O cerrado é a maior, mais rica e provavelmente a mais ameaçada savana tropical do mundo. No entanto, grande parte de sua área foi ocupada por empreendimentos de agropecuária, nos quais não foram respeitados princípios básicos de conservação, sendo que cada grupo ou táxon reage de forma diferente a mudanças ambientais desse tipo. As aves de rapina, como os Falconiformes e os Strigiformes, são especialmente prejudicadas, pois são considerados predadores de topo de muitas teias alimentares. Porém, para saber como essas aves são afetadas pelas mudanças ambientais causadas pela ação do homem é necessário entender quais fatores são relevantes na \"escolha\" do ambiente de determinada espécie e assim compreender a razão de uma possível seletividade de hábitat. Sendo assim, o presente estudo observou características ecológicas de duas espécies de corujas comuns e bem distribuídas no Brasil, Megascops choliba e Athene cunicularia. Dentre os objetivos estão analisar a metodologia de estudo dessas aves de rapina, com possíveis efeitos na detecção de contatos e verificar o uso de hábitat, em diferentes fisionomias de cerrado, por parte das duas espécies de corujas. O estudo foi realizado na região da Estação Ecológica de Itirapina, no interior do estado de São Paulo. Para contatar as corujas foram realizados experimentos de playback em pontos de amostragem distribuídos em quatro fisionomias (neste estudo consideradas habitats) de cerrado. A atividade vocal de M. choliba variou conforme a temperatura e a umidade relativa. Esta espécie respondeu mais ao playback em condições de temperatura e umidade relativa altas. Athene cunicularia mostrou variar sua atividade vocal conforme a fase da lua e a intensidade do vento. Indivíduos desta espécie respondem mais intensamente ao playback em noites de lua cheia e menos em noites com ventos mais fortes. As duas espécies de corujas se distribuem diferentemente entre as fisionomias de cerrado. Athene cunicularia distribui-se distintamente entre fisionomias fechadas e abertas (Hk-w = 9,976; p = 0,0188), utilizando mais frequentemente as os campos limpo e sujo. Megascops choliba também se distribui diferentemente entre as fisionomias de cerrado (Hk-w = 10,88; p = 2 0,0137), utilizando preferencialmente o campo cerrado e o cerrado s.s.. Segundo os modelos tidos como os melhores, pela seleção de modelos feita através do AIC (Aikaike\'s Information Criterion), a variável com maior poder explicativo é o número de arbóreas para as duas espécies. Megascops choliba e A. cunicularia se segregam ecologicamente, havendo partição divergente de recursos espaciais, devido a seus requisitos para nidificação e forrageamento. Ocorre sobreposição intermediária no uso do habitat entre ambas espécies (O = 0,466). Já quanto a amplitude de nicho espacial (uso de habitat) M. choliba foi generalista (Bst = 0,753) e A. cunicularia intermediária (Bst = 0,453). Sendo assim, estas espécies divergem na seleção de habitat, se distribuindo diferentemente entre as fisionomias de cerrado de acordo com o número de arbóreas. Este estudo sugere, ainda, a importância de se levar em consideração as variáveis climáticas em estudos com o uso de vocalizações de aves de rapina noturnas, servindo também de subsídio para pesquisas futuras sobre censo dessas aves. / The Cerrado biome is the largest, richest and perhaps the most threatened tropical savannah of the world. However, most part of its natural areas has been transformed on agrosystems and pastures where basic principles of conservation weren\'t respected. Each biological group or taxa are affected on different ways by this change. Birds of prey are particularly affected because of its position in trophic webs, as they are top predators. To understand how these birds are affected by change caused by human land use, it is necessary to understand which factors are important for habitat selection, and then understand the species-habitat relationship. Thus, we observed ecological aspects of two widespread and common owls on Brazil: Tropical Screech-Owls (Megascops choliba) and Burrowing Owl (Athene cunicularia). The main objectives of this study included an analysis of methodological aspects of studying these owls species through playback and observe their habitat use. The study was conducted in the Estação Ecológica de Itirapina, State of São Paulo, Brazil. For doing it, we used playback experiments to detect these owls on four different cerrado physiognomies Vocal activities of Tropical Screech-owls were more detected in conditions of higher temperature and humidity. On the other hand, the Athene cunicularia answered more to playback in lower wind speed conditions and/or at full moon nights. The Burrowing Owl explored more frequently open physiognomies of cerrado, as campo limpo and campo sujo (Hk-w = 9.976; p = 0.0188). Conversely, Megascops choliba is more often found on campo cerrado, avoiding campo limpo (Hk-w = 10.88; p = 0.0137). According to Aikaike\'s Information Criterion (AIC) selection model, the most important variable to explain the distribution of both species in cerrado is the number of trees. There was ecological segregation between Megascops choliba and A. cunicularia. The spatial niche was intermediarily segregated (Pianka´s niche overlap measure O = 0.466), according their different needs for nesting and foraging. Additionally, these owls displayed broader (M. choliba Bst = 0.753) or intermediate (A. cunicularia Bst = 0.453) spatial niche breadths. On this sense, these owls have different needs on habitat selection, and their different distributions in cerrado were related more intrinsically to the number of trees present on each physiognomy, which is related to their nesting and foraging requirements. Aditionally, this study suggests, the importance to consider the influence of weather conditions on broadcast survey techniques for nocturnal raptors, which may be considered in further studies on census of these birds.

