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  <channel rdf:about="http://hdl.handle.net/10023/167">
    <title>DSpace Collection:</title>
    <link>http://hdl.handle.net/10023/167</link>
    <description />
    <items>
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        <rdf:li rdf:resource="http://hdl.handle.net/10023/3463" />
        <rdf:li rdf:resource="http://hdl.handle.net/10023/3414" />
        <rdf:li rdf:resource="http://hdl.handle.net/10023/1635" />
        <rdf:li rdf:resource="http://hdl.handle.net/10023/579" />
        <rdf:li rdf:resource="http://hdl.handle.net/10023/391" />
        <rdf:li rdf:resource="http://hdl.handle.net/10023/174" />
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    </items>
    <dc:date>2013-04-17T15:56:00Z</dc:date>
  </channel>
  <item rdf:about="http://hdl.handle.net/10023/3463">
    <title>Estimating whale abundance using sparse hydrophone arrays</title>
    <link>http://hdl.handle.net/10023/3463</link>
    <description>Abstract: Passive acoustic monitoring has been used to investigate many aspects of marine mammal ecology, although methods to estimate absolute abundance and density using acoustic data have only been developed in recent years.  The instrument configuration in an acoustic survey determines which abundance estimation methods can be used.  Sparsely distributed arrays of instruments are useful because wide geographic areas can be covered.  However, instrument spacing in sparse arrays is such that the same vocalisation will not be detected on multiple instruments, excluding the use of some abundance estimation methods.  The aim of this thesis was to explore cetacean abundance and density estimation using novel sparse array datasets, applying existing methods where possible, or developing new approaches.&#xD;
&#xD;
The wealth of data collected by sparse arrays was demonstrated by analysing a 10-year dataset collected by the U.S. Navy’s Sound Surveillance System in the north-east Atlantic.  Spatial and temporal patterns of blue (Balaenoptera musculus) and fin whale (Balaenoptera physalus) vocal activity were investigated using generalised additive models.&#xD;
&#xD;
Distance sampling-based methods were applied to fin whale calls recorded by an array of Ocean Bottom Seismometers in the north-east Atlantic.  Estimated call density was 993 calls/1000 km².hr⁻¹ (CV: 0.39).  Animal density could not be estimated because the call rate was unknown.  Further development of the call localisation method is required so the current density estimate may be biased.  Furthermore, analysing a single day of data resulted in a high variance estimate.  &#xD;
&#xD;
Finally, a new simulation-based method developed to estimate density from single hydrophones was applied to blue whale calls recorded in the northern Indian Ocean.  Estimated call density was 3 calls/1000 km².hr⁻¹ (CV: 0.17).  Again, density of whales could not be estimated as the vocalisation rate was unknown.  Lack of biological knowledge poses the greatest limitation to abundance and density estimation using acoustic data.</description>
    <dc:date>2012-06-20T00:00:00Z</dc:date>
    <dc:creator>Harris, Danielle V.</dc:creator>
    <dc:description>Passive acoustic monitoring has been used to investigate many aspects of marine mammal ecology, although methods to estimate absolute abundance and density using acoustic data have only been developed in recent years.  The instrument configuration in an acoustic survey determines which abundance estimation methods can be used.  Sparsely distributed arrays of instruments are useful because wide geographic areas can be covered.  However, instrument spacing in sparse arrays is such that the same vocalisation will not be detected on multiple instruments, excluding the use of some abundance estimation methods.  The aim of this thesis was to explore cetacean abundance and density estimation using novel sparse array datasets, applying existing methods where possible, or developing new approaches.&#xD;
&#xD;
The wealth of data collected by sparse arrays was demonstrated by analysing a 10-year dataset collected by the U.S. Navy’s Sound Surveillance System in the north-east Atlantic.  Spatial and temporal patterns of blue (Balaenoptera musculus) and fin whale (Balaenoptera physalus) vocal activity were investigated using generalised additive models.&#xD;
&#xD;
Distance sampling-based methods were applied to fin whale calls recorded by an array of Ocean Bottom Seismometers in the north-east Atlantic.  Estimated call density was 993 calls/1000 km².hr⁻¹ (CV: 0.39).  Animal density could not be estimated because the call rate was unknown.  Further development of the call localisation method is required so the current density estimate may be biased.  Furthermore, analysing a single day of data resulted in a high variance estimate.  &#xD;
&#xD;
Finally, a new simulation-based method developed to estimate density from single hydrophones was applied to blue whale calls recorded in the northern Indian Ocean.  Estimated call density was 3 calls/1000 km².hr⁻¹ (CV: 0.17).  Again, density of whales could not be estimated as the vocalisation rate was unknown.  Lack of biological knowledge poses the greatest limitation to abundance and density estimation using acoustic data.</dc:description>
  </item>
  <item rdf:about="http://hdl.handle.net/10023/3414">
    <title>Quantifying biodiversity trends in time and space</title>
