林隙对小兴安岭阔叶红松林树种更新及物种多样性的影响

研究了小兴安岭阔叶红松林不同林隙梯度(林隙中心、林隙近中心、林隙边缘)中主要树种的数量特征,以及林隙大小对树种更新的影响.结果表明:不同梯度林隙内灌木树种的密度均明显高于非林隙,同种灌木密度的比值在1.08～18.15之间;随林隙面积增加,乔木幼苗更新密度逐渐增大,幼树Ⅰ(高度H≥1 m,胸径DBH≤2 cm)和幼树Ⅱ(H≥1 m,2 cm＜DBH≤5 cm)的更新密度呈多峰曲线.林隙灌木总体更新密度主要随幼苗和幼树Ⅰ数量而变化.林隙内不同位置幼苗的平均树高、平均基径、种密度和个体密度有所差异.从林隙中心到非林隙,更新层乔木幼苗重要值的大小顺序为:林隙中心＞林隙近中心＞林隙边缘＞非林隙;物种均匀度呈高-低-高的变化,物种多样性的变化为早期林隙＞中期林隙＞晚期林隙.     

基于无人机影像探讨格氏栲天然林林窗数量分布及其影响因素

探讨格氏栲( Castanopsis kawakamii)天然林林窗数量特征及其空间分布对预测森林种群动态变化及演替具有重要意义。该文采用无人机航拍获取格氏栲天然林正射影像图并结合野外调查,通过提取林窗特征参数和计算植被覆盖率来探讨林窗空间分布及其影响因素。结果表明:(1)保护区内格氏栲天然林植被覆盖率为75.53%,部分地区出现一定面积裸露土地。(2)研究区林窗空隙率为2.40%,密度为6.50 ind.·hm^-2,平均林窗面积为36.86 m²。(3)研究区林窗数量随林窗面积增加呈负指数分布,以微、小和中型林窗为主,面积100 m²以上的林窗数量较少。(4)低海拔林冠层覆盖度好,中海拔地区林窗个体数和平均林窗面积较大,高海拔地区林窗密度和空隙率相对较大。林窗主要分布在缓坡和斜坡上,其平均面积、密度和林窗空隙率也明显较高。西和南方位林窗数量较多,北、西北和东南方向林窗密度和空隙率相对较大。格氏栲天然林植被覆盖率较高,以微、小和中型林窗为主,地形因子通过改变林窗面积、林窗密度和林窗空隙率特征驱动了格氏栲天然林林窗数量与空间分布格局。     

昆明城市绿地结构对鸟类多样性的影响

岛屿化的绿地格局对城市鸟类的群落结构及空间分布会产生重要影响。通过样线法和样方法调查昆明城区19块绿地内的鸟类种类和数量、乔木种类和数量,结合遥感影像和现场调查,使用ArcGIS分析绿地生境结构,研究了城市绿地与鸟类的关系。结果表明,鸟类种类和数量与绿地面积呈正相关、与绿地距市中心距离无相关性;绿地内水域、硬化地、建筑地面积与鸟类种类和数量呈一定的负相关;乔木种数和食源乔木种数与鸟类种类呈显著正相关;城市绿地结构对鸟类的影响还与鸟类的生态习性相关。因此可以通过优化生境结构、改变绿地面积及乔木组成来提高城市鸟类多样性。     

哀牢山中山湿性常绿阔叶林林窗更新研究

对云南哀牢山中山湿性常绿阔叶林林窗更新状况的调查结果表明,林内优势树种在林窗阶段不占优势,其在林窗内的重要值显著低于成熟林分;林窗内外的乔木幼苗在组成上存在较大差异,林窗内的幼苗多样性(H=2．73,D=0．89)高于林冠下(H=2．25,D=0．82),二者的Jaccard相似系数只有0．6．许多树种的幼苗只出现在林窗内;林窗内的乔木幼苗密度(38636株·hm²)远远高于林冠下(17323株·hm²)．林窗内和林冠下的乔木幼苗(H≤50cm)均以高度为11～20cm幼苗的在数量上占优势,但林窗内高度超过20cm的幼苗比例明显高于林冠下;林窗大小对乔木幼苗更新有重要影响,不同树种的幼苗密度高峰出现在不同大小级别的林窗内．     

