ESA, Proposed Threatened ESA, Threatened New Mexico-WCA, Endangered

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Scientific Name: Gambusia nobilis Common Name: Pecos gambusia BISON No.: 010225 Legal Status: Arizona, Species of Special Concern ESA, Endangered ESA, Proposed Endangered ESA, Proposed Threatened ESA, Threatened New Mexico-WCA, Endangered New Mexico-WCA, Threatened USFS-Region 3, Sensitive None Distribution: Endemic to Arizona Endemic to Arizona and New Mexico Endemic to New Mexico Not Restricted to Arizona or New Mexico Northern Limit of Range Major River Drainages: Dry Cimmaron River Canadian River Southern High Plains Pecos River Estancia Basin Tularosa Basin Salt Basin Rio Grande Rio Mimbres Zuni River Gila River Southern Limit of Range Western Limit of Range Eastern Limit of Range Very Local Rio Yaqui Basin Wilcox Playa Rio Magdalena Basin Rio Sonoita Basin Little Colorado River Mainstream Colorado River Virgin River Basin Hualapai Lake Bill Williams Basin Status/Trends/Threats (narrative): Federal (USDI): Endangered, State NM: Endangered. The populations are endangered, but stable in New Mexico. In New Mexico it is presently limited to seven isolated locations at Bitter Lake National Refuge (Chaves County) and one population at Blue Spring (Bednarz 1979, Lee et al 1981). The historic range of Pecos gambusia was limited mainly to spring complexes on Bitter Lake National Wildlife Refuge, Blue Spring, Toyah Creek drainage, Leon Creek drainage, and Comanche Springs (Propst 1999), but, groundwater pumping dried Comanche Springs and thus extirpated this population by the 1950s (Echelle and Echelle, 1980). The greatest threat to the Pecos gambusia is hybridization and competition with the western mosquitofish (Bednarz 1979, Echelle ans Echelle 1980, Lee et al. 1981), however, structural differences in female genitalia, keeping hybridization at a low rate (Bednarz 1979). The

apparent reproductive capacity and smaller size at maturity for males, the western mosquitofish appears capable of expanding its population more rapidly than the Pecos gambusia (Bednarz 1979). Pecos gambusia appears to co-exist well with all species of fish found in the same habitat except other gambusia (Bednarz 1979). Echelle and Echelle (1980) attributed the absence of Pecos gambusia from Lake St. Francis on that refuge to the presence of green sunfish. Hubbs and Echelle (1972, Lee et al. 1981) identified groundwater pumping as the greatest threat to extant populations of Pecos gambusia. Distribution (narrative): The historic range of Pecos gambusia was limited mainly to spring complexes on Bitter Lake National Wildlife Refuge, Blue Spring, Toyah Creek drainage, Leon Creek drainage, and Comanche Springs (Propst 1999). Historically, the Pecos gambusia occurred as far north as the Pecos River near Fort Sumner (Sublette et al 1990). The Pecos gambusia is endemic to springs and spring systems of the Pecos River basin of southeastern New Mexico and western Texas (Hubbs and Springer, 1957, Echelle et al.1989). The Pecos gambusia is also found in springs and gypsum sinkholes on Bitter Lake National Wildlife Refuge (near Roswell) and Blue Spring and its outflow (near Whites City) apparently are the only areas of regular occurrence of Pecos gambusia in New Mexico (Bednarz, 1979). The Pecos gambusia once occurred throughout the Pecos River drainage in southwestern Texas and southeastern New Mexico (Hubbs and Springer 1957, Hubbs and Echelle 1972, Bednarz 1979). Distribution in New Mexico is currently limited to the Bitter Lake National Wildlife Refuge and Blue Springs (Lee et al. 1981). Its range is restricted to sinkholes or springs and their outflow on the west side of the Pecos River in Chaves and Eddy countries (Bednarz 1979). Key Distribution/Abundance/Management Areas: Panel key distribution/abundance/management areas: Breeding (narrative): There is little information on the breeding behavior of Pecos gambusia, but they may spawn several times a year. Pecos gambusia produce live young (Propst 1999). Habitat (narrative): Natural cover used by the Pecos gambusia consisted of aquatic vegetation overhanging banks and submerged cliffs (Bednarz 1979). Any shallow area with aquatic vegetation seems suitable habitat if other factors are within the range of tolerance (Bednarz 1979). Bednarz (1979) reported the largest populations of Pecos gambusia were found near spring flows and seepages, while the western mosquitofish were found in temporary ponds and waters with unstable conditions. Typically Pecos gambusia inhabit shallow margins of clear vegetated spring waters high in calcium carbonate (Lee et al. 1981, Sublette et al. 1990). Bednarz (1979) reported Pecos gambusia most common near the springhead in habitats having zero-velocity water. Pecos

