(DRAFT) - Taxonomy
                    Species LIZARD, FRINGE-TOED, COACHELLA VALLEY
                                Species Id ESIS151001
                                   Date 14 MAR 96



TAXONOMY

NAME - LIZARD, FRINGE-TOED, COACHELLA VALLEY OTHER COMMON NAMES - LIZARD, FRINGE-TOED, COACHELLA VALLEY;LIZARD, SAND, FRINGE-TOED;LIZARD, SAND, FRINGE-FOOTED;LIZARD, FRINGE-FOOTED;LIZARD, SAND, COACHELLA;LIZARD, SAND, OCELLATED;LIZARD and SAND ELEMENT CODE - CATEGORY - Reptiles PHYLUM AND SUBPHYLUM - CHORDATA, CLASS AND SUBCLASS - REPTILIA, ORDER AND SUBORDER - SQUAMATA, FAMILY AND SUBFAMILY - IGUANIDAE, GENUS AND SUBGENUS - UMA, SPECIES AND SSP - INORNATA, SCIENTIFIC NAME - UMA INORNATA AUTHORITY - TAXONOMY REFERENCES - COMMENTS ON TAXONOMY - Coachella Valley Fringe-toed Lizard Uma inornata Cope, 1895 KINGDOM: Animal GROUP: Reptile PHYLUM: Chordata CLASS: Reptilia ORDER: Squamata FAMILY: Iguanidae Uma inornata is a medium sized lizard with granular dorsal scalation. The dorsal ground color is whitish-buff with a pattern of black ring-like markings (ocelli, maculae) that form broken longitudinal lines over the shoulder (01,02). Ventral color is white with black bars on the underside of the tail and thin black gular chevrons that are absent or faint in the mid-gular region. A black ventrolateral blotch is absent or present as a minute cluster of black dots in about 50% of individuals (01). Breeding coloration is present from May to September (03) and consists of pinkish (also described as reddish-orange) lateroventral suffusion between the axilla and groin along the lateral fold and orange washes over the anterior supralabials and infralabials and the posterior festoons of the eye (01,04). There are usually 3 internasal scales and there are 23-32 (mean 26.5) fringes on the posterior edge of the fourth toe of the hind foot. The fringes and lamallae are intercalated with small Taxonomy - 1 (DRAFT) - Taxonomy Species LIZARD, FRINGE-TOED, COACHELLA VALLEY Species Id ESIS151001 Date 14 MAR 96 subdigital scales (01). Sexually mature males (80-122 mm snout-vent length, mean 102 mm) are larger than mature females (70-99 mm snout-vent length, mean 81 mm) and males always have 2 enlarged postanal scales that are lacking in 97% of females (03). The holotype was housed at the U.S. National Museum 16500, and is now lost. The collector was C.R. Orcutt. The type locality was given as "Colorado Desert San Diego County, California", but was in error and was corrected to "Coachella Valley, Riverside County, CA" by Heifetz, 1941 (10). Uma inornata is a monotypic species. Taxonomic descriptions can be found in: Cope (11); Heifets (10); Smith (12); and Norris (01). Pough (13) reviewed the taxonomy of U. inornata and provided the following remarks: "Although it was adequately diagnosed by Cope (1894, 1900) Uma inornata was long considered a synonym of U. notata, probably as a result of the influential works of Camp (1916) and Van Denburgh (1922). References to "Uma notata" published between 1916 and 1941, when U. inornata was resurrected (Heifetz, 1941), can be correctly atributed to species only if detailed locality data or photographs are included." The taxonomic relationships within the genus Uma are subject to three interpretations: 1) U. inornata, U. scoparia and U. notata represent a single species, U. notata; 2) U. notata and U. scoparia are distinct species and U. inornata is a subspecies of U. notata; and 3) U. inornata, U. scoparia and U. notata are three separate species. Adest (15) and Zalusky et al. (16) suggested that U. notata, U. inornata and U. scoparia should all be regarded as a single species (U. notata) on the basis of electrophoretic analysis of allelic frequencies (15) and cranial osteology (16). Schmidt (09) and Norris (01) analyzed phenotypic characters and concluded that U. inornata was a subspecies of U. notata, but U. scoparia was distinct from U. notata. Mayhew (17) proposed that U. inornata be retained as a distinct species and as evidence he presented a number of physiological and behavioral differences between U. notata and U. inornata. In view of the non-morphological evidence and allopatric relationship between U. notata and U. inornata, Pough concurred with Mayhew that U. inornata should be retained as a distinct species and that all three forms should be recognized as separate species. The fringe-toed lizard has been known by the scientific synonyms Callisaurus inornatus Cope, 1896 (06); Uma notata (part) Camp, 1916 (07); Callisaurus notatus (part) Stejneger and Barbour, 1917 (08); and Uma notata inornata Schmidt, 1953 (09). A variety of common names have been used for the genus Uma in general and for the species U. inornata: sand lizard; ocellated sand lizard; Coachella sand lizard; fringe-footed lizard; fringe-footed sand lizard; fringe-toed sand lizard; and Coachella Valley fringe-toed lizard. Taxonomy - 2
                                  (DRAFT) - Status
                    Species LIZARD, FRINGE-TOED, COACHELLA VALLEY
                                Species Id ESIS151001
                                   Date 14 MAR 96



STATUS

Coded Status T: Federal Threatened Commercial COMMENTS ON STATUS - U.S. STATUSES AND LAWS: The Coachella Valley fringe-toed lizard (Uma inornata) has been designated a Threatened species 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 species has this status wherever found including the State of California. Critical Habitat has been designated in Riverside County, CA (50 CFR 17.95(c)). 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 (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. BIA -Responsible for the law enforcement/protection of this species with applicable State and Federal laws on public lands under their control. Also responsible for management/recovery on Bureau of Indian Affairs lands. 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), Status - 1 (DRAFT) - Status Species LIZARD, FRINGE-TOED, COACHELLA VALLEY Species Id ESIS151001 Date 14 MAR 96 and to utilize their authorities to carry out programs for the conservation of the species. STATE STATUSES AND LAWS: STATE: California DESIGNATED STATUS: Endangered ADMINISTRATIVE AGENCY: Department of Fish and Game STATE STATUTE: Title 14, California Administrative Code, Section 670.5 1981 Supplement. INTERNATIONAL STATUSES, TREATIES, AND AGREEMENTS: None. ECONOMIC STATUSES: The Coachella Valley fringe-toed lizard has commercial value for pet trade and collectors. The State of California regulates trade in reptiles and since the listing of the lizard such trade is illegal. 78/08/23:43 FR 63812/ - Proposed listing 80/05/28:45 FR 36038/36041 - Reproposal of Critical Habitat 80/09/25:45 FR 63812/63820 - Final rule and CH designation 85/07/22:50 FR 29901/29909 - Five year review Status - 2
     