闽北闽粤栲天然林林隙物种数量特征及更新规律分析

以福建省顺昌县的闽粤栲〔Castanopsis fissa(Champ.ex Benth.)Rehd.et Wils.〕天然林为研究对象,根据林隙面积(A)划定4个等级(A<50 m2、50 m2≤A<100 m2、100 m2≤A<150 m2和150 m2≤A<200 m2)的样地,并以非林隙样地为对照,对林隙和非林隙的乔木层、灌木层和灌草层中的物种分布、组成及生长状况进行调查和统计;在此基础上,对林隙和非林隙中主要物种的数量特征和更新响应规律进行比较分析.结果表明:闽粤栲天然林林隙和非林隙的乔木层分别有54和35种植物,共有种28种;灌木层分别有61和37种植物,共有种29种;灌草层分别有72和49种植物,共有种37种.从乔木层和灌木层各种类的重要值及灌草层各种类的密度看,林隙和非林隙中的优势种类均为闽粤栲和木荷(Schima superba Gardn.et Champ.)等,且林隙和非林隙间各优势种类的重要值差异不明显,其中,闽粤栲的重要值和密度均位居第一.从林隙和非林隙间各优势种类的重要值差值看,林隙的主要优势种类(如闽粤栲和木荷等)对林隙更新响应不明显,而其他种类对林隙则有强烈或中等的正、负更新响应,且在不同林层间有差异.从平均更新密度看,林隙面积对各优势树种的更新有一定影响,其中,林隙面积在150~200 m2时闽粤栲和丝栗栲(Castanopsis fargesii Franch.)的平均更新密度最大,林隙面积在100~150 m2时米槠〔Castanopsis carlesii(Hemsl.)Hay.〕、木荷、青冈〔Cyclobalanopsis glauca(Thunb.)Oerst.〕和黄毛润楠(Machilus chrysotricha H.W.Li)的平均更新密度最大,但在不同面积林隙间各树种的平均更新密度无显著差异(P=0.867).研究结果说明:在闽粤栲天然林中,对林隙更新响应不明显的种类较易成为林分的优势种或建群种,但林隙面积对树种的更新密度没有明显影响;从林隙到林冠的发育过程中,闽粤栲始终处于该林分的优势地位.     

红外相机安放于地面和林冠层对野生动物监测结果的影响

红外相机技术在野生动物研究中日趋普及, 逐渐成为重要的生物多样性监测手段。过去的监测常局限于地面, 而针对林冠层的监测较少, 这对野生动物的多样性评估影响尚未可知。为此, 本研究在生物多样性丰富的碧罗雪山南段, 将20台红外相机分别拍摄地面层(0.5-1.5 m)和林冠层(5-10 m)配对比较, 累计拍摄2,319个有效相机日, 平均每对相机同步进行112.5 d的监测。监测期间共拍摄到44种野生动物(不包括鼠形啮齿类), 其中兽类20种, 鸟类24种; 冠层和地面红外相机监测的物种相似度为29.54%; 15种动物仅拍摄于林冠层, 16种动物仅拍摄于地面, 13种动物拍摄于两个林层。研究结果表明不同林层监测的物种组成存在显著差异, 林冠层与地面层监测都具有不可替代性; 不同林层红外相机的监测手段也能用于研究野生动物的空间选择和生态位分化。红外相机监测中根据目标物种的习性在相应的林层设置相机能提高物种发现率; 为全面掌握区域森林生态系统野生动物的多样性, 红外相机监测需要兼顾不同林层这一点需要在监测规范中明细。     

