中国野生动物生境适宜性评价和生境破碎化研究

生境是生物出现的环境空间, 开展野生动物的生境适宜性评价和生境破碎化研究, 有助于濒危动物的保育。随着生态学科的发展, 多元统计分析、景观生态学和3S 技术被用于生境适宜性评价中, 使其研究结果广泛应用于生境质量评估、生境承载力分析、物种潜在分布预测和物种濒危机制评价等方面。然而研究对象基础资料的缺乏和研究时间较短常局限生境适宜性评价研究继续深入。生境破碎化研究常集中在破碎化现状及其对生物的影响。时空尺度的扩展和研究方向的分化应是今后生境破碎化研究的发展趋势。     

新疆塔什库尔干野生动物自然保护区马可波罗盘羊生境适宜性评价

马可波罗盘羊是帕米尔高原的代表性物种,开展生境适宜性评价对于该物种的保护与管理具有重要意义。综合考虑植被、地形等影响马可波罗盘羊生境选择的关键因子,以及道路和牧场等人为干扰因子,借助ArcGIS,构建生境适宜性指数模型,在不同尺度上评价分析马可波罗盘羊的生境适宜性及其季节变化特征。结果表明:15836 km²保护区内马可波罗盘羊夏季潜在适宜生境面积为2127.19 km²,冬季为1915.70 km²。保护区西北部面积3767.73 km²的马可波罗盘羊实际分布区内,夏季潜在适宜生境面积为1095.48 km²,冬季为1072.82 km²,马可波罗盘羊适宜生境集中分布于保护区内该物种实际分布区。受人为干扰,保护区内马可波罗盘羊夏季和冬季实际适宜生境丧失率分别为18.43%和17.78%,实际分布区内适宜生境丧失率分别为33.65%和29.73%,表明实际分布区马可波罗盘羊适宜生境受人类活动影响较大,应予以重点保护。总体而言,影响马可波罗盘羊生境适宜性的关...     

大兴安岭呼中区紫貂生境格局变化及采伐的影响

本文根据紫貂（Martes zibellina）行为生态学特征,利用景观生态学的原理和技术,将大兴安岭呼中区紫貂生境划分成最适、一般适宜和非适宜三种类型。以其紧邻的呼中自然保护区核心区1989年的生境格局代表呼中区1970年开发前的原始生境,揭示原始生境、1989年、2000年3个时期紫貂生境格局及变化。结果表明,1970-2000年紫貂生境格局持续恶化,已极不利于紫貂的生存。适宜生境向非适宜生境呈单一方向转变,且适宜生境由沟谷两侧向远离河谷的森林腹地大幅度萎缩。生境格局变化与经营时问长短关系密切,原始状态是以适宜生境为基质的均质状态,开发至一定时期,生境格局的异质化程度增大,继续开发则异质化程度又减小,形成以非适宜生境为基质的相对均质状态。大于巢区最小面积f4km0）的生境斑块的面积百分比、斑块密度明显下降,斑块间距离显著增大。进而对导致生境格局变化的要素进行分析后发现,持续采伐是紫貂生境格局变化的主要驱动因子,采伐改变了植被条件,而植被条件的非适宜性造成了紫貂非适宜生境。1989-2000年的采伐格局也并不合理,各年伐区在研究区内均匀分布,采伐设计时没有考虑动物生境保护。但可以推断,1999年后开始逐步实施的“天然林保护工程”有利于紫貂生境的恢复,本研究强调森林采伐经营的空间格局与动物生境保护之间的关系,旨在促进决策部门将生物保护作为采伐经营政策制定的重要决策因子。     

澳门地区鸟类生境的景观格局

以2006年澳门地区TM遥感图像为主要数据源,在RS、GIS技术支持下,根据与鸟类活动密切相关的生境特征,利用Fragstats 3.3分析生境格局的基本特征和地区差异,讨论了景观的破碎化程度、连通性、景观异质性等对鸟类有重要影响的生境因素。结果显示：澳门的鸟类生境格局在澳门半岛和路氹离岛差异较大,与其城市化的程度有较高的相关性;澳门半岛以建设用地为基底,绿地数量少且破碎,景观多样性和异质性较低;路氹离岛以林地为基底,中部填海区的建设用地和裸地以大斑块存在,生境类型分布较澳门半岛均匀,连通性较佳,总体鸟类生境格局优于澳门半岛。澳门半岛有鸟类72种,其中陆生鸟类48种、水鸟24种;路氹离岛有鸟类146种,其中陆生鸟类94种、水鸟52种。对鸟类调查数据分析发现,生境格局对于鸟类物种数、多样性和均匀度方面均有一定影响。澳门在珠江口地区候鸟迁徙和湿地保护方面的重要性较高,在城市发展过程中应重视提高景观多样性和异质性,保护重要鸟类生境,以适应不同鸟类对各种生境的需求。     

