Authors: Cathy Macdonald, Mary J. Russo, Global Invasive Species Team, The Nature Conservancy
- Senecio jacobaea is a biennial to short lived perennial herb native to Eurasia. Plants can reach 1-4 ft. (0.3-1.2 m) tall.
- The leaves of the basal rosette have petioles, cauline (stem) leaves are sessile and both are deeply lobed and alternate. The leaf lobes are oblong and web-shaped. The margins of the leaves are dentate. The leaves can measure between 1.5-8 in. (4-20 cm) long and 0.75-2.25 in. (2-6 cm) wide. The leaf is medium green above, lighter underneath and occasionally tomentose.
- Flowering occurs in summer to early fall, when numerous yellow, daisy-like flowers develop in a flat topped inflorescence at the apex of the stems. Flower heads are 0.8 in. (2 cm) in diameter.
- Fruit are small and have a persistent ring of white hairs (pappus) attached. 60,000-70,000 seeds produced per plant. Seeds can remain viable for up to 15 years.
- Ecological Threat
- S. jacobaea invades rangelands in the West where it is toxic to livestock. In the East it invades pastures, open forests, swamps, riverbeds, coastal grasslands and disturbed areas. It was first reported in the United States in the early 1900’s. It is native to most of Europe, North Africa and western Asia and may have been introduced into the United States as a medicinal plant.
The following description of Senecio jacobaea is adapted from Munz and Keck (1973).
Senecio jacobaea is a member of the Groundsel Tribe (Senecioneae) of the Sunflower Family (Asteraceae=Compositae). It is a biennial or short-lived perennial, 3-10 dm tall, with one to a few coarse, erect purplishªred stems, simple except above. The herbage is thinly floccose-tomentose, later becoming more or less glabrate. The leaves are well distributed, mostly 2-3 pinnatifid, about 5-20 cm long, with only the lower petioled.
The inflorescence is short, broad, and of several to many heads. The involucre is about 4 mm high. There are about 13 phyllaries, most with dark tips. The bracteoles are narrow, though sometimes quite evident. There are about 13 yellow rays, 5-10 mm long. The akenes of the disk flowers are pubescent, while those of the ray flowers are glabrous.
Senecio jacobaea can be distinguished from other Senecios by its perennial nature, being largely herbaceous but with a woody base; stems 3-10 dm; and leaves 5-20 cm long, not narrow linear or divided into linear segments, but being 2-3 times pinnatifid.
Senecio jacobaea is native to Europe and western Asia and has become a serious rangeland pest in New Zealand, Tasmania, Australia, South Africa, and North and South America.
S. jacobaea is a disturbance area plant; it is found on creek bottom lands, in pastures, forest clearcuts, overgrazed pasture, and along roadsides. In Cascade Head Preserve, Oregon, it has even been found growing in the cracks and crevices of cliffs and on shallow-soiled steep slopes.
S. jacobaea is considered a biennial species. It typically forms a rosette the first year and bolts into a single flowering stalk in the second year to flower, fruit, and die. However, this typical life cycle has many exceptions. Under extremely favorable conditions, tansy ragwort may behave like an annual. If conditions are poor or the plant is damaged, it may be induced into a mono- or polycarpic perennial habit. Polycarpic perennial plants often have large, woody rootstalks and more than one flowering stalk.
Ragwort flowers are arranged in capitula which in turn are arranged in a cymose inflorescence. Each capitula contains an outer row of radiate (ray) female flowers and many central tubular (disk) perfect flowers. The number of florets per capitula varies; Harper and Wood (1957) found an average of 57 disk florets and 13 ray florets. The number of capitula per plant is correlated with plant size; small plants may produce as few as ten capitula, while large, multi-stemmed plants may produce up to 4,000 capitula in a single year.
The morphologically distinct florets produce morphologically distinct achenes. Ray achenes are glabrous and shed their reduced pappus early in development. Disk achenes bear rows of trichomes and retain their pappus. The two achenes also differ in size, weight, dispersal mechanisms, germination requirements, and germination rates.
