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Influencia de los factores bioticos y abioticos sobre la estructura de las cuiseras de Microcavia australis.

Influence of biotic and abiotic factors on the structure of burrows of the cavy microcavia australis.

INTRODUCTION

The majority of rodents live in systems of galleries. Burrows are used for nesting, food storage, and hibernating, and provide rodents with shelter from predators during their surface activity (King, 1984; Reichman and Smith, 1987; Kinlaw 1999). Most desert rodents escape the excessive heat imposed by high solar radiation, and high air and soil temperature by remaining below ground in their burrows during the heat of the day (Ghobrial and Nour, 1975). Underground refuges, with their relatively stable microclimate, afford small animals protection from extreme temperatures on the surface (Kucheruk, 1983). Other authors suggest for Dipodomys spectabilis and D. compactus a relationship between their burrow architecture and abiotic factors such as air and soil temperature, surface-wind velocity, relative humidity and precipitation (Kay and Whitford, 1978; Best, 1988; Baumgardner, 1991). Orientation of holes was found to be not randomly distributed and seems to be related to environmental factors such as sunlight and prevalent direction of cold winds (Kay and Whitford, 1978; Best, 1988; Baumgardner, 1991). On the other hand, the various functions of burrows are associated with their complex structure represented by a number of functionally different chambers connected by a tunnel system (Shenbrot et al., 2002). Satellite burrows could be distinguished from main burrows by their location close to the foraging area where animals can hide when threatened (Armitage, 1988; Branch et al., 1994). The higher number of entrances is important for animals to hide from predators (Ebensperger and Bozinovic, 2000a). Predation risk would be related to the structure of vegetation. Ebensperger and Hurtado (2005) describe a differential effect of shrubs and herbaceous plants on the vigilance behavior of Octodon degus linked to the costs and benefits of each type of plant cover. Shrubs provide higher vertical protection than herbaceous plants, which in turn provide lateral cover but visually obstruct detection of predators and conspecifics, hindering escape.

Individuals of Microcavia australis live in systems of galleries that they actively build on highly compact to soft soils with high organic contents; however, this cavy shows no characteristic morphological adaptations such as claws or developed incisors typical of species that burrow in hard soils (Nowak and Paradiso, 1983; Tognelli et al., 2001). This cavy has diurnal habits and a social structure made up of several females, one or a few males, and the young and juveniles (Rood, 1967 and 1972; Redford and Eisenberg, 1992; Tognelli et al., 1995; Taraborelli and Moreno, accepted). In the Monte desert, burrows of M. australis reach their highest density in the mesquite community, under Prosopis chilensis and/or P. flexuosa trees with arched branches touching the soil (Rood, 1967; Tognelli et al., 1995; Campos, 1997), and according to Contreras and Roig (1979) they present numerous entrances, approximately 26 per burrow. Cavies do not need the burrow for their daily forage for food, but use it as shelter during relatively long periods of time. The response of these cavies to predators like foxes was to escape toward their satellite burrows, showing strong fidelity to them (Contreras and Roig, 1979). Burrow systems are also presumably used for sleeping at night, napping during the day, parturition and litter rearing, group nesting (social thermoregulation) and avoiding inclement weather (Ebensperger et al., 2006; Taraborelli and Moreno, accepted).

Torres et al. (2003) determined that environment factors such as incidence of the sun, cold winds, and water drainage on the surface would be determinant in the architecture of burrows built by the red vizcacha rat (Tympanoctomys barrerae). M. australis possibly makes an adjustment in burrow construction in response to environment factors. Therefore the objective was to determine the influence of biotic and abiotic factors on the structure of burrows used by the cavy M. australis. We compared the structure and use of gallery systems of cavies between two habitats (El Leoncito and Nacunan) with different climate conditions, plant cover and predation risk (Table 1) to test whether there are habitat-dependent differences in the architecture and microclimate of the burrows, and to relate burrow structure to some climate factors (e.g. predominant cold or warm winds, insolation, etc.). Predictions proposed would be that at both sites burrow architecture will depend on climate factors, size of plant patches and predation risk. For example, at Nacunan cold winds will negatively affect the layout of burrows, resulting in fewer holes aligned with the direction of the wind. At El Leoncito, a cold site, warm winds will positively affect the layout of burrows, resulting in more holes aligned with the direction of the wind. And, at both sites, the sun incidence will have a negative influence in summer, but a positive one in winter, with less or more holes being opened in a northward direction. Burrows will afford a stable microclimate at both sites, as temperature inside the burrows will be lower than soil temperature at the hottest time of the day. On the site with higher predation risk and cover that visually obstruct detection of predators, Nacunan, there will be more holes in main burrows and more satellite burrows to provide shelter from predators.

