RESUME Les données phytogéographiques reflètent la variabilité spatiale de la diversité des espèces et constituent donc un outil important dans le développement des politiques de conservation. Afin de stimuler et de valoriser le concept des systèmes phytogéographiques, cette étude dont le thème est «Analyse des structures spatiales des données de distribution phytogéographique des Acanthaceae en Afrique centrale» s’est donnée pour but (1) d’analyser la distribution spatiale de la famille des Acanthaceae en Afrique Centrale (R.D. Congo, Rwanda, Burundi) ; (2) de comparer cette distribution avec les théories phytogéographiques de Robyns (1948), White (1979, 1986) et Ndjele (1988); (3) d’utiliser les modèles de distribution spatiale comme support (outil) pour évaluer l'impact humain sur le paysage et la diversité; (4) d’identifier les espèces indicatrices potentielles des territoires phytogéographiques; (5) de mettre en évidence le phénomène de vicariance; et (6) de quantifier l’impact de la fragmentation du paysage forestier en Afrique centrale. Dans cette étude, deux niveaux de résolution spatiale ont été considérés: les systèmes phytogéographiques et les systèmes de maillage. Un système d’information géographique a été utilisé pour réaliser des cartes de distribution spatiale de chaque espèce. Le choix des Acanthaceae de l’herbier du Jardin Botanique National de Belgique (BR), a été dicté par le faite qu’elle a subit une révision systématique et par le nombre important de ses échantillons. L’aspect floristique a révélé 9181 échantillons, récoltés de 1888 à 2001 par environ 427 collecteurs en R.D. Congo, au Rwanda et au Burundi représentant 48 genres, 310 espèces et 6362 localités. La carte de distribution spatiale de l’ensemble des échantillons a mis en évidence les niveaux de prospection. Certains territoires phytogéographiques ont été plus explorés que d’autres. Les entités phytogéographiques les plus explorées et donc les plus diversifiées sont le centre régional d’endémisme Afromontagnard, incluant la Mosaïque régional du lac Victoria, et le centre régional d’endémisme Zambézien. Les cartes de distribution de chaque espèce mettent en évidence les patrons de distribution spatiale. Certaines espèces ont une large distribution alors que d’autres sont inféodées à certaines zones spécifiques. Ces dernières, qualifiées « d’espèces uniques » ou « espèces caractéristiques » peuvent être utilisées comme des bio-indicateurs pour stimuler et valoriser le concept de systèmes phytogéographiques dans la politique de la conservation. En utilisant uniquement la famille des Acanthaceae, il a été montré que l’impact de la fragmentation du paysage forestier est très important. Les espèces inféodées à une région phytogéographique sont des espèces vulnérables. Elles peuvent disparaître si leur biotope est détruit. La distribution potentielle, basées sur les localités de récolte et les variables environnementales, ont été réalisées afin de mieux déterminer les niches écologiques des espèces et les cas de vicariance. Deux types de vicariance ont été mis en évidence à travers les systèmes phytogéographiques de Robyns (1948) et de White (1979, 1986), au niveau générique et spécifique: la vicariance écologique et la vicariance géographique. La vicariance écologique s’applique aux espèces ou sous-espèces récoltées dans les mêmes territoires phytogéographiques tandis que la vicariance géographique concerne les espèces ou sous-espèces récoltées dans des territoires phytogéographiques séparés. L’analyse des cas de vicariance a mis en relief les zones de spéciation. L'analyse de classification hiérarchique a montré que les Acanthaceae suivent mieux le système phytogéographique de White (1979, 1986) que ceux proposés par Robyns (1948) et Ndjele (1988). Pour mieux valoriser cette approche, cette méthodologie doit être appliquée à d’autres familles largement récoltée en R.D. Congo, au Rwanda et au Burundi comme la famille des Rubiaceae, des Mimosoideae, afin de (1) synchroniser toutes les bases de données pour mieux mettre en évidence le degré d’exploration, les espèces à amplitude écologique restreinte (espèces uniques) et (2) de permettre d’identifier