We measured ventilation, oxygen consumption and blood gases in burrowing owls (Athene cunicularia) breathing moderate and extreme hypoxic gas mixtures to determine their hypoxic ventilatory threshold (HVT) and to assess if they, like other birds and mammals, exhibit a relationship between HVT and hemoglobin O2 affinity (P50) of their blood. An earlier report of an attenuated ventilatory responsiveness of this species to hypoxia was enigmatic given the low O2 affinity (high P50) of burrowing owl hemoglobin. In the current study, burrowing owls breathing 11% and 9% O2 showed a significantly elevated total ventilation. The arterial partial pressure of oxygen (PaO2) at which ventilation is elevated above normoxic values in burrowing owls was 58 mm Hg. This threshold value conforms well to expectations based on the high P50 of their hemoglobin and the HVT vs. P50 relationship for birds developed in this study. Correcting for phylogenetic relatedness in the multi-species analysis had no effect on the HVT vs. P50 relationship. Also, because burrowing owls in this study did not show a hypometabolic response at any level of hypoxia (even at 9% O2); HVT described in terms of percent change in oxygen convection requirement is identical to that based on ventilation alone.

In 2004, I initiated a year-long study to investigate the food habits of burrowing owls (Athene cunicularia). Burrowing owls have been found in a variety of human-altered landscapes; however, little is known about burrowing owl food habits in urban landscapes. Burrowing owl food habits during the non-breeding season are also largely undocumented, despite increasing concern over the survival of overwintering burrowing owls. Differences in prey consumption between reproductive and non-reproductive owls during the breeding season have not yet been examined. I collected pellets over a 12 month period at four study sites affected by different levels of human alteration in the southern San Joaquin Valley of California. Data was collected at four study sites representing natural (Wind Wolves), semi-natural (Allensworth Ecological Reserve), agricultural (Friant Kern Canal), and urban (Bakersfield) landscapes. Invertebrates, primarily ground dwelling insects, were the most commonly consumed prey type, found in 96% of all pellets examined. Among vertebrates, mammals were the most commonly consumed (18.5% of all pellets). Shannon-Weiner diversity indices identified differences in prey diversity consumed between seasons within each site and between sites within seasons, except during the breeding season where diversity was the same at all sites. The diversity indices at Wind Wolves (natural site) and Bakersfield (urban site) were the same, while the diversity indices at Allensworth Ecological Reserve (semi-natural site) and Friant Kern Canal (agricultural site) were the same. Binary logistic regression was used to determine if consumption of individual prey types varied by site, season, and a site/season interaction. Mammals were consumed in greater proportions during the breeding season at most sites compared to other seasons. The proportion of pellets containing mammals during the breeding season decreased as the level of human-alteration increased, with mammal consumption highest at Wind Wolves (60.0%) and lowest at Bakersfield (13.1%). Consumption of several insect categories differed by site and/or season (Coleoptera, Dermaptera, and Orthoptera), but overall consumption of insects was not different by either factor. To assess differences in prey consumption between reproductive and non-reproductive owls, pellets collected during the 2005 breeding season were classified as having come from a nest burrow or a non-nest burrow based on positive identification of reproduction. Shannon-Weiner diversity indices and binary logistic regression were calculated for this data set. No differences were detected in overall diversity or in the proportional consumption of individual prey categories. The results of this study indicate that burrowing owls have a highly variable diet and may have sufficient ecological plasticity to allow them to adjust their food habits to the prey species available in human-altered landscapes. However, the implications of altered food habits on burrowing owl fitness in heavily disturbed landscapes, particularly urban landscapes, needs further study.

There has been a global decline of specialist species observed in recent decades due to the impacts of climate change, invasive species, and habitat loss. Habitat loss and degradation may lead to a mismatch between habitat attractiveness and actual quality, otherwise known as an ecological trap. Ecological traps occur when an organism is constrained by its evolutionary past to select for cues that no longer accurately predict habitat quality. Specialist species are more susceptible to ecological traps due to greater reliance on and fidelity to historic sites and resources. The burrowing owl (Athene cunicularia), a specialist bird species adapted to open ecosystems, has declined throughout its extent. Anthropogenic activity has drastically and rapidly altered burrowing owl native habitat, exposing their habitat to disturbances such as cheatgrass (Bromus tectorum) invasion. The presence of cheatgrass is known to impact the biota of a region and understanding those impacts is becoming increasingly important. The purpose of this study was to quantify the impact of cheatgrass on burrowing owl populations. By assessing how cheatgrass influences the resource selection, nesting success, and food habits of burrowing owls, we provided information that can be utilized to make more informed decisions on how to conserve burrowing owls and their critical nesting habitat. In addition, this information can provide insight into the risk of ecological traps occurring to all specialist species experiencing degradation of their native habitat.