Pacific Island Ecosystems at Risk (PIER)
RISK ASSESSMENT RESULTS: High risk, score: 13
|
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 |
Cryptostegia madagascariensis Bojer (Madagascar rubber vine) |
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 |
n |
4.03 |
Parasitic |
y=1, n=0 |
y |
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 |
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 |
y |
4.11 |
Climbing or smothering growth habit |
y=1, n=0 |
|
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 |
y |
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 |
y |
6.05 |
Requires specialist pollinators |
y=-1, n=0 |
n |
6.06 |
Reproduction by vegetative fragmentation |
y=1, n=-1 |
2 |
6.07 |
Minimum generative time (years) 1 year = 1, 2 or 3 years = 0, 4+ years = -1 |
See left |
n |
7.01 |
Propagules likely to be dispersed unintentionally (plants growing in heavily trafficked areas) |
y=1, n=-1 |
y |
7.02 |
Propagules dispersed intentionally by people |
y=1, n=-1 |
n |
7.03 |
Propagules likely to disperse as a produce contaminant |
y=1, n=-1 |
y |
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 |
y |
8.03 |
Well controlled by herbicides |
y=-1, n=1 |
y |
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 |
1 |
Total score: |
13 |
Supporting data:
Notes |
Source |
|
1.01 |
no evidence |
|
1.02 |
"C. grandiflora and C. madagascariensis, are widely cultivated and have become pests in places where they are introduced, including Australia, where C. grandiflora has been called one of their worst weeds, and in Florida, where C. madagascariensis is considered a category II weed by the Florida Exotic Pest Plant Council." |
http://www.hear.org/starr/hiplants/reports/html/cryptostegia_spp.htm |
1.03 |
no evidence |
|
2.01 |
"Cryptostegia madagascariensis is distributed along the whole of the western part of Madagascar, mostly in western phytogeographical domain but is also found in the Toliara region in southwestern domain." |
Klackenberg, J. (2001) Revision of the genus Cryptostegia R. Br. (Apocynaceae, Periplocoideae). Adansonia, 2001, Vol. 23, No. 2, pp. 205-218, 20 ref. URL: http://www.mnhn.fr/publication/adanson/a01n2a3.pdf |
2.02 |
||
2.03 |
" It has been found from sea level up to 700 m alt., usually in full sun. It grows in dry forest (e.g. Didiereaceae, Euphorbia), savannah, tsingy, disturbed grazed grassland, on lateritic soil and sand, often on river beds." |
Klackenberg, J. (2001) Revision of the genus Cryptostegia R. Br. (Apocynaceae, Periplocoideae). Adansonia, 2001, Vol. 23, No. 2, pp. 205-218, 20 ref. URL: http://www.mnhn.fr/publication/adanson/a01n2a3.pdf |
2.04 |
"Cryptostegia madagascariensis is distributed along the whole of the western part of Madagascar, mostly in western phytogeographical domain but is also found in the Toliara region in southwestern domain." |
Klackenberg, J. (2001) Revision of the genus Cryptostegia R. Br. (Apocynaceae, Periplocoideae). Adansonia, 2001, Vol. 23, No. 2, pp. 205-218, 20 ref. URL: http://www.mnhn.fr/publication/adanson/a01n2a3.pdf |
2.05 |
(1) Florida; Puerto Rico; (2) Hawaii |
(1) USDA, NRCS. 2004. The PLANTS Database, Version 3.5 (http://plants.usda.gov). National Plant Data Center, Baton Rouge, LA 70874-4490 USA. (2) http://www.hear.org/starr/hiplants/reports/html/cryptostegia_spp.htm |
3.01 |
"C. grandiflora and C. madagascariensis, are widely cultivated and have become pests in places where they are introduced, including Australia, where C. grandiflora has been called one of their worst weeds, and in Florida, where C. madagascariensis is considered a category II weed by the Florida Exotic Pest Plant Council." |
http://www.hear.org/starr/hiplants/reports/html/cryptostegia_spp.htm |
3.02 |
no evidence |
|
3.03 |
no evidence |
|
3.04 |
(1)"C. madagascariensis is present in southern Florida in the Keys and in a few counties on the coast of south western Florida (PLANTS 2001). C. madagascariensis is listed by the Florida Exotic Pest Plant Council as a category II pest plant (FLEPPC 1999). These are species that have shown a potential to disrupt native plant communities." (2)Environmental weed of Western Australia and Northern Territory (3)Class 3 declared species - sale prohibited by Queensland’s Land Protection |
