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The Italian wall lizard, Podarcis siculus, along the Tuscanian coast of central Italy: biometrical features and phenotypic patterns M.A.L. Zuffi, V. Casu & S. Marino HERPETOLOGICAL JOURNAL 22: 207 212, 2012 Museum Natural History and Territory, University of Pisa, Via Roma 79, I-56011 Calci, Italy The Italian wall lizard, Podarcis siculus, has a wide distribution. However, information on several aspects of its ecology and biology are scarce, and relate mainly to insular populations. This paper describes the main morphological features of 123 individuals along a geographical gradient (five localities) in northwestern Tuscany (central Italy). Our results show a strong sexual dimorphism in most of the considered parameters, high geographic variation, low interaction between sex and locality and a similar distribution of external parasite load and tail autotomy between the sexes. Key words: biometry, geographic variation, Italian wall lizard, Podarcis siculus INTRODUCTION The Italian wall lizard, Podarcis siculus, is among the commonest reptile species of the Italian peninsula. It is distributed from north of the Apennines throughout central and southern Italy, from coastal to hilly areas, reaching high altitudes in Sicily (Corti, 2006; Corti et al., 2010). Based on the EU Habitats Directive and the IUCN red list of the Mediterranean reptile fauna (Crnobrnja-Isailovic et al., 2008), the Italian wall lizard receives particular conservation attention. The available information on the species biology is however often rather descriptive (e.g., atlases: Henle & Klaver, 1986; Corti, 2006) or based on small sample size (Lo Cascio & Corti, 2008). Recent further studies on this species biology however suggest that P. siculus is a suitable model organism to study, for example, morphological and functional patterns of adaptive responses to habitat change (Bruner & Costantini, 2007; Herrel et al., 2008; Fulgione et al., 2008; Biaggini et al., 2009). Knowledge about several P. siculus life-history traits is still scarce (see Corti et al., 2010 and literature therein), as are comparisons among populations (Lanza et al., 1993: meristic characters; Herrel et al., 2008: functional morphology; Biaggini et al., 2009: ecology and behaviour). Inter-specific comparisons within the genus Podarcis are mainly devoted to diet and the study of herbivory in an insular context (Perez-Mellado & Corti, 1993; Perez- Mellado et al., 2000). It would be desirable to investigate how P. siculus performs in natural versus anthropogenic habitats (Amo et al., 2006), which physiological responses can be recorded (Davis et al., 2008; French et al., 2008) and how it adapts its morphology to habitat characteristics and environmental change (Herrel et al., 2008). At present we ignore the degree and frequency of adaptive plasticity in P. siculus, and multiple comparisons and experimental analyses are needed (see Bombi et al., 2009). Correspondence: M.A.L. Zuffi; Museum Natural History and Territory, University of Pisa, Via Roma 79, I-56011 Calci, Italy; E-mail: marcoz@museo.unipi.it 207 This paper examines the extent of morphological (and likely functional) variation of P. siculus in central Italy. It aims at i) verifying patterns of body size variation at a local scale, ii) investigating the degree of sexual dimorphism among different areas, and iii) documenting the presence of external parasites. MATERIALS AND METHODS Study areas We studied four localities from the south of Viareggio (province of Lucca) to the south of Pisa (a 23 km North- South transect along the coast of Tuscany), and a fifth locality 15 km east of Pisa, in the fields around the Museum of Natural History of the University of Pisa. Habitats at the study sites are represented by sandy dunes, wooded areas and uncultivated fields. Altitudes range from a few metres to about 50 m above sea level (Table 1). Fig. 1. Sampling areas in north-western Tuscany (Tyrrhenian Sea) (locality dots in white)

