In lizards, one of the most important behavioral mechanisms to cope with spatial and temporal variations in thermal resources observed is activity time. The longer a lizard can maintain activity, the more time it has to forage and reach larger adult body size. We studied the behavioral adjustments to different climatic regimens on daily and seasonal scales in three natural populations of the lizard Microlophus atacamensis along a latitudinal temperature and rainfall gradient. We also used Niche Mapper to determinate the amount of thermally suitable time for activity for this species. Abundance and daily activity patterns varied greatly over the year for the three populations. In summer and spring, the daily activity times were greater, and were reduced in fall and winter seasons. In summer, when stressful heat loads should prohibit activity over a midday gap, lizards did not show bimodal patterns of activity. Instead, they move to the cooler intertidal habitat. Abundance and thermal quality in the southernmost coolest site was lower, and the potential annual activity time decreases with latitude. Contrary to expectations, lizards from this locality showed the largest body sizes possibly due to diet and/or time to sexual maturation. Our results indicate that the intertidal habitat is a key factor that influences daily and seasonal activity of M. atacamensis lizards. While this habitat is not climatically optimal for lizards, it allows them to behaviorally extend their activity window and gain access to food in the intertidal areas.
Citation: Sepúlveda M, Sabat P, Porter WP, Fariña JM (2014) One Solution for Two Challenges: The Lizard Microlophus atacamensis Avoids Overheating by Foraging in Intertidal Shores. PLoS ONE 9(5): e97735. https://doi.org/10.1371/journal.pone.0097735
Editor: Paul A. Bartell, Pennsylvania State University, United States of America
Received: October 18, 2013; Accepted: April 23, 2014; Published: May 19, 2014
Copyright: © 2014 Sepúlveda et al. This is an open-access article distributed under the terms of the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.
Funding: This study was supported by funding from Beca Universidad de Chile PG/3/2006 to MS, Fondecyt Grant number 1040783 to JMF, and Fondecyt Grant number 105096 to PS. The funders had no role in study design, data collection and analysis, decision to publish, or preparation of the manuscript.
Competing interests: The authors have declared that no competing interests exist.
One of the principal challenges for animals is to obtain enough food to provide nutrients and energy needed for maintenance, survival, growth, and reproduction . The energy allocated to these processes ultimately depends on the daily and annual energy budget, which in turn depends on activity time . In lizards, it has been demonstrated that the daily and seasonal activity times may be influenced by both endogenous and exogenous environmental factors , . The endogenous rhythms of activity are driven both by circadian and circannual clocks that allow changes in the duration of daily activity across seasons, allowing the lizard to anticipate the upcoming season . However, environmental exogenous factors may mask endogenous rhythms by either increasing or suppressing activity, the most important being ambient temperatures in the field, which influence both daily and seasonal activity patterns , , , . Assuming that lizards are foraging while active, and that food is not limiting in a given environment, changes in daily or seasonal activity times due to spatial and temporal variations in thermal resources influence the daily prey capture rate , , , thus ultimately affecting energy acquisition and the reproductive success of lizards.
Daily and seasonal activity may also lead to specific geographic patterns in growth and body size. Lizards with longer activity seasons are expected to grow faster . For example, in sagebrush lizards, it was found that longer seasonal activity was associated with an increase in individual growth and larger adult body size  (but see ). Therefore, variation in thermal environment, through its effect on thermoregulatory behavior and activity time, may have a profound and direct impact on time budgets of the lizards, and cause some of the observed variation in life histories among widespread populations , , , .
The family Tropiduridae is mostly composed by terrestrial feeders, but some species that dwell in desert coastal areas (with low levels of terrestrial productivity), feed almost exclusively on intertidal zones , . In Chile, two species from the genus Microlophus use this feeding strategy: Microlophus quadrivittatus and M. atacamensis . The geographical range of M. quadrivitattus (from Arica 18°00′S to Antofagasta 20°32′S) falls into an area where the extreme desert reaches the coast and there is practically no annual precipitation (maximum recorded = 2 mm year−1) , whereas the geographical range of M. atacamensis, the subject of this study and southernmost species of the genus, runs 500 km into the so-called Desert Coastal area which presents a gradient of precipitation from 2 mm year−1 in the North (at Antofagasta) to almost 120 mm year−1 in the South (La Serena 29°55′S) . For this species it is reported that the diet of this species is composed both of intertidal (algae and crustacea) and terrestrial (isopoda, coleoptera) prey . The importance of each of these dietary items is associated with spatial and temporal variation in the productivity levels of both habitats, with an increasing proportion of terrestrial items in a north to south gradient , .
