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.     

红河流域的外来人侵植物

红河流域是中国生物多样性最为丰富的地区,植物区系起源古老,生态系统类型复杂多样.本文论述了红河流域外来入侵植物的现状,列举了73种红河流域外来入侵物的种类,对危害比较严重的紫茎泽兰、飞机草、马樱丹、肿柄菊、凤眼莲和空心莲子草6种植物作了具体介绍.对外来入侵植物的控制对策,入侵植物本身的生物学特性的研究、保护生物多样性和退化生态系统的恢复以及路域生态系统管理等几方面作了论述.结果表明,减少人类对生态系统的干扰和破坏,恢复本地植被是防止外来入侵植物入侵的有效途径.     

中国农业生态系统外来种入侵及其管理现状

农业生态系统极易遭受外来生物入侵.作者根据文献资料和多年工作观察统计出入侵我国农业生态系统的外来生物共计92科175属239种,其中植物155种,动物55种,微生物29种,植物多为有意引入后逸生,而动物和微生物则主要是无意引入.外来入侵种发生数量呈现从南到北、从东到西逐渐减少的趋势.这些入侵种中,来源于美洲的最多(占45.04%),其次是欧洲(22.90%);菜地(包括温室大棚)和果园入侵种最多,分别达64.85%和66.53%,而半年期的秋熟旱地和夏熟旱地分别占34.31%和23.85%.其中17种外来杂草、10种害虫、7种病原菌为恶性有害生物,应作为防除的重点目标.目前农业生态系统外来入侵物种的控制以化学防治为主,但由于长期施用化学农药,在侵入我国农田的入侵种中,已有51种在世界不同地区演化出抗药性生物型,因而需重视生物防治、农业和生态防治以及检疫等的综合应用.今后外来种对农业生态系统的入侵格局、机制和趋势,入侵途径以及生物入侵和抗药性生物型对农业生态系统中有害生物群落演替的影响、转基因作物导致的生物入侵等问题值得关注.     

红河流域的外来入侵植物

红河流域是中国生物多样性最为丰富的地区,植物区系起源古老,生态系统类型复杂多样.本文论述了红河流域外来入侵植物的现状,列举了73种红河流域外来入侵物的种类,对危害比较严重的紫茎泽兰、飞机草、马樱丹、肿柄菊、凤眼莲和空心莲子草6种植物作了具体介绍.对外来入侵植物的控制对策,入侵植物本身的生物学特性的研究、保护生物多样性和退化生态系统的恢复以及路域生态系统管理等几方面作了论述.结果表明,减少人类对生态系统的干扰和破坏,恢复本地植被是防止外来入侵植物入侵的有效途径.     

本地种与外来种水生植物在不同基质营养下的生长比较

近年来,生物入侵由于其对生态系统,环境,经济等多方面造成的后果日益严重,逐渐成为目前全球普遍关注的生态问题。对于植物而言,外来入侵种不仅会大大降低本地物种的存活率,而且对本地物种的分布也会造成很大程度的负面影响。不仅如此,外来入侵种还会对本地水生或陆生生态系统造成十分严重的影响和破坏。随着国内外专家学者对外来种研究的深入,许多有关外来种入侵机制的假说和理论不断被提出。其中以资源假说(Resource Hypothesis,Davis 等 2000)研究的最为广泛和深入。在资源假说中,Davis等提出:伴随着一定数量繁殖体,外来物种的入侵会随着资源(例如光,营养和水份)的增加而加剧。为了验证(1)外来种和本地种的表现是否存在差异,如果存在,这种是否也会随着资源的增加而增强?(2)外来种与本地种的差异是否对我们预测和防治入侵有帮助?本文在此基础上,采用4种水生外来种,水鳖科(Hydrocharitaceae)两种,小二仙草科(Haloragidaceae)狐尾藻属(Myriophyllum)两种,与本地同科或同属且形态相似的3种水生植物为实验材料。分别配制两种不同营养级别的基质环境,比较了在高、低营养基质环境中外来种和本地种与生长相关的参数指标。结果显示:在高营养基质和低营养基质环境中,本地种较外来种更大地积累其生物量并且拥有更高的相对生长速率(relative growth rate)。结果还显示:在侧枝的生物量分配方面,外来种较本地种显著增高。由于断枝是水生植物无性繁殖的重要手段之一,并且断枝由侧枝或主茎受到生物或非生物的扰动产生。我们使用侧枝生物量的分配这一指标来间接反映水生植物的无性繁殖能力。结果表明,本地种较外来种能较好适应当地不同的基质营养环境;但是在无性繁殖体的传播方面,外来种较本地种占有一定的优势。因此,我们尝试提出:对外来水生植物的防治应继续以管理本地水生植物的栖息地和保护本地水生植物多样性为主,并且应加大对外来水生植物无性繁殖体特别是断枝传播的管理和控制力度。     

