Since European settlement, the woodlands and associated habitats, especially in the temperate zones of Australia, have been extensively cleared and converted to arable land and pastures. Much of the remaining vegetation in the agricultural zone occurs as small isolated patches prone to disturbance and degradation. Apart from habitat loss and fragmentation, altered fire regimes, periods of intense drought, and the introduction of exotic plants and animals, have contributed to the deterioration of most of the natural habitats across Australia, with a negative impact on the native wildlife, including birds. Many woodland bird species have undergone widespread declines, culminating in some local or even regional extinctions. In the mallee woodlands of south-east Australia two closely related species of whistlers (fam. Pachycephalidae) — Red-lored Whistler Pachycephala rufogularis and Gilbert’s Whistler P. inornata — have overlapping ranges, and in some areas they co-exist. These two species are morphologically and ecologically similar. However, despite the similarities, P. rufogularis has undergone greater declines in distribution and abundance than P. inornata. The ecology of these two species is poorly known, which renders adequate management impracticable. The major objectives of this thesis were to determine the key habitat requirements for the two species, to determine their habitat use, and to document the ecology and behaviour of the two species, particularly their foraging, and intra- and interspecific interactions. A sound knowledge of the ecology of the two species is needed to underpin appropriate actions for their management and conservation. Morphological features were measured from skins of P. rufogularis and P. inornata in the South Australian Museum collection, and from captured live birds, to detect if any aspect of the morphology could indicate possible niche partitioning between the two species. Also, the use of biometry as a tool for separating the sexes for P. rufogularis, for determining the species of the uncoloured immature birds and for sexing immatures, was evaluated. No morphological feature suggested niche partitioning. The biometry did not prove a very reliable tool for distinguishing sexes in adult P. rufogularis, but reliably identified the species of the uncoloured immatures. Sexing immatures based on biometrical data alone was not possible. Research was conducted in two main South Australian parks: Gluepot Reserve and Ngarkat Conservation Park. Ecological and behavioural data for P. rufogularis and P. inornata were collected by observing marked (colour-banded and radio-tagged) and unmarked individual birds of both species and sexes, over a two-year period from June 2004 to May 2006. The home ranges of P. rufogularis and P. inornata were determined by tracking the movements of birds in the landscape. Pachycephala rufogularis had much larger home ranges than P. inornata, especially when breeding. The striking differences in home range size between the two ecologically similar species might be related to differences in site fidelity. Pachycephala rufogularis at Gluepot was sedentary, being detected in the same locations throughout the year, and over several years. On the contrary, P. inornata generally showed poor site fidelity, being more mobile, and shifting home ranges between and within seasons. In the field the two species were segregated by habitat. Pachycephala rufogularis and P. inornata showed different habitat preferences, even in areas where they did not co-occur. Pachycephala rufogularis favoured low mallee with Triodia on sand dunes, while P. inornata favoured tall mallee with sparse shrub understorey in interdunes, but also other habitats, such as prickly Acacia thickets and Casuarina woodlands. However, both species used the mallee- Triodia with Callitris vegetation type. The key to coexistence in this habitat was a behavioural one, P. inornata acting as a subordinate species. Pachycephala rufogularis had strict habitat requirements, with the presence of Triodia being critical for the presence of the species. In contrast, P. inornata was more flexible in its habitat requirements, and used a broader range of vegetation types, being more of a habitat generalist. The investigation of habitat use from both a spatial and temporal perspective confirmed that both species actively selected habitat, and that the habitats they selected differed. The core areas of home ranges predominantly contained the preferred habitat for both species. In both species, core areas of home ranges of breeding individuals (where generally the nests were placed) contained preferred habitat in higher proportion than core areas of non-breeding birds. This suggests that during breeding, both species are more restricted to, and/or use more intensely the preferred habitat than when not breeding. The foraging behaviour did not differ consistently between the two species, both capturing insects mostly by snatching in canopy foliage, and also by gleaning on the vegetation, at different heights. However, the two species were already segregated by habitat. Thus the resource partitioning occurred spatially, at the macrohabitat level. In the instances when individuals of both species foraged in the same area and used the same resources, resource partitioning occurred at a temporal scale. Both species were generalists in foraging; therefore, a presumed foraging specialisation as a possible factor related to the decline of P. rufogularis was ruled out. Pachycephala rufogularis and P. inornata are unlikely to be competitors. Support for this argument came from the situation at Ngarkat, where P. inornata was absent. Despite this, P. rufogularis did not use a broader range of vegetation types in Ngarkat, as would be expected under ‘competitive release’. Instead the species maintained strict habitat requirements, specializing virtually on a single vegetation type. The rigid habitat requirements of P. rufogularis, together with its sedentary nature, render this species vulnerable to disturbances, such as wildfires. On the other hand, the apparent flexibility in habitat requirements and greater mobility may explain why P. inornata has been more successful than its sibling species. The information on habitat requirements, preference and use, and also on home ranges of P. rufogularis and P. inornata provided in this study should be included in future habitat suitability models and predictive models for these species, which will assist in their management. / http://proxy.library.adelaide.edu.au/login?url= http://library.adelaide.edu.au/cgi-bin/Pwebrecon.cgi?BBID=1374821 / Thesis (Ph.D.) -- University of Adelaide, School of Earth and Environmental Sciences, 2009

Thesis (Ph. D.)--University of Wisconsin--Madison, 1998. / Typescript. eContent provider-neutral record in process. Description based on print version record. Includes bibliographical references (leaves 339-361).

