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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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typically had TP levels <_ 0.10 ppm (Moyle 1956). Moyle noted that temperature <br />may also explain patterns of fish distribution in Minnesota and cautioned <br />against overemphasis on edaphic factors alone. <br />Ionic concentrations appear to be directly limiting to northern pike only <br />in coastal and arid environments. Ryder et al. (1974) noted that TDS levels <br />are rarely so low that ions essential for fish metabolism and growth are <br />limiting; these authors speculated that such a limit is near or below 3 ppm, <br />and very few natural waters are that dilute. Waters with high ionic concentra- <br />tions apparently do limit the distribution of northern pike, but the critical <br />concentration is unknown. Northern pike apparently do not utilize brackish <br />habitats in North America, but there are reports of pike occurring in the <br />Baltic Sea at salinities of 10 ppt and reproducing at salinities of 7 ppt <br />(Svardson, personal communication cited in Toner and Lawler 1969), and pike <br />have been commercially harvested from brackish waters in Finland (Lind 1977). <br />Rawson and Moore (1944) found northern pike in saline Saskatchewan lakes only <br />where TDS levels were less than about 3,500 ppm (roughly equivalent to a <br />salinity of 3.5 ppt). Northern pike are said to have "some tolerance" to TDS <br />levels of 2,200 to 3,800 ppm in alkaline Nebraska lakes (Schoenecker 1970), <br />but pike did not spawn in a Nebraska lake with a TDS level of 1,024 ppm <br />(McCarraher 1962). High concentrations of particular ions may be harmful at <br />salinities which do not cause general .osmoregulatory stress.' For example, <br />mortality of northern pike embryos and fry is extensive when total alkalinity <br />exceeds 950 mg/1 (McCarraher 1971). Until effects of individual ions are <br />clarified, it seems reasonable to assume an upper TDS limit of 3,500 ppm. <br />Self-sustaining populations of northern pike can persist at pH's as low <br />as 5.0 (Harvey 1980). Lower pH's are damaging to fry. Cumulative mortality <br />of fry held at a pH of 4.2 (range 4.0 to 4.3) was 96.5%, compared to 25.6% <br />mortality at a pH of 5.2 (4.7 to 6.0), and 17% mortality at a pN of 6.8 (6.5 <br />to 7.2) (Johansson and Kihlstrom 1975). Towards the opposite extreme, northern <br />pike occur in lakes with a pH of 8.9 (Rawson and Moore 1944; Priegel and Krohn <br />1975). Fingerling and large r.northern pike can survive pH's in the 9.0 to 9.5 <br />range, but it is not clear whether successful reproduction can occur at the <br />upper limit of this range (McCarraher 1962). <br />Northern pike grow through a broad size range; tolerances, requirements, <br />and preferences change as they grow. Although most developmental changes are <br />gradual, it is useful to describe habitat requirements for northern pike in <br />terms of four stages: spawning/embryo; fry; juvenile; and adult. These life <br />stages, for purposes of this discussion, are defined as follows: <br />1. Spawning/embryo. Includes spawning requirements and requirements of <br />the developing embryo. <br />2. Fry. Immediately after hatching to size .at which they assume adult <br />proportions; i.e., approximately 6.5 cm, according to Franklin and <br />Smith (1960). <br />3. Juvenile. From 6.5 cm to onset of sexual maturity (beginning of <br />gonadal maturation). <br />n <br />8 <br />
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