Thesis (M.S.)--University of Missouri-Columbia, 2007. / 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 October 29, 2007) Includes bibliographical references.

This study shows how the feeding behaviour of the increasing number of geese impacts their fragile breeding grounds in the Arctic region of Svalbard and, ultimately, may affect the geese themselves.  On arrival in their breeding grounds in spring, pink-footed geese, in common with other goose species, forage for below-ground plant parts.  This grubbing behaviour disturbs tundra ecosystems.  This thesis investigates the extent and distribution of grubbing on Svalbard, its impact on tundra ecosystems and feedbacks to the goose population in the long term. Grubbing geese reduce the abundance of plants, including moss, in tundra vegetation and cause the loss of substantial quantities of soil carbon.  A multi-habitat field manipulation experiment demonstrated that the impact of grubbing varies between communities; wetter communities with high moss cover are less negatively affected, but these are more likely to be grubbed by geese, particularly in valley bases and low lying coastal areas.  Using data collected in this project, the long-term effect of geese on tundra was simulated.  This resulted in predictions that geese will cause substantial degradation of their habitat if the population increases by another 50% to 75,000. Due to the negative effect of grubbing on vegetation, the long-term sustainable size of the population of pink-footed geese breeding on Svalband is estimated to be 95,000, less than 30% of the number expected based on the tundra’s productivity.  Pink-footed geese are therefore “ecosystem engineers” of the tundra, as they affect resource availability and “carrying capacity engineers”, as by degrading their own habitat they reduce the size of the goose population that it can support.

Based on the recommendations of both the 1993 Reintroduction biology of Australasian Fauna Conference and the 1994 Rock Wallaby Symposium, captive-bred Yellow footed rock wallabies were reintroduced into areas of their former ranges in both South Australia and Queensland

Thesis (M.S.)--University of North Carolina at Wilmington, 2004. / Includes bibliographical references (leaves : [79]-88).

