versão impressa ISSN 1870-3453
Rev. Mex. Biodiv. vol.79 no.2 México Dez. 2008
Comparative diet of three sympatric Sceloporus in the semiarid Zapotitlan Valley, Mexico
Comparación de la dieta de tres especies simpátridas de Sceloporus en el valle semiárido de Zapotitlán, México
Víctor Hugo SerranoCardozo1, 2*, Julio A. LemosEspinal2 and Geoffrey R. Smith3
1 Colección Herpetológica y Laboratorio de Biología Reproductiva de Vertebrados, Escuela de Biología, Grupo de Estudios en Biodiversidad, Universidad Industrial de Santander, AA 678, Bucaramanga, Colombia.
2 Laboratorio de Ecología, Unidad de Biología, Tecnología y Prototipos, Facultad de Estudios Superiores Iztacala, Universidad Nacional Autónoma de México, Los Reyes Iztacala 54090, Tlalnepantla, Estado de México, Mexico.
3 Department of Biology, Denison University, Granville, Ohio 43023 USA.
Recibido: 21 febrero 2008
Aceptado: 17 abril 2008
Ecology, morphology, and phylogeny contribute to the organization of lizard assemblages; however, the number of lizard assemblages for which detailed knowledge of closely related sympatric species is available is limited. We studied the diet of 3 sympatric species of lizards (Sceloporus gadoviae, S. horridus, and S. jalapae) from arid tropical scrub forest in Puebla, Mexico. These species prey primarily on arthropods, mostly termites, ants, and beetles. Spring and summer rains caused an increase in available prey biomass. However, lizards continued using the same resources throughout the study. These 3 species of Sceloporus are similar in their diet, especially the smaller bodied species, S. gadoviae and S. jalapae. Termites are a very important food for the 3 species throughout the year and are a major resource during the rainy season, which is not consistent with the hypothesis that many lizards eat termites only in the dry season.
Key words: diet, Sceloporus gadovieae, S. horridus, S. jalapae, Zapotitlán.
La ecología, morfología y la filogenia contribuyen a la organización de los ensambles de lagartijas. Sin embargo, son pocos los estudios detallados sobre la organización de estos ensambles y más aún, con especies simpátridas. Estudiamos la dieta, reproducción y dimorfismo sexual de 3 especies simpátridas de lagartijas (Sceloporus gadoviae, S. horridus, and S. jalapae) de un matorral árido tropical en Puebla, México. Estas especies se alimentaron de artrópodos; principalmente de termitas, hormigas y escarabajos. Las lluvias de primavera y verano causaron un incremento en la biomasa de presas; sin embargo, las lagartijas continuaron usando los mismos recursos. Las lagartijas fueron especialistas consumiendo presas en relación a su abundancia. Las 3 especies fueron similares en su dieta, especialmente las especies pequeñas S. gadoviae y S. jalapae. Las termitas son un importante recurso para estas 3 especies durante el todo año y la principal fuente alimenticia en la estación lluviosa, lo cual no es consistente con la hipótesis de que muchas lagartijas comen termitas solamente en la estación seca.
Palabras clave: dieta, Sceloporus gadovieae, S. horridus, S. jalapae, Zapotitlán.
Vitt and Pianka (2005) provided strong evidence for dramatic historical effects on contemporary ecological community structure of lizards, based on an unusually broadly sampled, ancient, and worldwide adaptive radiation (see also Losos, 1994; Vitt et al., 1999; Mesquita et al., 2006). Using phylogenies of lizards to reconstruct the evolutionary history of the included taxa and mean species body size as a covariate, these authors suggest that the early history of squamate reptiles appears to have played a profound role in determining lizard diets and accounts for a large portion of putative ''niche partitioning'' observed in phylogenetically diverse lizard assemblages throughout the world (Gainsbury and Colli, 2003; Vitt and Pianka, 2005). However, it appears that local selective pressures have been very important in some lizard assemblages, even more than historical factors (e.g. Melville et al., 2006). The exploration of the relationships between historic and contemporary factors in structuring ecological communities, and future progress will depend in part on a wider range of empirical studies (Greene, 2005).
