海南岛热带山地雨林林分生物量估测方法比较分析

本文通过对海南岛热带山地雨林林分生物量估测方法的比较分析,表明材积转换法不适宜估算海南岛热带山地雨林林分生物量,其结果与皆伐法相比较一般偏高20％—40％;而用实测资料建立的生物量回归模型,对原始林林分有较好的估测结果,除树枝和树叶生物量外,树干、树皮及地上部分生物量的回归模型值,与皆伐法的结果比较,相对误差一般在±10％以内,为允许误差范围,而对热带山地雨林的更新林生物量的估测则效果较差,应建立相应的估测模型。平均木法有工作量小的优点,且误差也在16％以下,但要注意取样的树种多样性和取样强度,在实际中应当慎用。另外本文对测定热带山地雨林生物量(原始林)的所需面积大小问题作了研究,提出了生物量-面积曲线的概念,确定其最小调查面积为2500m~2以上。     

海南岛霸王岭热带山地雨林群落结构及树种多样性特征的研究

 以海南岛霸王岭自然保护区1 hm2老龄原始林样地的调查材料为基础,分析了热带山地雨林群落的组成、高度结构、径级结构及有关的树种多样性特征。结果表明：霸王岭热带山地雨林树种较丰富,物种多样性指数较高。树种数和树木的密度都随高度级、径级的增加而呈负指数或负幂函数递减;热带山地雨林不同高度级、不同径级和不同小样方斑块内的树种数都与树木密度呈显著的正相关关系。热带山地雨林经过自然的演替达到老龄顶极群落后,最后进入主林层的只是少部分树种的少数个体。     

茂兰喀斯特森林林隙的植物多样性与更新

喀斯特森林是一类特殊的森林生态系统,蕴藏着丰富的生物多样性。以贵州茂兰喀斯特森林为研究对象,比较分析了林隙和非林隙林分中主要树种的数量特征以及不同发育阶段林隙物种多样性和生活型构成的变化规律。结果如下：（1）林隙中的树种组成主要有云贵鹅耳枥(Carpinus pubescens)、圆叶乌桕(Sapium rotundifolium)、圆果化香(Platycarya longipes)、黄连木(Pistacia chinensis)、朴树(Celtis sinensis)等。非林隙林分中的树种组成主要有青冈(Quercus glauca)、翅荚香槐(Cladrastis platycarpa)、轮叶木姜子(Litsea verticillata)、椤木石楠(Photinia davidsoniae)、狭叶润楠(Machilus rehderi)等。依照它们在林隙内外重要值的差异可将其划分为3种类型：一是对林隙更新反应不显著的物种,一般选择在林下更新,多数常绿大乔木树种属于此类型;二是对林隙有显著的正更新反应的物种,一般需依靠林隙繁殖更新,多数落叶大乔木和灌木树种属于此类型;三是对林隙反应不敏感的物种,在林隙和林下均能更新,多数林下小乔木种类属于此类型。（2）林隙各阶段物种多样性的顺序为：中期林隙（15-30年）>早期林隙（小于15年）>晚期林隙（30年以上）>非林隙,其中中期林隙阶段是物种多样性维持的重要时期。（3）早期林隙阶段常绿树种的物种数少于落叶树种;中期林隙阶段两类树种的丰富度都有大幅度增加,但落叶树种比常绿树种增幅更大;晚期林隙阶段常绿树种继续增多,而落叶树种则有明显下降趋势。（4）早期和中期林隙阶段,以灌木种类占优势,乔木所占比例介于灌木和草本之间;晚期林隙阶段,灌木种类迅速减少,而乔木的比例则增加。随着林隙的发育, 草本植物减少,而藤本植物则增加。研究结果进一步表明,林隙的存在提高了茂兰喀斯特森林的物种多样性,随着林隙的发育,群落结构趋于稳定。     

