Plant Assessment Form
More Senecio jacobaea resources
Senecio jacobaea
Common Names: tansy ragwort; stinking willie; stavewort; kettle-dock; felonweed; Fairies' horse; tansy butterweed; staggerwort
Evaluated on: 8/10/04
List committee review date: 27/08/2004
Re-evaluation date:
Evaluator(s)
California Invasive Plant Council
1442-A Walnut Street #462, Berkeley, CA 94709
510.843.3902
brichardson@cal-ipc.org
List committee members
Joe DiTomasoAlison Stanton
Peter Warner
John Randall
Jake Sigg
Cynthia Roye
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
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Documentation?
3 out of 5
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Score | Documentation | |||
1.1 | ?Impact on abiotic ecosystem processes | C. Minor | Other Published Material | |
1.2 | ?Impact on plant community | C. Minor | Other Published Material | |
1.3 | ?Impact on higher trophic levels | B. Moderate | Other Published Material | |
1.4 | ?Impact on genetic integrity | C. Minor/Low | Other Published Material | |
2.1 | ?Role of anthropogenic and natural disturbance in establishment | C. Minor | Other Published Material | |
2.2 | ?Local rate of spread with no management | A. Increases rapidly | Other Published Material | |
2.3 | ?Recent trend in total area infested within state | D. Declining | Other Published Material | |
2.4 |
?Innate reproductive potential (see Worksheet A) |
A. High | Other Published Material | |
2.5 | ?Potential for human-caused dispersal | B. Moderate | Other Published Material | |
2.6 | ? Potential for natural long-distance dispersal | B. Occasional | Other Published Material | |
2.7 | ?Other regions invaded | C. Already invaded | 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 | Reviewed Scientific Publication |
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 Other Published Material |
Identify ecosystem processes impacted: Dense infestations can increase soil erosion. May increase productivity among some pasture species. This in turn, may reduce microbial biomass in the soil. Only one source identified the ability of ragwort to increase soil erosion. Microbial biomass decreases appear to be a concern primarily in pastures. Sources of information: Coombs, EM, PB McEvoy, CE Turner. 1999. Tansy ragwort. In: Biology and Management of Noxious Rangeland Weeds. Sheley, RL, JK Petroff (eds.) |
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Question 1.2 Impact on plant community composition, structure, and interactions? |
C Other Published Material |
Identify type of impact or alteration: Can crowd out desireable forage species. Can form dense infestations when disturbance occurs. Pristine plant communities are generally resistant to ragwort infestation. Micro-disturbances in the soil created by rodent burrows and deer tracks can provide sufficient habitat for ragwort to invade and maintain its presence in less disturbed plant communities. Once established, ragwort can compete with grasses and clover. The dead rosette opens a space for germination of the seeds. Ragwort can dominate in highly disturbed plant communities. In OR, populations of the rare Sidalcea hirtipes increased >40% after ragwort biocontrols were released. Ragwort has been shown to inhibit seed germination and seedling emergence and growth of Lolium perenne and several legumes through allelopathy. Legumes were more affected by this. However, ragwort may increase productivity among some pasture species. Ragwort acts as a ruderal, colonizing after disturbance and relatively transient during periods of stability. More competitive at the rosette stage. Most literature focuses on the agricultural impacts of ragwort. Little evidence is available to support the idea that it can significantly threaten native plants. Though, it has impacted them in OR, no data was available for CA. Sources of information: Mitich, LW. 1995. Intriguing world of weeds: Tansy ragwort. Weed Technology. V.9: 402-404.here |
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Question 1.3 Impact on higher trophic levels? | B Other Published Material |
Identify type of impact or alteration: Contains pyrrolizidine alkaloids and is toxic to livestock and deer when grazed in a single large quantity or in small quantities over time. Has cause serious livestock losses in PNW. May be accidentally ingested by animals in the seedling stage. Young livestock is 2-3 times more susceptible to poisoning than older animals. Adult animals must eat 5-7% of their body weight to die. Many animals prefer other forage over tansy ragwort. Numerous insects pollinate it. In OR, ragwort provides an additional nectar source for the threatened Speyeria zerene hippolyta butterfly. May be a poisoning threat to deer. Sources of information: DiTomaso, J., E. Healy. Weeds of California and Other Western States. Not yet published. |
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Question 1.4 Impact on genetic integrity? | C Other Published Material |
No hybrids have been reported from North America. Many native Senecios exist. Does coexist w/native, potential exists, but has not been documented. Possible a pollen swamping situation exists on the Medocino coast with the native, rare S. bolanderi. Sources of information: Bain, JF. 1991. The biology of Canadian weeds. 96. Senecio jacobaea L. Canadian Journal of Plant Science. V.71: 127-140. |
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Section 2: Invasiveness | |
Question 2.1 Role of anthropogenic and natural disturbance in establishment? |
A Other Published Material |
Describe role of disturbance: Open areas result in better seedling establishment. One of the first plants to colonize cut-over forests. Rodent mounding and scratching can create ideal establishment conditions. Most references indicate that disturbance is required for ragwort establishment. Disturbance is required for germination of dormant, buried seeds. All literature notes that establishment requires disturbance. Sources of information: DiTomaso, J., E. Healy. Weeds of California and Other Western States. Not yet published. |
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Question 2.2 Local rate of spread with no management? | A Other Published Material |
