Kalmiopsis fragrans

Meinke & Kaye

North Umpqua Kalmiopsis

G2Imperiled Found in 5 roadless areas NatureServe Explorer →
G2ImperiledGlobal Rank
High - mediumThreat Impact
Identity
Unique IDELEMENT_GLOBAL.2.151001
Element CodePDERI0L020
Record TypeSPECIES
ClassificationSpecies
Classification StatusStandard
Name CategoryVascular Plant
Endemicendemic to a single state or province
KingdomPlantae
PhylumAnthophyta
ClassDicotyledoneae
OrderEricales
FamilyEricaceae
GenusKalmiopsis
Other Common Names
Fragrant Kalmiopsis (EN) North Umpqua kalmiopsis (EN) Umpqua Kalmiopsis (EN)
Concept Reference
Meinke, R. J. and T. N. Kaye. 2007. Kalmiopsis fragrans (Ericaceae), a new distylous species from the southern Cascade mountains of Oregon. Journal of the Botanical Research Institute of Texas 1(1): 9-19.
Taxonomic Comments
Newly published in 2007 (Meinke and Kaye 2007). This material had previously been considered to be part of Kalmiopsis leachiana; Kalmiopsis fragrans now refers to northern populations (Douglas County, OR), while Kalmiopsis leachiana is retained for the southern populations (Curry and Josephine counties, OR). The genus Kalmiopsis, consisting of only these two species, is endemic to Oregon.
Conservation Status
Rank Method Rank calculation - Biotics v2
Review Date2024-06-05
Change Date2013-04-02
Edition Date2024-06-05
Edition AuthorsVrilakas, Sue (1999), rev. K. Gravuer (2010), rev. Lindsey Wise (2012), rev. J. Johnson (2024)
Threat ImpactHigh - medium
Range Extent250-1000 square km (about 100-400 square miles)
Number of Occurrences6 - 20
Rank Reasons
Kalmiopsis fragrans is endemic to a narrow band of rocky habitat along the west slope of the southern Cascade Mountains within the North Umpqua River watershed in Douglas County, southwestern Oregon, USA. The number of known populations has increased since this species was first ranked (2010), and those populations appear to be stable. However, reproduction seems to be primarily vegetative, and only one seedling has ever been seen in the wild. Threats appear to be moderate, but high-intensity fires or logging activities could put populations at risk. The potential impact of herbivory is not yet well understood.
Range Extent Comments
Kalmiopsis fragrans is endemic to a narrow band of rocky habitat along the west slope of the southern Cascade Mountains within the North Umpqua River watershed in Douglas County, southwestern Oregon, USA (Meinke and Kaye 2007). Range extent was estimated using herbarium specimens, photo-based observations, and NatureServe Network occurrence data collected between 1993 and 2024 (iNaturalist 2024, NatureServe 2024, OBIC 2024, OSU 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 twelve occurrences range-wide (iNaturalist 2024, NatureServe 2024, OBIC 2024, OSU 2024, SEINet 2024).
Threat Impact Comments
The rocky and often steep nature of K. fragrans occurrences, its USFS Sensitive status, and co-occurring federally-managed peregrine falcon nests all afford the species some degree of protection from direct impacts. However, logging and road building adjacent to occurrences may alter habitat conditions. Habitat disturbance that results in reduced soil moisture and increased sunlight has been observed to cause population decline (Meinke and Kaye 2007). A study of the recovery of two K. fragrans sites from fire (Amsberry et al. 2007) showed that, although fire significantly reduced the standing cover of K. fragrans plants, a portion of the plants within each of the burned populations survived, resprouted, and grew slightly faster than those at the unburned site. Plants at the burned sites also flowered more profusely than those at the unburned site; the sporadic creation of canopy openings by fire (or other disturbance) may be a critical process facilitating sexual reproduction in this species (Amsberry et al. 2007). Herbivory, presumably by deer, impacted significant numbers of plants at one of the sites monitored by Amsberry et al. (2007). Wild collection does not appear to be a significant threat. K. fragrans is relatively easily grown from seed and commercially-grown plants are available in the horticultural trade (Meinke and Kaye 2007). This species is considered moderately vulnerable to climate change (OBIC 2024).
Ecology & Habitat

Description

Perennial, evergreen, multi-stemmed shrub that may be erect or trailing/matted. Stems have peeling reddish-gray bark. Leaves are oval to egg-shaped, dark green and shiny with golden crystalline glands on their undersides. There are 4-7 flowers per stem; flowers are reddish-purple to bright pink, fragrant, relatively large (16-28 mm), urn or bell-shaped (lacking a defined throat) to nearly flat as the petal lobes bend back. 10 stamens protrude conspicuously from each fully-open flower and have dense yellow hairs at their bases. Fruits are dry capsules that split open to release many tiny seeds. Flowers April to June and disperses seeds later in the summer (Amsberry et al. 2007, Oregon Flora Project 2007).

