O lobo-guará é uma espécie de ampla distribuição na América do Sul, tendo no Brasil sua maior área de ocorrência. No entanto, as modificações das áreas naturais principalmente destinadas à agropecuária tornam a espécie vulnerável à extinção. A investigação objetivou conhecer em larga escala a área de distribuição potencial gerada por atributos ambientais favoráveis e áreas adequadas à sua ocorrência nos biomas brasileiros e investigar como a espécie responde à estrutura da paisagem, avaliando os efeitos de ambientes modificados pelo homem na sua ecologia espacial, nos padrões de atividade e na movimentação. Modelos de distribuição de espécie foram gerados pelo Maxent, utilizando uma base de pontos de localização de presença a partir de 2000 para o Cerrado (Ce), Pantanal (Pa), Mata Atlântica (MA) e Pampas (Pp) e um conjunto de onze variáveis ambientais não correlacionadas (topográficas, climáticas e paisagísticas). Para análises de ecologia espacial, das atividades e de movimentação, utilizou-se localizações de telemetria (GPS) de animais habitantes de áreas protegidas (AP), e indivíduos em paisagens modificados (AM). Análises de áreas de vida (AV) foram realizadas utilizando o estimador AKDE e associadas com classificação da paisagem local. Os modelos de distribuição do lobo-guará apresentaram uma área de distribuição potencial de 78% do total dos biomas. Apesar de possuírem grandes proporções de áreas adequadas (Ce, 90%; Pa, 93%; MA, 65% e Pp, 6%), somente um pequeno percentual (4,4% do Ce e 4,7% da MA) possui adequabilidade ambiental acima de 50%. Dos atributos que favorecem sua presença, a altitude (para todos os biomas), a precipitação (Ce e Pa), diferenças de temperatura e uso e cobertura do solo (Ma e Pp) foram os mais importantes. Em nível local, animais apresentaram média de AV de 90Km2 em AP e 41Km2 em AM, uma diferença significativa (p<0,01) com áreas diretamente proporcionais ao percentual de áreas naturais na paisagem. Ainda, apesar dos padrões regulares de atividade não mostrarem grandes mudanças, o período de repouso foi significativamente maior (p<0,01) entre os animais AM (46% do dia) que em animais AP (25% do dia). Lobos-guarás de AP e AM não apresentaram grandes diferenças no deslocamento diário com média geral de 14km caminhados por dia, com comprimentos de passos de 1Km. Diferenças no comprimento de passo foram relacionadas à composição da diversidade de contato de classes da paisagem com a proporção de ambientes naturais no passo (quanto maior as variáveis, maior o passo). Passos menores refletem menor persistência de movimento interferindo no deslocamento diário. Com os resultados desse estudo identificou-se a MA e Pa muito importantes, mas o Ce como bioma mais adequado à espécie. Foram encontrados indícios de que a estrutura de suas AV, o uso da paisagem, as atividades e movimentação são afetados pela paisagem modificada. Isso pode comprometer a viabilidade populacional, interferindo na presença em uma área e refletindo no seu potencial de distribuição. As estratégias de manejo de uso do solo, e a recuperação e conexão de áreas adequadas são urgentes e necessárias para que o lobo-guará permaneça presente e funcional nas paisagens dos biomas brasileiros. / The maned wolf has an extensive distribution range throughout South America with Brazil holding the largest portion of this area. However, the species is presently under a vulnerable status due to natural habitats alteration especially from farming and ranching. This study aimed to observe in large scale the potential distribution area indicated by favorable environmental attributes and suitable habitats to its presence within the Brazilian biomes and further to investigate how the species respond to the landscape structure, evaluating the effects of human-modified landscapes on its spatial ecology, activity patterns and movements. Species distribution models were generated using Maxent with a database of presence-only locations from 2000 though 2015, of the Cerrado (Ce), Pantanal (Pa), the Atlantic Forest (AF), and the Pampas (Pp) biomes, and eleven uncorrelated environmental variables (topographic, climatic, and landscape-based). As for the spatial ecology, activity and movement analysis, GPS-based telemetry locations were used from animals inhabiting protected (PAs) and disturbed areas (DAs). Home range (HR) analysis was performed using the AKDE estimator and then associated with the landscape-classified image. The distribution models for the maned wolf showed a potential distribution area of 78% of the total biomes range. Despite the high proportion of suitable areas (Ce, 90%; Pa, 93%; AF, 65%, and Pp, 6%), only a small percentage of the biomes (4.4% for Ce and 4.7% for AF) presented values over 50% suitable. Concerning the attributes that favor its presence, the altitude (for all the biomes), the precipitation (Ce and Pa), the temperature differences and land use (AF and Pp) were the most important. At the local scale, maned wolves showed HR sizes (average) with significant differences (p<0.01) between the 90Km2 (PA) and 41Km2 (DA) with HR size directly related to the proportion of natural areas. Although the general activity patterns were not considerably different between PA and DA, the resting periods of DA\'s animals (46% of the day) were significantly different (p<0.01) than the period of PA\'s wolves (46% of the day). Animals did not show changes on the daily movement patterns, accounting with 14km in general average and 1km of average step length (no major differences as well). The variation on the