(DRAFT) - Taxonomy
                                Species TOAD, WYOMING
                                Species Id ESIS206001
                                   Date 14 MAR 96



TAXONOMY

NAME - TOAD, WYOMING OTHER COMMON NAMES - TOAD, WYOMING; TOAD, DAKOTA; TOAD, CANADIAN; TOAD and MANITOBA ELEMENT CODE - CATEGORY - Amphibians PHYLUM AND SUBPHYLUM - CHORDATA, CLASS AND SUBCLASS - AMPHIBIA, ORDER AND SUBORDER - ANURA, FAMILY AND SUBFAMILY - BUFONIDAE, GENUS AND SUBGENUS - BUFO, SPECIES AND SSP - HEMIOPHRYS, BAXTERI SCIENTIFIC NAME - BUFO HEMIOPHRYS BAXTERI AUTHORITY - TAXONOMY REFERENCES - Taxonomy - 1 (DRAFT) - Taxonomy Species TOAD, WYOMING Species Id ESIS206001 Date 14 MAR 96 COMMENTS ON TAXONOMY - Wyoming Toad Bufo hemiophrys baxteri Porter, 1968 KINGDOM: Animal GROUP: Amphibian PHYLUM: Chordata CLASS: Amphibia ORDER: Anura FAMILY: Bufonidae Adult length about 55 mm, females slightly larger than males. Dorsal surface of body with round warts. Cranial crests fusing medially to form an elongate boss, either a ridge with a median groove or paired parallel ridges. The boss often cornified. Postorbital ridges indistinct or absent. Tympanum round, smaller than the eye. Cutting tubercles on the hind foot well developed. Background color dark brown, gray or greenish, with small dark dorsal blotches and a median light stripe. Belly spotted; mature males with a dark throat. Distinguished from Bufo americanus, Bufo fowleri and Bufo woodhousei by its smaller size and the fused cranial crests (02). Other common names for the Wyoming toad include: Canadian toad, Dakota toad, and Manitoba toad. Type specimens, U.S. Nat. Museum (01). Additional specimens, University of Wyoming Zoology Museum; University of Kansas Museum of Zoology. Taxonomy - 2
                                  (DRAFT) - Status
                                Species TOAD, WYOMING
                                Species Id ESIS206001
                                   Date 14 MAR 96



STATUS

Coded Status E: Federal Endangered COMMENTS ON STATUS - U.S. STATUSES AND LAWS: The Wyoming toad (Bufo hemiophrys baxteri) has been designated as Endangered pursuant to the Endangered Species Act of 1973 (50 CFR 17.11; P.L. 93-205, 87 Stat. 884; 16 U.S.C. 1531-1540), as amended. The subspecies has this status wherever found including the State of Wyoming. This species is protected by the Lacey Act (P.L. 97-79, as amended; 16 U.S.C. 3371 et seq.) which makes it unlawful to import, export, transport, sell, receive, acquire, or purchase any wild animal (alive or dead including parts, products, eggs, or offspring): (1) in interstate or foreign commerce if taken, possessed, transported or sold in violation of any State law or regulation, or foreign law; or (2) if taken or possessed in violation of any U.S. law, treaty, or regulation or in violation of Indian tribal law. It is also unlawful to possess any wild animal (alive or dead including parts, products, eggs, and offspring) within the U.S. territorial or special maritime jurisdiction (as defined in 18 U.S.C. 7) that is taken, possessed, transported, or sold in violation of any State law or regulation, foreign law, or Indian tribal law. RESPONSIBLE FEDERAL AGENCIES: USFWS -Responsible for the management/recovery, listing, and law enforcement/protection of this species. BLM -Responsible for the law enforcement/protection of this species with applicable State and Federal laws on public land under their control (43 CFR 4140). Also responsible for management/recovery on Bureau of Land Management lands. All Federal agencies have responsibility to ensure that any action authorized, funded, or carried out by that agency is not likely to jeopardize the continued existence of the species or result in the destruction or adverse modification of Critical Habitat (50 CFR 402), and to utilize their authorities to carry out programs for the conservation of the species. STATE STATUSES AND LAWS: STATE: Wyoming STATUS: Recognized Endangered Status - 1 (DRAFT) - Status Species TOAD, WYOMING Species Id ESIS206001 Date 14 MAR 96 ADMINISTRATIVE AGENCY: Wyoming Game and Fish Dept. STATE STATUTE: WY Stat. Annot. 23-1-101, 23-1-103, 23-3-301, 23-4-101, and 23-1-302; Regs. Chapt. XXXIII, Issuance of Sci. Permits. INTERNATIONAL STATUSES, TREATIES, AND AGREEMENTS: None. ECONOMIC STATUSES: None. 82/12/30:47 FR 58454/58460 - Notice of review of proposed rule 83/01/27:48 FR 03794/03796 - Proposed rule 84/01/17:49 FR 01992/01994 - Final rule, Endangered Status - 2
     