黄土丘陵区油松天然次生林林窗特征与更新动态

研究了黄土丘陵区油松天然次生林林窗的形状、大小结构、分布、形成木特征及其更新状况.结果表明:在油松天然次生林中,林冠林窗(CG)和扩展林窗(EG)面积均呈以小林窗为主的偏态分布.CG平均面积为31.15 m²,以20～40 m²林窗的数量比和面积比最大,分别为38.24％和30.50％;EG平均面积为58.04 m²,以30～60 m²的数量比和面积比最大,分别为36.77％和27.79％,且CG的平均面积占EG平均面积的53.67％;林窗形状多呈椭圆形,高度多在14～16 m;林窗形成年龄以10～20年为主,占33.82％.林窗中基折和枯立木分别占形成木总数的47.66％和23.44％.林窗形成的主要因素是人为间伐或盗伐,树木衰老等引起的抗性下降、干旱、病虫害等也是导致树木死亡的原因之一;每个林窗中平均有1.89个形成木,其中以2株形成木的林窗最多.林窗形成木主要是油松,其次为山杨、白桦和辽东栎等.形成木的径级呈明显的偏态分布,以10～20 cm和21～30 cm径级最为普遍,分别占总数的25.0%和45.31%,与林窗面积偏态分布吻合;林窗内林木的更新状况好于林下,且油松幼苗不存在断层,而油松林下幼苗在年龄结构上有明显的断层.     

神农架地区常绿落叶阔叶混交林树种更新研究

神农架山区山体的中部,选取代表性的常绿落叶阎叶混交林样地,总面积为２．４ｈｍ＾２。在样地中对出现的林窗斑块以及相邻的对照的非林窗宙样方进行群落学调查。记录乔木树种的种类、胸径和高度以及它的幼苗和幼树的高度、数量。按照树种在林宙内外重要值的位序差值将群落出现的乔木层树种划分为４类生态种组,其中,对林窗强烈正更新反应的树种有６种,强烈负更新反应的树种９种,中等更新反应的９种,不明显更新反应的１０种。林窗内外乔木树种生态种组的组成明显不同。不同生态种组树种的幼苗在林宙与非林窗斑块中的更新表现出显著的差别。对神农架地区常绿落叶阎叶混交林树种更新的反应和过程的研究结果支持了林窗—分享假说的观点。     

乌鲁木齐市园林春秋季鸟类群落多样性

2011年4～5月、10～11月,用样线法对乌鲁木齐市中心城区5个园林鸟类群落的组成和多样性进行了调查,共记录到鸟类47种,隶属于9目23科,分布型以古北界为主。其中留鸟、夏候鸟和冬候鸟分别占鸟类总种数的44.68%、34.04%和10.64%,鸟类群落优势种为[树]麻雀Passer montanus、家麻雀Passer domesticus和乌鸫Turdus merula。园林鸟类的平均密度为(11.27±4.3)只/hm2(±S.D.),春季鸟类密度高于秋季,但二者差异不显著(F=0.002,P=0.194)。春季鸟类群落拥有较高物种丰富度和多样性,夏候鸟是此时鸟类群落的重要组成部分;秋季鸟类群落的多样性低而优势度较高,冬候鸟对群落结构影响不大。各园林样地记录到的鸟类种数和密度差异较为明显,园林的内部生境多样性与鸟类种数呈正相关(R=0.9,P=0.037)。     