des zones prioritaires pour la conservation. ABSTRACT Phytogeographic data reflect the spatial variability of plant diversity and constitute consequently a potential tool for conservation policy development. In order to stimulate and valorise the concept of phytogeographic systems, this dissertation entitled “Analysis of the spatial pattern of phytogeographic data of Acanthaceae in Central Africa” aims (1) to analyse the spatial distribution of the Acanthaceae family in Central Africa (Democratic Republic of the Congo, Rwanda, Burundi); (2) to compare this distribution with the known phytogeographic theories of Robyns (1948), White (1979, 1986) and Ndjele (1988); (3) to use the spatial distribution models as a tool for evaluating the human impact on landscapes and diversity; (4) to identify potential indicator species of the phytogeographic territories; (5) to evidence the phenomenon of vicariance; and (6) to quantify the impact of the fragmentation of forested landscapes in central Africa. In this study, two levels of spatial resolution have been considered: the phytogeographic systems themselves and a system of grid cells. A geographic information system has been used to draw maps of the spatial distribution of every species. The choice to analyse the Acanthaceae family of the herbarium of the National Botanical Garden of Belgium (BR) has been justified by the systematic revision of this collection and by its huge number of samples. The data set contained 9181 samples, collected between 1888 and 2001 by about 427 collectors in the Democratic Republic of the Congo, Rwanda and Burundi ; the samples represented 48 genera, 310 species and 6362 geographic positions. The maps showing the spatial distribution of all samples pooled evidenced the different levels of exploration of the study area. Certain phytogeographic territories have been explored more intensely than others. The mostly explored zones, consequently also denoted as the most diverse ones, were the Afromontane regional centre of endemism, including the regional mosaic of Lake Victoria, and the Zambezian regional center of endemism. Species distribution maps evidenced the spatial patterns of species presence. Certain species showed an overall distribution while others were clearly bound to particular territories. The latter species, denoted as “unique species” or “characteristic species” could be used as bio-indicators to stimulate and valorise the concept of the phytogeographic systems in the framework of conservation policy development. By means of the Acanthaceae family, it has been shown that the impact of forest fragmentation will be considerable; species bound to a specific phytogeographic zone are assumed vulnerable; they will disappear when their biotopes are destroyed. The potential distribution of the species, based on the geographic position of the samples and on environmental data, have been generated in order to describe more precisely the ecological niches of the species involved and to detect cases of vicariance. Two types of vicariance have been found using the phytogeographic territories of Robyns (1948) and White (1979, 1986) at the genus and the species levels: ecological vicariance and geographic vicariance; the former type involves species or subspecies observed in the same phytogeographic region while the latter type involves species and subspecies not found in the same territory. This analysis enabled us to identify zones of speciation. A cluster analyses showed that the spatial distribution of the Acanthaceae data corresponded more closely to the phytogeographic system of White (1979, 1986), than to those proposed by Robyns (1948) or Ndjele (1988). In order to valorise our approach, the current methodology should also be applied to other families widely collected in the Democratic Republic of the Congo, Rwanda and Burundi, such as the Rubiaceae or Mimosoideae families, this (1) to synchronise all data bases for a more profound understanding of the degree of exploration and of the existence of species with a limited ecological amplitude (unique species), and (2) to enable the identification of zones that should be prioritised for conservation.

