青藏高原胡兀鹫与巢域中峭壁生境营巢鸟类的种间互动关系初探

胡兀鹫(Gypaetus barbatus)是峭壁生境营巢鸟类,其领域是关系到繁殖与生存的必需资源。2010~2013年,在青藏高原4个省区中的7个胡兀鹫繁殖地进行了调查,结合1990~1993年的调查资料,用直接观察法记录了12个胡兀鹫繁殖巢域(距巢址500 m范围内)中的峭壁生境营巢繁殖鸟类,并初步评估了这些鸟类与胡兀鹫的种间关系。结果表明,巢区中观察到其体型可引起胡兀鹫警觉反应的鸟类计有23种,营巢繁殖的有11种。繁殖鸟类中猛禽有高山兀鹫(Gyps himalayensis)、猎隼(Felco cherrug)、金雕(Aquila chrysaetos)、大鵟(Buteo hemilasius)、长耳鸮(Asio otus)5种,鸦科鸟类有红嘴山鸦(Pyrrhocorax pyrrhocorax)、黄嘴山鸦(P.graculus)和大嘴乌鸦(Corvus macrorhynchos)3种。前述23种可引起胡兀鹫警觉反应的鸟类在胡兀鹫巢域中被记录到的活动行为频次为1 298次·只,观察到12种鸟与胡兀鹫发生种间互动行为,频次合计65次,其中鸦科鸟类与胡兀鹫发生的种间互动行为频次最高(34次)。观察到胡兀鹫驱赶巢域内的捕猎金雕导致其放弃猎物的行为。对种间关系的初步评估结论为:(1)毗邻高山兀鹫繁殖巢的胡兀鹫,表现出同种繁殖对之间巢间距明显缩短的现象,其巢间距由35.84 km(25.10~47.30 km,n=6个巢)缩短至7.39 km(6.22~8.58 km,n=5个巢);(2)在胡兀鹫巢域中营巢繁殖的猎隼,其同种间巢间距缩短至150~360 m(n=4个巢);(3)由于高山兀鹫在当地传统文化习俗中的重要地位,胡兀鹫与其毗邻营巢,可以在很大程度上降低人类直接干扰活动对其繁殖成功率的不利影响;(4)在人为干扰活动或其他原因导致胡兀鹫亲鸟离巢的情况下,鸦科鸟类和捕食性猛禽(尤其是猎隼)的存在,在很大程度上增加了胡兀鹫卵和幼雏被天敌掠食的可能性;(5)胡兀鹫育雏早期需要获取肉含量高的食物(体型较小的死亡动物),在胡兀鹫巢域或附近区域营巢的捕食性猛禽所遗落的猎物,很可能具有一定程度的补充作用。     

人类活动对青藏高原胡兀鹫繁殖成功率和种群现状的影响

2010至2013年,对青藏高原4个省区(西藏、四川、青海、甘肃)中的7个胡兀鹫(Gypaetus barbatus barbatus)繁殖地进行了调查,结合1991至1992年的调查资料,获得的调查结果为:产卵期12月上旬至翌年1月末(12月7日至1月28日,n=4),孵化期为55~61 d(n=3),窝卵数平均为1.9枚(n=14),测量3枚卵的平均长和宽分别为84.4 mm(83.1~88.3 mm)和68.0 mm(67.0~70.0 mm)。繁殖成功率为81.82%(2010~2012年,n=22)。巢址分布海拔为2 600~4 575 m。在具有代表性的繁殖地内,繁殖对之间距离平均为35.84 km(25.10~47.30 km),领域平均面积为1 284.51 km2(630.01~2 237.29 km2)。20年来(1990年以来)的种群结构变动为:胡兀鹫幼体数量比例从30.17%降低到16.67%,成鸟比例从61.21%提高到70.83%。采取与高山兀鹫(Gyps himalayensis)数量进行对比的方式,估算青藏高原250万km2面积的胡兀鹫种群数量少于1 410个繁殖对。威胁胡兀鹫生存的因素可分为4大类:(1)非法猎捕,包括非法获取胡兀鹫观赏标本和传统医药,方式为枪击、毒饵、网套等;(2)间接伤害,主要为鼠药中毒,其次是因人类在被食肉兽咬死的家畜体中施放毒药或在家畜尸体边布放的兽铗而造成伤害;(3)基础设施建设导致的伤害,如输电线路和风电场导致胡兀鹫触电和碰撞,道路建设直接对其巢址生境的破坏和人为干扰增加等;(4)人类生产和生活方式变化产生的负面影响,如对体弱家畜的快速加工和对家畜胴体的彻底利用,导致胡兀鹫的食物来源减少,家畜疫病防治导致胡兀鹫蒙受残留药物的影响,在寒冷季节柔软巢材(如羊毛)的缺乏,降低了胡兀鹫对卵和幼雏的保暖能力。     

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.     