蛟河阔叶红松林林冠干扰及林隙更新研究

研究了吉林蛟河实验林场阔叶红松林的林冠干扰状况及林隙更新的基本规律。结果表明,扩展林隙（ＥＧ）和冠空隙（ＣＧ）在阔叶红松林中所占的面积比例分别是１８．０９％和１２．５１％,林冠干扰的返回间隔期为７００ａ左右;ＣＧ的大小平均为ＥＧ的６９％,ＥＧ的面积变化在１７—２８４ｍ２之间,平均为７５．４９ｍ２,而ＣＧ的面积变化在１０—２３４ｍ２之间,平均为５１．９８ｍ２,大多数林隙的平均直径仅为主林层树高的２０—６０％;大多数的林隙是由单株形成木形成的,形成林隙最重的方式是干基折断和掘根风倒;林隙形成木主要是由红松、沙松、枫桦和鱼鳞松四个树种组成,林隙形成木的胸径大都在４０—８０ｃｍ之间,树高在２５—３０ｍ之间;林隙的空间分布格局是均匀型的。不同树种在林隙内外的数量特征不同,随着林隙与非林隙的交替变化,不同树种的优势地位亦发生相应的变化,根据不同树种在林隙内外重要值位序差值的大小,可将蛟河阔叶红松林内树种对林隙的更新反应划分为三种类型。林隙及非林隙林分的物种多样性特征不同     

海南岛霸王岭垂直带热带植被物多样性的空间分析

以常用的Shannon-Wiener指数,Simpson指数以及新近提出的两个非参数指数（Chao多样性指数和二阶刀切法多样性指数）,计测了海南岛霸王岭垂直止不同植被类型（包括热带低山雨林、热带山地雨林、热带云雾林、热带山地矮林）的物种多样性。在此基础上,借助地理信息系统的空间分析技术,模拟绘制了整经度的多样性变化谱。总体而言,样带下部的物种多样性高于上部,或者说热带低山雨林与热带山地雨林的物种多样性高于热带云雾林与热带山地矮林,而南部稍高于北部。这种基于插值方法的空间分析技术为探索植被结构分析提供了一条新的途径。     

长白山自然保护区阔叶红松林林隙更新的研究

通过对林隙及非林隙林分组成树种数量特征的对比分析,研究了长白山自然保护区阔叶红松林中主要树种对林隙的更新反应特点,阐述了林隙在阔叶红松林结构与多样性维持中的作用．随着林隙与非林隙的交替变化,红松和阔叶树以及主林层和中下层树种的相对优势（或重要性）亦呈现出交替变化的规律．林隙提高了阔叶红松林的物种丰富度,增加了其多样性,为不同特性物种的共存提供了可能,从而保持了阔叶红松林的整体稳定性．     

海南霸王岭热带山地雨林森林循环与树种多样性动态

通过对海南岛霸王岭热带山地雨林的调查 ,研究了热带山地雨林树种多样性特征随森林循环的动态变化规律。结果表明 :( 1 )热带山地雨林森林循环不同阶段斑块在森林景观中所占的面积比例分别是 :林隙阶段 ( G)占 38.5 0 % ,建立阶段 ( B)占 2 8.5 0 % ,成熟阶段 ( M)占 2 7.0 0 % ,衰退阶段 ( D)占 6 .0 0 %。 ( 2 )热带山地雨林中乔木树种的密度随森林循环的变化趋势是由 G→B→M呈现出逐渐增加的趋势 ,以成熟阶段达到最大 ,而到衰退阶段又趋于下降。灌木树种则表现出 G阶段斑块的密度最大 ,B阶段的最小 ,从 B到 M有所增加 ,到 D又稍有下降。 ( 3)热带山地雨林中不同高度级和不同径级的树木的密度在森林循环的不同阶段表现出不同的增减趋势 ,其随森林循环过程呈现出的动态变化可能与不同阶段斑块内的空间、环境及物种生物学特性有关。 ( 4 )热带山地雨林中树木的平均胸径、平均高、平均胸高断面积、平均单株材积随森林循环过程呈现出不断增加的趋势 ,其中平均胸径和平均高随森林循环的变化较为平缓 ,而平均胸高断面积和平均单株材积之变化较为陡急。 ( 5 )热带山地雨林森林循环不同阶段的物种多样性指数不同 ,其中 G和 B阶段的物种丰富度和多样性指数值较接近 ,M阶段的物种丰富度达到最大 ,D阶段则最小。     

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.     

