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Reproductive biology of the parsley frog, Pelodytes punctatus, at the northernmost part of its range


Abstract and Figures

The reproductive biology and population dynamics of Pelodytes punctatus were studied at the breeding season over a three year period in a coastal dune system located at the extreme northwestern border of the species' range. Adult population size estimates ranged from about 100 in the first year to 60 in the third year. Males were remarkably sedentary near the pond under artificially provided shelters. Many were observed during the most of the breeding season which lasted from mid-March or the end of March to the end of April or mid-May. Most spawning took place in the second half of March or early April. In two years out of three a second period of spawning involving fewer animals was observed in the first half of May. Both periods of spawning coincided with, or shortly followed, periods of rising median air temperature. Egg-clutches were deposited in the deepest parts of pond, mainly on submerged vegetation not reaching the surface. An average sized clutch contained approximately 360 eggs. Development of the embryos until hatching took from 4 to 14 days, depending on the ambient temperature. Larval development and growth were fast. Recently metamorphosed froglets at a size of around 18 mm were found from the end of May onwards. Juveniles may reach adult size in the autumn of the year that they were born. Adult frogs did not show a strong fidelity to the breeding pond between years. In the study area the population structure of Pelodytes punctatus seems to be best described by a source - sink model in which flourishing populations in the dunes give rise to short lived satellite populations outside the dunes.
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Reproductive biology of the parsley frog, Pelodytes punctatus, at
the northernmost part of its range
A.G. Toxopeus, M. Ohm, J.W. Arntzen1
Institute of Taxonomic Zoology,
of Amsterdam, Mauritskade 57, P.O. Box 4766, 1009 AT
The Netherlands
1 address for correspondence and reprint requests: Department of Zoology, University of Leicester,
Road, Leicester LE1 7RH, United Kingdom
Abstract. The reproductive biology
and population dynamics
of Pelodytes
were studied at the
breeding season over a three year period in a coastal dune system
located at the extreme northwestern
border of the species'
range. Adult population size estimates
ranged from about 100 in the first year to 60
in the third year. Males were remarkably sedentary near the pond under artificially provided shelters.
Many were observed
during the most of the breeding season
which lasted from mid-March or the end of
March to the end of April or mid-May.
Most spawning
took place in the second half of March or early
April. In two years out of three a second
period of spawning
fewer animals was observed
in the
first half of May. Both
periods of spawning
with, or shortly
of rising
median air
temperature. Egg-clutches
were deposited
in the deepest parts of pond, mainly on submerged vegetation
not reaching the surface.
An average
sized clutch contained approximately
360 eggs. Development
of the
until hatching took from 4 to 14 days, depending on the ambient temperature. Larval develop-
ment and growth were fast. Recently
metamorphosed froglets
at a size of around 18 mm were found from
the end of May onwards.
Juveniles may reach adult size in the autumn of the year that they were born.
Adult frogs did not show a strong fidelity to the breeding pond between years. In the study area the
population structure of Pelodytes punctatus
seems to be best described by a source - sink model in which
flourishing populations in the dunes give rise to short lived satellite
populations outside the dunes.
The parsley frog, Pelodytes punctatus (Daudin, 1803), is distributed over a major part of
western and south-western Europe. The French Channel coast is at the extreme north-
western part of its range (fig. 1). The species was discovered by Giard (1890) to occur
north of Boulogne-sur-Mer. In 1951 the species was found again by the late D. Hillenius
(pers. comm., 1976), while Arntzen and Gerats (1976) documented the existence of some
flourishing populations in the area.
We studied the reproductive biology and population dynamics of the parsley frog with
the aim of gaining a better understanding of its ecological requirements, especially those
that may govern its existence at the northern edge of its range.
Figure 1. Distribution of Pelodytes punctatus.
The study area in north-western France is: 1)
UTM grid NF27,
and Oliviera, 1989);
by an arrow. Reliable records documenting
the outer range of the
are numbered as follows.
(Boscá, 1880); 3)
Los Pedroches
et al., 1980); 4)
San Pablo
de los Montes,
(March 1984,
I. Esteban and A. Mugica, pers. comm.); 5) Uruefia,
(June 1990,
pers. comm.);
6) Cisneros,
(March 1980, J.W.
and A. Zuiderwijk, unpubl.);
7) UTM
grid WN14, (A. Bea, 1985); 8) Saint
Jean de Pied-de-Port,
(Martinez Rica, 1983); 9) Bellevue,
and Peuplingues
en van Leeuwen,
by M. Ohm and D. van der Kroef in
1983; 10-14) Institute Géographique National maps 1/50,000 nr. XXXI-10 (Montmedy),
all in Le Garff (1989);
Castino, (Bruno, 1977); 16)
Rapallo, Genova, (Bruno, 1977;
Sindaco and Andreone, 1988).
Numbers are
placed at the outside of the indicated distribution. The occurrence of the species
in Belgium
and Wolterstorff,
see Parent 1984 for further references), Luxemburg (Hoffmann, 1958), Germany
(Fournel, 1836 in: von Bedriaga, 1891)
and northwestern
Spain and Portugal (Regulez
Fernández, 1988;
Vieira, 1887;
Crespo, 1971)
is unconfirmed
(Holandre, 1851 in: von Bedriaga, 1891; Parent, 1970, 1984;
Arntzen, 1981;
Crespo and Oliveira, 1989;
M. Garcia-Paris.
pers. comm., 1991).
The map comprises
two as
yet unpublished
records in southeastern
and Vélez
in 1990 and 1991
by M. Garcia-
Paris, completing
recent maps such as in Crespo and Oliveira
Material and methods
Research was carried out in a coastal dune system ('Dunes de Slack') south of Amble-
teuse in the département Pas-de-Calais, France during the breeding season from 1981 to
1983. In the inner dune slacks many natural freshwater ponds can be found, while some
ponds have been enlarged and others newly created to serve for duck hunting. Three
ponds in an accessible part of the dunes were selected for the study on the parsley frog.
Two small and shallow ponds (maximum size of 90 m2, up to 35 cm deep) were located
close to one another in an abandoned sand quarry. (These ponds are very similar to the
dune slack depicted by Arntzen, 1981: fig. 31, and by Arntzen and Teunis, 1993). A
bigger and slightly deeper (up to 50 cm) horseshoe shaped pond with a surface of
approximately 1900 m2 was also selected. The ponds are separated by 300 m in direct
line. Due to an unacceptably high level of vandalism in the quarry, Horseshoe Pond only
was studied in 1982 (by Den Uijl, 1982) and in 1983. Each summer, the ponds gradually
decreased in size to dry out completely (in the quarry) or to reduce to about one third of
its original size (Horseshoe Pond).
The margins of Horseshoe Pond were covered with a dense vegetation of Leptodictyum
riparium, Claytonia perfoliata, Veronica scutella and Poa annua while higher up a dense Salix
repens, Salix purpurea and Hippophae rhamnoides vegetation and planted Pinus nigra was
found. In all ponds the aquatic vegetation was scarce, mainly consisting of Mentha
aquatica, Potamogeton perfoliatus,
Chara sp. and some Phragmites australis and Cirsium arvense.