Ragwort achenes are primarily dispersed by the wind. Disk achenes are dispersed earlier and farther than ray achenes. Ray achenes are retained in the capitula, pressed against the phyllaries. Eventually the ray achenes are shaken out of the capitula, usually falling near the base of the plant. Poole and Cairns (1940) studied the dispersal of ragwort achenes from an established stand. They found that 60% of the total seed shed landed within 4.6 m of the base of the plants; an additional 39% landed between 4.6 and 9 m from the plant. The distance an individual achene disperses depends on climatic conditions (humidity, wind velocity and direction), the structure of the surrounding vegetation, and at what height the achene is borne on the plant (McEvoy unpubl.).
On the Oregon coast, ragwort achenes mature in late summer and early fall. The achenes reach their maximum germination potential before dispersal; they do not possess an innate dormancy. There are two peaks of ragwort germination: fall and spring. However, some germination occurs year-round.
Soil moisture, soil surface humidity, and light are important factors in ragwort germination. Van der Meijden and van der Waals-kooi (1979) found germination of ragwort achenes to be greater at soil moisture levels between 15 and 29% and a relative humidity at the soil surface of 100%. They also found that a covering of more than 4 mm of sand led to enforced dormancy due to screening of light.
The effects of plant competition (probably acting on ragwort's light requirements for germination) on ragwort abundance has been documented both experimentally and observationally. Cameron (1935) planted ragwort seeds in long turf, short continuous turf, overgrazed pasture vegetation, hard exposed soil, and open soil. He obtained high establishment rates in the overgrazed pasture vegetation (86,000/acre) and both soil condition types (860,000/acre and 2,000,000/acre, respectively), but none in the long turf or short continuous turf plots. Van der Meijden and van der Waals-kooi (1979) also planted ragwort seeds in cleared and uncleared plots. Their results supported the hypothesis that ragwort needs an opening through some form of disturbance to become established. Several disturbance agents have been cited for increasing the abundance of ragwort in a community and include moles and gophers, ants, rabbits, livestock, and man.
Ragwort seeds remain viable in the soil for several years. In this way ragwort can wait for the occurrence of favorable conditions. McEvoy (unpubl.) found 0.75 viable ragwort seeds/cc in the upper 3 cm of soil underneath a pasture heavily infested with ragwort. Viable seeds were encountered in samples taken as deep as 25 cm below the surface.
Ragwort can also regenerate vegetatively. This occurs primarily with damaged plants, but it also occurs in undisturbed populations in closed swards. Vegetative regeneration is possible due to storage of carbohydrate reserves in the stem bases and roots. The plant's capacity to re-grow is related to the diameter of the plant and its root crown at the time of the damage. A damaged root crown may produce a single new rosette or several. Propagation of ragwort from root fragments was first attempted by Cairns (1938). Within a month, he obtained shoots from root fragments as small as 1.5 cm in length. Roots from rosettes are more vigorous sprouters than are roots from flowering plants.
S. jacobaea is native to Europe and western Asia and has become a serious rangeland pest in New Zealand, Tasmania, Australia, South Africa, and North and South America. Its complex reproductive and regenerative strategies have allowed it to undermine the action of most weed control methods and therefore spread rapidly. Furthermore, most ragwort control efforts (and the research on these control methods) have focused on rangeland and agricultural land. The characteristics and dynamics of nonagricultural lands are quite different than those of agricultural lands. Therefore, the efficiency and feasibility of any weed control method must be judged on cost, effectiveness, and compatibility with other land use practices and management objectives. Because local climate and site conditions may affect control methods, such methods need to be designed on a site by site basis.
There are two basic rules of biological control: (1) you can never eradicate a species, you can only control it, and because of this (2) if you do control it, it is not a once-and-for-all proposition. As ragwort populations decline, introduced flea beetle populations should also decline. If ragwort densities drop low enough the flea beetles could become locally extinct. The ability of ragwort seeds to remain dormant in the soil for many years give it the ability to 'out-wait' the flea beetles. Any disturbance, natural or otherwise, could allow ragwort a new toehold. It is important that any management actions that might constitute a significant disturbance be monitored for ragwort.
Hand pulling of the occasional plant is recommended as a follow-up control. At Cascade Head Preserve, ragwort abundance should be visually monitored in mid-August every year and transects should be re-read once every five years. Some local fluctuation in ragwort populations should be expected, but if the density starts to increase greatly, surveys for flea beetles should be conducted. Adult flea beetles and flea beetle damage is surveyed easiest in fall. If flea beetle density does not increase with the ragwort, new colonies should be introduced.
