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<br />Copeia, 1995(3), pp. 636-649 <br />Patterns of Morphological Variation among Endangered <br />Populations of Gila robusta and Gila cypha <br />(Teleostei: Cyprinidae) in the Upper Colorado River Basin <br />i <br />DOUGLAS M. MCELROY AND MICHAEL E. DOUGLAS <br />IX a 9 <br />The native fish fauna of the American southwest is in decline as a result of <br />t habitat destruction, disruption of natural water flows, and introduction of non- <br />native species. The status of several members of the cyprinidgenusl6.Gila-0ccur- <br />ring in the upper Colorado River basin-is-particularly tenuous, in part because._.- <br />of uncertainty regarding their taxonomic status. To examine this uncertainty, <br />we have sampled 363 specimens of G. robusta and G. cypha from eight localities <br />in the upper Colorado River basin and the Grand Canyon and used canonical <br />discriminant and cluster analysis to categorize patterns of morphological vari- <br />ation at three levels of biological organization. At the population level, all sam- <br />pled populations of both species differed significantly, although there was no <br />relationship between morphological similarity and geographic proximity of pop- <br />ulations in either species. At the species level, the two forms were clearly distinct <br />in morphology whether in sympatry or in allopatry. At the generic level, we <br />found two somewhat contradictory results: (1) conspecifics from altopatric lo- <br />calities generally clustered together to the exclusion of heterospecifics; and (2) <br />heterospecific populations at Cataract and Desolation canyons were more similar <br />to one another than to allopatric conspecifics. This locality effect influencing the <br />morphological similarities between species at these sites may be a consequence <br />of either introgressive hybridization and/or convergent local adaptation. In gen- <br />eral, allopatric populations of both G. robusta and G. cypha appear to represent <br />independent evolutionary and conservation units. Populations of Gila should <br />not be considered in isolation of congeners or of the environment in which they <br />occur, and biological foresight and an emphasis on habitat conservation should <br />be used in managing these species. <br />MEMBERS of the western North American <br />cyprinid genus Gila represent both a tax- <br />onomic conundrum and a morphological curi- <br />osity. Extensive (but poorly defined) morpho- <br />metric variation against a background of mor- <br />phological specialization is characteristic of the <br />group (Minckley, 1973; Douglas et al., 1989; <br />Douglas, 1993), a dichotomy that has hampered <br />attempts to elucidate species interrelationships <br />(Douglas et al., 1989). The G. robusta species- <br />complex has proven especially problematic. <br />Several big-river species of the Colorado River <br />basin (e.g., G. cypha, G. elegans) display extreme <br />morphologies, presumably reflecting adapta- <br />tions to life in high current regimes (Miller, <br />1946; Minckley, 1973; but see Kaeding et al., <br />1990). However, morphological variation with- <br />in and among populations of these and other <br />members of the G. robusta complex is extensive, <br />and few if any morphometric characters reliably <br />separate species (see Suttkus and Clemmer, <br />1977; Smith et al., 1979). Evidence (DeMarais <br />et al., 1992; Dowling and DeMarais, 1993) that <br />introgressive hybridization has contributed to <br />the evolutionary history of the group at several <br />levels further clouds the distinction among spe- <br />cies, and with other factors confound the iden- <br />tification of evolutionary units and limit confi- <br />dence in sorting individual specimens to species. <br />Questions of species identity in Gila have con- <br />sequences beyond evolutionary biology and tax- <br />onomy. To develop appropriate conservation <br />strategies for these endangered or threatened <br />taxa, it is desirable to clearly establish species <br />identity and distinctiveness (Valdez and Clem- <br />mer, 1982; Douglas et al., 1989). However, the <br />need to protect these fishes precludes extensive <br />sampling and/or handling of specimens. Con- <br />sequently, detailed quantitative studies on Gila <br />have been limited in both number and scale, <br />and recovery efforts remain stalled largely be- <br />cause of the taxonomic confusion surrounding <br />the G. robusta complex (Douglas et al., 1989). <br />Vanicek and Kramer (1969) found differ- <br />ences in growth and length-weight relationships <br />between G. robusta and G. elegans and suggested <br />that they constituted distinct species (as opposed <br />to subspecies of G. robusta). Holden and Stal- <br />naker (1970) concluded that G. robusta and G. <br />elegans were each morphologically homoge- <br />m 1995 by the American Society of ichthyologists and Herpetologists