Laserfiche WebLink
<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 />