HABITAT ASSOCIATIONS

HABITAT - TERRESTRIAL TERRESTRIAL LAND USE - Transportation, communications, and Util Sandy Areas other than Beaches COMMENTS ON HABITAT ASSOCIATIONS - Uma inornata occurs in aeolian sand habitats within the Coachella Valley, Riverside Co., CA. The species does not occur in other types of habitat or locations and is rarely found as far as 15 feet from a sand deposit (58). Suitable habitat is located in various areas including undeveloped parcels of land bounded by numerous road and highways and traversed by utility transmission corridors. The Coachella Valley is a northern extension of the Colorado Desert. It is bordered by the Little San Bernardino Mountains on the west, and the Santa Rosa Mountains and Salton Sea to the south. Much of the valley floor consists of aeolian or blow-sand and rocky alluvial deposits with sparse vegetation. Parts of the valley have been extensively urbanized and cultivated. Vegetation is sparse in the sand habitat of Uma inornata. England and Nelson (23) note that creosote bush (Larrea tridentata) comprises the dominant plant community. In addition, burrobush (Prosopis juliflora), cheesebush (Hymenoclea salsola), desert dicoria (Dicoria canescens), plicate coldenia (Coldenia placata), and Russian thistle (Salsola iberica) are found in varying degrees of abundance in Uma's environment. The spread of certain plants, particularly Russian thistle, may be having a detrimental impact on the blow-sand habitat by causing stabilization, and thus, allowing other plants to invade. Vertebrates which inhabit the aeolian sands of the Coachella Valley include: road-runner (Geococcyx californianus), badger (Taxidea taxus), shrike (Lanius ludovicianus), sparrow hawk (Falco sparverius), sidewinder (Crotalus cerastes), glossy snake (Arizona elegans), western whiptail (Cnemidophorus tigris), ground squirrels (Citellus sp.), and Kangaroo rats (Dipodomys sp.). England and Nelson (23) identified three general types of blow-sand deposits that are inhabited by the lizard: sandy plains; sand hummocks; and mesquite dunes. The general distribution of these habitats were mapped and representative photographs of each type are given in reference 23. Analyses of the size distribution of sand grains in areas of high and low population densities are found in Stebbins (20), Norris (01), Pough (30), England and Nelson (23) and Turner et al., (29). The results of the analyses for deposits from different areas within the Coachella Valley are consistent with each other as are conclusions regarding the affect of substrate parameters on the distribution of the lizard. Substrates with a high percentage (about 10%) of silt (modal grain; size greater than 1.0 mm) are avoided. Between these extremes the particle size distribution curves may assume a number of forms with the mean paticle diameter ranging from 0.1 to 0.3 mm with median diameters ranging from 0.1 to 0.4 mm. The specific environmental (substrate) parameters that are required by the species are the result of complex relationships between geological and meteorological processes (29). Blow-sand habitats are dynamic in space and time and the long-term existence of these habitats depends upon uninterupted sand transport from source areas where the lizard does not occur to areas of habitat where the lizard does occur. Sand source areas and habitat areas are usually Habitat Associations - 1 separated by several kilometers. The dynamics of sand transport, sand sources and aeolian deposition areas are discussed in detail by Weaver (28) as are the affects of windbreaks (sand impoundment) on the stability of viable habitat. The Coachella fringe-toed lizard escapes predators and extreme environmental conditions by burrowing in the sand or possibly utilizing existing rodent burrows. Habitat Associations - 2
                                (DRAFT) - Food Habits
                    Species LIZARD, FRINGE-TOED, COACHELLA VALLEY
                                Species Id ESIS151001
                                   Date 14 MAR 96



FOOD HABITS

TROPHIC LEVEL - OMNIVORE LIFESTAGE FOOD FOOD PART General Evergreen Shrubs-Leaves/Twigs General Poaceae General General Forb Leaves/Stems General Forb Flowers/Fruit/Seed General Arthropods General Evergreen Shrubs-Leaves/Twigs General Poaceae General General Forb Leaves/Stems General Forb Flowers/Fruit/Seed General Arthropods Food Habits - 1
                         (DRAFT) - Environment Associations
                    Species LIZARD, FRINGE-TOED, COACHELLA VALLEY
                                Species Id ESIS151001
                                   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 Terrestrial Features: Burrows G G Terrestrial Features: Burrows G Environment Associations - 1
                               (DRAFT) - Life History
                    Species LIZARD, FRINGE-TOED, COACHELLA VALLEY
                                Species Id ESIS151001
                                   Date 14 MAR 96



