Pacific Island Ecosystems at Risk (PIER)
RISK ASSESSMENT RESULTS: Low risk, score: -3
|
Australian/New Zealand Weed Risk Assessment adapted for Hawai‘i. Research directed by C. Daehler (UH Botany) with funding from the Kaulunani Urban Forestry Program and US Forest Service Information on
Risk Assessments |
Flindersia brayleyana (Queensland Maple, maple silkwood) |
Answer |
||
1.01 |
Is the species highly domesticated? |
y=-3, n=0 |
n |
1.02 |
Has the species become naturalized where grown? |
y=-1, n=-1 |
y |
1.03 |
Does the species have weedy races? |
y=-1, n=-1 |
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” |
See Append 2 |
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, n=0 |
|
2.04 |
Native or naturalized in regions with tropical or subtropical climates |
y=1, n=0 |
y |
2.05 |
Does the species have a history of repeated introductions outside its natural range? y=-2 |
?=-1, n=0 |
y |
3.01 |
Naturalized beyond native range y = 1*multiplier (see Append 2), n= question 2.05 |
y |
|
3.02 |
Garden/amenity/disturbance weed y = 1*multiplier (see Append 2) |
n=0 |
n |
3.03 |
Agricultural/forestry/horticultural weed y = 2*multiplier (see Append 2) |
n=0 |
n |
3.04 |
Environmental weed y = 2*multiplier (see Append 2) |
n=0 |
n |
3.05 |
Congeneric weed y = 1*multiplier (see Append 2) |
n=0 |
n |
4.01 |
Produces spines, thorns or burrs |
y=1, n=0 |
n |
4.02 |
Allelopathic |
y=1, n=0 |
n |
4.03 |
Parasitic |
y=1, n=0 |
n |
4.04 |
Unpalatable to grazing animals |
y=1, n=-1 |
n |
4.05 |
Toxic to animals |
y=1, n=0 |
n |
4.06 |
Host for recognized pests and pathogens |
y=1, n=0 |
y |
4.07 |
Causes allergies or is otherwise toxic to humans |
y=1, n=0 |
n |
4.08 |
Creates a fire hazard in natural ecosystems |
y=1, n=0 |
n |
4.09 |
Is a shade tolerant plant at some stage of its life cycle |
y=1, n=0 |
y |
4.1 |
Tolerates a wide range of soil conditions (or limestone conditions if not a volcanic island) |
y=1, n=0 |
n |
4.11 |
Climbing or smothering growth habit |
y=1, n=0 |
n |
4.12 |
Forms dense thickets |
y=1, n=0 |
n |
5.01 |
Aquatic |
y=5, n=0 |
n |
5.02 |
Grass |
y=1, n=0 |
n |
5.03 |
Nitrogen fixing woody plant |
y=1, n=0 |
n |
5.04 |
Geophyte (herbaceous with underground storage organs -- bulbs, corms, or tubers) |
y=1, n=0 |
n |
6.01 |
Evidence of substantial reproductive failure in native habitat |
y=1, n=0 |
n |
6.02 |
Produces viable seed. |
y=1, n=-1 |
y |
6.03 |
Hybridizes naturally |
y=1, n=-1 |
|
6.04 |
Self-compatible or apomictic |
y=1, n=-1 |
|
6.05 |
Requires specialist pollinators |
y=-1, n=0 |
n |
6.06 |
Reproduction by vegetative fragmentation |
y=1, n=-1 |
n |
6.07 |
Minimum generative time (years) 1 year = 1, 2 or 3 years = 0, 4+ years = -1 |
See left |
8 |
7.01 |
Propagules likely to be dispersed unintentionally (plants growing in heavily trafficked areas) |
y=1, n=-1 |
n |
7.02 |
Propagules dispersed intentionally by people |
y=1, n=-1 |
y |
7.03 |
Propagules likely to disperse as a produce contaminant |
y=1, n=-1 |
n |
7.04 |
Propagules adapted to wind dispersal |
y=1, n=-1 |
y |
7.05 |
Propagules water dispersed |
y=1, n=-1 |
n |
7.06 |
Propagules bird dispersed |
y=1, n=-1 |
n |
7.07 |
Propagules dispersed by other animals (externally) |
y=1, n=-1 |
n |
7.08 |
Propagules survive passage through the gut |
y=1, n=-1 |
n |
8.01 |
Prolific seed production (>1000/m2) |
y=1, n=-1 |
n |
8.02 |
Evidence that a persistent propagule bank is formed (>1 yr) |
y=1, n=-1 |
n |
8.03 |
Well controlled by herbicides |
y=-1, n=1 |
|
8.04 |
Tolerates, or benefits from, mutilation, cultivation, or fire |
y=1, n=-1 |
|
8.05 |
Effective natural enemies present locally (e.g. introduced biocontrol agents) |
y=-1, n=1 |
|
Total score: |
-3 |
Supporting data:
Notes |
Source |
|
1.01 |
No evidence |
|
1.02 |