This is probably the most commonly used method of control. The main objective of mowing is to stop the plants from producing seed. It is most effective if done just prior to flowering when the plant has exhausted the greatest amount of its stored reserves but before its seeds have started to develop. Although mowing can prevent flowering (if done more than once) it appears to increase rosette density, rather than reduce it (Hawkes pers. comm.).
Hand pulling is an effective method of eliminating ragwort, especially if it is done when soils are moist and the hole left after pulling is mulched. Mulching creates an unsuitable habitat for ragwort germination by removing necessary light. Pulling is most often used only after the population has been brought under control.
S. jacobaea can be controlled chemically with 2,4-D, dicamba, or a combination of the two. For effective control, the herbicides must be applied during specific developmental stages. 2,4-D is most effective when applied to seedlings and first year rosettes or second year plants prior to bolting. Brewster et al. (1978) obtained between 96 and 100% control from spring applications of 2,4-D at 20 western Oregon locations. Following bolting, a combination of 2,4-D and dicamba is more effective; it does not eliminate seed production but does reduce viability if sprayed in the early bud stage and prevents viability if sprayed in the late bud/early flowering stage. As with all herbicides, there is concern ver the long-term effects on the environment and on human health.
Unlike cattle and horses, sheep appear to be unaffected by ragwort's toxicity. They may be either grazed exclusively as a pre-treatment to cattle grazing or grazed with cattle. Continuous heavy grazing will prevent flowering and, in many cases, reduce density. However, sheep eat most herbaceous plant species, and their grazing has side effects. Disturbance due to their feeding and bedding down will leave openings in vegetation. If there is an abundant ragwort seed bank, these openings will allow for reestablishment.
In its native habitat three insects (cinnabar moth, tansy ragwort seed fly, and tansy ragwort flea beetle) have been identified as important population regulators ( Frick 1970). Unfortunately, ragwort has been introduced to other habitats without its associated natural predators. Without them it gained the competitive advantage it needed to become established. The aim of biological control is to reduce that advantage and restore the target weed's natural herbivore/ host plant population balance.
The cinnabar moth was first introduced into Oregon in 1960. Subsequent research has shown that the cinnabar moth can reduce ragwort populations by 50-75% on sites favorable for their survivorship. Adult cinnabar moths begin to emerge in late spring/early summer. Mating commences quickly, and females lay their eggs on the underside of ragwort leaves. Larvae hatch in about two weeks and begin feeding on ragwort foliage. By the third instar, larvae have migrated to the top of the plant to feed on the buds and flowers. With a good population of larvae, plants are stripped of flowers, buds and leaves.
Cinnabar moths are released in colonies of at least 1,000 individuals. Release sites should be well-drained and unlikely to be disturbed (plowing, logging, etc.) for five years following the introduction. Third, fourth, and fifth instar larvae are usually collected for release. It is important to keep the colony cool and well fed during the transport. Five to ten individuals should be allocated to each plant.
Cinnabar moths have been reported on three close relatives of S. jacobaea: S. vulgaris (another introduced weedy species), S. seneca (a garden species), and S. triangularis. The chances of cinnabar moths damaging native species are minor.
The tansy ragwort flea beetle was first released in Oregon in 1971. Adult flea beetles begin emerging in late spring. The beetles feed for several weeks, leaving shot hole damage on ragwort foliage. During mid-summer, the adults estivate. Short days and cooler temperatures bring the beetles out of estivation, and feeding and egg laying begin. Flea beetles lay their eggs in the soil near the base of ragwort plants. Egg laying continues through winter. Eggs hatch following a three week developmental period, and larvae migrate to ragwort root crowns and petioles. Feeding continues through the winter and spring. Pupae develop in spring and early summer. While adult flea damage is visible, it is the larval feeding that damages the plant. Feeding on the root crown of rosettes uses up carbohydrate reserves needed for bolting. There is some speculation that larval feeding may introduce a fungus that is partially responsible for plant death (Holden pers. comm.).
Host specificity studies found that the tansy ragwort flea beetle will feed to a limited extent on other Senecio species and on Emilia coccinea, Erechtites arguta, Adenostyles alpina, Helianthemum nummularium, Cynoglossum amabile, and Ligularia clivorum. Full development of the larvae only occurred on S. vulgaris and S. erucifolius.
