Abstracts
from Volume 52 of Notornis |
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| Part 1 |
| Papers |
Baillie, B.R.; Glaser, A.B. 2005. Roost habitat of a North Island
blue duck (Hymenolaimus malacorhynchos) population. Notornis 52(1):
1-5. Bester, A.J.; Charteris, M. 2005. The second census of Chatham
Island shag and Pitt Island shag – are numbers declining? Notornis
52(1): 6-10. Bell, M.; Bell, B.D.; Bell, E.A. 2004. Translocation of fluttering
shearwater (Puffinus gavia) chicks to create a new colony. Notornis
52(1): 11-15. McAllan, I.A.W.; Hobcroft, D. 2005. The further spread of introduced
birds in Samoa. Notornis 52(x): 16-20. Miskelly, C; Empson, R.; Wright, K. 2005. Forest birds recolonising
Wellington. Notornis 52(1): 21-26. Robertson, H.A.; McLennan, J.A.; Colbourne, R.M.; McCann,
A.J. 2005. Population status of great spotted kiwi (Apteryx haastii)
near Saxon
Hut, Heaphy Track, New Zealand. Notornis 52(Apteryx1): 27-33. Jensen, L.A.; Snoyink, R.J. 2005. The distribution and numbers of
Australasian crested grebe (kamana) in New Zealand, January 2004. Notornis
52(1): 34-42. Tennyson, A.J.D.; Bartle, J.A. 2005. A scientific name for fulmar
prions nesting at Auckland and Heard Islands. Notornis 52(1): 47-55. |
| Short notes |
Thompson, D.R.; Bearhop, S.;
Ross, B. 2005. Spread of Australasian pipit (Anthus novarseelandiae)
onto Campbell Island following eradication of Norway rats (Rattus
norvegicus).
Notornis 52(1): 43-46. Tove, M.H. 2005. Kermadec petrels (Pterodroma neglecta) in the Atlantic
Ocean – a rebuttal. Notornis 52(1): 56-58. Imber, M.J. 2005. A response to M. Tove’s rebuttal of Imber (2004). Notornis 52(1): 58-59. |
| Part 2 |
| Papers |
Morgan, D.; Waas, J.R.; Innes, J. 2005. Magpie interactions with other
birds in New Zealand: results from a literature review and public survey.
Notornis 52(2): 61-74. Sagar, P.M.; Murdoch, R.; Sagar, M.W.; Thompson, D.R. 2005. Rockhopper
penguin Eudyptes chrysocome filholi foraging at Antipodes Islands.
Notornis 52(2): 75-81. Jamieson, I.G.; Grant, J.L.; Beaven, B.M. Capture and handling of
saddlebacks during pre-nesting does not affect timing of egg-laying
or reproductive success. Notornis 52(2): 82-88. Spear, L.B.; Ainley, D.G.; Webb, S.W. 2005. Distribution, abundance,
habitat use and behaviour of three Procellaria petrels off South
America. Notornis 52(2): 89-106. |
| Short notes |
Winn, J.M.; Holdaway, R.N. 2005.
Egg predation by South Island kaka (Nestor meridionalis). Notornis 52(2):
107-109. Hawke, D.J.; Newman, J. 2005. Using isotopic analysis to identify incorporation
of marine nutrients in terrestrial birds at Snares Islands. Notornis
52(2): 109-112. Medway, D.G. 2005. Feeding association of tui (Prosthemadera n.
novaeseelandiae)
with North Island kaka (Nestor meridionalis septentrionalis). Notornis
52(2): 112-113. Berggren, A. 2005. Comparing anting hypothesis predictions to observations
of behaviour in a North Island robin (Petroica australis
longipes). Notornis
52(2): 113-115. Berggren, A. 2005. Prevalence and impact of the native blood-sucking
louse-fly (Ornithoica sp.) on the North Island robin (Petroica
australis longipes). Notornis 52(2): 115-117. Scofield, R.P. 2005. The supposed Macquarie Island parakeet in the collection
of Canterbury Museum. Notornis 52(2): 118-121. Miskelly, C.M.; Sagar, P.M. 2005. Longevity record for Snares Island
snipe (Coenocorypha aucklandica huegeli). Notornis 52(2):121-122. |
| Letter |
| Bourne, W.R.P. 2005. Kermadec petrels in the Atlantic Ocean. Notornis 52(2): 122-123. |
| Corrigendum |
| Corrections to McAllan, I.A.W.; Hobcroft, D. 2005. The further spread of introduced birds in Samoa. Notornis 52(1): 16-20. |
| Part 3 |
| Papers |
Imber, M.J.; Bell, B.D.; Bell, E.A. 2005. Antipodes Islands birds in autumn 2001. Notornis 52(3): 125-132 Observations of birds on Antipodes Islands during 24 April - 6 June
2001 represent a season of the year for which data are lacking. Activity
ashore of non-breeders of summer-breeding gadfly petrels Pterodroma spp. and black-bellied storm petrels (Fregetta tropica) continued until
late May or even June. Data were obtained on the non-breeding behaviour,
breeding cycle and burrow occupancy rates of grey petrels (Procellaria
cinerea); only 50% of their burrows were occupied by breeding pairs.