In marshy areas of Horseshoe Pond Hydrocotyle vulgaris, Rumex hydrolapathum, Iris pseu-
dacorus and Juncus inflexus
was found. The margins of the two quarry ponds were almost
barren. All three ponds were virtually unshaded.
The parsley frog is a nocturnal creature which hides during the day under vegetation
cover, trash or in self-dug holes. To trace the animals more easily than could otherwise
be achieved, artificial hiding places were created. These were pieces of wood, rags,
metal, carpet etc., varying in size from 0.4 to I m2 that were collected from the local
refuse dump. These were distributed around the pond at more less regular intervals
averaging from 1 1 m in 1981 to 8 m in 1983. The artificial shelters were placed in early
spring at a short distance from the pond margin (50 cm to 100 cm in spring), were they
remained for the whole study period, after which they were removed. The shelters were
checked for frogs on a daily basis. All animals were measured dorsally for snout - vent
length (SVL, from the tip of the snout to the posterior side of the urostyl). In 1981 and
1983 all captured animals were sexed (males are characterized by breeding pads on their
breast, arms and fingers). All metamorphosed animals with a SVL of mm could be
sexed unequivocally. They were released on the spot after being toe-clipped to allow
individual recognition. The adult population size (NJ was estimated by census, for
males and females (Nf) separately. Males were counted directly and the estimated
population (N £ equalled the total number of different males observed. For the females
Nf was estimated indirectly as equalling the total number of egg-clutches found in the
pond. To gain an impression about the frequency with which frogs go unnoticed, we
calculated a 'census oversight index', by dividing the number of days any individual frog
was observed in the time span between its first and last appearance around the pond by
the total number of opportunities (days) for observation and we then averaged this
measure for all males and all females.
The clear ponds were searched daily for newly deposited egg-strings. For each finding
the following parameters were recorded: location (relative to a grid system along the
shore of the pond), length of the egg-string in a straight line (as a multiple of 5 mm along
the unmanipulated egg-string), depth of the pond at egg-string location (in cm), the
depth of the water column from the centre of the egg-string to the surface (in cm) and
the number of days it took half of the eggs in the clutch to hatch. In 1983, embryonic
development was followed in more detail for seven clutches including some of the
earliest and some of the latest spawnings of the year. The water temperature was
measured daily on the spot by a minimum-maximum thermometer. Since it proved
difficult to find larvae in the pond after they had hatched, and to avoid the mixing of
larvae of different ages, growth was studied for a sample of larvae in netting cage (50 cm
high, diameter 70 cm) that was placed around an egg-string on a representative site in
the pond (see fig. 6). Growth was also studied for a single larval cohort in a pond at close
proximity in 1975. Measurements taken on larvae were total length (TL) from the tip of
the snout to the tip of the tail and SVL from the tip of the snout up to and including the
posterior side of the body.
Daily minimum and maximum air temperature were obtained from the meteorologi-
cal station Boulogne-semaphore (altitude 0 m) in Boulogne-sur-Mer, situated 10 km
from the study area.
Breeding and spawning
The number of male frogs found under the artificial hiding sites during the course of
1981 is shown in fig. 2. On 12 March the first male was found in the quarry. In
Horseshoe Pond the first males were observed on March 25. Their numbers were
highest by the middle of April (in Horseshoe Pond) and early May (in the quarry). From
those points in time onwards the numbers decreased gradually until by earlyJune all the
males had gone. Fifty-one different males were altogether observed in Horseshoe Pond
and 33 in the quarry ponds. Thirty-four males (67%) stayed at the shore of Horseshoe
Pond for a longer time and were observed four times or more. Some of them were found
throughout most of the study period. Others apparently were around for much shorter
periods and were found only once, or a few times (table 1 Towards the end of the study
period, males not observed before occasionally arrived at the pool while others left,
creating a certain turnover in the population. Fewer females than males were observed
both at Horseshoe Pond (n=10) and in the quarry (n=9). In contrast to the pattern
observed for the males, relatively few females at Horseshoe Pond were seen four times or
Figure 2. Daily
observed number
of males,
females and newly deposited egg-clutches of Pelodytes punctatus
northwestern France in 1981 in a) the Quarry Ponds and b) Horseshoe Pond. Shading
periods in
which no observations were made. Periods
of rising
air temperature
of increase of median values
per 24
are shown
in the lower
figure by hatched bars.
Table 1. Number of times
were observed at Horseshoe
Pond. For males,
total number observed is shown to approximate
population size (details
see text).
more. Compared to the males, females stayed at the pond shore line for a short time
being observed fewer times (table 1). ).
In 1981 spawning took place in two periods, the first period being from the end of
March to early April and the second period being in early May (fig. 2). A total of 46
clutches was found in Horseshoe Pond and 15 clutches were found in the quarry. In
making up 46 clutches the first period of egg-deposition was more important than the
second one, when only 12 clutches were deposited. Three more clutches were found
mid-April, in between the first and the second periods of spawning.
Similar temporal patterns of presence and abundance were found in 1982 and 1983,
with the highest numbers of adults present in the second half of April (in 1982) or the
first half of May (in 1983) (fig. 3). In 1982 most egg clutches (28 out of 35, 80%) were
deposited in the first half of April and in 1983 in the second half of March (23 out of 34,
68%). Five egg clutches were observed in May 1982 and none in May 1983. In each of
the study years egg deposition was preceded by a period of rising air temperatures (figs.
2 and 3).
Egg deposition
Apart from a few egg-strings that were not attached to any substratum, or that were torn
loose by the action of wind and waves, all the clutches were found deposited against
plant material in a zig-zag manner typical for Pelodytes punctatus (Toxopeus, 1985).
Submerged, short stiff branches from Phragmites australis and Cirsium arvense were most
often used for this purpose. Approximately nine out of ten clutches were deposited on
submerged vegetation that did not reach the water surface and about three out of four
clutches were laid closer to the bottom of the pool than to the surface. In 1981, 30 out of
44 (68%) of the clutches that were observed on the spot were deposited in the deep part
of the pond, 27% were deposited in areas of intermediate depth and 5% were deposited
Figure 3. Daily
numbers of males,
females and newly deposited egg-dutches
of Pelodytes punctatus
France in Horseshoe Pond in a) 1982,
and b) 1983.
as in fig. 2.
Table 2. Depth of Horseshoe Pond at the spots where egg clutches of Pelodytes punctatus
were deposited.
V as measured in 1982
in the shallow part of the pond. A similar pattern was found in 1982 (table 2). In 1983
more clutches were deposited at places of intermediate depth than at deep sites, but it
should be noted that in that year the pond was less deep than in the years before and
deep sites were not available.