One of the main reasons for the massive loss in plant species diversity is the fragmentation of habitats. In Europe, open pastures and meadows are the habitats going through the most changes during the 20th century, according to the agricultural changes. In this study vascular plants were invented at five different islands in the Lurö archipelago, Vänern, Sweden. The aim of the study was to sort out whether the diversity of plants has gone through any changes in abandoned managed grasslands compared to continuous managed grasslands. The aim was also to study if a change in the landscape has made any differences for the species development or decline. The results indicate that the number of vascular plants were significantly lower in the abandoned areas than the still managed areas. Results, only from the field layer, showed same results. There was a significant difference between the number of indicators in managed lands than lands that were abandoned for 30-40 and 100 years ago. A comparison from earlier study, from a time when grazing had just ceased at some islands, showed a significant difference in plant species diversity between the years. Just a few decades can impoverish a plant community that might have taken hundreds or even thousands of years to build up. To preserve the biological diversity formed by human impact, one must continue managing the lands. / En av de största orsakerna till den massiva förlusten av växtarter, är fragmenteringen av habitat. I Europa är öppna naturbetesmarker och ängar de habitat som genomgått de största förändringarna i och med jordbrukslandskapets omstruktureringar under 1900-talet. I den här studien inventerades kärlväxter på 5 olika öar i kulturlandskapet Lurö skärgårds naturreservat. Syftet var att ta reda på hur diversiteten bland kärlväxtarter skiljer sig mellan hävdade gräsmarker och f.d. gräsmarker där hävd upphört och hur ett förändrat landskap spelat roll för artantalets utveckling eller tillbakagång. Resultat visade att antalet kärlväxter var signifikant lägre i marker som slutat hävdas, än marker som fortfarande hävdas. Även jämförelser i enbart fältskiktet visade ett signifikant högre artantal hos välhävdade marker än marker där hävd upphört. Det fanns en signifikant skillnad mellan antalet indikatorarter i marker som var under hävd och marker som slutat hävdas för 30-40 år sedan, kontra 100 år sedan. Vid jämförelser med en tidigare studie, som ägt rum precis efter att hävden upphört på ett flertal lokaler visade resultat att det fanns en signifikant skillnad i artantal mellan de båda åren. På några få decennier kan ett helt växtsamhälle som byggts upp under hundratals eller kanske till och med tusentals år utarmas. För att bevara den biologiska mångfald som formas av en störningsregim beroende av människans inverkan, måste hävd fortsätta kontinuerligt.

Den här studien undersöker hur vegetationen förändras mellan 1979 och 2010 i området som idag är Hornborgasjöns naturreservat. Sjösänkningar i området ledde till att ett igenväxt träskområde ersatte en viktig vattenreservoar och närsaltfälla. Restaureringsarbetet under 80-talet var banbrytande och antagligen ett av vår tids mest omfattande naturvårdsarbete. Studien svarar också på om restaureringen uppnådde sitt mål och om resultatet blev som man tänkt sig. I arbetet skapades en aktuell vegetationskarta för 2010, denna jämfördes med en i arbetet digitaliserad vegetationskarta från 1979. Kartbilder skapades och justerades i ArcGIS och vegetationsytornas area framtogs för att möjliggöra en vegetationsanalys mellan kartorna. Vegetationsförändringarna i området visade sig vara omfattande mellan 1979 och 2010, där tydlig igenväxtningsmark med stora monokulturer ersattes med öppnare marker där vegetationstyperna var spridda över hela området i mindre ytor. Mångfalden i området ökade liksom vattenytan. Vattenytans stora utbredning efter restaureringen blev den stora överraskningen tillsammans med att sävvegetationen helt försvann. Undervattensvegetationens stora spridning räddade dock restaureringens syfte att gynna fågellivet trots sävruggarnas frånvaro. En ny viktig naturtyp framkom i vegetationskartan 2010, öppet vatten med död vegetation, där stora delar av vegetationstypen består av den för många hotade arter vitala biotopen död sumplövskog. / This study investigates vegetation changes in the nature reserve of Lake Hornborga between 1979 and 2010. Lowering of the surface of the lake had changed an important water reserve and nutritive salt trap into an overgrown fen and during the 80's a total pioneering restoration, perhaps the most important work of nature conservation of our time, was made. This study claims to answer if the restoration was successful and if its goals were reached. A current vegetation map for 2010 was created and adjusted in ArcGIS and this map was compared with a vegetation map of 1979. Vegetation areas were calculated to facilitate analyses between the maps. Large-scale vegetation changes have occurred between 1979 and 2010. Overgrown fenland with monoculture vegetation has been replaced by a more open landscape with a diversified growth and an open surface of water. The large extension of open surface and the disappearance of rush vegetation are two great surprises of the restoration. Thanks to a large-scale spread of underwater vegetation the aim of furthering birdlife could be reached despite the loss of rush vegetation. A new type of vegetation area has also been created, where  open water submerges dead vegetation, one of which is a biotope of dead marsh broadleaf trees, vital to many threatened species. / Vid kontakt med Lantmäteriet har muntlig bekräftelse getts gällande tillstånd av publicering av deras upphovsrätts skyddade material, där alla högskolearbeten ges sådant tillstånd vid alla Sveriges lärosäten. I mitt arbete gäller detta figur 1.

