Translator Disclaimer
1 June 2007 Spatial Variation in the Diet of the Barn Owl Tyto alba in the Caribbean
Maarten Flikweert, Tineke G. Prins, John A. de Freitas, Vincent Nijman
Author Affiliations +

On Bonaire we assessed Bam Owl Tyto alba diets at four discrete sites. The 233 fresh pellets contained 755 identifiable prey items from four taxonomic orders. Average prey diversity differed two- to threefold between sites. Dietary composition showed large spatial variations between sites, from predominantly insectivorous to avian. Between-island variation was assessed by comparing the dietary composition of populations of Barn Owls on nine islands throughout the Caribbean region as reported in the literature. On 8/9 islands mammals (mainly rodents and bats) formed the main diet. On half of the islands about a fifth or more of the prey comprised birds. Reptiles and/or insects were eaten on 5/9 islands, but rarely dominated the diet. These large within-island dietary differences reflect differential prey availabilities in the Caribbean, possibly enhanced locally by specialisation.


The Barn Owl Tyto alba has a cosmopolitan distribution, with populations occupying temperate and tropical zones. The Barn Owl is arguably the beststudied owl worldwide showing large temporal and spatial variation in the dietary composition within and between study areas (e.g. Bunn et al. 1982, Taylor 1994, Bruce 1999, Köning et al. 1999). Our knowledge of the biology of Barn Owls and, more specifically, of its diet is strongly biased towards studies from temperate regions (Taylor 1994). Relatively few data are available on the dietary composition of Barn Owls from tropical regions, and in particular from (small) tropical islands. Given that these islands typically have depaupered faunas (Woods & Sergile 2001) we expect that Barn Owls on these islands have a less diverse diet compared with those breeding on the mainland. On many islands exotic animals (rats, mice, rabbits) have been introduced and these may provide alternative food sources. Our aim is to quantify and analyse the diet of Barn Owls breeding in the Caribbean, and to quantify the spatial variation in diet between and within these isolated tropical islands.


Study area

We selected the Caribbean as our study region (Fig. 1) as the Bam Owl is widespread in the area and data on the dietary composition of several resident island populations is available. Within the Caribbean several island populations have been described as different at the subspecific level, viz T. a. pratincola in the north, T. a. furcata in the north and east, and T. a. bargei in the south (König et al. 1999; Prins et al. 2003). In much of the region only one species of barn owl is present, i.e. Tyto alba, but on Hispaniola and Tortuga the Ashyfaced Owl T. glaucops occurs sympatrically (König et al. 1999).

For our within-island comparison the island of Bonaire, Netherlands Antilles, was chosen. The island occupies a land surface of c. 288 km2 and is situated 87 km north of Venezuela from which it is separated by the 1700 m deep Bonaire Trench. Bonaire has an arid climate (mean annual rainfall 463 mm; mean annual temperature 28°C: Meteorological Service of the Netherlands Antilles and Aruba) with about 50% of rainfall recorded in October to December. The amount of permanent available surface water has increased the last decades following the construction of dams and ponds (Prins & Nijman 2005). The Barn Owl is the only owl species present on Bonaire; in addition a small number of resident and migrant birds of prey occur (Nijman et al. 2005).

Figure 1.

The Caribbean region, indicating the location of the island of Bonaire, and other localities mentioned in the text.


Data acquisition

Barn Owl pellets on Bonaire were collected in February–May 2003. The species proved to have a patchy distribution with concentrations along limestone escarpments within the terraced landscapes that rim the island. Areas to be searched were identified by the presence of Middle and Higher Terrace units (de Freitas et al. 2005). Accumulation of pellets was considered evidence for the presence of a roost. Roosts were clustered around four sites, i.e. Bolivia (a continuous stretch of the Middle Terrace on the windward coast of the central part of the island), Roi Sangu (a gorge bordered by high limestone escarpments in the Higher Terrace landscape unit in the southern part of the island), Playa Frans (isolated limestone hill in an undulating landscape unit of volcanic origin) and Fontein (Middle and Higher limestone terraces; Fig. 2). Within the four sites we identified 25 individual roosts (see Table 1 for details). Only fresh pellets (<2 months old) were collected, and later analysed at the Zoological Museum Amsterdam (ZMA). We collected 233 fresh pellets, with a total of 755 identified prey items.

Figure 2.

Barn Owl habitat on Bonaire, showing one of the higher limestone terraces near Fontein (photo Mansour Aliabadian, Archive ZMA)


From the literature we selected studies from other islands in the region, if samples were specifically collected from just one island (as opposed to an aggregate of islands), and prey identification included all taxonomic orders.


