Typescript. / Bibliography: leaves [208]-221. / xix,, 221 leaves illus., maps, tables 28 cm

During 1973 data was collected to analyze the seasonal variations of the tidal dynamics, water quality and sediments of the Alsea Estuary. A summary of historical information with a list of all known alterations to the estuary was made. A complete physical description, including the geographical setting and mixing classification of the estuary, was done. Times of high and low water and tidal ranges at three locations were measured. Tide measurements made at Waldport indicated that the published tide predictions for that location were reliable. At a location upstream of the estuary embayment noticeable damping of the tidal wave amplitude was detected during periods of high river flow and high tidal range. High water lag times were found to decrease during periods of high river flow, but low water lag times were unaffected by river flow. The tide motion was found to be a damped, partially standing wave, which altered its behavior according to the volume of water in the estuary. The high and low tide water quality parameters of salinity, temperature, dissolved oxygen, turbidity and pH were measured at 10 to 18 locations during each season to determine any seasonal changes in them. The parameters at a given location were found to be a function of river flow and tidal range. Winter and summer sediment samples were analyzed for grain size distribution, volatile solids and porosity. The sediments from the main channel exhibited characteristics of a high velocity regime and those of the north channel, a low velocity regime. / Graduation date: 1975

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The humpback whale was almost driven to extinction by commercial whaling in the Southern Ocean. Little is known about the degree of interchange among the remaining Southern Hemisphere populations. This thesis aimed to assess the connectivity among breeding grounds, feeding areas and migratory corridors of humpback whales using mitochondrial and nuclear DNA markers. The population structure of humpback whale populations in breeding grounds across the South Pacific and eastern Indian oceans was investigated, with an interest in the origins of whales in eastern Polynesia, using an extensive collection of mitochondrial DNA (mtDNA) sequences (n = 1,112; 470 base pairs in length). Samples were obtained from living whales at six breeding grounds: New Caledonia, Tonga, Cook Islands, French Polynesia (Society Islands), Colombia and western Australia. We found significant differentiation, at both the haplotype and nucleotide level, among the six breeding grounds (FST = 0.033; ΦST = 0.022) and for most pair-wise comparisons. The differentiation of the eastern Polynesia humpback whales is consistent with the hypothesis of a relic subpopulation, rather than vagrancy or colonization from known neighbouring breeding grounds. Regardless of their origin, it seems probable that islands of eastern Polynesia are now the primary breeding grounds for humpback whales feeding in the management Area VI (170°W – 120°W) of the Antarctic, as defined by the International Whaling Commission. A population of humpback whales migrates along the western South American coast, with breeding grounds mainly off Colombia and Ecuador and feeding areas off the western coast of the Antarctic Peninsula and in the channels and fjords ofsouthern Chile. We analysed the genetic relationship between humpback whales from these two summer feeding areas of the eastern South Pacific population to assess the potential heterogeneity in the migratory pattern of the population. We compared mitochondrial DNA control region sequences from 132 whales from the Antarctic Peninsula and 52 whales from the Magellan Strait areas. An AMOVA showed significant differences between the two feeding areas (FST = 0.180; ΦST = 0.169). A phylogenetic analysis showed both areas are represented in the AE clade that is only found in the Southern Hemisphere in the Colombian breeding ground. Genetic and previous demographic data (based on photo-identification) strongly suggest that both feeding areas are related to the same breeding ground but that heterogeneity exists among the feeding areas of this population, similar to that observed in the North Pacific and North Atlantic populations of humpback whales.Humpback whales migrating through eastern Australia and New Zealand have been linked with those breeding off northeastern Australia, New Caledonia, Fiji and Tonga, forming a single stock (Breeding Stock E). We investigated the relationship between the New Caledonian and Tongan breeding grounds, based on interchange of individual whales (genetically identified) and population genetic differentiation (mitochondrial DNA control region sequences and nuclear DNA microsatellites). We found significantly higher recapture probabilities within each breeding ground compared to the recapture probability between them using genetic identification, and significant differences at the population level in the FST and ΦST for mitochondrial and nuclear markers. These analyses suggest differentiation among the Breeding Stock E, supporting a proposed sub-stock division for New Caledonia (E2) and Tonga (E3). Historically, humpback whales off New Zealand coasts were caught during their migratory journeys between Antarctic feeding areas and tropical breeding grounds in the South Pacific. Here we investigated the genetic diversity of New Zealand humpback whales, comparing mitochondrial DNA control region sequence data with that from breeding grounds across the South Pacific (New Caledonia, Tonga, Cook Islands, French Polynesia and Colombia) and eastern Indian (western Australia) Oceans. We analyzed 30 samples collected around New Zealand, revealing 20 haplotypes. All haplotypes were found in New Caledonia and some were also found in other breeding grounds. New Zealand humpback whale haplotype diversity and nucleotide diversity were similar to those from the compared breeding grounds, but were significantly different at haplotype level from the Cook Islands, French Polynesia and Colombia breeding grounds. We found significant differences at haplotype level with the same three locations when a pair-wise AMOVA was performed. Three breeding grounds (western Australia, New Caledonia and Tonga) did not show significant differences at either nucleotide or haplotype levels. This genetic evidence and the available demographic data suggest a closer relationship of the New Zealand stock with New Caledonia and to a lesser extent with Tongan whales, supporting New Zealand as a primary migratory corridor for the humpback whales breeding in these western Pacific Islands.

