变化环境下北苍鹰的长期人口统计

IF 4.3 1区 生物学 Q1 ECOLOGY
Richard T. Reynolds, Jeffrey S. Lambert, Curtis H. Flather, Gary C. White, Benjamin J. Bird, L. Scott Baggett, Carrie Lambert, Shelley Bayard De Volo
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The pooled 20-year nestling sex ratio did not differ from unity (53% M; <i>n</i> = 410 M, 366 F) but was significantly male-biased in 2 years and female-biased in 1 year. Nonetheless, the overall greater production of male fledglings followed a strong trend of greater male production in other goshawk populations, suggesting that breeders might have been adaptively adjusting their offspring sex ratio, perhaps to produce more of the rarer (male) sex. Annual recruitment of new individuals into the breeding population averaged 43% during the study. Study area recruitment rate of hawks locally born (<i>in situ</i>) and banded was 0.12. Both sexes had equal tendencies to return to the Kaibab Plateau to breed (no differences in philopatry) and there were no differences in natal dispersal distances (natal to first breeding site) between the sexes. During the final years of study (1999–2010), an estimated 46% of breeding recruits were locally born and 54% were immigrants from distant forests. 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Although sex was not in the top survival model, models including age + sex were competitive, evidencing lower male than female survival, a finding corroborated by the occurrence of sex effects in the top λ model. Lower male survival may result from higher mortality associated with hunting agile prey in vegetation-filled environments during long breeding seasons when they are the primary forager. Lower survival may be compensated by the more frequent production (53%) of male fledglings. High-severity crown fire was an existential threat to the population. 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引用次数: 19