Title from title page of PDF (University of Missouri--St. Louis, viewed March 9, 2010). Includes bibliographical references.

The chevron skink (Oligosoma homalonotum) is one of the largest, yet least observed skink species in New Zealand. The species was thought to have once been widespread in Northern New Zealand, however currently it is only found on Great Barrier and Little Barrier Islands. Great Barrier Island is the apparent stronghold for the species although it appears to be in decline there, despite a net increase in habitat. Recent studies have increased the understanding of the general ecology of the species, however little is known about the threats to the survival of this species. This study had two main objectives; the first was to establish if rats are a threat to chevron skinks, and the second was to increase current knowledge of the species ecology. The research was undertaken in an area of extensive rodent control (Glenfern Sanctuary) and an adjacent unmanaged reserve in Port Fitzroy, on Great Barrier Island in 2008. The first objective of this study involved confirming that rat densities in the treatment (Glenfern Sanctuary) were sufficiently different to allow meaningful comparisons of chevron skink population characteristics between sites. This was achieved by determining absolute rat densities using Zippin’s removal method at four sites, and correlating these with a relative abundance measure (tracking rates) to give confidence in the observed trends. Rat densities were high (1.94 - 3.00 rats ha-1) in the control, and low (0.00 and 0.06 rats ha-1) in the treatment sites, and these correlated well with tracking rates. In light of these clear differences between the treatment and control, the population structure and condition of chevron skinks were compared between sites. The population structure showed erosion of juvenile and sub-adult size categories, which indicated differences in vulnerabilities between size categories. Physical evidence of failed rat predation was also observed in adult skinks in the unmanaged control, which confirmed that rats were interacting with chevron skinks. Although the adults survived the attacks they suffered injuries including eye damage, punctures, cuts and tail loss. Smaller skinks would be unlikely to survive such attacks due to the severity and scale of the injuries, supporting the assertions of the population structure that smaller skinks may be more vulnerable than adults. The extent of tail loss was converted to a condition index to determine if failed rat predation was more widespread in the population, than was observed by conspicuous injuries. This condition index (body-tail condition index) was stable through all size categories in the treatment, but significantly reduced in adults in the unmanaged sites. That there was no reduction in the condition of smaller skinks in the unmanaged control sites despite high rat densities suggests that interactions between rats and smaller skinks are fatal, and thus not represented in the data. Nine chevron skinks were radio-tracked to determine habitat use, home range and ranging behaviour. Habitat use of chevron skinks was similar to a previous study and demonstrated that trees, crevices and logs were important refuge sites. Chevron skinks were more likely to be found at sites with trees, crevices and debris dams. Chevron skink home ranges indicated that adults moved further away from streams than previously anticipated at this time of year, and skinks demonstrated site fidelity. There was also overlap in home ranges between individuals, and skinks with overlapping home ranges shared common refuges. During flooding events, chevron skinks exhibited an arboreal response that appears to be a behaviour specific to stream associated animals, which allows them to avoid being taken by floodwaters.