林窗对川西周公山柳杉人工林林下物种多样性的影响

采用典型样地法,以川西周公山柳杉人工林5种不同大小的林窗为研究对象,以林下非林窗为对照,研究了不同大小的林窗对柳杉人工林物种多样性的影响,同时分析了不同梯度林窗下林窗中心、林窗边缘、及林下群落的物种组成、物种多样性的变化情况。结果表明:(1)在所调查的18个样地231个样方中共记录到维管束植物141种,隶属于76科113属;随着林窗面积的增大,群落各层次的物种数呈现出先升高后降低的趋势,灌木层物种数在各林窗梯度上表现为林缘林下林窗中心,草本层物种数在各林窗梯度上表现为林缘林窗中心林下。(2)不同林窗优势种及其重要值不同,即在小林窗内,优势种为柳杉和野桐,其重要值之和高达0.292 3;在大林窗内,杉木及亮叶桦为群落优势物种,群落内出现大量其更新幼苗。(3)不同大小的林窗表现为灌木层物种丰富度指数(D)、Shannon-Wienner指数(H)、和Pielou均匀度指数(Jsw)值在400~450 m2面积的大林窗内达到一个均优水平,草本层物种的多样性在面积为100~150m2的小林窗内达到较高水平;不同梯度的林窗各层次群落D、H值整体表现为林缘林窗中心林下。研究认为:林窗的存在会改变群落物种组成,提高群落物种多样性水平,并且大林窗(400~450m2)更利于柳杉人工林林下树种更新及物种多样性的提高。     

顺德"青山工程"森林植被改造的群落学特征

以比较样地法对佛山市顺德区“青山工程”森林植被改造前后的群落学特征进行了研究,结果表明：该市以湿地松、隆缘桉、台湾相思、尾叶桉等人工林分为多,种类较单一,优势种明显,各群落种群重要值多集中于少数几个物种,导致生物多样性指数偏低,同时林分的胸径和树高结构大都不合理,影响了森林的生态效益和群落更新。通过林分改造,优化了群落结构,提高了多样性指数。在改造中不宜将上层乔木全伐,以保留郁闭度0．3为佳。     

The Finnish forest site type approach: ordination and classification studies of mesic forest sites in southern Finland

A.K. Cajander's forest site type classification system is based on definition of plant communities typical to certain climatical and edaphical site conditions, but the structure and composition of the tree stands in Finland are considered sensitive to random variation and are therefore not used as primary classification criteria. The system has often received criticism, usually that the effects of the tree stand and successional stage of the stand have been underestimated. Most of the present-day forest stands in Finland represent young successional stages and are subjected to intensive management. This should result in an additional difficulty in the application of the forest site types in the field.The present study is based on three independent data sets representing forests on mineral soil in southern part of Finland. TWINSPAN classification, DCA ordination and canonical correspondence analysis (CCA) techniques were applied in successive stages of the data analysis. It was found that the definition of the intermediately fertile, mesic site types was clearly confused by the effects of the tree species and age of the stand. The analyses also revealed that the succession pathways on mesic forest sites are largely determined by the tree species composition. In stands dominated by Pinus sylvestris, the succession follows the competitive hierarchy model, whereas in stands dominated by Picea abies, severe shading of the tree canopy governs the development of understorey vegetation.Abbreviations CCA Canonical correspondence Analysis - DCA Detrended correspondence Analysis - TWINSPAN Two-way indicator species analysis     

The gap theory in forest dynamics

Since the late 1970s, ecologists interested in forest dynamics have focused their attention to the responses of individuals, populations and communities to “gaps” which are openings created in the forest canopy. This review intended to introduce some collective knowledge on major subjects of the gap theory in forest dynamics, in relation to gap-disturbance regimes, tree regeneration behaviour and community structure.     

Considerations regarding species distribution models for forest insects

1. Species distribution models, or SDMs, have become important decision support tools by answering fundamental questions about where species, including invasive species, are likely to survive and thrive based on environmental conditions.
2. For an inexperienced modeller or model reviewer, the terminology and technical aspects of SDMs can be overwhelming, and even well-trained modellers can struggle to understand the implications of various modelling choices.
3. Here, I outline some key considerations with respect to SDMs, focusing on their application to forest insects. Foremost, I assert that a model should be developed and evaluated with attention to relationships between an insect and its hosts, as those relationships determine much about the places the insect may occupy.
4. In my view, the most successful models are constructed carefully and incorporate honest assessments of their limitations, sources of error and uncertainty, and the degree of linkage between the model and the real-world circumstances it is meant to portray.

