Winter Habitat Use by Boreal Chickadee Flocks Within a Managed Forest Landscape

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Winter Habitat Use by Boreal Chickadee Flocks Within a Managed Forest Landscape ADAM HADLEY WINTER HABITAT USE BY BOREAL CHICKADEE FLOCKS WITHIN A MANAGED FOREST LANDSCAPE Mémoire présentée à la Faculté des études supérieures de l’Université Laval dans le cadre du programme de maîtrise en sciences forestières pour l’obtention du grade de de maître ès sciences (M.Sc.) FACULTÉ DE FORESTERIE ET DE GÉOMATIQUE UNIVERSITÉ LAVAL QUÉBEC 2006 © Adam Hadley, 2006 i Résumé On considère que les espèces résidentes d’oiseaux habitant les latitudes nord sont les espèces les plus exposées aux effets de la perte d’habitat et de la fragmentation de la forêt boréale. Nous connaissons très peu l’écologie hivernale des oiseaux boréaux résidents bien que la dynamique de leur population semble être fortement influencée par des événements qui ont lieu en-dehors de la saison de reproduction. Mon objectif était de déterminer comment l’augmentation de la densité des lisières forestières et la réduction de la proportion de forêt boréale mature influencent une espèce résidente d’oiseau. J’ai enregistré les mouvements de 85 volées hivernales de mésanges à tête brune (Poecile hudsonica) non marquées et de sept volées dont les membres étaient marqués individuellement avec des bagues de couleur. De janvier à mars (2004 et 2005), j’ai suivi des volées de mésanges en raquettes à la forêt Montmorency et j’ai enregistré leurs déplacements en temps réel en utilisant un récepteur GPS. Grâce aux volées d’individus marqués, j’ai découvert que les mésanges à tête brune comptent en moyenne 4 oiseaux par volée, occupent un territoire hivernal moyen de 14.7 ha et conservent les mêmes membres dans leur volée pendant l’hiver. À partir des déplacements de volées sur 74 km, les mésanges à tête brune préféraient fortement les peuplements forestiers matures (>7m de hauteur), utilisaient un peu moins les peuplements d’arbres en régénération (4-7 m) et évitaient les jeunes peuplements (<4 m) et les milieux ouverts. Les volées de mésanges ne s’intéressaient pas aux lisières forestières lorsqu’elles utilisaient des peuplements forestiers matures. Par contre, dans les peuplements en régénération, les volées étaient plus près des lisières ouvertes (41±6 m) ainsi que des lisières de peuplements forestiers matures (11±2 m) que prévu. Les volées de mésanges à tête brune n’évitaient pas les lisières exposées durant des conditions hivernales difficiles. Une augmentation de la densité des lisières, due à la coupe totale dans les forêts boréales, ne réduit pas nécessairement la qualité des parties de forêt restantes pour la saison hivernale des mésanges à tête brune et ce, même pendant des températures inclémentes. Par contre, j’arrive à la conclusion que l’exploitation forestière réduira l’habitat hivernal optimal de cette espèce. ii Abstract Resident bird species inhabiting northern latitudes are considered to be the species most exposed to the effects of habitat loss and fragmentation of boreal forests. Despite the fact that their population dynamics appear to be strongly determined by events occurring during the non-breeding season, we have little knowledge of the winter ecology of boreal birds. My objective was to determine how increasing edge densities and reducing the proportion of mature boreal forest will affect a resident bird species. I recorded movements of 85 unmarked and seven colour banded winter flocks of the little-known Boreal Chickadee (Poecile hudsonica), in a 66 km2 boreal forest harvested for timber near Quebec City, Quebec, Canada. From January-March (2004 and 2005), I followed flocks on snowshoes and recorded their paths in real time using a handheld GPS receiver. Using marked individuals, I found winter Boreal Chickadee flocks included an average of 4 individuals, occupied a mean winter home range of 14.7 ha and showed stable membership. Based on 74 km of flock movements, Boreal Chickadees strongly preferred mature forest (>7 m in height), used regenerating forest (4-7 m) to a lesser extent and avoided younger stands (<4 m) and open areas. Chickadee flocks showed no response to forest edges when using mature forest stands. However, inside regenerating forest, flocks were significantly closer to both open edges (41 ± 6 m) and mature forest boundaries (11 ± 2 m) than would be expected from random use of the habitat. Boreal Chickadee flocks did not avoid exposed edges during harsh weather conditions. In fact, on colder days, they were found disproportionately more often along edges between mature and regenerating stands. Increasing edge densities, resulting from clearcutting in boreal forest, does not necessarily reduce the winter suitability of remaining forest patches, even under inclement weather. However, I conclude that forest harvesting will result in a reduction of optimal wintering habitat for this species. iii Preface I would like to thank my director André Desrochers for his help with the conception of this project and his assistance with the choice and implementation of the analysis involved. André’s enthusiasm and expertise definitely helped to encourage me throughout the execution of the study. I would also like to thank my family and the Fundy Wolfe Lake bird crew for providing me with the enthusiasm and drive necessary to accomplish the physically demanding fieldwork involved during the study. The Chickadee flocks followed during this project deserve special mention for their unwavering ability to lead me across the steepest ravines and through the toughest terrain at their disposal. Lastly, a special thanks to all of my lab mates who helped me with my French and provided helpful advice. This mémoire contains two scientific articles submitted to international caliber journals. I will be first author and André Desrochers second author. CHAPTER 1: Hadley1, A. S., and A. Desrochers1. Winter habitat use by Boreal Chickadee flocks. To be submitted to The Wilson Journal of Ornithology (Formerly the Wilson Bulletin) 1Centre de recherche en biologie forestière, Faculté de foresterie et de géomatique, Université Laval, Québec, Québec, G1K 7P4, Canada. CHAPTER 2: Hadley1, A. S., and A. Desrochers1. Response of wintering Boreal Chickadees to forest edges: Does weather matter? Submitted to The Auk, February 28, 2006. 1 Centre de recherche en biologie forestière, Faculté de foresterie et de géomatique, Université Laval, Québec, Québec, G1K 7P4, Canada. iv Eric, Jane and Matthew v Table of contents Résumé.....................................................................................................................................i Abstract.................................................................................................................................. ii Preface .................................................................................................................................. iii Table of contents.....................................................................................................................v List of Tables ....................................................................................................................... vii List of figures...................................................................................................................... viii General Introduction...............................................................................................................1 Edge effects and landscape structure..................................................................................1 Concerns in boreal regions .................................................................................................2 The importance of winter ...................................................................................................2 The Boreal Chickadee ........................................................................................................3 CHAPTER 1: Winter habitat use by Boreal Chickadee flocks ..............................................5 RÉSUMÉ ................................................................................................................................6 ABSTRACT............................................................................................................................7 INTRODUCTION ..................................................................................................................7 METHODS .............................................................................................................................9 Study area ...........................................................................................................................9 Use of forest stands.............................................................................................................9 Home range estimation.....................................................................................................13 Correlates of home range size ..........................................................................................15 RESULTS .............................................................................................................................16 Use of forest stands...........................................................................................................16 Flock and home range size ...............................................................................................16 Landscape structure and home range size ........................................................................18 DISCUSSION.......................................................................................................................20
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