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1 December 2009 Nest-Box use by the Barn Owl Tyto alba in a Biological Pest Control Program in the Beit She'an Valley, Israel
Kobi Meyrom, Yoav Motro, Yossi Leshem, Shaul Aviel, Ido Izhaki, Francis Argyle, Motti Charter
Author Affiliations +
Abstract

Starting in 1983, nest boxes for Barn Owls Tyto alba were erected as part of a biological pest control program to deal with rodents, in Kibbutz Sde Eliyahu, and later in other agricultural fields and plantations in the Beit She'an valley, Israel. More than a decade ago, the nest box scheme was extended to include other agricultural areas in the valley, and grew from 14 boxes on 3 km2 in 1983 to about 300 boxes on 90 km2 throughout the entire Beit She'an valley in 2007. Here we present the results of a study during the 2002 through 2006 breeding seasons, in which 156 to 243 nest boxes were monitored each season. Mean occupation of nest boxes during the study was 53.5% (SE 2.1, n = 248), and a total of 596 breeding attempts were recorded, of which 85.2% successfully fledged at least one young. Yearly occupation of nest boxes varied significantly between the years, ranging from 48.1% to 73.5%. The occupancy rate of first-year nest boxes was lower than that of those available for two or more years. The occupancy rate and the number of nestlings per box (per year) were positively correlated to the distance to the closest nest box and negatively correlated to the number of nest boxes within a 500 m radius. Similar to other studies in the world, the erection of nest boxes for Barn Owls in agricultural fields proved extremely successful in the Beit She'an valley, with 86.7% (n = 248) of nest boxes being occupied at least once during the five-year study period. This high occupancy rate demonstrates not only that natural nesting sites were lacking, but also that nest boxes can be used to increase Barn Owl populations in agricultural areas, both for conservation and for biological pest control.

INTRODUCTION

The Barn Owl Tyto alba is one of the most widespread owls in the world (Burton 1984), but information on its breeding success in the Middle East is lacking. Barn Owls are secondary cavity nesters but also breed in a wide variety of natural cavities such as holes in trees (Taylor 1994), and in man-made nest sites such as buildings and nest boxes (de Bruijn 1984, Petty et al. 1994, Taylor 1994). Nest boxes are used by researchers and conservationists as a popular management tool to increase nest site availability in sites where these are lacking. Furthermore, nest boxes can be easily designed to attract specific species to breed in designated locations, and are easily accessible, which allows capture of relevant species during the non-breeding seasons (Newton 1998). In areas where natural nest sites are limited, certain raptor populations nest almost exclusively in such nest boxes (Cavé 1968, Hakkarainen & Korpimäki 1996), whereas in other locations, although natural nest sites are present, the nest boxes are used because they are preferred (Petty et al. 1994). In many places in the world nest boxes are used as a conservation tool to increase populations in areas where natural nest sites are limited (Petty et al. 1994), and also in biological pest control projects (Duckett 1976, Hafidzi et al. 1999, Hafidzi et al. 2003), which promotes reduced use of pesticides (mainly rodenticides) and increased public awareness of owls.

Beginning in 1983, nest boxes for Barn Owls were erected first at Kibbutz Sde Eliyahu and later in other locations in agricultural fields and plantations in the Beit She'an valley Israel, as part of a biological pest control program to deal with rodents (Aviel et al. 2003). More than a decade ago, the installation of the nest boxes was extended to include other agricultural fields in the Beit She'an valley and increased from 14 boxes on 3 km2 in Sde Eliyahu in 1983 to about 300 boxes on 90 km2 throughout the entire Beit She'an valley in 2007. In the past, the major part of the project was applied with little scientific background, little analysis of the breeding data, and reference to only a few scientific publications (Tores et al. 2005). Barn Owls are one of the most common owls in Israel (Shirihai 1996) but little information has been published on them other than on their diet (Dor 1982, Pokines & Peterhans 1997, Yom-Tov & Wool 1997, Tores & Yom-Tov 2003, Tores et al. 2005, Charter et al. 2007, Motro unpubl. data), and very few data are available on their breeding success (Kahila, unpubl. data). The main objectives of this study were to characterize the use of nest boxes by Barn Owls breeding in the Beit She'an valley, Israel, as part of a biological pest control program to deal with rodents.