“世界100种恶性外来入侵物种”在我国大陆的入侵现状

[目的] 明确世界自然保护联盟公布的“世界100种恶性外来入侵物种”在我国大陆发生分布现状,为我国制定外来入侵物种管控对象和分级管理对策提供依据。[方法] 基于在线数据库系统、文献报道以及外来入侵物种本底调查结果,采用分类统计方法,对物种的分类地位、原产地、在我国的入侵状态及其所在的生态系统进行分析。[结果] 世界100种恶性外来入侵物种已有82种在我国发生分布,包括本地种33种、外来入侵种32种、外来非入侵种16种,以及未明确入侵状态1种。其中,32种外来入侵种包括陆生无脊椎动物8种、哺乳动物2种、鱼类2种、两栖动物1种、爬行动物1种、水生无脊椎动物2种、陆生植物9种、水生植物4种、真菌1种、卵菌1种和病毒1种。以上物种主要分布在东南沿海地区和西南地区,而较少分布在西北地区和东北地区;约75%物种分布在农田、城镇、森林和湿地4类生态系统。[结论] 建议外来入侵物种管理部门重点关注尚未在国内发生分布的18种潜在外来入侵物种,并列入国家外来入侵物种相关管理对象,严防其传入与扩散;严密监控国内已发生且具有潜在危险的外来物种,防止其向可能入侵的生态系统边缘扩散;继续对在国内已发生的外来入侵种实施区域性分级控制管理措施。     

汶川大地震对外来入侵种的影响与管理对策

2008年5月12日四川省汶川县发生的大地震对当地人民的生命财产造成了巨大的损失。为了营灾民及抢救财产，大量国际和国内救援物资和人员陆续到达地震灾区，对减轻灾区民众的痛苦起到了积极的作用。随着国际国内救援物资和人员的到达，一些外来入侵种有可能随之进入灾区。如果这些外来入侵种得不到有效的控制，就可能造成生物入侵的发生。因此应该采取科学的对策及早进行防治，包括：（1）加强对外来入侵种的生态风险评估，（2）严密监测外来入侵种的动态，（3）采取科学方法控制外来入侵种。     

植物功能性状与外来植物入侵

揭示影响外来植物入侵性的功能性状及其生态机制是入侵植物生态学的核心任务之一.本文综述了植物功能性状与外来植物入侵性的研究进展,通过分析植物功能性状对外来植物入侵的贡献以及外来植物的不同入侵阶段对其功能性状的需求,探讨植物功能性状与外来植物入侵的相关性及其入侵机理.迄今研究较多的影响外来植物入侵性的功能性状主要包括形态性状、生长性状、生理性状、繁殖性状、种子性状、克隆性状、表型可塑性和遗传变异等.这些功能性状对外来植物入侵的贡献随着入侵阶段的不同而变化.在传播到达阶段,种子性状对入侵具有重要影响;在定居建群阶段,与植物抗逆性和适应性相关的生理性状和繁殖性状发挥主要作用;在扩散入侵阶段.克隆性状和影响植物竞争能力的生理性状对植物成功入侵具有重要贡献.由于植物入侵性是其功能性状和环境因素互作的结果,且功能性状的作用随环境因素和入侵阶段不同而异,因此,结合外来植物入侵阶段,并考虑功能性状与环境因子的互作,是入侵生物学中植物功能性状研究的发展趋势.     

降雨年型变化及竞争对反枝苋和大豆生长的影响

为探索不同降雨年型及栽培方式下外来杂草与本地作物的竞争机制,为未来全球变化背景下控制外来杂草提供理论依据,本研究以广泛入侵东北农田生态系统的外来杂草反枝苋(Amaranthusretroflexus)和本地作物大豆(Glycine max)为研究对象,在遮雨棚内人工模拟正常、欠缺、丰沛三种降雨年型,采用盆栽实验的方法,研究两种植物在单种和混种条件下的生长季节动态。结果表明,降雨丰沛年两种植物的株高和总生物量均大于降雨正常年,降雨欠缺年则均小于降雨正常年。生长季初期两种植物的根冠比均在降雨欠缺年最高,说明两种植物均可通过增大根系的生物量分配,减少地上生物量的分配来适应干旱环境。在三种降雨年型下,混种时大豆的株高、相对生长速率及总生物量均显著小于单种大豆,而反枝苋则相反,尽管有时不显著,说明种间竞争抑制大豆生长而促进反枝苋的生长,两种植物之间的竞争是不对称竞争。总的来看,降雨增加有利于提高大豆的竞争能力,降雨减少有利于提高反枝苋的竞争能力,随着生长发育的推移,这种现象更明显。反枝苋可以在较广的降雨变化范围内保持较高的株高、相对生长速率及生物量,这很可能是其成为全球范围成功入侵的外来杂草的重要原因之一;干旱更有利于反枝苋入侵大豆田。     

