Acta Herpetologica 10(1): 39-45, 2015

ISSN 1827-9635 (print) © Firenze University Press 
ISSN 1827-9643 (online) www.fupress.com/ah

DOI: 10.13128/Acta_Herpetol-15003

Into a box interiors: clutch size variation and resource allocation in the 
European pond turtle

Marco A.L. Zuffi1,*, Simonetta Citi2, Elena Foschi1, Francesca Marsiglia1, Eva Martelli1

1 Museum of Natural History, University of Pisa, Via Roma 79, I-56011 Calci (Pisa), Italy. Corresponding author. E-mail: marco.zuffi@
unipi.it
2 Department of Veterinary Clinic. University of Pisa, Viale delle Piagge, 2 I-56124 Pisa, Italy

Submitted on 2014, 26th September; revised on 2015, 25th January; accepted on 2015, 21st February  
Editor: Sandra Hochscheid

Abstract. In order to highlight the temporal dynamics of different stages of follicula distribution on reproductive 
output, we analysed the female size and the reproductive frequency of the European pond turtle, Emys orbicularis, 
using 191 ultrasonographic and 67 x-ray images (collected from 2000 to 2011 in two different localities of a coastal 
plain area of NorthWestern Italy). To compare digital image results we also used anatomical topography of autopsied 
females. Although reproductive females were significantly longer in one locality and larger in the second one, clutch 
size did not differ between localities. Two main clutches were produced during a year, with occasionally a third one. 
Shelled eggs were frequent in May, June and July, while follicula were present till August, with a decrease in follicular 
size especially in July and August. Despite the presence of a number of follicles in late summer and in autumn, a third 
expected clutch was only an exceptional event, differently from what happens in other sites of the species’ distribution 
range. The permanence of follicles after the last deposition is interpreted as a possible extra energy source during the 
very hot and dry summers of coastal central Italy and for the hibernating phase. 

Key words. European pond turtle, ultrasonography, x-rays; reproductive investment.

INTRODUCTION

Life history strategies represent the ways in which 
animals acquire and expend resources. The amount of 
energy gained with food and stored in fat bodies, liv-
er and muscles indicates the potentiality of maximum 
reproductive capacity of each individual. The ecologi-
cal consequences of energy storage have attracted much 
attention quite recently (Hom, 1988; Bonnet et al., 1998; 
Santos and Llorente, 2004). The amount of stored energy 
and its seasonal duration may play an important role in 
the reproduction of every organism. Furthermore, the 
patterns of the subsequent use of the amount of energy 
may represent important aspects of interspecific and 
intra-specific variation in life histories. In fact, differences 

between the endothermic and the ectothermic model of 
energy storage and maintenance are marked, such as in 
mammals versus reptiles (Else and Hulbert, 1981). Specif-
ically, oviparous reptiles capitalize on their food income 
in the same season of reproduction and utilize only 
endogenous energy stores (Congdon and Tinkle, 1982; 
Bonnet et al., 1998; Santos and Llorente, 2004). 

Pathways from energy income to fat storage may 
be resumed as food, digestion and assimilation in body 
reserves. Income breeders do not store lipids to any great 
extent. The process of the production of youngsters, 
involves a complex series of biochemical steps that cannot 
be avoided. The synthesis of vitellogenin macro-molecules 
involves a large amount of energy as well as their incorpo-
ration and deposition in the oocytes. Yolk deposition is a 



40 Marco A.L. Zuffi et alii

continuous process which requires stored substances, even 
from short-term storage, in order to moderate the discon-
tinuous effects of the activities of feeding and digesting. 
Thus, the physiological pathways leading from resource 
acquisition to yolk deposition are similar among taxa, the 
differences depending on the magnitude and schedule of 
body reserve storage before reproduction (Allen, 1976; 
Congdon and Tinkle, 1982; Bonnet et al., 1998).

