The field identification of the orange-fronted parakeet (Cyanoramphus malherbi) has been a problem since the species was first described in 1857. Separating this critically endangered species from its more common, but also declining sympatric relative, the yellow-crowned parakeet (C. auriceps), can be difficult, as both species are cryptic and phenotypically similar. To develop criteria for consistent identification, we assessed >2,700 field observations on the orange-fronted parakeet and >10,000 field observations for the yellow-crowned parakeet, where the phenotypes of each bird was compared to the traits of the genetically defined species and verified type specimens. Observations on 117 nests also allowed observations of young from nestling to independence. We concluded that only 2 field marks can be used to reliably separate the 2 species but a clear view of either the frons or rump patch must be seen. The orange-fronted parakeet has an obvious orange frons and rump patch while these areas on the yellow-crowned parakeet are crimson. No other field traits consistently separated the 2 species. Even then, identification can be unreliable when observing juveniles, when light conditions are poor, or if the bird is high in the canopy. We recommend that unless the observer sees a clear and obvious colour in the frons or rump patch, then that bird must remain as unidentified to species.
The monitoring of endemic birds during the control of introduced mammalian predators is a common practice at community-based conservation projects in New Zealand. We describe long-term trends of endemic passerines monitored using the presence-absence technique during the control of stoats (Mustela erminea) and brushtail possums (Trichosurus vulpecula) in the Flora Valley, near Nelson, New Zealand. Data collected over an 8 year period by Friends of Flora, a community-based organisation, suggests that bellbirds (Anthornis melanura) significantly increased, while South Island robin (Petroica australis), tomtit (P. macrocephala) and rifleman (Acanthisitta chloris) populations showed little or no change, and grey warblers (Gerygone igata) significantly decreased. All species showed a greater increase during the first 4 years of the survey compared to the second 4 years, which suggests that meso-predator release of rats may have occurred from ~4 years after the start of the surveys. The presence-absence technique is simpler to conduct than the more commonly used 5-minute bird count method, and thus may be better suited for use by the community sector in similar situations.
The South Island kokako (Callaeas cinerea) was officially declared extinct in 2007, with the most recent report accepted by the Ornithological Society of New Zealand’s Rare Birds Committee, being in 1967. However reports of potential observations of South Island kokako continued to appear. We compiled a total of 241 reports between January 1990 and June 2012. These reports were categorised into 6 categories depending on the details provided by observers. The most highly ranked reports required identification of the wattles which are the most distinguishing feature of South Island kokako. The 13 reports from the highest category were submitted to the Bird Threat Ranking panel in June 2012 and, based on this evidence, the species was then reclassified from “extinct” to “data deficient”. The most compelling 11 reports were then submitted to the Ornithological Society of New Zealand’s Records Appraisal Committee (RAC). One report was accepted as a South Island kokako while 2 were deemed to be of North Island kokako. This paper reviews all available reports of the South Island kokako from 1990, the assessment process and a map of the distribution of reports. Our analysis of these reports suggests that the South Island kokako is extant.
I conducted observations on the diet of the Floreana mockingbird (Mimus trifasciatus) during its breeding season in February and March 2011. The Floreana mockingbird is a critically endangered species restricted to Gardner and Champion Islets off the coast of Floreana Island, in the Galápagos Islands, Ecuador. During 11 days, 172 feeding bouts of adult and nestling mockingbirds were observed. The majority of feeding bouts of adults (31%; 19 feeding bouts) involved the consumption of nectar and pollen of Opuntia megasperma. Another important food item consisted of Lepidopteran caterpillars (27%; 17 feeding bouts). The majority of food items fed to nestlings consisted of Lepidopteran caterpillars (26%; 29 observations), followed by adult spiders (19%; 21 observations). The reintroduction of the species to its historical range on Floreana Island is currently being planned with an emphasis on the control or eradication of invasive cats and rats. To identify key areas for reintroduction, a study on the year-round diet of the species as well as availability and variability of food items is recommended. Nectar and pollen of Opuntia megasperma was an important dietary item for the species during its breeding season. This slow-growing plant species was widespread on the lowlands of Floreana Island but introduced grazers removed Opuntia from most of its range. In the context of the potential reintroduction of this species to Floreana Island, it is important to establish if this high-energy resource is key for breeding, and consideration should be given to a supplementary food program as it has been successfully implemented for bird species elsewhere.
Translocations (deliberate movement and release of wildlife) have been of crucial importance in the management of New Zealand threatened birds, and as part of site restoration projects. We review attempts to translocate New Zealand birds for conservation reasons since 1863. Following an early pulse from 1895-1908, there was concerted and increasing effort (both in the number of translocations and the number of taxa translocated) and success since the early 1960s. Sixty- eight taxa (55 species) of New Zealand birds have been translocated in over 1100 separate releases, with new populations of 50 taxa (41 species) successfully established. Translocations of 9 further taxa (7 further species) are in progress. Overall, 61% of New Zealand’s extant endemic waterfowl, shorebird and landbird taxa have been translocated (51% of the total successfully, with an additional 4% in progress). Five taxa exist solely as translocated populations (little spotted kiwi Apteryx owenii, buff weka Gallirallus australis hectori, kakapo Strigops habroptilus, South Island saddleback Philesturnus carunculatus and black robin Petroica traversi), and 10 further taxa would be confined to single wild populations but for successful translocations. Most translocations were undertaken within historical ranges, however, 6 taxa have been established beyond their historical ranges, with attempts for 2 further taxa in progress.