step length was related to the association of the diversity of contacts between landscape classes with the proportion of natural classes at each step (as bigger the variable values, bigger the step). As a consequence of smaller steps, constancy of movement decreases. Considering the results, the AF and Pa outstand as very important biomes, however the Ce was indicated as the most suitable biome. Furthermore, the research indicated signs that the HR structure and the landscape use, besides the activity patterns and the movement are affected by altered landscapes. This might compromise the population viability, interfering directly on its presence in an area and affecting the species distribution. Thus, a proper land use management aiming the recovering of degraded habitats is an important strategy tor the maned wolf conservation, so the species can long last survive across the Brazilian biomes.

Abstract :Bluetongue (BT) is a vector-borne infectious disease primarily transmitted to even- toed ungulates by the bite of several Culicoides species. The global distribution of BT can be attributed to the ubiquity of its vectors and its rapid spread, likely to the enhancement of human activities (intensification of animal production, trans- port, changing habitat). During the last decades, BT established in Southern Europe and more recently emerged in Northern Europe, causing the death of millions of domestic ruminants. On the same time, a Belgian research project has been set up to develop remote-sensing tools to study the EPidemiology and Space-TIme dynamicS of infectious diseases (EPISTIS). In that general framework, this thesis aimed to study the space-time distribution of the main Culicoides vectors occurring in Italy and Belgium, at two different scales. Firstly, we aimed to clarify the role of several eco-climatic factors on the regional-scale distribution of C. imicola in time, based on weekly samplings achieved throughout Italy from 2001 to 2006 and to develop an easy-to-use and reproducible tool, which could be widely validated on the basis of former vector sampling and freely accessible remote-sensing data. Secondly, we aimed to investigate how Culicoides species were distributed in the fine-scale habitat encountered throughout the agro-ecological landscapes of Belgium, while recent studies have suggested that the landscapes configuration could explain the spatial distribution of BT. In the first part, we showed that an autoregressive model where the observed monthly growth rate is predicted by monthly temperature, allowed predicting >70% of the seasonal variability in C. imicola trap catches. The model predicted the seasonality, the altitudinal gradient, and the low populations’ activity taking place during the winter. Incorporating eco-climatic indices such as the Normalized Difference Vegetation Index into the model did not enhance its predictive power. In the second part, we quantified how Culicoides populations are spatially structured in the neighbourhood of farms, and demonstrated the unexpectedly high level of population found in forest. We also showed how four classes of land use could influence the relative abundances of Culicoides species in the agro-ecological landscapes of Belgium. Although in summer, BT vectors were abundant in each of the four classes investigated, their relative abundances varied strongly as a function of sex, species and environmental conditions, and we quantified these variations. Finally, we also presented a new method to quantify the interference between Onderstepoort light traps, and used it to measure their range of attraction for several of the most common BT vectors species in Northern Europe. The model developed on C. imicola in Italy provided enthusiastic perspectives regarding the regional-scale analyses of its distribution in time, although further improvements are nevertheless required in order to assess the broad scale ecology of BT vectors throughout Europe. Mapping the abundances of C. imicola in Sardinia high- lighted an important lack of reliability attributable to the many land use classes that are currently not sampled in the vector surveillance achieved across Europe. Together with the novelties presented in the second part and the recent findings establishing that BT could circulate among wild hosts in both epidemiological systems (i.e. in Southern and Northern Europe), we call for increasing epidemiological and entomo- logical studies at the interface between farms and the surrounding natural habitats. Last, depicting in time the landscape-scale findings for Northern Europe highlighted how dramatic could be the role played by intensive farming practices to maintain BT within the agro-ecological landscapes studied and to facilitate its circulation between them. Quantifying the amplitude of the risk of disease transmission linked to these practices would require a further complex modeling approach accounting simultaneously for the diel activity of hosts, mainly resulting from the farming activities, the diel activities of different vector species and the landscapes configuration found in contrasted agro-ecological systems.