Pacific Island Ecosystems at Risk (PIER)
RISK ASSESSMENT RESULTS: Low risk, score: 3 (low risk based on second screen)
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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 |
Ficus benghalensis; Indian banyan |
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 |
n |
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 |
y |
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 |
|
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 |
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 |
n |
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 |
y |
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 |
n |
6.04 |
Self-compatible or apomictic |
y=1, n=-1 |
|
6.05 |
Requires specialist pollinators |
y=-1, n=0 |
y |
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 |
4 |
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 |
y |
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 |
y |
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 |
n |
8.05 |
Effective natural enemies present locally (e.g. introduced biocontrol agents) |
y=-1, n=1 |
|
Total score: |
3 |
Supporting data:
Source |
Notes |
|
1.01 |
no evidence |
|
1.02 |
(1) Control of Non-native Plants in Natural Areas of Florida |
All three species (Ficus altissima, F. benghalensis, F. microcarpa ) invade the interior and edges of hammocks; often found growing as epiphytes (on trees) or epiliths (on rocks or stone structures); exercise care when treating epiphytic figs to ensure that herbicide does not come in contact with the host tree; members of this genus are very sensitive to Garlon 4; extreme care must be taken when treating any vegetation near the native strangler fig and shortleaf fig; spray that contacts surface roots can kill a large tree. |
1.03 |
no evidence |
|
2.01 |
CAB International, 2000. Forestry Compendium Global Module. Wallingford, UK: CAB International. |
Natural latitude range: Approximate limits north to south:
30N to 10S |
2.02 |
||
2.03 |
1)FC 2)http://www.floridata.com/ref/f/ficu_ben.cfm |
Natural latitude range: Approximate limits north to south:
30N to 10S |
2.04 |
CAB International, 2000. Forestry Compendium Global Module. Wallingford, UK: CAB International. |
Natural latitude range: Approximate limits north to south:
30N to 10S |
2.05 |
CAB International, 2000. Forestry Compendium Global Module. Wallingford, UK: CAB International. |
List of countries where planted |
3.01 |
Nadel, H.; Frank, J. H.; Knight, R. J., Jr. (1992) Escapees and accomplices: the naturalization of exotic Ficus and their associated faunas in Florida. Florida Entomologist, 1992, Vol.75, No.1, pp.29-38, 31 ref. |
Over 60 exotic Ficus species have been introduced into southern Florida as ornamentals. Three of these, F. altissima, F. benghalensis, F. microcarpa, are now weedy because they are pollinated routinely by immigrant aganoid wasps (Eupristina sp., E. masoni and Parapristina verticillata, resp.). Conditions for colonization by these wasps appear to have been met, and are potentially suitable for pollination of 2 other fig species. |
3.02 |
no evidence |
|
3.03 |
no evidence |
|
3.04 |
(1) Control of Non-native Plants in Natural Areas of Florida |
1) All three species (Ficus altissima, F. benghalensis, F.
microcarpa |
3.05 |
(1) Weeds in New Zealand (http://www.boprc.govt.nz/www/green/weedindx.htm)
contact: norb@kcbbs.gen.nz |
(1) F. pumila and F. rubiginosa are prohibited from
propagation, sale and distribution in New Zealand. |
4.01 |
||
4.02 |
(1) Verma, S. C.; Haider, M. M. (1998) Allelopathic
potential of leaf extracts of some forest trees on seed germination in
Leucaena leucocephala. Range Management & Agroforestry, 1998, Vol.19,
No.1, pp.83-85, 3 ref. |
(1) "The effects of different concentrations of aqueous leaf
extracts of Acacia nilotica , Albizia procera , Ficus benghalensis ,
Terminalia arjuna , Syzygium cumini and Leucaena leucocephala [3 varieties]
were investigated on the germination and speed of germination index in 3
varieties of Leucaena leucocephala (K-8, K-28 and K-132). Leaf extracts of
A. procera and F. benghalensis inhibited the germination and speed of
germination index in all 3 varieties while S. cumini leaf extract promoted
germination in K-132. There was no effect of leaf extract of the same
variety of Leucaena on its own seeds in the case of K-28 and K-132
varieties. However, in variety K-8 10% leaf extract gave a higher
germination percentage than the control value. The leaf extracts of other
tree species did not exhibit marked allelopathic effects on germination. "
(Lab Only, cannot extrapolate to nature) |
4.03 |
CAB International, 2000. Forestry Compendium Global Module. Wallingford, UK: CAB International. |
F. benghalensis is a very large, long-lived evergreen tree with thick spreading horizontal branches, from which numerous aerial roots descend and take root, forming new trunks. |
4.04 |
(1) Mondal, T.; Chakraborty, N.; Mandal, L. (1994) Nutritive
value of banyan (Ficus bengalensis ) tree leaves in male Black Bengal goats.
