外来植物入侵对陆地生态系统地下碳循环及碳库的影响

生物入侵是当今全球性重大环境问题之一, 是全球变化的主要研究内容.评价外来植物入侵对于生态系统影响的研究多集中在地上部分,对于生态系统地下部分影响的研究相对较少.陆地生态系统地下部分对于生态系统过程的重要性之一体现在它处于生态系统碳分配过程的核心环节.入侵种通过影响群落凋落物的输入数量、质量以及输入时间,影响到对于土壤的碳输入,而入侵种与土著种根系的差异以及入侵种对微生物群落的影响是造成土壤呼吸强度发生变化的主要因素,前者土壤呼吸强度一般比后者高.多数研究表明外来植物入侵对生态系统地下碳循环和碳库产生影响,但由于入侵植物种类较多以及研究地点环境条件的不同,关于外来植物入侵对于土壤碳库和土壤有机碳矿化影响的研究结论并不统一.最后,提出了今后该研究领域应加强的一些建议和方向.     

Increased precipitation magnifies the effects of N addition on performance of invasive plants in subtropical native communities

亚热带本地植物群落中增加降水扩大了氮增加对入侵植物表现的影响 氮沉降、降水以及它们的交互作用会影响氮和水是限制性资源的温带生态系统中的外来植物 入侵,但它们是否会影响以及怎样影响外来植物在富氮和降水丰富的亚热带植物群落中的入侵, 仍不清楚。本研究在亚热带生态系统中,在野外用12种常见本地植物构建群落,将4种入侵植物及其近缘的4种本地植物分别引入到群落中,对群落进行氮添加(0和5 g N m⁻² a⁻¹)和降水增加(自然降水和增加降水30%)交互处理,比较了引入的入侵植物和近缘本地植物在群落中的生长和定居表现以及群落特征(包括群落密度和地上生物量等)。研究结果显示,只增加降水没有提高入侵植物或近缘本地植物的表现;氮添加仅提高入侵植物地上生物量和相对密度;氮和降水同时增加提高了入侵植物和近缘本地植物在群落中的生长和定居表现。在氮添加、降水增加和氮与降水同时增加处理下,入侵植物的大多数生长和定居参数高于近缘本地植物。在氮与降水同时增加时,入侵植物所定居本地群落的密度和地上生物量显著低于近缘本地植物所定居本地群落的密度和地上生物量。这些结果说明,在富氮和降水丰富的亚热带本地群落中,降水增加扩大了氮增加对入侵植物表现的影响。这将有助于理解在富氮和降水丰富的亚热带生态系统中,全球变化对植物入侵的影响。     

外来植物入侵对土壤生物多样性和生态系统过程的影响

随着科学家对生态系统地下部分的重视,评价外来植物入侵对土壤生态系统的影响成为当前入侵生态学领域的研究热点之一。本文综述了外来植物入侵对土壤微生物、土壤动物以及土壤碳、氮循环动态影响的研究,并探讨了其影响机制。已有的研究表明,植物入侵对土壤生物多样性及相关生态系统过程的影响均存在不一致的格局,影响机制也是复杂多样的。外来植物与土著植物凋落物的质与量、根系特征、物候等多种生理生态特性的差异可能是形成格局多样性和影响机制复杂性的最主要原因。今后,加强多尺度和多生态系统的比较研究、机制性研究、生物多样性和生态系统过程的整合性研究及土壤生态系统对植物入侵的反馈研究是评价外来植物入侵对土壤生态系统影响的发展趋势。     

入侵植物对根际土壤微生物群落影响的研究进展

入侵植物根际土壤微生物是地下生态系统的重要组成部分。外来植物入侵到新的栖息地后能够促进其根际土壤微生物群落结构的演替、改变土壤理化性质, 强化微生物群落功能的发挥, 进而创造更适合外来植物生长的土壤微环境, 促进外来种的入侵进程。从外来入侵植物根际土壤微生物的研究方法、外来入侵植物对根际土壤微生物群落影响以及从地下生态学对外来植物入侵的影响等方面进行了综述。土壤微生物研究方法主要包括微生物计数法、微生物生理生化指标方法及分子技术 3 类; 入侵植物对根际土壤微生物的影响主要体现在对其生物量、多样性以及功能微生物菌群等方面。在今后的研究中, 应当注重对同一区域外来入侵植物和近缘本土种、及其伴生种的根际土壤微生物进行比较研究; 加强入侵植物根际微生物功能机理、环境因子与微生物间关联性的研究; 同时在研究方法上应注重传统方法与生物标记法及其与分子技术的结合。     

