This thesis uses molecular genetics as a tool to uncover information about the population structure and genetic variation in Hector’s dolphin (Cephalorhynchus hectori), to track population declines and to assess the evolutionary origins and taxonomic status of this species. A high-resolution genetic analysis of population structure was considered important for the determination of population boundaries and delimitation of conservation management units due to potentially unsustainable fisheries-related mortality. Population structure and dispersal rates were assessed using 281 samples collected from individual Hector’s dolphins of ten population groups representing the known geographic range of this species. Variation among mitochondrial DNA sequences (ΦST = 0.545) and microsatellite allele frequencies at six loci (RST = 0.252) indicated the presence of four genetically isolated regional populations, North Island (n = 29), East Coast South Island (n = 110), West Coast South Island (n = 122) and South Coast South Island (n = 19). Significant levels of genetic differentiation were not detected within local sub-populations of the East Coast and West Coast regional populations. However, the estimated geneflow between these sub-populations fitted a one-dimensional stepping-stone model (r2 = 0.6225) suggesting a vulnerability of local populations to fragmentation. A measure of expected mtDNA diversity (Tajima’s D statistic) suggested decline in eight of the ten populations. Microsatellite heterozygosity was also lower than expected in the East Coast and North Island regions, suggesting either further regional sub-structuring (Wahlund effect), loss of diversity due to population decline or the presence of null alleles. Examination of all Hector’s dolphin museum specimens of known origin (n = 55) enabled comparison of historic (1870 - 1987) genetic diversity to contemporary (1988 – 1999) diversity in two regional populations to assess the possibility that these populations have undergone recent declines. Over the last 20 years the North Island population has been reduced from at least three lineages (h = 0.41) to a single lineage (h = 0, p < 0.05). The diversity of the East Coast, South Island population has declined significantly from h = 0.65 to h = 0.35 (p < 0.05). These results suggest that the low abundance currently observed is due to recent population declines and that the North Island population is threatened with extinction in the near future. Based on a trend analysis of the mtDNA, it can be predicted that the East Coast South Island population may lose all mtDNA diversity within the next 20 years. Alternatively, detection of a one dimensional dispersal pattern may indicate that some populations are at risk of extirpation while others may not be in decline. If this is the case then the East Coast regional population is at risk of fragmentation. On a wider evolutionary scale, Hector’s dolphin is one of four species of the genus Cephalorhynchus, all of which suffer fisheries–related mortality. To describe the origin and radiation of these species, 485 bp of the mitochondrial DNA control region was sequenced from 320 individuals (including previously sequenced 200 Hector’s dolphins) representing nine of the ten species in the sub-family Lissodelphininae. The hypotheses that either Cephalorhynchus is a monophyletic genus or that the four species have arisen separately from pelagic Lissodelphine species and have converged morphologically were tested. The mtDNA phylogeny supported the monophyly of the genus and suggested that the genus Cephalorhynchus originated in the waters of South Africa and, following the West Wind Drift, colonised New Zealand and then South America. Secondary radiations resulting in two genetically isolated populations were found for the Kerguelen Island Commerson’s dolphin and the North Island Hector’s dolphin. A comparison of the genetic differentiation between the Commerson’s dolphins of the Kerguelen Islands (n = 11) and the coast of South America (n = 35), and between the North Island (n = 14) and South Island (n = 185) Hector’s dolphins, was conducted in order to assess the conservation and taxonomic status of these populations. A single fixed substitution in the mtDNA control region was diagnostic for the Kerguelen Island compared to South America (FST = 0.306, ΦST = 0.602) and the North Island compared to the South Island (FST = 0.442, ΦST = 0.495). Population differentiation of four microsatellite alleles (including unique alleles in each of the four populations) between the Kerguelen Island and South American Commerson’s dolphin (FST = 0.036, RST = 0.0493) and between the North and South Island Hector’s dolphins (FST = 0.391, RST = 0.3197) indicated restricted nuclear as well as maternal geneflow. These data, combined with additional evidence of morphological and geographic isolation, indicated that the Kerguelen Island Commerson’s dolphin and the North Island Hector’s dolphin are likely to be reproductively isolated from their alternate con-specific populations. Examination of various species concepts and definitions of conservation units leads to the conclusion that these four populations should each be considered unique at the subspecies level for the purposes of management, protection and evolutionary potential. These results lead to the conclusion that the Hector’s dolphin consists of highly subdivided populations. As a result of this and a low reproductive potential, Hector’s dolphin populations are vulnerable to extirpation through even low levels of human induced mortality. To manage such populations, it is appropriate to consider each of the two islands as separate sub-species. Within the South Island, the populations may be further subdivided into three demographically independent Management Units – the East, West and South Coasts. The South Coast management unit is vulnerable due to its low abundance and isolation and requires further investigation. Population modelling will need to reflect the fact that the local populations within the East and West coast regions share only limited dispersal with immediately adjacent populations and are thus susceptible to fragmentation. These results also show that the population declines of the East Coast South Island and the North Island populations are of recent origin thus implicating fisheries-related mortality as the principal threat to Hector’s dolphin. To prevent further decline or fragmentation of South Island populations more stringent control of inshore gillnet fisheries is required. By contrast, current decline of the North Island population may be a result of inbreeding depression. Given the low abundance and rapid decline of the North Island population, it is imperative to evaluate the potential for inbreeding depression while continuing to mitigate all human-related threats.