Prey remains were identified using keys published in Husson (1960) and Voous (1983), and a reference collection in the ZMA. Identification of insects was mostly restricted to family level. For vertebrates we determined the minimal number of prey items in pellets by tallying the number of skulls and mandibles. Mean prey mass was taken from Dunning (1993), Nowak (1999), and ZMA collections. Rodent body masses were calculated following Morris (1979) and de Groot (1983). Frequency analysis followed the method of de Groot (1983). Many diversity indexes tend to be sensitive to differences in sample sizes (Magurran 1988). For each site, therefore, we calculated an average prey diversity index when sample size exceeded 53 prey items (the smallest sample size for Bolivia) with EcoSim software (using a rarefaction analysis) allowing direct comparisons between sites (Gotelli & Entsminger 2001). The options were set at 100 iterations and independent sampling of randomly chosen items from the total prey-item pool. For within- and between-island comparisons, spatial variation in dietary composition of the major prey items was tested with a χ2test, with number of prey items or summed body mass within each category as independent variables (Sokal & Rohlf 1995). To reduce the number of low expected values in the analysis, arthropods were pooled and birds and mammals were analysed at the family level (with Coerebidae, Ichteridae and Passeridae pooled). Yates' correction for continuity was applied to the χ2-test, where appropriate. We made multiple comparisons; to reduce the overall experiment-wise error, we set significance at P < 0.01 in two-tailed tests.

Table 1.

Frequency of prey items in pellets of Barn Owl at four sites in Bonaire, Netherlands Antilles. For each site the number of pellets and the number of individual roosts is given in parentheses. Biomass is given as a percentage of the total biomass for the sites.



Within-island variation

Diet composition, expressed as number of prey items and biomass, differed significantly at the spatial level (number of prey items: χ2 = 791, df = 9, P < 0.001; biomass: χ2 = 559, df = 9, P < 0.01). Pair-wise comparisons, with each area tested for similarity against the other areas pooled together, revealed that differences between sites were significant.

Diet diversity, expressed as Average Prey Diversity Index (APDI), differed between the four sites, with APDIs at Playa Frans and Fontein (13 and 12, respectively) being much higher than those observed at Roi Sangu and Bolivia (8 and 5, respectively).

In terms of frequency of prey items in pellets, the diet of Barn Owls from Bolivia differed from the other sites combined (χ2 = 193, df = 7, P < 0.001), especially in the marked abundance of Yellow Warblers Dendroica petechia and Black Rats Rattus rattus and the absence of arthropods. Dietary composition at Roi Sangu differed from the other sites combined (χ2 = 380, df = 7, P < 0.001), with a preponderance of darkling beetles (Coleoptera; Tenebrionidae), whilst New World warblers (large Dendroica spp.), Bananaquits Coereba flaveola, Black-faced Grassquits Tiaris bicolor, Common Ground Doves Columbina passerina and Black Rats were underrepresented. The dietary composition at Playa Frans differed from the other sites combined (χ2 = 197, df = 7, P < 0.001) with a relatively large number of Common Ground Doves, New World warblers (small Dendroica spp.), Rufous-collared Sparrows Zonotrichia capensis, Miller's Long-tongued Bat Glossophaga longirostris, Black Rats and Bonaire Whiptails Cnemidophorus murinus. Also, in terms of number of items present in pellets, Fontein differed from the other three sites combined (χ2 = 137, df = 7, P < 0.001) with significantly more Bananaquits, Black-faced Grassquits, tyrants (Tyrannus spp.) and Common House Mouse Mus musculus than the other sites combined.

When comparing spatial variation in dietary composition in terms of biomass, a similar pattern emerged as with the frequency analysis. Although the relative importance of the larger species increased, each of the sites differed significantly in species composition from the other sites combined. Most prominent were the small contributions of reptiles in the diet of the Barn Owls at Fontein (3% vs. 7%; χ2 = 94.4, df = 1, P < 0.01), and birds at Roi Sangu (24% vs. 32%; χ2 = 172.4, df = 1, P < 0.01). At Playa Frans there was a relative large amount of birds but a small amount of mammals in the Barn Owls diet (birds 42% vs. 32%; mammals 47% vs. 60%; both χ2 > 212.4, df = 1, P <0.01).

Between-island variation

Data on dietary composition of the Barn Owl was available from nine islands in the Caribbean, i.e. the Netherlands Antilles, the Turks and Caicos Islands, the Cayman Islands, Hispaniola, and Jamaica (Table 2). Almost 90 different species were found in Barn Owl pellets throughout the Caribbean, clearly an underestimate because many insects and some birds were not identified to the species level. The differences in dietary composition of Barn Owls between the islands were significant (χ2 = 5281, df = 24, P < 0.001); exclusion of insects did not alter this picture (χ2 = 769, df = 16, P < 0.001). The observed between-island variation is not an artifact of different methodologies employed: within the Turks and Caicos Islands and within the Netherlands Antilles the observed differences were significant (χ2 = 63.9, df = 6, P < 0.001 and χ2 = 1049.0, df = 3, P < 0.001 for the Turks and Caicos Islands, and the Netherlands Antilles, respectively).