The work of which this study is an account was carried out while the author was Deputy Leader of the British Ornithologists' Union Centenary Expedition to Ascension Island , from November 1957 to April 1959. The objects of the expedition were to investigate the general breeding biology of the resident tropical seabirds with a view to discovering how the timing of their breeding was controlled. In most temperate birds the controlling factors are changes in day-length, temperature, and availability of food; the particular interest of the eleven species at Ascension was that they were living in an environment with no seasonal change in day-length or climate, and apparently a uniform availability of food. The author was responsible for studies on three of these species, the White Booby Sula dactylatra, the Brown Booby Sula leucogaster, and the Fairy Tern Gygis alba. A few observations were also made on the ten or so pairs of the Redfooted Booby Sula sula which were present. The bulk of this study is an account of the comparative breeding biology of the White and Brown Boobies. The Fairy Tern is not closely comparable to them, and only those aspects of its biology relevant to the general problem (breeding, food, and moult) are dealt with, in an Appendix. The study is divided into nine sections, of which four deal with the breeding of the boobies, and three with other observations on the species' biology, vis, moult and food (both of which were found to have an important relation to the breeding biology), and behaviour, which had neither been fully described nor analysed before. Section I is introductory, the aims, scope, and methods of study being described, together with the habitat. Ascension Island lies roughly in the middle of the South Atlantic (8°S, 14°25'W). It is a peak of the Mid-Atlantic Ridge, triangular in shape, with sides of about eight miles, and rises from coastal plains to 2,800 ft in the middle. Its volcanic origin is clearly seen in the numerous extinct craters, ash-fielda, and lava-flows, which are little weathered by the uniformly warm and sunny climate and the continuous south-east Trade-winds. Vegetation is confined to the slopes above about l,000 ft. As a result of man's introduction of rats and cats, the seabirds are no longer found on the main island and, with the exception of the Wideawake Tern, are now confined to off-shore stacks and islets. The expedition's main work was therefore done on Boatswain-bird Island, a volcanic plug some 300 ft high and 400 yds, across, about 300 yds, off the south-east corner of Ascension. Only intermittent visits could be paid to this island, and the author spent about 130 days, spaced over 15 months, on it. Section II deals with the colonies and breeding seasons. There were 1200-1300 pairs of White Boobies breeding on Boatswain-bird Island, and one or two pairs elsewhere. 600-700 pairs of Brown Boobies bred at Ascension, of which about two-thirds were on Boatswain-bird Island and the reminder on small stacks. In both species there were clearly-marked peaks of laying, with intervening periods when the number of new clutches was very small. In the White Booty breeding appeared to occur annually (only one fun season was studied, but deductions were made about the preceding and following ones), in the Brown about every eight months (two full seasons were seen, and again deductions were made about others). In both species the time taken from laying of eggs to fledging of chicks was the same, six to seven months. Individuals of both species conformed to the breeding seasons of the population, and if out of phase for some reason, they had a longer or shorter "rest" period as necessary to bring them into phase again at the next season, these two discoveries at once suggested that external factors were modifying the birds' internal physiological cycles and controlling the time of breeding. What these factors might be is discussed later in the study, in the light of subsequent discoveries about the species' breeding biology. The two species differed not only in periodicity of casual cycle but also in the time of year at which laying took place. The periodicity was such, however, that every two years the Brown Boobies would lay at almost the same time as the White. The significance of this, and its possible relation to annual variation in oceanic conditions with their origin in the melting of the Antarctic ice, is discussed, together with published information about the species' breeding seasons in other parts of the world. Section III deals with clutch-size and incubation. Both species were found to lay two eggs, with very few exceptions, but only one chick was raised. Incubation is described, and the attentive spells at the nest analysed; the attentive spells of both species were found to be variable, those of the White Booby being about 48 hours and those of the Brown about 24 hours. This probably indicated a difference in the birds' feeding range (partly confirmed by a study of their food), important in the consideration of the two species' ecologlcal differences. Some desertions occurred during the study of attention spells, and the circumstances of these strongly indicated that the birds were experiencing difficulty in finding food, this view subsequently being supported by other events. In Section IV the feeding, care, and growth of the chick are described. Records of growth rates of both normal, and abnormal chicks were obtained, and these provided further evidence of the operation of a food shortage. Losses in weight and reductions of growth rate occurred in chicks of varying ages but at roughly the sane date, August and September 1958. The second chick of the clutch hatched about five days after the first and never lived more than two or three days. The curious circumstances of this are described the smaller chick was apparently expelled from the nest by the larger, and not starved to death as a result of the larger chick's more vigorous demands, as has been shown in some other species of birds. Experiments with twins were carried, out to investigate this situation further; the larger chick's ability to establish a supremacy was found to be so strong as to operate even when the difference in size between artificial twins was very small; and some parents were able to raise twin chicks at apparently the normal rate of growth for two weeks or more. Possible reasons for this striking behaviour amongst the chicks and its relevance to clutch size and breeding success are discussed. In Section V, breeding success is described. Both species had a low breeding success, and big losses of eggs and chicks of the White Booby occurred in August and September 1958, supporting the other evidence concerning shortage of food. In one area of the White Booty colony studied only 4.5% of the eggs laid gave rise to flying young, in another area the figure being 9%. In the Brown Booby 5% of the eggs laid gave rise to flying young in one season, while in the following season the figure was 13%; the difference here was probably due to shortage of food in the first season causing late deaths among chicks. Section VI deals mainly with moult in the White Booby. Less information was obtained about the Brown Booty but the procedure appeared to be the same as in the White; in view of the Brown Booby's shorter sexual cycle, however, more information than could be obtained would have been interesting. The sequence of primary moult was discovered when examining juvenile White Boobies which had returned to the island after a post-fledging dispersal. The change from juvenile to adult plumage took more than two years, the shedding and regrowth of the primaries, from the innermost outwards, occurring in three spaced concurrent cycles.

