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Conservation ecology of kea - Kea Conservation Trust website

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abundance caused by heavy beech seeding (Chapter 1; King 1983). We only recorded a<br />

death if a carcass was found; the disappearance <strong>of</strong> a bird was not regarded as a death.<br />

The intensity <strong>of</strong> our radio tracking was such that we are confident that the disappearance<br />

<strong>of</strong> birds was due either to transmitter malfunction, flat batteries or emigration, rather than<br />

to dead birds falling down holes and being undetectable. Most radio-tagged individuals<br />

were monitored for more than one year, giving a total sample <strong>of</strong> 89 <strong>kea</strong>-years (70 male<br />

and 19 female). We calculated survivorship by dividing the number <strong>of</strong> deaths by 89 and<br />

subtracting this from 1.<br />

Adult female survival<br />

All <strong>kea</strong> in our study area were monogamous. If the sex ratio is uneven in a monogamous<br />

population then it is important to estimate the survivorship <strong>of</strong> the rarer gender rather than<br />

the more common one. Adult female <strong>kea</strong> perform all incubation and brooding, which<br />

makes them potentially more prone to mortality by predation than males (Elliott 1996b;<br />

Wilson et al. 1998). It is, therefore, likely that adult female survival is lower than adult<br />

male survival and that the sex ratio is accordingly skewed toward males. Unfortunately,<br />

logistical considerations prevented us from radio-tagging enough adult females to<br />

separately estimate their survival from telemetry data. Instead, we assume that somatic<br />

(non-reproductive) survival among adult females is equal to that measured from the<br />

telemetry data (above), and that overall adult female survival equals somatic survival<br />

minus nesting mortality. We aimed to measure nesting mortality by colour banding adult<br />

females so that we could tell whether they went missing when their nests were preyed<br />

upon.<br />

Juvenile survival<br />

We radio-tagged eleven chicks at fledging time in the 97/98 summer. In January 1999<br />

(one year later) we flew at 7-10 thousand feet, in a radio-telemetry equipped fixed-wing<br />

aircraft (Cessna 172), over all forested mountains within a 50 kilometre radius <strong>of</strong> the<br />

nests. Following the flight, we visited all <strong>of</strong> the birds on foot to see if they were alive.<br />

We are confident that we were just as likely to detect a dead bird as a live one, as<br />

reception and coverage from the plane was exceptionally good. For example, one<br />

35

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