BLM LIBRARY 88055389 97-1 IDAHO BUREAU OF LAND MANAGEMENT January 1997 Reptiles and Amphibians in Deep Canyons: The Big Jacks and Little Jacks Creek Drainages of Owyhee County, Idaho QL 84.2 .L352 no. 97-1 by Mark F. Gerber Dr. James C. Hunger Aaron Ames Jeff Stewart ■Ld52 no. Reptiles and Amphibians in Deep Canyons: oj <]-l The Big Jacks and Little Jacks Creek Drainages of Owyhee County, Idaho A challenge cost-share agreement between U.S. Bureau of Land Management and Boise State University December 13, 1996 Mark F. Gerber Dr. James C. Munger Aaron Ames Jeff Stewart Department of Biology, Boise State University, Boise, ED 83725 INTRODUCTION Many of the reptiles and amphibians that live in southern Idaho can be found in the canyons of Owyhee county. However, of the few studies on reptiles and amphibians that have been conducted in Owyhee county (Diller 1981, Munger et al.1993, 1994, Beck 1994) none have been conducted in the deep canyon areas, such as Big Jacks and Little Jacks Creeks. These canyons, which can reach a depth of 400 meters, contain habitat suitable for many native reptiles and amphibians. However, it is presently unknown whether canyons represent a hot spot of herpetological diversity, and therefore are worthy of protection, or whether they are relatively depauperate, or are somewhere in between. This study will examine the diversity and abundance of reptiles and amphibians in deep canyons of Owyhee County, and should therefore provide a model for other similar areas in Southern Idaho. For the purposes of this report, all areas within the Big Jacks and Little Jacks Creeks drainages will be referred to as the "study area". The term "herp" is used in this report to collectively refer to reptiles and amphibians. Of the species potentially found in the study area the Spotted Frog is listed by the U.S. Fish and Wildlife Service (USFWS) as a candidate species, the Idaho Department of Fish and Game (IDF&G) as a species of special concern A (priority species), and by the Bureau of Land Management (BLM) as a sensitive species. The Northern Leopard Frog and the Mojave Black-collared Lizard are listed by the BLM as sensitive, and by IDF&G as a species of special concern A. The Western Toad is listed as an IDF&G species of special concern C (undetermined status) and by the BLM as sensitive. The Western Ground Snake, and the Longnose Snake are listed by IDF&G as species of special concern B (peripheral species). This study was designed primarily as a survey to determine presence or absence of reptiles and amphibians of the deep canyons of the Big Jacks and Little Jacks creek drainages, and to provide baseline data for future studies. In addition, we collected data to determine movement patterns of snakes in the vicinity of Parker Trail on Big Jacks Creek. METHODS AND MATERIALS Two methods of determining presence of herps were utilized; drift fences in conjunction with funnel traps, and visual encounter searches. These two methods were employed in four regimes: upland, rirn, midslope/draws, and canyon bottom. The upland regime was not actively surveyed. Reptiles found in this regime were, therefore, incidental to the study, and included road sightings (both dead and alive) and reptiles that were seen while traveling within the study site. Rim sightings included animals encountered within 100 m of the rim, including those captured in drift fence arrays. Mid-slope sightings were characterized by draws, talus benches, and other suitable habitat that was below the cliff that defined the rim regime, but did not include talus that actually emerged onto the canyon bottom. Some areas of extremely steep canyon walls did not have a mid-slope regime. The canyon bottom was defined to include all sand bars, and talus or dirt that actually emerged onto the floor of the