Plusieurs études à grande échelle ont identifié la modification ou la perte d’habitats comme menace principale à la conservation des communautés de poissons d’eau douce. Au Canada, « aucune perte nette dans la capacité productive des habitats » (NNL) est le principe directeur de la politique de gestion des habitats du ministère des Pêches et Océans. Le respect du NNL implique l’avancement des connaissances au niveau des relations entre les poissons et leurs habitats, de même que des outils pour quantifier l’impact de la modification des habitats sur les poissons. Les modèles d’utilisation de l’habitat des poissons (FHUM) sont des outils qui permettent d’améliorer nos connaissances des relations poissons – habitat, de prédire la distribution des espèces, mais aussi leurs densités, biomasses ou abondances, sur la base des caractéristiques de l’environnement. L’objectif général de mon mémoire est d’améliorer la performance des FHUM pour les rivières des basses Laurentides, en suggérant des perfectionnements au niveau de 2 aspects cruciaux de l’élaboration de tels modèles : la description précise de la communauté de poissons et l’utilisation de modèles statistiques efficaces. Dans un premier chapitre, j’évalue la performance relative de la pêcheuse électrique et de l’échantillonnage en visuel (plongée de surface) pour estimer les abondances des combinaisons d’espèces et de classes de taille des poissons en rivière. J’évalue aussi l’effet des conditions environnementales sur les différences potentielles entre les communautés observées par ces 2 méthodes d’échantillonnage. Pour ce faire, 10 sections de rivière de 20 m de longueur ont été échantillonnées à l’aide de ces 2 méthodes alors qu’elles étaient fermées par des filets de blocage. 3 plongeurs performèrent l’échantillonnage en visuel en se déplaçant de l’aval vers l’amont des sections, tout en dénombrant les espèces et classes de taille. Par la suite, nous avons fait 3 passages de pêcheuse électrique et les abondances furent estimées grâce à un modèle restreint de maximum de vraisemblance, basé sur la diminution des abondances observées. De plus grandes abondances de poissons furent observées en visuel qu’avec la pêcheuse électrique à tous les sites. La richesse spécifique observée en visuel était plus élevée (6/10) ou égale (4/10) à celle observée avec la pêcheuse électrique. Les différences entre les communautés de poissons observées à l’aide de ces 2 méthodes ne purent être reliées aux conditions environnementales. Les résultats de cette expérience sont contraires à ceux de toutes les études comparant ces 2 méthodes d’échantillonnage, lesquels suggèrent une supériorité de la pêcheuse électrique. Les conditions environnementales de notre expérience étaient distinctes de celles observées dans les autres études (absence d’arbres tombés dans l’eau, très peu de substrats grossiers), mais la différence la plus marquante était en terme de communauté de poissons observée (dominance des cyprinidés et des centrarchidés plutôt que des salmonidés). Je termine ce chapitre en suggérant que les caractéristiques comportementales favorisant l’évitement de la capture (formation de bancs) et facilitant l’observation en visuel (curiosité) sont responsables de la supériorité de la plongée de surface pour échantillonner les communautés dans les rivières des basses Laurentides. Dans un deuxième chapitre, je développe des FHUM pour des communautés de poissons de rivière ayant plusieurs espèces. Dans le but de simplifier la modélisation de telles communautés et d’améliorer notre compréhension des relations poissons – habitat, j’utilise les concepts de guilde écologique et de filtre environnemental pour explorer les relations entre les guildes formées sur la bases de différents types de traits (reproducteurs, taxonomiques, éco-morphologiques et alimentaires) et les conditions environnementales locales à l’échelle du méso-habitat. Les modèles d’habitats basés sur les guildes reproductrices ont clairement surpassé les autres modèles, parce que l’habitat de fraie reflète l’habitat de préférence en dehors de la période de reproduction. J’ai également utilisé l’approche inverse, c’est à dire définir des guildes d’utilisation de l’habitat et les mettre en relation avec les traits des espèces. Les traits reliés à l’alimentation des poissons ont semblés être les meilleurs pour expliquer l’appartenance aux groupes d’utilisation de l’habitat, mais le modèle utilisé ne représentait pas bien la relation entre les groupes. La validation de notre modèle basé sur les guildes reproductrices avec un jeu de données indépendant pourrait confirmer notre découverte, laquelle représente une manière prometteuse de modéliser les relations poissons – environnement dans des communautés de poissons complexes. En conclusion, mon mémoire suggère d’importantes améliorations aux FHUM pour les communautés de poissons des basses Laurentides, en suggérant de prendre en compte les caractéristiques biologiques des cours d’eau dans le choix d’une méthode d’échantillonnage, et également en utilisant une méthode prometteuse pour simplifier les FHUM de communautés de poissons complexes : les guildes reproductrices. / Many large scale studies have identified habitat modification or habitat losses as primary threats for the conservation of freshwater fish communities. In Canada, No Net Loss (NNL) of the productive capacity of habitats is the guiding principle of the Department of Fisheries and Oceans’ policy for the management of fish habitat. To respect NNL, a better understanding of fish-habitat relationships is required, as well as tools to quantify the impact of habitat modifications on fish. Fish habitat use models (FHUM) are tools that can improve our understanding of fish-habitat relationships, predict species occurrences, densities or biomass on the basis of habitat descriptors and quantify habitat requirements. They consist in relationships between biological descriptors of fish and habitat descriptors. The general objective of my thesis is to improve the performance of FHUM for the lower Laurentian streams by suggesting refinements on 2 crucial aspects in the development of these models: a precise description of the fish community and the use of efficient statistical models. In the first chapter, I evaluate the relative performance of electrofishing and visual surveys (snorkeling) for estimating the abundance of combinations of fish species and size classes in rivers. I also assessed the effect of environmental conditions on potential differences between the results obtained using these two sampling methods. Sampling sites consisted in 10 river sections of 20 m in length distributed in the Laurentian region of Québec. Both methods were used while sections were blocked. Three snorkelers that swam the river sections upstream while identifying and counting fish of each species and size-classes performed visual surveys. Three-pass electrofishing was performed and abundances were estimated with a maximum likelihood depletion model. Greater abundances of fish were observed by snorkeling than by electrofishing at all sites. Snorkeling species richness was higher (6/10) or equal (4/10) to electrofishing richness. Differences in the fish communities observed by both sampling methods were not related to environmental conditions. The results of our work are therefore contrary to that of most published studies that suggested the superiority of electrofishing on visual surveys. Compared to the conditions found in previous studies, our sampling sites had different environmental characteristics (no fallen trees, insignificant cover of large cobble and boulder) but the most striking dissimilarity was in terms of fish communities (dominance of cyprinids and centrarchids instead of salmonids). Behavioural characteristics favouring capture avoidance (schooling) and facilitating underwater observation (curiosity) may be responsible for the superiority of visual surveys in our study rivers. Survey methods should be selected based on fish community composition. In the second chapter, I develop FHUM for complex stream fish communities. In order to simplify the modelling of such communities, as well as improve our understanding of fish – habitat relationships, I used the ecological guild concept and the niche filtering hypothesis to explore the relationships between guilds based on different types of traits (eco-morphological, reproductive, alimentary and taxonomic) and local environmental descriptors, at the coarse meso-habitat scale. Reproductive guilds led to FHUM that clearly outperformed the other 3 approaches, because of the close relationship between preferred spawning grounds and non spawning habitat preferences, and also because reproductive traits are linked to habitat characteristics at the reach or coarse mesohabitat scale. We also defined guilds based on habitat-use and related them to species traits. Traits related to the feeding biology of fishes seemed to be the best at explaining the habitat-use guilds, but our model did not correctly represent the among-guild relationships. Validation of our reproductive trait model on an independent dataset would confirm our finding, which represents a promising way of modelling fish - habitat relationships in complex fish communities. In conclusion, my thesis suggests important improvements to FHUM models in the Laurentian streams by giving new insights on the choice of a sampling method that take into account the biological characteristics of the streams targeted, and by using a promising way of simplifying FHUM for species rich communities: reproductive guilds.

