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88, Badzinski 2007, Hitch and Leberg 2007, Melles Et Al Nest site characteristics of Hooded Warblers at the northern edge of their breeding range By Benjamin J. Walters and Erica Nol Introduction The northern limit of the breeding range of the Hooded Warbler ( Setophaga citri - na ) extends from southeastern Nebraska to the southern Great Lakes Region and includes Wisconsin, Michigan, southern Ontario and New York (Chiver et al. 2011). The southern limit of the Hooded Warbler’s breeding range extends from Florida to eastern Texas, although breeding in California has been documented (Chiver et al. 2011). Hooded Warblers have been undergoing a population and range expansion in the northeastern portion of their range (Gartshore 1988, Badzinski 2007, Hitch and Leberg 2007, Melles et al . 2011). For example, between the first (1981 – 1985) and second (2001 – 2005) Ontario Breeding Bird Atlas, Hooded Warblers were found in 68 new 10 km x 10 km atlas squares, and 12 of the same squares, while the species became absent in eight squares (Cadman et al . 2007). The expansion has generally been attributed to climate change (Hitch and Leberg 2007, Melles et al. 2011), but may Photo by also be a result of increases in suitable Ben Walters forested habitat within portions of its range (Badzinski 2007). 88 Ontario Birds August 2011 Ganaraska Forest Figure 1. Location of the Ganaraska Forest owned by the Ganaraska Region Conservation Authority. The Hooded Warbler is listed as a Friesen et al. 2000, Whittam et al. “threatened” species in the federal 2002, Badzinski 2003). Species at Risk Act , and a “special con - Some breeding evidence north of cern” species in Ontario’s Endangered this range, such as a male feeding young Species Act , 2007. Less than 1% of the east of Peterborough, Ontario, in 1963 Hooded Warbler’s breeding range is in (Sadler 1968), has been reported, but a Canada (Environment Canada 2011) breeding population was not discov - and all of that is in southern Ontario ered. Evidence now suggests that (Badzinski 2007). The first document - Hooded Warblers may breed as far ed occurrence of the Hooded Warbler north as the Bruce Peninsula, Lake at the northern extent of its range in Simcoe-Rideau and the southern Can - Ontario was in 1878 and nesting was adian Shield regions (Badzinski 2007). first documented in 1949 (Peck and For example, an unsuccessful breeding James 1987). The northern extent of attempt was documented at Awenda the Canadian Hooded Warbler popula - Provincial Park in 1989 (Weir 1989) tion was considered to inhabit primari - and a pair with fledged young w as ly Carolinian Forests in southwestern observed there in 2010 (Friends of Ontario (Bisson and Stutchbury 2000, Awenda Park 2011). Volume 29 Number 2 89 Hooded Warblers mainly breed in harvest (Gart shore 1988, Heltzel and mid- to late-successional mixed decidu - Leberg 2006) and in hurri cane created ous forests. At the northern extent of gaps after two and three years (Green - their range, such as in Ontario, Penn - berg and Lanham 2001) rather than in sylvania, Ohio, and Missouri, they control stands without gaps. In some breed in beech-maple and oak-hickory regions, Hooded Warblers are observed dominated forests (Horn and Ben - only in sites that have undergone forest ninger-Truax 1997, Friesen et al . 2000, harvesting (Wallendorf et al. 2007, this Howlett and Stutchbury 2003, Wallen - study ). As well, because of their prefer - dorf et al . 2007, Chiver et al . 2011). At ence for dense understory, nesting can the southern edge of their range they occur close to skidder trails, old logging breed in wet lowlands such as cypress- roads and roads (Gartshore 1988, gum swamps (Heltzel and Leberg Howlett and Stutchbury 1996). 2006). Hooded Warblers will also In 2006, a small nesting population inhabit forests with coniferous compo - of Hooded Warbler was observed in the nents such as oak-pine in south-central Ganaraska Forest in south-central Ont - Missouri (Wallendorf et al. 2007), ario, approximately 200 km north of mature pine forests in North (Green - the previously documented northern berg and Lanham 2001) and South range (Friesen et al. 2000) (Fig. 1). Un - Carolina (Sargent et al. 1997) and coni - like the southwestern Ont ario popula - ferous plantations in southwestern tion in the Carolinian Forest Zone, this (Badzinski 2003) and south-central south-central Ontario population Ont ario ( this study ). inhabits the Great Lakes-St. Lawrence Hooded Warblers prefer mature Forest Zone. Similarly, however, the forests with a high canopy (Whittam Ganaraska Forest is mainly underlain and McCracken 1999), dense under - by sandy soils as is much of this species’ story, and canopy gaps for nest sites distribution in Ontario’s Carolinian and territories (Gartshore 1988, Whit - Forest (Gartshore 1988). The Ganaras - tam and McCracken 1999, Bisson and ka Forest is composed of beech-maple Stutchbury 2000, Friesen et al . 