The end of the adaptive landscape metaphor?

The concepts of adaptive/fitness landscapes and adaptive peaks are a central part of much of contemporary evolutionary biology; the concepts are introduced in introductory texts, developed in more detail in graduate-level treatments, and are used extensively in papers published in the major journals in the field. The appeal of visualizing the process of evolution in terms of the movement of populations on such landscapes is very strong; as one becomes familiar with the metaphor, one often develops the feeling that it is possible to gain deep insights into evolution by thinking about the movement of populations on landscapes consisting of adaptive valleys and peaks. But, since Wright first introduced the metaphor in 1932, the metaphor has been the subject of persistent confusion, from equivocation over just what the features of the landscape are meant to represent to how we ought to expect the landscapes to look. Recent advances—conceptual, empirical, and computational—have pointed towards the inadequacy and indeed incoherence of the landscapes as usually pictured. I argue that attempts to reform the metaphor are misguided; it is time to give up the pictorial metaphor of the landscape entirely and rely instead on the results of formal modeling, however difficult such results are to understand in ‘intuitive’ terms.

辽宁黄海海岸交错带的景观变化与设计

辽宁黄海海岸交错带的景观近几十来年变化很快,其中许多景观变化是有意识的人类活动或人工管理形成的景观设计可以看作是已经出现或即将出现的景观变化。由于这一区域海岸交错带有不同的海岸带类型,因而也就有了不同的景观设计方案。     

喀斯特峰丛洼地旱季土壤水分的空间变化及主要影响因子

基于动态监测样地(200 m×40 m)的网格(10 m×10 m)取样,用地统计学方法研究了喀斯特峰丛洼地4类典型生态景观类型旱季表层土壤(0—10 cm)水分的空间变化,通过主成分分析和相关分析,探讨了其生态学过程和机制。结果表明,沿严重、重度、中度和轻度的干扰递减梯度,喀斯特峰丛洼地产生了农作物(Ⅰ)→人工林(Ⅱ)→次生林(Ⅲ)→原生林(Ⅳ) 的4类典型生态景观格局变化,土壤水分显著提高,变异系数逐渐增大;4类生态景观类型的土壤水分均具有良好的空间自相关性,正负空间自相关距离反映了性质不同的两大斑块,Ⅰ、Ⅲ和Ⅳ下半部斑块的半径为50 m,拐点在坡地和洼地的分界处,Ⅱ的下半部斑块的半径为75 m,拐点是土地利用方式的转折点;不同景观类型空间变异特征不同,Ⅰ、Ⅱ、Ⅲ和Ⅳ的半变异函数分别符合指数模型、高斯模型、指数模型和球状模型,基台值(C0+C)升高,变程缩小,系统的空间总变异增强,其中Ⅰ和Ⅳ的\[C0/(C0+C)\]值分别为48.3%和39.4%,空间相关中等,Ⅱ和Ⅲ的\[C0/(C0+C)\]值≤25%,空间相关强烈;Kriging等值线图清楚表明Ⅰ和Ⅳ土壤水分呈凸型分布,Ⅱ呈单峰分布,Ⅲ呈凹型分布。主成分分析显示除海拔和坡位始终是影响4类生态景观类型土壤水分的主导因子外,不同景观类型的其他主导因子不同,且同一因子在不同景观类型与土壤水分的正负作用关系和相关程度也不同。因此,应根据4类典型生态景观类型土壤水分的空间变化及主要影响因子制定相应的水资源合理利用和管理策略。     

Isolated Pasture Trees and the Vegetation under their Canopies in the Chiapas Coastal Plain,Mexico1

