北京市郊区可持续景观生态规划及 优化生态生产范式研究——以昌平区为例

北京市郊区可持续景观生态规划及优化生态生产范式研究是指要遵循区域自然地理要素的分异规律，以土地利用现状格局为基础，以景观生态学原理和可持续发展准则为理论指导，以景观空间分析为具体研究内容来揭示区域土地利用类型结构、功能的异质性和有序性，以期提出优化的土地利用格局。本论文主要通过大量数据、图件的收集、野外考察与调查，文献查阅与数据处理、分析，得出以下主要结论： 一、理论方面 基于景观生态学理论——景观要素，空间结构与生态学过程，景观动态，异质性，等级结构，连接度以及景观的时空性等，以北京地区为例阐述了景观生态学理论如何合理地整合于生态建设与保育之中，并重点阐释了北京生态建设与保育“小三圈”格局的结构与功能，该系统包括山区外圈层、郊区平原中圈层和城区内圈层，其目标要实现：(1)山区发挥以水源涵养、水土保持防护为主的生态功能;(2)郊区创建农田、林地、草地异质性的人工稀树草原景观，形成带、网、片、点相结合的绿网系统;(3)城区以自身绿化和美化为主。同时，本研究针对我国的区域可持续发展进一步提出更加有效的建设性意见：(1)开展区域生态适宜性评价;(2)区域水平的土地利用格局、动态以及预测性研究;(3)进行区域可持续景观生态规划，建立区域优化生态生产范式，最终实现可持续发展目标。 二、研究方法方面 利用空间自相关指数，并结合“城-郊-乡”梯度分析法研究景观格局对尺度（包括粒度、幅度、方向）变化的响应。得出以下主要结论： 1、景观格局对于尺度变化有着不同的响应，随着空间粒度的增加，空间自相关均呈下降趋势;随着幅度的增加，空间自相关基本不变;人类干扰较多的景观几乎不受“划区效应”的影响;不同的数据类型，同一数据类型的不同景观对于尺度的变化均有着不同的响应。 2、沿“城-郊-乡”样带，空间自相关呈阶梯状增加趋势。景观空间自相关大小顺序：林牧景观>林果景观>农田景观>都市景观>都市化景观，人为干扰较多的景观具有较低的空间自相关，但对尺度的变化表现出较强的敏感性。 三、实例研究 北京市郊区可持续景观生态规划及优化生态生产范式研究是以昌平区为例，从昌平区经济与产业结构现状分析出发、以昌平区土壤理化性状分析为背景，以景观格局现状、动态，以及土地利用内部转移格局与过程、驱动因素分析为主要内容，并且重点探讨了昌平区城镇化的过程特征及空间特征，得出以下主要结论： 1、昌平区GDP配比方式，以及昌平区农村GDP结构模式均为“三二一”。昌平区在北京市农业中的地位，以及农业在昌平区GDP中所处地位均弱化。截止2001年，昌平区农业产值中，牧业>种植业>渔业>林业，牧业居于首位，占到46.70%，而传统种植业也正以小汤山为龙头向现代化、高科技、高效化的“六种农业”转化。