Pacific Island Ecosystems at Risk (PIER)
Cassia bakeriana
RISK ASSESSMENT RESULTS: Low risk, score: -2
|
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 |
Cassia bakeriana; pink shower tree |
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 |
|
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 |
n |
3.01 |
Naturalized beyond native range y = 1*multiplier (see Append 2), n= question 2.05 |
||
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 |
|
4.05 |
Toxic to animals |
y=1, n=0 |
n |
4.06 |
Host for recognized pests and pathogens |
y=1, n=0 |
n |
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 |
|
4.1 |
Tolerates a wide range of soil conditions (or limestone conditions if not a volcanic island) |
y=1, n=0 |
|
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 |
|
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 |
|
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 |
n |
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 |
|
7.08 |
Propagules survive passage through the gut |
y=1, n=-1 |
y |
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 |
y |
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: |
-2 |
Supporting data:
Source |
Notes |
|
1.01 |
no evidence |
|
1.02 |
Information on seeds supplied by ASEAN Forest Tree Seed
Centre |
Origin of seeds was indicated as from naturalized population |
1.03 |
no evidence |
|
2.01 |
USDA, ARS, National Genetic Resources Program. Germplasm Resources Information Network - (GRIN). [Online Database] National Germplasm Resources Laboratory, Beltsville, Maryland. Available: http://www.ars-grin.gov/cgi-bin/npgs/html/tax_search.pl?Cassia+bakeriana (30 September 2003) |
Distributional range: |
2.02 |
||
2.03 |
(1) USDA, ARS, National Genetic Resources Program. Germplasm Resources Information Network - (GRIN). [Online Database] National Germplasm Resources Laboratory, Beltsville, Maryland. Available: http://www.ars-grin.gov/cgi-bin/npgs/html/tax_search.pl?Cassia+bakeriana (30 September 2003) (2) http://www.ag-risk.org/FCICDOCU/NURSERY/98neplhi.pdf |
Distributional range: Native: Asia-Tropical: Myanmar; Thailand (2) Hardiness 10A-11 |
2.04 |
USDA, ARS, National Genetic Resources Program. Germplasm Resources Information Network - (GRIN). [Online Database] National Germplasm Resources Laboratory, Beltsville, Maryland. Available: http://www.ars-grin.gov/cgi-bin/npgs/html/tax_search.pl?Cassia+bakeriana (30 September 2003) |
Distributional range: |
2.05 |
(1) USDA, ARS, National Genetic Resources Program. Germplasm
Resources Information Network - (GRIN). [Online Database] National Germplasm
Resources Laboratory, Beltsville, Maryland. Available: http://www.ars-grin.gov/cgi-bin/npgs/html/tax_search.pl?Cassia+bakeriana
(30 September 2003) |
(1) Geographical Distribution: Pacific Ocean: Fiji (2)Hawaii |
3.01 |
Information on seeds supplied by ASEAN Forest Tree Seed
Centre |
Origin of seeds was indicated as from naturalized population |
3.02 |
no evidence |
|
3.03 |
no evidence |
|
3.04 |
no evidence |
|
3.05 |
no evidence [weedy species are now in the genus Senna] |
|
4.01 |
http://www.botany.hawaii.edu/faculty/carr/page5.htm |
a tree in UH campus shows no evidence of these traits |
4.02 |
no evidence |
|
4.03 |
no evidence |
|
4.04 |
no evidence |
|
4.05 |
no evidence |
|
4.06 |
http://www.rngr.net/Reforestation/Publications/TTSM/ch6 |
in Thailand, the loss of seeds due to infection of Pestalotiopsis sp. on Cassia bakeriana was 6 percent |
4.07 |
no evidence |
|
4.08 |
a single trunked deciduous tree |
|
4.09 |
no evidence |
|
4.1 |
no evidence |
|
4.11 |
http://biodiversity.soton.ac.uk/LegumeWeb?genus=Cassia&species=bakeriana |
Descriptors Perennial non-climbing tree |
4.12 |
no evidence |
|
5.01 |
terrestrial |
|
5.02 |
tree; Fabaceae |
|
5.03 |
tree; Fabaceae, but many Cassias do not fix N |
|
5.04 |
tree |
|
6.01 |
no evidence |
|
6.02 |
Tree Seed Suppliers Directory of the International Centre
for Research in Agroforestry (ICRAF) |
seeds were preserved and distributed |
6.03 |
no evidence |
|
6.04 |
no evidence |
|
6.05 |
no evidence |
|
6.06 |
no evidence |
|
6.07 |
tree |
|
7.01 |
unlikely, with large fruit 30-40cm long, and ca. 2cm in diameter. |
|
7.02 |
http://www.ag-risk.org/FCICDOCU/NURSERY/98neplhi.pdf |
on the "1998 NURSERY ELIGIBLE PLANT LISTING CONTAINER GROWN ORNAMENTAL PLANTS" |
7.03 |
unlikely, with large fruit 30-40cm long, and ca. 2cm in diameter. |
|
7.04 |
unlikely, with large fruit 30-40cm long, and ca. 2cm in diameter. |
|
7.05 |
no evidence |
|
7.06 |
fruit a woody pod |
|
7.07 |
no evidence |
|
7.08 |
no evidence of being ingested; however should survive the gut with its hard seed coats |
|
8.01 |
Tree Seed Suppliers Directory of the International Centre
for Research in Agroforestry (ICRAF) |
Viable seeds/kg : 3700 - 3800 [relatively large-sized seed] |
8.02 |
Tree Seed Suppliers Directory of the International Centre
for Research in Agroforestry (ICRAF) |
Seed type : orthodox |
8.03 |
no evidence of being controlled |
|
8.04 |
no evidence |
|
8.05 |
no evidence |
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This page updated 30 September 2005