群落组成及物种间相互作用对外来植物入侵的影响

外来植物入侵已成为严重的环境和社会问题,了解外来植物的入侵机制是有效控制其入侵的前提。生物阻抗假说认为,入侵地本地植物群落中的许多生物因子及生物过程能够抵御外来植物入侵。但关于群落抵抗外来种入侵的主要机制,目前还没有确定的结论。本文综述了群落中物种功能特征的多样性以及与外来种功能特征的相似度、植物与动物、植物与植物以及植物与土壤微生物间的相互作用等因素对外来植物入侵的影响,以及以前研究存在的不足。未来研究应该注重不同条件下植物与植物间的相互作用;不同竞争强度下,植物与食草动物的相互作用;植物、动物及土壤微生物三者之间的相互作用对外来植物入侵的影响。这些研究不仅能够丰富和完善入侵生态学理论,而且对于预测外来植物未来的扩散范围,合理有效地管理生态系统,防止外来植物入侵,保护本地生物多样性具有重要的实际意义。     

植物外来种入侵及其对生态系统的影响

对植物外来种的入侵及生态系统的影响进行综述与分析,植物入侵多种因子的影响,可分为外因和内因两类,植物外来种对生态系统的影响主要体现在生产力,土壤营养,水分,干扰体制,群落的结构和动态等方面,在管理外来种时,需对外来种的特性和影响因子进行系统的观察研究,采用机械法,化学方法和生物控制法等综合办法控制植物的入侵,引进植物引来种时,要对引进种的行为特性进行了调查研究,注意其安全性。     

不同光照强度对入侵植物薇甘菊（Mikania micrantha）和飞机草（Chromolaena odorata）生长及生物量分配的影响

外来植物入侵严重威胁着当地生物多样性和生态系统功能,引发巨大经济损失,已成为日益严重的全球性问题。光是热带和亚热带森林生态系统植物生长最重要的限制性资源之一,对光的捕获和利用直接影响植物在自然生态系统中的生存和适合度。本研究以华南地区危害严重的入侵植物薇甘菊(Mikania micrantha)和飞机草(Chromolaena odorata)为研究对象,对比二者生长、生物量分配及叶片特征对光照强度变化的响应,从而验证假设:外来植物入侵力受有效光辐射的限制,光照是影响不同演替阶段林型具有不同可入侵性的重要原因之一。研究结果表明,3%—60%全光照下两种外来植物均可存活,并显示较灵活的生物量分配策略,可见其对光照具有广适性,为其广泛分布提供生态学基础。低光严重抑制了两种外来植物的生物量积累,这可能是导致演替后期季风林入侵现象少的主要原因之一。对比两种植物叶片特征对光照强度变化的响应,高光下薇甘菊SLA降低,LAR、LARMR减小,叶片变小变厚,有利于植株保持强光下的水分平衡;低光下薇甘菊增加SLA和LAR,叶片变薄变大,增大对光的截获面积,以实现对光强减弱的适应。相比薇甘菊,3种光照处理对飞机草的SLA、LAR、LARMR无显著影响。以上结果提示:(1)光照影响所在群落对外来植物入侵的抵抗力;(2)攀援植物薇甘菊较丛生型草本飞机草对变化的光环境在叶片水平上具有更高的形态可塑性,有效寻觅光资源。     

外来入侵植物对土壤氮转化主要过程及相关微生物的影响

外来入侵植物不仅影响植物群落组成、生物多样性以及生态系统的结构和功能, 而且显著影响土壤氮(N)的转化过程。外来入侵植物对N循环影响的研究已成为入侵生态学的研究热点。N循环与凋落物的分解和养分释放有关, 外来入侵植物能够改变凋落物的组成与结构, 进而影响土壤的N转化过程。另外, 外来入侵植物的化感作用也会影响土壤N转化过程, 这些作用与土壤微生物的结构与功能变化密不可分。该文主要从凋落物分解与养分释放及外来入侵植物化感作用两个方面综述了外来入侵植物对土壤N转化的影响, 总结了外来入侵植物对土壤N转化相关土壤微生物(尤其是氨氧化细菌与氨氧化古菌)的影响, 探讨了土壤N转化对外来植物入侵的反馈, 并探讨了丛植菌根真菌与外来入侵植物的互相影响。     