The intertidal zone is an unfavorable thermal environment because lizards lose heat quickly by conduction, convection and evaporation when feeding on a wet rock substrate . For that reason, lizards may face a trade-off between feeding and thermoregulation. Because M. atacamensis populations are under different thermal constraints at latitudinal, seasonal and microhabitat scales, a temporal and geographical variability in their thermal biology is expected. Lack of physiological intraspecific variation in thermal biology in M. atacamensis (e.g. selected body temperatures and heating and cooling rates) suggests that lizards may compensate adequately the variations in their thermal environment through a behavioral mechanism instead of physiological adjustment .
Through field observations and using a process-driven mechanistic model (Niche Mapper)  we explored the behavioral adjustments of M. atacamensis to different climatic regimens, and their potential for activity at different temporal and spatial scales. We selected three populations along the entire geographical range of this species. Considering that environmental temperature decreases as latitude increases, we specifically assessed whether daily and seasonal activity patterns are modified with increasing latitude. Associated with this hypothesis, it is expected that body size should decrease in populations that exhibit shorter activity times.
Materials and Methods
Organism and study sites
From July 2005 to April 2006 we studied the abundance and activity patterns in three sites on the northern Chilean coast: Medano (24°37′S; 70°33′W), Zenteno (26°51′S; 70°49′W), and Arrayán (29°41′S; 71°19′W). Climatological data for the study sites are presented in Table 1. Medano and Zenteno are under a coastal desert climatic regime, characterized by less than 2 mm of rain per year . The southernmost locality, Arrayán, in contrast, falls into the per-arid Mediterranean zone. Rainfall in this site averages 120 mm/year. Terrestrial productivity also shows a gradient, with a significant increment of plant cover, from ca. 0% in Medano to 23% in Arrayán . Lizards live along the intertidal zone in a stretch of approximately 150–200 m dominated by flat areas of a mixture of rocks (with heights from 0.2 to 3 m), pebbles, cobblestones, and sand .
For each site, and every four months, the abundance of active M. atacamensis lizards at intertidal and terrestrial areas was assessed by visual counts. On each occasion, and for two consecutive days, censuses data were collected by walking parallel to the shoreline, covering both intertidal and the adjacent terrestrial (supralittoral) substrates. Censuses were made at 0900, 1100, 1300, 1500, and 1700 h, walking on each occasion for one hour and covering approximately 1 km of coast. The maximum number of lizards sighted during a census period was used as a relative index of abundance. This index does not provide a measure of the actual density of lizards, but allows the between-habitats and between-seasons comparison of abundance at a geographical scale . Lizards were differentiated by age class (juveniles or adults), recording their position on intertidal or terrestrial habitats. Air and soil temperatures (Tair and Tsoil) were measured immediately prior and after each census at the beginning and end of the transect.
Daily activity patterns
Simultaneously with the abundance analysis, one observer counted lizards from 0900 to 1800 h in a 1500 m2 area, recording the number of lizards sighted every 30 min. We selected this time window because M. atacamensis is a diurnal lizard that restricts their activity to daytime hours when Tsoil is above 22°C . As above, lizards were differentiated according to age classes (juveniles or adults) and substrate (intertidal or terrestrial habitat). To establish an approximation of thermal conditions of the habitat occupied by lizards, we placed six Tidbit temperature data loggers with an internal temperature sensor (three in the intertidal zone and three in terrestrial zones) at randomly selected microsites for each season and locality. Temperatures in the data loggers were registered every 30 min. Thermal profiles collected from the electronic devices do not differ substantially from copper lizards models exposed to the same conditions, suggesting that Tidbit could be used directly to monitor operative temperatures (Te) . To test if this assumption was true for our model species, in the laboratory we calibrated the tidbits measurements with those of dead lizards placed in a thermal gradient. The results showed that data recorded from electronic devices are highly correlated with temperatures from dead M. atacamensis lizards exposed to identical thermal conditions (r = 0.99).We also calculated the de index, which represents the thermal quality of the habitat, from the lizard's perspective . This index is calculated as the mean of the absolute value of the deviations of Te from selected temperature (Tsel) of the corresponding site and season. It was found that M. atacamensis lizards have a Tsel of 34.3°C, independent of localities or seasons . For this reason, we use this value for thermal quality measurements.
To estimate the maximum duration of daily and annual activity of lizards from the three sites, we used the Niche Mapper model , , to determinate the biophysical effects on the amount of thermally suitable time for activity, under realistic climatic conditions . The microclimate model in Niche Mapper allows the translation from macro to microclimatic environmental variables relevant to the organisms. More details of these models can be found in , , and at [http://www.zoology.wisc.edu/faculty/Por/Por.html].