Diagnostic Characteristics

Kalmiopsis fragrans differs most apparently from K. leachiana in its flowers (Meinke and Kaye 2007). In this respect, K. fragrans can be distinguished from K. leachiana by its (1) glandular-hairy flower pedicels (vs. flower pedicels not glandular-hairy), (2) larger corolla (16-28(-33) mm across vs. (12-)14-20 mm across), (3) petal sinuses deeply cleft, to within 2-3 mm of the floral tube (vs. moderately cleft, to within 4-7 mm of the floral tube), (4) corolla with a poorly-defined tube, becoming nearly flat and rotate as petal lobes reflex (vs. corolla with a more well-defined tube, petals reflexing but floral tubes remaining tubular-campanulate), (5) longer stamens (7-13 mm in long-styled morph vs. 3-7(-9) mm in long-styled morph), (6) larger anthers (1.2-3.0 mm long vs. 0.7-1.8 mm long), (7) flowers with yellowish cilia densely tufted at base of filaments surrounding ovary, evident in floral tube (tube area rarely subglabrous) (vs. flowers completely glabrous, or occasionally with fine cilia lining basal interior of floral tube, but not tufted or attached to filaments), and (8) flowers with spicy-sweet azalea-like scent, with nectar merely a trace or typically absent (vs. flowers lacking a pronounced odor, with nectar pooling in floral tube). K. fragrans also differs prominently from K. leachiana in its (9) erect to trailing or matted habit (vs. usually erect habit) and (10) stem length to 12 dm and rarely up to 30 dm (vs. 2-4 dm, rarely up to 8 dm). Less conspicuously, K. fragrans can be distinguished from K. leachiana by its (10) inflorescences usually with 4-8 flowers, sometimes as few as 2 or as many as 12 (vs. inflorescences usually with 7-12 flowers, sometimes as few as 5 or as many as 15), (11) petals sculpted with ridges connected within petals (vs. ridges connected between petals), (12) light pink or reddish-purple corolla (vs. rose to deep pink corolla), (13) style 11-15 mm long in long-styled morph (vs. style 7-10 mm long in long-styled morph), (14) anthers narrowly oblong or curved linear, the pore ± round, < 0.4 mm (vs. anthers oblong, the pore flared, 0.5-0.9 mm), (15) ovary pale yellow to gold (vs. greenish gold), and (16) clearly protogynous breeding system, with pollen shed from a few hours to a day after corolla expansion (vs. slightly protandrous to slightly protogynous breeding system, with pollen shed about the time of corolla expansion). The species also differ in habitat and geographic distribution (Meinke and Kaye 2007, Oregon Flora Project 2007, Flora of North America Editorial Committee 2009). Populations typically flower from mid-April to early June, depending on elevation. Seed production and dispersal occurs into August.

Habitat

Kalmiopsis fragrans usually grows on or closely adjacent to rock outcrops, steep rocky talus slopes, boulder piles, or large pillars from 400-1325 m; it can grow on nearly bare rock, in crevices, or on shallow soil. The rock type at occupied sites tends to be silicified tuff, an altered andesite substrate with a poorly developed soil layer. Sites often have south-facing aspects and can be deeply shaded to partially open. These rocky sites are found within cool, mesic mixed conifer forests dominated by Pseudotsuga menziesii, Pinus lambertiana, Abies grandis, Tsuga heterophylla, Calocedrus decurrens, and/or Thuja plicata, and often including some Arbutus menziesii. Understory associates include Mahonia nervosa, Holodiscus discolor, Gaultheria shallon, Oxalis oregana, Whipplea modesta, Chrysolepis chrysophylla, Polystichum munitum, Linnaea borealis, Rosa gymnocarpa, Pterospora andromedea, Pleuricospora fimbriolata, Allotropa virgata, Rhododendron macrophyllum, Acer circinatum, Toxicodendron diversilobum, Goodyera oblongifolia, Thermopsis montana, Iris chrysophylla, Pyrola picta, Sanicula graveolens, Viola orbiculata, Calypso bulbosa, Erythronium citrinum, and Luzula campestris (NatureServe 2024, OSU 2024).

Ecology

Flowering tends to occur most profusely in sites with consistent, filtered light. Populations also occur within more densely shaded conditions (e.g., within shallow caves or overhangs while growing from high rock ceilings or along deeply sheltered cliffs); these populations can persist for years, but seldom if ever produce flowers or seed. Habitat disturbance that results in reduced soil moisture and increased sunlight (e.g., clear cutting) has been observed to cause population decline, including increased anthocyanic pigmentation, greater disease susceptibility, and higher mortality; these effects are most pronounced in populations from deeper forests (Meinke and Kaye 2007).

