鱼类群落多样性研究的理论与方法

我国水域面积巨大,生物多样性居世界第三。然而因水体污染、水生植被破坏、湖泊围垦、江湖阻隔、过度捕捞等因素影响,目前我国许多水体的鱼类群落多样性不断下降,水生生态系统功能逐渐退化。通过鱼类群落多样性的相关研究,可在群落水平上反映水域生态系统结构与功能对生态环境变化的响应。为此,综述了鱼类群落研究中水下观察、蹦网、罩网、刺网、电捕、拖网、围网、定置张网等各种采样方法的特点,测度鱼类群落多样性的各种指数类型,距岸距离、水生植物、水深、底质、溶氧、温度、盐度等环境因子对鱼类群落多样性的影响,以及鱼类群落多样性与生态系统功能间的关系,旨在为鱼类群落多样性的研究提供理论参考,推动渔业生产与环境保护的协调发展。     

海州湾鱼类群落功能多样性的时空变化

功能多样性是联系物种、生态环境和生态系统功能的基础.从功能多样性的角度研究群落结构,有助于更好地理解生物多样性与生态系统功能之间的关系.本研究根据2011—2017年(除2012年外)春、秋季海州湾渔业资源底拖网调查数据,选取反映鱼类摄食、运动、生态适应性、繁殖行为和种群动态特征的13个功能性状,利用功能丰富度指数、功能均匀度指数、功能离散度指数和群落特征加权平均数指数(CWM),研究了海州湾鱼类群落功能多样性的季节、年际和空间的变化.结果表明: 海州湾鱼类群落功能多样性指数具有显著的季节差异,其中秋季功能丰富度指数显著高于春季,春季功能离散度指数显著高于秋季,鱼类洄游是造成功能多样性指数季节变化的主要原因;CWM分析表明,春季鱼类群落优势种为营养级较高、运动能力较强、生长系数、恢复力和脆弱性较高的冷/暖温性鱼类,秋季则相反,春、秋季鱼类群落均以产浮性卵鱼类为主;鱼类群落功能多样性指数呈现一定的年际变化,其中春、秋季各功能多样性指数在不同年际均呈波动趋势,表明海州湾鱼类群落稳定性较低;鱼类群落功能多样性指数呈现显著的空间差异,其中20 m以深远岸水域功能离散度指数较高.海州湾鱼类群落功能多样性具有明显的时空变化特征,鱼类生态位与其对资源的利用均随季节、年际和空间而变化.     

开垦对阿拉善荒漠啮齿动物群落功能多样性的影响

开垦会导致荒漠化的加剧,并对动物群落产生严重的影响。而功能多样性恰恰能体现环境或干扰胁迫导致的群落结构差异。但有关啮齿动物群落功能多样性的研究并不多见,为此,我们在2018至2020年的4月、7月和10月利用铗日法对开垦区和未开垦区的啮齿动物群落进行调查,选择并量化了与其营养、生活史、生理、形态及活动节律等相关的5个功能性状,以探讨开垦对啮齿动物群落组成的影响,以及性状组成和功能多样性变化。研究结果表明：(1)开垦区群落的丰富度指数、多样性指数和均匀度指数均低于未开垦区,开垦改变了啮齿动物群落性状组成;(2)阿拉善荒漠啮齿动物群落组成与蛰眠、繁殖周期和食性等功能性状显著相关;(3)开垦区春、秋季群落功能丰富度和功能均匀度高于未开垦区,各季节群落功能离散度显著高于未开垦区;而未开垦区夏季群落功能丰富度高于开垦区,秋季群落功能均匀度高于开垦区;(4)开垦区和未开垦区群落功能丰富度最高值均出现在夏季,二者在不同季节间差异较大;开垦区群落功能均匀度最高值出现在春季、功能离散度最高值出现在秋季,二者在季节间差异均较小;未开垦群落功能均匀度最高值出现在秋季、功能离散度最高值出现在夏季,二者在季节间差异均较大。上述结果说明,阿拉善荒漠区啮齿动物群落功能多样性变化与土地开垦和季节相关联,开垦会从啮齿动物群落的生态空间利用程度、资源利用、种间竞争及生态位等方面影响群落功能多样性。     

