昆嵛山盐肤木RhuschinensisMill．群落特征及其物种多样性

根据野外典型样方调查结果,以群落植物种类组成、群落外貌特征、群落垂直结构特征、群落多样性几项指标,分析山东半岛昆嵛山国家级自然保护区盐肤木Rhuschinensis群落特征。结果表明：盐肤木群落共出现种子植物66种,隶属于32科57属。在盐肤木群落属的区系组成中,群落植物主要由温带区系和热带区系成分组成,其中温带植物属占显著优势,其次为热带分布属,说明该群落具有明显的温带性质,并具有过渡特征。群落层次分明,有乔木层、灌木层、草本层3个层次,各层次的优势种依次为盐肤木和赤松Pinusdensiflora、麻栎Quercusacutissima、披针叶苔草Carexlanceolata。盐肤木群落的物种多样性由高到低依次为灌木层、乔木层、草本层,低均匀度导致物种丰富度最高的草本层具有最低的物种多样性。调查显示盐肤木幼苗幼树多,自我更新良好,群落处于稳定增长状态。通过对群落特征和物种多样性的研究,揭示了昆嵛山盐肤木群落的自然生态规律,为保护和开发利用盐肤木提供了科学依据。     

古田山国家级自然保护区黄山松群落特征及物种多样性研究

通过对黄山松群落特征及物种多样性进行分析,结果表明,古田山自然保护区黄山松群落植物种类较丰富,科属组成分散,区系成分较复杂。从属的地理成分来看,温带分布的属多于热带分布的属。群落的生活型以高位芽植物为主,地下芽植物次之。该群落叶的性质以小型叶、单叶、草质、非全缘为主。群落垂直结构复杂,地上成层现象明显,可分为乔木层、灌木层和草本层,并有一定数量的层间植物。乔木层、灌木层和草本层的物种多样性大小依次为灌木层>乔木层>草本层。     

金沙江流域干热河谷草地群落物种数量及多样性特征

选择金沙江干流及支流小江干热河谷典型草地,采用标准样地调查法,对其上游、中游、下游以及支流干热河谷草地植物群落数量特征、物种特性、以及物种丰富度、多样性、均匀度等特征等开展研究,结果表明,①金沙江干热河谷草地植物群落密度自上游至下游显著增加（F=5.226;P≤0.01）。金沙江干流河谷内植物分布受经向的影响较大,纬向对河谷内植物群落影响较小,河谷间影响较大。草地植物群落中扭黄茅（Heteropogon contortus）种群在数量上占优势,同时扭黄茅种群密度沿着河谷走向逐渐增加,但在群落中的比例逐渐降低。②金沙江干流及支流小江东川干热河谷草地植物群落以禾本科（Gramineae）、豆科（Leguminosae）、莎草科（Cyperaceae）、菊科（Compositae）为主。③金沙江干热河谷草地植物群落丰富度分析发现,群落丰富度指数自上游至下游逐渐降低。Simpson多样性指数、Shannon-Wiener多样性指数及Peilow均匀性指数自上游至下游逐渐升高。     

重庆四面山杉木群落物种多样性研究

通过对重庆四面山杉木(Cunninghamia lanceolata)林样地的调查,运用丰富度指数、Shannon-Wiener多样性指数、Simpson多样性指数和Pielou均匀度指数,分析了该地区杉木群落物种多样性特征,将该地区现存杉木群落划分为2个群系组(杉木林和杉木针阔混交林),8个群系,10个群丛。结果表明,杉木群落可分为乔木层、灌木层和草本层。在杉木林群系组中,丰富度指数、多样性指数和均匀度指数均表现为灌木层>草本层>乔木层。在杉木针阔混交林群系组中,丰富度指数表现为灌木层>乔木层>草本层;多样性指数多数表现为灌木层>乔木层>草本层;均匀度指数变化较为复杂,没有统一规律。杉木群落各层的丰富度指数随海拔高度的升高总体上呈下降趋势。群落各层的多样性指数随海拔高度的升高在特定区间内表现出一定规律性:在海拔1180m以下低海拔区域,随海拔高度的升高呈下降趋势;在海拔1180～1351m范围内,随海拔高度的升高呈波动状态;而在海拔1351m以上高海拔区域,又呈下降趋势。群落各层的均匀度指数随海拔梯度变化较为复杂,未表现出明显规律。     