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.     

西藏冷杉原始林林隙对草本植物和灌木树种多样性的影响

研究了西藏东南部亚高山原始冷杉林林隙对草本植物和灌木树种多样性的影响．结果表明,西藏东南部亚高山原始冷杉林林隙与非林隙林分内草本植物和灌木树种的种类组成、数量、密度和物种多样性均存在较大的差异．由于林隙内光照条件的改善,草本植物和灌木树种更加丰富;林隙内有喜光的草本植物和灌木,也有耐荫性较强的草本植物和灌木,而非林隙林分内仅有耐荫和较耐荫的草本植物和灌木;大部分林隙内的草本植物和灌木树种的物种多样性和均匀度大于非林隙林分;林隙内与非林隙林分的群落相似系数较小,表明林隙与非林隙林分草本植物和灌木群落组成存在差异．林隙大小在174．2～562．2m^2之间,群落相似系数与林隙大小无明显关联．林隙促进了草本植物和灌木树种的繁衍,在维持藏东南亚高山原始冷杉林的物种多样性方面起着重要作用．     

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。     

Study on canopy disturbance regime and mechanism of tree species diversity maintenance in the lower subtropical evergreen broad-leaved forest,South China

ABSTRACT

The canopy disturbance, the gap environment, gap regeneration and maintenance of tree species diversity in the lower subtropical evergreen broad-leaved forest (LSEBF) of South China were studied in this paper. The most common manner of gap formation in the forest was by stem breakage. Most gaps were formed by two gap makers. The sizes of most expanded gaps (EG) and canopy gaps (CG) were in the range of 100 – 300 m² and 50 – 100 m², respectively. The ecological factors in gaps were analysed on the basis of contrasting measurement of the microclimatic regimes in gaps of different sizes and in non-gap stands. Tree species in the LSEBF were classified into 5 ecological species groups on the bases of their changes in order of importance values in gaps and in non-gap stands. Most of the species reached their peak of regeneration density around the gap sizes of 100 m² and 500 m². The curves of regeneration density vs. gap age for major species revealed two types. Regeneration densities of most species, and species diversity indices in gaps were greater than those in non-gap stands.     

Gap characteristics and gap regeneration in subalpine old-growth coniferous forests,central Japan

Gap characteristics and gap regeneration were studied in three old-growth stands of subalpine coniferous forests in the northern Yatsugatake and the northern Akaishi mountains, central Japan. With the results of the present study and those of a previous study conducted in another locality, general features of gap characteristics and gap regeneration behavior of major tree species in subalpine coniferous forests of central Japan were summarized and discussed. Of the total 237 gaps investigated in the 14.48 ha of forested area, the percentage gap area to surveyed area, gap density and mean gap size were 7.3%, 17.2 ha⁻¹, and 43.3 m², respectively. The gap size distributions were similar among stands and showed a strong positive skewness with a few large and many small gaps; gaps <40m² were most frequent and those >200 m² were rare. Gaps due to the death of multiple canopy trees comprised 44.7% of the total ones. Canopy trees died in various states; standing dead (42.6%) or trunk broken (43.7%) were common and uprooted (12.2%) was an uncommon type of death of canopy trees. These figures indicate that general features of gap characteristics in this forest type are the low proportion of gap area and the high proportions of small gap size and multiple-tree gap formation. In general, shade-tolerantAbies frequently, andTsuga, infrequently, regenerate in gaps from advance regenerations recruited before gap formation, whilePicea and shade-intolerantBetula possibly regenerate in gaps from new individuals recruited after gap formation. Gap successors of conifers occurred in a wide range of gap size and did not show the clear preference to species specific gap size. In old-growth stands without large-scale disturbance (≥0.1 ha in area) of subalpine coniferous forests of central Japan, major tree species may coexist with their different gap-regeneration behaviors and, probably, different life history traits.     