长江安庆新洲水域鱼类群落结构及多样性

沙洲水域环境良好,饵料资源丰富,栖息生境多样,为鱼类的生长繁殖提供了优良的生存环境。为了解长江安庆新洲水域鱼类群落结构特征,于2017年4月、7月、10月和12月对安庆江段新洲水域鱼类群落进行季节性调查。共采集鱼类64种,分属5目11科48属,其中62.5%为鲤科鱼类。以物种数和多样性指数分析群落多样性特征,结果表明新洲水域鱼类种类多样性水平较高。单因素方差分析表明,该群落多样性季节差异显著(P0.05),空间差异不明显。新洲水域鱼类群落优势种为鳊(Parabramis pekinensis Basilewsky, 1855)、鲤(Cyprinus carpio Linnaeus, 1758)、贝氏■(Hemiculter bleekeri Warpachowsky, 1887)、银鮈(Squalidus argentatus Sauvage et Dabry, 1874)和似鳊(Pseudobrama simoni Bleeker, 1864)。4种摄食功能群中,杂食性(42.19%)和肉食性(35.94%)鱼类物种数比例较高;3种生态类群中,淡水定居性鱼类占绝对优势(84.37%);3种栖息水层类型中,底层鱼类物种数比例较高,占37.50%。大型经济鱼类占总渔获物比例低(0.01%),但个体较大,因而相对重要性指数(IRI)高。总体上,新洲鱼类群落多样性和丰富度指数较高,均匀度指数偏低,个体小型化趋势明显。捕捞强度过大、水利工程建设导致的江湖阻隔及外来物种入侵是新洲水域渔业资源衰退的主要因素。由此,建议持续开展长江渔业资源监测,加强长江干流沙洲水域渔业资源保护。     

淡水鱼类功能生态学研究进展

在全球变化和人类活动的影响下,生物多样性正以前所未有的速度丧失,全球生物正经受第六次生物多样性危机。淡水生态系统是最脆弱的生态系统之一。淡水鱼类作为淡水生态系统的重要组成部分,承受着日趋严重的气候变化、栖息地退化、生物入侵和过度捕捞等压力,面临巨大的威胁。在此背景下,如何准确评估鱼类种群和群落对环境变化的响应,以及鱼类群落结构和功能的变化对生态系统功能的影响是淡水鱼类多样性和淡水生态系统保护的关键问题。近年来,淡水鱼类功能生态学的快速发展为解答这一问题提供了一个框架。系统地介绍了淡水鱼类功能生态学主要研究内容、方法、进展及其应用,并着重介绍了淡水鱼类功能特征及其与环境的关系、环境变化下的功能生态学响应研究。据此提出了淡水鱼类功能生态学未来的重点研究方向,指出了其在鱼类多样性保护和资源利用等领域的应用前景。     

种间互作网络的结构、生态系统功能及稳定性机制研究

生态群落中不同物种间发生多样化的相互作用, 形成了复杂的种间互作网络。复杂生态网络的结构如何影响群落的生态系统功能及稳定性是群落生态学的核心问题之一。种间互作直接影响到物质和能量在生态系统不同组分之间的流动和循环以及群落构建过程, 使得网络结构与生态系统功能和群落稳定性密切相关。在群落及生态系统水平上开展种间互作网络研究将为群落的构建机制、生物多样性维持、生态系统稳定性、物种协同进化和性状分化等领域提供新的视野。当前生物多样性及生态系统功能受到全球变化的极大影响, 研究种间互作网络的拓扑结构、构建机制、稳定性和生态功能也可为生物多样性的保护和管理提供依据。该文从网络结构、构建机制、网络结构和稳定性关系、种间互作对生态系统功能的影响等4个方面综述当前种间网络研究进展, 并提出在今后的研究中利用机器学习和多层网络等来探究环境变化对种间互作网络结构和功能的影响, 并实现理论和实证研究的有效整合。     

鱼类多样性监测的理论方法及中国内陆 水体鱼类多样性监测

近年来, 生物多样性监测网络的建设得到广泛重视, 全球、地区或国家生物多样性观测网不断组建。生物多样性观测的理论框架得到发展, 提出了生物多样性核心监测指标(Essential Biodiversity Variables, EBV)。鱼类多样性监测的理论框架包含于生物多样性核心监测指标之内, 在遗传、物种、生态系统等多层次进行。基于鱼类监测提出的生物完整性指数(index of biotic integrity, IBI)强调不同物种的生态功能, 可以综合反映群落结构和功能的变化, 得到广泛应用。鱼类多样性的监测方法是传统网具和现代水声学等方法的结合。监测结果的分析可以进行简单的指数比较, 也可以进行长期的趋势分析, 寻找关键节点, 探讨宏观生态格局的变化。中国内陆水体鱼类多样性监测网隶属于中国生物多样性监测与研究网络, 拟选取长江、黄河、黑龙江、珠江、澜沧江、怒江、塔里木河及青海湖8大流域, 对25个重要区域和24个重点物种(类群)进行监测, 从重要区域鱼类群落结构、重点物种(类群)种群动态和个体生物学特征、遗传多样性、早期资源等不同层次, 全面监测我国内陆水体鱼类生物多样性状况。     