The yearly average size of the egg strings ranged from 70 mm (SD=26.2 mm, n=36) in
1982 to 81 mm (SD=27.0, n=33) in 1983. These values are not significantly different
from one another. The number of eggs in an average sized string is estimated at 360, but
clutches existed with as few as 100 and as many as 700 eggs. Interestingly, in 1981 the
mean length of the clutches from the first period of spawning was significantly larger
than those from the second period (83 mm versus 67 mm; t-test, p<0.05). No correlation
was found between the pond depth at the spawning site and the size of the clutches (in all
three years the product-momènt correlation coefficient r was <0.2 and the correspond-
ing p value >0.05).
Embryonic development,
larval growth, metamorphosis
and adult size
With the exception of a single moulding egg clutch in 1982, all clutches had developing
eggs and, despite the presence of potential predators like the newt species Triturus
cristatus and T. vulgaris in Horseshoe Pond, the disappearance of eggs or entire clutches
was not observed. (See Isle de Dreneuf, 1862, for a report of predation on a Pelodytes egg-
clutch). The development of the eggs until hatching ranged from a maximum of 19 days
at the start of the season (in 1983) to a minimum of 3 days (observed in May 1981). A
strong negative relationship was observed between water temperature and age at
hatching. At a median temperature of 90 C embryonic development till hatching took
10-14 days; at 170 C this was reduced to 4 days (fig. 4). The first free-swimming larvae
were observed the earliest on April 6th (in 1983) and at the latest on April 16 (in 1981). ).
Spawning was not observed in 1975 but is likely to have peaked in early April when
temperature rose sharply after a three week long cold spell with average median air
temperatures below 50 C (Arntzen and Gerats, 1976). By the end of May the larvae from
these clutches had reached an average SVL of 16.1 mm. The small variance in size of
this cohort (SD=1.2 mm, n=50) indicates that the tadpoles were of similar age. A further
two weeks of rapid growth made the sample reach maximum mean body size of 24.6 mm
Figure 4. Duration of embryonic development
as a function of water temperature (median
value per 24
for seven selected
of Pelodytes punctatus
in Horseshoe Pond. The curve is fitted by a third
order polynomial.
(fig. 5). By then hind limbs had appeared in all tadpoles. Fore-limbs were visible behind
the transparent skin by June 19 and in the sample taken nine days later fore-limbs had
appeared in all but one of the specimens. We assume that most larvae had meta-
morphosed at July 8 because only a single (metamorphosing) larvae could be obtained at
that date.
In the cage that was placed around an egg-string, mean SVL increased from 3 mm for
23 hatching embryo's on April 20, 1982 to 18 mm for tadpoles at June 14. By then hind
limbs had appeared, followed six days later by the fore limbs. Eight larvae (35%) had
completed metamorphosis at July 14 with a SVL of 17 mm (fig. 5). Metamorphosed
froglets in close proximity to the ponds were observed in 1981 from 6 to 27 July (n=5), in
1982 from 15-21 May (n=5) and in 1983 on May 26 (n=14). The number of days passed
since the peak in spawning till the day the first metamorphs were observed ranged from
67 days in 1983, approximately 90 days in 1975 and in 1982, to 102 days in 1981.
Average size of the metamorphs in the biggest sample, that of 1983 (n=14) was in the
range of 15-21 mm. By the end of August 1983 a sample from this cohort (n=8) had
obtained a size range of 21-28 mm.
Adult males as measured in 1983 were on average significantly smaller than females
(SVL of 37.5±3.02 mm, n=24 versus 40.6±3.56 mm, n=11; p<0.05 in t-test).
Adult population size and spatial distribution
Altogether 33 different males, 9 females and 15 egg clutches were observed in and
around the quarry ponds in 1981. The number of males observed around Horseshoe
Figure 5. Growth
of tadpoles of Pelodytes punctatus
in north-western France.
snout - vent
length (SVL)
is indicated
by squares,
total length by dots and standard deviation
by vertical
bars. Numbers
to sample
size. Data points connected
by interrupted lines are approximated;
details see text. The graph connecting
symbols represents
in a cage
(data from
den Uijl, 1982;
see text and fig.
To the
right average
SVL and standard deviation for adult males
and females
(g, as measured in 1983.
Pond in that year was 51 and 24 were observed in 1983. The vast majority were
recorded more than once, with a maximum of 56 records over 78 observation days and
low values were obtained for the index of daily census oversight (0.35 in 1981 and 0.24
in 1983). It is therefore unlikely that many male frogs will have been overlooked. Even
frogs using a single shelter for a single day are not likely to have escaped our attention,
and we conclude that Nm closely reflects reality. Comparing the number of egg-strings
in Horseshoe Pond with the observed number of females under the shelters it is
concluded that many females have gone unnoticed, i.e. they do not seem to use the
shelters to the same extent as the males. The female population size, estimated from a
count of egg-clutches, was 46 in 1981 and went down to 35 in 1982 and to 34 in 1983.
Assuming that each female deposits only once a year, the female population size in 1981
was 46 individuals. The estimated sex-ratio expressed as 1Vm over l%r (5 1 /46
in 1981 and
24/34 in 1983), in neither year is significantly different from unity (G-test for goodness
of fit). The total estimated population size for the adults declined from 97 in 1981 to 58
in 1983. On the assumption that sex-ratio was at unity in 1982 Na can be estimated from
Ñf to give a value of 70 for that year.
Out of 51 males marked around Horseshoe Pond in 1981, nine ( 18%) were recaptured
in later years. Interestingly, six more recaptures were found that were originally marked
in the quarry at 300 m distance (6 out of 33, 18%). Only one female was ever recaptured
between years. The parsley frog seems to swap breeding site easily from year to year
between the quarry and Horseshoe Ponds. Unfortunately, this behaviour with the
adults moving away from their original breeding site to take up residency at another site
precludes the estimation of yearly survival rates.
A different pattern is observed during the breeding season when the males are
remarkably sedentary. They were found under the same shelter up to 38 times in a row,
with no gaps in the recording. Other males occasionally moved to another shelter, but
the pattern as a whole is that of sedentariness. In 1981 most males had taken up
residency on the spit of land (fig. 6 spot C), with another aggregation at the opposite
corner of the pond (fig. 6 spot E), spanning that part of the pond where most egg-strings
were deposited. Similar patterns of clumped male frog distribution were found in 1982
and 1983
(fig. 7). Visual inspection of figs 6 and 7 reveals a tendency for the females not
choosing the shelters where male frogs were residing. In 1981 and 1983 most females
were found close to, but outside the areas were males aggregated. Choruses of males
displaying their mating call in the evenings (Hotz, 1971; Paillette et al., 1992), were
observed near the centre of the pond. Most males were calling from above the water
surface, although some called from a submerged position.