The energy budget is primarily stored in the corpora 
lutea, subsequently used for follicular formation, ovula-
tion process and egg formation. From a series of multi-
ple follicles, females ovulate to produce shelled eggs. In 
chelonians multiple clutches represent the rule: it is the 
case in all marine turtles, in most terrestrial tortoises and 
freshwater turtles. Radiography to assess reproductive 
status, clutch size and clutch frequency has been used for 
many years in Chelonians (Gibbons and Greene, 1979; 
Andreu and Villamor, 1986; Zuffi et al., 1999; Servan and 
Roy, 2004; Bertolero and Marín, 2005). The ultrasono-

graphic technique instead has been applied only recently 
(Table 1). On the contrary, the post-reproductive period 
of Chelonians has received virtually no attention. This 
period could offer further information on the evolution 
of remnant follicular eggs of adult turtle and tortoise spe-
cies, from immediately after the last egg laying to the end 
of the active season, prior to wintering. This contribution 
is aimed at describing the occurrence and the seasonal 
variability of developed and undeveloped follicula, their 
size and their possible function, during and especially 
after the reproductive period, considering also the influ-
ence of body structure (e.g. shell size and shape).

As model species we selected the European pond tur-
tle (Emys orbicularis) as it is abundant in Europe (Pod-
loucky, 1997; Sillero et al., 2014), and in many Italian areas 
(Zuffi, 2000; Zuffi et al., 2011), it lays multiple clutches per 
year (e.g. Zuffi and Odetti, 1998; Fritz, 2003, and data revi-
sion herein), and its reproductive variation strongly corre-
lates to localities, habitat features and female size (Mitrus 

Table 1. Comparative source data (in chronological order) of ultrasonographic and radiographic techniques to assess reproductive status in 
Chelonians

Species Ultrasound n X-Ray n

Kinosternon subrubrum X 3 Gibbons and Greene, 1979
Deirochelys reticularia X 2 Gibbons and Greene, 1979
Sternotherus odoratus X 2 Gibbons and Greene, 1979
Chrysemys picta X 129 Congdon and Tinkle, 1982
Pseudemys scripta X 65 Congdon and Gibbons, 1983
Emydoidea blandingi X 90 Congdon et al., 1983
Chelydra serpentina, 
Chrysemys picta dorsalis
Deirochelys reticularia
Pseudemys concinna
Pseudemys floridana
Pseudemys scripta
Terrapene carolina
Clemmys marmorata
Gopherus polyphemus
Kinosternum subrubrum
Sternotherus odoratus
Trionyx ferox

X
X
X
X
X
X
X
X
X
X
X
X

4
1

13
1

11
88
8
2
1

19
9
1

Congdon and Gibbons, 1985
Congdon and Gibbons, 1985
Congdon and Gibbons, 1985
Congdon and Gibbons, 1985
Congdon and Gibbons, 1985
Congdon and Gibbons, 1985
Congdon and Gibbons, 1985
Congdon and Gibbons, 1985
Congdon and Gibbons, 1985
Congdon and Gibbons, 1985
Congdon and Gibbons, 1985
Congdon and Gibbons, 1985

Testudo graeca X 38 Andreu and Villamor, 1986
Mauremys leprosa X 27 Andreu and Villamor, 1986
Chrysemys picta X 17 Christens and Bider, 1987
Chelydra serpentina X 68 Congdon et al., 1987
Emydoidea blandingi X 280 Congdon and van Loben Sels, 1991
Emys orbicularis X 15 Zuffi et al., 1999
Emys orbicularis X 30 Servan and Roy, 2004 
Cuora amboinensis X 13 Haies and Kalb, 2010
Cuora flavomarginata X 24 X 24 Ting-Yu et al., 2011
Emys orbicularis X 191 X 66 Present research 



41Follicles and eggs of the fresh water turtle

and Zemanek, 1998; Zuffi et al., 1999, 2007; Kotenko, 2000; 
Zinenko, 2004). Despite it being among the species listed 
in the EU Habitat Directive and in several European Red 
Lists, it is much less studied than expected and should cer-
tainly be the object of further research.