Les plantes envahissantes sont considérées comme l'une des plus grandes menaces sur les espèces, mais leurs impacts sur les amphibiens demeurent peu connus. L’objectif de ce projet est de déterminer l’effet de l’établissement du roseau commun (Phragmites australis) sur la répartition des amphibiens et sur leur développement larvaire. Il est présumé que cette plante s'accapare l'espace et les ressources disponibles en produisant une importante biomasse, qu’elle peut modifier l’hydrologie des marais et la structure des communautés d’amphibiens. J’ai évalué les facteurs influençant la répartition des amphibiens selon les caractéristiques des étangs et du paysage dans 50 sites envahis ou non à divers degrés. Des expériences ont également été menées afin d’étudier les répercussions de trois densités de roseau sur des têtards de la Grenouille des bois (Lithobates sylvaticus) et sur la qualité de son habitat. Mes résultats suggèrent que le roseau à forte densité ralentit le développement larvaire de la grenouille des bois et influence les assemblages phytoplanctoniques. Cependant, il n’y a aucune relation entre la densité de la plante et la survie, la morphologie des têtards et les caractéristiques biotiques et abiotiques de l’eau. Dans notre aire d’étude, le paysage autour des étangs a une plus grande influence sur la répartition des amphibiens que l'établissement du roseau. Toutefois, la probabilité d’assèchement est plus élevée lorsque la plante est établie en grande quantité, ce qui, si l’envahissement s’intensifie, aura un effet néfaste sur la survie des têtards et mettra en péril la persistance des populations. / Invasive plants are considered one of the greatest threats to species, but their impact on amphibians is still poorly understood. The objective of this project is to determine the effect of the establishment of common reed (Phragmites australis) on amphibian distribution and larval development. It is thought that this plant monopolizes space and resources by producing a large biomass, and may alter wetland hydrology and amphibian community structure. I evaluated the factors influencing amphibian distribution according to the characteristics of ponds and the surrounding landscape in 50 sites invaded or not by reeds to varying degrees. Experiments were also conducted to study the impacts of three reed densities on wood frog tadpoles (Lithobates sylvaticus) and the quality of their habitat. My results suggest that high reed density slows wood frog larval development and influences phytoplankton assemblages. However, there is no relationship between, plant density and survival, tadpole morphology and water biotic and abiotic characteristic. In our study area, the landscape surrounding ponds has a greater influence on amphibian distribution than does reed establishment. However, the desiccation probability is higher when the plant is established in high quantities, which, if the invasion intensifies, will have an adverse effect on tadpole survival and therefore population persistence.

The marbled murrelet (Brachyramphus marmoratus) is listed as threatened in both Canada and the United States due to logging of old-growth forest stands, their primary nesting habitat. Existing research is primarily focused on this terrestrial aspect of the species’ ecology. Our understanding of their at-sea foraging ecology, however, is limited to broad-scale studies of population abundance and dynamics. In order to further understand the spatial and temporal variations of marbled murrelet at-sea foraging behaviour and habitat use, bi-weekly surveys of marbled murrelets were conducted in Clayoquot Sound, BC, between May 1 and September 1, 2007 and 2008. Data were first analysed using a Getis-Ord Gi* spatial analysis to identify high-use foraging areas. Total marbled murrelet presence was consistent between years, but spatial distribution varied significantly in both years. A subsequent analysis of oceanic environmental variables found that temperature, salinity and phytoplankton densities (measured as chl a) were spatially ubiquitous, with no significant variation in measures across the study area. Chl a levels showed significant temporal variation, though similar trends in marbled murrelet abundance over time in both seasons suggest that phytoplankton levels do not directly affect murrelet presence. Marbled murrelets were also observed foraging within several metres of gray whales (Eschrictius robustus) feeding on epibenthic zooplankton in 2006 and 2008, a previously undocumented relationship. Join count statistics identified significant clustering of murrelets up to 300m from 39 feeding gray whales in 2006, and no association with 5 gray whales in 2008, marking a foraging association conditional on the abundance of both gray whales and their prey, but potentially significant to marbled murrelet survival and fecundity.