2000, and oak-maple forest with some mixed Pasher et al. 2007). Hooded Warbler pine-oak forest and coniferous planta - nest sites would naturally be found in tions. Som e trees and shrub s such as tree-fall gaps (Chiver et al. 2011), but tulip-tree ( Liriodendron tulipifera ), sas - because of a lack of mature forest safras ( Sassafras albidum ) and spicebush throughout their range, they are typi - (Lindera benzoin ), that are present in cally found in sites that are selectively the Hooded Warbler’s south western logged (Tarof and Stutchbury 1996, Ont ario breeding habitat, are absent Whittam and McCracken 1999, from the Gan araska Forest. Therefore, Greenberg and Lanham 2001). Hood - differences in forest structure such as ed Warblers appear to be more abun - tree spacing, canopy height and clo - dant at sites within 12 to 18 years after sure, and shrub laye r density, between 90 Ontario Birds August 2011 Figure 2. Deciduous habitat used by nesting Hooded Warblers in the Ganaraska Forest. Photo by Ben Walters the Carolinian Forest Zone and the they could be the same across this Ganaraska Forest could result in differ - species’ Canadian range. Furthermore, ences in habitat selection. Our objective identifying the similarities or differ - was to determine whether the structure ences in structural characteristics would of nesting habitat in the Ganaraska For - help in future assessments of potential est was similar to that in other areas of breeding habitat availability in the this species’ range, particularly in Great Lakes-St. Lawrence Forest Z one. southwestern Ontario. Determining We expected that Hooded W ar blers the similarity in nest-site habitat would use nest -site s with th e sam e requirements among forest types would structural charac teristics as as individu - be useful for understanding what forest als to the south , despite a difference in management practices are most benefi - forest type. We expected that, because cial to Hooded Warblers and whether Hooded Warblers are a gap-dependent Volume 29 Number 2 91 species (Bisson and Stutchbury 2000, surroun ding land use is largely agricul - Shifley et al. 2006), nesting habitat tural. Pa sture lands for horse and cattle would be structurally similar to areas production dominate with some hay to the south with dense undergrowth fields and few row crops. Similar to the and an open canopy. St. Williams forest where a large per - centage of Canada’s Hooded Warblers Methods breed (Whittam et al. 2002), tree har - Study area vesting in the Ganaraska Forest is per - The Ganaraska Forest (N44° 5.8’ formed by either single-tree selection W78° 30.5’), owned by the Ganaraska in mixed deciduous forest or row-thin - Region Conservation Authority, is a ning in pine plantations. 4,228 ha forest on the Oak Ridges Moraine (Figure 1). The boundaries of Nest site vegetation the Ganaraska Forest are within characteristics Durham Regional Municipality, an d Hooded Warbler nest sites were located Peterboroug h and Northumberland in 2006 ( n = 4) and 2007 ( n = 8) counties. Forest soils are dominated by through intensive foot searches near Pontypool series gravely sand, Dun - singing males and agitated females. donald sandy loam, Bridgman sand Vegetation characteristics were meas - and Pontypool sandy loam underlain ured at eight of the 12 sites in 200 7. by Black River Trenton group lime - We measured the habitat character - stone. Forest elevations range from 200 istics at nest sites within a 5m x 10m m to 408 m above sea level (Tedford area centered on the nest. The habitat 1978). variables measured included percent In the early 1900s, reforestation of cover of overstory canopy cover, stem the Ganarask a Forest was necessar y density of saplings and trees, ground to stabilize the soils that began to erode cover and vegetation stratification after they were cleared for farmland. (Kilgo et al. 1996). We then compared The forest is approximately equally the vegetation characteristics from the comprised of coniferous plantation nest patch to the vegetation character - and mixed hardwoods. The coniferous istics at randomly chosen unused sites plantations consist of red pine ( Pinus (Kilgo et al. 1996, Bisson and Stutch - resin osa ) with smaller areas of scots bury 2000). To test nest-site selection, pine ( Pinus sylvestris ), jack pine ( Pinus we pooled nests from 2006 and 2007 bank siana ), white spruce ( Picea glau - because of small sample sizes (Whittam ca ), European larch ( Larix deciduas ) et al. 2002). and American larch ( Larix laricina ). All statistical analyses were per - The mixed hardwoods are dominated formed using STATISTICA (Statsoft by red oak ( Quercus rubra ), sugar 2004). Normality was tested using the maple ( Acer sacc harum ) and poplar Kolmorogov-Smirnov test and homo - (Populus spp .) (Tedford 1978). The geneity of variances was tested using 92 Ontario Birds August 2011 the Levene’s test. Variables tha t were distance. Litter depth was measured at normally distributed, or normalized the edge of the plot in all cardinal direc - using a transformation, were tested for tions and at the centre point of the plot.
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