MATERIALS AND METHODS

Study areas

The study was carried out in two populations in the Monte desert. One population of M. australis is located in the semiarid Monte desert, in the Man and Biosphere Reserve of Nacunan (34[degrees] 2' S, 67[degrees] 58' W, 12 300 ha, 540 m a.s.l.) in the center west of Mendoza Province (Ojeda et al., 1998). Soils are sandy clay, deep; the surface soil is soft and relatively steady (Tanquilevich, 1971; Abraham, 2001; Table 1). The climate is semiarid, warm and dry. Approximately 50% of precipitations occur in the summer months (Cabrera, 1976; Estrella et al., 2001; Table 1). The mesquite community is the habitat preferred by M. australis, because of its structural complexity and the food supply it provides (Campos, 1997; Taraborelli, 2006). This community is composed of three plant layers: the tree layer, dominated by Prosopis flexuosa, the shrub layer, and the herbaceous layer (Roig, 1971). The second population is located in the arid Monte (scrubland) of El Leoncito National Park (31[degrees] 47' S, 69[degrees] 17' W; 76 000 ha), in the southwest of San Juan Province (Marquez, 1999). Cienaga del Medio (2484 m a.s.l.) is the habitat preferred by M. australis at El Leoncito. In this locality soils are sandy and present the typical desert varnish on the surface (Bracco and Contreras, 2000; Table 1). The climate is arid, cold and dry, with marked diurnal, nocturnal and seasonal temperature ranges (winter -4-20 [degrees]C, summer 8-32 [degrees]C; Bracco and Contreras, 2000; Marquez and Dalmasso, 2003). Precipitations are in the form of snow and hail and reach 75 mm in winter and in the form of rain and lower than 10 mm in summer (Le Houerou, 1999; Marquez et al., 2000; Marquez and Dalmasso, 2003; Table 1). Predominant winds are dry and warm from the NW (Bracco and Contreras, 2000; Table 1). In Cienaga del Medio there occurs a shrubland of Larrea nitida with low cover, and the herb layer is lower than 10 cm in height (Marquez et al., 2000; Marquez and Dalmasso, 2003; Taraborelli, 2006).

Records of predators were searched and taken from footprints, feces and aegagropiles (Taraborelli et al., in revision). Also the records were from direct observations during the day (8:00-20:30 hrs) during 7-11 days at three times of the year (November-February, April-August and September March) from 2003 through 2005. The ratios of predators to cavies were calculated for each time of the year, and then Taraborelli et al. (in revision) estimated the mean and standard error for all data. At Nacunan, diurnal raptors were Buteo polyosoma and Milvago chimango; and mammalian carnivores were Lycalopex gymnocercus, Galictis cuja, Conepatus chinga and Felis catus. Predators recorded throughout the year at El Leoncito were crepuscular and nocturnal mammalian carnivores; such as Lycalopex sp. (records of Lycalopex culpaeus are the highest) and P. concolor. Diurnal raptors recorded were Athene cunicularia, Geranoaetus melanoleucus, Buteo polysoma, Falco femoralis, Falco sparverius and Circus cinereus (Taraborelli et al., in revision).

Characterization of burrows

We considered the compound structure with several entrances to the galleries, close to one another and connected by active trails, as the main burrow. Main burrows were generally guarded by patches of vegetation and inhabited by a social group. Only the main burrows were used continually by the cavies during the night (Ebensperger et al., 2006). Satellite burrows have a few entrances to the galleries, are at great distance from the vegetation, and are not stably occupied by the cavies.