Die vorliegende Studie untersucht die nächtliche Habitatnutzung von Feldhasen in drei unterschiedlichen Habitaten. Das Untersuchungsgebiet Opferbaum ist stark ackerbaulich geprägt und das Untersuchungsgebiet Güntersleben sehr strukturreich durch das Vorkommen von Gehölzen und Waldrändern. Das Untersuchungsgebiet Fritzlar besitzt einen waldrandgeprägten sowie einen ackerbaulich intensiv genutzten Landschaftsteil. Die nächtlichen Aufenthaltsorte von Feldhasen wurden mittels Wärmebildkamera zwischen September 2004 bis April 2005 und September 2005 bis April 2006 kartiert. In jedem der Untersuchungsgebiete wurden einmal monatlich sogenannte Festpunkte angefahren, die umliegenden Landschaftsbereiche abgesucht und beobachtete Feldhasen in Arbeitskarten eingezeichnet. Eine Kartierung der von den Festpunkten einsehbaren Landschaftsteile geschah vor jedem Erfassungstermin bei Tageslicht. Den kartierten Feldhasen (Präsenz-Punkte) wurde im GIS eine zufällige Punktverteilung im beobachteten Landschaftsraum gegenüber gestellt (Pseudo-Absenz-Punkte). Für jeden dieser Punkte wurden bis zu 20 Minimaldistanzen zu verschiedenen Strukturelementen der Landschaft berechnet. In Generalisierten Linearen Modellen (GLM) wurden die univariaten und multivariaten Zusammenhänge der erklärenden Variablen mit der binomialen Zielvariablen modelliert. Zeitliche Aspekte der Habitatnutzung im Verlauf des Winterhalbjahres wurden mit einer multitemporalen Modellierung für zusammengefasste Zwei-Monats-Zeiträume untersucht. Die Modellselektion geschah mit Hilfe des Akaike Information Criterion (AIC). Insgesamt wurden 4.494 Standorte von Feldhasen in Opferbaum, 2.418 in Güntersleben und 1.391 in Fritzlar kartiert. Die univariate Analyse zeigt eine Meidung von Verkehrs- und Siedlungsstrukturen. Waldränder, Gehölze, Buntbrachen und Grünland werden in den Untersuchungsgebieten Fritzlar und Opferbaum bevorzugt, in Güntersleben werden die zwei letzteren gemieden. Die multivariaten Modelle zeigen eine Präferenz der Nahrungshabitate Wintergetreide und Raps, in Fritzlar und Opferbaum wird auch Grünland bevorzugt. Nach dem Nahrungshabitat wird von Feldhasen die Nähe zu potentiellen Deckungshabitaten präferiert, dabei werden nur Buntbrachen in allen Untersuchungsgebieten bevorzugt. Besonders Verkehrswege und Siedlungen werden gemiedenen, Ausnahme ist die Bevorzugung von Siedlungsbereichen in Güntersleben. Teilweise gegensätzliche Ergebnisse zeigt die Modellierung der Zwei-Monats-Zeiträume zwischen den Untersuchungsgebieten. Sie zeigen aber nur geringe Veränderungen der Habitatnutzung von Feldhasen im Verlauf des Winterhalbjahres. Allen selektierten Modellen gemein ist die geringe Erklärungsgüte von weniger als 5 % der Datenvarianz. Die Eignung der entwickelten Aufnahmemethodik und die Ergebnisse werden anhand der umfangreichen Literatur diskutiert. Die Art des Habitats ist von großer Bedeutung für die Habitatnutzung der Feldhasen. Durch die landwirtschaftliche Fruchtfolge bedingte strukturelle Veränderungen verändern ebenso die kleinräumige Habitatnutzung wie die Veränderungen der landwirtschaftlichen Schläge im Verlauf des Herbstes und Winters. Das opportunistische Habitatverhalten von Feldhasen erschwert dabei die Beobachtung von speziellem Habitatverhalten. Die zum Teil gegensätzlichen Ergebnisse werden auch vor dem Hintergrund potentieller Fehlerquellen der Methodik und einem möglichen Einfluss vernachlässigter Variablen diskutiert. Dabei stellt sich die Frage nach grundsätzlichen Konsequenzen für zukünftige Untersuchungen. Die unterschiedliche Habitatnutzung des Feldhasen in unterschiedlichen Habitaten muss sowohl bei der Wahl der Methodik als auch bei der Wahl der Gebietskulisse berücksichtigt werden. / The study presented in this thesis examined the nocturnal habitat use by hares in three different habitats. The study area Opferbaum is strongly influenced by agriculture whereas the landscape of the study area Güntersleben has very diverse structures such as groves and forest edges. The study area Fritzlar has a forest dominated landscape on the one hand and a landscape of intensive agricultural activities on the other hand. Hare locations were mapped using thermography between September 2004 to April 2005 and September 2005 to April 2006. In each of the study sites the surrounding landscape of selected viewpoints was observed once a month and hare distribution was plotted in topographical maps. Mapping of the visible landscape of the viewpoints took place during daytime. Up to 20 minimum distances to different structural elements of the landscape were calculated for each hare location (presence-points) and randomly distributed points (pseudo-absence points) in the observed landscape. Generalized linear models (GLM) were applied to model the univariate and multivariate relationships of explanatory variables with the binomial response variables (hare 1; pseudo-absence 0). Temporal aspects of habitat use during the winter were analyzed by multi-temporal modeling for combined two-month periods. The model selection was done using the Akaike Information Criterion (AIC). A total of 4,494 locations by hares were mapped in Opferbaum, 2,418 in Güntersleben and 1,391 in Fritzlar. The univariate analysis shows an avoidance of traffic and urban areas. Forest edges and groves are preferred in all study areas. Pasture and wildlife-friendly set-asides are preferred in Fritzlar and Opferbaum, but avoided in Güntersleben. The multivariate models show a preference of feeding habitats such as winter cereals and oilseed rape, hares also prefer pasture in Fritzlar and Opferbaum. After the feeding habitat, hares show a preference to be in proximity to shelter providing habitats. Wildlife-friendly set-asides were preferred in all study sites. Traffic and urban areas are avoided in Opferbaum and Fritzlar but urban areas preferred in Güntersleben. Modeling the two-month periods shows different results between the study areas but only small changes in habitat use by brown hares during the winter months. All selected models explain less than 5 % of the variance of data. The consideration of comparable studies shows that besides methodology and surveying time, the results of habitat use of brown hares are primarily influenced by the kind of the examined landscapes. The small-scale habitat use of brown hare is also influenced by structural changes in the agricultural crop rotation as well as a changing vegetation in autumn and winter. The opportunistic behaviour of brown hares make the observation of special habitat use difficult. The results are discussed in connection with error in methodology and unconsidered variables but also to fundamental consequences for future investigations. The differences in habitat use of brown hares in different habitats have to be considered in both, the choice of methodology and when choosing the study sites.