Thesis (B.S.)--University of Wisconsin -- La Crosse, 2008. / Also available online. Includes bibliographical references (leaf [41]).

Thesis (B.S.)--University of Wisconsin -- La Crosse, 2008. / Also available online. Includes bibliographical references (leaves 47-48).

Thesis (M.A.)--Carleton University, 1993. / Includes bibliographical references. Also available in electronic format on the Internet.

Thesis (M.S.)--University of Alberta, 1998. / Includes bibliographical references (leaves 45-56).

Thesis (M.A.)--University of Missouri-Columbia, 2005. / The entire dissertation/thesis text is included in the research.pdf file; the official abstract appears in the short.pdf file (which also appears in the research.pdf); a non-technical general description, or public abstract, appears in the public.pdf file. Title from title screen of research.pdf file viewed on (November 27, 2006) Vita. Includes bibliographical references.

This thesis presents a local interpretation of an ecosystem approach; 'energyscapes' constructed through mixed methods, which captures private estate manager perception on land use, woodland expansion and collaboration over four case study areas in the Scottish Highlands. Each case study area of three contiguous estates forms a small landscape cluster, with every estate participating in field interviews, woodland planning and collaborative discussions. Private estates in Scotland cover a significant area of the Highlands and are dominated by traditional sporting interests and recreation that is not always considered compatible with woodland expansion, creating a culture of woodland neglect. Subsequently planting rates are falling and Scottish government woodland expansion targets are not being met, despite large areas of vacant land. Key areas of estate and woodland resilience are identified by land managers to improve social and structural connectivity using the novel landscape resilience mapping method, which presents land manager perceptions over a spatial scale linked to resilience concepts. The Forest Energy Tool developed in response to the need for economic justification for woodland expansion demonstrates the potential profitability of local woodfuel markets, as well as providing silvicultural treatments for further management aims. Estate resilience involves fostering effective integration between sporting uses, renewable energy and enhanced rural markets, such as value added forestry. Ecosystem approaches are normally expressed through aspirational policy that is difficult to translate into relevant practice for individual land managers. Energyscapes provides meaning to ecosystem approach policy through CBD principles and operational guidelines, and local practice; including integration of hydro schemes, forest energy and carbon sequestration at estate level and bridging of local and regional scales through six land manager identified landscape partnerships. However, developing leadership, as well as expertise and social capacity in landscape management, is required to mobilise such frameworks. Fundamental to realising these local ecosystem approaches is land manager trust and confidence, which can generate support for emerging land uses alongside tradition, increasing resilience by capturing and utilising the culture embedded within the landscape.

This research problem concerns a follow-up study of seventy-nine boys who have undergone extensive therapy and supervised training in group-living over an extended period of time at Camp Woodland Springs, Dallas, Texas. The problem under consideration is one of determining the operating efficiency of this institution in its main purpose of rehabilitating boys who have generally lacked the social and personal skills necessary to satisfactory adjustment in their respective environments.

I assessed avian communities of Gam bel oak (Quercus gambelii) woodland and surrounding habitats at Camp W. G. Williams State Military Reservation , Utah, during summer of 1993-1998. I used point counts and incidental observations to compile an avian checklist. I observed 100 species, accounting for one third of all birds known from Utah. Overlap in species composition among habitats was considerable, yet each habitat supported a distinct complement of common species. I compared bird species composition, abundance, richness, and diversity before and after fire in burned and unburned Gam bel oak woodland using point counts. I also investigated how similarity of the Gam bel oak avian community to surrounding communities changed after fire. Post-fire changes in individual species abundances reflected a shift from a woodland to a grassland/shrubland community. However, this shift occurred through elimination rather than addition of species, i.e., the post-fire Gambel oak avifauna was a subset of the pre- fire avifauna. Species richness and diversity on burned plots decreased significantly after fi re; unburned plots experienced significant increases in richness and diversity. I also used point counts to evaluate recovery of the Gam bel oak avian community by comparing species composition, abundance, richness, and diversity in different-age burned and unburned Gambel oak woodland. Total abundance, richness, diversity, and similarity to the unburned community increased with post-fire age. I observed significant differences in the abundance of 10 species. Fire did not result in sequential invasion and replacement of bird species assemblages; rather, species found in burned plots were a subset of the avifauna in unburned plots. Return of individual species was related to recovery of preferred nesting and foraging substrates. Over 25% of species found in unburned plots were still absent 11 years post-fire. I conclude that fire had pronounced effects on avian community composition and structure in this habitat. The contention that almost all bird species associated with Gambel oak woodlands are tolerant to fire is not substantiated by the results of this study. Due to the lack of spatial replication in this study, a comparison of avian response to fire in several sites across Gambel oak range would be desirable.