More recently, the tansy ragwort seed fly was released as a control agent. Adult emergence of the seed fly coincides with the appearance of ragwort flower buds. Eggs are laid between the involucral bracts and the outermost florets. Egg hatch and larval development occur within a one-month period. The larvae feed on developing seeds. At a release site in New Zealand, ragwort seed flies infested 98% of all capitula and were responsible for an 87% reduction in viable seed production.
Host specificity tests were conducted prior to the seed fly introduction into the U.S.. Forty-four species in the Asteraceae were tested for host suitability. Of these, eggs were laid on S. vulgaris, S. cineraria, Cota tinctoria, Chrysanthemum segetum, Erigeron canadensis, a species of Calendula, and Cichorium endivia. Eggs laid on these species failed to develop. Apparently, larval development can only occur on species with similar chemical composition and capitular structure in which budding is closely synchronized with the emergence of the adult fly.
These three biological control agents complement one another by being targeted on different plant parts. The cinnabar moth feeds primarily on summer foliage, the flea beetle feeds on the root crown in winter, and the seed fly feeds on the seeds in summer. The combined pressure of these three insect species should have greater control than any of the agents alone. Overlap between the cinnabar moth and seed fly may limit population levels of one of the two, but this has not yet been studied.
Although fire is important in the management of grassland systems, there are no data available on which to judge the effectiveness of it as a control for ragwort. Observations suggest that fire actually increases ragwort abundance (Holden pers. comm.).
Management Research Programs
A monitoring program is being undertaken at TNC's Cascade Head Preserve in Oregon.
Research has been done on controlling this weedy species (particularly with respect to rangeland and agricultural land use). Monitoring should tell whether or not further research is needed.
There have been active control efforts made at Cascade Head Preserve in Oregon. The distribution, abundance, and vigor of S. jacobaea was measured there in 1980 and 1982. Ragwort flowering plants and rosettes were counted, and the height and number of capitula per flowering plant were recorded from ten half-square-meter plots along 14 transects. Aerial photographs of the preserve were taken in late August of both years. The intensity of yellow in the photographs was used to map the distribution of four ragwort density classes.
Biological control proved to be the most attractive method here. On July 15, 1980, 6,000 third, fourth and fifth instar cinnabar moth larvae were released. On October 10, 1980, four colonies (300 individuals/colony) of ragwort flea beetles were released. The populations of these bio-control agents and evidence of their damage was monitored from 1980 to 1983. A dramatic decline in ragwort abundance in a zone around the flea beetle release sites was documented in 1982. Flea beetle abundance on the preserve is high, and the flea beetles have spread to most parts of the preserve. Cinnabar moths are still present but in small numbers. The decline in ragwort abundance between 1980 and 1982 is attributed to flea beetle feeding.
For a more complete description of the control efforts at Cascade Head, see Macdonald (1983).
Management Research Needs:
- Identify those places where ragwort is a problem
- Determine control method (if biological control methods are used, determine the effect such controls might have on native species)
- Implement program
- Monitor results
Global Invasive Species Database. 2011. Invasive Species Specialist Group (ISSG) of the IUCN Species Survival Commission 
King County Department of Natural Resources and Parks Water and Land Resources Division 
Oregon Department of Agriculture Plant Programs, Noxious Weed Control 
University of Alaska Anchorage, Alaska Natural Heritage Program 
Washington State Noxious Weed Control Board 
University of California, Jepson Flora Project 
Invasive Plant Atlas of New England (IPANE) 
Flora of North America, www.eFloras.org 
California Invasive Plant Council 
USDA NRCS PLANTS 
USDA ARS GRIN 
- Munz, P.A. and D.D. Keck. 1973. A California flora and supplement. Univ. of California Press, Berkeley.
