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Monitoring and management of kereru (Hemiphaga novaeseelandiae)
Available Online

Hay, Rod

,

Mander, Christine

,

Powlesland, Ralph

1998
The endemic kereru (Hemiphaga novaeseelandiae) (also known as kuku, kukupa or New Zealand pigeon, but henceforth referred to as kereru) and the Chatham Island subspecies, parea (Hemiphaga novaeseelandiae chathamensis), are the only extant representatives of the genus Hemiphaga. A programme has been set up to monitor kereru populations. The aim of this monitoring programme is to provide a clearer picture of medium- to long-term trends in kereru populations at key sites (e.g., mainland “island” management sites and their paired non-treatment sites), and to document the responses of kereru populations to management actions. This report sets out the requirements for monitoring kereru at key sites as part of a national programme. In addition, it is intended to be used as a practical guide for anyone (e.g., iwi, conservation groups, school groups) planning to initiate a kereru monitoring project. The most efficient way of detecting and interpreting kereru population trends is considered to be by undertaking 5-minute counts with distance estimates in conjunction with phenology monitoring and display flight monitoring. It is therefore recommended that others use these methods wherever possible. A section on other techniques is included to cover situations where 5-minute counts may not be practicable. Wherever possible, kereru monitoring should be integrated into existing Department of Conservation bird monitoring and management programmes, rather than requiring the initiation of new projects. Iwi, conservation groups and interested members of the public will be encouraged to participate in kereru monitoring and conservation management. Annual results from each site should be forwarded to the programme co-ordinator, who will review and collate the data, and prepare an annual report for distribution to all participants and interested parties. Explanation of the programme, relevant aspects of kereru ecology, and background information are provided in the main text. Descriptions of the actual methods are given in the appendices.
Environmental effects of rodent Talon baiting Part I : Monitoring for toxic residues : Part II Impacts on invertebrate populations
BRB
Available Online

Morgan, D. R.

,

Spurr, E. B.

,

Wright, G. R.

1998
Although Talon® baits containing brodifacoum have been used successfully in eradicating rats from some of New Zealand’s offshore islands, little is known about any environmental effects of this toxin. We sampled invertebrates, blackbirds, soil, and water at intervals of 2 days to 9 months to determine whether brodifacoum residues were present after aerial distribution of Talon® 20P cereal pellets on Red Mercury Island and after bait-station use of Talon® 50WB wax-coated cereal blocks on Coppermine Island. No brodifacoum residues were found in soil, water, or most (99%) invertebrate samples. Low to moderate residues were found in one sample of slugs collected 2 days after aerial sowing. Tissues from all birds (n=4) and rats (n=3) found dead and livers from all six birds collected alive 8 months after aerial baiting also contained low to moderate residues. These preliminary results suggest that few invertebrates are likely to be contaminated as a result of Talon® baiting. Tentatively, we suggest that although some invertebrates may eat Talon® baits, it appears that the brodifacoum is either metabolised and/or excreted within a few days. The dead blackbirds found, therefore, were more likely to have been killed by primary than by secondary poisoning. Further monitoring for brodifacoum residues after Talon® operations should be undertaken to confirm that contamination of invertebrates, soil, and water is unlikely. Some bird species may be at risk from Talon® baiting. Likely effects on population levels of such species should be considered to help assess the risk and benefits of Talon® use in rodent eradication.