棕背黑头鸫繁殖习性初步观察

2008年和2009年的4～8月,在四川省雅江县帕姆岭对棕背黑头鸫Turdus kessleri的繁殖生态进行了初步观察.该鸟繁殖期在4月下旬至7月上旬,营树上巢,营巢树种为高山栎Quercus aquifolioides和鳞皮冷杉Abies squamata.窝卵数为2~3枚(n=7),平均卵重(7.96±0.03)g(n=8),卵长径(32.7±0.17)mm,短径(21.9±0.13)mm(n=13),雌雄共同孵卵,以雌性为主,孵化期为15~17 d(n=2),孵化率为83.3%(n=18).雌雄共同育雏,以雄性为主,雏鸟出飞后主要在巢周围的林下或灌从活动,这时亲鸟仍会对幼鸟喂食.在同一繁殖季对巢有重复利用的现象.     

荒漠伯劳巢址选择和繁殖成功

2011年5～7月对甘肃安西极旱荒漠国家级自然保护区(N40°21'～40°22',E96°13'～96°14',海拔1 306 m)荒漠伯劳(Lanius isabellinus)巢址选择和繁殖成功进行研究。调查了58巢的巢址因子,巢主要位于营巢树主枝上,巢距地面高度多为2.0～2.5 m。主成分分析结果表明,巢距地面高度、营巢树高度、营巢树胸径和营巢处树干直径是影响荒漠伯劳巢址选择的主要因素,这也是荒漠伯劳适应繁殖地大风天气的结果。既调查巢址数据又明确繁殖情况的49个巢中,红柳(Tamarix ramosissima)(5棵)上巢的繁殖成功率明显高于沙枣(Elaeagnus angusifolia)(43棵)和胡杨(Populus euphratica)(1棵)上的巢,原因可能是红柳郁闭度大。已知窝卵数和繁殖情况的30个巢中,窝卵数分别为2(1巢)、4(7巢)、5(18巢)、6(4巢)。卡方检验结果表明,窝卵数和繁殖成功率之间差异不显著(χ2=3.921,df=3,P0.05)。发现的63个巢中跟踪监测了54个巢(包括调查巢址数据的和未调查巢址数据的)的繁殖情况,54巢中37巢繁殖成功,成功率为68.52%。所有繁殖失败的巢均为产卵阶段或育雏早期阶段由于同类的破坏而导致繁殖失败,繁殖失败巢的数量随着相邻最近巢的距离的增加而减少,因而,繁殖失败可能与种群密度以及种内竞争有关。     

广西防城港黑翅长脚鹬的繁殖行为

本研究于2021年3～9月,采用目标观察和全事件记录法,对广西防城港市钦州湾八路水湿地黑翅长脚鹬（Himantopus himantopus）的繁殖习性进行全过程观察记录。黑翅长脚鹬的栖息生境主要在盐田、虾塘和鱼塘,而巢主要分布在盐田生境。共发现39巢,雌雄共同营巢,按照主要巢材将其巢分为干草巢、碎石巢、泥皮巢和牛毛毡草巢4种;巢材包括禾本科（Gramineae）和莎草科（Cyperaceae）植物以及碎石、贝壳等;巢外径为（23.3±10.7）cm,巢内径为（11.2±1.9）cm,巢深为（1.6±0.5）cm,巢高为（6.5±4.3）cm(n=39);筑巢需（3±2）d(n=6)。窝卵数2～4枚,1～2 d产1枚卵,7 d内产完满窝卵（n=6）。雌雄均参与孵卵,雄性孵卵时间比雌性长,但二者差异不显著（P> 0.05）,雄性（8 550±245.9）min,雌性（7 530±263.3）min,孵卵期为（25±2）d(n=6)。育雏期（26±3）d(n=6),雌雄轮流育雏,育雏前、中期（雏鸟1～20d日龄）,雌性育雏时间比雄性长,是雄性的2倍,育雏后期（雏鸟大于20 d日龄）,...     

