陆地生态系统环境控制实验的研究方法及技术体系

生物及生态系统与环境变化间的反馈关系及其过程机制是生态学研究的重要内容。不同类型的生物环境因素控制实验以及大尺度的联网野外控制实验被认为是认识生态系统响应和适应环境变化过程机制、精细定量表达的有效手段及认知过程的加速器。近年来发展了大型野外物理模拟实验装置网络(如ECOTRON)、生态系统分析与实验平台(AnaEE)、国际干旱实验研究网络(Drought Network)、氮沉降联合实验网络(Nutrient Network),以及基于各区域性生态观测实验站的联网控制实验(如USA-ILTER)。发展大陆尺度联网实验研究平台事业正日益受到学术界的重视,将会在认知生态系统环境响应过程机制方面发挥更重要的作用。基于以上背景,本文综述了生态系统环境控制实验的研究方法和实验体系的发展,明确指出各种类型的生物环境控制实验需要形成联合协作体系,共同解决生态系统对环境变化的响应及适应的基本科学问题。目前的控制实验包括: 1) 实验室封闭装置内的生物生理生态学控制实验;2) 野外实验场的半开放部分环境要素控制实验;3) 近自然状态的野外环境控制实验;以及4) 基于野外生态站的联网控制实验。进而,本文还深入讨论了陆地生态系统的环境响应及适应过程机制实验系统设计的发展趋势,分析了基于大尺度自然环境梯度实验及生态站尺度的要素控制实验的优势,提出了整合两种实验技术、发展新一代的野外联网实验体系的科学设想,讨论了基于野外联网控制实验的研究体系,论证了研究生态系统对环境变化短期响应和长期适应的规律和机制、生态系统环境响应定量表达的技术途径。若本文提出的控制实验体系设计方案能够得以实施,必将大大促进我国乃至全球生态系统和环境变化科学的研究水平,对我国应对气候变化和生态环境建设具有重要的科学意义。     

模拟水生态系统及其在环境研究中的应用

随着70年代污染生态毒理学的发展,微宇宙作为评价化学品的环境影响的有力工具日益受到重视。由于从点源和非点源释放的化学物质可经直接或间接途径进入水生态系统,水生微宇宙在环境研究中的应用发展很快。早期的研究工作侧重于化学污染物在水环境的归宿。自70年代末以来,研究注意力逐渐集中于有毒物质在水生态系统内不同生物学组织水平上的生态学效应。本文分下列4个方面进行述评:(1)关于模拟生态系统的若干基本概念;(2)应用于环境研究的不同类型水生微宇宙;(3)尚有争议的若干问题;(4)水生微宇宙技术应用的新动向和展望。     

Responses of freshwater ecosystems to global change: research progress and outlook

全球变化已经通过提高水温、改变降水格局和水流状况、促进物种入侵、增加极端事件, 对不同的淡水生态系统造成严重的威胁。该文将全球变化背景下淡水生态学的主要研究内容归纳为: (1)全球变化各要素对个体、种群、群落及至生态系统水平的影响; (2)全球变化过程中生态系统生物地球化学循环的改变; (3)淡水生态系统对全球变化的适应对策。最近10-15年淡水生态系统与全球变化研究快速发展, 取得的重要突破有: (1)阐明淡水生态系统结构与功能对全球气候变化尤其是水温升高的响应过程与机制; (2)揭示淡水生态系统(湿地、湖泊、河流等)是全球碳循环的重要组成部分, 在全球变化因素的影响下呈现有机碳埋藏减少和矿化速率提高。今后的研究中, 需要进一步加强对淡水生态系统全要素的系统观测与整合; 开展以“河流”为介质耦合多系统的碳输运和转化过程研究; 强化基础理论研究揭示淡水生态系统对全球变化的适应机制。     

