Effects of starvation on larval growth, survival, and metamorphosis of Manila clam Ruditapes philippinarum

The effects of starvation on larval growth, survival, and metamorphosis of Manila clam Ruditapes philippinarum at the temperature of 19.6–21.6 °C, the salinity of 34‰ and pH of 8.0 were investigated from May 18 to July 18, 2006. In this study, the early, middle and late umbo-veliger larvae with the shell lengths of 100, 140, and 190 μm were subject to temporary food deprivation for up to 4.5, 20, and 25d at 0.5, 4, 5d intervals, followed by refeeding for the remaining of a 24, 20, 25d period, respectively. The results suggested that the larvae should have shown considerable tolerance to starvation due to their endogenous and exterior nutrition material, for larvae and time to the point-of-no-return (PNR: the threshold point during starvation after which larvae could no longer metamorphose even if food is provided) were calculated to be 4.25, 17.54, and 22.17d. As the starvation period prolonged, the mean shell length of larvae starved got close to constants at 1.5, 4, and 15d after starvation, which were different for larvae at different stages when starvation began, survival of larvae decreased, and was lower in treatments starved earlier in development than those starved later, for the early, middle and late umbo-veliger larvae, after 4.5, 20 and 25d of starvation period, few larvaes were alive. After starvation period, the alive larvaes were able to metamorphose and had a capability of compensatory growth when refeeding was given. Starvation not only affected metamorphosis rate, but also caused the delay in the time to metamorphosis and the decrease in the metamorphosed sizes. For example, for the continuously-fed larvae, duration to metamorphosis was 20.7d, for larvae with a size of 100-μm starved for up to 4d, larvae with a size of 140-μm starved for up to 16d, larvae with a size of 190-μm starved for up to 20d, duration to metamorphosis were 29.7, 31.7, and 37.7d, the delay in duration to metamorphosis were 9, 11, and 17d, respectively. Furthermore, importance of nutrition material for maintaining larval survival during starvation and the compensatory growth on larvae at the same feeding time were discussed.     

Effects of starvation on larval growth, survival, and metamorphosis of Manila clam Ruditapes philippinarum

The effects of starvation on larval growth, survival, and metamorphosis of Manila clam Ruditapes philippinarum at the temperature of 19.6–21.6 °C, the salinity of 34‰ and pH of 8.0 were investigated from May 18 to July 18, 2006. In this study, the early, middle and late umbo-veliger larvae with the shell lengths of 100, 140, and 190 μm were subject to temporary food deprivation for up to 4.5, 20, and 25d at 0.5, 4, 5d intervals, followed by refeeding for the remaining of a 24, 20, 25d period, respectively. The results suggested that the larvae should have shown considerable tolerance to starvation due to their endogenous and exterior nutrition material, for larvae and time to the point-of-no-return (PNR: the threshold point during starvation after which larvae could no longer metamorphose even if food is provided) were calculated to be 4.25, 17.54, and 22.17d. As the starvation period prolonged, the mean shell length of larvae starved got close to constants at 1.5, 4, and 15d after starvation, which were different for larvae at different stages when starvation began, survival of larvae decreased, and was lower in treatments starved earlier in development than those starved later, for the early, middle and late umbo-veliger larvae, after 4.5, 20 and 25d of starvation period, few larvaes were alive. After starvation period, the alive larvaes were able to metamorphose and had a capability of compensatory growth when refeeding was given. Starvation not only affected metamorphosis rate, but also caused the delay in the time to metamorphosis and the decrease in the metamorphosed sizes. For example, for the continuously-fed larvae, duration to metamorphosis was 20.7d, for larvae with a size of 100-μm starved for up to 4d, larvae with a size of 140-μm starved for up to 16d, larvae with a size of 190-μm starved for up to 20d, duration to metamorphosis were 29.7, 31.7, and 37.7d, the delay in duration to metamorphosis were 9, 11, and 17d, respectively. Furthermore, importance of nutrition material for maintaining larval survival during starvation and the compensatory growth on larvae at the same feeding time were discussed.     

