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SPECIES:  Hepatica nobilis var. acuta
Sharplobe hepatica. Image by Jennifer Anderson, hosted by the USDA-NRCS PLANTS Database.

 


Introductory

SPECIES: Hepatica nobilis var. acuta
AUTHORSHIP AND CITATION: Pavek, Diane S. 1992. Hepatica nobilis var. acuta. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Available: https://www.fs.usda.gov/database/feis/plants/forb/hepnoba/all.html []. Revisions: On 16 May 2016, the scientific name of this taxon was changed in FEIS from: Hepatica acutiloba to: Hepatica nobilis var. acuta. Images were also added.
ABBREVIATION: HEPNOBA SYNONYMS: Hepatica acutiloba DC. [6,16,21] Hepatica acutiloba forma acutiloba R. Hoffm. Hepatica acutiloba f. diversiloba Raymond Hepatica acutiloba f. albiflora R. Hoffm. Hepatica acutiloba f. rosea R. Hoffm. Hepatica acutiloba f. plena Fern. [6] NRCS PLANT CODE: HENOA COMMON NAMES: sharplobe hepatica sharp-lobed liverleaf TAXONOMY: The scientific name of sharplobe hepatica is Hepatica nobilis Schreb. var. acuta. (Pursh) Steyerm. [19,21]. LIFE FORM: Forb FEDERAL LEGAL STATUS: No special status OTHER STATUS: NO-ENTRY


DISTRIBUTION AND OCCURRENCE

SPECIES: Hepatica nobilis var. acuta
GENERAL DISTRIBUTION: Sharplobe hepatica is native to the Northeast and Southeast. It is found in most states east of the Mississippi River. Extending from Ontario, Quebec, and Maine [8,15,18], it proceeds south through the eastern United States to Missouri, Georgia, and Alabama [9,13,16].
Distribution of sharplobe hepatica. Map courtesy of USDA, NRCS. 2018. The PLANTS Database. National Plant Data Team, Greensboro, NC [2018, May 16] [21].
ECOSYSTEMS: 
   FRES13  Loblolly - shortleaf pine
   FRES14  Oak - pine
   FRES15  Oak - hickory
   FRES16  Oak - gum - cypress
   FRES17  Elm - ash - cottonwood
   FRES18  Maple - beech - birch


STATES: 
     AL  CT  GA  ID  IL  IA  KY  ME  MA  MI
     MN  NH  NJ  NY  NC  OH  PA  RI  SC  TN
     VT  VA  WV  WI  ON  PQ


BLM PHYSIOGRAPHIC REGIONS: 
None


KUCHLER PLANT ASSOCIATIONS: 
   K099  Maple - basswood forest
   K102  Beech - maple forest
   K103  Mixed mesophytic forest
   K106  Northern hardwoods
   K107  Northern hardwoods - fir forest


SAF COVER TYPES: 
    16  Aspen
    24  Hemlock - yellow birch
    25  Sugar maple - beech
    26  Sugar maple - basswood
    27  Sugar maple
    28  Black cherry - maple
    60  Beech - sugar maple
   108  Red maple
   109  Hawthorn


SRM (RANGELAND) COVER TYPES: 
801 Savanna
805 Riparian


HABITAT TYPES AND PLANT COMMUNITIES: 
Sharplobe hepatica is listed as a dominant or indicator species in this 
vegeation classification: 

Field guide to forest habitat types of northern Wisconsin [10].

MANAGEMENT CONSIDERATIONS

SPECIES: Hepatica nobilis var. acuta
IMPORTANCE TO LIVESTOCK AND WILDLIFE: NO-ENTRY PALATABILITY: NO-ENTRY NUTRITIONAL VALUE: No food value is listed for sharplobe hepatica. A lipid-rich eliasome that attracts ants and rodent herbivores is attached to seeds [17]. COVER VALUE: NO-ENTRY VALUE FOR REHABILITATION OF DISTURBED SITES: Projects using sharplobe hepatica have not been found in the literature. However, as a rhizomatous perennial, it could be used as a soil stabilizer in shaded habitats. OTHER USES AND VALUES: NO-ENTRY OTHER MANAGEMENT CONSIDERATIONS: NO-ENTRY

