海岛退化生态系统的恢复

海岛在干扰极下极易退化且不易恢复,这些干扰包括毁林、引种不当和自然灾害三类。海岛恢复的限制性因子是缺乏淡水和土壤,生物资源缺乏、严重的风害或暴雨。不同大小的海岛和海岛不同部分的恢复策略不同。海岛植被恢复可参考其群落演替过程,其恢复至少是一个群落或生态系统水平的恢复。海岛恢复的长期利益包括重建海岛的生物群落,再现海岛生态系统的营养循环,恢复海岛的进化过程。海岛恢复的过程比较复杂,最关键的是要选择好适生的关键种。     

海岛退化生态系统的恢复

海岛在干扰下极易退化且不易恢复,这些干扰包括毁林、引种不当和自然灾害三类。海岛恢复的限制性因子是缺乏淡水和土壤、生物资源缺乏、严重的风害或暴雨。不同大小的海岛和海岛不同部分的恢复策略不同。海岛植被恢复可参考其群落演替过程,其恢复至少是一个群落或生态系统水平的恢复。海岛恢复的长期利益包括重建海岛的生物群落,再现海岛生态系统的营养循环,恢复海岛的进化过程。海岛恢复的过程比较复杂,最关键的是要选择好适生的关键种。     

海岛生态保护红线划定技术方法

划定海岛生态保护红线是维护海岛生态安全,协调海岛开发与保护之间矛盾的重要方法。目前,海岛生态保护红线在概念内涵、划定内容、划定方法等方面尚未统一定性,且极易与海洋生态红线的概念混淆,不同类型和形态的海岛红线划定的方法及原则要求也有所区分,例如,单岛、列岛、群岛、有居民和无居民海岛等。论述了海岛生态保护红线概念、海岛生态保护红线与海洋生态红线的区别和联系;结合生态科学、地理科学和管理科学属性,基于发展观点和底线思维阐述了海岛生态保护红线划定原则;海岛生态保护红线类型主要包括:海岛重点生态功能区、海岛生态敏感区/脆弱区和海岛禁止开发区;筛选出海岛生态保护红线划定需要重点考量的指标,提出海岛生态保护红线划定的技术路线,同时针对海岛生态保护红线区划面临的若干问题进行探讨;最后对今后海岛生态保护红线划定研究进行了展望。     

Biogeography of body size in Pacific island birds

Many insular vertebrates have undergone rapid and dramatic changes in body size compared to their mainland counterparts. Here we explore the relationship between two well known patterns of island body size – the tendency for large‐bodied species to dwarf and small‐bodied species to get larger on islands, known as the “island rule”, and the scaling of maximum and minimum body size of island assemblages with island area. Drawing on both fossil and modern data, we examined the relationship between body size and island area in Pacific island birds, both within clades and at the island assemblage level. We found that the size of the smallest bird on each island decreased with island area while the maximum body size increased with island area. Similarly, within clades the body size of small‐bodied groups decreased and large‐bodied groups increased from small to large islands, consistent with the island rule. However, the magnitude of size change within clades was not sufficient to explain the overall scaling of maximum size with island area. Instead, the pattern was driven primarily by the evolution of very large, flightless birds on large islands. Human‐mediated extinctions on islands over the past few millennia severely impacted large, flightless birds, to the effect that this macroecological pattern has been virtually erased. After controlling for effects of biogeographic region and island area, we found island productivity to be the best predictor of maximum size in flightless birds. This result, and the striking similarities in maximum body size between flightless birds and island mammals, suggests a common energetic mechanism linking body size and landmass area in both the island rule and the scaling of island body size extremes.     