淡水生态系统对全球变化的响应:研究进展与展望

全球变化已经通过提高水温、改变降水格局和水流状况、促进物种入侵、增加极端事件,对不同的淡水生态系统造成严重的威胁。该文将全球变化背景下淡水生态学的主要研究内容归纳为:(1)全球变化各要素对个体、种群、群落及至生态系统水平的影响;(2)全球变化过程中生态系统生物地球化学循环的改变;(3)淡水生态系统对全球变化的适应对策。最近10–15年淡水生态系统与全球变化研究快速发展,取得的重要突破有:(1)阐明淡水生态系统结构与功能对全球气候变化尤其是水温升高的响应过程与机制;(2)揭示淡水生态系统(湿地、湖泊、河流等)是全球碳循环的重要组成部分,在全球变化因素的影响下呈现有机碳埋藏减少和矿化速率提高。今后的研究中,需要进一步加强对淡水生态系统全要素的系统观测与整合;开展以"河流"为介质耦合多系统的碳输运和转化过程研究;强化基础理论研究揭示淡水生态系统对全球变化的适应机制。     

微型生物群落eDNA-PFU监测

微型生物群落在水生态系统中起着至关重要的作用, 是水生态系统食物链的关键环节, 其结构和功能可以很好地反映不同生境的水质特征。《水质 微型生物群落监测 PFU法》是我国首个生物监测国家标准, 被证明是一种快速、经济、准确的监测方法。然而, 由于PFU法对专业知识要求较高、费时耗力且不易标准化, 严重阻碍了该方法进一步的推广与应用。近年来, 环境DNA(eDNA)技术的快速发展突破了微型生物形态鉴定的瓶颈, 能高效、准确地鉴定出水环境中包括微型生物在内的各种水生生物。为此, 文章提出微型生物群落eDNA-PFU法, 即基于eDNA技术改进的PFU法, 对微型生物群落进行监测。为了对eDNA-PFU法进行验证, 文章针对武汉东湖水体中的原生动物群落开展了预实验, 结果表明eDNA-PFU法较传统PFU法覆盖度与灵敏度均更高, 可以真实、全面、准确地揭示水体中微型生物群落结构特征。因此, 基于eDNA-PFU法的微型生物群落监测有望为湖泊、河流、水库等水体的生态考核提供新一代的生物监测标准。     

粤港澳大湾区水生态修复及展望

水是生态系统物质循环和能量流动的重要纽带,水生态系统修复在区域生态系统修复中起到关键作用。粤港澳大湾区剧烈人类活动对江河湖库生态系统造成破坏和干扰,江河湖库污染严重,水生物减少,导致流域水生态服务功能退化甚至丧失;从生态修复科学内涵出发,判断湾区水生态系统健康状况已处于非生物控制跃迁阈值之下;针对该形势,从工程建设、水环境治理、空间规划和管理机制四个方面,梳理湾区近期开展的与水生态修复相关的水生态文明建设、水污染防治行动计划、水生态空间划定和推进河长制等工作,并对其中用到的技术、指标和制度进行条理;然后以茅洲河流域综合治理和广东万里碧道作为水生态修复的点、面代表,从水生态修复的整体目标、采用的技术措施、效果评价的指标体系和管理制度方法等方面分析当前的工作现状;总结湾区现状水生态修复工作,认为湾区水生态系统的非生物修复阶段基本结束;基于生态系统修复理论结合湾区江河湖库生态系统特点,提出适合湾区的水生态修复框架,讨论水生态系统修复面临的问题和未来工作的展望,为大湾区水生态修复提供直接依据。     

中国内陆河流域城市景观过程对涉水生态系统服务的影响评价研究进展

掌握我国内陆河流域城市景观过程对涉水生态系统服务的影响评价研究现状，对于提高内陆河流域人类福祉和促进区域城市可持续发展具有重要意义。系统综述了我国内陆河流域城市景观过程对涉水生态系统服务的影响评价。结果表明：相关中英文论文数量与被引频次整体呈上升趋势，研究对象侧重于水源涵养、水质净化和淡水供给服务，研究方法主要包括价值量评价法和物质量评价法，研究结果则表明城市景观过程已造成涉水生态系统服务总量下降和空间异质性增加，同时还加剧了服务间的权衡关系。相关研究为深入理解内陆河城市景观过程对涉水生态系统服务的影响奠定了良好基础，但在揭示影响机理、模拟未来影响、分析服务权衡、协同与供需流关系以及探索可持续的内陆河流域综合优化管理等方面还存在不足。因此，未来应基于"机理-过程-可持续性"的思路建立内陆河流域城市景观过程对涉水生态系统服务影响评价框架，开展综合评价研究，为我国内陆河流域城市与山水林田湖草综合优化管理提供帮助。     