This thesis fills a research gap in our knowledge of kokako song by looking at how song evolves in multi-dialect areas. Kokako only exist in small remnant populations separated by large tracts of unsuitable land. Kokako are very poor flyers, only able to fly for approximately 100 metres at a time. In order to prevent inbreeding and a loss of genetic diversity in the remaining kokako populations, managers are carrying out translocations to establish new populations, maintain gene flow and prevent inbreeding. However, these translocations have the potential to be unsuccessful because kokako exhibit macrogeographic variation in their dialects, and tend not to breed with individuals who do not share the same dialect as them. If the purpose of the translocation is to enhance genetic diversity by having kokako from different areas breed then song is an important factor that must be dealt with. Song is extremely important to kokako for a number of reasons. Chiefly, it is hypothesised that song is their primary means of territory defence. A kokako gains all its resources from its territory, so it is imperative that they successfully defend it. Their duet song functions in territory defence, but also acts to form and maintain pair bonds. In order to try and address the problem that song causes in translocations I studied if and how song evolves in a multiple dialect area. I conducted research at Pukaha Mount Bruce, where there is a population of kokako originating from two different source populations, and thus two different dialects, Northern Mapara and Mangatutu. I looked at the Northern Mapara dialect, and recorded kokako belonging to three groups; kokako currently living in the source population, kokako that were translocated to Pukaha and kokako that were born at Pukaha. In order to determine how the song may be changing I looked at element repertoires, the levels of sharing between groups, the number of unique elements in repertoires and the syntactical and temporal characteristics of phrases. This study shows that translocation into multiple dialect areas can affect kokako song. Translocation did not affect the size of the kokako repertoire, but it seemed to affect the amount of sharing within and between different groups of kokako. Currently the level of sharing within the groups at Pukaha is lower than the level of sharing within the source Mapara population, indicating that the song may be diverging. There also seem to be more unique elements found at Pukaha, which in part explains the lack of sharing. There appears to be microgeographic variation at Pukaha, with birds clustered around the second (Mangatutu) dialect sharing less with the source population than do those kokako whose territories are lower down in the reserve. The phrases which are used are also evolving, with only one phrase truly shared among all groups. There are other phrases which show additions or deletions of elements, and so are evolving. The main change found in the phrases is the timing between elements, with six out of seven phrases examined showing changes. These results have repercussions for future kokako translocations, and the future of the Pukaha kokako. A low amount of phrase and element type sharing combined with changes of intra-phrase timing could lead to the Pukaha kokako’s inability to successfully defend their territories. This research shows how kokako song can give conservation managers information on the status of their populations in regards to interbreeding and raises questions which can be answered by further research, both at Pukaha and in other mixeddialect kokako populations.

This thesis fills a research gap in our knowledge of kokako song by looking at how song evolves in multi-dialect areas. Kokako only exist in small remnant populations separated by large tracts of unsuitable land. Kokako are very poor flyers, only able to fly for approximately 100 metres at a time. In order to prevent inbreeding and a loss of genetic diversity in the remaining kokako populations, managers are carrying out translocations to establish new populations, maintain gene flow and prevent inbreeding. However, these translocations have the potential to be unsuccessful because kokako exhibit macrogeographic variation in their dialects, and tend not to breed with individuals who do not share the same dialect as them. If the purpose of the translocation is to enhance genetic diversity by having kokako from different areas breed then song is an important factor that must be dealt with. Song is extremely important to kokako for a number of reasons. Chiefly, it is hypothesised that song is their primary means of territory defence. A kokako gains all its resources from its territory, so it is imperative that they successfully defend it. Their duet song functions in territory defence, but also acts to form and maintain pair bonds. In order to try and address the problem that song causes in translocations I studied if and how song evolves in a multiple dialect area. I conducted research at Pukaha Mount Bruce, where there is a population of kokako originating from two different source populations, and thus two different dialects, Northern Mapara and Mangatutu. I looked at the Northern Mapara dialect, and recorded kokako belonging to three groups; kokako currently living in the source population, kokako that were translocated to Pukaha and kokako that were born at Pukaha. In order to determine how the song may be changing I looked at element repertoires, the levels of sharing between groups, the number of unique elements in repertoires and the syntactical and temporal characteristics of phrases. This study shows that translocation into multiple dialect areas can affect kokako song. Translocation did not affect the size of the kokako repertoire, but it seemed to affect the amount of sharing within and between different groups of kokako. Currently the level of sharing within the groups at Pukaha is lower than the level of sharing within the source Mapara population, indicating that the song may be diverging. There also seem to be more unique elements found at Pukaha, which in part explains the lack of sharing. There appears to be microgeographic variation at Pukaha, with birds clustered around the second (Mangatutu) dialect sharing less with the source population than do those kokako whose territories are lower down in the reserve. The phrases which are used are also evolving, with only one phrase truly shared among all groups. There are other phrases which show additions or deletions of elements, and so are evolving. The main change found in the phrases is the timing between elements, with six out of seven phrases examined showing changes. These results have repercussions for future kokako translocations, and the future of the Pukaha kokako. A low amount of phrase and element type sharing combined with changes of intra-phrase timing could lead to the Pukaha kokako’s inability to successfully defend their territories. This research shows how kokako song can give conservation managers information on the status of their populations in regards to interbreeding and raises questions which can be answered by further research, both at Pukaha and in other mixeddialect kokako populations.