Reproduction

Kalmiopsis fragrans flowers are distylous - i.e., each plant has one of two different reproductive morphologies: longer styles/shorter stamens or longer stamens/shorter styles. In other plants, such morphologies are believed to have evolved to ensure a high rate of outcrossing; however, whether this is true for K. fragrans is still somewhat unclear (Meinke and Kaye 2007). Beyond K. fragrans and K. leachiana, distyly is otherwise unknown in the Ericaceae. Kalmiopsis fragrans floral morphology is not typical of heterostylous species (which tend to have strongly tubular, campanulate, or funnelform corollas), and the degree to which it possesses other primary traits that define heterostyly (e.g., diallelic self-incompatibility) requires further evaluation (Meinke and Kaye 2007). Field observations of pollinators indicate that the different floral morphs may facilitate outcrossing, and a controlled pollination study found that intermorph pollinations produced the greatest number of seeds, followed by intramorph pollinations and self-pollinations. However, the intramorph pollinations still produced a significant number of apparently viable seeds (statistically greater than the self-pollinations), suggesting that the degree to which heterostyly ensures outcrossing in K. fragrans may be limited. Research on this issue is ongoing (Meinke and Kaye 2007).
Terrestrial Habitats
Forest/WoodlandForest - ConiferForest - MixedBare rock/talus/scree
Other Nations (1)
United StatesN2
ProvinceRankNative
OregonS2Yes
Threat Assessments
ThreatScopeSeverityTiming
5 - Biological resource useLarge - restrictedModerate or 11-30% pop. declineModerate (short-term)
5.3 - Logging & wood harvestingLarge - restrictedModerate or 11-30% pop. declineModerate (short-term)
7 - Natural system modificationsLarge (31-70%)Moderate or 11-30% pop. declineHigh (continuing)
7.1 - Fire & fire suppressionLarge (31-70%)Moderate or 11-30% pop. declineHigh (continuing)
8 - Invasive & other problematic species, genes & diseasesPervasive (71-100%)Moderate - slightHigh (continuing)
8.2 - Problematic native species/diseasesPervasive (71-100%)Moderate - slightHigh (continuing)

Plant Characteristics
DurationPERENNIAL, Long-lived
Economic Value (Genus)No
Roadless Areas (5)
Oregon (5)
AreaForestAcres
Calf - Copeland CreekUmpqua National Forest15,696
Cougar BluffUmpqua National Forest5,574
FairviewUmpqua National Forest7,417
Limpy RockUmpqua National Forest6,782
Williams CreekUmpqua National Forest5,844
References (10)
  1. Amsberry, K., K. Mitchell, L. Martin, and R. Meinke. 2007. Evaluating population viability and the effects of fire on <i>Kalmiopsis fragrans</i>. Oregon Department of Agriculture Native Plant Conservation Program for U.S. Forest Service, Umpqua National Forest (No. 04-CS-11061500-015, Mod. No. 2, Study Year 3 ). 18 October 2007. Online. Available: (Accessed 2010).
  2. Flora of North America Editorial Committee (FNA). 2009. Flora of North America north of Mexico. Vol. 8. Magnoliophyta: Paeoniaceae to Ericaceae. Oxford University Press, New York. xxiv + 585 pp.
  3. iNaturalist. 2024. Online. Available: https://www.inaturalist.org (accessed 2024).
  4. Meinke, R.J. 1982. Threatened and Endangered Vascular Plants of Oregon: An Illustrated Guide. U.S. Fish and Wildlife Service, Region 1, Portland, Oregon. 326 pp.
  5. Meinke, R. J. and T. N. Kaye. 2007. <i>Kalmiopsis fragrans</i> (Ericaceae), a new distylous species from the southern Cascade mountains of Oregon. Journal of the Botanical Research Institute of Texas 1(1): 9-19.
  6. NatureServe. 2024. NatureServe Network Biodiversity Location Data. NatureServe, Arlington, Virginia.
  7. Oregon Biodiversity Information Center (OBIC). 2024. Biodiversity Tracking and Conservation System (Biotics 5). Oregon Biodiversity Information Center, Institute for Natural Resources, Portland State University, Portland, Oregon.
  8. Oregon Flora Project. 2007 last update. Rare Plant Guide. Online. Available: http://www.oregonflora.org/rareplants/index.php (Accessed 2008).
  9. Oregon State University (OSU). 2024. Oregon Flora website. Oregon State University Herbarium at Oregon State University. Online. Available: https://oregonflora.org/ (accessed 2024).
  10. Southwest Environmental Information Network (SEINet). 2024. Collections Databases. Online. Available: https://swbiodiversity.org/seinet/collections/index.php (accessed 2024).