Pacific Island Ecosystems at Risk (PIER)
RISK ASSESSMENT RESULTS: Low risk, score: 5 (low risk based on second screen)
|
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 siamea (Senna siamea); Siamese cassia |
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 |
y |
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 |
y |
4.01 |
Produces spines, thorns or burrs |
y=1, n=0 |
n |
4.02 |
Allelopathic |
y=1, n=0 |
y |
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 |
y |
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 |
|
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 |
n |
4.1 |
Tolerates a wide range of soil conditions (or limestone conditions if not a volcanic island) |
y=1, n=0 |
y |
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 |
2 |
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 |
n |
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 |
y |
8.05 |
Effective natural enemies present locally (e.g. introduced biocontrol agents) |
y=-1, n=1 |
|
Total score: |
5 |
Supporting data:
Source |
Notes |
|
1.01 |
no evidence |
|
1.02 |
CAB International, (2000) Forestry Compendium Global Module. Wallingford, UK: CAB International. |
"To date it has been extensively cultivated throughout India, both within forest areas, and also in wasteland afforestation projects, for example in Uttar Pradesh, Bihar, Madhaya Pradesh, West Bengal and Gujarat; in these and in other states it has become naturalized. " |
1.03 |
no evidence |
|
2.01 |
CAB International, (2000) Forestry Compendium Global Module. Wallingford, UK: CAB International. |
Review of natural distribution |
2.02 |
||
2.03 |
(1)CAB International, (2000) Forestry Compendium Global Module. Wallingford, UK: CAB International. (2)http://pppis.fao.org/ |
(1) S. siamea is indigenous to southern India, Sri Lanka,
Myanmar, Thailand, Malaysia and parts of Indonesia (Sumatra). |
2.04 |
CAB International, (2000) Forestry Compendium Global Module. Wallingford, UK: CAB International. |
Review of natural distribution |
2.05 |
CAB International, (2000) Forestry Compendium Global Module. Wallingford, UK: CAB International. |
Location of introductions |
3.01 |
CAB International, (2000) Forestry Compendium Global Module. Wallingford, UK: CAB International. |
"To date it has been extensively cultivated throughout India, both within forest areas, and also in wasteland afforestation projects, for example in Uttar Pradesh, Bihar, Madhaya Pradesh, West Bengal and Gujarat; in these and in other states it has become naturalized. " |
3.02 |
no evidence |
|
3.03 |
no evidence |
|
3.04 |
no evidence |
|
3.05 |
Noxious Weed List, Search the Weeds Australia Database. Webpage available at: <http://www.weeds.org.au/noxious.htm> |
5 Senna spp. are listed as noxious weeds in Australia |
4.01 |
no description of these traits |
|
4.02 |
(1) Prawoto, A. A.(1997) A study of allelopathy effect of Cassia siamea and Adenanthera microsperma to cocoa. [FT: Uji alelopati Cassia siamea dan Adenanthera microsperma terhadap tanaman kakao.] Pelita Perkebunan, 1997, Vol.13, No.1, pp.16-23, 14 ref. (2) Hauser, S.(1993) Effect of Acioa barteri , Cassia siamea , Flemingia macrophylla and Gmelina arborea leaves on germination and early development of maize and cassava. Agriculture, Ecosystems & Environment, 1993, Vol.45, No.3-4, pp.263-273, 16 ref. |