网格尺度下外来入侵植物对高黎贡山生态系统服务影响的空间分析

【目的】高黎贡山生物多样性资源丰富,蕴藏着极高的生态系统服务价值,是中国重要的西南生态安全屏障。在气候变化和人类活动等影响下,高黎贡山正面临越来越多的外来植物入侵。明确外来入侵植物分布特征与生态系统服务重要区的空间对应关系,能够为高黎贡山外来入侵植物防控及生态安全屏障建设提供科学支撑。【方法】利用当量因子法,在3 km×3 km网格单元尺度下评估高黎贡山生态系统服务价值并进行重要性分级分区;以文献资料分析和实地调查相结合分析高黎贡山区域外来入侵植物的空间分布格局;利用Arcgis 10.2软件分析空间对应关系。【结果】高黎贡山生态系统服务重要性分为5级,单位面积价值量最高的生态系统类型为水系、阔叶林、针叶林、灌木林和灌草丛。外来入侵植物为59种,入侵等级为Ⅰ~Ⅴ级的物种分别有12、17、8、11和11种。除1级重要区外,其他区域均分布有外来入侵植物,其中3级和4级重要区(主要为灌木林地和耕地)分布的外来入侵植物的种类和数量最多。【结论】外来植物入侵威胁高黎贡山生态系统服务供给,亟需开展外来入侵植物系统调查评估以识别高等级入侵植物实施外来入侵植物差别化管控;陆生外来入侵植物应该成为高黎贡山外来入侵植物研究的重点;人工灌木林地和耕地作为高黎贡山外来入侵植物集聚区应该重点关注开展外来入侵植物防控。     

Effects of plant invasion on soil nitrogen transformation processes and its associated microbes

外来入侵植物不仅影响植物群落组成、生物多样性以及生态系统的结构和功能, 而且显著影响土壤氮(N)的转化过程。外来入侵植物对N循环影响的研究已成为入侵生态学的研究热点。N循环与凋落物的分解和养分释放有关, 外来入侵植物能够改变凋落物的组成与结构, 进而影响土壤的N转化过程。另外, 外来入侵植物的化感作用也会影响土壤N转化过程, 这些作用与土壤微生物的结构与功能变化密不可分。该文主要从凋落物分解与养分释放及外来入侵植物化感作用两个方面综述了外来入侵植物对土壤N转化的影响, 总结了外来入侵植物对土壤N转化相关土壤微生物(尤其是氨氧化细菌与氨氧化古菌)的影响, 探讨了土壤N转化对外来植物入侵的反馈, 并探讨了丛植菌根真菌与外来入侵植物的互相影响。     

Impacts of invasive plants on resident animals across ecosystems,taxa, and feeding types: a global assessment

As drivers of global change, biological invasions have fundamental ecological consequences. However, it remains unclear how invasive plant effects on resident animals vary across ecosystems, animal classes, and functional groups. We performed a comprehensive meta‐analysis covering 198 field and laboratory studies reporting a total of 3624 observations of invasive plant effects on animals. Invasive plants had reducing (56%) or neutral (44%) effects on animal abundance, diversity, fitness, and ecosystem function across different ecosystems, animal classes, and feeding types while we could not find any increasing effect. Most importantly, we found that invasive plants reduced overall animal abundance, diversity and fitness. However, this significant overall effect was contingent on ecosystems, taxa, and feeding types of animals. Decreasing effects of invasive plants were most evident in riparian ecosystems, possibly because frequent disturbance facilitates more intense plant invasions compared to other ecosystem types. In accordance with their immediate reliance on plants for food, invasive plant effects were strongest on herbivores. Regarding taxonomic groups, birds and insects were most strongly affected. In insects, this may be explained by their high frequency of herbivory, while birds demonstrate that invasive plant effects can also cascade up to secondary consumers. Since data on impacts of invasive plants are rather limited for many animal groups in most ecosystems, we argue for overcoming gaps in knowledge and for a more differentiated discussion on effects of invasive plant on native fauna.     

Effects of Exotic Plant Invasions on Soil Nutrient Cycling Processes

Although it is generally acknowledged that invasions by exotic plant species represent a major threat to biodiversity and ecosystem stability, little attention has been paid to the potential impacts of these invasions on nutrient cycling processes in the soil. The literature on plant–soil interactions strongly suggests that the introduction of a new plant species, such as an invasive exotic, has the potential to change many components of the carbon (C), nitrogen (N), water, and other cycles of an ecosystem. I have reviewed studies that compare pool sizes and flux rates of the major nutrient cycles in invaded and noninvaded systems for invasions of 56 species. The available data suggest that invasive plant species frequently increase biomass and net primary production, increase N availability, alter N fixation rates, and produce litter with higher decomposition rates than co-occurring natives. However, the opposite patterns also occur, and patterns of difference between exotics and native species show no trends in some other components of nutrient cycles (for example, the size of soil pools of C and N). In some cases, a given species has different effects at different sites, suggesting that the composition of the invaded community and/or environmental factors such as soil type may determine the direction and magnitude of ecosystem-level impacts. Exotic plants alter soil nutrient dynamics by differing from native species in biomass and productivity, tissue chemistry, plant morphology, and phenology. Future research is needed to (a) experimentally test the patterns suggested by this data set; (b) examine fluxes and pools for which few data are available, including whole-site budgets; and (c) determine the magnitude of the difference in plant characteristics and in plant dominance within a community that is needed to alter ecosystem processes. Such research should be an integral component of the evaluation of the impacts of invasive species.     

