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Biota Neotropica

Print version ISSN 1678-6424On-line version ISSN 1676-0611

Biota Neotrop. vol.13 no.3 Campinas July/Sept. 2013 


Ecology and diversity of a lizard community in the semiarid region of Brazil

Ecologia e diversidade de uma comunidade de lagartos na região semiárida do Brasil

Maria Jaqueline Monte de Andrade1  2  3 

Raul Fernandes Dantas Sales1 

Eliza Maria Xavier Freire1 

ILaboratório de Herpetologia, Departamento de Botânica, Ecologia e Zoologia, Centro de Biociências, Universidade Federal do Rio Grande do Norte – UFRN, Campus Universitário Lagoa Nova, CEP 59072-970, Natal, RN, Brazil

2Programa de Pós-Graduação em Ciências Biológicas, Centro de Biociências, Universidade Federal do Rio Grande do Norte – UFRN, Campus Universitário Lagoa Nova, CEP 59072-970, Natal, RN, Brazil


Composition, species diversity and resource usage in terms of space and time were evaluated for the lizard community of the Ecological Station of the Seridó (ESEC Seridó), Rio Grande do Norte. An observation area of 150 m × 150 m (2.25 ha) was delimited and surveyed monthly in alternate turns (morning, afternoon and night) for three consecutive days from April to October 2011, covering dry and rainy seasons. Fourteen species belonging to eight families were recorded, being Tropidurus semitaeniatus the most abundant. Seasonality influenced species richness and abundance. Regarding habitat usage, Lygodactylus klugei was the most generalist species, whilePhyllopezus periosus, P. pollicaris and T. semitaeniatus were specialists, showing affinity for rocky formations. About microhabitat usage, the most generalist species was T. hispidus and the most specialized wasL. klugei . Ten of the recorded species have diurnal habits and four are nocturnal. The space and time usage profiles of the dominant species corroborated data obtained in previous autoecological studies conducted in the same area and suggest a pattern of resource usage by these species in the ESEC Seridó.

Key words: caatinga; activity periods; habitat use; microhabitat use; richness; seasonality


Neste trabalho foram avaliadas a composição, diversidade de espécies e a utilização dos recursos espaço e tempo na comunidade de lagartos da Estação Ecológica do Seridó (ESEC Seridó), Rio Grande do Norte. Para isso, uma área de observação de 150m × 150m (2,25 ha) foi delimitada e percorrida mensalmente em turnos alternados (manhã, tarde e noite) por três dias consecutivos nos meses de abril a outubro de 2011, cobrindo as estações seca e chuvosa. Foram registradas 14 espécies pertencentes a oito famílias, dentre as quais a mais abundante foi Tropidurus semitaeniatus. A sazonalidade influenciou a riqueza e abundância das espécies. Quanto ao uso do hábitat, Lygodactylus klugei foi a espécie mais generalista, enquantoPhylopezus periosus, P. pollicaris e T. semitaeniatus demonstraram especialidade às áreas de formações rochosas. Quanto ao uso de microhábitats, a espécie mais generalista foi T. hispidus e a mais especialista foi L. klugei. Dez das espécies registradas possuem hábito diurno e quatro são noturnas. Os perfis de uso do espaço e do tempo pelas espécies dominantes corroboram dados obtidos em estudos anteriores nesta mesma área e sugerem a existência de padrões na utilização desses recursos por estas espécies na ESEC Seridó.

Palavras-Chave: caatinga; período de atividade; uso do habitat; uso do micro-habitat; riqueza; sazonalidade


The Caatinga is a mosaic of thorny bushlands and seasonally dry forests occupying about 750.000 km2 of the Brazilian territory, bordered by the Atlantic Rainforest to the east, by the Amazonian Forest to the west and by the Cerrado to the south (Leal et al. 2005), being the only exclusively Brazilian biome (Silva et al. 2003, Leal et al. 2003, 2005). In spite of occupying a unique position among biomes, the Caatinga is the proportionally less studied one (Leal et al. 2003), a fact that maintained for a long time the idea of the Caatinga as being a homogeneous region, poor in biodiversity and endemisms. These assertions do not correspond with reality, because even being necessary more studies with wider geographical coverage, the Caatinga is more diverse than other regions with the same climate and soil conditions (Silva et al. 2003, Albuquerque et al. 2012).

