Translator Disclaimer
1 December 2017 Juvenile Dispersal of Harpy Eagles (Harpia harpyja) in Ecuador
Author Affiliations +
Abstract

The movement ecology of Harpy Eagles (Harpia harpyja) is poorly known due to the difficulty observing this species. We studied the movements of two juvenile Harpy Eagles before and during dispersal using GPS satellite telemetry in the Reserva de Producción Faunística Cuyabeno, Ecuador. Both eagles were tagged at their respective nest tree. For each eagle, we calculated the daily distance moved and the distance from each recorded position to the nest. One eagle started dispersal during its 28th month, while at the same age the other eagle remained in its nest area, suffering repeated parental attacks that may have caused its death. The juvenile that dispersed moved a maximum of 35.1 km from the nest and occupied an area of 386 km2. The long post-fledging and dispersal periods underscore the importance of directing conservation plans toward juveniles as well as adults. In addition, dispersal movements that are close to the natal nest facilitate the delimitation of areas for protection of Harpy Eagle nests.

The Harpy Eagle (Harpia harpyja) is one of the largest and heaviest raptors in the world (Brown and Amadon 1968). This species occupies lowland rainforests, with a discontinuous distribution from southern Mexico to northern Argentina (Ferguson-Lees and Christie 2001). Due to habitat loss and human persecution, populations of this eagle are declining (Álvarez-Cordero 1996, Vargas et al. 2006, BirdLife International 2016). Its long breeding interval, estimated at 2.5–3 yr (Rettig 1978, Álvarez-Cordero 1996), makes the species even more vulnerable. Currently, it is considered a Near Threatened species by the International Union for Conservation of Nature and Natural Resources (IUCN 2013), and in Ecuador it is included within the category Vulnerable (Granizo et al. 1997).

Different aspects of the biology of the Harpy Eagle have been studied, including trophic ecology (Fowler and Cope 1964, Piana 2007, Lenz and dos Reis 2011, Aguiar-Silva et al. 2014, 2015, Miranda 2016) and breeding behavior (Rettig 1978, Álvarez-Cordero 1996, Muñiz-López 2007, Rotenberg et al. 2012). Although there are some studies on its movement ecology (Álvarez-Cordero 1996, Campbell-Thompson et al. 2012, Muñiz-López et al. 2012, Aguiar-Silva and Sanaiotti 2013), due to the difficulty of observing this species, some aspects of its spatial ecology (e.g., juvenile dispersal) are still poorly known. Juvenile dispersal comprises the movements undertaken by juveniles in their search for a breeding area once they are independent from their parents (Greenwood and Harvey 1982, Clobert et al. 2001). In large raptors this process may take 3–4 yr (Urios et al. 2007, Cadahía et al. 2009, Whitfield et al. 2009), and it is preceded by a period of parental dependence called the post-fledging period. This post-fledging period occurs between the first flights of the bird and the onset of dispersal (Soutullo et al. 2006). The onset of dispersal is not easy to detect, and it can be influenced by a reduction in parental investment of their offspring (e.g., decreasing the food supply), or the presence of parent-offspring or between-sibling aggression (Holleback 1974, Alonso et al. 1987). We studied the movements of two female juvenile Harpy Eagles tracked by GPS satellite telemetry before and during the juvenile dispersal period.

Methods

Capture and Tagging. We trapped two juvenile female Harpy Eagles, “Masakay” and “Tava,” at their respective nest trees in the Reserva de Producción Faunística Cuyabeno, Sucumbíos Province, northeastern Ecuador (0°7.00′S, 75°50.00′W). Located in the Amazon region of Ecuador, this is one of the most biodiverse places on the planet, dominated by primary lowland tropical moist forest between 250 and 300 masl and flooded tropical evergreen forests (Cañadas 1983, Stotz et al. 1996, Cerón et al. 1999, Palacios et al. 1999). For additional details on capture methods, see Muñiz-López et al. (2012).