人类基因组上CpG岛的定位和系统分析

为了研究CpG岛产生和消失机制以及位于基因启动子区域外的CpG岛保守性等问题,我们通过序列比对和进化保守性分析等方法,分析在人类和小鼠中保守的基因上的CpG岛。结果显示已有保守序列的突变以及序列插入删除是CpG岛产生和消失的主要原因,进一步分析发现52%的在小鼠基因组上保守序列完全缺失的CpG岛位于两个转座子之间,提示转座子所介导的序列插入是CpG岛形成和消失的重要原因。人类基因组上在启动子区域外的CpG岛中约有79%为新产生的CpG岛,显著高于启动子区域内新产生的CpG岛比例(41%)。GO分析表明与这些CpG岛相关的部分基因与神经系统发育显著相关,提示新产生的CpG岛参与神经发育过程。     

千岛湖岛屿特征与节肢动物多样性的关系

采用栅格采样法,于2006年4、5、8和10月对千岛湖库区50个不同大小岛屿中节肢动物的种类与数量进行了调查,分析了岛屿面积、海拔、形状和距离等因素对岛屿节肢动物物种丰富度的影响.结果表明:岛屿上节肢动物总物种丰富度、高扩散力物种丰富度和低扩散力物种丰富度均随岛屿面积的增大而增加,且岛屿面积与物种丰富度之间的关系符合经典岛屿生物地理学模型;节肢动物物种丰富度受岛屿面积、海拔和形状的综合影响,距离对岛屿上物种的丰富度没有显著影响;总的物种丰富度与岛屿形状指数和海拔呈显著正相关,岛屿面积和海拔与高扩散力物种的物种丰富度显著相关,而低扩散力物种与岛屿各地理因素之间的相关性均不显著.     

Vicariance and marine migration in continental island populations of a frog endemic to the Atlantic Coastal forest

The theory of island biogeography is most often studied in the context of oceanic islands where all island inhabitants are descendants from founding events involving migration from mainland source populations. Far fewer studies have considered predictions of island biogeography in the case of continental islands, where island formation typically splits continuous populations and thus vicariance also contributes to the diversity of island populations. We examined one such case on continental islands in southeastern Brazil, to determine how classic island biogeography predictions and past vicariance explain the population genetic diversity of Thoropa taophora, a frog endemic to the Atlantic Coastal Forest. We used nuclear microsatellite markers to examine the genetic diversity of coastal and island populations of this species. We found that island isolation has a role in shaping the genetic diversity of continental island species, with island populations being significantly less diverse than coastal populations. However, area of the island and distance from coast had no significant effect on genetic diversity. We also found no significant differences between migration among coastal populations and migration to and from islands. We discuss how vicariance and the effects of continued migration between coastal and island populations interact to shape evolutionary patterns on continental islands.     

热岛效应对植物生长的影响以及叶片形态构成的适应性

热岛效应是一种由于地表覆盖改变及人类活动导致的热量在城区空间范围内聚集的现象,是城市气候最明显的特征之一,随着越来越多的人口涌入城市以及伴随而生的超大城市的出现,城市热岛效应将更加凸显,这种环境温度的升高必将影响到各种景观园林植物的生理状态乃至形态结构。选取以生长在热岛点和有大量绿植覆盖的低温点的两种典型园林植物大叶黄杨和丁香作为实验材料,研究了这两种植物叶在城市热岛效应影响下,在热岛点和低温点中的形态特征。结果表明,在热岛点环境温度和二氧化碳浓度显著高于低温点,但其他环境要素差异并不显著。热岛点的大叶黄杨和丁香叶生物量分别是低温点的1.6倍和1.4倍。进一步研究表明,相较于低温点,在热岛点生长的植物叶表现出较低的比叶面积、单位重量和单位面积叶氮含量。生物量在向各部分组织分配时,热岛点的植物叶倾向于将更多的生物量分配给叶肉部分,而减少了对叶柄的生物量投入。     