Various aspects of metabolism and physiology were investigated during the ontogeny of yellowtail kingfish (Seriola lalandi), a fish of growing aquaculture importance in both New Zealand and other countries. Incubation experiments between 18-24°C showed that developing eggs and larvae were heavily influenced by temperature. It appeared that at warmer temperatures larvae hatched smaller but grew on the yolk sac, whereas at cooler temperatures larvae grew inside the chorion. Oxygen consumption data supported this, with a negative correlation found between total embryonic oxygen consumption and temperature. A mechanism was proposed to explain the differential effect of temperature on ontogeny and growth. Like other marine fish with pelagic eggs, yellowtail kingfish were found to be heavily reliant on free amino acids as a source of energy. At 23°C the pattern of substrate utilisation in eggs was considerably different from that at 17-21°C, indicating that 23°C exceeded the tolerance for normal development. Inter-individual aggression by large individuals was associated with the development of size heterogeneity in juveniles. Although this aggression also affected the survival of smaller juveniles, it was not the primary agent of much of the mortality that occurs during this phase, as many of these individuals were on a degenerate developmental trajectory. Yellowtail kingfish fingerlings used for ongrowing were robust to the stressors imposed by live transport. The ontogenetic development of metabolic rate from 0.6 mg-2.2 kg did not follow the same scaling exponent as that observed for mammalian models of allometry, and has implications for interspecific studies of mass-dependent metabolism.

The Chilean oyster, Tiostrea chilensis, is a commercially important species that is native to New Zealand and the Pacific Coast of South America. The description of the variability in life history characteristics among populations of the Chilean oyster is fundamental to understanding its biology and may help in solving some of the problems encountered in culturing this species. Research presented in this thesis describes some aspects of the reproductive biology of the Chilean oyster from four populations, mainly in northern New Zealand, and compares the results with previous studies from elsewhere. Similar patterns of gametogenesis were found among three study populations at Manukau Harbour, Hauraki Gulf and Foveaux Strait. Oysters were protandrous, maturing firstly as males and later also producing ova. In all three populations the majority of the contents of all the gonads were male reproductive products. There was no evidence that the sexuality of oysters alternated rhythmically as has been reported in other species of larviparous oysters. For spawning females, the often concurrent release of ripe sperm indicated the possible presence of self fertilisation. In samples of oysters examined from Foveaux strait the sexuality of oysters was found to change markedly with size. This suggested that the infection of oysters by the parasite Bonamia may not be related to their sexuality as was previously thought. At two northern populations (Hauraki Gulf and Manukau Harbour) larvae were produced from young, small oysters, and a much larger proportion of the population was brooding larvae each year than has been reported elsewhere. In both populations, larvae were being brooded, released and were settling at all times of the year, unlike other populations. The mean fertility of the Manukau Harbour oysters was the highest so far reported for any population of this species. The size of larvae in all three northern populations were smaller than has been reported for all other locations in New Zealand and chile and is thought to be related to differences in water temperatures. Overall, the results highlight the importance of investigations into populations of molluscs across their geographical range for revealing variation in life history characteristics which may be of benefit for aquaculture. / Whole document restricted, but available by request, use the feedback form to request access.