En el marc d'un projecte més ampli sobre la comunitat de peixos de la conca lacustre de Banyoles, s'ha estudiat la distribució espacial de les diferents espècies així com l'ús que aquestes fan de l'hàbitat. El poblament piscícola de l'estany de Banyoles és el resultat d'un llarg historial d'introducció d'espècies exòtiques i extinció de les poblacions autòctones locals. S'ha revisat la seva composició actual detectant un total de 18 espècies (4 autòctones i 14 introduïdes) de les quals només 13 presenten una població estable.L'estudi de l'hàbitat s'ha centrat a l'Estany, l'element principal del sistema lacustre, analitzant per separat la zona litoral i la zona limnètica. En el primer cas s'han realitzat les captures d'individus mitjançant pesca elèctrica des d'una embarcació adaptada per aquesta pràctica. La totalitat del litoral ha estat dividida en trams de característiques homogènies on s'han obtingut les captures per unitat d'esforç per cada espècie. El mostreig s'ha desenvolupat entre l'estiu de 1997 i la primavera del 2000 realitzant un total de 10 campanyes de pesca. Les espècies més abundants al litoral són la perca americana (Micropterus salmoides) i el peix sol (Lepomis gibbosus), essent també presents la perca (Perca fluviatilis), carpa (Cyprinus carpio) i el gardí (Scardinius erythrophthalmus). S'han capturat altres espècies com ara anguila (Anguilla anguilla), bagra (Squalius cephalus), sandra (Sander lucioperca), carpí (Carassius auratus) i madrilleta vera (Rutilus rutilus), però són molt menys abundants en nombre. S'ha examinat, per cadascuna de les espècies, si existeix selecció de l'hàbitat i en cas afirmatiu, quin és el preferent en base a la classificació del litoral en sis tipus de vegetació predominant. Les espècies més abundants, perca americana i peix sol, ocupen tots els hàbitats disponibles però amb una densitat diferent. La perca mostra també una clara selecció de l'hàbitat a favor de les zones molt estructurades amb abundant presència de jonca litoral. Carpa i gardí seleccionen els ambients més fondos amb major presència de matèria orgànica d'origen vegetal procedent del bogar. En general els individus ocupen les zones amb una densitat de vegetació intermèdia, majoritàriament zones de jonca a l'estiu i zones amb mansega a l'hivern, on troben refugi i els recursos tròfics necessaris. La perca americana, a més, presenta una elevada fidelitat a un mateix punt del litoral al llarg de la seva vida.La zona limnètica ha estat prospectada mensualment mitjançant ecosondació, realitzant transectes perpendiculars a l'eix principal de l'Estany, cobrint la seva totalitat. La composició d'espècies s'ha obtingut a partir de les captures fetes amb xarxes (tresmalls) amb periodicitat estacional. L'anàlisi geoestadística de la densitat de peixos ha permès descriure l'estructura espacial d'aquesta a partir dels variogrames, així com la seva variabilitat tant espacial com temporal, i obtenir els mapes de densitat. A l'hivern, la densitat de peixos a la zona limnètica assoleix els seus valors mínims i els individus es troben formant agregats dispersos, pels diferents estrats de fondària. A partir de la primavera la densitat augmenta, pel reclutament i la major freqüència d'individus que abandonen el litoral; la densitat esdevé més homogènia a les primer capes de fondària. A l'estiu la densitat és màxima i l'estrat més homogeni coincideix amb la posició de la termoclina. Aquest estructura varia en disminuir la temperatura i barrejar-se la columna d'aigua, tornant a la situació hivernal. La perca i la madrilleta vera són les espècies predominants en aquest ambient, juntament amb la carpa. La seva distribució no és homogènia i respon a les característiques limnològiques de les diferents cubetes de l'Estany. Una particularitat d'aquest, relacionada amb el seu origen càrstic, es la formació d'una ploma hidrotermal que afecta la distribució dels peixos, probablement en augmentar la terbolesa.S'ha integrat l'ús de l'hàbitat de les espècies que ocupen tant la zona limnètica com la litoral a partir del seguiment d'individus, concretament de perca i bagra. S'ha utilitzat un sistema automàtic de posicionament que estima la localització dels individus marcats amb transmissor de telemetria acústica. L'anàlisi dels desplaçaments mostra un rang superior per la bagra en comparació amb la perca. Ambdues espècies mostren una orientació en els seus desplaçaments. La perca ocupa el litoral a la nit i es desplaça a la zona limnètica de dia, amb un ritme d'activitat marcat per dos màxims coincidint amb la sortida i posta de sol; en canvi la bagra mostra una major activitat nocturna amb zones de repòs properes al litoral. S'ha estimat igualment els dominis vital de cada individu marcat. / Habitat use and spatial distribution patterns of fish community from Lake Banyoles has been studied. Fish assemblage of this lake is the result of a long history of fish introductions and its current state has been assessed showing a high diversity with 14 exotic species and 4 native species. This study has been focused in the Lake, the main element of Banyoles's karstic system. Fish were captured in the littoral zone using a electrofishing boat. The whole perimeter of the lake was divided in 43 transects or sample units where all the fish were captured, processed and, finally, released at the same position. Sampling was divided in ten campaigns, between summer 1997 and winter 1999. Largemouth bass (Micropterus salmoides) and pumpkinseed sunfish (Lepomis gibbosus) were the most abundant in littoral zone. Other catches correspond to perch (Perca fluviatilis), common carp (Cyprinus carpio) and rudd (Scardinius erythrophthalmus). Habitat selection was analysed using both, the Manly Index of selection and the analysis of variance. Results showed that juvenile of largemouth bass, pumpkinseed sunfish and perch present a positive selection of habitat were Schoenoplectus litoralis or Cladium mariscus are dominants. Common carp and rudd present selection of littoral zones with Typha. Habitat selection is related with structurally complex environments. Perch and largemouth bass show temporal variation in the habitat distribution and smaller sizes preferred the intermediate vegetation density. Large bass presented also a high site fidelity. Limnetic zone was prospected monthly from December 1997 until December 1999, using both echosounding and trammel nets. Different species were detected including perch (Perca fluviatilis), roach (Rutilus rutilus), common carp (Cyprinus carpio), chub (Squalius cephalus) and pikeperch (Sander lucioperca). Fish density was maximum in summer and minimum in autumn-winter. Spatial pattern was described using geostatistics. In winter, fish formed aggregates in the center of the lake; with the increasing of fish density, in summer, the spatial distribution became more homogeneous with a maximum located at the same depth than thermocline. Abundance of different species varied with depth and limnological characteristics of basins. Also, the development of a hydrothermal plume due to underwater inflow, increase the turbidity of different parts of the lake altering fish distribution which avoid the presence of sediments. In order to monitoring the movements of perch and chub, 14 individuals were tagged with ultrasonic transmitters. Movements were followed by means of an automatic system showing a partition of habitat use between littoral zone and limnetic zone. Chub describes a pattern of movements bigger than perch but both species presents a main orientation of paths according with basin morphology. Activity (measured as velocity of displacements) was maximum at dawn and dusk in perch, with a diurnal increase while chub activity can be considered nocturnal.

