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Last modified
7/14/2009 5:01:46 PM
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5/20/2009 1:40:28 PM
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UCREFRP
UCREFRP Catalog Number
7950
Author
Williams, J. E. and G. R. Wilde
Title
Taxonomic Status And Morphology Of Isolated Populations Of The White River Springfish,
USFW Year
1981
Copyright Material
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<br />TABLE 1. Temperature and minimum dissolved oxygen values of the spring source in waters <br />containing Crenichthys baileyi. Data from Hubbs and Hettler (1964) and personal observation. <br /> <br />SPRING <br /> <br />TEMPERATURE (oC) <br /> <br />OXYGEN (ppm) <br /> <br />PRESTON BIG <br />MORMON <br />HOT CREEK <br />MOON RIVER <br />HIKO <br />CRYSTAL <br />ASH HEAD POOL <br />OUTFLOW CREEK <br />MOAPA HEADWATER SPRINGS <br />TAYLOR (=HOME) <br /> <br />21.0 <br />37.0 <br />31.3 <br />33.3 <br />26.3 <br />26.0-27.0 <br />35.9 <br />34.0 <br />30.0-31.1 <br />31.0 <br /> <br />3.3 <br />0.7 <br />1.6 <br /> <br />3.0 <br />1.6-3.0 <br />2.4 <br />2.1-2.6 <br />4.0-5.8 <br />5.7 <br /> <br />of various populations of C. baileyi. The need for such an investigation was made urgent <br />by the recent loss of the Hiko Spring population due to exotic fish introductions. <br />Largemouth bass (Micropterus salmoides) apparently were introduced into Hiko Spring <br />in February 1965 (B. L. Wilson, pers. comm.). Shortfin molIies (Poecilia mexicana) and <br />mosquito fish (Gambusia affinis) were introduced into Hiko in January or February <br />1965. Shortfin mollies, mosquitofish, and largemouth bass increased in abundance <br />through 1965. By February 1966, springfish were rare, and were extinct in June 1967. Part <br />of the Crenichthys decline also is attributable to a parasite, Lernaea, that probably was <br />introduced along with the exotic fishes. Crenichthys baileyi of Hot Creek Spring were <br />thought to have been extirpated in the early 1970's when largemouth bass entered the <br />spring from Dacey Reservoir, where they had been introduced as game fish. Fortunately, <br />a recently discovered group of the springfish from Hot Creek survived because they were <br />isolated by den~e emergent vegetation from the main pool area. Exotic species (Poecilia <br />mexicana, P. reticulata, Gambusia affinis, and Cichlasoma nigrofasciatum) have been <br />introduced into other springs inhabited by Crenichthys baileyi (Deacon and Bradley <br />1972, Hubbs and Deacon 1964). Establishment of exotic species has resulted in depressed <br />activity cycles and reduced population numbers of C. baileyi in these springs (Deacon <br />and Wilson 1967, Deacon et aI. 1964). Exotic species also have been indicated as sources <br />of Lernaea (Copepoda) and Contracaecum (Nematoda) that parasitize Crenichthys <br />baileyi in Moapa River headwater springs (Wilson et aI. 1966). The current status of each <br />population will be treated in later sections. <br />The published material relating to this species usually has centered around the fish's <br />ability to inhabit seemingly hostile environments (Hubbs and Hettler 1964) and their <br />resulting activity patterns (Deacon and Wilson 1967, Hubbs et aI. 1967). Kopec (1949) <br />reported on aspects of early life history of C. baileyi. Relatively little attention has been <br />afforded the taxonomy of this species despit~ the sugge~tion by work on other <br />cyprinodonts in the southwestern United States that subspecific status might be <br />warranted for certain populations (Miller 1948). Reider (1971) compared the <br />morphology of four spring populations of Crenichthys baileyi. However, his failure to <br />examine specimens from other springs or to separate data by sex ham pered interpretations <br />of his results and no attempt at describing distinct populations was made. <br /> <br />MATERIALS AND METHODS. During the course of this study we attempted to examine <br />specimens of Crenichthys baileyi from every locality where they exist or have historically existed. <br />Specifically, we based our study on series of 30 adult fish from the following springs: Preston Big, <br /> <br />487 <br />
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