马尾松低产林套种木荷的林地与根际土壤养分特性的研究

马尾松低产林套种木荷的混交林林地与根际土壤养分特性研究表明，木荷根际对土壤养分的活化能力大于马尾松，这利于混交林中马尾松的生长．套种后所形成的混交林根际微区对土壤养分活化程度的提高改善了两树种的养分利用状况，这可能是低产林改造后林地土壤养分高于纯林地且林分生产力提高的主要原因之一．     

兰州市土地利用变化及生态服务价值

以典型河谷型大城市兰州市为例,在RS和GIS技术支持下,剖析了1997-2009年该市各县区土地利用及其变化情况。在此基础上,参考Costanza等生态系统服务价值计算方法和中国陆地生态系统单位面积服务价值表,分析r近12年来研究区土地利用变化对生态系统服务价值的影响及其变化情况。结果表明：1997-2009年兰州市林地增长面积最大,主要来源于耕地的转出及两山绿化,其次为建设用地,主要是对耕地、草地和未利用地的占用;土地利用类型面积减少最大的是耕地,主要转变为林地、草地和建设用地。土地利用变化引起生态系统服务价值及GDP变化,其分别从1997年的59．99亿元,210．27亿元上升到2009年的61．52亿元,920亿元。总体呈增长趋势,表明该区域生态环境整体向良性方向发展。     

桂东南地区马尾松工程幼林郁闭过程的生态环境变化特征

１９９１ ～１９９６ 年,对桂东南马尾松工程幼林郁闭过程的生态环境变化进行定位观测研究．结果表明：①１ ～３ ａ 林地与灌草坡的主要气象要素无多大差别,４ ａ 后,林地逐渐显示增湿降温等良好的小气候环境,至ａ６ 基本恢复到成熟林的水平．②１～６ ａ 林地的水土流失量为３３８．５９～２１３６．９２ｔｈｍ －２ａ－１ ,径流系数２ ．１４％ ～２１．５０％ ,比灌草坡减少１２．５ ％ ～２９．４％ ,其中１ ～３ ａ 林的泥沙流失量比灌草坡增大１１２．９％ ～２１４．５ ％ ,４ ａ 后,林地泥沙流失量逐渐减少,至６ ａ 林时比灌草坡减少１８．２％ ．③６ ａ 林时的土壤物理性质比造林前有所改善,但土壤的主要养分（ 有机质、Ｎ、Ｐ、Ｋ）含量则比造林前降低４．３％ ～７．０％ ．④６ ａ 林的林木蓄积量为３６．１６ ｍ３／ｈｍ２ ,产出与投入的比值为２ ．９９ ,经济效益极为显著．     

桉树人工林生态系统养分循环与平衡研究Ⅴ.桉树林间种山毛豆对土壤肥力与林木生长的作用

桉树人工林间种山毛豆对提高土壤肥力和促进林木生长有极其显著的作用。间种5年后，林地表层土壤有机质和全量养分N、P、K的质量分数，分别为18．21kg／hm^2、0．85kg/hm^2、0．43kg／hm^2、1．30kg/hm^2，而对照林地分别为13．70kg/hm^2、0.56kghm^2、0．34kg/hm^2、1．10kg/hm^2；林地土壤有效养分含量显著提高；土壤结构和土壤水分物理性质显著改善；桉树生长量显著增加，刚果W5桉平均株高增长16％，平均胸径增长22％，单位面积的木材蓄积量增加59％。     

湖南省隆回县金银花产业现状及发展对策

介绍了隆回县金银花资源培育和加工利用现状,综合分析了金银花的综合价值和发展前景,针对当前金银花产业发展中存在的经营方式落后、加工粗放、销售不畅等问题,提出了金银花产业发展的对策.     

