Boechera fecunda

(Rollins) Dorn

Sapphire Rockcress

G2Imperiled Found in 1 roadless area NatureServe Explorer →
G2ImperiledGlobal Rank
HighThreat Impact
Identity
Unique IDELEMENT_GLOBAL.2.159353
Element CodePDBRA06290
Record TypeSPECIES
ClassificationSpecies
Classification StatusStandard
Name CategoryVascular Plant
Endemicendemic to a single state or province
KingdomPlantae
PhylumAnthophyta
ClassDicotyledoneae
OrderCapparales
FamilyBrassicaceae
GenusBoechera
Synonyms
Arabis fecundaRollins
Other Common Names
Mt. Sapphire rockcress (EN) Mt. Sapphire Rockcress (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.
Taxonomic Comments
Treated by FNA (2010, vol. 7) in the genus Boechera.
Conservation Status
Rank Method Rank calculation - Biotics v2
Review Date2024-12-04
Change Date1988-12-16
Edition Date2024-12-04
Edition AuthorsShelly, J. (1989) ,rev. B. Heidel (1999), rev. Johnson, J. (2024)
Threat ImpactHigh
Range Extent5000-20,000 square km (about 2000-8000 square miles)
Number of Occurrences6 - 20
Rank Reasons
Boechera fecunda is a perennial herb endemic to Montana, USA. It is known from 27 occurrences in a small geographic area. A large part of this species' habitat is threatened by spotted knapweed (Centaurea maculosa), an aggressive, introduced weed.
Range Extent Comments
Boechera fecunda is endemic to Ravalli, Beaverhead, and Silver Bow counties in southwestern Montana. Range extent was estimated using herbarium specimens and NatureServe Network occurrence data collected between 1993 and 2024 (GBIF 2024, NatureServe 2024, SEINet 2024).
Occurrences Comments
By applying a 1 km separation distance to herbarium specimens, photo-based observations, and NatureServe Network occurrence data documented between 1993 and 2024, it is estimated that there are 20 occurrences rangewide (GBIF 2024, iNaturalist 2024, NatureServe 2024, SEINet 2024).
Threat Impact Comments
Several factors may affect the long-term persistence of this species, including exotic weed encroachment, grazing, herbicide application, mining, and conifer encroachment.

The Montana Natural Heritage Program (2024) describes the threats to Boechera fecunda as follows:

Livestock grazing occurs at most sites, although fewer than half are reported to have heavy grazing. Direct herbivory has never been observed and is probably rare, however, soil crusts are beneficial to the species' survivorship at some sites; such crusts are often destroyed by livestock. Livestock can also adversely affect survivorship by trampling plants. Exclosure studies were conducted at two sites near the Big Hole River. At one site, Boechera fecunda increased in one grazing exclosure while decreased in another. Boechera fecunda establishes best when not competing with other species, and grazing may limit competition. It is interesting to note that some of the largest populations (Birch Creek and Jerry Creek) are in areas with the most intensive grazing.

Spotted knapweed (Centaurea maculosa) poses a major threat to populations in Ravalli County, where it has severely invaded this species' habitat. Studies indicate that knapweed reduces the successful establishment of sapphire rockcress seedlings. Most Boechera fecunda sites have severe infestations of spotted knapweed. Research on water use efficiency in this species has shown significant differences between low-elevation populations in the Bitterroot Valley and those at higher sites in Beaverhead County, suggesting that Bitterroot Valley populations, which are most threatened by weed encroachment, may be genetically distinct.

Roads are a major source of weed infestation, and road construction or other major disturbances can introduce or provide avenues for the introduction of weeds. Livestock can also be a significant vector for exotic weed encroachment. Currently, spotted knapweed does not occur at the Beaverhead or Silver Bow County sites, but it does occur in these counties and may become a problem.

Only one sapphire rockcress site is near an active mine, and has not been impacted to date. Other populations are near mining claims or inactive mines that could become active with improved extraction methods or increased demand for the minerals.