The parsley frog, Pelodytes punctatus, is among the least known species of the Palaearctic
herpetofauna. For just over a century now it has been known to occur in Pas-de-Calais,
close to the northern edge of its range. However, the existence of a relatively large
(Ña=60-100) and a successfully reproducing population north of Boulogne-sur-Mer
is only documented for Horseshoe Pond. In estimating Na several assumptions are
made. For the males it is assumed that none of them go unnoticed, or - in other words -
that all, at some time or other, use the shelters provided for a period of time long enough
(approximately 24 hours) to be observed at at least one of the daily checking routines
during the breeding season.
As judged from the comparison of the number of females and the number of egg-
strings, females, in contrast to the males, do not seem to be using the shelters to an
extent that N fwould be reliably estimated. However, the clear pond does allow a correct
count of all egg-strings. Some reports indicate that females deposit several clutches in a
single mating. Studying the breeding of the parsley frog in captivity, Raehmel (1983),
Toxopeus (1985) and Hartley (1990) all observed 2 or 3 clutches laid by single females,
with a time span between deposits of 15 minutes in an interrupted amplexus with spatial
Figure 6. Map of Horseshoe Pond with the egg clutches of Pelodytes
indicated as found in 1981
(round symbols, n=44), 1982
(square symbols, n=35)
and 1983
symbols, n=33). Position
of cage
which larvae were raised is indicated
by an asterisk. Isobaths are given
for pond depths
of 15 and 25 cm, as
measured in 1982.
the shore line are schematically
indicated where
and females
(grey shading)
were found
in 1981. For the spatial
distribution of the adults in 1982
and 1983 see
fig. 7.
Figure 7. Distribution of adult
Pelodytes punctatus
around Horseshoe Pond in 1981, 1982,
and 1983. Number
of male observed at shelters is indicated above the horizontal
females shown below the horizontal axis
the exception
of 1982
data when data for males and females were pooled).
Note that the total surface
by the graphs
varies over the years not only
as a function of the number of animals
but also
with the number of artificial
in 1981,
36 in 1982
and 41 in 1983).
Letters A to E indicate the
corners of the pond as shown
in fig. 6.
relocation (Hartley, 1990) to two hours in a continued amplexus (Toxopeus, 1985). In
another study (van den Elzen, 1976) it is implicitly stated that generally more than 10 0
clutches are deposited per female! If in the wild indeed more than one clutch is
deposited per female, as seems to be the case in captivity, this would mean that Nfis
overestimated. This could be by as much as a factor 1.7 in the quarry and a factor of 3.0
- 4.4 in Horseshoe Pond (cf. tables I and 2). Circumstantial evidence counting against
this interpretation is that the clutches are spaced out all over the deeper parts of the
pond (fig. 6) and that no indications were found for two or more of the shorter egg-
strings to be deposited in close proximity to each other. We suggest that several short
clutches instead of a single larger one are normally laid only in shallow water where not
enough vertical space is available for the female to climb the vegetation during egg-
deposition. (See the description of the breeding behaviour of the frog by Toxopeus,
1985). Observations supporting this view were made in two ponds in very close prox-
imity to each other but differing in depth, in a sand-quarry near Montelimar in
southeastern France (J. W. Arntzen and A. Zuiderwijk, 1983 unpubl.). It was found that,
the freshly deposited egg-strings found in the shallower of the two ponds (8 cm versus 18 8
cm water depth) were significantly shorter than those found in the deeper pond (52.2 ±
9.6 mm, n=ll, versus 74.7±24.5 mm, n=15; p<0.01, t-test). For the relatively deep
Horseshoe Pond we therefore favour the interpretation in which each egg-clutch repre-
sents an adult female. A corollary of the alternative explanation in which females each
year deposit several clutches, is a male biased sex-ratio that at Horseshoe Pond would
significantly differ from unity (p<0.05; G-test for goodness of fit).
The artificial shelters are intensively used by the males. The fact that during the
breeding season the males congregate in groups in and around the pond seems to
indicate the existence of a lek breeding system (cf. Bourne, 1992). Interestingly, indica-
tions are found that females assemble at places that are satellite to these male groups
(figs 6 and 7), and we speculate that they enter the lek when ready for breeding, acquire
a mate and enter the pond in copula. It may be that the observed preferences for the
deepest parts of the pond to mate, and for non-emerging aquatic vegetation to use as a
substratum for egg-deposition (cf. H6ron-Royer, 1879) are interdependent. The sugges-
tion that the parsley frog prefers the shallowest parts of the ponds to spawn (von
Bedriaga, 1891), where vegetation is densest (H6ron-Royer, 1879), cannot be
Compared to most other Palaearctic anurans the embryonic development of the
parsley frog is rapid and larval growth is fast (Diaz-Paniagua, 1988). Embryo's are
reported to hatch in 8.5 to 10 days (von Bedriaga, 1891; Raehmel, 1983; Diaz-Paniagua
and Arizabalaga, 1987) and to complete metamorphosis in a further 73 to 97 days
(Balcells, 1955; Raehmel, 1983; cf. Girard, 1989), all in line with our observations. In
hibernating tadpoles it may take up to 8 months to reach metamorphosis (Lataste, 1876;
van den Elzen, 1976). In southern France tadpoles are reported to metamorphose at a
SVL of apto 25 mm in 2-3 months after hatching (von Bedriaga, 1891). In a study of 5
species of anurans in southern Spain, the fast growth of Pelodytes punctatus
tadpoles is only
matched by that of Pelobates cultripes (Diaz-Paniagua, 1988), reaching a large size at
metamorphosis (up to 23 mm) in approximately 70 days.
The growth curve obtained for free-swimming tadpoles of the parsley frog at the
northern edge of its range is surprisingly similar to that at the very south of its range
(data from Diaz-Paniagua and Arrizabalaga, 1987; Diaz-Paniagua, 1988, 1989 and
pers. comm., 1992). In this context, two observations are relevant. Firstly, in the south
of Spain, the frog breeds in November and the larvae develop during the coldest months
of the year (Diaz-Paniagua, 1988), while in the north the larval period falls in spring and
early summer. Secondly, in the north most successfully reproducing populations of the
parsley frog are found in the warmest environments. Applying a method in which the
(temperature dependant) inversion of sucrose into glucose was used to determine
additively the water temperature of ponds, Kleyn and Smit (1986) demonstrated that in
spring and early summer the dune ponds in the same study area (some of them with
parley frogs) were significantly warmer than similar sized ponds outside the dunes. The
temperature difference averaged at 3.50 C. We have shown that ambient temperature
strongly influences developmental rates in the parsley frog. It may well be that effec-
tively the temperature regimes in ponds at opposite sites of the N-S distribution during
larval development are altogether not markedly different.
Algae and detritus constitute the bulk of the diet of tadpoles of the parsley frog (Diaz-
Paniagua, 1989). They possess an efficient filter apparatus and a long digestive tract that
enables them to successfully exploit the algal blooms (Sokol, 1981; Diaz-Paniagua,
1989) that develop in early spring in the otherwise oligotrophic dune slacks, acquiring a
large size at metamorphosis in a relatively short larval period.