We tagged eagles with 70-g Argos/GPS satellite transmitters (Microwave Telemetry Inc., Columbia, MD U.S.A.) affixed to their backs using a Teflon harness. This equipment did not exceed 1.5% of body mass, which is within the recommended limits (Kenward 2001). One GPS position (nominal accuracy of ±18 m) was recorded every hour between 0900 and 0300 H (local time) for Masakay and between 1100 and 0300 H for Tava. Masakay was tagged on 15 July 2006 in its third month of age, and Tava on 28 March 2009 in its seventh month of age. In addition, in collaboration with the natives of nationality A'i/Cofan, a 30-m-high observation tower was built, which allowed us to observe Masakay. This tower was used from 0700 to 1630 H continuously every day until Masakay was 1 yr old. After that age, we monitored the juvenile for 5 hr in the morning (0700–1200 H), and used the tower sporadically to improve upon observations from the ground, because the juvenile did not stay in the nest and thus it was necessary to follow it on foot.

Statistical Analyses. We retrieved the data and managed it using the program Satellite Tracking and Analysis Tools (STAT; Coyne and Godley 2005). We calculated the distances covered every day for each eagle, selecting a location per day that was closest to midnight. These data failed a test for normality, so we used the nonparametric Mann-Whitney U-test to evaluate the differences in these daily distances between Masakay and Tava during the months that data were available for both birds. We also calculated the distance to the nest from every recorded position, and tested the differences between Masakay and Tava in the same way. In the case of Tava, we also analyzed the differences between the daily distances before the onset of dispersal when she was in the natal area, and the distances covered once the dispersal period began. Daily distances calculated between nonconsecutive days (due to lack of data) were excluded from the analysis. In addition, we estimated the hourly distances travelled as the straight-line distance between two locations corresponding to consecutive hours. These distances could be calculated between 0900 and 0300 H (local time), the time period during which the locations were obtained. We used the Kruskal-Wallis test (data were non-normal) to examine whether there were differences in the hourly distances according to the time of day, and the multiple comparison Games-Howell test (Zar 1999) to check whether there was any peak of activity. All statistical analyses were performed with IBM SPSS Statistics ver. 22.0. Significance level was established at P < 0.05 and we present data as mean ± SD.

Home-range Estimation. We estimated the home range of both Harpy Eagles during the period in which the eagles were using the natal area and during the dispersal period, using all GPS locations. We calculated the 95%, 75%, and 50% fixed kernels (Worton 1989) using the Animal Movement extension for ArcView 3.2 (Hooge and Eichenlaub 1997). We used the least squares cross-validation procedure to calculate the smoothing parameter H (Silverman 1986). To estimate the real size of home ranges, we transformed the kernel polygons in geographic coordinates to an equal-area cylindrical projection using the Projector! Extension for ArcView 3.2. We also calculated the minimum convex polygon (MCP) encompassing all the locations obtained for the different periods (post-fledging and dispersal period), performing the same transformation as for the kernel analyses.

Results

Muñiz-López et al. (2012) described the movements of these two Harpy Eagles from hatching until they reached the age of 2 yr. In this study, we documented their movements after the age of 2 yr. Using the transmitters, we monitored Tava for 15 mo, until she was 39 mo old, and monitored Masakay for 4 mo, until she was 27 mo old.

The two young Harpy Eagles exhibited different behaviors. Tava remained in the natal area until the beginning of her 28th mo: on 6 December 2010 she began her juvenile dispersal by moving away from the nest toward the north (Fig. 1). Masakay remained within her natal area throughout the period that GPS data were available. Coinciding with the second month of dispersal of Tava, Masakay, in the middle of her 29th mo, began to suffer attacks by one of the parents, presumably the male. We were able to observe these attacks from the observation tower. The attacks consisted of quick flights by the adult, showing its talons and approaching the juvenile who was perched on a branch of a tree adjacent to the nest tree. Subsequently, Masakay was found dead the following month (at 30 mo old) a few meters from the nest tree.

Figure 1.

Dispersal and home range of two juvenile female Harpy Eagles in Ecuador, 2006 and 2009. GPS locations for one female eagle (Tava) are indicated by open dots connected by track lines. Polygons represent fixed kernels and Minimum Convex Polygon (MCP, solid line) for: (A) Tava's post-fledging area; (B) Tava's dispersal area; and, (C) Masakay's post-fledging area (MCP).