紫貂冬季生境的偏好

采用无线电跟踪技术和全球定位系统对大兴安岭阿巴河流域紫貂冬季的生境选择进行了研究。结果表明,紫貂偏好成熟林地和老龄林地。（１）紫貂冬季栖息地主要的优势树种是落叶松林,对中等盖度的林地选择性强,而开阔地带和特别高盖度地区。（２）主要栖息中,下坡位,而对上坡位选择性不强。（３）对小树密度,大树密度,乔木胸径,倒木长度,倒木密度,倒木直径等有正选择性。     

大兴安岭地区紫貂冬季生境选择的研究

１９９１～１９９３年在大兴安岭的呼中和图强区,采用雪地足迹跟踪法研究了紫貂（Ｍａｒｔｅｓｚｉ－ｂｅｌｉｎａ）冬季对取食和休息生境的选择特点,结果表明紫貂喜好植被演替晚期的林型,具体特点如下：（１）喜好中等到高等树冠盖度的乔木林地（Ｐ＝０．０００１）和混合型林地（Ｐ＝０．０２）,回避单一树种优势林地和空地。（２）对灌木盖度无选择性（Ｐ＝０．０９）,但喜好混合型灌木林地（Ｐ＝０．０３）。（３）取食时喜好下坡位及岸边,休息时选择上坡位（Ｐ＝０．００９）,且倒木、大胸径树和树根较多的生境,不选择坡向（Ｐ＝０．３９）。（４）对大树密度（Ｐ＝０．０００１）、落叶松基区面积（Ｐ＝０．００５）、大树胸径（Ｐ＝０．０００１）、落叶松胸径（Ｐ＝０．００１４）、倒木全长（Ｐ＝０．０００６）、倒木直径（Ｐ＝０．００１４）及倒木覆盖面积（Ｐ＝０．０００１）都有明显的正选择性,且休息对生境的选择强于取食。对小树密度取食时喜好中等密度（１．２１～１．８２棵／ｍ２）林地,而休息时回避高密度区（１．８２～３．０３棵／ｍ２）。根据上述结果建议在择伐过程中应当保留植被演替晚期的林型和胸径在４０ｃｍ左右的大树。     

1987年大兴安岭特大火灾后北坡森林景观生态恢复评价

通过空间直观景观模型(LAND IS)来探讨大兴安岭北坡1987年特大森林火灾后,在目前这种恢复方案下以及完全依靠天然更新下森林景观的长期动态,通过对比研究来评价目前所采取的恢复措施是否能够有效地恢复森林资源。研究结果表明:1987年大火后所采取的恢复措施可以在很大程度上增加针叶树种在该区所占的比例,而相应地降低阔叶树种的比重。由于在目前的恢复措施下,不仅大面积地种植针叶树种,同时也采伐了大量的成、过熟林,使落叶松和樟子松的蓄积量在开始阶段不仅没有增加,反而有大幅度的下降。但最终,所更新的幼苗逐渐成材,落叶松和樟子松的蓄积量逐渐超过天然更新下的。在演替前期,白桦的蓄积量在这2种模拟方案下相差不大;而在演替后期,白桦在天然更新方案下的蓄积量要高于在目前恢复措施下的蓄积量。另外,物种在不同的区域的变化动态又有较大的差异。在重度火烧区,由于人为种植大量的针叶树种,使它们所占的面积比例明显高于完全依靠天然更新下其在重度火烧区所占的比例;而阔叶树种则相反,在完全依靠天然更新方案下所占的面积百分比明显高于在目前恢复方案下的比例。而在未火烧和轻中度火烧区,由于火后人为采伐大量的落叶松和樟子松,使这2个树种在该区所占的比例在开始100多年里要低于完全依靠天然更新下的比例,随后逐渐高于天然更新下所占的比例,但相差不大;阔叶树种则正好相反。另外,目前恢复方案不仅极大地改变了主要物种在该区所占的比例,而且还明显的影响了它们的空间分布格局。     

基于生境适宜性指数模型的俚岛海黍子生境层级分布

为了深入了解海黍子生境,利用模型对山东俚岛海黍子生境进行适宜性分析,分别选取温度、盐度、水深、浊度、底质、无机氮浓度、磷酸盐浓度和距海藻床距离8种环境因子,通过层次分析法赋值因子权重,结合空间分析方法建立了海黍子HSI模型.利用该模型对山东俚岛近岸海域2018年春、秋两季的环境因子调查结果进行了海黍子生境分析.结果 表...     

