Plant Assessment Form
More Cakile maritima resources
Cakile maritima
Common Names: European sea rocket
Evaluated on: 5/20/04
List committee review date: 03/12/2017
Re-evaluation date:
Evaluator(s)
Catalina Island Conservancy
P.O. 2739 Avalon, CA 90704
(310) 510-1299
jknapp@catalinaconservancy.org
University of California, Davis
Dept. Plant Sci., Mail Stop 4, Davis, CA 95616
530-754-8715
jmditomaso@ucdavis.edu
List committee members
Jake SiggPeter Warner
Bob Case
John Knapp
Elizabeth Brusati
General Comments
No general comments for this species
Table 2. Criteria, Section, and Overall Scores
Overall Score?
Limited
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Alert Status?
No Alert
|
Documentation?
3.5 out of 5
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Score | Documentation | |||
1.1 | ?Impact on abiotic ecosystem processes | C. Minor | Reviewed Scientific Publication | |
1.2 | ?Impact on plant community | C. Minor | Other Published Material | |
1.3 | ?Impact on higher trophic levels | C. Minor | Other Published Material | |
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 | B. Increases less rapidly | Reviewed Scientific Publication | |
2.3 | ?Recent trend in total area infested within state | C. Stable | Reviewed Scientific Publication | |
2.4 |
?Innate reproductive potential (see Worksheet A) |
B. Moderate | Reviewed Scientific Publication | |
2.5 | ?Potential for human-caused dispersal | C. Low | Reviewed Scientific Publication | |
2.6 | ? Potential for natural long-distance dispersal | A. Frequent | Reviewed Scientific Publication | |
2.7 | ?Other regions invaded | C. Already invaded | Reviewed Scientific Publication | |
3.1 |
?Ecological amplitude/Range (see Worksheet C) |
D. Narrow | Reviewed Scientific Publication | |
3.2 |
?Distribution/Peak frequency (see Worksheet C) |
A. High | 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? | C Reviewed Scientific Publication |
Identify ecosystem processes impacted: C. maritima demonstrates weak allelophy. C. maritima has demonstrated evidence of allelopathic effects in replicated growth chamber experiments; however, the effect was not detected under field experiments. Sources of information: Boyd, R.S. 1993. Replacement of Cakile endentula by C. maritima in the strand habitat of California. American Midland Naturalist, 130(2):209-228. |
|
Question 1.2 Impact on plant community composition, structure, and interactions? |
C Other Published Material |
Identify type of impact or alteration: C. maritima has lead to the reduction, and in some situations the extirpation of Abronia spp. However, in most places its impacts are minor. C. maritima is invasive, with the ability to produce more seed, tolerate disturbance, and disperse greater distances than native Abronia spp. Sources of information: Wood, L. 19??. Dune stabilization. Fremontia, ?(?):27. |
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Question 1.3 Impact on higher trophic levels? | C Other Published Material |
Identify type of impact or alteration: Competes for pollination visitation with native vegetation but this may not impact native species. Although self-compatible, insect pollination plays an intergral part in reproduction. Sources of information: Barbour, M.G. and Rodman, J.E. 1970. Saga of the west coast sea-rockets: Cakile edentula ssp. californica and C. maritima. Rhodora, 72(791):370-386. |
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Question 1.4 Impact on genetic integrity? | D Other Published Material |
No hybridization is known to occur with native California taxa. No related native California taxa in the genus Cakile. Sources of information: Hickman, J.C. (ed.). 1993. The Jepson manual of higher plants of California. Pp. 406. University of California Press, Berkeley. |
|
Section 2: Invasiveness | |
Question 2.1 Role of anthropogenic and natural disturbance in establishment? |
B Reviewed Scientific Publication |
Describe role of disturbance: Establishes quickly on beaches and dunes that are frequently disturbed and have low diversity. Able to colonize beach and dune habitats along coast that are frequently disturbed by surf and wind, and have low biodiversity. Sources of information: Haubensak, K. 1999. Cakile maritima. Channel Islands National Park Sevice Species Literature Review. Unpublished. |
|
Question 2.2 Local rate of spread with no management? | B Reviewed Scientific Publication |
Describe rate of spread: No populations were recorded in the first Catalina Island flora in 1923, but by 1966, C. maritima was widespread throughout the beaches and dunes of the Island, and has a similar distribution and abundance in 2003. If C. maritima can survive into a second or even a third year of reproduction, it can produce an 18-fold difference in seed output. Seed production is increased during colonization, and has a high fecundity. Sources of information: Thorne, R.F. 1967. A Flora of Santa Catalina Island, California. Aliso, 6(3):1-77. |
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Question 2.3 Recent trend in total area infested within state? | C Reviewed Scientific Publication |
Describe trend: Occupies all avaliable habitats along the California and Baja coast. Santa Cruz Island. On Catalina Island, 101,225 square feet are infested. C. maritima has similar xeric region of origin similar to California, with the average temperature at Santa Cruz Island being the optimal for germination. Sources of information: Wood, L. 19XX. Dune stabilization. Fremontia, X(X):27. |