- ↑ Baker, A.L. 1982. Disk and ray achene development and germination characteristics of tansy ragwort. MS Thesis, Washington State University. 2.0 2.1 2.2 2.3 2.4
- ↑ Macdonald, C.A. 1983. Ragwort abundance and distribution on the Cascade Head Preserve and efforts to control it. The Nature Conservancy, Oregon Field Office, 1205 NW 25th Ave, Portland, OR. 3.0 3.1
- ↑ Forbes, J.C. 1977. Population flux and mortality in ragwort infestations on permanent pastures, Scotland. Weed Res. Frick, K.E. 1970. Longitarsus jacobaea (Coleoptera: Chrysomelidae): A lea beetle for the control of tansy ragwort. 1. Host plant specificity studies. Ann. Entomol. Soc. Amer. 63:284-296. 4.0 4.1
- ↑ Meijden, E. van der and R.E. van der Waals-kooi. 1979. The population ecology of Senecio jacobaea in the Netherlands sand dune system. I. Reproductive strategy and the biennial habit. J. Ecol. 67:131-154. 5.0 5.1 5.2 5.3
- ↑ Cameron, E. 1935. A study of the natural control of ragwort (Senecio jacobaea L.). J. Ecol. 23:265-322. 6.0 6.1 6.2
- ↑ Harper, J.L. and W.A. Wood. 1957. Biological flora of the British Isles: Senecio jacobaea L. J. Ecol. 45:617-637. 7.0 7.1 7.2
- Harper, J.L. 1965. Establishment, aggression and cohabitation in weedy species. Pp. 243-268 in H.G. Baker and G.L. Stebbins (eds.), the genetics of colonizing species. Academic Press, NY.
- Burtt, B.L. 1977. Aspects of diversification in the capitulum. Pp. 41-59 in V.H. Heywood, J.B. Harborne, and B.L. Turner (eds.), The biology and chemistry of the Compositae. Vol. 1. Academic Press, London.
- Green, H.E. 1937. Dispersal of Senecio jacobaea. J. Ecol. 25:569.
- ↑ Poole, A.L. and D. Cairns. 1940. Botanical aspects of ragwort (Senecio jacobaea L.) control. Bull. Dept. Sci. Indust. Res. 82:1-61. 11.0 11.1
- Harris, P.L., et .al. 1979. Reproductive biology of tansy ragwort climate and biological control by the cinnabar moth in Canada. Pp. 163-173 in T.E. Freeman (ed.), Proc. IV Intl. Biol. Cont. Weeds. Univ. of Florida Press, Gainesville.
- Cairns, D. 1938. Vegetative propagation of ragwort. New Zeal. J. Sci. Technol. 20:173a-183a.
- Brewster, B.D., M.P. Rolston, and A.P. Appleby. 1978. Control of tansy ragwort in western Oregon pastures with 2,4-D. Oregon State University Agric. Exper. Stat. Circular 665.
- Peabody, D.V. 1980. Chemical control of tansy ragwort. Washington State Univ. Coop. Ext. Ser., May (3944). 2 pp.
- Sharrow, S.H. and W.D. Mosher. 1982. Sheep as a biological control agent for tansy ragwort. J. of Range Management 35:480-482.
- Bedell, T.E., R.E. Whitesides, and R.B. Hawkes. 1981. Pasture management for control of tansy ragwort. Pacific Northwest Cooperative Extension Publication No. 210.
- ↑ Isaacson, D.L. and D.T. Ehrensing. 1977. Biological control of tansy ragwort. Oregon Dept. of Agriculture, Weed Control Bulletin No. 1. 18.0 18.1
- ↑ Frick, K.E. and L.A. Andres. 1967. Host specificity on the ragwort seed fly. J. Econ. Entomol. 60:457-462. 19.0 19.1
OTHER (UNCITED) REFERENCES
Brehm, B.G. and V. Marttala. 1976. Checklist of the vascular plants of Cascade Head natural area.
Cox, C.S. and P.B. McEvoy. 1983. Effect of summer moisture stress on the capacity of tansy ragwort (Senecio jacobaea) to compensate for defoliation by cinnabar moth (TYRIA jacobaea). J. Appl. Ecol. 20:225-234. George, T.L. and P.N. Reinthal. 1979. A stewardship plan for the Cascade Head Natural Area, The Nature Conservancy.
Isaacson, D.L. 1973. Population dynamics of the cinnabar moth, Tyria jacobaea (Lepidoptera: Arctiidae). MS Thesis, Oregon State Univ.
Whitesides, R.E. 1981. Oregon Weed Control Handbook, Oregon State Univ. Ext. Service.
Images from Bugwood.org