Indian grass (Sorghastrum nutans) is a common grass of some rocky summit grasslands. Indian grass roots can grow to depths of seven feet, comprising two-thirds of the grass's total biomass! Indian grass is also the host plant of common wood nymph and wood satyr butterflies. These butterflies lay their eggs on Indian grass and the caterpillars eat the grass's leaves.
There are likely several hundred occurrences throughout upstate New York. Some of the documented occurrences have good viability and many are protected on public land or private conservation land, although most are relatively small and disturbed. This community has probably declined substantially from historical numbers and a few of the currently documented occurrences contain invasive plants and are threatened by fire suppression.
The number and acreage of rocky summit grasslands in New York have probably declined slightly in recent decades as a result of fire suppression, antenna tower construction, recreational disturbances, and invasive species.
The number and acreage of rocky summit grasslands in New York have probably declined substantially from historical numbers as a result of fire suppression.
Rocky summit grasslands are threatened by development within the community (especially plans for cellular telephone and radio towers, wind farms, and logging roads) and in the surrounding landscape. Popular sites with scenic views are threatened by trampling by recreational visitors (e.g., mountain bikers, hikers, graffiti). Natural fire regimes (i.e., fires started through lightning strikes) appear suppressed at several sites resulting in woody plant invasion. Invasive plants, such as bluegrass (Poa compressa), sheep sorrel (Rumex acetosella), and knapweed (Centaurea beibersteinii), are a threat at several rocky summit grasslands. Over-browsing by deer of characteristic rocky summit grassland plants may be perceived as a minor threat at a few sites, but may benefit the community by helping maintain the open structure.
Management activities should include the development and implementation of prescribed burn plans at appropriate sites. Fragmenting features such as roads, abandoned tower clearings, and unnecessary trails should be reduced or minimized, and high-impact activities such as mountain biking and hang-gliding should be restricted to trails and least sensitive areas. Prevent the dumping of trash.
Soils are very thin in and around this community and the effect of clearing and construction on soil retention and erosion must be considered during any development activities. Similarly, these soils are acidic and nutrient-poor and any soil enrichment contamination (e.g., from septic leach fields and fertilized lawns) may alter alter community structure and function. The open structure of this community is maintained by fire and presents a fire hazard to existing and proposed development. Unprotected structures located within or near this community are more susceptible to damage from fire.
Survey for occurrences statewide to advance documentation and classification of rocky summit grasslands. A statewide review of rocky summit grasslands is desirable. Continue searching for large sites in good condition (A- to AB-ranked).
Research the composition of rocky summit grasslands statewide in order to characterize variations (e.g., identify those dominated by different grass species). Collect sufficient plot data to support the recognition of several distinct rocky summit grasslands based on ecoregion, geology, and dominant grass species.
This community is widespread throughout upstate New York, north of the North Atlantic Coast Ecoregion. Rocky summit grasslands are more common in the southern and eastern parts of this range and are probably represented by different regional variants. This community is concentrated in the Lower New England Ecoregion within the Hudson Highlands, but it is also known from the Taconic Mountains, the Adirondack Mountains, the St. Lawrence and Lake Champlain Valley, and possibly the western part of the state.
The range of the broadly-defined community is probably global. Examples with the greatest biotic affinities to New York occurrences are suspected to be widespread throughout the mountainous areas of the Appalachian Range. Occurrences are suspected of being concentrated near the middle of this range. This range is estimated to span north to southern Canada, west to Ohio and Kentucky, south to Alabama and Georgia, and southeast to New Jersey.
A grassland community that occurs on rocky summits, ridges, and exposed outcrops. The vegetation is dominated by herbaceous plants, especially grasses. Woody species, such as red oak (Quercus rubra) and lowbush blueberry (Vaccinium pallidum, V. angustifolium), are sparse, and may be present near the community margins (Edinger et al. 2002).
