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Assessment of plant invasiveness is done by evaluating biological and ecological characteristics such as germination requirements, growth rate, competitive ability, reproduction methods and dispersal mechanisms. Assessment of plant impacts, however, is determined by the extent to which a plant affects a land manager’s environmental, economic and social resources.
The relative importance of these resources varies depending upon the value people place on them and, as such, the assessment process is subjective. For example, a farmer is likely to place a higher emphasis on the impact of a plant on production (economic resource) than its impact on areas of natural vegetation occurring on the farm. Conversely, a Landcare or Friends group would value environmental or social resources more than economic resources.
Recognising that the value of resources vary between different land tenures, plant impact assessments allow a prioritisation of resources by land managers. Assessments can apply at a local, regional or state level, and the relative values of each resource identified may differ at each level.
The impact assessment method used in the Victorian Pest Plant Prioritisation Process uses three broad resource categories: social, environmental and agricultural, each with a number of related attributes. For example, social resources include such attributes as how the plant affects human access for recreation, or if it creates a health risk due to toxicity or by producing allergens.
Each resource attribute, or criterion, is assessed relative to a list of intensity ratings. Depending upon information found in relation to each criterion, a rating of Low, Medium Low, Medium High or High is assigned. Descriptions of the impact criteria and intensity ratings used in this process can be viewed here. |
Question | Comments | Reference | Rating |
Recreation | |||
1. Restrict human access? | An erect perennial herb commonly 60 to 90 cm high. Growth is prolific and patches with 130 shoots per square metre are not uncommon, but not all shoots produce flower stems. The leaf margins bear spines. Densely infested areas would be an annoyance humans requiring access. | MH | |
2. Reduce tourism? | In addition to agricultural situations, the plant occurs on neglected sites and roadsides. Recreational activities in these areas would be affected, with a major impact on aesthetics during growth and flowering. | P & C (2001) | MH |
3. Injurious to people? | Spines are present for most of the year. “The fine pappus bristles are claimed to irritate the skin and eyes of some people.” | P & C (2001) | MH |
4. Damage to cultural sites? | Its presence would create a moderate visual effect. The root system is extensive and aggressive, however, there is no evidence to suggest roots or growth habit would affect physical structures. It grows poorly in shaded conditions. | P & C (2001) WSNWCB1 | ML |
Abiotic | |||
5. Impact flow? | Terrestrial species. | P & C (2001) | L |
6. Impact water quality? | Terrestrial species. | P & C (2001) | L |
7. Increase soil erosion? | Aerial parts of the plant die off in late summer and with its strongly competitive nature it is likely to leave infested areas exposed to wind erosion. The extensive perennial root system provides soil stability against erosion by water. | P & C (2001) | ML |
8. Reduce biomass? | Occurs mostly in open situations such as pastures and neglected sites. Direct replacement of biomass or slightly increase. | P & C (2001) | ML |
9. Change fire regime? | In dense infestations, the dry matter left when the plant dies off in late summer may result in a slight increase in fire frequency risk. | P & C (2001) | ML |
Community Habitat | |||
10. Impact on composition (a) high value EVC | EVC= Plains grassy woodland (E); CMA=West Gippsland; Bioreg=Gipplsand Plain; VH CLIMATE potential “[It] is a successful weed in grassland…[and] is strongly competitive in pasture.” However it does not, “…establish where there is existing ground cover.” Displace grasses/forbs in disturbed areas. | P & C (2001) | MH |
(b) medium value EVC | EVC=n/a; CMA=n/a; Bioreg=n/a Does not appear likely to occur in any medium value EVCs in Victoria. | L | |
(c) low value EVC | EVC=Heathy woodland (LC); CMA=Wimmera; Bioreg=Glenelg Plain; VH CLIMATE potential “[It] is a successful weed in grassland…[and] is strongly competitive in pasture.” However it does not, “…establish where there is existing ground cover.” Displace grasses/forbs in disturbed areas. | P & C (2001) | MH |
11. Impact on structure? | The plant has prolific growth, competes strongly for soil resources and produces allelopathic compounds inhibiting the growth of other plants. In non-agricultural areas it is generally confined to roadsides and neglected sites and its presence in these areas would dominate the floral structure. In the USA it is reported to occur in forest margins, however, it grows poorly in shaded areas and is unlikely to affect overstorey layers in these areas. | P & C (2001) WSNWCB | ML |
12. Effect on threatened flora? | |||
Fauna | |||
13. Effect on threatened fauna? | |||
14. Effect on non-threatened fauna? | It has not occurred as a significant weed in natural ecosystems in Victoria (it is not recorded in Carr et al (1992)). In the United States it is recorded as occurring in natural communities, reducing plant and animal diversity. It is highly invasive and, as its prickly nature deters grazing, dense infestations would affect habitat. | Thunhorst & Swearingen (1997)2 | ML |
15. Benefits fauna? | No known benefits. | H | |
16. Injurious to fauna? | If forced to eat the weed, young sheep can injure their mouths, possibly leading to infection. Potential for native fauna to suffer similarly. | P & C (2001) | MH |
Pest Animal | |||
17. Food source to pests? | Not known as a food source to pest animals. In Germany, rats are known to use plant parts for food | P & C (2001) | L |
18. Provides harbor? | Not known as a harbor for pests. May provide limited harbor for minor pest such as rodents. | ML | |
Agriculture | |||
19. Impact yield? | “It is strongly competitive in pastures (reducing forage) and crops such as potatoes, asparagus and peas. In the United States heavy infestations reduce yields of spring cereals by between 40% and 70%.” | WSNWCB P & C (2001) | H |
20. Impact quality? | Its dispersal throughout the world has been attributed to contaminated agricultural seeds. Thus its presence would affect the quality of seed harvests. It is also a problem in pea crops, “…the flower buds are similar in size, shape and texture to shelled peas and are difficult to grade out of the final product.” | P & C (2001) | H |
21. Affect land value? | The plant is difficult to control particularly in cropping situations where cultivation can spread the weed and herbicides tolerated by crops have little or no effect. Its presence would affect the value of land. | P & C (2001)Dept of Ag, WA3 | M |
22. Change land use? | The presence of the weed in cropping situations may dictate a change to grazing until it is controlled. | M | |
23. Increase harvest costs? | Apart from the problem in pea crops, C. arvense is not known to have an appreciable impact on harvesting costs. | P & C (2001) | M |
24. Disease host/vector? | “It harbours insects that attack some commercial crops and it is an alternate host for certain plant pathogens.” | P & C (2001) | H |