Coordenação de Aperfeiçoamento de Pessoal de Nível Superior / As populações introduzidas de saguis preocupam biólogos e conservacionistas, por causa do seu potencial de ocupação de hábitat, hibridação com congêneres nativos, predação de representantes da fauna local, transmissão de doenças e competição com outras espécies. É necessário entendermos o que favorece essa flexibilidade na utilização do suporte e no padrão comportamental que possibilita que os saguis sobrevivam em ambientes florestais tão diversos e até mesmo em regiões muito alteradas e antropizadas, como as grandes metrópoles. Foram acompanhados indivíduos de Callithrix sp. no arboreto do JBRJ. O trabalho de campo foi feito entre agosto de 2012 e agosto de 2013 e acumulou 205 horas de observações e 400 horas de esforço amostral. O método de amostragem utilizado foi o Animal Focal, no qual apenas um indivíduo do grupo foi analisado por sessão amostral, de 3 minutos com 7 minutos de intervalo. A cada dez minutos, em uma nova sessão amostral, o foco era mudado para outro indivíduo do grupo. Adultos, subadultos e jovens foram observados. Os indivíduos de Callithrix sp. no JBRJ utilizam de forma diferenciada as categorias de utilização de habitat, com maior frequência a estratificação vertical inferior (entre 0 e 4,9m), suportes de diâmetro fino (até aproximadamente 14 cm de diâmetro), superfície média e inclinação horizontal (0 a 30), corroborando a outros estudos realizados que também verificaram estes padrões. Houve diferenças comportamentais dos indivíduos de Callithrix sp. no JBRJ entre as classes de machos e fêmeas adultos, subadultos e jovens. Os indivíduos machos realizaram com maior frequência todos os comportamentos. Resultados que contribuem para o conhecimento aprofundado sobre o comportamento desses primatas, no qual até então não tinham sido feitas comparações diretas entre as classes consideradas. Principalmente o resultado encontrado de que os machos são mais ativos que as demais classes, o que não é mencionado na literatura até o presente e favorece para compreendermos mais sobre essas espécies / Introduced populations of marmosets concern biologists and conservationists because of its potential occupancy of habitat, hybridization with native congeners, predation on representatives of the local fauna, disease transmission and competition with other species. It is necessary to understand which favors this flexible use of habitat and behavioral pattern which enables marmosets to survive in such diverse forest environments and even much altered and disturbed areas, such as large cities. Individuals of Callithrix sp.were followed at the Arboretum JBRJ. The fieldwork was done between August 2012 and August 2013 and accumulated a total of 205 hours of observations and 400 hours of sampling effort. The sampling method used was the " Focal Animal ", in which only one individual in the group was analyzed at a three minutes sampling session with 7 minutes apart. Every ten minutes, in a new sampling session, the animal focus was shifted to another individual in the group. Adults, sub-adults and young were observed. Individuals of Callithrix sp. in JBRJ use the categories of habitat differently, most often the lower vertical stratification (between 0 and 4.9 m), thinner supports (to about 14 cm diameter), with an average surface and a horizontal tilt (0 to 30 ), corroborating other studies that also found these patterns. There were also behavioral differences of individuals of Callithrix sp. in JBRJ between classes of male and female adults, sub-adults and youth. Male individuals used more frequently all behaviors. Results that contribute to the knowledge about the behavior of these primates, which had not been direct comparisons made between the classes considered. Mainly the result found that males are more active than the other classes, which is not mentioned in the literature to date and helps to understand more about these species.

Made available in DSpace on 2014-12-17T15:36:35Z (GMT). No. of bitstreams: 1 LeonardoBR_TESE_Cap_II_III.pdf: 677404 bytes, checksum: 247b1251f8d1d16cb41bf4f8ec2f3c18 (MD5) Previous issue date: 2010-03-19 / Universidade Federal do Rio Grande do Norte / This study evaluated the spatial, time and alimentary niches of Tropidurus hispidus and Tropidurus semitaeniatus in sympatry in a caatinga of Rio Grande do Norte, Brazil, as well as their foraging and termoregulatory behaviors, the activity body temperature and their reproductive and fat body cycles. Monthly excursions, from October 2006 to May 2008, were conducted at the Ecological Station of the Serid? (ESEC Serid?), Serra Negra do Norte municipality, using specific methodology for investigation of the aforementioned objectives. The two species presented similarities in space niche use, mainly in rocky habitat, however they differed in vertical microhabitat use with T. hispidus using a larger vertical microhabitat range. In the dry season the time of activity of both species was bimodal. In the wet season T. semitaeniatus showed a unimodal activity period, while T. hispidus maintained an bimodal activity period. In terms of importance in the diet, to both species, Hymenoptera/Formicidae and Isoptera predominated during the dry season. In the wet season, although Hymenoptera/Formicidae had larger importance among the prey items, lizards opportunistically predated on Lepidoptera larvae, Coleoptera larvae/adults and Orthoptera nymphs/adults. The foraging intensity revealed differences between the species, mainly in the wet season, when T. semitaeniatus was more active than T. hispidus. The mean activity body temperature of T. semitaeniatus was significantly higher than that of T. hispidus. The thermoregulatory behavior showed that during the dry season T. hispidus and T. semitaeniatus spent more time in shade or under filtered sun. In the wet season, T. hispidus did not show differences in the amount of time spent among the light exposure locations, however T. semitaeniatus spent most of their time exposed to direct sun or filtered sun. The reproductive cicle of T. hispidus and T. semitaeniatus occurred from the middle of the dry season to the beginning of the wet season. In both species, female reproductive activity was influenced by precipitation, whereas males exhibited spermatozoa in their testes throughout the year, and their reproductive activity was not related with any of the climatic variables analysed. In the two species, the fat storage varied inversely with reproductive activity, and there was no difference in fat body mass between females and males. We concluded that the segregation between T. hispidus and T. semitaeniatus in this caatinga area occurs in vertical space use, in the largest vagility of T. hispidus in microhabitat use and larger range size of their alimentary xviii items. Additionally, significant seasonal differences in relation to the activity period, body temperature, and foraging and termoregulatory behaviors between these two Tropidurus species facilitate their