The microclimate model contains a subroutine for computing solar radiation given a specific date, time, latitude, longitude, slope, and aspect . Time dependent input data consist of monthly 2 m shade air temperatures, wind speed, and relative humidities. These data for the three sites were obtained from the Servicio Hidrológico y Oceanográfico of the Armada de Chile (Table 1). The microclimate model calculates the hourly intensity of solar radiation and the profiles of Tair and Tsoil, wind and humidity above the surface. These data were used for calculating the hottest (maximum sunlight available) and coolest (maximum shade available) microclimates available to the lizards in the rocks for each hour of the day and for each location. Hourly output from the microclimate model for the hottest and coolest above and below ground conditions were used to define the full range of environmental conditions available locally. Time dependent input data used for the microclimate simulations can be found in Tables 1, 2 and 3. The microclimate output conditions were then used as input for the ectotherm model, in addition to various properties of the animal relating to morphological, physical, physiological, food, and behavioral properties .
The ectotherm program uses the results from the microclimate model to determine which hours of the day an ectotherm can stay within its preferred body temperature range. We used this model to examine the frequency distribution of expected daytime body temperature (Tb) of M. atacamensis lizards throughout the year in the three sites. The model assumes that the animal is always active (and exposed to local wind and humidity) when thermal conditions permit. If conditions are too hot or cold for activity, the animal retreats (close to the sea or underground) to a temperature as close to its optimal Tb as possible. Analyses were done separately for wet and dry conditions, simulating both intertidal and terrestrial substrates, respectively. Calculations for the wet substrates assumed a 100% wet surface. Wet and dry reflectivities of local substrates were measured using an ASD portable spectroreflectometer for the energy balance calculations for all habitats. The spectral range of these measurements was 350–2500 nm, approximately 97% of the sunlight reaching the surface of the earth. Rock reflectivities were 21/32% (dark/light) for Medano, 21% for Zenteno, and 16% for Arrayán. Input data for the ectotherm simulations can be found in Table 2.
Live lizards from the three populations were captured during the study period (N = 55 for Medano, N = 50 for Zenteno, and N = 27 for Arrayán). Two measures of body size were registered at each capture: (1) snout-vent length (SVL), which was measured to the nearest millimeter using a caliper, and (2) mass, which was measured to the nearest 0.1 g using a Pesola scale. The analyses were restricted to adults and, because this species exhibits a clear sexual dimorphism in body size , , sexes were analyzed separately. As soon as the measurements were taken the individuals were liberated.
The protocol of capture was done with research permits from the Chilean Agriculture and Livestock Bureau (SAG) (Permit Number 98), and under the approval of the Pontificia Universidad Católica de Santiago Ethics Committee. No specific permissions were required in the study sites because they are within an open access zone of the Atacama Desert coast. Also, M. atacamensis is classified as Vulnerable under the Chilean Hunting Law (DS 5).
The abundance of M. atacamensis was analyzed with a two-way ANOVA , using sites and seasons as factors, with 3 and 4 levels, respectively. Kendall-rank correlations were used to determine whether the mean number of lizards was correlated with Tair or Tsoil. Means of Tair and Tsoil were used to compute this statistic. Thermal conditions during the daily activity patterns (using the de index) were compared among sites and seasons using a two-way ANOVA. Body size data (SVL and mass) was analyzed with a two-way ANOVA, using sites and sex as factors. Normality of the data was checked by Shapiro-Wilk's test of normality and, when necessary, the data were log-transformed. Post-hoc comparisons were performed using a Tukey's honest significance difference test. All comparisons were performed using Statistica 8.0 for Windows .
The abundance of M. atacamensis was significantly different among sites (F2,12 = 14.40, P<0.001), seasons (F3,12 = 9.73, P = 0.002), and for the interactions between these factors (F6,12 = 4.44, P = 0.014). Highest mean values occurred in Medano and Zenteno (at the north and mid geographical range, respectively) compared to the southernmost site (Arrayán) (Fig. 1). In terms of seasonality, fewer individuals were found in winter, compared to the summer. Tair, Tsoil, and Te were higher in summer, related to the other seasons (Table 3).Tair and Tsoil were significantly correlated with the number of lizards observed during the censuses, for the three sites studied (τ = 0.49 and τ = 0.35 in Medano; τ = 0.35 and τ = 0.40 in Zenteno; τ = 0.18 and τ = 0.14 in Arrayán, for Tair and Tsoil, respectively) (all Kendall rank correlation coefficients significant at P<0.001).