<p>Résumé :La fièvre catarrhale ovine (FCO), encore appelée maladie de la langue bleue, est une maladie infectieuse des ruminants transmise par la piqûre d’un vecteur de type moucheron appartenant au genre Culicoides (Diptera :Ceratopogonidae). L’ubiquité de ses vecteurs peut expliquer son succès d’installation à l’échelle globale. Par ailleurs, sa rapide expansion a été grandement facilitée par l’importante activité anthropique (élevage, transport, modification de l’habitat) et peut-être même par les changements climatiques globaux. La FCO a été récemment qualifiée de maladie infectieuse émergente en Europe du fait de (i) son récent établissement dans la région, bien au delà de son aire de répartition traditionnelle, (ii) de sa forte capacité de dispersion affectant chaque jour un nombre plus important d’hôtes et enfin (iii) de sa forte virulence. Après avoir détaillé les caractéristiques majeures des deux principaux foyers de FCO rencontrés en Europe depuis 1998, la présente thèse s’est plus particulièrement intéressée à l’étude de la distribution spatio-temporelle de ses principaux vecteurs dans le sud (partie 1) puis dans le nord (partie 2) de l’Europe, à différentes échelles. Dans la première partie, un modèle discret, spatialement et temporellement explicite, a été développé afin de mesurer l’influence de différents facteurs éco-climatiques sur la distribution de Culicoides imicola, principal vecteur de la FCO dans le Bassin Méditerranéen. Les profils mensuels de distribution rencontrés en Sardaigne durant 6 années consécutives ont ainsi pu être reconstitués, principalement sur base de la température. Une cartographie de l’abondance de C. imicola sur le territoire a permis de mettre à jour le manque d’information sur sa distribution en dehors des exploitations agricoles. Dans la deuxième partie du travail, nous nous sommes penchés sur la distribution spatiale des Culicoides tels qu’on peut les rencontrer au sein de différents paysages agro-écologiques de Belgique. Nous avons ainsi pu décrire la structure adoptée par les populations de Culicoides au voisinage des fermes ainsi que quantifier l’importante population présente dans les forêts avoisinantes. Nous avons par ailleurs montré l’influence de différentes catégories d’utilisation du sol sur l’abondance et la composition en espèces. Enfin, nous avons présenté une méthode permettant de quantifier l’interférence entre des pièges lumineux utilisés dans un même paysage pour échantillonner les populations, et l’avons utilisé afin de mesurer leur rayon d’attractivité sur les espèces vectrices les plus communément rencontrées dans le nord de l’Europe. En guise de conclusion générale et conjointement aux récentes découvertes de cas de FCO au sein de la faune sauvage européenne, nous appelons à réaliser un plus grand nombre d’études éco-épidémiologiques à l’interface entre exploitations agricoles et zones (semi-) naturelles avoisinantes. En outres, les résultats présentés dans la seconde partie ont été mis en relation avec le mode de fonctionnement journalier de nos exploitations agricoles. Nous avons ainsi pu déduire le rôle dramatique joué par les pratiques agricoles intensives dans le maintien du virus de la FCO au sein de nos paysages agro-écologiques, ainsi que dans sa circulation d’un paysage à l’autre. Un cadre de modélisation complexe permettant une analyse simultanée de l’activité nycthémérale des hôtes de la FCO et de ses vecteurs Culicoides en fonction de la configuration des paysages agro-écologiques est néanmoins requis afin de quantifier l’amplitude du risque de transmission de la FCO lié aux pratiques agricoles intensives. / Doctorat en Sciences agronomiques et ingénierie biologique / info:eu-repo/semantics/nonPublished

The conservation of leopards in the Eastern Cape Province requires a holistic approach that considers both predator-human interactions as well as the biology of the carnivore. Numerous studies have been conducted on leopards within protected areas; however more information regarding the species is needed outside these areas to facilitate effective management of predators. The spatial ecology of the leopard (Panthera pardus) were studied in the Baviaanskloof and GAENP in the Eastern Cape. The Baviaanskloof is an extensive area of mountainous terrain (approximately 2665km²) which has a mosaic of land uses, and leopards move from conservation areas to farmland where they come into contact and conflict with farmers. This study examined the spatial ecology of leopards living on farmlands adjacent to protected land. The space utilization and activity patterns of six leopards were analysed. These animals were caught and released on farmlands in the Baviaanskloof (n=4) or translocated (n=2) when not possible to release on site. The animals were caught by means of fall-door, walk-in traps and fitted with Vectronic GPS collars that facilitated the collection of high quality GPS fixes from each animal. Data was collected using VHF and UHF telemetry to download data. An understanding of spatial requirements in areas with different land use, and the extent of overlap of space use with other leopards allow, for the first time in the region, the calculation of possible maximum population size. Analysis of range size was carried out using two methods: minimum convex polygon, and Kernel Utilization Distribution. Finally, a key predictor of space use is prey availability. I assessed the prey base using a grid of camera traps. The studied leopards revealed large range utilization with minimal overlap. The activity patterns suggest there is no preference between diurnal and nocturnal activity patterns and the population density was estimated between 0.3 - 1.3 leopards per 100km². Large home range sizes and low population densities suggest that leopards require large areas of suitable habitat, and that conservation efforts need to be extended beyond protected areas to ensure the long-term viability of leopard populations in such areas.

