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新西兰泰阿罗阿头北部皇家信天翁的人口率。

Demographic rates of northern royal albatross at Taiaroa Head, New Zealand.

机构信息

Dragonfly Science , Wellington , New Zealand.

Department of Conservation , Moray Place, Dunedin , New Zealand.

出版信息

PeerJ. 2015 Apr 28;3:e906. doi: 10.7717/peerj.906. eCollection 2015.

DOI:10.7717/peerj.906
PMID:25945308
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC4419553/
Abstract

Demographic rates, such as annual survival rate, are generally difficult to estimate for long-lived seabirds, because of the length of time required for this kind of study and the remoteness of colonies. However, a small colony of northern royal albatross (Diomedea sanfordi) established itself on the mainland of New Zealand at Taiaroa Head, making possible regular banding and monitoring of its individuals since the first chick fledged, in 1938. Data on the presence/absence of birds, as well as on breeding outcomes, were available for the period from 1989-90 to 2011-12, and included 2128 annual resightings of 355 banded individuals of known age. The main goal of the present study was to estimate the annual survival rate of juveniles, pre-breeders, and adults at Taiaroa Head. These rates were estimated simultaneously in a single Bayesian multi-state capture-recapture model. Several models were fitted to the data, with different levels of complexity. From the most parsimonious model, the overall annual adult survival rate was estimated as 0.950 (95% CI [0.941-0.959]). In this model, adult survival declined with age, from 0.976 (95% CI [0.963-0.988]) at 6 years, the minimum age at first breeding, to 0.915 (95% CI [0.879-0.946]) at 40 years. Mean annual survival of pre-breeders was 0.966 (95% CI [0.950-0.980]), and 0.933 (95% CI [0.908-0.966]) for juveniles. There was no discernible difference in survival between males and females, and there was no apparent trend in survival over time. Estimates of other demographic rates were also obtained during the estimation process. The mean age at first return of juveniles to the colony was estimated as 4.8 years (95% CI [4.6-5.1]), and the mean age at first breeding as 8.9 years (95% CI [8.5-9.3]). Because all the birds of the colony were banded, it was possible to estimate the total population size. The number of northern royal albatross present annually at the Taiaroa Head colony has doubled since 1989-90, and the current total population size was estimated to be over 200 individuals. The ratio of the total population size to the number of annual breeding pairs varied from 5 to 12 among years, with an overall mean of 7.65 (95% CI [7.56-7.78]), and this high variability highlights the need for a sufficient number of surveys of seabird breeding populations before reliable conclusions on population trends can be made. Although long-term data allowed estimates of demographic rates of northern royal albatross at Taiaroa Head, the location of the colony and the ongoing management by staff mean that the population dynamics may differ from those of the main population on the Chatham Islands.

摘要

人口增长率,如年存活率,通常很难对长寿海鸟进行估计,因为这项研究需要很长的时间,而且海鸟的栖息地通常很偏远。然而,在新西兰的泰阿罗阿角,一个北皇家信天翁(Diomedea sanfordi)的小群体在大陆上建立了自己的栖息地,自 1938 年第一只雏鸟离巢以来,对其个体进行定期的环志和监测成为可能。1989-90 年至 2011-12 年期间,有关于鸟类存在/不存在以及繁殖结果的数据,包括已知年龄的 355 只佩戴标记的个体的 2128 次年度重见记录。本研究的主要目的是估计泰阿罗阿角北皇家信天翁幼鸟、亚成体和成鸟的年存活率。这些比率在单个贝叶斯多状态捕获-再捕获模型中同时进行了估计。对数据进行了不同复杂程度的几个模型拟合。从最简约的模型中,估计出成年个体的总体年存活率为 0.950(95%置信区间[0.941-0.959])。在这个模型中,成年个体的存活率随年龄的增长而下降,从 6 岁(首次繁殖的最小年龄)的 0.976(95%置信区间[0.963-0.988])下降到 40 岁的 0.915(95%置信区间[0.879-0.946])。亚成体的平均年存活率为 0.966(95%置信区间[0.950-0.980]),幼鸟的平均年存活率为 0.933(95%置信区间[0.908-0.966])。雌雄个体的存活率没有明显差异,而且随着时间的推移,存活率也没有明显的趋势。在估计过程中还获得了其他人口增长率的估计值。幼鸟返回栖息地的首次平均年龄估计为 4.8 岁(95%置信区间[4.6-5.1]),首次繁殖的平均年龄估计为 8.9 岁(95%置信区间[8.5-9.3])。由于所有的鸟都佩戴了环志,因此可以估计出种群的总体规模。自 1989-90 年以来,泰阿罗阿角北皇家信天翁的数量每年翻一番,目前的总种群数量估计超过 200 只。种群总规模与每年繁殖对的数量之比在不同年份从 5 到 12 不等,总体平均值为 7.65(95%置信区间[7.56-7.78]),这种高度的可变性突出表明,在能够就种群趋势得出可靠结论之前,需要对海鸟繁殖种群进行足够数量的调查。尽管长期数据可以估计泰阿罗阿角北皇家信天翁的人口增长率,但由于栖息地的位置和工作人员的持续管理,种群动态可能与查塔姆群岛主要种群的动态不同。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/e365/4419553/1ce6b7b6d538/peerj-03-906-g009.jpg
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https://cdn.ncbi.nlm.nih.gov/pmc/blobs/e365/4419553/3b0dcef910a2/peerj-03-906-g007.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/e365/4419553/87f88f3a1d6a/peerj-03-906-g008.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/e365/4419553/1ce6b7b6d538/peerj-03-906-g009.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/e365/4419553/f6d2696daa8b/peerj-03-906-g001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/e365/4419553/cf84b21e0d63/peerj-03-906-g002.jpg
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https://cdn.ncbi.nlm.nih.gov/pmc/blobs/e365/4419553/00654e0fe09c/peerj-03-906-g004.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/e365/4419553/7c9304831d11/peerj-03-906-g005.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/e365/4419553/0269a08d3e0e/peerj-03-906-g006.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/e365/4419553/3b0dcef910a2/peerj-03-906-g007.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/e365/4419553/87f88f3a1d6a/peerj-03-906-g008.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/e365/4419553/1ce6b7b6d538/peerj-03-906-g009.jpg

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