(1) AB: Research on the allelopathic effects of C. siamea , A. microsperma and Leucaena glauca [L. leucocephala ] (used as shade trees for cocoa) on cocoa clone ICS 60 was conducted in greenhouses at the Indonesian Coffee and Cocoa Research Institute, using the Salisbury & Ross method. Cocoa seedlings were grown in polybags for 1 month and then watered with leachate from growing medium in which C. siamea , A. microsperma or L. leucocephala had been growing for 2 months. Control plants were watered with ground water and other set of seedlings were treated with leachate from growing medium without plants to assess the effects of the nutrients supplied from this source. Every 2 days, each seedling was treated with 200 ml leachate/water. Leachate from C. siamea and A. microsperma retarded cocoa growth, but that from L. leucocephala did not. Stem expansion and dry weight increase were significantly inhibited. The leachate from the growing medium without plants increased cocoa seedling growth indicating that the i |
4.03 |
no evidence |
|
4.04 |
(1)Hitinayake, H. M. G. S. B.; Ratnayake, R. M. W. R. (2000) Secondary forests in the dry zone as a source of tree fodder. Gunasena, H. P. M. (editor) Department of Crop Science, Faculty of Agriculture, University of Peradeniya, Peradeniya, Sri Lanka. 2000, pp.78-90, 2 ref. (2)http://www.winrock.org/forestry/factpub/FACTSH/S_siamea.html (3)CAB International, (2000) Forestry Compendium Global Module. Wallingford, UK: CAB International. |
(1)" Wa (Cassia siamea ), Ehela (C. fistula ), Seru (Premna tomentosa ), Burutha (Chloroxylon swietenia ) and Wal Kurundu (Cinnamomum litsaeaefolium ) were the species having high population density due to low palatability to goats and cattle." (2)The leaves and seeds can be eaten by ruminants (3)Grazing livestock can severely damage small trees |
4.05 |
(1)CAB International, (2000) Forestry Compendium Global Module. Wallingford, UK: CAB International. (2)Little and Wadsworth. 1964. Common trees of Puerto Rico and the Virgin Islands. USDA Forest Service Handbook No 249 |
(1)"The leaves, pods and seeds may be eaten by pigs, but are toxic to them." (2)As hogs relish the poisonous leaves, farmers in Puerto Rico have suffered losses |
4.06 |
(1) CAB International, (2000) Forestry Compendium Global
Module. Wallingford, UK: CAB International. |
(1) Protection |
4.07 |
CAB International, (2000) Forestry Compendium Global Module. Wallingford, UK: CAB International. |
"Contact with wood shavings irritates the skin. " [such contact would rarely occur] |
4.08 |
http://www.winrock.org/forestry/factpub/FACTSH/S_siamea.html |
Probably not because it is a single trunked evegreen tree. |
4.09 |
CAB International, (2000) Forestry Compendium Global Module. Wallingford, UK: CAB International. |
"S. siamea is a strong light demander and is sensitive to poor drainage." |
4.1 |
(1)CAB International, (2000) Forestry Compendium Global Module. Wallingford, UK: CAB International. (2)http://www.winrock.org/forestry/factpub/FACTSH/S_siamea.html |
S. siamea is not exacting in soil requirements, but prefers
moist soils with good drainage (Troup and Joshi, 1983) and a soil pH of
5.5-7.5 (Gutteridge, 1997). In West Bengal, it has been grown in lateric
soil after deep soil working. It tolerates denuded shallow soils (Hocking,
1993), but its growth will stagnate in dry areas, with the tree becoming
stunted after 4 to 5 years; coppice growth will also be reduced. S. siamea
is suitable for use on vertisols, xerosol/calcisols, aerisol/alisols,
ferrasols, and nitosol/nitisols (FAO classification). It flourishes on both
flat terrain and hill slopes, |
4.11 |
CAB International, (2000) Forestry Compendium Global Module. Wallingford, UK: CAB International. |
"S. siamea is a medium-size tree rarely exceeding 20 m in height, more usually 10 to 12 m. " |
4.12 |
no evidence |
|
5.01 |
terrestrial |
|
5.02 |
tree; Fabaceae |
|
5.03 |
(1)CAB International, (2000) Forestry Compendium Global Module. Wallingford, UK: CAB International. (2)http://www.winrock.org/forestry/factpub/FACTSH/S_siamea.html |