Ecology, morphology, and phylogeny contribute to the organization of lizard assemblages (Toft, 1985; Vitt and Pianka, 2005). Closer examination of ecological variation within taxa (e.g. family) on a broad geographic scale and comparisons among many communities in a historical context are needed to begin to understand the relative importance of phylogeny and local species interactions in structuring lizard assemblages (Vitt and Zani, 1996). Morphology in particular, which often reflects phylogeny, appears tied to numerous aspects of the ecology of lizards including prey and habitat use (Vitt and Zani, 1996). Previous studies on lizard assemblages have suggested that they can be structured with respect to microhabitat or habitat use (e.g. Vitt et al., 1999; James and M'Closkey, 2002; D'Cruze and Stafford, 2006; Attum et al., 2007; Garcíade la Peña et al., 2007a), diet (Vitt and Zani, 1998a, b; Gainsbury and Colli, 2003; D'Cruze and Stafford, 2006), or activity periods (Fuentes, 1976; Creusere and Whitford, 1982; Garcíade la Peña et al., 2007a, b; Rouag et al., 2007).
Relatively little detailed information is known about the biology and ecology of many lizards in Mexico (LemosEspinal et al., 2003), especially from the tropical dry forest regions. Thus, conclusions regarding the ecology and life history characteristics of lizards from such habitats will not be known until considerably more data become available. To put existing data in a broader geographic and taxonomic context and to understand the combined influence of environment and history on lizards better, data describing patterns of species occurring sympatrically as well as closely related species living in different habitats are needed (Watling et al., 2005). Therefore, the goal of this paper is to present data that describe the diet of 3 sympatric species of lizards (genus Sceloporus) from the relatively understudied tropical dry forest of Mexico.
Materials and methods
The study was carried out at Valle de Zapotitlán de las Salinas, Puebla, Mexico. The area is located in the TehuacánCuicatlán Valley system, located in the mountainous region of southeastern Puebla (18°20'N, 97°20'W; elevation 1 450 1 600 m), close to the northeastern limits of the state of Oaxaca. The climate is dry with a rainy season occurring between May and August (sometimes extending to September). Total annual precipitation is ca. 300350 mm, and mean annual temperature is ca. 20°C (ValienteBanuet, 1991). The major vegetation associations, with no clear ecotones in many parts, are: thorny scrub or matorral espinoso (with Acacia cochliacantha, Cercidium praecox, Ipomoea pauciflora, Mimosa luisiana, Prosopis laevigata), tetechera (dominated by columnar cacti, Cephalocereus hoppenstedtii and Neobuxbaumia tetetzo), cardonal (dominated by cacti, Cephalocereus hoppenstedtii), izotal (dominated by Yucca periculosa (Agavaceae) and Beaucarnea gracilis (Nolinaceae)), and tropical dry forest (with Bursera, Ceiba parviflora, Lysiloma microphylla, Plumeria rubra). Approximately 290 species of flowering plants are known to occur in the area (Dávila et al., 1993).
The community of lizards of Zapotitlán consists of up to 13 species: Anolis quercorum, Aspidoscelis parvisocia, Aspidoscelis sacki, Ctenosaura pectinata, Gerrhonotus liocephalus, Phrynosoma braconnieri, Phrynosoma taurus, Phyllodactylus bordai, Sceloporus gadoviae, Sceloporus horridus, Sceloporus jalapae, Urosaurus bicarinatus, and Xenosaurus rectocollaris (WoolrichPina et al., 2005). We focused our work on 3 species of sceloporines (Sceloporus gadoviae, Sceloporus horridus, and Sceloporus jalapae) which live in syntopy and sympatry in the study area.
