广州钟岭村风水林的群落结构及其珍稀濒危植物保护

风水林是区域乡土植物的重要栖息地和种源地, 也是一些珍稀濒危植物的生长地。以广州市增城钟岭村的风水林为对象, 研究其群落结构和生境特征, 并分析群落内珍稀濒危植物格木和土沉香的种群特征。在800 m2 样地内有维管束植物31种, 隶属于21 科28 属, 以热带分布科和属占优势。林内优势种有5 种。群落可分为乔木层、灌木层和草本层3 个层次, 缺少层间植物。生活型以中、小高位芽为主。该风水林内有珍稀濒危植物格木(Erythrophleum fordii)和土沉香(Aquilaria sinensis), 格木以大个体为主, 缺乏幼苗, 自然更新不良, 而仅有1株土沉香幼苗。为了保护区域内的乡土种种源, 建议将广州市内有珍稀濒危植物生长的风水林设为自然保护小区并进行严格管理。     

喀斯特风水林和荒山生态系统碳储量的研究

所研究的风水林和荒山属于喀斯特地貌。喀斯特森林是一种脆弱的低生物量生态系统,土壤贫瘠,自我修复能力低,易受人为因素干扰。风水林指人们居住地附近的一片茂盛的森林,认为有神居住而崇拜,严禁被砍伐和破坏。荒山是喀斯特森林植被在人为干扰后出现岩石裸露产生的石漠化现象。该研究通过野外调查、实验室分析、数理统计等对广西罗城喀斯特风水林和荒山生态系统碳储量进行对比性研究。结果表明:喀斯特风水林植被、土壤和枯落物碳储量分别是荒山的7.42倍、5.9倍和1.1倍,风水林和荒山生态系统碳储量分别为137.06、93.73 t·hm~(-2),其中土壤碳库贡献率最高,而林下植被和枯落物却较低,表明风水林森林生态系统碳储量明显高于荒山。通过风水林和荒山的碳储量比较研究,为评价风水林碳汇提供依据,为制定森林管理政策、保护村社水平的植被提供数据参考。此外,还探讨了少数民族朴素的生态伦理思想在保护森林和增汇方面的作用,丰富了生态伦理学内容,对传承和弘扬少数民族传统文化、恢复生态具有重要意义。     

破碎化生境中粗柄独尾草种群大小对繁殖特性的影响

景观破碎化是目前存在的一种普遍现象,导致物种生存的原有生境总面积减小,产生许多大小不一的斑块种群。不同斑块生境中植物种群的大小直接反映植物对环境的响应特征和适应对策,与植物繁殖有关的开花结实特性、种子形态及萌发特性的研究将有助于深入了解植物在不同生境中的生存策略。以粗柄独尾草(Eremurus inderiensis)为研究对象,以野外调查为基础,对比研究不同斑块粗柄独尾草种群的种群大小和生殖成功,揭示不同生境中粗柄独尾草的生态适应性。结果表明:(1)不同斑块生境中,种群大小差异较大,且较小的种群幼苗比例也较小,种群大小与种群幼苗比例呈显著相关;(2)较小的种群自然座果率、结籽率较低,种群间差异显著;(3)随着生境破碎化程度增加,种子千粒重,种子长、宽等形态特征呈减小趋势,但种翅占比增大;(4)在粗柄独尾草最适萌发温度下,随着生境破碎化程度增加,种子萌发率有下降趋势。针对人类干扰程度强的衰退型粗柄独尾草种群,亟需减少人为干扰,依据不同生境中的干扰因素及种群生存现状,制定科学与切实可行的保护和恢复策略。     

