西伯利亚西部东南部常见红尾鸲Phoenicurus Phoenicurus (L., 1758)的繁殖生物学

IF 0.4 Q4 BIOLOGY
B. Kuranov, O. G. Nekhoroshev, Sergei V. Kilin
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Nest-boxes were placed in deciduous (aspen-birch and birch), mixed (pine-birch-aspen) and coniferous (pine and Siberian pine) forests. The density of nest-boxes in all types of forests was 107/10 ha. Nest-box occupation average rate was 10.3 ± 1.4 % and population average density was 11.4 ± 1.6 pairs/10 ha. Nest-box occupation rate in deciduous forests was 4.4 ± 0.5%; in mixed - 15.3 ± 1.3%; in coniferous - 10.4 ± 2.2%, and population density was 4.9 ± 0.6, 17.0 ± 1.5 and 11.6 ± 2.4 pairs/10 ha, respectively. In spring, redstarts appear in last decade of April-first decade of May (21 April -7 May), on average, April 28. The mean long-term date of the earliest egg laying was May 19 (13 May - 27 May); the median laying date was May 29 (23 May - 3 June). No certain long-term trend in the timing of reproduction was detected. There were no cases of two breeding cycles in the study area confirmed by ringing. However, once we observed how 8 days after the departure of fledglings a new clutch was laid in the same nest-box from which fledglings flew out. The mean clutch size is 6.84 ± 0.04 eggs, the mean length of eggs -18.60 ± 0.02 mm, the breadth of eggs -13.83 ± 0.01 mm and the mean volume of eggs - 1818 ± 3 mm3 (n = 2734 eggs). The share (proportion) of successful nests where, at least, one young fledged is 55.0%. From 3081 eggs, 1875 chicks hatched and 1667 fledglings flew out. The success of incubation is 60.9% (hatched chicks / eggs in nests where, at least, one egg was laid), feeding (fledglings / hatched chicks) -88.9%, breeding (fledglings / eggs in nests where at least one egg was laid) - 54.1%, reproductive success in successful nests - 86.0%. Embryonic mortality is 8.3%, partial brood mortality - 5.6% of the total number of hatched nestlings. The mean number of fledglings per successful attempt and breeding attempt are 5.83 ± 0.07 and 3.21 ± 0.13, respectively. Predators ravaged 41.7% of nests, in which 28.3% of eggs in incomplete and completed clutches and 4.2% of nestlings were destroyed. In total, 3.3% of nests were abandoned, and losses amounted to 1.7% of eggs in incomplete and completed clutches and 1.3% of nestlings. Reproductive success, numbers of fledglings per breeding attempt in the group of deciduous and mixed forests are significantly higher than those in coniferous forests, respectively 58.0%, 3.55 ± 0.16 and 42.8%, 2.33 ± 0.25. This is due to higher predation in coniferous forests. Clutch size, volume of eggs and number of fledglings per successful attempt in the group of deciduous and mixed forests and coniferous forests does not significantly differ, 6.88 ± 0.05, 1820 ± 4 мм3, 5.85 ± 0.08 and 6.69 ± 0.09, 1813 ± 6 мм3, 5.73 ± 0.18, respectively. In the European part of the redstart's range, in the latitude range of 48-69° N, clutch size (first breeding cycle) varies between 6.13 - 6.86 eggs (on average, 6.51 ± 0.04 eggs) (See Table 2), which is significantly less than in Western Siberia (6.84 ± 0.04 eggs) (p < 0.001). The average clutch size in the European latitude range (55-60° N) close