With several months available for terrestrial feeding, metamorphs may be able to
reach adult size (28 mm) before they go into hibernation. Indeed, some specimens were
recorded reaching adult size as early as the end of August in the year that they were
born. That small animals may be sexually mature was shown by Hartley's (1990)
observation of a successfully reproducing female of only 25 mm. Considering the fast
larval and juvenile growth as documented in the present study, we assume that in
northern France the parsley frog normally breeds for the first time at the beginning of its
second year. Compared to other Palaearctic anurans the juvenile phase of the parsley
frog is unusually short.
Several hypothesis can be put forward that would explain the existence of a second
peak of breeding activity as observed in 1981 and in 1982. The second peak of breeding
could be caused by: i) some particularly successful females producing not one but two
clutches a year (cf. Wells, 1976); ii) new recruits to the breeding population that had not
yet maturated earlier that year (cf. T J.C. Beebee, in: Silverin and Andrén, 1992); or iii)
by females that postponed oviposition, in response to environmental conditions such as
drought (cf. Silverin and Andrén, 1992). Our observation that clutches laid by Pelodytes
punctatus in the second period are smaller than those laid in the first period is not in line
with the latter scenario; it does, however, not allow to discriminate between the other
two explanations. Smaller clutches may be expected to be produced by new breeders
because recruits will be comparatively small and female fecncity may be related to body
size. Alternatively, resources might be insufficient to produce a second clutch that is
equally large to the first one, considering the short time span available (cf. Howard,
1978). To complicate matters further, some authors report autumnal breeding of
Pelodytes punctatus in Italy and southern France (Von Bedriaga, 1891; Sindaco and
Andreone, 1988), but such has not been observed in the d6partement Pas-de-Calais.
Despite extensive inventories in Pas-de-Calais, the Parsley Frog is rarely found
outside the dunes (Zuiderwijk and Hooghiemstra, 1975; Arntzen and Gerats, 1976;
Kroese and Van Leeuwen, 1979), and a similar distribution pattern is found in the
d6partement Somme, to the south of Pas-de-Calais (Godet, 1990). Outside the dune
areas the species has been found in an abandoned marble quarry and in two cattle
drinking troughs in pasture land. Outside the dunes the presence / absence of Pelodytes
punctatus in Pas-de-Calais is not clearly associated to any environmental variable, as
seems to be the case for western Europe on the whole; generally, its presence is localized
and most difficult to predict (A. Zuiderwijk, pers. comm., 1983; Paillette et al., 1992).
We have shown the adult frogs to be quite migratory and we assume that in this way new
populations are occasionally founded. On the whole however opportunities for success-
ful reproduction will be rare and many populations may not survive. Such a 'source -
sink' pattern of population structure fits the distributional observations very well. In
Pas-de-Calais the main sources of dispersal are found in the dunes. These sandy habitats
provide easy shelter for the adults as well as relatively warm and oligotrophic aquatic
conditions for the tadpoles. The ultimate factor governing successful reproduction in the
dunes may well be annual rainfall. Occasionally ponds were observed to dry out well
before metamorphosis while in other years, with less than average levels of precipitation,
many ponds ceased to exist altogether. In such conditions a flexible mode of life with the
potential to quickly invade new ponds when they come into existence is a requirement to
Acknowledgements. We thank Dirk van der Kroef for assistance in the field, Dr. Mario Garcia-Paris
and Dr. P. Galin for their help in the construction
of fig.
Carlos Abrahams for polishing
the english
Mr. P. Sauvage for support and the organization 'Espace Naturel Régional, Littoral Pas-de-Calais' for
access to the study sites.
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... The field study was carried out from September 2007 Each pond was surveyed twice each month. The parsley frog's embryonic period ranges from 5 days at 15°C to 15 days at 10°C (Toxopeus, Ohm et al. 1993). Moreover, embryos stay attached to the egg jelly for several days after hatching We assessed the success of a reproductive event by estimating the hatching rate, the larval survival (from hatching to metamorphosis) and the survival from egg to metamorphosis. ...
... Jourdan-Pineau, ) and it wasn't our aim in this study to deal with larval development. Besides, the impact of rainfall and air temperature on breeding activity has also been previously established for parsley frog (Toxopeus, Ohm et al. 1993;ACEMAV-coll., Duguet et al. 2003;). In brief, in temporary ponds, oviposition takes place after heavy rains whereas in more permanent ponds, an increase in diurnal temperature seems sufficient to induce breeding activity. ...
... The breeding pattern characterized with two seasonal peaks is similar to what was previously described in Mediterranean regions and was explained by the favourable climatic conditions (Toxopeus, Ohm et al. 1993; . It is probable that the timing of reproduction responds to a trade-off between adult and larvae requirements. ...
Full-text available
Phenotypic variability tends to increase in temporally and spatially variable environments. This thesis deals with the variability of life-history traits in fragmented populations. In Mediterranean regions, Parsley frog, Pelodytes punctatus, breeds both in spring and in autumn, in response to temporal variations of its environment. I studied the origin and evolutionary consequences of its breeding strategies. Both breeding periods produce offspring (much more in autumn, though) and spring tadpoles suffer from intraspecific competition with older autumn tadpoles. Autumn laid juveniles are bigger and emerged sooner from the ponds. These developmental differences are not due to genetic differences between seasonal populations. They are explained by phenotypic plasticity in response to drastically different conditions. Even if it seems more favourable to breed in autumn, both strategies are maintained either by bet-hedging or pure opportunism. Besides, fragmentation, which increases with global changes, tends to reduce population effective size and increase genetic heterogeneity within populations. However, no inbreeding was found in the studied populations but a high family structure induced allele/fitness correlations. Together, these results enlighten the variability of breeding strategies and larval traits in Parsley frog and indicate a high phenotypic plasticity in response to environmental variations.
... This encompasses general accounts on the biology of the species (e.g., Elzen 1975Elzen , 1976, diet analysis of adults from Catalonia (Bea et al. 1994), and diet preferences of tadpoles (Richter- Boix et al. 2007). Reproduction is related to an increase in seasonal rainfall and occurs early in the year, usually before that of other anuran species, with two breeding periods: one at mid-fall and another in late winter and spring (Sindaco & Andreone 1988;Toxopeus et al. 1993;Guyétant et al. 1999;Boix et al. 2004;Egea-Serrano et al. 2005;Richter-Boix et al. 2006;Petitot et al. 2014). Reproduction in autumn is often minor and irregular (Cayuela et al. 2012), however, in southern populations the breeding season extends all year round (A. ...
... Eggs are black and small (diameter 1.5-2 mm), arranged in strings of 70-80 mm length and containing 40-700 eggs. Overall clutch size can be up to 1,600 eggs (Boulenger, 1897;Lanza 1983;Toxopeus et al. 1993). Hatching success might be related to water oxygen content (Guyétant et al. 1999). ...