This thesis fills a research gap in our knowledge of kokako song by looking at how song evolves in multi-dialect areas. Kokako only exist in small remnant populations separated by large tracts of unsuitable land. Kokako are very poor flyers, only able to fly for approximately 100 metres at a time. In order to prevent inbreeding and a loss of genetic diversity in the remaining kokako populations, managers are carrying out translocations to establish new populations, maintain gene flow and prevent inbreeding. However, these translocations have the potential to be unsuccessful because kokako exhibit macrogeographic variation in their dialects, and tend not to breed with individuals who do not share the same dialect as them. If the purpose of the translocation is to enhance genetic diversity by having kokako from different areas breed then song is an important factor that must be dealt with. Song is extremely important to kokako for a number of reasons. Chiefly, it is hypothesised that song is their primary means of territory defence. A kokako gains all its resources from its territory, so it is imperative that they successfully defend it. Their duet song functions in territory defence, but also acts to form and maintain pair bonds. In order to try and address the problem that song causes in translocations I studied if and how song evolves in a multiple dialect area. I conducted research at Pukaha Mount Bruce, where there is a population of kokako originating from two different source populations, and thus two different dialects, Northern Mapara and Mangatutu. I looked at the Northern Mapara dialect, and recorded kokako belonging to three groups; kokako currently living in the source population, kokako that were translocated to Pukaha and kokako that were born at Pukaha. In order to determine how the song may be changing I looked at element repertoires, the levels of sharing between groups, the number of unique elements in repertoires and the syntactical and temporal characteristics of phrases. This study shows that translocation into multiple dialect areas can affect kokako song. Translocation did not affect the size of the kokako repertoire, but it seemed to affect the amount of sharing within and between different groups of kokako. Currently the level of sharing within the groups at Pukaha is lower than the level of sharing within the source Mapara population, indicating that the song may be diverging. There also seem to be more unique elements found at Pukaha, which in part explains the lack of sharing. There appears to be microgeographic variation at Pukaha, with birds clustered around the second (Mangatutu) dialect sharing less with the source population than do those kokako whose territories are lower down in the reserve. The phrases which are used are also evolving, with only one phrase truly shared among all groups. There are other phrases which show additions or deletions of elements, and so are evolving. The main change found in the phrases is the timing between elements, with six out of seven phrases examined showing changes. These results have repercussions for future kokako translocations, and the future of the Pukaha kokako. A low amount of phrase and element type sharing combined with changes of intra-phrase timing could lead to the Pukaha kokako’s inability to successfully defend their territories. This research shows how kokako song can give conservation managers information on the status of their populations in regards to interbreeding and raises questions which can be answered by further research, both at Pukaha and in other mixeddialect kokako populations.