White-capped albatross (Thalassarche steadi) fledglings on Bollons
Island were counted. There had been an autumnal immigration of some
Passerines. Birds seen at sea on the voyages from Akaroa, Banks Peninsula
and returning to Port Chalmers, Dunedin included the rarely-sighted
Chatham taiko (Pterodroma magentae). Quintana, R.D.; Pratolongo, P.D.; Agraz, J.L.; Benitez, O.; Mengual, A.R. 2005. Activity rhythms at a gentoo penguin (Pygoscelis papua) colony at Cierva Point, Antarctic Peninsula. Notornis 52(3): 133-137 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. Alexander, L.; Duthie, C.; Fyfe, J.; Haws, Z.; Hunt, S.; Montoya, I.; Ochoa, C.; Siva, A.; Stringer, L.; Van Horik, J.; Burns, K.C. 2005. An experimental evaluation of food hoarding by North Island robins (Petroica australis longipes). Notornis 52(3): 138-142. We experimentally evaluated the food hoarding behaviour of North Island
robins (Petroica australis longipes) at Karori Wildlife Sanctuary,
Wellington. Mealworms were offered to free-ranging pairs of male and
female robins to evaluate whether their food hoarding behaviour was
similar to previous observations of South Island robins. We also tested
theoretical predictions derived in the Northern Hemisphere, which argue
that competitively subordinate birds should hoard more food than dominant
birds. Results showed that the food hoarding behaviour of North Island
robins was similar to South Island robins, except that North Island
robins repeatedly used the same cache sites, which is rare in South
Island robins. Data did not support the prediction that competitively
subordinate birds hoard more food than dominant birds. Males acquired
most of the mealworms offered to birds during trials, and won nearly
all aggressive interactions observed between sexes. Therefore, males
appeared to be competitively dominant to females in winter. However,
males stored over five times as many mealworms as females, which is
opposite to theoretical predictions. We interpret the reluctance of
females to cache food as a strategy to avoid food loss to competitively
dominant males. Barker, D.; Carroll, J.W.A.; Edmonds, H.K.; Fraser, J.R.; Miskelly, C.M. 2005. Discovery of a previously unknown Coenocorypha snipe in the Campbell Island group, New Zealand subantarctic. Notornis 52(3): 143-149. A previously unknown population of Coenocorypha snipe was discovered
on Jacquemart Island, a rat-free 19 ha islet adjacent to Campbell Island
in the New Zealand subantarctic, on 9 November 1997. This was the first
evidence of Coenocorypha snipe occurring in the Campbell Island group,
which is believed to have been infested by Norway rats (Rattus
norvegicus)
before the first naturalists visited in 1840. Rats were eradicated
from 11,268 ha Campbell Island by the New Zealand Department of Conservation
in July 2001. Two snipe were seen, and one caught, on Campbell Island
adjacent to Jacquemart Island on 10 March 2005. The bird caught was
a fully-feathered chick, indicating successful breeding on Campbell
Island. The Campbell Island snipe remains undescribed and critically
endangered. Lee, M. 2005. Failed attempts to reintroduce bellbirds (Anthornis melanura) to Waiheke Island, Hauraki Gulf, 1988-91. Notornis 52(3): 150-157. New Zealand bellbirds (Anthornis melanura) disappeared suddenly from
the northern New Zealand mainland and several large northern islands
in the late 19th century. During the past 75 years, several unsuccessful
attempts were made to reintroduce them. Between 1988 and 1991, four
translocations (111 birds) were made to Waiheke Island near Auckland,
sourced from Kaingaroa (21 birds) and Cuvier Island (90 birds). The
birds were conspicuous immediately after release but became progressively
less visible within six months and the translocations failed. While
the cause(s) of failure are unknown, predation by mammalian predators,
especially ship rats (Rattus rattus) is likely to have been a critical
factor. Other possible reasons for failure of bellbird translocations
are discussed, along with the reasons why original bellbird populations
disappeared from northern New Zealand and subsequently failed to re-establish. Hawke, D.J.; Clark, J.M.; Challies, C.N. 2005. Verification of seabird contributions to Australasian harrier diet at Motunau Island, North Canterbury, using stable isotope analysis. Notornis 52(3): 158-162. We analysed 13C and 15N isotopic enrichment in Australasian harrier
(Circus approximans) eggshell and two discarded harrier feathers from
Motunau Island, a regionally important seabird breeding island. Among
the prey remains found at the nest was a prion (Pachyptila sp.) wing
fragment and a predated blue penguin (Eudyptula minor). We combined
isotope data from the prey remains, plus potential prey items obtained
from the mainland, to reconstruct harrier diet and evaluate incorporation
of seabird nutrients. During egg material formation, blue penguins
made up a major part of the female harrier’s diet. During autumn,
when feathers were re-growing, the two feathers (which may or may not
have been from different individuals) gave very different results.