甘肃卓尼橙翅噪鹛繁殖生态报道

2005年5~7月,在甘肃省卓尼县洮河林业局卡车林场对橙翅噪鹛(Garrulaxelliotii)的繁殖生态进行了研究。橙翅噪鹛多选择在较小的云杉树上营巢,巢距地面高为1.56±0.38m(n=10),其窝卵数平均为3.4±0.5枚(n=10),卵重为5.8±0.2g(n=17)。橙翅噪鹛孵卵期为14天,育雏期为15天,孵化率为67.6%。     

人工巢箱中大山雀和褐头山雀的繁殖比较

2009年3-7月,在北京小龙门森林公园悬挂人工巢箱,对大山雀(Parus major)和褐头山雀(P.montanus;)的繁殖进行比较研究.野外共悬挂100个巢箱,其中19巢(19.0%)被大山雀、11巢(11.0%)被褐头山雀进驻,总利用率为30.0%.同域繁殖的大山雀和褐头山雀在窝卵数、孵化期上有极显著差异(P＜0.01),其中大山雀的窝卵数(8.21枚±0.25枚,n=19)极显著大于褐头山雀(6.18枚±0.23枚,n=11),而褐头山雀的孵化期(14.22d±0.44d,n=10)极显著长于大山雀(13.17 d±O.83 d,n=12).两者在卵重、卵大小、出雏数、雏鸟出飞数上无显著差异(P＞0.05).大山雀的繁殖成功率(27.0%)和营巢成效(63.2%)均显著低于褐头山雀(54.5%和100%)(P＜0.01).表明大山雀可能采取高产卵数、低存活率的繁殖对策,而褐头山雀的繁殖策略则可能为低产卵数、高存活率.     

陕西红碱淖白喉林莺繁殖生态

2012~2013年每年的4~7月,在陕西神木县红碱淖(39°04'21″~39°04'43″N,109°53'12″~109°53'40″E)对白喉林莺(Sylvia curruca)的繁殖生态进行了研究。结果表明,白喉林莺4月末迁来繁殖,5月初开始营巢于油蒿(Artemisia ordosia)、臭柏(Sabina vulgaris)和沙棘(Hippophae rhamnoides)灌丛中,巢口向上呈深杯状,巢由柳絮、枯枝和干草编织而成。对33个巢的参数进行了测量,巢外径(9.62±0.227)cm,巢内径(5.21±0.084)cm,巢深(5.05±0.160)cm,巢高(9.03±0.185)cm,巢距地面高度(24.91±1.084)cm,巢约位于植株高度的1/3处(由下而上)。营巢成功率为77.1%(n=35),窝卵数4~5枚(n=27),卵重(7.49±0.021)g,卵长径(17.27±0.057)mm,卵短径(12.86±0.080)mm(n=130)。孵化期为11~13 d,孵化率为93.1%,雏鸟出飞为90.9%。雏鸟的形态参数生长符合Logistic曲线方程拟合。植被高度、植被盖度和单株植物冠径是制约白喉林莺巢址选择的主要因素,同时恶劣天气和人为干扰是影响繁殖成效的主要原因。     

四川雉鹑繁殖习性初报

2005～2008年,在四川省雅江县对四川雉鹑(Tetraophasis szechenyii)的繁殖习性,包括巢、卵、孵卵时间、生长量度和日行为节律进行了初步观察.四川雉鹑同时营树上巢和地面巢,以树上巢为主,占68%(n=25);产卵期集中在4月,正常窝卵数2～5枚(n=9),窝卵孵化率为63.89%(n=12);雌鸟在孵卵期每天离巢1次,离巢平均时间(63.0±22.6)min(n=18),孵卵期24～29 d(n=4);150日龄幼鸟的体重接近成体.在繁殖期,四川雉鹑6:30～7:00时从夜栖树上飞下,行至觅食地觅食,17:00时左右返回夜栖地,19:00～19:30时上树夜栖.     