BOTANICAL AND ECOLOGICAL CHARACTERISTICS

SPECIES: Hepatica nobilis var. acuta
GENERAL BOTANICAL CHARACTERISTICS: Sharplobe hepatica is a small rhizomatous perennial, 2 to 7 inches (5-18 cm) tall [18]. Three leaves arise from the plant base. Leaves are simple but deeply lobed. The three leaves are longer than they are wide, with acutely pointed lobe tips and indented (cordate) bases [6,15,18]. Long, hairy flowerstalks have a single small (0.05-0.1 inch [12-25 mm]) flower. Achenes are very hairy. RAUNKIAER LIFE FORM: Hemicryptophyte Geophyte REGENERATION PROCESSES: Sharplobe hepatica sprouts from short rhizomes, producing small colonies [15,18]. Mature achenes form aggregates. Seeds are carried away from the parent plant by ants and rodents. Ant dispersal is most successful for establishment in young sparse populations. Seedling establishment is low in older dense populations of sharplobe hepatica [17]. Seeds have epicotyl dormancy which requires a warm stratification [1]. This is followed by a cold stratification of 2 to 3 months before cotyledons emerge [1]. SITE CHARACTERISTICS: Sharplobe hepatica is found on topography that varies from gently rolling hills to bluffs and outcroppings [3]. It occurs on soils of low fertility and low moisture-holding capacity (e.g. sandy loam) to calcareous moist upland woods [3,8]. Sharplobe hepatica is often found on north-facing wooded slopes [8]. Species associated with sharplobe hepatica are those found in upland mesic deciduous forests. Sugar maple (Acer saccharum) is often dominant with red elm (Ulmus rubra) and basswood (Tilia americana) [20]. Of the numerous herbaceous species, the dominant plants are eastern springbeauty (Claytonia virginica), catchweed bedstraw (Galium aparine), recurved wakerobin (Trillium recurvatum), common mayapple (Podophyllum pedatum), and black snakeroot (Sanicula gregaria) [20]. SUCCESSIONAL STATUS: Sharplobe hepatica occurs in late-intermediate to early climax forests of sugar maple (Acer saccharum), basswood (Tilia americana), yellow birch (Betula alleghaniensis), and white ash (Fraxinus americana) [4,20]. Daubenmire [4] also reported sharplobe hepatica present in subclimax associations of red oak (Quercus rubra), white oak (Quercus alba), and aspen (Populus tremuloides). Although an early vernal species, it is shade tolerant. It occurs infrequently; Brundrett and Kendrick [3] reported 0.22 percent importance value for sharplobe hepatica in Ontario forests. SEASONAL DEVELOPMENT: Thick leaves are kept through the winter on this clonal perennial, allowing photosynthesis to begin quickly in the spring before the canopy closes [3]. With this physiological jump-start, sharplobe hepatica flowers from February to June throughout its range [6,8,9,13,16,18]. After flowering, the overwintering leaves become senescent, and new leaves are produced. The new leaves are more shade tolerant and, therefore, more efficient at light harvesting [3]. Seeds mature approximately 1 month after flowering [17]. Sharplobe hepatica remains green when all other herbs have senesced in the fall.

FIRE ECOLOGY

SPECIES: Hepatica nobilis var. acuta
FIRE ECOLOGY OR ADAPTATIONS: Occurring in mixed mesophytic forest, sharplobe hepatica has evolved with fire. The degree of resistance sharplobe hepatica has to fire depends upon the protection its caudex and rhizomes receive from soil cover. FIRE REGIMES: Find fire regime information for the plant communities in which this species may occur by entering the species name in the FEIS home page under "Find Fire Regimes". POSTFIRE REGENERATION STRATEGY: Rhizomatous herb, rhizome in soil Secondary colonizer - off-site seed

FIRE EFFECTS

SPECIES: Hepatica nobilis var. acuta
IMMEDIATE FIRE EFFECT ON PLANT: Fire effects have not been studied on sharplobe hepatica. It is probably top-killed by fire. Rhizomes probably would survive. Seedlings most likely would be killed. If the lipid sack (eliasome) attached to the seed burns, the seed probably dies. PLANT RESPONSE TO FIRE: Fire severity and rooting depth of caudex and rhizomes control the recovery of sharplobe hepatica. Surviving rhizomes probably sprout and produce leaves postfire. Sharplobe hepatica grows vigorously in sparsely vegetated areas with freed nutrients (e.g., ant hills high in nitrogen and phosphorus) [17]. It probably will flower and produce seed in the first postfire year. Long-term postfire recovery should be fairly successful. Sharplobe hepatica reproduces vegetatively by short rhizomes, ensuring on-site colony growth. Sexual reproduction results in seeds that are readily transported by ants and rodents, which ensures wide areas of dispersal [17]. FIRE MANAGEMENT CONSIDERATIONS: NO-ENTRY

