老君山自然保护区四川山鹧鸪非繁殖期对栖息地的利用

四川山鹧鸪（Arborophila rufipectus）是中国西南山地特产珍稀鸟类，由于亚热带阔叶林破碎化，其种群数量显著下降。2005年11—12月在老君山自然保护区，共记录四川山鹧鸪非繁殖期栖息地20个。以其新鲜粪便为中心设一个10 m×10 m大样方和4个1 m×1 m的小样方，测量每个样方中与栖息地利用有关的12个生境因子(海拔、坡向、坡度、乔木层盖度、灌木高、灌木密度、灌木层盖度、竹盖度、竹密度、雪盖度、林缘距离和道路距离)；并在距栖息地100 m处任意设对照样方1—2个，共获取30个对照样方，测量相同的生境因子。结果表明，四川山鹧鸪非繁殖期以靠近林间小道和森林边缘的次生落叶阔叶林为栖息地，主要利用海拔高度为1 000—1 600 m，坡度为2—15°的南坡；其偏爱的栖息地竹盖度、竹密度和雪盖度明显小于对照样方，而灌木盖度明显大于对照样方。对栖息地变量进一步分析表明，影响四川山鹧鸪栖息地利用的主要因子依次为地面层食物因子、地型因子、隐蔽因子、温度因子等，其中食物条件的贡献率为29.407%。四川山鹧鸪在利用栖息地时可能面对食物资源与天敌风险的权衡。因此，为了更好地保护四川山鹧鸪栖息地，应重视阔叶林的保护和恢复。     

白眉山鹧鸪冬季觅食地选择

2010年11—12月,在广西九万山国家级自然保护区对白眉山鹧鸪冬季觅食地选择进行研究。发现觅食点34个,设置利用样方和对照样方各25个,测量并分析19个有关参数。结果显示,白眉山鹧鸪对阔叶林、针阔混交林、阔叶摆竹混交林和摆竹林表现为随机利用,对毛竹林和杉木林表现为避开选择;其偏向选择面朝东南方向的山坡,觅食地坡度在20～44°之间,觅食地摆竹灌丛密度和摆竹灌丛盖度、草本密度和草本盖度都显著低于对照样方,落叶盖度显著高于对照样方。逐步判别分析结果表明,落叶盖度、坡度和摆竹灌丛盖度是区分冬季觅食地和对照样方的主要参数,判别准确率达86.0%。白眉山鹧鸪冬季对觅食地的选择与食物资源和躲避危险有关。因此,建议在保护白眉山鹧鸪时应着重关注这两个因素。     

四川山鹧鸪冬季栖息地特征

四川山鹧鸪(Arborophila rufipectus)是我国西南山地特有的珍稀濒危鸟类,迄今对其越冬栖息地的了解甚少。2013年1月和2014年1—2月,在四川老君山国家级自然保护区对其冬季栖息地特征进行了研究。野外共测定了48个利用样方和30个对照样方的特征参数。结果表明:四川山鹧鸪偏好选择海拔较低、坡度平缓、乔木盖度较小、竹子较矮、草本低矮稀疏、1.0 m层盖度较大、4.0~5.0 m层盖度较小、距小路和林缘较近的栖息地。此外,四川山鹧鸪还倾向于选择在距水源较近及地表落叶丰富的栖息地活动。安全与食物条件可能是影响四川山鹧鸪冬季栖息地选择的关键因素。     

四川麻咪泽自然保护区四川山鹧鸪繁殖期对栖息地的利用

四川山鹧鸪Arborophila rufipectus属鸡形目雉科山鹧鸪属,是我国特产珍稀鸟类,国家Ⅰ级重点保护动物,世界自然保护联盟濒危物种。2014年4—5月,在四川麻咪泽自然保护区对四川山鹧鸪及其栖息地进行了野外调查。结果表明,四川山鹧鸪分布在海拔1700~2550 m,主要分布在2100~2300 m;其栖息生境主要为天然阔叶林,尤喜原始林;利用的坡度集中在20°~40°;偏好乔木数量多、高大和郁闭度大的森林生境;其中乔木均高是影响四川山鹧鸪栖息地利用的主要因子。保护四川山鹧鸪偏好的天然阔叶林,减少栖息地的人类干扰,是保护四川山鹧鸪这一濒危物种的首要措施。     