coexistence. / Este estudo avaliou o uso dos recursos espacial, temporal e alimentar por Tropidurus hispidus e Tropidurus semitaeniatus em simpatria em uma caatinga do Rio Grande do Norte, Brasil, bem como seus comportamentos de forrageamento e termorregulat?rio, suas temperaturas corp?reas em atividade e seus ciclos reprodutivos e de gordura corp?rea. Excurs?es mensais, de outubro de 2006 a maio de 2008, foram realizadas ? Esta??o Ecol?gica do Serid? (ESEC Serid?), munic?pio de Serra Negra do Norte, com utiliza??o de metodologia espec?fica para a investiga??o dos objetivos acima mencionados. As duas esp?cies apresentaram similaridades no uso do nicho espacial, especialmente no h?bitat rochoso; contudo, elas diferiram no uso vertical do micro-h?bitat com T. hispidus usando uma faixa vertical maior do micro-h?bitat. Na esta??o seca o per?odo de atividade de ambas as esp?cies foi bimodal. Na esta??o chuvosa, a atividade de T. semitaeniatus mostrou um per?odo unimodal, enquanto T. hispidus manteve uma atividade bimodal. Em termos de import?ncia na dieta, para ambas as esp?cies, os Hymenoptera/Formicidae e Isoptera predominaram na esta??o seca. Na esta??o chuvosa ainda que os Hymenoptera/Formicidae continuaram a ter maior import?ncia entre os itens alimentares, os lagartos predaram oportunisticamente larvas de Lepidoptera, larvas/adultos de Coleoptera e ninfas/adultos de Orthoptera. A medida de intensidade de forrageamento revelou diferen?as entre as esp?cies, especialmente na esta??o chuvosa, quando T. semitaeniatus foi mais ativo do que T. hispidus. A temperatura corp?rea m?dia em atividade de T. semitaeniatus foi significativamente superior a de T. hispidus. O comportamento termorregulat?rio mostrou que, durante a esta??o seca, T. hispidus e T. semitaeniatus gastaram mais tempo expostos ? sombra ou sob sol filtrado. Na esta??o chuvosa, T. hispidus n?o mostrou diferen?as no tempo gasto entre os locais de exposi??o ? luz, contudo T. semitaeniatus esteve a maior parte de seu tempo exposto ao sol ou sob sol filtrado. A reprodu??o de T. hispidus e T. semitaeniatus ocorreu entre a metade da esta??o seca e o in?cio da esta??o chuvosa. Em ambas as esp?cies, a atividade reprodutiva das f?meas foi influenciada pela precipita??o, enquanto os machos apresentaram espermatoz?ides nos test?culos ao longo de todo o ano, e sua atividade reprodutiva n?o foi relacionada com nenhuma das vari?veis clim?ticas analisadas. O estoque de gordura corp?rea variou inversamente com a atividade reprodutiva nas duas esp?cies, e n?o houve diferen?a entre f?meas e machos quanto a massa dos corpos adiposos. Conclu?mos que xvi a segrega??o entre T. hispidus e T. semitaeniatus nesta ?rea de caatinga ocorre no uso vertical do espa?o, na maior vagilidade de T. hispidus na utiliza??o de micro-h?bitats e maior amplitude de tamanho de seus itens alimentares. Adicionalmente, diferen?as sazonais significativas em rela??o ao per?odo de atividade, temperatura corp?rea, e comportamentos de forrageamento e termorregulat?rio entre essas duas esp?cies de Tropidurus, possibilitam a coexist?ncia.

Coordenação de Aperfeiçoamento de Pessoal de Nível Superior / As populações introduzidas de saguis preocupam biólogos e conservacionistas, por causa do seu potencial de ocupação de hábitat, hibridação com congêneres nativos, predação de representantes da fauna local, transmissão de doenças e competição com outras espécies. É necessário entendermos o que favorece essa flexibilidade na utilização do suporte e no padrão comportamental que possibilita que os saguis sobrevivam em ambientes florestais tão diversos e até mesmo em regiões muito alteradas e antropizadas, como as grandes metrópoles. Foram acompanhados indivíduos de Callithrix sp. no arboreto do JBRJ. O trabalho de campo foi feito entre agosto de 2012 e agosto de 2013 e acumulou 205 horas de observações e 400 horas de esforço amostral. O método de amostragem utilizado foi o Animal Focal, no qual apenas um indivíduo do grupo foi analisado por sessão amostral, de 3 minutos com 7 minutos de intervalo. A cada dez minutos, em uma nova sessão amostral, o foco era mudado para outro indivíduo do grupo. Adultos, subadultos e jovens foram observados. Os indivíduos de Callithrix sp. no JBRJ utilizam de forma diferenciada as categorias de utilização de habitat, com maior frequência a estratificação vertical inferior (entre 0 e 4,9m), suportes de diâmetro fino (até aproximadamente 14 cm de diâmetro), superfície média e inclinação horizontal (0 a 30), corroborando a outros estudos realizados que também verificaram estes padrões. Houve diferenças comportamentais dos indivíduos de Callithrix sp. no JBRJ entre as classes de machos e fêmeas adultos, subadultos e jovens. Os indivíduos machos realizaram com maior frequência todos os comportamentos. Resultados que contribuem para o conhecimento aprofundado sobre o comportamento desses primatas, no qual até então não tinham sido feitas comparações diretas entre as classes consideradas. Principalmente o resultado encontrado de que os machos são mais ativos que as demais classes, o que não é mencionado na literatura até o presente e favorece para compreendermos mais sobre essas espécies / Introduced populations of marmosets concern biologists and conservationists because of its potential occupancy of habitat, hybridization with native congeners, predation on representatives of the local fauna, disease transmission and competition with other species. It is necessary to understand which favors this flexible use of habitat and behavioral pattern which enables marmosets to survive in such diverse forest environments and even much altered and disturbed areas, such as large cities. Individuals of Callithrix sp.were followed at the Arboretum JBRJ. The fieldwork was done between August 2012 and August 2013 and accumulated a total of 205 hours of observations and 400 hours of sampling effort. The sampling method used was the " Focal Animal ", in which only one individual in the group was analyzed at a three minutes sampling session with 7 minutes apart. Every ten minutes, in a new sampling session, the animal focus was shifted to another individual in the group. Adults, sub-adults and young were observed. Individuals of Callithrix sp. in JBRJ use the categories of habitat differently, most often the lower vertical stratification (between 0 and 4.9 m), thinner supports (to about 14 cm diameter), with an average surface and a horizontal tilt (0 to 30 ), corroborating other studies that also found these patterns. There were also behavioral differences of individuals of Callithrix sp. in JBRJ between classes of male and female adults, sub-adults and youth. Male individuals used more frequently all behaviors. Results that contribute to the knowledge about the behavior of these primates, which had not been direct comparisons made between the classes considered. Mainly the result found that males are more active than the other classes, which is not mentioned in the literature to date and helps to understand more about these species.