鄱阳湖鱼类多样性的时空变化特征研究

研究基于2010年4月、7月和2018年8月、2019年5月在鄱阳湖9个区域的鱼类多样性调查数据,分析鱼类物种多样性、功能多样性和分类差异指数的时空变化以及其与环境之间的关系,了解鄱阳湖近十年来鱼类群落多样性的时空变化特征。结果显示, 2010年和2018—2019年分别调查到鱼类74种和93种,群落结构差异显著(P<0.05),差异贡献率最高的物种为短颌鲚、似鳊、鲫、光泽黄颡鱼和鲤;水温、总悬浮物和叶绿素等环境因素具有显著的年际和季节差异(P<0.05)。与2010年相比, 2018—2019年鱼类物种多样性和功能多样性指数有一定增加,分类差异指数没有显著变化。分类差异指数的随机检验显示(Randomization test),与2010年相比, 2018—2019年位于95%概率置信范围下方的区域增加。水温、总悬浮物和叶绿素等环境因素对物种多样性、功能多样性和分类差异指数有显著的影响(P<0.05)。结果表明,近十年来,鄱阳湖鱼类群落结构发生明显改变,但是小型鱼类依旧是优势种,鱼类群落小型化明显,主要原因可能是过度捕捞的影响。同时,鄱阳湖的人类活动干扰增大,鄱阳县...     

江西柘林水库鱼类群落结构及功能多样性分析

为了解江西柘林水库鱼类群落结构和多样性的时空变化特征,研究鱼类物种多样性和功能多样性的关系,于2020年9月至2021年4月在该水库调查分析了鱼类物种组成、优势度及群落物种多样性和功能多样性。结果表明,共采集鱼类53种,分属于5目12科36属。其中,鲤形目(38种)种类最多,占调查物种数的71.69%,柘林水库上、中、下游库区分别采集到鱼类36、40和32种,各库区均以鲤形目鱼类为主,分别占采集物种数的72.97%、85.00%和75.00%。优势物种主要是■(Hemiculter leucisculus)、鳙(Aristichthys nobilis)和黄尾鲴(Xenocypris davidi),重要种主要是草鱼(Ctenopharyngodon idella)、鲢(Hypophthalmichthys molitrix)、鳊(Parabramis pekinensis)、鲫(Carassius auratus)、蒙古红鲌(Erythroculter mongolicus)等。鱼类群落结构季节性差异大于空间格局差异,主要表现为秋季和冬季之间;生物多样性指数Margalef和功能丰富...     

嘉陵江中游蓬安段鱼类群落功能多样性研究

研究调查了蓬安段2014—2019年洪水期 (6、7和8月)和枯水期 (11、12和1月)渔获物, 用11项鱼类功能性状类型结合蓬安段鱼类群落结构特点来分析该江段鱼类群落功能多样性在洪、枯期上的变化及与水环境的关系。研究结果表明, (1)2014—2019年洪水期的物种丰富度指数、辛普森多样性指数、Pielou均匀度指数和香浓威纳指数均高于枯水期; (2)SIMPER分析显示, 大鳍鳠Mystus macropterus、子陵吻鰕虎鱼Ctenogobius giurinus、似鳊Pseudobrama simoni、黄颡鱼Pelteobagrus fulvidraco、鳜Siniperca chuatsi、蛇 Saurogobio dabryi、飘鱼Pseudolaubuca sinensis、鲫Carassius auratus、黄尾鲴Xenocypris davidi和? Hemiculter leucisculus是造成洪水期与枯水期鱼类群落结构变化的主要差异贡献种; (3)各年份洪水期的功能丰富度FRic、功能离散度FDiv、功能散布度FDis和二次熵指数Rao及2015、2016和2017年的功能均匀度指数FEve均显著高于枯水期(P<0.05), 表明枯水期鱼群落的抵抗力稳定性和恢复力稳定性显著低于洪水期, 即枯水期水生生态系统功能较脆弱; (4)鱼类群落功能多样性与水环境因子存在显著相关关系, 但不同时期的功能多样性指数与环境因子相关性程度则呈现较大差异, 表明功能多样性是鱼类群落结构和各水环境因子综合作用的结果。     