四川铁布梅花鹿自然保护区梅花鹿夏季栖息地选择

四川梅花鹿Cervus nippon sichuanicus为国家Ⅰ级重点保护动物,四川铁布梅花鹿自然保护区分布有我国现存最大的梅花鹿野生种群。2011年6-9月,采用样方法对保护区梅花鹿夏季栖息地选择进行了调查,共布设109个样方(利用样方61个,对照样方48个),测量并比较了海拔、坡度等20个生境因子。结果显示,梅花鹿偏好利用的植被类型为灌丛、草甸、针叶林,同时选择隐蔽度较高的生境;此外,距水源距离、灌木高度、灌木盖度、灌木密度、草本高度和草本盖度6个连续变量在利用样方和对照样方之间差异有统计学意义(F<0.05或U<0.05)。回归模型分析结果表明,梅花鹿夏季偏好选择草本盖度大、靠近水源和林缘的生境,回避远离水源和林缘的生境。     

清凉峰自然保护区梅花鹿秋季对栖息地利用的初步分析

20 0 3年 9～ 1 1月 ,作者在浙江省清凉峰自然保护区 ,对梅花鹿栖息地的利用进行了研究 ,选择 9类生态因子 ,并设置 3 89个 1 0m× 1 0m样方。选择指数的结果表明 ,梅花鹿喜欢选择草甸 沼泽和灌丛、郁闭度较低、食物丰富度高、上坡位、海拔≥ 1 2 0 0m、人为干扰距离 >1 0 0 0m、向阳、坡度平缓的生境。分析表明 ,梅花鹿对灌木盖度的选择以适合为准。主成份分析表明 ,影响梅花鹿栖息地选择的主要因子有 4种 ,依次为 :干扰因子 (包括海拔、坡位和人为干扰距离 )、食物因子 (包括郁闭度、食物丰富度和植被型 )、灌木盖度因子和地形因子 (包括坡度和坡向 )。     

九龙山保护区黑麂栖息地选择的季节变化

2005年7月至2006年6月,以浙江省九龙山国家级自然保护区上寮坑保护站为中心,在其周围随机设置6条样线,每隔200m地面距离设置固定样方,共设定442个20m×20m的固定样方,并在其中设置灌木测量样方442个,草本植物盖度测量样方2210个。分春、夏、秋、冬4季记录样方的植被类型、乔木盖度、灌木盖度、草本盖度、坡位、坡度、坡向、食物丰富度、海拔、人为干扰距离和水源距离等11类生态因子,并用痕迹法检查样方是否被黑麂利用。通过Vanderloeg选择系数(Wi)和Scavia选择指数(Ei)研究影响黑麂栖息地利用和选择性的各生态因子,并采用主成分分析的方法研究影响黑麂栖息地选择的关键因子,得到了黑麂栖息地选择的主要特征及其季节变化。结果表明:黑麂总体上倾向选择在针阔混交林、乔木盖度60%-80%、灌木盖度中等(20%-60%)、草本盖度中等(20%-60%)、食物丰富度高(68%)和人为干扰距离远的生境,对海拔高度和坡位的选择表现出季节迁移性。     