Post-fire ecological succession: A theoretical modeling framework

Fire is considered as an extreme disturbance in Mediterranean grasslands or shrublands as it often brings about many sudden changes in the vegetation structure, composition, and diversity patterns. In addition, it creates opportunities for exotic plant species to establish successfully in foreign habitat, and to outperform dominating native species. Monitoring and simulating post-fire successional changes, therefore, are essential tasks to efficiently restore native grasslands or shrublands. In this paper, we develop a theoretical framework for simulating fire-induced successional changes, mainly for Mediterranean vegetation, based on a three-level hierarchy of successional causes. Within this proposed framework, fire effects are considered by associating it with the number of burned sites open-up and specific changes at the burned sites relative to unburned sites. Three distinct site-specific neighborhoods are constructed; changes within each neighborhood allow sequential replacement of plant species by another plant species with greater maximum size, age and lower maximum growth rates and dispersal abilities. The proposed framework can be used to develop a spatially explicit individual-based model which will be useful for monitoring and predicting successional changes and hence for restoring native grasslands or shrublands.     

Effects of starvation on growth, survival, and body biochemical composition among different sizes of Manila clam Ruditapes philippinarum

A study was conducted to investigate the impact of starvation on different sizes of Manila clam Ruditapes philippinarum (0.66 ± 0.11, 2.12 ± 0.38, and 11.65 ± 0.84 mm in shell length, respectively) in the summer of 2008. Different size clams were starved for 7, 15, 30, 45, and 60 d, respectively, and followed by refeeding for 30 d. During the study, the water temperature ranged 26.2–28.4 °C, salinity 22–24‰, and pH 7.80–8.12. Compensatory growth occurred in the smallest size-group after 7 and 15 d of starvation, respectively. The point-of-no-return (PNR₅₀) was determined to be 18.7 d. However, no compensatory growth was noted in the medium size-group, and the PNR₅₀ for this group was 25.2 d. The complete compensatory growth was observed for the largest size-group following food depravation for 7 and 30 d, respectively. In the same group, over-compensatory growth occurred 15 d post-starvation. The PNR₅₀ for the largest size-group was 46.3 d. The survival rate of different groups decreased as the starvation time prolonged. To discuss the change in body biochemical composition of individuals in the process of starvation and refeeding, the biochemical composition of the largest group individuals at different stages was determined. There were no significant differences in moisture and ash concentrations of the largest size-group during starvation and refeeding (P > 0.05). The relative body protein content increased as the starvation period prolonged and the level returned to normal after refeeding. The lipid content of the clam at the end of starvation was significantly lower than the initial level (P < 0.05), and remained below the initial level at end of the refeeding period.     

Effects of starvation on growth, survival, and body biochemical composition among different sizes of Manila clam Ruditapes philippinarum

A study was conducted to investigate the impact of starvation on different sizes of Manila clam Ruditapes philippinarum (0.66 ± 0.11, 2.12 ± 0.38, and 11.65 ± 0.84 mm in shell length, respectively) in the summer of 2008. Different size clams were starved for 7, 15, 30, 45, and 60 d, respectively, and followed by refeeding for 30 d. During the study, the water temperature ranged 26.2–28.4 °C, salinity 22–24‰, and pH 7.80–8.12. Compensatory growth occurred in the smallest size-group after 7 and 15 d of starvation, respectively. The point-of-no-return (PNR₅₀) was determined to be 18.7 d. However, no compensatory growth was noted in the medium size-group, and the PNR₅₀ for this group was 25.2 d. The complete compensatory growth was observed for the largest size-group following food depravation for 7 and 30 d, respectively. In the same group, over-compensatory growth occurred 15 d post-starvation. The PNR₅₀ for the largest size-group was 46.3 d. The survival rate of different groups decreased as the starvation time prolonged. To discuss the change in body biochemical composition of individuals in the process of starvation and refeeding, the biochemical composition of the largest group individuals at different stages was determined. There were no significant differences in moisture and ash concentrations of the largest size-group during starvation and refeeding (P > 0.05). The relative body protein content increased as the starvation period prolonged and the level returned to normal after refeeding. The lipid content of the clam at the end of starvation was significantly lower than the initial level (P < 0.05), and remained below the initial level at end of the refeeding period.     