Les forêts tropicales renferment des peuplements arborescents dont la gestion et l’aménagement nécessitent des connaissances sur leur organisation spatiale et leur dynamique. Les analyses de la structure spatiale des espèces arborescentes peuvent être utilisées en forêts naturelles pour identifier les mécanismes sous-jacents qui structurent les peuplements forestiers afin d’améliorer la compréhension des relations entre les espèces. Cette étude a été menée dans la Réserve Forestière de Yoko (RFY) aux environs de Kisangani à l’est de la RD Congo (R.D.C). Elle consiste à analyser la structure spatiale horizontale des espèces les plus abondantes et à tenter d’identifier, à l’échelle locale, les facteurs et/ou processus écologiques potentiellement explicatifs pour en retirer des enseignements utiles à la gestion des massifs forestiers situés à proximité de Kisangani. <p>Pour ce faire, une parcelle d’échantillonnage de 25 ha (500m 500m) a été délimitée dans le bloc sud de la RFY constitué d’une végétation ligneuse mixte et semi-décidue. Un inventaire forestier a permis d’analyser la composition floristique et structurale de la zone. Trois techniques (ou modèles statistiques) relevant de l’écologie spatiale pour l’analyse de la structure horizontale des espèces ont été utilisées :la méthode du voisin le plus proche de Clark & Evans (1954), la méthode d’échantillonnage aléatoire de Hines & Hines (1979), ces deux méthodes reposant sur une analyse à échelle unique de la parcelle d’étude, et la méthode de Ripley (1977) permettant non seulement une analyse multi-échelle mais aussi l’étude des relations intra et interspécifiques. Concernant ce point précis, les arbres ont été catégorisés en trois stades de développement sur la base de leurs diamètres (les jeunes, les immatures et les adultes). Une analyse comparative et théorique des trois méthodes a été effectuée. <p>Un total de 169 espèces appartenant à 36 familles dont 114 genres ont été identifiées, et la famille des Fabaceae dont la majorité des espèces appartiennent à la sous famille des Caesalpinioideae est apparue prépondérante. Trois espèces se sont révélées les plus abondantes et les plus représentatives du peuplement, et ont pour cette raison fait l’objet de toutes les analyses :Gilbertiodendron dewevrei J. Léonard (De Wild), Scorodophloeus zenkeri Harms et Uapaca guineensis Mull. Arg. Elles ont toutes les trois montré une structure agrégée, et cela à toutes les échelles d’analyse. Les agrégats observés présentent un rayon d’environ 25 m de distance. L’analyse en fonction du diamètre a indiqué une structure agrégée pour les plus petits diamètres et régulière pour les plus grands, et que l’agrégation diminue avec le diamètre. Les résultats montrent également que les structures spatiales observées dépendent de l’échelle d’analyse considérée et de la méthode utilisée. La méthode de Clark & Evans est sensible à la variation de l’étendue. À cet égard, l’échantillonnage aléatoire de Hines & Hines est apparu plus adaptée que celui de Clark & Evans. Les fonctions de Ripley et dérivées sont des outils efficaces et apportent plus d’information. Les analyses ont montré des associations positives entre G. dewevrei et S. zenkeri, ainsi qu’entre G. dewevrei et U. guineensis. Par contre, une indépendance a été constatée entre S. zenkeri et U. guineensis. Il apparaît également que les jeunes sont associés positivement aux adultes supposés reproducteurs, et que les immatures sont indépendants par rapport aux adultes. La dispersion faible ou limitée des graines à proximité des arbres parents en est le principal facteur endogène responsable. Ce facteur explique également les associations positives entre les jeunes et les adultes de la même espèce. La compétition entre des individus pour les besoins en espace, en lumière ou en nutriments dans le sol, explique la structure régulière observée ainsi que l’indépendance des immatures envers les adultes. La dispersion limitée n’est cependant pas le seul facteur explicatif de l’agrégation spatiale des arbres, d’autres facteurs tels que l’hétérogénéité environnementale (sol, topographie,…) ou la perturbation sont vraisemblablement aussi impliqués. La perturbation anthropique ou naturelle est un processus écologique qui devrait avoir joué un rôle déterminant dans l’organisation spatiale des communautés