METHODS

The study site comprised agricultural fields, orchards, and plantations located in the Beit She'an valley, Israel (32°30′N, 35°30′E), 150–250 m below sea level. The climate is arid with maximum and minimum mean daily temperatures (during March and July 1999) of 32.3°C and 16.7°C, respectively, and average yearly rainfall of 267 mm (for 2001–06).

The study site is divided mainly into crop fields and date plantations (combined area 90 km2). The crop fields comprise cattle fodder (wheat, sweet corn, alfalfa, clover, vetch and oats), grain crops and seeds (wheat and sweet corn) and spices and herbs (oregano, hyssop, basil, and dill). During the study 156–243 nest boxes (50 cm wide × 75 cm long × 50 cm high; entrance 25 cm high × 15 cm, raised 2.5 to 3 m above the ground) located in the fields and date palm plantations were monitored yearly. The nest boxes were erected between 1983 and 2005 in Kibbutz Tirat Tsvi, Kibbutz Maoz Haim, Kibbutz Kfar Ruppin, Kibbutz Neve Eitan, Kibbutz Ein Hanatziv, and Kiibutz Sde Eliyahu. The project was led by the Israel Ornithological Center, Society for the Protection of Nature, Israel, during 2002–04 and by Tel Aviv University and the Society for the Protection of Nature during 2005–06.

Active nests were determined by visits during the 2002 to 2006 breeding seasons for each breeding attempt (defined as a nest in which eggs were laid, after Steenhof 1987). All nestlings and some of the adults found inside the nest boxes were banded. Mean occupancy rate of nest boxes was noted (number of breeding attempts/number of years the nest box was available during the period of study); as was the percentage of breeding pairs that successfully fledged at least one young; and the mean number of young (number of young per breeding attempts/number of years the nest box was available during the period of study minus the number of dead birds found in the nest boxes after the young had fledged). Similar to breeding Barn Owls in the USA (Taylor 1994), Israel Barn Owls are very sensitive during incubation and abandon clutches when disturbed, so the clutch size of most pairs was unknown and is not presented here. Distances between nest boxes and number of nest boxes within a 500 m radius were calculated using ESRI ArcMap 9.2. Data are presented as means ± SE. All statistical tests were two-tailed and all tests were non-parametric. Descriptive breeding data were analyzed using Kruskal—Wallis ANOVA and Spearman correlations to analyze correlations. Chi-square tests were used for comparing nest success. Levels of significance were set at P < 0.05. Statistical analyses were performed using Statistica 7.1 software.

RESULTS

Mean percentage of nest boxes occupied was 53.5% ± 2.1 (n = 248), during which time 596 breeding attempts were recorded, of which 85.2% successfully fledged at least one young. Yearly occupation of nest boxes was significantly different between years (χ2 = 35.0, df = 4, P < 0.001), ranging from 48.1% (n = 243) to 73.5% (n = 215) (Table 1). The percentage of first-year nest boxes occupied was lower than that of older boxes (χ2 = 20.8, df = 4, P < 0.001). During the study, 86.7% of nest boxes were occupied at least once and only 13.3% were never occupied. The average number of nestlings per breeding attempt per nest box was 3.7 ± 1.5 (n = 211).

Table 1.

Breeding parameters of Barn Owls breeding in nest boxes located in the Beit She'an valley, Israel, during the 2002–06 breeding seasons. Sample sizes are in parentheses.

t01_463.gif

Figure 1.

A–D. Correlations between breeding parameters (percentage of nest boxes occupied and number of nestlings) to the distance from the nearest nest box and the number of nest boxes within a 500-m radius.

f01_463.eps

The mean distance between boxes was 182.8 ± 7.5 (n = 220), and the mean number of nest boxes in a 500 m radius was 6.33 ± 0.3 (n = 220). The distance of the closest nest box was positively correlated with both the percentage of nest boxes occupied (rs = 0.22, n = 213, P < 0.01; Fig. 1A), and the number of nestlings per box (rs = 0.17, n = 190, P < 0.05; Fig. 1B). The number of nest boxes within a 500 m radius per nest box was correlated with both the percentage of nest boxes occupied (rs = -0.17, n = 220, P < 0.05; Fig. 1C) and the number of nestlings per nest box (rs = -0.17, n = 198, P < 0.05; Fig 1D).