新疆塔里木马鹿沙雅种群的生境变化分析

塔里木马鹿(Cervus elaphus yarkandensis)沙雅种群主要分布在新疆维吾尔自治区沙雅县和库车县境内。为了评估该马鹿种群的生境现状、变化趋势和变化原因,通过野外实地考察,利用GIS和RS技术,分别解译了当地过去4个年份(1972～2006年)夏季的Landsat TM/ETM+遥感影像,得到了塔里木马鹿生境变化数据:①2006年的农田面积为27082.24hm2,高盖度植被面积22616.25hm2,中盖度植被面积66703.62hm2,低盖度植被面积64470.62hm2,水体面积39735.89hm2,荒漠面积63497.26hm2,沙漠面积40308.45hm2;②过去的34年间农田面积增加了89.2%(12768hm2),高盖度植被面积减少60.1%(34125hm2),中盖度植被面积增加了17.2%(9791hm2),低盖度植被面积增加了37.3%(17520hm2),水体面积减少26.6%(14429hm2),荒漠面积增加6.9%(4123hm2),沙漠面积增加12.6%(4523hm2);③高盖度植被的斑块数量增加了20.9%,平均斑块面积下降了48.3%,最大斑块指数下降了33.3%;景观丰富度并没有变化,但Shannon多样性指数和Shannon均匀度指数分别增加了2.5%;④高盖度植被面积变化分别与当地的人口数量和畜牧存栏数呈显著负相关(r=-1.000),而农田、沙漠和荒漠面积分别与当地人口数量及畜牧存栏数呈显著正相关(r=0.800,r=1.000,r=0.800)。表明塔里木马鹿沙雅种群生境的丧失及破碎化程度较为严重;生境丧失及破碎化是人类活动和自然环境变化共同作用的结果。     

森林所有制对景观格局和动物生境的影响研究进展

在欧美等地区的林业发达国家,多种森林所有制长期并存,至今,多种所有制影响下森林景观和生境格局的变化以及与动物保护之间的关系成为研究热点和重点.本文首先阐述了森林所有制对森林景观格局和动物生境的影响,以及林权分散和林权流转的加剧带来的生态后果,包括提供多样化的生境和导致原有大面积生境的破碎化;其次,总结了林业发达国家解决林权分散与生物保护之间矛盾的两个理论途径--改变所有制格局和相对统一各所有制的管理行为,分析现多采用后一种途径的原因,并指出目前森林所有制研究中模拟方法的局限;最后,论述我国的研究现状以及面临的机遇和挑战,提出近期发展建议.     

An expert-based landscape permeability model for assessing the impact of agricultural management on amphibian migration

The persistence of pond-breeding amphibian populations is influenced on different spatial scales ranging from the individual breeding pond to surrounding habitat patches to landscape clusters of breeding pond populations. The connectivity among breeding ponds as well as the availability of suitable terrestrial habitats surrounding the ponds plays a major role in long-term viability of amphibian species. Besides road traffic and urban structures agricultural land activity can disrupt landscape connectivity through the use of pesticides, fertilizers and physical activity such as tillage. We developed an expert-based model to assess the impact of agricultural management measures on the migration area and terrestrial habitat availability for seven amphibian species. The model is based on a Habitat Suitability Index to identify suitable terrestrial habitats and includes a landscape permeability approach. Size of migration areas, connectivity of breeding ponds and number of reachable terrestrial habitats were modeled considering species-specific migration ranges and habitat preferences. We consider how pesticides application might lead to fragmentation and isolation of amphibian breeding pond populations. Therefore the potential disrupting impact of pesticides was simulated by inflating landscape resistance to medium and high migration cost. One amphibian species showed a decrease of migration area by 48.3% and a decrease of reachable terrestrial habitats by 41.5% at high migration costs. Three additional species showed a decrease of their migration areas between 31.5 and 35.7%. At increased migration cost, some of the investigated populations were isolated at breeding pond level or restricted to pond clusters. Our model could be used to prioritize conservation efforts for pond-breeding amphibians with adequate consideration of agricultural land use and its impact on amphibian migration.     