生态学的多样性指数:功能与系统发育

生物多样性是生态学的核心问题。传统的多样性指数仅包含物种数和相对多度的信息,这类基于分类学的多样性指数并不能很好地帮助理解群落构建和生态系统功能。不同物种对群落构建和生态系统功能所起到的作用类型和贡献也不完全相同,且物种在生态过程中的作用和贡献往往与性状密切相关,因此功能多样性已经成为反映物种群落构建、干扰以及环境因素对群落影响的重要指标。同时,由于亲缘关系相近的物种往往具有相似的性状,系统发育多样性也可以作为功能多样性的一个替代。功能多样性和系统发育多样性各自具有优缺点,但二者均比分类多样性更能揭示群落和生态系统的构建、维持与功能。     

Climate change threats to the global functional diversity of freshwater fish

Climate change impacts on freshwater ecosystems and freshwater biodiversity show strong spatial variability, highlighting the importance of a global perspective. While previous studies on biodiversity mostly focused on species richness, functional diversity, which is a better predictor of ecosystem functioning, has received much less attention. This study aims to comprehensively assess climate change threats to the functional diversity of freshwater fish across the world, considering three complementary metrics—functional richness, evenness and divergence. We built on existing spatially explicit projections of geographical ranges for 11,425 riverine fish species as affected by changes in streamflow and water temperature extremes at four warming levels (1.5°C, 2.0°C, 3.2°C and 4.5°C). To estimate functional diversity, we considered the following four continuous, morphological and physiological traits: relative head length, relative body depth, trophic level and relative growth rate. Together, these traits cover five ecological functions. We treated missing trait values in two different ways: we either removed species with missing trait values or imputed them. Depending on the warming level, 6%–25% of the locations globally face a complete loss of functional diversity when assuming no dispersal (6%–17% when assuming maximal dispersal), with hotspots in the Amazon and Paraná River basins. The three facets of functional diversity do not always follow the same pattern. Sometimes, functional richness is not yet affected despite species loss, while functional evenness and divergence are already reducing. Other times, functional richness reduces, while functional evenness and/or divergence increase instead. The contrasting patterns of the three facets of functional diversity show their complementarity among each other and their added value compared to species richness. With increasing climate change, impacts on freshwater communities accelerate, making early mitigation critically important.     

The functional role of producer diversity in ecosystems

Over the past several decades, a rapidly expanding field of research known as biodiversity and ecosystem functioning has begun to quantify how the world's biological diversity can, as an independent variable, control ecological processes that are both essential for, and fundamental to, the functioning of ecosystems. Research in this area has often been justified on grounds that (1) loss of biological diversity ranks among the most pronounced changes to the global environment and that (2) reductions in diversity, and corresponding changes in species composition, could alter important services that ecosystems provide to humanity (e.g., food production, pest/disease control, water purification). Here we review over two decades of experiments that have examined how species richness of primary producers influences the suite of ecological processes that are controlled by plants and algae in terrestrial, marine, and freshwater ecosystems. Using formal meta-analyses, we assess the balance of evidence for eight fundamental questions and corresponding hypotheses about the functional role of producer diversity in ecosystems. These include questions about how primary producer diversity influences the efficiency of resource use and biomass production in ecosystems, how primary producer diversity influences the transfer and recycling of biomass to other trophic groups in a food web, and the number of species and spatial /temporal scales at which diversity effects are most apparent. After summarizing the balance of evidence and stating our own confidence in the conclusions, we outline several new questions that must now be addressed if this field is going to evolve into a predictive science that can help conserve and manage ecological processes in ecosystems.     

植物群落功能多样性计算方法

以性状为基础的功能多样性指数在预测生态系统功能中起到越来越重要的作用.本文对近年来陆续出现的植物群落功能多样性指数进行综述.依据物种多样性指数的组成,功能多样性指数分为功能丰富度、功能均匀度和功能离散度指数.介绍了这3类指数的计算方法,有助于更好、更准确地理解“生物多样性-环境-生态系统功能”的关系.     

Resilience and stability of a pelagic marine ecosystem

The accelerating loss of biodiversity and ecosystem services worldwide has accentuated a long-standing debate on the role of diversity in stabilizing ecological communities and has given rise to a field of research on biodiversity and ecosystem functioning (BEF). Although broad consensus has been reached regarding the positive BEF relationship, a number of important challenges remain unanswered. These primarily concern the underlying mechanisms by which diversity increases resilience and community stability, particularly the relative importance of statistical averaging and functional complementarity. Our understanding of these mechanisms relies heavily on theoretical and experimental studies, yet the degree to which theory adequately explains the dynamics and stability of natural ecosystems is largely unknown, especially in marine ecosystems. Using modelling and a unique 60-year dataset covering multiple trophic levels, we show that the pronounced multi-decadal variability of the Southern California Current System (SCCS) does not represent fundamental changes in ecosystem functioning, but a linear response to key environmental drivers channelled through bottom-up and physical control. Furthermore, we show strong temporal asynchrony between key species or functional groups within multiple trophic levels caused by opposite responses to these drivers. We argue that functional complementarity is the primary mechanism reducing community variability and promoting resilience and stability in the SCCS.     