A theoretical framework of ecological phase transitions for characterizing tree-grass dynamics

This paper describes a theoretical framework of ecological phase transitions for modeling tree-grass dynamics and analyzing the shifts or phase transitions from one vegetation structure to another in the southern Texas landscape. This framework implements the integration of percolation theory, fractal geometry and phase transition theory as a method for modeling the spatial patterns of tree-grass dynamics, and nonlinear Markov non-equilibrium thermodynamic stability theory as a method for characterizing temporal tree-grass dynamics and phase transition. An historical sequence of aerial photographs at a Prosopis - thornscrub savanna parkland site in southern Texas was used to determine the parameters of the models. The preliminary analytical result accords well with current understanding and field survey of vegetation dynamics in the southern Texas landscape. The potential of such approaches and other relevant theories such as self-organized criticality and synergetics to vegetation dynamics is also discussed.     

完全或部分的食物剥夺对中华鳖(Pelodiscus sinensis)幼体补偿生长反应的影响:生长率的时间变化模式与体组成的变化

为了探究中华鳖（Pelodiscus sinensis）幼体的补偿生长能力,我们对中华鳖幼鳖（平均湿重9．56g）进行如下6种处理：饥饿0（对照）、1、2、3、4周,或者食物限制4周,即只投喂体湿重百分之一的食物;然后对各组进行饱食处理直到10周的实验结束为止。结果发现在饱食期的第一周各饥饿处理组的特殊生长率均显著高于对照组（P〈0．05）,但是终体重均没有赶上对照组。当饥饿或食物限制结束时,脂肪含量随着饥饿期的延长而降低,灰分和水分则表现出相反的变化趋势：脂肪含量显著低于对照（P〈0．05）,而灰分和水分则显著高于对照（P〈0．05）。蛋白含量则没有显著变化（P〉0．05）。实验结束时,除了灰分外（P〈0．05）,其他个体组成指标均恢复到对照组的水平。以上结果表明中华鳖幼体在饥饿胁迫下首先利用脂肪作为主要能源以维持生存,以及在该研究条件下完全的食物剥夺可以诱发其部分补偿生长反应．而部分食物剥夺则不能诱发此反应。     

基于生态系统服务供需的城市群生态安全格局构建框架

近年来,生态系统服务供需失调引发了一系列问题,诸如城市热岛、生态用地流失、环境污染、生物多样性减少等生态风险问题,已成为威胁生态安全、制约社会经济可持续发展的重要因素,因此维持生态系统服务供需平衡是生态安全健康发展的保障和关键。梳理了生态系统服务评价、生态安全格局构建的研究现状,指出了存在的不足,同时构建了基于生态系统服务的城市群生态安全格局基本框架,并提出了生态安全格局未来的研究重点:城市群区域和城市内部生态系统服务的多尺度综合评价、城市功能区的划分及对生态安全的胁迫作用、生态过程与生态系统服务与生态安全的耦合、基于生态系统服务流的生态安全格局构建、模拟和优化。通过耦合社会经济数据、卫星遥感数据、城市地图大数据,评价城市内部和外部不同尺度的生态系统服务,保障城市群生态系统服务流畅通传输,实现城市群生态安全格局评价和优化。     