Habitat partitioning in endangered Cantabrian capercaillie Tetrao urogallus cantabricus

The endangered Cantabrian capercaillie (Tetrao urogallus cantabricus) lives at the southern edge of tetraonids’ distribution range, in entirely deciduous forests. Its conservation planning has been always lek-centred. There is very little information about the specific habitat requirements of hens and broods, even though reproductive success appears to be a limiting factor. We analysed summer surveys from 1997 to 2004, carried out to estimate the reproductive success of the population. We compared the habitat characteristics at different spatial scales of hens with broods, broodless hens, and cocks in summer, with the better known spring habitat in display areas. Summer habitat showed higher proportion of open areas and was associated with more rugged zones at moderate spatial scales (78 ha) than spring habitat at display areas. Cocks and hens showed summer habitat partitioning; hens were associated with higher proportions of open and shrubby habitats. Furthermore, broodless hens preferred areas with higher slope variability than the display and summer areas preferred by cocks. These differences may reflect the sexual dimorphism of the species in reproductive role, energetic demands and conspicuousness. At larger spatial scales a previously developed habitat suitability model performed well to predict good brood-rearing areas. Hens with broods were located in the best-preserved areas in the range, mainly characterized by higher proportion of forest cover at a large (50 km²) scale. We suggest that these characteristics indicate refuge habitats where Cantabrian capercaillie can still breed successfully.     

Does forest loss affect the communities of trap-nesting wasps (Hymenoptera: Aculeata) in forests? Landscape vs. local habitat conditions

We investigated changes in the communities of trap-nesting Hymenoptera in forests in relation to forest loss on a landscape scale and understory conditions on a local habitat scale. Two specific questions were addressed. (1) Do the communities change with degrees of forest loss? (2) Do the communities change with varying local environmental conditions of understory habitats? The study was made in a landscape characterized by distributed forest patches within intensively managed agricultural surroundings. We deployed trap-nests at eight randomly selected sites in forests in summer. To quantify forest loss, the amount of forest coverage was calculated using GIS. To indicate local habitat conditions, the species richness of understory flowering plants was used. All together, 12 species of wasps and no bees were captured. Regression analyses showed that both abundance and species richness of the wasps were not significantly related to forest coverage. However, abundance of trap-nesting wasps was significantly related to species richness of understory plants, but species richness of the wasps was not significantly related to the plants. These results suggest that communities of trap-nesting wasps in forests are influenced more by the local habitat conditions than by forest loss.     

缙云山片断常绿阔叶林小气候边缘效应的初步研究

对缙云山5个片断常绿阔叶林和1个连续常绿阔叶林林缘附近的小气候要素水平梯度分布进行测定.结果表明,各片断阔叶林斑块边缘均存在明显的小气候边缘效应.林缘与林内最高和最低气温、光合有效辐射、最小相对湿度均为干季高于或大于雨季,而地表最高温度则为雨季高于干季;各阔叶林斑块的小气候边缘效应以最大斑块波及林内的深度最浅、最小斑块波及林内的深度最深.     

Effects of fragmentation on forest structure and litter dynamics in Atlantic rainforest in Pernambuco, Brazil

This study evaluates the effects of fragmentation on the spatial and temporal dynamics of small litterfall production in Atlantic rainforest in Pernambuco State, Brazil. Litterfall was collected for 24 months at two 0.2 ha sites, located in the forest edge zone and the forest interior, within a rainforest patch of about 300 ha. Structural parameters of both forest sites were recorded. Litter was sorted into six fractions (foliage, twigs, buds/flowers, fruits/seeds, peduncles, rest), dried and weighed. The interior forest plot contained 314 live trees with a dbh 5 cm and a stand basal area of 41.8±8.7 m², whereas the forest edge contained 211 live trees and a stand basal area of 23.4±3.6 m². Total small litterfall was extraordinarily high and totalled 12.62±4.73 t ha⁻¹ yr⁻¹ in interior forest and 14.74±2.78 t ha⁻¹ yr⁻¹ in forest edge. High litterfall rates are probably due to a pronounced periodicity, edge effects alter litterfall strongly.     

