Pacific Island Ecosystems at Risk (PIER)
RISK ASSESSMENT RESULTS: High risk, score: 15
|
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 |
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Stenotaphrum secundatum; St. Augustine grass |
Answer |
||
|
1.01 |
Is the species highly domesticated? |
y=-3, n=0 |
|
|
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 |
y |
|
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 |
n |
|
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 |
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 |
|
|
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 |
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 |
y |
|
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 |
y |
|
6.07 |
Minimum generative time (years) 1 year = 1, 2 or 3 years = 0, 4+ years = -1 |
See left |
1 |
|
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 |
y |
|
7.03 |
Propagules likely to disperse as a produce contaminant |
y=1, n=-1 |
|
|
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 |
|
|
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 |
|
|
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 |
y |
|
8.05 |
Effective natural enemies present locally (e.g. introduced biocontrol agents) |
y=-1, n=1 |
|
|
Total score: |
15 |
||
Supporting data:
|
Source |
Notes |
|
|
1.01 |
(1) Sauer, J. D. (1972) Revision of Stenotaphrum (Gramineae:
Paniceae) with attention to its historical geography. Brittonia, 1972,
Vol.24, No.2, pp.202-222, 10 ref. |
(1) AB: "S. secundatum includes fertile diploids and sterile
polyploids and is widely distributed in both forms." |
|
1.02 |
(1)Stefanak, M. (1985) Stenotaphrum secundatum a new adventive species in Greece. Zizaniologia, 1985, Vol.1, No.4, pp.243-245, 13 ref. (2)Hickman. Jepson Manual (3)Wunderlin, R. P. 1998, Guide to the vascular plants of Florida. Gainesville, University Press of Florida. |
(1) The morphological and biological characteristics and the geographical distribution of S. secundatum (Walter) O. Kuntze are described. The species was probably introduced into Greece along with the seeds of other lawn grass species and it has since spread. It is well adapted to warm, dry conditions. The possibility of it becoming a serious weed are considered. (2)Fields and roadsides of California (3) riverbanks, hammocks, disturbed sites, frequent |
|
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/var/apache/cgi-bin/npgs/html/taxon.pl?35523 (12 June 2002) |
Distributional range: |
|
2.02 |
||
|
2.03 |
(1) Horticopia A-Z.Horticopia, Inc., Purcellville, VA. ISBN
1-887215-07-7. |
(1) Hardiness Range 7B to 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/var/apache/cgi-bin/npgs/html/taxon.pl?35523 (12 June 2002) |
Distributional range: |
|
2.05 |
(1) Pares, R. D.; Gillings, M. R. (1990) Two new records of
diseases caused by potyviruses in Australia. Australasian Plant Pathology,
1990, Vol.19, No.2, pp.36-37, 18 ref. |
(1) Australia (2) Japan (3) Taiwan (4) Italy |
|
3.01 |
(1)Stefanak, M. (1985) Stenotaphrum secundatum a new adventive species in Greece. Zizaniologia, 1985, Vol.1, No.4, pp.243-245, 13 ref. (2)Hickman. Jepson Manual (3)Wunderlin, R. P. 1998, Guide to the vascular plants of Florida. Gainesville, University Press of Florida. |
(1) The morphological and biological characteristics and the geographical distribution of S. secundatum (Walter) O. Kuntze are described. The species was probably introduced into Greece along with the seeds of other lawn grass species and it has since spread. It is well adapted to warm, dry conditions. The possibility of it becoming a serious weed are considered. (2)Fields and roadsides of California (3) riverbanks, hammocks, disturbed sites, frequent |
|
3.02 |
no evidence |
|
|
3.03 |
Bacon, P., P.J. Terry, N. Waltham, & P.Castro S. (1997) An Electronic Atlas of World Weed and Invasive Plants. Version 1.0, 1997. A database based on the original work "A Geographical Atlas of World Weeds" by Holm et al 1979. |
It was listed as a common weed in Puerto Rico. |
|
3.04 |
http://www.boprc.govt.nz/www/green/weed32.htm |
Spreads strongly into coastal environments, especially on sand country. Deeply smothers the smaller native plants, and adversely affects the regeneration opportunities for coastal trees such as pohutukawa. |
|
3.05 |
no evidence |
|
|
4.01 |
Drake, R. & M. Griffiths eds. (1994) Manual of Grasses. Timber Press, Inc., Portland, Oregon, USA. 169 pp. p.143 |
no description of these traits |
|
4.02 |
Sutton, D. L.; Portier, K. M. (1989) Influence of allelochemicals and aqueous plant extracts on growth of duckweed. Journal of Aquatic Plant Management, 1989, Vol.27, pp.90-95, 22 ref. |
AB: " Extracts from green (alive when collected) and brown (dead when collected) Casuarina sp. needles, and leaves of Lantana camara and Stenotaphrum secundatum were also found to inhibit growth of the duckweed plants." |
|
4.03 |
no evidence |
|
|
4.04 |
(1) Nada, Y. (1985) Palatability and adaptability of 10
tropical grasses used as grazing pasture in Kyushu. Journal of the Japanese
Society of Grassland Science, 1985, Vol.30, No.4, pp.434-440, 14 ref. |
(1) AB: 10 tropical grass spp. which survived winter
conditions at Nishigoshi were studied for seasonal productivity and
palatability to cattle. Intake ratio of sorghum cv. Silk and Axonopus
compressus was high, of Stenotaphrum secundatum, Paspalum urvillei, Panicum
virgatum, Scizachyrium scoparium and P. distichum was medium and of Cynodon
dactylon cv. Common and Tifton and Eragrostis curvula was low. Percentage DM
and palatability were negatively correlated. All spp., except E. curvula had
good persistence. A. compressus, P. distichum and P. urvillei showed
increasing productivity during the summer, while both C. dactylon cv. showed
stable productivity and the remaining spp. showed decreasing productivity.
