<?xml version="1.0" encoding="UTF-8"?>
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  <title>DSpace Community:</title>
  <link rel="alternate" href="http://hdl.handle.net/10023/95" />
  <subtitle />
  <id>http://hdl.handle.net/10023/95</id>
  <updated>2013-05-20T00:41:22Z</updated>
  <dc:date>2013-05-20T00:41:22Z</dc:date>
  <entry>
    <title>Estimating animal population density using passive acoustics</title>
    <link rel="alternate" href="http://hdl.handle.net/10023/3496" />
    <author>
      <name>Marques, Tiago A.</name>
    </author>
    <author>
      <name>Thomas, Len</name>
    </author>
    <author>
      <name>Martin, Stephen</name>
    </author>
    <author>
      <name>Mellinger, David</name>
    </author>
    <author>
      <name>Ward, Jessica</name>
    </author>
    <author>
      <name>Moretti, David</name>
    </author>
    <author>
      <name>Harris, Danielle Veronica</name>
    </author>
    <author>
      <name>Tyack, Peter Lloyd</name>
    </author>
    <id>http://hdl.handle.net/10023/3496</id>
    <updated>2013-04-26T08:31:02Z</updated>
    <published>2013-05-01T00:00:00Z</published>
    <summary type="text">Abstract: Reliable estimation of the size or density of wild animal populations is very important for effective wildlife management, conservation and ecology. Currently, the most widely used methods for obtaining such estimates involve either sighting animals from transect lines or some form of capture-recapture on marked or uniquely identifiable individuals. However, many species are difficult to sight, and cannot be easily marked or recaptured. Some of these species produce readily identifiable sounds, providing an opportunity to use passive acoustic data to estimate animal density. In addition, even for species for which other visually based methods are feasible, passive acoustic methods offer the potential for greater detection ranges in some environments (e.g. underwater or in dense forest), and hence potentially better precision. Automated data collection means that surveys can take place at times and in places where it would be too expensive or dangerous to send human observers. Here, we present an overview of animal density estimation using passive acoustic data, a relatively new and fast-developing field. We review the types of data and methodological approaches currently available to researchers and we provide a framework for acoustics-based density estimation, illustrated with examples from real-world case studies. We mention moving sensor platforms (e.g. towed acoustics), but then focus on methods involving sensors at fixed locations, particularly hydrophones to survey marine mammals, as acoustic-based density estimation research to date has been concentrated in this area. Primary among these are methods based on distance sampling and spatially explicit capture-recapture. The methods are also applicable to other aquatic and terrestrial sound-producing taxa. We conclude that, despite being in its infancy, density estimation based on passive acoustic data likely will become an important method for surveying a number of diverse taxa, such as sea mammals, fish, birds, amphibians, and insects, especially in situations where inferences are required over long periods of time. There is considerable work ahead, with several potentially fruitful research areas, including the development of (i) hardware and software for data acquisition, (ii) efficient, calibrated, automated detection and classification systems, and (iii) statistical approaches optimized for this application. Further, survey design will need to be developed, and research is needed on the acoustic behaviour of target species. Fundamental research on vocalization rates and group sizes, and the relation between these and other factors such as season or behaviour state, is critical. Evaluation of the methods under known density scenarios will be important for empirically validating the approaches presented here</summary>
    <dc:date>2013-05-01T00:00:00Z</dc:date>
    <dc:creator>Marques, Tiago A.</dc:creator>
    <dc:creator>Thomas, Len</dc:creator>
    <dc:creator>Martin, Stephen</dc:creator>
    <dc:creator>Mellinger, David</dc:creator>
    <dc:creator>Ward, Jessica</dc:creator>
    <dc:creator>Moretti, David</dc:creator>
    <dc:creator>Harris, Danielle Veronica</dc:creator>
    <dc:creator>Tyack, Peter Lloyd</dc:creator>
    <dc:description>Reliable estimation of the size or density of wild animal populations is very important for effective wildlife management, conservation and ecology. Currently, the most widely used methods for obtaining such estimates involve either sighting animals from transect lines or some form of capture-recapture on marked or uniquely identifiable individuals. However, many species are difficult to sight, and cannot be easily marked or recaptured. Some of these species produce readily identifiable sounds, providing an opportunity to use passive acoustic data to estimate animal density. In addition, even for species for which other visually based methods are feasible, passive acoustic methods offer the potential for greater detection ranges in some environments (e.g. underwater or in dense forest), and hence potentially better precision. Automated data collection means that surveys can take place at times and in places where it would be too expensive or dangerous to send human observers. Here, we present an overview of animal density estimation using passive acoustic data, a relatively new and fast-developing field. We review the types of data and methodological approaches currently available to researchers and we provide a framework for acoustics-based density estimation, illustrated with examples from real-world case studies. We mention moving sensor platforms (e.g. towed acoustics), but then focus on methods involving sensors at fixed locations, particularly hydrophones to survey marine mammals, as acoustic-based density estimation research to date has been concentrated in this area. Primary among these are methods based on distance sampling and spatially explicit capture-recapture. The methods are also applicable to other aquatic and terrestrial sound-producing taxa. We conclude that, despite being in its infancy, density estimation based on passive acoustic data likely will become an important method for surveying a number of diverse taxa, such as sea mammals, fish, birds, amphibians, and insects, especially in situations where inferences are required over long periods of time. There is considerable work ahead, with several potentially fruitful research areas, including the development of (i) hardware and software for data acquisition, (ii) efficient, calibrated, automated detection and classification systems, and (iii) statistical approaches optimized for this application. Further, survey design will need to be developed, and research is needed on the acoustic behaviour of target species. Fundamental research on vocalization rates and group sizes, and the relation between these and other factors such as season or behaviour state, is critical. Evaluation of the methods under known density scenarios will be important for empirically validating the approaches presented here</dc:description>
  </entry>
  <entry>
    <title>Decomposition tables for experiments. II. Two–one randomizations</title>
    <link rel="alternate" href="http://hdl.handle.net/10023/3479" />
    <author>
      <name>Brien, C. J.</name>
    </author>
    <author>
      <name>Bailey, R. A.</name>
    </author>
    <id>http://hdl.handle.net/10023/3479</id>
    <updated>2013-04-15T14:01:04Z</updated>
    <published>2010-10-01T00:00:00Z</published>
    <summary type="text">Abstract: We investigate structure for pairs of randomizations that do not follow each other in a chain. These are unrandomized-inclusive, independent, coincident or double randomizations. This involves taking several structures that satisfy particular relations and combining them to form the appropriate orthogonal decomposition of the data space for the experiment. We show how to establish the decomposition table giving the sources of variation, their relationships and their degrees of freedom, so that competing designs can be evaluated. This leads to recommendations for when the different types of multiple randomization should be used.</summary>
    <dc:date>2010-10-01T00:00:00Z</dc:date>
    <dc:creator>Brien, C. J.</dc:creator>
    <dc:creator>Bailey, R. A.</dc:creator>
    <dc:description>We investigate structure for pairs of randomizations that do not follow each other in a chain. These are unrandomized-inclusive, independent, coincident or double randomizations. This involves taking several structures that satisfy particular relations and combining them to form the appropriate orthogonal decomposition of the data space for the experiment. We show how to establish the decomposition table giving the sources of variation, their relationships and their degrees of freedom, so that competing designs can be evaluated. This leads to recommendations for when the different types of multiple randomization should be used.</dc:description>
  </entry>
  <entry>
    <title>Decomposition tables for experiments I. A chain of randomizations</title>
    <link rel="alternate" href="http://hdl.handle.net/10023/3478" />
    <author>
      <name>Brien, C. J.</name>
    </author>
    <author>
      <name>Bailey, R. A.</name>
    </author>
    <id>http://hdl.handle.net/10023/3478</id>
    <updated>2013-04-15T14:01:03Z</updated>
    <published>2009-12-01T00:00:00Z</published>
    <summary type="text">Abstract: One aspect of evaluating the design for an experiment is the discovery of the relationships between subspaces of the data space. Initially we establish the notation and methods for evaluating an experiment with a single randomization. Starting with two structures, or orthogonal decompositions of the data space, we describe how to combine them to form the overall decomposition for a single-randomization experiment that is "structure balanced." The relationships between the two structures are characterized using efficiency factors. The decomposition is encapsulated in a decomposition table. Then, for experiments that involve multiple randomizations forming a chain, we take several structures that pairwise are structure balanced and combine them to establish the form of the orthogonal decomposition for the experiment. In particular, it is proven that the properties of the design for Such an experiment are derived in a straightforward manner from those of the individual designs. We show how to formulate an extended decomposition table giving the sources of variation, their relationships and their degrees of freedom, so that competing designs can be evaluated.</summary>
    <dc:date>2009-12-01T00:00:00Z</dc:date>
    <dc:creator>Brien, C. J.</dc:creator>
    <dc:creator>Bailey, R. A.</dc:creator>
    <dc:description>One aspect of evaluating the design for an experiment is the discovery of the relationships between subspaces of the data space. Initially we establish the notation and methods for evaluating an experiment with a single randomization. Starting with two structures, or orthogonal decompositions of the data space, we describe how to combine them to form the overall decomposition for a single-randomization experiment that is "structure balanced." The relationships between the two structures are characterized using efficiency factors. The decomposition is encapsulated in a decomposition table. Then, for experiments that involve multiple randomizations forming a chain, we take several structures that pairwise are structure balanced and combine them to establish the form of the orthogonal decomposition for the experiment. In particular, it is proven that the properties of the design for Such an experiment are derived in a straightforward manner from those of the individual designs. We show how to formulate an extended decomposition table giving the sources of variation, their relationships and their degrees of freedom, so that competing designs can be evaluated.</dc:description>
  </entry>
  <entry>
    <title>Quantifying biodiversity trends in time and space</title>
    <link rel="alternate" href="http://hdl.handle.net/10023/3414" />
    <author>
      <name>Studeny, Angelika C.</name>
    </author>
    <id>http://hdl.handle.net/10023/3414</id>
    <updated>2013-03-22T09:32:00Z</updated>
    <published>2012-11-30T00:00:00Z</published>
    <summary type="text">Abstract: The global loss of biodiversity calls for robust large-scale diversity assessment. Biological diversity is a multi-faceted concept; defined as the “variety of life”, answering questions such as “How much is there?” or more precisely “Have we succeeded in reducing the rate of its decline?” is not straightforward. While various aspects of biodiversity give rise to numerous ways of quantification, we focus on temporal (and spatial) trends and their changes in species diversity.&#xD;
Traditional diversity indices summarise information contained in the species abundance distribution, i.e. each species' proportional contribution to total abundance. Estimated from data, these indices can be biased if variation in detection probability is ignored. We discuss differences between diversity indices and demonstrate possible adjustments for detectability. &#xD;
Additionally, most indices focus on the most abundant species in ecological communities. We introduce a new set of diversity measures, based on a family of goodness-of-fit statistics. A function of a free parameter, this family allows us to vary the sensitivity of these measures to dominance and rarity of species. &#xD;
Their performance is studied by assessing temporal trends in diversity for five communities of British breeding birds based on 14 years of survey data, where they are applied alongside the current headline index, a geometric mean of relative abundances. Revealing the contributions of both rare and common species to biodiversity trends, these "goodness-of-fit" measures provide novel insights into how ecological communities change over time.&#xD;
Biodiversity is not only subject to temporal changes, but it also varies across space. We take first steps towards estimating spatial diversity trends. Finally, processes maintaining biodiversity act locally, at specific spatial scales. Contrary to abundance-based summary statistics, spatial characteristics of ecological communities may distinguish these processes. We suggest a generalisation to a spatial summary, the cross-pair overlap distribution, to render it more flexible to spatial scale.</summary>
    <dc:date>2012-11-30T00:00:00Z</dc:date>
    <dc:creator>Studeny, Angelika C.</dc:creator>
    <dc:description>The global loss of biodiversity calls for robust large-scale diversity assessment. Biological diversity is a multi-faceted concept; defined as the “variety of life”, answering questions such as “How much is there?” or more precisely “Have we succeeded in reducing the rate of its decline?” is not straightforward. While various aspects of biodiversity give rise to numerous ways of quantification, we focus on temporal (and spatial) trends and their changes in species diversity.&#xD;
Traditional diversity indices summarise information contained in the species abundance distribution, i.e. each species' proportional contribution to total abundance. Estimated from data, these indices can be biased if variation in detection probability is ignored. We discuss differences between diversity indices and demonstrate possible adjustments for detectability. &#xD;
Additionally, most indices focus on the most abundant species in ecological communities. We introduce a new set of diversity measures, based on a family of goodness-of-fit statistics. A function of a free parameter, this family allows us to vary the sensitivity of these measures to dominance and rarity of species. &#xD;