高山兀鹫繁殖期交配及筑巢行为初步观察

高山兀鹫(Gyps himalayensis)在海拔2 400~4 800 m的悬崖峭壁之上营巢,行为观测难度较大,资料匮缺。2013年至2015年,在天山采用样线调查法、问卷调查法,寻找到上百个巢穴。通过布设红外自动相机的方法,对高山兀鹫繁殖期巢内行为进行拍摄,同时结合焦点动物取样法和瞬时扫描法,对其交配及巢内行为进行观察和研究。共拍摄11万张照片,选出有效照片2 150张。对繁殖期行为进行了描述和定义,共7大类16种行为。根据照片逐一对比每种行为,统计各种行为拍摄张数及所占比例,其中,交配135张(6.3%),筑巢403张(18.7%),休息420张(19.5%),警戒375张(17.4%),保养335张(15.6%),运动200张(9.3%),其他282张(13.1%)。照片记录显示,交配行为从1月16日持续到3月2日,在一天的8:00~16:00时间段内,除9:00~10:00时没有记录到交配行为外,其余时间段内都有发生。交配行为次数(张数)在13:00~14:00时达到高峰,与气温同期达到高峰。交配过程持续8~15 s。筑巢期间,巢材由雌雄兀鹫运输,雌性负责将巢材放入巢中,整理、铺垫和修缮。筑巢行为在白天有三个高峰期,分别为11:00~12:00时、13:00~14:00时和15:00~16:00时。在每个高峰期后,往往出现一个短暂的低谷期。冬季食物短缺,照片显示雕鸮(Bubo bubo)、雪豹(Uncia uncia)等食肉动物进入巢内,对兀鹫繁殖造成干扰,甚至中断繁殖。作为高原健康指示物种,高山兀鹫生存状况不容乐观,急需加强保护。     

4. ONE YEAR'S CENSUS AND STUDY OF BIRDS IN 2½ ACRES OF ALEANY BUSHVELD. (Part 2.) April, 1945, to March, 1946

Hooded Vultures Necrosyrtes monachus are critically endangered but little is known of their year-round use of nests or whether other species usurp Hooded Vulture nest sites. We investigated visitation rates by Hooded Vultures and other species (including potential nest predators and usurpers) to examine their effect on Hooded Vulture breeding success. We present observations of 33 species recorded by camera traps at 12 Hooded Vulture nests over a total of 93 nest-months (2 095 nest-days). Several pairs of Hooded Vultures visited their nests regularly during the non-breeding season, some adding nesting material, highlighting that pairs visited their nest(s) year round. Egyptian Geese Alopochen aegyptiaca, potential usurpers of raptor nests, were present at occupied and unoccupied Hooded Vulture nests, but we recorded no usurpation of nests by Egyptian Geese and they had no impact on vulture breeding success. Hooded Vulture breeding failure was linked to two species only: camera-trap imagery recorded one case of predation of a vulture egg by a Chacma Baboon Papio ursinus, and one case of a Martial Eagle Polemaetus bellicosus predating a vulture nestling. We recommend expanding the Hooded Vulture nest monitoring programme to include more pairs.     

Assessing the accuracy of plotless density estimators using census counts to refine population estimates of the vultures of Kruger National Park

Breeding population estimates for three vulture species in Kruger National Park (KNP), South Africa, were made in 2013 using data from aerial censuses and a plotless density estimator (PDE). PDEs are distance-based methods used to assess sparse populations unsuitable for plot-based methods. A correction factor was applied to the 2013 estimates to reflect the difference between the survey counts and the PDE figures. We flew additional censuses across most of KNP and counted all visible nests to assess the 2013 estimates. Survey counts were within 95% confidence limits of corrected PDE estimates for White-backed Vulture Gyps africanus (count: 892; estimate: 904 [95% CI ±162]), at the limit of confidence for White-headed Vulture Trigonoceps occipitalis (count: 48; estimate: 60 [±13]) and outside confidence limits for Lappet-faced Vulture Torgos tracheliotos (count: 44; estimate: 78 [±18]). Uncorrected PDE estimates accurately reflected White-headed and Lappet-faced Vulture nest counts. The clustered patterns of White-backed Vulture nests and dispersed patterns of White-headed and Lappet-faced Vulture nests offer an explanation for these results and means that corrected PDE densities are inaccurate for estimating dispersed nests but accurate for estimating clustered nests. Using PDE methods, aerial surveys over ～35% of KNP are probably sufficient to assess changes in these vulture populations over time. Our results highlight these globally important breeding populations.     

