenessQ wasdue to a decreased capacity to detect predation risk
(Ferno and Jarvi, 1998). Mussels exposed to predator
odours developed smaller and thicker shells, stronger
byssal attachment and a larger adductor muscle than
non-exposed mussels, which made them less vulnerable
to predation by sea stars and crabs (Hancock, 1965;
Reimer and Tedengren, 1996; Reimer and Harms-Ring-
dahl, 2001). In the scallops Pecten maximus and Pla-
copecten magellanicus, weaker shells (i.e. less resistant
to mechanical pressure) have been observed in cultured
stocks when compared to wild populations (Haugum et
al., 1999; Lafrance et al., 2003). Moreover, the intensity
of the escape response (i.e. swimming speed) was lower
in cultured than in wild juvenile P. magellanicus
(Lafrance et al., 2003) and mortality due to predation
was greater in cultured stocks of P. maximus (Haugum
et al., 1999).
Differences between cultured and wild populations
may also be affected by reproductive status, as invest-
ment in reproduction affects the energetic reserves
used for fleeing predators in several marine and ter-
restrial taxa (Koch and Wieser, 1983; Hughes and
Rayner, 1993; Brokordt et al., 2000a,b, 2003). Scal-
lops are exceptional among bivalve molluscs in having
an excellent swimming capacity, which is exhibited
upon detection of predators (Vogel, 1997). Investment
in reproduction (i.e. gonad maturation and spawning)
markedly reduced the capacity of sub-Arctic (Chlamys
islandica) and tropical (Euvola ziczac) scallops to
escape predators (Brokordt et al., 2000a,b). In both
species, investment in gonads led to an important
decrease in muscle glycogen content and in the
metabolic enzymes that support adductor muscle con-
traction and recuperation during and after the escape
response (Brokordt et al., 2000a,b; Brokordt and
Guderley, 2004). A similar trend was observed in
Argopecten purpuratus, which exhibits an important
decline of muscle carbohydrates and the enzyme octo-
pine dehydrogenase (implicated in muscle contraction
and recuperation), after gonad maturation (Martınez et
al., 2000).
Many marine and terrestrial wild populations have
declined over the past several decades, largely as a
result of fishing or hunting pressure (Brown and
Laland, 2001; Fuller, 2002; Letty et al., 2002; Friedman
and Finley, 2003). Most restocking programs of wild
populations rely on farm- or hatchery-reared stocks
(Brown and Laland, 2001; Friedman and Finley,
2003; Huntingford, 2004). However, the mortality
rates of hatchery reared individuals after release are
very high, mainly due to diseases and predation (Hatch-
er et al., 1996; Barbeau and McDowell, 1998; Brown
and Laland, 2001; Friedman and Finley, 2003). In Chile
the scallop A. purpuratus is becoming a fully domesti-
cated species, as ~90% of the individuals are kept in
suspended cultures along the Chilean coast (Stotz,
1999). Only two natural seabeds remain, and they
show low scallop densities and high predator (sea
stars and crabs) abundance (Ortiz et al., 2003; Stotz,
1999). Thus, the persistence of A. purpuratus popula-
tions in Chile will most probably rely on descendants of
bdomesticatedQ (cultured) scallops to restore natural
beds (Stotz, 1999). Moreover, the settlement of scallop
larvae on collectors, which in the past was exclusively
dependent on wild populations, is now strongly based
on larvae produced in hatcheries. Therefore, these ani-
mals are deprived of direct stimuli by natural predators
for several consecutive generations.
In the present study, we compared escape response
capacities between wild and hatchery cultured A. pur-
puratus, evaluating the effect of gonad maturation and
spawning. We discuss the implications of our results for
conservation and restoration of wild populations, given
the current increase of cultured stocks of several marine
species and the reliance of restocking on hatchery-
reared individuals.