生态退耕与植被演替的时空格局

综述了多重尺度上生态退耕的时空格局及其对植被演替时空变异影响的研究进展,提出了生态退耕与植被演替的时空格局研究方向.在自然和人文等因子的驱动下,全球兴起了生态退耕的热潮,生态退耕类型正在由人工恢复为主向自然弃耕为主发展.尽管国内外很多学者开始关注不同尺度上生态退耕的时空格局及其影响因子,但是生态退耕的时空变异性研究仍然比较薄弱,尤其缺乏多重尺度上生态退耕时空格局及其驱动因子的综合研究,在很大程度上限制了研究结果外推.研究表明,受到多因子的综合影响,生态退耕后植被演替呈现出复杂多样的时空变化特征;退耕植被演替研究从植物群落结构特征分析为主向群落功能分析发展,从传统的演替过程规律分析转向退耕植被演替的时空变异性分析;相对来说,生态退耕后植被演替的时空分异、影响因子和机制方面的研究比较薄弱.加强多重尺度上生态退耕时空格局与植被演替时空变异的综合研究是将来的研究重点.     

SEED: A framework for integrating ecological stoichiometry and eco-evolutionary dynamics

Characterising the extent and sources of intraspecific variation and their ecological consequences is a central challenge in the study of eco-evolutionary dynamics. Ecological stoichiometry, which uses elemental variation of organisms and their environment to understand ecosystem patterns and processes, can be a powerful framework for characterising eco-evolutionary dynamics. However, the current emphasis on the relative content of elements in the body (i.e. organismal stoichiometry) has constrained its application. Intraspecific variation in the rates at which elements are acquired, assimilated, allocated or lost is often greater than the variation in organismal stoichiometry. There is much to gain from studying these traits together as components of an ‘elemental phenotype’. Furthermore, each of these traits can have distinct ecological effects that are underappreciated in the current literature. We propose a conceptual framework that explores how microevolutionary change in the elemental phenotype occurs, how its components interact with each other and with other traits, and how its changes can affect a wide range of ecological processes. We demonstrate how the framework can be used to generate novel hypotheses and outline pathways for future research that enhance our ability to explain, analyse and predict eco-evolutionary dynamics.     

Amenity and ecological management: A framework for policy and practice

Amenity is a term that has re‐emerged within both public policy and environmental management organisations in response to an increasing emphasis on the human benefits derived from ecosystems. However, practical implementation of amenity management has been difficult due to a lack of definitional clarity within operational and academic literature. This article discusses the need for definitional clarity and understanding of the component elements of amenity that are integral to ecological management and reviews the literature on the perceptions and definitions of amenity in varied contexts. This study argues that positive perceptions of amenity benefits of a place are influenced by both physical elements such as sight, sound and smell and social elements such as age, education and cultural values. These elements should be considered by management agencies in a structured manner in order for the full potential of amenity to be realised. We present a conceptual framework to provide definitional clarity to the concept of amenity and highlight the interactions among its constituent elements. For the management of human‐dominated landscapes, considering the relationship between amenity and biodiversity may improve the integration of ecological and social goals.     

River forcing at work: ecological modeling of prograding and regressive deltas

Two explicit landscape simulation models were used to investigate habitat shifts in coastal Louisiana due to varying river forcing and sea level rise scenarios. Wetland conversion to open water and yearly shifts of marsh habitats in two contrasting estuarine regions were examined; the Atchafalaya delta which is a prograding delta area with strong riverine input, and the Barataria Basin is a regressive delta with high wetland loss which is isolated from riverine input. The models linked several modules dynamically across spatial and temporal scales. Both models consisted of a vertically integrated hydrodynamic model coupled with process-based biological modules of above and below ground primary productivity and soil dynamics. The models explored future effects of possible sea level rise and river diversion plans for 30 and 70-year projections starting in 1988. Results showed that increased river forcing had large land preservation impacts, and indicated that healthy functioning of the Mississippi Delta depends largely on inputs of freshwater, nutrients, and sediments in river water. These types of models are useful for research and as management tools for predicting the effects of regional impacts on structural landscape level changes.     

