新疆木垒波斑鸨营巢成功率的初步研究

1998年 4月中旬～ 7月中旬 ,对分布于新疆木垒的波斑鸨 (Chlamydotisundulatamacqueenii)种群的营巢成功率进行了初步考察与研究。考察中共发现 16个巢、2 5窝幼雏。每巢产卵 3～ 6枚 ,卵鲜重 (6 4 7± 5 8)g ,卵径为 6 0 9mm× 43 9mm。产卵有两个高峰期 ,表明雌鸟第 1次繁殖失败后可再次产卵。第 1产卵期的巢卵数为(4 1± 0 8)枚 ,第 2产卵期的巢卵数为 (3 5± 0 6 )枚。雌鸟营巢成功率为 77 5 %～ 87 5 % ,卵的孵化率为83 6 %。每窝内从破壳到具备飞行能力的幼雏数基本不变 ,表明繁殖雌鸟大都能将幼雏全部抚育到可以飞行的年龄     

吉林白城地区草原栗斑腹(巫鸟)窝卵数、营巢成功率和繁殖成功率的研究

对分布于吉林白城地区草原生境中栗斑腹巫鸟的窝卵数、营巢成功率和繁殖成功率的初步研究结果表明 ,繁殖期栗斑腹巫鸟种群的平均窝卵数为 5 .0 9± 0 .5 8枚 /巢 ;窝卵数与产卵期、出巢数与产卵期、窝卵数与卵大小之间呈负相关 ,产卵期与孵化率之间存在极显著的负相关关系 ,巢外径与窝卵数之间存在显著的正相关关系 ,巢的其余指标均与窝卵数呈正相关 ;平均孵化期为 12± 0 .4 9d ,孵化率为 36 .3% ,繁殖成功率为 11.11% ;7日龄以上的雏鸟群体大小为 2 .5 6± 1.5 3只 ,栗斑腹巫鸟的雏鸟存活率为 2 7.6 9% .     

新疆木垒波斑鸨卵的孵化温度及雌鸟孵化行为的初步研究

1999年 5月 2 2日到 6月 11日 ,在新疆木垒波斑鸨分布区利用装有温度记录仪的假卵成功地监测了2只雌性波斑鸨 (Chlamydotisundulatamacqueenii)的繁殖行为。研究表明 :在孵化期 ,雌鸟的日活动节律呈现出双峰模式 ,即晨昏活动。雌鸟平均每天离巢 3～ 9次 ,每次 8～ 2 6min。孵化过程中 ,雌鸟每天花费 (94±2 ) %的时间孵卵。当雌鸟孵卵时 ,卵的日均孵化温度为 31 9～ 36 5℃。当雌鸟离开巢时 ,卵的温度平均下降到(2 4 9± 3 2 )℃。随着孵化的进行 ,卵的日均温从 31 9℃上升到 36 2℃ ,与环境温度的变化呈正相关。     

灰椋鸟的繁殖生态

1994年 3月至 7月在吉林省左家自然保护区对灰椋鸟的繁殖生态研究发现 ,在 1 2 2hm2 的面积内共有 36个灰椋鸟巢 ,繁殖密度为 0 32 1巢 hm2 。繁殖期由 4月 2 4日持续到 7月 1 1日共 79d。平均窝卵数为 5 89(SD =1 1 7,n =36 ) ,窝卵数同繁殖季节呈显著负相关 (r=-0 75 72 ,P <0 0 1 )。平均孵化期为1 3 6d ,平均育雏期 2 1 6d。平均每巢出飞 5 1只幼鸟。幼体 (卵、雏鸟 )死亡的最主要原因是人为干扰。     

