Plant Assessment Form
More Arctotheca calendula resources
Arctotheca calendula
Synonyms: Arctotheca calendulacea (R. Br.) Lewin, Arctotis calendula L.; Cryptostemma calendulaceum (L.) R.Br
Common Names: fertile capeweed
Evaluated on: 12/9/04
List committee review date: 11/02/2005
Re-evaluation date:
Evaluator(s)
California Dept. of Food and Agriculture
20235 Charlanne Dr., Redding, CA. 96002
530-224-2425, fax 530-224-2427
efinley@cdfa.ca.gov
List committee members
Carla BossardJohn Randall
Cynthia Roye
Jake Sigg
Peter Warner
General Comments
Two forms of capeweed occur in California, a fertile seed producing form with limited distrubtion in the state and a sterile form available from nurserys. The fertile form is currently A-rated by CDFA, but the sterile form is not rated. The fertile form was first intercepted as a contaminant of Australian subterranean clover seed in 1974 and the first established infestation was reported in 1988 on a dairy in Humboldt County (Barbe, Doug. 1988. CDFA Pest Detection Advisory, PD33-88). This assessment will address the fertile form.
Removed second scientific name, Arctotheca calendula (without fertile form), 3/28/17. Ramona Robison
Table 2. Criteria, Section, and Overall Scores
Overall Score?
Moderate
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Alert Status?
Alert
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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 | B. Moderate | Reviewed Scientific Publication | |
1.3 | ?Impact on higher trophic levels | D. Negligible | Reviewed Scientific Publication | |
1.4 | ?Impact on genetic integrity | D. None | Reviewed Scientific Publication | |
2.1 | ?Role of anthropogenic and natural disturbance in establishment | C. Minor | Reviewed Scientific Publication | |
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 | Other Published Material | |
2.4 |
?Innate reproductive potential (see Worksheet A) |
A. High | Other Published Material | |
2.5 | ?Potential for human-caused dispersal | A. High | Reviewed Scientific Publication | |
2.6 | ? Potential for natural long-distance dispersal | D. None | Observational | |
2.7 | ?Other regions invaded | C. Already invaded | Reviewed Scientific Publication | |
3.1 |
?Ecological amplitude/Range (see Worksheet C) |
B. Moderate | Reviewed Scientific Publication | |
3.2 |
?Distribution/Peak frequency (see Worksheet C) |
D. Very 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? | C Reviewed Scientific Publication |
Identify ecosystem processes impacted: Capeweed probably impacts soil moisture and nutrient avilability. Capeweed infestations in agriculture may attain percent plant cover ratios approaching 100%. Such a dominance would likely affect soil moisture and nutrient availablity to the detrement of other species, but capeweed does not seem to compete well in wildland situations, thus it would normally pose only a minor alteration of these ecosystem processes. Sources of information: McIvor, J.G.; Smith D.F. 1973. Competitive growth of capeweed, Arctotheca calendula, and some annual pasture species. Australian Journal of ExperimentalAgriculture & Animal Husbandry. 13(61): 185-189. |
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Question 1.2 Impact on plant community composition, structure, and interactions? |
B Reviewed Scientific Publication |
Identify type of impact or alteration: Capeweed seems to be a relatively poor competitor with native species, but if established may pose a moderate impact on native plant communities. Capeweed has the potential to invade disturbed areas (bare ground) and establish nearly pure stands, thereby excluding native plants from re-colonizing such areas and possibly expanding into surrounding plant communities. Again, capeweed seems to be a relatively poor competitor, thus posing a moderate threat. Sources of information: McIvor, J.G.; Smith D.F. 1973. Competitive growth of capeweed, Arctotheca calendula, and some annual pasture species. Australian Journal of ExperimentalAgriculture & Animal Husbandry. 13(61): 185-189 |
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Question 1.3 Impact on higher trophic levels? | D Reviewed Scientific Publication |
Identify type of impact or alteration: Fertile capeweed probably would have little effect on higher trophic levels. Since fertile capeweed is distributed mainly in agricultural situations, its impact on higher trophic levels would be negligible. Though not preferred, stock may feed on fertile capeweed. Sources of information: Anonymous. Capeweed Arctotheca calendula. Http://weeds.tassie.net.au//txts/capeweed.html. accessed on 8/16/1999 |
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Question 1.4 Impact on genetic integrity? | D Reviewed Scientific Publication |
There are no reports of fertile capeweed hybridization in California. There are no native species of Arctotheca in California. Sources of information: Hickman, James C., ed. 1993. The Jepson Manual Higher Plants of California. University of California Press, Berkeley and Los Angeles, California |
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Section 2: Invasiveness | |
Question 2.1 Role of anthropogenic and natural disturbance in establishment? |
B Reviewed Scientific Publication |
Describe role of disturbance: It appears that fertile capeweed needs anthropogenic disturbance to establish. Distributions of fertile capeweed are generally in agricultural situations, particularly swards, pastures, and vineyards. There is very little spread into wildland situations without some disturbance, typically caused by agricultural practices (cultivation and transportation of stock fodder) or actual planting of specimens. Sources of information: Wood, Helen. 1994. The Introduction and spread of Capeweed, Arctotheca calendula, (l.) Levyns (Asteraceae) in Australia. Plant Protection Quarterly. 9(3): 94-100. |
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Question 2.2 Local rate of spread with no management? | B Reviewed Scientific Publication |