The tellinid bivalve, Macomona liliana, is important to the structure and organisation of intertidal sandflat communities in Manukau Harbour. This thesis reports on features of the reproductive, larval supply and recruitment biology of Macomona liliana in relation to environmental factors in the harbour. Macomona liliana is gonochoric. In a mid-tide population sexual maturity occurred in animals ≥ 22 mm (shell length). Spawning is asynchronous and protracted from late November to March throughout the harbour and timing of the reproductive cycle is associated with seasonal changes in environmental variables: temperature, salinity and seasonal production of phytoplankton and benthic microalgae. A visual gonad index was useful for establishing the main periods of spawning activity. Favourable habitats are at mid-tide on the large exposed sandflats characterised by well sorted fine sands. Less favourable habitats are in sheltered bays characterised by moderate-poorly sorted sands. A delay in the onset of gametogenesis in small compared to large adults (July-August of. May-June) indicates size and/or age dependent resource allocation to growth and reproduction. Adult size classes are evenly represented in favourable habitats whereas in less favourable habitats size classes are dominated by small adults. Favourable habitats have an equal sex ratio or are biased towards females whereas in less favourable habitats the converse is true. Early life-history stages are described and techniques employed to facilitate their identification in plankton and sediment samples. A spatial Taylor's Power Plot (slope, b = 1.31) demonstrates thorough mixing of larvae in the main channels. Spatial autocorrelation models confirm that densities of larvae are higher to the south of Karore Bank than to the north. The recruitment period is December to early March but varies between successive years. Physical transport processes, post-settlement migration and high levels of mortality in Boccardia syrtis tube-mats dominate recruitment patterns in the high energy environments. Larval supply and active habitat selection by settling larvae may, however, be significant determinants of population structure in sheltered bays. Generalisations are made on the effect of habitat quality on the reproduction and recruitment biology of the Manukau Harbour metapopulation.

The use of enterococci as a microbiological indicator of water quality requires an understanding of the sources, persistence, and ecology of this group of bacteria in the environment. This research describes a series of investigations undertaken to describe the abundance, occurrence, and diversity of enterococci from aquatic and terrestrial environments. A screening protocol for environmentally sourced enterococci was developed to describe species and sub-species variability. This protocol combined classical microbiological methods of selective culture and biochemical characterisation, with molecular techniques including gene probe screening for identity and RAPD-PCR for genotypic diversity. Preliminary studies on the occurrence of enterococci in terrestrial and aquatic environments suggested that these organisms are ubiquitous. However, abundance varied between individual samples taken from terrestrial (e.g. leaf litter, sand, seaweed, animal faeces) or aquatic (marine or freshwater) environments, complicating the ability to predict the enterococci load from these sources. Enumeration of enterococci from bathing beach environments indicated occasionally high levels from seaweed and sand, where levels of up to 660 CFU/100 g (wet weight) were recorded from aged and degrading seaweed but not from fresh seaweed samples. Restriction enzyme analysis (REA) of isolates from degraded seaweed indicated a dominance of clonal populations and supported the notion of replication or survival of strains. Laboratory studies conducted to investigate enterococci persistence and growth on seaweed were not conclusive, although there was some evidence to suggest enterococci replication was occurring. This was indicated by molecular fingerprinting (REA analysis), which showed that the inoculated strain persisted for the full duration of experiments (up to 28 days). The isolation of non-inoculum strains from seaweed treatments, combined with increased abundance of these strains with incubation, suggested the persistence or replication of enterococci that were naturally occurring on seaweed. To investigate the occurrence of enterococci in bathing environments a statistical analysis of Auckland Regional Council (ARC) bathing water quality data was undertaken. This analysis indicated a strong positive correlation between enterococci and turbidity, and hence turbidity may serve as a useful physical measure to indicate deteriorating water quality. Surveys of three marine bathing beaches on Auckland's North Shore (Long Bay, Mairangi Bay, and Rothesay Bay) indicated the abundance of enterococci in all bathing beach environments surveyed. These included marine and fresh water, sand, seaweed, and stream sediment, and a significant association between enterococci levels found in the sand and in the seaweed. Enterococci screening protocols were evaluated for use in describing enterococci species and sub-species diversity in bathing beach environments. This investigation showed a diversity of enterococci from all beach environmental sources, with highest levels of species diversity from marine and stream water. Enterococci diversity did not provide clues as to the sources in marine water samples. RAPD-PCR analysis and phenotypic screening of enterococci isolates did not indicate a pattern of niche-specific associations of enterococci strains, and there was no strong evidence from this study that enterococci sub-species associate with specific environments. However, the presence of identical genotypes indicated that enterococci can persist and possibly replicate in environments such as sand and seaweed. Calculation of similarity coefficients from Ent. faecalis and Ent. casseliflavus sub-species groupings indicated a greater level of sub-specific similarity between selected environments, for example, seaweed:sand, marine water:stream water, seaweed:marine water, although this was not a guarantee that environments were biologically or ecologically associated. Where an elevated level of enterococci is measured in the absence in identifiable pollution source the separation of pigmented from non-pigmented enterococci was proposed as an indicator of the environmental or faecal nature of the enterococci within the sample. Although not tested under controlled conditions, this concept was found to have good utility for discriminating sources from elevated marine bathing water samples. Enterococci from one of 13 elevated ARC marine water samples examined was shown to be environmentally derived, with 5 of the 13 samples attributed to putative human or animal faecal sources. With further validation, this concept may be a useful means of determining source.