Their performance is studied by assessing temporal trends in diversity for five communities of British breeding birds based on 14 years of survey data, where they are applied alongside the current headline index, a geometric mean of relative abundances. Revealing the contributions of both rare and common species to biodiversity trends, these "goodness-of-fit" measures provide novel insights into how ecological communities change over time.&#xD;
Biodiversity is not only subject to temporal changes, but it also varies across space. We take first steps towards estimating spatial diversity trends. Finally, processes maintaining biodiversity act locally, at specific spatial scales. Contrary to abundance-based summary statistics, spatial characteristics of ecological communities may distinguish these processes. We suggest a generalisation to a spatial summary, the cross-pair overlap distribution, to render it more flexible to spatial scale.</dc:description>
  </entry>
  <entry>
    <title>Finite and infinite ergodic theory for linear and conformal dynamical systems</title>
    <link rel="alternate" href="http://hdl.handle.net/10023/3220" />
    <author>
      <name>Munday, Sara Ann</name>
    </author>
    <id>http://hdl.handle.net/10023/3220</id>
    <updated>2012-10-24T14:10:53Z</updated>
    <published>2011-11-30T00:00:00Z</published>
    <summary type="text">Abstract: The first main topic of this thesis is the thorough analysis of two families of piecewise linear&#xD;
maps on the unit interval, the α-Lüroth and α-Farey maps. Here, α denotes a countably infinite&#xD;
partition of the unit interval whose atoms only accumulate at the origin. The basic properties&#xD;
of these maps will be developed, including that each α-Lüroth map (denoted Lα) gives rise to a&#xD;
series expansion of real numbers in [0,1], a certain type of Generalised Lüroth Series. The first&#xD;
example of such an expansion was given by Lüroth. The map Lα is the jump transformation&#xD;
of the corresponding α-Farey map Fα. The maps Lα and Fα share the same relationship as the&#xD;
classical Farey and Gauss maps which give rise to the continued fraction expansion of a real&#xD;
number. We also consider the topological properties of Fα and some Diophantine-type sets of&#xD;
numbers expressed in terms of the α-Lüroth expansion.&#xD;
Next we investigate certain ergodic-theoretic properties of the maps Lα and Fα. It will turn&#xD;
out that the Lebesgue measure λ is invariant for every map Lα and that there exists a unique&#xD;
Lebesgue-absolutely continuous  invariant measure for Fα. We will give a precise expression for&#xD;
the density of this measure. Our main result is that both Lα and Fα are exact, and thus ergodic.&#xD;
The interest in the invariant measure for Fα lies in the fact that under a particular condition on&#xD;
the underlying partition α, the invariant measure associated to the map Fα is infinite.&#xD;
Then we proceed to introduce and examine the sequence of α-sum-level sets arising from&#xD;
the α-Lüroth map, for an arbitrary given partition α. These sets can be written dynamically in&#xD;
terms of Fα. The main result concerning the α-sum-level sets is to establish weak and strong&#xD;
renewal laws. Note that for the Farey map and the Gauss map, the analogue of this result has&#xD;
been obtained by Kesseböhmer and Stratmann. There the results were derived by using advanced&#xD;
infinite ergodic theory, rather than the strong renewal theorems employed here. This underlines&#xD;
the fact that one of the main ingredients of infinite ergodic theory is provided by some delicate&#xD;
estimates in renewal theory.&#xD;
Our final main result concerning the α-Lüroth and α-Farey systems is to provide a fractal-geometric&#xD;
description of the Lyapunov spectra associated with each of the maps Lα and Fα.&#xD;
The Lyapunov spectra for the Farey map and the Gauss map have been investigated in detail by&#xD;
Kesseböhmer and Stratmann. The Farey map and the Gauss map are non-linear, whereas the&#xD;
systems we consider are always piecewise linear. However, since our analysis is based on a large&#xD;
family of different partitions of U , the class of maps which we consider in this paper allows us&#xD;
to detect a variety of interesting new phenomena, including that of phase transitions.&#xD;
Finally, we come to the conformal systems of the title. These are the limit sets of discrete&#xD;
subgroups of the group of isometries of the hyperbolic plane. For these so-called Fuchsian&#xD;
groups, our first main result is to establish the Hausdorff dimension of some Diophantine-type&#xD;
sets contained in the limit set that are similar to those considered for the maps Lα. These sets&#xD;
are then used in our second main result to analyse the more geometrically defined strict-Jarník&#xD;
limit set of a Fuchsian group. Finally, we obtain a “weak multifractal spectrum” for the Patterson&#xD;
measure associated to the Fuchsian group.</summary>
    <dc:date>2011-11-30T00:00:00Z</dc:date>
    <dc:creator>Munday, Sara Ann</dc:creator>
    <dc:description>The first main topic of this thesis is the thorough analysis of two families of piecewise linear&#xD;
maps on the unit interval, the α-Lüroth and α-Farey maps. Here, α denotes a countably infinite&#xD;
partition of the unit interval whose atoms only accumulate at the origin. The basic properties&#xD;
of these maps will be developed, including that each α-Lüroth map (denoted Lα) gives rise to a&#xD;
series expansion of real numbers in [0,1], a certain type of Generalised Lüroth Series. The first&#xD;
example of such an expansion was given by Lüroth. The map Lα is the jump transformation&#xD;
of the corresponding α-Farey map Fα. The maps Lα and Fα share the same relationship as the&#xD;
classical Farey and Gauss maps which give rise to the continued fraction expansion of a real&#xD;
number. We also consider the topological properties of Fα and some Diophantine-type sets of&#xD;
numbers expressed in terms of the α-Lüroth expansion.&#xD;
Next we investigate certain ergodic-theoretic properties of the maps Lα and Fα. It will turn&#xD;
out that the Lebesgue measure λ is invariant for every map Lα and that there exists a unique&#xD;
Lebesgue-absolutely continuous  invariant measure for Fα. We will give a precise expression for&#xD;
the density of this measure. Our main result is that both Lα and Fα are exact, and thus ergodic.&#xD;
The interest in the invariant measure for Fα lies in the fact that under a particular condition on&#xD;
the underlying partition α, the invariant measure associated to the map Fα is infinite.&#xD;
Then we proceed to introduce and examine the sequence of α-sum-level sets arising from&#xD;
the α-Lüroth map, for an arbitrary given partition α. These sets can be written dynamically in&#xD;
terms of Fα. The main result concerning the α-sum-level sets is to establish weak and strong&#xD;
renewal laws. Note that for the Farey map and the Gauss map, the analogue of this result has&#xD;
been obtained by Kesseböhmer and Stratmann. There the results were derived by using advanced&#xD;
infinite ergodic theory, rather than the strong renewal theorems employed here. This underlines&#xD;
the fact that one of the main ingredients of infinite ergodic theory is provided by some delicate&#xD;
estimates in renewal theory.&#xD;
Our final main result concerning the α-Lüroth and α-Farey systems is to provide a fractal-geometric&#xD;
description of the Lyapunov spectra associated with each of the maps Lα and Fα.&#xD;
The Lyapunov spectra for the Farey map and the Gauss map have been investigated in detail by&#xD;
Kesseböhmer and Stratmann. The Farey map and the Gauss map are non-linear, whereas the&#xD;
systems we consider are always piecewise linear. However, since our analysis is based on a large&#xD;
family of different partitions of U , the class of maps which we consider in this paper allows us&#xD;
to detect a variety of interesting new phenomena, including that of phase transitions.&#xD;
Finally, we come to the conformal systems of the title. These are the limit sets of discrete&#xD;
subgroups of the group of isometries of the hyperbolic plane. For these so-called Fuchsian&#xD;
groups, our first main result is to establish the Hausdorff dimension of some Diophantine-type&#xD;
sets contained in the limit set that are similar to those considered for the maps Lα. These sets&#xD;
are then used in our second main result to analyse the more geometrically defined strict-Jarník&#xD;
limit set of a Fuchsian group. Finally, we obtain a “weak multifractal spectrum” for the Patterson&#xD;
measure associated to the Fuchsian group.</dc:description>
  </entry>
  <entry>
    <title>Workshop on new developments in cetacean survey methods</title>
    <link rel="alternate" href="http://hdl.handle.net/10023/3216" />
    <author>
      <name>Borchers, David Louis</name>
    </author>
    <author>
      <name>Thomas, Len</name>
    </author>
    <author>
      <name>Buckland, Stephen Terrence</name>
    </author>
    <author>
      <name>Skaug, Hans</name>
    </author>
    <author>
      <name>Barlow, Jay</name>
    </author>
    <id>http://hdl.handle.net/10023/3216</id>
    <updated>2012-12-12T10:20:18Z</updated>
    <published>2011-01-01T00:00:00Z</published>
    <summary type="text">Abstract: This report contains the slides from a workshop on New Developments in Cetacean Survey Methods held on 27th November 2011 at the 19th Biennial Conference on the Biology of Marine Mammals, Tampa, Florida. Review talks were given on Passive Acoustic Density Estimation (Len Thomas); Dealing with g(0)&lt;1: Perception Bias (Stephen Buckland); Dealing with g(0)&lt;1: Availability Bias (Hans Skaug); Dealing with Measurement Error (David Borchers); and Density Surface Modelling (Jay Barlow). The sessions were followed by a discussion, and this is summarized at the end of the report.</summary>
    <dc:date>2011-01-01T00:00:00Z</dc:date>
    <dc:creator>Borchers, David Louis</dc:creator>
    <dc:creator>Thomas, Len</dc:creator>
    <dc:creator>Buckland, Stephen Terrence</dc:creator>
    <dc:creator>Skaug, Hans</dc:creator>
    <dc:creator>Barlow, Jay</dc:creator>
    <dc:description>This report contains the slides from a workshop on New Developments in Cetacean Survey Methods held on 27th November 2011 at the 19th Biennial Conference on the Biology of Marine Mammals, Tampa, Florida. Review talks were given on Passive Acoustic Density Estimation (Len Thomas); Dealing with g(0)&lt;1: Perception Bias (Stephen Buckland); Dealing with g(0)&lt;1: Availability Bias (Hans Skaug); Dealing with Measurement Error (David Borchers); and Density Surface Modelling (Jay Barlow). The sessions were followed by a discussion, and this is summarized at the end of the report.</dc:description>
  </entry>
  <entry>
    <title>Spatial patterns and species coexistence : using spatial statistics to identify underlying ecological processes in plant communities</title>
    <link rel="alternate" href="http://hdl.handle.net/10023/3084" />
    <author>
      <name>Brown, Calum</name>
    </author>
    <id>http://hdl.handle.net/10023/3084</id>
    <updated>2012-10-24T11:38:02Z</updated>
    <published>2012-11-01T00:00:00Z</published>
    <summary type="text">Abstract: The use of spatial statistics to investigate ecological processes in plant communities is becoming increasingly widespread.  In diverse communities such as tropical rainforests, analysis of spatial structure may help to unravel the various processes that act and interact to maintain high levels of diversity.  In particular, a number of contrasting mechanisms have been suggested to explain species coexistence, and these differ greatly in their practical implications for the ecology and conservation of tropical forests.  Traditional first-order measures of community structure have proved unable to distinguish these mechanisms in practice, but statistics that describe spatial structure may be able to do so.  This is of great interest and relevance as spatially explicit data become available for a range of ecological communities and analysis methods for these data become more accessible.&#xD;
This thesis investigates the potential for inference about underlying ecological processes in plant communities using spatial statistics.  Current methodologies for spatial analysis are reviewed and extended, and are used to characterise the spatial signals of the principal theorised mechanisms of coexistence.  The sensitivity of a range of spatial statistics to these signals is assessed, and the strength of such signals in natural communities is investigated.     &#xD;
The spatial signals of the processes considered here are found to be strong and robust to modelled stochastic variation.  Several new and existing spatial statistics are found to be sensitive to these signals, and offer great promise for inference about underlying processes from empirical data.  The relative strengths of particular processes are found to vary between natural communities, with any one theory being insufficient to explain observed patterns.  This thesis extends both understanding of species coexistence in diverse plant communities and the methodology for assessing underlying process in particular cases.  It demonstrates that the potential of spatial statistics in ecology is great and largely unexplored.</summary>
    <dc:date>2012-11-01T00:00:00Z</dc:date>
    <dc:creator>Brown, Calum</dc:creator>
    <dc:description>The use of spatial statistics to investigate ecological processes in plant communities is becoming increasingly widespread.  In diverse communities such as tropical rainforests, analysis of spatial structure may help to unravel the various processes that act and interact to maintain high levels of diversity.  In particular, a number of contrasting mechanisms have been suggested to explain species coexistence, and these differ greatly in their practical implications for the ecology and conservation of tropical forests.  Traditional first-order measures of community structure have proved unable to distinguish these mechanisms in practice, but statistics that describe spatial structure may be able to do so.  This is of great interest and relevance as spatially explicit data become available for a range of ecological communities and analysis methods for these data become more accessible.&#xD;
This thesis investigates the potential for inference about underlying ecological processes in plant communities using spatial statistics.  Current methodologies for spatial analysis are reviewed and extended, and are used to characterise the spatial signals of the principal theorised mechanisms of coexistence.  The sensitivity of a range of spatial statistics to these signals is assessed, and the strength of such signals in natural communities is investigated.     &#xD;
The spatial signals of the processes considered here are found to be strong and robust to modelled stochastic variation.  Several new and existing spatial statistics are found to be sensitive to these signals, and offer great promise for inference about underlying processes from empirical data.  The relative strengths of particular processes are found to vary between natural communities, with any one theory being insufficient to explain observed patterns.  This thesis extends both understanding of species coexistence in diverse plant communities and the methodology for assessing underlying process in particular cases.  It demonstrates that the potential of spatial statistics in ecology is great and largely unexplored.</dc:description>
  </entry>
  <entry>
    <title>Vessel noise affects beaked whale behavior : Results of a dedicated acoustic response study</title>
    <link rel="alternate" href="http://hdl.handle.net/10023/3078" />
    <author>
      <name>Pirotta, Enrico</name>
    </author>
    <author>
      <name>Milor, Rachel</name>
    </author>
    <author>
      <name>Quick, Nicola Jane</name>
    </author>
    <author>
      <name>Moretti, David</name>
    </author>
    <author>
      <name>Dimarzio, Nancy</name>
    </author>
    <author>
      <name>Tyack, Peter Lloyd</name>
    </author>
    <author>
      <name>Boyd, Ian</name>
    </author>
    <author>
      <name>Hastie, Gordon Drummond</name>
    </author>
