Publications Archive

Introduced mallards (Anas platyrhynchos) occur on many islands of the South Pacific, where they hybridise with the resident grey duck (A. superciliosa). In October 2007, we conducted systematic surveys of Lord Howe Island to estimate the abundance and distribution of grey ducks, mallards, and their hybrids. Hybrids were common in areas of high public use, particularly where there was mown or grazed grass. Phenotypic characteristics suggest that mallards are now dominant and have supplanted the native grey duck, with 81% of birds classified as mallard or mallard-like hybrids, 17% as intermediate hybrids and only 2% as grey duck-like hybrids. No pure grey duck were observed. These hybrids pose direct and indirect economic, social and environmental impacts to Lord Howe Island. A management program to remove mallards using trapping, shooting and opportunistic capture by hand was conducted in October 2007. Standardised indices of duck abundance before and after management indicates that the total population was reduced by 71.7%. Eradication of mallard and hybrids from Lord Howe Island is considered achievable with a program of education, monitoring, and continued control to prevent re-establishment.

A small black-and-white storm petrel seen off Whitianga, New Zealand, in Jan 2003 was tentatively identified as a New Zealand storm petrel (Pealeornis maoriana). A further sighting in the Hauraki Gulf in Nov 2003 of multiple birds identified as New Zealand storm petrels led to the realisation that the species was both extant and apparently locally common. Prior to these sightings this enigmatic seabird was known only from 3 specimens collected in the 1800s, and unreported since. This paper reviews these 2 sightings that constitute the rediscovery of an

The nesting of variable oystercatchers (Haematopus unicolor) on the Kaikoura Peninsula was studied at 6 sites over 8 years. Only in 1 year were birds known to have laid eggs at all 6 sites and only at 2 sites was nesting observed every year. Loss of nests often resulted in re-nesting and at 1 site birds made 4 attempts in 1 season. Over the 8 years, 117 eggs were found in 53 nesting attempts between mid-Oct and late Jan. The average size of 114 eggs was 58.2 x 40.6 mm. Thirty of 53 nesting attempts were completed and averaged 2.4 eggs/clutch (range 1

Thirty-four species of birds are recorded from the isolated Pacific island of Nauru. Six are treated as hypothetical pending corroboration; 3 others are introductions. Eighteen of the 25 indigenous species are non-breeding visitors (mainly migrating seabirds and shorebirds). The 7 confirmed or probable resident breeders include only 2 land birds, the Micronesian pigeon (Ducula oceanica) and the endemic Nauru reed-warbler (Acrocephalus rehsei). The Australian pelican (Pelecanus conspicillatus) and white-winged tern (Chlidonias leucopterus) are reported as first records for Nauru. Hunting pressure and habitat degradation have contributed to reduced numbers of the Micronesian pigeon and the once abundant black noddy (Anous minutus), but the Nauru reed-warbler occurs commonly in degraded and modified habitats. Second-stage mining to recover phosphate deposits will likely reduce available habitat further for all resident breeding species, although land restoration is also planned. Bird band recoveries indicate that many seabirds, especially black noddies, reach Nauru thousands of kilometres from where they were fledged, but to what extent they are recruited into the local breeding population is unknown.

During 1971-75 and 1991-95, surveys of Caspian tern (Sterna caspia) colonies throughout New Zealand were carried out. The breeding population in 1971-75 was 1266 pairs, in 16 colonies, predominately in the northern North Is. In 1991-95, there were 1190 breeding pairs found in 17 mainly northern colonies, suggesting the population had been relatively stable over the 20-year period. As census methodology may under-record the breeding of isolated pairs, we included an estimate of the number of isolated pairs to give a total national population of 1300-1400 breeding pairs. This is less than 3% of the global population. Colony size and location showed some change between survey periods; 6 colonies disappeared and 8 new colonies were formed. Addition surveys in 2011-2015 are recommended to compare recent population trends.

[First paragraph…] Members of the parvorder Corvida, including the Australian magpie Gymnorhina tibicen, have a relatively high level of innovative behaviour amongst birds (Timmermans et al. 2000; Lefebvre et al. 2004). An example of this behaviour is tool use in Corvus spp. (Hunt 1996; Caffrey 2000). Although Australian magpies (magpies hereafter) are known to manipulate objects in behaviour such as play (Pellis 1981ab; Kaplan 2004) they have not been reported to use tools. Here, I report a possible case of tool use by an adult magpie.