HABITAT ASSOCIATIONS

HABITAT - AQUATIC TERRESTRIAL INLAND AQUATIC LAND USE - Cropland and Pasture Mixed Rangeland Streams and Canals Lakes Nonforested Wetland NATIONAL WETLAND INVENTORY CODES NWI NWICLS NWIMOD NWISPEC Lacustrine, littoral EM2 2AB Lacustrine, littoral AB1 Lacustrine, littoral AB Lacustrine, littoral Palustrine EM5 Palustrine EM1 Palustrine EM Palustrine AB2 Palustrine AB1 Palustrine AB Palustrine COMMENTS ON HABITAT ASSOCIATIONS - During the period from 1939 when it was first recognized in the Laramie Basin, until at least the mid-sixties, the Wyoming toad was relatively abundant but restricted to a relatively small range of not more than about 600 square miles. The Laramie Basin is at an elevation of between 7200 and 7500 feet above sea level; it is a semi-arid, intermountain basin characterized by a predominant vegetation of short-grasses and sagebrush. Since settlement and development of agriculture, the central, lower portions of the basin are irrigated using water diverted from the two major rivers, the Big and Little Laramie Rivers (04). The habitats utilized by the Wyoming toad were floodplains ponds, small ponds and lakes produced by irrigation runoff, and the many small seepage lakes in the basin. These last mentioned habitats are shallow, seepage lakes whose basins were produced by wind erosion in a prehistoric dry period when many blowout basins as well as sand dunes were created in the Basin. They were surely very saline, and even dry during periods of drought, in the years before irrigation was initiated in the area. In the years when they were abundant in the Basin, adult and immature toads were restricted to the sedge and grass wet-meadows at the margins of these lakes, and to ponds on the floodplain of the streams in the Basin. And adult toads were not evident at all in late summer; they probably resorted to burrowing and being active at night during late summer (04). The habitat is unique in that the toads inhabit the bogs created by underground water collecting into seepage lakes at the base of plateaus in "hollows" created by the wind erosion. The habitat is very wet and be classified as a wet grassland rangeland (09). Any major change in land use patterns, and particularly in the Habitat Associations - 1 manner of irrigation, such as sprinkle irrigation in place of flooding, would affect the toad, probably adversely. Hibernation (winter dormancy) behavior was never studied carefully in this area. It was not believed to have been water-related. In Minnesota, the parent species has been observed to burrow into so-called Mima-mounds to a depth of 46 inches or more (07). In the Laramie Basin, a good guess is that the toads burrowed into softer soils such as areas where pocket gophers have tilled the soils, possibly into the pocket gopher burrows themselves, possibly into the extinct sand dunes that are quite common in areas where the toad formerly occurred. In one way or another, the toad needed to burrow to a depth below the frost line (08). Mima-mound topography occurs in the Laramie Basin, but out on the short-grass prairies these mounds are capped with cobblestones and are of a texture making it difficult for a toad to burrow. On the floodplains, in the areas where the toad was last observed, the "Mimi-mounds" produce elevations two or three feet above the water level when the meadows are being irrigated, and the caps of the mounds are frquently heavily utilized by pocket gophers. It seems quite likely that the Wyoming toad may have used such situations for burrowing and winter dormancy, much the same as was observed in Minnesota. Again, this is speculative; no one ever studied this possibility scientifically. But herpetologists have speculated that the existence of Mima-mound topography in the Laramie Basin may explain the presence of the relict population of the "Canadian" or Wyoming toad in Albany County, Wyoming (02). Habitat Associations - 2
                                (DRAFT) - Food Habits
                                Species TOAD, WYOMING
                                Species Id ESIS206001
                                   Date 14 MAR 96