Daily and annual activity patterns
Daily activity patterns varied greatly among seasons for the three populations. During summer, lizards emerged from their burrows as early as 0900 h, when Te was above 20°C. Lizards remain active all day, and did not show a clear abundance pattern (Fig. 2). When we finished our observation period (1800 h), we could still observe some individuals above the rocks. Both juveniles and adults emerged at 0900 h, and remained active until 1800 h.
Circles represent Te (measured with Tidbits data loggers).
The activity time was shorter in fall and winter, especially for Medano and Arrayán sites. Lizards' appearance coincided with an increase in Te (above 25°C), showing a unimodal activity pattern. In general, juveniles emerged earlier than adults in the three sites and disappear before them in late afternoon. In spring, daily activity pattern was similar to fall and winter, showing a unimodal activity pattern, with maximal abundances near midday for both juveniles and adults. The activity period in spring months was similar to summer, but lizards emerged around 1000 h for the three sites. Again, juveniles emerged earlier than adults, but disappear before them in the afternoon.
Operative temperature was strongly correlated with the number of observed active lizards, for the three sites studied (τ = 0.62 in Medano; τ = 0.34 in Zenteno; τ = 0.57 in Arrayán) (all Kendall rank correlation coefficients significant at P<0.001, seasons pooled). The deviation of Te from Tsel (de) varied significantly among sites (F2,216 = 9.19, P<0.001), seasons (F3,216 = 35.52, P<0.001), and for the interaction of these two factors (F6,216 = 8.80, P<0.001). Thus in Medano, average de was smallest (i.e. a highest thermal quality) than in the other sites. Seasonally, de index was lowest in summer and highest in winter. No differences were found between spring and fall (Fig. 3). Te varied considerably with time of day for each season and site. In summer, and for all sites, thermal suitability for lizards was high during the day. In contrast, in the other seasons thermal suitability was lower, especially in early morning and late afternoon, and higher at midday hours, when lizards were active.
Microlophus atacamensis also shows geographical and seasonal differences in the use of intertidal and terrestrial habitats. In Medano, lizards show a clear pattern of use of both habitats. Individuals were found in the intertidal zone when Te surpasses 25°C. In winter, when Te almost never exceeds this temperature, lizards remain in the terrestrial areas (Fig. 4). In summer and spring, lizards from Zenteno and Arrayán were found both in the intertidal and terrestrial habitats during the day. In fall, only a few individuals were found in the intertidal zone during a short period of time. In winter, no individuals were found in the intertidal zone for any site.
White bars represent the proportion of individuals in the terrestrial or supralittoral zone; the black ones represent the proportion in the intertidal zone. Maximal abundance in the day was considered as 100%. Circles represent Te (measured with Tidbits data loggers) in the intertidal and terrestrial habitats.
Calculations of core temperature throughout a typical day in different months and hours of day were made for two different body weights (100 g in males and 36 g in females) in each site, which represent the average weights for both sexes' measured levels of activity. Considering that the voluntary thermal minimum and maximum for lizards are 28 and 37°C, respectively (Table 2), constraints on daily and seasonal potential activity times under the dry (terrestrial) and wet (intertidal) conditions were estimated (Fig. 5). As was observed in the field, our simulations largely reflect seasonal variations in activity times in all sites, with winter activity significantly curtailed by temperature. The thermal constraints on lizard activity precluded the occurrence of M. atacamensis in the intertidal habitat in late fall and early winter months, especially for Arrayán site.
Gray contours indicate suitable temperatures (28–36°C) for activity.
Based on the biophysical model, the activity hours for lizards in the three localities are highest in spring and summer months, when the ability to exploit both habitats is enhanced (Fig. 6). However, the activity decreases in fall and winter months, especially in the intertidal habitat. Potential annual activity time decreases with latitude, ranging from 3099 h yr−1 in Medano to 2981 h yr−1 in Arrayán in dry conditions, and also in wet conditions from 2918 to 2860 h yr−1 in Medano and Arrayán, respectively. Limited activity is manifested in reduced opportunities for feeding, which can be assessed by measuring the required foraging rates in each locality and habitat. In northern sites, and in dry conditions, the foraging rate increases because of increased opportunities for activity (Fig. 7). In wet and southern habitats, lizards are compromised in terms of total annual activity hours, but their annual food requirements are reduced. Through the year, foraging rates are generally higher (∼0.1 g h−1) during spring and summer months and lower (<0.07 g h−1) during fall and winter seasons.
Body size (SVL and mass) differed significantly among sites and sexes (Table 4). For SVL comparisons, females were significantly smaller than males in all the sites studied. However, for each sex, lizards from Medano, Zenteno, and Arrayán were similar in size. With regard to body mass, males were heavier than females. In females, body mass of Arrayán lizards was greater than both Medano and Zenteno lizards. Medano and Zenteno lizards were similar in weight. In the case of males, body mass from Medano lizards was smaller than lizards from Zenteno and Arrayán, but similar between Zenteno and Arrayán.