(1)http://www.hear.org/starr/hiplants/reports/html/cryptostegia_spp.htm (2)Randall, R. 2001. Garden thugs, a national list of invasive and potentially invasive garden plants. Plant Protection Quarterly 16:138-171. (3)http://www.weeds.crc.org.au/documents/backyard_beauties_bushland_bullies_040903_.pdf |
3.05 |
rubber vine (Cryptostegia grandiflora) is a weed in Australia |
Tomley, A. J. (1995) The biology of Australian weeds. 26. Cryptostegia grandiflora R. Br. Plant Protection Quarterly, 1995, Vol. 10, No. 4, pp. 122-130, 50 ref. |
no description of these traits |
Klackenberg, J. (2001) Revision of the genus Cryptostegia R. Br. (Apocynaceae, Periplocoideae). Adansonia, 2001, Vol. 23, No. 2, pp. 205-218, 20 ref. URL: http://www.mnhn.fr/publication/adanson/a01n2a3.pdf |
|
4.01 |
no evidence |
|
4.02 |
no evidence |
|
4.03 |
The major impact on primary industry is through the loss of cattle production from infested areas and subsequent control costs. As rubber vine invades open pasture, grass growth decreases as rubber vine cover increases (Vitelli 1995) and the weed utilises soil moisture and this translates directly into a loss of carrying capacity. |
http://www.nrme.qld.gov.au/pests/psas/pdfs/Rubbervine.pdf |
4.04 |
Feeding tests have shown the leaves of rubber vine to be toxic to cattle, horses, goats and sheep (McGavin 1969, Everist 1974). Horses are particularly susceptible; toxic effects follow after consumption of only 0.03-0.06% of their body weight (McGavin 1969, Cook et al. 1990). [effects found in feeding trials, not in nature - it seems to be unpalatable under normal conditions, see 4.04] |
http://www.nrme.qld.gov.au/pests/psas/pdfs/Rubbervine.pdf |
4.05 |
Acrostalagmus aphidum: Puerto Rico; Virgin Islands
[generalist] |
Farr, D.F., Rossman, A.Y., Palm, M.E., & McCray, E.B. (n.d.) Fungal Databases, Systematic Botany & Mycology Laboratory, ARS, USDA. Retrieved July 7, 2004, from http://nt.ars-grin.gov/fungaldatabases/ |
4.06 |
(1) "Contact with all parts of the plant can cause
dermatitis (Hardin and Arena 1974)." |
(1) http://bodd.cf.ac.uk/index.html (2) Klackenberg, J. (2001) Revision of the genus Cryptostegia R. Br. (Apocynaceae, Periplocoideae). Adansonia, 2001, Vol. 23, No. 2, pp. 205-218, 20 ref. URL: http://www.mnhn.fr/publication/adanson/a01n2a3.pdf (3)http://www.allergenica.com/Details.asp?PLANTID=52 |
4.07 |
no evidence [grandiflora forms thickets that can be burned, but no evidence for madagascariensis] |
|
4.08 |
"It has been found from sea level up to 700 m alt., usually in full sun. It grows in dry forest (e.g. Didiereaceae, Euphorbia), savannah, tsingy, disturbed grazed grassland, on lateritic soil and sand, often on river beds." [probably not, only found in places with ample sun exposure] |
Klackenberg, J. (2001) Revision of the genus Cryptostegia R. Br. (Apocynaceae, Periplocoideae). Adansonia, 2001, Vol. 23, No. 2, pp. 205-218, 20 ref. URL: http://www.mnhn.fr/publication/adanson/a01n2a3.pdf |
4.09 |
"It grows... on lateritic soil and sand, often on river beds." [yes, lateritic soil is nutrient poor, rich of clay (2)] |
(1) Klackenberg, J. (2001) Revision of the genus
Cryptostegia R. Br. (Apocynaceae, Periplocoideae). Adansonia, 2001, Vol. 23,
No. 2, pp. 205-218, 20 ref. URL: http://www.mnhn.fr/publication/adanson/a01n2a3.pdf |
4.1 |
"Woody liana to shrub with scrambling branches, usually 2-3 m high and self-supporting but sometimes climbing up to 10 m high" |
Klackenberg, J. (2001) Revision of the genus Cryptostegia R. Br. (Apocynaceae, Periplocoideae). Adansonia, 2001, Vol. 23, No. 2, pp. 205-218, 20 ref. URL: http://www.mnhn.fr/publication/adanson/a01n2a3.pdf |
4.11 |
impedes access of stock to water and hinders mustering. [grandiflora; don't know if madagascariensis does the same] |
http://www.nrme.qld.gov.au/pests/psas/pdfs/Rubbervine.pdf |
4.12 |
"It has been found from sea level up to 700 m alt., usually in full sun. It grows in dry forest (e.g. Didiereaceae, Euphorbia), savannah, tsingy, disturbed grazed grassland, on lateritic soil and sand, often on river beds." |