FOOD HABITS

TROPHIC LEVEL - OMNIVORE LIFESTAGE FOOD FOOD PART General Algae General Arthropods Food Habits - 1
                         (DRAFT) - Environment Associations
                                Species TOAD, WYOMING
                                Species Id ESIS206001
                                   Date 14 MAR 96



ENVIRONMENTAL ASSOCIATIONS

G = General A = Adult LIM = Limiting RA = Resting Adult J = Juvenile FA = Feeding Adult RJ = Resting Juvenile BA = Breeding Adult FJ = Feeding Juvenile P = Pupae L = Larvae E = Egg RL = Resting Larvae FL = Feeding Larvae
LIFESTAGE ENVIRONMENTAL ASSOCIATIONS G G G Aquatic Features: Springs [flowing] G Inland Wetlands: Bogs G Terrestrial Features: Burrows G Environment Associations - 1
                               (DRAFT) - Life History
                                Species TOAD, WYOMING
                                Species Id ESIS206001
                                   Date 14 MAR 96



LIFE HISTORY

Detailed food habit studies for the Wyoming toad have never been made. Adult toads are insectivorous and opportunistic in selection of food. The literature on toad food habits always mentions ants and beetles as preferred foods, but this may be simply because those hard- to-digest items are the most conspicuous items in stomach contents. Larvae of anurans feed primarily on periphytic algae. It is unlikely that availability of food for either adults or larvae was in any way limiting for this toad. HOME RANGE/TERRITORY: Home range and territory behavior of the Wyoming toad are unknown. PERIODICITY: The adults and sub-adults are abundant and active during the daylight hours in the sedges and grasses on the floodplain during June and early July, but adults disappear during late July, probably becoming largely nocturnal during the dry part of the summer and remaining beneath the surface of the ground during the day; from Baxter, 1950 (04). MIGRATION PATTERNS: This species is non-migratory (04). COVER/SHELTER REQUIREMENTS: The Wyoming toad needs vegetative cover such as sedges, grasses, in a moist situation throughout the summer to protect against the high evaporative power of the air in the relatively arid climate of the Laramie Basin. It probably utilizes any soft earth such as pocket gopher burrows, sand dunes, etc., to burrow to below the frost line for winter dormancy (04,08). REPRODUCTIVE SITE REQUIREMENTS: The Wyoming toad requires warm (over 60 degrees F), shallow ponds or lake margins, for reproduction; these ponds must remain filled during the period from late May until at least mid-August for completion of the tadpole stage (04,08). REPRODUCTIVE CHARACTERISTICS: In the period when this toad was common in the Larami Basin, the adult toads emerged from winter dormancy in late May or early June, after daily air temperatures approach 80 degrees F. Breeding congresses developed in the warm, shallow floodplain ponds, and eggs were laid there. Tadpoles normally completed their transformation to adults by early August. Drying up of the floodplain ponds was a noticeable cause of considerable mortality to the tadpoles (04). Breckenridge and Testor determined that the parental subspecies in Minnesota becomes sexually mature after about 23 months (07). This was never determined for the subspecies found in Wyoming, but is believed to be the same, at least for males; females may require a year longer to become sexually mature (04,08). Life History - 1 (DRAFT) - Life History Species TOAD, WYOMING Species Id ESIS206001 Date 14 MAR 96 PARENTAL CARE: None (04). POPULATION BIOLOGY: Never studied in detail. SPECIES INTERRELATIONSHIPS: None. OTHER LIFE HISTORY DESCRIPTORS: None known. Life History - 2
                           (DRAFT) - Management Practices
                                Species TOAD, WYOMING
                                Species Id ESIS206001
                                   Date 14 MAR 96