M.A.L Zuffi et al. Table 1. Sampling sites for Podarcis siculus in northwestern Tuscany Study area Habitat Distance from the sea (km) Latitude Longitude Altitude (m) Human presence Lecciona dunal 0.2 43 50 10 14 0 YES Cascine Vecchie uncultivated fields and ruins 5 43 43 10 20 2 YES Gombo retrodunal 0.1 43 42 10 16 0 NO Calci Lamone uncultivated fields and dry walls uncultivated fields and dry walls 20 43 43 10 31 46 YES 2 43 39 10 18 0 YES Sampling We captured lizards with a noose on a stick or by hand (i.e. when turning up stones and barks). Sampling occurred throughout the day, from May to August 2007 and from March to September 2009. We considered lizards to be adult at a minimum snout to vent length (SVL) of 51.7 mm (males) and 49 mm (females, see Henle & Klaver, 1986). Other age classes (i.e., subadults, juveniles, newborns) were not considered. We took standard measurements of body size and head dimensions: head length (snout tip to pileus), head width, head height at the widest and highest point correspondingly (Kaliontzopoulou et al., 2007), maxilla length (from snout tip to the distal portion of the maxilla articular), inter-orbital distance (between the median point of the external margin of the supraoculars), internasal (between the inner margins of nostrils), distance between eye and nostril (from the anterior part of the eye to the posterior nostril margin) and eye diameter. We also measured SVL and tail length, and recorded tail status (as entire, damaged or regenerated) and body mass. We used a centesimal calliper and an electronic balance to record the above variables. Values were expressed as mm±1 SD and g±1 SD, with an accuracy of ±0.5 mm and 0.5 g respectively. We took dorsal, lateral and ventral photographs of all captured lizards (head and abdominal region) to detect the presence of external parasites. Statistical analyses Normality of data (sexes pooled together) was tested prior to each analysis (Kolmogorov-Smirnov test, all with P>0.05). Body mass of males (7.384±2.19 g, n=32) and females (4.682±1.34 g, n=33) with entire tails was comparable to males (7.585±1.86 g, n=34) and females (4.848±1.06 g, n=21) with regenerated tail (Student t-test, male=-0.402, df=64, P=0.689; Student t-test, female=-0.478, df=52, P=0.635). Thus, tail status did not affect body mass estimation and individuals were pooled for further analyses. We compared body mass, head length, maxilla length, eye diameter, nostril-eye distance, internasal and inter-orbital distances as dependent variables separately for each sex using t-tests and Mann-Whitney U tests (depending on normality of data). A multivariate General Linear Model (GLM, multi-way ANOVA) was used to test for sexual and/or locality effects with SVL as covariate, and sex and capture locality as factors between sexes in each sampling locality. We excluded the individuals from Calci, because we had only three females from that site. The distribution of tail status (entire, damaged, regenerated) was examined using Mann-Whitney U tests. Body condition index, calculated as body mass divided by SVL, was arcsine transformed, tested for normality and analysed with parametric statistics (GLM, univariate ANOVA, with sex and locality as independent factors and as interacting variables). The ratios of head width/ head length and head height/head length were tested for differences among localities and between sexes using arcsine transformed values (excluding the Calci sample). Finally, we performed a GLM ANCOVA with sex as factor, latitude and longitude as covariates, considering the interaction sex*latitude and sex*longitude. We used SPSS v.13.0 for all statistical analyses, set α at 0.05, and all tests were two-tailed. RESULTS We captured 123 adult P. siculus, including 68 males and 55 females. Normality was reached in all variables except head width and head height (Z=1.484, P=0.024 and Z=1.372, P=0.046 respectively). Males were longer, heavier and larger in all considered parameters (Student Fig. 2. Head length variation between sexes and among 208