台湾中部暗绿绣眼鸟的繁殖生物学

本研究将暗绿绣眼鸟 (Zosteropsjaponicasimplex)捕捉、套彩色环后释放 ,分别于 1999年和 2 0 0 1年 3～ 8月追踪监测 7对和 13对暗绿绣眼鸟的繁殖行为。总结此二年对 2 0对暗绿绣眼鸟的监测 ,其繁殖期始于 3月中旬 ,终止于 8月下旬。 1对最多可年产 5窝 ,但以 3～ 4窝为常见。初次筑巢所需时间平均为 10 4d ,筑第 2、3巢的时间依次减少 ;窝与窝之间的繁殖间隔视情况而定 ,如孵化或喂养失败 ,通常都在 1～ 2d内再筑巢 ,如繁殖育雏成功 ,平均相隔 7d再筑巢。 2年 6 3窝的窝卵数平均为 2 6 8± 0 71(n =6 3)枚 ;孵化期平均为 11±0 6 4 (n =4 7)d ;6 3窝孵化成功 4 7窝 ,孵化成功率为 74 6 % ;雏鸟离巢日龄平均为 10 5± 0 88(n =35 )d ;4 7窝雏鸟喂养成功 35窝 ,育雏成功率为 74 5 % ;6 3窝繁殖成功 35窝 ,繁殖成功率为 5 5 5 %。失败因素包括气候、动物掠食、人为破坏和其它不明原因     

斑背大尾莺sinensis亚种的繁殖生物学

斑背大尾莺（Megalurus pryeri）为东亚特有鸟类,数量稀少（常家传,1995;马敬能等,2000）,2003年IUCN世界濒危物种红皮书将斑背大尾莺列为易危物种（汪松、解焱,2004）。斑背大尾莺有2个亚种,指名亚种（M．P．pryeri）仅在日本本州岛北部的Kanto平原北部繁殖,越冬区在本州岛中部的太平洋沿岸（Fujitaand Nagata,1997）;sinensis亚种在我国仅见于湖北汉口（冬候鸟）、河北秦皇岛（旅鸟）和辽宁朝阳地区（繁殖鸟？）（郑作新,1987）。     

江西吉安乌鸫的繁殖生态研究

2009～2010年对江西省吉安地区乌鸫Turdus merula的繁殖进行了调查研究,结果表明:当地乌鸫的营巢时间在3月9日至16日,产卵时间是3月18日至26日,平均窝卵数5.14(4～6)枚(n=14),平均卵大小29.71 mm×21.16 mm,平均卵重6.63 g(n=71).孵卵和暖巢主要由雌鸟承担,但雄鸟也有暖巢行为,孵化率为65.83%,育雏期13～15 d,离巢率高达100%.与高海拔的乌鸫相比,当地乌鸫产大窝小卵,这一特征保证了大窝雏数和高离巢率,繁殖对策属于r-选择.     

北热带石灰岩地区红耳鹎的繁殖生态和巢址选择

热带鸟类的生活史进化策略与温带鸟类的不同,而迄今国内对热带鸟类的研究却非常缺乏,红耳鹎(Pycnonotus jocosus)在我国北热带地区分布广泛,是较为理想的研究对象。2010年至2014年春夏季,对北热带石灰岩地区红耳鹎的繁殖生态和巢址选择进行了研究。采用系统搜寻法并根据亲鸟行为寻巢,应用方差分析和主成分分析对相关数据进行处理。结果显示,红耳鹎的产卵期集中在4月中旬至5月下旬,喜筑巢于灌木和人工种植的苹婆(Sterculia nobilis)树。平均窝卵数为(3.4±0.5)枚(3~4枚),卵重(2.59±0.29)g,卵大小(21.10±1.73)mm×(15.35±1.50)mm(n=31)。总的繁殖成功率为36.16%,繁殖失败的主要原因是天敌捕食、弃巢和人为干扰。一年繁殖一次和较低的繁殖成功率是研究地的红耳鹎有较大窝卵数的主要原因。红耳鹎在巢址选择时主要考虑避雨因子、避敌因子和灌木因子。     

