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Introductory

SPECIES: Thelypteris noveboracensis | New York Fern
ABBREVIATION : THENOV SYNONYMS : Dryopteris noveboracensis (L.) Gray Polypodium noveboracensis L. Aspidium noveboracensis Schrad. Aspidium conterminum strigosum Eaton Dryopteris contermina stigosa Underw. SCS PLANT CODE : THNO COMMON NAMES : New York fern TAXONOMY : The currently accepted scientific name of New York fern is Thelypteris noveboracensis (L.) Nieuwl. in the Polypodiaceae family [14]. There are two forms: T. n. noveboracensis forma noveboracensis and T. n. forma fragrans (Peck) Burnham [8,24]. The most commonly used synonym in the literature is Dryopteris novebaracensis. LIFE FORM : Fern or Fern Ally FEDERAL LEGAL STATUS : No special status OTHER STATUS : NO-ENTRY COMPILED BY AND DATE : S. A. Snyder, August 1993 LAST REVISED BY AND DATE : NO-ENTRY AUTHORSHIP AND CITATION : Snyder, S. A. 1993. Thelypteris noveboracensis. In: Remainder of Citation

DISTRIBUTION AND OCCURRENCE

SPECIES: Thelypteris noveboracensis | New York Fern
GENERAL DISTRIBUTION : New York fern is distributed from Newfoundland west to Ontario and south to Arkansas and Georgia [8]. It occurs throughout the New England and Atlantic coastal states and has been noted in some parts of Florida [14,24,25]. It is also found in Hawaii and some midwestern states [21]. ECOSYSTEMS : FRES10 White - red - jack pine FRES15 Oak - hickory FRES16 Oak - gum - cypress FRES17 Elm - ash - cottonwood FRES18 Maple - beech - birch FRES14 Oak - pine STATES : AL AR CT FL GA HI IL IN KY ME MD MA MI MS NH NJ NY NC OH PA RI SC TN VT VA WV NB NF NS ON PQ ADMINISTRATIVE UNITS : ACAD ALPO BISO CATO COLO CUGA CUVA DEWA GWMP GRSM HOBE INDU JOFL MACA MORR NERI OBRI PRWI RICH ROCR SARA SHEN SHIL SLBE BLM PHYSIOGRAPHIC REGIONS : NO-ENTRY KUCHLER PLANT ASSOCIATIONS : K098 Northern floodplain forest K099 Maple - basswood forest K100 Oak - hickory forest K101 Elm - ash forest K103 Mixed mesophytic forest K104 Appalachian oak forest K106 Northern hardwoods K110 Northeastern oak - pine forest K111 Oak - hickory - pine forest K112 Southern mixed forest SAF COVER TYPES : 14 Northern pin oak 15 Red pine 20 White pine - northern red oak - red maple 21 Eastern white pine 22 White pine - hemlock 23 Eastern hemlock 25 Sugar maple - beech - yellow birch 27 Sugar maple 28 Black cherry - maple 39 Black ash - American elm - red maple 44 Chestnut oak 46 Eastern redcedar 52 White oak - black oak - northern red oak 53 White oak 55 Northern red oak 57 Yellow-poplar 58 Yellow-poplar - eastern hemlock 59 Yellow-poplar - white oak - northern red oak 64 Sassafras - persimmon 108 Red maple 110 Black oak SRM (RANGELAND) COVER TYPES : NO-ENTRY HABITAT TYPES AND PLANT COMMUNITIES : New York fern is an understory component of the yellow birch (Betula alleghaniensis)-sugar maple (Acer saccharum) association in Quebec [15]..

VALUE AND USE

SPECIES: Thelypteris noveboracensis | New York Fern
WOOD PRODUCTS VALUE : NO-ENTRY IMPORTANCE TO LIVESTOCK AND WILDLIFE : NO-ENTRY PALATABILITY : NO-ENTRY NUTRITIONAL VALUE : NO-ENTRY COVER VALUE : NO-ENTRY VALUE FOR REHABILITATION OF DISTURBED SITES : NO-ENTRY OTHER USES AND VALUES : NO-ENTRY MANAGEMENT CONSIDERATIONS : In hardwood forests of the Northeast, New York fern can sometimes be an undesirable species because of its ability to outcompete seedlings of commercially important tree species [3,10,11,12]. It can form a dense ground cover, especially following clearcutting, preventing establishment of hardwood seedlings. Treatment with glyphosate or sulfometuron before clearcutting is recommended to reduce New York fern cover [10,12]. White-tailed deer browsing of Allegheny hardwood seedlings, particularly black cherry (Prunus serotina), can cause increases of New York fern [11,26]. New York fern produces phenols which can kill black cherry seedlings [5]. Acid rain studies on Long Island, New York, showed that New York fern became a dominant understory species where pH levels declined to between 3.8 to 4.1 [9].