canyon. Drift Fence installation and construction: Twenty seven drift fence arrays were placed in and near Big Jack's Creek Canyon, as shown in Fig. 1 . Drift fences were constructed of two sections of material, either construction grade silt fence or strips of sheet metal flashing. Forty-three sections were constructed of steel flashing, each section used a piece 21" wide by 25* long. The edge of each section was buried a minimum of six inches underground. On plateaus and windy slopes the bottom four inches was bent over before burying to keep the fence from blowing out of the ground. Steel fencing was installed in a trench that was no deeper than six inches and only wide enough to fit the steel in with the bottom four inches bent at a right angle to the fence (Fig. 2). Eight sections were constructed of silt fence, each section was twenty-five feet long by three feet wide with a two by two wooden post at each end and two spaced evenly between the end posts. The posts were driven into the ground at angles so they only contacted the fence at the top. Three foot long strip lathe was used to brace cloth that sagged due to uneven ground. Twenty-seven arrays were erected, 25 of which were comprised of 2 sections and the remainder of one twenty-five foot section of steel fence each. Of the twenty-seven arrays, eight were comprised of one section of steel fence and one section of silt fence, with the objective of determining whether or not there was a difference in effectiveness of each type offence. Funnel Traps: Funnel traps were constructed of aluminum window screen. A piece of screen was cut 24" on one side and 20" on the other. This piece was rolled into a cylinder 24" long and stapled together with household staples. One end of the cylinder was flattened, folded over, and clipped with clothespins. To make the funnel, a half circle was cut from the same material as the body and rolled into a funnel with a diameter of 22cm at the widest point. The point end of the funnel was cut off to make a hole that was about 3cm across. This funnel was inserted into the open end of the cylinder and stapled in place with the small hole inside the trap (Fig. 3). On each section of drift fence were placed four funnel traps, two on either side of each end of the fence. Each funnel trap was placed tightly against and parallel to the fence with the opening facing the center of the section of drift fence as in fig. 3. A dirt ramp was constructed into the opening of the funnel trap to keep reptiles from passing underneath the trap and to help guide them into the trap. To give reptiles a place of refuge from the sun, a piece of cardboard Figure 1. Location of drift fence arrays within Big JacKs Creek, Owyiiee Co., Idaho. Each array consisted of two lengths of drift fence in the orientations shown. Traps at either end of the fences are denoted in the appendix by the following code: If the fences perpendicular, the traps at the N end of the N-S segment were labeled A and B with A on the west side; traps on the S end were labeled C and D with C on the west side. Traps on the W end of the E-W fence were labeled E and F, with E to the N, and the E end labeled G and H with O to the W. IfarrayswereinaN-S line, the traps were labeled (from the N end) A, C, E, and G on the W side and B.D.F, and Hon the E side. Ifina E-W line, traps were labeled (from the W end) A, C, E, and G on the N side and B, D, F, and H on the S side. V If-, f " VI .