Rodrigues (2003) recognized 47 lizard species for the Caatinga, apart from the species found in wet forest enclaves, which would make this biome as rich as the Cerrado and the Atlantic Rainforest (Rodrigues 2005). Despite this, the level of knowledge about the herpetofauna of the Caatinga is still considered unsatisfactory (Rodrigues 2003), because large areas of this biome were never sampled (Borges-Nojosa & Arzabe 2005, Albuquerque et al. 2012) and many new species have been described in the last 15 years (e.g. Rodrigues 1996, Arias et al. 2011a, b).

In spite of lizards being considered model organisms for ecological studies, being easily handled animals and because they are more abundant and frequent to find than other reptiles (Rocha 1994), for a long time the only available paper about community ecology of lizards of the Caatinga was the result of a study developed in the Exu region, Pernambuco State (Vitt 1995). Ecological studies covering different geographical areas of the Caatinga are fundamental to test patterns, particularly those related to space usage, activity time, diet and reproduction. In this context, a long-term study, making part of the Long-Term Ecological Research Program (Programa de Pesquisas Ecológicas de Longa Duração) – PELD /CNPq Caatinga, was performed from 2002 to 2011 in a Conservation Unit of the Seridó region, Rio Grande do Norte State. The results of this study, partially summarized by Freire et al. (2009), were relevant to yield knowledge about lizard ecology in the Caatinga. Firstly, an inventory of the lizard species of the ESEC Seridó was conducted, including a survey on habitat usage and activity time of the dominant species (Kolodiuk 2005). At the same time, Maggi (2005) studied the population ecology of the geckosPhyllopezus periosus and P. pollicaris. Subsequently, substantial studies on behavioral ecology of the populations of Tropidurus hispidus andT. semitaeniatus (Ribeiro 2010, Ribeiro et al. 2008, 2010,2012, Ribeiro & Freire 2009a, b, 2010,2011b, Kolodiuk et al. 2009, 2010) and of the populations ofAmeiva ameiva and Ameivula cf. ocellifera(Sales et al. 2011a, b, 2012) were performed.

Considering nine study years since the initial inventory, and the results of the autoecological studies, this work had the objective of evaluating composition, diversity, space usage and activity periods of the lizard species in the ESEC Seridó, with the sight of consolidating the knowledge about community ecology of lizards in this Conservation Unit. This consolidation would be effective by answering the following questions: Is there a pattern, in terms of spatial distribution and habitat/microhabitat usage, for the species composing the lizard community of the ESEC Seridó? Could this pattern be confirmed for other similar areas of Caatinga (sensu stricto)? Does seasonality interfere with this pattern?

Material and Methods

1.Study area

This work was carried out in the ESEC Seridó (06° 34′ 36.2″ S and 37° 15′ 20.7″ W), a Conservation Unit occupying an area of 1,166.38 ha, in the municipality of Serra Negra do Norte, Seridó region, Rio Grande do Norte state (Varela-Freire 2002). Similar to other areas located in the Northern Depression (Depressão Sertaneja Setentrional), the ESEC Seridó supports climatic extremes, with low, open vegetation and extensive grasslands (Velloso et al. 2002). Irregularity in rainfall is one of the main factors of this ecorregion, characterized by hydric deficits along most of the year, reaching up to 10 dry months; the climate is semiarid, hot and dry (Bswh in Köppen's classification; Velloso et al. 2002). In general, the mean annual precipitation of the ESEC fluctuates between 500 and 800 mm/year (Varela-Freire 2002). In 2011, when this study was conducted, rainfall reached 1249 mm (Figure 1), being above the annual average for the area. Mean annual temperatures range between 28 °C and 30 °C, with highest temperatures reaching 40 °C and lower ones between 17 °C and 20 °C (Varela-Freire 2002). Air relative humidity varies between 30 and 50% during dry season and between 80 and 90% in the rainy season (Varela-Freire 2002).

Figure 1. Total monthly rainfall recorded for the Ecological Station of the Seridó (ESEC Seridó) from January to October, 2011 (Source: Laboratório de Recursos Hídricos da Universidade Federal do Rio Grande do Norte). 

2.Methodological procedures

An inspection to choose a sampling area containing the different habitats covered by the ESEC was initially made. A 150 m × 150 m square (2.25 ha), close to the access pathway to the buffer zone of the ESEC (06° 34′ 72″ S and 37° 15′ 11″ W), was delimited in the selected area for observation and/or collecting of lizards. Fourteen transects, seven parallel and seven perpendiculars to the pathway, distant 25 m from each other were delineated. The crossings, every 25 m, were marked with zebra tape as stop/sampling points for registering of lizards, making a total of 49 sample points (Figure 2).