BREEDING OF THE INDIAN WHITEBACKED VULTURE AT JODHPUR

Vulture populations have declined globally as well as regionally within Africa. Little is known about the status of the African White-backed Vulture Gyps africanus in Kenya, but ongoing studies indicate that its population has declined over the last two decades. A total of 32 African White-backed Vulture nests were monitored in the Masai Mara National Reserve over a five-year period between 2003 and 2007. Mean nesting success was 59%, which is comparable to that of populations from southern Africa. Nearest neighbour distances were significantly closer in wooded habitats (‘trees and shrubs savanna’) than in more open grassland habitats (‘open low shrubs’). Based on nearest neighbour distances, the estimated total breeding population within the Masai Mara National Reserve is 1 106 pairs, a figure that may be an overestimate and requires ground-truthing. Collecting baseline data on numbers of breeding pairs and regular nest monitoring are essential in order to assess the impact of various threats to vultures in Kenya, which include growing threats (elephant-mediated habitat disturbance and fire) as well as emerging threats (such as poisoning with the carbamate-based pesticide Furadan?).     

Hooded Vulture Necrosyrtes monachus and African White-backed Vulture Gyps africanus nesting at the Olifants River Private Nature Reserve,Limpopo province,South Africa

Basic ecological information is still lacking for many species of African vultures. The Hooded Vulture Necrosyrtes monachus is known as a rare breeding resident in north-eastern South Africa. This study set out to monitor the nests of Hooded Vultures and, secondarily, White-backed Vultures Gyps africanus in the Olifants River Private Nature Reserve over two breeding seasons in 2013 and 2014. A total of 12 Hooded Vulture nests, placed mostly in the tree Diospyros mespiliformis, were found along the Olifants River, with an average inter- nest distance of 0.76 km. Nest success was estimated to be between 0.44–0.89 offspring pair?1 y?1 in 2013 and 0.50–0.67 offspring pair?1 y?1 in 2014, which are the first estimates for Hooded Vultures in South Africa. It is thought that nests of this species have been under-reported due to the fact that they are placed within or below the canopy of densely leafed trees and hence difficult to view from aerial surveys. African White-backed Vultures also bred along the Olifants River, with nests placed in clusters of up to six. Nesting density of this species ranged from about 1.0 to 1.2 nests km?1 and nests were predominantly placed in Ficus sycomorus trees.     

Effects of nest-site characteristics and parental activity on cowbird parasitism and nest predation in Brown-and-yellow Marshbirds

ABSTRACT Nest‐site selection and nest defense are strategies for reducing the costs of brood parasitism and nest predation, two selective forces that can influence avian nesting success and fitness. During 2001–2002, we analyzed the effect of nest‐site characteristics, nesting pattern, and parental activity on nest predation and brood parasitism by cowbirds (Molothrus spp.) in a population of Brown‐and‐yellow Marshbirds (Pseudoleistes virescens) in the Buenos Aires province, Argentina. We examined the possible effects of nest detectability, nest accessibility, and nest defense on rates of parasitism and nest predation. We also compared rates of parasitism and nest predation and nest survival time of marshbird nests during the egg stage (active nests) with those of the same nests artificially baited with passerine eggs after young fledged or nests failed (experimental nests). Most nests (45 of 48, or 94%) found during the building or laying stages were parasitized, and 79% suffered at least one egg‐predation event. Cowbirds were responsible for most egg predation, with 82 of 107 (77%) egg‐predation events corresponding to eggs punctured by cowbirds. Nests built in thistles had higher rates of parasitism and egg predation than nests in other plant, probably because cowbirds were most active in the area where thistles were almost the only available nesting substrate. Parasitism rates also tended to increase as the distance to conspecific nests increased, possibly due to cooperative mobbing and parental defense by marshbirds. The proportion of nests discovered by cowbirds was higher for active (95%) than for experimental (29%) nests, suggesting that cowbirds used host parental activity to locate nests. Despite active nest defense, parental activity did not affect either predation rates or nest‐survival time. Thus, although nest defense by Brown‐and‐yellow Marshbirds appears to be based on cooperative group defense, such behavior did not reduce the impact of brood parasites and predators.     