浙江长兴金钱松群落结构特征及其资源保护研究

金钱松属于国家二级重点保护植物,为能科学有效地对该物种进行保护,对浙江长兴县分布的金钱群落特征进行了研究。本研究利用群落调查方法,在浙江长兴县设置18个面积约为100 m~2的样圆,调查群落内的物种组成及其结构特征。结果表明,群落内共有种子植物74种,隶属于37科56属;种属组成较为分散,优势科不明显。Raunkiaer频度定律表现为ABCDE。重要值结果显示位列前六的物种分别为金钱松、毛竹、栗、苦槠、冬青和盐肤木,其值分别为17.48%、15.86%、4.83%、4.81%、4.43%和4.09%。金钱松群落垂直结构可分为4层,层次结构较为简单。随着群落的进一步发展,金钱松优势地位可能会被毛竹及其他常绿阔叶树种所取代;控制竹类植物的扩张,对保护现存金钱松种群有积极意义。     

三种裸子植物木质部结构与功能对不同生境的适应

生境异质性是影响植物生长发育的重要因素。植物木质部水力系统是土壤-植物-大气连续体的主要通路,直接影响植物的基本行为和功能,同时也反映了植物对环境变化的适应性。为对比天目山3种裸子植物枝条木质部水力功能、机械和解剖结构性状在不同生境(自然生境与人工生境)的差异,揭示裸子植物对不同生境的适应机制,该研究以金钱松(Pseudolarix amabilis)、杉木(Cunninghamia lanceolata)和雪松(Cedrus deodara)为研究对象,测定枝木质部导水率、栓塞抗性(导水率损失50%时的水势)、机械以及解剖结构性状。结果发现:1)人工生境植株比自然生境植株水力效率弱,但栓塞抗性强。2)自然生境雪松木质部导水系统存在效率-安全权衡;不论自然还是人工生境杉木、金钱松木质部导水系统均无效率-安全权衡。3)人工生境雪松和金钱松木质部存在机械-安全权衡。相比人工生境,土壤水分有效性低的自然生境中,植物采用增大纹孔膜直径来提高水力效率,此外,还可通过增加木材密度、扩大管胞直径来避免栓塞带来的威胁。     

基于回归保护的东北红豆杉野生种群维持的制约因素

为明确东北红豆杉野生种群维持的关键制约因素,制定现有种群的保护策略与技术环节,本研究调查了我国主要分布区内东北红豆杉野生种群的更新状况与分布格局,分析了林分因子与人为干扰对种群更新与维持的影响。结果表明：目前我国东北红豆杉野生种群整体更新情况较差,更新个体的径级与高度级结构呈现出不健康的状态,但有19%区域更新较好,种群整体表现为成树少更新差、成树多更新差、成树少但更新较好3种类型。东北红豆杉所在群落可以划分为臭冷杉+紫椴林、杂木林、兴安鱼鳞云杉+臭冷杉林,其中臭冷杉+紫椴林的更新数量显著多于杂木林;林分密度增加与适度的人为干扰对东北红豆杉更新有一定的促进作用,林分由低密度增到中等密度时东北红豆杉更新幼苗数量显著增加,所在生境受到适度干扰的种群更新数量显著多于轻度干扰下的种群。人为干扰和栖息地生境是目前东北红豆杉野生种群维持与更新的关键制约因素。东北红豆杉的保护应基于各生境斑块种群的更新现状制定相应的就地保护和回归保护等措施,并在保护过程中重点考虑干扰和生境条件等关键因素的影响。     

复合种群中扩散的研究进展

复合种群理论是近年来景观生态学和保护生物学研究的热点之一,但有关复合种群的野外试验研究大多集中在面积和隔离度等方面,对影响复合种群动态因子的具体报道较少。事实上,复合种群的影响因子还有很多,如连通性、扩散和生境质量等。本文就复合种群中扩散进行了综述,主要包括以下的几个方面:(1)扩散的影响因子。生境质量、斑块连通性和种群自身密度等;(2)扩散方向与测定。扩散的方向是有选择的,在其方向的测定中微卫星标记(microsatellitemarker)得到了较广泛的应用;(3)扩散距离与测定。扩散的距离除受到物种自身特性的影响外,还受到踏脚石等生境因素的影响;(4)扩散对复合种群的影响。扩散受到复合种群空间结构以及生境质量等自身条件的影响,同时又反作用于复合种群的动态变化,在以后物种保护工作中必须加以重视。     