LIFE HISTORY

FOOD HABITS: The food habits of Uma inornata are not well studied. Stebbins (20) compiled a list of plant and animal food items from observations in the field and laboratory and from the examination of stomachs and fecal pellets. Minnich and Shoemaker (31) studied water and electrolyte turnover in a closely related species, Uma scoparia, and reported food items in the diet. There are no compelling reasons to believe that the diet of U. inornata and U. scoparia should markedly differ and the results of the two studies are in general agreement. In both studies insects were not identified beyond the family level. Plant food items differed between the study areas, but this may only reflect different years, seasons and relative abundance of food items at the time that the studies were done. Stebbins (20) found that U. inornata consumed insects from the orders Coleoptera (tenebrionids, curculionids, and coccinellids), Hymenoptera (ants and bees), Hemiptera, Orthoptera, and Lepidoptera (caterpillars). U. inornata also consumed plants from the following families: Asteraceae (Dicoria, seeds), Bignoniaceae (Chilopsis, leaves and buds), Boroginaceae (Cryptantha, leaves) and Zygophyllaceae (Larrae, leaves). Food items taken in captivity by U. inornata include, from the arthropods, millipedes, sow bugs, carabid beetles, termites, meal worms, cockroaches, and flies; and from the plant kingdom, Dandilions (flowers and fruits) and grass blades. Minnich and Shoemaker (31) found that the closely related U. scoparia ate some food types not found in Stebbins' study. These foods are, from the insects, Lepidoptera (moths), from the arachnids, Arachnida (scorpions), from plants Boroginaceae (Coldenia plicata, leaves), Euphorbiaceae (Croton californicus, seeds), Fabaceae (Dalea emoryi, leaves), Poaceae (Aristida adscensionis and Bouteba barbata, flowers, fruit, leaves and stems of both species). The composition of the diet differed greatly for adult and juvenile U. scoparia: 60% of the adult diet was plant material and less than 10% of the juvenile diet was plant material. These differences in diet have a significant affect on water turnover and electrolyte flux rates (31) and dietary differences might also affect growth and reproduction (32). There are no comparative data for the diet of adult and juvenile U. inornata. However, Mayhew (33) demonstrated that reproduction was curtailed during drought conditions and he inferred that a decrease in annual plant germination and secondary productivity of insects were the cause of the decline in reproduction. The relationships between seasonal availability and abundance of food items and growth and reproduction in U. inornata deserve further study. Carpenter (33) maintained U. inornata, U. notata and U. scoparia in an outdoor enclosure and fed them "insects and spiders captured with sweep nets." The enclosure was located in Oklahoma, several hundred kilometers east of the range of Uma sp. and presumably the "insects and spiders" were novel food items (i.e., species that Uma sp. would not encounter within its range). This observation indicates Life History - 1 (DRAFT) - Life History Species LIZARD, FRINGE-TOED, COACHELLA VALLEY Species Id ESIS151001 Date 14 MAR 96 that Uma is most likely a generalist and would take any available arthropods that it encounters. Carpenter also observed cannibalism and saurophagy in all three species of Uma. Large males ate juveniles of their own species and small Depsosaurus dorsalis and Cnemidophorus sexlineatus. The Uma sp. also ate their own shedding skin and the skin of other individuals. Leaves of a "sunflower plant" were eaten by U. inornata as were the petals from "flowers". In summary, the results and observations that are available for the genus Uma (31,33) and U. inornata (20) indicate that U. inornata is probably a generalist in food habits. Arthropods, plants and possibly other lizards are consumed and there may be ontogenetic changes in the composition of the diet. HOME RANGE/TERRITORY: The social behavior and spatial relationships of Uma inornata have not been studied in the field. Carpenter (33) studied social organization and behavior of captive U. inornata, U. notata and U. scoparia and concluded that: "These three fring-toed lizards show typical iguanid patterns of behavior in their social structure, which is based on territoriality." In a recent review of social behavior and spacing patterns of inguanid lizards, Stamps (34) reported that of 67 studies of 60 species only three iguanids were not territorial. All other species of iguanids are "territorial and agressive, but depending on the species, the extent of territoriality seems to vary seasonally, geographically or locally." The enclosure studies of Carpenter (33) and the generalizations that emerged from the review by Stamps (34) strongly support the contention that, when studied in the field, U. inornata will be shown to be territorial. Strong support for this can also be drawn from Pough's (30) observation that: "Adult males appear to take stations on the large central dune at intervals of 50-100 feet. The intervals remained constant from day to day, but no marking experiments were carried out to determine if individual lizards occupied the same spot each day." Pough (30) also stated in a discussion of the use of rodent burrows that were scarce relative to the number of lizards on the site that: ". . . to shelter the entire population of Uma would require crowding several lizards into each burrow. As Uma are very territorial, such crowding seems likely." PERIODICITY: Mayhew (04) and Pough (30) described the daily and seasonal activity patterns of Uma inornata in the field and recent reviews (35, 36,37) have focused on the physiological and environmental factors that affect activity patterns of lizards. The daily activity pattern of U. inornata is unimodal during cool months of the year (Jan.