Minimum requirements for modelling bivalve carrying capacity
By A. Smaal, T. Prins, Norbert Dankers, B. Ball. Aquatic Ecology, 2004
92 citations recorded by the source corpus.
Subfields: Environmental Engineering, Global and Planetary Change
View Paper: https://www.semanticscholar.org/paper/97b974d81017427f97b2bdbcfc62b0a53fc50460
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In Environmental Engineering
In Global and Planetary Change
Citations in the corpus
- Predicting the carrying capacity of bivalve shellfish culture using a steady, linear food web model (2005, methodology): “attempt to predict carrying capacity of coastal regions (e.g. Dame and Prins, 1997; Smaal et al., 1997; Bacher et al., 1998; Duarte et al., 2003).”
- Integrated assessment of ecosystem-scale carrying capacity in shellfish growing areas (2008, background): “Carrying capacity for shellfish culture has been further defined as the standing stock at which the annual production of the marketable cohort is maximized (Bacher et al., 1998; Smaal et al., 1998), which will differ substantially from the ecological carrying capacity.”
- The impacts of aquacultured oysters, Crassostrea virginica (Gmelin, 1791) on water column nitrogen and sedimentation: results of a mesocosm study (2003, unknown): “…has been used to mean the stocking density achievable without incurring density-dependent stunting (Incze et al., 1981) or alternatively in the population ecology sense of the maximum stocking density achievable without causing food depletion or population mortalities (Smaal et al., 1998).”
- Integrating ecological, economic and social aspects to generate useful management information under the EU Directives' ‘ecosystem approach’ (2012, background): “The same happens when models on carrying capacity are applied to estimate optimumgrowth andexploitation of commercial species (e.g. Duarte et al., 2003; Smaal et al., 1998), or even to evaluate the outcome of management strategies and promote efficient measures (e.g. Thébault et al., 2008).”