Tuctoria greenei

(Vasey) J. Reeder

Green's Awnless Orcutt Grass

G1Critically Imperiled Found in 24 roadless areas NatureServe Explorer →
G1Critically ImperiledGlobal Rank
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
Synonyms
Orcuttia greeneiVasey
Other Common Names
Awnless Spiralgrass (EN) awnless spiralgrass (EN) Greene's tuctoria (EN)
Concept Reference
Kartesz, 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 Reasons
Restricted 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 Comments
Endemic 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 Comments
In 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 Comments
The 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).
Ecology & Habitat

Description

Grows in tufts of several unbranched stems 5-15 cm tall, erect or decumbent and breaking easily at the base. Entire plant often has soft shaggy hairs, but is only slightly sticky. Has purplish nodes and leaves 5 mm or narrower. Inflorescence can be up to 8 cm long; it may be partly hidden by the leaves when young, but is held above the leaves when mature. Inflorescence usually consists of 7-15 spikelets, but may contain up to 40. Spikelets are arranged in a spiral, with those in the upper half crowded together and those near the base more widely separated. Each spikelet has 5-15 florets and 2 glumes. Lemmas are 4-5 mm long and have squarish tips with 5-9 very short teeth; central tooth is tipped by a very small spine. Roughened seeds are about 2 mm long and weigh about 0.5 mg (USFWS 2005).

Diagnostic Characteristics

Differs from the closely related Tuctoria mucronata, found only in Solano and Yolo counties, by being larger in stature (30 cm vs. 12 cm), by its squarish lemma tip, by its smaller and roughened seeds, and in having inflorescences not included in the leaf (held above the leaf) when fully mature. Both can be told from the remaining Tuctoria species by stem length, seed shape, and range. The chromosome number of T. greenei also differs from the other two species in the genus. May also be confused with plants from the Orcuttia and Neostapfia genera. Neostapfia can be distinguished by its stout cylindrical spikes which look like tiny ears of corn. Orcuttia has its spikelets arranged in two rows on opposite sides of the spike (distichous) rather than spirally as in Tuctoria and has floating juvenile leaves (absent in T. greenei). Its short-toothed, narrow lemmas also distinguish T. greenei from Orcuttia and Neostapfia plants.
In general, the Orcuttieae tribe of grasses (Tuctoria, Orcuttia, and Neostapfia) differs from other grasses in (1) having a pith-filled (vs. hollow) stem, (2) producing 2-3 different types of leaves (vs. a single type) during their life cycle: cylindrical juvenile leaves which form underwater clustered into a basal rosette, and terrestrial leaves with flattened blades distributed along the stem, (3) having terrestrial leaves that are broad throughout with the lower portion enfolding the stem only loosely (vs. leaves differentiated into a narrow, tubular sheath that clasps the stem tightly and a broader blade that projects away from the stem), (4) having leaves which lack a ligule, and (5) producing an aromatic exudate, which changes from clear to brown during the growing season (USFWS 2005).

Habitat

Grows in the bottom of dried Vernal Pools on the eastern side of the Sacramento and San Joaquin Valleys.Occurs in Northern Basalt Flow, Northern Claypan, and Northern Hardpan vernal pools (Sawyer and Keeler-Wolf 1995) on both low and high terraces within grassland communities, or, rarely, pine forest (one Shasta Co. occurrence). Plants have been documented on clay, loam, and stony clay loam soils, and pools are underlain by iron-silica cemented hardpan, tuffaceous alluvium, or claypan. Occupied pools range in size from 50 square meters to 3.4 hectares (median size 0.6 hectares). Tends to grow in shallower pools than its relatives (Neostapfia and Orcuttia) or on the shallow margins of deeper pools. Associated species include Eryngium castrense, Marsilea vestita, Eryngium vaseyi, Plagiobothrys stipitatus, Alopecurus saccatus, Chamaesyce hooveri, Orcuttia pilosa, O. inaequalis, O. tenuis, Neostapfia colusana, and Gratiola heterosepala. 30-135 m in Central Valley; 1100 m in Shasta Co. (one occurrence).