-Apr., Oct.) and bimodal during the warm months (May-Sept.). There is a precipitous decrease in activity in November and rarely will an active lizard be encountered in December and January. During this period the lizards are in hibernation (brumation, 38). A circadian rhythm of physiological responses and temperature-independent morning emergence was demonstrated by Pough (39). These responses preceed activity on the surface. Mayhew (04) Life History - 2 (DRAFT) - Life History Species LIZARD, FRINGE-TOED, COACHELLA VALLEY Species Id ESIS151001 Date 14 MAR 96 collected monthly samples of U. inornata over a four year period (1959-1962) and recorded the time of day that the lizards were active on the surface (Table 1) and Pough described the behavior of lizards during the active period. TABLE 1: Activity times for Uma inornata collected monthly over a four year period. Data from Mayhew (03,04). YEAR (Adult male/female) MONTH TIME IMMATURE 59 60 61 62 -------------------------------------------------------------------- Jan 1000-1400 1 1/0 - - - Feb 1030-1600 0 1/0 - 1/0 - Mar 0900-1700 7 1/3 5/6 9/4 3/2 Apr 0700-1830 8 7/6 6/6 9/2 3/2 May 0700-1230, 1430-1830 9 6/6 10/6 9/2 7/2 Jun 0600-1230, 1600-1900 11 3/10 8/2 3/5 10/6 Jul 0500-1100, 1630-1930 6 3/11 3/4 5/7 6/6 Aug 1530-1330, 1630-1900 19 7/9 17/33 6/5 7/11 Sep 0730-1330, 1630-1830 4 5/7 7/17 6/8 5/7 Oct 0730-1400 3 3/3 3/3 4/6 2/3 Nov 1000-1300 1 - - - - Dec --- - - - - - -------------------------------------------------------------------- TOTAL 69 37/55 59/78 52/42 43/38 ____________________________________________________________________ ____________________________________________________________________ REPRODUCTIVE SITE REQUIREMENTS: Carpenter (33) described the breeding behavior and other social behavior of Uma inornata. No reference was made to specific site requirements that are necessary for successful courtship. The location of oviposition sites and environmental factors required for successful incubation of the eggs are unknown. However, there are studies of the temperature and moisture requirements of two lizard species that are frequently found in the same habitat as U. inornata. Desert iguana, Dipsosaurus dorsalis, eggs hatch normally between 28 and 38 degrees C at environmental water potentials between -50 and -1500 kPa (40). In the Palm Desert area, egg burrows should be located out of the root zone of perennial plants at a depth of about 22 cm. At this depth the environmental conditions would remain within the tolerance limits of the eggs throughout the incubation period of desert iguana eggs (40). Zebra-tailed lizards, Callisaurus draconoides, are closely related to U. inornata and the eggs of C. draconoides have been successfully hatched when incubated in environmental conditions within the ranges reported for desert iguanas (41). There are no reasons to suppose that the embryonic tolerances of U. inornata should differ greatly from that of other sympatric iguanids. Pending specific studies of the tolerance limits of U. inornata embryos and the edaphic environment of aeolian sand deposits, the results of Muth (40) and Packard et al. (41) can probably be used Life History - 3 (DRAFT) - Life History Species LIZARD, FRINGE-TOED, COACHELLA VALLEY Species Id ESIS151001 Date 14 MAR 96 to approximate reproductive site requirements. PARENTAL CARE: There is no known parental care of eggs or hatchlings. POPULATION BIOLOGY: The population biology of Uma inornata has not been studied. This is a major gap in the data base of the species and the formulation of management goals could be severely hampered by lack of demographic data. SPECIES INTERRELATIONSHIPS: There are no known species interrelationships. OTHER LIFE HISTORY DESCRIPTORS: Several behavioral and morphological adaptations allow the Coachella Valley fringe-toed lizard, CVFTL, to exist in its habitat (20,51). The CVFTL has the ability to run across the sand at relatively high speeds and literally dive into it. It may move short distances after burial, engaging in what has been called "sand-swimming" until it is completely buried. The smooth scales reduce friction and make it easier for the lizard to "swim" through the sand. The enlarged fringe scales on the toes increase the foot surfaces thus aiding locomotion on and beneath the sand. The additional surface area created by the scales increases traction when moving across the sand. Numerous morphological adaptations function to protect the lizard's body from abrasion and keep sand particles out of body openings. The CVFTL can partially close its nostrils to exclude most sand. When particles do get in, they are trapped in a U shaped nasal passage, analogous to a kitchen-sink trap, and are blown out by a burst of air. The snout is wedge- or shovel-shaped rather than blunt; this wedge spreads the sand as the lizard dives. Because the upper jaw is longer and overlaps the lower jaw, the lizard can dive into sand without filling its mouth. Other adaptations include fringed eyelids with a double seal and a loose flap of skin that covers the ears when the lizard dives into the sand. CVFTL attempt to escape predators by "sand-swimming" and, to a lesser extent, by entering rodent burrows. "Sand-swimming" can also be used to reach cool sand (29), thus avoiding high summer surface temperatures that can exceed 71 degrees C (160 degrees F). However, when shallow subsurface temperatures exceed tolerable limits, lizards may be forced to seek shelter under a shrub or in a rodent burrow (29). They also are capable of excavating a burrow to depths sufficient to reach cooler substrates (59). Additional information regarding physiology, morphology and comparative reproduction in the genus Uma can be found in references 42-57. Life History - 4
                           (DRAFT) - Management Practices
                    Species LIZARD, FRINGE-TOED, COACHELLA VALLEY
                                Species Id ESIS151001
                                   Date 14 MAR 96