Allee效应对具有生境恢复的集合种群的影响

Allee效应与种群的灭绝密切相关,其研究对生态保护和管理至关重要。Allee效应对物种续存是潜在的干扰因素,濒危物种更容易受其影响,可能会增加生存于生境破碎化斑块的濒危物种的死亡风险,因此研究Allee效应对种群的动态和续存的影响是必要的。从包含由生物有机体对环境的修复产生的Allee效应的集合种群模型出发,引入由其他机制形成的Allee效应,建立了常微分动力系统模型和基于网格模型的元胞自动机模型。通过理论分析和计算机模拟表明:(1)强Allee效应不利于具有生境恢复的集合种群的续存;(2)生境恢复有利于种群续存;(3)局部扩散影响了集合种群的空间结构、动态行为和稳定性,生境斑块之间的局部作用将会减缓或消除集合种群的Allee效应,有利于集合种群的续存。     

独龙江流域羚牛的种群、分布和保护

2012年11月至2013年7月间研究了独龙江乡区域羚牛指名亚种Budorcas taxicolor taxicolor(后文简称羚牛)的种群分布、数量和保护现状的问题。研究采用了改良的访问调查和实地调查相结合的方法。其中实地调查独龙江乡羚牛种群一群,调查面积35.70 km2,目测羚牛种群数量58头,适宜生境面积24.46 km2。计算羚牛适宜生境种群密度为2.4头/km2。种群数量和访查信息相符合,说明采用访问调查的方法是可靠的。本研究共计访问调查了独龙江乡的25个村庄,发现共有12个羚牛种群分布在独龙江乡,分布区羚牛适宜生境面积总和为167 km2。综合羚牛分布区面积和访查结果,本研究估算当前独龙江羚牛种群数量为400~450头。根据实地调查中羚牛利用的生境类型,利用GIS分析获得全独龙江羚牛适宜生境面积为1726 km2,可承载超过4000头,因此独龙江区域应为羚牛指名亚种的主要分布区。基于访查结果本研究还分析了羚牛的垂直分布和保护现状,提出降低人为干扰和保护羚牛生境廊道是独龙江羚牛保护的关键。     

广州市风水林群落空间异质性及其对区域物种多样性的贡献

以广州地区村边风水林为研究对象,选取了67个风水林斑块,并在每个斑块内建立了一个20m×20m的样方,调查了其胸径大于1cm的植物组成。首先以种面积关系外推法和非参数法估计了风水林群落对区域生物多样性的贡献;然后以加法准则拆分了gamma多样性,以分析风水林群落物种组成的异质性;最后根据每个风水林群落的物种丰富度、稀有种(在所有群落中只出现一次的物种)数目和谱系多样性分析了在保护中需要优先考虑的区域。结果发现：（1）广州地区风水林群落至少保存了32.74%的区域物种多样性;（2）gamma多样性(184)中绝大部分由beta多样性(163.43)构建,只有很小部分来自于alpha多样性(20.57)。这表明风水林群落在物种组成上具有较高的空间异质性,要想尽可能多地保护风水林内物种多样性,就需要尽可能多地保护风水林群落斑块;（3）相对于平原地区,位于山区的风水林群落具有更高的物种丰富度和谱系多样性以及更多的稀有种数目。在保护资金和土地资源有限的情况下,位于山区的风水林群落应该给予优先考虑。     