Describe rate of spread: Fertile capeweed is still only locally distributed in California and has increased its population very slowly, if at all. In Australia, capeweed seems to have the potential for further spread, but apparently in agriculture. In limited disjunct California populations of fertile capeweed, there is little indication of spread ito wildland situation. In Australia, capeweed is still spreading in agriculture. Sources of information: Wood, Helen. 1994. The Introduction and spread of Capeweed, Arctotheca calendula, (l.) Levyns (Asteraceae) in Australia. Plant Protection Quarterly. 9(3): 94-100. |
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Question 2.3 Recent trend in total area infested within state? | C Other Published Material |
Describe trend: Disjunct California populations do not seem to be spreading and are declining only with repeated treatments (hand removal or herbicidal). Very small populations in the GGNRAand Point Reyes National Seashore have been eradicated by hand removal. Herbicidal treatments on the larger populations at a dairy in Humboldt County and a vineyard in Monterey County have had only limited success. Sources of information: Barbe, Doug. 1990. CDFA, Division of Plant Industry, Pest Detection Advisory, PD30-90. |
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Question 2.4 Innate reproductive potential? | A Other Published Material |
Describe key reproductive characteristics: Hickman, James C., ed. 1993. The Jepson Manual Higher Plants of California. University of California Press, Berkeley and Los Angeles, California Sources of information: Fertile capeweed may disperse via contaminated seed, hay, fodder, sheep wool, horses, and through direct movement by humans. Fertile capeweed was originally introduced into California via contaminated alfalfa seed, and in Australia by practically all of the above mentioned routes. |
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Question 2.5 Potential for human-caused dispersal? | A Reviewed Scientific Publication |
Identify dispersal mechanisms: Fertile capeweed may disperse via contaminated seed, hay, fodder, sheep wool, horses, and through direct movement by humans. Fertile capeweed was originally introduced into California via contaminated alfalfa seed, and in Australia by practically all of the above mentioned routes. Sources of information: Wood, Helen. 1994. The Introduction and spread of Capeweed, Arctotheca calendula, (l.) Levyns (Asteraceae) in Australia. Plant Protection Quarterly. 9(3): 94-100. |
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Question 2.6 Potential for natural long-distance dispersal? | D Observational |
Identify dispersal mechanisms: It appears that California infestations of fertile capeweed have not spread more than 1 km. The California fertile capeweed populations have been relatively stable. Human-caused dispersal seems to be the primary means of spread. There may be some movement of seed, which is covered by dense wooly hairs, by animals, wind, or water, but so far this is limited. Sources of information: Finley, Ed. 2004. Personal observations of fertile capeweed on a Humboldt County dairy, 2001 to present. 530-224-2425 efinley@cdfa.ca.gov |
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Question 2.7 Other regions invaded? | C Reviewed Scientific Publication |
Identify other regions: Fertile capeweed is an invasive species in agricultural regions in Australia. Fertile capeweed is a pest in swards of Australia, presumably equivelant to coastal praire and scrub ecological types converted to agriculture in California. Sources of information: Wood, Helen. 1994. The Introduction and spread of Capeweed, Arctotheca calendula, (l.) Levyns (Asteraceae) in Australia. Plant Protection Quarterly. 9(3): 94-100. |
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Section 3: Distribution | |
Question 3.1 Ecological amplitude/Range? | B Reviewed Scientific Publication |
It appears that fertile capeweed is capable of moderate tendency to invade different ecological types. In California, fertile capeweed has a distribution so far limited to coastal praire (Humboldt County) and costal scrub (Monterey County). In Australia, it has invaded agricultural areas and is most successful in regions with climates similar to its range in South Africa. Sources of information: Wood, Helen. 1994. The Introduction and spread of Capeweed, Arctotheca calendula, (l.) Levyns (Asteraceae) in Australia. Plant Protection Quarterly. 9(3): 94-100. |
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Question 3.2 Distribution/Peak frequency? | D Other Published Material |
Describe distribution: Fertile capeweed has not dominated any of the ecological types in which it occurs. So far, fertile capeweed is limited to two ecological types in California and it has not achieved dominance in either. Sources of information: Barbe, Doug. 1988. CDFA, Division of Plant Industry, Pest Detection Advisory, PD33-88. |
Worksheet A - Innate reproductive potential
Reaches reproductive maturity in 2 years or less | Yes |
Dense infestations produce >1,000 viable seed per square meter | Yes |
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 | 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 | Yes |
Resprouts readily when cut, grazed, or burned | Yes |
Total points: | 8 |
Total unknowns: | 3 |
Total score: | A? |
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? |
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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 | ||
Grasslands, Vernal Pools, Meadows, and other Herb Communities | coastal prairie | D, < 5% |
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): | B | |
Distribution (highest score): | D |
Infested Jepson Regions
Click here for a map of Jepson regions
- Central West
- Great Valley
- Northwest
- Sierra Nevada
- Southwest