MANAGEMENT PRACTICES

RESULT MANAGEMENT PRACTICE Beneficial Controlling/Restricting Off-Road Vehicles Beneficial Maintaining undisturbed/undeveloped areas Beneficial Land Acquisition Beneficial Reforestation Beneficial Controlling/Removing Nonnative Vegetation Adverse Incidental Capturing/Killing Existing Incidental Capturing/Killing Adverse Off Road Vehicles Existing Off Road Vehicles Adverse Rural Residential/Industrial Areas Existing Rural Residential/Industrial Areas Adverse Recreational development Existing Recreational development Adverse Highway/Railroads Existing Highway/Railroads Adverse Transmission Lines/Towers Existing Transmission Lines/Towers Adverse Reservoirs Existing Reservoirs Adverse Exotic/Feral/Introducted Species Existing Exotic/Feral/Introducted Species Adverse Existing Adverse Vegetation Composition Changes Existing Vegetation Composition Changes Beneficial Controlling/Restricting Off-Road Vehicles Beneficial Maintaining undisturbed/undeveloped areas Beneficial Land Acquisition Beneficial Reforestation Beneficial Controlling/Removing Nonnative Vegetation Adverse Incidental Capturing/Killing Existing Incidental Capturing/Killing Adverse Off Road Vehicles Existing Off Road Vehicles Adverse Rural Residential/Industrial Areas Existing Rural Residential/Industrial Areas Adverse Recreational development Existing Recreational development Adverse Highway/Railroads Existing Highway/Railroads Adverse Transmission Lines/Towers Existing Transmission Lines/Towers Adverse Reservoirs Existing Reservoirs Adverse Exotic/Feral/Introducted Species Existing Exotic/Feral/Introducted Species Adverse Existing Adverse Vegetation Composition Changes Management Practices - 1 (DRAFT) - Management Practices Species LIZARD, FRINGE-TOED, COACHELLA VALLEY Species Id ESIS151001 Date 14 MAR 96 RESULT MANAGEMENT PRACTICE Existing Vegetation Composition Changes COMMENTS ON MANAGEMENT PRACTICES - Habitat destruction and modification are the primary threats to the long-term existence of Uma inornata. England and Nelson (23) and England (24) reconstructed the historic range and surveyed the Coachella Valley for suitable habitat. Their results indicate that the original range was about 840 square km (324 square mi) and that the range in 1975 had been reduced to 612 square km (236 square mi), a 27% reduction in range. However, within the areal extent of the range in 1975 only about 311 square km (120 square mi) or 51% was comprised of suitable aeolian sand habitat. Recreation oriented development (golf courses and country clubs) and agriculture were responsible for the loss of habitat. England (24) resurveyed the Coachella Valley in August and December 1982 and found only 245.5 square km (94.8 square mi) of habitat west of the Coachella Canal and 14 square km (5.5 square km) east of the canal; a 17% reduction in the total amount of suitable habitat in just 7 years. The habitat west of the canal was primarily developed for country clubs, condominiums, homes and associated utility and commercial development, and east of the canal the development was primarily agricultural. In 1982 the Southern California Association of Governments (25) projected more than a doubling of the permanent population in Coachella Valley from 128,478 to 266,575. The Coachella Valley is a seasonal resort area and the part-time population could be more than 50% of the permanent population from November to May of each year. The rate of development will increase west of the canal to accommodate growth. This pattern is evident from development that occurred in 1983. At least 11 square km (4.25 square mi) were developed or approved for development west of the canal (26). The development in 1983 represents 4.5% of the habitat that was identified by England in 1982. Two major transportation corriders, Interstate Highway 10/Southern Pacific railroad and the Highway 111 right-of-way, may act as barriers to lizard movement, affectively dividing the valley into three populations. Habitat fragmentation may prevent reestablishment in areas where population declines occur, resulting in local extirpation (58). The quality of aeolian sand habitat is degraded by windbreaks and destruction of sand transport upwind from any given site. Thus, development has both a primary impact of direct habitat loss and a secondary impact on habitat quality downwind from the development. The negative influence of development will, in the long-term extend the entire length of the valley. The complex dynamics of aeolian sand transport are discussed in detail by Weaver (27,28). About 80% of the aeolian deposition area of the Coachella Valley is either developed or affected by disruption of the sand transport system. The wind shielded areas will eventually be lost as Uma inornata habitat. The rate of habitat degradation by sand depletion and surface Management Practices - 2 (DRAFT) - Management Practices Species LIZARD, FRINGE-TOED, COACHELLA VALLEY Species Id ESIS151001 Date 14 MAR 96 stabilization varies from 0.40 km (0.25 mi) to 1.21 km (0.75 mi) per year downwind from an obstruction (27). The relationship between the rate of habitat degradation caused by physical processes and the rate of decline in populations of Uma innornata requires further study. However, all studies to date have demonstrated reduced abundance downwind from obstructions to the sand transport system (29). The U.S. Army Corps of Engineers is considering a flood-control project on the Whitewater River. Depending upon the alternative plan selected, the facility may be designed to prevent new sands from entering the Coachella Valley. If constructed, the dam(s) would act as a giant windbreak, causing substantial adverse impacts on the remaining CVFTL habitat. Since the 1950's large portions of remaining CVFTL habitat have been invaded by Russian thistle, a noxious weed from Asia that can form dense mats one to two feet thick which completely cover and stabilize the soil. CVFTL habitat usually is characterized by large, open sandy areas with scattered vegetation. Over a period of years, the composition of the plant community may be altered, the food base changed, and the soil stabilized, resulting in CVFTL population reductions or local extirpations. In addition, plantain (Plantago insularis) and the introduced grass Schismus barbatus are invading substantial habitat in the Coachella Valley. These species may also stabilize the soil and reduce the suitability of the habitat for CVFTL. Unrestricted off-road vehicle use is another cause of habitat degradation and loss. Two areas are severely degraded; Flat Top Mountain/Edom Hill and Windy Point. The total area of these sites is about 7.8 square km (3.0 square mi) (24). Off-road activity also occurs at many smaller areas throughout the valley wherever there is a significant accumulation of blow-sand. The cumulative area of the smaller sites is not known. The cumulative impact of development, wind shielding and off-road vehicle activities on Uma inornata populations and habitat is difficult to quantify. Each of these factors have a negative impact, but synergistic effects have not been analyzed. However, a grave prediction emerges with even the most simplistic analysis of the rate of habitat loss: if the present rate of development continued, all of the remaining habitat in the Coachella Valley would be lost in 24 years and Uma inornata would be extinct by the year 2007. APPROVED PLAN: U.S. Fish and Wildlife Service. 1984. The Coachella Valley Fringe-toed Lizard Recovery Plan. U.S. Fish and Wildlife Service, Portland, OR. 54 pp. The following actions need to be taken in priority order to preserve the Coachella Valley fringe-toed lizard (CVFTL) and its habitat: 1. Habitat needs to be acquired for preservation. This is probably the most important element in the Recovery Plan. Without the establishment of two or more large-scale reserves, and supporting Management Practices - 3 (DRAFT) - Management Practices Species LIZARD, FRINGE-TOED, COACHELLA VALLEY Species Id ESIS151001 Date 14 MAR 96 viable self-sustaining populations, the long-term survival of the CVFTL cannot be assured. 2. CVFTL biological requirements are in urgent need of study. 3. CVFTL populations throughout the Coachella Valley need monitoring to determine trends in numbers and areas inhabited. 4. The effects of habitat modifications including Tamarisk (Tamarix sp.) windbreaks, and the encroachment of exotic vegetation such as Russian thistle (Salsola australis) and mustards (Brassica sp.), etc., on the CVFTL need further study, and appropriate management actions taken. 5. Restoration of CVFTL habitat through rehabilitation needs study. 6. Public information and education programs need to be developed and conducted to further public support and awareness of the importance of preserving this species. 7. Existing laws and regulations protecting CVFTL and their habitat must be enforced. Because of permanent habitat destruction, the CVFTL will never inhabit more than a fraction of its former range. Even with the implementation of suggested actions in the recovery plan, the population levels will continue to decline on unprotected lands as development in the Valley continues. Without implementation of the recovery plan, it is entirely conceivable this decline will continue to the point of extinction. The establishment of two or more large-scale reserves containing viable populations of CVFTL and secure habitat, should overcome the primary threat to the species existence. APPROVED PLAN: U.S. Fish and Wildlife Service. 1984. The Coachella Valley Fringe-toed Lizard Recovery Plan. U.S. Fish and Wildlife Service, Portland, OR. 54 pp. The following actions need to be taken in priority order to preserve the Coachella Valley fringe-toed lizard (CVFTL) and its habitat: 1. Habitat needs to be acquired for preservation. This is probably the most important element in the Recovery Plan. Without the establishment of two or more large-scale reserves, and supporting viable self-sustaining populations, the long-term survival of the CVFTL cannot be assured. 2. CVFTL biological requirements are in urgent need of study. 3. CVFTL populations throughout the Coachella Valley need monitoring Management Practices - 4 (DRAFT) - Management Practices Species LIZARD, FRINGE-TOED, COACHELLA VALLEY Species Id ESIS151001 Date 14 MAR 96 to determine trends in numbers and areas inhabited. 4. The effects of habitat modifications including Tamarisk (Tamarix sp.) windbreaks, and the encroachment of exotic vegetation such as Russian thistle (Salsola australis) and mustards (Brassica sp.), etc., on the CVFTL need further study, and appropriate management actions taken. 5. Restoration of CVFTL habitat through rehabilitation needs study. 6. Public information and education programs need to be developed and conducted to further public support and awareness of the importance of preserving this species. 7. Existing laws and regulations protecting CVFTL and their habitat must be enforced. Because of permanent habitat destruction, the CVFTL will never inhabit more than a fraction of its former range. Even with the implementation of suggested actions in the recovery plan, the population levels will continue to decline on unprotected lands as development in the Valley continues. Without implementation of the recovery plan, it is entirely conceivable this decline will continue to the point of extinction. The establishment of two or more large-scale reserves containing viable populations of CVFTL and secure habitat, should overcome the primary threat to the species existence. Management Practices - 5
                                   (DRAFT) - References
                      Species LIZARD, FRINGE-TOED, COACHELLA VALLEY
                                  Species Id ESIS151001
                                      Date 14 MAR 96