城市空间扩展对生态系统服务价值的影响——以南宁市区为例

以南宁市区1994～2004年土地利用统计数据为基础,参照中国陆地生态系统服务价值系数,分析了南宁市区土地利用变化特征及其对生态系统服务价值的影响。结果表明,10年来,南宁市区土地利用变化比较剧烈,建设用地增加明显,且占用耕地和林地现象较为突出,林地、草地和水田面积减少较多,园地、旱地面积增加明显;区域生态系统服务价值由1994年的8751．9×106元／a下降到2004年的8 636．5×106元／a,区域生态系统服务功能出现明显衰退。     

仙居县城乡居民消费差异的生态足迹分析

根据生态足迹理论，以浙江省仙居县为例，利用统计调查和问卷调查资料，分别计算了城乡居民生活消费的生态系统占用情况。计算结果表明，该地城市居民的生活消费所占用的生态系统是农村居民所占用的1．73倍，差异最大的是草地，其次是水域、建筑用地、化石能源和耕地，对于林地的占用则是农村居民大于城市居民。     

基于道路网络特征的建设用地扩张及其对林地景观的影响——以深圳市为例

道路作为景观廊道,与建设用地景观、林地景观之间存在着复杂的生态学联系。在道路网络迅猛扩展的同时,深圳市建设用地迅速扩张,并对林地景观产生了一定影响。基于土地利用变更调查数据,对1996-2008年快速城市化地区深圳市道路密度与建设用地扩张强度、道路密度与建设用地-林地边界动态的相互关系进行了研究。结果表明,建设用地规模与道路密度、建设用地扩张强度与道路拓展强度呈相关关系,道路网络对城市的社会经济发展有着重要的支撑能力。另一方面,研究期间深圳市林地退化严重,与建设用地接触的单个林地斑块的平均边界长度（林建边界长度）增加,建设用地-林地边界呈现出复杂化的趋势。林建边界长度与道路密度成相关关系,道路密度小于2.5 km.km-2时,道路密度越大,林建边界长度越大,建设用地景观和林地景观的生态学作用越剧烈。     

土地利用方式对土壤动物多样性的影响

为了解不同利用方式下土壤动物多样性状况及其演变,对广州市东部郊区的水稻田、蔬菜地、果园旱地和林地4种土地利用类型0～5、5～10、10～15、15～20cm土层进行了土壤动物取样调查,共获得土壤动物24683只,分别隶属于4门10纲23类。统计分析结果表明,土壤动物多样性受土地利用方式的影响明显。果园旱地和林地的个体数显著高于蔬菜地和水稻田,但果园旱地与林地、蔬菜地与水稻田之间无显著差异;果园旱地和林地的土壤动物类群数显著高于水稻田,但果园旱地与林地、林地与蔬菜地、蔬菜地与水稻田之间的差异不显著;林地和果园旱地的复杂性指数显著高于蔬菜地,但林地与果园旱地和水稻田、水稻田与蔬菜地之间的差异不显著（P〈O．05）。土壤动物的个体数和类群数量随着土壤深度的增加而明显减少,但不同土地利用方式下各层土壤动物的丰富度及其随土层加深而递减的程度则有明显不同,其中,林地和果园旱地的土壤动物在不同土层中较丰富,垂直变化比较和缓,水稻田和蔬菜地的类群数和个体数则随土层的加深而急剧减少。     

西庄河流域土地利用方式对土壤肥力影响的研究

采用野外调查、取样和实验分析相结合的方法对云南省保山市西庄河山地流域内4种主要土地利用方式（林地、耕地、茶园、灌丛）的土壤理化性质进行对比研究,讨论了不同土地利用方式对土壤肥力的影响,结果表明,不同的土地利用方式对土壤肥力具有比较明显的影响：土壤有机质和全氮质量分数变化从大到小依次为灌丛＞林地＞茶园＞耕地;磷、钾元素表现为耕地＞茶园＞林地＞灌丛;土壤阳离子交换量表现为耕地＞茶园＞灌丛＞林地;盐基饱和度表现为耕地＞灌丛＞林地＞茶园;农业耕作活动对表层土壤物理性质影响明显。     