舟山群岛春秋季獐栖息地的生态特征

2008 年3 月和2008 年11 月,在舟山群岛以獐的足迹、粪便和卧迹等新鲜活动痕迹为依据,对獐春、秋季栖息地利用特征进行研究。共设置样方420 个,对样方内生境类型、乔木盖度、灌木盖度、草本盖度、坡位、坡度、坡向、海拔、人为干扰距离和水源距离等10 个生态因子进行测量评估。结果发现,獐春、秋两季的栖息地利用特征是(1)隐蔽和食物因子:春、秋季利用阔叶林、农田和山坡地,秋季对灌木林也有较高的利用率,而对农田的利用率下降;春、秋季乔木盖度、灌木盖度和草本盖度较低处(≤50%) 利用率较高,但春季对乔木盖度较高处(> 50% )也有较高的利用率; (2) 地形因子:春季对坡度较缓、中下坡位、海拔较低处(< 100 m)利用率较高;秋季对坡度较缓、中下坡位、海拔较低(<100 m)的南坡利用率较高; (3) 水源因子:春季利用水源距离较近(< 200 m) 的区域;秋季对水源距离较近(< 200 m)和较远(>600 m) 区域的利用率均较高; (4) 干扰因子:春季主要利用距离人为干扰近处(< 100 m),秋季主要利用距离人为干扰远(> 200 m)处。逐步判别分析显示,春、秋季獐栖息地利用特征存在显著差异,乔木盖度、坡度、坡向、海拔和人为干扰5 个因子是主要的区分因子。舟山群岛人为干扰剧烈、次生乔木和灌木较为发达以及草本植物不发达等一系列特点,造成了舟山群岛獐特殊的栖息地现状。本研究将对制订适合于海岛的动物栖息地保护对策提供理论依据,也为了解海岛生境下獐不同季节的生存状况提供科学依据。     

峨眉山灰胸薮鹛冬季栖息地特征

对于特有珍稀鸟类的保护而言,了解其对特定栖息地的要求至关重要。灰胸薮鹛(Liocichla omeiensis)是我国西南山地一种特有的画眉科(Timaliidae)珍稀鸟类。2010~2013年冬季,采用样线法和样方法,在四川峨眉山对灰胸薮鹛的冬季栖息地特征进行了调查。沿山间公路、山脊或林中小径布设观察样线。样线共计26条,总长70 km。观察发现,灰胸薮鹛主要在常绿阔叶林林缘地带活动,海拔范围约500~1 300 m。共设置47个利用样方和25个对照样方。χ²检验的结果表明,灰胸薮鹛主要选择阳坡。与对照样方的差异性检验显示,灰胸薮鹛喜好利用海拔较低、乔木数量较少、乔木胸径较小、乔木均高较低、乔木盖度较小、灌木盖度较大、竹子均高较高、竹子盖度较大、草本盖度较大、藤本植物较丰富、植被总盖度较大和距林缘距离较小的生境。逐步判别分析结果表明,灌木盖度、草本盖度、竹子盖度和距林缘距离是区分利用样方与对照样方的关键因子,判别准确率达87.5%。灰胸薮鹛对冬季栖息地的选择主要与食物和隐蔽条件有关。     

江西官山自然保护区四种雉类的生境选择差异

2009年10月—2010年11月在江西官山国家级自然保护区对白颈长尾雉、白鹇、勺鸡和灰胸竹鸡4种雉类的生境选择进行了研究:共调查了6条样线上的388个样方,选取了与这四种雉类栖息地相关的17个生态因子进行观测和测量。结果显示,4种雉类均偏好阔叶林和针阔混交林、阳坡或半阴半阳坡的生境。Kruskal-Wallistest检验表明,4种雉类在海拔、坡度、乔木盖度、灌木盖度、灌木数量、灌木高度、草本盖度、草本种类、草本数量、落叶层盖度和水源距离11个生态因子上存在极显著差异(P<0.01),乔木种类存在显著差异(P<0.05),其余生态因子无显著差异(P>0.05)。典则判别函数图显示,4种雉类在生境选择上存在一定程度的重叠,又有比较明显的差异。逐步判别表明在区分4种雉类生境选择差异方面有一系列的生态因子发挥作用,依照贡献值的大小依次为海拔、草本数量、灌木高度、水源距离、灌木盖度、乔木盖度、坡度、落叶层盖度、灌木数量、草本盖度。由这10个变量构成的方程对4种雉类生境选择差异的正确区分率为74.7%。     