陆地生态系统野外增温控制实验的技术与方法

由于人类活动导致的碳排放急剧增加, 工业革命以来全球地表温度显著增加约1 ℃, 未来全球气候还将持续变暖, 到21世纪末最高可升温4 ℃。这种前所未有的气候变化不仅影响陆地植被的适应策略, 也深刻影响生态系统的结构和功能。其中陆地生态系统碳收支对全球变暖的反馈, 是决定未来气候变化强度的关键因素, 因此全球已经开展了大量的生态系统尺度的野外增温控制实验, 研究生态系统碳收支对气温升高的响应, 从而提高地球系统模型的预测精度。然而由于增温技术和方法的不同, 不同研究的结果之间难以进行比较。该文系统总结了常见的野外增温技术和方法, 包括主动增温和被动增温, 阐述了其优缺点、适用对象以及相关研究成果。同时简要介绍了野外增温控制实验的前沿研究方向——新一代野外增温技术(包括全土壤剖面增温和全生态系统增温)和基于新一代增温技术开展的野外增温联网实验。     

生物完整性指数与水生态系统健康评价

生物完整性指数是目前水生态系统健康评价中应用最广泛的一个生态指标。本文扼要介绍了生物完整性指数的概念、水生态系统健康评价的原理以及大型底栖无脊椎动物完整性指数的构建方法,介绍了生物完整性指数在水生态系统健康评价中的应用及我国开展这方面工作的建议。     

湖泊的水生态模型

由于城市化进程的不断加快,大量的污染物排放到湖泊中,打破了湖泊的生态平衡.湖泊的水生态模型不仅能够研究湖泊的富营养化现象,而且还可以模拟工业毒物等污染物对湖泊生态系统的影响,是湖泊管理的有力工具.本文从分析湖泊的污染现状以及污染趋势出发,介绍了湖泊水生态模型的研究现状,并根据模型的模拟对象和空间模拟能力对湖泊水生态模型进行了分类.在此基础上介绍了AQUATOX、PAMOLARE、CAEDYM、WASP、OOMAS等比较成熟的模拟湖泊生态系统的模型软件,阐述了它们的产生、发展、主要特点以及应用,总结了当今湖泊水生态模型在模拟过程中遇到的问题,并对水生态模型的发展趋势进行了展望.本文为湖泊水生态模型的选择提供了建议.     

Mesocosms Reveal Ecological Surprises from Climate Change

Understanding, predicting, and mitigating the impacts of climate change on biodiversity poses one of the most crucial challenges this century. Currently, we know more about how future climates are likely to shift across the globe than about how species will respond to these changes. Two recent studies show how mesocosm experiments can hasten understanding of the ecological consequences of climate change on species’ extinction risk, community structure, and ecosystem functions. Using a large-scale terrestrial warming experiment, Bestion et al. provide the first direct evidence that future global warming can increase extinction risk for temperate ectotherms. Using aquatic mesocosms, Yvon-Durocher et al. show that human-induced climate change could, in some cases, actually enhance the diversity of local communities, increasing productivity. Blending these theoretical and empirical results with computational models will improve forecasts of biodiversity loss and altered ecosystem processes due to climate change.     

Salinity as a driver of aquatic invertebrate colonisation behaviour and distribution in the wheatbelt of Western Australia