     

References

***** REFERENCES FOR ALL NARRATIVES EXCEPT N-OCCURRENCE ***** 01 Norris, K.S. 1958. The evolution and systematics of the iguanid genus Uma and its relation to the evolution of other North American desert reptiles. Bull. Am. Mus. Nat. Hist. 114(3):253-326. 02 Stebbins, R.C. 1954. Amphibians and reptiles of western North America. McGraw-Hill Book Company, New York. 528 pp. 03 Mayhew, W.W. 1965. Reproduction in the sand-dwelling lizard Uma inornata. Herpetologica 21(1):39-55. 04 Mayhew, W.W. 1964. Photoperiodic responses in three species of the lizard genus Uma. Herpetologica 20(2):95-113. 05 Cope, E.D. 1895. On the species of Uma and Xantusia. Amer. Nat. 29:938-939. 06 Cope, E.D. 1896. On the genus Callisaurus. Amer. Nat. 30:1049-1050. 07 Camp, C.L. 1916. Notes on the local distribution and habits of the amphibians and reptiles of southeastern California in the vicinity of the Turtle Mountains. Univ. Calif. Publ. Zool. 12(17):503-544. 08 Stejneger, L. and T. Barbour. 1917. A check list of North American amphibians and reptiles. Harvard Univ. Press, Cambridge. 125 pp. 09 Schmidt, K.P. 1953. A check list of North American amphibians and reptiles. Sixth edition. Publ. Amer. Soc. Ichthyol. Herpetol., Chicago. 280 pp. 10 Heifetz, W. 1941. A review of the lizards of the genus Uma. Copeia 1941(2):99-111. 11 Cope, E.D. 1900. The crocodilians, lizards and snakes of North America. Ann. Rept. U.S. Natl. Mus. 1898:153-1294. 12 Smith, H.M. 1946. Handbook of Lizards: Lizards of the United States and of Canada. Comstock Publ. Co., Ithaca. 557 pp. 13 Pough, F.H. 1973. Uma inornata Cope, Coachella Valley fringe-toed lizard. Catalog Amer. Amphib. Reptiles, Species Account #126, Soc. Study of Amphib. Reptiles. 2 pp. 14 Van Denburgh, J. 1922. The reptiles of western North America. Vol.1. Occas. Pap. Calif. Acad. Sci. 10:1-611. 15 Adest, G.A. 1977. Genetic relationships in the genus Uma (Iguanidae). Copeia 1977:47-52. 16 Zalusky, S.B., A.J. Gaudin, and J.R. Swanson. 1980. A comparative study of cranial osteology in the North American sand lizards, genus Uma (Reptilia:Iguanidae). Copeia 1980(2):296-310. 17 Mayhew, W.W. 1964. Taxonomic status of California populations of the lizard genus Uma. Herpetologica 20(3):170-183. 18 Mosauer, W. 1935. The reptiles of a sand dune area and its surroundings in the Colorado Desert, California: A study in habitat preference. Ecology 22(2):125-140. 19 Cowles, R.B. 1941. Observations on the winter activities of desert reptiles. Ecology 22(2):125-140. 20 Stebbins, R.C. 1944. Some aspects of the ecology of the iguanid genus Uma. Ecol. Monogr. 14(3):311-332. 21 Stebbins, R.C. 1966. A field guide to western reptiles and References - 1 (DRAFT) - References Species LIZARD, FRINGE-TOED, COACHELLA VALLEY Species Id ESIS151001 Date 14 MAR 96 amphibians. Houghton Mifflin Co., Boston. 279 pp. 22 Cornett, J. 1983. A masterpiece of adaptation -- Uma, the fringe-toed sand lizard. Pacific Discovery 36(2):2-10. 23 England, A.S. and S.G. Nelson. 1976. Status of the fringe-toed lizard (Uma inornata), Calif. Dept. Fish and Game, Inland Fisheries, Admin. Rept. No. 77. 129 pp. 24 England, A.S. 1983. The Coachella Valley, and endangered ecosystem: progress report on conservation and management efforts. Wildl. Soc. Cal-Neva. Wildl. Trans. In press. 25 County of Riverside. 1982. Southern California Association of Governments population forecasts. Riverside Cty. Plan. Dept., Riverside, CA. 26 Muth, A. 1984. Personal observation. Coachella Valley Ecological Reserve Foundation, P.O. Box 2821, Palm Desert, CA 92261. 27 Weaver, D.C. 1979. Assessment of effects of flood control alternatives on blowsand conditions in the Coachella Valley, Whitewater River Basin. Army Corps of Engrs., Los Angeles Dist., CA. 28 Weaver, D.C. 1981. Aeolian sand transport and deposit characteristics at ten sites in Coachella Valley, California, Part 2, IN: The effect of blowsand reduction on the abundance of the fringe-toed lizard (Uma inornata) in the Coachella Valley, California. U.S. Army Corps of Engineers, Los Angeles, CA. 29 Turner, F.G., D.C. Weaver, and T.C. Rorabaugh. 1981. The abundance of the fringe-toed lizard (Uma inornata) at 10 sites in the Coachella Valley, California. Part 1, IN: The effect of blowsand reduction on the abundance of the fringe-toed lizard (Uma inornata) in the Coachella Valley, California. U.S. Army Corps of Engineers, Los Angeles. 30 Pough, F.H. 1970. The burrowing ecology of the sand lizard, Uma notata. Copeia 1970(1):145-157. 31 Minnich, J.E. and V.H. Shoemaker. 1972. Water and electrolyte turnover in a field population of the lizard, Uma scoparia. Copeia 1972(4):650-659. 32 Mayhew, W.W. 1966. Reproduction in the psammophilous lizard Uma scoparia. Copeia 1966(1):114-122. 