BOTANICAL AND ECOLOGICAL CHARACTERISTICS

SPECIES: Thelypteris noveboracensis | New York Fern
GENERAL BOTANICAL CHARACTERISTICS : New York fern is a deciduous fern with leaves about 18 inches (46 cm) long and 6 inches (15 cm) wide. It grows in tufts along horizontal rhizomes which are somewhat scaly and widely creeping [2,25]. Spore clusters are submarginal, and spore covers are absent or minute and quickly shrivel [24,25]. The fronds of Thelypteris noveboracensis forma fragrans are glandular and aromatic [8,24]. RAUNKIAER LIFE FORM : Chamaephyte Geophyte Hemicrytophyte REGENERATION PROCESSES : Sexual reproduction will occur on bare mineral soil, but New York fern reproduces mainly by a creeping rootstock that allows it to form dense ground cover [11]. The rhizomes grow faster in partially cut than in uncut stands. New rhizomes form on the frond petiole [11]. The rhizomes can be pulled out of the ground like a mat of sod and transplanted [25]. SITE CHARACTERISTICS : New York fern grows in moist woodlands and pastures, ravines, bogs, swamps, and field margins of Eastern deciduous forests [24,25,28]. It is rarely found in dry woodlands of Illinois [21]. In the Adirondack Mountains it grows on well-drained to "imperfectly-drained" sites from 100 feet (30 m) in elevation near Lake Champlain to 2,300 feet (701 m) in the MacIntyre Range [14]. It occurs up to 5,000 feet (1,524 m) elevation in the Blue Ridge Province [25]. It is found on marine sandy and glacial meltwater sites on well-drained slopes in disturbed forests southwest of Montreal, Quebec [20]. It grows on calcareous sites in the southern Blue Ridge escarpment. Soils ther are Brevard phyllite, with a pH of 6.2 to 6.5 [6]. It can also grow on sites with a pH as low as 3.8 [9]. Some overstory species with which New York fern is associated are swamp white oak (Quercus bicolor), mazzard cherry (Prunus avium), mockernut hickory (Carya tomentosa), pignut hickory (C. glabra), shagbark hickory (C. ovata), white ash (Fraxinus americana), American hornbeam (Carpinus caroliniana), black locust (Robinia pseudoacacia), and spicebush (Lindera benzoin) [19,29]. Some understory associates include hayscented fern (Dennstaedtia punctilobula), short huskgrass (Bracheylytrum erectum), violet (Viola spp.), woodsorrel (Oxalis spp.), aster (Aster spp.), clubmoss (Lycopodium spp.), viburnum (Viburnum spp.), evergreen woodfern (Dryopteris intermedia), common greenbrier (Smilax rotundifolia), circaea (Circaea quadrisulcata), ladyfern (Athyrium filex-femina), Indian jack-in-the-pulpit (Arisaema triphyllum), Virginia creeper (Parthenocissus quinquefolia), and wild lily-of-the-valley (Maianthemum canadense) [1,9,17,18]. SUCCESSIONAL STATUS : Facultative Seral Species New York fern is shade tolerant, but will grow in canopy openings in hardwood forests [2,11,29]. SEASONAL DEVELOPMENT : New York fern produces spores from May through August from Virginia south to Georgia [28], from late July through late September in New England [24], and from June through September in Illinois [21]. Leaves turn brown in autumn, usually before other wood ferns [25].

FIRE ECOLOGY

SPECIES: Thelypteris noveboracensis | New York Fern
FIRE ECOLOGY OR ADAPTATIONS : New York fern has widely creeping rhizomes that allow it to regenerate following fire [11]. POSTFIRE REGENERATION STRATEGY : Rhizomatous herb, rhizome in soil Ground residual colonizer (on-site, initial community)

FIRE EFFECTS

SPECIES: Thelypteris noveboracensis | New York Fern
IMMEDIATE FIRE EFFECT ON PLANT : NO-ENTRY DISCUSSION AND QUALIFICATION OF FIRE EFFECT : NO-ENTRY PLANT RESPONSE TO FIRE : In general, rhizomatous species respond to fire by sprouting. No specific effects of fire on New York fern were found in the literature. DISCUSSION AND QUALIFICATION OF PLANT RESPONSE : FIRE MANAGEMENT CONSIDERATIONS : In Allegheny hardwood types, fire does not control undesirable species like New York fern [12].