    <id>http://hdl.handle.net/10023/3078</id>
    <updated>2013-05-12T04:35:54Z</updated>
    <published>2012-08-03T00:00:00Z</published>
    <summary type="text">Abstract: Some beaked whale species are susceptible to the detrimental effects of anthropogenic noise. Most studies have concentrated on the effects of military sonar, but other forms of acoustic disturbance (e.g. shipping noise) may disrupt behavior. An experiment involving the exposure of target whale groups to intense vessel-generated noise tested how these exposures influenced the foraging behavior of Blainville’s beaked whales (Mesoplodon densirostris) in the Tongue of the Ocean (Bahamas). A military array of bottom-mounted hydrophones was used to measure the response based upon changes in the spatial and temporal pattern of vocalizations. The archived acoustic data were used to compute metrics the echolocation-based foraging behavior for 16 targeted groups, 10 groups further away on the range, and 26 nonexposed groups. The duration of foraging bouts was not significantly affected by the exposure. Changes in the hydrophone over which the group was most frequently detected occurred as the animals moved around within a foraging bout, and their number was significantly less the closer the whales were to the sound source. Non-exposed groups also had significantly more changes in the primary hydrophone than exposed groups irrespective of distance. Our results suggested that broadband ship noise caused a significant change in beaked whale behavior up to at least 5.2 kilometers away from the vessel. The observed change could potentially correspond to a restriction in the movement of groups, a period of more directional travel, a reduction in the number of individuals clicking within the group, or a response to changes in prey movement.</summary>
    <dc:date>2012-08-03T00:00:00Z</dc:date>
    <dc:creator>Pirotta, Enrico</dc:creator>
    <dc:creator>Milor, Rachel</dc:creator>
    <dc:creator>Quick, Nicola Jane</dc:creator>
    <dc:creator>Moretti, David</dc:creator>
    <dc:creator>Dimarzio, Nancy</dc:creator>
    <dc:creator>Tyack, Peter Lloyd</dc:creator>
    <dc:creator>Boyd, Ian</dc:creator>
    <dc:creator>Hastie, Gordon Drummond</dc:creator>
    <dc:description>Some beaked whale species are susceptible to the detrimental effects of anthropogenic noise. Most studies have concentrated on the effects of military sonar, but other forms of acoustic disturbance (e.g. shipping noise) may disrupt behavior. An experiment involving the exposure of target whale groups to intense vessel-generated noise tested how these exposures influenced the foraging behavior of Blainville’s beaked whales (Mesoplodon densirostris) in the Tongue of the Ocean (Bahamas). A military array of bottom-mounted hydrophones was used to measure the response based upon changes in the spatial and temporal pattern of vocalizations. The archived acoustic data were used to compute metrics the echolocation-based foraging behavior for 16 targeted groups, 10 groups further away on the range, and 26 nonexposed groups. The duration of foraging bouts was not significantly affected by the exposure. Changes in the hydrophone over which the group was most frequently detected occurred as the animals moved around within a foraging bout, and their number was significantly less the closer the whales were to the sound source. Non-exposed groups also had significantly more changes in the primary hydrophone than exposed groups irrespective of distance. Our results suggested that broadband ship noise caused a significant change in beaked whale behavior up to at least 5.2 kilometers away from the vessel. The observed change could potentially correspond to a restriction in the movement of groups, a period of more directional travel, a reduction in the number of individuals clicking within the group, or a response to changes in prey movement.</dc:description>
  </entry>
  <entry>
    <title>Global analysis of cetacean line-transect surveys : detecting trends in cetacean density</title>
    <link rel="alternate" href="http://hdl.handle.net/10023/2747" />
    <author>
      <name>Jewell, Rebecca Lucy</name>
    </author>
    <author>
      <name>Thomas, Len</name>
    </author>
    <author>
      <name>Harris, Catriona M</name>
    </author>
    <author>
      <name>Kaschner, Kristin</name>
    </author>
    <author>
      <name>Wiff, Rodrigo Alexis</name>
    </author>
    <author>
      <name>Hammond, Philip Steven</name>
    </author>
    <author>
      <name>Quick, Nicola Jane</name>
    </author>
    <id>http://hdl.handle.net/10023/2747</id>
    <updated>2013-05-12T04:14:22Z</updated>
    <published>2012-05-07T00:00:00Z</published>
    <summary type="text">Abstract: Measuring the effect of anthropogenic change on cetacean populations is hampered by our lack of understanding about population status and a lack of power in the available data to detect trends in abundance. Often long-term data from repeated surveys are lacking, and alternative approaches to trend detection must be considered. We utilised an existing database of line transect survey records to determine whether temporal trends could be detected when survey effort from around the world was combined. We extracted density estimates for 25 species and fitted generalised additive models (GAMs) to investigate whether taxonomic, spatial or methodological differences among systematic line-transect surveys affect estimates of density and whether we can identify temporal trends in the data once these factors are accounted for. The selected GAM consisted of 2 parts: an intercept term that was a complex interaction of taxonomic, spatial and methodological factors and a smooth temporal term with trends varying by family and ocean basin. We discuss the trends found and assess the suitability of published density estimates for detecting temporal trends using retrospective power analysis. In conclusion, increasing sample size through combining survey effort across a global scale does not necessarily result in sufficient power to detect trends because of the extent of variability across surveys, species and oceans. Instead, results from repeated dedicated surveys designed specifically for the species and geographical region of interest should be used to inform conservation and management.</summary>
    <dc:date>2012-05-07T00:00:00Z</dc:date>
    <dc:creator>Jewell, Rebecca Lucy</dc:creator>
    <dc:creator>Thomas, Len</dc:creator>
    <dc:creator>Harris, Catriona M</dc:creator>
    <dc:creator>Kaschner, Kristin</dc:creator>
    <dc:creator>Wiff, Rodrigo Alexis</dc:creator>
    <dc:creator>Hammond, Philip Steven</dc:creator>
    <dc:creator>Quick, Nicola Jane</dc:creator>
    <dc:description>Measuring the effect of anthropogenic change on cetacean populations is hampered by our lack of understanding about population status and a lack of power in the available data to detect trends in abundance. Often long-term data from repeated surveys are lacking, and alternative approaches to trend detection must be considered. We utilised an existing database of line transect survey records to determine whether temporal trends could be detected when survey effort from around the world was combined. We extracted density estimates for 25 species and fitted generalised additive models (GAMs) to investigate whether taxonomic, spatial or methodological differences among systematic line-transect surveys affect estimates of density and whether we can identify temporal trends in the data once these factors are accounted for. The selected GAM consisted of 2 parts: an intercept term that was a complex interaction of taxonomic, spatial and methodological factors and a smooth temporal term with trends varying by family and ocean basin. We discuss the trends found and assess the suitability of published density estimates for detecting temporal trends using retrospective power analysis. In conclusion, increasing sample size through combining survey effort across a global scale does not necessarily result in sufficient power to detect trends because of the extent of variability across surveys, species and oceans. Instead, results from repeated dedicated surveys designed specifically for the species and geographical region of interest should be used to inform conservation and management.</dc:description>
  </entry>
  <entry>
    <title>A critical review of the literature on population modelling</title>
    <link rel="alternate" href="http://hdl.handle.net/10023/2241" />
    <author>
      <name>Cabrelli, Abigail</name>
    </author>
    <author>
      <name>Harwood, John</name>
    </author>
    <author>
      <name>Matthiopoulos, Jason</name>
    </author>
    <author>
      <name>New, Leslie Frances</name>
    </author>
    <author>
      <name>Thomas, Len</name>
    </author>
    <id>http://hdl.handle.net/10023/2241</id>
    <updated>2012-12-12T10:19:28Z</updated>
    <published>2009-01-01T00:00:00Z</published>
    <summary type="text">Abstract: The 2005 report of the National Research Council’s ‘Committee on Characterizing Biologically Significant Marine Mammal Behavior’ proposed a framework, which they called PCAD - Population Consequences of Acoustic Disturbance, that uses a series of transfer functions to link behavioural responses to sound with life functions, vital rates, and population change. The Committee suggested that the best understood transfer functions are those linking vital rates to population change. One of the main aims of this report is to document that understanding. However, we also show how the existing frameworks for modelling the dynamics of marine mammal populations can be extended to include the effects of behavioural responses on vital rates. In Chapter 1 we introduce the central concept of the rate of increase (lambda) of a population, which we believe is the most useful measure of the effects of behavioural responses on the dynamics of a population. If the value of lambda exceeds one, then thepopulation will increase over time; if it is less than one it will decrease. We show how changes in lambda provide a measure of the impact of human activities (such as exploitation, conservation, or disturbance) on a population. We also introduce structured population models, which take account of the fact that all individuals in a population are not identical, and show how the dynamics of different parts of a population can be modelled using a population projection matrix. The mathematical properties of this projection matrix can be used to determine the sensitivity of lambda to small changes in vital rates. Finally, we provide a very brief introduction to the concept of stochasticity, and the use of lambda to predict when (and if) a population might be driven to extinction. Chapter 2 describes how lambda also provides a measure of the Darwinian fitness of the individual members of a population. An individual’s fitness, the contribution it will make to future generations, depends to a large extent on its body condition and on the risks of mortality to which it is exposed. Both of these could be affected by behaviour responses to sound. We also explain current theories about the relationship between an individual’s feeding behaviour and the abundance and distribution of prey, and how this can affect body condition. Chapter 3 provides a more detailed description of how elasticity analysis can be used to investigate the impact of changes in vital rates on lambda . Elasticity analysis is a useful tool for detecting which vital rates are most important in determining the dynamics of a population. However, its value is limited because it does not take account of random variations (stochasticity) and, in theory, it can only predict the effect of small changes in vital rates. Chapter 4 describes the fundamental concept of density dependence: the way in which vital rates change with population size or the availability of resources, such as prey. Not only is density dependence an essential prerequisite for population stability and sustainable use, but the form it takes will also determine how a population responds to behavioural changes. This is because behaviour, and particularly the effect of behavioural change on body condition, plays a central role in many of the mechanistic models of density dependence. Chapters 5 and 6 explore the way in which additional complexities, such as social structure and the way in which populations are distributed in space, can affect the dynamics of populations. Models that account for these complexities behave in a much less predictable way than the relatively simple structured models that form the core of Chapters 1-4. So far, the models of population dynamics that we have reviewed have been deterministic. That is, they have assumed that the only way in which vital rates can vary is in response to a change in abundance, via density dependent mechanisms. In Chapters 7 and 8 we investigate the effect of random variation (stochasticity) on population dynamics. We distinguish the effects of demographic stochasticity, chance variations in the number of animals that die or give birth in a time interval that occur even if vital rates do not vary over time, and environmental stochasticity, which is the result of variations in vital rates across years. Variation in abundance may also occur as a result of environmental change and changes in the ecological community of which a population is a part. The effect of all these sources of variation is to reduce the realised growth rate of a population, and therefore its risk of extinction. In Chapter 9 we consider how the basic population modelling framework described in Chapters 1-8 might be extended to take account of the life functions identified by the NRC Committee. We suggest that these life functions are useful for defining the context in which behavioural responses might affect vital rates, but that they do not need to be modelled explicitly. Removing vital functions from the PCAD framework results in a much simpler structure, which is compatible with existing population modelling frameworks. However, these will have to be extended to allow population states, like body condition, that vary continuously to be modelled. Chapter 10 describes how changes in lambda can be detected. The simple analytical frameworks that are available for this are all vulnerable to the effects of variability that we introduced in Chapter 7. However, there is a framework (state-space and hidden Markov process modelling) that can account for the effects of this variability, and we recommend its use for detecting trends. The additional benefit of this approach is that its use results in a detailed model of the dynamics of the population that is under investigation. Chapter 11 reviews the different model structures that can be used to describe the dynamics of a population, and explains when different forms of population models (e.g. discrete vs. continuous time, deterministic vs. stochastic) are most appropriate. We also discuss how these different frameworks can be extended to account for continuous population states, as recommended in Chapter 8. The final focus is on how state-space models can be fitted to time series of abundance estimates and information on vital rates. Chapter 12 looks at the relevance of the different modelling approaches described in the previous chapters for analysing the potential effects of behavioural responses to sound on population dynamics, particularly the kinds of sounds that may be generated by the oil and gas industry. We conclude that lambda , the population rate of increase, and its variation provides a useful measure of these effects. We also believe that the models used for this purpose will certainly have to account for the effects of variability and density dependence. They will probably also have to account for the effects of social structure and the way in which populations use space. The state-space modelling framework outlined in Chapter 11 can, in principle, be extended to capture all of these features although work on this is still in its infancy.