土地利用方式对紫色土丘陵区土壤剖面碳、氮影响

采取野外调查与室内分析相结合的方法研究了紫色土丘陵区林地、撂荒地、水田、旱地土壤剖面(0～40 cm)有机碳、全氮变化特征.结果表明.有机碳、全氮均随土层深度增加而逐渐减小,且林地、撂荒地有机碳递减幅度高于水田、旱地.相对于撂荒地和旱地,水田、林地更利于有机碳、全氮的积累.林地有机碳和全氮在0～5 cm土层表现出绝对优势;随土层递增,与水田、撂荒地和旱地的差异逐渐减小.水田有机碳和全氮在大于10 cm土层显示最大值.而撂荒地有机碳和全氮仅在土壤表层高于旱地.有机碳与全氮存在显著正相关关系;w(C)/w(N)随土层深度增加而降低,且林地、撂荒地降低幅度较大.因此相对于水田、旱地,林地和撂荒地w(C)/w(N)仅在0～10 cm显示较大值.可见,土地利用方式对陆地生态系统碳、氮蓄积有明显影响,通过旱地还林或撂荒可以增加土壤特别是表层土壤对碳、氮的积累.     

Gap Crossing Decisions by Forest Songbirds during the Post-Fledging Period

Gaps in forest cover, created by agriculture, forestry, and other anthropogenic activities, are assumed to impede the movements of many forest songbirds. Little is known, however, about the reluctance of different species of birds to cross habitat gaps. We studied this by inducing birds in the post-fledging period to cross gaps of varying widths and to choose between routes through woodland or across open areas by attracting them to a recording of mobbing calls by Chickadees (  Parus atricapillus). In 278 experiments conducted in boreal forest and agricultural landscapes near Québec city, 157 birds or flocks of birds of five species were attracted. Overall, birds were twice as likely to travel through 50 m of woodland than through 50 m in the open to reach the recording. When given a choice of traveling through woodland or across a gap, the majority of respondents preferred woodland routes, even when they were three times longer than shortcuts in the open. However, species differed greatly in their response to gaps. Our results show that woodland links significantly facilitate movements of birds across fragmented landscapes.     

Reptile and arboreal marsupial response to replanted vegetation in agricultural landscapes.

We report reptile and arboreal marsupial responses to vegetation planting and remnant native vegetation in agricultural landscapes in southeastern Australia. We used a hierarchical survey to select 23 landscapes that varied in the amounts of remnant native vegetation and planted native vegetation. We selected two farms within each landscape. In landscapes with plantings, we selected one farm with and one farm without plantings. We surveyed arboreal marsupials and reptiles on four sites on each farm that encompassed four vegetation types (plantings 7-20 years old, old-growth woodland, naturally occurring seedling regrowth woodland, and coppice [i.e., multistemmed] regrowth woodland). Reptiles and arboreal marsupials were less likely to occur on farms and in landscapes with comparatively large areas of plantings. Such farms and landscapes had less native vegetation, fewer paddock trees, and less woody debris within those areas of natural vegetation. The relatively large area of planting on these farms was insufficient to overcome the lack of these key structural attributes. Old-growth woodland, coppice regrowth, seedling regrowth, and planted areas had different habitat values for different reptiles and arboreal marsupials. We conclude that, although plantings may improve habitat conditions for some taxa, they may not effectively offset the negative effects of native vegetation clearing for all species, especially those reliant on old-growth woodland. Restoring suitable habitat for such species may take decades to centuries.     

Habitat Fragmentation Effects on Trophic Processes of Insect-Plant Food Webs

Abstract:  Habitat fragmentation is the transformation of once-extensive landscapes into smaller, isolated remnants surrounded by new types of habitat. There is ample evidence of impoverished biodiversity as a consequence of habitat fragmentation, but its most profound effects may actually result from functional changes in ecological processes such as trophic interactions. We studied the trophic processes of herbivory and parasitism in insect-plant food webs composed of hundreds of species in a fragmented woodland landscape. We recorded all plant species, collected mined leaves, and reared leafminers and parasitoids from 19 woodland remnants. Herbivory and parasitism rates were then analyzed in relation to woodland size and edge or interior location. Herbivory by leaf-mining insects and their overall parasitism rates decreased as woodland remnants became smaller. For each remnant the intensity of both processes differed between edge and interior. Our results provide novel evidence of the magnitude of habitat fragmentation effects, showing they can be so pervasive as to affect trophic processes of highly complex food webs and suggesting a response associated with trophic specialization of the involved organisms as much as with their trophic level.     