Our results indicate that the latitude and climate are important factors in modulating the activity patterns of M. atacamensis lizards. We predicted that lizards from northern sites should have longer daily and seasonal activity times because they experience a warmer environment. Accordingly, we found a small de and a higher potential annual activity time in Medano, implying that this northern locality offers better quality thermal conditions for the activity of lizards . A decrease in potential activity time in the southernmost site (Arrayán) is explained because the thermal quality of the environment in this locality is lower. It is likely that lizards from this site compensate for the high time cost of thermoregulation by allocating more time to basking than to other activities , which in turn may imply a trade-off between feeding and thermoregulation. An increase in basking time activities can affect foraging time and consequently the energy budget , and ultimately the reproductive success of lizards in high-latitude populations. The abundance of lizards in Arrayán was significantly lower than in Medano and Zenteno, suggesting that in this southern locality the animals were under a higher cost of thermoregulation. Lizards from Arrayán should allocate more time to thermoregulation with a consequently smaller proportion of the time budget allocated to foraging, thus decreasing the energy available for growth and reproduction. It is important to note that the smaller population size in Arrayán compared to Medano and Zentano might be also due to higher predation (e.g. more birds and snakes in a more mesic environment) on adult and juvenile lizards .
We found that these lizards also shift their daily activity times during the year. In summer and spring the daily activity time was longer, and reduced in the fall and winter seasons as expected for diurnal lizards , , . Our biophysical model also revealed similar results, with a longer period of activity in summer and spring and lower in fall and winter, providing good correspondence with empirical data. Similar to the differences among localities, longer daily activity times found in summer and spring could be explained because the de index was lower in these seasons, indicating a high thermal quality for the activity of lizards.
During the fall, winter and spring seasons, lizards showed a unimodal activity pattern, being active around midday when solar radiation and Te were high. This pattern is typical of several species of lizards , . In particular, M. peruvianus (a species that belongs to the M. peruvianus group, as does M. atacamensis) also shows a unimodal pattern of activity during this period of time . Nevertheless, a shift in activity from unimodal to bimodal has been found in several species of diurnal desert lizards in summer , , , generally observed at sites where air and soil temperatures reached risky highest levels. Around midday, lizards retreat into the shade or burrow to avoid overheating, but become active again during the afternoon and thus exhibit a markedly bimodal activity pattern . Traditionally, this daily pattern of activity has been explained as the behavioral response of these animals to the very high levels of air and soil temperatures at that time of day . However, laboratory experiments in some species of lizards demonstrate that summer bimodality is not merely a proximate response of lizards to high levels of soil temperature, but is a clock driven phenomenon mediated by circadian rhythmic changes of plasma melatonin levels , , , which has most probably evolved as a behavioral adaptation to high levels of air temperature occurring predictably around midday , .
Regardless of the mechanism associated with a unimodal/bimodal activity pattern, during summer M. atacamensis faces a stressful heat load in midday hours, which should prohibit activity during these hours. However, they did not show a bimodal pattern of activity, but interestingly they used the behavioral strategy of moving to the intertidal habitat, where temperatures are lower and wind speed on the shore is greater. This strategy of lizards of moving to the intertidal habitat as the temperature rises allows them to engage in continuous daily activity associated with the use of different substrates, extending their activity period close to a source of food, maintaining a similar temperature during the day . Also, this behavior benefits lizards because food and energy requirements in wet habitats are reduced. However, it also represents costs for thermoregulation, because the low substrate and air temperatures in the intertidal habitat increase the heat lost by conduction, substrate radiation and local air temperature due to local substrate evaporation .
Body temperature showed significant variation throughout the year, being lower in fall and winter months . Biophysical simulations using Niche Mapper also demonstrated that food intake and foraging rate were lower during these seasons. Lower Tb in winter compared to summer suggests that in winter lizards are under environmental constraints for thermoregulation and should operate as low-energy systems , . Thus there appears to be a trade-off in choosing the use of terrestrial and/or intertidal habitats by a lizard. In summer when Te in the intertidal habitat is >25°C lizards use this microhabitat, extending their daily activity time and accepting the physiological cost of heat loss (i.e. a decrease in metabolic rate), while in seasons other than summer, the cost of heat loss appears to surpass the benefits and lizards are restricted in their visits to the intertidal habitat. Thus the net ecological benefit establishes the use of different microhabitats and consequently the activity period at seasonal (and geographical) scales.