DISCUSSION

Similar to other studies in the world (Marti 1994, Taylor 1994, Petty et al. 1994), the erection of nest boxes for Barn Owls in the Beit She'an valley proved extremely successful, with 86.7% of the 248 nest boxes being occupied at least once during the five-year study. The occupancy of first year boxes was lower than in the following years but, interestingly, no differences occurred thereafter. Barn Owl nest boxes have been used in the region since 1983 and, unlike new regions to the project in Israel, where the rate of occupation of nest boxes is lower (Charter, unpubl. data), the high rate of occupancy reported in the second and following years have been an artifact of the large population of Barn Owls already present in the valley, and the length of the project.

In addition to nest boxes, Barn Owls also breed in the surveyed villages in man-made structures (Meyrom et al. 2008) and in Mexican Fan Palms Washingtonia robusta. Meyrom (unpubl. data) estimated 50 such pairs yearly, while in the fields themselves few to no nest sites are available. Even though Barn Owls breed anyway in the nest boxes, the particularly high nest box occupancy reported in this study is most likely due to a lack of nest sites in the valley.

The number of young per nest was found to be within the range of other studies (range 1.9–4.6 nestlings) in Europe (Pikula et al. 1984, Baudvin 1986, Muller 1989, Taylor 1994, Martínez & López 1999), USA (Otteni et al. 1972, Klaas et al. 1978, Marti & Wagner 1985, Marti 1994), Asia (Lenton 1984) and Africa (Wilson et al. 1984). The high occupancy of nest boxes in 2004 was probably due to a high abundance of Levant Voles Microtus socialis guentheri, which peaked during that year in the study sites as well as in some other agricultural regions in Israel (Aviel pers. comm.). No rodent trapping took place during the study, but Motro (pers. comm.) counted vole burrows during the study and found more burrows during 2004 than in other years (in some areas almost 10 000 burrows/ha). The percentage of nest boxes occupied and the number of nestlings per box were positively correlated to the distance of the closest nest box and negatively correlated to the number of nest boxes within a 500 m radius per nest box, possibly due to intraspecific competition and first-year Barn Owls breeding in crowded areas. However, these two latter hypotheses require experimental verification.

Examination of pellets from the region revealed that 90% of the Barn Owls diet is composed of rodents from agricultural fields and plantations (Tores et al. 2005, Charter et al. 2007). The presence of Barn Owls is thus welcomed by farmers. Since the establishment of the pest control project, many farmers use Barn Owls as an alternative method of rodent control and thereby drastically reduce the use of rodenticides. The high occupancy of nest boxes by Barn Owls detailed in this study demonstrates, as also found in other studies throughout the world, that not only were natural nest sites lacking in the area, but also that nest boxes offer Barn Owls alternative nest sites, that can increase owl numbers in agricultural fields both for conservation and biological pest control projects. Further studies are needed to compare between the use of Barn Owls and of pesticides in order to determine whether these result in economic differences in crop yield.

ACKNOWLEDGEMENTS

To David Glasner, Eitan Shapira, Uria Shahak, and Moshe Nachtomi for promoting nest box placement in valley. To Ena Olze, Ben Davir, Manor Gor, Roi Ben-Yossef, Yehezkel Giladi, for their assistance in checking nest boxes and Michael Hyman for weather data,. Special thanks to Desh Institute (SPNI's Open Landscape Institute) for their assistance with using GIS and Naomi Paz for editorial help. Thanks to David H. Johnson and Alan Sieradzki for comments on the text. The project was led by the Israel Ornithological Center (special thanks to Dan Alon) of the Society for the Protection of Nature, Israel, and funded by the European Commission during 2002–2004 and led and funded by the Tel Aviv University, The Hebrew University of Jerusalem, and Society for the Protection of Nature, Israel during 2005 to 2006.

