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<br />Deductive Evidence <br />Perhaps the most compelling, albeit circumstantial, evidence supporting <br />the argument that introduced fishes have negatively affected populations of <br />endangered Colorado River fishes is obtained through a deductive assessment <br />based on our general knowledge of fishery ecology, the Colorado River <br />ecosystem and the changes that have occurred therein. It is generally agreed <br />that the overall decline of native fishes of the Colorado River basin is the <br />result of stream dewatering, altered flow and temperature regions downstream <br />from dams and water diversions, poor land-use practices that have affected <br />water quality and quantity, "pollution," the negative effects of introduced <br />fishes and perhaps other factors. However, the relative importance of each of <br />these is not always understood. Indeed, aside from the obvious detrimental <br />effect of dewatering, only that of reduced temperatures below dams has been <br />clearly demonstrated. However, there are river reaches in the upper basin <br />(e.g. lower Colorado and Green rivers) that have not had their flow or <br />temperature regimes or water quality meaningfully altered but nonetheless <br />their populations of endangered fishes have significantly declined. Because <br />these reaches have been very successfully colonized by-several introduced <br />species (Tyus et al. 1982), one cannot escape the seemingly well-founded <br />speculation that introduced fishes played an important role in this decline. <br />Kaeding and Osmundson (MS) present this argument in more detail and also point <br />out that unusually slow growth of Colorado squawfish in the upper basin (the <br />upstream limit of historic range) makes their population especially vulnerable <br />to the negative effects of increased early-life mortality that would result <br />from competition with or predation by introduced fishes. <br />Additional information indicating potential competition between Colorado <br />squawfish and introduced fishes was provided by McAda and Tyus (1984). They <br />analyzed diets and habitat use of age-0 Colorado squawfish and those of <br />sympatric species. McAda and Tyus found high dietary overlap among squawfish, <br />channel catfish and red shiner (both introduced species) and- high spatial <br />overlap among squawfish, red shiner and fathead minnow (also an introduced <br />species). However, the authors cautioned that such overlap is perhaps not <br />important if dietary and spatial resources are not limited. <br />SUMMARY <br />Although definitive data are lacking, available information strongly <br />suggests introduced fishes have negative effects on populations of endangered <br />fishes in some river reaches of the Colorado River basin. Like Colorado <br />squawfish, these introduced forms are commonly considered warm- water species. <br />Coldwater fishes, such as salmonids, do not persist in river reaches occupied <br />by Colorado squawfish and therefore do not have important direct negative <br />effects on this or other endangered Colorado River fishes. <br />References <br />Brooks, J.E. No date. Annual reintroduction and monitoring report for <br />razorback sucker, Xyrauchen texanus, in the Gila River basin, Arizona, <br />1985. Arizona Game and Fish Department, unpublished mimeographed report.