The feather with the more marine signature was growing when harrier
diet included a significant proportion of blue penguin and/or fairy
prion (Pachyptila turtur) material. Formation of the other feather
may have occurred while harrier diet was primarily terrestrial. Our
results are indicative of the usefulness of stable isotopic analysis
in elucidating nutrient flows and contributions to animal diet. |
| Short notes |
Miskelly, C.M. 2005. Evidence
for ‘hakawai’ aerial displaying by Snares Island snipe (Coenocorypha
aucklandica huegeli). Notornis 52(3): 163-165. Schuckard, R. 2005. Marlborough Sounds, an important nesting and wintering
area for white-fronted terns (Sterna striata). Notornis 52(3): 165-167. Imber, M.J. 2005. Status of Kermadec petrels (Pterodroma neglecta) on
the Meyer Islets, and prospects for their re-colonisation of Raoul Island,
Kermadec group. Notornis 52(3): 168-169. Nicholson, R.S. 2005. Assessment of relative conspicuousness: a correction
to McKinlay (2001). Notornis 52(3): 170. Scofield, P.; McAllan, I.A.W.; Palma, R.; Worthy, T.H. 2005. Stabilisation
of the genus-group name of the New Zealand bellbird. Notornis 52(3):
171-172. Abstracts of papers presented at the Ornithological Society of New Zealand
AGM and Conference, 5 June 2005, Hamilton, New Zealand. Notornis 52(3):
173-178. |
| Part 4 |
| Papers |
Gaskin, C.; Baird, K. 2005. Observations of black and white storm petrels in the Hauraki Gulf, November 2003 - June 2005: Were they of New Zealand storm petrels? Notornis 52(4): 181-194. We observed black and white-plumaged storm petrels on 27 seabird-watching
trips to the outer Hauraki Gulf, New Zealand, November 2003 - June
2005. We studied their plumage characteristics, behaviour and seasonal
occurrence: the birds had common plumage characteristics and sightings
of them were concentrated in the outer Hauraki Gulf from October to
March and further offshore in April-May. Their presence in the Hauraki
Gulf coincided with summer breeding of other seabirds, in particular
white-faced storm petrels (Pelagodroma marina). Their pattern of occurrence
off northern New Zealand suggests the birds may be breeding in the
Hauraki Gulf; the Mokohinau Islands, rid of rats (Rattus exulans) 15
years ago, is a potential breeding site In our view these black and
white storm petrels do not conform to descriptions of any extant species
known from New Zealand waters, and, consequently, we speculate that
our observations may have been of New Zealand storm petrels (Pealeornis
maoriana Mathews1932), a species known from only three specimens collected
in the 19th century. Moore, P.J.; Bettany, S. 2005. Band recoveries of southern royal albatrosses (Diomedea epomophora) from Campbell Island, 1943-2003. Notornis 52(4): 195-205. 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. Walker, K.; Elliott, G. 2005. Population changes and biology of the Antipodean wandering albatross (Diomedea antipodensis). Notornis 52(4): 206-214. The Antipodean wandering albatross (Diomedea antipodensis) is endemic
to Antipodes Island in the New Zealand subantarctic. A programme of
regular census and population study was initiated on Antipodes Island
in 1994 to determine the status of the species. This paper reports
on field work carried out every summer from 1994 to 2005. Aspects of
breeding biology are described and compared with those of other species
of wandering albatross, particularly the closely related Gibson’s
wandering albatross (D. gibsoni) on Adams Island. Average annual survival
over 10 years was 0.957. Productivity was measured over 11 years and
averaged 0.74 chicks per nesting pair. Survivorship was similar to
that in the increasing Diomedea exulans population on Crozet Island,
and productivity higher than recorded in all other wandering albatross
populations. Between 1994 and 1997, the average annual number of pairs
nesting on Antipodes Island was 5136. There is evidence of population
decline during the 1970s but numbers are now increasing. Elliott, G.; Walker, K. 2005. Detecting population trends of Gibson’s and Antipodean wandering albatrosses. Notornis 52(4): 215-222. Counts, mark-recapture estimates of abundance, and simulations were
used to assess the population trends of Antipodean wandering albatross
(Diomedea antipodensis) and Gibson’s wandering albatross (D.