La vie en collectivité confère de nombreux avantages, mais aussi des inconvénients avec lesquels l’animal doit s’accommoder. Afin de maintenir la cohésion sociale, les membres d’un groupe doivent donc faire des compromis et résoudre rapidement les conflits d’intérêts. Comprendre comment les individus arrivent à des décisions communes et optimales permet d’en savoir plus sur l’organisation sociale, les patterns de mouvements et l’utilisation de l’habitat de l’espèce. En retour, ces informations sont essentielles au développement de nouvelles stratégies de gestion. Dans ce contexte, je me suis intéressée à la vie de groupe et aux déplacements collectifs chez le bison d’Europe, espèce expérimentant son grand retour sur son continent d’origine. Mes travaux ont pu mettre en évidence que (1) les liens matrilinéaires étaient au cœur de la vie sociale de l’espèce, (2) le bison européen, contrairement à l’idée populaire, était loin d’être un animal strictement forestier et (3) les déplacements de groupe étaient préférentiellement menés par les femelles dominantes les plus âgées et ayant un veau à leur charge. La prise en compte de ces résultats pourrait grandement améliorer la réintroduction et la gestion des populations de bisons et permettre, par là même, une meilleure cohabitation avec l’Homme. / Community life gives many advantages, but also disadvantages with which animal must accommodate. In order to maintain social cohesion, group members must therefore make compromise and resolve quickly conflicts of interest. Understanding how individuals reach common and optimal decisions helps to learn more about the social organization, movement patterns and habitat use of the species. In return, this information is essential to the development of new management strategies. In this context, I was interested in group life and collective movements of the European bison, species which experiencing its great come back on its continent of origin. My works have shown that (1) matrilineal ties were at the core of the species’ social life, (2) the European bison, contrary to popular opinion, was far from a strictly forest animal and (3) group movements were preferentially lead by the oldest dominant females which had a calf. Taking into account these results could be greatly improve the reintroduction and management of bison populations and, thereby, allow a better cohabitation with humans.

Die vorliegende Studie untersucht die nächtliche Habitatnutzung von Feldhasen in drei unterschiedlichen Habitaten. Das Untersuchungsgebiet Opferbaum ist stark ackerbaulich geprägt und das Untersuchungsgebiet Güntersleben sehr strukturreich durch das Vorkommen von Gehölzen und Waldrändern. Das Untersuchungsgebiet Fritzlar besitzt einen waldrandgeprägten sowie einen ackerbaulich intensiv genutzten Landschaftsteil. Die nächtlichen Aufenthaltsorte von Feldhasen wurden mittels Wärmebildkamera zwischen September 2004 bis April 2005 und September 2005 bis April 2006 kartiert. In jedem der Untersuchungsgebiete wurden einmal monatlich sogenannte Festpunkte angefahren, die umliegenden Landschaftsbereiche abgesucht und beobachtete Feldhasen in Arbeitskarten eingezeichnet. Eine Kartierung der von den Festpunkten einsehbaren Landschaftsteile geschah vor jedem Erfassungstermin bei Tageslicht. Den kartierten Feldhasen (Präsenz-Punkte) wurde im GIS eine zufällige Punktverteilung im beobachteten Landschaftsraum gegenüber gestellt (Pseudo-Absenz-Punkte). Für jeden dieser Punkte wurden bis zu 20 Minimaldistanzen zu verschiedenen Strukturelementen der Landschaft berechnet. In Generalisierten Linearen Modellen (GLM) wurden die univariaten und multivariaten Zusammenhänge der erklärenden Variablen mit der binomialen Zielvariablen modelliert. Zeitliche Aspekte der Habitatnutzung im Verlauf des Winterhalbjahres wurden mit einer multitemporalen Modellierung für zusammengefasste Zwei-Monats-Zeiträume untersucht. Die Modellselektion geschah mit Hilfe des Akaike Information Criterion (AIC). Insgesamt wurden 4.494 Standorte von Feldhasen in Opferbaum, 2.418 in Güntersleben und 1.391 in Fritzlar kartiert. Die univariate Analyse zeigt eine Meidung von Verkehrs- und Siedlungsstrukturen. Waldränder, Gehölze, Buntbrachen und Grünland werden in den Untersuchungsgebieten Fritzlar und Opferbaum bevorzugt, in Güntersleben werden die zwei letzteren gemieden. Die multivariaten Modelle zeigen eine Präferenz der Nahrungshabitate Wintergetreide und Raps, in Fritzlar und Opferbaum wird auch Grünland bevorzugt. Nach dem Nahrungshabitat wird von Feldhasen die Nähe zu potentiellen Deckungshabitaten präferiert, dabei werden nur Buntbrachen in allen Untersuchungsgebieten bevorzugt. Besonders Verkehrswege und Siedlungen werden gemiedenen, Ausnahme ist die Bevorzugung von Siedlungsbereichen in Güntersleben. Teilweise gegensätzliche Ergebnisse zeigt die Modellierung der Zwei-Monats-Zeiträume zwischen den Untersuchungsgebieten. Sie zeigen aber nur geringe Veränderungen der Habitatnutzung von Feldhasen im Verlauf des Winterhalbjahres. Allen selektierten Modellen gemein ist die geringe Erklärungsgüte von weniger als 5 % der Datenvarianz. Die Eignung der entwickelten Aufnahmemethodik und die Ergebnisse werden anhand der umfangreichen Literatur diskutiert. Die Art des Habitats ist von großer Bedeutung für die Habitatnutzung der Feldhasen. Durch die landwirtschaftliche Fruchtfolge bedingte strukturelle Veränderungen verändern ebenso die kleinräumige Habitatnutzung wie die Veränderungen der landwirtschaftlichen Schläge im Verlauf des Herbstes und Winters. Das opportunistische Habitatverhalten von Feldhasen erschwert dabei die Beobachtung von speziellem Habitatverhalten. Die zum Teil gegensätzlichen Ergebnisse werden auch vor dem Hintergrund potentieller Fehlerquellen der Methodik und einem möglichen Einfluss vernachlässigter Variablen diskutiert. Dabei stellt sich die Frage nach grundsätzlichen Konsequenzen für zukünftige Untersuchungen. Die unterschiedliche Habitatnutzung des Feldhasen in unterschiedlichen Habitaten muss sowohl bei der Wahl der Methodik als auch bei der Wahl der Gebietskulisse berücksichtigt werden.:Inhalt 1 Einleitung 1 1.1 Motivation 1 1.2 Methodenüberblick 2 1.3 Stand des Wissens 4 1.4 Ziele 13 2 Material und Methoden 14 2.1 Untersuchungsgebiete 14 2.1.1 Fritzlar 14 2.1.2 Güntersleben 18 2.1.3 Opferbaum 21 2.2 Feldökologische Methoden 24 2.2.1 Methodenentwicklung 24 2.2.2 Feldhasenerfassung 27 2.2.3 GIS-Anwendung 31 2.2.4 