The Coastal Plain of Chiapas (southern Mexico) was formerly covered by large tracts of subhumid tropical forests but is heavily deforested at present. In this region, 15 pastures were selected to characterize species composition of isolated trees, as well as to describe species composition, growth form patterns, and patterns of dispersal units in the vegetation growing under their canopies. The 65 recorded pasture trees belonged to 20 species and 11 families, of which Fabaceae and Moraceae were the most species-rich. Coccoloba barbadensis (Polygonaceae) and Enterolobium cyclocarpum (Fabaceae) were the most abundant and frequent trees in the studied pastures. More than half (55%) of isolated tree species were fleshy-fruited. In the vegetation sampled under pasture trees, 134 species and 45 families were found. Fabaceae and Poaceae had the largest numbers of species. Herbs were the predominant growth form (46.3%), followed by shrubs (23.9%), trees (23.1%), and lianas (2.2%); 6 species could nor be placed in any growth form category. Most species of this flora were fleshy-fruited (43.3%), followed by heavy, gravity-dispersed fruits (17.9%). The analysis of dispersal units by growth form category confirmed the prevalence of fleshy fruits, although their predominance was not so obvious among herb species. Almost half (49.2%) of the flora under pasture trees was typical of secondary vegetation; this pattern was true for herbs but not for most woody species, which were typical of primary vegetation. A numeric classification of the vegetation samples taken under pasture trees produced eight floristic groups, all of which were independent of the specific identity of pasture trees. No significant effect of dispersal unit type of pasture tree on the characteristics of the vegetation growing under them was found. Future attempts to re-create the original forest cover using isolated trees in pastures as regeneration foci should pay more attention to the maintenance of a large specific diversity independently of the dispersal types among these components of tropical landscapes.     

上海南京东路热舒适分析与评价

为探析夏热冬冷地区城市街道的空间因子对小气候与人体热舒适的影响及相互作用规律,通过对上海南京东路步行街中典型的风景园林空间按顶面遮蔽方式分为4种空间类型下的12个测点进行冬夏两季小气候实测及热舒适问卷调查,分析不同顶面遮蔽对风景园林小气候风湿热的影响差异,并结合热舒适评价指标的计算和使用者热舒适问卷,评价不同顶面遮蔽空间下人体热舒适感受。结果显示：1）根据热舒适问卷,建筑遮蔽区位于街道北侧的悬挑区在冬季最舒适,夏季最舒适的是树荫全遮蔽区;2）通过改善空间遮蔽程度与类型,根据风向与距街道十字交叉口的距离合理进行街道设计可以对街道中的太阳辐射与风环境产生显著影响,从而改善街道热舒适;3）采用生理等效温度（PET）指标计算的热中性范围冬季是16.90~28.95℃,夏季是9.05~22.57℃;4）PET评价在高温季节低估了风速对热舒适的影响,提出了基于问卷的热舒适预测方程。可为未来城市街道的舒适性规划建设提供经验与参考。     

斑块边缘效应的定量评价及其生态学意义

边缘效应是生态系统 (斑块 )边缘和生态过渡区所呈现出的生态效应。但由于景观性质、研究目标和斑块形状的变化 ,边缘效应影响的范围和程度差异较大。核心斑块与周边景观之间的相似性既可以增强边缘效应 ,也可以减弱边缘效应。正确理解和确定边缘效应的影响范围和程度直接关系到对野外环境观测数据的科学使用。许多情况下 ,由于未能正确认识一个生态系统(斑块 )的边缘效应 ,时常会将在边缘效应地区获得的数据与系统内部核心区的观测数据混淆使用 ,得出一些不科学的结论。边缘效应的定量评价对于进行科学的野外环境观测 ,及其在自然保护区功能区设计和生物多样性保护中具有重要意义。但如何定量评价生态系统 (斑块 )的边缘效应目前还缺乏科学有效的方法。从分析边缘效应的概念和影响因子出发 ,结合地理信息系统 ,提出了开展定量评价斑块边缘效应的方法 ,并探讨了定量研究边缘效应的生态学意义。     

风景园林与绿色基础设施在城市流域水资源规划中的重要作用

通过绿色基础设施途径,处理美国波士顿北部的马萨诸塞州城市流域的水资源规划问题。从多个尺度为风景园林师提供水资源规划的经验与启发,探究公众对新型绿色基础设施解决方案的态度与偏好,以及公众偏好对于整体规划设计的重要作用。     