总体讲，农业的粮食生产功能在昌平区已不再是一个重要功能，传统种植业正逐步地让位于畜牧业（人工牧草）、林业（疏林、苗圃），突出体现了具有良好生态学效益的牧草、林果在未来大农业发展中的战略地位。 2、昌平土壤肥力状况良好，景观分区与土壤理化性质是吻合的。基于土壤理化基质，昌平区应形成林、灌、草为主的山区景观，园林式城镇、林、果、灌相结合的山前倾斜平原景观，以及农、林、草配置的生态农业景观和花卉、种苗、绿化带相辉映的绿色生态住宅景观。 3、从1989~2001年期间，研究区内土地利用景观经历了很大的变化。土地利用景观的量变主要体现在城镇用地的迅速扩张和耕地的锐减，而土地利用类型的变化则体现在水田、传统菜地的逐渐消失，以及2001年后人工牧草的大面积推广种植。景观格局在不同景观分区的差异也得以论证，中北部山麓平原卫星城镇、旅游林果区（III）具有最高的多样性和最低的优势度、聚集度，中南部平原高科技、都市生态农业区（II）的多样性最低，而优势度、聚集度最高，对于南部平原都市边缘、城镇住宅区（I）各指标则介于III和II区之间。 4、从1989~2001年期间，土地利用的内部转移主要体现在耕地向城镇用地的大面积转移，其次，传统菜地转向城镇用地和其他种植耕地，而人工牧草是由部分耕地转移而来的。城镇化、水资源短缺和农业政策是主要驱动因素。土地利用的内部转移具有明显的区域差异，中北部山麓平原卫星城、旅游林果区体现出卫星城镇的发展，南部平原都市边缘住宅区则反映出北京都市边缘的向外扩张，而中南部平原高科技都市农业区则正向现代化的、高科技都市农业示范区发展。 5、昌平区三种主要的城镇化模式，即都市边缘带状城镇扩展模式、交通主轴线状城镇扩展模式和卫星城面状城镇扩展模式。研究表明，昌平区的城镇化主要集中在1989~1996年期间。 基于昌平区的产业与经济结构现状，土壤养分状况，景观结构现状、动态，土地利用转移方向，并且结合昌平区自然地理分异规律，社会经济因素对昌平区进行了可持续景观规划，昌平区应遵循的四个景观分区为：北部中低山生态保护、生态旅游区;中北部山麓平原卫星城镇、旅游林果区;中南部平原高科技、都市生态农业区;南部平原都市边缘、城镇住宅区。 最后作为总结、归纳，我们提出昌平区优化生态生产范式，昌平区的发展应定位于（1）生态环境保护与水源涵养的生态功能;（2）教育、示范、创新功能;（3）生活功能，并且遵循自然地域分异规律原则、因地制宜原则、生态主导性原则、统筹兼顾原则，大力发展昌平区经济的优势产业，即畜牧业、林果业和旅游业，突出肉羊、苹果、牧草和林木种苗等四个具有昌平特色的主导产业。 景观生态学;景观空间格局;可持续景观生态规划;土地利用变化;优化生态生产范式;北京昌平区