(1)Naturalized from plantings at Waiakea Forest Reserve, Hawaii Island (2) 'Commonly introduced to Hawai‘i as a forestry tree and now naturalized.' (3)natural regeneration was often prolific under dense canopies. |
(1)Wagner et al 1990. Mannual of the Flowering Plants of Hawaii. University of Hawaii Press (2)http://www.hear.org/pier/flbra.htm (3)http://www.hawaii.gov/dlnr/dofaw/pubs/Waiakea.PDF |
1.03 |
No evidence |
|
2.01 |
It is endemic to northeast Queensland, Australia. The distribution is in the warm humid, hot humid and the warm sub-humid, winter-dry climatic zones. A common species distributed in lowland and highland rainforest. |
CAB International, 2000. Forestry Compendium Global Module. Wallingford, UK: CAB International. |
2.02 |
||
2.03 |
(1)Approximate limits north to south: 16°S to 19°S -
Altitude range: 0 - 1200 m |
(1)CAB International, 2000. Forestry Compendium Global Module. Wallingford, UK: CAB International. (2)http://www.forests.qld.gov.au/qts/treetext.html |
2.04 |
It is endemic to northeast Queensland, Australia. The distribution is in the warm humid, hot humid and the warm sub-humid, winter-dry climatic zones. A common species distributed in lowland and highland rainforest. |
CAB International, 2000. Forestry Compendium Global Module. Wallingford, UK: CAB International. |
2.05 |
List of countries where planted North America [USA] Hawaii South America: Paraguay, Peru Oceania [Australia] Queensland, Fiji, Samoa |
CAB International, 2000. Forestry Compendium Global Module. Wallingford, UK: CAB International. |
3.01 |
(1)Naturalized from plantings at Waiakea Forest Reserve, Hawaii Island (2) 'Commonly introduced to Hawai‘i as a forestry tree and now naturalized.' (3)natural regeneration was often prolific under dense canopies. |
(1)Wagner et al 1990. Mannual of the Flowering Plants of Hawaii. University of Hawaii Press (2)http://www.hear.org/pier/flbra.htm (3)http://www.hawaii.gov/dlnr/dofaw/pubs/Waiakea.PDF |
3.02 |
No evidence |
|
3.03 |
No evidence |
|
3.04 |
No evidence |
|
3.05 |
No evidence |
|
4.01 |
No evidence |
http://www.hear.org/pier/flbra.htm |
4.02 |
No evidence |
|
4.03 |
No evidence |
|
4.04 |
Common use as a fodder |
http://www.nrm.qld.gov.au/factsheets/pdf/vegetation/T37.pdf |
4.05 |
No evidence |
|
4.06 |
(1) The following fungi were listed to be associated with F.
brayleyana: Agrobacterium sp.: Australia - 6767 |
(1)http://nt.ars-grin.gov/fungaldatabases/all/FindRecOneFungusFrame.cfm (2)http://www.actahort.org/books/439/439_132.htm |
4.07 |
No evidence |
|
4.08 |
Probably not - a rainforest species. |
|
4.09 |
(1) 'Young seedlings should be provided overhead shade for
about the first 2 months. ' |
http://216.239.53.104/search?q=cache:lJ-G9ws-zOEJ:wpsm.net/Flindersia.pdf+Flindersia+brayleyana&hl=en&ie=UTF-8
|
4.1 |
'Soils vary from skeletal to deep loams, but this species
reaches its best development on basalt and granite. It has become scarce on
fertile, red volcanic soils. It needs well-drained soils and plenty of water
during establishment. ' |
(1)http://216.239.53.104/search?q=cache:lJ-G9ws-zOEJ:wpsm.net/Flindersia.pdf+Flindersia+brayleyana&hl=en&ie=UTF-8
|
4.11 |
Not climbing - a tree. |
CAB International, 2000. Forestry Compendium Global Module. Wallingford, UK: CAB International. |
4.12 |
Grows in a variety of rainforest types and is associated with a large number of tree species. |
http://www.forestfarmers.com.au/Species/F-bray.htm |
5.01 |
Terrestrial |
|
5.02 |
F. brayleana is a medium to tall tree 35-45 m in height and to 2.5 m in diameter with a spreading crown. |
CAB International, 2000. Forestry Compendium Global Module. Wallingford, UK: CAB International. |
5.03 |
No evidence |
|
5.04 |
Tree |
|
6.01 |
'In Queensland, Swain (1928) reported a range of 6,600 to 11,000 seeds/kg (3,000 to 5,000 seeds/lb).' |