Indian Journal of Animal Nutrition, 1994, Vol.11, No.2, pp.117-119, 9 ref.
|
(1) "Fresh banyan (Ficus bengalensis [F. benghalensis] )
tree leaves were given to 4 healthy male Black Bengal goats, average
liveweight 7.62 plus or minus 0.32 kg, as sole feed. Voluntary DM intake was
3.59 plus or minus 0.07 kg/100 kg body weight. Banyan tree leaves contained
3.81% digestible CP and 49.78% total digestible nutrients on a DM basis. All
goats were in positive nitrogen, calcium and phosphorus balance, though a
loss in body weight was noted. It was therefore recommended to supplement
this feed with a concentrate mixture. " |
4.05 |
no evidence |
|
4.06 |
CAB International, 2000. Forestry Compendium Global Module. Wallingford, UK: CAB International. |
Insect pests: |
4.07 |
1)CAB International, 2000. Forestry Compendium Global Module. Wallingford, UK: CAB International. 2)http://www.floridata.com/ref/f/ficu_ben.cfm |
Generally the fruit is only eaten in times of famine. F. benghalensis has medicinal properties: the sap is used to treat rheumatism and lumbago; the bark may cure dysentery, diarrhoea and diabetes; leaves are applied to abscesses; and root fibres are used in gonad problems (Hocking, 1993). 2)The foliage and milky sap of all figs can sometimes be an irritant to skin and eyes for especially sensitive people, but most people are not effected |
4.08 |
no evidence |
|
4.09 |
CAB International, 2000. Forestry Compendium Global Module. Wallingford, UK: CAB International.; (1) Hocking D, 1993. Trees for drylands. 1993, xiii + 370 pp.; Originally published by Oxford & IBH Publishing, New Delhi, India; 12 pp. of ref. (2) Gupta RK, 1993. Multipurpose trees for agroforestry and wasteland utilisation. 1993, xv + 562 pp.; 18 pp. of ref + refs in text. |
(1) F. benghalensis is a strong light-demander and is unable to germinate or grow in the shade (Hocking, 1993). (2)Both seedlings and cuttings require light and plenty of moisture for optimum growth (Gupta, 1993). |
4.1 |
CAB International, 2000. Forestry Compendium Global Module. Wallingford, UK: CAB International.; Hocking D, 1993. Trees for drylands. 1993, xiii + 370 pp.; Originally published by Oxford & IBH Publishing, New Delhi, India; 12 pp. of ref. |
- Soil texture: light; medium |
4.11 |
CAB International, 2000. Forestry Compendium Global Module. Wallingford, UK: CAB International. |
This species initially exists as an epiphyte that will rapidly send down roots and begin to envelop the host tree, eventually killing it. |
4.12 |
CAB International, 2000. Forestry Compendium Global Module. Wallingford, UK: CAB International. |
F. benghalensis is a very large, long-lived evergreen tree with thick spreading horizontal branches, from which numerous aerial roots descend and take root, forming new trunks. |
5.01 |
CAB International, 2000. Forestry Compendium Global Module. Wallingford, UK: CAB International. |
F. benghalensis is a very large, long-lived evergreen tree with thick spreading horizontal branches, from which numerous aerial roots descend and take root, forming new trunks. |
5.02 |
CAB International, 2000. Forestry Compendium Global Module. Wallingford, UK: CAB International. |
F. benghalensis is a very large, long-lived evergreen tree with thick spreading horizontal branches, from which numerous aerial roots descend and take root, forming new trunks. |
5.03 |