This thesis fills a research gap in our knowledge of kokako song by looking at how song evolves in multi-dialect areas. Kokako only exist in small remnant populations separated by large tracts of unsuitable land. Kokako are very poor flyers, only able to fly for approximately 100 metres at a time. In order to prevent inbreeding and a loss of genetic diversity in the remaining kokako populations, managers are carrying out translocations to establish new populations, maintain gene flow and prevent inbreeding. However, these translocations have the potential to be unsuccessful because kokako exhibit macrogeographic variation in their dialects, and tend not to breed with individuals who do not share the same dialect as them. If the purpose of the translocation is to enhance genetic diversity by having kokako from different areas breed then song is an important factor that must be dealt with. Song is extremely important to kokako for a number of reasons. Chiefly, it is hypothesised that song is their primary means of territory defence. A kokako gains all its resources from its territory, so it is imperative that they successfully defend it. Their duet song functions in territory defence, but also acts to form and maintain pair bonds. In order to try and address the problem that song causes in translocations I studied if and how song evolves in a multiple dialect area. I conducted research at Pukaha Mount Bruce, where there is a population of kokako originating from two different source populations, and thus two different dialects, Northern Mapara and Mangatutu. I looked at the Northern Mapara dialect, and recorded kokako belonging to three groups; kokako currently living in the source population, kokako that were translocated to Pukaha and kokako that were born at Pukaha. In order to determine how the song may be changing I looked at element repertoires, the levels of sharing between groups, the number of unique elements in repertoires and the syntactical and temporal characteristics of phrases. This study shows that translocation into multiple dialect areas can affect kokako song. Translocation did not affect the size of the kokako repertoire, but it seemed to affect the amount of sharing within and between different groups of kokako. Currently the level of sharing within the groups at Pukaha is lower than the level of sharing within the source Mapara population, indicating that the song may be diverging. There also seem to be more unique elements found at Pukaha, which in part explains the lack of sharing. There appears to be microgeographic variation at Pukaha, with birds clustered around the second (Mangatutu) dialect sharing less with the source population than do those kokako whose territories are lower down in the reserve. The phrases which are used are also evolving, with only one phrase truly shared among all groups. There are other phrases which show additions or deletions of elements, and so are evolving. The main change found in the phrases is the timing between elements, with six out of seven phrases examined showing changes. These results have repercussions for future kokako translocations, and the future of the Pukaha kokako. A low amount of phrase and element type sharing combined with changes of intra-phrase timing could lead to the Pukaha kokako’s inability to successfully defend their territories. This research shows how kokako song can give conservation managers information on the status of their populations in regards to interbreeding and raises questions which can be answered by further research, both at Pukaha and in other mixeddialect kokako populations.

This thesis fills a research gap in our knowledge of kokako song by looking at how song evolves in multi-dialect areas. Kokako only exist in small remnant populations separated by large tracts of unsuitable land. Kokako are very poor flyers, only able to fly for approximately 100 metres at a time. In order to prevent inbreeding and a loss of genetic diversity in the remaining kokako populations, managers are carrying out translocations to establish new populations, maintain gene flow and prevent inbreeding. However, these translocations have the potential to be unsuccessful because kokako exhibit macrogeographic variation in their dialects, and tend not to breed with individuals who do not share the same dialect as them. If the purpose of the translocation is to enhance genetic diversity by having kokako from different areas breed then song is an important factor that must be dealt with. Song is extremely important to kokako for a number of reasons. Chiefly, it is hypothesised that song is their primary means of territory defence. A kokako gains all its resources from its territory, so it is imperative that they successfully defend it. Their duet song functions in territory defence, but also acts to form and maintain pair bonds. In order to try and address the problem that song causes in translocations I studied if and how song evolves in a multiple dialect area. I conducted research at Pukaha Mount Bruce, where there is a population of kokako originating from two different source populations, and thus two different dialects, Northern Mapara and Mangatutu. I looked at the Northern Mapara dialect, and recorded kokako belonging to three groups; kokako currently living in the source population, kokako that were translocated to Pukaha and kokako that were born at Pukaha. In order to determine how the song may be changing I looked at element repertoires, the levels of sharing between groups, the number of unique elements in repertoires and the syntactical and temporal characteristics of phrases. This study shows that translocation into multiple dialect areas can affect kokako song. Translocation did not affect the size of the kokako repertoire, but it seemed to affect the amount of sharing within and between different groups of kokako. Currently the level of sharing within the groups at Pukaha is lower than the level of sharing within the source Mapara population, indicating that the song may be diverging. There also seem to be more unique elements found at Pukaha, which in part explains the lack of sharing. There appears to be microgeographic variation at Pukaha, with birds clustered around the second (Mangatutu) dialect sharing less with the source population than do those kokako whose territories are lower down in the reserve. The phrases which are used are also evolving, with only one phrase truly shared among all groups. There are other phrases which show additions or deletions of elements, and so are evolving. The main change found in the phrases is the timing between elements, with six out of seven phrases examined showing changes. These results have repercussions for future kokako translocations, and the future of the Pukaha kokako. A low amount of phrase and element type sharing combined with changes of intra-phrase timing could lead to the Pukaha kokako’s inability to successfully defend their territories. This research shows how kokako song can give conservation managers information on the status of their populations in regards to interbreeding and raises questions which can be answered by further research, both at Pukaha and in other mixeddialect kokako populations.