Density-dependent effects on productivity in the Griffon Vulture Gyps fulvus: the role of interference and habitat heterogeneity

Griffon Vultures Gyps fulvus in northern Spain were studied between 1969 and 1994. The number of breeding pairs increased from 221 in 1969–1975 to 1395 in 1994. The annual population growth rate decreased in the last 5 years, and this may reflect population regulation through density-dependent phenomena. Breeding success was monitored in 1994 and examined in relation to colony size, density of breeding pairs within a radius of 25 km (regional density), climate, human disturbance and food availability. We also recorded whether the year of first occupation of each nest site was before 1989 or after 1989 and whether or not the nest had a rocky shelter. The probability of successfully raising young declined as the regional density increased, which suggests that resource limitation would take place at foraging sites because the Griffon Vulture scavenges socially and no permanent feeding hierarchies are established. The other significant variable was the year of occupation of the nest; nests occupied after 1989 had a lower probability of raising a chick. The increase in the regional density of Griffon Vultures produced a decrease in the productivity at both optimal and suboptimal nest sites. This suggests that density-dependent regulation of breeding success operates through interference and that all the individuals in a colony are similarly affected. In birds of prey, prevalence of interference or habitat heterogeneity may be dependent on the social strategy of each species in space exploitation.     

Nesting biology of Eastern Yellow Wagtails at Cape Romanzof, Alaska

ABSTRACT.   The nesting biology of the Eastern Yellow Wagtail ( Motacilla tschutschensis ) was studied at Cape Romanzof, Alaska, an arctic tundra site on the Bering Sea coast near the northeastern limit of the breeding distribution of the Yellow Wagtail ( Motacilla flava/citreola/tschutschensis ) species complex. Ninety-four nests were located and monitored from 1996 to 1999. Females built nests in 5–7 d, and nests were located on the ground. The mean clutch size was 5.6 eggs, and the mean incubation period was 11 d. Both adults incubated, and some males had a partial brood patch. The mean duration of the nestling period was 11.6 d, and both parents brooded and fed the young. Some adults began the complete prebasic molt (including primaries) while their young were still in the nest. Nestling development was similar to that reported for other Yellow Wagtails ( sensu lato ), but the breeding cycle and breeding season of Eastern Yellow Wagtails was compressed relative to Western Yellow Wagtails in Europe and to other passerine species breeding in western Alaska. Some breeding events overlapped, including initiation of egg laying before completion of nest building and initiation of adult molt while young were still in the nest. Clutch sizes were larger than reported for most European relatives. Clutch size generally fit with models predicting an increase of about one egg per 19 degrees of increased latitude. Rapid nest initiation, overlap of breeding cycle events, nest attendance (including incubation) by males, and slightly larger clutches appear to be adaptations to high-latitude breeding in this long-distance migrant.     

Removal (and attempted removal) of material from a Hooded Vulture Necrosyrtes monachus nest by a starling and a Hooded Vulture§

Relatively little is documented about nest material theft in vultures. We used camera traps to monitor Hooded Vulture Necrosyrtes monachus nests for a year. We report camera trap photographs of a starling Lamprotornis sp. removing what appeared to be dung from an inactive Hooded Vulture nest on Cleveland Game Reserve, north-eastern South Africa, in October 2016. We also had evidence of a Hooded Vulture attempting to remove twigs from the same nest in August 2016. This behaviour is previously unrecorded in Hooded Vultures and, although seemingly rare, it represents an attempt to reduce the energetic costs of nest building in this species.     

乌鸫繁殖生态的研究

乌鸫 (Ｔｕｒｄｕｓｍｅｒｕｌａｍａｎｄａｒｉｎｕｓ)是紫蓬山区常见的留鸟[1,3 ] 。吴至康等[2 ] 报道其在贵州的繁殖习性。有关巢空间资源利用特点、护雏行为、雏鸟生长模式的研究未见报道。本文是 1996年 3月份在安徽省肥西县的几个居民点对其繁殖初期活动进行了初步观察 ,4～7月又在紫蓬山区国家级森林公园的圆通山林区对其繁殖生态进行了系统研究的结果。现报道如下。1　工作方法根据样地鸟巢统计繁殖鸟类的数量 ,记录巢位特征以及巢和卵的参数 ,观察繁殖行为 ,记录雏鸟的生长情况。拟合雏鸟的生长曲线方程[9] 。2　结　果2 1　繁殖…