We established a 24 ha plot (800 x 300 m) that we visited 5 days per month. Random searches for lizards were conducted during the survey. We collected lizards by hand, noose, or rubber band monthly from February to December 2003. We obtained from each individual the following data: snoutvent length (SVL; to the nearest 1 mm), tail length (to the nearest 1 mm), and body mass (with an AVINETTM scale, to the nearest 0.2 g). All animals were killed by cardiac injection of 2% xylocaine, and fixed in 10% formalin, preserved in 70 % ethyl alcohol, labeled, and deposited in the herpetological collection of the UBIPRO, FES Iztacala, Universidad Nacional Autónoma de México.
We removed stomachs, examined their contents, and identified arthropods to order and occasionally to species in ants, using keys to ants (Bolton, 1994; RíosCasanova et al., 2004), termites (Constantino, 2002), and other arthropods (Borror et al., 1989).The presence of plant material was noted and classified into broad categories (e.g., fruit, seeds, leaves).We determined size of food items using fluid displacement to the nearest 0.1 mL (Milstead, 1957). To describe the importance of each prey category consumed (t), we calculated the index of relative importance (Pinkas et al., 1971) as IRIt = %Ot (%Nt + %Vt), where %Ot is the occurrence percentage (i.e., the number of stomachs containing each t item), %Nt is the percentage of the number of t items in all stomachs, and %Vt is the percentage of the volume of t items in all stomachs.
We used analysis of covariance (ANCOVA) with body size (SVL) as the covariate to examine differences in size of ingested prey between males and females. Food niche breadth was calculated using Levins standardized formula (Hurlbert, 1978): BA = [(1 / ∑ pi2)1]/(n1); where pi = proportion of occurrence of each prey species in each agesex category of diet; n = number of prey species in the lizards diet. BA ranges from 0 to 1, a value of 1 for BA means that all of prey were used in equal proportions, whereas a value near 0 for BA means that only 1 or a few categories were used with high frequency and that most prey were used in low frequencies.
We also used an analysis of similarity (ANOSIM; Clarke, 1993) to examine differences in diet among the 3 species. We pooled samples from March to July because they were the months that had the most diet data available (Fig. 1). To assess compositional differences between the diets of the 3 species, a matrix of similarity among species was developed using a BrayCurtis index based on the percentage of each prey taxon detected in the diet of each species. The data matrices were standardized and transformed (log[x+1]). This nonparametric permutation based procedure compares mean ranks of dissimilarities of samples within and among groups. When groups of samples are distinct from each other, the compositional dissimilarities between samples within a group are smaller than dissimilarities between samples from different groups. The ANOSIM test statistic, R, varies between 1 and 1, reaching its maximum value when all between group dissimilarities are greater than all withingroup dissimilarities. Statistical significance is determined by comparing the sample R with those produced by randomly assigning samples to groups. The proportion of random arrangements with Rvalues higher than the sample value is the significance level of the test (Clarke and Gorley, 2001).
The SIMPER (Similarity percentage) procedure was used to identify those prey species contributing most to the similarity within species, and the dissimilarity between groups. Both the ANOSIM and SIMPER procedures were conducted using the PRIMER Software package (Clarke and Warwick, 1994).
We surveyed 1 transect of 100 m to sample arthropods with pitfall trapping (PT). The PT method used plastic cups (450 ml) containing a salt and soap solution. Two traps were placed every 10 meters along the transect for a total of 20 traps. Traps were open for 24 hours every month. Samples was dried at 60°C for 7 days and then weighed with an analytical scale to the nearest 0.0001 g. The samples served as a reference collection and to estimate the availability of food resources (mg dry mass/m2).
We also used an analysis of variance to examine differences in food resources among months. We used a Spearman's correlation to evaluate if there was a relationship between volume of prey with rainfall.