Pacific oyster (Crassostrea gigas) farming in New Zealand has reached a point where the pressures on resources appear likely to constrain current, and future, development. To maintain industry growth, security of juvenile oyster (spat) supply and productivity gains within the existing farm leases, are becoming industry imperatives. The use of hatchery technology could achieve both of these requirements, but it is expensive to establish and maintain. The additional expense of a hatchery could be offset by the establishment of, for example, a selective breeding program to enhance oyster productivity and/or marketability. Consequently a pilot-scale oyster hatchery facility was constructed to investigate the potential for establishing hatchery production of Pacific oysters in New Zealand. This study showed that in the pilot-scale hatchery, oysters could be successfully spawned from in-season broodstock, the eggs fertilised and the resultant larvae reared through to settlement for on-growing to adult size. This process was successful for both oysters selected for morphological characteristics and those which were not. On-growing of the resultant stock indicated growth rate could be normal relative to wild caught oysters spat, although data was limited by the small scale of the experiment. However, an investigation of broodstock conditioning, to achieve out-of-season spawning, was less successful. Disease occurred and condition was lost in some broodstock, suggesting they were enduring stress within the conditioning system. The microalgal food supply was examined but the clearance rate of the microalgal species suggested they were an acceptable feed supply which agreed with previous reports of successful conditioning techniques. Comparing the pilot-scale facility in this study with descriptions of facilities which reported successful broodstock conditioning suggested that the use of a microfiltered recirculating water supply, as opposed to the more common flow-through, natural seawater systems containing a range of small size particles, limited necessary nutrient and/or maturation factors and may have had a significant impact on conditioning. The nanoplanktonic (< 10 μm), food resource, which includes key microalgal species such as Chaetoceros spp. and Isochrysis spp., is generally considered the primary food resource for suspension feeding bivalves, including C. gigas. However, the picoplanktonic fraction (< 3 μm) can provide the largest proportion of this food resource in the water column in terms of abundance and biomass. Consequently, an investigation of the in situ retention of picoplankton populations (picoeukaryotes, Synechococcus-type cyanobacteria and heterotrophic bacteria) by oysters was undertaken. Flow cytometry was used to quantify the picoplankton populations in water samples taken from the inhalant and exhalant feeding currents of individual oysters, allowing retention efficiency of the particles to be calculated. Five picoplankton populations were identifiable by flow cytometry (picoeukaryotes, heterotrophic bacteria and 3 populations tentatively identified as cyanobacteria) and accounted for a large proportion (up to 97 %) of the estimated available carbon (picoplankton + microalgae) in Kerikeri Inlet water. Generally the heterotrophic bacteria accounted for the largest proportion of the biomass with up to 564 ± 51 ng C ml-1. Retention of each picoplankton population was found to be variable and not directly related to particle concentration. Cyanobacteria (Cy2 population) were retained with the greatest efficiency (up to 42 ± 4.4 %), followed by heterotrophic bacteria (up to 38 ± 4.5 %) and picoeukaryotes (up to 12 ± 3.8 %). Overall more picoplankton biomass was retained during the summer months, of which the heterotrophic bacteria made the largest contribution in either cell number or estimated carbon retained. Tracking of the condition and constituent fractions (glycogen, lipid and protein) of the subject oysters showed that in the summer months, post-spawn, these levels were lowest, indicting a period of nutritional stress. This appeared to suggest that C. gigas was able to alter its retention efficiency to expand the range of particles captured, and consequently the available nutrient pool. The retention of greater quantities of heterotrophic bacteria may allow for the acquisition of essential nutrients required for growth and later gametogenesis (such as B vitamins). However, it is also possible that the heterotrophic bacteria mediate access to otherwise inaccessible, or inefficiently accessed, nutrient resources through their degradation of, for example, crystalline cellulose. Consequently, the microbial flora associated with the oyster gut was investigated. An initial investigation, cultivating bacteria from gut contents, showed considerable variability in the numbers of colonies present