Massive mortality of invasive bivalves as a potential resource subsidy for the adjacent terrestrial food web

Large-scale mortality of invasive bivalves was observed in the River Danube basin in the autumn of 2011 due to a particularly low water discharge. The aim of this study was to quantify and compare the biomass of invasive and native bivalve die-offs amongst eight different sites and to assess the potential role of invasive bivalve die-offs as a resource subsidy for the adjacent terrestrial food web. Invasive bivalve die-offs dominated half of the study sites and their highest density and biomass were recorded at the warm water effluent. The density and biomass values recorded in this study are amongst the highest values recorded for aquatic ecosystems and show that a habitat affected by heated water can sustain an extremely high biomass of invasive bivalves. These mortalities highlight invasive bivalves as a major resource subsidy, possibly contributing remarkable amounts of nutrients and energy to the adjacent terrestrial ecosystem. Given the widespread occurrence of these invasive bivalves and the predicted increase in the frequency and intensity of extreme climatic events, the ecological impacts generated by their massive mortalities should be taken into account in other geographical areas as well.     

Invasive plants negatively impact native,but not exotic,animals

Despite our growing understanding of the impacts of invasive plants on ecosystem structure and function, important gaps remain, including whether native and exotic species respond differently to plant invasion. This would elucidate basic ecological interactions and inform management. We performed a meta‐analytic review of the effects of invasive plants on native and exotic resident animals. We found that invasive plants reduced the abundance of native, but not exotic, animals. This varied by animal phyla, with invasive plants reducing the abundance of native annelids and chordates, but not mollusks or arthropods. We found dissimilar impacts among “wet” and “dry” ecosystems, but not among animal trophic levels. Additionally, the impact of invasive plants increased over time, but this did not vary with animal nativity. Our review found that no studies considered resident nativity differences, and most did not identify animals to species. We call for more rigorous studies of invaded community impacts across taxa, and most importantly, explicit consideration of resident biogeographic origin. We provide an important first insight into how native and exotic species respond differently to invasion, the consequences of which may facilitate cascading trophic disruptions further exacerbating global change consequences to ecosystem structure and function.     

Ecological impacts of the invasive grass Sorghum halepense on native tallgrass prairie

Invasive plants frequently have competitive advantages over native species. These advantages have been characterized in systems in which the invading species has already become well established. Surprisingly, invader impacts on native communities currently undergoing invasion are lacking from most ecological studies. In this work we document and quantify shifting patterns in plant community structure in a native ecosystem (remnant tallgrass prairie) undergoing invasion by the invasive exotic Sorghum halepense (Johnsongrass). Further, we use manipulative field and greenhouse studies to quantify impacts of potential allelochemicals contained in whole-plant S. halepense leachates on growth of the dominant native grass, Schizachyrium scoparium (Little Bluestem), and tested the inhibitory effects of the potential soil legacy of S. halepense on the native grass in the greenhouse. Plant diversity indices revealed three distinct plant communities within the remnant prairie: a native community, a densely S. halepense invaded area, and a transitional zone between the two. Dominance of the native grass, determined by relative percent cover, significantly declined with increased S. halepense invasion via rhizomatous growth. Annual global positioning system monitoring of the S. halepense invasion front was used to quantify advancement into native prairie, documented at an average rate of 0.45 m year^?1. In the manipulative field and greenhouse studies, native S. scoparium treated with invasive S. halepense leachate had significantly less biomass and fewer inflorescences than control plants. These findings indicate the prolific clonal growth in conjunction with the plant chemistry of S. halepense play a significant role in displacement of the native grass.     