... Males reach sexual maturity at one year of age and females at two years and longevity can reach 8 years (in males) and 10 years (in females), similarly to other species of the genus (Esteban et al. 2004, Erişmiş et al. 2011. The sex ratio within a population is close to 1:1 (Toxopeus et al. 1993). The IUCN threat status of P. punctatus is Least Concern (Denoël et al. 2009); however, in the edge of its range (north of France, Italy and east of Spain), the species is generally scarce and highly threatened, due to the loss of breeding sites, close to local extinction in some areas (Parent 1989;Salvidio et al. 2004;Escoriza 2015). ...
Parsley frogs (Pelodytes) comprise the only genus in the family Pelodytidae, an ancient anuran lineage that split from their closest relatives over 140 million years ago. Pelodytes is a Palearctic group restricted to Western Eurasia including three extant species: the eastern species P. caucasicus, endemic to the Caucasus area, and two closely related species inhabiting Western Europe: the Iberian endemic P. ibericus and the more widespread P. punctatus. Previous studies based on mitochondrial and nuclear DNA markers have revealed the existence of two additional lineages of Parsley frogs in the Iberian Peninsula, which have been flagged as candidate species. Here, we integrate novel molecular, morphological and bioacoustical data to assess the differentiation of the four western Parsley frog lineages. Species trees and Bayesian population assignment analyses based on nuclear markers confirm previous studies and concordantly delineate four parapatric lineages with narrow hybrid zones. Mitochondrial divergence is low (< 2% pairwise distances in the 16S rRNA gene), in line with previously reported low mitochondrial substitution rates in non-neobatrachian frogs. Based on concordance between mitochondrial and nuclear markers, we conclude that four species of Parsley frogs occur in Western Europe: Pelodytes punctatus, distributed from northern Italy to northeastern Spain; Pelodytes ibericus, inhabiting southern Spain and southern Portugal; Pelodytes atlanticus sp. nov., from the Portuguese Atlantic coast; and Pelodytes hespericus sp. nov., occurring in central and eastern Spain. However, bioacoustical and morphological differentiation of these species is low, with no obvious and qualitative diagnostic characters allowing full species discrimination. Differences in the relative size of metacarpal tubercles exist but this character is variable. Pelodytes ibericus and Pelodytes atlanticus are smaller than the other two species, and P. ibericus has shorter limbs and various distinctive osteological characters. Bioacoustically, the pattern by which two different note types are combined in advertisement calls separates P. hespericus from the remaining species. Despite these differences, we emphasize that the taxonomic status of all four western Parsley frogs requires additional investigation, especially the patterns of genetic admixture across contact zones. While a status of separate species best conforms to the currently available data, alternative hypotheses are also discussed.
... The mean number of eggs in a clutch of Pelodytes punctatus (Daudin), the smallest species in the genus Pelodytes Bonaparte is 360 (Toxopeus et al., 1993). It was also reported that the number of eggs spawned by a Pelodytes caucasicus Boulenger female changed with altitude, e.g., fewer eggs near sea level and more eggs in higher environments (Tuniev, 1989). ...
... In Pelodytes punctatus, which was reported to have rather rapid embryonic and larval development, the embryonic development until hatching took 4-14 days, depending on the ambient temperature, and metamorphosis was completed in approximately 70 days (Toxopeus et al., 1993). Also, metamorphosis was completed in 73 days for Rana pseudodalmatina in Golestan Province, Iran (Pesarakloo et al., 2015), 43-90 days for P. ridibundus in Anzali Lagoon, Iran (Mirzajani et al., 2006) and 80-120 days in France (Momeni and Zamatkesh, 2005). ...
... The mean number of eggs in a clutch of Pelodytes punctatus (Daudin), the smallest species in the genus Pelodytes Bonaparte is 360 (Toxopeus et al., 1993). It was also reported that the number of eggs spawned by a Pelodytes caucasicus Boulenger female changed with altitude, e.g., fewer eggs near sea level and more eggs in higher environments (Tuniev, 1989). ...
... In Pelodytes punctatus, which was reported to have rather rapid embryonic and larval development, the embryonic development until hatching took 4-14 days, depending on the ambient temperature, and metamorphosis was completed in approximately 70 days (Toxopeus et al., 1993). Also, metamorphosis was completed in 73 days for Rana pseudodalmatina in Golestan Province, Iran (Pesarakloo et al., 2015), 43-90 days for P. ridibundus in Anzali Lagoon, Iran (Mirzajani et al., 2006) and 80-120 days in France (Momeni and Zamatkesh, 2005). ...
We studied the development and morphology of different larval stages of Pelophylax bedriagae at two rearing temperatures (20 and 24°C). Eggs collected from a breeding site in south-western Iran. Diagnostic morphological characters are provided for Gosner (1960) larval stages 1-46. The larvae hatched about seven days after egg deposition. Principal diagnostic feature including the formation of the funnel-shaped oral disc became discernible about ten days after hatch at Gosner stage 21 and degenerated at Gosner stage 42. Larvae developed faster at higher temperatures. The largest body length of larval P. bedriagae measured about 54mm in 70 days after egg deposition. Based on our results, the longest metamorphosis time was observed on temperature (20°C) whilst the shortest metamorphosis time occurred on temperature (24°C). Compared with the majority of other Palearctic Anurans, it appears that embryonic and larval development is usually slow rapid in P. bedriagae.
... The northern parsley frog (Pelodytes punctatus) is a generalist anuran that shows a preference for open landscapes in Northwestern Europe, such as coastal dune areas or partially forested areas, avoiding dense woodlands (Toxopeus et al. 1993;Boyer and Dohogne 2008), although it depends especially on the existence of water bodies for its reproduction (Richter-Boix et al. 2007). The Aesculapian snake (Zamenis longissimus) prefers sunny forested habitats such as bushlands and deciduous woodlands, although it also uses open spaces for thermoregulation (Levièvre et al. 2010a, b). ...
Full-text available
The Meuse and its tributary valleys contain numerous Late Pleistocene cave sites that have yielded one of the largest collections of Neanderthal and Mousterian lithic industries in Europe. Today, it is an important north–south migratory corridor for flora and fauna, generating rich biotopes. The Quaternary collections of the Royal Belgian Institute of Natural Sciences (Brussels, Belgium) are here used to complement our knowledge of the successive herpetofaunal assemblages in Belgium during the last interglacial-glacial cycle (marine isotope stages 5 to 1). Herpetofauna from 18 caves are described for the first time. In total, 17 taxa (10 amphibians and seven reptiles) are identified, three of which correspond to their first fossil record for Belgium (Alytes obstetricans, Pelobates fuscus, and Hyla arborea). The thermophilic snake Zamenis longissimus is documented for the first time in the Holocene (Atlantic/Subboreal period) of Belgium. After marine isotope stage (MIS) 5, the Belgian herpetofauna was still reasonably diverse during MIS 3, but it seems to be represented only by the common frog Rana temporaria and a viper during MIS 2. Paleoenvironmental and paleoclimatic reconstructions are proposed for a selection of the chronologically best-constrained sites, using the quantified ecology method. More specifically, the late Magdalenian of the Trou de Chaleux is reconstructed as particularly cold and dry. The seasonal contrast reaches its maximum during this period. The quantitative parameters calculated in this study provide a new paleoecological context for understanding the conditions with which the successive human species had to cope in Northwestern Europe during the last interglacial-glacial cycle.