It was concluded that sorghum cv. Silk, A. compressus and P. urvillei were
the most promising grasses for Kyushu. |
|
4.05 |
(1) Nada, Y. (1985) Palatability and adaptability of 10
tropical grasses used as grazing pasture in Kyushu. Journal of the Japanese
Society of Grassland Science, 1985, Vol.30, No.4, pp.434-440, 14 ref. |
(1) AB: 10 tropical grass spp. which survived winter
conditions at Nishigoshi were studied for seasonal productivity and
palatability to cattle. Intake ratio of sorghum cv. Silk and Axonopus
compressus was high, of Stenotaphrum secundatum, Paspalum urvillei, Panicum
virgatum, Scizachyrium scoparium and P. distichum was medium and of Cynodon
dactylon cv. Common and Tifton and Eragrostis curvula was low. Percentage DM
and palatability were negatively correlated. All spp., except E. curvula had
good persistence. A. compressus, P. distichum and P. urvillei showed
increasing productivity during the summer, while both C. dactylon cv. showed
stable productivity and the remaining spp. showed decreasing productivity.
It was concluded that sorghum cv. Silk, A. compressus and P. urvillei were
the most promising grasses for Kyushu. |
|
4.06 |
(1) Reinert, J. A.; Read, J. C.; Engelke, M. C.; Colbaugh,
P. F.; Maranz, S. J.; Wiseman, B. R. (1998) Fall armyworm, Spodoptera
frugiperda resistance in turfgrass. Mededelingen - Faculteit Landbouwkundige
en Toegepaste Biologische Wetenschappen, Universiteit Gent, 1998, Vol.63,
No.2b, pp.467-471, 15 ref. |
(1) AB: "Spodoptera frugiperda is a primary pest of
turfgrass across the USA. Resistance to the pest has been identified among
several grass species that are used for turfgrass." " No resistance was
identified in two diploid B. dactyloides cv. Stampede and UCR-95, or among
other cultivars of Z. matrella or Z. japonica Steud or in Cynodon dactylon ,
C. dactylon x C. transvaalensis and Stenotaphrum secundatum ." |
|
4.07 |
no evidence |
|
|
4.08 |
possibly, if dry |
|
|
4.09 |
(1) Morton, S. J.; Engelke, M. C.; White, R. H. (1989)
Performance of four warm-season turfgrass genera cultured in dense shade.
II. Stenotaphrum secundatum . Progress Report - Texas Agricultural
Experiment Station, 1991, No.4881/4921, pp.49-50, 2 ref. |
(1) AB: All 26 entries of the 1989 National Turf Evaluation
Program St. Augustinegrass trial (including commercial cultivars Raleigh,
Sunclipse, Bitterblue and Floratam) plus 2 Dallas experimental lines were
planted during 1990 in parkland conditions with only 15% full sunlight.
Acceptable canopy density was observed for 6 of the experimental lines,
including DALSA8402 from Dallas, but none of the commercial lines could be
included in this category. FX313, FX33 and M1 showed an increase in density
by late summer. Excellent colour quality was noted for 7 lines, including
FX313, S67-72-107, Delmar and Jade. Generally, these grasses spread quickly
and extensively and 8 lines produced stolons of at least 30 cm. Poorest
development was observed for FX33, FX10 and Bitterblue. |
|
4.1 |
(1) Dudeck, A. E. (1990) Influence of planting method,
fertility program, cultivar, and soil type on St. Augustinegrass.