    <link>http://hdl.handle.net/10023/3414</link>
    <description>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.</description>
    <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>
  </item>
  <item rdf:about="http://hdl.handle.net/10023/1635">
    <title>Bayesian modelling of integrated data and its application to seabird populations</title>
    <link>http://hdl.handle.net/10023/1635</link>
    <description>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.</description>
    <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>
  </item>
  <item rdf:about="http://hdl.handle.net/10023/579">
    <title>Acoustic and ecological investigations into predator-prey interactions between Antarctic krill (Euphausia superba) and seal and bird predators</title>
    <link>http://hdl.handle.net/10023/579</link>
    <description>Abstract: 1. Antarctic krill (Euphausia superba) form aggregations known as swarms that vary greatly in size and density. Six acoustic surveys were conducted as part of multidisciplinary studies at two study sites, the western and eastern core boxes (WCB and ECB), during the 1997, 1998 and 1999 austral summers, at South Georgia. A quantitative, automated, image processing algorithm was used to identify swarms, and calculate swarm descriptors, or metrics. In contrast to acoustic surveys of aggregations of other pelagic species, a strong correlation (r = 0.88, p = 0.02, 95% C.I.= 0.24 to 0.99) between the number of krill swarms and the mean areal krill density [rho.hat] was found.  Multivariate analysis was used to partition swarms into three types, based on contrasting morphological and internal krill density parameters. Swarm types were distributed differently between inter-surveys and between on and off-shelf regions. &#xD;
&#xD;
This swarm type variation has implications for krill predators, by causing spatial  heterogeneity in swarm detectability, suggesting that for optimal foraging to occur, predators must engage in some sort of adaptive foraging strategy. &#xD;
&#xD;
2. Krill predator-prey interactions were found to occur at multiple spatial and temporal scales, in a nested, or hierarchical structure. At the largest inter-survey scale, an index of variability, I, was developed to compare variation in survey-scale predator sightings, sea temperature and [rho.hat].  Using I and a two-way ANOVA, core box, rather than year, was found to be a more important factor in determining species distribution.  The absence of Blue-petrels (Halobaena caerulea) and the elevated number of Antarctic fur seals (Arctocephalus gazella) suggest that 1998 was a characterised by colder than average water surrounding South Georgia, and a high [rho.hat] in the ECB. At the smaller, intra-survey scales (&lt;80 km, &lt;5 day), the  characteristic scale (distances in which &#xD;
predator group size, or krill density were similar, L_s) were determined.  For krill and predators L_s varied by survey and the L_s of krill also varied by depth within a survey.  Overlap in L_s were stronger between predator species than between a predator species and krill, indicating predators were taking foraging cues from the activity of predators, rather than from the underlying krill distribution.  No relationship was found between swarm characteristics and predator activity, suggesting either there is no relationship between krill swarms and predators, or that the predator and acoustic observation techniques may not be appropriate to detect such a relationship.&#xD;
&#xD;
3. To overcome the 2-D sampling limitations of conventional echosounders, a multibeam echosounder (MBE) observed entire swarms in three-dimensions.  Swarms found in the nearshore environment of Livingston Island situated in the South Shetland Islands, exhibited only a narrow range of surface area to volume ratios or roughnesses (R = 3.3, CV = 0.23), suggesting that krill adopt a consistent group behaviour to maintain swarm shape. Generalized additive models (GAM) suggested that the presence of air-breathing predators influenced the shape of a krill swarm (R decreased in the presence of predators: the swarm became more spherical).  A 2D distance sampling framework was used to estimate the abundance, N, and associated variance of krill swarms. This technique took into account angular and range detectability (half-normal, [sigma_r.hat] = 365.00 m, CV = 0.16) and determined the vertical distribution of krill swarms to be best approximated by a beta-distribution ([alpha.hat] = 2.62, [CV.hat] = 0.19;   [beta.hat] = 2.41, [CV.hat] = 0.15), giving the abundance of swarms in survey region as [N.hat] = 5,062 ([CV.hat] = 0.35).  This research represents a substantial contribution to developing estimation of pelagic biomass using MBEs.&#xD;
&#xD;
4. When using a single- or split-beam missing pings occur when the transmit or receive cycles are interrupted, often by aeration of the water column, under the echosounder transducer during rough weather. A thin-plate regression spline based approach was used to model the missing krill data, with knots chosen using a branch and bound algorithm. This method performs well for acoustic observations of krill swarms where data are tightly clustered and change rapidly. For these data the technique outperformed the standard MGCV GAM, and the technique is applicable for estimating acoustically derived biomass from line transect surveys.</description>