Description: Final Report to the Joint Industry Project of the International Association of Oil &amp; Gas Producers on contract JIP22 07_20</summary>
    <dc:date>2009-01-01T00:00:00Z</dc:date>
    <dc:creator>Cabrelli, Abigail</dc:creator>
    <dc:creator>Harwood, John</dc:creator>
    <dc:creator>Matthiopoulos, Jason</dc:creator>
    <dc:creator>New, Leslie Frances</dc:creator>
    <dc:creator>Thomas, Len</dc:creator>
    <dc:description>The 2005 report of the National Research Council’s ‘Committee on Characterizing Biologically Significant Marine Mammal Behavior’ proposed a framework, which they called PCAD - Population Consequences of Acoustic Disturbance, that uses a series of transfer functions to link behavioural responses to sound with life functions, vital rates, and population change. The Committee suggested that the best understood transfer functions are those linking vital rates to population change. One of the main aims of this report is to document that understanding. However, we also show how the existing frameworks for modelling the dynamics of marine mammal populations can be extended to include the effects of behavioural responses on vital rates. In Chapter 1 we introduce the central concept of the rate of increase (lambda) of a population, which we believe is the most useful measure of the effects of behavioural responses on the dynamics of a population. If the value of lambda exceeds one, then thepopulation will increase over time; if it is less than one it will decrease. We show how changes in lambda provide a measure of the impact of human activities (such as exploitation, conservation, or disturbance) on a population. We also introduce structured population models, which take account of the fact that all individuals in a population are not identical, and show how the dynamics of different parts of a population can be modelled using a population projection matrix. The mathematical properties of this projection matrix can be used to determine the sensitivity of lambda to small changes in vital rates. Finally, we provide a very brief introduction to the concept of stochasticity, and the use of lambda to predict when (and if) a population might be driven to extinction. Chapter 2 describes how lambda also provides a measure of the Darwinian fitness of the individual members of a population. An individual’s fitness, the contribution it will make to future generations, depends to a large extent on its body condition and on the risks of mortality to which it is exposed. Both of these could be affected by behaviour responses to sound. We also explain current theories about the relationship between an individual’s feeding behaviour and the abundance and distribution of prey, and how this can affect body condition. Chapter 3 provides a more detailed description of how elasticity analysis can be used to investigate the impact of changes in vital rates on lambda . Elasticity analysis is a useful tool for detecting which vital rates are most important in determining the dynamics of a population. However, its value is limited because it does not take account of random variations (stochasticity) and, in theory, it can only predict the effect of small changes in vital rates. Chapter 4 describes the fundamental concept of density dependence: the way in which vital rates change with population size or the availability of resources, such as prey. Not only is density dependence an essential prerequisite for population stability and sustainable use, but the form it takes will also determine how a population responds to behavioural changes. This is because behaviour, and particularly the effect of behavioural change on body condition, plays a central role in many of the mechanistic models of density dependence. Chapters 5 and 6 explore the way in which additional complexities, such as social structure and the way in which populations are distributed in space, can affect the dynamics of populations. Models that account for these complexities behave in a much less predictable way than the relatively simple structured models that form the core of Chapters 1-4. So far, the models of population dynamics that we have reviewed have been deterministic. That is, they have assumed that the only way in which vital rates can vary is in response to a change in abundance, via density dependent mechanisms. In Chapters 7 and 8 we investigate the effect of random variation (stochasticity) on population dynamics. We distinguish the effects of demographic stochasticity, chance variations in the number of animals that die or give birth in a time interval that occur even if vital rates do not vary over time, and environmental stochasticity, which is the result of variations in vital rates across years. Variation in abundance may also occur as a result of environmental change and changes in the ecological community of which a population is a part. The effect of all these sources of variation is to reduce the realised growth rate of a population, and therefore its risk of extinction. In Chapter 9 we consider how the basic population modelling framework described in Chapters 1-8 might be extended to take account of the life functions identified by the NRC Committee. We suggest that these life functions are useful for defining the context in which behavioural responses might affect vital rates, but that they do not need to be modelled explicitly. Removing vital functions from the PCAD framework results in a much simpler structure, which is compatible with existing population modelling frameworks. However, these will have to be extended to allow population states, like body condition, that vary continuously to be modelled. Chapter 10 describes how changes in lambda can be detected. The simple analytical frameworks that are available for this are all vulnerable to the effects of variability that we introduced in Chapter 7. However, there is a framework (state-space and hidden Markov process modelling) that can account for the effects of this variability, and we recommend its use for detecting trends. The additional benefit of this approach is that its use results in a detailed model of the dynamics of the population that is under investigation. Chapter 11 reviews the different model structures that can be used to describe the dynamics of a population, and explains when different forms of population models (e.g. discrete vs. continuous time, deterministic vs. stochastic) are most appropriate. We also discuss how these different frameworks can be extended to account for continuous population states, as recommended in Chapter 8. The final focus is on how state-space models can be fitted to time series of abundance estimates and information on vital rates. Chapter 12 looks at the relevance of the different modelling approaches described in the previous chapters for analysing the potential effects of behavioural responses to sound on population dynamics, particularly the kinds of sounds that may be generated by the oil and gas industry. We conclude that lambda , the population rate of increase, and its variation provides a useful measure of these effects. We also believe that the models used for this purpose will certainly have to account for the effects of variability and density dependence. They will probably also have to account for the effects of social structure and the way in which populations use space. The state-space modelling framework outlined in Chapter 11 can, in principle, be extended to capture all of these features although work on this is still in its infancy.</dc:description>
  </entry>
  <entry>
    <title>An update to the methods in Endangered Species Research 2011 paper "Estimating North Pacific right whale Eubalaena japonica density using passive acoustic cue counting"</title>
    <link rel="alternate" href="http://hdl.handle.net/10023/2158" />
    <author>
      <name>Marques, Tiago A.</name>
    </author>
    <author>
      <name>Munger, Lisa</name>
    </author>
    <author>
      <name>Thomas, Len</name>
    </author>
    <author>
      <name>Wiggins, Sean</name>
    </author>
    <author>
      <name>Hildebrand, John</name>
    </author>
    <id>http://hdl.handle.net/10023/2158</id>
    <updated>2012-12-12T10:19:25Z</updated>
    <published>2012-01-01T00:00:00Z</published>
    <dc:date>2012-01-01T00:00:00Z</dc:date>
    <dc:creator>Marques, Tiago A.</dc:creator>
    <dc:creator>Munger, Lisa</dc:creator>
    <dc:creator>Thomas, Len</dc:creator>
    <dc:creator>Wiggins, Sean</dc:creator>
    <dc:creator>Hildebrand, John</dc:creator>
  </entry>
  <entry>
    <title>Estimating abundance of rare, small mammals: A case study of the Key Largo woodrat (Neotoma floridana smalli)</title>
    <link rel="alternate" href="http://hdl.handle.net/10023/2068" />
    <author>
      <name>Potts, Joanne M.</name>
    </author>
    <id>http://hdl.handle.net/10023/2068</id>
    <updated>2013-04-15T12:04:48Z</updated>
    <published>2011-01-01T00:00:00Z</published>
    <summary type="text">Abstract: Estimates of animal abundance or density are fundamental quantities in ecology and conservation, but for many species such as rare, small mammals, obtaining robust estimates is problematic. In this thesis, I combine elements of two standard abundance estimation methods, capture-recapture and distance sampling, to develop a method called trapping point transects (TPT). In TPT, a "detection function", g(r) (i.e. the probability of capturing an animal, given it is r m from a trap when the trap is set) is estimated using a subset of animals whose locations are known prior to traps being set. Generalised linear models are used to estimate the detection function, and the model can be extended to include random effects to allow for heterogeneity in capture probabilities. Standard point transect methods are modified to estimate abundance. Two abundance estimators are available. The first estimator is based on the reciprocal of the expected probability of detecting an animal, ^P, where the expectation is over r;&#xD;
whereas the second estimator is the expectation of the reciprocal of ^P.&#xD;
Performance of the TPT method under various sampling efforts and underlying true detection probabilities of individuals in the population was investigated in a simulation study. When underlying probability of detection was high (g(0) = 0:88) and between-individual variation was small, survey effort could be surprisingly low (c. 510 trap nights) to yield low bias (c. 4%) in the two estimators;&#xD;
but under certain situations, the second estimator can be extremely biased. Uncertainty and relative bias in population estimates increased with decreasing detectability and increasing between-individual variation.&#xD;
Abundance of the Key Largo woodrat (Neotoma floridana smalli), an endangered rodent with a restricted geographic range, was estimated using TPT. The TPT method compared well to other viable methods (capture-recapture and spatially-explicit capture-recapture), in terms of both field practicality and cost. The TPT method may generally be useful in estimating animal abundance in trapping studies and variants of the TPT method are presented.</summary>
    <dc:date>2011-01-01T00:00:00Z</dc:date>
    <dc:creator>Potts, Joanne M.</dc:creator>
    <dc:description>Estimates of animal abundance or density are fundamental quantities in ecology and conservation, but for many species such as rare, small mammals, obtaining robust estimates is problematic. In this thesis, I combine elements of two standard abundance estimation methods, capture-recapture and distance sampling, to develop a method called trapping point transects (TPT). In TPT, a "detection function", g(r) (i.e. the probability of capturing an animal, given it is r m from a trap when the trap is set) is estimated using a subset of animals whose locations are known prior to traps being set. Generalised linear models are used to estimate the detection function, and the model can be extended to include random effects to allow for heterogeneity in capture probabilities. Standard point transect methods are modified to estimate abundance. Two abundance estimators are available. The first estimator is based on the reciprocal of the expected probability of detecting an animal, ^P, where the expectation is over r;&#xD;
whereas the second estimator is the expectation of the reciprocal of ^P.&#xD;
Performance of the TPT method under various sampling efforts and underlying true detection probabilities of individuals in the population was investigated in a simulation study. When underlying probability of detection was high (g(0) = 0:88) and between-individual variation was small, survey effort could be surprisingly low (c. 510 trap nights) to yield low bias (c. 4%) in the two estimators;&#xD;
but under certain situations, the second estimator can be extremely biased. Uncertainty and relative bias in population estimates increased with decreasing detectability and increasing between-individual variation.&#xD;
Abundance of the Key Largo woodrat (Neotoma floridana smalli), an endangered rodent with a restricted geographic range, was estimated using TPT. The TPT method compared well to other viable methods (capture-recapture and spatially-explicit capture-recapture), in terms of both field practicality and cost. The TPT method may generally be useful in estimating animal abundance in trapping studies and variants of the TPT method are presented.</dc:description>
  </entry>
  <entry>
    <title>Complex Region Spatial Smoother (CReSS)</title>
    <link rel="alternate" href="http://hdl.handle.net/10023/2048" />
    <author>
      <name>Scott Hayward, Lindesay Alexandra Sarah</name>
    </author>
    <author>
      <name>MacKenzie, Monique Lea</name>
    </author>
    <author>
      <name>Donovan, Carl Robert</name>
    </author>
    <author>
      <name>Walker, Cameron</name>
    </author>
    <author>
      <name>Ashe, Erin</name>
    </author>
    <id>http://hdl.handle.net/10023/2048</id>
    <updated>2012-12-12T10:18:54Z</updated>
    <published>2011-01-01T00:00:00Z</published>
    <summary type="text">Abstract: Conventional smoothing over complicated coastal and island regions may result in errors across boundaries, due to the use of Euclidean distances to represent inter-point similarity. The new Complex Region Spatial Smoother (CReSS) method presented here, uses estimated geodesic distances, model averaging and a local radial basis function to provide improved smoothing over complex domains. CReSS is compared, via simulation, to recent related smoothing techniques, Thin Plate Splines (TPS, Harder and Desmarais, 1972), geodesic low rank TPS [Wang and Ranalli, 2007] and the Soap film smoother [Wood et al., 2008]. The GLTPS method cannot be used in areas with islands and SOAP can be hard to parameterize. CReSS is comparable with, if not better than, all considered methods on a range of simulations. Supplementary materials for this article are available online.</summary>
    <dc:date>2011-01-01T00:00:00Z</dc:date>
    <dc:creator>Scott Hayward, Lindesay Alexandra Sarah</dc:creator>
    <dc:creator>MacKenzie, Monique Lea</dc:creator>
    <dc:creator>Donovan, Carl Robert</dc:creator>
    <dc:creator>Walker, Cameron</dc:creator>
    <dc:creator>Ashe, Erin</dc:creator>
    <dc:description>Conventional smoothing over complicated coastal and island regions may result in errors across boundaries, due to the use of Euclidean distances to represent inter-point similarity. The new Complex Region Spatial Smoother (CReSS) method presented here, uses estimated geodesic distances, model averaging and a local radial basis function to provide improved smoothing over complex domains. CReSS is compared, via simulation, to recent related smoothing techniques, Thin Plate Splines (TPS, Harder and Desmarais, 1972), geodesic low rank TPS [Wang and Ranalli, 2007] and the Soap film smoother [Wood et al., 2008]. The GLTPS method cannot be used in areas with islands and SOAP can be hard to parameterize. CReSS is comparable with, if not better than, all considered methods on a range of simulations. Supplementary materials for this article are available online.</dc:description>
  </entry>
  <entry>
    <title>Bayesian modelling of integrated data and its application to seabird populations</title>
    <link rel="alternate" href="http://hdl.handle.net/10023/1635" />
    <author>
      <name>Reynolds, Toby J.</name>
    </author>
    <id>http://hdl.handle.net/10023/1635</id>
    <updated>2010-12-13T16:48:23Z</updated>
    <published>2010-11-30T00:00:00Z</published>
    <summary type="text">Abstract: Integrated data analyses are becoming increasingly popular in studies of wild animal populations where two or more separate sources of data contain information about common parameters. Here we develop an integrated population model using abundance and demographic data from a study of common guillemots (Uria aalge) on the Isle of May, southeast Scotland. A state-space model for the count data is supplemented by three demographic time series (productivity and two mark-recapture-recovery (MRR)), enabling the estimation of prebreeder emigration rate - a parameter for which there is no direct observational data, and which is unidentifiable in the separate analysis of MRR data. A Bayesian approach using MCMC provides a flexible and powerful analysis framework.&#xD;
&#xD;
This model is extended to provide predictions of future population trajectories. Adopting random effects models for the survival and productivity parameters, we implement the MCMC algorithm to obtain a posterior sample of the underlying process means and variances (and population sizes) within the study period. Given this sample, we predict future demographic parameters, which in turn allows us to predict future population sizes and obtain the corresponding posterior distribution. Under the assumption that recent, unfavourable conditions persist in the future, we obtain a posterior probability of 70% that there is a population decline of &gt;25% over a 10-year period.&#xD;
&#xD;
Lastly, using MRR data we test for spatial, temporal and age-related correlations in guillemot survival among three widely separated Scottish colonies that have varying overlap in nonbreeding distribution. We show that survival is highly correlated over time for colonies/age classes sharing wintering areas, and essentially uncorrelated for those with separate wintering areas. These results strongly suggest that one or more aspects of winter environment are responsible for spatiotemporal variation in survival of British guillemots, and provide insight into the factors driving multi-population dynamics of the species.</summary>
    <dc:date>2010-11-30T00:00:00Z</dc:date>
    <dc:creator>Reynolds, Toby J.</dc:creator>