within and between samples, but was inconclusive for identifying differences in species diversity. Using culture independent histological and 16S rDNA PCR/RFLP techniques to investigate the oyster gut microflora a spirochaete flora, commonly associated with bivalve crystalline styles, was clearly present. Molecular analyses provided evidence of other bacterial in the gut. A signature RFLP band pattern was found in oysters at low tide and this generally reoccurred in oysters that had been immersed for varying lengths of time up to high tide. However, the signature RFLP pattern became more dilute as immersion time/potential feeding time extended. The isolation of culturable bacteria from the oyster gut allowed characterisation and identification of a subset of the oyster gut microflora. 16S rDNA sequence analysis from selected isolates showed a predominance of Vibrio spp. These bacteria had previously been associated with marine molluscs, including as symbionts. Characterisation of these and other isolates from oyster gut showed a diversity of attributes including the ability to degrade cellulose. This suggests the bacterial production of enzymes, such as cellulases, which have been reported by other researchers as being present in ineffectual or low native levels in oysters. Consequently the bacterial presence in the oyster gut may be essential to efficient nutrient acquisition. The results of these investigations have highlighted the potential importance of the heterotrophic bacteria to C. gigas. To date, bacteria have received relatively little attention in terms of their potential nutritive contribution to oysters, primarily due to observations that they are retained with low efficiency. However, even at low retention efficiencies the potential nutritive contribution is large due to the available abundances of heterotrophic bacteria. While the mechanisms and controls of bivalve suspension feeding have yet to be fully elucidated, the published literature indicates that selective mechanisms are available to bivalves including C. gigas and this current research suggests that even pico-sized particles, retained with apparently low efficiency, can be subject to selection. The importance of the heterotrophic bacteria to C. gigas requires further investigation as it will have implications for not only hatchery production, but also farm management, public health and environmental impact monitoring.

Orca (Orcinus orca), also known as killer whales, are more widely recognised than other marine mammals. Although they have been reported from all oceans of the world, including the seas around New Zealand, information above anecdotal notes exists for only a few places. Orca are an apex marine predator that exhibits cultural differences in diet, vocalisations, and behaviour, between and within populations. This study was established to determine baseline information on New Zealand orca and to provide recommendations for future management and conservation. The conservation status of orca worldwide is poorly known, although two populations of the Pacific North West Coast of North America have recently been classified as ‘Threatened’ and ‘Vulnerable’. Photo identification was used to determine the population size, distribution around New Zealand waters, as well as range use and association among individuals. The total New Zealand orca population is small (range 65-167 animals, with 115 calculated alive in 1997). Resighting rates were high, with 75 % (n = 88) of the animals seen on more than two occasions. The mean number of sightings for the 117 photo-identified animals was 5.4, the mode was one sighting, and the median 9 – 10 sightings. One orca was photographed over a 20 year period. Population structure, frequency of association with others, and other social behaviours were used to determine population demographics. The New Zealand orca population appears to be made up of at least three sub-populations based on geographic distribution (North-Island-only, South- Island-only and North+South-Island sub-populations). Preliminary mtDNA analysis supports the hypothesis that some New Zealand orca do not mix. The mean Association Indices within the North-Island-only and South-Island-only sub-populations are significantly greater than within the North+South-Island sub-population. Those animals sharing food had higher Association Indices than those who did not share food. Sex ratios appear similar within each sub-population and calves were present in each, suggesting all sub-populations are breeding. Feeding behaviour was observed to assess habitat use and differences between foraging strategies and prey preferences. Twenty four different species of prey have been recorded in the New Zealand orca diet. Of these, ten have not been recorded elsewhere. The prey consists of four types; rays (the most common food type), sharks, fin-fish