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  • 1
    Online-Ressource
    Online-Ressource
    Oxford :Oxford University Press, Incorporated,
    Schlagwort(e): Marine biodiversity -- Effect of human beings on. ; Marine ecology -- Effect of human beings on. ; Electronic books.
    Beschreibung / Inhaltsverzeichnis: This edited volume is the first to address the latest advances in biodiversity-function science using marine examples. It provides an in-depth evaluation of the science before offering a perspective on future research directions for some of the most pressing environmental issues facing society today and in the future.
    Materialart: Online-Ressource
    Seiten: 1 online resource (257 pages)
    Ausgabe: 1st ed.
    ISBN: 9780191637384
    DDC: 333.95614
    Sprache: Englisch
    Anmerkung: Cover -- Contents -- List of Contributors -- 1. Marine biodiversity: its past development, present status, and future threats -- 1.1 Introduction -- 1.2 What is biodiversity? -- 1.3 Comparing marine and terrestrial biodiversity -- 1.4 The rise of marine biodiversity -- 1.5 The distribution of marine biodiversity -- 1.6 Human impacts on marine biodiversity -- 1.7 The relationship between global climate and marine biodiversity -- 1.8 Could marine biodiversity be facing large-scale climate-induced extinction? -- 1.9 Additional impacts of CO[sub(2)] on the marine environment -- 1.10 Hypoxia and 'dead zones' -- 1.11 Summary -- 2. Biodiversity in the context of ecosystem function -- 2.1 Historical development of the concept -- 2.2 Biological diversity-meaning and measurement -- 2.3 Biodiversity in the context of function -- 2.4 Conclusions -- 3. Ecosystem function and co-evolution of terminology in marine science and management -- 3.1 Introduction -- 3.2 What's in a name? Ecosystem function -- 3.2.1 Ecosystem function defined -- 3.3 Measuring ecosystem function -- 3.4 Ecological terms and the co-evolutionary model -- 3.5 Co-evolution, policy drivers, and opportunities -- 3.6 Conclusions -- 4. Ecological consequences of declining biodiversity: a biodiversity-ecosystem function (BEF) framework for marine systems -- 4.1 The significance of marine biological diversity -- 4.1.1 Significance -- 4.1.2 A three-point framework for marine biodiversity -- 4.2 Marine biodiversity and ecosystem function -- 4.2.1 Daunting scales -- 4.2.2 Marine biodiversity -- 4.2.3 Marine ecosystem functioning -- 4.3 Marine biotic impoverishment -- 4.4 Marine BEF findings -- 4.5 The fundamental marine BEF relationship in abstraction -- 4.5.1 Where's the inflection point? -- 4.5.2 The BEF curve for marine systems -- 4.6 Synthesis -- 4.6.1 A simple but telling marine BEF framework. , 4.6.2 Remember the humongous multipliers -- 4.6.3 Future directions -- 4.7 Conclusions -- 5. Lessons from the fossil record: the Ediacaran radiation, the Cambrian radiation, and the end-Permian mass extinction -- 5.1 Introduction -- 5.2 Strengths and limitations of the geological record -- 5.3 Ediacaran ecosystems -- 5.3.1 Productivity-biodiversity relationship -- 5.3.2 Influence of bioturbation on ecosystem functioning -- 5.3.3 Species richness-functional diversity relationship -- 5.4 Cambrian ecosystems -- 5.4.1 Productivity-biodiversity relationship -- 5.4.2 Influence of bioturbation on ecosystem functioning -- 5.4.3 Species richness-functional diversity relationship -- 5.5 The end-Permian mass extinction and its aftermath -- 5.5.1 Environmental changes during the late Paleozoic to early Mesozoic -- 5.5.2 Permian-Triassic marine nutrient levels and primary productivity -- 5.5.3 Productivity-biodiversity-biomass relationship -- 5.5.4 Discussion -- 5.6 Conclusions -- 6. The analysis of biodiversity-ecosystem function experiments: partitioning richness and density-dependent effects -- 6.1 Introduction -- 6.2 Partitioning richness and abundance effects -- 6.3 Empirical example -- 6.3.1 Experimental layout -- 6.3.2 Fitting the mixed-effect model and evaluating contrasts -- 6.4 Results -- 6.5 Conclusions -- 7. The importance of body size, abundance, and food-web structure for ecosystem functioning -- 7.1 Introduction -- 7.2 Historical context and the evolution of an idea -- 7.2.1 Integrating body mass, abundance, and food-web structure into biodiversity and ecosystem functioning studies -- 7.3 The relevance of body mass to biodiversity-ecosystem functioning research -- 7.4 Abundance, body mass, and species diversity patterns -- 7.5 Conclusions -- 8. Effects of biodiversity-environment conditions on the interpretation of biodiversity-function relations. , 8.1 Introduction -- 8.2 Methods of analysis -- 8.2.1 Compilation of publications -- 8.2.2 Calculation of effect sizes -- 8.2.3 Extraction of data -- 8.2.4 Statistical Analysis -- 8.3 Are alternative drivers of change more important than species richness for ecosystem properties? -- 8.3.1 Summary of studies focusing on relationship between species richness and ecosystem properties -- 8.3.2 Effects of species richness and/or additional drivers of change on ecosystem properties -- 8.3.3 Distinguishing the effects of biodiversity, the abiotic and/or biotic environment on ecosystem properties -- 8.4 Conclusions -- 9. Extending the approaches of biodiversity and ecosystem functioning to the deep ocean -- 9.1 Deep-sea ecosystems: characteristics, biodiversity, and functioning -- 9.2 Approaches to the investigation of deep-sea biodiversity and ecosystem functioning -- 9.2.1 Biodiversity metrics -- 9.2.2 Functional diversity -- 9.2.3 Deep-sea ecosystem functioning -- 9.2.4 Variables used for measuring ecosystem efficiency -- 9.3 Relationships between biodiversity and ecosystem functioning in the deep sea -- 9.4 Relationships between biodiversity and ecosystem functioning in different deep-sea