i0892-1016-51-4-439-f01.tif

The daily distances covered by Tava and Masakay during the months for which data are available for both birds (i.e., within their natal area) differed significantly (Z = −10.72, P < 0.000); Tava averaged 0.48 (±0.46) km per day whereas Masakay made much shorter movements, averaging 0.03 (±0.05) km per day. Similarly, the daily distances to the nest were significantly different (Z = −34.29, P < 0.000): Tava was 0.35 (±0.38) km from the nest before the onset of the dispersal while Masakay moved away an average distance of only 0.03 (±0.04) km (maximum distance = 2.2 km and 0.24 respectively; Fig. 2). The daily distances covered before and after the onset of the dispersal by Tava also differed significantly (Z = −8.72, P < 0.000), with an average of 0.48 (±0.46) km before dispersal and 1.47 (±0.90) km during dispersal. The maximum daily distance recorded was close to 4 km, although during the dispersal period it was >2 km in most cases (69%). Only in 4% of the daily segments did the distance exceed 3 km. During the study period (i.e., from age 24–39 mo old), Tava moved away from the nest a maximum of 35.1 km (during her 35th month; Fig. 2). Tava's transmitter stopped functioning when she was 39 mo old.

Figure 2.

Distances to nest of two juvenile Harpy Eagles (blue squares for Masakay and red dots for Tava) for every month during the study period, Ecuador, 2006 and 2009. Distances were calculated from every recorded GPS location (and from visual records for Masakay during months 28–30). The black arrow indicates the month we observed the parental attacks suffered by Masakay, found dead in the 30th mo of life.

i0892-1016-51-4-439-f02.tif

Hourly distances were only calculated for Tava because Masakay remained static most of the time, making only short movements. The average hourly distances moved by Tava (0.11 ± 0.14 km/hr) changed significantly throughout the day (χ2 = 65.61, df = 11, P < 0.001), although there was no prominent peak of activity. The maximum distance recorded in one hour was 0.99 km, although in 95% of the hourly movements it was <0.42 km. There was activity during all daylight hours.

During the time that Tava remained in the natal area (Fig. 1A), she occupied an area of 0.39 km2 according to the 95% fixed kernel (0.07 and 0.03 km2 for 75% and 50% kernels respectively, and 6.06 km2 for MCP). The estimated area during the 11 mo of dispersal (Fig. 1B) that we studied was 386 km2 according to the 95% fixed kernel (137 and 42 km2 for 75% and 50% kernels, and 579 km2 for MCP). The 95% kernel for Masakay encompassed only 2.78 × 10−3 km2 (7.93 × 10−4 and 3.70 × 10−4 km2 for 75% and 50% kernels, and 0.112 km2 for MCP; Fig. 1C).

Discussion

The Harpy Eagle and Philippine Eagle (Pithecophaga jefferyi) exhibit the longest post-fledging dependence period within raptors (del Hoyo et al. 1994, Álvarez-Cordero 1996, Muñiz-López et al. 2012). According to our data, based on only one female, Harpy Eagles in Ecuador begin their juvenile dispersal period around the 28th mo of life, which is older than in other eagles (Wood et al. 1998, Soutullo et al. 2006, Cadahía et al. 2008). Perhaps coincidentally, the onset of the dispersal of Tava and of the aggressive behavior by one of the parents of Masakay occurred at the same approximate age. At 28–29 mo old, Tava began to disperse, whereas Masakay remained near the nest, making shorter movements (Fig. 2) and perhaps inciting the parental attacks that might have caused her death. Although not common in all raptors (Bustamante and Hiraldo 1990, Bustamante 1994, Boileau and Bretagnolle 2014), parental aggression toward the juveniles has been observed in other species, such as the Spanish Imperial Eagle (Aquila adalberti; Alonso et al. 1987). This conflict between adults and offspring (Trivers 1974), promoted by parents that reduce the food supply or increase their aggressive behavior toward juveniles, favors independence and the onset of the dispersal (Hiraldo et al. 1989, Arroyo et al. 2002, Balbontín and Ferrer 2005).

Once she initiated dispersal, Tava remained north of the natal area and explored the area without stopping permanently in any region until 39 mo of age, at which time her transmitter stopped functioning and we could no longer track her movements. Rotenberg et al. (2012) tracked the movements of a juvenile Harpy Eagle after fledging; it explored an area of approximately 3.2 km2 during the first months of the post-fledging period. Based on her MCP, Tava occupied an area twice as large for the last 4 mo of the post-fledging period, a consistent result as the juvenile increases its distance from the nest during this post-fledging period (Muñiz-López et al. 2012). The area explored by Tava during dispersal comprised hundreds of square km, considerably larger than the size of a breeding territory occupied by a breeding pair (range = 16–79 km2; Álvarez-Cordero 1996, Muñiz-López 2008, Vargas and Vargas 2011). This suggests that juvenile Harpy Eagles cover a large area before settling in a breeding territory.