and cetaceans (pinnipeds have not been identified as a prey source). Foraging strategies were different for each prey type, with benthic foraging for rays in shallow waters the most diverse strategy used in New Zealand. Food sharing was observed for all prey types. One of the three proposed New Zealand subpopulations appears to be generalist or opportunistic foragers, feeding on all four prey types, another sub-population slightly less so, feeding on three prey types, and the third sub-population appears to be a more specialist forager, only recorded taking one prey type (cetaceans). Potential threats to orca, in addition to small population size, such as bioaccumulation of toxic chemicals, oil spills, boat strikes and shootings are considered and recommendations for conservation and future management are offered. Whether the three sub-divisions within the New Zealand orca population are reproductively isolated and hence require separate management, and whether there is further sub-division within the proposed North+South-Island sub-population, requires further study including genetic analysis. Some level of ongoing monitoring is recommended to ensure that the population of New Zealand orca does not decline. In addition, records of stranding locations and details of strandings are appended. Twenty-four live strandings occurred, involving 63 killer whales, of which 17 animals were successfully refloated and two of these resighted. One was seen after three years (nine resightings) and the other after four months (10 resightings). Refloating stranded orca is recommended.

The biochemical pathways involved in nitrogen (N) utilisation by marine phytoplankton have received considerable attention over the last forty years, but our understanding of these processes, and how they are affected by environmental change is still far from complete. This study investigates N metabolism in marine phytoplankton in both a controlled laboratory environment (using the coastal marine diatom Phaeodactylum tricomutum), and in the open ocean (e.g. Jellicoe Channel and the Subtropical Convergence Zone, New Zealand). Although the characteristics of ammonium uptake have been extensively studied in marine phytoplankton, comparatively little information exists on rates of assimilation. In this study, a robust method for measuring the rate of ammonium assimilation after a transient addition of ammonium is described. The method relies on the measured ability of the protonophore carbonyl cyanide m-chlorophenylhydrazone (CCCP) to release unassimilated ammonium from the cell and prevent further assimilation. There was little or no correspondence between the rate of ammonium assimilation and rates of ammonium uptake or maximum glutamine synthetase (GS) activity in Phaeodactylum tricomutum. Moreover, in N-limited cells maximum GS activity was a poor measure of N incorporation under steady-state conditions. However, GS activity did provide reliable information on N status (e.g. increased GS activity with increased N-limitation). Comparisons of the effects of varying N-source suggest that nitrate-grown cells are not disadvantaged under conditions of N-limitation due to the extra costs associated with nitrate reductase (NR) and nitrite reductase (NiR) activity. The metabolic costs of growth on nitrate may be significantly increased under iron (Fe)-limitation, as both NR and NiR require Fe. Fe-limited chemostat cultures excreted nitrite and ammonium when grown on nitrate. This release is probably a response to insufficient photoreductant under Fe-limited conditions. However, under Fe-limitation cellular N and C was similar to that of Fe-replete cells, suggesting that the N-source used for growth (nitrate or ammonium) did not influence N-assimilation (i.e. that nitrate-grown cells were able to secure the extra reductant required to support growth) under Fe-limited, light saturating conditions. The Gln:Glu ratio (an index of the cellular N-status) was significantly reduced under N-limitation, but not under Fe-limitation. Measurement of several biochemical indicators of the physiological state of phytoplankton cells (e.g. Gln:Glu ratio, GS activity, and Fv/Fm ratio) permitted the nutrient status of phytoplankton populations to be investigated during the NIWA Ocean Fronts programme over the Subtropical Convergence Zone, New Zealand. Low Gln:Glu ratios suggested that phytoplankton in both Subtropical and Subantarctic waters were N-limited, with a marked increase in this ratio when Fe was added to Subantarctic phytoplankton. The temporal utilisation of N by neritic phytoplankton was also investigated in Jellicoe Channel, northeastern New Zealand. Again, several biochemical indicators (e.g. Gln:Glu ratio, GS activity, and Fv/Fm ratio) were used to identify the N-status of this neritic phytoplankton assemblage both during bloom and non-bloom periods.