Ecology

Grows in Vernal Pools. Common associates include; coyote thistle (Eryngium), spikerush (Eleocharis), Hoover's spurge (Chamaesyce hooveri), colusa grass (Neostapfia colusana), and hairy Orcutt grass (Orcuttia pilosa). Seeds are almost entirely dependant on a combination of anaerobic conditions and light for germination. Fungi may play a role in the germination process. Such cues are specific to the uppermost soil strata overlain by H2O for a significant period of time. This prevents seeds which are too deep from germinating, or germination in years when insufficient precipitation has fallen to allow the plant to complete its life cycle. seeds can persist for many years in the ground. The shrink/swell nature of the clay soils in the Central Valley act as conveyors to bring deeply buried seeds to the surface.
Terrestrial Habitats
Forest/WoodlandForest - ConiferGrassland/herbaceous
Palustrine Habitats
TEMPORARY POOL
Other Nations (1)
United StatesN1
ProvinceRankNative
CaliforniaS1Yes
Threat Assessments
ThreatScopeSeverityTiming
1 - Residential & commercial developmentLarge - restrictedSerious or 31-70% pop. declineHigh - moderate
1.1 - Housing & urban areasLarge - restrictedSerious or 31-70% pop. declineHigh - moderate
2 - Agriculture & aquacultureLarge - restrictedSerious - moderateHigh - moderate
2.1 - Annual & perennial non-timber cropsLarge - restrictedModerate or 11-30% pop. declineHigh - moderate
2.3 - Livestock farming & ranchingLarge - restrictedSerious or 31-70% pop. declineHigh (continuing)
3 - Energy production & miningLarge - restrictedModerate or 11-30% pop. declineHigh - moderate
3.2 - Mining & quarryingLarge - restrictedModerate or 11-30% pop. declineHigh - moderate
4 - Transportation & service corridorsLarge - restrictedModerate or 11-30% pop. declineHigh - moderate
4.1 - Roads & railroadsLarge - restrictedModerate or 11-30% pop. declineHigh - moderate
4.2 - Utility & service linesLarge - restrictedModerate or 11-30% pop. declineHigh - moderate
6 - Human intrusions & disturbanceLarge - restrictedModerate or 11-30% pop. declineHigh (continuing)
6.1 - Recreational activitiesLarge - restrictedModerate or 11-30% pop. declineHigh (continuing)
8 - Invasive & other problematic species, genes & diseasesLarge - restrictedSerious or 31-70% pop. declineHigh (continuing)
8.1 - Invasive non-native/alien species/diseasesLarge - restrictedSerious or 31-70% pop. declineHigh (continuing)
9 - PollutionLarge - restrictedModerate or 11-30% pop. declineHigh (continuing)
11 - Climate change & severe weatherLarge - restrictedModerate or 11-30% pop. declineModerate - low
11.1 - Habitat shifting & alterationLarge - restrictedModerate or 11-30% pop. declineModerate - low

Plant Characteristics
DurationANNUAL
Economic Value (Genus)No
Roadless Areas (24)
California (21)
AreaForestAcres
Bear Camp FlatModoc National Forest2,471
Big CanyonModoc National Forest6,615
Burnt Lava FlowModoc National Forest8,387
Crane Mtn.Modoc National Forest1,269
Damon ButteModoc National Forest25,022
Dobie FlatModoc National Forest15,079
DryModoc National Forest7,726
GrangerModoc National Forest23
Hat Mtn.Modoc National Forest9,478
Knox Mtn.Modoc National Forest5,975
LavasModoc National Forest25,864
MillModoc National Forest321
Mt. BidwellModoc National Forest11,687
Mt. HoffmanModoc National Forest9,780
Mt. VidaModoc National Forest7,771
ParsnipModoc National Forest8,485
PepperdineModoc National Forest10
PowleyModoc National Forest6,268
SoldierModoc National Forest10,102
Steele SwampModoc National Forest18,958
Timbered CraterLassen National Forest4,096
Oregon (2)
AreaForestAcres
Crane MountainFremont National Forest23,096
Mt. BidwellFremont National Forest4,449
South Dakota (1)
AreaForestAcres
Indian CreekBuffalo Gap National Grassland24,666
References (8)
  1. California Department of Fish and Game. 1986. California Native Plant Status Report, <i>Tuctoria greenei</i>. California Dept. of Fish and Game, Natural Diversity Database.
  2. California Natural Diversity Database, Natural Heritage Program. 1979.
  3. Hickman, J. C., ed. 1993. The Jepson manual: Higher plants of California. University of California Press, Berkeley, CA. 1400 pp.
  4. Kartesz, 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.
  5. Sawyer, J.O. and T. Keeler-Wolf. 1995. A Manual of California Vegetation. California Native Plant Society, Sacramento.
  6. Skinner, M.W., and B.M. Pavlik, eds. 1994. California Native Plant Society's Inventory of rare and endangered vascular plants of California. 5th edition. California Native Plant Society, Sacramento. 338 pp.
  7. U.S. Fish and Wildlife Service (USFWS). 1997. Determination of endangered status for three plants and threatened status for five plants from vernal pools in the Central Valley of California. Federal Register 62(58): 14338-14352.
  8. U.S. Fish and Wildlife Service (USFWS). 2005. Recovery Plan for Vernal Pool Ecosystems of California and Southern Oregon. Portland, Oregon. xxvi + 606 pages. Online. Available: https://ecos.fws.gov/docs/recovery_plan/Vernal%20Pool%20Ecosystem%20Final%20Recovery%20Plan.pdf