This thesis examined the relative importance of natural and human influences to the population and assemblage dynamics of reef fishes in northeastern New Zealand. In particular, how different reef fishes responded to the implementation of no-take and partial marine reserve protection, and physical factors responsible for spatial differences in fish abundance. Included were data from prior to the establishment of a no-take marine reserve, multiple fished reference locations, biannual sampling and the use of two independent methods to provide quantitative estimates of fish abundance and size. This combination of factors is rare in studies of marine reserves was an important strategy leading to an improved understanding of the mechanisms structuring fish communities. Responses of the reef fish assemblage to changes in fishing mortality were examined at the Poor Knights Islands Marine Reserve. Full no-take marine reserve protection was implemented on the 1st Oct 1998 but for the prior 17 years, the Poor Knights Reserve comprised only two small no-take zones and allowed recreational fishing in the rest of the reserve. Following implementation of no-take marine reserve status the reef fish community changed rapidly; there were no obvious changes at either reference location. Species targeted by fishers, such as Pagrus auratus (snapper) and Caprodon longimanus (pink maomao), responded most strongly to protection. An increase in the density of some non-targeted species can probably be attributed to climatic effects, rather than a reduction in fishing pressure. A decline in the abundance of several species at the Poor Knights may have been a result of natural mortality, or competitive or predatory interactions with snapper. Along with human influences (fishing), physical variables are important in determining the distribution and abundance of reef fish. Four locations (two mainland and two island) were surveyed in northeastern New Zealand to determine spatial patterns for seven labrid species, one of the most abundant and widespread taxa of reef fish in New Zealand. The underlying mechanisms were then explored through an examination of the relationship between swimming ability (as examined through pectoral fin morphology), exposure and depth. Each of the four locations consistently displayed distinct labrid assemblages, likely due to the influence of the East Auckland Current. Regardless of location, there was a consistent depthrelated trend for most labrids and a trend for some species to be associated with certain levels of wave exposure. By analogy with tropical labrid assemblages, it was expected that there would be a clear relationship between pectoral fin aspect ratio and depth and/or exposure. However, this relationship was not strongly evident suggesting that wave exposure may not be as important for labrids on northeastern New Zealand reefs as hypothesised for tropical coral reef systems. The response of snapper, an important recreational and commercial finfish, was investigated following the cessation of all fishing at the Poor Knights. The rate of response of snapper to protection was rapid, in areas that had previously been partially protected as well as in those that had been fully protected from fishing, with the overall density of legal sized fish increasing by 7.4 times over 4 years, likely a result of recolonisation rather than recruitment. The 818% increase in snapper biomass has the potential to enhance areas outside or within the reserve through the export of biomass (eggs and/or larvae and adults) - the daily batch fecundity was 11 to 18 times higher at the Poor Knights compared to the reference locations. The effects of partial protection on reef fish were further examined at the Mimiwhangata Marine Park, an area where recreational fishing is permitted but all commercial fishing has been prohibited for 18 years. Snapper showed no difference in abundance or size between the Mimiwhangata Marine Park and adjacent control areas, with the density of snapper most similar to fished reference locations. The lack of any recovery by snapper within the Marine Park, despite the exclusion of commercial fishers and restrictions on recreational fishing, and results from the Poor Knights, indicates that partial fishing regulations are ineffective as conservation tools for protecting targeted species or for fish communities in general (i.e. through reduction in by-catch). Results from this study provide evidence that recreational fishing has significant impacts on reef fishes.