Table 2.

Dietary composition of Barn Owls on Caribbean Islands by percentage (number of items) of total number of prey items identified.


The analysis shows that, apart from Bonaire, small mammals (mainly rats and mice but also various species of bats) and to a lesser degree birds, make up the majority of the Barn Owls' diet in the Caribbean. Insects and reptiles are preyed upon by Barn Owls on few islands, but rarely feature prominently in the species' diet.


We found large spatial differences in diets within Bonaire. At one roost, 86% of all prey items were Arthropoda, but this taxonomic group was rare at other roosts. Lizards were important prey for owls at one site (9% of all prey items), but were almost completely absent at other. Only at the roosts of Playa Frans, bats featured in the Barn Owl's diet (12% of all prey items). Prey diversity differed almost threefold between sites. Between islands the variation was almost as large. On 8 out of 9 islands small mammals (mainly rodents and bats) form the bulk of the Barn Owl's diet. On half of the islands about a fifth or more of the prey comprise birds, but reptiles and/or insects rarely dominated the diet although found in pellets on half of the islands.

Taylor (1994) reviewed the dietary composition of Bam Owls worldwide and concluded that in 80% of the cases small mammals made up >90% of the total number of prey items. On some small island ecosystems this general conclusion seems to hold, as for instance studies from the Turks and Caicos Islands (Buden 1974), the Cayman Islands (Johnston 1974), and coastal islands off West Australia (Dickman et al. 1991) indicate that rats and/or mice are important prey items. It seems that in more arid tropical islands Barn Owls often catch a greater proportion of non-mammalian prey, as for instance in the Galapagos Islands insects made up 63% of prey items (de Groot 1983), and our results indicate a similar picture for Bonaire. In arid areas Barn Owls seem to have a catholic diet, taking a wide variety of insects, lizards, birds and small mammals (Taylor 1994; cf. Debrot et al. 2001).

This large spatial variation in dietary composition may point at (a) temporal and geographic variations in the species composition and abundance of food supply, or (b) some degree of local specialization. Given the small size of Bonaire, the proximity of study sites, and distances covered by hunting Barn Owls (1–5 km from nest sites), the latter hypothesis may have some support. However, as we have no information on variations in prey availability within and between islands, the more likely first explanation cannot be ruled out. We feel that pinpointing proximate causes of local variations in diet would be an interesting avenue for further research.


Fieldwork on Bonaire was made possible through generous financial contributions from the Prins Bernhard Cultuurfonds Nederlandse Antillen en Aruba and the P.A. Hens Memorial Fund. We thank W Bergmans (ZMA), A.O. Debrot (CARMABI), G. van Hoorn (DROB), P. Montanus (DROB), and GS. Roselaar (ZMA) for help and support. We thank the two reviewers for their suggestions and comments.



M.D. Bruce 1999. Family Tytonidae (Barn-owls). In: J. Del Hoyo, A. Elliott & J. Sargatal (eds) Handbook of the birds of the World. Part 5. Bam-owls to Hummingbirds: 34–75. Lynx Edicions, Barcelona. Google Scholar


D.W. Buden 1974. Prey remains of Barn Owls in the southern Bahama Islands. Wilson Bull. 86: 336–343. Google Scholar


D.S. Bunn , A.B. Warburton & R.D.S Wilson 1982. The Barn Owl. Poyser, London. Google Scholar


Freitas J.A. de , B.S.J. Nijhof , A.C. Rojer & A.O. Debrot 2005. Landscape ecological vegetation map of the island of Bonaire (southern Caribbean). Caribbean Research and Management of Biodiversity Foundation, Willemstad, Curaçao and Royal Netherlands Academy of Arts and Sciences, Amsterdam, the Netherlands. Google Scholar


R.S. de Groot 1983. Origin, status and ecology of the owls in Galapagos. Ardea 71: 167–182. Google Scholar


A.O. Debrot , J.A. de Freitas , A. Brouwer & M. van Marwijk Kooy 2001. The Curaçao Barn Owl: status and diet, 1987–1989. Car. J. Sci. 37: 185–193. Google Scholar


C.R. Dickman , S.E.J. Daly & G.W. Connell 1991. Dietary relationships of the Barn Owl and Australian Kestrel on islands off the coast of Western Australia. Emu 91: 69–72. Google Scholar


J.B. Dunning Jr. 1993. CRC Handbook of avian body masses. CRC Press, Boca Raton. Google Scholar