基于景观格局变化评价的梯级水电开发规划方案研究

根据景观生态学理论,借助地理信息系统工具,采用定量的方法分析工程景观格局状况,通过建立水电开发建设规划方案的景观格局变化评价的指标体系和评价方法,研究水电开发规划方案对区域景观格局的影响。本方法应用于黄河上游黑山峡河段水电开发建设方案析分析。结果表明:不同规划方案实施后对原有生态环境均产生了一定影响。通过对不同方案与研究区域生态现状进行灰色关联分析,红山峡、五佛、小观音和大柳树4个坝址均修建低坝的方案的景观格局指数最高,研究区域景观生态风险最小。最终确定该方案为最优方案,该方案对区域原有生态体系性质和功能影响较小。

中国新疆塔里木河中下游河流廊道的景观生态学研究

中国西部干旱区是干旱区研究的天然实验场。塔里木河是西部干早区重要的生态河流。塔里木河中下游尉犁一若羌段以沙地景观为基质，以河渠、公路、防护林为连接廊道，草地、盐碱地、湿地、耕地为镶嵌斑块，是典型的干旱区河流廊道景观区域，是南疆第一大城市库尔勒与未来重建的新楼兰的唯一景观廊道，在塔里木河流域的可持续发展中起着重要的连通作用。本文以塔里木河下游绿色走廊为主体的塔里木河中下游河流廊道区域为研究对象，在区域景观生态特征的认识和景观生态建设方略的探讨上，具有重要意义。本文在景观生态学的应用研究中，注重其理论体系的构建。（1）全面收集国内外景观生态学研究的最新进展，提出景观生态学研究的核心研究框架与原理，阐明景观生态学研究的热点和新的领域。干旱区多功能景观研究，有着极其广阔的理论与实践上的创新潜力。根据以往研究成果，揭示中国西部干旱区的景观生态特征，展望其关键研究领域的前景和方向，其中绿洲研究、湿地研究、廊道研究和景观生态建设研究，各具特有的角度，又有相互的联系，最具景观生态学研究的特质和潜质。（2）收集卫星影像资料并进行解译（1980年MS航片校正、1990年TM、2000年TM），以土地利用类型为基础，以塔里木河中下游河流廊道区域现状为参照，建立了干早区河流廊道景观区域景观生态分类体系，结合野外植被和土壤调查，以及相关图件，全面研究了各类研究区景观的土壤和植物生态属性与功能特征。（3）通过景观格局指数的计算，以及景观类型的转换矩阵，揭示20世纪80年代以来区域廊道景观格局的变化过程与趋势，结合区域水资源、生态及人文变化，对变化的驱动力因子进行研究。在区域景观尺度上，构建景观生态空间分析模式，包括格局指数分析、转移矩阵分析和空间过程分析，并以此寻求区域景观格局变化的驱动力。（4）应用景观生态学原理，确定景观生态功能区划的原则，构建其区划系统。据此划分了三个景观生态功能类型区：①尉犁一卡拉水库段塔里木河一孔雀河中游城镇一绿洲农业区，②卡拉水库一大西海子水库塔里木河下游上中段农垦绿洲区，③大西海子水库一台特玛湖一若羌塔里木河下游下段一车尔臣河下游生态重建和恢复区。通过景观格局指数，对比不同功能区的景观生态差异；根据不同景观生态功能区，不同宽度的河流廊道缓冲带景观格局指数的分析，以及次一级廊道指数的计算，揭示景观廊道区域相关指数的变化规律及其廊道效应。（5）根据干旱区景观生态特点，建立干旱区生态环境质量评价概念模型，以研究区为案例，提出基于遥感和GIS的景观生态环境质量现状与预警指标体系，采用层次分析法，对塔里木河中下游以河流廊道为特征的研究区域进行景观生态评价分析。（6）在了解廊道区域景观时空变化驱动力的基础上，对不同的生态治理方式的景观生态效应进行分析，提出塔河中下游河流廊道区域“大塔里木河”景观生态建设的总体原则（包括减少对沙地基质的干扰，充分利用和适度开发草地资源，保护和恢复湿地景观的多功能性，畅通输水过程以稳定和增加植被覆盖及其多样性与经济性，通过节水灌溉和重视排水减轻次生盐渍化程度），及其相应的景观生态工程设计，确定不同景观生态功能区的景观生态建设与设计的模式与途径（包括生态恢复、生境更新与调整、生态功能重建和生态移民）。