http://216.239.53.104/search?q=cache:lJ-G9ws-zOEJ:wpsm.net/Flindersia.pdf+Flindersia+brayleyana&hl=en&ie=UTF-8 |
6.02 |
In Hawaii, good germination was obtained without any pregermination treatment (Wick 1974). In a test in Queensland, germination rates were 70% in 7 days and 90% in 20 days (Swain 1928).' |
http://216.239.53.104/search?q=cache:lJ-G9ws-zOEJ:wpsm.net/Flindersia.pdf+Flindersia+brayleyana&hl=en&ie=UTF-8 |
6.03 |
No evidence |
|
6.04 |
No evidence |
|
6.05 |
(1) 'A species like the flower scarab Phyllotocus apicalis
Maclaey, that pollinates the rainforest tree Flindersia brayleyana F. Muell,
is a potential crop pollinator because it is also attracted to many non
rainforest plants'. |
(1)
http://216.239.53.104/search?q=cache:UNTd1DToTHgJ:www.rainforest-crc.jcu.edu.au/publications/research%2520reports/ReportPDFs/InsectServices.pdf |
6.06 |
No evidence of vegetative spread in the wild. |
|
6.07 |
'It usually starts bearing seed at 8 years of age and
produces an abundant crop annually.' |
(1)
http://216.239.53.104/search?q=cache:lJ-G9ws-zOEJ:wpsm.net |
7.01 |
Probably not - winged seeds. |
(1)http://216.239.53.104/search?q=cache:lJ-G9ws-zOEJ:wpsm.net |
7.02 |
It is used for mixed planting on degraded farmlands and as an ornamental tub plant. |
CAB International, 2000. Forestry Compendium Global Module. Wallingford, UK: CAB International. |
7.03 |
No evidence |
(1)http://216.239.53.104/search?q=cache:lJ-G9ws-zOEJ:wpsm.net |
7.04 |
(1) 'The fruit is a cylindrical, hard-shelled, warty, 5-valved dehiscent capsule, about 6 cm long and 2.5 cm in diameter (Little and Skolmen 1989). In Hawaii, it generally ripens from June to July, and releases its several flat, winged seeds measuring 5 by 1 cm, from July through September …' (2)Seeds winged at both ends, 4.5-6 cm long. |
(1)http://216.239.53.104/search?q=cache:lJ-G9ws-zOEJ:wpsm.net |
7.05 |
No evidence |
|
7.06 |
No evidence |
|
7.07 |
No evidence of any means of attachment. |
|
7.08 |
No evidence of being ingested. |
|
8.01 |
(1) Seeds winged at both ends, 4.5-6 cm long. (2)'In Hawaii,
there are between 9,800 and 11,700 seeds/kg (4,400 to 5,300 seeds/lb), or an
average of about 10,500 seeds/kg (4,800 seeds/lb) (Wick 1974). In
Queensland, Swain (1928) reported a range of 6,600 to 11,000 seeds/kg (3,000
to 5,000 seeds/lb).' (3)9300 fresh seeds and 13700 dried seeds per kilogram.
(4)There can be about 200 trees per acre in a plantation. [probably not
seeds are relativley large, 4.5x6=27sq cm] |
(1) http://www.forestfarmers.com.au/Species/F-bray.htm
(2)http://216.239.53.104/search?q=cache:lJ-G9ws-zOEJ:wpsm.net/Flindersia.pdf+Flindersia+brayleyana&hl=en&ie=UTF-8
(3)http://www.forestfarmers.com.au/Species/F-bray.htm
(4)http://216.239.53.104/search?q=cache:yMABCwnw2s0J:www.state.hi. |
8.02 |
(1) 'The seeds do not store well and lose their viability
within a year.' |
(1)
http://216.239.53.104/search?q=cache:lJ-G9ws-zOEJ:wpsm.net |
8.03 |
No evidence of being controlled. |
|
8.04 |
(1)" In a 2-year trial, 20 trees of each of 5 planted species were cut to a 4-in stump, and the height and d.b.h. of the coppice shoots were recorded. The prospect for producing crop trees by coppicing was greatest in Toona australis and Fraxinus uhdei, intermediate in Araucaria cunninghamii and Castanospermum australe, and least in Flindersia brayleyana. " (2)Tolerates lopping [conflicting information] |
(1)Walters, G. A. (1972) Coppicing to convert small cull trees to growing stock. USDA Forest Service Research Note, Pacific Southwest Forest and Range Experiment Station, 1972, No.PSW-272, 4 pp., 4 ref. (2)http://www.nrm.qld.gov.au/factsheets/pdf/vegetation/T37.pdf |
8.05 |
Don’t know |
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This page updated 4 March 2005