The impact of no-take marine reserves on spiny lobster, Jasus edwardsii, populations and the adjacent lobster fishery was assessed in a study that determined: the response of lobster populations to protection, if lobsters within marine reserves moved out into the surrounding fishery, examined the behavioural characteristic of lobsters that contributed to their recovery and spillover, and contrasted catch characteristics around a north-east New Zealand marine reserve with 2 unprotected sites. Surveys of 4 no-take marine reserves of different ages and 4 unprotected control sites confirmed that J. edwardsii increase in mean size and abundance within protected areas. Total lobster density was estimated to increase by 6.1% per year of protection. The relationship between age of reserve and the density of lobsters above the legal size limit (>100 mm carapace length) was complicated by depth related interactions between reserves, due to seasonal changes in the depth distribution of lobsters and differences in the timing of surveys among locations. However, density increases in legal sized lobsters were greater than those of the overall population. Mean size of protected lobsters increased in a non-linear fashion, reflecting the asymptotic growth characteristics of the species. Mean carapace length of lobsters increased by 11.24 mm after 3 years of protection and only by 16.25 mm after 2l years of protection. Corresponding increases in biomass (kg.500 m-2) and egg production (eggs.500 m-2) were estimated to be 7.4% and 6.6% respectively per year of protection. A tag recapture program indicated that the limited scale of movements and relatively high site fidelity of mature J. edwardsii aided the recovery of lobster populations in protected areas. Of 737 lobsters tagged in and around the Leigh Marine Reserve,212 were subsequently resighted. Seventy percent of resighted lobsters were relocated less than 250 m along the shore from their initial site after a mean period of liberty of 146 (se = 13.42) days. However, seasonal offshore movements took lobsters beyond the seaward boundary of the reserve where they were susceptible to capture. Of the 521 lobsters tagged on inshore reefs within the Leigh Marine Reserve. l.9% were caught over the seaward boundary by commercial fishers, and 14.4% of the 181 lobsters tagged over the seaward boundary were resighted on inshore reefs within the reserve. Movements into or out of the reserve across the longshore boundaries were also recorded for 7 out of the 27 lobsters moving further than 250 m along the shore. Acoustic tracking confirmed that J. edwardsii have a high site fidelity, with tracked lobsters spending a median of 84% of their time at their home site. Twenty one percent of the 26 lobsters fitted with acoustic tags never left their tagging site and, of those that did leave 56% eventually returned. Lobsters moved up to 3.1km away from their home sites but managed to find their way back after periods of 1 to 103 days away. Five lobsters had strong associations with two separate sites and made repeated movements between these alternate home sites. The straight line distance between alternate home sites ranged from 200 m to 1.3 km, and the period between visits to their primary or secondary home sites ranged from 1 to 93 days. Movement activity varied throughout the year, and seasonal patterns differed between males and females. Females displayed one peak in movement activity per year, around the time of larval release in September-October. Males displayed a summer peak centred on January, and a winter peak centred on July. The onset of high movement activity was often accompanied by a shift to deeper water and l0 of the 14 lobsters tracked for over 6 months spent periods away from the inshore reef system. Exposed groups of lobsters were observed aggregating in offshore areas of sand and low lying patch reef during the day. Offshore aggregations were observed over 7 months of the year and lobsters within the aggregations displayed behaviour consistent with the use of mutual defence. The sexual composition of the aggregations reflected seasonal patterns in male and female movement rates. Male J. edwardsii dominated the aggregations in winter and summer; times when peak feeding rates of males held in captivity were also recorded. Females dominated the offshore aggregations in September-October when larvae are released. Seven of the 26 lobsters fitted with acoustic tags moved over the boundaries of the Leigh Marine Reserve and Tawharanui Marine Park during offshore movements. Despite the fact that there is no fishing access to inshore reefs within the Leigh Marine Reserve, no significant difference was detected between the catch per unit effort (kg.trap haul-1) of lobsters caught around the reserve, nearby coastal Leigh or Little Barrier Island. However, catches around the marine reserve contained fewer (P=0.0009) but larger lobsters than at Little Barrier Island. The catch characteristics of lobsters from coastal Leigh were intermediate between the other two sites. As access to inshore reefs around the Leigh Marine Reserve was limited to a small area at either end of the reserve, traps tended to be set in offshore locations and the sexual composition of the total catch around the Leigh Marine Reserve reflected the seasonal movements of males and females into, and out, offshore areas. At coastal Leigh and Little Barrier Island the location of traps was not restricted and greater use was made of coastal fringing reefs. As a result the sexual composition of the catch at these locations did not reflect the movement of various components of the lobster population into and out of specific habitats or locations. Overall, the results of this study suggest that relatively small (~ 5 km2) no-take marine reserves increase lobster biomass and egg production, without adversely affecting catch rates in the surrounding fishery. Marine reserves may therefore represent a viable management tool, which if used in conjunction with other management regimes, could provide a more precautionary approach to the management of the J. edwardsii fishery at minimal cost to the industry.