de la forêt. Combinée au phénomène de masting, aux effets de Janzen-Connell et aux ectomycorhizes, elle est très probablement à la base des structures spatiales et des relations spatiales observées entre les espèces de la RFY. / Tropical forests contain tree-stands with management and planning requires knowledge of their spatial organization and dynamics. Analyses of the spatial structure of tree species can be used in natural forests to identify the underlying mechanisms that structure of forest stands to improve the understanding of the relationships between species. This study was conducted in the Yoko Forest Reserve (YFR) around Kisangani in eastern DR Congo (DRC). It is to analyze the horizontal spatial structure of the most abundant species and to try to identify, on a local scale, factors and / or potentially explicative ecological processes to draw valuable lessons for the management of forest areas nearby Kisangani. <p>To do this, a sample plot of 25 ha (500m x 500m) was delineated in the southern block of the YFR consists of a mixed woody vegetation and semi-deciduous. A forest inventory was used to analyze the floristic and structural composition of the area. Three techniques (or statistical models) under spatial ecology for the analysis of the horizontal structure of the species were used: the nearest neighbor method of Clark & Evans (1954), the random sampling method Hines & Hines (1979), these two methods based on a single scale analysis of the study plot, and the method of Ripley (1977) allows not only a multi-scale analysis, but also the study of intra- and inter-relationships. Regarding this point, the trees were categorized into three stages of development on the basis of their diameters (young, immature and adult). A comparative and theoretical analysis of the three methods was performed. <p>A total of 169 species belonging to 36 families with 114 genera have been identified and the family Fabaceae which the majority of species belong to the subfamily Caesalpinioideae appeared decisive. Three species have proved the most abundant and the most representative of the stand, and for this reason the subject of all analyzes Gilbertiodendron dewevrei J. Léonard (De Wild) Scorodophloeus zenkeri Harms and Uapaca guineensis Mull. Arg. They all three showed an aggregated structure, and that all scales of analysis. Observed aggregates have a radius of about 25 m distance. The analysis based on the diameter indicated an aggregated structure for smaller diameters and regular for larger and that aggregation decreases with diameter. The results also show that the observed spatial structures depend on the considered analysis of scale and the method used. The method of Clark & Evans is sensitive to the variation in the extent. In this regard, the random sampling of Hines & Hines appeared more suitable than that of Clark & Evans. Ripley's functions and derivatives are effective tools and provide more information. Analyses showed positive associations between G. dewevrei and S. zenkeri, and between G. dewevrei and U. guineensis. By against, independence was found between S. zenkeri and U. guineensis. It also appears that young people are positively associated with the supposed breeding adults and immatures are independent compared to adults. The low or limited seed dispersal near parent trees is the main endogenous factor responsible. This factor also explains the positive associations between youth and adults of the same species. The competition between individuals to space requirements, light or nutrients in the soil, explains the observed regular structure and the independence of immature towards adults. Limited dispersal, however, is not the only factor explaining the spatial aggregation trees, other factors such as environmental heterogeneity (soil, topography, ) or disturbance are probably also involved. Anthropogenic or natural disturbance is an environmentally friendly process that should have played a decisive role in the spatial organization of forest communities. Combined with masting phenomenon, the effects of Janzen-Connell and Ectomycorrhizae, it is very probably the basis of spatial structures and spatial relationships observed between species of the YFR.<p><p> / Doctorat en Sciences agronomiques et ingénierie biologique / info:eu-repo/semantics/nonPublished