MATERIALS AND METHODS

Sampled individuals were from San Rossore (average 
coordinate: 9 m asl, 43°42’51”N, 10°18’30”E) and from the 
US Army Camp Darby areas (10 m asl, average coordinate: 
43°38’03”N, 10°20’11”E), both in the Natural Regional park of 
“Migliarino San Rossore Massaciuccoli” (Pisa, Tuscany, central 
Italy) (Fig. 1). The two areas are separated by the Arno river, a 
natural barrier that has been intensively used by humans since 
the time of the Second World War, including the construction 
of houses, a touristic harbour and anchoring hundreds of boats 
along the river. We are confident that no exchange of individu-
als has occurred since then. The two areas are characterised by 
a mixed wood of pines and oaks, artificial canals, ponds and 
marshy areas, fully described elsewhere (Zuffi and Rovina, 2006; 
Zuffi et al., 2007). No data nor information is however avail-
able on animal movements in this area. Thus we considered two 
populations as independent. Wild individuals were captured 
by hand and with fishing nets, placed along borders of artifi-
cial canals and ponds, from 2000 to 2011. Adult females were 
marked individually with notches on the marginal scutes, as 
described in Stubbs et al. (1984) and Zuffi et al. (1999), in order 
to recognize them when recaptured and avoid any pseudorep-
lication in analyses. We examined 191 E. orbicularis galloitalica 
adult females (secondary sexual characters described in Zuffi 
et al., 1999), to assess adulthood features and body size varia-
tion. Carapace and plastron measurements, body mass record-
ing, individual marking or recognition took on average 10 
minutes. We processed each individual in the field and turtles 
were released immediately afterwards. During ovulation and the 
egg-laying period, that is from early-mid May to late July (see 
Zuffi et al., 2007, and references herein), we re-captured marked 
females and we assessed their reproductive condition using 
manual inguinal palpation and ultrasonography (respectively 
to detect follicles or eggs, and quantify oviductal and shelled 
eggs), and X-ray techniques to measure clutch size before lay-
ing (Gibbons and Greene, 1979; Zuffi et al., 1999, 2005). Data 
were also collected from several females during late July and 
August, a period when females were reported to reproduce rare-
ly or not reproduce at all (e.g. Mitrus and Zemanek, 1998; Zuffi 
and Odetti, 1998; Fritz, 2003). Ovulating and or checked adult 
females were brought to the vet lab and kept 24 hours at maxi-
mum in captivity. After ultrasonographic and x-ray analysis, the 
individuals were released. Clutch size was determined by X-ray 
techniques only. As a consequence, sample size of females bear-
ing follicular eggs differed from sample size of females bearing 
shelled eggs. Two autopsied preserved females (Corsica, 2 May 
1998, MSNT-1127 and 2 June 1998, MSNT-1128, Natural His-
tory Museum herpetological collection), belonging to the same 
subspecies (Fritz, 2003), were used to take direct images of the 

various statuses of developing follicula and of shelled eggs (Fig. 
2). Follicular and oviductal egg estimation of each female was 
obtained by summing (from ultrasonographic images) the visi-
ble eggs on the right side plus those visible on the left side, then 
dividing the results by two. Even if just one single ultrasono-
graphic image could represent most of the internal environ-
ment, we used both side images to build the average estimation, 
in order to minimize the risk of underestimating the whole 
follicular set. The reproductive phenology was considered as a 
whole, merging data of the two populations. 

We measured turtles with standard methods, follow-
ing Zuffi et al. (1999): variables considered were cara-
pace length and width, plastron length and width, cara-
pace height, tail length (from cloaca distal opening to 
tail tip), and body mass. Measurements were  ±  1 mm 
and mass  ±  1 g accuracy. A caliper and an electronic 
dynamometer were used for measurements. Biometric 
data of two sampling localities were analyzed for normal-
ity, then processed with the Student t-test. Ultrasound 
and x-ray data were analyzed between localities with the 
Mann-Whitney U test. Egg data were tested for normal-

Fig. 1. Sampling areas for Emys orbicularis in north-western coastal 
Tuscany. Empty ovals indicate female sampling areas.



42 Marco A.L. Zuffi et alii

ity, then processed with the non-parametric Kolmogorov-
Smirnov ranking test using month as factor; they were 
also analyzed for skewness and kurtosis (http://mvppro-
grams.com/help/mvpstats/distributions/SkewnessCritical-
Values) to detect any asymmetry of the distribution pat-
terns. Spearman correlation test was then applied in ana-
lyzing number of developing follicular eggs and month. 
Significance was selected at 0.05. Analyses were carried 
out with IBM SPSS 21.0.0 release. 