Describe rate of spread: In MT, one infestation has "expanded exponentially" since it was first discovered in 1993 (in 1997 it covered 1500 net acres over 150 sq.miles.) Ragwort can dominate an area in less than 10 years if disturbance occurs (ex. overgrazing, logging). Can double in less than 10 years if appropriate habitat is available. Sources of information: Mott, Gary. 1997. Tansy ragwort (Senecio jacobaea) briefing paper. Western Area Weed Council. (This is a memo or email) |
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Question 2.3 Recent trend in total area infested within state? | D Other Published Material |
Describe trend: Populations have been dramatically reduced in CA and OR since the introduction of two biocontrols (Tyria jacobaeae, Longitarsus jacobaeae). Biocontrols have greatly reduced populations of ragwort. Sources of information: DiTomaso, J., E. Healy. Weeds of California and Other Western States. Not yet published. |
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Question 2.4 Innate reproductive potential? | A Other Published Material |
Describe key reproductive characteristics: Annual, biennial, or perennial. Behaves as a short-lived perennial when mowed, grazed or injured. Develops many spreading lateral roots, which can send up new shoots in response to injury; and which can produce new shoots if fragmented. Flowers July-September. Each shoot produces 20-60 flower heads with numerous disk and ray flowers on each head. Seeds typically remain viable in the soil for 6 years, may remain viable for up to 20 yrs. A single plant can produce 5,000-200,000 seeds over a 4-6 week period. 9 points. Sources of information: DiTomaso, J., E. Healy. Weeds of California and Other Western States. Not yet published. |
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Question 2.5 Potential for human-caused dispersal? | B Other Published Material |
Identify dispersal mechanisms: Spread by agricultural equipment, human activity, on the tires of vehicles, and on the shoes and clothes of people. Can be spread in contaminated hay or straw. Seeds may be spread in the manure of livestock. Can be spread by fire-fighting activity. Human dispersal is unintentional but does occur. Sources of information: DiTomaso, J., E. Healy. Weeds of California and Other Western States. Not yet published. |
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Question 2.6 Potential for natural long-distance dispersal? | B Other Published Material |
Identify dispersal mechanisms: Seeds can be dispersed a short distance (a few meters) by wind. While not verified, very strong winds may be able to blow seeds many kilometers, but only if they are pulled into the atmosphere. Water dipsersal is likely. Also dispersed by clinging to the fur, feathers, and feet of animals. Seeds may survive ingestion by birds, but some experiments have found this unlikely. Occassionally dispersed long distances by animals and water. Sources of information: DiTomaso, J., E. Healy. Weeds of California and Other Western States. Not yet published. |
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Question 2.7 Other regions invaded? | C Other Published Material |
Identify other regions: State-listed noxious weed in AZ, CO, ID, OR, WA. Distribution includes ID, MT, OR, WA to British Columbia, IL, MI, some northeastern states. Naturalized in India, Africa, Canada, Argentina, Australia, and New Zealand. Occurs along beaches in OR. Same ecotypes as in CA. Sources of information: DiTomaso, J., E. Healy. Weeds of California and Other Western States. Not yet published. |
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Section 3: Distribution | |
Question 3.1 Ecological amplitude/Range? | A Other Published Material |
First reported in OR in 1922. Disturbed sites, waste places, roadsides, pastures, fields, rangeland, near riparian areas, forested areas. Inhabits grassland, woodland, and dunes in its native range. Often found in grasslands, cut-over forests, nonirrigated patures, and woodland pastures in PNW. Inhabits at least 3 major ecotypes and 6 minor in CA. Sources of information: DiTomaso, J., E. Healy. Weeds of California and Other Western States. Not yet published. |
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Question 3.2 Distribution/Peak frequency? | C Reviewed Scientific Publication |
Describe distribution: North Coast, western Klamath Ranges, soutwestern Cascade Range, northern Sierra Nevada, northern Sacramento Valley, San Francisco Bay region. Requires areas of sufficient rainfall. Infests 3 million acres in the PNW including northern CA. Requires a climate similar to central Europe, cooler and wetter than much of California. Dry summer months greatly inhibit seedling establishment. present in at least 6-20% of north coast coniferous forest Sources of information: DiTomaso, J., E. Healy. Weeds of California and Other Western States. Not yet published. |
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 | No |
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 | Yes |
Fragments easily and fragments can become established elsewhere | No |
Resprouts readily when cut, grazed, or burned | Yes |
Total points: | 9 |
Total unknowns: | 0 |
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 | D, < 5% |
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 | 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 | D, < 5% |
riparian woodland | D, < 5% | |
riparian scrub (incl.desert washes) | ||
Woodland | cismontane woodland | |
piñon and juniper woodland | ||
Sonoran thorn woodland | ||
Forest | broadleaved upland forest | |
North Coast coniferous forest | C, 5% - 20% | |
closed cone coniferous forest | ||
lower montane coniferous forest | D, < 5% | |
upper montane coniferous forest | ||
subalpine coniferous forest | ||
Alpine Habitats | alpine boulder and rock field | |
alpine dwarf scrub | ||
Amplitude (breadth): | A | |
Distribution (highest score): | C |
Infested Jepson Regions
Click here for a map of Jepson regions
- CA Floristic Province
- Cascade Range
- Central West
- Great Valley
- Northwest
- Sierra Nevada
- Southwest
- Mojave Desert