Biology and Ecology of Podarcis siculus Table 2. Biometrical features of adult Podarcis siculus from northwestern Tuscany. Body mass in g, other variables in mm; for each locality: sample size; mean±1sd). Variable Sex Lecciona C.ne Vecchie Gombo Calci Lamone body mass male 26; 7.6±1.9 16; 7.7±1.8 12; 7.8±1.9 8; 5.1±0.8 6; 8.9±2.4 female 22; 4.7±1.4 12; 5.1±1.0 13; 4.2±1.1 3; 4.8±1.5 5; 5.6±0.3 SVL male 26; 65.4±6 16; 67.6±5.8 12; 68.9±5.6 8; 60.0±1.9 6; 69.4±5.9 female 22; 58.6±5.3 12; 61.9±4.5 13; 57.8±5.2 3; 54.7±3.0 5; 64.7±1.0 tail length male 26; 118.2±25 16;110.6±30.9 12; 116.0±30.0 8; 78.7±20.3 6; 121.5±34.7 female 22; 93.3±23 12; 92.2±39.9 13; 102.2±15.4 3; 99.3±16.5 5; 102.4±16.4 head length male 26; 15.6±2.1 16; 17.0±1.5 12; 17.5±1.5 8; 15.1±0.6 6; 17.8 ± 1.6 female 22; 12.8±1.2 12; 13.7±1.1 13; 13.2±0.9 3; 12.8±0.1 5; 14.3±0.3 head width male 26; 9.4±1.1 16; 10.0±0.9 12; 10.1±1.1 8; 8.9±0.3 6; 10.4±1.0 female 22;7.8±0.5 12; 8.1±0.4 13; 7.8±0.6 3; 7.8±0.2 5; 8.7±0.3 head height male 26; 8.0±0.9 16; 8.±1.0 12; 8.5±1.0 8; 7.4±0.4 6; 8.6±1.0 female 22; 6.5±0.5 12; 6.6±0.5 13; 6.5±0.7 3; 6.4±0.2 5; 6.9±0.3 nostril eye male 26; 4.6±0.4 16; 4.5±0.5 12; 4.8±0.4 8; 4.1±0.3 6; 4.8±0.4 female 22; 4.2±0.4 12; 3.7± 0.4 13; 3.8±0.3 3; 3.5±0.1 5; 3.8±0.2 eye diameter male 26; 3.4±1.1 16; 4.2±0.4 12; 4.0±0.4 8; 3.8±0.3 6; 4.8±0.7 female 22; 2.6±0.8 12; 3.4±0.3 13; 3.4±0.3 3; 3.4±0.4 5; 3.6±0.3 inter-nasal male 26; 2.1±0.3 16; 2.2±0.3 12; 2.4±0.3 8; 1.9±0.1 6; 2.3±0.3 female 22; 1.7±0.2 12; 1.8±0.2 13; 1.8±0.2 3; 1.8±0.1 5; 1.9±0.1 inter-orbital male 26; 6.2±0.5 16; 6.3±0.5 12; 6.4±0.5 8; 5.6±0.4 6; 6.5±0.6 female 22; 5.1±1.2 12; 5.5±0.3 13; 5.2±0.3 3; 5.1±0.3 5; 5.6±0.1 maxilla male 26; 17.9±2.1 16; 18.7±1.3 12; 19.4±1.7 8; 16.9±0.6 6; 19.2±2.3 female 22; 14.3±1.8 12; 15.3±0.8 13; 14.5±0.9 3; 14.4±03 5; 16.3±0.2 t-tests with P<0.005 to P<0.0001 on the whole data set; Table 2). Head width and head height were also significantly larger in males (U=-8.055 and U=-8.087 respectively, both with P<0.0001). A general linear model with SVL as a covariate and sex and locality as fixed factors, including the interactions sex*locality and sex*svl, showed that all variables were highly correlated with SVL (P<0.0001 in all cases). The effect of sex after taking SVL into account was only significant for head length (P=0.032; Fig. 2) and nostrileye distance (P=0.027; Fig. 3). The effect of locality was significant for all variables except inter-orbital and maxilla (P=0.995 and P=0.06, respectively). Sex and locality interacted significantly only for body mass (P=0.007) and nostril-eye distance (P=0.038). Sex and SVL interacted significantly for all variables (P ranging from 0.025 to 0.002) with the exception of eye diameter (P=0.454) and inter-orbital distance (P=0.998). Head width/head length and head height/head length ratios did not vary between sexes and were not affected by sex*locality, but significantly differed among localities (F=4.331, df=3, P=0.006 and F=5.311, df=3, P=0.002, respectively; Figs. 4 and 5). Head height/head width ratios did not show any variation in the model. After arcsine transformation of the ratio nostril-eye distance/ head length and tested with a GLM analysis, we found locality effects (F=14.996, df=3, P<0.0001) and SVL covariation (F=23.061, df=1, P<0.0001), but no effects of sex or sex*locality. Fig. 3. Nostril-eye distance between sexes and among Fig. 4. Head width/head length variation among 209

M.A.L Zuffi et al. Fig. 5. Head height/head length distribution among Sixty-five adults (32 males and 33 females) had undamaged tails, while three had recently damaged tails and 55 (34 males and 21 females) had regenerated tails. Excluding individuals with recently damaged tails, tail status was not affected by sex (U=-1.375, P=0.169) or locality (Median test=2.090, df=4, P=0.719). The Gombo locality was characterized by a high proportion of lizards with undamaged tails (16 undamaged and 9 regenerated tails). From images taken from 94 lizards (49 males, 45 females), the proportion of lizards parasitized by ticks was similar between sexes (28.57% in males and 35.55% in females). Similarly, no correlation was found among locality, sex, body size, tail status and the presence of external parasites (detailed data not shown). The body condition index showed a marked sexual dimorphism, with males having significantly higher values (F=82.753, df=1, P<0.0001). There were no significant effects due to locality (F=1.496, df=3, P=0.22), nor any interaction between sex and locality (F=0.356, df=3, P=0.785) (Fig. 6). A relationship close to significance was found with latitude (Ρ=-0.949, df=4, P=0.051) suggesting a possible geographical cline in body status. There was a marked latitudinal effect especially on head size and a significant sex*latitude interaction on nostril-eye distance (corrected models, df=5, P Fig. 6. Body condition index (bm/svl) in Podarcis siculus (males in dark grey, ranging from 0.0025 to 0.0001, see