Klackenberg, J. (2001) Revision of the genus Cryptostegia R. Br. (Apocynaceae, Periplocoideae). Adansonia, 2001, Vol. 23, No. 2, pp. 205-218, 20 ref. URL: http://www.mnhn.fr/publication/adanson/a01n2a3.pdf |
5.01 |
"Woody liana to shrub with scrambling branches, usually 2-3 m high and self-supporting but sometimes climbing up to 10 m high" |
Klackenberg, J. (2001) Revision of the genus Cryptostegia R. Br. (Apocynaceae, Periplocoideae). Adansonia, 2001, Vol. 23, No. 2, pp. 205-218, 20 ref. URL: http://www.mnhn.fr/publication/adanson/a01n2a3.pdf |
5.02 |
Asclepiadaceae |
|
5.03 |
"Woody liana to shrub with scrambling branches, usually 2-3 m high and self-supporting but sometimes climbing up to 10 m high" |
Klackenberg, J. (2001) Revision of the genus Cryptostegia R. Br. (Apocynaceae, Periplocoideae). Adansonia, 2001, Vol. 23, No. 2, pp. 205-218, 20 ref. URL: http://www.mnhn.fr/publication/adanson/a01n2a3.pdf |
5.04 |
"C. madagascariensis is present in southern Florida in the Keys and in a few counties on the coast of south western Florida (PLANTS 2001). C. madagascariensis is listed by the Florida Exotic Pest Plant Council as a category II pest plant (FLEPPC 1999). These are species that have shown a potential to disrupt native plant communities." [invade natural habitat] |
http://www.hear.org/starr/hiplants/reports/html/cryptostegia_spp.htm |
6.01 |
"Cryptostegia spp. can propagate by seeds, which are approximately 95% viable " |
|
6.02 |
AB: The genus Cryptostegia R. Br. comprises two species, both of which are endemic to Madagascar. One species, C. grandiflora Roxb. ex R. Br., is widely naturalised in tropical regions of the world. The other species, C. madagascariensis Bojer ex Decne., comprises three varieties, of which C. madagascariensis var. glaberrima (Hochreutiner) J. Marohasy and P. Forster is a new combination [.tbd. C. glaberrima] and C. madagascariensis var. septentrionalis J. Marohasy and P. Forster is newly described. Interspecific hybrids occur in a narrow zone where the two species are sympatric. |
http://www.hear.org/starr/hiplants/reports/html/cryptostegia_spp.htm |
6.03 |
Rubber vine is insect pollinated but and in Queensland pollination has not been observed, although viable seed is produced (Tomley 1995a). [chracteristics of C. grandiflora] |
http://www.nrme.qld.gov.au/pests/psas/pdfs/Rubbervine.pdf |
6.04 |
(1)Xylocopa spp. (carpenter bees); Batocnema coquereli (hawkmoth);
Madagascar Hippotion saclavorum (hawkmoth); Nephele comma (hawkmoth) |
(1)http://www.uni-bayreuth.de/departments/planta2/research_wgl/pollina/as_pol_d.html (2)http://www.nrme.qld.gov.au/pests/psas/pdfs/Rubbervine.pdf |
6.05 |
no evidence |
|
6.06 |
(1) "Plants can begin to reproduce (flowering) after about
200 days and seeds remain viable for approximately 12 months (Russell
2001)." [description of Cryptostegia species as a whole] |
(1) http://www.hear.org/starr/hiplants/reports/html/cryptostegia_spp.htm (2) http://www.nrme.qld.gov.au/pests/psas/pdfs/Rubbervine.pdf |
6.07 |
no evidence |
|
7.01 |
"C. grandiflora and C. madagascariensis, are widely cultivated" |
http://www.hear.org/starr/hiplants/reports/html/cryptostegia_spp.htm |
7.02 |
no evidence |
|
7.03 |
(1) "Follicles (5-)7-9 × 1-3 cm, glabrous to finely
pubescent. Seeds 5-8 mm long; hairs 2-3 cm long. |
(1) Klackenberg, J. (2001) Revision of the genus
Cryptostegia R. Br. (Apocynaceae, Periplocoideae). Adansonia, 2001, Vol. 23,
No. 2, pp. 205-218, 20 ref. URL: http://www.mnhn.fr/publication/adanson/a01n2a3.pdf |
7.04 |
(1)Numerous seed with tufts of silky hairs help disperse the seeds in the wind.(2)often on river beds [habitat provides opportunity for floating seeds] |
(1)http://www.hear.org/starr/hiplants/reports/html/cryptostegia_spp.htm (2)Klackenberg, J. (2001) Revision of the genus Cryptostegia R. Br. (Apocynaceae, Periplocoideae). Adansonia, 2001, Vol. 23, No. 2, pp. 205-218, 20 ref. URL: http://www.mnhn.fr/publication/adanson/a01n2a3.pdf |
7.05 |
"Follicles (5-)7-9 × 1-3 cm, glabrous to finely pubescent. Seeds 5-8 mm long; hairs 2-3 cm long." |
Klackenberg, J. (2001) Revision of the genus Cryptostegia R. Br. (Apocynaceae, Periplocoideae). Adansonia, 2001, Vol. 23, No. 2, pp. 205-218, 20 ref. URL: http://www.mnhn.fr/publication/adanson/a01n2a3.pdf |
7.06 |