MANAGEMENT PRACTICES

RESULT MANAGEMENT PRACTICE Beneficial Maintaining/Controlling Water Flow Beneficial Developing/maintaining/protecting wetlands Beneficial Controlling water levels Beneficial Controlling/Restricting Pesticide Use Beneficial Maintaining Sperm/Seed Banks Beneficial Stocking captive-reared wild-strain animals Beneficial Transplanting Wild Eggs/Wild Seeds Beneficial Disease Control Measures Adverse Food Supply Reduction Existing Food Supply Reduction Adverse Low Gene Pool Existing Low Gene Pool Adverse Disease Existing Disease Adverse Predation Existing Predation Adverse Strip mining Existing Strip mining Adverse Water Level Fluctuation Existing Water Level Fluctuation Adverse Irrigating Existing Irrigating Adverse Applying herbicides Existing Applying herbicides Adverse Applying pesticides Existing Applying pesticides Adverse Grazing Existing Grazing Adverse Existing Adverse Vegetation Composition Changes Existing Vegetation Composition Changes COMMENTS ON MANAGEMENT PRACTICES - Reasons for the population decline are not entirely clear. The 1985 edition of Amphibians and Reptiles of Wyoming (02) stating, "Widespread spraying of insecticides to control mosquitoes, changes in agricultural practices, increases in predation, diseases, and climatic changes have been suggested as casuses of the decline in numbers of the Wyoming toad, but no certain cause has been identified." The widespread decline of the Wyoming toad and other amphibian species in the Laramie Basin coincided with the aerial application of Baytex (Fenthion), an organophosphate pesticide, for mosquito control. Although some laboratory tests have shown that Baytex is not toxic to amphibians at levels prescribed for field applications, these results do not entirely refute the connection between this pesticide toxicity and the decline in the Wyoming toad population. Hall (10) reported that ranid frog (Rana catesbeiana) tad poles significantly Management Practices - 1 (DRAFT) - Management Practices Species TOAD, WYOMING Species Id ESIS206001 Date 14 MAR 96 bioconcentrate Baytex, up to 62 times. These elevated concentrations could have significant affects on larva toads when they undergo metamorphosis into subadults. The biomagnification of Baytex by algae is another major concern, since this is primarily found in larval toads. Baytex spraying may also have significant effects on subadults and adults food sources (insects), and could affect the ability of the toad to overwinter. Predation has been suggested as a possible cause of the population crash. Toads in general do not suffer much predation losses, since predators normally avoid them due to the bad taste produced from their skin glands. During the time of the toads massive decline, the California gull population has more than doubled. Gulls are known to be a significant predator on other aquatic vertebrates and it is conceivable that they maybe preying on the toads especially tadpoles and larval toads undergoing metamorphosis. Raccoons and white pelicans can not be ruled out either. Both species have increased significantly in the Basin during the period of the toads population decline. Predation of larvae and eggs by aquatic insects also may be a concern. The overall concensus of the recovery working group is that predation probably was not a significant factor in the decline of the species, but is expected to be a major factor in preventing the toads recovery. Diseases are another possible cause of the population decline. Amphibians are very susceptible to most fish diseases, especially red leg. This disease has been suggested as a possible cause of frog declines in upper mid-western United States (11). An additional scenario may have been involved in the reduction in numbers and possible extinction of the Wyoming toad. In the Laramie Basin, the floodplains of the streams are utilized by agriculture, as irrigated native hay meadows. In prehistoric times, the Wyoming toad was probably restricted to these floodplains. In late May and early June, during the spring runoff from the surrounding mountains, the hay meadows are flooded and become an almost continuous shallow aquatic system for many square miles. This period coincides exactly with the breeding period of the Wyoming toad. In order to dry out the meadows so that the hay can be harvested, the irrigation waters are turned off abruptly sometime between the middle of July and the first of August. Within a relatively short time, the hay is mowed. The habitat is transformed from a very wet situation with a great deal of vegetative cover to a very dry situation with almost no cover whatsoever. The larvae may have not yet transformed at this time and suffered high or complete mortalities, or the newly metamorphosed immature toads may have been exposed to high rates of evaporation and suffered high mortalities. This is speculative. It is not known for sure what the specific reason for the decline in numbers of the Wyoming toads. UNAPPROVED PLAN: No recovery plan has been prepared for the Wyoming toad as of yet. The plan is scheduled to be completed in 1988. The 1987 discovery of a healthy breeding population of this Management Practices - 2 (DRAFT) - Management Practices Species TOAD, WYOMING Species Id ESIS206001 Date 14 MAR 96 species has prompted the Service to establish a recovery working group. This group will be responsible for developing the recovery plan and assisting in its implementation. Mike Stone of the Wyoming Game and Fish Department has the lead in writing the plan, which is scheduled to be completed in 1988. Conservation measures being discussed include: 1. Studies to determine exact reason for the decline, i.e., Baytex toxicity studies on surrogate species, predation, diseases. 2. Egg transplants into suitable habitat. The concensus of the working group is not to try adult transplants (apparently adults have a strong homing ability); but to transplant portions of egg masses and keep them in protective cages until metamorphism has occurred. 3. Captive propagation was viewed as a last ditch effort by the group. Zoos, however, may provide a good fall back situation to keep a few individuals in case something happened to the wild population. 4. Studies to determine important components of this species wintering and breeding life histories. 5. Since the only known population is located solely on private lands, it is extremely important that good landowner relationship be maintained. Members of the working group have contacted the primary landowner, and he has been very supportive of our recovery efforts. The Nature Conservancy has also been contacted, and they have indicated their willingness to assist in the recovery efforts, both monetarily and with landowner relationships. 6. Work with the local Mosquito Central Districts in an effort to get a more biological sound mosquito control program implemented. This program has been initiated. Management Practices - 3
                                   (DRAFT) - References
                                  Species TOAD, WYOMING
                                  Species Id ESIS206001
                                      Date 14 MAR 96