Figure 2. Sampling points marked in the 150 m × 150 m (2.25 ha) quadrant delineated in the Ecological Station of the Serido (ESEC Seridó). 

Monthly visits from April to October of 2011 (except in August due to logistic reasons) were made. Three rainy months were considered along this period: April, May and June, being worth mentioning that despite June showed a low rainfall index (Figure 1), the vegetation was still exuberant as in the previous months, so June was considered a rainy season month. The three dry season months were July, September and October. The surveys were made by two collectors (MJMA and RFDS), with equal effort along the 14 transects and with intensive search at the stop points. The collectors traveled the transects during daytime and nighttime, in alternate turns, during 3 consecutive days each month. On the first day of each excursion, searches took place from 1800 h to 0000 h, in the second from 0800 h to 1300 h, and the third and final day from 0000 h to 0500 h and 1300 h to 1800 h.

A detailed inspection of the environment was made at each stop point in a radius of 10 m around it, in order to characterize and identify the different physiognomies, and the predominant habitats along all the transects. Five different habitats were determined and categorized this way: Tree-Shrubby Vegetation (TSV), Dense Shrubby Vegetation (DSV), Sparse Shrubby Vegetation (SSV), Herbaceous Vegetation in Open Area (HVOA) and Areas with Rocky Formations (ARF). Ten microhabitat categories were identified and inspected in these five habitats, representing the place where the lizard specimens were firstly seen: Trees and Shrubs (TS); Soil with Herbaceous Vegetation (SHV), Soil with Leaf Litter (SLL), Exposed Soil (ES), Stony Soil (SS), On Decomposing Log or Branch (ODLB), Inside Decomposing Log or Branch (IDLB), On Boulder (OB), Rock Outcrop (RO), Crack of Rock Outcrop (CRO).

Each individual observed in the field was identified and notes with information about habitat and microhabitat, light exposition category for diurnal species (sunlight or shade), and date and time of observation were recorded. To measure activity periods of the species, observations of active individuals were categorized in one-hour intervals, ranging from 00 to 59 minutes (e.g. 1300 h to 1359 h). A few specimens, unidentifiable in the field, were collected and examined in the laboratory, where they were identified, fixed in 10% formalin, preserved in 70% ethanol and deposited in the Herpetological Collection of the Universidade Federal do Rio Grande do Norte (CHBEZ).

3.Quantitative data analysis

The niche amplitude of each species for space and time dimensions was calculated by the inverse of Simpson's Diversity Index (Simpson 1949). It is worth to highlight that inactive individuals were not included in the analysis of niche amplitude for time, just for space usage. The difference in the values of niche amplitude in the species for the dry and the rainy season was calculated through a paired Student's t-test. Niche overlap was examined using the Pianka's Overlap Index - Ojk (Pianka 1973). Both indexes were calculated in the Ecological Methodology program (Kenney & Krebs 2000), and only species with n ≥ 5 were considered in the analyses. Diversity in rainy and dry seasons was obtained using the Shannon-Wiener Index (H') (Magurran 1988).


Species richness and abundance

Sampling effort totalized 95 hours (155 man-hours, 79 during daytime and 76 during nighttime; 75 during the rainy season and 80 during the dry season). A total of 663 records of habitat and microhabitat usage were made (643 for active individuals and 20 for inactive individuals). Fourteen species, belonging to eight families were recorded (Table 1). Most of the field records belonged to the following species in descending order: Tropidurus semitaeniatus (45.2%),Phyllopezus periosus (15.5%), T. hispidus(13.4%), P. pollicaris (9.2%),Ameivula cf. ocellifera (6.8%),Ligodactylus klugei (4.2%), Hemidactylus agrius(2.3%) and Gymnodactylus geckoides (1.2%) (Figure 3 and 4).