Patterns of island treeline elevation – a global perspective

Treeline research has strongly focused on mountain systems on the mainland. However, island treelines offer the opportunity to contribute to the global framework on treeline elevation due to their island‐specific attributes such as isolation, small area, low species richness and relative youth. We hypothesize that, similar to the mainland, latitude‐driven temperature variation is the most important determinant of island treeline elevation on a global scale. To test this hypothesis, we compared mainland with island treeline elevations. Then we focused 1) on the global effects of latitude, 2) on the regional effects of island type (continental vs oceanic islands) and 3) the local effects of several specific island characteristics (age, area, maximum island elevation, isolation and plant species richness). We collected a global dataset of islands (n = 86) by applying a stratified design using GoogleEarth and the Global Island Database. For each island we extracted data on latitude and local characteristics. Treeline elevation decreased from the mainland through continental to oceanic islands. Island treeline elevation followed a hump‐shaped latitudinal distribution, which is fundamentally different from the mainland double‐hump. Higher maximum island elevation generated higher treeline elevation and was found the best single predictor of island treeline elevation, even better than latitude. Lower island treeline elevation may be the result of a low mass elevation effect (MEE) influencing island climates and an increasingly impoverished species pool but also trade wind inversion‐associated aridity. The maximum island elevation effect possibly results from an increasing mass elevation effect (MEE) with increasing island elevation but also range shifts during climatic fluctuations and the summit syndrome (i.e. high wind speeds and poor soils in peak regions). Investigating islands in treeline research has enabled disentangling the global effect of latitude from regional and local effects and, at least for islands, a comprehensive quantification of the MEE.     

Testing island biogeography theory with visitation rates of birds to British islands

Aim We consider three hypotheses – MacArthur and Wilson’s island biogeography theory (IBT), Lack’s habitat diversity idea and the ‘target effect’– that explain the pattern of decreased species richness on small and distant islands. Location We evaluate these hypotheses using a detailed dataset on the occurrence and abundance of terrestrial birds on nine islands off the coast of Britain and the Republic of Ireland. Methods  Unlike previous studies, we compile data on species that visit the islands, rather than just those that breed on them. We divided the species into five mutually exclusive categories based upon their migratory status and where they regularly breed: British residents, summer visitors to Britain, winter visitors to Britain, and vagrants from Europe or beyond Europe. For each species group on each island we calculated the average number of species visiting each year. We then regressed the average number of species against island area and distance to the mainland (all variables were log‐transformed). We also compared the average number of species visiting each island with the average number of species breeding on each island. Results  Average number of visiting British residents decreased significantly with increasing island distance, but showed no relationship with island area. There was no significant relationship between island area or island distance and average number of summer or winter visitors. European and non‐European vagrants likewise showed no relationship between numbers of species visiting and island distance. However, the relationship between island area and number of visiting species was significant for both these categories; as island area increases so too does the number of visiting species. Main conclusions  As predicted by IBT, there were fewer visiting species on more distant islands. There were substantially more visitors to each island than breeding species, supporting Lack’s argument that lower bird richness is not a result of varying immigration rates (as predicted by IBT) but rather a result of some other island property, e.g. fewer resources. Birds make a decision to either leave an island or stay and breed. The target effect was also clearly demonstrated by the increase in European and non‐European breeders with increasing island size.     

大陆性海岛野生植物功能性状特征及其演变趋势——以平潭岛为例

探讨海岛植物功能性状的演变机制,对福州市平潭岛和福州国家森林公园的野生植物功能性状进行了比较。结果表明,平潭岛和公园植物的共有科占总科数的63%,共有种占总种数的19%。海岛植物为适应强风、干旱、贫瘠的环境,以草本植物为主,占65.75%。海岛植物的叶级明显小于大陆植物,叶被毛植物占62.39%,并呈木质化和肉质化特征。海岛植物的繁殖能力提高,海岛植物花期长于大陆,以r-繁殖策略为主。海岛植物的传播能力提高,颖果和瘦果比例高于大陆植物,而核果和浆果比例相反;微型果为79.20%,以风力和蚁类传播为主。总体而言,大陆性海岛与大陆野生植物具有相同起源,海岛植物为适应脆弱的生态环境,其适应-繁殖-传播相关的功能性状发生演变,呈现出适应能力增强、繁殖和传播能力提高的特点。     