N.J. Gotelli & G.L. Entsminger 2001. EcoSim: Null models software for ecology. Version 7.0. Acquired Intelligence Inc. & Kesey-Bear. Google Scholar


A.M. Husson 1960. Mammals of the Netherlands Antilles. Martinus Nijhof, Den Haag. Google Scholar


D.W. Johnston 1974. Food of the Barn Owl on Grand Cayman, B.W.I. Q. J. Florida Acad. Sci. 35: 171–172. Google Scholar


C. Köning , F. Weick & J.H. Becking 1999. Owls. A guide to the owls of the world. Pica Press, Sussex. Google Scholar


A.E. Magurran 1988. Ecological diversity and its measurement. Chapman and Hall, London. Google Scholar


D.A. McFarlane & K.L. Garrett 1989. The prey of Common Barn-owls (Tyto alba) in dry limestone scrub forest of Southern Jamaica. Car. J. Sci. 25: 21–23. Google Scholar


P. Morris 1979. Rats in the diet of the Barn Owl (Tyto alba). J. Zool. 189: 540–545. Google Scholar


V. Nijman , T.G. Prins & J.H. Reuter 2005 Timing and abundance of migrant raptors on Bonaire, Netherlands Antilles. J. Raptor Res. 30: 96–99. Google Scholar


R.M. Nowak 1999. Walker's mammals of the World, sixth edition. John Hopkins University Press, Baltimore. Google Scholar


T.G. Prins & V. Nijman 2005. Historic changes in status of Caribbean coot in the Netherlands Antilles. Oryx 39: 125–126. Google Scholar


T.G. Prins , J.A. de Freitas & C.S. Roselaar 2003. First specimen record of the Barn Owl Tyto alba in Bonaire, Netherlands Antilles. Car. J. Sci. 39: 144–147. Google Scholar


R.R. Sokal & J.F. Rohlf 1995. Biometry: the principles and practice of statistics in biological research. Third edition. Freeman, New York. Google Scholar


I. Taylor 1994. Barn owls. Predator-prey relationships and conservation. Cambridge University Press, London. Google Scholar


K.H. Voous 1983. The birds of the Netherlands Antilles. Walburg Pers, Zutphen. Google Scholar


A. Wetmore & H.S. Bradshaw 1931. The birds of Haiti and the Dominican Republic. Bull. U.S. Nat. Mus. 155: 1–783. Google Scholar


G.A. Woods & F.E. Sergile 2001. Biogeography of the West Indies: patterns and perspective. Second edition. CRC Press, Boca Raton. Google Scholar



De kosmopolitische Kerkuil Tyto alba is de enige uilensoort die op Bonaire, Nederlandse Antillen, voorkomt. De soort zit vooral op de kalksteenhellingen die het eiland omzomen. Bonaire is slechts 288 km2 groot, en ligt 87 km ten noorden van Venezuela. Er heerst een aride klimaat met een gemiddelde temperatuur van 28°C en een gemiddelde neerslag van 463 mm per jaar. Over het menu van de Kerkuilen van Bonaire is niets bekend. In februari-maart 2003 werden daarom op 25 verschillende roestplekken 233 verse braakballen verzameld; deze waren goed voor 755 identificeerbare prooiresten. Er werden opvallende verschillen in samenstelling van menu gevonden, afhankelijk van de verzamelplek. Waar op de ene locatie insecten ontbraken in het menu, en een zangertje Dendroica petechia en Zwarte Ratten Rattus rattus de hoofdtoon voerden, bestonden de braakballen op andere plekken overwegend uit insecten, of uit verschillende vogelsoorten, al dan niet aangevuld met reptielen. Deze verschillen bleven overeind als de prooikeus werd uitgedrukt in biomassa. In vergelijking met braakbalanalyses van Kerkuilen eiders uit het Caribische gebied, waaronder de rest van de Nederlandse Antillen, de Turks - en Caicos Eilanden, de Kaaimaneilanden, Hispaniola en Jamaica, bleken de uilen van Bonaire veel insecten en vogels te vangen. Eiders betraf dat overwegend ratten en muizen, en in mindere mate vogels. Mogelijk dat het aride klimaat van Bonaire tot een veelzijdiger menu heeft geleid, waarbij insecten en reptielen een groter aandeel in de voedselkeus vormen. Daarnaast is het mogelijk dat sommige uilen van Bonaire zieh hebben gespecialiseerd in bepaalde prooisoorten. (RGB)

Maarten Flikweert, Tineke G. Prins, John A. de Freitas, and Vincent Nijman "Spatial Variation in the Diet of the Barn Owl Tyto alba in the Caribbean," Ardea 95(1), 75-82, (1 June 2007).
Received: 31 March 2006; Accepted: 1 February 2007; Published: 1 June 2007

Back to Top