33 Carpenter, C.C. 1963. Patterns of behavior in three forms of the fringe-toed lizards (Uma,Iguanidae). Copeia 1963(2):406-412. 34 Stamps, J.A. 1977. Social behavior and spacing patterns in lizards. Pages 265-334. IN: C. Gans and D.W. Tinkle (eds.), Biology of the Reptilia, Vol.7, Ecology and Behavior A. Academic Press, New York. 720 pp. 35 Huey, R.B. 1982. Temperature, physiology, and the ecology of reptiles. Pages 25-91. IN: C.Gans and F.H. Pough (eds.), Biology of the Reptilia, Vol.12, Physiology C, Physiological Ecology, Part 1. Academic Press, New York. 536 pp. 36 Avery, R.A. 1982. Field Studies of body temperature and thermoregulation. Pages 93-166. IN: C.Gans and F.H. Pough (eds.), Biology of the Reptilia, Vol.12, Physiology C, Physiological Ecology, Part 1. Academic Press, New York. 536 pp. 37 Tracy, C.R. 1982. Biophysical modeling in reptilian physiology and ecology. IN: C.Gans and F.H. Pough (eds.), Biology of the Reptilia, Vol.12, Physiology C, Physiological Ecology, Part 1. References - 2 (DRAFT) - References Species LIZARD, FRINGE-TOED, COACHELLA VALLEY Species Id ESIS151001 Date 14 MAR 96 Academic Press, New York. 536 pp. 38 Mayhew, W.W. 1965. Hibernation in the horned lizard, Phrynosoma m'calli. Comp. Biochem. Physiol 16(1):103-119. 39 Pough, F.H. 1969. Physiological aspects of the burrowing of sand lizards (Uma, Iguanidae) and other lizards. Comp. Biochem. Physiol. 31(6):869-884. 40 Muth, A. 1980. Physiological ecology of desert iguana (Dipsosaurus dorsalis) eggs: temperature and water relations. Ecology 61(6):1335-1343. 41 Packard, M.J., G.C. Packard, and T.J. Boardman. 1981. Water balance of parchment-shelled eggs of a desert lizard (Callisaurus draconoides). Can. J. Zool. 58:2051-2058. 42 Burt, C.E. 1931. On the occurrence of a throat fan in the sand lizard Uma notata Baird, with notes on the adaptive specializations of the form. Copeia 1931(1):15-16. 43 Campbell, H.W. 1969. The effects of temperature on the auditory sensitivity of lizards. Physiol. Zool. 42(2):183-210. 44 Cook, S.F. 1949. Respiratory metabolism of certain reptiles and amphibians. Univ. California Publ. Zool. 53(10):367-376. 45 Cowles, R.B. and C.M. Bogert. 1944. A preliminary study of the thermal requirements of desert reptiles. Bull. Amer. Mus. Nat. Hist. 83(5):261-296. 46 Etheridge, R. 1964. The skeletal morphology and systematic relations of sceloporine lizards. Copeia 1964(4):610-631. 47 Mayhew, W.W. 1967. Comparative reproduction in three species of the genus Uma. Pages 45-61. IN: W.W. Milstead (ed.), Lizard Ecology: A symposium. Univ. Missouri Press, Columbia, MO. 300pp. 48 Mayhew, W.W. and S.J. Wright. 1970. Seasonal changes in testicular histology of three species of the lizard genus Uma. J. Morph. 130(2):163-186. 49 Norris, K.S. 1967. Color adaptation in desert reptiles and its thermal relationships. Pages 162-229. IN: W.W. Milstead (ed.), Lizard Ecology: A symposium. Univ. Missouri Press, Columbia, MO. 300 pp. 50 Pough, F.H. 1969. Environmental adaptations in the blood of lizards. Comp. Biochem. Physiol. 31(6):885-901. 51 Pough, F.H. 1969. The morphology of undersand respiration in reptiles. Herpetologica 25(3):216-223. 52 Stebbins, R.C. 1943. Adaptations in the nasal passages for sand burrowing in the saurian genus Uma. Amer. Nat. 77:38-52. 53 Stebbins, R.C. 1948. Nasal structure in lizards with reference to olfaction and conditioning of the inspired air. Amer. J. Anat. 83(2):183-222. 54 Stebbins, R.C. and R.M. Eakin. 1958. The role of the "third eye" in reptilian behavior. Amer. Mus. Novitates (1870):1-40. 55 Cornett, J.W. 1982. Interbreeding between Uma inornata and Uma notata. Southwest Nat. 27(2):223. 56 Mayhew, W.W. 1961. Photoperiodic response of female fringe-toed lizards. Science 134(3496):2104-2105. 57 Mayhew, W.W. 1966. Reproduction in the arenicolous lizard Uma notata. Ecology 47(1):9-18. 58 Mayhew, W.W. 1983. Conflicts between the fringe-toed lizard and development in the Coachella Valley. Wildl. Soc. Cal-Neva. Wildl. References - 3 (DRAFT) - References Species LIZARD, FRINGE-TOED, COACHELLA VALLEY Species Id ESIS151001 Date 14 MAR 96 Trans., In press. 59 U.S. Fish and Wildlife Service. 1985. Coachella Valley Fringe-toed Lizard Recovery Plan. Agency Draft. 60 England, A.S. and Wear. 1983. Manuscript in preparation. ***** REFERENCES FOR N-OCCURRENCE NARRATIVE ONLY ***** 01 Adest, G.A. 1977. Genetic relationships in the genus Uma (Iguanidae). Copeia 1977:47-52. 02 Brode, J. 1975. Personal communication. California Dept. of Fish and Game, Inland Fisheries, 1701 Nimbus Rd., Rancho Cordova, CA 95670. 03 Cornett, J.W. 1981. Biotic survey and population status of the Coachella Valley fringe-toed lizard (Uma inornata) on Indian Avenue properties. Biological survey for Draft Environmental Impact Report, Highland-Gateway Development Project, Palm Springs Redevelopment Agency, Palm Springs, CA 92263. 