DRAFT March 2012 PLANTS Ash Meadows Gumplant (Grindelia fraxino-pratensis) Ash Meadows Gumplant Grindelia fraxino-pratensis Legal Status State: S1.21 California Rare Plant Rank: 1B.22 Federal: Threatened Critical Habitat: Originally designated on May 20, 1985 (50 FR 20777–20794) Recovery Planning: Recovery Plan for the Endangered and Threatened Species of Ash Meadows, Nevada (Sada 1990) Notes: N/A Taxonomy Ash Meadows gumplant (Grindelia fraxino-pratensis) is a perennial (or sometimes biennial) herb in the sunflower (Asteraceae) family. The species was originally described by Reveal (1977), and according to the U.S. Fish and Wildlife Service (USFWS) 5-year review, the taxonomy of Ash Meadows gumplant has not been changed since the species was listed (USFWS 2007). Ash meadows gumplant stands approximately 5 to 12 decimeters (1.6 to 3.9 feet) in height. A full physical description of the species can be found in The Jepson Interchange (2011). Distribution General Ash Meadows gumplant is only known to occur in mesic meadows within Carson Slough in Nye County in Nevada and Inyo County in California (Figure SP-P5). Its distribution includes three main populations and several smaller populations over an area of approximately 2,260 acres and that are mostly concentrated in the Ash Meadows National Wildlife Refuge (NWR) in Nevada (USFWS 1 2 S1: Critically imperiled; X.2: Threatened. 1B: Rare, threatened, or endangered in California and elsewhere. X.2: Fairly endangered in California. 1 6668 March 2012 DRAFT March 2012 PLANTS Ash Meadows Gumplant (Grindelia fraxino-pratensis) 2007). One population is located on Bureau of Land Management (BLM) lands outside of the Refuge in Carson Slough and includes the population that extends into California. Distribution and Occurrences within the Plan Area Historical Much of the mesic meadow habitat of the endemic Ash Meadows gumplant has been destroyed, and historically large, continuous populations are now fragmented. Several large populations in Ash Meadows were observed to be scarcely present in 1976 (USDA 2003). Of the two occurrences documented in the California Natural Diversity Database (CNDDB), one population on private property near Shoshone, California, is considered historical since the plants have not been observed since 1989. However, this occurrence is still presumed to be extant (CDFG 2012a) (Figure SP-P5). The other location in the Carson Slough was re-surveyed in 2003 and is discussed below. Recent Carson Slough is the location of the only recent occurrence of Ash Meadows gumplant that is reported in the Plan Area by the CNDDB (CDFG 2012a). This population numbered an estimated 250,000 individuals in 2003 and includes the previously documented population observed in the 1980s (Occurrence #2 in the CNDDB) (CDFG 2012a). The populations at Carson Slough occur on lands owned and managed by the BLM. Rangewide, based on surveys conducted in 1998, Ash Meadows gumplant was noted to be present at the majority of the sites it occupied in 1985 when the species was originally listed (USFWS 2007). Although some sites on private property were not accessed in 1998, six new populations were identified in Ash Meadows. The species has been reported from two locations in Lower Carson Slough of the Amargosa River drainage (BLM 2006). 2 6668 March 2012 DRAFT March 2012 PLANTS Ash Meadows Gumplant (Grindelia fraxino-pratensis) Natural History Habitat Requirements Ash Meadows gumplant occurs at elevations between 630 and 707 meters (2,070 and 2,320 feet) and prefers open sun exposure in areas with standing water or locally high groundwater tables (Table 1; BLM 2006). Table 1. Habitat Associations for Ash Meadows Gumplant Land Cover Type Saltgrass meadow, Ash–screwbean mesquite woodland Habitat Designation Primary Habitat Parameters Clay barrens, 635 to 700 meters (2,070 to 2,320 feet) elevation Supporting Information CNPS 2011; USDA 2003; BLM 2006 Ash Meadows gumplant occurs most frequently in meadows along stream channels and associated shallow pools, but occasionally it can be found in more xeric alkaline scrub as well. The species has been documented in other habitats including saltgrass (Distichlis