The alimentary tracts of S. gadoviae (nfemales = 27, nmales = 28) all contained identifiable food items. Dietary index of relative importance (IRI) indicate that termites (Tenuirostritermes), ants (Camponotus rubrithorax), and coleopterans were the most important prey in the diet of S. gadoviae (Table 1). Termites were present in the diet from April to October (Fig. 1a). The ants, Camponotus rubrithorax and Pogonomyrmex barbatus, were also an important resource, because of its high volume and frequency in the stomachs (Fig. 1a). Some individuals (10.16%) were found to contain plant material (e.g. flowers). Analysis of covariance (ANCOVA) with SVL as the covariate, revealed that the sexes did not differ in length of ingested prey in S. gadoviae (F1,44 = 0.01, P = 0.98). Dietary niche breadth of S. gadoviae was BA = 0.075.
The alimentary tracts of 2 of the 47 individuals of S. jalapae were empty (nfemales/ = 15, nmales = 32). In S. jalapae, termites, coleopterans, and ants (Solenopsis) were important prey items based on the IRI (Table 1). Termites were present in the diet in more than 40% of S. jalapae in the first 5 months (Fig. 1b). Analysis of covariance (ANCOVA) with SVL as the covariate, revealed that the sexes did not differ in length of ingested prey in S. jalapae (F1,39 = 3.2, P = 0.051). Dietary niche breadth of S. jalapae was BA = 0.03.
The alimentary tracts of all of the S. horridus contained identifiable food items (nfemales = 6, nmales = 10). Ants (Camponotus rubrithorax), coleopterans, termites (Tenuirostritermes) and larval Lepidoptera were important prey items, based on the IRI, for S. horridus (Table 1). We observed coleopterans in the diet of S. horridus from March to July. Termites and ants (C. rubrithorax) were also important items in the diet of this species (Fig. 1c). Analysis of covariance (ANCOVA) with SVL as the covariate, revealed that the sexes did not differ in length of ingested prey in S. horridus (F1,13 = 0.15, P = 0.69). Dietary niche breadth of S. horridus was BA = 0.084.
ANOSIM test confirmed differences in diets of the 3 species (ANOSIM, global R = 0.288, P = 0.015). We found S. gadoviae significantly differed from S. horridus (ANOSIM, R = 0.596, P = 0.008), but no differences between S. gadoviae and S. jalapae (ANOSIM, R = 0.062, P = 0.238) and between S. jalapae and S. horridus (ANOSIM, R = 0.24, P = 0.087) were detected. The abundance of Tenuirostritermes, C. rubrithorax, P. barbatus, Coleoptera, Lepidoptera larvae, and plant material contributed the most (63.7%) to pairwise dissimilarities between the diet of S. gadoviae and S. horridus (SIMPER analysis). Although both species consume the same prey species, they do so in different quantities (Fig. 1).
Food resources varied significant among the months of study. Arthropod biomass (mg/m2) was highest in June and July (ANOVAone way; F9,59 = 29.06 P < 0.001) (Fig. 2). We found a positive relationship between arthropod availability and monthly mean precipitation (Spearman Rank Correlation, rs = 0.84, P = 0.002). In the study area we observed many termites under rocks and leaf litter during the months we sampled lizards, but we were not able to quantify this resource because termites did not fall into pitfall traps.
