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  • 1
    Online-Ressource
    Online-Ressource
    Newark :John Wiley & Sons, Incorporated,
    Schlagwort(e): Fisheries -- Environmental aspects. ; Marine ecology. ; Electronic books.
    Materialart: Online-Ressource
    Seiten: 1 online resource (74 pages)
    Ausgabe: 1st ed.
    ISBN: 9780470694855
    Serie: British Ecological Society Ecological Issues Series
    Sprache: Englisch
    Anmerkung: Commercial fishing: the wider ecological impacts -- Contents -- Key Points -- 1 Commercial fishing: the wider ecological impacts -- 1.1 Introduction -- 2 Fishing gears and their operation -- 2.1 Gear selectivity -- 2.2 Pelagic drifting gears -- 2.3 Bottom set gears -- 2.4 Pelagic mobile gears -- 2.5 Bottom mobile gears -- 2.6 SCUBA diving, explosives, poisons -- 3 Effects of litter from fishing gear -- 3.1 'Ghost' fishing -- 3.2 Ingestion offragments offishinggear by marine mammals, turtles and seabirds -- 4 Vulnerability of different marine habitats -- 4.1 Mud -- 4.2 Sand -- 4.3 Gravel and mixed grounds -- 4.4 Maerl -- 4.5 Coral, coralligene and rocky reef habitats -- 4.6 Seagrass meadows -- 4.7 Kelp forests -- 4.8 Sea mounts -- 4.9 Relative vunerability -- 5 Effects on non-target organisms -- 5.1 Sea birds -- 5.2 Sea mammals -- 5.3 Sea turtles -- 5.4 Sea snakes -- 5.5 Benthic scavengers -- 6 Community and ecosystem responses -- 6.1 Community diversity -- 6.2 Habitat structure -- 6.3 Benthopelagic coupling -- 6.4 Species interactions -- 6.5 Assessing fisheries effects -- 7 Conservation aspects and the way forward -- 7.1 Marine reserves -- 7.2 Practical conservation measures -- 8 Further reading -- 9 Glossary -- 10 Acronyms -- 11 Addresses of contributors.
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  • 2
    Online-Ressource
    Online-Ressource
    Newark :John Wiley & Sons, Incorporated,
    Schlagwort(e): Marine fishes -- Ecology. ; Electronic books.
    Materialart: Online-Ressource
    Seiten: 1 online resource (434 pages)
    Ausgabe: 1st ed.
    ISBN: 9781444311358
    DDC: 333.95/6
    Sprache: Englisch
    Anmerkung: Intro -- Marine Fisheries Ecology -- Contents -- Preface -- Acknowledgements -- 1 Marine fisheries ecology: an introduction -- 1.1 Introduction -- 1.2 Fisheries of the world -- 1.2.1 History of fisheries -- 1.2.2 Fishery science -- 1.2.3 Diversity of fisheries -- 1.3 Patterns of exploitation -- 1.3.1 Boom and bust -- 1.3.2 Conservation and ecosystem concerns -- 1.4 Why manage fisheries? -- 1.5 Objectives of management -- 1.5.1 Range of objectives -- 1.5.2 Balancing objectives -- 1.5.3 From objective to action -- 1.6 Meeting management objectives -- 1.7 Structure of this book -- Summary -- 2 Marine ecology and production processes -- 2.1 Introduction -- 2.2 Primary production: sources and magnitude -- 2.3 Phytoplanktonic production -- 2.3.1 Links between production and physical processes -- 2.3.2 Upwellings and fronts -- 2.3.3 Rates of phytoplanktonic production -- 2.4 Non-phytoplanktonic production -- 2.4.1 Macroalgae -- 2.4.2 Mangroves -- 2.4.3 Coral reef algae -- 2.4.4 Seagrasses and marsh plants -- 2.4.5 Microphytobenthos -- 2.5 Heterotrophic production -- 2.5.1 The fate of primary production -- 2.5.2 Transfer along the food chain -- 2.5.3 Production of fished species -- 2.5.4 Linking primary production and landings -- Summary -- 3 Fished species, life histories and distribution -- 3.1 Introduction -- 3.2 Fishes -- 3.3 Invertebrates -- 3.4 Life histories -- 3.4.1 Sex, sex reversal and sex ratios -- 3.4.2 Growth, maturity and longevity -- 3.4.3 Egg size, fecundity and reproduction -- 3.5 Distribution in space and time -- 3.5.1 Geographical ranges and stock structures -- 3.5.2 Migration -- 3.5.3 Larval transport, retention and dispersal -- 3.5.4 Metapopulations -- Summary -- 4 Population structure in space and time -- 4.1 Introduction -- 4.2 Recruitment -- 4.2.1 Spawner and recruit relationships -- 4.2.2 Mortality during the early life history. , 4.2.3 Depensation -- 4.2.4 Regulation in fish populations -- 4.3 Density-dependent habitat use -- Summary -- 5 Fishing gears and techniques -- 5.1 Introduction -- 5.2 From shoreline gathering to satellites -- 5.3 Modern commercial fishing gears -- 5.3.1 Towed fishing gear -- 5.3.2 Static fishing gear -- 5.4 Other fishing techniques -- 5.5 Conservation methods -- Summary -- 6 Fishers: socioeconomics and human ecology -- 6.1 Introduction -- 6.2 Motivations for fishing -- 6.2.1 Food -- 6.2.2 Income -- 6.3 Modifications to fishing behaviour -- 6.3.1 Social -- 6.3.2 Religion -- 6.4 Conflicts and conflict resolution -- 6.4.1 Competing for fish -- 6.4.2 Fish wars -- 6.4.3 Fishers in the political process -- 6.4.4 Traditional management systems -- 6.4.5 Customary marine tenure -- 6.4.6 Co-management -- Summary -- 7 Single-species stock assessment -- 7.1 Introduction -- 7.2 Balancing birth and death -- 7.3 Surplus production models -- 7.3.1 Stability -- 7.3.2 Models of population growth -- 7.3.3 Fitting models to data -- 7.3.4 Surplus production models in action -- 7.4 Delay-difference models -- 7.4.1 Delay-difference models in action -- 7.5 Virtual population analysis -- 7.5.1 Age-based cohort analysis -- 7.5.2 Length-based cohort analysis -- 7.6 Statistical catch-at-age methods -- 7.7 Yield-per-recruit models -- 7.7.1 Yield-per-recruit models in action -- 7.8 Incorporating recruitment -- 7.8.1 Replacement lines -- 7.8.2 Replacement lines in action -- 7.9 Confronting risk and uncertainty -- 7.9.1 Bayesian analysis -- 7.9.2 Resampling methods -- 7.10 Biological reference points -- Summary -- 8 Multispecies assessment and ecosystem modelling -- 8.1 Introduction -- 8.2 Multispecies surplus production -- 8.2.1 Multispecies surplus production in action -- 8.3 Multispecies yield per recruit -- 8.3.1 Multispecies yield per recruit in action. , 8.4 Multispecies virtual population analysis -- 8.4.1 Multispecies VPA in action -- 8.4.2 Applying MSVPA data to single-species models -- 8.5 Predators, prey and competitors -- 8.5.1 Predator-prey dynamics -- 8.5.2 Competition, an unexpected result -- 8.5.3 Management implications -- 8.6 Size spectra -- 8.7 Ecosystem models -- 8.7.1 Ecosystem models in action -- Summary -- 9 Getting the data: stock identity and dynamics -- 9.1 Introduction -- 9.2 Stock identification -- 9.2.1 The stock concept -- 9.2.2 Methods for stock identification -- 9.3 Stock dynamics -- 9.3.1 Sampling -- 9.3.2 Length, weight and age -- 9.3.3 Growth -- 9.3.4 Maturity -- 9.3.5 Fecundity -- 9.3.6 Mortality -- 9.4 The impact of errors -- Summary -- 10 Getting the data: abundance, catch and effort -- 10.1 Introduction -- 10.2 Abundance -- 10.2.1 Survey design -- 10.2.2 Visual census methods -- 10.2.3 Acoustic methods -- 10.2.4 Trawl surveys -- 10.2.5 Depletion methods -- 10.2.6 Mark-recapture methods -- 10.2.7 Egg production methods -- 10.3 The fishery -- Summary -- 11 Bioeconomics -- 11.1 Introduction -- 