Bird‐community responses to habitat creation in a long‐term,large‐scale natural experiment

Ecosystem function and resilience are compromised when habitats become fragmented due to land‐use change. This has led to national and international conservation strategies aimed at restoring habitat extent and improving functional connectivity (i.e., maintaining dispersal processes). However, biodiversity responses to landscape‐scale habitat creation and the relative importance of spatial and temporal scales are poorly understood, and there is disagreement over which conservation strategies should be prioritized. We used 160 years of historic post‐agricultural woodland creation as a natural experiment to evaluate biodiversity responses to habitat creation in a landscape context. Birds were surveyed in 101 secondary, broadleaf woodlands aged 10–160 years with ≥80% canopy cover and in landscapes with 0‐17% broadleaf woodland cover within 3000 m. We used piecewise structural equation modeling to examine the direct and indirect relationships between bird abundance and diversity, ecological continuity, patch characteristics, and landscape structure and quantified the relative conservation value of local and landscape scales for bird communities. Ecological continuity indirectly affected overall bird abundance and species richness through its effects on stand structure, but had a weaker influence (effect size near 0) on the abundance and diversity of species most closely associated with woodland habitats. This was probably because woodlands were rapidly colonized by woodland generalists in ≤10 years (minimum patch age) but were on average too young (median 50 years) to be colonized by woodland specialists. Local patch characteristics were relatively more important than landscape characteristics for bird communities. Based on our results, biodiversity responses to habitat creation depended on local‐ and landscape‐scale factors that interacted across time and space. We suggest that there is a need for further studies that focus on habitat creation in a landscape context and that knowledge gained from studies of habitat fragmentation and loss should be used to inform habitat creation with caution because the outcomes are not necessarily reciprocal.     

The transition from isolated patches to a metapopulation in the eastern collared lizard in response to prescribed fires

Habitat fragmentation often arises from human-induced alterations to the matrix that reduce or eliminate dispersal between habitat patches. Elimination of dispersal increases local extinction and decreases recolonization. These phenomena were observed in the eastern collared lizard (Crotaphytus collaris collaris), which lives in the mid-continental highland region of the Ozarks (Missouri, USA) on glades: habitats of exposed bedrock that form desert-like habitats imbedded in a woodland matrix. With the onset of woodland fire suppression, glade habitats degenerated and the woodland matrix was altered to create a strong barrier to dispersal. By 1980, lizard populations in the Ozarks were rapidly going extinct. In response to this decline, some glades were restored by clearing and burning. Starting in 1984, collared lizard populations were translocated onto these restored habitats. The translocated populations persisted but did not colonize nearby glades or disperse among one another. In 1994 prescribed woodland fires were initiated, which unleashed much dispersal and colonizing behavior. Dispersal was highly nonrandom by both intrinsic variables (age, gender) and extrinsic variables (overall demography, glade population sizes, glade areas, landscape features), resulting in different classes of lizards being dominant in creating demographic cohesiveness among glades, colonizing new glades on a mountain, and colonizing new mountain systems. A dramatic transition was documented from isolated fragments, to a nonequilibrium colonizing metapopulation, and finally to a stable metapopulation. This transition is characterized by the convergence of rates of extinction and recolonization and a major alteration of dispersal probabilities and pattern in going from the nonequilibrium to stable metapopulation states.     

Value of Semi-Open Corridors for Simultaneously Connecting Open and Wooded Habitats: a Case Study with Ground Beetles