Figure 3. The eight most abundant lizard species in the Ecological Station of the Seridó (ESEC Seridó) in this study, along the period of April to October 2011. (A) Tropidurus semitaeniatus, (B) T. hispidus, (C) Ameivula cf. ocellifera, (D)Ligodactylus klugei, (E) Phyllopezus periosus, (F) P. pollicaris, (G) Hemidactylus agrius, (H) Gymnodactylus geckoides

Figure 4. Absolute abundance of visual records of lizard species of the Ecological Station of the Seridó (ESEC Seridó), during the dry (grey bars) and rainy (black bars) seasons, along the period of April to October 2011. Acronyms represent the initials of the specific names, according to Table 1

Table 1. Lizard species and number of visual records in the different habitats of the Ecological Station of the Seridó (ESEC Seridó), along the period of April to October 2011. ARF: Areas with Rocky Formations, DSV: Dense Shrubby Vegetation, SSV: Sparse Shrubby Vegetation, TSV: Tree-Shrubby Vegetation and HVOA: Herbaceous Vegetation in Open Area. A dash (-) indicates absence of records. 

Hemidactylus agrius Vanzolini 1978 11 3 - 1 -
Lygodactylus klugei (Smith, Martin & Swain, 1977) 9 9 5 5 -
Vanzosaura rubricauda (Boulenger 1902) 1 - - - -
Iguana iguana (Linnaeus, 1758) - - 1 - -
Gymnodactylus geckoides Spix, 1825 2 1 3 2 -
Phyllopezus periosus Rodrigues, 1986 103 - - - -
Phyllopezus pollicaris Spix, 1825 60 - 1 - -
Polychrus acutirostris Spix, 1825 - - - 1 -
Mabuya heathi (Schimdt & Inger, 1951) - 1 2 2 -
Ameiva ameiva (Linnaeus,1758) 1 - - 3 -
Ameivula cf. ocellifera (Spix, 1825) 3 8 24 1 9
Salvator merianae (Duméril & Bibron,1839) 2 - - - -
Tropidurus hispidus (Spix, 1825) 43 25 9 12 -
Tropidurus semitaeniatus (Spix, 1825) 256 23 14 7 -
Total 491 70 59 34 9

Of 14 recorded species, eight were seen during both seasons, four only during the rainy season and just two exclusively during the dry season (Iguana iguana andPolychrus acutirostris) (Figure 3). The five most frequent species showed a higher abundance during the rainy season (Figure 4). Most individuals of the geckosL. klugei, H. agrius, and G. geckoides were recorded in the dry season (Figure 4). Even the rainy season showing a higher richness and abundance of individuals, the total diversity was the same for both seasons (H' = 2.4).

1.Habitat usage

The most used habitat by the lizard species was Areas with Rocky Formations (ARF), showing the greatest richness and the highest number of recorded individuals (Table 1). In total, 11 of the 14 observed species and 74% (n = 491) of the individual visual records made in this study happened in this habitat. On the other hand, the habitat of Herbaceous Vegetation in Open Area (HVOA) was the poorest, with just a single species, A. cf.ocellifera, and also the lowest number of individual visual records: 1.3% (n = 9) (Table 1).

The most generalist species in terms of habitat usage were L. klugei(BH = 3.69), G. geckoides (BH = 3.55) and T. hispidus (BH = 2.93) (Table 2). The species with more restricted exigencies/fidelity in habitat usage, with BH = 1, was P. periosus, followed by P. pollicaris with BH 1.03, andT. semitaeniatus with BH = 1.35 (Table 2). No significant difference was identified in the niche amplitude of the species between seasons (t = −1.401; gl = 7; p = 0.204).

Table 2. Space niche amplitude for habitat (BH) and microhabitat (BM) of the species of lizards (n ≥ 5) in the ESEC Seridó, along the period of April to October, 2011. 

Species n BH BM
T. semitaeniatus 300 1.35 2.55
P. periosus 103 1 4.08
T. hispidus 89 2.93 5.37
P. pollicaris 61 1.03 4.08
A. cf. ocellifera 45 2.77 1.69
L. klugei 28 3.69 1.32
H. agrius 15 1.71 4.41
G. geckoides 8 3.55 1.6
M. heathi 5 2.77 1

Most of the species pairs showed high niche overlaps in habitat usage (Table 3). The highest overlapping was confirmed forP. periosus and P. pollicarisPpe ×ØPpo = 0.999), followed by the overlaps between each of these two species and T. semitaeniatus (Table 3). Low overlapping indexes were obtained between A. cf.ocellifera and H. agrius, and between A. cf.ocellifera and the species using mainly ARF (P. periosus,P. pollicaris and T. semitaeniatus) (Table 3). A markedly low overlapping index was also obtained between Mabuya heathi and the following species: P. pollicaris, T. semitaeniatus and H. agrius (Table 3). Overlapping was null just between M. heathi and P. periosus.