Flächennutzungs- & Habitatkartierung 32 2.3 Statistik 34 2.3.1 Bestimmung der Variablen 34 2.3.2 Modellbildung 39 2.3.2.1 Präsenz- und Pseudo-Absenz-Verteilung 39 2.3.2.2 Logistische Regression 40 2.3.2.3 Modellselektion 42 3 Ergebnisse 48 3.1 Anzahl und Dichte beobachteter Feldhasen 48 3.2 Struktur der untersuchten Landschaften 49 3.3 Generalisierte Lineare Modelle zur nächtlichen Habitatnutzung von Feldhasen 53 3.3.1 Univariate Analyse der potentiellen erklärenden Variablen 53 3.3.2 Multivariate Analyse der potentiellen erklärenden Variablen 55 3.3.2.1 Multivariate Modelle für das Untersuchungsgebiet Fritzlar 55 3.3.2.2 Multivariate Modelle für das Untersuchungsgebiet Güntersleben 57 3.3.2.3 Multivariate Modelle für das Untersuchungsgebiet Opferbaum 59 3.3.2.4 Multitemporale Modelle der Zwei-Monats-Zeiträume 62 3.3.2.5 Multivariate Modelle für alle Untersuchungsgebiete 68 4 Diskussion 72 4.1 Methodenkritik 72 4.1.1 Einfluss der maximalen Erfassungsdistanz 72 4.1.2 Eignung der entwickelten Methodik 73 4.2 Habitatnutzung von Feldhasen 75 4.2.1 Nutzung einzelner Strukturelemente 75 4.2.2 Habitatnutzung im Untersuchungsgebiet Fritzlar 85 4.2.3 Habitatnutzung im Untersuchungsgebiet Güntersleben 87 4.2.4 Habitatnutzung im Untersuchungsgebiet Opferbaum 93 4.2.5 Habitatnutzung im zeitlichen Verlauf 96 4.2.6 Multivariates Gesamtmodell 98 4.3 Betrachtung unberücksichtigter Variablen 99 4.4 Schlussbetrachtung und Ausblick 102 5 Zusammenfassung 105 6 Literatur 109 7 Anhang 121 / The study presented in this thesis examined the nocturnal habitat use by hares in three different habitats. The study area Opferbaum is strongly influenced by agriculture whereas the landscape of the study area Güntersleben has very diverse structures such as groves and forest edges. The study area Fritzlar has a forest dominated landscape on the one hand and a landscape of intensive agricultural activities on the other hand. Hare locations were mapped using thermography between September 2004 to April 2005 and September 2005 to April 2006. In each of the study sites the surrounding landscape of selected viewpoints was observed once a month and hare distribution was plotted in topographical maps. Mapping of the visible landscape of the viewpoints took place during daytime. Up to 20 minimum distances to different structural elements of the landscape were calculated for each hare location (presence-points) and randomly distributed points (pseudo-absence points) in the observed landscape. Generalized linear models (GLM) were applied to model the univariate and multivariate relationships of explanatory variables with the binomial response variables (hare 1; pseudo-absence 0). Temporal aspects of habitat use during the winter were analyzed by multi-temporal modeling for combined two-month periods. The model selection was done using the Akaike Information Criterion (AIC). A total of 4,494 locations by hares were mapped in Opferbaum, 2,418 in Güntersleben and 1,391 in Fritzlar. The univariate analysis shows an avoidance of traffic and urban areas. Forest edges and groves are preferred in all study areas. Pasture and wildlife-friendly set-asides are preferred in Fritzlar and Opferbaum, but avoided in Güntersleben. The multivariate models show a preference of feeding habitats such as winter cereals and oilseed rape, hares also prefer pasture in Fritzlar and Opferbaum. After the feeding habitat, hares show a preference to be in proximity to shelter providing habitats. Wildlife-friendly set-asides were preferred in all study sites. Traffic and urban areas are avoided in Opferbaum and Fritzlar but urban areas preferred in Güntersleben. Modeling the two-month periods shows different results between the study areas but only small changes in habitat use by brown hares during the winter months. All selected models explain less than 5 % of the variance of data. The consideration of comparable studies shows that besides methodology and surveying time, the results of habitat use of brown hares are primarily influenced by the kind of the examined landscapes. The small-scale habitat use of brown hare is also influenced by structural changes in the agricultural crop rotation as well as a changing vegetation in autumn and winter. The opportunistic behaviour of brown hares make the observation of special habitat use difficult. The results are discussed in connection with error in methodology and unconsidered variables but also to fundamental consequences for future investigations. The differences in habitat use of brown hares in different habitats have to be considered in both, the choice of methodology and when choosing the study sites.:Inhalt 1 Einleitung 1 1.1 Motivation 1 1.2 Methodenüberblick 2 1.3 Stand des Wissens 4 1.4 Ziele 13 2 Material und Methoden 14 2.1 Untersuchungsgebiete 14 2.1.1 Fritzlar 14 2.1.2 Güntersleben 18 2.1.3 Opferbaum 21 2.2 Feldökologische Methoden 24 2.2.1 Methodenentwicklung 24 2.2.2 Feldhasenerfassung 27 2.2.3 GIS-Anwendung 31 2.2.4 Flächennutzungs- & Habitatkartierung 32 2.3 Statistik 34 2.3.1 Bestimmung der Variablen 34 2.3.2 Modellbildung 39 2.3.2.1 Präsenz- und Pseudo-Absenz-Verteilung 39 2.3.2.2 Logistische Regression 40 2.3.2.3 Modellselektion 42 3 Ergebnisse 48 3.1 Anzahl und Dichte beobachteter Feldhasen 48 3.2 Struktur der untersuchten Landschaften 49 3.3 Generalisierte Lineare Modelle zur nächtlichen Habitatnutzung von Feldhasen 53 3.3.1 Univariate Analyse der potentiellen erklärenden Variablen 53 3.3.2 Multivariate Analyse der potentiellen erklärenden Variablen 55 3.3.2.1 Multivariate Modelle für das Untersuchungsgebiet Fritzlar 55 3.3.2.2 Multivariate Modelle für das Untersuchungsgebiet Güntersleben 57 3.3.2.3 Multivariate Modelle für das Untersuchungsgebiet Opferbaum 59 3.3.2.4 Multitemporale Modelle der Zwei-Monats-Zeiträume 62 3.3.2.5 Multivariate Modelle für alle Untersuchungsgebiete 68 4 Diskussion 72 4.1 Methodenkritik 72 4.1.1 Einfluss der maximalen Erfassungsdistanz 72 4.1.2 Eignung der entwickelten Methodik 73 4.2 Habitatnutzung von Feldhasen 75 4.2.1 Nutzung einzelner Strukturelemente 75 4.2.2 Habitatnutzung im Untersuchungsgebiet Fritzlar 85 4.2.3 Habitatnutzung im Untersuchungsgebiet Güntersleben 87 4.2.4 Habitatnutzung im Untersuchungsgebiet Opferbaum 93 4.2.5 Habitatnutzung im zeitlichen Verlauf 96 4.2.6 Multivariates Gesamtmodell 98 4.3 Betrachtung unberücksichtigter Variablen 99 4.4 Schlussbetrachtung und Ausblick 102 5 Zusammenfassung 105 6 Literatur 109 7 Anhang 121