基于元胞自动机的森林水源涵养量模型新方法—— 概念与理论框架

模型方法是定量评价森林水源涵养的重要途径。根据元胞自动机的基本理论,结合森林水源涵养效应的多尺度特征,提出了一个新的基于元胞自动机的森林水源涵养量计算模型。该模型将森林"水文响应单元"网格化作为元胞空间的基本单元,邻域定义为摩尔(Moore)型,元胞"水库"水量状态变化范围定义在一个连续的实数空间上。将元胞单元对不同降雨事件的响应分为不产生径流和产生径流两种情况,通过对蒸散发、邻域元胞间水量传输、深层渗漏等制定转换规则,模拟森林在不同尺度上的水源涵养动态特征。这种新模型方法将为森林水源涵养由小尺度(水文响应单元)向流域、景观尺度上推提供有效的定量研究途径,从而进一步推动森林水源涵养功能研究的深入。     

生物多样性保护的一个理论框架

稳定而复杂多样的自然生境有利于多样性的形成和保存,剧变并趋于简单化的干扰生境常使多样性丧失。现实中的森林破碎化使区域物种丧失。多样性保护要求具备促使物种能长久生存的生境。生物最小面积概念集中讨论物种长久生存与群落（景观）面积的关系,是多样性保护的最基本的理论基础。根据自然保护实践,提出最小景观,扩充了生物最小面积概念。讨论了生物最小面积概念在建立自然保护区的理论框架、了解被保护生物及其生境的自然特点以及建立更全面的自然保护网络等方面的应用     

区域综合生态风险评价框架——以雄安新区为例

构建区域生态风险评价框架有助于清晰地识别、评估、模拟、预测与管理区域生态风险,进而为区域生态安全网络构建和生态安全格局保障提供支撑。雄安新区的建设,使该区域面临巨大的土地利用变化,对区域生态系统的结构和功能产生不可忽视的影响,洪涝和干旱灾害对雄安新区及其周边区域生态系统具有显著的威胁。以雄安新区为例,构建包含暴露-响应关系、人为源和自然源相结合的区域综合生态风险评价框架,分别对城市化和气候变化背景下的雄安新区土地利用变化、洪涝灾害、干旱灾害三类胁迫引起的区域生态风险进行了评价和预测,确定其生态风险空间分布特征及变化趋势。结果表明：(1)从时间序列上来看,由于气候变化导致洪涝、干旱等自然灾害的影响,加上雄安新区的土地利用变化,雄安新区的生态风险在2025年后有所上升,但有序的规划和良好的地类配置使得雄安新区起步区在2025年后生态风险程度下降;(2)从空间上看,雄安新区风险高值区主要集中在白洋淀区以西和以南,以及新区东北部部分区域。最后,从土地利用管理、洪涝和干旱灾害预防等角度提出了生态风险防控对策：(1)雄安新区应坚持对土地利用的合理规划和严格管理,切实防止土地的无序利用,密切关注景观...     

A theoretical framework for biological control of soil-borne plant pathogens: Identifying effective strategies

We develop and analyse a flexible compartmental model of the interaction between a plant host, a soil-borne pathogen and a microbial antagonist, for use in optimising biological control. By extracting invasion and persistence thresholds of host, pathogen and biological control agent, performing an equilibrium analysis, and numerical investigation of sensitivity to parameters and initial conditions, we determine criteria for successful biological control. We identify conditions for biological control (i) to prevent a pathogen entering a system, (ii) to eradicate a pathogen that is already present and, if that is not possible, (iii) to reduce the density of the pathogen. Control depends upon the epidemiology of the pathogen and how efficiently the antagonist can colonise particular habitats (i.e. healthy tissue, infected tissue and/or soil-borne inoculum). A sharp transition between totally effective control (i.e. eradication of the pathogen) and totally ineffective control can follow slight changes in biologically interpretable parameters or to the initial amounts of pathogen and biological control agent present. Effective biological control requires careful matching of antagonists to pathosystems. For preventative/eradicative control, antagonists must colonise susceptible hosts. However, for reduction in disease prevalence, the range of habitat is less important than the antagonist's bulking-up efficiency.     

Avian ecological succession in the Amazon: A long‐term case study following experimental deforestation

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