Condition of burrow holes (active or inactive) was determined, inactive holes were recognized by the presence of spider webs, or for being covered with leaves or earth, and active holes were identified by signs such as fresh excrements, urine and footprints. Areas and number of active and inactive holes were determined for main and satellite burrows. Orientation (N, E, W, S, SE, SW, NE and NW) was defined for all holes. Height of active holes was recorded, and for the galleries, depth of the first tunnel section up to the first tunnel forking, tilt (Fig. 1) and inner temperature at 50 cm from the entrance. We used the methodology applied by Hoogland (1995) and Torres et al. (2003), and observed and recorded the same burrow systems at different times of year during 20032005. Temperature records were established using a thermometer (0-50 [degrees]C), during three days on each trapping occasion (morning, midday, afternoon, evening), and also measurements of surface soil temperature and environment temperature were made to enable comparisons to be drawn. Environmental temperature was recorded at 1.5 m from the ground. Size of plant patches, plant species present and cover (%) on burrows (Hays et al., 1981; Matteucci and Colma, 1982) were recorded for each plant layer (herb, shrub and tree layers) affording protection to burrows, for comparison with plant availability in the environment. For this purpose, we used a method of strip transects divided into rectangular segments (Matteucci and Colma, 1982) randomly setting up ten 50-m long transects, covering the whole site area. These samplings were performed at three times of the year: time of food abundance (November-February), time of food shortage (April-July), and reproductive season (September-October) for each study site.

[FIGURE 1 OMITTED]

Statistical analysis

ANOVA with repeated measures in time was used to determine existing differences in both number of holes and burrow area among times of the year (time of food abundance or shortage, reproductive season) for the different kinds of burrows (main and satellite). The different kinds of burrows were included as a factor with two levels during the analyses. The same method was used to compare mean tilt and mean depth of burrow tunnels between sites (El Leoncito and Nacunan) and among times of the year. It was also used at both sites to check for differences in mean temperature records (environment, soil and inside the galleries) between times of the year and periods of the day (morning, midday, afternoon, evening). Post ANOVA tests (Tukey test, p<0.05) were performed among the variables considered. Results are shown as sampling mean [+ or -] standard error. Results are shown as sampling mean [+ or -] standard error. Circular Statistics (Batschelet, 1981) was used to verify whether distribution of active holes in burrows at Nacunan and El Leoncito was at random (Rayleigh test). The Watson-Williams test was employed to determine whether there were differences in the orientation of active burrow holes between sampled sites. It was established whether orientation of burrow holes differed significantly from that of inactive holes at Nacunan and at El Leoncito using the Pairwise Chi-Square Test. Circular Statistical analysis was also used by Torres et al. (2003). The depth up to which the sunbeams reach inside the galleries at midday in winter and summer was determined by trigonometric calculations. Such theoretical calculations were made for both sites, which are located at different latitudes. Every calculation was obtained by relating the angle of the sun at midday to gallery depth, for two times of the year (winter and summer) with two different inclinations of the Earth's axis. The X2 test was used to compare the cover of plant species present in the burrows and in the study area for both sites. Pearson Residuals (r=fobs-fexp/Vfexp) were used to test for differences between frequencies.

RESULTS

A total of 18 main and 13 satellite burrows were characterized at Nacunan, in a 2.7-ha plot, and 12 main and 3 satellites burrows at El Leoncito, in a 2.1-ha plot. All the holes were shielded by patches of vegetation (shrubs, herbs, trees) in both sites. At Nacunan, satellite burrows had lower number of holes than main burrows (Table 2; F=85.56; p<0.0001; df=1; N=31). Also the area covered was smaller for satellite burrows (Table 2; F=85.56; p<0.0001; df=1; N=31). At El Leoncito it was possible to locate satellite burrows with a single hole, some near the plant cover, at a distance of 1-3.5 m, and others farther away, at 5-7 m. Main burrows were more numerous than satellite burrows (F=8.48; p=0.0048; df=1; N=15; Table 2). The average number of holes per main and satellite burrow at El Leoncito was significantly lower than it was at Nacunan (main burrow: F=98.31; p<0.0001; df=1; N=31; satellite burrow: F=6.9; p=0.039; df=1; N=16; Table 2). On both sites, the number of holes per burrow remained constant throughout the year.