Table 3. Overlapping values for spatial niche. Values above the traced diagonal correspond to habitat usage and values below the diagonal correspond to microhabitat usage, obtained for the lizard species (n ≥ 5) of the Ecological Station of the Seridó (ESEC Seridó), along the period of April to October 2011. For both categories analyzed, the boldface values correspond to the highest overlapping indexes, while those in italics correspond to the lowest indexes. Acronyms represent the initials of the specific names, according to Table 1

T.sem P.per T.his P.pol A. oce L. klu H. agr G. gec M. hea
T.sem - 0.994 0.881 0.994 0.186 0.697 0.981 0.54 0.08
P.per 0.750 - 0.827 0.999 0.11 0.618 0.961 0.471 0
T.his 0.712 0.639 - 0.83 0.396 0.947 0.941 0.734 0.429
P.pol 0.787 0.873 0.735 - 0.125 0.623 0.96 0.483 0.011
A. oce 0.019 0 0.209 0 - 0.569 0.187 0.767 0.715
L. klu 0.072 0.548 0.329 0.461 0 - 0.786 0.841 0.663
H. agr 0.378 0.274 0.744 0.468 0.158 0.092 - 0.556 0.145
G. gec 0.008 0 0.115 0.03 0.11 0 0.664 - 0.864
M. hea 0.01 0 0.07 0 0.926 0 0 0 -

2.Microhabitat usage

The highest numbers of species records happened in the microhabitats Soil with Herbaceous Vegetation (SHV), On Decomposing Log or Branch (ODLB) and Trees and Shrubs (TS), with the respective occurrence of seven, six and six species. The microhabitats Exposed Soil (ES), Stony Soil (SS) and Inside Decomposing Log or Branch (IDLB) were the poorest, with just three species found at each one. The microhabitat ES was used by T. semitaeniatus, T. hispidus andSalvator merianae; SS was used by T. semitaeniatus, A. ameiva andVanzosaura rubricauda, and IDLB by G. geckoides, H. agrius andP. pollicaris. Rock Outcrop (RO) microhabitat was the one with the highest percentage of individuals (33.4%, n = 222), while Exposed Soil (ES) yielded the lowest number of records, just 0.7% (n = 5).

The most generalist species in terms of microhabitat usage were T. hispidus (BM = 5.37), H. agrius(BM= 4.41), P. periosus (BM = 4.08) and P. pollicaris (BM = 4.08) (Table 2). The most microhabitat usage-restricted species wasM. heathi (BM = 1), which occurred just in Soil with Herbaceous Vegetation (SHV), followed by L. klugei (BM= 1.32), which used mainly Trees and Shrubs (TS), and by ocellifera (BM = 1.69) (Table 2), with most of its records happening in SHV. No significant difference was identified in the niche amplitude of the species between seasons (t = 0.569; gl = 7; p = 0.587).

An almost complete overlapping in microhabitat usage (Ø = 0.926) happened only between the pair of species using mostly SHV: A. cf.ocellifera and M. heathiAo x Mh= 0.926), followed by the overlapping among the dominant species using mostly ARF (P. pollicaris X P. periosus X T. semitaeniatus) (Table 3) and the two more generalist species in terms of microhabitat usage: H. agrius and T. hispidusHa x Th = 0.744). In most of the cases, overlapping was null or very low (Table 3).

3.Activity periods

Ten of the fourteen species composing this lizard assemblage have diurnal habits, with an activity period between 0800 h and 1700 h (Figure 5). The nocturnal species (P. pollicaris, P. periosus, H. agriusand G. geckoides) showed an activity period between 1800 h and 0500 h (Figure 5); G. geckoides andP. periosus were also registered during the day, with G. geckoidesbeing hidden, while P. periosus was active (see below).

