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`t' <br /> <br />competition as the causative agents ,fqr the.de.cline of ths,.chub. Discussion <br />of our observations on the ecology of Gila nigrescens-axe relevent here. <br />Among the eight stations where taken, adult chubs- were present only in those <br />habitats. that had some combination of pools at least 1 m deep, shade, and <br />undercut banks or cover (~e.g., downed logs-, submerged shrubs). Juveniles <br />were found in shallower Habitats, with or without cover. This- seems to suggest <br />that the habitat requirements of the adults are the limiting factor for the <br />survival of the species. That is, as the natural waterways are being continuously <br />modified by hydrological projects, it is the adult habitats that are diminished. <br />For example, it is obvious that habitats such as we observed in the .Rio <br />San Miguel at Ignacio Zaragoza, with a maximum depth of SQ mm, could not support <br />adult Chihuahua chubs, whose body depth. is nearly as great as this. A 'constant <br />flow of water is not necessarily important to adult survival and spawning. <br />Rather it is the-maintenance of those critical features listed above that is. <br />necessary. For example, the presence of adult and juvenile Gila nigrescens <br />in the small, isolated pool at the base of a bridge in the Bus illos. basin may <br />indicate- that this species: can survive i'n intermittent environments asp long <br />as-the pools persist tfirougliout the. dry seasons. This description also <br />characterizes the situation at Arroyo de Aguila, Minckley-(1973,108) reported <br />this: type of ecological adaptation ,for the Sonora chub, Gila ditaenia Miller. <br />It may be argued that large. volumes of water would. be best for the survival - <br />of the Chihuahua chub.. Our observations support this- contention as-long as <br />ample. pools, etc., are maintained. For example., the population in the Rio <br />Santa Maria above. Buenaventura is abundant, b.ut further modification of the <br />habitat that would increase.._currents:and decrease the number of pools, undercut <br />banks and embayments~ would drive the population to extinction. Such a ~' <br />scenario may have occurred in-the Mimbres River. <br />The marked reduction in abundance and distribution of Gila ni'grescens <br />thus may be attributed to habitat alteration or loss from groundwater mining, <br />channelizati.on, water diversion, deforestation, and pollution. We also noted <br />the frequent occurrence of exotic species. However, what role they may play <br />has-not b.een~determined and we can only assume that five introductions (carp, <br />longfin dace, black bullhead, mosquitofi'sh, and rock bass) into an area <br />characterized by a depauperate fish fauna can scarcely enhance the survival of <br />the native fishes-. Gila niQrescens is not reproducing successfully in the <br />Mimbres River (only 12 small to large adults have been taken since 1975), whereas <br />long~in dace. (Agosa chrysogaster), are. excessively abundant; it is tempting to <br />infer that this exotic not only eliminated the native Notropis formosus but <br />also may be suppressing the survival of the. Chihuahua chub. However, that <br />hypothesis must be tested be.~ore competition is inferred. <br />We recommend that (1) the Chihuahua chub. be officially designated an ' <br />endangered species, for both the U.S. and Mexico; (2):a rehabilitated refuge be <br />selected for it, with.adeduate protection, in the Mimbres River basin; (3) a <br />stock of the Mimbres population, now being developed at llexter National Fish <br />Hatchery, be reestablished in the Mimbres- refuge when appropriate; (4) additional <br />populations of the species be sought and monitored in the Rio Casas Grandes, <br />Chihuahua - the genetically closest stock to that of the Mimbres River; and <br />(5) an attempt be made to designate a refuge for the species in Mexico so <br />as to assure perpetuation, should the Mimbres- River population be extirpated. <br /> <br />