Ramana, D. B. V.; Sultan Singh; Solanki, K. R.; Negi, A. S. (2000) Nutritive evaluation of some nitrogen and non-nitrogen fixing multipurpose tree species. Animal Feed Science and Technology, 2000, Vol.88, No.1/2, pp.103-111, 37 ref. |
"The nutritive value of leaf materials from five each of nitrogen (NFT), namely, Acacia nilotica, Albizia lebbeck, Butea monosperma, Leucaena leucocephala, Pongamia pinnata and non-nitrogen fixing multipurpose tree (non-NFT) species, namely, Anogeissus pendula, Azadirachta indica, Ficus benghalensis, Terminalia arjuna and Syzygium cumini grown at National Research Centre for Agroforestry, were evaluated by chemical and in sacco methods. " |
5.04 |
CAB International, 2000. Forestry Compendium Global Module. Wallingford, UK: CAB International. |
F. benghalensis is a very large, long-lived evergreen tree with thick spreading horizontal branches, from which numerous aerial roots descend and take root, forming new trunks. |
6.01 |
no evidence |
|
6.02 |
(1) Rai, S. N.; Nagaveni, H. C.; Padmanabha, H. S. A. (1988) Germination and nursery technique of four species of Ficus. Indian Forester, 1988, Vol.114, No.2, pp.63-68, 3 ref. (2)FC |
(1) Fruits were collected from F. mysorences [F. mysorensis], F. bengalensis [F. benghalensis], F. glomerata and F. religiosa (all important multipurpose trees) at different stages of maturation: yellow ripening fruits; brownish yellow moderately ripe fruits; and cherry brown fully ripe fruits. The fruits were squeezed in water and the resultant floating seeds collected and dried on blotting paper in the shade for several days; wt. was recorded. Six soaking pre-treatments were given to seeds before a germination test: water at 60 deg C for 10 min; water at room temp. for 2 h; 50 p.p.m. Ethrel [ethephon] for 2 h; 100 p.p.m. gibberellic acid for 2 h; 100 p.p.m. thiourea for 2 h; and 0.3% HCl for 2 h. Treated seeds, and control (dry) untreated seeds were broadcast sown in twice the quantity of dry sand on a bed of sand or sand and red earth (2:1). Germination started in 7-8 days and was complete within 15 days. Seed wt. was very variable according to both ripeness and species. Best germination (18-20%) occurred |
6.03 |
Pollinated only by species specific fig wasp; unlilkely to hybridize |
|
6.04 |
||
6.05 |
(1)Stange, L. A.; Knight, R. J., Jr. (1987) Fig pollinating wasps of Florida (Hymenoptera: Agaonidae). Entomology Circular, Division of Plant Industry, Florida Department of Agriculture and Consumer Services, 1987, No.296, 4 pp., 9 ref. (2)Nadel, H.; Frank, J. H.; Knight, R. J., Jr. (1992) Escapees and accomplices: the naturalization of exotic Ficus and their associated faunas in Florida. Florida Entomologist, 1992, Vol.75, No.1, pp.29-38, 31 ref. |
(1) Of the 18 species of Hymenoptera found on Ficus spp. in Florida, only 4 (all agaonids) are known to be pollinators, and a key to the females of these species is given. Notes are provided on the history and biology of Parapristina verticillata on F. microcarpa (which is becoming a weed pest) and F. aurea, Eupristina masoni on F. benghalensis (banyan), Pegoscapus assuetus on F. citrifolia and F. aurea, and P. jimenezi on F. aurea and F. septica. Other Hymenoptera found on the Ficus pseudofruits are listed, many of these are torymids which probably parasitised the agaonids. Edible fig (F. carica ), although grown in Florida, does not depend on the agaonids for pollination, and Blastophaga psenes was not found in that state. (2) Over 60 exotic Ficus species have been introduced into southern Florida as ornamentals. Three of these, F. altissima, F. benghalensis, F. microcarpa, are now weedy because they are pollinated routinely by immigrant aganoid wasps (Eupristina sp., E. masoni and Parapristina verticillata |