Figure 5. Activity periods of lizard species (n ≥ 5) of the Ecological Station of the Seridó (ESEC Seridó), during the dry season (white bars) and rainy season (back bars), along the period of April to October 2011. Diurnal species: (A) Tropidurus semitaeniatus, (B) T. hispidus, (C) Ameivula cf. ocellifera, (D)Ligodactylus klugei, (E) Mabuya heathi. Nocturnal species: (F) Phyllopezus periosus, (G) P. pollicaris, (H) Hemidactylus agrius

Among the diurnal species, L. klugei (BT = 8.57), T. hispidus (BT = 8.51) and T. semitaeniatus (BT = 8.31) were the species with a wider niche amplitude and showed wider and/or bimodal activity profiles (Figure 5A, B and D). These three species share the specificities of being recorded from the initial hours of observation, remaining active all day long, but with reduction of activity during the hottest hours. However, during the rainy season, L. klugei started activities later, around 1000 h, without any reduction of activity until the end of the day (Figure 5D). A relatively narrower niche amplitude value (BT = 4.60), when compared with the tropidurids, was obtained for the teiid A. cf. ocellifera, reflecting and intermediate activity period (Figure 4C); this species started activities around 0800 h, reaching the highest number of appearances in the hottest hours and ending activities early, around 1400 h (Figure 5C). On the other hand,M. heathi presented the narrowest niche amplitude (BT = 1.8) and showed a bimodal profile, during the initial and final hours of the day, corresponding to moderate temperatures (Figure 5E).

Among the nocturnal species, P. periosus (BT= 9.51) and P. pollicaris (BT = 7.68) were the ones with a wider activity period (Figure 5F and G). These species remained active during all the nocturnal observation period in both seasons. Furthermore, P. periosus was active not only at night; two individual were found active at the end of the afternoon, between 1700h and 1800h (Figure 5G), and one individual was found active at 0900 h (not shown in Figure 4). An intermediate value for niche amplitude (BT = 5.26) was obtained for H. agrius, with a very variable activity along the night and being recorded mainly during the dry season (Figure 4H). No significant difference was identified in the niche amplitude of the species between seasons (t = 0.652; gl = 6; p = 0.539).

The greatest overlapping in temporal niche happened between T. hispidus and T. semitaeniatusTh × Ts= 0.938), followed by P. periosus and P. pollicarisPpe × Ppo = 0.891), and by L. klugei and the tropidurids (ØLk x Ts = 0.898 and ØLk x Th = 0.795). Null or markedly low overlapping indexes were obtained mostly between nocturnal and diurnal species.

4.Considerations about seasonal variation for sunny and/or shaded microhabitat usage

Variations in the usage profiles of sunny and shaded microhabitats were recorded for the most common diurnal species (n ≥ 10). During the rainy season, tropidurids made use of sunny microhabitats along all of the day (Figure 6Aand C), while in the dry season they used mainly shaded microhabitats (Figure 6B and D). On the other hand, the profiles of light exposition of A. cf. ocellifera and L. klugeiwere similar along seasons; A. cf. ocellifera used just sunny microhabitats (Figure 6E and F), while L. klugei was recorded mainly from shaded environments (Figure 6G and H).

Figure 6. Usage of sunny (white bars) and shaded (black bars) microhabitats byTropidurus semitaeniatus (A, B), T. hispidus (C, D), Ameivula cf. ocellifera (E, F) andLigodactylus klugei (G, H) in the Ecological Station of the Seridó (ESEC Seridó), during the dry (A, C, E, G) and rainy (B, D, F, H) seasons. 


Of the 16 species recorded by Freire et al. (2009) for the ESEC Seridó, just two (Hemidactylus brasilianus e Micrablepharus maximiliani) were not found during this study performed in the same area. The longer sampling effort during the first work (several field excursions between 2002 and 2008) could have been a factor responsible for this difference. The richness of the lizard community of the ESEC Seridó is, therefore, similar to that found in other areas of Caatinga sensu stricto (Andrade-Lima 1981), considering that the richness of these areas oscillates between 10 and 19 species, depending on the locality (Vanzolini et al. 1980, Vitt 1995, Ribeiro & Freire 2011a,Moura et al. 2010, Garda et al. 2013).

The most frequent species in this study was T. semitaeniatus, which is a typical species of the Caatinga biome (Vitt 1995, Rodrigues 2003, Freire et al. 2009), but has also been registered in a transitional area between Caatinga and “campos rupestres” (rocky fields) (Menezes et al. 2011) and in the Atlantic Rainforest biome (Freire 2001). The second and third most abundant diurnal species (T. hispidus andA. cf. ocellifera) are common in the open formations of Brazil (Vitt 1995, Rodrigues 2003).Ameivula cf. ocellifera is a new species widely distributed in the Caatinga (F. Arias, pers. comm.), formerly treated as A. ocellifera in several studies (e.g. Vitt 1995, Ribeiro et al. 2011,Sales et al. 2012). These results agree with the data obtained by Kolodiuk (2005) for the ESEC Seridó, except for A. cf. ocellifera being more abundant than T. hispidus in that study, a fact that might have been the result of a more extensive sampling in the habitat of Herbaceous Vegetation in Open Area (HVOA). New information arising from this study is the presence of L. klugei among the most frequent species, confirming its predominance in open formations (Vitt 1995, Rodrigues 2003, Werneck et al. 2009).