干扰强度对群落中紫茎泽兰种子萌发、幼苗定居和生长的影响

干扰与外来植物入侵密切相关,种子萌发和幼苗定居是植物生活史中最脆弱、也是外来植物入侵最关键的阶段.为研究干扰在恶性外来入侵植物紫茎泽兰成功入侵过程中的作用,采用人工牧草群落代替自然群落,人为干扰(去除不同面积的牧草)模拟自然干扰的方式,研究了紫茎泽兰入侵初期种子萌发、幼苗定居和生长对不同干扰强度的响应与适应.结果表明:...     

Woody exotic plant invasions and fire: reciprocal impacts and consequences for native ecosystems

Fire regimes influence and are influenced by the structure and composition of plant communities. This complex reciprocal relationship has implications for the success of plant invasions and the subsequent impact of invasive species on native biota. Although much attention has been given to the role of invasive grasses in transforming fire regimes and native plant communities, little is known about the relationship between woody invasive species and fire regime. Despite this, prescribed burning is frequently used for managing invasive woody species. In this study we review relationships between woody exotic plant invasions and fire in invaded ecosystems worldwide. Woody invaders may increase or decrease aspects of the fire regime, including fire frequency, intensity and extent. This is in contrast to grass invaders which almost uniformly increase fire frequency. Woody plant invasion can lead to escape from a grass-fire cycle, but the resulting reduction in fire frequency can sometimes lead to a cycle of rare but more intense fires. Prescribed fires may be a useful management tool for controlling woody exotic invaders in some systems, but they are rarely sufficient to eliminate an invasive species, and a dearth of controlled experiments hampers evaluation of their benefits. Nevertheless, because some woody invaders have fuel properties that differ substantially from native species, understanding and managing the impacts of woody invaders on fire regimes and on prescribed burns should become an important component of resource and biodiversity management.     

Global change and biological invasions

Invasion by exotic species is one of the serious socio-economic, environmental and ecological problems currently faced by mankind. Biological invasions have changed the species composition, structure and function of ecosystems, and are seriously threatening global biodiversity, economy and human health (Iqbal et al. 2021; Wang et al. 2020; Yang et al. 2021; Zhao et al. 2020; Zheng et al. 2015). Biological invasions have resulted in an economic loss of at least US$ 1.288 trillion over the past few decades worldwide (Diagne et al. 2021). As a consequence of these far-reaching impacts, biological invasions have become a hot research topic in modern ecology, and attract major attention from international organizations, governments and scientists all over the world. There is a complex interaction between biological invasions and global environmental change. Biological invasions are not only passengers of global change, but can also be major drivers of global change (MacDougall and Turkington 2005). Other components of global change, such as atmospheric CO₂ enrichment, global warming, nitrogen deposition, changes in precipitation regimes, habitat fragmentation and land-use change, affect species distributions and resource dynamics of ecosystems, and consequently drive invasion success of many exotic species. On the other hand, invasion by exotic species can also alter basic ecosystem properties, which in turn affect many components of global change. Research on the patterns, processes and mechanisms of biological invasion can shed light on the drivers and consequences of biological invasions in the light of global change, and serve as a scientific basis for forward-thinking management plans. The overarching challenge is to understand the basic ecological interactions of, e.g., invasive and native species, plants and soil, and plants and animals.     

An Invasive Grass Increases Live Fuel Proportion and Reduces Fire Spread in a Simulated Grassland

Fire is a globally important ecosystem process, and invasive grass species generally increase fire spread by increasing the fuel load and continuity of native grassland fuelbeds. We suggest that invasive grasses that are photosynthetically active, while the native plant community is dormant reduce fire spread by introducing high-moisture, live vegetation gaps in the fuelbed. We describe the invasion pattern of a high-moisture, cool-season grass, tall fescue (Schedonorus phoenix (Scop.) Holub), in tallgrass prairie, and use spatially explicit fire behavior models to simulate fire spread under several combinations of fuel load, invasion, and fire weather scenarios. Reduced fuel load and increased extent of tall fescue invasion reduced fire spread, but high wind speed and low relative humidity can partially mitigate these effects. We attribute reduced fire spread to asynchrony in the growing seasons of the exotic, cool-season grass, tall fescue, and the native, warm-season tallgrass prairie community in this model system. Reduced fire spread under low fuel load scenarios indicate that fuel load is an important factor in fire spread, especially in invaded fuel beds. These results present a novel connection between fire behavior and asynchronous phenology between invasive grasses and native plant communities in pyrogenic ecosystems.     