RESULTS

Considering body size of the sampled reproductive 
females and sampling areas, San Rossore females were 
larger than Camp Darby females in terms of carapace 
length and smaller than Camp Darby females as regards 
carapace width (SR carapace length: 136.9  ±  13.7cm, 
CD carapace length: 132.4  ±  11.3 cm; unequal variances, 
Student’s t88,224, 2.174, P  =  0.032; SR carapace width: 
95.3  ±  9.4 cm, CD carapace width: 98.8  ±  7.5 cm; une-
qual variances, Student’s t86,188, -2.447, P  =  0.016) with no 
differences in the other variables. 

Number of x-ray eggs did not differ between 
localities (San Rossore, 6.2  ±  1.1, n  =  48; Camp Dar-
by, 5.9  ±  1.2, n  =  18; Mann-Whitney U test  =  1.017, 
P  =  0.309). Ultrasound eggs were significantly different 
between localities (San Rossore, 5.3  ±  2.6, n  =  152; Camp 
Darby, 3.3  ±  1.5, n  =  39; Mann-Whitney U test  =  4.017, 
P  <  0.0001), while no difference was found in ultrasound 
egg size between localities (San Rossore, 11.7  ±  5.9, 
n  =  151; Camp Darby, 12.7  ±  5.5, n  =  39; Mann-Whitney 
U test = 1.096, P = 0.273). 

We found reproductive females with shelled eggs in 
May, June and July, with an average clutch size (x-ray) 
of 6.1  ±  1.1 eggs (n  =  66, range 2-9). Adult females with 
calcified eggs were found in May (n  =  9, 27%), in June 
(n  =  25, 67.6%) and in July (n  =  2, 5.4%). On the whole, 
developing follicular eggs were 4.9  ±  2.5 (n  =  191), with 
an average size of 11.8  ±  5.9 mm. Developing follicular 
eggs were 3.2  ±  1.9 in May (range 1-8, n  =  19, 9.5%), 
4.2  ±  1.9 in June (range 1-9, n  =  64, 33.7%), 5.4  ±  2.5 in 
July (range 0-16, n  =  77, 40.5%) and 6.1  ±  3.2 in August 
(range 1-11, n  =  31, 16.3%) (Table 2). The skewness 
was significant in May and July (P  <  0.05 and P  <  0.01, 
respectively). Difference of ultrasound eggs distribu-
tion among months was significant (rank Kolmogorov-
Smirnov test  =  24.708, 3 df, P  <  0.0001; Fig.  3). Devel-
oping follicular eggs were 19.5  ±  9.1 mm in May (range 
8-35.8 mm, n  =  19), 14.1  ±  6.1 mm in June (range 6.2-35 
mm, n  =  64; Fig.  4), 9.6  ±  2.3 mm in July (range 4.5-13.8 
mm, n  =  76) and 7.9  ±  2.3 mm in August (range 5.3-10.9 
mm, n  =  31). The skewness was significant only in June 
(P  <  0.01). Egg size differences among months was sig-
nificant (rank Kolmogorov-Smirnov test  =  63.983, 3 df, 
P < 0.0001; Fig. 5).

Fig. 2. Autopsied female Emys orbicularis, showing eggs (SE = 
shelled eggs) and follicula (FE = follicular eggs) distribution.

Table 2. Clutch laying temporal distribution versus follicle distribu-
tion. Values are expressed in %.

Distribution May June July August 

Clutch 27.0 67.7 5.4 0.0
Follicles 9.5 33.7 40.5 16.3

Fig. 3. Ultrasonographic distribution of developing follicula per 
month.



43Follicles and eggs of the fresh water turtle

The number of developing follicular eggs were posi-
tively correlated with month, while size of developing 
follicular eggs were negatively correlated with month 
(Spearman ρnumber, 0.345, P  <  0.0001, n  =  191; Spearman 
ρsize, -0.581, P < 0.0001, n = 190).

DISCUSSION

External shell morphology and size differences of 
reproductive females between localities are limited to 
carapace length and width. Our results agree only in part 
with previously published papers on the same popula-
tions, where differences were much more marked and 
significant for almost all variables (Zuffi et al., 2004, 
2007). Sample size of x-rayed females is however a lim-
ited fraction of the much larger adult female sample we 
have been monitoring for other purposes for more than 
25 years. It is evident that our sampled females are more 
similar in size and in reproductive output (they actually 
produced the same number of shelled-eggs; see results) as 
expected from previous results (see Zuffi et al., 2004).