若尔盖自然保护区高原林蛙(Rana kukunoris)扩散模型与景观连接分析

揭示水体中繁殖的两栖动物在异质性景观中的空间扩散特点，探讨景观面积丧失和破碎化对于两栖动物的影响，为两栖动物的保护提供理论依据。本文以四川西北部若尔盖湿地自然保护区的高原林蛙(Rana kukunoris)为研究对象，通过运用地理信息系统及建立景观模型等方法，在分析若尔盖湿地自然保护区范围内现有景观格局的基础上，建立了高原林蛙的景观扩散模型，并模拟了“沼泽→草甸”的湿地逆演化过程下高原林蛙的空间分布与景观连接的变化特点。主要结果是： 1．若尔盖湿地自然保护区呈典型的沼泽—草甸式斑块—基质景观格局。草甸面积占整个景观面积的79.42%，景观蔓延度指数（CONTAG）为79.00远离最小值0而更趋向于最大值100，面积和景观蔓延度指数表明草甸是整个景观中面积占绝对优势且景观连接好的类型，构成了景观的基质，对景观的动态格局演变起主导作用。沼泽面积仅占整个景观面积的18.08%，但却是整个景观中斑块数目最多的单元，占所有斑块数的82.9%。因此沼泽斑块与草甸基质之间的动态结构对高原林蛙的扩散起着决定性的作用。 2．空间扩散模型表明，其它类型的景观不但扩展了高原林蛙的活动范围，而且也为高原林蛙在不同沼泽斑块间的连接提供了通道。高原林蛙的空间扩散区域使得彼此间成斑块化隔离状分布的沼泽形成了潜在景观功能连接，促进了不同斑块间物种的交流。小型沼泽作为垫脚石（stepping-stone），使得整个景观中的相隔距离较远的大型斑块联结为一个功能整体，促进了高原林蛙在整个景观中的相互动态联系。 3．模拟“沼泽→草甸”的湿地逆演化过程表明，大量小型沼泽湿地的消失将会 对在沼泽中繁殖并扩散到其它景观类型中去的高原林蛙造成潜在影响。逆演化过程不仅使沼泽斑块的分布范围，沼泽源斑块的面积和空间扩散面积减少，而且对景观连接也有很大影响。小型沼泽的消失，将使得景观斑块的功能连接变小，使得依靠小型沼泽作为跳板的动物在沼泽斑块之间的移动将变得更加困难。 本文是对生境丧失与破碎化影响下两栖动物的行为反应的一种尝试。影响模型的因素很多，包括动物对各种类型景观的偏好程度，地理数据的精度，及模型的可靠程度都是制约模型准确度的因素。 The spatial diffusion of water—breeding amphibian through heterogeneous landscape and the effects of landscape losing and fragmentation to amphibian were the core theory of the landscape ecology of amphibian. Geographical information system (GIS) and landscape model were used to model the diffused area of Rana kukunoris in Zoige Wetland Natural Reserve. Model was also used to analysis the spatial distribution variation of R. kukunoris and the change of landscape connectivity when simulated the retrogressive succession of landscape. The main results are below: 1. There was peatland—meadow pattern which was typical patch—matrix landscape pattern in Zoige Natural Reserve. The meadow area occupied 79.42% of the entire landscape area, contagion index (CONTAG) was 79.00 which was far away the minimum value (0) but tend to the maximum value (100). Both of these showed that meadow was the largest part and the most continue units. It was shown that meadow was matrix of the landscape, which evolved the leading role to the landscape dynamic pattern. Though their area only occupies 18.08% of entire landscape area, peatlands were according to 82.9% of the total patches. Dynamic of the pattern between peatlands and meadows decided the spatial diffusion of R. kukunoris. 2．The model indicated that the other types of landscape not only expanded diffusion of R. kukunoris, but also have provided the potential channels for frog's connections among different peatlands. The spatial diffusion zone of R. kukunoris forced isolated patch peatlands to be potential landscape functional connectivity. The small peatlands, as stepping-stone, made the large peatlands connect as a functional one and promoted the integrated and dynamic connectivity of R. kukunoris in the whole landscape. 3. The simulation of “peatlands→meadows”retrogressive succession process indicated that the decrease of small peatlands will have potential effect to R. kukunoris because they must bred in peatlands and diffuse to other type of the landscape. Retrogressive succession process not only made the decrease of distribution of peatlands, patches number of peatlands and diffused area of R. kukunoris, but also reduced the connectivity among source patches. As stepping-stone, the disappearance of small peatlands will made the migration of R. kukunoris among patches more difficult. The model was an experiment of the amphibian behavior reaction to habitat losing and fragmentation. There were many factors that could influence the accuracy of model, such as the preference of animals to each type of landscape, the geographical data precision, reliable degree of model.

