Oak wilt is a fatal disease of oaks caused by the fungus Ceratocystis fagacearum. Loss or degradation of habitat due to the disease may negatively affect the federally endangered golden-cheeked warbler (Setophaga chrysoparia). To assess the impact of oak wilt on golden-cheeked warblers, I investigated its influence on habitat selection and quality. I used remote sensing to estimate the amount of potential golden-cheeked warbler habitat currently affected by oak wilt, to predict the amount of potential habitat likely to be affected in the near future, and to assess the current probability of warbler occupancy in areas affected by oak wilt historically. I also quantified vegetative characteristics to assess overstory vegetation and regeneration in areas affected by the disease. I found proportional occupancy and territory density in unaffected areas to be, respectively, 3.5 and 1.8 times that of affected areas. Pairing success was 27% lower for territories containing oak wilt but fledging success was not affected. I estimated that 6.9% of potential golden-cheeked warbler habitat and 7.7% of the total area within my study region was affected by oak wilt in 2008. By 2018, I predicted that 13.3% of potential golden-cheeked warbler habitat and 16.0% of the study region would be affected by the disease. Using historical imagery, I found that areas affected by oak wilt in the past are less likely to be classified as current potential warbler habitat than areas never affected by the disease. I found no differences between the understory vegetation of affected and unaffected areas but that oaks were more common in the overstory than in the understory, suggesting that species composition in affected areas may shift in the years following an outbreak of the disease. My results suggest that the presence of oak wilt negatively influences habitat selection and quality for golden-cheeked warblers, likely due to reduced canopy cover in susceptible oak species. Additionally, oak wilt frequently occurs in golden-cheeked warbler habitat and will continue to spread into warbler habitat in the coming years. Future management efforts should address the threat oak wilt poses to golden-cheeked warblers by incorporating applicable preventative measures.

Phytophthora cinnamomi is a soil-borne oomycete pathogen causing root rot in susceptible host species. P. cinnamomi is thought to have originated in Southeast Asia, but has since been introduced to many regions around the world, where it causes dramatic declines in many forest tree species. In the eastern US, the primary susceptible tree species of concern are American chestnut (Castanea dentata), white oak (Quercus alba), and shortleaf pine (Pinus echinata). American chestnut, functionally eliminated in the early 1900s by the rapidly acting chestnut blight (Cryphonectria parasitica), has been the subject of decades-long breeding efforts aimed at improving chestnut resistance to chestnut blight. To improve chestnut restoration success, and restoration of other susceptible species, the distribution patterns of P. cinnamomi on a landscape scale must be better understood. This project was initiated to develop an improved method for detecting P. cinnamomi to permit high-throughput screening of forest soils, and to implement the improved detection approach in characterizing the distribution patterns of P. cinnamomi in developing soils on reclaimed surface mines in eastern Kentucky, as well as mature forest soils within an undisturbed watershed in a reference-quality eastern Kentucky forest. We developed an improved detection method using a molecular DNA-amplification approach (PCR), which demonstrated similar sensitivity to traditional culture-based methods, but required less time and space than traditional methods. We used this detection approach to screen soils from a chronosequence of reclaimed surface mines (reclaimed at different points in time) to evaluate whether reclaimed surface mined sites become favorable for P. cinnamomi colonization over time. Our analysis detected P. cinnamomi at the two older sites (reclaimed in 1997 and 2003), but we did not detect P. cinnamomi at the two newer sites sampled (reclaimed in 2005 and 2007). These results suggest that surface mined sites become favorable for P. cinnamomi colonization over time, and should not be considered permanently “Phytophthora-free.” We also collected ~200 samples from a watershed in UK’s Robinson Forest, from plots representing a gradient of topographic position, slope, and aspect. This survey indicated that P. cinnamomi distribution in forests is complex and can be difficult to predict; however, P. cinnamomi was detected in both drier upslope sites and in moister drainage sites.

Dans la forêt de pin maritime (Pinus pinaster) des Landes de Gascogne (sud-ouest de France), la mortalité des pins causée par le champignon pourridié Armillaria ostoyae (Basidiomycète) a augmenté au cours des 30 dernières années. Les premiers cas de cette maladie ont été signalés quelques années après un changement majeur dans l'utilisation des terres, qui a eu lieu dans cette région suite au remplacement des landes et marais d'origine par une forêt plantée et gérée da façon intensive. Notre objectif était de comprendre les facteurs à l'origine de cette maladie émergente. Pour cela, nous avons étudié la distribution spatiale des dommages causés par le pathogène en relation avec des facteurs historiques, estimé la variabilité des traits fongiques liés au parasitisme et saprophytisme, et étudié l'histoire démographique d'A. ostoyae. La répartition actuelle de la mortalité induite par A. ostoyae est apparue dépendre de la présence des forêts préexistantes, ce qui suggère qu'A. ostoyae était fréquent dans ces zones forestières anciennes, qui ont agi comme un réservoir pour la colonisation des forêts plantées récentes. La production de rhizomorphes était significativement corrélée avec la virulence, suggérant que ce trait joue un rôle important dans le stade parasitaire d'A. ostoyae. Aucune relation significative entre le parasitisme et saprophytisme n'a été détectée, suggérant une absence de compromis évolutif entre ces traits. Enfin, le meilleur scénario démographique pour expliquer la structure de la population d'A. ostoyae dans la forêt des Landes est un scénario en deux étapes : il y aurait eu d'abord une diminution puis une expansion de la population fongique, qui semblait suivre la dynamique de la population d'hôtes. Le temps de génération d’A. ostoyae a été estimé entre 10 et 20 ans. / In the maritime pine (Pinus pinaster) forest of the Landes de Gascogne (south-western France), pine mortality due to the root rot fungus Armillaria ostoyae (Basidiomycete) has been increasing over the last 30 years. The first cases of this disease were reported a few years after a major change in land use which occurred in this region following the replacement of original moors by an intensively managed planted forest. Our aim was to understand the factors driving this disease emergence. For this, we investigated the spatial distribution of pathogen damage related to historical factors, estimated the variation in fungal traits related to parasitism and saprophytism and investigated the demographic history of A. ostoyae. The current distribution of A. ostoyae mortality appeared depending on the pre-existing forests, suggesting that A. ostoyae was commonly distributed in pre-existing forest areas which acted as a reservoir for the colonization of recent planted forests. The rhizomorphs production was significantly correlated with virulence, suggesting that this trait plays an important role in the parasitic stage of A. ostoyae, but no significant relationship between parasitism and saprophytism components was detected, which may suggest that there is no trade-off between these traits. Finally, the best demographic scenario to explain A. ostoyae population structure in the Landes forest is a two step scenario: there was first a decrease and then an expansion in the fungal population, which appeared to follow the dynamics of the host population. The generation time of A. ostoyae was estimated between 10 and 20 years.