Roost sites in Whangarei Harbour and Ruakaka Estuary were used regularly by 12 wader species and 6 other species were present occasionally between 1974 and 2000. Counts at 7 roost sites in Nov, Jun/Jul, and Mar showed that 4 species, eastern bar-tailed godwit (Limosa lapponica), lesser knot (Calidris canutus), pied stilt (Himantopus leucocephalus), and South Island pied oystercatcher (Haematopus ostralegus finschi) contributed 70-99% (median 94%) of the waders. Most of the common waders used several roosts at each tide, but numbers and species richness of resident and vagrant species were greatest along the southern margin of the harbour. Changes in roost structure and proximity to feeding areas, and differences in migration patterns affected counts at individual roosts and the overall totals of wading birds counted in the harbour and its environs.

[First paragraphs…] At c.0800 h on 6 Nov 2006, PB and TC caught a whitehead (Mohoua albicilla) while mist-netting on Tiritiri Matangi I, Hauraki Gulf, North I, New Zealand. The net was set in “Bush 1”, on the northwestern side of the island. The bird carried a metal band (B57955) and 2 (green, blue) faded, inter-twined wrap-around plastic bands: the band combination could have been either metal-GB or metal-BG. It was thought to be male because it had a bright white head (Gill & McLean 1986) and an enlarged cloacal area. The only whiteheads that had been banded recently on the island had all been processed by NL and received split colour bands. We therefore thought that this whitehead was from the original trans-located population which was transferred to Tiritiri Matangi I from Little Barrier I in 1989 and 1990, which would mean that it was at least 16 years old. age of 8 years 7 months for another Little Barrier I bird (Gill 1993).

[First paragraph…]New Zealand pipits (Anthus n. novaeseelandiae) were apparently common in the open landscapes of the last glacial period (Worthy & Holdaway 1996). Before humans arrived, there were no mammalian predators in New Zealand but the pipit was an important food of the New Zealand falcon (Falco novaeseelandiae) and the laughing owl (Sceloglaux albifacies) (Worthy & Holdaway 2002). New Zealand pipits would have been likely to increase as more open habitats developed during the 700 years since Polynesian settlement, because their close relatives on continents live with mammalian and avian predators (Sibley & Ahlquist 1990), and New Zealand pipits have an 8-month (Aug-Mar) breeding season during which multiple clutches of 1-4 are raised (Heather & Robertson 1996). Pipits did apparently initially increase in numbers during the phase of forest and scrub clearance following European settlement (Buller 1888, Guthrie-Smith 1927), but no recent studies have found pipits in high densities in any habitat (Beauchamp 1995). The factors that could be controlling pipit numbers include the deteriorating quality of open habitats (Lovegrove 1980), and high levels of predation by endemic avian and introduced mammalian predators (Wilkinson & Wilkinson 1952).

Collections of bird specimens assembled by T.F. Cheeseman

We investigated whether the abundance of the South Island robin (Petroica australis australis) could be explained by the abundance, species richness, diversity, or evenness of leaf-litter invertebrates. We recorded robin abundance indices and collected leaf-litter invertebrates in 3 forest types: mature Douglas fir (Pseudotsuga menziesii); mature Monterey pine (Pinus radiata); and old growth kanuka-manuka (Kunzea ericoides – Leptospermum scoparium). Robins were attracted to stations using 5-min playbacks of robin full song in each forest type. Invertebrates were extracted from leaf-litter samples using ‘Tullgren-type’ heat extraction funnels. There was no significant difference between the numbers of robins detected in the Douglas fir (1.14 5 min count-1), or kanuka-manuka forest (0.86 5 min count-1), and no robins were detected in the Monterey pine forest. Kanuka-manuka forest had the greatest biomass and species richness of leaf-litter invertebrates, but the lowest evenness. We believe that the abundance of the South Island robin can not be sufficiently explained by the density or directly of leaf-litter invertebrates.

[First paragraphs…]With the death of Roger Sutton in September 2006 at the age of 84, the Ornithological Society of New Zealand lost a long-standing and stalwart member.A member of the OSNZ for nigh on 50 years, Roger became the Southland Regional Representative in 1966, and served in the role for 17 years, years during which ornithology made considerable strides in Southland and when the local membership reached its peak. Roger was an inspirational RR, introducing many young (and some not so young) people to the delights of bird watching and study. During his time as RR the Southland Region hosted the highly successful 1969 field study course. The members who took part completed the 1st full survey of the main wader sites in the region, and started annual summer and winter wader censuses that were then undertaken at all main roost sites from 1976 to 1999.