以高绩效为目标的校园景观设计方法与实践——同济大学嘉定体育中心景观设计研究

结合景观绩效的评价与设计方法目前正被不断地探索。梳理介绍了景观绩效的相关概念以及现有量化评价实践,探讨了从景观绩效角度出发指导设计实践的途径,以同济大学嘉定体育中心景观设计为例,分析基于景观绩效理论的校园景观设计实践方法,以期为未来的校园景观建设实践提供新思路。     

人工管理和自然驱动下盐城海滨湿地互花米草沼泽演变及空间差异

将盐城国家级自然保护区核心区划分为人工管理区和自然湿地区两种模式,根据2000年、2006年、2011年3个时相的ETM+影像,运用RS、GIS技术和景观生态学方法,分析不同驱动力下互花米草沼泽景观变化的差异.结果表明:(1)人工管理区,2000-2011年,互花米草沼泽面积由272hm2增加到781hm2;平均分维数呈下降的趋势,聚合度指数呈上升的趋势,表明互花米草沼泽在空间上趋于聚集,在形状上趋于规则;从互花米草沼泽增长速率看,2000-2011年,呈现先快后慢的特征.在景观空间演变上,互花米草沼泽的平均宽度从598.679m增加到1719.002m,表现出向海陆两个方向扩张的特征.(2)自然湿地区,2000-2011年互花米草沼泽面积由2023hm2增加到3974hm2;平均分维数和聚合度指数呈先上升后下降的趋势;米草沼泽增长稳定,年增长约160-180 hm2/a,单位长度岸线年增长面积约为15 hm2· km-1·a-1左右;比较发现,自然湿地区互花米草沼泽的增长速度高于人工管理区的增长速度.在景观空间演变上,互花米草沼泽平均宽度从1625.586m增加到3193.317m,2000-2006年表现出向海洋单方向扩张的特征,2006-2011年表现出向海陆两个方向扩张的性质.(3)在自然条件下互花米草沼泽扩张受到气候、地貌过程、水文过程、植被类型及种间竞争的影响,表现出明显的带状特征.在人工管理下,通过建设拦水堤坝等,阻止了潮汐作用下海水的扩散能力,生态过程发生改变,致使生态系统类型向淡水湿地方向演变,抑制了互花米草沼泽的扩张,表现出一定的镶嵌格局.     

上海环城林带景观美学评价及优化策略

选取上海环城林带7种植物群落,采用美景度评判法,从林内景观和林外景观2个空间层次和春、夏、秋、冬4个季节,应用数量化理论Ⅰ建立了美景度和各景观因子类目之间的景观评价与预测的多元回归模型,分析了群落的结构特征和季相特征对林内景观以及外貌特征对林外景观的影响,并提出相应的优化对策。结果表明:(1)群落结构特征对林内景观的影响主要因子为胸径(平均胸径和胸径变异系数)、郁闭度和疏透度。在春季,林内美景度随着树木胸径增大而增加;在夏季,郁闭度增大会提升林内美景度;在秋季,胸径变异小的群落具有更高的林内观赏性;在冬季,疏透度对林内景观美景度影响最大。(2)群落季相特征对林内景观的影响,在各季节表现亦不同。在春季,黄色、紫色等明度较高的色相和开花量适中的群落美景度最佳;在夏季,生长势好、林冠层变化小以及树干清晰度高的群落具较高的美景度,且观花可显著提高夏季林内美景度;在秋季,色彩越纯美景度越高;而在冬季,树皮颜色深的群落美景度高。(3)群落外貌特征对林外景观有显著影响,其中林冠线对林外景观美景度影响最大,其次为林缘线。具有起伏不大林冠线和自然流畅林缘线的植物群落美景度高。旨在通过对典型植被群落不同季相的美景度评价,对上海环城林带的群落景观进行定量的评价,进而为不同情景下的群落结构优化提出相应的对策,为城市森林的群落建构与管理提供科学依据。