2. Materials and methods
2.1. Sampling and reproductive conditioning of
scallops
Wild Argopecten purpuratus were sampled by
SCUBA diving from Puerto Aldea, one of the few
natural beds that remain in the Chilean coast, located
in Tongoy Bay, northern Chile (308 18V S, 718 33V W)
(Fig. 1). Hatchery reared scallops were obtained from a
scallop farm (Cultivos San Jose), also located in Tongoy
Bay (308 16V S; 718 35V W). Adult scallops (75–85 mm
in shell height) from both populations were transported
to the Central Culture Laboratory at the Universidad
CHILE
Coquimbo
Tongoy Bay
Puerto Aldea
0 1 2
TONGOY BAY
Km
25˚S
45˚S
90˚ 53˚
30˚S
71˚S 20’W
Tongoy
Wild scallops bed
Scallop culture
Pacific Ocean
•
•
Fig. 1. Location (!) of the wild and hatchery cultured Argopecten purpuratus scallop populations in Tongoy Bay, Coquimbo.
K.B. Brokordt et al. / J. Exp. Mar. Biol. Ecol. 329 (2006) 11–19 13
Catolica del Norte, Coquimbo. From each stock, 180
individuals were maintained and conditioned in twelve
200-l tanks (30 scallops per tank) with filtered sea water,
constant aeration and at 16 8C (suggested conditioning
temperature for A. purpuratus; sensu Martınez et al.,
2000). To standardize initial reproductive conditions,
scallops were induced to spawn by increasing the tem-
perature and adding excess microalgae. After spawning,
scallops from both stocks were then conditioned during
~80 days to reach complete gonad maturation (Martınez
et al., 2000). This period permitted standardization of
the nutritional status of both the wild and cultured
stocks. During the conditioning period, scallops were
fed with a mixture of microalgae (50% Isochrysis gal-
bana, 50% Chaetoceros calcitrans) at a daily food
ration of 5% the animals’ dry mass. The food ration of
microalgae was supplied by a continuous dropping sys-
tem. Reproductive stages were determined using quali-
tative and quantitative criteria. As qualitative criteria
and before the behavioural trials, we evaluated the
shape and colour of the gonad and the degree of vascu-
larization by secondary genital ducts which were ob-
servable through the gonad epithelium (Mason, 1958).
As quantitative criteria, we determined gonad stage
using the gonad index corrected by the size of the
scallop [(gonad mass� total soft tissues mass�1)� shell
shell height�1], as described by Bonardelli and Him-
melman (1995). Based on these assessments, three re-
productive stages were determined: maturing, mature
and spawned.
2.2. Evaluation of escape responses
We evaluated the escape capacities in laboratory
conditioned wild and cultured scallops, at three differ-
ent reproductive stages: maturing, mature and spawned
(24 h after induced spawning). The day after the beha-
vioural trials were conducted, scallops were dissected
for quantitative assessments of reproductive stage. Es-
cape responses were quantified at least in 54 scallops
for each reproductive stage, for each population.
Each experimental animal was individually placed in
25-l containers with filtered running sea water at
16 8C. Preliminary observations showed that when
A. purpuratus was stimulated by its natural predator,
the sea star Meyenaster gelatinosus (Ortiz et al., 2003),
they showed a strong escape response that is highly
stereotyped and consistent. The escape response started
with a series of valve claps (alternate adduction and
abduction of the valves). If the stimulus was maintained
Table 1
Two-way ANOVA used to compare gonad indices between wild and
cultured populations (P) of the scallop Argopecten purpuratus at three
different reproductive stages (RS)
Source df F P
Population 1 0.02 0.884
Reproductive stage 2 117.57 b0.001
P*RS 1 31.78 b0.001
Error 344
a
b
c
d d d
Maturing Mature Spawned0
0.05
0.1
0.15
Wild scallops
Cultured scallops
GI (
shel
l hei
ght)
-1
Fig. 2. Gonad index (GI) corrected by the size of the scallop [(gonad
mass� total soft tissues mass�1)� shell height�1], for wild and cul-
tured Argopecten purpuratus conditioned and sampled at three dif-
ferent reproductive stages. Values represent meansFS.E. (n =58 per
reproductive stage, per population). Means sharing the same letter are
not significantly different ( Pz0.05) as indicated by LS means a
posteriori multiple comparisons.