Proceedings of the Florida State Horticultural Society, 1990, Vol.103,
pp.355-360, 7 ref. |
(1) AB: "Different vegetative planting methods and spacings
were evaluated for the production of Stenotaphrum secundatum turf. The
greatest coverage rate on both clay and sand soils for cv. Floratam was
obtained with 4-inch plugs planted one ft apart (59 and 55%, respectively,
during the growing season). " |
|
4.11 |
Dehgan, B. (1998) Landscape Plants for Subtropical Climates. University Press of Florida., Gainesville, FL. 638pp. p.193 |
low-growing lawn grasses |
|
4.12 |
Dehgan, B. (1998) Landscape Plants for Subtropical Climates. University Press of Florida., Gainesville, FL. 638pp. p.193 |
low-growing lawn grasses |
|
5.01 |
terrestrial |
|
|
5.02 |
Poaceae |
|
|
5.03 |
grass |
|
|
5.04 |
low-growing lawn grasses |
|
|
6.01 |
no evidence |
|
|
6.02 |
(1) Sauer, J. D. (1972) Revision of Stenotaphrum (Gramineae:
Paniceae) with attention to its historical geography. Brittonia, 1972,
Vol.24, No.2, pp.202-222, 10 ref. |
(1) AB: "S. secundatum includes fertile diploids and sterile
polyploids and is widely distributed in both forms." |
|
6.03 |
no evidence |
|
|
6.04 |
no evidence |
|
|
6.05 |
wind |
|
|
6.06 |
Dehgan, B. (1998) Landscape Plants for Subtropical Climates. University Press of Florida., Gainesville, FL. 638pp. p.193 |
"Fruit: seed-like grain (caryopsis), sterile.[polyploidy cultivars] Spreads by thick fleshy stolons. Propasgation: sod of cultivars; new seeded types are not widely available and expensive." |
|
6.07 |
based on it being a fast growing grass |
|
|
7.01 |
lawn clippings/yeard waste |
|
|
7.02 |
(1) Mullen, B. F.; Shelton, H. M. (1996) Stenotaphrum
secundatum : a valuable forage species for shaded environments. Tropical
Grasslands, 1996, Vol.30, No.3, pp.289-297, 46 ref. |
(1) AB: "The potential of S. secundatum (buffalo grass) as a
forage species for ruminants is reviewed. Buffalo grass has been used as a
pasture grass to a limited extent in Florida, the Caribbean, the Pacific
Islands and Australia." |
|
7.03 |
Stefanak, M. (1985) Stenotaphrum secundatum a new adventive species in Greece. Zizaniologia, 1985, Vol.1, No.4, pp.243-245, 13 ref. |
AB: "The species was probably introduced into Greece along with the seeds of other lawn grass species and it has since spread." [intentional or unintentional?] |
|
7.04 |
no evidence |
|
|
7.05 |
no evidence |
|
|
7.06 |
no evidence |
|
|
7.07 |
no evidence |
|
|
7.08 |
no evidence |
|
|
8.01 |
(1)Dehgan, B. (1998) Landscape Plants for Subtropical Climates. University Press of Florida., Gainesville, FL. 638pp. p.193 (2)http://www.outsidepride.com/infostaugustinegrass.asp |
(1)"Fruit: seed-like grain (caryopsis), sterile.[polyploidy cultivars] Spreads by thick fleshy stolons. Propasgation: sod of cultivars; new seeded types are not widely available and expensive." (2)seed production is very poor. |
|
8.02 |
Dehgan, B. (1998) Landscape Plants for Subtropical Climates. University Press of Florida., Gainesville, FL. 638pp. p.194 |
"Fruit: seed-like grain (caryopsis), sterile.[polyploidy cultivars] Spreads by thick fleshy stolons. Propasgation: sod of cultivars; new seeded types are not widely available and expensive." |
|
8.03 |
(1)Meissner, R. (1976) The effect of dicamba on some turf grasses. Agroplantae, 1976, Vol.8, No.3, pp.63-64, 2 ref. (2)http://www.boprc.govt.nz/www/green/weed32.htm |
(1) Dicamba at 2.4 kg/ha applied as a single treatment or repeated after 4 weeks effectively controls the lawn weeds Alternanthera pungens and Brayulinea densa. In this study, dicamba was applied at 2 kg/ha in February and November to a range of turf grass species and cvs. in order to test their tolerance to the herbicide; observations were made from 3 days to 12 weeks after the application. "Of the other grasses, injury to Kikuyu (Pennisetum clandestinum) and St. Augustine (Stenotaphrum secundatum) was severe whereas on Swazi (Digitaria swazilandensis) and zoysia (Zoysia japonica) it was not significant. All the grasses recovered from the injury after varying lengths of time." (2)Spray with Roundup herbicide, 150 ml to 15 l Knapsack with addition of Pulse. |
|
8.04 |
tolerates frequent mowing, progation by vegetative fragments |
|
|
8.05 |
Murdoch, C. L.; Tashiro, H.; Tavares, J. W.; Mitchell, W. C. (1990) Economic damage and host preference of lepidopterous pests of major warm season turfgrasses of Hawaii. Proceedings of the Hawaiian Entomological Society, 1990, Vol.No. 30, pp.63-70, 11 ref. |
AB: "The effects of different larval densities of the 4 major lepidopterous pests of turfgrasses in Hawaii, Herpetogramma licarsisalis, Spodoptera mauritia, Agrotis ipsilon and Hylephila phylaeus", "All larvae of H. phylaeus fed St. Augustinegrass, Stenotaphrum secundatum, died after 7-8 days." |
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This page updated 8 March 2005