关于不同森林群落物种多样性比较的问题讨论

对一篇论文中不同森林群落物种多样性的比较研究的方法和结论作了一些讨论 ,供读者参考 .参 2     

古田山国家级自然保护区常绿阔叶林类型及其群落物种多样性研究

在群落调查的基础上，分析了古田山自然保护区常绿阔叶林的群落类型和群落物种多样性特征．结果表明：古田山自然保护区常绿阔叶林主要有6种类型(群系)，即甜槠林、栲树林、野含笑-钩栗林、青冈林、虎皮楠-甜槠林、乌冈栎-青冈林，并对各群落类型的结构和物种组成进行了描述．从各群落的外貌、结构和种类组成上看，均具有我国典型常绿阔叶林的基本特征．不同群落类型其物种多样性大小不同，栲树林和野含笑-钩栗林物种多样性较高，虎皮楠-甜槠林和乌冈栎-青冈林物种多样性较低．在群落垂直结构中，灌木层→乔木层→草本层物种多样性依次降低，乔木层与灌木层之间物种多样性差异不显著，草本层的物种丰富度、物种多样性指数均明显小于乔木层和灌木层．与邻近4个山地常绿阔叶林物种多样性相比较，古田山常绿阔叶林物种多样性比纬度位置高的黄山和大别山要大，但比纬度位置低的乌岩岭和缙云山小．     

喀斯特山地草地植物群落物种数量特征及多样性分析

选择贵州典型喀斯特山地草地植物群落为研究对象,采用标准样地调查法,对不同海拔、坡向的植物群落数量特征、物种特性、以及物种丰富度、多样性、均匀性等特征展开研究,结果表明,（1）喀斯特山地草地植物群落密度随海拔升高呈显著增加趋势（F=20.600;P≤0.01）。植物群落中矛叶荩草（Arthraxon lanceolatus）和扭黄茅（Heteropogon contortus）种群在数量上占优势,同时矛叶荩草和扭黄茅种群密度随海拔升高呈现出增加趋势;但矛叶荩草种群密度在群落中的比例呈现出下降趋势,而扭黄茅种群密度在群落中的比例呈现出升高趋势。（2）喀斯特山地草地植物群落以禾本科（Gramineae）、菊科（Compositae）、蔷薇科（Rosaceae）、唇形科（Labiatae）为主;其中禾本科植物种类比例随海拔升高呈现出下降趋势,而菊科、蔷薇科、唇形科植物种类比例呈现出升高趋势。（3）喀斯特山地草地植物群落丰富度指数随海拔升高呈现出增加趋势,Simpson多样性指数、Shannon-Wiener多样性指数随海拔升高呈现先降后升趋势,Peilow均匀性指数随海拔升高呈现下降趋势。     

昆嵛山不同植被带线蚓群落结构特征

为明确昆嵛山不同植被带线蚓分布特征及影响因子,于2011年9月对山东省昆嵛山不同植被带线蚓群落结构进行调查。共采集线蚓科环带动物351条,隶属4属10种,其中白线蚓属5种,半线蚓属2种,线蚓属2种,玛利安蚓属1种。叉肾半线蚓(Hemienchytraeus bifurcatus)、白线蚓属种5(Fridericia sp5)和滇池白线蚓(Fridericia dianchiensis)为优势种,平均密度分别为2 458、2 125和1 333条·m-2,相对丰度分别为16.5%、14.2%和8.9%。不同植被带线蚓密度和生物多样性整体表现为针阔叶混交林区最大,阔叶林区次之,针叶林区和农田区较小;其中线蚓密度均值为14 917条·m-2,Shannon-Wiener多样性指数均值为0.92,Margalef多样性指数均值为0.22,物种丰富度指数均值为4,Simpson优势度指数均值为0.52;应用非度量多维标度排序法研究群落结构相似性,发现S1和S2站位相似性较高,S5和S6站位相似性较高,S3、S4站位分别与其他站位群落结构存在较大差异。典范对应分析表明土壤水分、总氮和硝态氮含量为影响区域线蚓群落结构的主要因子。     