K.B. Brokordt et al. / J. Exp. Mar. Biol. Ecol. 329 (2006) 11–1914
until exhaustion (i.e. scallops did not respond during 2
min), most scallops closed their valves firmly and
remained closed for a certain period, after which the
valves slowly reopened. Based on these behaviours, we
ran the following experiment. Scallops were left undis-
turbed during 5 min before stimulation, in order to
reduce handling stress (Ordzie and Garofalo, 1980).
Then, we stimulated escape responses by touching the
scallops’ mantle edge with an arm of M. gelatinosus,
recording several indicators of scallops’ escape re-
sponse: (1) btime to reactionQ, which is the time elapsed
between the first contact between the sea star arm and
the mantle edge of the scallops and the first clap; this
initial reaction was an indicator of the reactiveness of
scallops to the contact with their predator; (2) the total
number of claps, (3) the duration of the clapping re-
sponse (clapping time) and (4) the clapping rate until
exhaustion. After exhaustion, the experimental animals
were allowed to recuperate for 20 min, which was
sufficient for recovering ~80% of the initial escape
response capacity as indicated by preliminary trials.
We recorded the time that the animals remained with
the valves closed after exhaustion and we then started a
new predator stimulation period, recording the follow-
ing behaviours: (1) the total number of claps, (2) clap-
ping time after recuperation and (3) clapping rate after
recuperation. All the behaviours recorded before and
after the recuperation period were indicators of the
scallops’ escape capacities. We report the results of
the initial stimulation as follows: time to reaction,
number of initial claps, initial clapping time, initial
clapping rate, and the behaviours after recuperation:
proportion of claps recovered, clapping time after recu-
peration and clapping rate after recuperation.
2.3. Statistical analyses
Two-way ANOVAs were used to test the null hypoth-
esis of no differences between scallop populations (wild
and cultured), and reproductive status on gonad index
for each escape response variable (Sokal and Rohlf,
1981). When the assumptions of normality and homo-
scedasticity were not met, the data were ln-transformed.
Normality was tested using a Shapiro–Wilk’s test (SAS,
1999) and homogeneity of variances using a Levene test
(Snedecor and Cochran, 1989). In cases where assump-
tions were not met, ANOVAs were applied to both the
raw and to rank-transformed data and we presented the
results of the former when they were the same for the
two analyses (Conover, 1980). Multiple pairwise com-
parisons tests (LS means) were used to test a posteriori
for specific differences (PV0.05) (SAS, 1999).
3. Results
3.1. Reproductive stages
In both wild and cultured Argopecten purpuratus,
gonad index changed significantly between reproduc-
tive stages, increasing after gonad maturation and de-
creasing after spawning (Table 1, Fig. 2). A significant
interaction between the population and the reproductive
stage indicated that the reproductive status had a dif-
ferent impact according to the population (Table 1).
Maturing animals from wild populations showed sig-
nificantly lower gonad indices than maturing indivi-
duals from cultured populations, but mature animals
from wild populations showed a greater gonad index
than cultured ones (P b0.05; Fig. 2). Maturing animals
from wild populations did not differ from spawned
individuals from both populations (P N0.05). After
spawning both wild and cultured scallops presented
similar gonad masses (P N0.05; Fig. 2).
K.B. Brokordt et al. / J. Exp. Mar. Biol. Ecol. 329 (2006) 11–19 15
3.2. Escape responses
We found strong differences in reactions to predator
stimulation between wild and cultured scallops (Table
2, Fig. 3). Significant interactions between the popula-
tion and the reproductive stage again indicated that the
Table 2
Two-way ANOVAs used to compare escape responses variables
between wild and cultured populations (P) of the scallop Argopecten
purpuratus at three different reproductive stages (RS)
Source df F P
Time to reaction
Population 1 90.38 b0.001
Reproductive stage 2 7.98 b0.001
P*RS 2 4.91 0.008
Error 341
Number of initial claps
Population 1 9.49 0.002
Reproductive stage 2 24.61 b0.001
P*RS 2 6.23 0.002
Error 342
Initial clapping time
Population 1 39.52 b0.001
Reproductive stage 2 20.02 b0.001
P*RS 2 10.96 b0.001
Error 340
Initial clapping rate
Population 1 25.25 b0.001
Reproductive stage 2 5.17 0.006
P*RS 2 8.51 b0.001
Error 340
Time spent closed
Population 1 10.27 0.002
Reproductive stage 2 1.51 0.223
P*RS 2 1.44 0.239
Error 236
Proportion of claps recovered
Population 1 8.12 0.005
Reproductive stage 2 13.36 b0.001
P*RS 2 5.03 0.007
Error 331
Clapping time after recuperation
Population 1 25.55 b0.001
Reproductive stage 2 22.71 b0.001
P*RS 2 14.46 b0.001
Error 315
Clapping rate after recuperation
Population 1 8.84 0.003
Reproductive stage 2 2.72 0.068
P*RS 2 5.91 0.003
Error 316
reproductive status had a different impact according to
the population (Table 2). Wild animals showed a faster
reaction to predators, regardless of the reproductive
stage (Fig. 3A). Cultured scallops were particularly
slow to react in maturing and spawned stages (Fig.