     

Factors influencing sapling composition in canopy gaps of a temperate deciduous forest

To detect the factors that affect sapling species composition in gaps, we investigated 55 gaps in an old-growth temperate deciduous forest in Ogawa Forest Reserve, central Japan. Gap size, gap age, gap maker species, topographic location, adult tree composition around gaps, and saplings of tree species growing in the gaps were censused. For gaps 5 m², mean gap size was 70 m² and the maximum was 330 m². Estimated ages of gaps had a tendency to be concentrated in particular periods relating to strong wind records in the past. The sapling composition in gaps was highly and significantly correlated to that under closed canopy, indicating the importance of advance regeneration in this forest. However, some species showed significant occurrence biases in gaps or under closed canopy, suggesting differences in shade tolerance. The result of MANOVA showed that gap size and topography were important factors in determining the sapling composition in gaps. Species of gap makers affected the sapling composition indirectly by influencing gap size. The existence of parent trees around gaps had effects on sapling densities of several species. Gap age did not have clear influences on sapling composition. Variations in gap size and topography were considered as important factors that contribute to maintenance of species diversity in this forest.     

森林生态系统健康评估的一般性途径探讨

生态系统健康评估方法及指标体系成为21世纪生态系统健康研究的核心内容．作为陆地生态系统的重要组成部分,森林生态系统健康的评估研究引起了广泛的关注．学者们对森林生态系统健康的定义、测度、评估和管理开始做出积极的探讨和实践,提出了一些理论和应用上的评价方法、评估途径和框架,为解决陆地生态系统危机甚至全球环境问题提供了新的概念和一系列研究手段．但由于多种条件的限制,目前仍然没有通用有效的评估森林生态系统健康的一般模式．文中简要探讨了森林生态系统健康问题,提出有效评估森林健康的3个前提：1)清晰明确的概念框架;2)充分有效的数据信息;3)正确合理的研究途径和技术手段．并分别进行了探讨．在此基础上总结阐述了可用于森林生态系统健康评估研究的途径：长期研究和定位监测、时空互换、历史研究途径、经济价值评估及其途径等．     

The forest communities of Table Mountain,South Africa

Summary The forest communities of Table Mountain have been classified using the Braun-Blanquet technique together with numerical analysis. Three major communities, termed associations, have been recognised. Some of these associations have been subdivided. Each community has been described in terms of floristic, structural and environmental factors. The dominant factors affecting the distribution of forest communities appear to be moisture conditions, soil rockiness and soil depth. Information from other South-Western Cape forest areas is discussed. The forests from Table Mountain are similar to these.However, two forest communities are not found on the Cape Peninsula and extensive areas of Cassine dominated forest on deep soils referred to as the Scolopia mundii — Cassine capensis varlant do not appear to be foun outside Orange Kloof.Nomenclature follows that used in the Bolus Herbarium, University of Cape Town.The authors wish to thank the Course III Botany classes of 1974 and 1975 for assisting in collecting some of the field data, and the South African Council for Scientific and Industrial Research and Smuts Scholarship Board for some financial assistance (B. M. Campbell).     

Structure,biomass and production of a resprouted holm-oak (Quercus ilex L.) forest in NE Spain

When considered as a compartment of nutrients (biomass) and as a flux between compartments (production) vegetation plays an important role in the biogeochemical forest research that is carried out at the Prades research station in two adjacent catchments: L'Avic (51.6 ha) and La Teula (38.5 ha). The forest density at the Prades site, considering both the tree and shrub layers, is 9182 stems ha^–1, with 4527 stems ha^–1 being the tree layer. The predominant species is Quercus ilex with Arbutus unedo and Phillyrea media less common. The structure of the population, estimated by grouping the numbers of the stems in classes of 2.5 cm, shows a distribution which conforms, in both catchments, to a negative exponential equation following the Yoda law. The distribution observed at different altitudes shows great heterogeneity, the number of stems of Q. ilex increases with altitude, from 4000 stems ha^–1 at 800 m, to 14000 stems ha^–1 at 1000 m of altitude. The upper and the lower parts of the watershed show differences in forest production that explain this variation. In this paper the influence of human activities and physical factors on the origin of this structure is discussed. The tree and shrub biomass was calculated by applying allometric regressions for the three predominant species and has been estimated as 113.2 t ha^–1. The tree layer accounts for 92%. Net production was calculated from annual increases (by differences between the 1981 and 1986 basal area measures) of the woody part and the litterfall. The above-ground net production was about 6.5 t ha^–1 year^–1, 95.4% of it being from trees and shrubs and only 4.6% from grasses.     