— .'".;- 19 _/ 20 1 21 1 22 J 23 j 24 r x50. Silt Fence Installed (broken line depicts underground configuration) Figure 2a. Configuration of silt fence installation. steel drift fence installed [Straiten line depicts underground configuration) xd -:;;:-7:E4" Figure 2b. Steel drift fence installation configuration. Figure 3. Position of traps on the drift fence end. was placed inside each trap and a shade of wood, cardboard, or branches was placed over the top. Site Selection: Arrays were placed, when possible, at the junction of habitat types within each regime because of the greater likelihood of finding reptiles there that were moving between habitat types to forage. Arrays were placed in the regime defined for rim, mid-slope, and bottom of the canyon. Placement of the drift fence arrays was decided on site and on a per-array basis. Positioning of the arrays was based on practical placement with regards ease of installation, and presence of appropriate habitat. .orlng: The arrays were checked on a three day rotating basis to avoid casualties. Each trap was removed and thoroughly examined for the presence of animals. If a snake was caught in the trap, it was removed and sex, length, and species were recorded. Each snake within a 5 km radius of Parker Trail was marked with a unique number so it could be identified if recaptured. The marks were made on the ventral scales in the rear third of the snakes body. Scales were clipped to flank the number of undipped scales for each digit of the marked number. For example, three clipped scales with three undipped scales between the first two clipped scales and four between the second and third clipped scales would constitute number thirty-four. Lizards that were caught in traps were not marked, but all other data was recorded as for snakes. Animals other than reptiles or amphibians (e.g., birds and mammals) were released and no data was taken other than noting their presence in the trap. Visual Searches: Visual searches consisted of selecting a section of canyon within the Big Jacks and Little Jacks Creeks drainages that was reasonably accessible, and hiking that section looking for reptiles. While performing visual searches, rocks and other surface debris were turned. All reptiles that were captured were sexed and sized, but not marked unless they were within 5 km of the drift fence arrays. Survey areas outside the trapping area were only surveyed once. All habitat that was disturbed when performing a visual search was replaced as close to its original condition as possible. When we encountered a skin from a reptile, it was identified to species, and recorded as a capture but note was made that it was a skin. We also noted the cloud cover, temperature in Celsius, time, location, and any distinguishing features of the reptiles encountered. Visual searches of Big Jacks creek consisted of areas south of the Cottonwood/Big Jacks creek confluence three miles and north of the Cottonwood/Big Jacks creek confluence to the Wickahoney Creek confluence. We also conducted visual encounter searches for 1/4 mi north and south of where Big Jacks creek crosses Battle creek road. We surveyed Cottonwood creek from Cottonwood springs to the Big Jacks creek confluence. We surveyed a one mile section of Big Jacks creek, five miles south of the Big Jacks/Little Jacks creek confluence. The confluence of Big Jacks/Little Jacks creek was surveyed extensively as well as tributaries in the vicinity and surrounding hills. This area was visited on three occasions because of the frequency that we passed through on our way to other sections of the creeks. The bench above the confluence was searched as well as Rattlesnake creek which drains the bench into Little Jacks creek. Little Jacks creek was surveyed in fewer places because of limited access points. We surveyed a one mile section of the creek near OX reservoir and approximately two miles south of the confluence with Big Jacks creek. We also surveyed approximately one mile of Little Jacks creek on either side of the Rattlesnake creek confluence, and a one mile section beginning approximately two miles south of the Rattlesnake creek confluence. In addition