共查询到20条相似文献,搜索用时 15 毫秒
2.
通过野外定枝追踪,对乌丹地区文冠果年生长周期的物候、生殖过程进行连续观测,研究了文冠果的果实生长进程与有效积温的关系、数量动态和落花落果率.结果表明:文冠果物候变化与有效积温之间存在极显著的线性函数关系;雄花花丝的伸长和花药的开裂在时间上具有先后性;文冠果果实生长发育过程中经历3次落果,授粉率为26.4%,落花率达73.6%,落果率可达92.9%,落花、落果现象十分严重;6月上中旬果实的纵径生长较快,6月中下旬果实横径生长较快,纵横径比可达2.17;个体间物候有一定的差异,不利于文冠果异株授粉和授粉率的提高. 相似文献
3.
In recent decades, community groups have transformed habitat restoration, pest control and species translocations in New Zealand. Large areas of wild New Zealand benefit hugely from ongoing management by community‐based restoration groups. Areas near cities and towns have especially good access to pools of keen volunteers. Community groups are involved in monitoring progress with their work, as well as monitoring biodiversity changes in general at their project sites. New tools powered by modern technologies are creating the opportunity for New Zealand's community volunteers to play a transformative role in biodiversity monitoring for either purpose. These tools are reducing the resources and expertise required for species detection and identification. Smartphones with cameras, GPS, audio recorders and data apps make it easier than ever to record species observations. Crowd‐sourced identification of species in photographs and sounds loaded onto NatureWatch NZ allow volunteers to make observations of a much wider range of taxa than just common birds and trees. Realising this potential requires community groups, scientists and their institutions to collaborate in building and maintaining simple, accessible monitoring systems that (i) require and promote standard monitoring methods, (ii) provide efficient data entry in standard formats, (iii) generate automated results of use to community groups and (iv) facilitate public sharing of data to contribute to regional, national and global biodiversity monitoring. Some New Zealand monitoring systems developed recently to assist community‐based restoration groups with monitoring mammalian predator control are good examples of this approach. Making this happen at a large scale across many community groups and taxa requires increased and coordinated long‐term institutional support for monitoring systems and training. 相似文献
4.
The Upwey Corridor Biodiversity Project has seen substantial investment by agencies and in‐kind voluntary work by the community over a ten year period. Comparison of Habitat Hectare scores prior to the project and after ten years showed that significant improvement in ecological condition of weed‐degraded areas is possible given adequate investment, appropriate re‐treatment and continuous management. 相似文献
5.
6.
Andrew F. Bennett Angie Haslem David C. Cheal Michael F. Clarke Roger N. Jones John D. Koehn P. Sam Lake Linda F. Lumsden Ian D. Lunt Brendan G. Mackey Ralph Mac Nally Peter W. Menkhorst Tim R. New Graeme R. Newell Tim O’Hara Gerry P. Quinn James Q. Radford Doug Robinson James E. M. Watson Alan L. Yen 《Ecological Management & Restoration》2009,10(3):192-199
Summary A common approach to nature conservation is to identify and protect natural ‘assets’ such as ecosystems and threatened species. While such actions are essential, protection of assets will not be effective unless the ecological processes that sustain them are maintained. Here, we consider the role of ecological processes and the complementary perspective for conservation arising from an emphasis on process. Many kinds of ecological processes sustain biodiversity: including climatic processes, primary productivity, hydrological processes, formation of biophysical habitats, interactions between species, movements of organisms and natural disturbance regimes. Anthropogenic threats to conservation exert their influence by modifying or disrupting these processes. Such threats extend across tenures, they frequently occur offsite, they commonly induce non‐linear responses, changes may be irreversible and the full consequences may not be experienced for lengthy periods. While many managers acknowledge these considerations in principle, there is much scope for greater recognition of ecological processes in nature conservation and greater emphasis on long time‐frames and large spatial scales in conservation planning. Practical measures that promote ecological processes include: monitoring to determine the trajectory and rate of processes; incorporating surrogates for processes in conservation and restoration projects; specific interventions to manipulate and restore processes; and planning for the ecological future before options are foreclosed. The long‐term conservation of biodiversity and the well‐being of human society depend upon both the protection of natural assets and maintaining the integrity of the ecological processes that sustain them. 相似文献
7.
Ecological connectivity, as a research method related to spatial ecology and conservation biology, has attracted increasing attention from researchers at home and abroad in recent years. Habitat connectivity, as a key link in ecological connectivity, is of great significance to promote coastal ecological restoration and protection. However, there has been less systematic research about habitat connectivity due to lack of corresponding theories and practices. Therefore, this paper discusses habitat connectivity from three aspects: (1) the concept of habitat connectivity is introduced and clarified; (2) the application of connectivity in artificial habitat and adjacent waters and its relationship with biodiversity conservation are reviewed and illustrated with examples; and (3) the future development trends of this research direction are summarized and prospected in order to provide a scientific basis and useful reference for the related work of coastal restoration projects in China. Generally, this paper argues that an increase in human behaviour irreversibly destroys the connectivity between marine habitats and threatens the spatial and temporal scales of biodiversity and ecosystem services. Therefore, the theoretical research results and practical experience of ecological connectivity should be fully applied to marine ecosystems, and the restoration of degraded ecosystems should be encouraged and supported in ways that promote natural recovery. 相似文献
8.