to our study area is 6.56 ± 0.05 (6.34-6.68 eggs), also significantly less compared to our data (p < 0,001) (See Table 2). Our calculations based on the literature data given in Table 2 showed a significant tendency of increasing the clutch size in latitude range from 48 to 69° N. The dependence of the clutch size (y) on latitude (x) is described by linear regression equation: y = 5.73+0.013x (R2 = 0.24, p = 0.03, n = 20). The egg volume in Europe varied in the limits 1 700 - 1 899 мм3 (in average 1791 ± 16 mm3) and was not connected with latitude (r = 0.18, our calculations on the data are given in Table 2). 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Data were collected in the surroundings of Tomsk (56°28'N, 84°54'E, 90-100 m a.s.l.), the village Kireyevsk (Tomsk oblast, 56°22N, 84°05'E, 90 m a.s.l.) and the village Lomachevka (Kemerovo oblast, 56°08N, 86°50'E, 190 m a.s.l.). In total, we examined 516 nests. The study was conducted according to the guidelines of the Declaration of Helsinki, and approved by the Institutional Review Board (or Ethics Committee) of Institute of Biology of Tomsk State University (protocol code № 23 of 21.03.2022). Nest-boxes were placed in deciduous (aspen-birch and birch), mixed (pine-birch-aspen) and coniferous (pine and Siberian pine) forests. The density of nest-boxes in all types of forests was 107/10 ha. Nest-box occupation average rate was 10.3 ± 1.4 % and population average density was 11.4 ± 1.6 pairs/10 ha. 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Reproductive success, numbers of fledglings per breeding attempt in the group of deciduous and mixed forests are significantly higher than those in coniferous forests, respectively 58.0%, 3.55 ± 0.16 and 42.8%, 2.33 ± 0.25. This is due to higher predation in coniferous forests. Clutch size, volume of eggs and number of fledglings per successful attempt in the group of deciduous and mixed forests and coniferous forests does not significantly differ, 6.88 ± 0.05, 1820 ± 4 мм3, 5.85 ± 0.08 and 6.69 ± 0.09, 1813 ± 6 мм3, 5.73 ± 0.18, respectively. In the European part of the redstart's range, in the latitude range of 48-69° N, clutch size (first breeding cycle) varies between 6.13 - 6.86 eggs (on average, 6.51 ± 0.04 eggs) (See Table 2), which is significantly less than in Western Siberia (6.84 ± 0.04 eggs) (p < 0.001). 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引用次数: 0

摘要

对西西伯利亚东南部亚针叶林亚带常见红尾鸲(Phoenicurus Phoenicurus)繁殖生物学的长期研究结果(1983-2019)进行了分析。数据收集于托木斯克周边地区(56°28′n, 84°54′e, a.s.l. 90-100 m)、基列耶夫斯克村(托木斯克州,56°22′n, 84°05′e, a.s.l. 90 m)和洛马切夫卡村(克麦罗沃州,56°08′n, 86°50′e, a.s.l. 190 m)。我们总共检查了516个巢穴。该研究是根据赫尔辛基宣言的指导方针进行的,并得到托木斯克国立大学生物研究所机构审查委员会(或伦理委员会)的批准(议定书代码21.03.2022№23)。巢箱被放置在落叶(白杨-桦树和桦树)、混交林(松树-桦树-白杨)和针叶林(松树和西伯利亚松)中。各类型森林的巢箱密度均为107/10 ha。平均占巢率为10.3±1.4%,平均密度为11.4±1.6对/10 ha。落叶林的巢箱占用率为4.4±0.5%;混合- 15.3±1.3%;针叶林种群密度为- 10.4±2.2%,分别为4.9±0.6、17.0±1.5和11.6±2.4对/10 ha。在春季,红星出现在4月的最后一个十年至5月的第一个十年(4月21日至5月7日),平均在4月28日。平均最早产蛋的长期日期为5月19日(5月13日至5月27日);中位敷设日期为5月29日(5月23日至6月3日)。在繁殖时间方面没有发现一定的长期趋势。研究区未发现经清铃确认的两次繁殖周期病例。然而,有一次我们观察到,雏鸟离开后8天,在雏鸟飞出的同一个巢箱里产下了一窝新的蛋。平均卵数为6.84±0.04个,平均卵长-18.60±0.02 mm,平均卵宽-13.83±0.01 mm,平均卵体积- 1818±3mm3 (n = 2734个卵)。至少有一只雏鸟成功筑巢的比例为55.0%。从3081枚蛋中,孵出了1875只小鸡,1667只雏鸟飞了出来。