gambusia tended to occupy mainly still-water and low-velocity habitats in the presence of western mosquitofish (Propst 1999). Hubbs et al. (1995) found that Pecos gambusia occupied vegetated habitats and avoided open water in areas that also had largespring gambusia (Gambusia geiseri). Key Habitat Components: stenothermal, high conductivity springs and spring runs. Breeding Season: January June October February July November March August December April September May Panel breeding season comments: Aquatic Habitats: Large Scale: Rivers Streams Springs Spring runs Lakes Ponds Sinkholes Cienegas Small Scale: Runs Riffles Pools Open Water Shorelines Panel comments on aquatic habitats: Important Habitat Features (Water characteristics): Current Gradient Water Depth Fast (> 75 cm/sec) High gradient (>1%) Very Deep (> 1 m) Intermediate (10-75 cm/sec) Intermediate Gradient (0.25-1%) Deep (0.25-1 m) Intermediate (0.1-0.25 Slow (< 10 cm/sec) Low Gradient m) None (<0.25%) Shallow (< 0.1 m) None Panel comments on water characteristics:

Important Habitat Features (Water Chemistry) Temperature (general) Turbidity Cold Water (4-15 C) High Cool Water (10-21 C) Intermediate Warm Water (15- Low 27 C) Panel comments on water chemistry: Conductivity Very High (> 2000 μs/cm) High (750-2000 μs/cm) Intermediate (250-750 μs/cm) Low (< 250 μs/cm) Important Habitat Features (Structural elements): Substrate Bedrock Silt/Clay Detritus Sand Gravel Cobble Boulders Cover Rocks, boulders Undercut banks Woody debris Aquatic vegetation Rootwads Not important Overhanging vegetation Panel comments on structural elements: Diet (narrative): The Pecos gambusia is a carnivorous surface feeder consuming any insect settling on the water surface (Bednarz 1979). Although the Pecos gambusia feeds all day, the primary time of feeding correlates with insect activity at night (Bednarz 1979). The Pecos gambusia will prey on any type of surface and mid-water insects of adequate size especially Culicidae and Corixidae. (Bednarz 1979).

Diet category (list): Planktivore Herbivore Insectivore Piscivore (Fish) Omnivore Detritivore Grazing Effects (narrative): There is no specific information with respect to cattle grazing and the Pecos gambusia, however, grazing could have an impact on spring habitats occupied by the species. Panel limiting habitat component relative to grazing and comments: Panel assessment: Is this species a priority for selecting a grazing strategy? Throughout the species distribution in New Mexico and Arizona YES NO UNKNOWN In key management area(s) YES NO UNKNOWN Principle Mechanisms Through Which Grazing Impacts This Species (list): **May be Revised** Alteration of bank structures Alteration of substrate Alteration of water regimes Altered stream channel characteristics Altered aquatic vegetation composition Altered bank vegetation structure Change in food availability Change in water temperature Change in water quality Habitat fragmentation Increased turbidity Other biotic factors Parasites or pathogens Population genetic structure loss Range improvements Trampling, scratching Panel causal mechanisms comments:

Authors Draft: Magaña, H.A. and Rinne, J.N. GP 2001: GP 2002: Revision: Bibliography: Bednarz, J.C. 1979. Ecology and Status of the Pecos Gambusia, Gambusia Nobilis (Poeciliidae), in New Mexico (Pecos Gambusia). The Southwestern Naturalist 24 (2):311-322. Lee, D. S., Gilbert C. R., Hocutt C. H., Jenkins R. E., Callister D. E., and Stauffer J. R. 1981. Atlas of North American Freshwater Fishes: North Carolina, North Carolina State Museum of Natural History, 1981, c1980. Propst, D. L. 1999. Threatened and endangered fishes of New Mexico. New Mexico Game and Fish Tech Report 1. 84 pp. Sublette, J. E., M. D. Hatch, and M. Sublette. 1990. The Fishes of New Mexico. University of New Mexico Press. Albuquerque. 393 pp.