35,289 southern royal albatrosses (Diomedea epomophora) were banded on Campbell Island between 1941 and 1998, including 24,258 chicks and 11,031 adults. By 2003, 240 (0.68%) band recoveries and live recaptures away from Campbell Island had been reported. Birds banded as chicks were reported at a median age of 2 years (range 1-28 yrs), and adults at a median of 4 years after banding (range 0-27 yrs). The peak of band recoveries occurred close to the peak of banding in the late 1960s. Recoveries were generally made between latitudes 30-55°S in southern Australasia and South America; 43% were on coasts and 56% at sea. Birds recovered at sea (n = 134) were usually in waters over the continental shelf (up to c. 200 m deep water; 55% of records) or slope (200-1000 m; 19%). Distribution varied with age, with 56% of juveniles (<20 months old, n = 78) found on the west side of South America (especially in December – February), 54% of immature birds (<6 years old, n = 48) on the east side of South America (especially in June – July) and 55% of adults (≥ 6 years old, n = 114) in the New Zealand region. Most (94%, n = 102) birds recovered on the coast were dead, compared with 46% (n = 134) of those found at sea. Some birds were apparently caught to read bands, and 36% of the live birds (n = 78) were released without their bands, and of the remainder, 3 birds were seen again on Campbell Island. About half (49%, n = 61) of deaths at sea were caused by accidental capture on fishing lines. A possible decrease in the population during the 1970s – early 1980s coincided with the peak in long-line fishing in the New Zealand region and suggests this albatross could be affected by any new fisheries or intensification of fishing without adequate mitigation. It would be prudent to monitor the trends, dynamics and foraging of a range of New Zealand albatross species within an, as yet undeveloped, strategy for research and monitoring of seabirds in New Zealand.
The Australasian crested grebe (kamana: Podiceps cristatus australis) is nationally endangered within New Zealand. A census, conducted on 24 January 2004 by 81 observers, recorded 300 adults and estimated a further 15 as present on 41 of the 93 lakes counted. Assuming approximately 30 grebes to be present on lakes not counted, the national population of adult crested grebes is estimated to be 340-350. This is 40% higher than the population recorded in 1980. In addition, 75 juveniles were counted on 18 lakes. As in the 1980 survey, approximately 55% of the adult crested grebes were recorded on Canterbury lakes. A significant regional change has occurred with birds now present on lakes in Otago, absent from Nelson lakes, and in reduced numbers in Marlborough, North Canterbury, Westland and Fiordland. In addition, a significant decline has occurred at Lake Alexandrina, one of the strongholds identified in the 1980s. Forty percent of the present adult population was recorded on two lakes, Lake Heron and Lake Hayes. We identify priority sites where management to reverse declines could be implemented and we recommend a suite of management actions.
We studied activity rhythms at a gentoo penguin (Pygoscelis papua) colony at Cierva Point, Antarctic Peninsula, during the 1992-93 summer. We counted the number of penguins crossing a specific point on their route to and from the colony. Penguins showed a strong daily rhythm of activity, with a two-peak pattern for those leaving the colony and a one-peak pattern for those returning. The peak of penguins departing to sea was at dawn, with a secondary peak in the afternoon which was coincident with the peak of returns. Although this behaviour could be explained by nest relief schedules, the pattern remained once crèches had formed. The main peak of departures strongly correlated with sunrise, which might support the existence of a light signal synchronizing activity. Even though an external factor could be triggering movements, an endogenous circadian clock might drive both patterns.
Kaka (Nestor meridionalis), red-crowned parakeet (Cyanoramphus novaezelandiae), whitehead (Mohoua albicilla), tomtit (Petroica macrocephala), and bellbird (Anthornis melanura) have all recently been reintroduced to sites in or near Wellington city. Prior to or concurrent with these translocations, unmarked individuals of all five species were detected in forested reserves on Wellington peninsula. Based on the number of birds seen, and frequency of sightings, we suggest that red-crowned parakeets, whiteheads and bellbirds have established resident populations in some reserves independent of translocations. We attribute these successful re-establishments to the effective control of possums (Trichosurus vulpecula) and rats (Rattus sp.) undertaken by Greater Wellington Regional Council and the Department of Conservation.
The effects of time of day and observer vantage points on recorded waterbird species diversity and numbers of individuals of each species (especially New Zealand scaup (Aythya novaeseelandiae), the most common species) from a New Zealand wetland were analysed statistically and compared using rank abundance plots. There were significant differences between counts of total numbers of species, total numbers of individuals, and numbers of New Zealand scaup made from three observer positions and this effect was attributed to differences in observer elevation. Time of day had no significant effect on total numbers of species, total numbers of individuals of all species, and numbers of New Zealand scaup counted. However, rank abundance plots indicated a time of day effect on counts made at the least elevated of the observer positions. Overall, these effects were sufficient to introduce bias into waterbird counts and to require they be assessed during long-term monitoring programmes.
Parental and nestling behaviour of New Zealand pigeon (Hemiphaga novaeseelandiae) was observed from August 1998 to March 1999 at Motatau Forest, Northland, New Zealand. Four successful nests from three pairs were monitored using infra-red cameras and direct observation. Incubation was shared (female: dusk till 0643-1106 hrs; male: remainder of the day). Three stages of daytime nestling care were apparent: full-attendance brooding by either parent (day 0 to day 8-12); female-only brooding (day 9-13 to day 12-26); and feeding only (day 13-27 to fledging) except in wet weather. Females brooded the nestlings for significantly longer than did males. Young nestlings were fed more frequently, and for longer, than when older. Parents appeared to select fruit of pigeonwood (Hedycarya arborea) and nikau (Rhopalostylis sapida) for feeding nestlings. Development and growth was rapid and one nestling weighed 565 g (similar to adult weight) by day 26. Feathers first appeared on day 5-8.
The North Solomons Province of Papua New Guinea consists of two main islands, Bougainville and Buka as well as several atolls to the north and east. The avifauna on five atolls, Nissan, Nuguria, Tulun, Takuu and Nukumanu, was recorded during visits in 2001. A bird list for each atoll group was compiled, incorporating previously published observations, and the local language names of birds recorded.