Principal source:
Compiler: IUCN/SSC Invasive Species Specialist Group (ISSG) with support from ASB Community Trust, New Zealand
Updates with support from the Overseas Territories Environmental Programme (OTEP) project XOT603, a joint project with the Cayman Islands Government - Department of Environment
Review:
Publication date: 2010-10-04
Recommended citation: Global Invasive Species Database (2024) Species profile: Senecio jacobaea. Downloaded from http://iucngisd.org/gisd/species.php?sc=1348 on 25-11-2024.
The Ragwort Control Guide outlines all the Do’s and Don’ts of ragwort control, including all the control and management options. The Herbicides for Ragwort control page lists all the herbicides that can be used for ragwort control, including application methods and concentrations.
Preventative measures: A wide range of preventative measures can be utilised to control further spread of ragwort. For example, ensuring that seed for planting is not contaminated with the seeds of S. jacobaea; using thoroughly cleaned vehicles, machinery and equipment; quarantine of heavily infested areas and careful disposal of plant seeds or flowers (DPI, 2007).
Physical: The most commonly adopted method is handpulling or grubbing, with the primary objective being preventing the plant from producing seed. Due to the plant’s regenerative properties, manual control must ensure that the entire crown and roots of the plants are removed. Cultivation of the soil should be carried out systematically to reduce regrowth. For example, the soil should be cultivated to a depth of at least 15cm in spring, with timed seasonal cropping programmes coupled with pasture improving regimes (DPI, 2007). Additionally, in Australia DPI (2007) suggests that afforestation with radiata pine or eucalyptus plantation can effectively suppress the spread of S. jacobaea via competition as well as acting as a windbreak and limiting seed dispersal (DPI, 2007).
Chemical: The best time for application is during the active growth phase of the plant, such that the pesticide is taken up by the crown and the root which is situated deep beneath the surface. A programme requires re-application and should primarily be targeted at the seedlings and rosettes during autumn and spring. It may be more effective to use herbicides that are selective for broadleaf weeds, so that other vegetation is left to compete with remaining ragwort. S. jacobaea can be chemically controlled via the use of 2,4-D and/or dicamba. In order for this method to be effective, the herbicides should be applied during certain developmental stages. For example, 2,4-D nets the best results when applied to seedlings and first year rosettes. A combination of 2,4-D and dicamba is shown to be successful just after the bolting phase (Macdonal & Russo, 1989).
Biological: Sheep appear to be less susceptible to the alkaloid toxicity and thus, heavy grazing can be an effective form of prevention, although it has been shown that even after extensive grazing, regrowth can rapidly occur after the removal of the stock. Thus animal grazing should be used as supplementary scheme only. In its native range, S. jacobaea has a number of natural predators, namely the cinnabar moth (Tyria jacobaeae), tansy ragwort seed fly (Pegohylemyia seneciella) and tansy ragwort flea beetle (Longitarsus jacobaea). The absence of these insects in the introduced range is thought to be directly responsible for its establishment in the respective regions. As a result, the introduction of these natural predators has shown to be an effective means of keeping the population of ragwort in balance (Macdonal & Russo, 1989).