The diets of the 3 species of Sceloporus in this study differed in both taxonomic and volumetric composition from those reported for Iguania by Vitt et al. (2003), primarily because of the importance of termites in all 3 species. However, termites have been shown to be significant components in the diets of other Sceloporus from Mexico. FeriaOrtiz and PérezMalváez (2001) found that termites were a significant component of the diet of S. gadoviae from southwestern Puebla, with ants, coleopterans, and lepidopteran larvae also being important. In a comparative study of trophic niches on an assemblage of diurnal insectivorous lizards in the Chihuahuan Desert, Gadsden and PalaciosOrona (1997a) found that Formicidae and Isoptera were the most important prey in Cnemidophorus tigris, Uma paraphygas, and Uta stransburiana. Termites also make up a substantial portion of the diets of S. clarkii and S. nelsoni from Sonora (Brooks and Mitchell, 1989). The degree of vertebrate termitivory is highest in semiarid and arid biomes (AbenspergTraun, 1994). In the dry season, many insectivorous vertebrates rely on termites as staple prey (James, 1991). Reduced termite biomass at this time has more severe consequences than during the rainy season when alternative prey is available (Whitford and Creusere, 1977; AbenspergTraun, 1994). Gadsden and PalaciosOrona (1995) found that termites were an important item for the diet of Scelophorus undulatus consobrinus, and that ingestion of termites varies seasonally. We found the termites were a very important food for the 3 species throughout the year and were more important during the rainy season, which is not consistent with this hypothesis. Termites are diverse and abundant, suggesting that they may act as a keystone species in the assemblage of lizards we studied (Redford, 1984; Colli et al., 2006). Given the abundance of termites observed in Zapotitlán (V.H. SerranoCardozo, pers. observ.), it is not surprising that these 3 species of Sceloporus might include large numbers and volumes of termites in their diet. Indeed, AbenspergTraun and Steven (1997) found that specialization on termites by lizards is very frequent in the arid zones of Australia (AbenspergTraun, 1994). Likewise, Barbaut and Maury (1981), and Gadsden and PalaciosOrona (1995, 1997a) have reported the importance of termites and dietary specialization of lizards in the Chichuahuan Desert. The abundance of termite prey in many different microhabitats and at different times may be 1 of the key elements contributing to the relatively finescale microhabitat separation of the 3 species Sceloporus and the overall high alphadiversity of lizards in the Zapotitlán area (V.H. SerranoCardozo and J. LemosEspinal, unpubl. data). Likewise, Colli et al. (2006) found that a rich and abundant termite fauna may moderate local extinction of lizards.
That flowers were found in nearly 10.20% of the examined lizards suggests that ingestion is not accidental and that flowers are a common food item. We found flowers in 6 lizards (5 males and 1 female) among February and June. Gadsden and PalaciosOrona (1997b) and Gansden et al. (2001) found that the ingestion of plant parts in stomachs of Uma exsul and U. paraphygas respectively were greater than 50% and that the ingestion was not accidental. These authors found that males ingest more plants than females. The role of plants in the diet of lizards is unclear, but it is possible that in desert lizards the ingestion of flowers can constitute an additional source of water.
Rain during the summer and spring caused an increase in the abundance of prey, and an overall increase in prey biomass available for lizards, but the lizards continued using the same resources. The 3 species of Sceloporus appear to be specialists in their diet, as evidenced by the relatively small food niche breadths (S. gadoviae, BA = 0.075; S. jalapae, BA = 0.03; S. horridus, BA = 0.084). Seasonal variation in diet composition of lizards has been reported in several studies in different regions (e.g. Chapman and Chapman, 1964; Pianka, 1970; Fleming and Hooker, 1975; Best and Gennaro, 1984; Burquez et al., 1986; Maya and Malone, 1989; Rocha, 1996; Whitfield and Donnelly, 2006). These variations have been attributed mainly to seasonal changes in prey availability (Maury, 1995). However, we did not find seasonal variation in diet composition in our 3 species, only variation in the volume of consumed prey (i.e. the amount consumed).
In conclusion, the 3 studied species of Sceloporus have relatively similar diets, with the most dissimilar diets being S. gadoviae and S. horridus. The general similarity arises from the extensive use of termites in their diets.
We thank the Posgrado en Ciencias Biológicas (PCBIOLUNAM), Dirección General de Estudios del Postgrado (DGEP), Universidad Nacional Autónoma de México (UNAM), Universidad Industrial de Santander (UIS), for Ph.D. fellowship financial support to VHSC. Support for this study was provided by PAPIIT (IN200102). We are grateful to F. Serrano and M. Flores for logistical aid, to I. F. Castillo and E. Castillo for field assistance during lizard collection, and to Commissary Márquez for allowing us to work in Zapotitlán de las Salinas. We thank anonymous reviewers who offered constructive and insightful comments on the manuscript. All appropriate collecting permits from the Mexican government were obtained by J. A. LemosEspinal prior to commencement of this study (Dirección General de Vida Silvestre SEMARNAT, SGPA/DGVS/07609).