    <dc:description>Integrated data analyses are becoming increasingly popular in studies of wild animal populations where two or more separate sources of data contain information about common parameters. Here we develop an integrated population model using abundance and demographic data from a study of common guillemots (Uria aalge) on the Isle of May, southeast Scotland. A state-space model for the count data is supplemented by three demographic time series (productivity and two mark-recapture-recovery (MRR)), enabling the estimation of prebreeder emigration rate - a parameter for which there is no direct observational data, and which is unidentifiable in the separate analysis of MRR data. A Bayesian approach using MCMC provides a flexible and powerful analysis framework.&#xD;
&#xD;
This model is extended to provide predictions of future population trajectories. Adopting random effects models for the survival and productivity parameters, we implement the MCMC algorithm to obtain a posterior sample of the underlying process means and variances (and population sizes) within the study period. Given this sample, we predict future demographic parameters, which in turn allows us to predict future population sizes and obtain the corresponding posterior distribution. Under the assumption that recent, unfavourable conditions persist in the future, we obtain a posterior probability of 70% that there is a population decline of &gt;25% over a 10-year period.&#xD;
&#xD;
Lastly, using MRR data we test for spatial, temporal and age-related correlations in guillemot survival among three widely separated Scottish colonies that have varying overlap in nonbreeding distribution. We show that survival is highly correlated over time for colonies/age classes sharing wintering areas, and essentially uncorrelated for those with separate wintering areas. These results strongly suggest that one or more aspects of winter environment are responsible for spatiotemporal variation in survival of British guillemots, and provide insight into the factors driving multi-population dynamics of the species.</dc:description>
  </entry>
  <entry>
    <title>Statistical models for the long-term monitoring of songbird populations: a Bayesian analysis of constant effort sites and ring-recovery data</title>
    <link rel="alternate" href="http://hdl.handle.net/10023/885" />
    <author>
      <name>Cave, Vanessa M.</name>
    </author>
    <id>http://hdl.handle.net/10023/885</id>
    <updated>2010-12-13T16:13:06Z</updated>
    <published>2010-06-25T00:00:00Z</published>
    <summary type="text">Abstract: To underpin and improve advice given to government and other interested parties&#xD;
on the state of Britain’s common songbird populations, new models for&#xD;
analysing ecological data are developed in this thesis. These models use data&#xD;
from the British Trust for Ornithology’s Constant Effort Sites (CES) scheme,&#xD;
an annual bird-ringing programme in which catch effort is standardised. Data&#xD;
from the CES scheme are routinely used to index abundance and productivity,&#xD;
and to a lesser extent estimate adult survival rates. However, two features of&#xD;
the CES data that complicate analysis were previously inadequately addressed,&#xD;
namely the presence in the catch of “transient” birds not associated with the&#xD;
local population, and the sporadic failure in the constancy of effort assumption&#xD;
arising from the absence of within-year catch data. The current methodology&#xD;
is extended, with efficient Bayesian models developed for each of these demographic&#xD;
parameters that account for both of these data nuances, and from which&#xD;
reliable and usefully precise estimates are obtained.&#xD;
Of increasing interest is the relationship between abundance and the underlying&#xD;
vital rates, an understanding of which facilitates effective conservation.&#xD;
CES data are particularly amenable to an integrated approach to population&#xD;
modelling, providing a combination of demographic information from a single&#xD;
source. Such an integrated approach is developed here, employing Bayesian&#xD;
methodology and a simple population model to unite abundance, productivity&#xD;
and survival within a consistent framework. Independent data from ring-recoveries&#xD;
provide additional information on adult and juvenile survival rates.&#xD;
Specific advantages of this new integrated approach are identified, among which&#xD;
is the ability to determine juvenile survival accurately, disentangle the probabilities&#xD;
of survival and permanent emigration, and to obtain estimates of total&#xD;
seasonal productivity.&#xD;
The methodologies developed in this thesis are applied to CES data from Sedge&#xD;
Warbler, Acrocephalus schoenobaenus, and Reed Warbler, A. scirpaceus.</summary>
    <dc:date>2010-06-25T00:00:00Z</dc:date>
    <dc:creator>Cave, Vanessa M.</dc:creator>
    <dc:description>To underpin and improve advice given to government and other interested parties&#xD;
on the state of Britain’s common songbird populations, new models for&#xD;
analysing ecological data are developed in this thesis. These models use data&#xD;
from the British Trust for Ornithology’s Constant Effort Sites (CES) scheme,&#xD;
an annual bird-ringing programme in which catch effort is standardised. Data&#xD;
from the CES scheme are routinely used to index abundance and productivity,&#xD;
and to a lesser extent estimate adult survival rates. However, two features of&#xD;
the CES data that complicate analysis were previously inadequately addressed,&#xD;
namely the presence in the catch of “transient” birds not associated with the&#xD;
local population, and the sporadic failure in the constancy of effort assumption&#xD;
arising from the absence of within-year catch data. The current methodology&#xD;
is extended, with efficient Bayesian models developed for each of these demographic&#xD;
parameters that account for both of these data nuances, and from which&#xD;
reliable and usefully precise estimates are obtained.&#xD;
Of increasing interest is the relationship between abundance and the underlying&#xD;
vital rates, an understanding of which facilitates effective conservation.&#xD;
CES data are particularly amenable to an integrated approach to population&#xD;
modelling, providing a combination of demographic information from a single&#xD;
source. Such an integrated approach is developed here, employing Bayesian&#xD;
methodology and a simple population model to unite abundance, productivity&#xD;
and survival within a consistent framework. Independent data from ring-recoveries&#xD;
provide additional information on adult and juvenile survival rates.&#xD;
Specific advantages of this new integrated approach are identified, among which&#xD;
is the ability to determine juvenile survival accurately, disentangle the probabilities&#xD;
of survival and permanent emigration, and to obtain estimates of total&#xD;
seasonal productivity.&#xD;
The methodologies developed in this thesis are applied to CES data from Sedge&#xD;
Warbler, Acrocephalus schoenobaenus, and Reed Warbler, A. scirpaceus.</dc:description>
  </entry>
  <entry>
    <title>Topics in estimation of quantum channels</title>
    <link rel="alternate" href="http://hdl.handle.net/10023/869" />
    <author>
      <name>O'Loan, Caleb J.</name>
    </author>
    <id>http://hdl.handle.net/10023/869</id>
    <updated>2010-11-10T14:20:54Z</updated>
    <published>2010-06-23T00:00:00Z</published>
    <summary type="text">Abstract: A quantum channel is a mapping which sends density matrices to density&#xD;
matrices. The estimation of quantum channels is of great importance to the&#xD;
field of quantum information. In this thesis two topics related to estimation&#xD;
of quantum channels are investigated. The first of these is the upper&#xD;
bound of Sarovar and Milburn (2006) on the Fisher information obtainable&#xD;
by measuring the output of a channel. Two questions raised by Sarovar and&#xD;
Milburn about their bound are answered. A Riemannian metric on the space&#xD;
of quantum states is introduced, related to the construction of the Sarovar&#xD;
and Milburn bound. Its properties are characterized.&#xD;
The second topic investigated is the estimation of unitary channels. The&#xD;
situation is considered in which an experimenter has several non-identical&#xD;
unitary channels that have the same parameter. It is shown that it is possible&#xD;
to improve estimation using the channels together, analogous to the case of&#xD;
identical unitary channels. Also, a new method of phase estimation is given&#xD;
based on a method sketched by Kitaev (1996). Unlike other phase estimation&#xD;
procedures which perform similarly, this procedure requires only very basic&#xD;
experimental resources.</summary>
    <dc:date>2010-06-23T00:00:00Z</dc:date>
    <dc:creator>O'Loan, Caleb J.</dc:creator>
    <dc:description>A quantum channel is a mapping which sends density matrices to density&#xD;
matrices. The estimation of quantum channels is of great importance to the&#xD;
field of quantum information. In this thesis two topics related to estimation&#xD;
of quantum channels are investigated. The first of these is the upper&#xD;
bound of Sarovar and Milburn (2006) on the Fisher information obtainable&#xD;
by measuring the output of a channel. Two questions raised by Sarovar and&#xD;
Milburn about their bound are answered. A Riemannian metric on the space&#xD;
of quantum states is introduced, related to the construction of the Sarovar&#xD;
and Milburn bound. Its properties are characterized.&#xD;
The second topic investigated is the estimation of unitary channels. The&#xD;
situation is considered in which an experimenter has several non-identical&#xD;
unitary channels that have the same parameter. It is shown that it is possible&#xD;
to improve estimation using the channels together, analogous to the case of&#xD;
identical unitary channels. Also, a new method of phase estimation is given&#xD;
based on a method sketched by Kitaev (1996). Unlike other phase estimation&#xD;
procedures which perform similarly, this procedure requires only very basic&#xD;
experimental resources.</dc:description>
  </entry>
  <entry>
    <title>Multi-species state-space modelling of the hen harrier (Circus cyaneus) and red grouse (Lagopus lagopus scoticus) in Scotland</title>
    <link rel="alternate" href="http://hdl.handle.net/10023/864" />
    <author>
      <name>New, Leslie F.</name>
    </author>
    <id>http://hdl.handle.net/10023/864</id>
    <updated>2010-04-06T11:32:11Z</updated>
    <published>2010-06-23T00:00:00Z</published>
    <summary type="text">Abstract: State-space modelling is a powerful tool to study ecological systems. The direct inclusion of uncertainty, unification of models and data, and ability to model unobserved, hidden states increases our knowledge about the environment and provides&#xD;
new ecological insights. I extend the state-space framework to create multi-species&#xD;
models, showing that the ability to model ecosystem interactions is limited only by data availability.                State-space models are fit using both Bayesian and Frequentist methods, making them independent of a statistical school of thought. Bayesian approaches can have the advantage in their ability to account for missing data and fit hierarchical structures&#xD;
and models with many parameters to limited data; often the case in ecological studies.&#xD;
I have taken a Bayesian model fitting approach in this thesis.&#xD;
The predator-prey interactions between the hen harrier (Circus cyaneus) and red grouse (Lagopus lagopus scoticus) are used to demonstrate state-space modelling’s&#xD;
capabilities. The harrier data are believed to be known without error, while missing&#xD;
data make the cyclic dynamics of the grouse harder to model. The grouse-harrier interactions are modelled in a multi-species state-space model, rather than including&#xD;
one species as a covariate in the other’s model. Finally, models are included for the&#xD;
harriers’ alternate prey.&#xD;
The single- and multi-species state-space models for the predator-prey interactions&#xD;
provide insight into the species’ management. The models investigate aspects of the species’ behaviour, from the mechanisms behind grouse cycles to what motivates harrier immigration. The inferences drawn from these models are applicable to management, suggesting actions to halt grouse cycles or mitigate the grouse-harrier conflict. Overall, the multi-species models suggest that two popular ideas for grouse-harrier management, diversionary feeding and habitat manipulation to reduce alternate prey densities, will not have the desired effect, and in the case of reducing prey densities, may even increase the harriers’ impact on grouse chicks.</summary>
    <dc:date>2010-06-23T00:00:00Z</dc:date>
    <dc:creator>New, Leslie F.</dc:creator>
    <dc:description>State-space modelling is a powerful tool to study ecological systems. The direct inclusion of uncertainty, unification of models and data, and ability to model unobserved, hidden states increases our knowledge about the environment and provides&#xD;
new ecological insights. I extend the state-space framework to create multi-species&#xD;
models, showing that the ability to model ecosystem interactions is limited only by data availability.                State-space models are fit using both Bayesian and Frequentist methods, making them independent of a statistical school of thought. Bayesian approaches can have the advantage in their ability to account for missing data and fit hierarchical structures&#xD;
and models with many parameters to limited data; often the case in ecological studies.&#xD;
I have taken a Bayesian model fitting approach in this thesis.&#xD;
The predator-prey interactions between the hen harrier (Circus cyaneus) and red grouse (Lagopus lagopus scoticus) are used to demonstrate state-space modelling’s&#xD;
capabilities. The harrier data are believed to be known without error, while missing&#xD;
data make the cyclic dynamics of the grouse harder to model. The grouse-harrier interactions are modelled in a multi-species state-space model, rather than including&#xD;
one species as a covariate in the other’s model. Finally, models are included for the&#xD;
harriers’ alternate prey.&#xD;
The single- and multi-species state-space models for the predator-prey interactions&#xD;
provide insight into the species’ management. The models investigate aspects of the species’ behaviour, from the mechanisms behind grouse cycles to what motivates harrier immigration. The inferences drawn from these models are applicable to management, suggesting actions to halt grouse cycles or mitigate the grouse-harrier conflict. Overall, the multi-species models suggest that two popular ideas for grouse-harrier management, diversionary feeding and habitat manipulation to reduce alternate prey densities, will not have the desired effect, and in the case of reducing prey densities, may even increase the harriers’ impact on grouse chicks.</dc:description>
  </entry>
  <entry>
    <title>Distance software: design and analysis of distance sampling surveys for estimating population size</title>
    <link rel="alternate" href="http://hdl.handle.net/10023/817" />
    <author>
      <name>Thomas, Len</name>
    </author>
    <author>
      <name>Buckland, Stephen Terrence</name>
    </author>
    <author>
      <name>Rexstad, Eric</name>
    </author>
    <author>
      <name>Laake, J L</name>
    </author>
    <author>
      <name>Strindberg, S</name>
    </author>
    <author>
      <name>Hedley, S L</name>
    </author>
    <author>
      <name>Bishop, J R B</name>
    </author>
    <author>
      <name>Marques, Tiago Andre Lamas Oliveira</name>
    </author>
    <id>http://hdl.handle.net/10023/817</id>
    <updated>2011-10-10T10:42:15Z</updated>
    <published>2010-01-01T00:00:00Z</published>
    <summary type="text">Abstract: 1. Distance sampling is a widely used technique for estimating the size or density of biological populations. Many distance sampling designs and most analyses use the software Distance. 2. We briefly review distance sampling and its assumptions, outline the history, structure and capabilities of Distance, and provide hints on its use. 3. Good survey design is a crucial pre-requisite for obtaining reliable results. Distance has a survey design engine, with a built-in geographic information system, that allows properties of different proposed designs to be examined via simulation, and survey plans to be generated. 4. A first step in analysis of distance sampling data is modelling the probability of detection. Distance contains three increasingly sophisticated analysis engines for this: CDS (conventional distance sampling), which models detection probability as a function of distance from the transect and assumes all objects at zero distance are detected; MCDS (multiple covariate distance sampling), which allows covariates in addition to distance; and MRDS (mark-recapture distance sampling), which relaxes the assumption of certain detection at zero distance. 5. All three engines allow estimation of density or abundance, stratified if required, with associated measures of precision calculated either analytically or via the bootstrap. 6. Advanced analysis topics covered include the use of multipliers to allow analysis of indirect surveys (such as dung or nest surveys), the DSM (density surface modelling) analysis engine for spatial and habitat modelling, and information about accessing the analysis engines directly from other software. 7. Synthesis and applications. Distance sampling is a key method for producing abundance and density estimates in challenging field conditions. The theory underlying the methods continues to expand to cope with realistic estimation situations. In step with theoretical developments, state-of-the-art software that implements these methods is described that makes the methods accessible to practicing ecologists.</summary>
    <dc:date>2010-01-01T00:00:00Z</dc:date>
    <dc:creator>Thomas, Len</dc:creator>
    <dc:creator>Buckland, Stephen Terrence</dc:creator>
    <dc:creator>Rexstad, Eric</dc:creator>
    <dc:creator>Laake, J L</dc:creator>
    <dc:creator>Strindberg, S</dc:creator>
    <dc:creator>Hedley, S L</dc:creator>
    <dc:creator>Bishop, J R B</dc:creator>
    <dc:creator>Marques, Tiago Andre Lamas Oliveira</dc:creator>
