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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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i , <br />The user must decide what part of a body of water is to qualify as "summer <br />j habitat". To this point, it .has been implied that the entire area would be <br />( used. This is not necessarily so. In the case of a large, stratified lake, <br />for example, only that area shallower than the depth of the bottom of the <br />thermocline might be included as as "available habitat". In a river, areas <br />where the velocity exceeds some threshold value might be excluded. If such a <br />preliminary screening step is taken, the decision about limiting the area used <br />j as available habitat applies for all model variables. The area included as <br />summer habitat for V1 should also be used as the total area (that is, the <br />divisor) for V3 and V8i the model output (HSI) applies only to this area. <br />Interpreting Model Outputs <br />The model described above can generate HSI's to any. desired number of <br />decimal places, but it would be misleading to present results to a level of <br />precision greater than ±0.1. The model cannot be expected to discriminate <br />among different habitats with high resolution at this stage of development. <br />It depends on a series of untested assumptions and known oversimplifications. <br />Interactions among model variables and species interactions both play a role <br />in determining habitat quality for northern pike, but these influences are <br />ignored. I recommend interpreting HSI outputs as indicators (or predictors) <br />of excellent (0.8-1.0}, good (0.5-0.7), fair (0.2-0.4), or poor (0.0-0.1) <br />habitat. <br />Habitats with high HSI's would, on average, be expected to have higher <br />standing crops of northern pike than habitats with low HSI's, but a close <br />correlation between population size and HSI is unlikely. Factors not included <br />in this habitat model can also limit northern pike populations. <br />ADDITIONAL HABITRT MODELS <br />Aggus and Bivin (in press) used angler harvest as the criterion of habitat <br />suitability and calculated a regression equation relating harvest to reservoir <br />habitat variables for 37 impoundments in the conterminous United States: <br />Loglo harvest = 3.7882 - 0.0177 (growing season) - 0.8447 (Log,o outlet depth) <br />RZ = 0.67 <br />Units are kg/ha (harvest), days (growing season), and feet below a specified <br />elevation (outlet depth). These authors discuss procedures for converting <br />measured or predicted harvest values to HSI's. <br />28 <br />r~ <br />l~ <br />
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