Although the studies on juvenile dispersal for large forest eagles are scarce, estimated dispersal area and the distances covered in the first months after the start of the dispersal by Harpy Eagles are lower than those for other species. For instance, Spanish Imperial Eagles (González et al. 1989, Muriel et al. 2015), Bonelli's Eagles (Aquila fasciata; Cadahía et al. 2005, 2010) and Crowned Solitary Eagles (Buteogallus coronatus; Urios et al. 2014) move hundreds of km away from the natal nest and explore large areas before occupying a territory. These differences may be due to the homogeneity of the forested habitat occupied by the Harpy Eagle, allowing for suitable conditions and prey availability in a smaller area (Muñiz-López 2008, Aguiar-Silva et al. 2015). In addition, the Harpy Eagle uses perch-hunting and does not soar like other eagles, so this species does not need to cover large distances when hunting. Abaño et al. (2015) also reported greater movements for the Philippine Eagle, a species similar to the Harpy Eagle in size and biology (del Hoyo et al. 1994). However, the results are not directly comparable because that study involved released individuals. The Papuan Eagle (Harpyopsis novaeguineae), which is smaller in size, inhabits tropical forests of similar homogeneity, in which it occupies relatively small territories of several tens of square kilometers (Watson and Asoyama 2001). There are no quantitative data on dispersal areas for other large forest eagles, such as the Crested Eagle (Morphnus guianensis) and the African Crowned Eagle (Stephanoaetus coronatus).

Despite the need to conduct more studies on juvenile Harpy Eagle dispersal and movement ecology, important implications for the conservation of this species can be discerned from our results. The small clutch size and long breeding period (Rettig 1978), together with the long post-fledging and dispersal period, underscore the importance of directing conservation plans at juveniles as well as adults. Therefore, understanding the movements of juveniles during dispersal, a period with relevant demographic consequences, may be of great importance for the conservation of the species (Clobert et al. 2001, Soutullo et al. 2008, Penteriani et al. 2011). The long time period spent in the nesting area and the relatively short-distance dispersal movements, facilitate the delimitation of buffers around Harpy Eagle nests that should be protected from harmful human activities for ≥30 mo (i.e., 2 mo of incubation and the 28 mo that juveniles remain in the natal area).

Acknowledgments

Special thanks are due to Terra Natura Foundation for funding the Project on tracking of Harpy Eagles in Ecuador. SIMBIOE, the Environment Ministry of Ecuador and EcoFondo funded the fieldwork. We are also thankful to Alexander Blanco and the team of participants and volunteers for their help in the captures, and to the indigenous communities for their constant support and for allowing us to work in their territories. Permissions for the study were granted from the Environment Ministry of Ecuador (18-2009-IC-FAU-DPS-MA-2009). J. Vidal-Mateo was supported by FPU grant of the Spanish Ministry of Education (reference FPU014/04671). This report is a portion of the Ph.D. dissertation of R. Muñiz-López at the University of Alicante.

Literature Cited

1.

Abaño, T.R.C., G.G. Tampos, R.L. Taraya, D.J.I. Salvador, and J.C. Ibañez. 2015. Dispersal of Philippine Eagles released in the forests of Mindanao, Philippines. Journal of Raptor Research 49:506–512. Google Scholar

2.

Aguiar-Silva, F.H., T.G. Junqueira, T.M. Sanaiotti, V.Y. Guimarães, P.V.C. Mathias, and C.V. Mendonça. 2015. Resource availability and diet in Harpy Eagle breeding territories on the Xingu River, Brazilian Amazon. Brazilian Journal of Biology 75:181–189. Google Scholar

3.

Aguiar-Silva, F.H. and T.M. Sanaiotti. 2013. Mapping the home range of Harpy Eagles in the Brazilian Amazon Basin. ARGOS Forum 76:4–5. Google Scholar

4.

Aguiar-Silva, F.H., T.M. Sanaiotti. and B.B. Luz. 2014. Food habits of the Harpy Eagle, a top predator from the Amazonian rainforest canopy. Journal of Raptor Research 48:24–35. Google Scholar

5.