The most frequent nocturnal species was P. periosus, endemic to the Caatinga and widely distributed across this biome at the present time, being found in the states of Alagoas, Pernambuco, Paraiba and Rio Grande do Norte (Freire et al. 2000, 2009). The second most frequent nocturnal species was P. pollicaris, a widespread species in the Caatinga (Vitt 1995, Rodrigues 1986, 2003). These results contradicts those obtained by Maggi (2005), who indicated that P. pollicaris was much more abundant than P. periosus. It is probable that this difference could be related with differences in the physiognomy of the sampled areas.

The relatively common occurrence of H. agrius is a quite relevant novelty, as it was a rare species in other areas of the Caatinga (Vanzolini et al. 1980, Vitt 1995) and relictual in distribution (Rodrigues 2003). On the other hand, H. mabouia, which is a widespread invasive species in urban areas as well as in natural environments belonging to several different biomes, including the Caatinga (Vanzolini et al. 1980, Vitt 1986, 1995, Rodrigues 2003, Rocha et al. 2011), remains unrecorded from the ESEC Seridó (Freire et al. 2009 and this study), a fact worth to be further investigated.

Seasonality represented an important influence on the lizard assemblage of the ESEC, as most of the species showed a higher number of records during the rainy season and a decrease in the dry season, thus confirming the results obtained by Kolodiuk et al. (2010), Ribeiro (2010) andSales et al. (2011a). These authors suggested that this variation may be related to more pleasant temperatures and/or more food availability during the rainy season.

As for habitat usage, the highest richness and frequency of species in the Areas with Rocky Formations (ARF) may be related to the great abundance of this kind of areas in the ESEC Seridó (Freire et al. 2009, Ribeiro & Freire 2010), while the wide variety of available microhabitats, such as leaf litter and rock crevices, propitiate, mainly during the dry season, microhabitats with more pleasant temperatures (Mares et al. 1981).

Habitat usage by the most common species agrees with profiles already described for the ESEC Seridó by Kolodiuk (2005), Maggi (2005), Freire et al. (2009), Kolodiuk et al. (2009,2010) and Ribeiro (2010), as these studies also showed T. hispidus as the most generalist species (Kolodiuk 2005, Ribeiro 2010) and A. cf. ocelliferaoccurring mostly in the Herbaceous Vegetation in Open Area (HVOA) (Kolodiuk 2005). The low values for niche amplitude recorded for T. semitaeniatus, P. periosus and P. pollicaris indicate specialization for the habitat of Areas with Rocky Formations (ARF). Other species lacking autoecological studies in the ESEC Seridó, such asL. klugei and M. heathi, showed high values of niche amplitude and, therefore, make part of the group of generalist species in terms of habitat usage, differing from the results achieved by Vitt (1995).

In spite of a considerable segregation between some pairs of species regarding habitat usage, there was high overlapping among the majority of the species of this assemblage. However, it is possible that divergences in other niche variables may exist, as sympatric species use to be segregated in at least one niche dimension like microhabitat, activity time and diet, or combinations of those variables (Vitt 1995, Werneck et al. 2009).

About microhabitat usage, this study showed that T. semitaeniatuswas a strictly saxicolous species, T. hispidus was present in most of the microhabitats, and A. cf. ocellifera showed terrestrial habits, thus agreeing with the profiles outlined in previous studies performed in the ESEC Seridó (Kolodiuk 2005, Kolodiuk et al. 2009, 2010, Ribeiro 2010, Freire et al. 2009). The arboreal and terrestrial habits of L. klugei and M. heathi, respectively, confirmed profiles already described in other Caatinga site (Vitt 1995).