Extent and spatial patterns of grass bald land cover change (1948–2000), Oregon Coast Range,USA

Globally, temperate grasslands and meadows have sharply declined in spatial extent. Loss and fragmentation of grasslands and meadows may impact biodiversity, carbon storage, energy balance, and climate change. In the Pacific Northwest region of North America, grasslands and meadows have declined in extent over the past century. Largely undocumented in this regional decline are the grass balds of the Oregon Coast Range, isolated grasslands in a landscape dominated by coniferous forests. This study was conducted to quantify the spatial extent and patterns of grass bald change. Five balds in the Oregon Coast Range were evaluated using historical aerial photographs and recent digital orthophoto quadrangles (DOQ). Over the time period of study (1948/1953 to 1994/2000), bald area declined by 66%, primarily from forest encroachment. The number and average size of bald vegetation patches declined, while edge density increased. Tree encroachment into balds was inversely related to distance from nearest potential parent trees. Spatial patterns of bald loss may result from a forest to bald gradient of unfavorable environmental conditions for tree establishment and/or seed dispersal limitation. Species dependent on balds may be at risk from loss of bald area and increased fragmentation, although metrics of habitat fragmentation may not reflect species-specific habitat requirements. Tree encroachment patterns and increased bald edge densities suggest increasing rates of bald loss in the future. The remote sensing nature of this study cannot determine the fundamental causes of bald decline, although prior research suggests climate change, cessation of native burning, successional changes in response to prior wildfires, and cessation of livestock grazing all may have potential influence.     

Species-specific distribution of two sympatric Maculinea butterflies across different meadow edges

An important consequence of habitat fragmentation is the increase of edge habitats. Environmental factors in the edges are different from those in the interiors, which causes changes in the distribution of plant and animal species. We aimed to study how edges affect the distribution of two butterfly species within meadow fragments. We therefore investigated the effect of distance from edge and edge type (road edge versus tree edge) on two sympatric large blue species (Maculinea teleius and M. nausithous). Our results showed that edge type had contrasting effects on the two species. M. teleius favoured both interiors and road edges, while M. nausithous preferred the tree edges. In the case of the latter species a strong positive edge effect was also found. This kind of within-habitat niche segregation is probably related to the different microenvironmental conditions at the edges. Foodplant density did not seem to limit the distribution of these species. Our results suggest that interiors of meadows are important for M. teleius, while tree edges maintain the habitats of the regionally rarer butterfly, M. nausithous.     

Effects of management and adjacent forest on the heathland bryophyte layer

Heathlands are severely threatened by decreasing habitat quantity and quality. In these habitats, bryophytes form an important component of plant diversity. Therefore, the aims of this study were to investigate the effects of management and adjacent forest land use on the heathland bryophyte layer. Furthermore, effects of these factors on invasive bryophyte species were studied.

Bryophyte communities of 11 dry heathland patches bordering forest were surveyed. In these heathlands, management turned out to be an important factor explaining community composition of bryophytes. Furthermore, significant effects of adjacent land use on bryophyte community composition and species richness were found. However, these effects were rather limited in extent, occurring only close to habitat borders, i.e., up to maximum 5 m into the heathland patch. Also for individual bryophyte species, effects of adjacent forest could only be observed within maximum 5 m from the edge. One remarkable edge effect was the increased dominance of the invasive species Campylopus introflexus near the forest edge, especially at grazed sites. Effects of adjacent land use seemed to predominate management effects. Consequently, management cannot serve as a tool to mitigate edge effects on bryophyte species in heathland patches.     

Changes in plant species density in an experimentally fragmented forest landscape: Are the effects scale‐dependent?

The establishment of commercial tree plantations is a common cause of habitat fragmentation globally, yet the influence of this land use on plant species density in fragmented native forests requires further understanding. Theory predicts species density will be highest in large areas of habitat, and should decline as area is reduced, but whether these effects are scale‐dependent is largely unknown. We assessed plant species density (total, common and uncommon species) in experimentally fragmented eucalypt forest remnants (0.25, 0.88, 3.06 ha) surrounded by a pine plantation, at three spatial scales using nested quadrats. Specifically, we consider how plant species density varies across three different sized fragments, and whether the response of species density is magnified in common or uncommon species. Species density in small fragments was higher than continuous forest for all species groupings at the smallest spatial scale (1 m²), and for total and common species at the next smallest spatial scale (16 m²). No species groupings responded to reductions in habitat area at the largest spatial scale (144 m²). We suggest that pine plantations may cause higher species density in small fragments via two mechanisms, either by allowing species to infill unoccupied areas within small fragments, or by buffering small fragments from species losses during a severe and prolonged drought. In both cases we suspect reduced moisture stress (e.g. increased soil moisture, higher shading and reduced temperature) in small fragments has led to the observed changes in species density.