孵化成功率为60.9%(巢中至少有一枚蛋孵出的小鸡/蛋),饲养成功率(雏鸟/孵出的小鸡)为88.9%,繁殖成功率(巢中至少有一枚蛋孵出的雏鸟/蛋)为54.1%,成功巢中繁殖成功率为86.0%。胚胎死亡率为8.3%,部分雏鸟死亡率-占孵化雏鸟总数的5.6%。平均每次尝试成功雏鸟数为5.83±0.07只,平均每次尝试繁殖雏鸟数为3.21±0.13只。41.7%的巢被捕食者破坏,其中28.3%的未孵蛋和已孵蛋被破坏,4.2%的雏鸟被破坏。总共有3.3%的巢被遗弃,损失的卵占未完成窝和未完成窝的1.7%,雏鸟占1.3%。阔叶林和混交林组的繁殖成功率和雏鸟数均显著高于针叶林组,分别为58.0%、3.55±0.16和42.8%、2.33±0.25。这是由于针叶林的捕食率更高。落叶混交林组和针叶林组的窝卵数、卵体积和雏鸟数分别为6.88±0.05、1820±4 мм3、5.85±0.08和6.69±0.09、1813±6 мм3、5.73±0.18,差异不显著。在红尾鸲活动范围的欧洲部分,在纬度48-69°N范围内,窝卵数(第一个繁殖周期)在6.13 - 6.86个蛋之间变化(平均为6.51±0.04个蛋)(见表2),显著低于西伯利亚西部(6.84±0.04个蛋)(p < 0.001)。离合器的平均尺寸在欧洲纬度范围(则高达55 -°N)接近我们的研究区域是6.56±0.05(6.34 - -6.68鸡蛋),我们的数据相比也大大减少(p < 0001)(见表2)。我们的计算基于文献表2中数据显示增加离合器大小的一个重要趋势的纬度范围从48到69°N .离合器尺寸的依赖(y)纬度(x)是由线性回归方程描述:y = 5.73 + 0.013 x (R2 = 0.24, p = 0.03, N = 20)。欧洲的鸡蛋体积变化范围为1700 - 1 899 мм3(平均1791±16 mm3),与纬度无关(r = 0.18,我们对数据的计算见表2)。欧洲和西西伯利亚的平均鸡蛋体积没有显著差异。欧洲的繁殖成功率(雏鸟/蛋在至少有一个蛋的巢中)在41.5 - 82.8%的范围内变化,每次成功尝试和繁殖尝试的雏鸟分别为5.73±0.08和4.31±0.16(我们对文献数据的计算见表3)。Вreeding西伯利亚西部红尾鸲的成功率处于欧洲已知指标的下限。西西伯利亚地区每次尝试雏鸟的数量显著低于欧洲地区(p < 0.05)。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Breeding biology of the common redstart Phoenicurus phoenicurus (L., 1758) in the south-east of Western Siberia
We analyzed the results of long-term studies (1983-2019) of breeding biology of the common redstart (Phoenicurus phoenicurus) in the sub-taiga forest subzone of the south-eastern part of Western Siberia. Data were collected in the surroundings of Tomsk (56°28'N, 84°54'E, 90-100 m a.s.l.), the village Kireyevsk (Tomsk oblast, 56°22N, 84°05'E, 90 m a.s.l.) and the village Lomachevka (Kemerovo oblast, 56°08N, 86°50'E, 190 m a.s.l.). In total, we examined 516 nests. The study was conducted according to the guidelines of the Declaration of Helsinki, and approved by the Institutional Review Board (or Ethics Committee) of Institute of Biology of Tomsk State University (protocol code № 23 of 21.03.2022). Nest-boxes were placed in deciduous (aspen-birch and birch), mixed (pine-birch-aspen) and coniferous (pine and Siberian pine) forests. The density of nest-boxes in all types of forests was 107/10 ha. Nest-box occupation average rate was 10.3 ± 1.4 % and population average density was 11.4 ± 1.6 pairs/10 ha. Nest-box occupation rate in deciduous forests was 4.4 ± 0.5%; in mixed - 15.3 ± 1.3%; in coniferous - 10.4 ± 2.2%, and population density was 4.9 ± 0.6, 17.0 ± 1.5 and 11.6 ± 2.4 pairs/10 ha, respectively. In spring, redstarts appear in last decade of April-first decade of May (21 April -7 May), on average, April 28. The mean long-term date of the earliest egg laying was May 19 (13 May - 27 May); the median laying date was May 29 (23 May - 3 June). No certain long-term trend in the timing of reproduction was detected. There were no cases of two breeding cycles in the study area confirmed by ringing. However, once we observed how 8 days after the departure of fledglings a new clutch was laid in the same nest-box from which fledglings flew out. The mean clutch size is 6.84 ± 0.04 eggs, the mean length of eggs -18.60 ± 0.02 mm, the breadth of eggs -13.83 ± 0.01 mm and the mean volume of eggs - 1818 ± 3 mm3 (n = 2734 eggs). The share (proportion) of successful nests where, at least, one young fledged is 55.0%. From 3081 eggs, 