Conservation biology is primarily concerned with the amelioration of species decline. The Yellow-footed Rock-wallaby (Petrogale xanthopus xanthopus) is a medium sized Macropod that inhabits the semiarid rangelands of South Australia and New South Wales. Its conservation status is Vulnerable C2a(i). In this study, population modelling, spatially explicit habitat modelling and Population Viability Analysis (PVA) have been used to better understand the factors that affect the abundance and distribution of the P. x. xanthopus in South Australia. The processes that drive the population dynamics of a species operate at different scales. As such this research involves a collection of several inter-related and scale-specific empirical studies that provide insights about the population dynamics of P. x. xanthopus. Each of these studies captures environmental, demographic and behavioural process acting on the population at different scales. These include the analysis of relative abundance data derived from an aerial census, mark recapture sampling of demographic parameters in relation to rainfall patterns and a collection of habitat models derived at different scales using presence-absence data. Spatially explicit PVAs enable the population dynamics of a species to be modelled in space and time. Using these data, a PVA is conducted to explore and rank the importance of the factors that threaten this species and help guide their future monitoring and management. Movement is also a key issue when considering problems such as isolation and inbreeding. Given that little is known about the dispersal behaviour of this species, a range of different dispersal behaviours are also simulated in the PVA using random and non-random mating algorithms, to estimate the potential for inbreeding. / Thesis (PhD)--University of South Australia, 2004.

Based on the recommendations of both the 1993 Reintroduction biology of Australasian Fauna Conference and the 1994 Rock Wallaby Symposium, captive-bred Yellow footed rock wallabies were reintroduced into areas of their former ranges in both South Australia and Queensland

Spatiotemporal heterogeneity in predator activity can generate and influence the availability of refugia to prey. In eastern forests, white-footed mice (Peromyscus leucopus) and eastern chipmunks (Tamias striatus) are abundant generalist rodents, and large-scale removal experiments have confirmed they are important predators of gypsy moth (Lymantria dispar) pupae and songbird nests and eggs. Models predict the extinction of gypsy moth populations when confronted with abundant mouse populations, but small-scale (10s of m) heterogeneity in rodent activity may allow for the persistence of moth populations. I quantified the magnitude, variability, temporal persistence, and spatial structure of white-footed mouse and eastern chipmunk activity, and evaluated the effects of small-scale (30 x 30 m "spots") rodent removal, on 3 pairs of oak-dominated plots for 3, 2-week periods in summers 2008 and 2009 at the Cary Institute of Ecosystem Studies, Millbrook, NY, USA. Small-mammal track activity (1/check) was best fit by a beta-binomial distribution, and the mean and CV ranges of mouse and chipmunk track activity were similar between years. Disattenuated correlations of mouse and chipmunk activity were similar between sampling periods, as well as between years. I found little evidence of spatial structure in rodent activity at the scales sampled (15-250 m). Mean local track activity counterintuitively increased in removal spots compared to control spots for mice in 2008 and chipmunks in 2009. Local, between-year track activity was more strongly correlated and of greater magnitude in persistent removal spots than in non-persistent removal spots for both mice and chipmunks Environmental factors like abundant alternative food sources can influence predator foraging behavior by concentrating predator space use and altering predation rates on incidental prey items. However, the spatial scale of this aggregative effect, and impact on consumption rates on incidental prey items, are not well understood. In spring 2010, I conducted live-trapping, measured local rodent track activity, and quantified consumption rates on two incidental prey items (almonds [Prunus dulcis] and maple [Acer saccharum] seeds) on 6 plots provided with 3 supplemental food treatments (control, corn, and sunflower seeds) at Touch of Nature Environmental Center, Carbondale, IL, USA. A half-normal, cosine detectability function best fit our live-trapping data in both pre- and post-experiment trapping sessions, but considerable support remained for other models. Overall mean track activity was greater in control treatments than in sunflower and corn treatments. I found a significant interaction effect of treatment and distance, and significantly increased activity in control treatments at distances of 0, 10, and 40 m. Overall mean almond and maple seed consumption was greater in control treatments than in sunflower and corn treatments, but was greater in corn than sunflower treatments and increased from period 1 to period 3 at all distances. Mean almond consumption by mouse only and mouse + unknown predator groups was greater in control treatments than in sunflower and corn treatments. Mean maple seed consumption by mouse only and mouse + unknown predator groups was greater in control treatments than in sunflower and corn treatments.

No description available.

No description available.