Galena Creek rockcress (Arabis rigidissima v. demote) is a slender perennial plant in the Brassicaceae (mustard) family. The species occurs on sandy to rocky soils or on outcrops derived from granitic or volcanic materials, mostly on moderate to steep terrain with northerly aspects. Galena Creek rockcress has a global rank of G3T3Q (vulnerable but has taxonomic questions), a state rank of S1 (critically imperilled), a California Native Plant Society Rare Plant Rank of 1B.2 (rare, threatened or endangered in California and elsewhere; fairly endangered in California), and is on the at-risk list of the Nevada Natural Heritage Program. The species is restricted to Washoe County in Nevada and Placer and Nevada counties in California, and just an estimated 10,000 individuals are known from private, state and USDA Forest Service land. The primary threats to the species are recreational activities that might trample or uproot plants (e.g., camping, hiking, equestrian use, trail construction, snowmobiles) and climate change.  Projects such as fencing and signage near plants are aimed at reducing recreation impacts around known sites. Galena Creek rockcress is monitored by the USDA Forest Service. 

Status
Galena Rock Cress - Arabis Rigidissima V. Demote
By:

No reported data for this Indicator

(a) Number of LTBMU subpopulations where Galena Creek rockcress plant counts were absent, increased, misidentified, stable, or unverified as of 2014. (b)-(d) Census counts for the three verified subpopulations of Galena Creek rockcress. Source: U.S. Forest Service-LTBMU.
2019 Evaluation
See how thresholds are evaluated
Status
Considerably Worse Than Target
Trend
Little or No Change
Confidence
Not available
Applicable Standard
VP22: Maintain a minimum of 7 Arabis rigidissima v. demote population sites.
Key Points
  • This species has not been monitored since 2014. There are no known disturbances that have impacted this species so the status is estimated to have remained the same. 
  • In 2015, Galena creek rockcress was the lone sensitive plant species not in attainment. However, USDA Forest Service botanists questioned the identification of the desired number of plant populations as ever actually being accurately observed in the Region.
About the Threshold
Galena Creek rockcress (Boechera rigidissima var. demote formerly known as Arabis rigidissima var demota) is a slender perennial plant in the Brassicaceae (mustard) family. The species occurs on sandy to rocky soils or on outcrops derived from granitic or volcanic materials, mostly on moderate to steep terrain with northerly aspects. It often occurs in drainage ways, near meadow edges, or in other moisture accumulating microsites, generally in openings in upper montane coniferous forest (Abies-Pinus) and aspen (Populus tremuloides) associations (Nevada Natural Heritage Program 2015a, CNPS Rare Plant Program 2016). It is difficult to identify in the field, and often forms hybrids with Elko rockcress (Boechera elkoensis = Arabis platysperma var. platysperma) (McKnight and Rowe 2015). Characteristics for positive identification include auriculate stem leaves, proximally pubescent stems, glabrous pedicels and fruits, narrow fruits (2.5 to 3.5 millimetres) that are erect but not appressed to rachis and basal leaves with branched hairs (2 to 5 rays) (Morefield 2001, McKnight and Rowe 2015). The taxon is classified under Boechera rigidissma in the Jepson Manual and Flora of North America (Al-Shehbaz and Windham 2003, Baldwin et al. 2012), but recent genetic work indicates var. demota is a distinct species of Boechera (McKnight and Rowe 2015). Galena Creek rockcress was first recommended for inclusion as a TRPA identified sensitive plant species in the 2001 Threshold Evaluation Report, based on the fact that it was identified as a focal species in the Lake Tahoe Watershed Assessment, and the U.S. Forest Service had listed it as a species of concern (Schlesinger and Holst 2000, TRPA 2001). However, TRPA did not evaluate the species in the 2006 Threshold Evaluation Report, citing concerns over the validity of the species and a lack of information (TRPA 2007). Galena Creek rockcress has a global rank of G3T3Q (vulnerable but has taxonomic questions), a state rank of S1 (critically imperilled), a California Native Plant Society Rare Plant Rank of 1B.2 (rare, threatened or endangered in California and elsewhere; fairly endangered in California), and is on the at-risk list of the Nevada Natural Heritage Program (Nevada Natural Heritage Program 2015, CNPS Rare Plant Program 2016). The species is restricted to Washoe County in Nevada and Placer and Nevada counties in California, with 41 element occurrences reported (Nevada Natural Heritage Program 2015) (seven element occurrences reported by CNPS Rare Plant Program), and an estimated 10,000 individuals are known from private, state and Forest Service land (McKnight and Rowe 2015). Taxonomic confusion and difficult identification have led to misidentification of many occurrences of Galena Creek rockcress (see above figure, part a), and fluctuations in the number of populations reported (McKnight and Rowe 2015). At present there are two populations with three subpopulations of Galena Creek rockcress verified in the Region (McKnight and Rowe 2015). Thus the species is likely more threatened in the Region than originally thought, and the current threshold standard of seven populations is likely not attainable.
The primary threat to the species are recreational activities that might trample or uproot plants (e.g., camping, hiking, equestrian use, trail construction, snowmobiles) (McKnight and Rowe 2015). Other direct human threats include forest management such as road construction and maintenance, logging, fire suppression, and fuel reduction treatments (Morefield 2003, CNPS Rare Plant Program 2016). The small population sizes that are typical (e.g. all confirmed LTBMU populations are less than 150 individual plants) make this species susceptible to catastrophic loss from stochastic events. As with other high elevation species, changes in precipitation type, timing, and quantity associated with climate change may adversely affect the species by altering plant community composition and species interactions, and/or decoupling plant flowering periods and insect pollinator visitation.
Delivering and Measuring Success