AbenspergTraun, M. 1994. The influence of climate on patterns of termite eating in Australian mammals and lizards. Australian Journal of Ecology 19:6571. [ Links ]
AbenspergTraun, M. and D. Steven. 1997. Ant and termiteeating in Australian mammals and lizards: a comparison. Australian Journal of Ecology 22:917. [ Links ]
Attum, O., P. Eason and G. Cobbs. 2007. Morphology, niche segregation, and escape tactics in a sand dune lizard community. Journal of Arid Environments 68:564573. [ Links ]
Barbault, R. and M. E. Maury. 1981. Ecological organization of a Chihuahuan Desert lizard community. Oecologia(Berl) 51:335342. [ Links ]
Best, T. L. and A. L. Gennaro. 1984. Feeding ecology of the lizard, Uta stansburiana in southeastern New Mexico. Journal of Herpetology 18:291301. [ Links ]
Bolton, B. 1994. Identification Guide to the Ant Genera of the World. Harvard University Press, Massachusetts. [ Links ]
Borror, D. J., C. A. Triplehorn and N. F. Johnson. 1989. Introduction to the Study of Insects. Harcourt College Publishers, New York. 875 p. [ Links ]
Brooks, G. R. and J. C. Mitchell. 1989. Predatorprey size relations in three species of lizards from Sonora, Mexico. Southwestern Naturalist 34:541546. [ Links ]
Burquez, A., O. FloresVillela and A. Hernández. 1986. Herbivory in a small iguanid lizard, Sceloporus torquatus torquatus. Journal of Herpetology 20:262264. [ Links ]
Chapman, B. M. and F. Chapman. 1964. Observations on the biology of the lizard Agama agama in Ghana. Proceedings of the Zoological Society of London 143:121132. [ Links ]
Clarke, K. R. 1993. Nonparametric multivariate analyses of changes in community structure. Australian Journal of Ecology 18:117143. [ Links ]
Clarke, K. R. and R. M. Warwick. 1994. Change in marine communities: an approach to statistics analysis and interpretation (Plymouth Marine Laboratory). 369 p. [ Links ]
Clarke, K. R. and R. N. Gorley. 2001. PRIMER. Version 5 user manual/tutorial. PRIMER5 Ltd., Plymouth, United Kingdom. [ Links ]
Colli, G. R., R. Constantino and G. C. Costa. 2006. Lizards and termites revisited. Austral Ecology 31:417424. [ Links ]
Constantino, R. 2002. Online Termite database. Departamento de Zoologia, Universidade de Brasilia. http://www.unb.br/ib/zoo/docente/constant/catal/catnew.html (Accessed December 2005). [ Links ]
Creusere, F. M. and W. G. Whitford. 1982. Temporal and spatial resource partitioning in a Chihuahuan Desert lizard community. In Herpetological Communities, N. J. Scott, Jr. (ed.). US Dep. Interior Wildlife Research Report 13, Washington, D.C. p. 121127. [ Links ]
Dávila, P., J. L. Villaseñor, R. Medina, A. Ramírez, A. Salinas, J. SánchezKen and P. Tenorio. 1993. Listados florísticos de México. X. Flora del valle de Tehuacán Cuicatlán. Instituto de Biología, Universidad Nacional Autónoma de México. México D. F. 195 p. [ Links ]
D'Cruze, N. C. and P. J. Stafford. 2006. Resource partitioning of sympatric Norops (Beta Anolis) in a subtropical mainland community. Herpetological Journal 16:273280. [ Links ]
FeriaOrtiz, M. and C. PérezMalváez. 2001. Composición de la dieta de la lagartija ovipara Sceloporus gadoviae (Phrynosomatidae) en el suroeste del Estado de Puebla, México. Boletín de la Sociedad Herpetológica Mexicana 9:4550. [ Links ]