... According to our field observations, the metamorphosis was completed approximately 102 days after egg deposition, and body size at metamorphosis measured 10 mm. The embryonic and larval periods in anurans vary across between species and geographically within species in the region: Toxopeus et al. (1993) describe a study of Pelodytes punctatus from France (i.e., not Iran or elsewhere in Central Asia), so it doesn't make sense to cite it here in the context of "the region" (i.e., Central Asia). For example, the metamorphosis was completed in 73 days for Rana pseudodalmatina in Golestan Province, Iran (Pesarakloo et al. 2015), and 43-90 days for P. ridibundus in Anzali Lagoon, Iran (Mirzajani et al. 2006), but 80-120 days for another population of the latter species in France (Momeni & Zamatkesh 2005). ...
Full-text available
The life-history of an organism consists of its lifetime pattern of growth, development, storage, age, and reproduction. In this study, some life-history traits of Hyla savignyi were studied in populations from different parts of Iran. The microscopic and macroscopic analysis showed that testicular activity in H. savignyi is potentially continuous, reaching its peak level in April. Metamorphosis was completed in approximately 102 days after egg deposition, and body size at metamorphosis was 10 mm. Significant sexual size dimorphism was present in all populations, and a larger female asymptotic body size was observed (43.07 mm for females vs 41.16 mm for males). The adult survival rate (S) and life expectancy (ESP) were the same for both sexes (S = 0.73 and ESP = 4.2 years). Age and body size were positively correlated with each other for both females and males. Maximum longevity was recorded to be six years in both females and males, and ages of sexual maturity were estimated to be two or three years in breeding individuals. The adult sample age ranged from two to six years (mean age of females: 4.40±0.68 years; males: 3.63±0.13 years). Our data confirm the general patterns of body size variation and mean age in anurans and show that females are larger than males and live longer.
... Sanchiz, 2000, from southern Spain and southern Portugal, and P. punctatus (Daudin, 1802) ( Fig. 1). The distribution of the parsley frog P. punctatus ranges from central and eastern Spain, to France and NW Italy ( Toxopeus et al., 1993Guyétant, 1997). Peracca (1886) firstly cited this species in Italy. ...
Full-text available
In Italy, the parsley frog (Pelodytes punctatus) reaches the eastern limit of its distribution range along the Mediterranean coast in Liguria and in southern Piedmont. The status of the Italian populations was analysed on the basis of a complete survey of known breeding sites. Since 1993, the reproduction of P. punctatus has been observed in only 15 sites, several of which were discovered during the monitoring project. Spawning sites were mainly small temporary pools, small streams and artificial tanks in Mediterranean habitats. The number of breeding females was estimated indirectly counting egg strings both in spring and autumn, from 2000 to 2002. Populations appeared isolated and made up of an extremely low number of reproductive females (range 2-19, mean 9). In Italy. P. punctatus populations show a fragmented distribution and appear threatened mainly by the drying up of pools or habitat destruction. For each reproductive site, the conservation status was evaluated, and a general conservation strategy was proposed. Active management of breeding sites, with the maintenance and/or creation of small temporary water bodies should be planned. The collaboration of private landowners and local administrations was requested, and in one case, active management of a relevant breeding site obtained.
... Su abundancia se ha estimado en algunas poblaciones periféricas (Liguria y extremo noroeste de Francia; Toxopeus et al., 1993; Salvidio et al., 2004), oscilando entre las 2–46 hembras reproductoras por masa de agua. En algunas regiones de la península Ibérica muestra una ocupación casi total de los medios acuáticos disponibles (Ruhí et al., 2014) lo que sugiere que es una especie bien distribuida localmente. ...
... Salvador & García–París, 2001; 20. Salvador, 2005; 21. Toxopeus et al., 1993; * Experience of the authors. ...
Full-text available
Amphibians in the Region of Murcia (SE Iberian peninsula): conservation status and priority areas Anfibios en la Región de Murcia (SE península ibérica): estatus de conservación y áreas prioritarias.- Se ha analizado el estado de conservación de las especies de anfibios presentes en la región de Murcia en función de 10 variables relacionadas con la biología y distribución de dichas especies. Los resultados obtenidos muestran que las especies de anfibios expuestas al mayor riesgo de extinción en el área de estudio son aquéllas que presentan un desarrollo larvario prolongado y una distribución restringida. En función de esta clasificación de las especies, se propone un índice que permita evaluar las áreas cuya conservación es prioritaria. En la Región de Murcia, la mayor parte de estas áreas están localizadas en los principales sistemas montañosos y limitadas principalmente a la comarca nordoccidental del área de estudio. El solapamiento entre los Parques Regionales y las áreas propuestas de conservación prioritaria es sólo del 12%. El aislamiento actual de estas áreas hace necesario emprender programas de restauración del hábitat para garantizar su conexión.
Full-text available
The population dynamics of the crested newt, Triturus cristatus, in a newly created aquatic habitat in a dune area in northwestern France was studied over a six year period. After a rapid colonization of the pond in year 1, and a fast initial increase to reach 335 newts in year 5, the adult population size dropped dramatically to 16 in year 7. Variation in the adult population among years was largely due to variation in juvenile recruitment. In the longer term, the population stabilized at about 40 newts. Since the population has survived for five times the minimum generation time of the species, the colonization was judged to be a success. An estimated 50% of the juveniles joined the breeding population at age 2; those that did not breed by then spent the third year on land. The average annual survival rate for the juveniles was 0.22. For the adults survival was 0.49 and showed almost no fluctuations over time or with age. Given a short distance to disperse, the crested newt can be an opportunistic species.
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Diets of both species studied were basically composed of algae and detritus. For Pelodytes punctatus, other food types exhibited minor contributions to the diet. For Bufo bufo, phanerogams reached considerable proportions too and the frequency of animals may be considered noteworthy if related to other species in the area. Morphologically they seem to be both conditioned to bottom dwelling rather than to the use of water column.
Field studies were conducted on factor affecting embryo mortality in bullfrogs, Rana catesbeiana, in 1975 and 1976 at the E. S. George Reserve of the University of Michigan. Larger @V produced significantly larger clutches than smaller @V (6000 to >20,000). Older @V produced 2 clutches each year with 2nd clutches containing significantly fewer eggs than 1st clutches. Egg size appeared to be unrelated to @V size; however, 2nd clutches contained significantly smaller eggs than initial clutches for all @V @V. Embryo mortality depended on @V choice of oviposition sites. Such sites were controlled by territorial @M @M. Larger @M @M controlled oviposition sites that had significantly lower embryo mortality than the sites of smaller @M @M. Sources of embryo mortality included developmental abnormalities and predation. Choice of oviposition sites included: (a) advance of areas with high water temperatures (>32 degrees C) that result in increased developmental abnormalities and (b) preference for areas that increase embryo survival by increasing developmental rate and/or decreasing efficiency of predation on embryos by the leech. Macrobdella decora.
