(Vasey) J. Reeder
Identity
Unique IDELEMENT_GLOBAL.2.144317
Element CodePMPOA6N010
Record TypeSPECIES
ClassificationSpecies
Classification StatusStandard
Name CategoryVascular Plant
Endemicendemic to a single state or province
KingdomPlantae
PhylumAnthophyta
ClassMonocotyledoneae
OrderCyperales
FamilyPoaceae
GenusTuctoria
SynonymsOrcuttia greeneiVasey
Other Common NamesAwnless Spiralgrass (EN) awnless spiralgrass (EN) Greene's tuctoria (EN)
Concept ReferenceKartesz, J.T. 1994. A synonymized checklist of the vascular flora of the United States, Canada, and Greenland. 2nd edition. 2 vols. Timber Press, Portland, OR.
Conservation Status
Rank MethodLegacy Rank calculation - Excel v3.1x
Review Date2016-10-11
Change Date2013-08-20
Edition Date1997-04-18
Edition AuthorsMichael Schindel (Mar/1997); K. Maybury (Apr/1997), rev. K. Gravuer (2009)
Range Extent5000-20,000 square km (about 2000-8000 square miles)
Number of Occurrences6 - 80
Rank ReasonsRestricted to vernal pools in the Central Valley of California. Of the total 43 occurrences ever recorded, 21 are currently considered historical and 2 are considered extirpated; 20 (47%) remain extant. Vernal pool habitats in California's Central Valley have been greatly reduced from pre-European times; the remaining habitats are limited in extent, fragmented, and are facing on-going degradation and elimination due to numerous housing development projects and other types of urban development, agricultural activities and development, grazing, the invasion of non-native plant species, and other threats.
Range Extent CommentsEndemic to the Central Valley of California. Occurs in three Vernal Pool Regions: the Northeastern Sacramento Valley Vernal Pool Region (Tehama Co. and Butte Co.), particularly in the Vina Plains; the Modoc Plateau Vernal Pool Region to the north (Shasta Co.); and the Southern Sierra Foothills Vernal Pool Region some distance to the south (eastern Merced Co., with one historical occurrence in Madera Co.). Considered historical in Tulare, Fresno, San Joaquin, and Stanislaus Cos., and extirpated from Glenn Co. Current range is estimated to be about 17,000 square km.
Occurrences CommentsIn total, 20 occurrences are believed extant, a further 21 occurrences are considered historical, and 2 occurrences are extirpated. Recent genetic study suggests that the number of populations may be less than this (i.e. some mapped sites should be lumped into the same occurrence, suggested by high gene flow/genetic similarity) (S. Gordon pers. comm. 2009). Of the occurrences currently mapped, 13 extant occurrences are in the Northeastern Sacramento Valley Vernal Pool Region (9 in Tehama Co. and 4 in Butte Co.); this region also contains 4 historical and 1 extirpated occurrence. 6 extant occurrences are in the Southern Sierra Foothills Vernal Pool Region (eastern Merced Co.), along with 6 historical occurrences (5 in Merced Co. and one in Madera Co.). 1 extant occurrence is in the Modoc Plateau Vernal Pool Region (Shasta Co.). Only historical occurrences are known from Tulare, Fresno, San Joaquin, and Stanislaus Cos., and the Glenn Co. occurrence is considered extirpated (USFWS 2005, CNDDB 2008).
Threat Impact CommentsThe largest threat to California and southern Oregon vernal pools is habitat loss and fragmentation. In general, habitat loss in this region is driven by urbanization, agricultural conversion, and mining. Habitat alteration and degradation is occurring as a result of numerous factors, including changes to natural hydrology; invasive species; incompatible grazing (including insufficient grazing for prolonged periods); infrastructure projects (e.g. roads, water storage and conveyance, utilities); recreational activities (e.g. off-highway vehicles and hiking); erosion; climatic and environmental change; and contamination. Habitat fragementation resulting from activities associated with habitat loss, especially new infrastructure projects, further threatens California and southern Oregon vernal pool species (USFWS 2005).
For Tuctoria greenei specifically, agricultural conversion and inappropriate livestock grazing practices pose threats to virtually all occurrences in the San Joaquin Valley. Approximately 15 occurrences are adversely affected by cattle grazing. Urbanization, including construction of a landfill, is a potential threat. One potential factor unique to this and some other vernal pool plant species may be decimation by grasshopper outbreaks; grasshoppers have been noted consuming entire populations of T. greenei before they set seed, although the seed bank may permit some recovery in subsequent years (USFWS 2005).