Fleming, T. H. and R. S. Hooker. 1975. Anolis cupreus: the reponse of a lizards to tropical seasonality. Ecology 56:12431261. [ Links ]
Fuentes, E. R. 1976. Ecological convergence of lizard communities in Chile and California. Ecology 57:317. [ Links ]
Gainsbury, A. M. and G. R. Colli. 2003. Lizard assemblages from natural Cerrado enclaves in southeastern Amazonia: The role of stochastic extinctions and isolation. Biotropica 35:503519. [ Links ]
Gadsden, H. E. and L. E. PalaciosOrona. 1995. Variación de la alimentación de Sceloporus undulatus (Reptilia: Phrynosomatidae) en el Bolsón de Mapimí, México. Boletín de la Sociedad Herpetológica Mexicana 6:3239. [ Links ]
Gadsden, H. E. and L. E. PalaciosOrona. E. 1997a. Patrones alimentarios de un gremio de lagartijas en dunas del Bolsón de Mapimí, México. Vida Silvestre Neotropical 6:3747. [ Links ]
Gadsden, H. E. and L. E. PalaciosOrona. 1997b. Seasonal dietary patterns of the Mexican fringetoed (Uma paraphygas). Journal of Herpetology 31:19. [ Links ]
Gadsden, H. E., L. E. PalaciosOrona and G. A. CruzSoto. 2001. Diet of the Mexican Fringetoed Lizard (Uma exsul). Journal of Herpetology 35:493496. [ Links ]
Garcíade la Peña, C., G. Castañeda, H. E. Gadsden and A. J. ContrerasBalderas. 2007a. Niche segregation within a dune lizard community in Coahuila, Mexico. The Southwestern Naturalist 52:251257. [ Links ]
Garcíade la Peña, C., H. E. Gadsden, A. J. ContrerasBalderas and G. Castañeda. 2007b. Ciclos de actividad diaria y estacional de un gremio de saurios en las dunas de arena de Viesca, Coahuila, México. Revista Mexicana de Biodiversidad. Instituto de Biología, Universidad Nacional Autónoma de México 78:141147. [ Links ]
Greene, H. W. 2005. Historical influences on community ecology. Proceedings of the National Academy of the Sciences 102:83958396. [ Links ]
Hurlbert, S. H. 1978. The measurement of niche overlap and some relatives. Ecology 59:6777. [ Links ]
James, C. D. 1991. Temporal variation in diets and trophic partitioning by coexisting lizards (Ctenotus: Scincidae) in central Australia. Oecologia 85:553561. [ Links ]
James, S. E. and R. T. M'Closkey. 2002. Patterns of microhabitat use in a sympatric lizard assemblage. Canadian Journal of Zoology 80:22262234. [ Links ]
LemosEspinal, J. A., G. R. Smith, R. E. Ballinger and H. M. Smith. 2003. Ecology of Sceloporus undulatus speari (Sauria: Phrynosomatidae) from northcentral Chihuahua, México. Journal of Herpetology 37:722725. [ Links ]
Losos, J. B. 1994. Historical contingency and lizard community ecology. In Lizard Ecology: historical and experimental perspectives, L. J. Vitt and E. R. Pianka (eds.). Princeton University Press, New Jersey. p. 319333. [ Links ]
Maury, M. E. 1995. Diet composition of the greater earless lizard Cophosaurus texanus in Central Chihuahua desert. Journal of Herpetology 29:266272 [ Links ]
Maya, J. E. and P. Malone. 1989. Feeding habitats and behavior of the whiptail lizard, Cnemidophorus tigris tigris. Journal of Herpetology 23:309311. [ Links ]
Melville, J., L. J. Harmon and J. B. Losos. 2006. Intercontinental community convergence of ecology and morphology in desert lizards. Proceedings of the Royal Society 273B:557563. [ Links ]
Mesquita, D. O., G. R. Colli., F. G. R. França and L. J. Vitt. 2006. Ecology of a Cerrado lizard assemblage in the Jalapåo Region of Brazil. Copeia 2006:460471. [ Links ]