    <dc:date>2008-11-27T00:00:00Z</dc:date>
    <dc:creator>Cox, Martin James</dc:creator>
    <dc:description>1. Antarctic krill (Euphausia superba) form aggregations known as swarms that vary greatly in size and density. Six acoustic surveys were conducted as part of multidisciplinary studies at two study sites, the western and eastern core boxes (WCB and ECB), during the 1997, 1998 and 1999 austral summers, at South Georgia. A quantitative, automated, image processing algorithm was used to identify swarms, and calculate swarm descriptors, or metrics. In contrast to acoustic surveys of aggregations of other pelagic species, a strong correlation (r = 0.88, p = 0.02, 95% C.I.= 0.24 to 0.99) between the number of krill swarms and the mean areal krill density [rho.hat] was found.  Multivariate analysis was used to partition swarms into three types, based on contrasting morphological and internal krill density parameters. Swarm types were distributed differently between inter-surveys and between on and off-shelf regions. &#xD;
&#xD;
This swarm type variation has implications for krill predators, by causing spatial  heterogeneity in swarm detectability, suggesting that for optimal foraging to occur, predators must engage in some sort of adaptive foraging strategy. &#xD;
&#xD;
2. Krill predator-prey interactions were found to occur at multiple spatial and temporal scales, in a nested, or hierarchical structure. At the largest inter-survey scale, an index of variability, I, was developed to compare variation in survey-scale predator sightings, sea temperature and [rho.hat].  Using I and a two-way ANOVA, core box, rather than year, was found to be a more important factor in determining species distribution.  The absence of Blue-petrels (Halobaena caerulea) and the elevated number of Antarctic fur seals (Arctocephalus gazella) suggest that 1998 was a characterised by colder than average water surrounding South Georgia, and a high [rho.hat] in the ECB. At the smaller, intra-survey scales (&lt;80 km, &lt;5 day), the  characteristic scale (distances in which &#xD;
predator group size, or krill density were similar, L_s) were determined.  For krill and predators L_s varied by survey and the L_s of krill also varied by depth within a survey.  Overlap in L_s were stronger between predator species than between a predator species and krill, indicating predators were taking foraging cues from the activity of predators, rather than from the underlying krill distribution.  No relationship was found between swarm characteristics and predator activity, suggesting either there is no relationship between krill swarms and predators, or that the predator and acoustic observation techniques may not be appropriate to detect such a relationship.&#xD;
&#xD;
3. To overcome the 2-D sampling limitations of conventional echosounders, a multibeam echosounder (MBE) observed entire swarms in three-dimensions.  Swarms found in the nearshore environment of Livingston Island situated in the South Shetland Islands, exhibited only a narrow range of surface area to volume ratios or roughnesses (R = 3.3, CV = 0.23), suggesting that krill adopt a consistent group behaviour to maintain swarm shape. Generalized additive models (GAM) suggested that the presence of air-breathing predators influenced the shape of a krill swarm (R decreased in the presence of predators: the swarm became more spherical).  A 2D distance sampling framework was used to estimate the abundance, N, and associated variance of krill swarms. This technique took into account angular and range detectability (half-normal, [sigma_r.hat] = 365.00 m, CV = 0.16) and determined the vertical distribution of krill swarms to be best approximated by a beta-distribution ([alpha.hat] = 2.62, [CV.hat] = 0.19;   [beta.hat] = 2.41, [CV.hat] = 0.15), giving the abundance of swarms in survey region as [N.hat] = 5,062 ([CV.hat] = 0.35).  This research represents a substantial contribution to developing estimation of pelagic biomass using MBEs.&#xD;
&#xD;
4. When using a single- or split-beam missing pings occur when the transmit or receive cycles are interrupted, often by aeration of the water column, under the echosounder transducer during rough weather. A thin-plate regression spline based approach was used to model the missing krill data, with knots chosen using a branch and bound algorithm. This method performs well for acoustic observations of krill swarms where data are tightly clustered and change rapidly. For these data the technique outperformed the standard MGCV GAM, and the technique is applicable for estimating acoustically derived biomass from line transect surveys.</dc:description>
  </item>
  <item rdf:about="http://hdl.handle.net/10023/391">
    <title>Incorporating measurement error and density gradients in distance sampling surveys</title>
    <link>http://hdl.handle.net/10023/391</link>
    <description>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.</description>
    <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>
  </item>
  <item rdf:about="http://hdl.handle.net/10023/174">
    <title>A Bayesian approach to modelling field data on multi-species predator prey-interactions</title>
    <link>http://hdl.handle.net/10023/174</link>
    <description>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.</description>
    <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>
  </item>
</rdf:RDF>