to the main creeks we conducted visual encounter surveys in other areas that contained apparently good habitat for herps. Most of these areas fell along roads that travelled parallel to the main creeks. The areas that we visited on these occasions were: Hole in Rock, Big Horse Basin Gap, Rattlesnake Gulch, Wickahoney, Whites Reservoir, Mud Flat Road and Shoofly CutoffRoad. RESULTS A total of 623 reptiles were encountered during the course of the study. Two hundred eighty-five reptiles were caught in the rim regime, 53 were caught mid-slope, and 1 16 were caught on the canyon bottom. The remaining 169 reptiles were incidental to the study. Snakes: Six species of snakes were found in the canyons of the study area: Gopher Snakes, Western Whipsnakes, Western Rattlesnakes, Night Snakes, Western Terrestrial Gartersnakes, and Western Racers. An additional two species that were found incidental to the study: Western Ground Snakes, and Longnose Snakes. Snakes were found in approximately the same numbers on the rim as in the canyon bottoms. Only a small percent of the snakes found were found mid-slope (Fig. 4). Snakes amounted to about one third of all reptiles caught on the rim, as did snakes caught mid-slope. Snakes accounted for about 80% of all reptiles caught on the canyon bottom. Eighty-nine snakes were marked within 5km of Parker Trail. A total recapture count of each species appears in Fig. 5. Lizards: Seven species of lizards were found in the canyons surveyed; Side-blotched lizards, Western Fence lizards, Desert Horned lizards, Short Horned lizards, Longnose Leopard lizards, Western Whiptails, and Western Skinks. One additional species was found incidental to the study, the Mojave Black-collared lizard. Lizards comprised about 70% of the reptiles found on the rim, and two-thirds of those reptiles found mid-slope. Lizards accounted for only about 20% of the reptiles found on the canyon bottom; lizards were found almost strictly on the rim (Fig. 6). Amphibians: There was only one species of amphibian found in the study area, Pacific Tree Frog, which was identified by Jim Munger, by call. All others were incidental to the study. This frog accounted for one percent of all herps found on the canyon bottom. Herp Survey Data 1995 100 80 "£ 60 O W Q) en c «: 40 20 Snakes Caught in Each Regime w- - ■:■ : ml,: ill 1 "^" T. elegans C. viridis H. torquata total P. catenifer M. taeniatus C. constrictor species Figure 4. Herp Survey Data 1995 x: D) CO O 03 O CD Q. CO .c o TO LLJ o 110 100 90 80 - 70 60 50 40 - 30 20 10 0 Capture Rate for 6 Species □ Captured 1x M Captured 2x ^ Captured 3x EQ Captured 4x ea Captured 5x P. catenifer M. taeniatus C. vindis H. torquata Species T. elegans C. constrictor Figure 5. Herp Survey Data 1995 210 180 150 § 120 Hi o CO £ 90 60 — 30 m rim g£3 mid-slope - bottom U. stansburiana S. occidentalis P. platyrhinos C. tigris E. skiltonianus total species Figure 6 1! Visual Encounter Searches: In addition to the data obtained from trapping, we found some notable herps during our visual encounter searches. On July 3, we stopped at Big Horse Basin Gap to survey primarily for Crotaphytus bicinctores. We found only one C. bicinctores, but in the wash that emerges from the gap, we found an unusually high number of Sonora semiannulata skins and living specimens. We also found one Hypsiglena torquata. All herps except the C. bicinctores were found by turning rocks. We returned to this site on Sept. 9, and found two C. bincinctores juveniles and no fresh S. semiannulata skins nor live specimens. We found C. bicinctores on hot sunny days in rocky areas north of the main bench. We found a C. bicinctores population at Big Jacks Creek where the pipeline and the creek meet. We found them consistently for about .5 mi to the east of Big Jacks creek and for about 1 .5 mi to the west. We found a population on the Oreana-Triangle road just before climbing the bench. DISCUSSION Based on their geographic ranges (Nussbaum et al. 1985 and Stebbins 1986) the following reptiles and amphibians potentially occur in the study area; those marked with an asterisk were found during the course of this study. Snakes: 'Western Rattlesnake {Crotalus viridis) *Great Basin Gopher Snake {Pituophis catenifer) 'Western Yellow-bellied Racer (Coluber constrictor) 'Western Striped Whipsnake (Masticophis taeniatus) *Westem Ground Snake {Sonora semiannulata) *Night Snake (Hypsiglena torquata) 'Western Longnose Snake (Rhinocheilus lecontei) 'Western Terrestrial Garter Snake (Thamnophis elegans) Common Garter Snake (Thamnophis sirtalis) Rubber Boa (Charina bottae) Lizards: 'Longnose Leopard Lizard (Gambelia wislizenii) *Westem WMptail (Cnemidophorus tigris) 'Desert Homed Lizard (Phrynosoma platyrhinos) * Short Homed Lizard (Phrynosoma douglassi) * Side-blotched Lizard (Uta stanshuriana) 'Western Fence Lizard (Sceloporus occidentalis) 'Sagebrush Lizard (Sceloporus graciosus) *Mojave Black-collared Lizard (Crotaphytus bicinctores) 'Western Sldnk (Eumeces skiltonianus) 12 Amphibians: *Pacific Treefrog {Pseudacris regilla) Spotted Frog {Rana pretiosa) Northern Leopard Frog {Rana pipiens) Western Toad (Bufo boreas) Woodhouse's Toad {Bufo woodhousei) Great Basin Spadefoot Toad {Spea intermontanus) Reptiles and amphibians potentially found in the study area represent 69% of the total species of reptiles and amphibians in Idaho. Additionally, Long-toed Salamanders (Ambystoma macrodactylum) could possibly be found in the study area because the salamander's range borders the study area, and habitat within the study area is similar to the preferred habitat of the salamander. As marked by an asterisk above, we found 17 of 19 potential reptile species during the course of the study. We found reptiles in all three of the regimes that we surveyed: canyon bottom, mid-slope, and rim. The rim and canyon bottom regimes contained the most reptiles; relatively few were seen in the mid-slope regime, especially during the hottest part of the summer (Fig. 7). Big Jacks Creek was surveyed using mainly standard drift fence arrays. The drift fence arrays were of two types, steel flashing and silt fence. Silt fence was set up to determine its effectiveness. Insufficient data was obtained to determine to what extent silt fence is effective. Lizards were seen climbing on the silt fence itself. Snakes have been observed using the upright posts to climb over the fence if the posts are placed too close to the fence (M. Gerber pers. obs.). We angled the uprights to eliminate the latter problem. Movement by reptiles in the trapping area was negligible, with very few being recaptured more than 50m from the original site of capture. We did capture an unusually high number of rattlesnakes in one array on the rim in the spring, but by mid summer we could only find one. This could be the result of a den in the vicinity of the array. Visual searches did not appear to be effective during this study. We found a limited number of species of reptiles using this method. The areas that were surveyed were very rocky, and although rocks were turned, there were many deep talus runs that enabled snakes to retreat far below the surface, thus limiting the habitat that was practical to survey using this method. Except for one Western Groundsnake population, all reptiles that were seen were active foraging, diurnal species such as Gopher snakes, Racers, Whipsnakes, and Western Terrestrial Garter snakes. We occasionally encountered Western Rattlesnakes, which are usually crepuscular but were found frequently during mid morning hours. Representatives of all nine species of lizards found in this study were found