REFERENCES

1.

S. Aviel , Y. Motro , G. Kahila Bar-Gal & Y. Leshem 2003. The Barn Owl as a biological pest control of rodents. Billet Studios Press, Tel Aviv. (In Hebrew) Google Scholar

2.

H. Baudvin 1986. La reproduction de la Chouette Effraie, Tyto alba. Le Jean le-Blanc 25: 1–125. Google Scholar

3.

A.J. Cavé 1968. The breeding of the kestrel (Falco tinnunculus) in the reclaimed area Oostelijk Flevoland. Neth. J. Zool. 18: 313–407. Google Scholar

4.

M. Charter , I. Izhaki , L. Shapira & Y. Leshem 2007. Diets of Urban Breeding Barn Owls, Tyto alba in Tel Aviv, Israel. Wilson J. Ornithol. 119: 484–485. Google Scholar

5.

Bruijn O. de 1994. Population ecology and conservation of the Barn Owl Tyto alba in farmland habitats in Liemers and Achterhoek (The Netherlands). Ardea 82: 1–109. Google Scholar

6.

M. Dor 1982. The Barn Owl- An aid to science. Torgos 2: 29–35. Google Scholar

7.

J.E. Duckett 1976. Owls as major predators of rats in oil palm estates with particular reference to Barn Owl (Tyto alba). Planters, Kuala lumpur 52: 4–15. Google Scholar

8.

M.N. Hafidzi & N. Mohd 2003. The use of the Bam Owl, Tyto alba, to suppress rat damage in rice fields in Malaysia. In: G.R. Singleton , L.A. Hinds , C.J. Krebs & D.M. Spratt (eds) Rats, mice and people: Rodent biology and management. ACIAR Monograph No. 96, pp. 274–276. Google Scholar

9.

M.N. Hafidzi , A. Zulkifli & A.A. Kamaruddin 1999. Barn Owls as a biological control agent of rats in paddy fields. Towards efficient biodiversity and bioresources management for effective biological control In: Proc. Symp. on biological control in the tropics, Serdang, Malaysia. MARDI Training Centre, Kuala Lumpur, pp. 85–88. Google Scholar

10.

H. Hakkarainen & E. Korpimäki 1996. Competitive and predatory interactions among raptors: an observational and experimental study. Ecology 77: 1134–1142. Google Scholar

11.

E.E. Klaas , S.N. Wiemeyer , H.M. Ohlendorf & D.M. Swineford 1978. Organochlorine residues, egg shell thickness, and nest success in Barn Owls from the Chesapeake Bay. Estuaries 1: 46–53. Google Scholar

12.

G.M. Lenton 1984. The feeding and breeding ecology of Bam Owls, Tyto alba, in peninsular Malaysia. Ibis 126: 551–575. Google Scholar

13.

C.D. Marti 1994. Barn Owl reproduction: Patterns and variation near the limit of the species distribution. Condor 96: 468–484. Google Scholar

14.

C.D. Marti & P.W. Wagner 1985. Winter mortality in common Bam Owls and its effects on population density and reproduction. Condor 87: 111–115. Google Scholar

15.

J.A. Martínez & G. López 1999. Breeding ecology of the Bam Owl Tyto alba in Valencia (SE Spain). J. Ornithol. 140: 93–99. Google Scholar

16.

K. Meyrom , Y. Leshem & M. Charter 2008. Bam owl Tyto alba breeding success in man- made structures in the Jordan Rift valley, Israel. Sandgrouse 30: 134–137. Google Scholar

17.

Y. Muller 1989. Fluctuations d'abondance de la Chouette effraie Tyto alba en Alsace-Lorraine de 1977–1988. Aves 26: 131–141. Google Scholar

18.

I. Newton 1998. Population limitation in birds. Academic Press, London. Google Scholar

19.

L.C. Otteni , E.G. Bolen & C. Cottam 1972. Predator-prey relationships and reproduction of the Barn Owl in Southern Texas. Wilson Bull. 48: 434–448. Google Scholar

20.