04 Cornett, J.W. 1983. Personal Communication. Palm Springs Desert Museum, P.O. Box 2288, Palm Springs, CA 92263. 05 Cowles, R.B. 1941. Observations on the winter activities of desert reptiles. Ecology 22(2):125-140. 06 Davis, J. 1969-1975. Personal communication to A.S. England. 07 England, A.S. 1983. The Coachella Valley, and endangered ecosystem: progress report on conservation and management efforts. Wildl. Soc. Cal-Neva. Wildl. Trans. 08 England, A.S. and S.G. Nelson. 1976. Status of the fringe-toed lizard (Uma inornata), Calif. Dept. Fish and Game, Inland Fisheries, Admin. Rept. No. 77-1. 09 England, A.S. and S.G. Nelson. 1976. Personal communication. A.S.E., Dept. Wildlife and Fisheries, Univ. California, Davis, CA 95616; S.G.N., Environmental Consultants, P.O. Box 1026, Riverside, CA 92502. 10 Friesen, R.D. 1983. Biological assessment, Palm Valley Country Club, Specific Plan No. 181-E, Riverside Co., CA. Friesen Biological Surveys, 615 Bermuda Dr., Redlands, CA 922373. 11 LaPre, L.F. 1982. Endangered species survey of the Devers-Valley-Serrano Transmission line project. Southern California Edison Company, DEIR/EIR SCH 80120519, Calif. Public. Util. Comm., A59982. 12 LaPre, L.F. 1983a. Personal communication. The Mission Inn Rotunda, Suite 501, 3616 Main Street, Riverside, CA 92501. 13 LaPre, L.F. 1983b. The Monterey Avenue and Avenue 34 extensions: Biological inventory and impact analysis. Final Environmental Impact Report No. 178, Riverside Co. Planning Dept., Riverside, CA. 14 LaPre, L.F. and J.W. Cornett. 1981. Public lands survey for the Coachella Valley fringe-toed lizard. Bureau of Land Management, Riverside, CA. 15 Mayhew, W.W. 1965. Reproduction in the sand-dwelling lizard Uma inornata. Herpetologica 21(1):39-55. 16 Mayhew, W.W. 1958-1973. Personal communication. Dept. of Biology, Univ. of California, Riverside, CA 92521. 17 Mayhew, W.W. 1981. Line transects and photo sites on the Deep References - 4 (DRAFT) - References Species LIZARD, FRINGE-TOED, COACHELLA VALLEY Species Id ESIS151001 Date 14 MAR 96 Canyon transect. Philip L. Boyd Deep Canyon Desert Research Center, Univ. of California, Riverside, CA 92521. 18 Museum Records. 1900-1975. A.S. England, personal communication. Collections examined: Los Angeles County Museum of Natural History; San Diego Natural History Museum; University of California Museum of Vertebrate Zoology. 19 Muth, A. 1983. Personal observation. Coachella Valley Ecological Reserve Foundation, P.O. Box 2821, Palm Desert, CA 92261. 20 Norris, K.S. 1958. The evolution and systematics of the iguanid genus Uma and its relation to the evolution of other North American desert reptiles. Bull. Am. Mus. Nat. Hist. 114(3):253-326. 21 Pough, F.H. 1970. The burrowing ecology of the sand lizard, Uma notata. Copeia 1970(1):145-157. 22 Stebbins, R.C. 1944. Some aspects of the ecology of the iguanid genus Uma. Ecol. Monogr. 14(3):311-332. 23 Stevens, D.W. 1983. Personal communication. Environmental and Regulatory Affairs, Southern California Edison Company, P.O. Box 800, Rosemead, CA 91770. 24 Turner, F.G., D.C. Weaver, and T.C. Rorabaugh. 1981. The abundance of the fringe-toed lizard (Uma inornata) at 10 sites in the Coachella Valley, California. Part 1, IN: The effect of blowsand reduction on the abundance of the fringe-toed lizard (Uma inornata) in the Coachella Valley, California. U.S. Army Corps of Engineers, Los Angeles. 25 Tinkham, E.R. 1980. Biological survey of the Winte-Dresselhaus property North Jackson Street, Indio, California. Annexation #50, City of Indio, 100 Civic Center Mall, Indio, CA 92202. 26 U.S. Fish and Wildlife Service. 1982. Endangered and Threatened wildlife and plants; Listing as threatened with critical habitat for the Coachella Valley fringe-toed lizard. 50 CFR Part 17. 27 Vitt, J.T. 1983. Personal communication. Department of Biology, Univ. of California, Los Angeles, CA 90024. 28 Weaver, D.C. 1981. Aeolian sand transport and deposit characteristics at ten sites in Coachella Valley, California, Part 2, IN: The effect of blowsand reduction on the abundance of the fringe-toed lizard (Uma inornata) in the Coachella Valley, California. U.S. Army Corps of Engineers, Los Angeles. 29 Wilbanks, J.B. 1983. Personal communication. Planning Department, City of Indio, 100 Civic Center Mall, Indio, CA 92202. 30 Cornett, J.W. 1983. Biological survey of a seventy two acre parcel near Bermuda Dunes, Riverside Co., California. Riverside County Planning Department, Environmental Consultants, 933 Calle Loro, Palm Springs, CA 92263. 31 Tierra Madre Consultants. 1984. Personal communication. Tierra Madre Consultants, Mission Inn Rotunda, Suite 306, 3616 Main St., Riverside, CA 92501. References - 5