Abstract:  To counteract habitat fragmentation, the connectivity of a landscape should be enhanced. Corridors are thought to facilitate movement between disconnected patches of habitat, and linear strips of habitat connecting isolated patches are a popular type of corridor. On the other hand, the creation of new corridors can lead to fragmentation of the surrounding habitat. For example, heathland corridors connect patches of heathland and alternatively hedgerows connect patches of woodland. Nevertheless, these corridors themselves also break up previously connected patches of their surrounding habitat and in so doing fragment another type of habitat (heathland corridors fragment woodlands and woodland strips or hedgerows fragment heathlands). To overcome this challenge we propose the use of semi-open habitats (a mixture of heathland and woodland vegetation) as conservation corridors to enable dispersal of both stenotopic heathland and woodland species. We used two semi-open corridors with a mosaic of heathland and woody vegetation to investigate the efficiency of semi-open corridors for species dispersal and to assess whether these corridors might be a suitable approach for nature conservation. We conducted a mark-recapture study on three stenotopic flightless carabid beetles of heathlands and woodlands and took an inventory of all the carabid species in two semi-open corridors. Both methodological approaches showed simultaneous immigration of woodland and heathland species in the semi-open corridor. Detrended correspondence analysis showed a clear separation of the given habitats and affirmed that semi-open corridors are a good strategy for connecting woodlands and heathlands. The best means of creating and preserving semi-open corridors is probably through extensive grazing .     

Open Corridors Appear to Facilitate Dispersal by Ringlet Butterflies (Aphantopus hyperantus) between Woodland Clearings

We studied the ringlet butterfly (Aphantopus hyperantus) in an area of woodland in eastern England. A. hyperantus occurs in open fields, rides (grassy tracks), and glades within the woodland. Mark-recapture methods showed that exchange rates of adult A. hyperantus between fields and glades can be predicted better by distance-via-rides than by direct distance. Behavioral observations showed that A. hyperantus readily moved from glades into rides but rarely moved from glades into dense woodland. The rides are likely to be corridors that act as conduits between fields and glades. In the A. hyperantus system, connectivity could reduce local extinctions and increase rates of recolonization in the event of local extinction.     

Mapping woodland vegetation in SW Ethiopia based on a hybrid model

SUMMARY

Despite the fact that indigenous inhabitants have sustainably managed the forests and woodlands for centuries, Ethiopia's woodland resources are now under severe pressure. At the request of the Ethiopian Government, in 1996/97 the Savanna Woodland Management Study Project was initiated by the German Technical Cooperation (GTZ). A detailed analysis of the woodland resources in SW Ethiopia and a vegetation map were produced. The map was generated using multispectral remote-sensing data, and provides details of the variety within Ethiopian woodlands. A hybrid data classification procedure was applied to incorporate relief and climatic conditions. After analysis of the remote sensing data by image processing, a spatial overlay was performed to incorporate the additional site condition factors. The vegetation map shows the spatial distribution of all existing woodland types in the area and enhances our knowledge of the rich biodiversity of SW Ethiopia. Such mapping gives us a better understanding of existing ecosystems and indigenous land-use systems, and hence, can lead to more sustainable management of the natural resources in the future.     

Elephants, fire, and frost can determine community structure and composition in Kalahari Woodlands.

Fire, elephants, and frost are important disturbance factors in many African savannas, but the relative magnitude of their effects on vegetation and their interactions have not been quantified. Understanding how disturbance shapes savanna structure and composition is critical for predicting changes in tree cover and for formulating management and conservation policy. A simulation model was used to investigate how the disturbance regime determines vegetation structure and composition in a mixed Kalahari sand woodland savanna in western Zimbabwe. The model consisted of submodels for tree growth, tree damage caused by disturbance, mortality, and recruitment that were parameterized from field data collected over a two-year period. The model predicts that, under the current disturbance regime, tree basal area in the study area will decline by two-thirds over the next two decades and become dominated by species unpalatable to elephants. Changes in the disturbance regime are predicted to greatly modify vegetation structure and community composition. Elephants are the primary drivers of woodland change in this community at present-day population densities, and their impacts are exacerbated by the effects of fire and frost. Frost, in particular, does not play an important role when acting independently but appears to be a key secondary factor in the presence of elephants and/or fire. Unlike fire and frost, which cannot suppress the woodland phase on their own in this ecosystem, elephants can independently drive the vegetation to the scrub phase. The results suggest that elephant and fire management may be critical for the persistence of certain woodland communities within dry-season elephant habitats in the eastern Kalahari, particularly those dominated by Brachystegia spiciformis and other palatable species.