大兴安岭不同演替阶段天然林物种多度格局模拟

为实现大兴安岭地区落叶松天然林的全周期可持续经营,以新林林业局翠岗林场3块100m×100m不同演替阶段(白桦林、落叶松-白桦混交林和落叶松林)的天然林固定调查样地数据为基础,采用统计模型(对数正态模型)、生态位模型(断棍模型、生态位优先占领模型、Zipf模型、Zipf-Mandelbrot模型)和中性模型(群落零和多项式模型、Volkov模型)对不同演替阶段天然林的乔木层、幼苗层和由乔木层划分的不同林层的物种多度格局进行拟合,并用χ² 检验和Kolmogorov-Smirnov检验选择最佳模型。结果表明:(1) 在大兴安岭地区不同演替阶段的落叶松天然林群落中,Zipf-Mandelbrot模型的拟合效果均最好。(2) 对数正态模型对于稳定的演替阶段白桦林和落叶松林的群落相较于过渡阶段群落落叶松-白桦混交林的物种多度分布的拟合效果更好。(3) 在大兴安岭地区落叶松天然林中,生境过滤主导群落构建,随着群落不断演替生境过滤和中性过程减弱。(4) 天然林群落乔木层的群落构建过程与乔木层内不同生长阶段林层的构建过程不同,生境过滤过程在落叶松林乔木层中逐渐减弱,而在落叶松林不同生长阶段的林层和更新层中增强。     

Pine forest structure in a human-dominated landscape system in Korea

To elucidate the characteristics of spatial heterogeneity in a human-dominated landscape, vegetation and community structure of pine (Pinus densiflora andP. rigida) forests were studied at rural Teokseong-ri in Chollanam-do, in the southwestern part of Korea. Daily removal of undergrowth for firewood affects the stratification and species composition in the community. In general, stratification of the pine forest develops in proportion to its distance from the main habitat of farmers, involving the residential and cultivated land. In pine forests near the main habitat of farmers, sun-demanding herbaceous plants grow well, while in remote forests, Fagaceous plants such asQuercus serrata, Q. actissima andCastanea crenata grow well. This zonation results from the fact that removal of undergrowth is greater in the forest near the main habitat of farmers, than in the remote forest. Construction and maintenance of graveyards, however, prevents development of stratification of the forest even in remote stands.     

Forest Fragmentation Alters the Population Dynamics of a Late‐successional Tropical Tree

Tropical late‐successional tree species are at high risk of local extinction due to habitat loss and fragmentation. Population‐growth rates in fragmented populations are predicted to decline as a result of reduced fecundity, survival and growth. We examined the demographic effects of habitat fragmentation by comparing the population dynamics of the late‐successional tree Poulsenia armata (Moraceae) in southern Mexico between a continuous forest and several forest fragments using integral projection models (IPMs) during 2010–2012. Forest fragmentation did not lead to differences in population density and even resulted in a higher population‐growth rate (λ) in fragments compared to continuous forests. Habitat fragmentation had drastic effects on the dynamics of P. armata, causing the population structure to shift toward smaller sizes. Fragmented populations experienced a significant decrease in juvenile survival and growth compared to unaltered populations. Adult survival and growth made the greatest relative contributions to λ in both habitat types during 2011–2012. However, the relative importance of juvenile survival and growth to λ was highest in the fragmented forest in 2010–2011. Our Life Table Response Experiment analysis revealed that positive contributions of adult fecundity explained most of the variation of λ between both habitats and annual periods. Finally, P. armata has a relatively slow speed of recovery after disturbances, compromising persistence of fragmented populations. Developing a mechanistic understanding of how forest fragmentation affects plant population dynamics, as done here, will prove essential for the preservation of natural areas.     

Orangutan Nesting Behavior in Disturbed Forest of Sabah,Malaysia: Implications for Nest Census

High concentrations of orangutans remain in the multiple-use forests of the Lower Kinabatangan, Sabah, Malaysia. Compared to primary forest, the habitat is highly fragmented, characterized by a low tree density (332 stems/ha), small tree size (83.6% of trees are <20 m high), low basal area (18 m²/ha), abundance of canopy gaps and high level of soil disturbance. The forest structure and composition influence orangutan nesting patterns, and thus directly influence the results of nest surveys used to determine orangutan population size. In logged forests, tall and large trees are the preferred nesting sites of orangutans. The scarcity of suitable nesting sites in the logged-over forests of Kinabatangan, could partly explain the lower daily rate of nest construction (r = 1.00) versus those of other orangutan populations. The nest decay rate t recorded at the study site (average ± SD = 202 ± 151 days) strongly depends on the species of tree in which a nest is built. Our results illustrate that the nest-related parameters used for orangutan censuses fluctuate among habitat types and emphasize the need to determine specific values of r for specific orangutan populations and of t for different tree species in order to achieve accurate analysis of census data.     