In all the turtle species studied to date, the repro-
duction period lasts some months (Ernst et al., 1994). 
The constitutive elements of the clutch (e.g. follicles, ovi-
ductal eggs, corpora lutea) are present at the same time 
in the female body and characterize a reproductive fea-
ture of all Chelonians. The follicles show two distinct 
stages,  <  10 mm diameter and  >  10 mm diameter (Con-
gdon and Gibbons, 1985). As observed (Congdon and 
Tinkle, 1982), the presence of discrete classes of enlarged 
follicles shows evidence of multiple clutches. In addition, 

we were also able to assess the presence of discrete class-
es of enlarged follicles. 

In our study area adult females monitored in late 
summer bear a large number of follicles, especially in 
July. Follicle diameters range on average from 8 to 10 
mm, as is the case in preovulatory females. In July we 
recorded only two reproducing females (with shelled 
eggs), while in no other cases (using manual palpation, 
ultrasonography, or radiography) did we have any evi-
dence of a third clutch. A third reproduction is therefore 
particularly rare, if not exceptional, in this area. In fact, 
from previous ecological research, a maximum of two 
clutches was found in Emys orbicularis (Zuffi and Odetti, 
1998; Zuffi et al., 1999), and a third deposition was only 
hypothesized. However, three or even more depositions 
have been recorded in other parts of the species’ range 
(see revision in Fritz, 2003).

Interestingly, even if not surprisingly, the number 
of undeveloping follicles decreases after the last repro-
ductive period (i.e. July, August). Reasonable questions 
are i) do late summer follicles have a function, and if so, 
which is it? and ii) what does this extra amount of energy 
reserve represent? Do small follicles simply represent the 
extra amount of undeveloped eggs? 

In all probability, during the post reproductive 
phase, follicula that have not been used in reproduction 
may indicate the start of an absorbing process, and pri-
or to estivation during hot summers in dry canals and 
ponds (Naulleau, 1991) they may represent an energy 
reserve to compensate for metabolic demand (Hutton et 
al., 1960; Huey, 1982). Alternatively, the unused follicles 

Fig. 4. Ultrasonographic image of a June female with different stag-
es of follicula (on the left: developing follicles; on the right: trans-
verse image of a shelled egg).

Fig. 5. Distribution of size of developing follicula per month deter-
mined through ultrasonography.



44 Marco A.L. Zuffi et alii

may remain inactive (not enlarging, not being absorbed) 
for the last part of the season (and of the year) and will 
contribute to the next year’s clutch (Congdon and Tin-
kle, 1982).

In the painted turtle, Chrysemys picta, it has been 
found that each female shows three groups of follicles, 
with different developing stages, suggesting a three year 
cycle to complete the potential maximum reproductive 
output (Christiansen and Moll, 1973; Callard et al., 1978). 
As a member of the Emydidae family, Emys orbicularis 
could reasonably be expected to follow the same pattern 
recorded in North-American species. On the contrary, 
our ultrasonographic (and x-ray) data which are, as far 
as we are aware, the only available dataset for the species, 
seem to contradict the patterns found elsewhere, suggest-
ing that the reproductive cycle may likely be completed 
within one year or at maximum in two years (many fol-
licles of a smaller size in August, see Figs. 4 and 5). How-
ever, it remains unclear which pattern follicles do follow 
in autumn (September-November), prior to wintering. 
Keller et al. (1998) found that in south western Spain, the 
European pond turtle (Emys orbicularis occidentalis) lays 
multiple clutches regularly, especially during wet sum-
mers (up to five clutches in one year), suggesting how 
abundant rains enable turtles to reproduce frequently. 
However, in other parts of the species’ distribution range, 
where multiple clutches were also recorded (Fritz, 2003), 
climatic data and turtle reproductive patterns were not 
studied or available data are still scarce or anecdotal (see 
Rogner, 2009). Thus, it is not simple to shed light on the 
biological and ecological reproductive model of the Euro-
pean pond turtle, Emys orbicularis, which appears to be 
highly variable, likely depending on site climatic condi-
tions, food and water abundance and on female size. 