REFERENCES

SPECIES: Thelypteris noveboracensis | New York Fern
REFERENCES : 1. Baird, John W. 1980. The selection and use of fruit by birds in an eastern forest. Wilson Bulletin. 92(1): 63-73. [10004] 2. Cobb, Broughton. 1956. A field guide to the ferns. Boston: Houghton Mifflin Company. 281 p. [21691] 3. Drew, Allan P. 1988. Interference of black cherry by ground flora of the Allegheny uplands. Canadian Journal of Forest Research. 18: 652-656. [8729] 4. Eyre, F. H., ed. 1980. Forest cover types of the United States and Canada. Washington, DC: Society of American Foresters. 148 p. [905] 5. Fisher, Richard F. 1980. Allelopathy: a potential cause of regeneration failure. Journal of Forestry. 78: 1980. [9049] 6. Gaddy, L. L. 1990. Glade Fern Ravine, a rich fern site in the Blue Ridge province of South Carolina. Castanea. 55(4): 282-285. [21692] 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. 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] 9. Greller, Andrew M.; Locke, David C.; Kilanowski, Victoria; Lotowycz, G. Elizabeth. 1990. Changes in vegetation composition and soil acidity between 1922 and 1985 at a site on the north shore of Long Island, New York. Bulletin of the Torrey Botanical Club. 117(4): 450-458. [19192] 10. Horsley, Stephen B. 1982. Development of reproduction in Allegheny hardwood stands after herbicide-clearcuts and herbicide-shelterwood cuts. NE-308. Upper Darby, PA: U.S. Department of Agriculture, Forest Service, Northeastern Forest Experiment Station. 4 p. [12575] 11. Horsley, Stephen B. 1988. How vegetation can influence regeneration. In: Smith, H. Clay; Perkey, Arlyn W.; Kidd, William E., Jr, eds. Guidelines for regenerating Appalachian hardwood stands: Workshop proceedings; 1988 May 24-26; Morgantown, WV. Society of American Foresters Publ. 88-03. Morgantown, WV: West Virginia University Books: 38-54. [13544] 12. Horsley, Stephen B. 1991. Using Roundup and Oust to control interfering understories in Allegheny hardwood stands. In: McCormick, Larry H.; Gottschalk, Kurt W., eds. Proceedings, 8th central hardwood forest conference; 1991 March 4-6; University Park, PA. Gen. Tech. Rep. NE-148. Radnor, PA: U.S. Department of Agriculture, Forest Service, Northeastern Forest Experiment Station: 281-290. [15317] 13. 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] 14. Kudish, Michael. 1992. Adirondack upland flora: an ecological perspective. Saranac, NY: The Chauncy Press. 320 p. [19376] 15. Lemieux, G. J. 1963. Soil-vegetation relationships in northern hardwoods of Quebec. In: Forest-soil relationships in North America. Corvallis, OR: Oregon State University Press: 163-176. [8874] 16. 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] 17. Mackun, I. R.; Brach, A. R.; Smallidge, P. J.; [and others]. 1990. Upland vegetation responses to watershed liming studied. Restoration & Management Notes. 8(1): 36-37. [13551] 18. Marquis, David A. 1990. Prunus serotina Ehrh. black cherry. In: Burns, Russell M.; Honkala, Barbara H., technical coordinators. Silvics of North America. Volume 2. Hardwoods. Agric. Handb. 654. Washington, DC: U.S. Department of Agriculture, Forest Service: 594-604. [13972] 19. McNab, W. Henry. 1991. Land classification in the Blue Ridge province: state-of-the-science report. In: Mengel, Dennis L.; Tew, D. Thompson, eds. Ecological land classification: applications to identify the productive potential of southern forests: Proc. of a symp; 1991 January 7-9; Charlotte, NC. Gen. Tech. Rep. SE-68. Asheville, NC: U.S. Department of Agriculture, Forest Service, Southeastern Forest Experiment Station: 37-47. [15708] 20. Meilleur, A.; Bouchard, A.; Bergeron, Y. 1992. The use of understory spp. as indicators of landform ecosystem type in heavily disturb. forest: an evaluat. in the Haut-Saint-Laurent, Quebec. Vegetatio. 102: 13-32. [20101] 21. Mohlenbrock, Robert H. 1986. (Revised edition). Guide to the vascular flora of Illinois. Carbondale, IL: Southern Illinois University Press. 507 p. [17383] 22. Raunkiaer, C. 1934. The life forms of plants and statistical plant geography. Oxford: Clarendon Press. 632 p. [2843] 23. Ross, S. Rachel. 1978. The effects of prescribed burning on ground cover vegetation of white pine and mixed hardwood forests in southeastern New Hampshire. Durham, NH: University of New Hamshire. 151 p. Thesis. [20674] 24. 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] 25. Small, John Kunkel. 1964. Ferns of the southeastern states. New York: Hafner Publishing Company. 517 p. [21690] 26. Tilghman, Nancy G. 1989. Impacts of white-tailed deer on forest regeneration in northwestern Pennsylvania. Journal of Wildlife Management. 53(3): 524-532. [8914] 27. U.S. Department of Agriculture, Soil Conservation Service. 1982. National list of scientific plant names. Vol. 1. List of plant names. SCS-TP-159. Washington, DC. 416 p. [11573] 28. Wofford, B. Eugene. 1989. Guide to the vascular plants of the Blue Ridge. Athens, GA: The University of Georgia Press. 384 p. [12908] 29. Yahner, R. H.; Storm, G. L.; Melton, R. E.; Vecellio, G. M.; Cottam, D. F. 1991. Floral inventory and vegetative cover type mapping of Gettysburg National Military Park and Eisenhower National Historic Site. Tech. Rep. NPS/MAR/NRTR - 91/050. Philadelphia, PA: U.S. Department of the Interior, National Park Service, Mid-Atlantic Region. 149 p. [17988]

Index

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