Bird communities in habitats along a successional gradient: Divergent patterns of species richness,specialization and threat

The long history of human influence on northern temperate landscapes has created a mosaic of successional stages, from closed forest to open grassland. Various species thus adapted to different habitats and it is interesting to explore how these differences in species composition among particular successional stages translate into differences at the community level. For this purpose, we surveyed breeding birds in 233 patches of five different habitats covering a gradient from bare ground to forest in 29 abandoned military training sites scattered throughout the Czech Republic. Linear mixed effects modelling revealed that late-successional habitats (dense scrubland and forest) were the most species-rich, whereas early-successional stages hosted bird communities with the highest habitat specialization and threat level. These results suggest that the habitats of late-successional stages are important for the maintenance of high bird species richness, but that early-successional habitats are essential for highly specialized and threatened bird species. Given the highly adverse impacts of agricultural intensification and land abandonment on open habitats, it is necessary to promote factors creating initial successional stages suitable for specialized and threatened species.     

Birds in Anthropogenic Landscapes: The Responses of Ecological Groups to Forest Loss in the Brazilian Atlantic Forest

Habitat loss is the dominant threat to biodiversity and ecosystem functioning in terrestrial environments. In this study, we used an a priori classification of bird species based on their dependence on native forest habitats (forest-specialist and habitat generalists) and specific food resources (frugivores and insectivores) to evaluate their responses to forest cover reduction in landscapes in the Brazilian Atlantic Forest. From the patch-landscapes approach, we delimited 40 forest sites, and quantified the percentage of native forest within a 2 km radius around the center of each site (from 6 - 85%). At each site, we sampled birds using the point-count method. We used a null model, a generalized linear model and a four-parameter logistic model to evaluate the relationship between richness and abundance of the bird groups and the native forest amount. A piecewise model was then used to determine the threshold value for bird groups that showed nonlinear responses. The richness and abundance of the bird community as a whole were not affected by changes in forest cover in this region. However, a decrease in forest cover had a negative effect on diversity of forest-specialist, frugivorous and insectivorous birds, and a positive effect on generalist birds. The species richness and abundance of all ecological groups were nonlinearly related to forest reduction and showed similar threshold values, i.e., there were abrupt changes in individuals and species numbers when forest amount was less than approximately 50%. Forest sites within landscapes with forest cover that was less than 50% contained a different bird species composition than more extensively forested sites and had fewer forest-specialist species and higher beta-diversity. Our study demonstrated the pervasive effect of forest reduction on bird communities in one of the most important hotspots for bird conservation and shows that many vulnerable species require extensive forest cover to persist.     

Assessing the role of invasive weeds in the impact of successional habitats on the bird assemblage in overgrowing agriculture

Agricultural habitats are assumed to be biodiversity refuges. However, some studies treat agricultural land management as a cause of the biodiversity decline, to which habitat loss and heterogeneity may contribute. Between the crops, the successional habitats appear – ruderal plant communities and bush areas. Their influence on farmland biodiversity is unknown. This research assessed the impact of spatial relationships between agricultural areas, semi-natural meadows and successional habitats on the bird species richness, Shannon diversity index, and Faith’s phylogenetic diversity index. An additional habitat variable was the presence of weeds, i.e., invasive Caucasian hogweeds Heracleum sp., treated as crops in the past. The birds and habitats research was on 74 sites set in pairs (invaded vs control) in south-eastern Poland. Results showed that birds assembling in agricultural and semi-natural areas were more diverse and contained protected farmland species, while birds appearing in overgrown habitats (i.e., successional and invaded) were clumped with their habitat requirements. In the presence of plant invaders, ruderal habitats negatively affected the bird phylogenetic diversity index. In invaded sites, bush areas had no positive effects on the Shannon diversity index and species richness of birds, in contrast with control sites. The presented research suggests the need to re-evaluate the importance of successional non-crop habitats considered positive in agricultural landscapes if those habitats develop in areas with plant invasion.     