景观农业研究的兴起及其实际意义

Landscape agriculture is the combination of landscape ecology and agriculture. Its basic idea is from the system theory and landscape ecology. Now landscape agriculture is getting more and more attention because of its multi-functional roles. For example, it can exploit the agricultural ecosystem more rationally, make full use of the self-adjustment function of the natural patches and corridors in the field, as well as the effects from landform types and topological components. It uses regenerative biological energy to a large extent, constitutes beautiful scenic view and protects the diversity of genetics, species, ecosystems and landscapes. Landscape agriculture emphasizes environment improvement, bio-diversity protection and tourism development, thus provides new possibility for the increase of economical benefits and gets the positive feedback loop started. An example from the former Soviet Union is presented as well in this paper

欧洲景观条约与景观生态学研究

In view of the growing social demand, the Council of Europe's Congress of Local and Regional Authorities (CLRAE) drew up the European Landscape Convention to promote landscape protection, management and planning, and to organize European co-operation on landscape issues in Europe. This paper summarizes the properties, origins, structure and content of the convention, and discusses the definitions on landscape and landscape policy to which the convention refers. Moreover, this paper sums up and concludes the perspective of landscape ecology in Europe.

Modelling the long-term sustainability of indigenous hunting in Manu National Park, Peru: landscape-scale management implications for Amazonia

P> Widespread hunting throughout Amazonia threatens the persistence of large primates and other vertebrates. Most studies have used models of limited validity and restricted spatial and temporal scales to assess the sustainability. We use human-demographi

A data-model fusion approach for upscaling gross ecosystem productivity to the landscape scale based on remote sensing and flux footprint modelling

Chinese Academy of Sciences ; National Science Foundation of China [41071059]; National Key Technology R&D Program of China [2008BAK50B06-02]; National Basic Research Program of China [2010CB950900, 2010CB950704]; Natural Sciences and Engineering Research Council of Canada

Landscape change detection of the newly created wetland in Yellow River Delta

Four models are employed in the landscape change detection of the newly created wetland. The models include ones for patch connectivity. ecological diversity, human impact intensity and mean center of land cover. The landscape data of the newly created wetland in Yellow River Delta in 1984, 1991, and 1996 are produced from the unsupervised classification and the supervised classification on the basis of integrating Landsat TM images of the newly created wetland in the four seasons of the each year. The result from operating the models into the data shows that the newly created wetland landscape in Yellow River Delta had a great chance. The driving focus of the change are mainly from natural evolution of the newly created wetland and rapid population growth, especially non-peasant population growth in Yellow River Delta because a considerable amount of oil and gas fields have been found in the Yellow River Delta. For preventing the newly created wetland from more destruction and conserving benign Succession of the ecosystems in the newly created wetland, six measures are suggested on the basis of research results. (C) 2003 Elsevier Science B.V. All rights reserved.

Burrowing rodents as ecosystem engineers: the ecology and management of plateau zokors Myospalax fontanierii in alpine meadow ecosystems on the Tibetan Plateau

1. Plateau zokors, Myospalax fontanierii, are the only subterranean herbivores on the Tibetan plateau of China. Although the population biology of plateau zokors has been studied for many years, the interactions between zokors and plants, especially for the maintenance and structure of ecological communities, have been poorly recognized. In the past, plateau zokors have been traditionally viewed as pests, competitors with cattle, and agents of soil erosion, thus eradication programmes have been carried out by local governments and farmers. Zokors are also widely and heavily exploited for their use in traditional Chinese medicine.2. Like other fossorial animals, such as pocket gophers Geomys spp. and prairie dogs Cynomys spp. in similar ecosystems, zokors may act to increase local environmental heterogeneity at the landscape level, aid in the formation, aeration and mixing of soil, and enhance infiltration of water into the soil thus curtailing erosion. The changes that zokors cause in the physical environment, vegetation and soil clearly affect the herbivore food web. Equally, plateau zokors also provide a significant food source for many avian and mammalian predators on the plateau. Zokor control leading to depletion of prey and secondary poisoning may therefore present problems for populations of numerous other animals.3. We highlight the important role plateau zokors play in the Tibetan plateau ecosystem. Plateau zokors should be managed in concert with other comprehensive rangeland treatments to ensure the ecological equilibrium and preservation of native biodiversity, as well as the long-term sustainable use of pastureland by domestic livestock.