Geographic isolation and climate govern the functional diversity of native fish communities in European drainage basins

Aim In times of biodiversity crisis, it is extremely important to understand diversity gradients. In particular, the study of the diversity of ecological functions is a key issue for the management of ecosystem integrity. Here we identify areas of low functional diversity of the native fish fauna in European drainage basins and we determine the relative importance of three underlying mechanisms: environmental filtering, geographic isolation and climatic history. Location The European continent. Methods Based on 14 morphological traits that are closely related to fish function (habitat and dietary niches), three independent functional diversity indices [functional richness (FR), functional evenness (FE), functional divergence (FD)] were calculated for 128 European drainage basins with a total of 230 fish species. The indices were standardized for species richness using null models. The patterns of the standardized indices are described and three potentially underlying mechanisms are tested using variance partitioning and multi‐linear regression models. Results FR and FD were highest in eastern European drainage basins and in Great Britain and lowest in the Mediterranean. FE patterns were less pronounced. All observed patterns were mainly governed by geographic isolation and present environmental conditions. Within the environmental conditions, average annual temperature and precipitation were good predictors for functional diversity. The role of habitat diversity and size was negligible. Main conclusions Geographic isolation coupled with harsh environmental conditions such as extreme temperatures and low precipitation, as in Mediterranean regions, can lead to low FR and FD. This can be explained by extinction that could not be compensated by re‐colonization and high speciation. Due to their high functional redundancy, communities in these areas might better withstand further species extinctions on a small scale. Over the short term, however, their often extremely low FR suggests a less flexible functioning that can hinder their ability to withstand today's rapid environmental and anthropogenic threats.     

Biodiversity acts as insurance of productivity of bacterial communities under abiotic perturbations

Anthropogenic disturbances are detrimental to the functioning and stability of natural ecosystems. Critical ecosystem processes driven by microbial communities are subjected to these disturbances. Here, we examine the stabilizing role of bacterial diversity on community biomass in the presence of abiotic perturbations such as addition of heavy metals, NaCl and warming. Bacterial communities with a diversity gradient of 1–12 species were subjected to the different treatments, and community biomass (OD₆₀₀) was measured after 24 h. We found that initial species richness and phylogenetic structure impact the biomass of communities. Under abiotic perturbations, the presence of tolerant species in community largely contributed in community biomass production. Bacterial diversity stabilized the biomass across the treatments, and differential response of bacterial species to different perturbations was the key reason behind these effects. The results suggest that biodiversity is crucial for maintaining the stability of ecosystem functioning and acts as ecological insurance under abiotic perturbations. Biodiversity in natural ecosystems may also uphold the ecosystem functioning under anthropogenic disturbance.     

Environmental DNA reveals a mismatch between diversity facets of Amazonian fishes in response to contrasting geographical,environmental and anthropogenic effects

Freshwater ecosystems are among the most endangered ecosystem in the world. Understanding how human activities affect these ecosystems requires disentangling and quantifying the contribution of the factors driving community assembly. While it has been largely studied in temperate freshwaters, tropical ecosystems remain challenging to study due to the high species richness and the lack of knowledge on species distribution. Here, the use of eDNA-based fish inventories combined to a community-level modelling approach allowed depicting of assembly rules and quantifying the relative contribution of geographic, environmental and anthropic factors to fish assembly. We then used the model predictions to map spatial biodiversity and assess the representativity of sites surveyed in French Guiana within the EU Water Framework Directive (WFD) and highlighted areas that should host unique freshwater fish assemblages. We demonstrated a mismatch between the taxonomic and functional diversity. Taxonomic assemblages between but also within basins were mainly the results of dispersal limitation resulting from basin isolation and natural river barriers. Contrastingly, functional assemblages were ruled by environmental and anthropic factors. The regional mapping of fish diversity indicated that the sites surveyed within the EU WFD had a better representativity of the regional functional diversity than taxonomic diversity. Importantly, we also showed that the assemblages expected to be the most altered by anthropic factors were the most poorly represented in terms of functional diversity in the surveyed sites. The predictions of unique functional and taxonomic assemblages could, therefore, guide the establishment of new survey sites to increase fish diversity representativity and improve this monitoring program.