WHY ARE QUANTITATIVE RELATIONSHIPS BETWEEN ENVIRONMENTAL QUALITY AND FISH POPULATIONS SO ELUSIVE
By K. Rose. 2000
262 citations recorded by the source corpus.
Subfields: Aquatic Science, Global and Planetary Change, Nature and Landscape Conservation
View Paper: https://www.semanticscholar.org/paper/e68aa8964736262aac17dd9576574181832db1ae
How researchers see this paper
The researchers whose trusted networks rank it highest, strongest advocate first. Every researcher gets a different order.
In Aquatic Science
- A. Arthington
- Julian D. Olden
- B. Pusey
- M. Kennard
- C. Peterson
- Francine H. Mejia
- N. LeRoy Poff
- Steven F. Railsback
In Global and Planetary Change
- F. Nordlie
- Ted R. Sommer
- Francine H. Mejia
- B. Rinkevich
- M. Nobriga
- C. Peterson
- M. J. Powers
- J. Rosenfeld
In Nature and Landscape Conservation
- Julian D. Olden
- N. LeRoy Poff
- A. Arthington
- M. Kennard
- B. Pusey
- Ted R. Sommer
- Francine H. Mejia
- J. Rosenfeld
Citations in the corpus
- Impacts of varying habitat quality on the physiological stress of spotted salamanders (Ambystoma maculatum) (2003, background): “In particular, the sub-lethal impacts of environmental degradation on individuals and populations can be difficult to evaluate (Belden, Wildy & Blaustein, 2000; Rose, 2000; Reed, 2002).”
- Multidecadal trends for three declining fish species: habitat patterns and mechanisms in the San Francisco Estuary, California, USA (2007, methodology): “…author (e-mail: ffeyrer@water.ca.gov). fish–habitat relationships and long-term trends in habitat suitability is critical because abiotic habitat components can affect the population dynamics of fishes in most habitat types (e.g., Cardinale and Arrhenius 2000; Claramunt and Wahl 2000; Rose 2000).”
- Concepts from complex adaptive systems as a framework for individual-based modelling (2001, background): “…building a model of an individual organism is easier than building a model of a population: individuals can be tested in controlled ways that populations cannot, and are more limited in their range of responses and therefore more predictable in their behavior than are populations (Rose, 2000).”
- Environmental variability and fisheries: what can models do? (2008, background): “It is hardly imaginable that only one environmental factor is relevant for the performance of a biotic entity (e.g., Solomon 1949; Fry 1971; Baumann 1998; Rose 2000; Stenseth et al. 2003).”
- Steps in the construction of underwater coral nursery, an essential component in reef restoration acts (2006, background): “However, established theories and approved management and restoration techniques for marine ecosystems, including coral reefs, still lag behind and rely largely on those developed for terrestrial habitats (Allison et al. 1998; Keough and Quinn 2000; Rose 2000).”
- Assessing the Habitat Requirements of Stream Fishes: An Overview and Evaluation of Different Approaches (2003, background): “Development of habitat models must be placed within the context of the life history of the organism when different habitat requirements are associated with different life stages (Minns et al. 1996; Rose 2000).”
- A Bayesian network of eutrophication models for synthesis, prediction, and uncertainty analysis (2004, background): “The interacting effects of unpredictable natural events and anthropogenic changes in water quality is a common source of difficulty in developing predictive models for fisheries management (Rose, 2000) and suggests a probabilistic approach.”
- Multiscale effects of flow regime and habitat and their interaction on fish assemblage structure in eastern Australia (2007, background): “However, these ecological factors, together with the complex hierarchical linkages evident in natural river ecosystems, can make it difficult to develop accurate predictive models and to isolate the importance of individual and interacting environmental controls on fish assemblages (Rose 2000).”
- Effects of global climate change on marine and estuarine fishes and fisheries (2004, background): “Many fishes experience high mortality (due to predation or fishing pressure) and high growth rates (dependent on environmental quality) during larval and juvenile stages, which influences the subsequent survival and abundance of these fishes (Houde, 1987; Rose, 2000).”
- A Place to Call Home: A Synthesis of Delta Smelt Habitat in the Upper San Francisco Estuary (2013, background): “We assume that the maintenance of appropriate habitat quality is essential to the long-term resilience of the delta smelt population (Rose 2000; Peterson 2003).”
- Hypoxia tolerance in two juvenile estuary-dependent fishes (2005, unknown): “For example, the highest larval survival of the naked goby (Gobiosoma bosci) occurs at intermediate DO concentrations, rather than the highest concentrations (Rose, 2000).”
- Physicochemical environments and tolerances of cyprinodontoid fishes found in estuaries and salt marshes of eastern North America (2006, background): “However, there are significant difficulties in quantifying effects of changes in environmental quality on fish population dynamics (Rose 2000).”
- Habitat degradation from intermittent hypoxia: impacts on demersal fishes (2005, background): “…habitat characteristics or changes in environmental quality and fish population dynamics and production is critical to improving management, but it is rarely done (but see Landahl et al. 1997, Rose 2000), and is especially difficult in species that use multiple habitats throughout their life.”