|
|---|
Warning: Undefined property: stdClass::$Photo1 in /var/www/vhosts/virtualzoo/classifications/display.php on line 584
| Subspecies: | Unknown |
|---|---|
| Est. World Population: | 9300 |
| CITES Status: | NOT LISTED |
| IUCN Status: | Vulnerable |
| U.S. ESA Status: | NOT LISTED |
| Body Length: | |
| Tail Length: | |
| Shoulder Height: | |
| Weight: | |
| Top Speed: | |
| Jumping Ability: | (Horizontal) |
| Life Span: | in the Wild |
| Life Span: | in Captivity |
| Sexual Maturity: | (Females) |
| Sexual Maturity: | (Males) |
| Litter Size: | |
| Gestation Period: | |
Habitat:
Habitat It lives in forested mountains from sea-level to 1,600 m, but mainly in the upland zone of 700-1,300 m. It uses a wide variety of habitats including tussock grasslands, beech forests, podocarp/hardwood forests, scrub and pasture. Diet It feeds primarily on invertebrates but fallen fruit and leaves are also taken (Heather and Robertson 2015). Breeding A single egg is laid, usually in a burrow (Marchant and Higgins 1990). Incubation is amongst the longest of any bird, between 75-85 days (Calder et al. 1978). Chicks hatch fully-feathered, and first leave the nest unaccompanied after about a week. Young birds can stay with their parents for more than 12 months. It is long-lived, with mean life expectancy of radio-tagged adults of c. 50 years.
Range:
Apteryx haastii has always been confined to the South Island of New Zealand, but its range has contracted and been fragmented significantly since European settlement, and several populations have disappeared. The three main populations are: north-western Nelson to Buller River, Paparoa Range, and Hurunui River to Arthur's Pass (Heather and Robertson 2015). Translocations have introduced birds into Lake Rotoiti National park, the Flora Valley in the Arthur Range, and the Nina Valley near Lewis Pass (Heather and Robertson 2015).
Conservation:
Conservation Actions Underway
Monitoring is intensive and nationally coordinated, and uses call-counts, radio-tracking studies, and 5-yearly territory mapping at a couple of sites (Saxon and North Hurunui) in which specially-trained dogs find banded birds whose territories are mapped from radio-tracking records. Several small populations in the eastern Southern Alps, Paparoa Range, Lake Rotoiti National Park and in the Arthur Range are managed intensively by controlling predators (H.A. Robertson in litt. 1999), and also by removing and incubating eggs and returning the subadults once they are large enough to fend off predators (Holzapfel et al. 2008). The latter approach is known as Operation Nest Egg (ONE) (Colbourne et al. 2005). Landscape-scale aerial 1080 operations of 10,000 - 200,000 ha are likely to be of great benefit to the species, judging by the high numbers of subadult birds found at such sites in the 2-3 years after such operations. Leg-hold traps for predators are routinely raised above the ground in kiwi areas to prevent accidental trapping (H.A. Robertson in litt. 1999).
Conservation Actions Proposed
Increase the proportion of the kiwi population that is managed and control predators at a landscape scale to produce growth rates of 2% per year or greater (Germano et al. 2018). Measure the response of kiwi to management to determine optimal landscape-scale management (Germano et al. 2018). Carry out large-scale 3-yearly aerial 1080 operations to benefit populations of >200 pairs in NW Nelson, North Westland, Paparoa Range and Southern Alps (H. Robertson in litt. 2016) and potentially create a source for introductions into other areas. Encourage community groups to carry out predator trapping at other sites. Intensively manage at least three (preferably four) populations to secure a minimum of 200 pairs within each managed population (Holzapfel et al. 2008, H. Robertson in litt. 2016). Use ONE in a few accessible sites or where nests are threatened by mining activities. Undertake population modelling to determine regional variation in population dynamics (Holzapfel et al. 2008). Investigate landscape-scale remote monitoring techniques for sparse populations (Holzapfel et al. 2008). Promote legislative and policy changes to protect populations and encourage high-quality advocacy at all levels (Robertson 1998, Holzapfel et al. 2008). Educate and inform the public and encourage community involvement in Kiwi conservation (Robertson 2003, Holzapfel et al. 2008).
Monitoring is intensive and nationally coordinated, and uses call-counts, radio-tracking studies, and 5-yearly territory mapping at a couple of sites (Saxon and North Hurunui) in which specially-trained dogs find banded birds whose territories are mapped from radio-tracking records. Several small populations in the eastern Southern Alps, Paparoa Range, Lake Rotoiti National Park and in the Arthur Range are managed intensively by controlling predators (H.A. Robertson in litt. 1999), and also by removing and incubating eggs and returning the subadults once they are large enough to fend off predators (Holzapfel et al. 2008). The latter approach is known as Operation Nest Egg (ONE) (Colbourne et al. 2005). Landscape-scale aerial 1080 operations of 10,000 - 200,000 ha are likely to be of great benefit to the species, judging by the high numbers of subadult birds found at such sites in the 2-3 years after such operations. Leg-hold traps for predators are routinely raised above the ground in kiwi areas to prevent accidental trapping (H.A. Robertson in litt. 1999).
Conservation Actions Proposed
Increase the proportion of the kiwi population that is managed and control predators at a landscape scale to produce growth rates of 2% per year or greater (Germano et al. 2018). Measure the response of kiwi to management to determine optimal landscape-scale management (Germano et al. 2018). Carry out large-scale 3-yearly aerial 1080 operations to benefit populations of >200 pairs in NW Nelson, North Westland, Paparoa Range and Southern Alps (H. Robertson in litt. 2016) and potentially create a source for introductions into other areas. Encourage community groups to carry out predator trapping at other sites. Intensively manage at least three (preferably four) populations to secure a minimum of 200 pairs within each managed population (Holzapfel et al. 2008, H. Robertson in litt. 2016). Use ONE in a few accessible sites or where nests are threatened by mining activities. Undertake population modelling to determine regional variation in population dynamics (Holzapfel et al. 2008). Investigate landscape-scale remote monitoring techniques for sparse populations (Holzapfel et al. 2008). Promote legislative and policy changes to protect populations and encourage high-quality advocacy at all levels (Robertson 1998, Holzapfel et al. 2008). Educate and inform the public and encourage community involvement in Kiwi conservation (Robertson 2003, Holzapfel et al. 2008).