     

References

***** REFERENCES FOR ALL NARRATIVES EXCEPT N-OCCURRENCE ***** 01 Porter, K.R. 1968. Evolutionary status of a relict population of Bufo hemiophrys Cope. Evolution 22:583-594. 02 Baxter, G.T., and M.D. Stone. 1985. Amphibians and reptiles of Wyoming. 2nd Ed. WY Game and Fish Dept., Laramie, WY. 03 Baxter, G.T. 1946. A study of the amphibians and reptiles of Wyoming. Unpubl. M.S. thesis. Univ. of WY. 04 Baxter, G.T. 1952. The relation of temperature to the altitudinal distribution of frogs and toads in southwestern Wyoming. Unpubl. Ph.D. thesis. Univ. of Mich., Ann Arbor, Mich. 05 Baxter, G.T., and J.S. Meyer. 1982. The status and decline of the Wyoming toad, Bufo hemiophrys baxteri. J. CO-WY Acad. of Sci. 14:33. 06 Baxter, G.T., M.R. Stromberg, and C.K. Doss, Jr. 1982. The status of the Wyoming toad (Bufo hemiophrys baxteri). Environmental Conserv. 9:348. 07 Breckenridge, W.J., and J.R. Tester. 1961. Growth, local movements and hibernation of the Manitoba toad, Bufo hemiophrys. Ecology 42(4):637-646. 08 Baxter, G.T. 1985. Pers. observ. Laramie, WY 82070. 09 Baxter, G.T. 1987. Pers. observ. Laramie, WY 82070. 10 Hall, R.J., Kolbe, E. 1980. Bioconcentration of organophosphorous pesticides to hazardous levels by amphibians. J. Toxicol. Environ. Health 6:853-860. 11 Anderson, A. 1988. Pers. knowledge. U.S. Fish and Wildl. Serv., Cheyenne, WY. ***** REFERENCES FOR N-OCCURRENCE NARRATIVE ONLY ***** 01 Baxter, G.T. 1964. A study of the amphibians and reptiles of Wyoming. Unpubl. thesis, Univ. of WY., Laramie. 02 Baxter, G.T. and M.D. Stone. 1985. Amphibians and Reptiles of Wyoming, 2nd Ed. Wyoming Game and Fish Dept., Laramie. 03 Baxter, G.T., and J.S. Meyer. 1982. The status and decline of the Wyoming toad, Bufo hemiophrys baxteri. J. Colorado-Wyoming Acad. of Sci. 14:33. 04 Lewis, D.L., et al. 1985. Possible extinction of the Wyoming toad, Bufo hemiophrys baxteri. J. Herpetology 19(1):166-168. 05 Baxter, G.T. 1985. Pers. observ. Laramie, WY 82070. 06 Baxter, G.T. 1987. Pers. observ. Laramie, WY 82070. 07 Anderson, A. 1988. Pers. observ. U.S. Fish and Wildl. Serv., Cheyenne, WY. References - 1