唐山市域1993-2009年热场变化

唐山市是河北省经济和城市化发展都很快的区域,为了给唐山市生态市规划提供生态建设空间布局依据,利用1993年8月18日和2009年8月30日的TM卫星影像,对其市域的热场变化情况进行了研究。结果表明,唐山市域热场都呈现出东部和中部热场较强、其余区域相对较较弱的空间特征。强热岛主要集中在南部的低平原湿地生态系统保护亚区和曹妃甸循环经济与生态港城建设亚区,以及中部的平原生态城镇建设亚区。从相对亮温来看,在1993年到2009年,唐山市的绿岛面积和强热岛面积增加的数量最大,分别达到了38326.05hm²和25497.81hm²,极强热岛的面积2009年是1993年相应面积的3.88倍。最稳定的热力景观斑块类型为绿岛斑块,其保持不变的面积达到了77.6%;而最不稳定的景观斑块类型为极强热岛,其发生变化的面积比例达到了97.05%;其他类型的稳定性相对较小,均低于50%。文章还从植被、土地利用、城市建设和工业发展等方面,分析了唐山市热场变化的原因。     

Relationships between the demography and distribution of two bird-dispersed plants in an island archipelago

Aim I evaluated relationships between the demography and distribution of two bird‐dispersed shrubs in an island archipelago to better understand the life history precursors of different island distributional patterns. Location Barkley Sound, Vancouver Island, British Columbia, Canada (48°80′ N, 125°20′ W). Methods The abundance and occurrence of Lonicera involucrata Rich. (Caprifoliaceae) and Ribes divaricatum Dougl. (Grossulariaceae) were measured on 69 islands measuring between 25 and 800 m². Light and soil conditions were quantified to broadly characterize changes in environmental conditions with island area and isolation. Several experiments and field observations were conducted to evaluate the life history response of each species to changes in island environments. Results Lonicera showed a typical island distribution; it increased in abundance and occurrence with island area. Ribes had a more unusual distributional pattern; it showed no differences in occurrence or abundance with island area. The distribution of both species was unrelated to island isolation. Small islands had less soil and more light than large islands, while environmental conditions were unrelated to island isolation. Lonicera had higher seed germination rates and adult survivorship in large island environments, but similar rates of seed dispersal, seedling survivorship and sapling survivorship in large and small island environments. Ribes had similar rates of seed dispersal, germination and adult survivorship in large and small island environments. However, slightly higher seedling survivorship in large island environments was offset by decreased sapling survivorship. Conclusions Demographic advantages accrued at particular life history stages were either enhanced (Lonicera) or erased (Ribes) at other life history stages. Nevertheless, overall life history trends were consistent with distributional patterns, and suggest different suites of life history characteristics promote different island distributions.     

Genetic and phylogenetic consequences of island biogeography

Abstract.— Island biogeography theory predicts that the number of species on an island should increase with island size and decrease with island distance to the mainland. These predictions are generally well supported in comparative and experimental studies. These ecological, equilibrium predictions arise as a result of colonization and extinction processes. Because colonization and extinction are also important processes in evolution, we develop methods to test evolutionary predictions of island biogeography. We derive a population genetic model of island biogeography that incorporates island colonization, migration of individuals from the mainland, and extinction of island populations. The model provides a means of estimating the rates of migration and extinction from population genetic data. This model predicts that within an island population the distribution of genetic divergences with respect to the mainland source population should be bimodal, with much of the divergence dating to the colonization event. Across islands, this model predicts that populations on large islands should be on average more genetically divergent from mainland source populations than those on small islands. Likewise, populations on distant islands should be more divergent than those on close islands. Published observations of a larger proportion of endemic species on large and distant islands support these predictions.     

The influence of geographical and ecological factors on island beta diversity patterns