    <dc:description>1. Distance sampling is a widely used technique for estimating the size or density of biological populations. Many distance sampling designs and most analyses use the software Distance. 2. We briefly review distance sampling and its assumptions, outline the history, structure and capabilities of Distance, and provide hints on its use. 3. Good survey design is a crucial pre-requisite for obtaining reliable results. Distance has a survey design engine, with a built-in geographic information system, that allows properties of different proposed designs to be examined via simulation, and survey plans to be generated. 4. A first step in analysis of distance sampling data is modelling the probability of detection. Distance contains three increasingly sophisticated analysis engines for this: CDS (conventional distance sampling), which models detection probability as a function of distance from the transect and assumes all objects at zero distance are detected; MCDS (multiple covariate distance sampling), which allows covariates in addition to distance; and MRDS (mark-recapture distance sampling), which relaxes the assumption of certain detection at zero distance. 5. All three engines allow estimation of density or abundance, stratified if required, with associated measures of precision calculated either analytically or via the bootstrap. 6. Advanced analysis topics covered include the use of multipliers to allow analysis of indirect surveys (such as dung or nest surveys), the DSM (density surface modelling) analysis engine for spatial and habitat modelling, and information about accessing the analysis engines directly from other software. 7. Synthesis and applications. Distance sampling is a key method for producing abundance and density estimates in challenging field conditions. The theory underlying the methods continues to expand to cope with realistic estimation situations. In step with theoretical developments, state-of-the-art software that implements these methods is described that makes the methods accessible to practicing ecologists.</dc:description>
  </entry>
  <entry>
    <title>Embedding population dynamics in mark-recapture models</title>
    <link rel="alternate" href="http://hdl.handle.net/10023/718" />
    <author>
      <name>Bishop, Jonathan R. B.</name>
    </author>
    <id>http://hdl.handle.net/10023/718</id>
    <updated>2010-12-14T09:07:50Z</updated>
    <published>2009-06-24T00:00:00Z</published>
    <summary type="text">Abstract: Mark-recapture methods use repeated captures of individually identifiable animals to provide estimates of properties of populations.  Different models allow estimates to be obtained for population size and rates of processes governing population dynamics.  State-space models consist of two linked processes evolving simultaneously over time.  The state process models the evolution of the true, but unknown, states of the population.  The observation process relates observations on the population to these true states.&#xD;
&#xD;
Mark-recapture models specified within a state-space framework allow population dynamics models to be embedded in inference ensuring that estimated changes in the population are consistent with assumptions regarding the biology of the modelled population.  This overcomes a limitation of current mark-recapture methods.&#xD;
&#xD;
Two alternative approaches are considered.  The "conditional" approach conditions on known numbers of animals possessing capture history patterns including capture in the current time period.  An animal's capture history determines its state; consequently, capture parameters appear in the state process rather than the observation process.  There is no observation error in the model.  Uncertainty occurs only through the numbers of animals not captured in the current time period.&#xD;
&#xD;
An "unconditional" approach is considered in which the capture histories are regarded as observations.  Consequently, capture histories do not influence an animal's state and capture probability parameters appear in the observation process.  Capture histories are considered a random realization of the stochastic observation process.  This is more consistent with traditional mark-recapture methods.&#xD;
&#xD;
Development and implementation of particle filtering techniques for fitting these models under each approach are discussed.  Simulation studies show reasonable performance for the unconditional approach and highlight problems with the conditional approach.  Strengths and limitations of each approach are outlined, with reference to Soay sheep data analysis, and suggestions are presented for future analyses.</summary>
    <dc:date>2009-06-24T00:00:00Z</dc:date>
    <dc:creator>Bishop, Jonathan R. B.</dc:creator>
    <dc:description>Mark-recapture methods use repeated captures of individually identifiable animals to provide estimates of properties of populations.  Different models allow estimates to be obtained for population size and rates of processes governing population dynamics.  State-space models consist of two linked processes evolving simultaneously over time.  The state process models the evolution of the true, but unknown, states of the population.  The observation process relates observations on the population to these true states.&#xD;
&#xD;
Mark-recapture models specified within a state-space framework allow population dynamics models to be embedded in inference ensuring that estimated changes in the population are consistent with assumptions regarding the biology of the modelled population.  This overcomes a limitation of current mark-recapture methods.&#xD;
&#xD;
Two alternative approaches are considered.  The "conditional" approach conditions on known numbers of animals possessing capture history patterns including capture in the current time period.  An animal's capture history determines its state; consequently, capture parameters appear in the state process rather than the observation process.  There is no observation error in the model.  Uncertainty occurs only through the numbers of animals not captured in the current time period.&#xD;
&#xD;
An "unconditional" approach is considered in which the capture histories are regarded as observations.  Consequently, capture histories do not influence an animal's state and capture probability parameters appear in the observation process.  Capture histories are considered a random realization of the stochastic observation process.  This is more consistent with traditional mark-recapture methods.&#xD;
&#xD;
Development and implementation of particle filtering techniques for fitting these models under each approach are discussed.  Simulation studies show reasonable performance for the unconditional approach and highlight problems with the conditional approach.  Strengths and limitations of each approach are outlined, with reference to Soay sheep data analysis, and suggestions are presented for future analyses.</dc:description>
  </entry>
  <entry>
    <title>The importance of analysis method for breeding bird survey population trend estimates</title>
    <link rel="alternate" href="http://hdl.handle.net/10023/685" />
    <author>
      <name>Thomas, Len</name>
    </author>
    <author>
      <name>Martin, Kathy</name>
    </author>
    <id>http://hdl.handle.net/10023/685</id>
    <updated>2010-12-14T09:08:07Z</updated>
    <published>1996-01-01T00:00:00Z</published>
    <summary type="text">Abstract: Population trends from the Breeding Bird Survey are widely used to focus conservation efforts on species thought to be in decline and to test preliminary hypotheses regarding the causes of these declines. A number of statistical methods have been used to estimate population trends, but there is no consensus us to which is the most reliable. We quantified differences in trend estimates or different analysis methods applied to the same subset of Breeding Bird Survey data. We estimated trends for 115 species in British Columbia using three analysis methods: U.S. National Biological Service route regression, Canadian Wildlife Service route regression, and nonparametric rank-trends analysis. Overall, the number of species estimated to be declining was similar among the three methods, but the number of statistically significant declines was not similar (15, 8, and 29 respectively). In addition, many differences existed among methods in the trend estimates assigned to individual species. Comparing the two route regression methods, Canadian Wildlife Service estimates had a greater absolute magnitude on average than those of the U.S. National Biological Service method. U.S. National Biological Service estimates were on average more positive than the Canadian Wildlife Service estimates when the respective agency's data selection criteria were applied separately. These results imply that our ability to detect population declines and to prioritize species of conservation concern depend strongly upon the analysis method used. This highlights the need for further research to determine how best to accurately estimate trends from the data. We suggest a method for evaluating the performance of the analysis methods by using simulated Breeding Bird Survey data.</summary>
    <dc:date>1996-01-01T00:00:00Z</dc:date>
    <dc:creator>Thomas, Len</dc:creator>
    <dc:creator>Martin, Kathy</dc:creator>
    <dc:description>Population trends from the Breeding Bird Survey are widely used to focus conservation efforts on species thought to be in decline and to test preliminary hypotheses regarding the causes of these declines. A number of statistical methods have been used to estimate population trends, but there is no consensus us to which is the most reliable. We quantified differences in trend estimates or different analysis methods applied to the same subset of Breeding Bird Survey data. We estimated trends for 115 species in British Columbia using three analysis methods: U.S. National Biological Service route regression, Canadian Wildlife Service route regression, and nonparametric rank-trends analysis. Overall, the number of species estimated to be declining was similar among the three methods, but the number of statistically significant declines was not similar (15, 8, and 29 respectively). In addition, many differences existed among methods in the trend estimates assigned to individual species. Comparing the two route regression methods, Canadian Wildlife Service estimates had a greater absolute magnitude on average than those of the U.S. National Biological Service method. U.S. National Biological Service estimates were on average more positive than the Canadian Wildlife Service estimates when the respective agency's data selection criteria were applied separately. These results imply that our ability to detect population declines and to prioritize species of conservation concern depend strongly upon the analysis method used. This highlights the need for further research to determine how best to accurately estimate trends from the data. We suggest a method for evaluating the performance of the analysis methods by using simulated Breeding Bird Survey data.</dc:description>
  </entry>
  <entry>
    <title>Retrospective power analysis</title>
    <link rel="alternate" href="http://hdl.handle.net/10023/679" />
    <author>
      <name>Thomas, Len</name>
    </author>
    <id>http://hdl.handle.net/10023/679</id>
    <updated>2010-12-14T09:08:43Z</updated>
    <published>1997-01-01T00:00:00Z</published>
    <summary type="text">Abstract: Many papers have appeared in the recent biological literature encouraging us to incorporate statistical power analysis into our hypothesis testing protocol (Peterman 1990; Fairweather 1991; Muller &amp; Benignus 1992; Taylor &amp; Gerrodette 1993; Searcy-Bernal 1994; Thomas &amp; Juanes 1996). The importance of doing a power analysis before beginning a study (prospective power analysis) is universally accepted: such analyses help us to decide how many samples are required to have a good chance of getting unambiguous results. In contrast, the role of power analysis after the data are collected and analyzed (retrospective power analysis) is controversial, as is evidenced by the papers of Reed and Blaustein (1995) and Hayes and Steidl (1997). The controversy is over the use of information from the sample data in retrospective power calculations. As I will show, the type of information used has fundamental implications for the value of such analyses. I compare the approaches to calculating retrospective power, noting the strengths and weaknesses of each, and make general recommendations as to how and when retrospective power analyses should be conducted.
Description: The pdf contains the article; the ASCII file contains SAS code to calculate power and confidence limits for simple linear regression, as detailed in the article appendix.</summary>
    <dc:date>1997-01-01T00:00:00Z</dc:date>
    <dc:creator>Thomas, Len</dc:creator>
    <dc:description>Many papers have appeared in the recent biological literature encouraging us to incorporate statistical power analysis into our hypothesis testing protocol (Peterman 1990; Fairweather 1991; Muller &amp; Benignus 1992; Taylor &amp; Gerrodette 1993; Searcy-Bernal 1994; Thomas &amp; Juanes 1996). The importance of doing a power analysis before beginning a study (prospective power analysis) is universally accepted: such analyses help us to decide how many samples are required to have a good chance of getting unambiguous results. In contrast, the role of power analysis after the data are collected and analyzed (retrospective power analysis) is controversial, as is evidenced by the papers of Reed and Blaustein (1995) and Hayes and Steidl (1997). The controversy is over the use of information from the sample data in retrospective power calculations. As I will show, the type of information used has fundamental implications for the value of such analyses. I compare the approaches to calculating retrospective power, noting the strengths and weaknesses of each, and make general recommendations as to how and when retrospective power analyses should be conducted.</dc:description>
  </entry>
  <entry>
    <title>A unified framework for modelling wildlife population dynamics</title>
    <link rel="alternate" href="http://hdl.handle.net/10023/678" />
    <author>
      <name>Thomas, Len</name>
    </author>
    <author>
      <name>Buckland, Stephen T.</name>
    </author>
    <author>
      <name>Newman, KB</name>
    </author>
    <author>
      <name>Harwood, John</name>
    </author>
    <id>http://hdl.handle.net/10023/678</id>
    <updated>2010-12-14T09:08:58Z</updated>
    <published>2005-01-01T00:00:00Z</published>
    <summary type="text">Abstract: This paper proposes a unified framework for defining and fitting stochastic, discrete-time, discrete-stage population dynamics models. The biological system is described by a state–space model, where the true but unknown state of the population is modelled by a state process, and this is linked to survey data by an observation process. All sources of uncertainty in the inputs, including uncertainty about model specification, are readily incorporated. The paper shows how the state process can be represented as a generalization of the standard Leslie or Lefkovitch matrix. By dividing the state process into subprocesses, complex models can be constructed from manageable building blocks. The paper illustrates the approach with a model of the British Grey Seal metapopulation, using sequential importance sampling with kernel smoothing to fit the model.
Description: The pdf document contains the full article text; program code (in S-PLUS 6.1) for the example analysis is in the three text files; data is available from the Sea Mammal Research Unit (http://www.smru.st-and.ac.uk)</summary>
    <dc:date>2005-01-01T00:00:00Z</dc:date>
    <dc:creator>Thomas, Len</dc:creator>
    <dc:creator>Buckland, Stephen T.</dc:creator>
    <dc:creator>Newman, KB</dc:creator>
    <dc:creator>Harwood, John</dc:creator>
    <dc:description>This paper proposes a unified framework for defining and fitting stochastic, discrete-time, discrete-stage population dynamics models. The biological system is described by a state–space model, where the true but unknown state of the population is modelled by a state process, and this is linked to survey data by an observation process. All sources of uncertainty in the inputs, including uncertainty about model specification, are readily incorporated. The paper shows how the state process can be represented as a generalization of the standard Leslie or Lefkovitch matrix. By dividing the state process into subprocesses, complex models can be constructed from manageable building blocks. The paper illustrates the approach with a model of the British Grey Seal metapopulation, using sequential importance sampling with kernel smoothing to fit the model.</dc:description>
  </entry>
  <entry>
    <title>WinBUGS for population ecologists: Bayesian modeling using Markov Chain Monte Carlo methods.</title>
    <link rel="alternate" href="http://hdl.handle.net/10023/677" />
    <author>
      <name>Giminez, O</name>
    </author>
    <author>
      <name>Bonner, S J</name>
    </author>
    <author>
      <name>King, Ruth, 1977-</name>
    </author>
    <author>
      <name>Parker, R A</name>
    </author>
    <author>
      <name>Brooks, S P</name>
    </author>
    <author>
      <name>Jamieson, L E</name>
    </author>
    <author>
      <name>Grosbois, V</name>
    </author>
    <author>
      <name>Morgan, B J T</name>
    </author>
    <author>
      <name>Thomas, Len</name>
    </author>
    <id>http://hdl.handle.net/10023/677</id>
    <updated>2010-12-14T09:09:16Z</updated>
    <published>2008-01-01T00:00:00Z</published>
    <summary type="text">Abstract: The computer package WinBUGS is introduced. We first give a brief introduction to Bayesian theory and its implementation using Markov chain Monte Carlo (MCMC) algorithms. We then present three case studies showing how WinBUGS can be used when classical theory is difficult to implement. The first example uses data on white storks from Baden Württemberg, Germany, to demonstrate the use of mark-recapture models to estimate survival, and also how to cope with unexplained variance through random effects. Recent advances in methodology and also the WinBUGS software allow us to introduce (i) a flexible way of incorporating covariates using spline smoothing and (ii) a method to deal with missing values in covariates. The second example shows how to estimate population density while accounting for detectability, using distance sampling methods applied to a test dataset collected on a known population of wooden stakes. Finally, the third case study involves the use of state-space models of wildlife population dynamics to make inferences about density dependence in a North American duck species. Reversible Jump MCMC is used to calculate the probability of various candidate models. For all examples, data and WinBUGS code are provided.