杂色山雀的繁殖成功率

2004～2006年的3～7月,在辽宁省白石砬子国家级自然保护区,对杂色山雀(Parus varius)的繁殖及繁殖成功率进行了初步研究。结果显示,杂色山雀主要营巢于海拔400～900m的阔叶杂木林、针叶林及林缘地带;繁殖期在3～7月,其洞巢种类多样,筑巢期约15d;巢为碗状,巢结构的2/3由苔藓构成;窝卵数为6～8枚,平均(6·92±0·92)枚(n=13);雌鸟单独孵卵,孵化期为(14·00±0·00)d(n=10);育雏由雌雄鸟共同承担,育雏期为(17·50±0·58)d(n=4)。杂色山雀繁殖成功率为50·95%,繁殖力为2·22。人为干扰是造成卵和雏鸟损失的主要原因,占总损失的74·19%。     

Characterization of 22 microsatellites loci from the endangered Houbara bustard (Chlamydotis undulata undulata)

Here we present a new set of 22 microsatellite loci isolated from Chlamydotis undulata undulata, an endangered Houbara bustard found across North Africa. The number of alleles per locus ranged from one to nine, and heterozygosities ranged from 0.167 to 0.944. Total exclusionary probabilities using these loci for the first and the second parent were 0.992932 and 0.999915, respectively. Successful cross‐amplification was observed in eight other Otididae species (12–22 of the 22 loci). These microsatellite markers are powerful tools for genetic identification, paternity assignment and population genetic studies.     

Genetic variability characterization of the moroccan houbara bustard (Chlamydotis undulata undulata) inferred from pedigree analysis

A Moroccan Houbara Bustard pedigree was analyzed to evaluate the genetic variability in captive breeding population using genealogical approaches. The whole Houbara breeding flock (WP) for the period 1993–2004 was made up of 531 birds comprising 346 females and 185 males. The reference population (RP) comprised 198 individuals ready for reproduction from 2000 to 2004 cohorts. The corresponding percentage of known ancestors was estimated as 98.23% for the parent generation, 41.19% for the grandparent generation and 7.00% for the great grandparents generation. The average generation interval for Houbara was computed as 4.64 years. Genetic variability loss per generation was ascertained using the effective population size (), the founder genome equivalent (fge), the effective number of ancestors and founders (fa) and (fe), respectively, for the RP and across each cohort. The results showed no bottleneck events in the breed but some loss of genetic variability just after the initiation of the conservation program. However, the annual effective population size based on the realized increase in inbreeding () was estimated to be 207 for the RP and 1,000 for the WP. With regard to conservation breeding schemes, the genealogical evidence presented here is very useful as it revealed the positive effect of migration on Houbara breeding. The mating strategies will assist in the future control and management of the genetic variability of this population. Zoo Biol. 32:366‐373, 2013. © 2012 Wiley Periodicals, Inc.     

Genetic variation across the current range of the Asian houbara bustard (Chlamydotis undulata macqueenii)

The houbara bustard (Chlamydotisundulata), the main quarry for Arab falconry,is currently threatened by excessive huntingand poaching as well as by habitat loss andfragmentation. We have investigated the geneticdiversity, population structure and demographichistory of houbara bustards across theirgeographical range by analyzing mitochondrial(mt)DNA sequences (a 370 bp fragment of controlregion I and a 264 bp fragment of thecytochrome b gene) and 4 microsatelliteloci in 74 individuals sampled from the CanaryIslands to China. Both markers revealed low tomoderate diversity that could be partitionedinto two monophyletic groups or evolutionarysignificant units belonging to the NorthAfrican (C. u. undulata) and Asian (C. u. macqueenii) subspecies. A history ofrelatively recent population growth (35,000years ago) accompanied by range expansion isthe most likely demographic scenario for theAsian subspecies. In addition, Macqueen'sbustards are able to disperse efficiently overbroad areas, which is consistent with ourinference of weak phylogeographic structure(global F _ST = 0.20 and 0.04 formtDNA and microsatellites, respectively) andhigh levels of homogenizing gene flow on widegeographical scales. We therefore suggest thatmanagement actions should focus on maintainingmigratory connectivity between breeding andnon-breeding areas.     