The area of plant patches covered was smaller at El Leoncito than at Nacunan (F=53; p<0.0001; df=1; N=31, El Leoncito 54.61 [+ or -] 3.1 [m.sup.2], Nacunan 102.05 [+ or -] 6.52 [m.sup.2]). Significant differences were found in the cover of plant species present in the burrow and in the study area ([X.sup.2]=95.35; p<0.0001; df=17; N=31). For example at El Leoncito, the only shrub present, Larrea nitida, occurs on the burrows in a much higher percentage than in the entire environment (99.9% versus 24.7%). At Nacunan, plant species showing higher cover on the burrow than in the area are herbs such as Lecanophora ecristata and Parietaria debilis, and those showing lower cover on the burrow than in the area are sub-shrubs like Acantholippia seriphioides and Verbena aspera, the remaining species occur in the same proportions in both burrows and area. The mean number of plant species forming the refuge at Nacunan was 5.3 [+ or -] 0.28, always including the presence of all three plant layers (tree, shrub and herb layers). At El Leoncito only one shrub species afforded cover to the burrows, namely L. nitida.

With respect to the design of galleries, their tilt angle was significantly higher at Nacunan than at El Leoncito (Table 2; F=36.77; p<0.0001; df=1; N=46), and in no case did they show differences throughout the year (F=0.25; p=0.7826; df=2; N=46), or between orientations of burrow holes (F=0.77; p=0.6139; df=7; N=46). The depth of galleries was significantly greater at Nacunan compared to El Leoncito (Table 2; F=20.46; p=0.0001; df=1; N=46). No differences in depth were found between orientations of burrow holes for either site (F=1.72; p=0.1021; df=7; N=46). Height of holes was equal for both sites (Table 2). At Nacunan, midday sunbeams arrive in winter at an angle of 32[degrees] 58' coming into the galleries up to 48.86 cm; whereas in summer midday sunbeams do not enter the burrows directly (78[degrees] 58') because of their inclination (23[degrees]), penetrating only 5.8 cm into them (Fig. 1). At El Leoncito, midday sunbeams in winter fall at an angle of 35[degrees] 13', reaching a depth of 27.74 cm into the gallery that has a tilt angle of 18[degrees]; at summer midday hours the sunbeams would arrive at an angle of 81[degrees] 13' and would penetrate up to 4.38 cm into the gallery.

There were differences in the orientation of active burrow holes between the sites sampled (Watson-Williams test, F= 157.21; p<0.0001; N=46). At Nacunan, the orientation distribution of active burrow holes is not homogeneous; holes are most frequently easterly-oriented (mean angle of orientation 88[degrees] 01'[+ or -] 8[degrees] 15'; Rayleigh test of uniformity p<0.0001; N=31; Table 2). At El Leoncito, active burrow holes are not homogeneously distributed either, most of them are oriented toward the northwest (mean angle 333[degrees] 33'[+ or -] 10[degrees] 37'; Rayleigh test of uniformity p<0.0001; N=15; Table 2).

At El Leoncito, temperature within the burrows differs from the soil temperature at midday and in the afternoon (F=3.56; p=0.0024; df=6; N=46; Fig. 2B), and only at midday at Nacunan (F=3.13; p=0.0065; df=6; N=46; Fig. 2A).