Alonso, J.C., L.M. González, B. Heredia, and J.L. González. 1987. Parental care and the transition to independence of Spanish Imperial Eagles Aquila heliaca in Doñana National Park, southwest Spain. Ibis 129:212–224. Google Scholar

6.

Álvarez-Cordero, E. 1996. Biology and conservation of the Harpy Eagle in Venezuela and Panama. Ph.D. dissertation, University of Florida, Gainesville, FL U.S.A. Google Scholar

7.

Arroyo, B.E., T. De Cornulier, and V. Bretagnolle. 2002. Parental investment and parent-offspring conflicts during the post-fledging period in Montagu's Harriers. Animal Behaviour 63:235–244. Google Scholar

8.

Balbontín, J. and M. Ferrer. 2005. Factors affecting the length of the post-fledging period in the Bonelli's Eagle Hieraaetus fasciatus. Ardea 93:189–198. Google Scholar

9.

BirdLife International. 2016. Species factsheet: Harpia harpyja.  http://www.birdlife.org (last accessed 1 June 2016). Google Scholar

10.

Boileau, N. and V. Bretagnolle. 2014. Post-fledging dependence period in the Eurasian Kestrel (Falco tinnunculus) in western France. Journal of Raptor Research 48:248–256. Google Scholar

11.

Brown, L. and D. Amadon. 1968. Eagles, hawks, and falcons of the world. McGraw Hill, New York, NY U.S.A. Google Scholar

12.

Bustamante, J. 1994. Family break-up in Black and Red kites Milvus migrans and M. milvus: is time of independence an offspring decision?Ibis 136:176–184. Google Scholar

13.

Bustamante, J. and F. Hiraldo. 1990. Factors influencing family rupture and parent-offspring conflict in the Black Kite (Milvus migrans). Ibis 132:58–67. Google Scholar

14.

Cadahía, L., P. López-López, V. Urios, and J.J. Negro. 2008. Estimating the onset of dispersal in endangered Bonelli's Eagle Hieraaetus fasciatus tracked by satellite telemetry: a comparison among methods. Ibis 150:416–420. Google Scholar

15.

Cadahía, L., P. López-López, V. Urios, and J.J. Negro. 2009. Natal dispersal and recruitment of two Bonelli's eagles Aquila fasciata: a four year satellite tracking study. Acta Ornitholica 44:193–198. Google Scholar

16.

Cadahía, L., P. López-López, V. Urios, and J.J. Negro. 2010. Satellite telemetry reveals individual variation in juvenile Bonelli's Eagle dispersal areas. European Journal of Wildlife Research 56:923–930. Google Scholar

17.

Cadahía, L., V. Urios, and J.J. Negro. 2005. Survival and movements of satellite-tracked Bonelli's Eagles Hieraaetus fasciatus during their first winter. Ibis 147:415–419. Google Scholar

18.

Campbell-Thompson, E., F.H. Vargas, R.T. Watson, A. Muela, and N.C. Cáceres. 2012. Effect of sex and age at release on the independence of hacked Harpy Eagles. Journal of Raptor Research 46:158–167. Google Scholar

19.

Cañadas, L. 1983. El mapa bioclimático y ecológico del Ecuador. Banco Central del Ecuador, Quito, Ecuador. Google Scholar

20.

Cerón, C., W. Palacios, R. Valencia, and R. Sierra. 1999. Las formaciones naturales de la costa del Ecuador. Pages 55–80 in R. Sierra[Ed.], Propuesta preliminar de un sistema de clasificación de vegetación para el Ecuador continental. Ministerio del Medio Ambiente, Proyecto INEFAN/GEF-BIRF y EcoCiencia, Quito, Ecuador. Google Scholar

21.

Clobert, J., E. Danchin, A.A. Dhont, and J. Nichols[Eds.]. 2001. Dispersal, causes, consequences and mechanisms of dispersal at the individual, population and community level. Oxford University Press, Oxford, U.K. Google Scholar

22.

Coyne, M.S. and B.J. Godley. 2005. Satellite tracking and analysis tool (STAT): an integrated system for archiving, analyzing and mapping animal tracking data. Marine Ecology Progress Series 301:1–7. Google Scholar

23.

del Hoyo, J., A. Elliott, and J. Sargatal. 1994. Handbook of the birds of the world. Vol. 2: New world vultures to guineafowl. Lynx Editions, Barcelona, Spain. Google Scholar

24.