Evaluation of secondary dispersal in a large-seeded tree Aesculus turbinata: a test of directed dispersal

Gap characteristics and gap phase replacement of major tree species were examined in two primary old-growth (mean DBHs of the canopy trees were 45.2 and 56.1 cm) and four secondary developing (range of mean DBH of the canopy trees was 23.5–39.9 cm) beech (Fagus crenata) stands in the Daisen Forest Reserve, southwestern Japan, and these were analyzed in relation to stand development as expressed by the difference of mean DBH of canopy trees. Percentage gap area (percentage of total gap area to total surveyed area) and mean and maximum gap size varied widely and ranged from 1.7 to 20.0%, from 19.4 to 162.8 m2, and from 35.7 to 585.1 m2, respectively. Mean percentage gap area and mean gap size were significantly greater in old-growth than in developing stands. However, they and maximum gap size might not increase linearly with stand development, and the gap feature of less developed stands was greater than that of later stages in developing stands. The cause was a higher formation rate, in younger developing stands, of gaps formed by simultaneous death (multiple trees falling down in domino fashion) which tends to produce larger gaps. In developing stands mean DBH of gapmakers (canopy trees that formed a gap) was smaller than that of canopy trees, though the inverse trend might be found in old-growth stands. Three typical types of death or injury states of gapmakers such as standing dead, trunk broken and uprooted were found in every study stand and the difference in stand development may not cause stand-to-stand variations for them. Importance of F. crenata (the most dominant species) in the canopy layer increased and its importance in the understory layer decreased with stand development. Shade-intolerant Quercus mongolica in the canopy layer was more important in younger than in old-growth stands, and there was no Quercus regeneration in old-growth stands. Acer mono consistently appeared, though in much less abundance than other species, in both canopy and understory layers of all study stands. Sub-canopy layers, which are mainly formed by sub-canopy tree species such as Acanthopanax sciadophylloides and Acer japonicum, may gradually develop with stand development.p>     

Spatial and temporal patterns of rowan (<Emphasis Type="Italic">Sorbus aucuparia</Emphasis> L.) regeneration in West Carpathian subalpine spruce forest

Non-random seed shadows are commonly seen in plant species whose seeds are dispersed by animals, in particular by birds. The behaviour of birds can influence the spatial pattern of seed dispersal and, consequently, the entire regeneration process of fleshy-fruited trees. This study examined regeneration patterns in a fleshy-fruited tree species, rowan (Sorbus aucuparia L.), growing in West Carpathian subalpine spruce forests, focussing on two problems: the temporal relationship between rowan regeneration and gap formation, and the spatial relationship between rowan regeneration and stand structure. It was found that rowan seedlings and saplings were recruited in advance of gap formation. Establishment of new rowan individuals in gaps was infrequent, but gaps enhanced their regeneration nearby under spruce canopy, where they occurred densely in a narrow belt about 15 m wide. Inside spruce stands, the highest density of young rowans was directly under crowns, especially near trunk bases. Few rowan saplings were found growing under mature rowan trees. The presence of a rowan seedling and sapling bank determines whether rowans fill spruce stand gaps. Dense rowan groves can develop mainly in extensive but slowly expanding gaps.     

山西霍山灌丛空隙草本植物物种多样性与更新

采用物种重要值和物种多样性指数,分析了山西霍山灌丛空隙内主要草本组成及其多样性随灌丛空隙面积梯度的变化规律。结果表明:在自然状况下形成的10 m2的灌丛空隙最多,占51.2%。灌丛空隙内草本植物的重要值高于灌丛下草本,且以10~20 m2的空隙为最高。主要草本可分为3类:(1)对灌丛空隙更新反应不明显的草本,(2)对灌丛空隙有正更新反应的草本,(3)对灌丛空隙有负更新反应的草本。灌丛空隙内的物种丰富度、多样性指数和均匀度指数均高于灌丛下,而生态优势度均小于灌丛下,呈现"单峰型"的变化趋势,且在10~20 m2达到峰值。因此,适宜大小的灌丛空隙是森林生态系统草本层植物多样性维持的重要途径。     