[First paragraph…] Occurring on both Auckland and Campbell Is. (52°32.4’S, 169°8.7’E; 11,300 ha), the Auckland Is pipit (Anthus novaeseelandiae aucklandicus G.R. Gray) is a subspecies of the New Zealand pipit, Anthus novaeseelandiae novaeseelandiae Gmelin (Turbott 1990). At Campbell Is, the pipit is restricted to small offshore islets. A similarly restricted distribution of this southern subspecies to offshore stacks at Campbell Is is reported by Heather & Robertson (1996), and Foggo (1984) who suggested that this situation is caused by the effects of Norway rat (Rattus norvegicus) and cat (Felis silvestris catus) predation. Foggo (1984) noted that the inability of pipits to co-exist with rats on subantarctic islands has been demonstrated in South Georgia by Pye & Bonner (1980). Foggo & Meurk (1981) commented that it is likely that rats and cats have eliminated this species from the main island. Deliberate burning of vegetation as a farming practice in the early 19th century (Wilmshurst et al. 2004) may also have restricted the distribution of the pipit. Foggo (1984) collected pipits on Dent Is in 1975 and reported that they “were immediately obvious and very tame” during a brief helicopter visit to the summit of Jacquemart Is in 1980 (Foggo & Meurk 1981), adding that on each of these offshore islands the birds had fulvous plumage. Thompson et al. (2005) encountered pipits at 2 locations on Campbell Is in 2003 and that they were distributed more extensively in 2004, 2 main centres being around Penguin Bay in the southwest, and towards the south around Eboulé Peak.

Forbes’ parakeet (Cyanoramphus forbesi) is an endangered taxon now endemic to Mangere I and Little Mangere I in the Chatham Is group, 500 km east of New Zealand. This taxon exists now as a single mixed population consisting of Forbes’ parakeets, Chatham I red-crowned parakeets (C. novaezelandiae chathamensis) and their hybrids (Taylor 1975; Nixon 1982; Chan et al. 2006). Increased attention on the conservation of Forbes’ parakeets followed from the presentation of allozyme and mitochondrial DNA control region genetic evidence which suggested that Forbes’ parakeet should be elevated from a subspecies of yellow-crowned parakeet (C. auriceps forbesi) to full species status (Triggs & Daugherty 1996; Boon et al. 2000).

[First paragraphs …] The ‘sandspit’  on the True Right bank of the Manawatu River, in Foxton Beach Village, (175°14’E 40°30’S) is a significant roosting site for migratory and resident waders, gulls, terns, pied stilts (Himantopus himantopus), royal spoonbills (Platalea regia), shags, ducks, and other birds. The ‘sandspit’  is 2-5 ha, depending on the state of the tide, c.1 km from the Tasman Sea, It is surrounded on 3 sides by the main course of the river and by tidal flats, and as well as this natural isolation, it is protected as a “bird sanctuary” by local bye-laws. On 14 Jan 2006, I observed a flock of 29 wrybills (Anarhynchus frontalis) arrive on the ‘sandspit’, rest briefly, then take flight again and leave the area. The weather was sunny and warm, with a light south-easterly wind, and visibility was good. The tide was rising, being about mid-tide when the birds arrived. The wrybill flock arrived at c.0930 in a compact group and landed on dry sand above high water mark c.20 m in front of my position on the western edge of the ‘sandspit’. The birds settled quickly after landing and, with a few exceptions, they scarcely moved but remained close together,with c.½ of the birds resting on 1 leg. However, the birds in the flock were sufficiently separated to be counted easily using 9 × 25 binoculars. No birds attempted to feed and the flock was silent when resting. The flock rested slightly apart from the numerous lesser knots (Calidris canutus), variable oystercatchers (Haematopus unicolor), bar-tailed godwits (Limosa lapponica), pied stilts (Himantopus himantopus), and several Pacific golden plovers (Pluvialis fulva) that were also roosting on the sandspit. After about 10 min, the wrybills departed, with a few calling as they took flight. The flock quickly gained height to 10–25 m and headed south-west along the river towards the sea, returning the way they had come.