摘要

新北极北部苍鹰(学名:Accipiter gentilis atricapillis)栖息在北美北部到西南山区的针叶林、阔叶林和混交林中。作者报告了在美国亚利桑那州北部的凯巴布高原(Kaibab Plateau)进行的一项为期20年的捕鸟调查(1991-2010),对该物种的繁殖者分布和密度、繁殖的时空变异性、雏鸟性别比、本地与外来繁殖者的招募、繁殖年龄结构、年龄特异性存活率和种群变化率(λ)进行了调查。我们使用信息论方法对模型进行排序,这些模型代表了降水年波动对苍鹰繁殖和羽翼产量的年频率影响的不同假设。我们研究了125个苍鹰繁殖地,在一个1728平方公里的研究区域中,根据区域中心之间的平均距离3.8公里,估计了144个区域,约占总数的87%。种群的显著人口统计学特征是繁殖的年际变化较大,表现为产卵对比例、雏鸟大小、筑巢失败率和雏鸟产量的年际变化较大。上一年已知的当年产卵区域的比例为8% ~ 86% (= 37%,SE = 4.51),年平均筑巢失败率(活动巢失败)为12% ~ 48%(总体= 23%,SE = 2.48),年平均成功巢(羽翼≥1只羽翼)的孵化量为1.5 ~ 2.5只(总体= 2.0只,SE = 0.03)。繁殖的年际变化与降水的年际变化密切相关,我们假设降水影响了原始森林生产力和鸟类和哺乳动物的猎物丰度。最好的繁殖年份(1992-1993年,产卵对的77-87%)与创纪录的El Niño-Southern涛动(ENSO)湿期一致;最差的繁殖年份(2003年);这是连续3年创纪录干旱的最后一次。总体育种成功率为83%,大多数失败发生在孵化期间;一旦蛋孵出,苍鹰往往会孵出雏鸟。合并20年的雏鸟性别比与统一组没有差异(53% M;n = 410 M, 366 F),但在2年内有显著的男性偏倚,在1年内有显著的女性偏倚。尽管如此,在其他苍鹰种群中,雄性雏鸟的总体产量较高,而雄性雏鸟的产量也较高,这表明繁殖者可能已经适应性地调整了它们后代的性别比例,也许是为了产生更多罕见的(雄性)性别。在研究期间,每年新个体进入繁殖种群的平均比例为43%。研究区本地出生(原位)和带状的鹰的招募率为0.12。两性返回凯巴布高原繁殖的倾向相同(在哲学上没有差异),两性之间的出生分散距离(出生到第一繁殖地)没有差异。在研究的最后几年(1999-2010年),估计46%的繁殖新兵是本地出生的,54%是来自遥远森林的移民。首次繁殖的最小年龄为2岁,已知年龄的雄鹰(雏鹰时被绑扎或首次繁殖时在羽毛上长大)首次繁殖的平均年龄为3.7岁,雌性为3.5岁。已知年龄的苍鹰的平均寿命(从雏鸟第一次佩戴到最后一次佩戴)男女均为6.9年。年龄≥4岁的种鸡,以首次捕获时的羽毛为基础,平均最小表观寿命为6.5年。首次被发现的苍鹰的平均年龄为3.9岁,当时雌雄苍鹰的表观存活率估计为0.77,略低于年龄函数的峰值存活率0.78。年龄特异性生存率估计显示,9岁后稳步下降,20岁时接近0。繁殖成虫λ估计值(M, 0.94, SE = 0.037;F, 0.98, SE = 0.038)仅提供了研究期间种群下降的微弱证据。尽管性别不在最高生存模型中,但包括年龄+性别在内的模型是竞争性的,表明雄性比雌性存活率低,这一发现在最高λ模型中得到了性别效应的证实。在漫长的繁殖季节,雄性是主要的觅食者,在植被茂密的环境中捕猎敏捷的猎物,这可能导致雄性存活率较低,死亡率较高。较低的存活率可以通过雄性雏鸟的频繁繁殖(53%)来弥补。严重程度高的冠火对人口构成了生存威胁。 在1991年之前的30年里,除了4次严重的大火烧毁了大约3770公顷(相当于3个苍鹰领地),在我们的研究期间,6次严重的大火烧毁了另外30945公顷,并杀死了8个已知领地的大部分森林(64%),可能还有2次在我们完成调查之前被烧毁。基于在年龄结构上缺乏任何近期的人口结构扰动,相对较高且时间恒定的年成鸟存活率,在成鸟λ估计附近的置信区间重叠1.0,以及研究区域饱和,我们推测在20年的研究中,凯巴布高原的苍鹰种群是稳定的。尽管如此,由于种群的繁殖频率呈下降趋势,非繁殖成虫的状态(死亡、存活、迁移)不确定,育种存在广泛的时空差异,以及凯巴布高原繁殖种群的高迁移频率,种群的未来状况仍然存在不确定性。如果长达一个世纪的降水下降持续下去,特别是以1980年以来的增加速度持续下去,并表现为更严重的干旱、更少的湿润期和更弱的森林生产力脉冲,那么凯巴布高原的苍鹰数量将显示出明确的下降证据。证据包括当地和区域苍鹰的繁殖和生存减少,迁徙频率减少,灾难性火灾导致栖息地进一步丧失。©2017野生动物协会。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Long-term demography of the Northern Goshawk in a variable environment