ecosystems -- 9.5 Conclusions and perspectives -- 10. Incorporating extinction risk and realistic biodiversity futures: implementation of trait-based extinction scenarios -- 10.1 Introduction -- 10.2 How to implement non-random extinction scenarios -- 10.3 Case study: implications of regional biodiversity loss on carbon cycling in the shelf sea sediments of the North Sea -- 10.3.1 Study sites and data collection -- 10.3.2 Benthic bioturbation characterization -- 10.3.3 Modelling -- 10.3.4 Estimating non-linear changes in ecosystem functioning -- 10.4 Results and discussion -- 10.5 Conclusions and recommendations. , 11. Biodiversity and ecosystem functioning: an ecosystem-level approach -- 11.1 The need to work at seascape scales -- 11.2 Building a credible evidence base -- 11.3 Case study 1: The Ythan estuary, Scotland -- 11.3.1 Biodiversity in the two periods -- 11.3.2 Ecological functioning in the two periods -- 11.4 Case study 2: Hawaii and the northern Line Islands, central Pacific -- 11.4.1 Hawaii -- 11.4.2 Northern Line Islands -- 11.5 Effects of fishing on fish assemblage structure -- 11.5.1 Hawaii -- 11.5.2 Northern Line Islands -- 11.6 Implications for ecosystem function -- 11.7 Conclusions -- 12. Multitrophic biodiversity and the responses of marine ecosystems to global change -- 12.1 Introduction -- 12.2 How and why biodiversity is changing in oceans and estuaries -- 12.3 Lessons learned: different designs for different questions -- 12.4 Biodiversity and ecosystem functioning in the Anthropocene -- 13. Reality check: issues of scale and abstraction in biodiversity research, and potential solutions -- 13.1 Introduction -- 13.2 At which spatial and temporal scales have most biodiversity-ecosystem function (BEF) studies been conducted to date? -- 13.3 What important ecological processes or patterns may be lost in abstracting BEF experimental systems from natural ecosystems? -- 13.4 Does the reduced temporal/spatial scale or compromised ecological realism of marine BEF studies affect our ability to extrapolate results to other systems? -- 13.5 Relative merits of different approaches to overcoming limitations of BEF studies -- 13.5.1 Empirical research to elucidate ecological concepts -- 13.5.2 Empirical research for direct application to management/conservation -- 13.6 Conclusions -- 14. Why bother going outside: the role of observational studies in understanding biodiversity-ecosystem function relationships. , 14.1 The role of observation in the design, execution, and interpretation of BEF relationships -- 14.2 The heterogeneous nature of seafloor landscapes -- 14.3 Observing the nature of functions -- 14.4 Scaling laws and relevance to BEF -- 14.5 A more integrative approach to empirical research in biodiversity-ecosystem function studies -- 15. Implementing an ecosystem approach: predicting and safeguarding marine biodiversity futures -- 15.1 Introduction -- 15.1.1 Taking an ecosystem approach -- 15.2 Ecosystem services, function, and biodiversity -- 15.2.1 Taking a systems perspective -- 15.2.2 Linking ecology and economics -- 15.3 An economic framework for ecosystem services -- 15.3.1 Valuation of ecosystem services -- 15.3.2 Valuation methods -- 15.4 A framework for implementing an ecosystem approach -- 15.5 Challenges for the future -- 15.5.1 Science needs -- 15.5.2 Policy needs -- 15.5.3 Conclusions -- Index -- A -- B -- C -- D -- E -- F -- G -- H -- I -- K -- L -- M -- N -- O -- P -- R -- S -- T -- U -- V -- W -- Y.
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  • 2
    Publikationsdatum: 2015-06-16
    Beschreibung: The relationship between biodiversity and stability of marine benthic assemblages was investigated through meta-analyses using existing data sets (n = 28) covering various spatial (m-km) and temporal (1973-2006; ranging from 5 to 〉250 months) scales in different benthic habitats (emergent rock, rock pools and sedimentary habitats) over different European marine systems (North Atlantic and western Mediterranean). Stability was measured by a lower variability in time, and variability was estimated as temporal variance of species richness, total abundance (density or % cover) and community structure (using Bray-Curtis dissimilarities on species composition and abundance). Stability generally decreased with species richness. Temporal variability in species richness increased with the number of species at both quadrat (〈1 m2) and site (100 m2) scales, while no relationship was observed by multivariate analyses. Positive relationships were also observed at the scale of site between temporal variability in species richness and variability in community structure with evenness estimates. This implies that the relationship between species richness or evenness and species richness variability is slightly positive and depends on the scale of observation. Thus, species richness does not stabilize temporal fluctuations in species number, rather species rich assemblages are those most likely to undergo the largest fluctuations in species numbers and abundance from time to time. Changes within community assemblages in terms of structure are, however, generally independent of biodiversity. Except for sedimentary and rock pool habitats, no relationship was observed between temporal variation of total abundances and diversity at either scale. Overall, our results emphasise that the relation between species richness and species-level measures of temporal variability depend on scale of measurements, type of habitats and the marine system (North Atlantic and Mediterranean) considered.
    Repository-Name: EPIC Alfred Wegener Institut
    Materialart: Article , isiRev
    Standort Signatur Einschränkungen Verfügbarkeit
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