3A). Maturing cultured scallops showed a significantly
higher number of initial claps (first stimulation) com-
pared to maturing wild ones (Fig. 3B). However, the
number of initial claps did not differ between wild and
cultured populations for mature and spawned indivi-
duals (Fig. 3B). Cultured scallops clapped for a longer
time than wild ones for maturing and spawned indivi-
duals, but not for mature ones (Fig. 3C). In contrast,
wild scallops clapped at higher rates (initial clapping
rate) than cultured ones for both maturing and spawned
individuals (Fig. 3D). Although the reproductive stage
did not affect the time that the valves remained closed
after exhaustion (time spent closed), differences between
wild and cultured populations were found (Table 2, Fig.
3E). Scallops from wild populations remained with the
valves closed for a shorter time after exhaustion than
cultured scallops, for both maturing and mature indivi-
duals (Fig. 3E). After 20 min of recuperation from
exhaustion, both wild and cultured maturing scallops
recovered ~75% of their initial number of claps (Fig.
3F). Gonad maturation and spawning decreased the
proportion of claps recovered in cultured scallops, but
not in wild ones (Fig. 3F). Both wild and cultured
scallops maintained their patterns of clapping time
and clapping rate (Fig. 3G, H). As shown for the initial
clapping time of cultured scallops, clapping time after
recuperation for these scallops decreased after gonad
maturation and spawning. However, in wild scallops
there was only a slight decrease in clapping time after
spawning (Fig. 3G). Clapping rate after recuperation of
cultured scallops increased after gonad maturation, but
in wild scallops clapping rate increased after spawning
(Fig. 3H).
4. Discussion
Our study shows that wild Argopecten purpuratus,
compared to cultured ones: (1) reacted earlier when
contacted by their natural predator, the sea star Meye-
naster gelatinosus, (2) exhibited higher clapping rates,
(3) spent less time with their valves closed when
exhausted, and (4) most of their escape capacities
were less affected by the energetic requirements im-
posed by gonad maturation and/or spawning. All the
differences mentioned above would make wild scallops
less vulnerable to predation than cultured scallops.
Thus, future restoration of natural beds based on seed-
min
0
10
20
30
40
B. Number of initial clapsa
b
cbc bc
num
ber
c
0
0.2
0.4
0.6
A. Time to reaction
a
b
dd
d
c
0
1
2
3
4
Wild scallops
Cultured scallops
C. Initial clapping time
bc bcc
c
b
a
min
0
5
10
15
20
25
D. Initial clapping rate
a a aa
bb
clap
s m
in-1
0
5
10
15
20
25
0
1
2
3
E. Time spent closed
bb
bb
a a
min
0
1
2
3
4
Maturing Mature Spawned
G. Clapping time after
recuperationa
b
d
bc
cdbcm
in
0
20
40
60
80
F. Proportion of claps
recovereda
ab ab
cd
bc
d
%
Maturing Mature Spawned Maturing Mature Spawned
H. Clapping rate after
recuperation
bbc
b
bcc
a
clap
s m
in-1
Maturing Mature Spawned
Fig. 3. Escape responses in wild and cultured Argopecten purpuratus after stimulation with their predator, the sea star Meyenaster gelatinosus, at
three reproductive stages (maturing, mature and spawned). Values represent meansFS.E. (n =40–58 per reproductive stage, per population). Means
sharing the same letter are not significantly different ( Pz0.05) as indicated by LS means a posteriori multiple comparisons.