To understand how environmental change will modify community assembly and the distribution of organisms it is valuable to understand mechanisms that drive the occurrence of organisms across the landscape. Salinisation of agricultural land in southwest Western Australia, as a result of land clearing, is a widespread environmental change, which threatens numerous taxa, but provides an opportunity to elucidate such mechanisms. Although salinisation affects terrestrial fauna and flora, the greatest impacts are seen in wetlands and waterways. Many aquatic insect taxa colonise ephemeral water bodies directly as adults or by oviposition. Few empirical studies, however, evaluate the influence of abiotic factors, such as water body salinity, on the colonisation behaviour of aquatic fauna. We conducted a manipulative experiment using mesocosms to test whether colonising insect fauna select aquatic habitats based upon salinity. We found that halosensitive fauna selected less saline mesocosms for oviposition and colonisation, demonstrating that behaviour can influence the distribution of aquatic organisms. Additionally, we utilised field surveys of insects from ephemeral water bodies across a broad region of southwest Western Australia to determine if mesocosm results reflected field observation. The abundance of the same insect taxa and taxonomic groups in the field were highly variable and, with the exceptions of Culex australicus Dobrotworksy and Drummond and Anopheles annulipes Giles (Diptera: Culicidae), did not show similar patterns of distribution to those observed in the mesocosm experiment. Both mesocosm and field assemblages exhibited similar and significant trajectories associated with the salinity gradient, even though there were differences in assemblage structure between the two. Our findings give empirical support to the importance of behaviour in the spatial distribution and assembly of some aquatic insects. Handling editor: K. Martens     

Development of an epiphyte indicator of nutrient enrichment: A critical evaluation of observational and experimental studies

An extensive review of the literature describing epiphytes on submerged aquatic vegetation (SAV), especially seagrasses, was conducted in order to evaluate the evidence for response of epiphyte metrics to increased nutrients. Evidence from field observational studies, together with laboratory and field mesocosm experiments, was assembled from the literature and evaluated for a hypothesized positive response to nutrient addition. There was general consistency in the results to confirm that elevated nutrients tended to increase the load of epiphytes on the surface of SAV, in the absence of other limiting factors. In spite of multiple sources of uncontrolled variation, positive relationships of epiphyte load to nutrient concentration or load (either nitrogen or phosphorus) often were observed along strong anthropogenic or natural nutrient gradients in coastal regions. Such response patterns may only be evident for parts of the year. Results from both mesocosm and field experiments also generally support the increase of epiphytes with increased nutrients, although outcomes from field experiments tended to be more variable. Relatively few studies with nutrient addition in mesocosms have been done with tropical or subtropical species, and more such controlled experiments would be helpful. Experimental duration influenced results, with more positive responses of epiphytes to nutrients at shorter durations in mesocosm experiments versus more positive responses at longer durations in field experiments. In the field, response of epiphyte biomass to nutrient additions was independent of climate zone. Mesograzer activity was a critical covariate for epiphyte response under experimental nutrient elevation, but the epiphyte response was highly dependent on factors such as grazer identity and density, as well as nutrient and ambient light levels. The balance of evidence suggests that epiphytes on SAV will be a useful indicator of persistent nutrient enhancement in many situations. Careful selection of appropriate temporal and spatial constraints for data collection, and concurrent evaluation of confounding factors will help increase the signal to noise ratio for this indicator.     

Determining the mechanism by which fish diversity influences production

Understanding the ability of biodiversity to govern ecosystem function is essential with current pressures on natural communities from species invasions and extirpations. Changes in fish communities can be a major determinant of food web dynamics, and even small shifts in species composition or richness can translate into large effects on ecosystems. In addition, there is a large information gap in extrapolating results of small-scale biodiversity–ecosystem function experiments to natural systems with realistic environmental complexity. Thus, we tested the key mechanisms (resource complementarity and selection effect) for biodiversity to influence fish production in mesocosms and ponds. Fish diversity treatments were created by replicating species richness and species composition within each richness level. In mesocosms, increasing richness had a positive effect on fish biomass with an overyielding pattern indicating species mixtures were more productive than any individual species. Additive partitioning confirmed a positive net effect of biodiversity driven by a complementarity effect. Productivity was less affected by species diversity when species were more similar. Thus, the primary mechanism driving fish production in the mesocosms was resource complementarity. In the ponds, the mechanism driving fish production changed through time. The key mechanism was initially resource complementarity until production was influenced by the selection effect. Varying strength of intraspecific interactions resulting from differences in resource levels and heterogeneity likely caused differences in mechanisms between the mesocosm and pond experiments, as well as changes through time in the ponds. Understanding the mechanisms by which fish diversity governs ecosystem function and how environmental complexity and resource levels alter these relationships can be used to improve predictions for natural systems.     