井冈山猴头杜鹃群落特征的研究

以井冈山猴头杜鹃（Rhododendron simiarum）群落5个样地调查资料为基础,对该群落的物种组成、区系成分、群落结构和物种多样性进行了研究,结果表明：群落有维管植物30科43属50种,其中蕨类植物有5科6属6种,裸子植物4科4属4种,被子植物21科33属40种。区系分析显示该植物区系起源古老,地理成分复杂,以热带性成分为主,温带性成分占有一定的比例。群落为复层异龄结构,猴头杜鹃、甜槠（Castanopsis eyrei）、福建柏（Fokienia hodginsii）、台湾松（Pinus taiwanensis）、薯豆（Elaeocarpus japonicus）和白豆杉（Pseudotaxus chienii）为群落的建群种。除Pielou指数外,群落物种多样性指数较低,各样地间多样性指数测值变幅较大;测度猴头杜鹃群落物种多样性时,各种多样性指数基本表现出相同的趋势;总体来看,猴头杜鹃群落物种多样性在群落不同层次的变化规律为：灌木层〉乔木层〉草本层。     

历山山核桃群落物种多样性特征

采用Patrick指数、Simpson指数、Shannon指数、Pielou指数、Alatalo指数等5个多样性指数,结合TWINSPAN分类,研究历山自然保护区山核桃(Juglans mandshurica)群落的物种多样性与群落类型、结构及环境因子的关系.结果表明:TWINSPAN分类将35个样方分为7个群丛,各群丛的物种丰富度指数、多样性指数和均匀度指数之间存在差异,各群丛乔木层、灌木层和草本层之间的丰富度指数和均匀度指数也存在差异,山核桃群落物种多样性受其所处的坡向、坡度、土壤类型等物理微环境及群落物种组成、干扰等共同影响.方差分析结果表明:各群丛间丰富度指数、多样性指数和均匀度指数差异不显著,各群丛乔木层、灌木层和草本层之间的丰富度指数和均匀度指数也差异不显著,这说明山核桃群落生境异质性小,物种对地带性气候有相似的适应特征以及相似的资源利用方式.     

火炬树叶片腐解物浸提液对上海青种苗生长的影响

用培养皿方法测定了土壤腐解对火炬树（Rhus typhina）叶片化感作用潜力的影响。试验结果表明：腐解0、5 d的火炬树叶片,在浸提液质量浓度为0.02、0.04、0.08 g.mL-1时,对上海青（Brassica chinensis）种子萌发及幼苗生长表现为抑制作用,且抑制作用强度随浸提液质量浓度增大和腐解时间延长而加强。腐解时间达10、20和30 d时,0.01、0.02 g.mL-1的浸提液对上海青种子萌发及幼苗生长表现为促进作用,0.04、0.08 g.mL-1的浸提液仍对上海青种子萌发及幼苗生长表现为抑制作用,且促进作用随腐解时间延长而加强,抑制作用均随腐解时间延长而减弱。     

Fuel breaks affect nonnative species abundance in Californian plant communities.

We evaluated the abundance of nonnative plants on fuel breaks and in adjacent untreated areas to determine if fuel treatments promote the invasion of nonnative plant species. Understanding the relationship between fuel treatments and nonnative plants is becoming increasingly important as federal and state agencies are currently implementing large fuel treatment programs throughout the United States to reduce the threat of wildland fire. Our study included 24 fuel breaks located across the State of California. We found that nonnative plant abundance was over 200% higher on fuel breaks than in adjacent wildland areas. Relative nonnative cover was greater on fuel breaks constructed by bulldozers (28%) than on fuel breaks constructed by other methods (7%). Canopy cover, litter cover, and duff depth also were significantly lower on fuel breaks constructed by bulldozers, and these fuel breaks had significantly more exposed bare ground than other types of fuel breaks. There was a significant decline in relative nonnative cover with increasing distance from the fuel break, particularly in areas that had experienced more numerous fires during the past 50 years, and in areas that had been grazed. These data suggest that fuel breaks could provide establishment sites for nonnative plants, and that nonnatives may invade surrounding areas, especially after disturbances such as fire or grazing. Fuel break construction and maintenance methods that leave some overstory canopy and minimize exposure of bare ground may be less likely to promote nonnative plants.     