(1)"It is now well accepted that S. siamea does not fix nitrogen through Rhizobium symbiosis in nodules, although there is some evidence that nitrogen-fixing activity may occur in the warty, lenticellate bark (Gutteridge RC, 1997. Senna siamea (Lamk.) Irwin & Barneby. In: Faridah Hanum I, Van der Maesen LJG, eds, 1997. Plant Resources of South-East Asia. No. 11. Auxillary plants. Leiden, Netherlands; Backhuys.)." (2)a nonnitrogen-fixing leguminous tree |
5.04 |
tree |
|
6.01 |
CAB International, (2000) Forestry Compendium Global Module. Wallingford, UK: CAB International. |
There are no records of ex situ conservation of S. siamea. As it is common within its natural distribution range, and is planted extensively, it does not seem to be endangered, nor is it considered liable to genetic erosion (Sosef et al., 1998). |
6.02 |
CAB International, (2000) Forestry Compendium Global Module. Wallingford, UK: CAB International. |
"For stump plant production, seeds are sown in beds in lines about 23 cm apart. Germination starts 1-4 weeks after sowing. " |
6.03 |
no evidence |
|
6.04 |
no evidence |
|
6.05 |
[http://www.barbadine.com/pages/cassia_siamea_lien.htm] |
no evidence [Picture of flowers does not suggest adaptation to specialist pollinators] |
6.06 |
no evidence |
|
6.07 |
http://216.239.57.100/search?q=cache:InuxTDodBRMJ:www.dfsc.dk/pdf/ |
Flowering and fruiting begin at the age of 2-3 years |
7.01 |
no evidence |
|
7.02 |
CAB International, (2000) Forestry Compendium Global Module. Wallingford, UK: CAB International. |
Location of introductions |
7.03 |
no evidence |
|
7.04 |
http://www.dfsc.dk/pdf/Seedleaflets/Senna%20siamea_int.pdf |
no evidence [indehiscent pod ..'.When the pods have turned brown, they can be harvested from the tree. It is also possible to collect mature, half opened pods from the ground.' This probably suggests dispersal by gravity. No evidence of adaptive structures for wind dispersal] |
7.05 |
no evidence |
|
7.06 |
no evidence |
|
7.07 |
no evidence |
|
7.08 |
http://www.winrock.org/forestry/factpub/FACTSH/S_siamea.html |
seeds can be eaten by ruminants [with hard seed coat] |
8.01 |
CAB International, (2000) Forestry Compendium Global Module. Wallingford, UK: CAB International. |
"There are between 35,000 and 41,000 seeds per kilogram (Sosef
et al., 1998). The number of plants that can be expected from a kilogram of
seeds is about 32,200. |
8.02 |
(1) CAB International, (2000) Forestry Compendium Global
Module. Wallingford, UK: CAB International. |
(1) "S. siamea seeds are orthodox, and will keep for several
years in dry storage at ambient temperature (Heinsleigh TE, Holaway BK,
1988. Agroforestry Species for the Philippines. Manila, Philippines: US
Peace Corps, AJA Printers.8). "; "It regenerates naturally by seed, and
seeds may lie dormant on the ground for many years until favourable
conditions occur for germination. It has spread naturally in the dry
deciduous forests of southern India, and is reported to regenerate naturally
in West Bengal." |
8.03 |
no evidence |
|
8.04 |
http://www.winrock.org/forestry/factpub/FACTSH/S_siamea.html |
Plantations can be managed by coppicing, lopping, or pollarding, For mulch or leaf production, the first cut may be 12-18 months after sowing, followed by 3-4 cuts per year thereafter |
8.05 |
FACT Sheet, FACT 99-04, (June 1999) Senna siamea - a widely
used legume tree. Webpage available at
<http://www.winrock.org/forestry/FACTPUB/FACTSH/S_siamea.html> |
No significant pest or disease damage has been recorded, but minor damage can be caused by the wood rot, Ganoderma lucidum (Khan and Alam 1996). Insects that damage seed include Caryedon lineaticollis and Bruchidius maculatipes. Seed-borne fungi reported in Thailand include Aspergillus niger and Curvularia pallescens (Hor 1993). The fungus Phaeolus manihotis occasionally causes damage to the root system (Gutteridge 1997). |
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This page updated 8 March 2005