Implications of guppy (Poecilia reticulata) life‐history phenotype for mosquito control

Guppies (Poecilia reticulata) are frequently introduced to both natural and artificial water bodies as a mosquito control. Laboratory studies have demonstrated that guppies can consume large numbers of larval mosquitoes. Our study investigates how intraspecific variability in guppy phenotype affects their importance as a mosquito biocontrol and how habitat conditions (natural ponds vs. water storage containers) may influence insect biomass and guppy feeding. Using a blocked experimental design, we established stream‐side mesocosm ponds with half receiving gravel substrate to simulate pond‐bottom habitat. To provide realistic diet choices and insect abundances, we allowed the mesocosms to colonize naturally with aquatic insect larvae for 1 month before introducing guppies. We tested two distinct guppy phenotypes (from high‐ and low‐predation streams) alongside fish‐free controls. After 1 month, we measured insect biomass in the mesocosms and examined guppy gut contents to document direct predation. While overall insect biomass was not significantly different across the three fish treatments, we observed a significant reduction in mosquito biomass in fish treatments compared to fish‐free controls, as well as intraspecific differences in feeding. Overall insect biomass was significantly higher in mesocosms without gravel, while habitat condition had no effect on mosquito biomass. As guppy phenotype responds to changes in their environments, it is an important consideration for biocontrol policy to anticipate potential ecosystem effects. We close by relating our findings to other studies and by discussing the implications and potential risks of using guppies to control mosquitoes.     

Evaluating a predator–prey interaction in the field: the interaction between beetle larvae (predator) and tadpoles (prey)

The larval amphibian community of temporary pond ecosystems has served as a model for studies in community ecology, with a majority of this work being conducted in mesocosms. Recent research has suggested that mesocosms may overestimate ecological effects; therefore, experimental studies conducted under field conditions are required to gauge the results of mesocosm studies. To assess a species interaction under more natural conditions, we conducted a series of field experiments examining the predator–prey interaction between beetle larvae ( Dytiscus sp.; predator) and larval wood frogs Rana sylvatica (prey) in central Pennsylvania, USA. Quantitative sampling of woodland ponds indicated that beetle larvae of the genus Dytiscus were the most common predator of tadpoles. In a field enclosure experiment, dytiscids were effective predators of tadpoles in the pond environment. Moreover, tadpoles avoided areas in a pond containing caged dytiscids, demonstrating that tadpoles recognize the chemical stimuli of predators in complex environments. The results of this study are consistent with data from prior laboratory and mesocosm studies and suggest that these venues can produce reliable interpretations of predator–prey dynamics in this community.     

Survival of Bacillus licheniformis in Seawater Model Ecosystems

The fate of Bacillus licheniformis DSM 13 was monitored after introduction into laboratory microcosms and mesocosms established in the Knebel Vig estuary, Denmark. The model organism was detected by a combination of immunofluorescence microscopy and nonselective plating followed by colony blotting. This allowed simultaneous quantification of intact cells and culturable cells. B. licheniformis DSM 13 adapted poorly to the conditions in filtered (0.2-μm-pore-size filter) seawater. Results from additional microcosm studies using natural seawater demonstrated that protozoan grazing also was important in regulating the population of the introduced model organism. In experiments using mesocosms, B. licheniformis DSM 13 also showed a rapid die-off. The introduction of the organism led to increased nutrient levels and to increased growth of both autotrophic and heterotrophic components of the plankton community compared with those of control enclosures. Thereby, a more intensive predation impact on the bacterioplankton community was induced. The combination of microcosm and mesocosm experiments provides a scenario in which the influence of single biotic and abiotic factors on survival of introduced organisms can be tested and in which the effect of the introduction on ecosystem structure and function can be evaluated. This test concept might prove useful in risk assessment of genetically modified microorganisms.     