S.J. Petty , G. Shaw & D.I.K. Anderson 1994. Value of nest boxes for population studies and conservation of owls in coniferous forests in Britain. J. Raptor. Res. 28: 134–142. Google Scholar

21.

J.M. Pikula , M. Beklova & V. Kubik 1984. The breeding bionomy of Tyto alba. Acta Sci. Nat. Acad. Sci. Bohemoslov. Bmo 18: 1–53. Google Scholar

22.

J.T. Pokines & J.K. Peterhans 1997. Bam Owls Tyto alba taphonomy in the Negev Desert, Israel. Israel J. Zool. 43: 19–27. Google Scholar

23.

H. Shirihai 1996. The Birds of Israel. Academic press, London. Google Scholar

24.

K. Steenhof 1987. Assessing raptor reproductive success and productivity. In: Giron Pendleton B.A., B.A. Millsap , K.W. Cline & D.M. Bird (eds) Raptor management techniques manual. Natl. Wildl. Fed., Washington, DC U.S.A, pp. 157–170. Google Scholar

25.

I.R. Taylor 1994. Bam Owls. Predator-prey relationships and conservation. Cambridge University Press, Cambridge. Google Scholar

26.

M. Tores & Y. Yom-Tov 2003. The diet of the Barn Owl (Tyto alba) in the Negev Desert. Israel J. Zool. 49: 233–236. Google Scholar

27.

M. Tores , Y. Motro , U. Motro & Y. Yom-Tov 2005. The Barn Owl—a selective opportunist predator. Israel J. Zool. 51: 349–360. Google Scholar

28.

R.T. Wilson , M.P. Wilson & J.W Durkin 1986. Breeding biology of the Bam Owl Tyto alba in central Mali. Ibis 128: 81–90. Google Scholar

29.

Tov Y. Yom & D. Wool 1997. Do the contents of Bam Owl pellets accurately represent the proportion of prey species in the field? Condor 99: 972–976. Google Scholar

Appendices

SAMENVATTING

Vanaf 1983 zijn in Israël in het kader van een biologisch bestrijdingsprogramma tegen knaagdieren nestkasten voor Kerkuilen Tyto alba geplaatst, eerst alleen in de kibboets Sde Eliyahu, later ook in de rest van de Beit She'an vallei. In 1983 waren er 14 nestkasten op 3 km2, in 2007 300 op 90 km2. In dit artikel worden de resultaten van de broedseizoenen 2002 tot en met 2006 (156–243 nestkasten gecontroleerd per seizoen) besproken. De bezetting van de kasten varieerde van 48,1% tot 73,5% en bedroeg gemiddeld 53,5%. Dit leverde 596 broedpogingen op, waarvan 85,2% minstens één uitgevlogen jong voortbracht. De bezettingsgraad was het eerste jaar na het ophangen van de kasten lager dan later. De bezettingsgraad en het aantal nestjongen per jaar correleerden beide positief met de afstand tot de dichtstbijzijnde nestkast en negatief met het aantal nestkasten binnen een straal van 500 m. Tijdens het vijf jaar durende onderzoek waren 215 kasten (86,7% van de 248) minstens eenmaal bezet. De hoge bezettingsgraad toont aan dat aanvankelijk natuurlijke nestgelegenheid in de onderzochte landbouwgebieden ontbrak en dat het aanbrengen van nestkasten kan leiden tot een toename van het aantal Kerkuilen in zulke gebieden. Uit oogpunt van soortbescherming en de biologische bestrijding van knaagdieren een interessant gegeven.

Kobi Meyrom, Yoav Motro, Yossi Leshem, Shaul Aviel, Ido Izhaki, Francis Argyle, and Motti Charter "Nest-Box use by the Barn Owl Tyto alba in a Biological Pest Control Program in the Beit She'an Valley, Israel," Ardea 97(4), 463-467, (1 December 2009). https://doi.org/10.5253/078.097.0410
Published: 1 December 2009
KEYWORDS
agriculture
barn owl
biological pest control
Israel
nest boxes
occupancy
Tyto alba
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