Eared Owls &Lpar;<I>Asio Otus</I>

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Eared Owls &Lpar;<I>Asio Otus</I> DECEMBER 1994 SHORT COMMUNICATIONS 265 COLLOPY,M.W. AND K.L. BILDSTEIN. 1987. Foraging relation to prey biomassand habitat structure.Condor behaviorof northernharriers wintering in southeastern 92:107-112. salt and freshwater marshes. Auk 104:11-16. PYLYPE½,B. 1991. Impacts of fire on bird populations CONOVER,W.J. 1980. Practical nonparametricstatistics. in a fescueprairie. Can. Field-Nat. 105:346-349. 2nd ed. John Wiley, New York, NY U.S.A. RUDOLPH,S.G. 1982. Foraging strategiesof American HAMERSTROM,F.N. 1974. Raptor Management. Pages kestrelsduring breeding.Ecology 63:1268-1276. 5-8 in F.N. Hamerstrom, B.E. Harrell, and R.R. SCHIPPER,W.J.A., L.S. BURMA AND P. BOSSENBROEK. Olendorff [EDS.],Management of raptors. Raptor Res. 1975. Comparative study of hunting behaviorof win- Rep. 2. tering hen harriers (Circuscyaneus ) and marshharriers (Circusaeruginosus). Ardea 63:1-29. JtaqES,S.W. 1985. Habitat selectionin raptorial birds. SMALLWOOD,J.A. 1987. Sexual segregationby habitat Pages159-188 in M.L. Cody [ED.], Habitat selection in Americankestrels wintering in southcentralFlorida: in birds. Academic Press, New York, NY U.S.A. vegetativestructure and responsesto differential prey LUDWIG, J.A., AND J.F. REYNOLDS. 1988. Statistical availability. Condor89:842-849. ecology.Wiley and SonsInc., New York, NY U.S.A. , M. WOODRE¾,M.J. SMALLWOODAND M.A. MILLSAP,B.A., K.W. CLINE ANDB.A. GIRON PENDLETON. KETTLER. 1982. Foraging by cattle egretsand Amer- 1987. Habitat Management. Pages215-237 in B.A. ican kestrelsat a fire's edge.]. Field Ornithol.53:171- Giron Pendleton,B.A. Millsap, K.W. Cline, and D.M. 172. Bird lEDs.I, Raptor managementtechniques manual. TOLAND,B.R. 1987. The effect of vegetativecover on Natl. Wildl. Fed., Washington,DC U.S.A. foraging strategies,hunting success,and nesting dis- PETERSON,K.L. AND LB. BEST. 1987. Effects of pre- tribution of American kestrelsin central Missouri. J. scribedburning on nongamebirds in a sagebrushcom- Raptor Res. 21:14-20. munity. Wildl. Soc.Bull. 15:317-329. PRESTON,C.R. 1990. Distribution of raptor foraging in Received24 January 1994; accepted6 August 1994 ]. Raptor Res. 28(4):265-268 ¸ 1994 The Raptor ResearchFoundation, Inc. WINTER DIET or LONG-EAREDOWLS (AsIO OTUS) IN THE PO PLAIN (NORTHERN ITALY) PAOLO GALEOTTI AND LUCA CANOVA Dipartimentodi BiologiaAnitaale Universitddi Pavia - Piazza Botta 9, 27100 Pavia, Italy KEY WORDS: foodhabits; diet; Italy; long-earedowl; Asio part of their Italian wintering and breedingrange (Ga- otus. leotti 1990). In this paper, we review the diet of long-earedowls in The winter diet of the long-earedowl (Asiootus) has the Po Plain to: (1) providenew information on the trophm beenwell documentedin northernand centralEurope and nicheof southernwintering populationsof long-earedowls, North America (see Cramp 1985 for review), but there (2) comparelocal diets, and (3) determinethe hunting are few data for southernEurope and particularly Italy. habitatsmost utilized by the species. In northern Europe, the long-eared owl specializesin STUDY AREAS AND METHODS hunting voles(Microtus spp.) in open fields (Herrera and Hiraldo 1976), and it is considered a restricted feeder This area has a sublittoralcontinental temperate climate (Marti 1976, K511ander1977, Nilsson 1981). Likewise, with two peaksof rainfall in spring and autumn; during •n the Mediterranean regionvoles are the mostimportant winter the mean temperature ranges from 0-10øC and precipitationaverages 50-60 mm monthly. componentin the diet of long-earedowls (Araujo et al. Pelletswere collectedbetween January and March from 1973, Tome 1991). Only three studies(Gerdol and Perco eight winter roosts located in the Po Plain. Roosts 1, 2, 1977, Casini and Magnaghi 1988, Canova 1989) have and 3 (Table 1) were closeto the easternedge of the study reportedthe diet and prey selectionof long-earedowls in area, a few kilometers from the Adriatic Sea, while all the Po Plain of northernItaly, which is the mostimportant other roostswere locatedin Lombardy, the central part 266 SHORT COMMUNICATIONS VOL. 28, NO. 4 DECEMBER 1994 SHORT COMMUNICATIONS 267 of the Po Plain. Roostswere between25-450 km apart. rare prey in the diets. The frequencyof farmland species The habitattypes surrounding each roost (2.5 km radius) in the diet (Rattusrattus, Apodemus agrarius, and Microtus are reported in Table 1. arvalis) increasedtoward the east,while woodlandspecies Although the long time span over which pellets were (Clethrionomysglareolus, and Microtus multiplex) were collected(16 yr) couldbe responsiblefor variation in local preyedon more often at westernsites. This was consistent diets, we found no evidenceof fluctuations in small rodent with the localized distribution of Clethrionomysglareolus