Bottlenose dolphins (Tursiops truncatus) are frequently brought into contact with humans, due to their coastal habitat use. Over the last decade there has been considerable growth in the commercial dolphin-based tourism industry. This growth exposes coastal populations to boats and swimmers. New Zealand has allowed commercial operations offering swimming with wild dolphins since 1989. Little is known about the effects of boats and swimmers on dolphin behaviour. The present study examines a population of bottlenose dolphins that utilise the Bay of Islands as part of their range along the northeastern coast of New Zealand, and their behavioural response to commercial swim-with-dolphin operations. Data were collected from an independent research boat and the commercial dolphinwatching boats from December 1996 to February 2000. Photo-identification showed a closed population of 446 (95% C.I. 418-487) dolphins, with an 81% resight rate of the 378 catalogued individuals. Group size ranged from 2 – 50 dolphins, with 80% of groups (n = 160) containing 2 - 20 dolphins. The number of groups with calves present increased from 32% (n = 17) in 1997, to 63% (n = 47) in 1999. This could be explained by the increased number of neonates born; from four in 1997, to nine in 1999. Photo-identification in areas outside the Bay of Islands showed that individuals ranged minimum distances of 82 km north, and 388 km south of the Bay of Islands. All photographs taken outside the Bay of Islands were matched to known animals, suggesting that the majority of the northeastern coastal population is seen in the Bay. With the next nearest population of bottlenose dolphins approximately 1,000 km south, these dolphins probably form an isolated population ranging along the east coast of the northeastern North Island. Habitat use by the dolphins was examined using Geographic Positioning System (GPS) points simultaneously linked to behavioural states. In total, 31 groups were followed, and 847 GPS points were recorded. Position of initial encounter was recorded for 138 groups of dolphins. There was a significant correlation between water depth and sea-surface temperature, with dolphins found in deeper waters in summer when water temperature was highest, and in shallow waters in winter when the water temperature was lowest. Only one behavioural state, slow travel, was significantly different by season. Although all behaviours were observed in all zones, dolphins had preferential habitat use throughout the four zones within the Bay. To determine the level of impact on dolphin behaviour due to boat traffic, focal-group follows using a scan sample methodology were conducted from an independent research boat. A CATMOD analysis was used to determine dolphin behaviour by season, number of boats, and group size. Dolphin behaviour differed by boat number; in particular, resting behaviour decreased as boat number increased and milling behaviour increased as boat number increased. Behaviour differed when the research boat was the only boat present. Closer examination of boat type, i.e., permitted dolphin watching boats, non-permitted tour boats, and recreational boats, found a difference in dolphin behaviour in the presence of the permitted boats when compared to the other types. Dolphins rested less and engaged in more milling behaviour when the permitted boats were present. Responses to swim attempts from the commercial boats were compared from 1994 - 1995 to 1997 - 1998. In total, 255 groups were encountered of which 36% (n = 93) were exposed to at least one swim attempt. Successful swims (i.e., where at least one dolphin remained within 5 m of at least one swimmer) decreased from 48% in 1994 - 1995 to 34% in 1997 - 1998 and avoidance responses increased from 22% to 31%. Dolphin response varied according to swimmer placement from the boats. The ‘in path’ placement had the highest level of avoidance. Only ‘line abreast’ placement resulted in a decrease in avoidance. Based on the photo-identification sighting records, it was estimated that an average dolphin was exposed to 31 swim attempts per year. This suggests that individual dolphins have, with cumulative experience, become sensitised to swim attempts. If a swim attempt was successful, on average, it involved 19% of the group. Juveniles were more likely to interact with swimmers than adults. The present study suggests that the wide-ranging population of bottlenose dolphins that frequents the Bay of Islands is exposed to levels of tourism which can affect the dolphins behaviour. In particular, the permitted boats’ presence results in decreased resting behaviour by the dolphins. The apparent sensitisation of this population to swim attempts, and the relatively small number of individual dolphins that interact with swimmers, are grounds for concern about the long-term impact of interactions. Ongoing monitoring of this populations’ response to swimmers and boats, combined with a precautionary approach to management of boats and swimmers, are recommended.