Woody plant invasions and restoration in forests of island ecosystems: lessons from Robinson Crusoe Island,Chile

Islands are susceptible to exotic plant invasion, and Robinson Crusoe Island (RCI), Juan Fernandez Archipelago (33°S, 78°7′W, Chile) is no exception. Through a literature review, we assessed plant invasion and compared it to other oceanic islands worldwide. Here, we discuss measures to enhance forest recovery on RCI based on knowledge accumulated from studies on RCI and other islands. Although these findings are designed to halt the progress of invasion on RCI, they could also be applied to other insular ecosystems. We addressed the following questions: (1) What is the plant invasion status on RCI in relation to other islands worldwide? (2) How imminent is biodiversity loss by plant invasion on RCI? (3) How is woody plant invasion taking place on RCI? (4) What methods are effective in controlling invasive woody species on islands worldwide? (5) What is the ability of natural forests to recover after controlling invasive plants on RCI? We found that (1) RCI is globally the fourth most invaded island for woody species. (2) Invasive woody species expansion is estimated at 4.3 ha annually. (3) Some invasive species establish under forest canopy gaps, out-competing native species. (4) Control of invasive plant species should focus on small gaps, and restoration should promote plant cover and soil protection. Mechanical and chemical control of invasive species seemed to be insufficient to prevent biodiversity loss. Developing alternatives like biological control are indispensable on RCI. (5) Six years after invasive species control, floristic composition tended to recover.     

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.     

Managed livestock grazing for conservation outcomes in a Queensland fragmented landscape

Protecting native biodiversity is a difficult prospect in extremely modified landscapes, especially where high‐impact exotic species are widespread. Using new data and a review of the literature, this paper comments on the use of livestock grazing to manage the invasive and highly combustible pasture grass species, Buffel Grass (Cenchrus ciliaris) and thereby help conserve fire‐sensitive Brigalow (Acacia harpophylla) vegetation in reserves in Queensland, Australia. We cite evidence that shows that grazing is a potentially useful management tool in such cases and its use can be compatible with the protection of both fire‐sensitive vegetation and other native plant species within the understorey. However, there are limitations in implementing grazing within conservation reserves including the lack of a clear understanding of the influence of grazing on biodiversity and resource condition. Importantly, we highlight secondary invasion by the exotic grass Indian Couch (Bothriochloa pertusa) as a key emerging threat that may undermine the biodiversity benefits gained by grazing in reserves. Grazing can be a useful tool for conservation management in particular scenarios, but the associated risks demand accompanying monitoring and reporting of positive and negative impacts to ensure the fundamental aim of biodiversity protection is being achieved.     

Poor historical data drive conservation complacency: The case of mammal decline in south‐eastern Australian forests

Forested ecosystems of south‐eastern Australia now differ physically, compositionally and functionally from their condition prior to European settlement. Understanding these changes, and how native species and entire ecosystems have responded, is crucial for biodiversity conservation and ecosystem management. Here I argue that a combination of limited historical information and a knowledge base biased towards modern ecological studies has resulted in a distorted perception of ecosystem condition, hindering the instigation of effective biodiversity conservation measures. This argument is based on recently obtained information about changes to the non‐volant mammal community, which reveals relatively recent but underreported ecological changes, including major declines in species distribution and abundance, shifts in niche utilization and associated disruption of ecosystem functions. Ultimately, many mammal species are being denied the capacity to function to the extent they did historically. Following this re‐assessment, it is evident that current forest management does not adequately address contemporary conservation dilemmas posed by detrimental ecosystem changes. This is especially salient when most of the factors responsible for causing changes to the mammal community are still active and include forest management and utilization activities. Therefore, additional conservation measures are essential to meet forest stewardship and biodiversity conservation obligations. For the health, functionality and sustainability of forested ecosystems, native mammal species must be capable of functioning to their ecological potential and occupy their original niche. This will be facilitated by the suppression of threatening processes (primarily exotic species), ensuring ecologically sensitive fire regimes and the reintroduction/translocation of missing species. The recovery or restoration of forest functionality based on mammal conservation should have wide‐scale benefits for biodiversity conservation.