during visual searches. Most of the lizards were found on the canyon rim while lizards on the canyon bottom were second in abundance. Mojave Black-collared lizards and Longnose Leopard lizard were recorded as incidentals. Herp Survey Data 1995 300 200 o 100 Totals of Reptiles Caug mmm^mmmm nm mid Regime M snakes B lizards ■ total reptiles bottom Figure 7 14 SUMMARY Sixteen species of reptiles and amphibians were found in this study, of which 13 were associated with the deep canyons. Canyon rims and canyon bottoms were utilized by reptiles the most. Western Terrestrial Garter Snakes were found strictly on the bottoms, and Western Rattlesnakes were found primarily on the rim. Gopher Snakes, Racers, and Striped Whipsnakes were found to be relatively abundant in all three regimes surveyed. There appeared to be little or no vertical movement of reptiles between regimes. These deep canyons are important areas in the desert for reptiles because they provide apparently suitable cover and forage for most of Idaho's reptiles. Most of the waterways in these deep canyons are perennial and provide apparently good habitat for reptile and amphibian species. LITERATURE CITED Beck, J. M. and C. R. Peterson. 1995. Movements and habitat selection of the longnose snake (Rhinocheilus lecontei) in southwestern Idaho. Idaho Bureau of Land Management, Technical Bulletin 95-18. Diller, L. V. and D. R. Johnson. 1982. Ecology of reptiles in the Snake River Birds of Prey Area. Report to the Bureau of Land Management. Munger, J., L. Heberger, D. Logan, W. Peterson, L. Mealy, and M. Caughlin. 1994. A survey of the herpetofauna of the Bruneau Resource Area, with focus on the Spotted Frog, Rana pretiosa. Idaho Bureau of Land Management Technical Bulletin No. 94-7. Munger, J. C, M. Gerber, M. Carroll, K. Madrid, T. Bert. 1995. Herpetofauna of Bruneau and Owyhee Resource Areas, Boise District, with focus on the Spotted Frog, Rana pretiosa: a second year. Idaho Bureau of Land Management Technical Bulletin No. 96-1 . Nussbaum, R., E. Brodie, Jr., and R. Storm. 1983. Amphibians and reptiles of the Pacific northwest. University Press of Idaho, Moscow, Idaho. Stebbins, R. C. 1985. A field guide to western reptiles and amphibians. Houghton Mifflin Co., Boston. Appendix. 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E 28 m/c none 4.5 T10S R4E SEC 4 NW SW NE 4715440 502000 4440 06/26/95 1221 Uta stansbunana no 1:A 32 clear brebz--- 4 T10S R4E SEC 4 SE NE NE 4715740 533- 30 4610 OS/26/95 1235 Uta stansbunana no 2:H 32 c!&;;r breezy 5 T10S R4E SEC 4 NW NE NE 4715760 583350 -,200 OS/26/95 1235 Uta stansbunana no 2:E 32 clear breezy 1 4 T10S R4E SEC 4 NW NE NE 4715760 5B3350 ■2200 06/27/95 •i SCO Uta stansbunana no 6:A 27 clear breezy 4 T10S R4E SEC 4 NE NW NE 4715840 583050 46C0 06/28/95 1026 Uta stansbunana no 22 clear breezy 45 T10S R4E SEC 4 SW SW NE 4715180 582920 4620 06/28/95 1654 Uta stansbunana m no 10:G 30 clear breezy 4 T10S R4E SEC 4 NW SW NE 4715440 582900 4440 05/28/95 1115 Uta stansbunana no 3:C 22 clear breezv 5 T10S R4E SEC 4 NW NE NE 4715790 583260 2330 OS/28/93 1058 Uta stansbunana no 2:G 20 clear breezy 4.5 T10S R4E SEC 4 NW NE NE 4715760 563350 2530 0S/28/95 1032 Uta stansbunana no 20 clear breezy 4.5 T10S R4E SEC 4 SW SW NE 4715210 32:22:20 4520 05/28795 1032 Uta stansbunana no 20 clear breezy •'•5 T10S R4E SEC 4 SW SW NE 4715210 5S2920 4620 06/28/95 1323 Uta stansbunana no 4.5:G 29 clear brisv« 4.5 T10S R4E SEC 4 NE NW NE 4715740 583120 ■.."" 