A few populations are located where conifer encroachment is expected to reduce habitat quality, and eventually displace existing populations without intervention.
Ecology & Habitat

Description

Sapphire rockcress is a small perennial with one to many unbranched flowering stems reaching up to 30 cm in height, arising from a simple or branched rootcrown. The spoon-shaped or lance-shaped basal leaves are 10-30 mm long and 2-4 mm wide, and have margins that are untoothed or with a few shallow lobes toward the tip; those produced in the fall are usually larger and broader than those produced in the spring. The stem leaves are smaller and clasping at the base. Both stem and leaves are grayish-white with a dense cover of small, branched hairs.

Several to many white or blueish-tinged flowers are borne in an unbranched spike-like inflorescence. Each flower has 4 petals (9-13 mm long and 3-5 mm wide) and densely hairy sepals (6-7 mm long and about 2 mm wide). The flowers are tightly clustered at first, but become farther apart as the fruits develop. The pods are grayish, hairy and 3-5 cm long by 1-2 mm wide; they are held nearly erect when mature and have two narrow chambers with a single row of small seeds in each one.

Diagnostic Characteristics

Distinguished from other ARABIS in Montana by the nearly erect fruits, densely grayish covering of branched hairs on the foliage and fruits, and the two different types of basal leaves.

Habitat

This species occurs in open, rocky, eroding slopes in the foothills and montane zones between lower treeline and shrub/grasslands (Schassberger 1990). Soils are sandy, light-colored, highly calcareous, and derived from metamorphosed calcium silicate parent materials. Sites are usually sparsely vegetated and distinctive in relation to the surrounding area (erosion and a dry, warm microclimate probably help maintain this open habitat). Scattered Pseudotsuga menziesii and Pinus ponderosa are often present. (Lesica 1985)

Ecology

Sapphire rockcress grows in areas of relatively sparse vegetation on steep slopes with periodic natural erosion. Periodic erosion and slumping of steep slope habitat may be partially responsible for maintaining sparse vegetation and reducing competition for light, water and nutrients (Lesica 1993). Many sites would be considered early successional or edaphic disclimaxes, and these conditions may be important for species persistence. At three sites in Ravalli and Beaverhead counties, coverage of rock varied from 2-15%, coverage of bare soil varied from 40-77%, and coverage of basal vegetation varied from 19-48% (Lesica and Shelly 1994). Some slopes support cryptogamic soil crusts that are beneficial to the survival of older, larger plants of sapphire rockcress (Lesica and Shelly 1992). Fire was relatively frequent in many of these areas, but the sparse vegetation on the slopes occupied by this species probably did not carry fire well.

Reproduction

Flowers and fruits mature acropetally. The valves of the siliques open from the tip downward to expose seeds that then drop or are shaken to the ground; however, the fruits are also grazed by small mammals, and it is likely that this also aids in seed dispersal.
Terrestrial Habitats
Shrubland/chaparral
Other Nations (1)
United StatesN2
ProvinceRankNative
MontanaS2Yes
Threat Assessments
ThreatScopeSeverityTiming
2 - Agriculture & aquaculturePervasive (71-100%)Moderate - slightHigh (continuing)
2.3 - Livestock farming & ranchingPervasive (71-100%)Moderate - slightHigh (continuing)
3 - Energy production & miningSmall (1-10%)Moderate - slightModerate - low
3.2 - Mining & quarryingSmall (1-10%)Moderate - slightModerate - low
4 - Transportation & service corridorsRestricted (11-30%)Serious - slightHigh (continuing)
4.1 - Roads & railroadsRestricted (11-30%)Serious - slightHigh (continuing)
7 - Natural system modificationsSmall (1-10%)Moderate - slightModerate (short-term)
8 - Invasive & other problematic species, genes & diseasesLarge (31-70%)Moderate or 11-30% pop. declineHigh (continuing)
8.1 - Invasive non-native/alien species/diseasesLarge (31-70%)Moderate or 11-30% pop. declineHigh (continuing)

Plant Characteristics
DurationPERENNIAL, Short-lived
Economic Value (Genus)No
Roadless Areas (1)
Montana (1)
AreaForestAcres
Stony MountainBitterroot National Forest44,057
References (34)
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