Incentivizing biodiversity conservation in artisanal fishing communities through territorial user rights and business model innovation

Territorial user rights for fisheries are being promoted to enhance the sustainability of small‐scale fisheries. Using Chile as a case study, we designed a market‐based program aimed at improving fishers’ livelihoods while incentivizing the establishment and enforcement of no‐take areas within areas managed with territorial user right regimes. Building on explicit enabling conditions (i.e., high levels of governance, participation, and empowerment), we used a place‐based, human‐centered approach to design a program that will have the necessary support and buy‐in from local fishers to result in landscape‐scale biodiversity benefits. Transactional infrastructure must be complex enough to capture the biodiversity benefits being created, but simple enough so that the program can be scaled up and is attractive to potential financiers. Biodiversity benefits created must be commoditized, and desired behavioral changes must be verified within a transactional context. Demand must be generated for fisher‐created biodiversity benefits in order to attract financing and to scale the market model. Important design decisions around these 3 components—supply, transactional infrastructure, and demand—must be made based on local social‐ecological conditions. Our market model, which is being piloted in Chile, is a flexible foundation on which to base scalable opportunities to operationalize a scheme that incentivizes local, verifiable biodiversity benefits via conservation behaviors by fishers that could likely result in significant marine conservation gains and novel cross‐sector alliances. Incentivar la Conservación de la Biodiversidad con Comunidades de Pesca Artesanal por medio de Derechos de Uso Territorial y la Innovación de Modelos de Negocio     

Alarming decline of freshwater trigger species in western Mediterranean key biodiversity areas

Theidentification of key biodiversity areas (KBA) was initiated by the International Union for Conservation of Nature in 2004 to overcome taxonomic biases in the selection of important areas for conservation, including freshwater ecosystems. Since then, several KBAs have been identified mainly based on the presence of trigger species (i.e., species that trigger either the vulnerability and or the irreplaceability criterion and thus identify a site as a KBA). However, to our knowledge, many of these KBAs have not been validated. Therefore, classical surveys of the taxa used to identify freshwater KBAs (fishes, molluscs, odonates, and aquatic plants) were conducted in Douro (Iberian Peninsula) and Sebou (Morocco) River basins in the Mediterranean Biodiversity Hotspot. Environmental DNA analyses were undertaken in the Moroccan KBAs. There was a mismatch between the supposed and actual presence of trigger species. None of the trigger species were found in 43% and 50% of all KBAs surveyed in the Douro and Sebou basins, respectively. Shortcomings of freshwater KBA identification relate to flawed or lack of distribution data for trigger species. This situation results from a misleading initial identification of KBAs based on poor (or even inaccurate) ecological information or due to increased human disturbance between initial KBA identification and the present. To improve identification of future freshwater KBAs, we suggest selecting trigger species with a more conservative approach; use of local expert knowledge and digital data (to assess habitat quality, species distribution, and potential threats); consideration of the subcatchment when delineating KBAs boundaries; thoughtful consideration of terrestrial special areas for conservation limits; and periodic field validation.     