K.B. Brokordt et al. / J. Exp. Mar. Biol. Ecol. 329 (2006) 11–1916
ing cultured scallops would probably reduce the
chances of success of restocked populations. Although
no study has evaluated the relationship between escape
response capacities and predation rates for scallops in
the natural environment, a quicker response (rather than
the number of claps) to evade dredge capture has been
shown to increase survival of the scallop Aequipecten
opercularis in natural beds (Jenkins et al., 2003).
Behavioural differences between wild and cultured
animals may be explained by: (1) different previous
experiences, (2) selection of some behavioural pheno-
types that increase rates of survival, and (3) the
inheritance of the selected behavioural characters
through several generations (Huntingford, 2004). The
production of several animal species in closed environ-
ments (e.g. farms, hatcheries) has led successive gen-
erations of individuals to lack exposure to stimuli
normally present in their natural habitat (e.g. predators).
Considering the plasticity of some phenotype traits (e.g.
behaviour, morphology) upon the presence–absence of
predators, we could predict that some responses of
individuals to natural stimuli could be attenuated or
even absent in reared organisms. Several studies have
demonstrated behavioural and morphological adjust-
ments to prevailing conditions of predation risk in
marine invertebrates (Cote, 1995; Reimer et al., 1995;
Reimer and Tedengren, 1996; Rochette et al., 1996;
Leonard et al., 1999). Whelks (Buccinum undatum)
from populations in the Bay of Fundy (western north
Atlantic, Canada), where their natural predator the sea
star Leptasterias polaris is absent, did not show the
characteristic escape response (Feder, 1967) observed
in populations from the Mingan Islands, where L. po-
laris is present (Rochette et al., 1996). However, escape
response learning has been observed in juvenile whelks
after short term exposure to predator odours (Rochette
K.B. Brokordt et al. / J. Exp. Mar. Biol. Ecol. 329 (2006) 11–19 17
et al., 1998). Social learning and training has also been
observed in hatchery-reared fishes (Brown and Laland,
2001).
Most behavioural comparisons between cultured and
wild aquatic species were accomplished on salmonid
fishes, given the great development of its aquaculture
and increasing reliance on cultured animals for restock-
ing programs (reviewed by Huntingford, 2004). Most
wild scallop beds in Iberoamerica have collapsed and,
as for salmonids, many restocking programs rely on
cultured stocks (Stotz and Mendo, 2001). Given the
high mortality rates of restocked scallops caused by
predation (Hatcher et al., 1996; Barbeau and McDo-
well, 1998), and the importance of the escape response
to avoid natural predators (Feder, 1972; Vogel, 1997;
Ordzie and Garofalo, 1980), it is surprising that few
studies provide evidence to compare the escape perfor-
mance between wild and cultured scallops and the
implications on mortality (Haugum et al., 1999;
Lafrance et al., 2003). Wild scallops Pecten maximus
exhibit harder shells than cultured scallops, which in-
creased their survival (~85%) compared to cultured
ones (~10%) when exposed to crab predation (Haugum
et al., 1999). As we found for wild maturing A.
purpuratus, wild juvenile Placopecten magellanicus
showed more intense escape responses (higher clapping
rates) than cultured juvenile scallops upon encounter
with the sea star Asterias vulgaris (Lafrance et al.,
2003). However, cultured juvenile P. magellanicus
responded with a greater number of claps, longer clap-
ping time and faster recuperation of clapping capacity.
Thus, in contrast to the better escape performance of
wild A. purpuratus, with the exception of the clapping
rate, wild P. magellanicus did not perform better than
cultured ones (Lafrance et al., 2003). Cultured A. pur-
puratus in the present study came from a stock reared
in hatchery for several generations. However, cultured
P. magellanicus juveniles were obtained from spat
collected from wild populations. Thus, the lower escape
behaviour performance observed in cultured A. purpur-
atus may be due, in addition to the lack of prior
experience with predators, to the absence of selection
of more performing escape traits which may have a
great importance in scallop beds (Huntingford, 2004).