The Nearctic northern goshawk (Accipiter gentilis atricapillis) is a resident of conifer, broadleaf, and mixed forests from the boreal to the southwestern montane regions of North America. We report on a 20-year mark-recapture investigation (1991–2010) of the distribution and density of breeders, temporal and spatial variability in breeding, nestling sex ratios, local versus immigrant recruitment of breeders, breeding age structure, age-specific survival rates, and rate of population change (λ) of this species on the Kaibab Plateau, a forested sky island in northern Arizona, USA. We used an information-theoretic approach to rank models representing alternative hypotheses about the influence of annual fluctuations in precipitation on the annual frequency of goshawk breeding and fledgling production. We studied 125 goshawk breeding territories, representing approximately 87% of an estimated 144 total territories based on a mean distance of 3.8 km between territory centers in a 1,728-km2 study area. The salient demographic feature of the population was extensive annual variation in breeding, which manifested as large inter-annual variation in proportions of pairs laying eggs, brood sizes, nest failure rates, and fledgling production. The percent of territories known in a prior year in which eggs were laid in a current year ranged from 8% to 86% ( = 37%, SE = 4.51), annual mean nest failure rate (active nests that failed) ranged from 12% to 48% (overall  = 23%, SE = 2.48), and mean annual brood size of successful nests (fledged ≥1 fledgling) ranged from 1.5 young to 2.5 young (overall  = 2.0 young, SE = 0.03). Inter-annual variation in reproduction closely tracked inter-annual variation in precipitation, which we hypothesize influenced primary forest productivity and bird and mammal prey abundance. The best breeding years (1992–1993, 77–87% of pairs laid eggs) were coincident with a record-long El Niño-Southern Oscillation (ENSO) wet period and the worst breeding year (2003; 8% of pairs laid eggs) was the last of a 3-year record drought. Overall breeding success was 83% with most failures occurring during incubation; once eggs hatched, goshawks tended to fledge young. The pooled 20-year nestling sex ratio did not differ from unity (53% M; n = 410 M, 366 F) but was significantly male-biased in 2 years and female-biased in 1 year. Nonetheless, the overall greater production of male fledglings followed a strong trend of greater male production in other goshawk populations, suggesting that breeders might have been adaptively adjusting their offspring sex ratio, perhaps to produce more of the rarer (male) sex. Annual recruitment of new individuals into the breeding population averaged 43% during the study. Study area recruitment rate of hawks locally born (in situ) and banded was 0.12. Both sexes had equal tendencies to return to the Kaibab Plateau to breed (no differences in philopatry) and there were no differences in natal dispersal distances (natal to first breeding site) between the sexes. During the final years of study (1999–2010), an estimated 46% of breeding recruits were locally born and 54% were immigrants from distant forests. Minimum age at first breeding was 2 years and mean age at first breeding by known-age hawks (banded as nestlings or aged on plumage at first breeding) was 3.7 years for males and 3.5 years for females. Mean lifespan (yr from first banding as nestling to last resighting) of known-age goshawks was 6.9 years for both sexes. Mean minimum apparent lifespan of breeders aged ≥4 years based on plumage at first capture was 6.5 years for both sexes. Average age of goshawks at their first detection was 3.9 years old, at which time apparent survival was estimated at 0.77 for both sexes, which was just slightly less than the peak survival of 0.78 as a function of age. Age-specific survival estimates showed a steady decline after 9 years old and approached 0 at 20 years of age. Estimates of λ for breeding adults (M, 0.94, SE = 0.037; F, 0.98, SE = 0.038) provided only weak evidence for a population decline during the study. Although sex was not in the top survival model, models including age + sex were competitive, evidencing lower male than female survival, a finding corroborated by the occurrence of sex effects in the top λ model. Lower male survival may result from higher mortality associated with hunting agile prey in vegetation-filled environments during long breeding seasons when they are the primary forager. Lower survival may be compensated by the more frequent production (53%) of male fledglings. High-severity crown fire was an existential threat to the population. In addition to 4 large high-severity fires that burned roughly 3,770 ha (equal to 3 goshawk territories) in the 30 years preceding 1991, 6 high-severity fires burned another 30,945 ha during our study and killed most (>64%) of the forests in 8 known territories and possibly another 2 that were burned before we completed surveys.

Based on a lack of any recent demographic perturbations in age structure, a relatively high and time-constant annual adult survival rate, confidence intervals around adult λ estimates overlapping 1.0, and a study area saturated with territories, we surmise that the goshawk population on the Kaibab Plateau was stable during the 20-year study. Nonetheless, uncertainty remains regarding the population's future status because of a declining trend in breeding frequency, uncertain status (dead, alive, emigrated) of non-breeding adults, extensive temporal and spatial variation in breeding, and high frequency of immigrant recruits to the breeding population on the Kaibab Plateau. If the century-long decline in precipitation persists, especially at the increased rate seen since 1980, and manifests as deeper droughts, diminished wet periods, and weaker pulses in forest productivity, then the Kaibab Plateau goshawk population would be expected to show unambiguous evidence of decline. Evidence would include reduced local and regional goshawk reproduction and survival, reduced frequency of immigration, and further habitat loss to catastrophic fire. © 2017 The Wildlife Society.

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来源期刊
Wildlife Monographs
Wildlife Monographs 生物-动物学
CiteScore
9.10
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0.00%
发文量
3
审稿时长
>12 weeks
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