11.2 The value of fisheries -- 11.2.1 Trade in fished species -- 11.2.2 Catch values and employment -- 11.3 Bioeconomic models -- 11.3.1 Descriptive bioeconomics -- 11.3.2 Optimal fishing strategies -- 11.3.3 Bayesian methods -- 11.4 Economic vs. social management objectives -- 11.4.1 Subsidies -- 11.4.2 The case for economic efficiency -- Summary -- 12 Fishing effects on populations and communities -- 12.1 Introduction -- 12.2 Vulnerability to fishing -- 12.2.1 Behaviour -- 12.2.2 Life histories -- 12.3 Intraspecific effects -- 12.3.1 Age and size structure -- 12.3.2 Reproduction -- 12.3.3 Genetic structure -- 12.4 Community effects -- 12.4.1 Diversity -- 12.4.2 Community structure -- 12.4.3 Size structure -- 12.4.4 Competition and trophic interactions -- Summary. , 13 Bycatches and discards -- 13.1 Introduction -- 13.2 Catches, bycatches and discards -- 13.2.1 Definitions -- 13.2.2 Reasons for discarding -- 13.3 Alternatives to discarding -- 13.4 Fisheries and bycatches -- 13.5 Incidental captures -- 13.5.1 Seabirds -- 13.5.2 Sea turtles -- 13.5.3 Sea snakes -- 13.5.4 Marine mammals -- 13.6 Methods to reduce bycatches -- 13.7 Ghost fishing -- 13.8 Sociocultural differences -- Summary -- 14 Impacts on benthic communities, habitats and coral reefs -- 14.1 Introduction -- 14.2 Fishing disturbance -- 14.2.1 Fishing vs. natural disturbance -- 14.2.2 Distribution of fishing disturbance -- 14.3 Direct effects of fishing gear on the seabed -- 14.3.1 Towed fishing gear -- 14.3.2 Direct effects on the substratum -- 14.3.3 Effects on infauna -- 14.3.4 Effects on epifauna -- 14.3.5 Meta-analysis -- 14.4 Effects of static fishing gears -- 14.5 Long-term effects -- 14.6 Fishing as a source of energy subsidies -- 14.6.1 Have population changes occurred? -- 14.7 Indirect effects on habitats -- 14.7.1 Loose seabeds -- 14.7.2 Coral reefs -- Summary -- 15 Fishery interactions with birds and mammals -- 15.1 Introduction -- 15.2 Birds -- 15.2.1 Competition between birds and fisheries -- 15.2.2 Benefits of discarding -- 15.2.3 Waders and shellfish -- 15.3 Mammals -- 15.3.1 Competition between mammals and fisheries -- 15.3.2 Prey release -- Summary -- 16 A role for aquaculture? -- 16.1 Introduction -- 16.2 Aquaculture past and present -- 16.3 What is cultivated? -- 16.4 Production systems -- 16.5 Feeding constraints -- 16.6 Prospects for expansion -- 16.6.1 Cage cultivation -- 16.6.2 Stock enhancement and ranching -- 16.7 Case studies -- 16.7.1 Shrimp farming -- 16.7.2 Bivalve mariculture -- Summary -- 17 Management and conservation options -- 17.1 Introduction -- 17.2 Management objectives, strategies and actions. , 17.2.1 From objective to action -- 17.2.2 Catch control -- 17.2.3 Effort control -- 17.2.4 Technical measures -- 17.2.5 Management in action -- 17.3 Improving management -- 17.3.1 Enforcement and compliance -- 17.3.2 Co-management -- 17.3.3 Ownership of resources and harvesting rights -- 17.3.4 Uncertainty and the precautionary approach -- 17.3.5 Role of science -- 17.4 Multispecies and ecosystem-based management -- 17.4.1 What are the objectives? -- 17.4.2 What can be achieved? -- 17.5 Managing fisheries for conservation -- 17.5.1 Endangered species -- 17.5.2 Habitats -- 17.5.3 Protected areas and no-take zones -- 17.6 Future trends -- 17.6.1 Fisheries science -- 17.6.2 Fisheries management -- Summary -- References -- Appendix 1: List of symbols -- Appendix 2: Fisheries websites -- Appendix 3: Geographic index -- Index.