Table 3). Longitude significantly affected only one variable (nostril-eye, F=5.534, P=0.002), without any interaction with sex. DISCUSSION Adult Italian wall lizards display strong sexual differences, a pattern well known in lizards (Henle & Klaver, 1986; Herrel et al., 2008). Our results revealed sexual size dimorphism (SSD) in head size, as already found in other Podarcis and Lacerta species (Olsson et al., 2002; Rubolini et al., 2006; Bruner & Costantini, 2007; Kaliontzopoulou et al., 2007). However, in Podarcis the variation of SSD among localities has been rarely tested (but see Kaliontzopoulou et al., 2007; Herrel et al., 2008). Extensive analyses on the evolution of SSD, its proximal causes and possible adaptive hypotheses have been recently discussed (Watkins, 1996; McBrayer, 2004; Bruner et al., 2005; Johnson et al., 2005). Our results clearly indicate a general pattern of covariation of all traits due to the influence of SVL, a strong sexual differentiation and a significant interaction of sex*svl, thus suggesting differential allometric patterns between sexes. Geographical variation is significant for many parameters, mainly along a latitudinal cline, but we cannot Table 3. Geographical effect on body size features of Podarcis siculus from northwestern Tuscany. Covariate dependent variable F df P latitude head length 7.579 1 0.007 head width/head length 5.452 1 0.021 eye diameter 11.812 1 0.001 internarial 10.397 1 0.002 maxilla length 4.105 1 0.045 longitude nostril-eye 5.534 1 0.020 sex*latitude nostril-eye 6.138 1 0.015 210

Biology and Ecology of Podarcis siculus deduce what could have generated the results we recorded. The whole organismal variation should be furthermore studied in depth (McBrayer, 2004; Bruner et al., 2005; Herrel et al., 2008, 2009). We also found that locality and sex interacted significantly only on head length and on distance between nostril openings and the anterior margin of the eye. These different patterns of head features likely relate to a different size of pre-maxillary and maxillary bones, the corresponding anatomical parts. Tail status patterns suggest that disturbed and/or attacked individuals, divided per sex, are likely in the same percentage across localities. Tail autotomy, usually induced by predation attempts or environmental, human dependent stress (Amo et al., 2006; French et al., 2008), is shared between sexes at similar frequency. Not surprisingly, the highest percentage of intact tails was observed in an undisturbed area (see Table 1). It is, however, important to underline that direct measures or indirect interactions among environmental features (i.e., vegetation coverage, food availability) and biological characteristics of the species (i.e., male-male fights, nesting habitat selection) remained unrecorded, preventing a hypothesis-driven analysis (e.g. Sacchi et al., 2009). Parasite load has been shown to influence population biology and ecology, ranging from the change of haematocrit formula and favouring the occurrence of haematoparasites to alteration of reproductive frequency and fitness or displacement performance (Davis et al., 2008; Roca & Galdón, 2010). Nevertheless, we are not able to speculate on possible effects of parasites on the sampled lizards. The ratio between SVL and body mass was not affected by any measured parameters. Given the fact that comparative information on P. siculus is scarce (see Biaggini et al., 2009; Corti et al., 2010), further research from ecological and functional perspectives as well as on reproductive and behavioural patterns is desirable (Olsson et al., 2002; Fulgione et al., 2008; Sacchi et al., 2009). ACKNOWLEDGEMENTS We would like to acknowledge the Director, Parco Regionale Migliarino S. Rossore Massaciuccoli, for having given us permission to enter protected areas. Special thanks are due to Antigoni Kaliontzopoulou, and to an anonymous reviewer for comments on previous drafts. Robert Jehle greatly improved the editing and grammar of this manuscript. REFERENCES Amo, L., López, P. & Martín, J. (2006). Nature-based tourism as a form of predation risk affects body condition and health state of Podarcis muralis lizard. Biological Conservation 131, 402 409. Biaggini, M., Berti, R. & Corti, C. (2009). Different habitats, different pressures? 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