Plant Assessment Form
More Crocosmia x crocosmiiflora resources
Crocosmia x crocosmiiflora
Synonyms: derived from C. pottsii X C. aurea; Tritonia X crocosmiiflora
Common Names: montbretia
Evaluated on: 8/25/04
List committee review date: 25/10/2017
Re-evaluation date:
Evaluator(s)
California Department of Parks and Recreation, Mendocino District
P. O. Box 603, Little River, CA 95456-0603
707/937-9172; 707/937-2278
pwarner@mcn.org
List committee members
Alison StantonJake Sigg
Cynthia Roye
John Randall
Joe DiTomaso
Peter Warner
General Comments
No general comments for this species
Table 2. Criteria, Section, and Overall Scores
Overall Score?
Limited
|
Alert Status?
No Alert
|
Documentation?
3 out of 5
|
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Score | Documentation | |||
1.1 | ?Impact on abiotic ecosystem processes | U. Unknown | Reviewed Scientific Publication | |
1.2 | ?Impact on plant community | C. Minor | Other Published Material | |
1.3 | ?Impact on higher trophic levels | C. Minor | Observational | |
1.4 | ?Impact on genetic integrity | D. None | Other Published Material | |
2.1 | ?Role of anthropogenic and natural disturbance in establishment | B. Moderate | Other Published Material | |
2.2 | ?Local rate of spread with no management | A. Increases rapidly | Observational | |
2.3 | ?Recent trend in total area infested within state | B. Increasing less rapidly | Other Published Material | |
2.4 |
?Innate reproductive potential (see Worksheet A) |
B. Moderate | Other Published Material | |
2.5 | ?Potential for human-caused dispersal | A. High | Other Published Material | |
2.6 | ? Potential for natural long-distance dispersal | C. Rare | Other Published Material | |
2.7 | ?Other regions invaded | B. Invades 1 or 2 ecological types | Other Published Material | |
3.1 |
?Ecological amplitude/Range (see Worksheet C) |
A. Widespread | Other Published Material | |
3.2 |
?Distribution/Peak frequency (see Worksheet C) |
C. Low | Other Published Material |
Table 3. Documentation
Scores are explained in the "Criteria for Categorizing Invasive Non-Native Plants that Threaten Wildlands".
Section 1: Impact | |
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Question 1.1 Impact on abiotic ecosystem processes? | U Reviewed Scientific Publication |
Identify ecosystem processes impacted: None known. No literature on ecological impacts has been located. Sources of information: None |
|
Question 1.2 Impact on plant community composition, structure, and interactions? |
C Other Published Material |
Identify type of impact or alteration: Sources of information: Nursery and Garden Industry Austraila @ http://www.ngia.com.au/np/2000No12/00-12.html |
|
Question 1.3 Impact on higher trophic levels? | C Observational |
Identify type of impact or alteration: None known; flowers are likely attractive to hummingbirds and perhaps butterflies. Observed displacing native Rubus species, a native food source for wildlife. No information in scientific literature; personal observation and web posting of hummingbird activity Sources of information: Warner, PJ. 2004. Personal observations, San Mateo, San Francisco, Marin, Sonoma, Mendocino Counties, 1999-2004. pwarner@mcn.org; 707/937-9172. |
|
Question 1.4 Impact on genetic integrity? | D Other Published Material |
None known; unlikely since no congeners exist in native California flora. Inferred from general knowledge of genetics and evolution. Sources of information: Hickman, JC. 1993. The Jepson Manual: Higher Plants of California. University of California Press, Berkeley, CA. p. 1152. |
|
Section 2: Invasiveness | |
Question 2.1 Role of anthropogenic and natural disturbance in establishment? |
A Observational |
Describe role of disturbance: Crocosmia is a widely cultivated garden plant, so does well with soil disturbance; often found in areas disturbed by human activities; horticulturalists cite the need to thin stands about every 3 years for maximum garden performance (flowering); also observed off trails, especially in damp forests and woodlands. From web-posted horticultural requirements, somewhat dependent upon disturbance of soil. However, montbretia is also capable of spreading without human intervention (personal observation). Sources of information: The Garden of Paghat the Ratgirl @ www.paghat.com/crocosmia2.html; |
|
Question 2.2 Local rate of spread with no management? | A Observational |
Describe rate of spread: Observed to spread slowly at first, then more rapidly, within a single patch. Can also spread to adjacent areas through seed or cormlet dispersal. My observations suggest that once a new plant is established, it will expand rapidly to occupy more space. Once flowering is initiated, seeds can spread plants to nearby unoccupied sites (within several meters). Sources of information: The Garden of Paghat the Ratgirl @ www.paghat.com/crocosmia2.html; |
|
Question 2.3 Recent trend in total area infested within state? | B Other Published Material |
