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Last modified
7/14/2009 5:02:29 PM
Creation date
6/1/2009 12:01:48 PM
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UCREFRP
UCREFRP Catalog Number
7143
Author
Inskip, P. D.
Title
Habitat Suitability Index Models
USFW Year
1982.
USFW - Doc Type
Northern Pike.
Copyright Material
NO
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Summer habitat for northern pike is limited in some lakes by a combination <br />of high surface temperatures and low oxygen concentrations in cooler, deeper <br />strata. Krohn (1969) reported a mid-August die-off in a Wisconsin lake follow- <br />ing several very warm days. Temperatures ranged from 32° C at the surface to <br />24° C at a depth of 3.7 m, the lower limit of oxygenated water. High surface <br />temperatures (32° C) coincided with the beginning of a northern pike die-off <br />in a Missouri reservoir (Goddard and Redmond 1978). Dead fish were found to <br />have bacterial, fungal, and protozoan infections. Nigh surface temperatures <br />can contribute to high incidences of infection by lowering resistance to <br />disease and by concentrating the pike in a narrow depth stratum. Substantial <br />mortality of northern pike occurred in an Iowa marsh when temperatures reached <br />35.6° C at the surface and 31.7° C at the bottom (Ridenhour 1957). In this <br />case, oxygen concentrations were adequate, but temperatures were too high at <br />all depths. <br />It seems likely that high summer and/or winter temperatures limit the <br />southern distribution of northern pike. Although present in the Mississippi <br />River drainage, pike are absent from waters south of the 32.2° C isotherm for <br />normal July daily maximal air temperature, except in thermally stratified <br />reservoirs where they have been introduced (Visher 1954; Grossman 1978). <br />Northern pike are absent from all but the upper reaches of the Ohio River and <br />its tributaries, although muskellunge (Esox masquinongy), a closely related <br />species with similar spawning habitat requirements, are widely distributed in <br />the drainage (Forbes and Richardson 1920; Gerking 1945; Trautman 1957; Grossman <br />1978). Much of the Ohio River is south of the 31° C isotherm for mean maximal <br />July air temperature.(National Oceanographic and Atmospheric Administration <br />1974). Surface water temperatures of 29 to 31° C are not unusual for Ohio <br />lakes (Tressler et al. 1940). In the. laboratory, young northern pike do not <br />grow at temperatures above 28° C, even when fed ad libitum (Casselman 1978). <br />Temperatures greater than 32° C can cause death within Z days (Scott 1964). <br />High temperatures at other times of the year may limit reproductive <br />success. In a laboratory study, the percentage of yellow perch that spawned <br />was highest when they were exposed to temperatures <_ 6° C for a minimum of 185 <br />days, beginning October 30 (Jones et al., unpublished data cited in Hokanson <br />1977). No successful spawning occurred among perch held at a minimum tempera- <br />ture of 12° C or higher. Northern pike, which occur farther north than do <br />yellow perch (Scott and Grossman 1973), are presumably also adapted to a <br />seasonal temperature cycle involving cold winters. <br />Dissolved oxygen concentration is usually the most important habitat <br />variable affecting overwinter survival of northern pike. Shallow, heavily <br />vegetated lakes and rivers with low discharges - habitats that might be quite <br />favorable for northern pike at other times of the year (Johnson and Moyle <br />1969) -frequently develop l.ow dissolved oxygen concentrations during winter. <br />Laboratory and field observations indicate that pike are more tolerant of low <br />dissolved oxygen conditions during winter than are many other temperate <br />species, including black crappie (Pomoxis nigromaculatus), largemouth bass <br />(Micropterus salmoides), bluegili (Lepomis macrochirus), walleye (Stizostedion <br />vitreum vitreum), and yellow perch (Cooper and Washburn 1949; Moyle and <br />Clothier 1959; Patriarche and Merna 1970; Petrosky and Magnuson 1973). If the <br />6 <br />
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