No related projects or programs defined for this indicator.

Rationale Details
Considerably worse than target. Two populations, with three subpopulations, of Galena Creek rockcress have been confirmed in the Region as of 2014. Three potential subpopulation sites remained where identification needed to be confirmed in 2015. Eight subpopulations were determined to be misidentified and two additional sites were likely misidentified given their location. At a minimum there are two known populations with three subpopulations of Galena Creek rockcress in the Tahoe Region. If all three of the remaining subpopulation sites are confirmed to be Galena Creek rockcress there are three populations with six subpopulations in the Region. Either way, the current status of Galena Creek rockcress was determined to be considerably worse than target.

Consideration should be given to the establishment of permanent, long-term monitoring plots for at least two, and three populations if present, to collect quantitative data on trend and drivers for Galena Creek rockcress. Protocols established and in place for monitoring long-petaled lewisia, Tahoe draba and Cup Lake draba could be followed, which will provide information on basic population trends (density), population demographic structure, climate change impacts, and associated community and habitat. Recording habitat information such as groundcover composition, associated species, slope, aspect, elevation, soil type, and any existing threats (e.g. recreation activities, canopy closure) for all known subpopulations (if not already available) would be beneficial.
Insufficient data to determine trend. Two of the three verified subpopulations of Galena Creek rockcress had recorded population increases between 2011 and 2014 and the third (and largest) population was stable. Of the three unverified subpopulations, one decreased in size between 2009 and 2014, one possibly increased between 2009 and 2011 but had not been revisited since, and one increased between 2011 and 2012. The trend determination of “insufficient data to determine” is based on the issues related to population verification. Based on the confirmed population the trend determination would be “little or no change.”
Confidence Details
Moderate. There is high confidence in the status of Galena Creek rockcress since nearly all known subpopulations have recently been revisited to confirm identification. However, three additional subpopulations require verification.
Low. There is low confidence in the trend since reporting data is available only from 2011 for the three verified subpopulations, and for only two sample periods for the remaining three subpopulations that need identification verification.
Low. Overall confidence takes the lower of the two confidence determinations.
Additional Figures and Resources

No photos available.


No documents available.