Determination of lethal dissolved oxygen levels for selected marine and estuarine fishes, crustaceans, and a bivalve
By M. D., Poucher S., Coiro L.. 2002
180 citations recorded by the source corpus.
Subfields: Health, Toxicology and Mutagenesis, Ocean Engineering, Oceanography
View Paper: https://www.semanticscholar.org/paper/7555237793d53b73ea19aed577fffdfbd63350d5
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In Health, Toxicology and Mutagenesis
In Ocean Engineering
In Oceanography
Citations in the corpus
- Tolerance of benthic macrofauna to hypoxia and anoxia in shallow coastal seas: a realistic scenario (2012, background): “Finally, physical and biological community structure can play a role, whereby the loss of 1 species can trigger further species loss, reducing ecosystem stability (O’Gorman et al. 2011).”
- Effects of natural and human-induced hypoxia on coastal benthos (2009, background): “7 ml L−1) (Miller et al., 2002) without showing significant change in behavior (Demers et al.”
- Impacts of hypoxia on the structure and processes in pelagic communities (zooplankton, macro-invertebrates and fish) (2009, background): “5–2 mL O2 L−1 in other experiments (e.g. Keister et al., 2000; Miller et al., 2002) was covered only marginally in his experiments.”
- Effects of low dissolved oxygen on zooplankton predation by the ctenophore Mnemiopsis leidyi (2004, background): “Not only does low DO have direct effects on mortality of organisms (reviewed in Marcus 2001 and Breitburg et al. 2001, Miller et al. 2002), but it can have indirect effects on mortality through predator–prey interactions.”
- Effects of low dissolved oxygen on planula settlement, polyp growth and asexual reproduction of Aurelia aurita (2008, background): “Hypoxic waters are stressful to fish and many other organisms, and their abundance, vertical migration and behavior can be significantly affected (Roman et al. 1993, Breitburg 1994, Breitburg et al. 1994, 1997, 1999, Miller et al. 2002).”
- Aggregation on the edge: effects of hypoxia avoidance on the spatial distribution of brown shrimp and demersal fishes in the Northern Gulf of Mexico (2012, background): “Similarly, the median LC50 for juveniles of several mid-Atlantic species was 0.5 to 1.6 mg l−1 (Miller et al. 2002), which is only slightly lower than the range of avoidance thresholds reported here (1.0 to 1.99 mg l−1).”
- Juvenile weakfish Cynoscion regalis distribution in relation to diel-cycling dissolved oxygen in an estuarine tributary (2007, background): “…much above the lethal DO concentrations (LC50 values) determined for the juvenile stage of some estuary-dependent fishes (Burton et al. 1980, USEPA 2000, Miller et al. 2002) and they overlap concentrations shown to be detrimental for growth (Bejda et al. 1992, USEPA 2000, Stierhoff et al. 2006).”
- Ecophysiological responses of juvenile summer and winter flounder to hypoxia: experimental and modeling analyses of effects on estuarine nursery quality (2006, background): “…as nurseries is attributed primarily to physicochemical regimes (e.g. temperature and salinity) that are physiologically suitable or optimal, abundant prey resources, and low predation risk, conditions that promote rapid growth and enhance survival of young fishes (Joseph 1973, Miller et al. 1985).”
- Effects of hypoxia, and the balance between hypoxia and enrichment, on coastal fishes and fisheries (2002, background): “Avoidance versus growth: Coutant 1985; Pihl et al. 1991b; Scholz and Waller 1992; Howell and Simpson 1994; Petersen and Pihl 1995; U.S. Environmental Protection Agency 2000; Eby 2001; McNatt 2002; Miller et al. 2002.”