REFERENCES

SPECIES: Hepatica nobilis var. acuta
REFERENCES: 1. Baskin, Jerry M.; Baskin, Carol C. 1985. Epicotyl dormancy in seeds of Cimicifuga racemosa and Hepatica acutiloba. Bulletin of the Torrey Botanical Club. 112(3): 253-257. [18960] 2. Bernard, Stephen R.; Brown, Kenneth F. 1977. Distribution of mammals, reptiles, and amphibians by BLM physiographic regions and A.W. Kuchler's associations for the eleven western states. Tech. Note 301. Denver, CO: U.S. Department of the Interior, Bureau of Land Management. 169 p. [434] 3. Brundrett, Mark C.; Kendrick, Bryce. 1988. The mycorrhizal status, root anatomy, and phenology of plants in a sugar maple forest. Canadian Journal of Botany. 66(6): 1153-1173. [14483] 4. Daubenmire, Rexford F. 1936. The "big woods" of Minnesota: its structure, and relation to climate, fire, and soils. Ecological Monographs. 6(2): 233-268. [2697] 5. Eyre, F. H., ed. 1980. Forest cover types of the United States and Canada. Washington, DC: Society of American Foresters. 148 p. [905] 6. Fernald, Merritt Lyndon. 1950. Gray's manual of botany. [Corrections supplied by R. C. Rollins]. Portland, OR: Dioscorides Press. 1632 p. (Dudley, Theodore R., gen. ed.; Biosystematics, Floristic & Phylogeny Series; vol. 2). [14935] 7. Garrison, George A.; Bjugstad, Ardell J.; Duncan, Don A.; [and others]. 1977. Vegetation and environmental features of forest and range ecosystems. Agric. Handb. 475. Washington, DC: U.S. Department of Agriculture, Forest Service. 68 p. [998] 8. Gleason, Henry A. 1952. Illustrated flora of the northeastern United States and adjacent Canada. Vol. 2. Choripetalous Dicotyledoneae. Lancaster, PA: Lancaster Press, Inc. 655 p. [18962] 9. Jones, G. N.; Fuller, G. D. 1955. Vascular plants of Illinois. Urbana, IL: University of Illinois Press. 593 p. [18964] 10. Kotar, John; Kovach, Joseph A.; Locey, Craig T. 1988. Field guide to forest habitat types of northern Wisconsin. Madison, WI: University of Wisconsin, Department of Forestry; Wisconsin Department of Natural Resources. 217 p. [11510] 11. Kuchler, A. W. 1964. Manual to accompany the map of potential vegetation of the conterminous United States. Special Publication No. 36. New York: American Geographical Society. 77 p. [1384] 12. Stickney, Peter F. 1989. Seral origin of species originating in northern Rocky Mountain forests. Unpublished draft on file at: U.S. Department of Agriculture, Forest Service, Intermountain Research Station, Fire Sciences Laboratory, Missoula, MT; RWU 4403 files. 7 p. [20090] 13. Radford, Albert E.; Ahles, Harry E.; Bell, C. Ritchie. 1968. Manual of the vascular flora of the Carolinas. Chapel Hill, NC: The University of North Carolina Press. 1183 p. [7606] 14. Raunkiaer, C. 1934. The life forms of plants and statistical plant geography. Oxford: Clarendon Press. 632 p. [2843] 15. Scoggan, H. J. 1978. The flora of Canada. Ottawa, Canada: National Museums of Canada. (4 volumes). [18143] 16. Seymour, Frank Conkling. 1982. The flora of New England. 2d ed. Phytologia Memoirs 5. Plainfield, NJ: Harold N. Moldenke and Alma L. Moldenke. 611 p. [7604] 17. Smith, Brent H.; Forman, Paul D.; Boyd, Amy E. 1989. Spatial patterns of seed dispersal and predation of two myrmecochorous forest herbs. Ecology. 70(6): 1649-1656. [15861] 18. Steyermark, J. A. 1963. Flora of Missouri. Ames, IA: Iowa State University Press. 1725 p. [18144] 19. Steyermark, J. A.; Steyermark, C. S. 1960. Hepatica in North America. Rhodora. 62: 223-232. [18965] 20. Struik, Gwendolyn J.; Curtis, J. T. 1962. Herb distribution in an Acer saccharum forest. American Midland Naturalist. 68(2): 285-296. [18966] 21. USDA Natural Resources Conservation Service. 2018. PLANTS Database, [Online]. U.S. Department of Agriculture, Natural Resources Conservation Service (Producer). Available: https://plants.usda.gov/. [34262]

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