卧龙自然保护区林隙干扰特征

 林隙干扰对森林的结构和多样性的维持具有重要意义。对五一棚周围林隙干扰格局和林隙特征进行了3条样线调查,样线总长度为4.4 km。结果表明：1)本区以小型林隙干扰为主,林隙平均密度为12.5个•km-1,林隙的分布格局在阳坡和山脊为集聚分布,阴坡近均匀分布;林隙形成木以针叶树为主,岷江冷杉(Abies faxoniana)、铁杉(Tsuga chinensis)和糙皮桦(Betula utilis)在形成木的数量和径级组成上均居前列。2)林隙形成木的腐烂等级分布揭示出林隙形成木的形成方式和种类组成均随时间变化。表现为针叶树组形成木对林隙的贡献随时间降低,阔叶树组反之;砍伐和倒木是早期林隙形成的主要方式,而枯立和折干是近期林隙形成的主要方式。3)林隙木形成方式关联度分析结果为砍伐与倒木、折干与倒木之间存在显著负关联,林隙其它各形成方式之间的关联不显著,但砍伐与其它形成方式的负联结系数均较高。     

长白山红松阔叶混交林林冠空隙树种更新动态规律的研究

分析了长白山红松阔叶混交林林冠空隙(Gap)内更新树种的数量特征.结果表明, 在34个林冠空隙中, 更新乔木树种出现频度为7.27%, 更新灌木树种出现频度为21.02%, Gap形成后, 阳性先锋树种首先侵入, 出现频度较高, 占据较宽的生态位, 随着Gap年龄的增加, 树种间的竞争逐渐增大, 阳性树种的生长逐渐受到限制, 阴性树种逐渐增多;Gap年龄与Gap郁闭度和Gap面积呈负相关, Gap面积与树种出现频度呈负相关;Gap年龄主要分布在5～15a和46～55a两段期间, 树种出现频度与Gap年龄存在着密切关系, 当Gap年龄小于25a时, 二者呈正相关;当Gap年龄在25～40a时, 二者呈负相关;当Gap年龄大于40a时, 树种出现频度趋于稳定;34个Gap内4种主要乔木更新树种和4种主要灌木更新树种的胸径均基本上呈正态分布, 乔木更新树种的最高点胸径为4～6cm径级, 灌木更新树种的最高点胸径为1.2cm径级.     

Gap characteristics and gap regeneration in a subalpine coniferous forest on Mt Ontake,central Honshu,Japan

Gap characteristics and gap regeneration were studied in three mature stands belonging to different community types in a subalpine coniferous forest on Mt Ontake, central Honshu, Japan. Gap disturbance regimes were remarkably similar among stands studied; percentage gap area to surveyed area, gap density and mean gap size were 7.3–8.5%, 17.8–20.0 ha⁻¹ and 40.8–42.5 m², respectively. The gap size class distributions were also similar and showed a strong positive skewness with a few large and many small gaps; gaps <40m² were most frequent and gaps >200m² were rare. Forty-five to 66% of gaps were due to the death of single canopy trees. Canopy trees more often died leaving standing dead wood (40–5.7%) or broken trunks (43–49%). Shade tolerantAbies mariesii andAbies veitchii, frequently, andTsuga diversifolia, less frequently, regenerated in gaps, from advance regenerations recruited before gap formation.Picea jezoensis var.hondoensis may regenerate in gaps, from new individuals recruited after gap formation. The breakage of denseSasa coverage and the mineral soils exposed by the uprooted plants that form gaps might provide regeneration opportunities for shade intolerantBetula. Of the important species limited to the ridge site,Chamaecyparis obtusa, frequently, andThuja standishii, infrequently, regenerated from plants alreadyin situ. Regeneration ofPinus parviflora was not seen. Based on the gap characteristics and gap regeneration behaviour of each species described, stand dynamics in each stand are discussed.