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Species
Melinis minutiflora Beauv.
IUCN
NCBI
EOL Text
"Perennial herbs; culms slender, erect or geniculate up to 1 m tall, rooting from the lower nodes; nodes villous. Leaf blades linear-lanceolate, rounded at base, acuminate, 10-15 x 0.6-1cm, densely hairy with simple and tubercle- based hairs; sheath striate, with long tubercle based hairs especially towards the apex; ligule a rim of long hairs. Panicle 10-15 cm long; branches 4-6 cm long. Spikelets pedicelled, 1.75-2 mm long, awned, on zig-zag, 2-3 mm long scabrid pedicels; glumes unequal, membraneous, the lower a minute hyaline scale, the upper 1.75-2 mm long, prominently 7-nerved, sometimes bifid at apex with a short awn. Lower floret sterile; lemma 1.75-2 mm long, 5-nerved, notched at the tip, awned, awn up to 1 cm long; palea absent. Upper floret bisexual; lemma & palea hyaline, c. 1.5 mm long. Stamens 3; anthers 0.75 mm long, dark brown in colour."
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More info for the terms: cover, mesic, shrub, succession
Molasses grass is shade-intolerant [11] and thrives in open, disturbed areas [4,19,34] such as burned sites [13,29,45]. Molasses grass is not tolerant of heavy grazing [32,49]. Establishment and spread of molasses grass in native plant communities in Hawaii may alter succession in invaded communities [1].
At Hawai`i Volcanoes National Park, nonnative bush beardgrass (Schizachyrium condensatum) is abundant in unburned, seasonally dry woodlands [11]. Following fire, molasses grass partially replaces bush beardgrass. In the absence of fire, molasses grass establishment in bush beardgrass communities is depressed due to low light levels. In a controlled experiment, molasses grass established in unburned woodlands following the removal of bush beardgrass. Additionally, when molasses grass seedlings established in bush beardgrass communities or when bush beardgrass and molasses grass seedlings emerge on the same site simultaneously, molasses grass came to dominate the site [11].
Lowland dry shrublands in Hawaii are relatively intolerant of fire and are often replaced by nonnative-dominated communities after fire. See FIRE REGIMES for more information on the role of molasses grass in these changes. In Venezuela, Baruch and others [3,4] suggest that the spread of molasses grass was likely aided by the burning of savannas in the Coastal Mountains to improve pastures. Molasses grass may alter the successional dynamics of shrublands in Hawaii [1,49]. Molasses grass "appears capable of displacing" many of the native lowland mesic shrublands in Hawaii [49]. On the upper leeward slopes of Moloka`i Island, monospecific molasses grass stands and shrub (pūkiawe (Styphelia tameiameiae) and `a`ali`i) stands with molasses grass had significantly greater soil nitrogen pools than uninvaded shrublands (P<0.05). The increase of nitrogen may promote further establishment of molasses grass and other nonnatives in native Hawaiian shrublands that are normally nutrient-poor [1]. Conversion of Hawaiian woodlands to grasslands via fires appears to increase nitrogen available to plants. In a molasses grass-dominated grassland converted via fire from a `ōhi`a woodland in Hawai`i Volcanoes National Park, net nitrogen mineralization was 3.4 times greater than in an unburned `ōhi`a woodland [27].
Molasses grass can tolerate low grazing pressure, giving it an advantage over less tolerant species [33]. However, molasses grass is intolerant of heavy grazing, and changes in dominance have been observed with changes in grazing pressure. Beginning in the 1970s in Hawai`i Volcanoes National Park, there has been a shift in the central coastal lowland grasslands from dominance of annual and short-statured perennial grasses to dominance of mid-sized, fire-tolerant, perennial grasses including molasses grass [32]. Following the removal of feral goats from the park between 1971 and 1975 [31,33], Japanese lovegrass (Eragrostis amibilis), golden false beardgrass (Chrysopogon aciculatus), Bermudagrass (Cynodon dactylon), and native pili grass were replaced by nonnative thatching grass (Hyparrhenia spp.) and molasses grass. In 1970 there were approximately 14,000 goats in the park and by 1980 there were fewer than 200 [44]. At Pu'u Kaone in Hawai`i Volcanoes National Park, goat removal led to molasses grass dominance. In a 5-year period, molasses grass became a dominant species with 25% cover in a formerly closed golden false beardgrass-Bermudagrass community [32]. Molasses grass grasslands subjected to heavy grazing by axis deer on Lāna'i are "becoming barren, eroded landscapes" [49].
This species has been introduced into many tropical countries for fodder (Molasses Grass).
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Rights holder/Author | eFloras.org Copyright © Missouri Botanical Garden |
Source | http://www.efloras.org/florataxon.aspx?flora_id=2&taxon_id=200025690 |
Muhlenbergia brasiliensis Steudel; Panicum melinis Trinius, nom illeg. superfl.; P. minutiflorum (P. Beauvois) Raspail; Suardia picta Schrank; Tristegis glutinosa Nees.