Aim To investigate the importance of various island characteristics in determining spatial patterns of variations in beta diversity for various animal groups. Location Analyses are presented for 10 animal groups living on the Aeolian Islands, a volcanic archipelago in the central Mediterranean, near Sicily. Methods Three hypotheses were formulated to explain patterns of beta diversity: the target‐area–distance effect, stepping stone dispersal and island age. Matrices of inter‐island dissimilarities were constructed under each hypothesis and correlated with matrices of faunal dissimilarities using Mantel tests. For the ‘target‐area–distance effect’ hypothesis, inter‐island dissimilarities were calculated using island sizes and distances to nearest mainland areas. For the ‘stepping stone dispersal’ hypothesis, inter‐island distances were measured. Finally, for the ‘island age’ hypothesis, inter‐island dissimilarities were calculated on the basis of the geological age of the islands. Cluster analysis was used to investigate inter‐island faunal relationships. Results Support for a target‐area–distance effect was found only for birds. For these highly mobile animals, inter‐island distances had no significant effects on beta diversity. Birds are known to colonize islands by crossing large sea barriers and thus they can easily reach the Aeolian Islands, which are close to source areas (notably Sicily). Inter‐island distances had a significant role in determining patterns of beta diversity in most invertebrates. For Mollusca, Opiliones, Chilopoda, Heteroptera, coprophagous Scarabaeoidea, and Tenebrionidae, even relatively short distances preclude invertebrates from colonizing an island regularly from the mainland, and most colonization probably results from inter‐island faunal exchanges. Island age was proved to be important only for orthopterans. Main conclusions The origin of most of the Aeolian invertebrate fauna is quite recent, and species appear to have established on the islands predominantly by stepping stone dispersal. Birds, which are highly mobile organisms, follow more direct mainland–island dynamics. As further studies on other islands become available, comparative analyses will confirm whether the factors influencing variations in beta diversity in this study and their relationships with species dispersal ability are consistent across scales and geographical context.     

Experimental analysis of ventral blood island hematopoiesis in Xenopus embryonic chimeras

The frequencies and potentialities of hematopoietic stem cells from 20-hr-old Xenopus embryos were examined by transplanting cytogenetically distinct ventral blood island tissue from diploid to triploid embryos. Thirty-five-day-old larvae were examined for the presence of donor-derived cells in their erythrocyte, thymocyte, and B lymphocyte populations by analyzing DNA content using flow cytometry. These experiments demonstrated that B lymphocytes, as well as erythrocytes and thymocytes, were derived from the ventral blood island. Data obtained by transplanting graded sized pieces of ventral blood island suggested that restricted erythroid precursors were present within the region by 20 hr postfertilization. Differentiation of both B- and T-lymphoid precursors from small pieces of ventral blood island was markedly enhanced when this tissue was grafted onto peripheral areas within the blood island region. Analysis of these data using repopulation statistics suggested that circulating larval erythrocytes of ventral blood island origin were derived from six or seven precursors. Each lobe of the thymus was colonized by three precursors, one of which was ventral blood island derived.     

Characterization and expression analysis of Staphylococcus aureus pathogenicity island 3. Implications for the evolution of staphylococcal pathogenicity islands

We describe the complete sequence of the 15.9-kb staphylococcal pathogenicity island 3 encoding staphylococcal enterotoxin serotypes B, K, and Q. The island, which meets the generally accepted definition of pathogenicity islands, contains 24 open reading frames potentially encoding proteins of more than 50 amino acids, including an apparently functional integrase. The element is bordered by two 17-bp direct repeats identical to those found flanking staphylococcal pathogenicity island 1. The island has extensive regions of homology to previously described pathogenicity islands, particularly staphylococcal pathogenicity islands 1 and bov. The expression of 22 of the 24 open reading frames contained on staphylococcal pathogenicity island 3 was detected either in vitro during growth in a laboratory medium or serum or in vivo in a rabbit model of toxic shock syndrome using DNA microarrays. The effect of oxygen tension on staphylococcal pathogenicity island 3 gene expression was also examined. By comparison with the known staphylococcal pathogenicity islands in the context of gene expression described here, we propose a model of pathogenicity island origin and evolution involving specialized transduction events and addition, deletion, or recombination of pathogenicity island "modules."     