Grey Partridge Perdix perdix in the UK: recovery status,set‐aside and shooting

The Grey Partridge Perdix perdix is a European Species of Conservation Concern and a priority species under the UK Biodiversity Action Plan. The Game & Wildlife Conservation Trust (GWCT) launched a major programme to help partridge recovery in the UK, built on the GWCT’s Partridge Count Scheme (PCS) and including a demonstration site from 2002. We contrast the national picture of no population change since 1999 from BTO monitoring with a doubling of spring pair density on PCS sites. At the demonstration site, where set‐aside was used for habitat creation, Grey Partridge breeding density increased six‐fold, to 18 pairs/km², then fell back. The drop coincided with bad weather but also with the disappearance of rotational set‐aside when the set‐aside rate fell to zero, which halved the amount of brood‐rearing habitat. Non‐rotational set‐aside remained unchanged, as did the amount of nesting habitat that it provided. Grey Partridge density was significantly linked to rotational set‐aside, especially wild bird cover, but not to non‐rotational set‐aside. The demonstration project also showed that, with appropriate precautions, it was possible to shoot over 60% of Red‐legged Partridges Alectoris rufa while maintaining Grey Partridge losses below 5%. On PCS sites, the annual change in spring density in recent years differed in relation to neither shooting pressure nor intensity of Red‐legged Partridge releasing. Provision of brood‐rearing habitats and game cover increased with the latter, and probably counteracts the shooting losses of Grey Partridges on Red‐legged Partridge shoots when, as on PCS sites, active measures keep those losses below 20%. Targeted personal advice channelled through the PCS has been fundamental to these successes and must be expanded.     

Birds,Cattle, and Bracken Ferns: Bird Community Responses to a Neotropical Landscape Shaped by Cattle Grazing Activities

Large areas of tropical moist forests have been converted to cattle pastures, generating complex landscapes where different habitats are represented by small patches with an uneven spatial distribution. Here, we describe how bird communities respond to the different elements present in a livestock landscape that was originally dominated by tropical moist forest. We surveyed six habitats: open pastures, pastures with shrubs, early‐ and middle‐secondary forests, mature forest, and pastures invaded by bracken ferns (Pteridium aquilinum). Bird diversity was high in secondary and mature forests, and low in fern‐invaded sites and open pastures. Fern‐dominated sites had the lowest bird species richness, and trophic guild diversity of all habitats. Habitat structure affected both bird species richness and densities in similar ways. Tree species richness was the habitat attribute that had a bigger positive effect on bird species richness. Bird community structure varied among sampled habitats, separating habitats in two major groups (forests and pastures). Our data indicate that bracken fern‐invaded pastures were the worst habitat condition for avian communities. To increase bird diversity, we recommend to eliminate or manage bracken fern and to increase shrub and tree cover in open pastures to provide food resources and shelter for birds. Finally, we encourage the maintenance of secondary and mature forest remnants as a strategy to conserve resident birds within a landscape dominated by livestock activities.     

石鸡繁殖期栖息地的特征

2005年4~7月,对甘肃西部(东阿尔金山地区和西祁连山地区)和东南部(西秦岭地区)的石鸡(Alectoris chukar)种群栖息地选择进行了调查。主成分分析表明,草本密度、地面异质性和草本盖度是栖息地选择的主要影响因子;方差分析表明,甘肃西部(东阿尔金山和西祁连山)的石鸡种群在海拔、坡度和小石块数目的选择上差异显著。甘肃西部和东南部的石鸡种群在栖息地选择上存在显著的地理变异,西秦岭种群选择海拔低、坡度大、坡位偏上、草本密度低和草本高度高的栖息地。栖息地选择差异可能是在不同的选择压力下,经过长期的隔离进化形成。     