spicata var. stricta)–dominated meadows, woodlands dominated by velvet ash (Fraxinus velutina var. coriacea) and screwbean mesquite (Prosopis pubescens), and desert scrub dominated by shadscale (Atriplex confertifolia). Ash Meadows gumplant has also been documented on open alkali clay soils or in clay barrens where it cooccurs with other endemic plant species such as alkali ivesia (Ivesia kingii var. eremica) and Ash Meadows sunray (Enceliopsis nudicaulis var. corrugata) (BLM 2006). Common co-occurring plant species may include other facultative wetland and obligate plants such as spring-loving centaury (Centaurium namophilum var. namophilum), yerba mansa (Anemopsis californica), loosestrife (Lythrum californicum), and iva (Iva acerosa). Common co-occurring upland plant species may include alkali sacaton (Sporobolus airoides), alkali goldenbush (Isocoma acradenia), and rabbitbush (Chrysothamnus albidus) (BLM 2006). 3 6668 March 2012 DRAFT March 2012 PLANTS Ash Meadows Gumplant (Grindelia fraxino-pratensis) Reproduction Ash Meadows gumplant is an erect biennial or more commonly a perennial herb (USFWS 2007). Individual plants can produce hundreds of seeds under suitable conditions (Lane 1992). Dispersal of the small seed is most likely accomplished by strong winds because they could be blown for some distance. Seeds that fall in close proximity to the parent plant could be farther transported by water during the winter rainy season or during summer flash floods (Lane 1992; BLM 2006; USFWS 2007). Pollinator relationships for this species are unknown (BLM 2006), but during a recent pollinator study in the BLM Amargosa Preserve area, five unreported, different insect pollinators were observed visiting this species (Bio-West 2009). Ash Meadows gumplant does not appear to hybridize with any other species within the genus (Lane 1992). Ecological Relationships Habitat for Ash Meadows gumplant typically occurs on plains dominated by very fine textured soils that have a high salt content and a high water table (USDA 2003). The primary habitat for Ash Meadow gumplant occurs within Ash Meadows, which includes a system of springs (including 7 major springs and over 20 smaller ones) that have been heavily manipulated by human activities (see Threats and Environmental Stressors). The Ash Meadows area is a unique ecosystem that supports many plant and animals species that are associated with the wetland and aquatic habitats in the area (USFWS 2007). Other than the habitat and species associations noted in the Habitat Requirement section, little is known of the species’ ecological relationships. Population Status and Trends Global: G2, Imperiled (CDFG 2012b) State: S1.2, Critically Imperiled (CDFG 2012b) Within Plan Area: Same as above Based on the new observations in 1998 compared to the known population in 1985 when it was listed, the distribution of Ash Meadows gumplant appears to have increased since the species was 4 6668 March 2012 DRAFT March 2012 PLANTS Ash Meadows Gumplant (Grindelia fraxino-pratensis) listed in 1985 (USFWS 2007). However, there are no systematic quantitative population or demographic data available to establish population trends for the Ash Meadows gumplant. A visually based population estimate in 2000 for the entire population was about 81,000 individuals in the 2,260 acres of habitat. In contrast, a 2002 transect-based survey of the only the Inyo County, California population estimated 241,514 ± 69,660 plants within 88 acres, indicating that the visual estimate severely underestimated the population (Soil Ecology and Restoration Group 2004, cited in USFWS 2007). It has been noted that in dense vegetation, surveyors have reported difficulty identifying individual plants (USDA 2003), so there is some risk of the populations being underreported. Threats and Environmental Stressors Loss of habitat and reduction of the species’ range by non-native and invasive plants is the most significant remaining threat to the species (USFWS 2007). Habitat loss is particularly true at Carson Slough and in the northern part of Ash Meadows where the primary habitat for this species has been either been destroyed or degraded (Fraser and Martinez 2002). In addition, surface mining and groundwater and surface water extraction, although not imminent, also present potential threats to the species as of the 5-year review (USFWS 2007). Habitat loss may also potentially occur in areas where clay mining claims have been granted or transportation corridors are proposed (USDA 2003). Degradation of suitable habitat within the species’ range may also occur as a result of trampling and/or grazing by wild horses and offroad vehicle use. In addition, the spread of tamarisk (Tamarix ramosissima) may threaten the integrity of the surface water supply and available habitat for Ash Meadows gumplant (BLM 2006). Although the species can occur as a weed on disturbed areas within its range, the potential for long-term reestablishment in disturbed areas that are being allowed to recover is unknown (USDA 2003). Conservation and Management Activities The “Amargosa River Area of Critical Environmental Concern Implementation Plan” (BLM 2006) includes conservation and 5 6668 March 2012 DRAFT March 2012 PLANTS Ash Meadows Gumplant (Grindelia fraxino-pratensis) management activities for Ash Meadows gumplant. In consultation and coordination with Ash Meadows NWR, recovery and research actions include: establishment of new Ash Meadows gumplant populations in unoccupied, suitable habitat, based on monitoring results and literature review and monitoring to better determine specific habitat requirements for Ash Meadows gumplant. In addition, the wild horse population is limited in size and the wild burrow population was eliminated (BLM 2006). Within it range including the Nevada populations in the Ash Meadows NWR, important conservation measures have been implemented to protect the groundwater and surface water within the range of the Ash Meadows gumplant, including monitoring groundwater pumping within the hydrologically connected springs of Ash Meadows. A minimum water level in Devils Hole is being maintained to protect the Devils Hole pupfish, and this effort and ongoing monitoring by the U.S. Geological Survey (USGS) helps protect the hydrologic integrity of all the Ash Meadows springs (USFWS 2007). Management for the species includes preparation of an Integrated Pest Management Plan to help control invasive species (USFWS 2007). Purchase of 11,173 acres of land and surface water rights in the Ash Meadows area by the Nature Conservancy and subsequent sale to the USFWS to establish the refuge in June 1984 have significantly reduced many of the threats to the Ash Meadows gumplant (USFWS 2007). Data Characterization The most recent data in the Plan Area are from 2003 (CDFG 2012a). As described above under Population Status and Trends, existing data regarding the species populations cannot be used to determine trends because earlier data and population estimates were based on visual surveys. When these visual survey data are compared to systematic transect data it is clear that the visual data grossly underestimate population sizes (USFWS 2007). Further, it has been noted that the species can be hard to detect in dense vegetation (USDA 2003). Nonetheless, the distribution on public lands in the Ash Meadows and Carson Slough areas seems fairly well understood based on the 1998 survey data. One of the BLM identified actions for recovery and 6 6668 March 2012 DRAFT March 2012 PLANTS Ash Meadows Gumplant (Grindelia fraxino-pratensis) research is monitoring to better understand habitat requirements (BLM 2006). Management and Monitoring Considerations Management primarily involves ensuring adequate groundwater and high salt content soils to maintain suitable habitat for Ash Meadows gumplant. Control of invasive species such as tamarisk, which competes for water and increase fire hazards, is also an important management consideration. The USFWS (2007) identified several measures in the 5-year review for the species that should be completed between 2008 and 2013. These include monitoring existing populations, providing pre-and post-restoration quantification to document any success that restoration activities may be providing, securing funding to implement weed control throughout the