A global comparison of plant invasions on oceanic islands

Oceanic islands have long been considered to be particularly vulnerable to biotic invasions, and much research has focused on invasive plants on oceanic islands. However, findings from individual islands have rarely been compared between islands within or between biogeographic regions. We present in this study the most comprehensive, standardized dataset to date on the global distribution of invasive plant species in natural areas of oceanic islands. We compiled lists of moderate (5–25% cover) and dominant (>25% cover) invasive plant species for 30 island groups from four oceanic regions (Atlantic, Caribbean, Pacific, and Western Indian Ocean). To assess consistency of plant behaviour across island groups, we also recorded present but not invasive species in each island group.We tested the importance of different factors discussed in the literature in predicting the number of invasive plant species per island group, including island area and isolation, habitat diversity, native species diversity, and human development. Further we investigated whether particular invasive species are consistently and predictably invasive across island archipelagos or whether island-specific factors are more important than species traits in explaining the invasion success of particular species.We found in total 383 non-native spermatophyte plants that were invasive in natural areas on at least one of the 30 studied island groups, with between 3 and 74 invaders per island group. Of these invaders about 50% (181 species) were dominants or co-dominants of a habitat in at least one island group. An extrapolation from species accumulation curves across the 30 island groups indicates that the total current flora of invasive plants on oceanic islands at latitudes between c. 35°N and 35°S may eventually consist of 500–800 spermatophyte species, with 250–350 of these being dominant invaders in at least one island group. The number of invaders per island group was well predicted by a combination of human development (measured by the gross domestic product (GDP) per capita), habitat diversity (number of habitat types), island age, and oceanic region (87% of variation explained). Island area, latitude, isolation from continents, number of present, non-native species with a known invasion history, and native species richness were not retained as significant factors in the multivariate models.Among 259 invaders present in at least five island groups, only 9 species were dominant invaders in at least 50% of island groups where they were present. Most species were invasive only in one to a few island groups although they were typically present in many more island groups. Consequently, similarity between island groups was low for invader floras but considerably higher for introduced (but not necessarily invasive) species – especially in pairs of island groups that are spatially close or similar in latitude. Hence, for invasive plants of natural areas, biotic homogenization among oceanic islands may be driven by the recurrent deliberate human introduction of the same species to different islands, while post-introduction processes during establishment and spread in natural areas tend to reduce similarity in invader composition between oceanic islands. We discuss a number of possible mechanisms, including time lags, propagule pressure, local biotic and abiotic factors, invader community assembly history, and genotypic differences that may explain the inconsistent performance of particular invasive species in different island groups.     

Nestedness in island faunas: novel insights into island biogeography through butterfly community profiles of colonization ability and migration capacity

Aim To relate variation in the migration capacity and colonization ability of island communities to island geography and species island occupancy. Location Islands off mainland Britain and Ireland. Methods Mean migration (transfer) capacity and colonization (establishment) ability (ecological indices), indexed from 12 ecological variables for 56 butterfly species living on 103 islands, were related to species nestedness, island and mainland source geography and indices using linear regression models, RLQ analysis and fourth‐corner analysis. Random creation of faunas from source species, rank correlation and rank regression were used to examine differences between island and source ecological indices, and relationships to island geography. Results Island butterfly faunas are highly nested. The two ecological indices related closely to island occupancy, nestedness rank of species, island richness and geography. The key variables related to migration capacity were island area and isolation; for colonization ability they were area, isolation and longitude. Compared with colonization ability, migration capacity was found to correlate more strongly with island species occupancy and species richness. For island faunas, the means for both ecological indices decreased, and variation increased, with increasing island species richness. Mean colonization ability and migration capacity values were significantly higher for island faunas than for mainland source faunas, but these differences decreased with island latitude. Main conclusions The nested pattern of butterfly species on islands off mainland Britain and Ireland relates strongly to colonization ability but especially to migration capacity. Differences in colonization ability among species are most obvious for large, topographically varied islands. Generalists with abundant multiple resources and greater migration capacity are found on all islands, whereas specialists are restricted to large islands with varied and long‐lived biotopes, and islands close to shore. The inference is that source–sink dynamics dominate butterfly distributions on British and Irish islands; species are capable of dispersing to new areas, but, with the exception of large and northern islands, facilities (resources) for permanent colonization are limited. The pattern of colonization ability and migration capacity is likely to be repeated for mainland areas, where such indices should provide useful independent measures for assessing the conservation status of faunas within spatial units.