Recent studies in the scallops Chlamys islandica
and Euvola ziczac showed that reproductive invest-
ment decreased their capacity to recuperate from ex-
haustive escape response after stimulation with natural
predators (Brokordt et al., 2000a,b). The effect of
reproductive investment in cultured A. purpuratus
was stronger than in C. islandica and E. ziczac. Not
only the proportion of claps recovered after intense
escape decreased in cultured A. purpuratus, but also
the time to reaction (after spawning), the total number
of claps, the initial clapping time and the clapping
time after recuperation. In both C. islandica and E.
ziczac, the decrease observed in the capacity of recu-
peration was linked to an important decline in muscle
carbohydrates, as well as a decrease in muscle meta-
bolic capacity during gonad maturation and spawning
(Brokordt et al., 2000a,b). These muscle energetic and
metabolic reductions after gonad maturation, were also
observed in a previous study on A. purpuratus (de-
veloped under the same laboratory conditions as we
used) (Martınez et al., 2000), and this may explain the
decrease in the escape capacities of cultured A. pur-
puratus observed in the present study. Surprisingly,
our wild A. purpuratus were almost unaffected by
reproductive investment, and maintained most of
their escape capacities after gonad maturation and
spawning, even though during the period we condi-
tioned both cultured and wild scallops, the latter
invested more in reproduction as evidenced by a
greater gonad index. The lack of a negative effect of
reproductive investment on the escape capacities of
wild A. purpuratus is difficult to explain, given that
both wild and cultured scallops were conditioned until
gonad maturation and spawning under the same labo-
ratory conditions and during a period that may be
enough to standardize any original nutritional differ-
ence. We cannot eliminate the possibility of negative
effects of reproductive investment on energetic and
metabolic muscle status that we are evaluating in a
parallel study (Brokordt, unpublished data). On the
other hand, a positive association between genetic
variability and individual fitness has been demonstrat-
ed for a variety of plants and animals (Koehn and
Gaffney, 1984; Koehn and Hilbish, 1987; Zouros and
Pogson, 1994). Organisms with a high degree of
heterozygosity (genetically variable) have a surplus
of energy that may be used to increase fitness (e.g.
growth, reproductive output, escape and mobility ca-
pacities). Considering that hatchery-reared A. purpur-
atus are a product of a few numbers of progenitors
and are constantly under selective pressure for pro-
ductive traits, we might expect that wild scallops will
be more heterozygous and may use their surplus of
energy to reduce reproductive cost and its effect on
escape response performance. We are presently testing
this hypothesis.
In conclusion, wild and cultured A. purpuratus
showed strong escape responses upon contact with
the sea star M. gelatinosus, with wild scallops react-
ing earlier, clapping faster and spending less time
K.B. Brokordt et al. / J. Exp. Mar. Biol. Ecol. 329 (2006) 11–1918
closed when exhausted. On the other hand, before
gonad maturation, cultured scallops clapped more and
longer than wild ones, but their escape capacities
were considerably affected by reproductive invest-
ment. The stronger escape responses and maintenance
of escape capacities during reproduction shown by
wild scallops, may favor their survival in the pres-
ence of predatory sea stars and crabs. Given the
reduction of escape performance in cultured scallops,
and as predation is known to be a major cause of
high mortalities in restocking programs (Barbeau et
al., 1996; Stotz and Mendo, 2001), we suggest that
this aspect should be considered in strategies of
restoration of natural scallop beds. Social learning
and training of hatchery-reared fishes prior to their
release into the wild has been applied successfully to
improve survival of individuals in restocking pro-
grams (Brown and Laland, 2001). Conditioning of
scallops with predator odours, as accomplished with
whelks (Rochette et al., 1998) could be a possibility to
increase responsiveness of scallops to predators before
restocking. We are presently evaluating this hypothesis.
Acknowledgements
We are grateful to R. Vera, G. Gonzalez, D. Jurado,
N. Leiva and G. Nunez, for their unconditional techni-
cal assistance. The paper was improved by comments
of M. Thiel. This research was supported by FONDE-
CYT #3020034 operating grant to K. B. Brokordt.
[SS]
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