It is interesting to note that, although northern locations and dry conditions offer a considerable advantage in terms of time spent within optimal limits , the access of lizards to wet habitats give them the advantage of more food, reducing their energy requirements. For these reasons, spatial and temporal differences in the access to the intertidal habitat could affect energy acquisition differentially for populations of M. atacamensis. A latitudinal variation in the diet composition of M. atacamensis was found, with an increase in the proportion of terrestrial items in a north to south gradient . The diet of lizards from Medano (northernmost site) is composed almost exclusively of marine invertebrates and algae, thus lizards from this locality may be under a trade-off between feeding and thermoregulation, which may in turn determine differences in the use of the thermal substrate. Due to the lower Te, except in the warmest months, lizards from Medano are restricted in visits to intertidal zones and this would reduce the ingestion of intertidal prey. This energy constraint might explain the lower body mass found in Medano lizards. Although longer seasonal activity is usually associated with larger body size , we found that lizards (both males and females) from Arrayán, and not from Medano, were larger.
However, there are other possible contributing factors for the lack of relationship between activity duration and body size which should be considered. Together with a variation in temperature along the gradient there is a consistent increase in rainfall to the south, which promotes productivity. Lower abundance of terrestrial invertebrates available for lizards may force northern lizards to exploit intertidal feeding because of the lack of insects in the extremely dry supralittoral zone. Thus even with more activity time they may be food limited, which could either stunt growth resulting in smaller body size or accelerate sexual maturation , , which could also account for the observed smaller body sizes. Another hypothesis is that longer times at higher body temperature lead to higher metabolic rates and therefore more food and water are needed to sustain those higher rates . In fact, Maritza Sepúlveda (unpublished data) found that lizards from Medano exhibited higher metabolic rates than lizards from Zenteno and Arrayán. If food and/or water are limited, greater metabolic expenditures in the face of limited food could also affect the potential growth. Finally, due to the lower temperature and a shorter activity season, lizards from Arrayán may need to extend the time of sexual development, resulting in larger body size at sexual maturity .
The activity pattern of M. atacamensis differs between juveniles and adults. We found that juveniles emerge before adults and become inactive earlier in the afternoon. At least three not mutually exclusive explanations can be hypothesized. First, because smaller lizards heat up quickly and larger lizards cool down slowly , , it has been suggested that body size should play an important role in determining the activity pattern of large versus small lizards . Such an effect has been argued to explain why during the day juveniles of desert reptiles are active earlier and adults later . Second, it is possible that intraspecific social interactions lead to a temporal segregation between age classes. In this vein, a highly territorial behavior of adults and aggressive behavior towards juveniles was found , so it is possible that juveniles emerge earlier to minimize interactions with adults. Finally, some preliminary data suggest that juveniles and adults may be exploiting different classes of prey. José Miguel Fariña (unpublished data) found a relatively high proportion of Diptera in the diet of juvenile lizards compared to the diet of adults, which suggests that there may be a lack of overlap in food resources.
In conclusion, we found that the thermal environment is a key factor that modulates the daily and seasonal activity of M. atacamensis lizards, influencing their abundance, patterns of activity, foraging rates and body size. Lack of some thermal physiological adjustments among populations of this species  indicates that M. atacamensis mostly relies on behavioral strategies to cope with spatial and temporal variation in the thermal environment. The cost/benefit relationship appears to be critical in the use of the intertidal habitat by a lizard, representing a trade-off between thermoregulation and feeding. While the use of intertidal habitat does not offer high quality thermal conditions, it allows them to extend behaviorally their activity window and gain access to food in the intertidal areas. Because its use of intertidal habitat means that this species is not required to display a bimodal pattern, it will be interesting to test whether or not this species exhibits a bimodal pattern controlled by endogenous temporal programs under stressful thermal conditions. This kind of information will add to our understanding of the underlying evolutionary causes of the lizard's circadian system.
We thank María Victoria Reyna, Andrea O'pagina, Marcela Vidal, Eduardo Soto, Paulina Ossa-Zazzali, Manuel Valdés, Diego Hernández and Sandra González for field assistance and to Lafayette Eaton for language corrections. We also appreciate helpful suggestions from Paul Bartell and Augusto Foà on the manuscript. Michael Bergquist assisted with the model calculations and plots. We gratefully acknowledge the Meteorology Department of the Servicio Hidrológico y Oceanográfico of the Armada de Chile (SHOA) for the meteorological data.
Conceived and designed the experiments: MS PS JMF. Performed the experiments: MS WP JMF. Analyzed the data: MS PS WP JMF. Contributed reagents/materials/analysis tools: MS WP JMF. Wrote the paper: MS. Obtained permission: JMF. Designed the software used in analysis: WP.