gibsoni). Estimates of population size based on mark-recapture analysis
had much greater power to detect trends than did annual counts of nests.
In fact, nest counts were so variable that significant trends would
only be detected when populations had already changed by more than
25%. Population simulation models were constructed using survival and
productivity data from the two species, and recruitment data from closely
related species. The simulation models were sensitive to variation
in recruitment data and suggested that the recruitment of Gibson’s
wandering albatrosses is significantly lower than that of Antipodean
wandering albatrosses. The sensitivity of the models to variation in
the surrogate data compromises the usefulness of such models as predictive
tools. After large, probably fisheries-induced declines during the
1970s and 1980s, Antipodean wandering albatross populations are now
increasing at about 3.1% per annum, while Gibson’s wandering
albatross populations are static. Nicholls, D.G.; Robertson, C.J.R.; Naef-Daenzer, B. 2005. Evaluating distribution modelling using kernel functions for northern royal albatrosses (Diomedea sanfordi) at sea off South America. Notornis 52(4): 223-235. Satellite telemetry can provide unique information on the biology
and behaviour of mobile animals such as albatrosses. Determining areas
of concentrated activity, essential resources and time-related changes
in range use is of great importance for theoretical biology, practical
conservation, and fisheries management. Utilisation Distributions (UDs),
from a probabilistic model of the relative time spent by an animal
in an area, were prepared using a kernel function in a Geographical
Information System. Properties of the model were investigated, using
satellite-tracking data from six northern royal albatrosses (Diomedea
sanfordi) during eight over-wintering visits to seas off South America.
We analysed UD areas and shape for different settings of the kernel
smoothing parameter, a variety of location subsets associated with
different sample sizes, sampling time periods and telemetry regimes.
Small samples and intermittent transmission regimes reduced the UD
range area. Individual bird data sets were combined to give comparable
UDs. The UD model may help comparison of range areas and the identification
of resource use, but they cannot identify an activity without additional
information. For pelagic seabirds, UD preparation and interpretation
require judgement and care. Cassey, P.; Blackburn, T.M.; Evans, K.L. 2005. Changes in egg size of exotic passerines introduced to New Zealand. Notornis 52(4): 243-246. Bird species introduced to New Zealand from high northern latitudes
are expected to change their breeding behaviour to conform to well-known
geographic gradients in avian reproductive parameters. Here, we demonstrate
reductions in average egg size and clutch volume for eight species
of exotic passerine originating in the UK, and show that the magnitudes
of these reductions appear to trade-off against reductions in annual
variation in clutch size. Possible reasons for the trade-off are discussed. |
| Short notes |
| Robertson, C.J.R.; Klavitter, J.; McCarthy, R. 205.
Salvin’s albatross (Thalassarche salvini) on Midway Atoll. Notornis
52(4): 236-237. Keywords Salvin’s albatross; Thalassarche salvini; Midway Atoll National Wildlife Refuge; Sand Island. Robertson, C.J.R.; Stephenson, B.M. 2005. Cape gannet (Sula capensis)
breeding at Cape Kidnappers, New Zealand. Notornis 52(4): 238-242. Palma, R.L.; Tennyson, A.J.D. 2005. Designation of a lectotype and clarification
of authorship and date of publication for the New Caledonian petrel (Pterodroma
leucoptera caledonica). Notornis 52(4):247-248. Cherry, B. 2005. A little black cormorant (Phalacrocorax sulcirostris)
from Kadavu Island, Fiji. Notornis 52(4): 249. Chambers, G.K.; Boon, W.M. 2005. Molecular systematics of Macquarie
Island and Reischek’s parakeet. Notornis 52(4): 249-250. Ball, O.; Parrish, R. 2005. Lizard predation by North Island fernbird
(Bowdleria punctata vealeae). Notornis 52(4): 250-251. |
| Review |
O’Donnell, C.J.F. 2005. Herons, egrets and bitterns: their biology and conservation in Australia. Notornis 52(4): 251-252. |
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