Introducción Este trabajo es consecuencia de otros dos (Martínez Rica, 1979a y 1979b) en los que se estudia la herpetofauna del Alto Aragón occi-dental desde el punto de vista de su distribu-ción espacial. Inicialmente se pretendió tan sólo ampliar los límites de la zona estudiada hasta englobar la totalidad de la cordillera Pire-naica. Paralelamente se pretendía mejorar las técnicas de análisis corológico, profundizando en sus aplicaciones y en su interpretación. Sin embargo, las primeras páginas manus-critas pronto revelaron que el proyecto era de-masiado ambicioso: el trabajo concluido habría alcanzado varios centenares de páginas, y exi-gido un tiempo y esfuerzo excesivos; pero el material acumulado era suficiente para dar ori-gen a un conjunto de trabajos parciales que cu-briesen el ámbito del previsto al principio; en-tre dichos trabajos pueden contarse un Atlas Herpetológico del Pirineo, sendos estudios so-bre la distribución espacial de anfibios y repti-les, una síntesis de los datos conocidos sobre los ciclos biológicos de las formas pirenaicas, estudios sobre la densidad de población de las distintas especies, correlación de las mismas * Centro pirenaico de Biología experimental. Apdo. 64. Jaca (Huesca) España.
The mating call of Pelodytes punctatus from Algarve (Southern Portugal) is composed of two multipulsed motives, "a" and "b", lasting about 200 ms. One "a" is followed by two, three or more "b"s giving a sucession of "a-b-b-...". The inner timing in pulse rate acceleration distinguishes each motive. We suggest that the Algarve population has its own dialect, which is different from those of Camargue and Liguria, whose mating calls are longer (about 300 and 400 ms) with a syntax of "a-b" pairs. Pulse rates and durations change with temperature.
Parts of the larval filter apparatus (ventral velum, branchial food traps, filter plates) were studied, using scanning electron microscopy. The primary species studied was Pelodytes punctatus, but Alytes obstetricans, Pelobates cultripes, Scaphiopus holbrooki, Telmatobius culeus, Hyla cinerea and Rana sphenocephala were also examined. Other data were taken from literature. Previous authors, in similar studies, maintained that variations in larval filter apparatus morphology supported the anuran suborders Archeo- and Neobatrachia. The present study concludes that the larval filter apparatus cannot be used to support any subordinal arrangement, but affirms its potential value at lower systematic levels. Pelobatoids tend to have modified filter apparatuses. Four types are recognizeable: 1) Pelodytes; 2) Scaphiopus; 3) Megophrys; 4)Pelobates, Leptobrachium, Oreolalax. Although other beaked Asian genera remain unstudied, these groups are enough to indicate that current pelobatoid systematics is erroneous. Pelodytes has the most primitive pelobatoid filter apparatus. This, the moderately derived larval chondrocranium and the peculiar mixture of certain primitive and derived character states in the adult frog (none shared with other pelobatoids), indicate a long independent phylogeny for Pelodytes. This in turn, supports recognition of a separate monogeneric family Pelodytidae.
The ovarian cycle in natterjack toads Bufo calamita from an island population with unpredictable breeding conditions was studied in an archipelago off the Swedish west coast. About 80% of the female population bred during spring and early summer, and the rest later in summer and early autumn. Time of breeding and female size (age) were not correlated. It was found that first growth phase (FGP) oocytes were recruited from oogonia mainly during early spring and late autumn, but that recruitment could occur at any time of the year. The FGP oocytes grew rapidly immediately after recruitment, and when transferred into second growth phase (SGP) oocytes. In between these two periods the FGP oocytes seemed to be in a resting stage. Females showed an asynchrony in ovarian developed. We found females with fully developed SGP oocytes, ready for ovulation, as well as females with ovaries in only an early vitellogenic growth phase at all times of the year. Females did not neccessarily ovulate as soon as the vitellogenic oocytes had reached full size. There were strong indications that some females only ovulated and laid a fraction of the egg mass in their first batch, and that they laid a second batch later in the season. This second batch was thought to originate from the same recruitment of oocytes as the first batch. There was a tendency for SGP oocytes to grow faster during summer than during spring. It was also concluded that SGP oocytes coulde be recruited all year around. Bimodal size frequency distribution patterns were found both among the FGP and the SGP oocytes; they were most pronounced among the latter, where they were found throughout the year.
The amphibian community of the Biological Reserve of Doñana (SW Spain) is composed of 10 species, their period of larval occurrence commonly taking place from autumn to early summer, although it may vary from year to year in relation to the flooding conditions of ponds. A segregation is observed according to temporal use of temporary ponds by larvae of different species. Pelobates cultripes and Discoglossus galganoi tadpoles occur in ponds during their whole persistence, from flooding to drying up. Hyla meridionalis, Triturus marmoratus and Triturus boscai larvae commonly exploit a shorter temporal range, appearing about two months later until early summer. Bufo bufo, Bufo calamita and normally also Rana perezi have the shortest larval periods, of about two months. Rana perezi is also characterized by its delay in temporal use of the ponds in comparison with the other species. The flexibility of the larval period season is considered an adaptation to the unpredictability of temporary ponds. Thus, under certain climatic conditions, the two first groups of species may occur in the same temporal range.
This is the first study to document in detail the satisfaction of Bradbury's four criteria for categorizing any anuran as a classical lekking species. The paternal care of male neotropical frogs, Ololygon rubra, consisted of minimal contributions of their genes. Males competed acoustically at traditional, defended, clustered sites (Fig. 1, Table 3) to attract gravid females, who paired with the males at these locations but took the amplectant males to oviposition sites away from the pairing sites. Individual males apparently did not control resources necessary for attracting females, because there were no correlations between male numbers and measured habitat variables, or between male numbers and oviposition sites. On chorusing nights, males always arrived at their display arenas before any females were observed. Females moved freely among clusters and males, before making their choices of mates. However, males employed other mate acquisition strategies that tended to undermine the initial female choices. The predictions that lekking species should have a relatively extended breeding season, a highly biased operational sex ratio (OSR), and an absence of male control of resources essential for female acquisition were also evaluated and corroborated. These frogs have two long breeding seasons encompassing a total of about 6 months (Fig. 2). There were strongly male biased nightly OSRs (Table 1), that contributed to high variance in male reproductive success (RS), but reduced indices of sexual selection, and a relatively low coefficient of variation (CV) of male RS (Table 5) compared to other amphibians. Thus, all of this evidence supports the conclusion that O. rubra in coastal Guyana uses a lek mating system.