05/29/S5 1148 Uta stansbunana no 24 clear breezy 4.5 TBS R4E SEC 8 NW NW NE 4733220 581910 2780 05/29/95 948 Uta stansbunana no 17 clear windy 4 T7S R4E SEC 36 SE SW NE 4733500 586700 3100 06/29/95 r;--;s Uta stansbunana no 24 clear l- ftcvj 4.5 T8S R4E SEC 8 NW NW NE 4733220 581910 2780 07/01/95 1837 Uta stansbunana no 26 P/C L/F?" ■ 4.5 T10S R4E SEC 4 NW NE NE 4715750 583455 4610 07/01/95 195S Uta stansbunana no 5.5:A 24 P/C breezy 5 T10S R4E SEC 4 NE NW NE 4715850 583190 4300 07/01/95 2001 Uta Btansburiana RO 25 P/C breezy 4.5 T10S R4E SEC 4 NW NE NE 4715820 5S3260 -•:000 07/01/95 1900 Uta stansbunana no 3.5:D 25 P/C none 5 T10S R4E SEC 4 NW NE NE 4715730 583260 4580 07/01/95 1900 Uta stansbunana no 3.5:D 25 P/C none 5 T10S R4E SEC 4 NW NE NE 4715730 563260 4590 07/02/95 1515 uta stansbunana m no 8:A 28 cloudy windy 4,5 T10S R4E SEC 4 SW NW NE 4715620 382970 4400 07/02/95 945 Uta stansbunana no 21 M/S windy 4.5 T9S R4E SEC 33 SW SW SE 4716110 0000:2 4600 07/05/95 2021 Uta stansbunana no | 3D 28 P/C breezv 4.5 T10S R4E SEC 4 NW NE NE 4715790 383260 4600 07/05/95 2023 Uta stansbunana no 3:H 28 P/C breezy 4.5 T10S R4E SEC 4 NW NE NE 4715790 583260 4600 07/08/95 1111 Uta stansbunana no 27 M/C breezy 5 T10S R4E SEC 4 NE NW NE 4715870 . 2 '2 4600 07/08/95 1111 Uta stansbunana no 27 M/C breezy 45 T10S R4E SEC 4 NE NW NE 4715870 330070 -2500 07/08/95 1111 Uta stansbunana no 27 M/C breezy 4 3 T10S R4E SEC 4 NE NW NE 4715870 030070 2220 07/12/95 1318 Uta stansbunana no 3D 15 cloudy windy 4 T10S R4E SEC 4 NW NE NE 4715790 583260 2.250 07/1 5/95 1147 Uta stansbunana no 25 clear breezy 45 T9S R4E SEC 33 NW NE SW 4716S40 583025 4600 07/15/95 1157 Uta stansbunana b no 2b clear none 4.5 T9S R4E SEC 33 NW NE SW 4716500 002000 4090 07/15/25 1155 Uta stansbunana b no 25 clear none 45 T9S R4E SEC 33 NW NE SW 4716500 582550 4090 07/15/95 '; 1 57 Uta stansbunana b no 25 clear none 45 T9S R4E SEC 33 NW NE SW 4716500 582550 4090 07/15/95 "245 Uta stansbunana r no 5:G 31 clear breezy 5 T10S R4E SEC 4 NE NW NE 4715770 583070 4600 07/15/95 1200 Uta stansbunana b no 25 clear none 45 T9S R4E SEC 33 NW NE SW 4716500 582550 4090 07/15/95 1124 Uta stansbunana b no 29 clear none 4.5 T9S R4E SEC 33 NW NE SW 4717780 583470 4460 07/1 5/95 132C Uta stansbunana no 3:C 33 clear breezy 4.5 T10S R4E SEC 4 NW NE NE 47157SO 583260 4600 07/15/95 826 Uta stansbunana no 21 clear breezy 4 T10S R4E SEC 4 SW SW NE 4715130 583010 4620 07/1 5/95 1217 Uta stansbunana no 28 clear calm 4 T9S R4E SEC 33 NW NE SW 4715840 583060 4600 07/18/95 1130 Uta stansbunana no 28 clear breezv 4.5 T10SR4ESEC4NENWNE 4715780 5002000 4600 07/1 8/95 1135 Uta stansbunana no 4.5:C 31 CIS! :■- breezy 4.5 T10SR4ESEC4NENWNE 4715740 583120 4590 07/1 8/95 1107 Uta stansbunana no 26 cle , braezy 4.7 T10S R4E SEC 4 NE NW NE 4716870 582740 4460 07/18/95 1110 Uta stansbunana no 31 clear breezv 4 T10SR4ESEC4NENWNE 4716885 582740 4460 07/25/95 1036 Uta stansbunana m no 8:D 20 clear or 2V 2/ 4.5 T10S R4E SEC 4 SW NW NE 4715620 582970 4400 07/29/95 644 Uta stansbunana no 5.5:C 21 cloudy windy 4 T10S R4E SEC 4 NE NW NE 4715850 533190 4600 07/29/95 •343 Uta stansbunana no 5.5:B 21 cloudy windy 5 T10SR4ESEC4NENWNE 4715850 520: £0 4600 09/02/95 91 ' Uta stansbunana m no 11:E 24 cloudy none 2 T10S R4E SEC 4 SW NW NE 4715700 582870 4380 09/02/95 830 Uta stansbunana no 23 !■::,' udy none 3.5 T10S R4E SEC 4 NW NE NE 4715760 533390 2350 09/05/95 1612 Uta stansbunana no 4:E 27 clear breezy 3 T10S R4E SEC 4 NW NE NE 4715770 583180 2500 09/12/95 815 Uta stansbunana no 4.5:E 18 clear breezy 3 T10S R4E SEC 4 NE NW NE 4715740 583120 4500 09/16/95 848 Uta stansbunana 1 r no 4.5:B 21 P/C breezv 25 T10S R4E SEC 4 NE NW NE 4715740 583120 4590 09/19/95 809 Uta stansbunana no 2 A 16 clear breezy 2.5 T10S R4E SEC 4 NW NE NE 4715760 523000 4600 09/23/95 1744 Uta stansbunana no 2:F 22 M/C windy 3 T10S R4E SEC 4 NW NE NE 4715760 530050 4600 05/28/95 2000 Uta 6tansb 1-1 G-H 1 (d pq [.-■- ■H ffi £1 0) ■H J3 1 Xi Eh & Q W U z a h w w 0 b i. 0 QL 84.2 .L352 no. 97-1 88055389 Reptiles and amphibians in deep canyons ; The Big fc5LUl3 OU, & \ - lOUtt DENVER FEDERAL CENTER P.O. BOX 25047 DENVER, COLORADO 80225