The ecology, silviculture and biogeography of mahogany (Swietenia macrophylla): a critical review of the evidence

Recent studies of Swietenia macrophylla King argue that natural regeneration of this highly valued tree is episodic and occurs only after infrequent catastrophic disturbance. An analysis of 14 population size-distributions in natural forests shows that population structure varies across this species' range. In forests that are in successional transition from open deciduous forest to evergreen forest there is often prolific regeneration. We show that in this type of forest in southern Pará (Brazil) patches of even-sized trees are small. Large-scale disturbance may be necessary for regeneration only in evergreen forests where little light penetrates through the canopy. The transition zone between evergreen and deciduous forest in Pará is moving south, and we propose that mahogany populations to the north are in the process of competitive exclusion. Sustainable harvesting of mahogany must take account of the successional stage of the forest.     

The role of traditional forest gardens in the conservation of tree species in West Kalimantan, Indonesia

We compared forest gardens, or tembawang, in twoareas in West Kalimantan, Indonesia, to patches of primary forest in terms ofsuccessional stage, mode of dispersal and characteristics of human use ofnon-planted tree species. This information was acquired for 144 tree speciesinventoried in six tembawang forest gardens and two intactnatural forest patches, through interviews at the site and a survey of theliterature. In particular older tembawang were found tohave practically the same proportions of species of different successionalstages and modes of dispersal as natural forests, thus emphasising the potentialof tembawang in conserving tree species. Non-planted treespecies of tembawang and natural forests also havepractically indistinguishable spectra of human uses, indicating that themanagement of these tembawang does not significantlydiscriminate between species with certain uses. However, we also identified twoaspects that should be taken into account in considering the conservation roleof tembawang. The floras of the two study areas showedsignificant regional differentiation, implying that efficient conservation inWest Kalimantan needs to have a rather dense network. We also found that latesuccessional species and animal-dispersed species oftembawang were more commonly geographically widespread thanspecies of the same ecological characteristics found in natural forests. Thus,even if tembawang are similar to natural forests in termsof numbers of species with different ecological characteristics, the compositionof non-planted tree species in tembawang is not a randomsample from natural forest, but overrepresents species that are easily dispersedand/or established.     

八仙山不同类型松栎林群落主要特征分析

为探究八仙山保护区不同类型森林群落的更新潜力、多样性程度以及稳定性水平,阐明三者间的关系,该文以保护区内油松林、蒙古栎林和油松-栓皮栎混交林(松栎混交林) 3种不同类型天然次生林为对象,调查建群种径级结构和更新潜力,计算不同层次群落多样性,测定M. Godron稳定性,并采用主成分法建立评价模型。结果表明:(1)油松种群径级结构近似正态分布,处于成熟期,但幼苗较少;栓皮栎、蒙古栎以及阔叶杂木的幼苗、幼树较多,更新潜力较大。(2)松栎混交林的乔木层多样性较高,而灌木层多样性最低,油松林的草本层多样性最低;松栎混交林群落总体物种丰富度最低而均匀度最高。(3) M. Godron稳定性表明,蒙古栎林距离稳定点较近,而油松林偏离较远。(4) PCA双序图表明,M. Godron稳定性与种群更新潜力、Alatalo均匀度呈较强正相关,综合排序依次为松栎混交林、蒙古栎林和油松林。综上结果表明,建群种更新潜力和物种均匀度对群落稳定性影响较大,林地管理应注重对幼苗幼树的保护。     