9.
Jeffrey A. McNeely 《Biodiversity and Conservation》1992,1(1):2-18
Humans are making increasing demands on natural ecosystems. One recent study has concluded that our species is consuming or diverting some 40% of the net photosynthetic productivity of our planet. Many habitats are being converted to simpler systems which provide more harvestable goods to people. As a result, genetic diversity, species and whole ecosystems are disappearing; some scientists suggest that as many as 25% of the world's species could be lost in the next several decades.The sinking ark is usually characterized in terms of pollution, habitat loss, poaching, introduced species and illegal trade in wildlife products, but these are symptoms rather than causes. At a more fundamental level, many of the same factors which have enabled pollution to become such a problem have also been responsible for the loss in biodiversity; the most important factor is that the effects of pollutants on biodiversity have been considered an externality, an unintended side effect of industrial activity which brought measurable benefits to people. Development activities which have depleted biodiversity have proven profitable only because the real costs have been hidden.Keeping the ark afloat will require the Five-I Approach: investigation (learning how natural systems function); information (ensuring that the facts are available to inform decisions); incentives (using economic tools to help conserve biodiversity); integration (promoting a cross-sectoral approach to conserving biodiversity); and international support (building productive collaboration for conserving biodiversity). 相似文献
10.
生境破碎是生物多样性下降的主要原因之一。通常以岛屿生物地理学、异质种群生物学和景观生态学的理论来解释不同空间尺度中生境破碎化的生态学效应。生境破碎化引起面积效应、隔离效应和边缘效应。这些效应通过影响动物种群的绝灭阈值、分布和多度、种间关系以及生态系统过程,最终影响动物种群的存活。野外研究表明,破碎化对动物的影响,因物种、生境类型和地理区域不同而有所变化,因此,预测物种在破碎生境中的存活比较困难。研究热点集中于:确定生境面积损失和生境斑块的空间格局对破碎景观中物种绝灭的相对影响,破碎景观中物种的适宜生境比例和绝灭阈值,异质种群动态以及生态系统的生态过程。随着3S技术的发展,生境破碎化模型趋于复杂,而发展有效的模型和验证模型将成为一项富有挑战性的任务。 相似文献
11.
为研究生境恢复及地形变化导致的景观异质性对退化景观中生物多样性的影响,于2006和2007年对河北坝上3个不同海拔村庄的农田生境与恢复中的禁牧草地或再造林等半自然生境的尺蛾群落采用灯诱法进行取样调查,比较不同生境的尺蛾多样性.结果表明: 两种生境类型间物种数和个体数存在显著差异、不同海拔村庄物种数也存在显著差异,但不同海拔村庄间个体数差异不显著,不同海拔村庄间以及各村庄内农田和半自然生境稀疏标准化物种数和Fisher α指数无显著差异;非度量多维标度法(NMDS)显示不同海拔的不同生境下尺蛾群落结构显著不同.地形变化导致的景观异质性对坝上地区尺蛾群落组成及多样性影响显著,而无论是恢复中的草地、再造林等半自然生境还是农田生境均是维持尺蛾多样性的重要生境.注重不同地形条件下农田生境和半自然生境景观镶嵌体的保护对维持尺蛾群落γ多样性具有重要意义,但生境恢复能否促进尺蛾群落多样性恢复尚需长期监测. 相似文献
13.
14.
Summary A large number of projects have recently been initiated in Scotland aiming to restore native woodland, which are being undertaken by a variety of organisations, often in partnership, with environmental NGOs playing a leading role. The objectives, constraints and methodologies of these projects are critically reviewed, partly through a questionnaire survey. Most aim to restore ‘natural’ woodland, but the lack of appropriate reference ecosystems and uncertainty about the characteristics of the original forest hinder the development of precise objectives, and consequently the criteria for success are poorly defined. Most projects face major practical constraints, particularly browsing by herbivores and invasion by exotic species, indicating that they will require long-term management interventions. Most woodlands are isolated from other woodlands, which threatens their long-term viability, restricting colonisation by woodland organisms. Greater reference to ecological theory in practical restoration projects such as these would enable objectives to be defined with more precision, encourage a greater emphasis on ecological processes rather than community composition, and improve management plans through use of predictive tools. In particular, the integration of woodlands into habitat networks, increasing ecological connectivity between woodland fragments, is considered essential to ensure success in the long term. 相似文献
15.