Forthcoming research should cover analysis of any 
adult preserved museum specimens captured in autumn 
to verify the presence and the developmental stage of fol-
licula and in vivo study of the gonadal status of adult post 
reproductive females. 

ACKNOWLEDGEMENTS 

We thank collaborators and students that helped 
in the field: F. Di Benedetto, M.E. Fabbri, M. Giusti, 
M. Marconcini, F. Odetti, L. Rovina, A. Teti. Ministero 
dell’Ambiente e della Tutela del Territorio provided per-
missions to M.A.L.Z. (DPN/IID/2005/28177 7/11/2005; 
DPN-2007-0009336, 3/04/2007) to capture, handle and 
measure turtles; permissions to enter Natural Park Migli-
arino San Rossore Massaciuccoli was given to M.A.L.Z. 
(2232/9-5.1 on 26/02/2001; 2770/7-2.1 on 23/03/2005; 
8057/7-2.1 on 04/08/2005; 3739/7-2.1 on 7/04/2006). 

Chris Powell (International, Pisa) revised the English ver-
sion. No one of the authors has any conflict of interest to 
declare. Finally, many thanks to Sandra Hochscheid and 
Martin Bona for their precious suggestions for revision 
and comments to the submitted ms.

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	Acta Herpetologica
	Vol. 10, n. 1 - June 2015
	Firenze University Press
	Obituary: Valery K. Eremchenko (1949-2014)
	Leo J. Borkin1, Tatjana Dujsebayeva2, Roberto Sindaco3, Matthias Stöck4
	Haplotype variation in founders of the Mauremys annamensis population kept in European Zoos 
	Barbora Somerová1, Ivan Rehák2,*, Petr Velenský2, Klára Palupčíková1, Tomáš Protiva1, Daniel Frynta1
	Reproductive ecology of Sichuan digging frogs (Microhylidae: Kaloula rugifera)
	Wei Chen1,*, Lina Ren2, Dujuan He2, Ying Wang2, David Pike3
	Toxic effects of carbaryl on the histology of testes of Bufotes variabilis (Anura: Bufonidae)
	Özlem Çakici
	Basal frequency of micronuclei and hematological parameters in the Side-necked Turtle, Phrynops hilarii (Duméril & Bibron, 1835)
	María A. Latorre 1,2,*,#; Evelyn C. López González1,2, #; Pablo A. Siroski1,2,3; Gisela L. Poletta1,2,4
	Into a box interiors: clutch size variation and resource allocation in the European pond turtle
	Marco. A.L. Zuffi1,*, Simonetta Citi2, Elena Foschi1, Francesca Marsiglia1, Eva Martelli1
	Where to “Rock”? Choice of retreat sites by a gecko in a semi-arid habitat
	Andreia Penado1,2, Ricardo Rocha3,4,*, Marta Sampaio3, Vanessa Gil3, Bruno M. Carreira3, Rui Rebelo3
	Age structure, growth and longevity in the common toad, Rhinella arenarum, from Argentina 
	Clarisa de L. Bionda1,2,*, Silvia Kost 4, Nancy E. Salas1, Rafael C. Lajmanovich3, Ulrich Sinsch4, Adolfo L. Martino1
	On a putative type specimen of Pleurodema bibroni Tschudi, 1838 from Chile (Anura: Leptodactylidae)
	Daiana Paola Ferraro
	Re-description of the external morphology of Phyllomedusa iheringii Boulenger, 1885 larvae (Anura: Hylidae), with comments on the external morphology of tadpoles of the P. burmeisteri group
	Samanta Iop¹, Victor Mendes Lipinski¹, Bruno Madalozzo¹, Franciele Pereira Maragno¹, Sonia Zanini Cechin¹, Tiago Gomes Dos Santos²
	Book Review: 
	Harold Heatwole, John W. Wilkinson (Eds). Amphibians Biology. Volume 11 - Status of conservation and decline of Amphibians. Eastern Hemisphere. Part 4 . Southern Europe and Turkey
	Sebastiano Salvidio
	Book Review: 
	Antonio Romano. Atlante degli anfibi del Parco Nazionale del Cilento Vallo di Diano e Alburni - Distribuzione, biologia, ecologia e conservazione
	Sebastiano Salvidio
	ACTA HERPETOLOGICA
	Journal of the Societas Herpetologica Italica