Ferguson-Lees, J. and D.A. Christie. 2001. Raptors of the world. Christopher Helm, London, U.K. Google Scholar

25.

Fowler, J. and J. Cope. 1964. Notes on the Harpy Eagle in British Guiana. Auk 81:257–273. Google Scholar

26.

González, L.M., B. Heredia, J.L. González, and J.C. Alonso. 1989. Juvenile dispersal of Spanish Imperial Eagle. Journal of Field Ornithology 60:369–379. Google Scholar

27.

Granizo, T., M. Guerrero, C. Pacheco, R. Phillips, M.B. Ribadeneira, and L. Suárez. 1997. Lista de aves Amenazadas de extinción en el Ecuador. UICN-Sur, CECIA, INEFAN, EcoCiencia y BirdLife International, Quito, Ecuador. Google Scholar

28.

Greenwood P.J. and P.H. Harvey. 1982. The natal and breeding dispersal of birds. Annual Reviews of Ecology and Systematics 13:1–21. Google Scholar

29.

Hiraldo, E., M. Delibes, and R.R. Estrella. 1989. Observations of a Zone-tailed Hawk family during the post-fledging period. Journal of Raptor Research 23:103–106. Google Scholar

30.

Holleback, M. 1974. Behavioral interactions and the dispersal of the family in Black-capped Chickadees. Wilson Bulletin 76:28–36. Google Scholar

31.

Hooge, P.N. and B. Eichenlaub. 1997. Animal Movement Extension for ArcView. Alaska Science Center, Biological Science Office, U.S. Geological Survey, Anchorage, AK U.S.A. Google Scholar

32.

IUCN. 2013. The IUCN Red List of Threatened Species. Version 2015-4.  http://www.iucnredlist.org (last accessed 1 June 2016). Google Scholar

33.

Kenward, R.E. 2001. A manual for wildlife radio tagging. Academic Press, London, U.K. Google Scholar

34.

Lenz, B.B. and A.M. dos Reis. 2011. Harpy Eagle–primate interactions in the central Amazon. Wilson Journal of Ornithology 123:404–408. Google Scholar

35.

Miranda, E.B.P. 2016. Conservation implications of Harpy Eagle Harpia harpyja predation patterns. Endangered Species Research 29:69–79. Google Scholar

36.

Muñiz-López, R. 2007. Ecología, biología y hábitat del Águila Harpía (Harpia harpyja). Pages 190–251 in P. Tufiño[Ed.], Cunsi pindo: conservación del Águila Harpía en Ecuador. SIMBIOE, Quito, Ecuador. Google Scholar

37.

Muñiz-López, R. 2008. Revisión de la situación del águila Harpía Harpia harpyja en Ecuador. Cotinga 29:42–47. Google Scholar

38.

Muñiz-López, R., R. Limiñana, G.D Cortés, and V. Urios. 2012. Movements of Harpy Eagles Harpia harpyja during their first two years after hatching. Bird Study 59:509–514. Google Scholar

39.

Muriel, R., V. Morandini, M. Ferrer, and J. Balbontín. 2015. Independence and juvenile dispersal distances in wild and reintroduced Spanish Imperial Eagles. Biological Conservation 191:300–305. Google Scholar

40.

Palacios, W., C. Cerón, R. Valencia, and R. Sierra. 1999. Las formaciones naturales de la Amazonía del Ecuador. Pages 112–121 in R. Sierra[Ed.], Propuesta preliminar de un sistema de clasificación de vegetación para El Ecuador continental. Ministerio de Medio Ambiente, Proyecto INEFAN/GEF-BIRF y EcoCiencia, Quito, Ecuador. Google Scholar

41.

Penteriani, V., M. Ferrer, and M.M. Delgado. 2011. Floater strategies and dynamics in birds, and their importance in conservation biology: towards an understanding of nonbreeders in avian populations. Animal Conservation 14:233–241. Google Scholar

42.

Piana, R.P. 2007. Anidamiento y dieta de Harpia harpyja Linnaeus en la comunidad nativa de Infierno, Madre de Dios, Perú. Revista Peruana de Biología 14:135–138. Google Scholar

43.