populationsin northern Italy among years (L. Canova which is locally abundantin woodedhabitats in the west- unpubl. data). Moreover, there is evidencethat somevole ern portion of the Po Plain, but scatteredor absentin the speciesliving in Mediterraneanregions are notcyclic (Par- East (Canova et al. 1991). Hygrophilousspecies were also adis and Guedon 1993). Finally, the diet of long-eared mainly exploitedin westernlocations (roosts 4, 6, and 8), owls can be more variable between seasons than between where numerous ditches and canals were associated with years (Nilsson 1981). Therefore, we believethat, taken rice fields. together,these findings justify our tentativecomparison CONCLUSIONS amonglocal diets irrespective of the yearsin which pellets were collected. The diet of wintering long-eared owls in the Po Plain All pellets were examined using standardtechniques consistedmainly of mice, whereas elsewherein Europe (Yalden 1977). Prey remainswere identifiedusing taxo- long-earedowls prey mainly on voles (Saint Girons and nomic keys (Erome and Aulagnier 1982), and reference Martin 1973, Araujo et al. 1973, Glue and Hammond specimenscollected in the study areas.Because few work- 1974, Marti 1976, K•illander 1977, Tome 1991). This ers have identified birds to speciesin dietary studieswe differencewas probably due to both a lower richnessin consideredthem as a singlecategory. Because they were vole species(only eight of the 20 European Microtidae all smallpasserines (mainly Passerspp.), we useda mean speciesoccur in Italy) and low populationlevels in south- mass of 20 g for biomass calculations. Small mammal ern Europe comparedto the North (Herrera and Hiraldo biomass was derived from the literature (Di Palma and 1976). Moreover, the number of vole speciesdecreases Massa 1981, Galeotti et al. 1991). Frequencyby number acrossthe Po Plain from eastto west,with only four species and biomassfor each prey speciesand the mean massof beingpresent in the west (Niethammer and Krapp 1982). prey were calculatedfor diets at each roost. Voles are scarcer than mice in most habitats except in Diet breadth (basedon frequenciesof ecologicalprey- scrubs and woods (Canova and Fasola 1991, P. Galeottl categories)was determinedby the index:B = 1/R 2;p,2 and L. Canova unpubl. data). The apparently close re- (Feinsingeret al. 1981) where p is the proportionof the lationship betweendiet compositionand prey availability prey i in the total sample and R is the number of prey confirmsthe trophic plasticityof long-earedowls in their categoriescollected at eachstation; the B-index variesfrom Italian winter range (Canova 1989). 0 (no useof any resource)to 1 (full useof total resources). RESUMEN.--La dieta de Asio otus invernantes fue estu- RESULTS AND DISCUSSION diada en Po Plain al norte de Italia, a travgs de anfilisis Overall Diet. We identified 3499 prey items that de egaõrfipilasobtenidas desde ocho perchas de descanso amountedto a total biomassof 75 466 g. Prey included invernal. En contrastecon lo que ocurre en el norte y mammals (89.6%), birds (10.2%) and insects(0.2%). Al- centro de Europa, los ratonespredominaron por sobrelas though long-earedowls preyed on 16 mammal species ratas de aqua. La composici6ndietaria sugirio que las from four families, three species(Apodernus sylvaticus, Mi- tierras de cultivo eran los hfibitat de alimentaci6npreva- crotussavii, and Microraysminutus) accountedfor 64.8% lecientesalrededor de las perchas.La variaci6n dieteria of the diet and murid rodentspredominated overall (Table desdepresas de mamiferos a aves puede ocurrir en con- 1) The mean massof prey (21.5 g) was lower than that dicionesclimfiticas adversas (nieves otofiales) o en hfibitat calculated(32.2 g) by Marti (1976) from a number of urbanos. Europeanstudies; consequently, the averagemeal was also [Traducci6n de Ivan Lazo] slightlylower (51.8 g) than that reportedfrom a number of diets in northern Europe and North America (55-60 g) ACKNOWLEDGMENTS Local Diets and Feeding Habitats. Diets differedin We wish to thank D.A. Kirk and J.S. Marks for their type and proportionof mammal prey species.Murids were the most important prey categoryat all but two roosts. useful suggestionsand criticismon earlier drafts of the Microtids were the secondmost common prey used by paper, and M.T. Forlini for her help in pellet analysis. long-earedowls at all roostsbut one,and theywere preyed on more heavily at easternsites. Birds were preyed on at LITERATURE CITED all roosts,but predominatedin the diet of long-earedowls ARAuJo,J., J.M. REY,A. LANDINAND A. MORENO. 1973 in the urban roostand in willow/farmland. The impor- Contribucion al estudio del buho chico (Asio otus) en tance of birds in owl's diet at one roost was related to weather:the frequencyof bird prey increasedin relation Espafia. Ardeola19:397-428.
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