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Last modified
7/14/2009 5:02:32 PM
Creation date
5/17/2009 11:40:47 PM
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UCREFRP
UCREFRP Catalog Number
8095
Author
National Research Council.
Title
Impacts of Emerging Agricultural Trends on Fish and Wildlife Habitat.
USFW Year
1982.
USFW - Doc Type
Washington, D.C.
Copyright Material
NO
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<br />9 <br /> <br />the development of special agency groups to enforce them have spurred <br />evaluation efforts, while, at the same time, techniques have been <br />evolving for assessing other nonmarket goods and services that can be <br />applied to wildlife habitat values. <br />There are a variety of measurement techniques that can be used to <br />quantify wildlife numbers and habitat quality. These techniques <br />encompass fish and wildlife population surveys, wildlife community <br />enumerations, and habitat assessments. <br />A diversity of techniques has been devised to estimate fish and <br />wildlife density (i.e., the number of individuals of one species per <br />unit area or volume). Some are indexes that allow only year-to-year <br />or area-to-area comparisons; others are total censuses that purport to <br />count an entire population. These techniques are best summarized for <br />wildlife by Schemnitz (1980) and for fish by Bagenal (1978). <br />Traditionally, these estimates have been time-consuming, covering <br />several seasons or years, a span rarely allowed for in current impact <br />assessment work. Even methods like the Peterson-Lincoln index require <br />the marking of a significant number of animals and a high rate of <br />recapture. Newer indexes that also convert to density estimates are <br />being developed and tested, so that ultimately such population <br />assessment may demand less time and money and fewer people (Burnham et <br />al. 1980). <br />To assess the density of the numerous wildlife species coexisting <br />in an area is an enormous task. Nevertheless, some effort must be <br />made to determine the numbers of different species that occur (species <br />richness) and their relative abundance. Whereas line or spot censuses <br />may provide information on species richness, data necessary for total <br />censuses (for calculating species density indexes) are difficult to <br />obtain. with small birds, mist netting has been used regularly, and <br />fisheries scientists have used nets and traps of various sizes. <br />Mammalogists have combined live and dead traps to assure <br />representation of all species for an index to relative abundance. All <br />these techniques have problems of inaccuracy and are time-consuming, <br />but they are being improved. <br />Standard vegetation assessment techniques have been used to <br />sample the habitats of terrestrial wildlife. These include cover <br />maps, quadrats, transects, and bisects. Aquatic habitats are most <br />difficult to appraise and involve physical parameters such as depth, <br />size of substrate, chemistry, and vegetation. All are difficult to <br />relate to how fish and wildlife use the habitat, and many assessments <br />of habitat use fish or wildlife density as a measure of carrying <br />capacity and, thereby, quality of the habitat. Again, these <br />measurements are time-consuming and often require several seasons of <br />study because they involve observational rather than experimental <br />approaches. <br />New qualitative approaches to habitat assessment have been <br />developed by several federal agencies, which are often pressured to <br />make judgments or plan for future resource management needs with <br />little scientific justification. The U.S. Fish and Wildlife Service <br />is now testing a system called the Habitat Evaluation Procedure (HEP) <br />(Schamberger and Farmer 1978). This is a community-oriented approach <br />
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