DISCUSSION

External factors would be influencing the structure and microclimate of burrows used by the cavy Microcavia australis. Among the biotic factors that might affect burrow structure would be the risk of predation. At Nacunan, the number of holes per satellite and main burrow was significantly higher than at El Leoncito. Satellite burrows were clearly distinguished from main burrows because they presented at Nacunan 2-3 holes per burrow and were one third of the area covered by main burrows; and because they were not stably occupied by cavies. At El Leoncito satellite burrows had only one hole. At any rate they would have the same function on both sites, a refuge from predators. The highest predation risk occurs at Nacunan, and comes from raptors, as these predators were recorded from morning to afternoon. Mammalian carnivores, instead, would be overlapping in the evening, and records of these predators were few (Taraborelli et al., in revison). Only Galactis cuja (Mustelidae, Carnivore) may be able to penetrate the burrows because these carnivores have an elongated body, as described by Taraborelli (2006) for Nacunan. The higher number and development of main and satellite burrows at Nacunan is likely related to the higher risk of predation by raptors that overlap during the period of activity of cavies, as well as to the risk of ferret attacks (Taraborelli, 2006). Predation risk would be related to vegetation structure. At Nacunan, the individuals displayed their behavioral patterns in the burrow area, beneath the cover provided by trees, shrubs and herbaceous plants, where shrubs and trees would afford vertical protection from raptors, but herbaceous plants would obstruct visual detection of terrestrial mammalian predators and of the shadow of raptors on the ground (Taraborelli et al., 2008). At El Leoncito, the shrub Larrea nitida is the only species present in the burrows, reaching a much higher percentage than in the whole environment (99.9% to versus 24.7%). At Nacunan all three plant layers (tree, shrub and herb layers) are always present, with an average number of 5-9 plant species forming the refuge. Taraborelli et al. (2008) described that cavies responded to a threat by fleeing toward the burrow at greater speed, they reacted at a lower distance from predators, and the latency time until the first antipredator response was longer than in indi viduals from El Leoncito. The vision of cavies would be more impaired by shrubs and herbaceous plants at Nacunan (Taraborelli et al., 2008). Contreras and Roig (1979) have reported that sometimes the antipredator response of M. australis was to take refuge in the nearest satellite burrows rather than in their own burrow systems. When confronted with the fake predators, at both sites the cavies fled towards the burrow and/or hid in the galleries (Taraborelli et al., 2008). Ebensperger and Bozinovic (2000a) suggested that a higher number of entrances would be important for animals to hide more quickly from potential predators. Satellite burrows of Lagostomus maximus and Marmota flaviventris could also be distinguished from main burrows by their location close to the foraging area, where animals can hide when threatened (Armitage, 1988; Branch et al., 1994). Main burrows of M. australis were inhabited by a social group and used continually during the night for resting, napping during the day, parturition and litter rearing, and group nesting (social thermoregulation; Ebensperger et al., 2006; Taraborelli and Moreno, accepted). Use of the refuge would increase survival of the individuals in the presence of a predator, and if the refuge were also the nesting site it would directly increase the fitness of rodents (Kramer and Bonenfant, 1997; Sundell and Ylonen, 2004).

[FIGURE 2 OMITTED]

Burrow architecture could be affected by some abiotic factors such as air and soil temperature, surface-wind velocity, and sunlight. Burrows would provide a stable microclimate for the cavies. On both sites burrows would function as a shelter from the environment, as temperature within the burrows is lower than soil temperature at the hottest time of the day (6 [degrees]C at El Leoncito and 10 [degrees]C at Nacunan). Soil temperature would directly affect the activity of cavies, more than does environment temperature. In other rodents, both fossorial and semifossorial, such as Pappogeomys castanops, Octodon degus, Meriones crassus and Tympanoctomys barrerae, burrows would also be used to avoid extreme temperatures and predators; moreover, air moisture in the burrows is higher than environmental moisture (Hickman, 1977; Ebensperger and Bozinovic, 2000b; Ebensperger, 2001; Shenbrot et al., 2002; Torres et al., 2003). Temperature stability inside the burrows could be due to the orientation of active holes, which are easterly oriented at Nacunan, thus avoid ing winds from the S and SE (Estrella et al., 2001), that would diminish the inner temperature of burrows. The holes are northerly oriented at El Leoncito, receiving the dry and warm winds from the NW (Bracco and Contreras, 2000) that would maintain the inner temperature of burrows, softening the temperature range in the open. The sun would also have an effect on these orientations because in the morning hours its rays fall directly from the E and N, causing temperatures within burrows not to fall below the environment temperature. In this sense, El Leoncito is a place with harsher climate, strong temperature ranges for its being at 2484 m a.s.l., with a longer period of low temperatures that extends from autumn to spring inclusive (Taraborelli, 2006). Therefore, El Leoncito may be a more stressful place during winter compared to Nacunan. In the burrows of Tympanoctomys barrerae, distribution of holes is also positively influenced by the incidence of the sun from the northern sector, with a higher number of holes located towards the N, NE and NW, and negatively affected by the cold southern winds, there being less holes with S and SE orientation (Torres et al., 2003). In the burrows of Spalacopus cyanus, holes are also oriented towards the NW and W, and none towards the S (Reig, 1970). Due to the tilt angle of burrow galleries on both sites, the sun does not reach higher depth into the galleries at midday in the coldest season (winter) than in the warmest season (summer). The sun enters some 6 to 9 times deeper into the galleries in winter, which would help maintain the inner temperature of burrows in the coldest season. Another burrowing species (T. barrerae) seems to present the same pattern of direct incidence of the sun into the tunnels in winter; these tunnels have a tilt angle of 19[degrees]-20[degrees] (Torres et al., 2003).