- 1. Nagy KA, Huey RB, Bennett AF (1984) Field energetics and foraging mode of Kalahari lacertid lizards. Ecology 65: 588–596.
- 2. Adolph SC, Porter WP (1993) Temperature, activity, and lizard life histories. Am Nat 142: 273–295.
- 3. Winne CT, Keck MB (2004) Daily activity patterns of Whiptail Lizards (Squamata: Teiidae: Aspidoscelis): a proximate response to environmental conditions or an endogenous rhythm?. Funct Ecol 18: 314–321.
- 4. Kerr GD, Bottema MJ, Bull CM (2008) Lizards with rhythm? Multi-day patterns in total daily movement. J Zool 275: 79–88.
- 5. Bertolucci C, Leorati M, Innocenti A, Foà A (1999) Circannual variations of lizard circadian activity rhythms in constant darkness. Behav Ecol Sociobiol 46: 200–209.
- 6. Porter WP, Mitchell JW, Beckman WA, De Witt CB (1973) Behavioral implications of mechanistic ecology. Oecologia 13: 1–54.
- 7. Avery RA (1982) Field studies of body temperatures and thermoregulation. In: Gans C, Pough FH, editors. Biology of reptiles 12. Academic Press, NY. pp 93–166.
- 8. Huey RB (1982) Temperature, physiology, and the ecology of reptiles. In: Gans C, Pough FH, editors. Biology of the Reptilia 12. Academic Press, NY. pp. 25–91.
- 9. Grant BC, Dunham AE (1990) Elevational covariation in environmental constraints and life histories of the desert lizard Sceloporus merriami. Ecology 71: 1765–1776.
- 10. Grant BW, Porter WP (1992) Modeling global macroclimatic constraints on ectotherm energy budgets. Amer Zool 32: 154–178.
- 11. Sears MW (2005) Geographic variation in the life history of the sagebrush lizard: the role of thermal constraints on activity. Oecologia 143: 25–36.
- 12. Dunham AE, Grant BW, Overall KL (1989) Interfaces between biophysical and physiological ecology and the population ecology of terrestrial vertebrate ectotherms. Physiol Biochem Zool 62: 335–355.
- 13. Adolph SC, Porter WP (1996) Growth, seasonality, and lizard life histories: age and size of maturity. Oikos 77: 267–278.
- 14. Donoso-Barros R (1966) Reptiles de Chile. Ediciones de la Universidad de Chile, Santiago, Chile. 458 p.
- 15. Wikelski M, Wrege PH (2000) Niche expansion, body size, and survival in Galápagos marine iguanas. Oecologia 124: 107–115.
- 16. Ortiz JC (1980) Revisión taxonómica del género Tropidurus en Chile. Actas de la Primera Reunión Iberoamericana de Zoología de Vertebrados. Ediciones del Ministerio de Universidades e Investigación, La Rábida, España. pp. 355–377.
- 17. di Castri F, Hajek H (1976) Bioclimatología de Chile. Editorial Universidad Católica de Chile, Santiago, Chile. 129 p.
- 18. Fariña JM, Sepúlveda M, Reyna MV, Wallem KP, Ossa-Zazzali PG (2008) Geographical variation in the use of intertidal rocky shores by the lizard Microlophus atacamensis on the Atacama Desert coast. J Anim Ecol 77: 458–468.
- 19. Fariña JM, Castilla JC, Ojeda FP (2003) The “idiosyncratic” effect of a “sentinel” species on contaminated rocky intertidal communities. Ecol Appl 13: 1533–1552.
- 20. Catenazzi A, Carrillo J, Donnelly MA (2005) Seasonal and geographic eurythermy in a coastal peruvian lizard. Copeia 2005: 713–723.
- 21. Sepúlveda M, Vidal M, Fariña JM, Sabat P (2008) Seasonal and geographical variation in thermal biology of the lizard Microlophus atacamensis (Squamata:Tropiduridae). J Therm Biol 33: 141–148.
- 22. Porter WP, Mitchell JW (2006) Method and system for calculating the spatial-temporal effects of climate and other environmental conditions on animals. http://www.warf.org/technologies.jsp?ipnumber=P01251US.
- 23. Vidal M, Ortiz JC, Labra A (2002) Sexual and age differences in ecological variables of the lizard Microlophus atacamensis (Tropiduridae) from Northern Chile. Rev Chil Hist Nat 75: 283–292.
- 24. Díaz JA, Carrascal LM (1991) Regional distribution of a Mediterranean lizard: influence of habitat cues and prey abundance. J Biogeogr 18: 291–297.