This study focuses on an assessment of the health status of the yellowbelly flounder (Rhombosolea leporina) from two estuarine locations (site 1 – the mouth of the Henderson Creek; site 2 – the mouth of the Whau Creek) in the Waitemata Harbour. This harbour borders the highly urbanised and industrialised Auckland City metropolitan area. Whangaparaoa Peninsula, located approximately 30 km north of the other two collecting sites (away from the main urban area), was chosen as a reference site for comparative purposes. Physico-chemical analyses revealed differences in water quality at the sampling sites. A lower pH, oxygen deficiency and higher temperature were recorded in both the Waitemata Harbour locations in comparison with the reference site. Histopathological analyses revealed significantly higher prevalences and severity of pathological changes in the gills, blood, liver, kidney and gonads of the yellowbelly flounder from both harbour locations in comparison with fish from the reference site. ln addition, some types of lesions (eg. neoplasms) were observed in fish from the two harbour locations only. Abnormalities in the gill structure of fish from both harbour sites included: epithelial swelling (hyperplasia and hypertrophy), necrosis, and lifting with oedema; the fusion of secondary lamellae; aneurysms; filamental deformities; mucous cell proliferation, and infestation by Trichodina. The abnormalities found in the blood of these fish were manifested as: polycythaemia; erythrocytosis; erythroblastosis; leucocytosis (increased neutrophils); poikilocytosis; anisocytosis and an increased prevalence of erythrocytes undergoing necrosis. Vacuolar degeneration of the hepatocellular parenchyma due to lipid or glycogen accumulation was the most prominent liver change observed in fish from all sampling sites. The other liver abnormalities observed in flounder from the two harbour sites included: foci of cellular alterations (clear, basophilic and necrotic), congestion of the sinusoids, infestation by nematodes, and anaplastic growths (cholangiocellular carcinoma and teratoma). Pathological changes found in the kidneys of flounder collected at both harbour sites were classified as glomerular abnormalities (atrophy and dilatation of the glomerular tuft; enlargement of Bowman's space) and tubular vacuolar degeneration and necrosis. The presence of myxosporean parasites was also a common finding in the kidneys of harbour fish. Follicular atresia was the most prevalent change observed in the ovaries of flounder from the two harbour sites. Biochemical analysis of plasma proteins and electrolytes of flounder from the three sampling sites revealed hyperbilirubinaemia, hypoalbuminaemia and uraemia in those inhabiting both harbour sites. In addition, the concentration of total liver microsomal proteins was significantly depressed in flounder from harbour sites 1 and 2 when compared to that of fish from the reference site. Concentrations of heavy metals in the livers of flounder from different sampling localities were found to decrease in the order: site 2 > reference site > site 1, and did not correlate with the prevalences of liver abnormalities. Significantly more prominent pathological changes were thus observed in fish from both estuarine harbour sites in comparison with those from the reference open water site. The pathological changes noted are believed to occur in response to environmental changes. Contamination by different xenobiotics in the Whau and Henderson Creeks, which have been recorded in previous studies, suggest the possibility of direct toxic effects of the water contaminants on flounder from the estuarine parts of these creeks. In addition, the relatively high temperature, low pH and low oxygen levels recorded at the two sites in the Waitemata Harbour are believed to have induced oxygen deficiency-related tissue hypoxia which could then have led to the expression of a variety of diseases of which some have been detected in this study. However, the possibility that some unknown and unmeasured causal factors may have produced the observed pattern of flounder diseases cannot be eliminated.