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  • 3
    Schlagwort(e): Marine ecology ; Aufsatzsammlung ; Meeresökologie ; Meeresökologie ; Meeresökologie
    Materialart: Buch
    Seiten: xviii, 501 Seiten , Illustrationen, Diagramme, Karten , 24,5 cm
    Ausgabe: Second edition
    ISBN: 0199227020 , 9780199227020
    DDC: 577.7
    RVK:
    Sprache: Englisch
    Anmerkung: Literatur- und URL-Verzeichnis: Seiten 450-487
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  • 4
    Digitale Medien
    Digitale Medien
    Springer
    Reviews in fish biology and fisheries 10 (2000), S. 209-231 
    ISSN: 1573-5184
    Quelle: Springer Online Journal Archives 1860-2000
    Thema: Biologie , Land- und Forstwirtschaft, Gartenbau, Fischereiwirtschaft, Hauswirtschaft
    Notizen: Abstract Marine reserves (no-take zones) are widely recommended asconservation and fishery management tools. One potential benefitof marine reserves is that they can reduce fishing mortality.This can lead to increases in the abundance of spawners,providing insurance against recruitment failure and maintainingor enhancing yields in fished areas. This paper considers thefactors that influence recovery following marine reserveprotection, describes patterns of recovery in numbers andbiomass, and suggests how recovery rates can be predicted.Population recovery is determined by initial population size, theintrinsic rate of population increase r, and the degree ofcompensation (increases in recruits per spawner as spawnerabundance falls) or depensation (lower than expected recruitmentat low abundance, Allee effect) in the spawner-recruitrelationship. Within a reserve, theoretical recovery rates arefurther modified by metapopulation structure and the success ofindividual recruitment events. Recovery also depends on theextent of reductions in fishing mortality (F) as determined bythe relationship between patterns of movement, migration, anddensity-dependent habitat use (buffer effect) in relation to thesize, shape and location of the reserve. The effects ofreductions in F on population abundance have been calculatedusing a variety of models that incorporate transfer rates betweenthe reserve and fished areas, fishing mortality outside thereserve and life history parameters of the population. Thesemodels give useful indications of increases in production andbiomass (as yield per recruit and spawners per recruitrespectively) due to protection, but do not address recruitment.Many reserves are very small in relation to the geographicalrange of fish or invertebrate populations. In these reserves itmay be impossible to distinguish recovery due to populationgrowth from that due to redistribution. Mean rates of recoverycan be predicted from r, but the methods are data intensive. Thisis ironic when marine reserves are often favoured for managementor conservation in data-poor situations where conventional stockassessment is impossible. In these data-poor situations, it maybe possible to predict recovery rates from very low populationsizes by using maximum body size or age at maturity as simplecorrelates of the intrinsic rate of natural increase.
    Materialart: Digitale Medien
    Standort Signatur Einschränkungen Verfügbarkeit
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  • 5
    Digitale Medien
    Digitale Medien
    Springer
    Environmental biology of fishes 46 (1996), S. 15-25 
    ISSN: 1573-5133
    Schlagwort(e): Chaetodon ; Parupeneus ; Scarus ; Coral reef ; Rocky reef ; Substrate ; Fishing effects
    Quelle: Springer Online Journal Archives 1860-2000
    Thema: Biologie
    Notizen: Synopsis Relationships between quantitative measures of habitat type and the biomass of Chaetodon, Scarus and Parupeneus species were investigated across 35 reef sites in the Inner Seychelles Group. Multiple regression was used to determine the proportion of variance in biomass between sites which could be explained by depth, exposure, vertical relief, topographic complexity, live coral cover, coral rubble cover, rock cover, sand cover, underlying carbonate substrate, underlying sand substrate, underlying rock substrate and an index of fishing intensity. A significant proportion of the variance in biomass was explained by habitat variables and the index of fishing intensity for 7 of 12 Chaetodon species (23–52% of variance explained), 3 of 6 Parupeneus species (33–40%), and 10 of 13 Scarus species (14–46%). Within genera, different groups of habitat variables explained the variance in biomass for different species and, of the variables studied, only the proportion of underlying sand substrate failed to explain a significant proportion of the variance in biomass for any species. Quantitative relationships between the biomass of Chaetodon and habitat were often in accordance with those suggested by previous studies of their ecology, life-history and distribution at other Indo-Pacific locations. However, the habitat associations of the Parupeneus and some Scarus species have not been studied at other locations and clearly warrant further investigation. It was concluded that habitat was an important determinant of the distribution of many Seychelles reef fishes, but that the habitat variables examined were rarely the most important determinant of biomass. However, the inclusion of a procedure to collect habitat data provided a useful means by which to reduce the unexplained variance associated with visual census biomass estimates and therefore improves the possibility of elucidating the effects of other factors on the biomass of Seychelles reef fishes.
    Materialart: Digitale Medien
    Standort Signatur Einschränkungen Verfügbarkeit
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  • 6
    facet.materialart.
    Unbekannt
    In:  http://aquaticcommons.org/id/eprint/7463 | 704 | 2011-12-07 14:00:11 | 7463 | Fundacion Charles Darwin Foundation
    Publikationsdatum: 2021-07-03
    Schlagwort(e): Biology ; reef fishes ; solar eclipse ; light levels ; diurnal ; behaviour ; Isla Pinta
    Repository-Name: AquaDocs
    Materialart: article
    Format: application/pdf
    Format: application/pdf
    Format: 9-10
    Standort Signatur Einschränkungen Verfügbarkeit
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