no evidence |
|
7.07 |
no evidence of ingestion |
|
7.08 |
(1) Curtis (1946) also found of 1100 plants per hectare
produced 15 fruits per plant per annum [1.65 fruit per square meter], while
densities of 12000-29000 plants per hectare produced an average of 1 fruit
per plant per annum [0.34- 0.83 fruits per square meter]. Curtis (1946)
found the average time for fruit development from flowers to ripe open fruit
was 173 days. The average seed weight was 9 mg with 668 seeds per fruit
while 340-840 seeds per fruit have been recorded in Charters Towers (Vitelli
1987 unpublished report). A study in Haiti demonstrated that 3000 grafted
Cryptostegia grandiflora plants per acre produced 8,061,000 flowers per acre
per year and 182,700 fruit per acre per year (a flower to fruit ratio of
44:1) but in Queensland the flower to fruit ratio varies between around 6 to
150:1 depending on rainfall and soil type [description of C. grandiflora,
116 to 1386 seeds per square meter] |
(1) http://www.nrme.qld.gov.au/pests/psas/pdfs/Rubbervine.pdf (2) Klackenberg, J. (2001) Revision of the genus Cryptostegia R. Br. (Apocynaceae, Periplocoideae). Adansonia, 2001, Vol. 23, No. 2, pp. 205-218, 20 ref. URL: http://www.mnhn.fr/publication/adanson/a01n2a3.pdf |
8.01 |
AB: "In the field, the most rapid decline in viability
occurred under natural rainfall conditions, i.e. with no viable rubber vine
seeds remaining in the soil seed bank after one year, irrespective of the
burial depth. In contrast, viability of seed lots under conditions where
rainfall was excluded averaged 68, 29 and 0% after 1, 2 and 3 years,
respectively. Under dry storage, viability of 1-year-old seed was extremely
high (99%) and not significantly different to that of freshly collected
seed. In comparison, viability of 9- and 11-year-old seeds averaged 87%, and
only 20% of 20-year-old seeds remained viable. Almost all viable seeds had
sufficient vigour to develop into seedlings, irrespective of their age." |
Bebawi, F. F. , Campbell, S. D. , Lindsay, A. M. (2003) Effects of burial and age on viability of rubber vine (Cryptostegia grandiflora) seeds. Plant Protection Quarterly, 2003, Vol. 18, No. 4, pp. 147-151, 13 ref. |
8.02 |
(1) Probably yes, several herbicides successfully control
rubber vine (C. grandiflora, an invasive congeneric species) |
(1) Vitelli, J. S. , Mayer, R. J. , Jeffrey, P. L. (1994) Foliar application of 2,4-D/picloram, imazapyr, metsulfuron, triclopyr/picloram, and dicamba kills individual rubber vine (Cryptostegia grandiflora) plants. Tropical Grasslands, 1994, Vol. 28, No. 2, pp. 120-126, 20 ref. (2) http://www.hear.org/starr/hiplants/reports/pdf/cryptostegia_spp.pdf |
8.03 |
(1) " It has been found from sea level up to 700 m alt.,
usually in full sun. It grows in dry forest (e.g. Didiereaceae, Euphorbia),
savannah, tsingy, disturbed grazed grassland, on lateritic soil and sand,
often on river beds." [probabaly yes, grow in dry, fire-prone habitats] |
(1) Klackenberg, J. (2001) Revision of the genus Cryptostegia R. Br. (Apocynaceae, Periplocoideae). Adansonia, 2001, Vol. 23, No. 2, pp. 205-218, 20 ref. URL: http://www.mnhn.fr/publication/adanson/a01n2a3.pdfExotic shrubs are significant invaders of the tropical woodlands of northern Australia. They cause problems for pastoral industries and are likely to induce significant change in woodland communities. A single fire in the middle of the dry season affected the survival and vegetative growth of two important shrub species, Cryptostegia grandiflora and Ziziphus mauritiana, at a site in Queensland. The fire killed about 96% of small plants (height < 100 cm), 80% of medium-sized plants and 45% of large plants (height > 200 cm) of C. grandiflora. However, only about 10% of small Z. mauritiana were killed. Most plants of Z. mauritiana resprouted vigorously within three months of the fire. Effects on the vegetative phenology of C. grandiflora persisted until 10 months after the fire, but by four months after the |
8.04 |
Biological control: No biological controls have been introduced yet to Hawai'i. |
http://www.hear.org/starr/hiplants/reports/html/cryptostegia_spp.htm |
8.05 |
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