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Question 2.4 Innate reproductive potential? | B Reviewed Scientific Publication |
Describe key reproductive characteristics: Seed bank persists for al least 2 years in foredunes. C. maritima can survive disturbance into a second or even a third year of reproduction, producing an 18-fold difference in seed output. Seed production is increased during colonization, and has a high fecundity. Self pollination is possible. 90% seed set. Classified as an annual species; however, has shown to be biennial. Seeds are readily buried in foredunes, allowing them to escape predation by deer mice (Peromyscus maniculatus), which can remove 95% of seed, causing only 20% seed survivorship. During colonization of disturbed sites of native Abronia maritima, C. maritima will allocate energy to seed production rather than to biomass to survive until the next year leading to a greater level of invasiveness. C. maritima is a faculative annual, germinating in the winter and fruiting in the summer. One seed per fruit segment. Sources of information: Haubensak, K. 1999. Cakile maritima. Channel Islands National Park Sevice Species Literature Review. Unpublished. |
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Question 2.5 Potential for human-caused dispersal? | C Reviewed Scientific Publication |
Identify dispersal mechanisms: Sand transport, ship ballast, and trampling account for human-caused dispersal. The relocation of sand from areas infested with C. maritima to new locales, and trampling by hikers and campers in dunes may allow for plant material to roll (tumble weed effect), thus dispersing seed. Sources of information: Rodman, J.E. 1986. Introduction, establishment and replacement of sea-rockets (Cakile, Cruciferae) in Australia. Journal of Biogeography, 13(2):159-171. |
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Question 2.6 Potential for natural long-distance dispersal? | A Reviewed Scientific Publication |
Identify dispersal mechanisms: Fruits are adapted for both short and long distance dispersal by wind and water respectively. In California, C. maritima dispersed at a rate of 53 km per year. Deer mice act as microdispersal vectors; however, their herbivory has also impacted C. maritima. Fruits are composed of two segments and have superb dispersability- the upper segment detaches and is carried by the sea, allowing for 50% of detached fruits to stay afloat for over 100 days. The lower segment remains attached to the plant until wind events cause the plant to roll along the surface, thus breaking off the fruits break. Deer mice cachet seeds. Sources of information: Haubensak, K. 1999. Cakile maritima. Channel Islands National Park Sevice Species Literature Review. Unpublished. |
|
Question 2.7 Other regions invaded? | C Reviewed Scientific Publication |
Identify other regions: Eastern North America, western and southern Australia, Tasmania, and New Zealand are invaded. Sources of information: Haubensak, K. 1999. Cakile maritima. Channel Islands National Park Sevice Species Literature Review. Unpublished. |
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Section 3: Distribution | |
Question 3.1 Ecological amplitude/Range? | D Reviewed Scientific Publication |
Introduced to California, north of San Francisco in the 1930's. In 1967, Thorne found C. maritima to be well-established, while other botanists found it abundant on Santa Cruz, San Clemente and San Nicolas islands. First recorded on Catalina Island 1966 as well-established on beaches around the Island. Coastal beaches, dunes and sandy stream mouths. Occupies coast line with sandy substrate. On Catalina Island in 2003, 21 populations were recorded and the following are the percentages of habitat infested: beach and dune- 1.4%, and riparian creek mouth-<0.00%. Sources of information: Barbour, M.G. 1970. Seedling ecology of Calike maritima along the California coast. Bulletin of the Torrey Botatnical Club, 97(5):280-289. |
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Question 3.2 Distribution/Peak frequency? | A Other Published Material |
Describe distribution: Very common, but not typically in dense patches. Sources of information: Barbour, M.G. 1970. Seedling ecology of Calike maritima along the California coast. Bulletin of the Torrey Botatnical Club, 97(5):280-289. |
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 | Unknown |
Seeds remain viable in soil for three or more years | Yes |
Viable seed produced with both self-pollination and cross-pollination | Yes |
Has quickly spreading vegetative structures (rhizomes, roots, etc.) that may root at nodes | No |
Fragments easily and fragments can become established elsewhere | No |
Resprouts readily when cut, grazed, or burned | No |
Total points: | 5 |
Total unknowns: | 1 |
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 | A, > 50% |
desert | ||
interior | ||
Scrub and Chaparral | coastal bluff scrub | |
coastal scrub | ||
Sonoran desert scrub | ||
Mojavean desert scrub (incl. Joshua tree woodland) | ||
Great Basin scrub | ||
chenopod scrub | ||
montane dwarf scrub | ||
Upper Sonoran subshrub scrub | ||
chaparral | ||
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 | ||
Forest | broadleaved upland forest | |
North Coast coniferous forest | ||
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): | D | |
Distribution (highest score): | A |
Infested Jepson Regions
Click here for a map of Jepson regions
- Central West
- Northwest
- Southwest
- Sonoran Desert