Description: This paper was presented at the EURING 2007 Technical Meeting, January 14-21, Dunedin, New Zealand. It has been submitted for publication in the conference proceedings, which will appear as a special issue of Environmental and Ecological Statistics.; The zip file contains accompanying code in WinBUGS</summary>
    <dc:date>2008-01-01T00:00:00Z</dc:date>
    <dc:creator>Giminez, O</dc:creator>
    <dc:creator>Bonner, S J</dc:creator>
    <dc:creator>King, Ruth, 1977-</dc:creator>
    <dc:creator>Parker, R A</dc:creator>
    <dc:creator>Brooks, S P</dc:creator>
    <dc:creator>Jamieson, L E</dc:creator>
    <dc:creator>Grosbois, V</dc:creator>
    <dc:creator>Morgan, B J T</dc:creator>
    <dc:creator>Thomas, Len</dc:creator>
    <dc:description>The computer package WinBUGS is introduced. We first give a brief introduction to Bayesian theory and its implementation using Markov chain Monte Carlo (MCMC) algorithms. We then present three case studies showing how WinBUGS can be used when classical theory is difficult to implement. The first example uses data on white storks from Baden Württemberg, Germany, to demonstrate the use of mark-recapture models to estimate survival, and also how to cope with unexplained variance through random effects. Recent advances in methodology and also the WinBUGS software allow us to introduce (i) a flexible way of incorporating covariates using spline smoothing and (ii) a method to deal with missing values in covariates. The second example shows how to estimate population density while accounting for detectability, using distance sampling methods applied to a test dataset collected on a known population of wooden stakes. Finally, the third case study involves the use of state-space models of wildlife population dynamics to make inferences about density dependence in a North American duck species. Reversible Jump MCMC is used to calculate the probability of various candidate models. For all examples, data and WinBUGS code are provided.</dc:description>
  </entry>
  <entry>
    <title>Density estimation and time trend analysis of large herbivores in Nagarhole, India</title>
    <link rel="alternate" href="http://hdl.handle.net/10023/669" />
    <author>
      <name>Gangadharan, Aditya</name>
    </author>
    <id>http://hdl.handle.net/10023/669</id>
    <updated>2010-11-08T16:44:50Z</updated>
    <published>2005-01-01T00:00:00Z</published>
    <summary type="text">Abstract: Density estimates for six large herbivore species were obtained through&#xD;
analysis of line transect data from Nagarhole National Park, south-western India,&#xD;
collected between 1989 and 2000. These species were Chital (Axis axis), Sambar&#xD;
(Cervus unicolor), Gaur (Bos gaurus), Wild Pig (Sus scrofa), Muntjac (Muntiacus&#xD;
muntjak) and Asian Elephant (Elephas maximus). Multiple Covariate Distance&#xD;
Sampling (MCDS) models were used to derive these density estimates. The distance&#xD;
histograms showed a relatively large spike at zero, which can lead to problems when&#xD;
fitting MCDS models. The effects of this spike were investigated and remedied by&#xD;
forward truncation. Density estimates from unmodified dataset were 10-15% higher&#xD;
than estimates from the forward truncated data, with this going up to 37% for&#xD;
Muntjac. These could possibly be over estimates. Empirical trend models were then&#xD;
fit to the density estimates. Overall trends were stable, though there were intra-habitat&#xD;
differences in trends for some species. The trends were similar both in cases where&#xD;
forward truncation was done as well as in those where they were not.
Description: MRes in Environmental Biology</summary>
    <dc:date>2005-01-01T00:00:00Z</dc:date>
    <dc:creator>Gangadharan, Aditya</dc:creator>
    <dc:description>Density estimates for six large herbivore species were obtained through&#xD;
analysis of line transect data from Nagarhole National Park, south-western India,&#xD;
collected between 1989 and 2000. These species were Chital (Axis axis), Sambar&#xD;
(Cervus unicolor), Gaur (Bos gaurus), Wild Pig (Sus scrofa), Muntjac (Muntiacus&#xD;
muntjak) and Asian Elephant (Elephas maximus). Multiple Covariate Distance&#xD;
Sampling (MCDS) models were used to derive these density estimates. The distance&#xD;
histograms showed a relatively large spike at zero, which can lead to problems when&#xD;
fitting MCDS models. The effects of this spike were investigated and remedied by&#xD;
forward truncation. Density estimates from unmodified dataset were 10-15% higher&#xD;
than estimates from the forward truncated data, with this going up to 37% for&#xD;
Muntjac. These could possibly be over estimates. Empirical trend models were then&#xD;
fit to the density estimates. Overall trends were stable, though there were intra-habitat&#xD;
differences in trends for some species. The trends were similar both in cases where&#xD;
forward truncation was done as well as in those where they were not.</dc:description>
  </entry>
  <entry>
    <title>Models of random wildlife movement with an application to distance sampling</title>
    <link rel="alternate" href="http://hdl.handle.net/10023/668" />
    <author>
      <name>DiTraglia, Francis J.</name>
    </author>
    <id>http://hdl.handle.net/10023/668</id>
    <updated>2010-12-14T09:08:23Z</updated>
    <published>2007-01-01T00:00:00Z</published>
    <summary type="text">Abstract: In this paper we present three models of random wildlife movement: a one dimensional model of wildlife-observer encounters on roads, an analogous two dimensional model, and an further two-dimensional model that borrows from the ideas of statistical mechanics. We then derive unbiased estimates of wildlife density in terms of encounters for each of these models. By extending these results to incorporate uncertain detection, we suggest three novel distance sampling methods and briefly consider possible field applications.</summary>
    <dc:date>2007-01-01T00:00:00Z</dc:date>
    <dc:creator>DiTraglia, Francis J.</dc:creator>
    <dc:description>In this paper we present three models of random wildlife movement: a one dimensional model of wildlife-observer encounters on roads, an analogous two dimensional model, and an further two-dimensional model that borrows from the ideas of statistical mechanics. We then derive unbiased estimates of wildlife density in terms of encounters for each of these models. By extending these results to incorporate uncertain detection, we suggest three novel distance sampling methods and briefly consider possible field applications.</dc:description>
  </entry>
  <entry>
    <title>Designing a shipboard line transect survey to estimate cetacean abundance off the Azores Archipelago, Portugal</title>
    <link rel="alternate" href="http://hdl.handle.net/10023/667" />
    <author>
      <name>Faustino, Cláudia Estevinho Santos</name>
    </author>
    <id>http://hdl.handle.net/10023/667</id>
    <updated>2011-06-17T13:18:34Z</updated>
    <published>2008-01-01T00:00:00Z</published>
    <summary type="text">Abstract: Management schemes dedicated to the conservation of wildlife populations rely on the effective monitoring of population size, and this requires the accurate and precise estimation of abundance. The accuracy and precision of estimates are determined to a large extent by the survey design. Line transect surveys are commonly applied to wildlife population assessments in which the primary purpose of a survey design is to ensure that the critical distance sampling assumptions are met.&#xD;
Little information is available regarding cetacean abundance in the Archipelago of the Azores (Portugal). This study aims to design a line transect shipboard survey that allows the collection of data required to provide abundance estimates for such species. Several aspects must be taken into consideration when designing a survey to estimate cetacean abundance. This is an iterative process, and there is a constant trade off between the logistic constraints and the desired statistical robustness. Information on this process is provided to aid policy makers and environmental managers, such as the criteria used for the choices made when defining the elements of a survey design.&#xD;
Three survey effort scenarios are provided to illustrate the range of possibilities between statistical robustness and logistic/ management restrictions. A survey is designed for the more economical scenario (L=5000Km), although the second scenario is the one recommended to be implemented (L=17,600Km) given it provides robust estimates of&#xD;
abundance (CV&lt;=0.2).
Description: Revised version November 2008. MRes in Marine Mammal Science</summary>
    <dc:date>2008-01-01T00:00:00Z</dc:date>
    <dc:creator>Faustino, Cláudia Estevinho Santos</dc:creator>
    <dc:description>Management schemes dedicated to the conservation of wildlife populations rely on the effective monitoring of population size, and this requires the accurate and precise estimation of abundance. The accuracy and precision of estimates are determined to a large extent by the survey design. Line transect surveys are commonly applied to wildlife population assessments in which the primary purpose of a survey design is to ensure that the critical distance sampling assumptions are met.&#xD;
Little information is available regarding cetacean abundance in the Archipelago of the Azores (Portugal). This study aims to design a line transect shipboard survey that allows the collection of data required to provide abundance estimates for such species. Several aspects must be taken into consideration when designing a survey to estimate cetacean abundance. This is an iterative process, and there is a constant trade off between the logistic constraints and the desired statistical robustness. Information on this process is provided to aid policy makers and environmental managers, such as the criteria used for the choices made when defining the elements of a survey design.&#xD;
Three survey effort scenarios are provided to illustrate the range of possibilities between statistical robustness and logistic/ management restrictions. A survey is designed for the more economical scenario (L=5000Km), although the second scenario is the one recommended to be implemented (L=17,600Km) given it provides robust estimates of&#xD;
abundance (CV&lt;=0.2).</dc:description>
  </entry>
  <entry>
    <title>Behavioural changes of a long-ranging diver in response to oceanographic conditions</title>
    <link rel="alternate" href="http://hdl.handle.net/10023/665" />
    <author>
      <name>Photopoulos, Theoni</name>
    </author>
    <id>http://hdl.handle.net/10023/665</id>
    <updated>2010-11-08T16:43:07Z</updated>
    <published>2007-01-01T00:00:00Z</published>
    <summary type="text">Abstract: The development of an animal-borne instrument that can record oceanographic measurements (CTD-SRDL) has enabled the collection of oceanographic data at a scale relevant to the counterpart behavioural data, both in time and 3-dimensional space. This has advanced the potential for studies of the behaviour of deep-diving marine animals and the way in which they respond to their environment, yet the nature of the data delivered by CTD-SRDLs presents substantial analytical challenges and places constraints on its biological interpretation. Behavioural and environmental data, collected using CTD-SRDLs deployed on southern elephant seals (Mirounga leonina) from the South Georgia subpopulation in 2004 and 2005, are analysed for 13 females and 4 males (21,015 dives). Compressed dive profiles are used to classify individual dives into six distinct types based on their 2-dimensional time-depth characteristics using random forest classification. The relationship between dive type and environmental variables, derived from oceanographic data recorded on board the animals, is investigated in the context of regression analysis, employing a multinomial model, as well as independently fitted Generalized Linear Models (GLM) and Generalized Additive Models (GAM) for each dive type. Regression is not found to be an appropriate method for analysing abstracted behavioural dive data, and other methods are suggested. We show that functional specializations can be manifested within a dive type, using square bottom dives (SQ) as an example. The usefulness of dive classification is discussed in the context of behavioural interpretation, and validity of the ecological functions attached to each class. Preliminary analyses are important drivers of further research into improving the interpretability of abstracted behavioural data, and developing efficient, standardized methods for widespread application to this type of data, which is obtained in abundance via satellite telemetry.