Changes in patch mosaics and vegetation structure of rural forested landscapes under shifting human impacts in South Korea

Landscape change in rural ecosystems is a major global issue because they are an important ecological and socio-cultural resource. The aim of this study was to demonstrate the driving forces behind landscape changes. Changes in the patterns and processes of landscape mosaics and vegetation community in two rural areas (Teokdong-ri, TD and Teokseong-ri, TS) in Korea were studied between 1988 and 2002. Quantitative data of vegetation community, landscape mosaics, and local statistics of the two study areas were analyzed. Agricultural efficiency increased even decreasing household population and the agricultural area. In both areas, as the human dependence on natural resources decreased, the patterns and processes of landscape mosaics and forest structure were changed due to changing human impacts on land use. Owing to the abandonment of forest management for 14 years, the spatial heterogeneity of TD significantly increased more than that of TS. In detrended correspondence analysis ordination, floristic compositions of forest patches of two areas were unevenly located on the ordination axes. Pinus densiflora communities of both areas in 1988 were separately located in 2002 as two directions according to management intensity. The species composition of P. densiflora in one direction of 1988 became similar to those of Quercus forests in 2002. This may be because species composition of P. densiflora has been influenced due to changed habitat environments. Finally, we concluded that the development of forest communities and vegetation succession predicted the spatial pattern of future landscape mosaics and due to the vegetation dynamics of rural ecosystems in Korea.Nomenclature: Miyawaki et al. (1994), Lee (1993), and Lee (1998) for identifying plant species.     

沙地樟子松天然林南缘分布区林木竞争、空间格局及其更新特征

以呼伦贝尔沙地樟子松地理分布南缘天然林为研究对象,采用Hegyi竞争指数与点格局等分析方法,研究了沙地樟子松天然林的种群结构、种内竞争、空间格局及幼树更新等特征。结果表明:1)所调查区域天然沙地樟子松纯林处于中幼龄阶段,属增长型种群;2)其竞争指数与对象木胸径服从幂函数关系CI=242.24D~(-1.12)(R~2=0.91);3)幼树在小尺度上呈聚集分布,中树与大树在中大尺度上呈随机分布;幼树与中树在小尺度上呈正相关性,中树与大树在小尺度呈负相关性;4)竞争指数与更新幼树和存活更新幼树的密度均呈显著正相关性。在林分管理中需要充分考虑林木竞争、空间格局以及种群更新的关系,本研究可为沙地樟子松天然林的经营管理与保护提供重要的科学依据。     

Population dynamics of Japanese serow in relation to social organization and habitat conditions. II. Effects of clear-cutting and planted tree growth on Japanese serow populations

Population responses of Japanese serow (Capricornis crispus) to clear-cut logging and planted tree growth were studied by a direct count of the number observed in three areas, Takiyama (305 ha), Gentouziro (270 ha), and Tanokashira (324 ha), near Wakinosawa Village, Aomori Prefecture, Japan, during 1976–89. At Takiyama, a mature mixed forest ofThujopsis dolabrata var.hondai andFagus crenata decreased from 73 to 39% coverage of the area due to clear-cutting during 1978–83. The serow population maintained a relatively low stable density (3–6 individuals per km²) until 1985–87, and increased 5–10 years after the clear-cutting, reaching 9–10 km⁻² in 1988. At Gentouziro and Tanokashira, young plantations of Japanese cedar (Cryptomeria japonica) covered about half of each area. The population densities between 1980 and 1983 were relatively high (14–19 km⁻²), but declined thereafter, reaching 10–14 km⁻² in 1988–89. These results indicated that the density increase resulted from an improvement of food supply due to growth of scrub following the clear-cutting, and that the density decline resulted from a habitat change due to growth of planted Japanese cedar and a decrease in the food supply. In Wakinosawa Village, serow density began to increase 5–10 years after forest cutting, and the high population density, about three- or six-fold larger than that in mature forest, is expected to be maintained for about 20 years after logging.