Phyllopezus periosus and P. pollicaris showed a high fidelity to the habitat of ARF and used the microhabitats of Rock Outcrop (RO), Crack of Rock Outcrop (CRO) and or On Boulder (OB), confirming their saxicolous character already stated in other works (Rodrigues 1986, Vitt 1995, Rodrigues 2003, Maggi 2005). However, the relatively common occurrence of both species in microhabitat categories associated to vegetation contradict the results of Maggi (2005), where justP. pollicaris made significant use of vegetation associated to the ARF habitat. In this case, the differences between the two studies may be related to methodological differences. Besides the rock outcrops, this study considered checking regularly the surrounding vegetation of the ARF habitat, where several records, mainly of P. periosus, were made, suggesting some degree of arboreal habits for this species. This suggestion is supported byin loco observations of trees, more than 5 meters away from the rock outcrops, where individuals were seen roosting more than 2 m above the ground (Figure 3E).

The low overlapping indexes for microhabitat usage, obtained for most of the species pairs, may be considered a relevant factor for the co-occurrence of the lizard species in the studied assemblage. For pairs of species showing high overlapping in this niche dimension, it is possible to infer probable dimensions where segregation occurs. In the case of the tropidurids, for example, the two species differ in the vertical use of the rocky microhabitats, with T. hispidus using a larger vertical microhabitat range (Ribeiro 2010); in addition, the diet and foraging behavior of T. hispidus and T. semitaeniatus overlap under limiting conditions during the dry season, but are segregative factors that may contribute to the coexistence of these species in the wet season (Kolodiuk et al. 2010, Ribeiro & Freire 2011b). In the case of P. periosus and P. pollicaris, Maggi (2005) suggests that a difference in diet composition, enabled by differences in body size and foraging behavior between the two species, is the probable factor allowing the coexistence of them.

The activity periods of the dominant species reported in this study, where the tropidurids showed a wide activity period, being active all day long, with a reduction of activity during the hottest hours, while A. cf. ocellifera presented unimodal activity with a peak during the hottest hours of the day, also confirm data already described for the ESEC Seridó (Kolodiuk 2005,Maggi 2005, Freire et al. 2009, Ribeiro 2010, Ribeiro & Freire 2010), as well as some others performed in other areas of the Caatinga (Vitt 1995, Falcão 2006).

The activity profile recorded in this study for L. klugei differs in part with the profile described for other populations of this species in the Caatinga (e. g. Vitt 1995), because this species was active all day long in the ESEC Seridó. On the other hand, the bimodal profile exhibited by M. heathi in the ESEC, with activity during early morning and late afternoon, corroborates what was described in a study performed in the Cerrado (Sado et al. 2007) and in a study performed in the Atlantic Rainforest (Sales et al. 2009).

The seasonality of the ESEC Seridó affected the activity periods of diurnal lizards, corroborating previous results (Kolodiuk 2005,Kolodiuk et al. 2009, 2010, Ribeiro & Freire 2010, Ribeiro 2010). The lack of activity of the tropidurids andL. klugei in the hottest hours during the dry season may reflect, for example, the strong relation between environmental temperature and body temperature in these species, as all of them are ambush foragers (Rocha & Bergallo 1990, Vitt 1995). Preferential use of shaded environments by tropidurids during the dry season corroborated the results of Ribeiro & Freire (2010). Lygodactylus klugei used mainly shaded environments in both seasons, a trend also described by Vitt (1995). Ameivula cf.ocellifera, on the other hand, used in a preferential way sunny environments during both seasons, thus confirming the condition of an active forager needing to keep elevated body temperatures while active (Vitt 1995, Rocha et al. 2009,Menezes & Rocha 2011, Menezes et al. 2011).


The abundance of the species, and the profiles of time and space usage by the dominant species, corroborate long-term studies previously performed in the ESEC Seridó and suggest the existence of patterns in time and space usage in the lizard assemblage of this ESEC. Seasonal effects are remarkable and interfere mostly in the abundance of active individuals in the field and activity periods of the species. The overlapping in niche dimensions recorded for some pairs of species does not limit the co-occurrence of these, as they tend to be segregated in other variables like diet, activity periods, habitat and/or microhabitat.


We thank the Programa PELD/CNPq-Caatinga: Estrutura e Funcionamento (process n° 521134/01) for logistic support, and the administration and employees of the Estação Ecológica do Seridó – ESEC/IBAMA for allowing research and for the housing provided during the field work. MJM Andrade and EMX Freire received research grants from CNPq, and IBAMA issued the required permit (Permit 206/2006 and Process 02001.004294/03-15).


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Received: December 29, 2012; Revised: August 21, 2013; Received: September 20, 2013

3Corresponding author: Maria Jaqueline Monte de Andrade,

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