Non‐additive effects of invasive tree litter shift seasonal N release: a potential invasion feedback

Many invasive plant species strongly alter ecosystem processes by producing leaf litter that decomposes faster and releases N more quickly than that of native species. However, while most studies of invasive species litter impacts have only considered the decomposition of species in monoculture, forest litter layers typically contain litter from many species. Many litter mixtures decompose in a non‐additive manner, in which the mixture decomposes more quickly (synergistic effect) or more slowly (antagonistic effect) than would be expected based on decomposition of the component species’ litters in isolation. We investigated the potential for non‐additive effects of invasive species’ litter by conducting a one‐year litter bag experiment in which we mixed the litters of four native tree species with each of four invasive species. Litter mixtures frequently lost mass at non‐additive rates, although not at every loading ratio, and the presence, sign, and strength of effects depended on species composition. Non‐additive effects on N loss occurred in more litter combinations, and were almost always antagonistic at 90 days and synergistic at 365 days. Invasive species litter with lower C:N led to more strongly synergistic N loss with time. During the growing season, non‐additive patterns of N loss almost always resulted in increased N release – up to six times greater than would be expected based on single‐species decomposition. Consequently, we suggest that invasive species may further synchronize N release from the litter layer with plant N demand, enhancing any positive litter feedback to invasion. These results highlight the need to consider non‐additive effects of litter mixing in invaded forest communities, and suggest that estimates of invasive species’ impacts on ecosystem processes would be improved by considering these effects.     

Linking soil food web structure to above‐ and belowground ecosystem processes: a meta‐analysis

Soil fauna can be an important regulator of community parameters and ecosystem processes, but there have been few quantitative syntheses of the role of soil fauna in terrestrial soil communities and ecosystems. Here, we conducted a meta‐analysis to investigate the impacts of invertebrate soil micro‐ and mesofauna (grazers and predators) on plant productivity and microbial biomass. Overall our results indicate that an increase in the biomass of soil fauna increased aboveground plant productivity across ecosystems by 35% and decreased microbial biomass by 8%. In addition, we found no evidence for trophic cascades in terrestrial soil food webs, but the bacterivorous component of soil fauna influenced plant productivity and microbial biomass more than did the fungivorous component. Furthermore, changes in the biomass of soil fauna differentially affected plant productivity among plant functional groups: a higher biomass of soil fauna increased aboveground productivity by 70% in coniferous systems. However, in ecosystems dominated by legumes, a functional group with lower inorganic nitrogen requirements, there was no response of aboveground productivity to increases in the biomass of soil fauna. In sum, the results of this meta‐analysis indicate that soil fauna help to regulate ecosystem production, especially in nutrient‐limited ecosystems.     

植物功能性状对生态系统服务影响研究进展

全面认识和理解生态系统服务的形成机制是维持其持续供给的前提。植物功能性状直接参与多种生态系统过程, 影响生态系统服务供给, 探讨植物功能性状与生态系统服务的关系是揭示生态系统服务形成机制的重要途径。该文采用系统的文献综述方法, 分析了植物功能性状与生态系统服务关系的研究特点, 总结了影响不同生态系统服务的主要植物功能性状, 阐述了可能的影响途径。结果表明: 植物功能性状与生态系统服务关系研究以草地和森林等自然生态系统为主; 大部分研究集中在生态系统供给服务和支持服务, 包括生物量、净初级生产力、土壤肥力等; 根据植物功能性状对不同生态系统服务的影响程度, 植物功能性状可以聚类为土壤保持服务相关性状、水分循环相关性状、多功能相关性状、产品提供服务与养分循环相关性状以及授粉与生物控制服务相关性状; 并阐述了植物功能性状指标影响不同的生态系统服务途径。围绕植物功能性状对生态系统服务的影响, 今后尚需进一步探讨生态系统多功能性、植物功能性状相关性、气候变化和人类活动不确定性、时空尺度差异等因素对二者关系的影响。     

The Influence of Historical Land Use and Water Availability on Grassland Restoration

The ecological role of historical land use has rarely been explored in the context of grassland restoration. We conducted a 4‐year field experiment in a steppe and an old field in Inner Mongolia in northern China to examine the influence of historical land use and water availability on ecosystem restoration. Species richness, evenness, and plant cover were higher in the steppe than in the old field. The steppe was more temporally stable compared with the old field in terms of species richness, evenness, plant density, and cover. Water addition increased peak aboveground biomass, belowground net primary productivity, species richness, plant density, and cover in both the steppe and the old field. Water addition also enhanced the stability of ecosystems and the restoration of grassland. Our findings suggested that historical land use determines community structure and influences the process of grassland restoration. Converting grasslands to farmland in semiarid areas can cause the long‐term loss of biodiversity and instability of ecosystem with consequent impacts on ecosystem services. The amendment of limited resources is an effective practice to increase the success of ecosystem restoration.