External factors, including abiotic factors such as wind, temperature, and sunlight during summer and winter as well as biotic factors, like predation risk and type of plant patches over the burrow, would influence the structure and microclimate of the burrows of M. australis. Burrows would also provide a refuge from predators. Another factor that could influence burrow structure is the productivity of the environment, but this would require further study.

ACKNOWLEDGMENTS

This study was partially financed by CONICET, PICT N[degrees] 03281 and PIP 02884. The authors wish to express their thanks in the first place to A. Srur, P. Moreno, park ranger M. Martinez, M. C. Gonzalez, M. F. Carballido and V. Bauni for their cooperation in the field. To N. Horak for translating the manuscript into English. To Dr. R. Ojeda and M. Martella for the literature provided and the corrections. To Dr. E. Martinez Carretero for identification of the vegetation.

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Paula Taraborelli (1), Natalia Borruel (1), Ana J. Sandobal (2) and Stella Giannoni (3)

(1) Grupo de Investigaciones de la Biodiversidad, Instituto Argentino de Investigaciones de Zonas Aridas, CONICET. CC507, 5500 Mendoza, Argentina [Correspondence: P. Taraborelli <paulataraborelli@gmaiLcom>]. (2) Parque Nacional El Leoncito, San Juan, Argentina. (3) Instituto y Museo de Ciencias Naturales, San Juan, Argentina.

Recibido 25 septiembre 2008. Aceptado 02 diciembre 2008. Editor asociado: F Bozinovick
Table 1
Biotic and abiotic factors at El Leoncito and Nacunan. Mean
[+ or -] standard error.

Sites             Abioticfactors

                  Mean annual       Mean annual       Elevation
                  temperature       precipitation     (m a.s.l.)
                  ([degrees]C)       (mm)

El Leoncito       22                100               2484

Nacunan           15.6              329.4             540

Sites
                  Soil              Predominant
                  hardness          winds
                  (kg/c[m.sup.2])

El Leoncito       0.05 [+ or -]     NW2
                  0.06              20-30 km/h

Nacunan           0.14 [+ or -]     S and SE
                  0.15              9.8 km/h

Sites
                  Biotic factor-Risk of predation

                  Plant        Raptor/           Carnivores/
                  cover        cavy              cavy
                  (%)
El Leoncito                    0.20 + 0.09       0.21 + 0.05
                  21.9

Nacunan           54.3         0.45 + 0.14       0.09 + 0.05

Table 2
Burrow system characteristics at El Leoncito and Nacunan.
Mean [+ or -] standard error.

Sites          Number of active holes     Area covered ([m.sup.2])
               Main burrow   Satellite    Main burrow     Satellute
                               burrow                       burrow

El Leoncito    3 [+ or -]        1            53.6      0.01 [+ or -]
                   0.2                      [+ or -]        0.001
                                              3.2

Nacunan           21.6      2.9 [+ or-]      101.8      34.7 [+ or -]
                [+ or -]        0.5         [+ or -]         2.6
                   2.4                        7.9

Sites          Tilt angle    Depth of     Height of   Orientation of
                             galleries   holes (cm)    active burrow
                               (cm)                        holes

El Leoncito    18[grdos]       66.6          8.9            NW
                [+ or -]     [+ or -]     [+ or -]
                1[degrees]       2.7          0.2

Nacunan        23[degrees]      86.2          8.4             E
                [+ or -]     [+ or -]     [+ or -]
               0.5[degrees]      2.5          0.1
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Author:Taraborelli, Paula; Borruel, Natalia; Sandobal, Ana J.; Giannoni, Stella
Publication:Mastozoologia Neotropical
Date:Dec 1, 2009
Words:5658
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