6.06 |
CAB International, 2000. Forestry Compendium Global Module. Wallingford, UK: CAB International. |
Vegetative propagation by air layering (artificial) |
6.07 |
R. Criley, UH Department of Horticulture, personal communication |
|
7.01 |
CAB International, 2000. Forestry Compendium Global Module. Wallingford, UK: CAB International. |
In the wild, only seeds deposited in the canopy will germinate. (Although the small seeds embeded to pulp might stick to shoes, they are unlikely to germinate or survive near walking areas. Usually begins as an epiphyte) |
7.02 |
CAB International, 2000. Forestry Compendium Global Module. Wallingford, UK: CAB International. |
F. benghalensis is extensively planted for shade and as an ornamental in gardens, villages or along roadsides. |
7.03 |
no evidence |
|
7.04 |
no evidence |
|
7.05 |
no evidence |
|
7.06 |
CAB International, 2000. Forestry Compendium Global Module. Wallingford, UK: CAB International. |
In the wild, F. benghalensis is naturally dispersed via the excrement of birds and monkeys, and only seeds deposited in the canopy will germinate. |
7.07 |
Elangovan, V.; Marimuthu, G.; Kunz, T. H. (1999) Temporal patterns of individual and group foraging behaviour in the short-nosed fruit bat, Cynopterus sphinx , in south India. Journal of Tropical Ecology, 1999, Vol.15, No.5, pp.681-687, 13 ref. |
" The foraging behaviour of the short-nosed fruit bat, Cynopterus sphinx , was investigated in 10 species of fruit trees near the Madurai Kamaraj University campus in Tamil Nadu, over 121 nights between May 1996 and January 1998. The tree species were Annona squamosa, Polyalthia longifolia, P. pendula, Achras sapota [Manilkara zapota], Calophyllum inophyllum, Coccinia indica [C. grandis], Terminalia catappa, Ficus religiosa, F. benjamina and F. bengalensis [F. benghalensis] .The bat began to visit fruit-bearing trees about 30 min after sunset. Individual bats often hovered near or landed on fruits or on nearby branches to remove whole or parts of fruits with their mouths. These bats seldom remained in the fruit-bearing trees to feed, but instead carried fruits to feeding roosts, repeating this behaviour several times throughout the night. Analysis of the temporal distribution of feeding behaviour revealed 2 peaks of activity, one in the pre-midnight hours when bats fed mostly on 'steady state' fruits (those p |
7.08 |
Bird dispersal |
|
8.01 |
numerous minute seeds in small figs. |
|
8.02 |
Rai, S. N.; Nagaveni, H. C.; Padmanabha, H. S. A. (1988) Germination and nursery technique of four species of Ficus. Indian Forester, 1988, Vol.114, No.2, pp.63-68, 3 ref. |
"Germination started in 7-8 days and was complete within 15 days." |
8.03 |
(1) Control of Non-native Plants in Natural Areas of
Florida|<http://edis.ifas.ufl.edu/BODY_WG209#FOOTNOTE_1> |
(1) Basal bark application of 10% Garlon 4 is effective. |
8.04 |
CAB International, 2000. Forestry Compendium Global Module. Wallingford, UK: CAB International. |
It is susceptible to fire, although seldom are its many stems all killed by fire. |
8.05 |
no evidence |
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This page updated 4 March 2005