通过四合木异地播种生长量比较、以及四合木对土壤的适应性和对水热综合因子的适应性分析,得到如下结果:(1)四合木生长量高低的顺序为乌海区的东胜土(12.12g)〉乌海区的乌海土(10.62g)〉东胜区的乌海土(3.10g)〉东胜区的东胜土(2.59g)。同一地区不同土壤间四合木生长量之间没有差异(P≥0.05),不同地区相同土壤间的生长量之间却有十分显著的差异,说明了土壤条件对四合木的生存影响是次要的,气候条件是保证四合木生存的最重要的条件。(2)四合木分布区与异地保护区之间9种土壤微量元素具有差异,但由于四合木植株中的微量元素含量均高于土壤中的有效量,说明四合木对微量元素具有富集作用,土壤微量元素含量不是四合木成活与生长的限制因子。(3)四合木分布区与异地保护区之间各月平均温度差异显著;全年气温日较差以及温暖指数、寒冷指数、湿润指数和水热综合因子指数差异显著;生长季地表地温昼夜温差具有特殊性,这可能是异地保护不易成功的限制因子之一。 相似文献
16.
Ben D. Zelinsky Jason P. Karnezis Cynthia A. Studebaker Siena Lopez‐Johnston Anne M. Creason Lynne Krasnow Gary E. Johnson Ronald M. Thom 《Restoration Ecology》2018,26(2):360-369
We implemented and institutionalized an adaptive management (AM) process for the Columbia Estuary Ecosystem Restoration Program, which is a large‐scale restoration program focused on improving ecosystem conditions in the 234‐km lower Columbia River and estuary. For our purpose, “institutionalized” means the AM process and restoration programs are embedded in the work flow of the implementing agencies and affected parties. While plans outlining frameworks, processes, or approaches to AM of ecosystem restoration programs are commonplace, their establishment for the long‐term is not. This article presents the basic AM process and explains how AM was implemented and institutionalized. Starting with a common goal, we pursued a well‐understood governance and decision‐making structure, routine coordination and communication activities, data and information sharing, commitment from partners and upper agency management to the AM process, and meaningful cooperation among program managers and partners. The overall approach and steps to implement and institutionalize AM for ecosystem restoration explained here are applicable to situations in which it has been incomplete or, as in our case, the restoration program is just getting started. 相似文献
17.
Is local provenance important in habitat creation? A reply 总被引:4,自引:0,他引:4
N.R. Sackville Hamilton 《Journal of Applied Ecology》2001,38(6):1374-1376
18.
围填海造地的生态损害是指围填海造地所引致的海洋生态系统服务功能的下降,包括生物资源消失、生态调节功能减弱以及生物栖息地破坏等。针对胶州湾围填海造地规模及其生态影响,使用生境等价分析法,对围填海造地的资源和生态服务功能的受损程度和补偿规模进行了评估。结果表明,1988-2005年胶州湾填海造地的资源生态受损程度为41.33%,以退田还海作为修复工程,修复期为8a,在5%的折现率水平下,修复工程的规模应为22.47 km2,才能使被填海域的生态服务功能恢复到初始水平。这一结论可作为地方政府对胶州湾围填海造地实施生态修复建设和生态补偿管理的技术依据。 相似文献
19.
全球范围内关键生态系统服务的减少使人类社会面临巨大的威胁,生物多样性是生态系统提供各种产品和服务的基础。生态恢复工程对退化的生态系统服务和生物多样性进行修复,对于缓解人类环境压力具有非常重要的意义。长期的理论和实践工作形成了多种生态恢复措施:(1)单纯基于生态系统自我设计的自然恢复方式,(2)人为设计对环境条件进行干预,反馈影响生态系统的自我设计,(3)人为设计对目标种群和生态系统进行直接干预和重建。这3类恢复方式可以在不同程度上定向的影响生态系统的恢复进程,反映了人类对生态系统的低度、中度和高度介入。哪种恢复方式和介入程度能够实现更好的恢复效果,是生态恢复学中的一个关键问题,但到目前为止,虽广有争议,却无定量的分析和结论。针对这个空白,通过对ISI Web of Knowledge数据库中生态恢复相关文献的整合分析,基于数学统计的方法定量比较在不同条件下低度介入(自然恢复)、中度介入(环境干预)和高度介入(直接干预)3种恢复方式对生态系统服务与生物多样性的恢复效果。论文从4个方面展开研究:(1)低度、中度、高度介入生态恢复方式的划分,(2)比较3大类介入方式对生态系统服务和生物多样性恢复效果的差异,(3)不同气候条件、生态系统类型和恢复时间等背景因素的影响,(4)生物多样性恢复和生态系统服务恢复之间的关系。研究结果揭示了不同生态恢复方式的适用条件,以及对生物多样性和生态系统恢复相互关系的作用,对生态恢复实践中恢复方式的选择有指导作用。对未来的研究也有启示意义,如针对特定生态系统服务或具体研究问题进一步探索低度、中度和高度介入生态恢复方式的作用规律和机制;将地区的社会经济水平、生态系统的受损程度等因素纳入生态恢复方式的考察,以最优化生态恢复成本-效率等。 相似文献