Genetic assessment of a conservation breeding program of the houbara bustard (Chlamydotis undulata undulata) in Morocco,based on pedigree and molecular analyses

Protection and restoration of species in the wild may require conservation breeding programs under genetic management to minimize deleterious effects of genetic changes that occur in captivity, while preserving populations' genetic diversity and evolutionary resilience. Here, through interannual pedigree analyses, we first assessed the efficiency of a 21-year genetic management, including minimization of mean kinship, inbreeding avoidance, and regular addition of founders, of a conservation breeding program targeting on Houbara bustard (Chlamydotis undulata undulata) in Morocco. Secondly, we compared pedigree analyses, the classical way of assessing and managing genetic diversity in captivity, to molecular analyses based on seven microsatellites. Pedigree-based results indicated an efficient maintenance of the genetic diversity (99% of the initial genetic diversity retained) while molecular-based results indicated an increase in allelic richness and an increase in unbiased expected heterozygosity across time. The pedigree-based average inbreeding coefficient F remained low (between 0.0004 and 0.003 in 2017) while the proportion of highly inbred individuals (F > .1) decreased over time and reached 0.2% in 2017. Furthermore, pedigree-based F and molecular-based individual multilocus heterozygosity were weakly negatively correlated, (Pearson's r = −.061 when considering all genotyped individuals), suggesting that they cannot be considered as alternatives, but rather as complementary sources of information. These findings suggest that a strict genetic monitoring and management, based on both pedigree and molecular tools can help mitigate genetic changes and allow to preserve genetic diversity and evolutionary resilience in conservation breeding programs.     

Breeding success in a Houbara Bustard Chlamydotis [undulata] macqueenii population on the eastern fringe of the Jungar Basin, People's Republic of China

Nesting success and chick survival of a migratory population of Houbara Bustard Chlamydotis [undulata] macqueenii were studied during three consecutive years (1998–2000) in the Xinjiang province of north‐west China. A total of 45 nests was monitored and 85 broods comprising 227 chicks were captured, of which 82 chicks were radio‐tracked. Start of laying varied between 6 and 17 April between years but the laying mode fell consistently between 26 and 30 April. Mean clutch size was 4.0 (sd = 0.8) (range 2–6) for early clutches and 3.3 (sd = 1.1) for late clutches (range 2–5). The average nesting success was 0.588 (sd = 0.270) but great variations were observed between years –0.882 in 1998, 0.530 in 1999 and 0.351 in 2000. This was related to increased predation in 1999 and 2000, which is reflected by increased predator density (chiefly Corsac Fox Vulpes corsac and Long‐legged Buzzards Buteo rufinus). The overall hatchability, defined as the proportion of eggs hatched in successful nests was 0.839 sd = 0.238). The average brood size at hatching varied from 2.9 (sd = 0.8) to 3.3 (sd = 0.9) according to years, and no significant decrease in brood size was observed in the first 5 days post‐hatching. In 1999 and 2000 the brood size diminished sharply (14% and 27%, respectively) in prefledging chicks. A further severe decrease (37%) was observed in fledglings in 2000, probably due to predation by raptors. For the 3 years of the study, a successful female Houbara would bring on average 2.3 (sd = 0.9) chicks to fledging and would have lost 30.2% (sd = 14.9%) of its brood to adversity during the rearing process. The proportion of females that lost their entire brood was 0.181 in 1998, 0.708 in 1999 and 0.453 in 2000. For the 3 years of the study, only 55.3% (sd = 26.3%) of the females hatching eggs brought chicks to fledging. The overall chick production was 0.827 per breeding female per year and the probability of an egg laid producing a fledgling of 8 weeks old was 0.190.