Description: BL 5019 Research project. MRes Environmental Biology</summary>
    <dc:date>2007-01-01T00:00:00Z</dc:date>
    <dc:creator>Photopoulos, Theoni</dc:creator>
    <dc:description>The development of an animal-borne instrument that can record oceanographic measurements (CTD-SRDL) has enabled the collection of oceanographic data at a scale relevant to the counterpart behavioural data, both in time and 3-dimensional space. This has advanced the potential for studies of the behaviour of deep-diving marine animals and the way in which they respond to their environment, yet the nature of the data delivered by CTD-SRDLs presents substantial analytical challenges and places constraints on its biological interpretation. Behavioural and environmental data, collected using CTD-SRDLs deployed on southern elephant seals (Mirounga leonina) from the South Georgia subpopulation in 2004 and 2005, are analysed for 13 females and 4 males (21,015 dives). Compressed dive profiles are used to classify individual dives into six distinct types based on their 2-dimensional time-depth characteristics using random forest classification. The relationship between dive type and environmental variables, derived from oceanographic data recorded on board the animals, is investigated in the context of regression analysis, employing a multinomial model, as well as independently fitted Generalized Linear Models (GLM) and Generalized Additive Models (GAM) for each dive type. Regression is not found to be an appropriate method for analysing abstracted behavioural dive data, and other methods are suggested. We show that functional specializations can be manifested within a dive type, using square bottom dives (SQ) as an example. The usefulness of dive classification is discussed in the context of behavioural interpretation, and validity of the ecological functions attached to each class. Preliminary analyses are important drivers of further research into improving the interpretability of abstracted behavioural data, and developing efficient, standardized methods for widespread application to this type of data, which is obtained in abundance via satellite telemetry.</dc:description>
  </entry>
  <entry>
    <title>Using generalized estimating equations with regression splines to improve analysis of butterfly transect data</title>
    <link rel="alternate" href="http://hdl.handle.net/10023/488" />
    <author>
      <name>Brewer, Ciara</name>
    </author>
    <id>http://hdl.handle.net/10023/488</id>
    <updated>2008-06-18T09:51:15Z</updated>
    <published>2008-06-01T00:00:00Z</published>
    <summary type="text">Abstract: Surveying animal populations is an important aspect of wildlife&#xD;
management. Distinguishing trend from random fluctuations and&#xD;
quantifying trend are key goals in any analysis. &#xD;
The aim of this thesis is to review analyses of Butterfly Monitoring&#xD;
Survey (BMS) data and to develop new methods which address some&#xD;
flaws in previous studies. The BMS was established in 1976 at Monks&#xD;
Wood, Cambridgeshire and sites were added over time throughout&#xD;
Britain in order to monitor butterfly population trends. Weekly&#xD;
counts are made over the monitoring season and the main aims are to&#xD;
produce annual indices and compare these indices over time for any&#xD;
particular species. &#xD;
Originally, weekly counts were summed to produce relative indices&#xD;
and missing counts were estimated using linear interpolation. This&#xD;
thesis discusses the weaknesses of this basic method&#xD;
and suggests possible improvements. &#xD;
In recent years, with advancements in statistical methods and&#xD;
increased computer power, new methods can be applied to accommodate&#xD;
the longitudinal and flexible nature of ecological data. &#xD;
Mixed Models, Generalized Estimating Equations and Generalized&#xD;
Additive Models are used and the relative merits of each modelling&#xD;
approach discussed. These methods allow for correlation and&#xD;
non-linearity in data. &#xD;
Model selection is an important consideration when modelling and&#xD;
different tests are introduced and compared.&#xD;
Once a model is selected, site-level indices are estimated, which&#xD;
can be collated to produce regional and national indices. Different&#xD;
methods of estimating precision around indices are also contrasted.&#xD;
Bootstrapping is found to be a convenient and dependable approach.&#xD;
Abundance is difficult to disentangle from detectability when only&#xD;
counts of species are carried out. Methods for dealing with this&#xD;
problem are suggested.&#xD;
Once reliable annual abundance estimates are found, they can be&#xD;
compared over time using a variety of statistical techniques. The&#xD;
chain-ratio method is applied to a subset of real data.</summary>
    <dc:date>2008-06-01T00:00:00Z</dc:date>
    <dc:creator>Brewer, Ciara</dc:creator>
    <dc:description>Surveying animal populations is an important aspect of wildlife&#xD;
management. Distinguishing trend from random fluctuations and&#xD;
quantifying trend are key goals in any analysis. &#xD;
The aim of this thesis is to review analyses of Butterfly Monitoring&#xD;
Survey (BMS) data and to develop new methods which address some&#xD;
flaws in previous studies. The BMS was established in 1976 at Monks&#xD;
Wood, Cambridgeshire and sites were added over time throughout&#xD;
Britain in order to monitor butterfly population trends. Weekly&#xD;
counts are made over the monitoring season and the main aims are to&#xD;
produce annual indices and compare these indices over time for any&#xD;
particular species. &#xD;
Originally, weekly counts were summed to produce relative indices&#xD;
and missing counts were estimated using linear interpolation. This&#xD;
thesis discusses the weaknesses of this basic method&#xD;
and suggests possible improvements. &#xD;
In recent years, with advancements in statistical methods and&#xD;
increased computer power, new methods can be applied to accommodate&#xD;
the longitudinal and flexible nature of ecological data. &#xD;
Mixed Models, Generalized Estimating Equations and Generalized&#xD;
Additive Models are used and the relative merits of each modelling&#xD;
approach discussed. These methods allow for correlation and&#xD;
non-linearity in data. &#xD;
Model selection is an important consideration when modelling and&#xD;
different tests are introduced and compared.&#xD;
Once a model is selected, site-level indices are estimated, which&#xD;
can be collated to produce regional and national indices. Different&#xD;
methods of estimating precision around indices are also contrasted.&#xD;
Bootstrapping is found to be a convenient and dependable approach.&#xD;
Abundance is difficult to disentangle from detectability when only&#xD;
counts of species are carried out. Methods for dealing with this&#xD;
problem are suggested.&#xD;
Once reliable annual abundance estimates are found, they can be&#xD;
compared over time using a variety of statistical techniques. The&#xD;
chain-ratio method is applied to a subset of real data.</dc:description>
  </entry>
  <entry>
    <title>Incorporating measurement error and density gradients in distance sampling surveys</title>
    <link rel="alternate" href="http://hdl.handle.net/10023/391" />
    <author>
      <name>Marques, Tiago Andre Lamas Oliveira</name>
    </author>
    <id>http://hdl.handle.net/10023/391</id>
    <updated>2011-06-17T13:18:04Z</updated>
    <published>2007-11-01T00:00:00Z</published>
    <summary type="text">Abstract: Distance sampling is one of the most commonly used methods for estimating density&#xD;
and abundance. Conventional methods are based on the distances of detected animals&#xD;
from the center of point transects or the center line of line transects. These distances&#xD;
are used to model a detection function: the probability of detecting an animal, given&#xD;
its distance from the line or point. The probability of detecting an animal in the&#xD;
covered area is given by the mean value of the detection function with respect to&#xD;
the available distances to be detected. Given this probability, a Horvitz-Thompson-&#xD;
like estimator of abundance for the covered area follows, hence using a model-based&#xD;
framework. Inferences for the wider survey region are justified using the survey design.&#xD;
Conventional distance sampling methods are based on a set of assumptions. In&#xD;
this thesis I present results that extend distance sampling on two fronts.&#xD;
Firstly, estimators are derived for situations in which there is measurement error in&#xD;
the distances. These estimators use information about the measurement error in two&#xD;
ways: (1) a biased estimator based on the contaminated distances is multiplied by an&#xD;
appropriate correction factor, which is a function of the errors (PDF approach), and&#xD;
(2) cast into a likelihood framework that allows parameter estimation in the presence&#xD;
of measurement error (likelihood approach).&#xD;
Secondly, methods are developed that relax the conventional assumption that the&#xD;
distribution of animals is independent of distance from the lines or points (usually&#xD;
guaranteed by appropriate survey design). In particular, the new methods deal with&#xD;
the case where animal density gradients are caused by the use of non-random sampler&#xD;
allocation, for example transects placed along linear features such as roads or streams.&#xD;
This is dealt with separately for line and point transects, and at a later stage an&#xD;
approach for combining the two is presented.&#xD;
A considerable number of simulations and example analysis illustrate the performance of the proposed methods.</summary>
    <dc:date>2007-11-01T00:00:00Z</dc:date>
    <dc:creator>Marques, Tiago Andre Lamas Oliveira</dc:creator>
    <dc:description>Distance sampling is one of the most commonly used methods for estimating density&#xD;
and abundance. Conventional methods are based on the distances of detected animals&#xD;
from the center of point transects or the center line of line transects. These distances&#xD;
are used to model a detection function: the probability of detecting an animal, given&#xD;
its distance from the line or point. The probability of detecting an animal in the&#xD;
covered area is given by the mean value of the detection function with respect to&#xD;
the available distances to be detected. Given this probability, a Horvitz-Thompson-&#xD;
like estimator of abundance for the covered area follows, hence using a model-based&#xD;
framework. Inferences for the wider survey region are justified using the survey design.&#xD;
Conventional distance sampling methods are based on a set of assumptions. In&#xD;
this thesis I present results that extend distance sampling on two fronts.&#xD;
Firstly, estimators are derived for situations in which there is measurement error in&#xD;
the distances. These estimators use information about the measurement error in two&#xD;
ways: (1) a biased estimator based on the contaminated distances is multiplied by an&#xD;
appropriate correction factor, which is a function of the errors (PDF approach), and&#xD;
(2) cast into a likelihood framework that allows parameter estimation in the presence&#xD;
of measurement error (likelihood approach).&#xD;
Secondly, methods are developed that relax the conventional assumption that the&#xD;
distribution of animals is independent of distance from the lines or points (usually&#xD;
guaranteed by appropriate survey design). In particular, the new methods deal with&#xD;
the case where animal density gradients are caused by the use of non-random sampler&#xD;
allocation, for example transects placed along linear features such as roads or streams.&#xD;
This is dealt with separately for line and point transects, and at a later stage an&#xD;
approach for combining the two is presented.&#xD;
A considerable number of simulations and example analysis illustrate the performance of the proposed methods.</dc:description>
  </entry>
  <entry>
    <title>A Bayesian approach to modelling field data on multi-species predator prey-interactions</title>
    <link rel="alternate" href="http://hdl.handle.net/10023/174" />
    <author>
      <name>Asseburg, Christian</name>
    </author>
    <id>http://hdl.handle.net/10023/174</id>
    <updated>2012-07-26T12:58:31Z</updated>
    <published>2006-01-01T00:00:00Z</published>
    <summary type="text">Abstract: Multi-species functional response models are required to model the predation of generalist preda-&#xD;
tors, which consume more than one prey species. In chapter 2, a new model for the multi-species&#xD;
functional response is presented. This model can describe generalist predators that exhibit func-&#xD;
tional responses of Holling type II to some of their prey and of type III to other prey. In chapter&#xD;
3, I review some of the theoretical distinctions between Bayesian and frequentist statistics and&#xD;
show how Bayesian statistics are particularly well-suited for the fitting of functional response&#xD;
models because uncertainty can be represented comprehensively. In chapters 4 and 5, the multi-&#xD;
species functional response model is fitted to field data on two generalist predators: the hen&#xD;
harrier Circus cyaneus and the harp seal Phoca groenlandica. I am not aware of any previous&#xD;
Bayesian model of the multi-species functional response that has been fitted to field data.&#xD;
The hen harrier's functional response fitted in chapter 4 is strongly sigmoidal to the densities&#xD;
of red grouse Lagopus lagopus scoticus, but no type III shape was detected in the response to&#xD;
the two main prey species, field vole Microtus agrestis and meadow pipit Anthus pratensis. The&#xD;
impact of using Bayesian or frequentist models on the resulting functional response is discussed.&#xD;
In chapter 5, no functional response could be fitted to the data on harp seal predation. Possible&#xD;
reasons are discussed, including poor data quality or a lack of relevance of the available data for&#xD;
informing a behavioural functional response model.&#xD;
I conclude with a comparison of the role that functional responses play in behavioural, population&#xD;
and community ecology and emphasise the need for further research into unifying these different&#xD;
approaches to understanding predation with particular reference to predator movement.&#xD;
In an appendix, I evaluate the possibility of using a functional response for inferring the abun-&#xD;
dances of prey species from performance indicators of generalist predators feeding on these prey.&#xD;
I argue that this approach may be futile in general, because a generalist predator's energy intake&#xD;
does not depend on the density of any single of its prey, so that the possibly unknown densities&#xD;
of all prey need to be taken into account.</summary>
    <dc:date>2006-01-01T00:00:00Z</dc:date>
    <dc:creator>Asseburg, Christian</dc:creator>
    <dc:description>Multi-species functional response models are required to model the predation of generalist preda-&#xD;
tors, which consume more than one prey species. In chapter 2, a new model for the multi-species&#xD;
functional response is presented. This model can describe generalist predators that exhibit func-&#xD;
tional responses of Holling type II to some of their prey and of type III to other prey. In chapter&#xD;
3, I review some of the theoretical distinctions between Bayesian and frequentist statistics and&#xD;
show how Bayesian statistics are particularly well-suited for the fitting of functional response&#xD;
models because uncertainty can be represented comprehensively. In chapters 4 and 5, the multi-&#xD;
species functional response model is fitted to field data on two generalist predators: the hen&#xD;
harrier Circus cyaneus and the harp seal Phoca groenlandica. I am not aware of any previous&#xD;
Bayesian model of the multi-species functional response that has been fitted to field data.&#xD;
The hen harrier's functional response fitted in chapter 4 is strongly sigmoidal to the densities&#xD;
of red grouse Lagopus lagopus scoticus, but no type III shape was detected in the response to&#xD;
the two main prey species, field vole Microtus agrestis and meadow pipit Anthus pratensis. The&#xD;
impact of using Bayesian or frequentist models on the resulting functional response is discussed.&#xD;
In chapter 5, no functional response could be fitted to the data on harp seal predation. Possible&#xD;
reasons are discussed, including poor data quality or a lack of relevance of the available data for&#xD;
informing a behavioural functional response model.&#xD;
I conclude with a comparison of the role that functional responses play in behavioural, population&#xD;
and community ecology and emphasise the need for further research into unifying these different&#xD;
approaches to understanding predation with particular reference to predator movement.&#xD;
In an appendix, I evaluate the possibility of using a functional response for inferring the abun-&#xD;
dances of prey species from performance indicators of generalist predators feeding on these prey.&#xD;
I argue that this approach may be futile in general, because a generalist predator's energy intake&#xD;
does not depend on the density of any single of its prey, so that the possibly unknown densities&#xD;
of all prey need to be taken into account.</dc:description>
  </entry>
  <entry>
    <title>Reconstruction of foliations from directional information</title>
    <link rel="alternate" href="http://hdl.handle.net/10023/158" />
    <author>
      <name>Yeh, Shu-Ying</name>
    </author>
    <id>http://hdl.handle.net/10023/158</id>
    <updated>2007-03-14T10:43:14Z</updated>
    <published>2007-06-01T00:00:00Z</published>
    <summary type="text">Abstract: In many areas of science, especially geophysics, geography and&#xD;
meteorology, the data are often directions or axes rather than&#xD;
scalars or unrestricted vectors. Directional statistics considers&#xD;
data which are mainly unit vectors lying in two- or&#xD;
three-dimensional space (R² or R³). One&#xD;
way in which directional data arise is as normals to foliations. A&#xD;
(codimension-1) foliation of {R}^{d} is a system&#xD;
of non-intersecting (d-1)-dimensional surfaces filling out the&#xD;
whole of {R}^{d}. At each point z of {R}^{d}, any given codimension-1 foliation determines a&#xD;
unit vector v normal to the surface through z.&#xD;
The problem considered here is that of reconstructing the foliation&#xD;
from observations ({z}{i}, {v}{i}), i=1,...,n. One&#xD;
way of doing this is rather similar to fitting smooth splines to&#xD;
data. That is, the reconstructed foliation has to be as close to the&#xD;
data as possible, while the foliation itself is not too rough. A&#xD;
tradeoff parameter is introduced to control the balance between&#xD;
smoothness and&#xD;
closeness. The approach used in this thesis is to take the surfaces to be&#xD;
surfaces of constant values of a suitable real-valued function h&#xD;
on {R}^{d}. The problem of reconstructing a foliation is&#xD;
translated into the language of Schwartz distributions and a deep&#xD;
result in the theory of distributions is used to give the&#xD;
appropriate general form of the fitted function h. The model&#xD;
parameters are estimated by a simplified Newton method. Under appropriate distributional assumptions on v{1},...,v{n}, confidence regions for the true normals&#xD;
are developed and estimates of concentration are given.</summary>
    <dc:date>2007-06-01T00:00:00Z</dc:date>
    <dc:creator>Yeh, Shu-Ying</dc:creator>
    <dc:description>In many areas of science, especially geophysics, geography and&#xD;
meteorology, the data are often directions or axes rather than&#xD;
scalars or unrestricted vectors. Directional statistics considers&#xD;
data which are mainly unit vectors lying in two- or&#xD;
three-dimensional space (R² or R³). One&#xD;
way in which directional data arise is as normals to foliations. A&#xD;
(codimension-1) foliation of {R}^{d} is a system&#xD;
of non-intersecting (d-1)-dimensional surfaces filling out the&#xD;
whole of {R}^{d}. At each point z of {R}^{d}, any given codimension-1 foliation determines a&#xD;
unit vector v normal to the surface through z.&#xD;
The problem considered here is that of reconstructing the foliation&#xD;
from observations ({z}{i}, {v}{i}), i=1,...,n. One&#xD;
way of doing this is rather similar to fitting smooth splines to&#xD;
data. That is, the reconstructed foliation has to be as close to the&#xD;
data as possible, while the foliation itself is not too rough. A&#xD;
tradeoff parameter is introduced to control the balance between&#xD;
smoothness and&#xD;
closeness. The approach used in this thesis is to take the surfaces to be&#xD;
surfaces of constant values of a suitable real-valued function h&#xD;
on {R}^{d}. The problem of reconstructing a foliation is&#xD;
translated into the language of Schwartz distributions and a deep&#xD;
result in the theory of distributions is used to give the&#xD;
appropriate general form of the fitted function h. The model&#xD;
parameters are estimated by a simplified Newton method. Under appropriate distributional assumptions on v{1},...,v{n}, confidence regions for the true normals&#xD;
are developed and estimates of concentration are given.</dc:description>
  </entry>
</feed>