1875 chicks hatched and 1667 fledglings flew out. The success of incubation is 60.9% (hatched chicks / eggs in nests where, at least, one egg was laid), feeding (fledglings / hatched chicks) -88.9%, breeding (fledglings / eggs in nests where at least one egg was laid) - 54.1%, reproductive success in successful nests - 86.0%. Embryonic mortality is 8.3%, partial brood mortality - 5.6% of the total number of hatched nestlings. The mean number of fledglings per successful attempt and breeding attempt are 5.83 ± 0.07 and 3.21 ± 0.13, respectively. Predators ravaged 41.7% of nests, in which 28.3% of eggs in incomplete and completed clutches and 4.2% of nestlings were destroyed. In total, 3.3% of nests were abandoned, and losses amounted to 1.7% of eggs in incomplete and completed clutches and 1.3% of nestlings. Reproductive success, numbers of fledglings per breeding attempt in the group of deciduous and mixed forests are significantly higher than those in coniferous forests, respectively 58.0%, 3.55 ± 0.16 and 42.8%, 2.33 ± 0.25. This is due to higher predation in coniferous forests. Clutch size, volume of eggs and number of fledglings per successful attempt in the group of deciduous and mixed forests and coniferous forests does not significantly differ, 6.88 ± 0.05, 1820 ± 4 мм3, 5.85 ± 0.08 and 6.69 ± 0.09, 1813 ± 6 мм3, 5.73 ± 0.18, respectively. In the European part of the redstart's range, in the latitude range of 48-69° N, clutch size (first breeding cycle) varies between 6.13 - 6.86 eggs (on average, 6.51 ± 0.04 eggs) (See Table 2), which is significantly less than in Western Siberia (6.84 ± 0.04 eggs) (p < 0.001). The average clutch size in the European latitude range (55-60° N) close to our study area is 6.56 ± 0.05 (6.34-6.68 eggs), also significantly less compared to our data (p < 0,001) (See Table 2). Our calculations based on the literature data given in Table 2 showed a significant tendency of increasing the clutch size in latitude range from 48 to 69° N. The dependence of the clutch size (y) on latitude (x) is described by linear regression equation: y = 5.73+0.013x (R2 = 0.24, p = 0.03, n = 20). The egg volume in Europe varied in the limits 1 700 - 1 899 мм3 (in average 1791 ± 16 mm3) and was not connected with latitude (r = 0.18, our calculations on the data are given in Table 2). The mean egg volume in Europe and Western Siberia are not significantly different. Breeding success (fledglings / eggs in nests where, at least, one egg was laid) in Europe varies in limits 41.5 - 82.8%, fledglings per successful attempt and breeding attempt are 5.73 ± 0.08 and 4.31 ± 0.16, respectively (our calculations on the literature data are given in Table 3). Вreeding success of the redstart in Western Siberia is at the lower limit of the indicator known for Europe. The number of fledglings per attempt in Western Siberia was significantly less than that in the European part of the range (p < 0.001). We explain it by a higher level of predation in Western Siberia compared to most sites in the European part of the redstart's range. The number fledglings per successful attempt in Europe and Western Siberia is not significantly different.
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