Describe trend: Estimated to be slowly increasing as new plantings and dispersal mechanisms lead to new introductions and establishment. Not known as invasive in interior California _ reports found are all coastal, so some habitats may still be yet to be exploited Sources of information: Redwood National Park @ www.nps.gov/redw/exot2000.doc |
|
Question 2.4 Innate reproductive potential? | B Other Published Material |
Describe key reproductive characteristics: Corms (bud from existing corms); seeds Corms and seeds are both viable reproductive mechanisms. Sources of information: Hickman, JC. 1993. The Jepson Manual: Higher Plants of California. University of California Press, Berkeley, CA. p. 1152. |
|
Question 2.5 Potential for human-caused dispersal? | A Other Published Material |
Identify dispersal mechanisms: Sold commercially; entire plants, corms, seeds spread as garden waste debris; spreads from horticultural plantings to adjacent areas from corms that bud prolifically; also produces seed that is easily dispersed by water, in soil movement (perhaps by animals or on human footwear) Numerous mechanisms for dispersal, and most based on human activities. Sources of information: The Garden of Paghat the Ratgirl @ www.paghat.com/crocosmia2.html; |
|
Question 2.6 Potential for natural long-distance dispersal? | C Other Published Material |
Identify dispersal mechanisms: Corms and seeds can float; wind dispersal very unlikely; dispersal by animals unknown (seed ingestion by birds?); seeds are viable in warm moist areas Long-distance dispersal mechanisms appear lacking, although the potential for long-distance seed dispersal is unknown. Sources of information: The Plants Database @ http://plantsdatabase.com; |
|
Question 2.7 Other regions invaded? | B Other Published Material |
Identify other regions: Sources of information: The Plants Database @ http://plantsdatabase.com; |
|
Section 3: Distribution | |
Question 3.1 Ecological amplitude/Range? | A Other Published Material |
Occurs in coastal ecological types only in CA; well-established in CA gardens Reports and observations Sources of information: Redwood National Park @ www.nps.gov/redw/exot2000.doc; |
|
Question 3.2 Distribution/Peak frequency? | C Other Published Material |
Describe distribution: Sporadic, may be more extensive than perceived due to vegetative similarity to Iris species Reports and observations Sources of information: Redwood National Park @ www.nps.gov/redw/exot2000.doc; |
Worksheet A - Innate reproductive potential
Reaches reproductive maturity in 2 years or less | Yes |
Dense infestations produce >1,000 viable seed per square meter | No |
Populations of this species produce seeds every year. | Yes |
Seed production sustained over 3 or more months within a population annually | No |
Seeds remain viable in soil for three or more years | Unknown |
Viable seed produced with both self-pollination and cross-pollination | Unknown |
Has quickly spreading vegetative structures (rhizomes, roots, etc.) that may root at nodes | Yes |
Fragments easily and fragments can become established elsewhere | No |
Resprouts readily when cut, grazed, or burned | Yes |
Total points: | 4 |
Total unknowns: | 2 |
Total score: | B? |
Related traits:
Worksheet B - Arizona Ecological Types is not included here
Worksheet C - California Ecological Types
(sensu Holland 1986)Major Ecological Types | Minor Ecological Types | Code? |
---|---|---|
Marine Systems | marine systems | |
Freshwater and Estuarine | lakes, ponds, reservoirs | |
Aquatic Systems | rivers, streams, canals | |
estuaries | ||
Dunes | coastal | |
desert | ||
interior | ||
Scrub and Chaparral | coastal bluff scrub | |
coastal scrub | D, < 5% | |
Sonoran desert scrub | ||
Mojavean desert scrub (incl. Joshua tree woodland) | ||
Great Basin scrub | ||
chenopod scrub | ||
montane dwarf scrub | ||
Upper Sonoran subshrub scrub | ||
chaparral | D, < 5% | |
Grasslands, Vernal Pools, Meadows, and other Herb Communities | coastal prairie | |
valley and foothill grassland | ||
Great Basin grassland | ||
vernal pool | ||
meadow and seep | ||
alkali playa | ||
pebble plain | ||
Bog and Marsh | bog and fen | |
marsh and swamp | ||
Riparian and Bottomland habitat | riparian forest | |
riparian woodland | ||
riparian scrub (incl.desert washes) | ||
Woodland | cismontane woodland | |
piñon and juniper woodland | ||
Sonoran thorn woodland | D, < 5% | |
Forest | broadleaved upland forest | C, 5% - 20% |
North Coast coniferous forest | D, < 5% | |
closed cone coniferous forest | ||
lower montane coniferous forest | ||
upper montane coniferous forest | ||
subalpine coniferous forest | ||
Alpine Habitats | alpine boulder and rock field | |
alpine dwarf scrub | ||
Amplitude (breadth): | B | |
Distribution (highest score): | C |
Infested Jepson Regions
Click here for a map of Jepson regions
- Central West
- Northwest
- Southwest