Milstead, W. W. 1957. Observations on the natural history of four species of whiptail lizards, Cnemidophorus (Sauria: Teiidae) in transPecos Texas. Southwestern Naturalist 2:105121. [ Links ]
Pianka, E. R. 1970. Comparative autecology of the lizard Cnemidophorus tigris in different parts of its geographic range. Ecology 51:703720. [ Links ]
Pinkas, L., M. S. Olipant and Z. L. Iverson. 1971. Food habits of albacore bluefin, tuna and bonito in California Waters. California Departament Fish. Game, Fish Bulletin 152:11105. [ Links ]
Redford, K. H. 1984. The termitaria of Cornitermes cumulans (Isoptera, Termitidae) and their role in determining a potential keystone species. Biotropica 18:125135. [ Links ]
RíosCasanova, L., A. ValienteBanuet and V. RicoGray. 2004. Las hormigas del valle de Tehuacán (Hymenoptera: Formicidae): una comparación con otras zonas áridas de México. Acta Zoológica Mexicana 20:3754. [ Links ]
Rocha, C. F. D. 1996. Seasonal shift in lizard diet: the seasonality in food resources affecting the diet of Liolaemus lutzae (Tropiduridae). Ciência e Cultura 48:264269. [ Links ]
Rouag, R., H. Djilali., H. Gueraiche and L. Luiselli. 2007. Resource partitioning patterns between 2 sympatric lizard species from Algeria. Journal of Arid Environments 69:158168. [ Links ]
Toft, C. A. 1985. Resource partitioning in amphibians and reptiles. Copeia 1985:120. [ Links ]
ValienteBanuet, L. 1991. Patrones de precipitación en el valle semiárido de Tehuacán, Puebla, México. Tesis, Facultad de Ciencias, Universidad Nacional Autónoma de México, México D. F. 61 p. [ Links ]
Vitt, L. J. and P. A. Zani. 1996. Organization of a taxonomically diverse lizard assemblage in Amazonian Ecuador. Canadian Journal of Zoology 74:13131335. [ Links ]
Vitt, L. J. and P. A. Zani. 1998a. Ecological relationships among sympatric lizards in a transitional forest in the northen Amazon of Brazil. Journal of Tropical Ecology 14:6386. [ Links ]
Vitt, L. J. and P. A. Zani. 1998b. Prey use among sympatric lizard species in lowland rain forest of Nicaragua. Journal of Tropical Ecology 14:537559. [ Links ]
Vitt, L. J., P. A. Zani and M. C. Espósito. 1999. Historical ecology of Amazonian lizards: implications for community ecology. Oikos 87:286294. [ Links ]
Vitt, L. J., E. R. Pianka, W. E. Cooper Jr. and K. Schwenk. 2003. History and the global ecology of squamates reptiles. American Naturalist 162:4460. [ Links ]
Vitt, L. J. and E. R. Pianka. 2005. Deep history impacts presentday ecology and biodiversity. Proceedings of the National Academy of the Sciences 102:78777881. [ Links ]
Watling, J. I., J. H.Waddle, D. Kizirian and M. A. Donnelly. 2005. Reproductive phenology of three lizard species in Costa Rica, with comments on seasonal reproduction of neotropical lizards. Journal of Herpetology 39:341348. [ Links ]
Whitfield, S. M. and M. A. Donnelly. 2006. Ontogenetic and seasonal variation in the diets of a Costa Rican leaflitter herpetofauna. Journal of Tropical Ecology 22:409417. [ Links ]
Whitford, G. and F. M. Creusere. 1977. Seasonal and yearly fluctuations in Chihuahuan Desert lizard communities. Herpetologica 33:5465. [ Links ]
WoolrichPiña, G., L. OliverLópez and J. A. LemosEspinal. 2005. Anfibios y Reptiles del Valle de Zapotitlán Salinas, Puebla. CONABIO, Mexico. 54 p. [ Links ]