NWR, and withdrawing or purchasing outstanding mineral mining claims on BLM and USFWS lands within the range of the species. The BLM identified monitoring to better understand habitat requirements and establishment of new populations in unoccupied, suitable habitat and is monitoring the impacts of wild horses (BLM 2006). Predicted Species Distribution in Plan Area There are 154,063 acres of modeled suitable habitat for Ash Meadows gumplant in the Plan Area. The modeled suitable habitat is restricted to the Amargosa Desert-Pahrump Valley and Funeral Mountains-Greenwater Valley ecoregion subsections in the northeastern portion of the Plan Area, from 1,500 to 2,400 feet. Suitable habitat includes meadow or more xeric alkaline scrub vegetation types or areas near seeps/springs with clay soils. Appendix C includes specific model parameters and a figure showing the modeled suitable habitat in the Plan Area. Literature Cited 50 FR 20777–20794 Final Rule: “Endangered and Threatened Wildlife and Plants; Determination of Threatened Status with Critical Habitat for Six Plants and One Insect in Ash Meadows, Nevada, 7 6668 March 2012 DRAFT March 2012 PLANTS Ash Meadows Gumplant (Grindelia fraxino-pratensis) and California; and Endangered Status with Critical Habitat for One Plant in Ash Meadows, Nevada, and California. Bio-West Inc. 2009. Ash Meadows National Wildlife Refuge: Pollinator Study 2008 Annual Report. Logan, Utah: Bio-West Inc., p.15. BLM (Bureau of Land Management). 2006. “Amargosa River Area of Critical Environmental Concern Implementation Plan.” Barstow, California: BLM Field Office. 285 pp. BLM. 2011. “All BLM California Special-Status Plants.” BLM specialstatus plants under the jurisdiction of the California State Office as of December 17, 2010. Accessed May 2011. http://www.blm.gov/pgdata/etc/medialib/blm/ca/pdf/pa/ botany.Par.25833.File.dat/All%20CA%20Plants%20Detailed% 20Report-12-17-2010.pdf. CDFG (California Department of Fish and Game). 2012a. “Grindelia fraxino-pratensis.” Element Occurrence Query. California Natural Diversity Database (CNDDB). RareFind, Version 4.0 (Commercial Subscription). Sacramento, California: CDFG, Biogeographic Data Branch. Accessed February 2012. http://www.dfg.ca.gov/biogeodata/cnddb/mapsanddata.asp. CDFG. 2012b. Special Vascular Plants, Bryophytes, and Lichens List. California Natural Diversity Database (CNDDB). January 2012. Accessed February 2012. http://www.dfg.ca.gov/biogeodata/ cnddb/plants_and_animals.asp. Fraser, J., and C. Martinez. 2002. “Restoring a Desert Oasis.” Endangered Species Bulletin March/June. XXVII(2):18–19. Jepson Flora Project. 2011. “Grindelia fraxinipratensis.” The Jepson Online Interchange: California Floristics. Berkeley, California: University of California. Accessed August 2011. http://ucjeps.berkeley.edu/interchange.html. Lane M.A. 1992. “New Combinations in California Grindelia (Compositae: Astereae).” Novon 2:215–217. St. Louis, Missouri: Missouri Botanic Garden Press. 8 6668 March 2012 DRAFT March 2012 PLANTS Ash Meadows Gumplant (Grindelia fraxino-pratensis) NatureServe. 2010. “Grindelia fraxinopratensis.” NatureServe Explorer: An Online Encyclopedia of Life [web application]. Version 7.1. Arlington, Virginia: NatureServe. Accessed June 2011. http://www.natureserve.org/explorer. Sada, D.W. 1990. Recovery Plan for the Endangered and Threatened Species of Ash Meadows, Nevada. Prepared for the U.S. Fish and Wildlife Service (Portland, Oregon). Reno, Nevada: U.S. Fish and Wildlife Service. USDA (U.S. Department of Agriculture). 2003. Biological Assessment for the Sierra Nevada Forest Plan Amendment SEIS Final. Species Account No.33. Accessed May 2011. http://www.fs.fed.us/ r5/snfpa/final-seis/biological-documents/BA/VI/A/34.htm. USFWS. 2007. “Ash Meadows Gumplant (Grindelia fraxino-pratensis).” Five-Year Review: Summary and Evaluation. Las Vegas, Nevada: USFWS, Nevada Fish and Wildlife Office, http://ecos.fws.gov/ docs/five_year_review/doc1865.pdf. USFWS. 2010. Species profile for Ash Meadows Gumplant. Pacific Southwest Region, Nevada Office. Accessed May 2011. http://www.fws.gov/nevada/protected_species/plants/ species/am_gumplant.html. 9 6668 March 2012