An ecological study of southern Wisconsin fishes; the brook silversides (Labidesthes sicculus) and the cisco (Leucichthys artedi) in their relations to the region,

Cahn, Alvin R.

doi:10.5962/bhl.title.50172

Cited by 33 publications

(31 citation statements)

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“…Perhaps the first was Wells (1914) who reported on the temperature related movements of Micropterus dolomieu. His work, that of Shelford and Powers (1915) on Clupea pallasii, and that of Cahn (1927) on Labidesthes sicculus and Leucichthys artedi were criticized by Sullivan (1954) who suggested that the results they obtained could have been due to convection currents instead of to temperature, since this variable was not controlled in their experiments.…”

Section: Orientation and Movementmentioning

confidence: 99%

The Functions of Temperature in the Ecology of the Percoid Fish Girella nigricans (Ayres)

Norris¹

1963

Ecological Monographs

116

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Section: Orientation and Movementmentioning

confidence: 99%

The Functions of Temperature in the Ecology of the Percoid Fish Girella nigricans (Ayres)

Norris¹

1963

Ecological Monographs

116

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“…Cisco also exists in lakes over other northern states, e.g., Wisconsin and Michigan. The combination of a wide geographic distribution in northern Minnesota [15] and a requirement for cold, oxygenated water [4,16,17] makes cisco a sensitive indicator Notes: 1 H max is the maximum lake depth and GR is the lake geometry ratio (GR) = A s 0.25 /H max (A s is surface area in m 2 ); 2 Little Pine Lake at Otter Tail County; 3 Little Pine Lake at Crow Wing County; 4 number of pairs of simulated and observed T or DO data (at different days and at different depths) for computing model error parameters; 5 Root-mean-square error (RMSE) between simulated and measured (https://en.wikipedia.org/wiki/Root-mean-square_deviation); and 6 Nash-Sutcliff model efficiency (NSE) coefficient [19].…”

Section: Introductionmentioning

confidence: 99%

Simulation and Validation of Cisco Lethal Conditions in Minnesota Lakes under Past and Future Climate Scenarios Using Constant Survival Limits

Jiang

Fang

2016

Water

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Fish habitat in lakes is strongly constrained by water temperature (T) and available dissolved oxygen (DO) that are changed under climate warming. A one dimensional, dynamic water quality model MINLAKE2012 was used for T and DO simulation over 48 years. A fish habitat model FishHabitat2013 using simulated T and DO profiles as input was developed to determine lethal conditions of cisco Corgenous artedi in Minnesota lakes. Twenty-three lakes that had observations of cisco mortality or survival in the unusually warm summer of 2006 were used for model validation. The cisco habitat model used a lethal temperature of 22.1˝C and DO survival limit of 3 mg/L determined through model validation and sensitivity analysis. Cisco lethal conditions in 12 shallow, 16 medium-depth, and 30 deep virtual lakes were then simulated. Isopleths of total number of years with cisco kill and average cisco kill days for the years with kills under past and future climate were generated to understand/extrapolate climate impacts on cisco in 620 Minnesota lakes. Shallow and medium-depth lakes are projected to not be good candidates for cisco refuge lakes, but deep lakes are possible cisco refuge lakes based on lethal condition projection under future warmer climate.

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“…Diel inshore-offshore migrations of freshwater fish have been recognized for many years (Cahn 1927;Hasler and Bardach 1949;Moyle 1973). These diel migrations may be important for behavioral thermoregulation (Caulton 1978), spawning (Middaugh et al 198 l), predator avoidance (McFarland et al 1979;Hanych et al 1983), and feeding (Baumann and Kitchell 1974;Hall et al 1979;Bohl 1980).…”

mentioning

confidence: 99%

Diel migrations of a zooplanktivorous fish (Menidia beryllina) in relation to the distribution of its prey in a large eutrophic lake1

Wurtsbaugh

1985

Limnology & Oceanography

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Diel changes in the distribution of the tidewater silverside (Menidia beryllina) and its prey were measured in Clear Lake, California, a large, shallow, eutrophic lake. Zooplankton prey densities were low in the littoral zone, but increased rapidly to near peak abundances 50-200 m from shore. Gill netting, trawling, and visual observations showed that tidewater silversides migrated both horizontally and vertically to feed in areas of high zooplankton abundance. At night the fish concentrated near shore and did not feed. At dawn (8 x lo*-2 x lOlo photons cm-2 nm-' s-l) the fish migrated lakeward at least 50-l ,000 m, and littoral abundance decreased from more than 100 m-2 to only 0.1 rnM2. The migration preceded the initiation of feeding by 30-60 min. After feeding 2-4 h, the fish returned to the littoral zone and swam rapidly (6-l 1 body lengths s-l) parallel to shore in narrow, continuous schools until resting aggregations formed. The fish returned to shore before they were satiated, perhaps to balance predation losses in offshore areas against foraging gains. A second period of offshore activity and feeding occurred in the afternoon and evening.

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An ecological study of southern Wisconsin fishes; the brook silversides (Labidesthes sicculus) and the cisco (Leucichthys artedi) in their relations to the region,

Cited by 33 publications

References 1 publication

The Functions of Temperature in the Ecology of the Percoid Fish Girella nigricans (Ayres)

The Functions of Temperature in the Ecology of the Percoid Fish Girella nigricans (Ayres)

Simulation and Validation of Cisco Lethal Conditions in Minnesota Lakes under Past and Future Climate Scenarios Using Constant Survival Limits

Diel migrations of a zooplanktivorous fish (Menidia beryllina) in relation to the distribution of its prey in a large eutrophic lake1

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