Pacific Island Ecosystems at Risk (PIER)
Eucalyptus cloeziana
RISK ASSESSMENT RESULTS: Low risk, score: -1
|
Australian/New Zealand Weed Risk Assessment adapted for Hawai‘i. Information on Risk Assessments Original risk assessment |
| Eucalyptus cloeziana (Gympie messmate, messmate, dead finish, yellow messmate, Queensland messmate) | Answer | Score | |
| 1.01 | Is the species highly domesticated? | n | 0 |
| 1.02 | Has the species become naturalized where grown? | n | |
| 1.03 | Does the species have weedy races? | n | |
| 2.01 | Species suited to tropical or subtropical climate(s) (0-low; 1-intermediate; 2-high) – If island is primarily wet habitat, then substitute “wet tropical” for “tropical or subtropical” | 2 | |
| 2.02 | Quality of climate match data (0-low; 1-intermediate; 2-high) see appendix 2 | 2 | |
| 2.03 | Broad climate suitability (environmental versatility) | y | 1 |
| 2.04 | Native or naturalized in regions with tropical or subtropical climates | y | 1 |
| 2.05 | Does the species have a history of repeated introductions outside its natural range? y=-2 | y | |
| 3.01 | Naturalized beyond native range y = 1*multiplier (see Append 2), n= question 2.05 | n | -2 |
| 3.02 | Garden/amenity/disturbance weed y = 1*multiplier (see Append 2) | n | 0 |
| 3.03 | Agricultural/forestry/horticultural weed y = 2*multiplier (see Append 2) | n | 0 |
| 3.04 | Environmental weed y = 2*multiplier (see Append 2) | n | 0 |
| 3.05 | Congeneric weed y = 1*multiplier (see Append 2) | y | 2 |
| 4.01 | Produces spines, thorns or burrs | n | 0 |
| 4.02 | Allelopathic | n | 0 |
| 4.03 | Parasitic | n | 0 |
| 4.04 | Unpalatable to grazing animals | ||
| 4.05 | Toxic to animals | n | 0 |
| 4.06 | Host for recognized pests and pathogens | n | 0 |
| 4.07 | Causes allergies or is otherwise toxic to humans | n | 0 |
| 4.08 | Creates a fire hazard in natural ecosystems | ||
| 4.09 | Is a shade tolerant plant at some stage of its life cycle | y | 1 |
| 4.1 | Tolerates a wide range of soil conditions (or limestone conditions if not a volcanic island) | n | 0 |
| 4.11 | Climbing or smothering growth habit | n | 0 |
| 4.12 | Forms dense thickets | n | 0 |
| 5.01 | Aquatic | n | 0 |
| 5.02 | Grass | n | 0 |
| 5.03 | Nitrogen fixing woody plant | n | 0 |
| 5.04 | Geophyte (herbaceous with underground storage organs -- bulbs, corms, or tubers) | n | 0 |
| 6.01 | Evidence of substantial reproductive failure in native habitat | n | 0 |
| 6.02 | Produces viable seed. | y | 1 |
| 6.03 | Hybridizes naturally | y | 1 |
| 6.04 | Self-compatible or apomictic | n | -1 |
| 6.05 | Requires specialist pollinators | n | 0 |
| 6.06 | Reproduction by vegetative fragmentation | n | -1 |
| 6.07 | Minimum generative time (years) 1 year = 1, 2 or 3 years = 0, 4+ years = -1 | 9 | -1 |
| 7.01 | Propagules likely to be dispersed unintentionally (plants growing in heavily trafficked areas) | n | -1 |
| 7.02 | Propagules dispersed intentionally by people | y | 1 |
| 7.03 | Propagules likely to disperse as a produce contaminant | n | -1 |
| 7.04 | Propagules adapted to wind dispersal | y | 1 |
| 7.05 | Propagules water dispersed | n | -1 |
| 7.06 | Propagules bird dispersed | n | -1 |
| 7.07 | Propagules dispersed by other animals (externally) | n | -1 |
| 7.08 | Propagules survive passage through the gut | n | -1 |
| 8.01 | Prolific seed production (>1000/m2) | ||
| 8.02 | Evidence that a persistent propagule bank is formed (>1 yr) | ||
| 8.03 | Well controlled by herbicides | ||
| 8.04 | Tolerates, or benefits from, mutilation, cultivation, or fire | y | 1 |
| 8.05 | Effective natural enemies present locally (e.g. introduced biocontrol agents) | ||
| Total score: | -1 |
Supporting data:
| Notes | Reference | |
| 1.01 | No evidence. | |
| 1.02 | No evidence | |
| 1.03 | No evidence. | |
| 2.01 | 'This species is a tall straight tree with a scattered natural distribution in tropical and subtropical areas of Queensland.' | Forestry Compendium [Online database]. © CAB International, Wallingford, UK, 2005. |
| 2.02 | ||
| 2.03 |
(1) - Altitude range: 0 - 1500 m - Mean annual rainfall: 500 - 2300 mm - Rainfall regime: summer; uniform - Dry season duration: 0 - 5 months - Mean annual temperature: 16 - 27ºC - Mean maximum temperature of hottest month: 27 - 36ºC - Mean minimum temperature of coldest month: 5 - 17ºC - Absolute minimum temperature: > -3ºC (2)Hardiness range 10A -11. |
(1)Forestry Compendium [Online database]. © CAB International, Wallingford, UK, 2005. (2)http://www.horticopia.com/hortpix/html/pc2300.htm |
| 2.04 | 'This species is a tall straight tree with a scattered natural distribution in tropical and subtropical areas of Queensland.' | Forestry Compendium [Online database]. © CAB International, Wallingford, UK, 2005. |
| 2.05 | 'It has been successfully introduced for poles in Kenya, Malawi, Swaziland, South Africa, Uganda, Zambia and Zimbabwe in southern Africa principally in areas with an annual rainfall of 1000-1500 mm and a dry season of 4-5 months (FAO, 1974; Poynton, 1979). It also grows well in parts of Brazil, China, Congo, Madagascar and Nigeria. ' | Forestry Compendium [Online database]. © CAB International, Wallingford, UK, 2005. |
| 3.01 | No evidence | |
| 3.02 | No evidence | |
| 3.03 | No evidence | |
| 3.04 | 'It is not an aggressive colonizer and has no major disadvantages such as being a host for pests or diseases of crop plants, poisonous properties or parts, and extreme thorniness.' | Forestry Compendium [Online database]. © CAB International, Wallingford, UK, 2005. |
| 3.05 | Severa Eucalyptus species such as E. populnea,E. pilularis, E. ferruginear and E. cambageana are listed as principal weeds in Australia. | An electronic Atlas of Weeds and Invasive Species. CD ROM version 1. 1997. Based on the original work 'A Geographical Atlas of Weeds' by Holm et al. |
| 4.01 | No evidence of such structures. | Forestry Compendium [Online database]. © CAB International, Wallingford, UK, 2005. |
| 4.02 | No evidence. | |
| 4.03 | No evidence. | |
| 4.04 | Don’t know | |
| 4.05 | 'It is not an aggressive colonizer and has no major disadvantages such as being a host for pests or diseases of crop plants, poisonous properties or parts, and extreme thorniness.' | Forestry Compendium [Online database]. © CAB International, Wallingford, UK, 2005. |
| 4.06 |
The following pests were listed to be associated with E. cloeziana. Phytophthora (foot rot) fungus Causes damping-off in the nursery Puccinia psidii (guava rust) fungus Pythium fungus Causes damping-off in the nursery Rhizoctonia fungus Causes damping-off in the nursery Biston edwardsi insect A defoliating Lepidopter |