Restoration of ecosystems for biodiversity and carbon sequestration: Simulating growth dynamics of brigalow vegetation communities in Australia

Restoration of abandoned and degraded ecosystems through enhanced management of mature remnant patches and naturally regenerating (regrowth) forests is currently being used in the recovery of ecosystems for biodiversity protection and carbon sequestration. Knowledge of long-term dynamics of these ecosystems is often very limited. Vegetation models that examine long-term forest growth and succession of uneven aged, mixed-species forest ecosystems are integral to the planning and assessment of the recovery process of biodiversity values and biomass accumulation. This paper examined the use of the Ecosystem Dynamics Simulator (EDS) in projecting growth dynamics of mature remnant brigalow forest communities and recovery process of regrowth brigalow thickets. We used data from 188 long-term monitored plots of remnant and regrowth forests measured between 1963 and 2010. In this study the model was parameterised for 34 tree and shrub species and tested with independent long-term measurements. The model closely approximated actual development trajectories of mature forests and regrowth thickets but some inaccuracies in estimating regeneration through asexual reproduction and mortality were noted as reflected in stem density projections of remnant plots that had a mean of absolute relative bias of 46.2 (±12.4)%. Changes in species composition in remnant forests were projected with a 10% error. Basal area values observed in all remnant plots ranged from 6 to 29 m² ha⁻¹ and EDS projections between 1966 and 2005 (39 years) were 68.2 (±10.9)% of the observed basal area. Projected live aboveground biomass of remnant plots had a mean of 93.5 (±5.9) t ha⁻¹ compared to a mean of 91.3 (±8.0) t ha⁻¹ observed in the plots. In regrowth thicket, the model produced satisfactory projections of tree density (91%), basal area (89%), height (87%) and aboveground biomass (84%) compared to the observed attributes. Basal area and biomass accumulation in 45-year-old regrowth plots was approximately similar to that in remnant forests but recovery of woody understorey was very slow. The model projected that it would take 95 years for the regrowth to thin down to similar densities observed in original or remnant brigalow forests. These results indicated that EDS can produce relatively accurate projections of growth dynamics of brigalow regrowth forests necessary for informing restoration planning and projecting biomass accumulation.     

长白山区公路对路域植物物种组成及多样性的影响

采用样线法对长白山区公路旁天然次生林和原始阔叶林的植物物种组成及多样性进行调查。分别选取具有代表性的两个试验点,在公路两侧且其垂直走向布设3条相互平行的样线,间隔5m。在样线上布设样点,调查的生态因子包括光强、温度及湿度;样方调查分为灌木和草本样方,分别记录种类、高度、盖度、株数。根据公路两侧生态因子、灌草植物组成及多样性变化情况,分析公路建设的生态影响。结果表明：（1）随着离公路距离的增加,光照、温度、湿度等环境因子呈现规律性变化,距离公路10m的位置是生态因子变化从剧烈到缓和的转折点;（2）公路建设对植物组成产生影响,随着离公路距离的增加,呈现从喜光植物到耐阴植物的变化,0～20m之间是优势种变化较剧烈的范围,而10m之内和20m之外样方之间优势种变化不大;（3）受路域环境因子改变的影响,公路建设对沿线植物的多样性影响包括正负两种,既增加了路域植物的多样性,同时也破坏了原生植被群落的稳定性;（4）从长白山区公路对草本、灌木植物组成及生物多样性影响的范围和程度来看,草本的影响范围超过20m,灌木的影响范围达到10m,影响范围：草本灌木。随着与公路距离的增加,公路对植物组成及多样性的影响程度降低。     

Trade-offs, temporal variation, and species coexistence in communities with intraguild predation

Intraguild predation/parasitism (IGP: competing species preying on or parasitizing each other) is widespread in nature, but the mechanisms by which intraguild prey and predators coexist remain elusive. Theory predicts that a trade-off between resource competition and IGP should allow local niche partitioning, but such trade-offs are expressed only at intermediate resource productivity and cannot explain observations of stable coexistence at high productivity. Coexistence must therefore involve additional mechanisms beside the trade-off, but very little is known about the operation of such mechanisms in nature. Here I present the first experimental test of multiple coexistence mechanisms in a natural community exhibiting IGP. The results suggest that, when resource productivity constrains the competition-IGP trade-off, a temporal refuge for the intraguild prey can not only promote coexistence, but also change species abundances to a pattern qualitatively different from that expected based on the trade-off or a refuge alone. This is the first empirical study to demonstrate a mechanism for why communities with IGP do not lose species diversity in highly productive environments. These results have implications for diversity maintenance in multi-trophic communities, and the use of multiple natural enemies in biological control.