- 25. Vitt LJ, Sartorius SS (1999) HOBOs, Tidbits and lizard models: the utility of electronic devices in field studies of ectotherm thermoregulation. Funct Ecol 13: 670–674.
- 26. Hertz PE, Huey RB, Stevenson RD (1993) Evaluating temperature regulation by field-active ectotherms: the fallacy of the inappropriate question. Am Nat 142: 796–818.
- 27. Kearney M, Porter WP (2004) Mapping the fundamental niche: Physiology, climate, and the distribution of a nocturnal lizard. Ecology 85: 3119–3131.
- 28. McCullough EC, Porter WP (1971) Computing clear day solar radiation spectra for the terrestrial ecological environment. Ecology 52: 1008–1015.
- 29. Zar JH (1999) Biostatistical analysis, 4th edition. Prentice Hall, New Jersey, USA. 663 p.
- 30. StatSoft Inc. (2001) STATISTICA (data analysis software system).
- 31. Adolph SC (1990) Influence of behavioral thermoregulation on microhabitat use by two Sceloporus lizards. Ecology 71: 315–327.
- 32. Grant BW (1990) Trade-offs in activity time and physiological performance for thermoregulating desert lizards, Sceloporus merriami. Ecology 71: 2323–2333.
- 33. Sinervo B, Adolph SC (1994) Growth plasticity and thermal opportunity in Sceloporus lizards. Ecology 75: 776–790.
- 34. Gunderson AR, Leal M (2012) Geographic variation in vulnerability to climate warming in a tropical Caribbean lizard. Funct Ecol 26: 783–793.
- 35. Labra A, Soto-Gamboa M, Bozinovic F (2001) Behavioral and physiological thermoregulation of Atacama desert-dwelling Liolaemus lizards. Ecoscience 8: 413–420.
- 36. Niewiarowski PH (2001) Energy budgets, growth rates, and thermal constraints: toward and integrative approach to the study of life-history variation. Am Nat 157: 421–433.
- 37. Foà A, Monteforti G, Minutini L, Innocenti A, Quaglieri C, et al. (1994) Seasonal changes of locomotor activity patterns in ruin lizards Podarcis sicula. Behav Ecol Sociobiol 34: 267–274.
- 38. Díaz JA, Cabezas-Díaz S (2004) Seasonal variation in the contribution of different behavioural mechanisms to lizard thermoregulation. Funct Ecol 18: 867–875.
- 39. Grant BW, Dunham AE (1988) Thermally imposed time constraints on the activity of the desert lizard Sceloporus merriami. Ecology 69: 167–176.
- 40. Bertolucci C, Foà A, Van't Hof TJ (2002) Seasonal variations in circadian rhythms of plasma metalonin in ruin lizards. Horm Behav 41: 414–419.
- 41. Foà A, Bertolucci C (2003) Toward a seasonal model of the circadian system: The case of ruin lizards. Front Biosci 8: s236–242.
- 42. Ellis DJ, Firth BT, Belan I (2007) Circadian rhythms of locomotor activity and temperature selection in sleepy lizards, Tiliqua rugosa. J Comp Physiol A: 695–701.
- 43. Foà A, Bertolucci C (2001) Temperature cycles induce a bimodal activity pattern in ruin lizards: Masking or clock-controlled event? A seasonal problem. J Biol Rhythms 16: 574–584.
- 44. Kearney M, Shine R, Porter WP (2009) The potential for behavioral thermoregulation to buffer “cold-blooded” animals against climate warming. PNAS 106: 3835–3840.
- 45. Sears MW, Angilletta MJ (2004) Body size clines in Sceloporus lizards: proximate mechanisms and demographic constraints. Integr Comp Biol 44: 433–442.
- 46. Wikelski M, Carrillo V, Trillmich F (1997) Energy limits to body size in a grazing reptile, the Galápagos marine iguana. Ecology 78: 2204–2217.
- 47. Tracy CR (1999) Differences in body size among chuckwalla (Sauromalus obesus) populations. Ecology 80: 259–271.
- 48. Angilletta MJ Jr (2001) Variation in metabolic rate between populations of a geographically widespread lizard. Physiol Biochem Zool 74: 11–21.
- 49. Carothers JH, Marquet PA, Jaksic FM (1998) Thermal ecology of a Liolaemus assemblage along an Andean altitudinal gradient in Chile. Rev Chil Hist Nat 71: 39–50.
- 50. Cowles RB, Bogert CM (1944) A preliminary study of thermal requirements of desert reptiles. Bull Am Museum Nat Hist 83: 261–296.