Legacy forest structure increases bird diversity and abundance in aging young forests

Many studies have demonstrated the importance of early‐successional forest habitat for breeding bird abundance, composition, and diversity. However, very few studies directly link measures of bird diversity, composition and abundance to measures of forest composition, and structure and their dynamic change over early succession. This study examines the relationships between breeding bird community composition and forest structure in regenerating broadleaf forests of southern New England, USA, separating the influences of ecological succession from retained stand structure. We conducted bird point counts and vegetation surveys across a chronosequence of forest stands that originated between 2 and 24 years previously in shelterwood timber harvests, a silvicultural method of regenerating oak‐mixed broadleaf forests. We distinguish between vegetation variables that relate to condition of forest regeneration and those that reflect legacy stand structure. Using principal components analyses, we confirmed the distinction between regeneration and legacy vegetation variables. We ran regression analysis to test for relationships between bird community variables, including nesting and foraging functional guild abundances, and vegetation variables. We confirmed these relationships with hierarchical partitioning. Our results demonstrate that regenerating and legacy vegetation correlate with bird community variables across stand phases and that the strength with which they drive bird community composition changes with forest succession. While measures of regeneration condition explain bird abundance and diversity variables during late initiation, legacy stand structure explains them during stem exclusion. Canopy cover, ground‐story diversity, and canopy structure diversity are the most powerful and consistent explanatory variables. Our results suggest that leaving varied legacy stand structure to promote habitat heterogeneity in shelterwood harvests contributes to greater bird community diversity. Interestingly, this is particularly important during the structurally depauperate phase of stem exclusion of young regenerating forests.     

紫箭竹层鸟巢样方及有关资料分析

1980年中国科学院昆明分院选定哀牢山徐家坝林区开展森林生态系统结构和功能研究,我们在进行鸟类普查基础上,开展了对紫箭竹层鸟类的研究。 一、环境情况和工作方法 徐家坝位于哀牢山脉北段山顶,在云南省楚雄州的南华、双柏和思茅区的景东三县交江处,地处北纬24°32′、东经101°01′,在景东县城东北侧。该区常年温凉、潮湿多雨,年平均降雨     

神农架川金丝猴栖息地森林群落的数量分类与排序

在神农架川金丝猴生境典型地段设立样方58块,根据样方资料对神农架川金丝猴栖息地的森林群落用组平均法分类和DCA排序.用组平均法将58块样地分为9个群系,依据《中国植被》的分类原则和系统将研究区植物群落划归为7个植被型.样地的DCA排序较好地揭示了该区森林群落的分布格局与环境梯度的关系;DCA第二轴明显地反映出森林群落的海拔梯度变化,沿DCA第二轴从右到左,海拔逐渐升高;第一轴表现了各植物群落或植物种所在环境的坡度、坡向,即水分和光照因素,沿第一轴从下到上,坡度渐缓、坡向渐向阳.其中海拔梯度是环境因子中对森林群落起决定性作用的因子.研究表明,巴山冷杉+糙皮桦-大齿槭+尾萼蔷薇-高原露珠草+星果草群系发育较好,高大树木占有较大的比例,是神农架川金丝猴最适宜栖息地.7个植被型物种丰富度指数在群落梯度上呈规律性波动.其中针叶林和针叶-阔叶混交林中,物种丰富度指数在群落梯度上的总体趋势表现为灌木层＞草木层＞乔木层;在常绿阔叶林和常绿-落叶阔叶混交林中,该趋势为灌木层＞乔木层＞草本层;在落叶阔叶林中,其丰富度指数的趋势为灌木层＞草本层和乔木层.不同植被类型川金丝猴食源植物种类在群落梯度上的变化趋势与物种丰富度指数相同,但地衣类植物作为川金丝猴冬季的重要食物只在针叶林和针叶-阔叶混交林中生长.本研究为制定栖息地保护计划,更好地保护神农架川金丝猴提供了科学理论依据.