Habitat structure, trophic structure and ecosystem function: interactive effects in a bromeliad–insect community

Although previous studies have shown that ecosystem functions are affected by either trophic structure or habitat structure, there has been little consideration of their combined effects. Such interactions may be particularly important in systems where habitat and trophic structure covary. I use the aquatic insects in bromeliads to examine the combined effects of trophic structure and habitat structure on a key ecosystem function: detrital processing. In Costa Rican bromeliads, trophic structure naturally covaries with both habitat complexity and habitat size, precluding any observational analysis of interactions between factors. I therefore designed mesocosms that allowed each factor to be manipulated separately. Increases in mesocosm complexity reduced predator (damselfly larva) efficiency, resulting in high detritivore abundances, indirectly increasing detrital processing rates. However, increased complexity also directly reduced the per capita foraging efficiency of the detritivores. Over short time periods, these trends effectively cancelled each other out in terms of detrital processing. Over longer time periods, more complex patterns emerged. Increases in mesocosm size also reduced both predator efficiency and detritivore efficiency, leading to no net effect on detrital processing. In many systems, ecosystem functions may be impacted by strong interactions between trophic structure and habitat structure, cautioning against examining either effect in isolation.     

Sediment deposition from eroding peatlands alters headwater invertebrate biodiversity

Land use and climate change are driving widespread modifications to the biodiverse and functionally unique headwaters of rivers. In temperate and boreal regions, many headwaters drain peatlands where land management and climate change can cause significant soil erosion and peat deposition in rivers. However, effects of peat deposition in river ecosystems remain poorly understood. We provide two lines of evidence—derived from sediment deposition gradients in experimental mesocosms (0–7.5 g/m²) and headwaters (0.82–9.67 g/m²)—for the adverse impact of peat deposition on invertebrate community biodiversity. We found a consistent negative effect of sediment deposition across both the experiment and survey; at the community level, decreases in density (1956 to 56 individuals per m² in headwaters; mean 823 ± 129 (SE) to 288 ± 115 individuals per m² in mesocosms) and richness (mean 12 ± 1 to 6 ± 2 taxa in mesocosms) were observed. Sedimentation increased beta diversity amongst experimental replicates and headwaters, reflecting increasing stochasticity amongst tolerant groups in sedimented habitats. With increasing sedimentation, the density of the most common species, Leuctra inermis, declined from 290 ± 60 to 70 ± 30 individuals/m² on average in mesocosms and >800 individuals/m² to 0 in the field survey. Traits analysis of mesocosm assemblages suggested biodiversity loss was driven by decreasing abundance of invertebrates with trait combinations sensitive to sedimentation (longer life cycles, active aquatic dispersal of larvae, fixed aquatic eggs, shredding feeding habit). Functional diversity metrics reinforced the idea of more stochastic community assembly under higher sedimentation rates. While mesocosm assemblages showed some compositional differences to surveyed headwaters, ecological responses were consistent across these spatial scales. Our results suggest short‐term, small‐scale stressor experiments can inform understanding of “real‐world” peatland river ecosystems. As climate change and land‐use change are expected to enhance peatland erosion, significant alterations to invertebrate biodiversity can be expected where these eroded soils are deposited in rivers.     

Modelling and the monitoring of mesocosm experiments: two case studies

Mesocosm experiments have played an important role over thelast decade in increasing our understanding of marine ecosystems.Many studies use these controlled environments to examine ecosystemresponses to factors such as nutrient addition and light limitation.A few studies have been able to successfully model mesocosmexperiments using carefully designed and comprehensive modelsand experimental design. Nevertheless, it is rare for such modelsto be compared with oceanic studies, and to consider the sulphurcycle as well as the carbon and nitrogen budgets. Here we takean ecosystem model, including a dimethylsulphide loop, thathas been successfully used in modelling the evolution of theplanktonic system in a Lagrangian field experiment in the NorthAtlantic—the PRIME cruise of 1996—and apply it totwo mesocosm experiments. These were operated by two differentgroups of scientists, but in the same field station in a Norwegianfjord. The experiments were not explicitly designed with thedata requirements of any model in mind. We show that the modelis best able to simulate mesocosm data using model parameterstaken from the real ocean. However, most sensitivity tests aresignificantly less successful in the mesocosm environment thanthe real ocean, especially if the model parameters are allowedto vary in a best fit sense. The limitations of the model–mesocosmmatch highlight the importance of comprehensive monitoring ofmesocosms if they are to be useful for validating models suitablefor the open ocean.