License | http://creativecommons.org/licenses/by-nc-sa/3.0/ |
Rights holder/Author | eFloras.org Copyright © Missouri Botanical Garden |
Source | http://www.efloras.org/florataxon.aspx?flora_id=2&taxon_id=200025690 |
More info for the term: breeding system
Molasses grass may reproduce from seeds [5,11,21,34,46], stolons [5,27,28,33], basal meristems [45], or rhizomes [13,21,46].
At the time of this writing (2008), there is no information on molasses grass breeding system, pollination, seedling establishment and growth, or seed production.
Seed dispersal: Molasses grass seeds are dispersed by wind [38].
Seed banking: Molasses grass seeds can occur in the soil seed bank [11,46]; however, seed longevity is unknown. Tunison and others [46] found that molasses grass seed is "ubiquitous" in the soil of unburned `ōhi`a woodlands in Hawaii. Near Kipuka Nene, Hawai`i Volcanoes National Park, D'Antonio and others [11] extracted molasses grass seeds from soil samples 3 inches (8 cm) deep and 1.8 inches (4.5 cm) wide in October 1991 and February and June 1992. Following extractions, molasses grass seeds were planted in containers and seedling emergence was measured for 3 months following each of the 3 extraction dates. Seed bank samples were taken from an unburned woodland, a woodland burned in 1970, a woodland burned in 1987, and a site burned both in 1970 and 1987. In general, seedling emergence was significantly greater from seeds extracted from burned sites (P<0.05) [11].
Mean number of molasses grass seedlings emerging from soil samples in unburned and burned woodlands near Kipuka Nene, Hawai`i Volcanoes National Park [11] |
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Habitat | Collection date | ||
October 1991 | February 1992 | June 1992 | |
Unburned | 1.15a* | 5.60a | 1.50a |
Burned in 1987 | 2.60b | 15.25a,b | 8.10b |
Burned in 1970 | 10.00b | 25.40b | 8.10b |
Burned in 1970 and 1987 | 3.25b | 17.90b | 5.80a,b |
*Different lowercase letters in the same column indicate a significant difference (P<0.05) |
Germination: Molasses grass seed germination is better with increasing sunlight, is largely unaffected by heat [11], and is promoted by elevated CO2 [5]. In a controlled outdoor experiment, molasses grass seed germination and growth were significantly better with 49% or more sunlight (P<0.05). At 1%, 3%, and 33% of full sunlight, average (SE) molasses grass seed germination rates were 10.4% (1.8), 12.7% (2.5), and 13.9% (1.8), respectively. At 49% and 100% full sunlight, germination rates were 27.1% (2.6) and 25.5% (3.1), respectively [11].
The germination rate of heat-treated molasses grass seeds was not significantly different than that of unheated seeds (P<0.80) [11]. The average germination rate of molasses grass seeds heated for 4 minutes at temperatures ranging from 140 °F to 250 °F (60 °C-120 °C) was 18.8% [11].
Vegetative regeneration: Molasses grass regenerates vegetatively by stolons [5,27,28,33], basal meristems [45], and rhizomes [13,21,46].
Isotype for Melinis purpurea Stapf & C.E. Hubb.
Catalog Number: US 101694
Collection: Smithsonian Institution, National Museum of Natural History, Department of Botany
Verification Degree: Status verified by specimen annotations only
Preparation: Pressed specimen
Collector(s): A. Stolz
Locality: Nördl. Nyassaland., Tanzania, Africa
- Isotype: Stapf, O. & Hubbard, C. E. 1926. Bull. Misc. Inform. Kew. 1926: 444.
License | http://creativecommons.org/licenses/by/3.0/ |
Rights holder/Author | This image was obtained from the Smithsonian Institution. Unless otherwise noted, this image or its contents may be protected by international copyright laws. |
Source | http://collections.mnh.si.edu/search/botany/?irn=11234740 |
More info on this topic.
More info for the term: hemicryptophyte
RAUNKIAER [35] LIFE FORM:
Hemicryptophyte
molasses grass
Brazilian stink grass
calinguero
Wynne grass
greasy grass
Type collection for Melinis minutiflora var. mutica Hack.
Catalog Number: US 101664
Collection: Smithsonian Institution, National Museum of Natural History, Department of Botany
Verification Degree: Status verified by specimen annotations only
Preparation: Pressed specimen
Collector(s): J. Hildebrandt
Locality: Central Madagascar: Jmerima., Madagascar, Africa
- Type collection: Hackel, E. 1884. Sitzungsber. Kaiserl. Akad. Wiss., Math.-Naturwiss. Cl., Abt. 1. 89: 126.
License | http://creativecommons.org/licenses/by/3.0/ |
Rights holder/Author | This image was obtained from the Smithsonian Institution. Unless otherwise noted, this image or its contents may be protected by international copyright laws. |
Source | http://collections.mnh.si.edu/search/botany/?irn=11232604 |