Rettig, N.L. 1978. Breeding behavior of the Harpy Eagle (Harpia harpyja). Auk 95:629–643. Google Scholar

44.

Rotenberg, J.A., J.A. Marlin, L. Pop, and W. Garcia. 2012. First record of a Harpy Eagle (Harpia harpyja) nest in Belize. Wilson Journal of Ornithology 124:292–297. Google Scholar

45.

Silverman, B.W. 1986. Density estimation for statistics and data analysis. Chapman and Hall, London, U.K. Google Scholar

46.

Soutullo, A., P. López-López, and V. Urios. 2008. Incorporating spatial structure and stochasticity in endangered Bonelli's Eagle's population models: implications for conservation and management. Biological Conservation 141:1013–1020. Google Scholar

47.

Soutullo, A., V. Urios, M. Ferrer, and S.G. Peñarrubia. 2006. Post-fledging behaviour in Golden Eagles Aquila chrysaetos: onset of juvenile dispersal and progressive distancing from the nest. Ibis 148:307–312. Google Scholar

48.

Stotz, D.F., J.W. Fitzpatrick, T.A. Parker, III, and D.K. Moskovits. 1996. Neotropical birds: ecology and conservation. University of Chicago Press, Chicago, IL U.S.A. Google Scholar

49.

Trivers, R.L. 1974. Parent-offspring conflict. American Zoologist 14:249–264. Google Scholar

50.

Urios, V., M.P. Donat-Torres, M.J. Bechard, and M. Ferrer. 2014. Movements of a juvenile Crowned Eagle (Harpyhaliaetus coronatus) tracked by satellite telemetry in central Argentina. Journal of Biological Research-Thessaloniki 21:1–6. Google Scholar

51.

Urios, V., A. Soutullo, P. López-López, L. Cadahía. R. Limiñana, and M. Ferrer. 2007. First case of recruitment of a juvenile Golden Eagle (Aquila chrysaetos) tracked by satellite telemetry. Acta Ornitholica 42:205–209. Google Scholar

52.

Vargas, J.J. and H.F. Vargas. 2011. Nesting density of Harpy Eagles in Darien with population size estimates for Panama. Journal of Raptor Research 45:199–210. Google Scholar

53.

Vargas, J.J. D. Whitacre, R. Mosquera, J. Albuquerque, R.P. Piana, J.-M. Thiollay, C. Márquez, J.E. Sánchez, M. Lezama-López, S. Midence, S. Matola, S. Aguilar, N. Rettig, and T. Sanaiotti. 2006. Estado y distribución actual del águila arpía (Harpia harpyja) en Centro y Sur America. Ornitologia Neotropical 17:39–55. Google Scholar

54.

Watson, M. and S. Asoyama. 2001. Dispersion, habitat use, hunting behaviour, vocalizations, and conservation status of the New Guinea Harpy Eagle (Harpyopsis novaeguineae). Journal of Raptor Research 35:235–239. Google Scholar

55.

Whitfield, D.P., A. Douse, R.J. Evans, J. Grant, J. Love, D.R.A. McLeod, R. Reid, and J.D Wilson. 2009. Natal and breeding dispersal in a reintroduced population of White-tailed Eagles Haliaeetus albicilla. Bird Study 56:177–186. Google Scholar

56.

Wood, P.B., M.W. Collopy, and C.M. Sekerak. 1998. Post-fledging nest dependence period for Bald Eagles in Florida. Journal of Wildlife Management 62:333–339. Google Scholar

57.

Worton, B.J. 1989. Kernel methods for estimating the utilization distribution in home-range studies. Ecology 70:164–168. Google Scholar

58.

Zar, J.H. 1999. Biostatistical analysis, Fourth Ed. Prentice Hall, Upper Saddle River, NJ U.S.A. Google Scholar
© 2017 The Raptor Research Foundation, Inc.
Vicente Urios, Ruth Muñiz-López, and Javier Vidal-Mateo "Juvenile Dispersal of Harpy Eagles (Harpia harpyja) in Ecuador," Journal of Raptor Research 51(4), 439-445, (1 December 2017). https://doi.org/10.3356/JRR-16-54.1
Received: 20 June 2016; Accepted: 1 February 2017; Published: 1 December 2017
JOURNAL ARTICLE
7 PAGES


SHARE
ARTICLE IMPACT
Back to Top