Riparian disturbance and community structure of a Quercus-Ulmus forest in central Japan

Population structure and ecological characteristics of component species of a riparian Ulmus-Quercus forest in central Japan were analyzed with special reference to riparian disturbance regime. Though the dbh distribution of the whole community was L-shaped, those of several component tree populations had several modes, suggesting intermittent regeneration periods in the past. Correlation of spatial distributions among tree populations and subpopulations showed 6 major groups reflecting riparian disturbances in the past and different establishment patterns among species. A cluster of small-sized tree populations (Salix sachalinensis, Alnus hirsuta and Populus maximowiczii <30 cm dbh) were distributed on the lower terrace along the active river channel, while large-sized subpopulations (dbh 60 cm) of Quercus crispula and Ulumus davidiana var. japonica occurred on the higher terrace. The Phellodendron amurense population also occurred on the higher terrace in small clumps though the trees were small (less than 55 cm dbh). Subpopulations of intermediate-sized individuals (30 dbh < 60 cm) of Q. crispula and U. davidiana var. japonica, together with Betula and Acer spp. populations occurred on the intermediate terrace. Dendrochronological analyses indicated that the large and intermediate-sized tree groups were established about 330 and 90 years ago, respectively, while the small-sized tree group established about 35 years ago. A survey of historical disturbances showed that these periods of establishment of the former two groups almost coincided with the historically major floods occurring in 1662 and 1902. However, the disturbance that resulted in the establishment of the youngest group could not be precisely identified. Thus, the forest is a mosaic of three differently-aged patches, which is closely related to the frequency and scale of riparian disturbances. Longevity of trees and the preferred conditions for seed germination and/or seedling establishment were particularly important for the guild structure in this forest community.     

A sampling design strategy to reduce survey costs in forest monitoring

High-quality data and long-term time series are the basis of any research activity dealing with natural resources analysis. Adequate sampling designs are fundamental to allow a robust statistical analysis to be representative of a relevant set of target variables. In this work, the sampling strategy of ICP-Forests Level II European network has been proposed to define more efficient and cost-effective procedures under the hypothesis that the average value of single-tree growth (increment) is a proxy of forest health. ICP plots have a fixed spatial structure consisting of a square of 50 × 50 m framed into 25 squared sub-plots. To estimate basal area (G) and increase over time (ΔG), two different sub-sampling methods have been implemented based on a measure of (i) the dominant layer only (i.e. a subset of the highest trees in the plot), and (ii) a random sample of squared sub-plots. While the vertical sampling procedure was performed using a progressive threshold, the horizontal sampling followed a bootstrapping procedure with random extraction without replacement. The mean absolute relative error (MARE) was used to evaluate quality of the two sub-sampling methods. Results highlighted a low predictive power with both methodologies, preventing the possibility to reduce the sampling efforts when estimating ΔG directly. In this context, the vertical sampling was strictly related to species-specific ecology, spatial structure and forest age, being influenced by vertical distribution of trees. The use of horizontal sampling for direct ΔG estimation led to systematically high errors. However, the use of horizontal sampling for total G estimation and indirect estimation of ΔG may reveal as a more effective procedure for a coherent representation of horizontal distribution of trees. Estimate ΔG as the difference between G values at time t and t + Δt finally allows for a sensible reduction of costs with a controlled estimation error. An adequate level of MARE should be decided a-priori to select the number of sub-squares to be randomly sampled.