Rocky summit grasslands occur on rocky outcrops and summits with thin soils, and are dominated by grass species such as little bluestem (Schizachyrium scoparium), tufted hairgrass (Deschampsia flexuosa), poverty-grass (Danthonia spicata, D. compressa), and Indian grass (Sorghastrum nutans). Also common are Pennsylvania sedge (Carex pensylvanica), ebony spleenwort (Asplenium platyneuron), and fragrant goldenrod (Solidago odora).
Known examples of this community have been found at elevations between 10 feet and 4,365 feet.
Many of the grasses and forbs characteristic of this community, such as little bluestem and goldenrod, come into maturity in late summer.
This New York natural community encompasses all or part of the concept of the following International Vegetation Classification (IVC) natural community associations. These are often described at finer resolution than New York's natural communities. The IVC is developed and maintained by NatureServe.
This New York natural community falls into the following ecological system(s). Ecological systems are often described at a coarser resolution than New York's natural communities and tend to represent clusters of associations found in similar environments. The ecological systems project is developed and maintained by NatureServe.
Carya glabra (pignut hickory)
Quercus alba (white oak)
Quercus montana (chestnut oak)
Quercus rubra (northern red oak)
Pinus strobus (white pine)
Viburnum prunifolium (black-haw)
Comptonia peregrina (sweet-fern)
Gaylussacia baccata (black huckleberry)
Vaccinium angustifolium (common lowbush blueberry)
Vaccinium pallidum (hillside blueberry)
Asplenium platyneuron (ebony spleenwort)
Carex pensylvanica (Pennsylvania sedge)
Danthonia spicata (poverty grass)
Dichanthelium clandestinum (deer-tongue rosette grass)
Lysimachia quadrifolia (whorled-loosestrife)
Solidago odora (sweet goldenrod)
Solidago puberula (downy goldenrod)
Sorghastrum nutans (Indian grass)
Verbascum thapsus (common mullein)
This figure helps visualize the structure and "look" or "feel" of a typical Rocky Summit Grassland. Each bar represents the amount of "coverage" for all the species growing at that height. Because layers overlap (shrubs may grow under trees, for example), the shaded regions can add up to more than 100%.
Edinger, G. J., D. J. Evans, S. Gebauer, T. G. Howard, D. M. Hunt, and A. M. Olivero (editors). 2014. Ecological Communities of New York State. Second Edition. A revised and expanded edition of Carol Reschke’s Ecological Communities of New York State. New York Natural Heritage Program, New York State Department of Environmental Conservation, Albany, NY. http://www.dec.ny.gov/docs/wildlife_pdf/ecocomm2014.pdf
Edinger, Gregory J., D.J. Evans, Shane Gebauer, Timothy G. Howard, David M. Hunt, and Adele M. Olivero (editors). 2002. Ecological Communities of New York State. Second Edition. A revised and expanded edition of Carol Reschke's Ecological Communities of New York State. (Draft for review). New York Natural Heritage Program, New York State Department of Environmental Conservation. Albany, NY. 136 pp.
Fike, J. 1999. Terrestrial and Palustrine Plant Communities of Pennsylvania. Pennsylvania Natural Diversity Inventory, Harrisburg, PA.
Mark, A. F. 1959. The flora of the grass balds and fields of the southern Appalachian Mountains. Castanea 24:1-21.
Mark, A.F. 1958. The ecology of the southern Appalachian grass balds. Ecol. Monogr. 28: 293-336.
New York Natural Heritage Program. 2019. New York Natural Heritage Program Databases. Albany, NY.
Rentch, J.S. and R.H. Fortney. 1997. The vegetation of West Virginia grass bald communities. Castanea 62(3):147-160.
Reschke, Carol. 1990. Ecological communities of New York State. New York Natural Heritage Program, New York State Department of Environmental Conservation. Latham, NY. 96 pp. plus xi.
Swain, P. C., and J. B. Kearsley. 2001. Classification of natural communities of Massachusetts. September 2001 draft. Natural Heritage and Endangered Species Program, Massachusetts Division of Fisheries and Wildlife, Westborough, MA.
Wiegl, P. D., and T. W. Knowles. 1999. Antiquity of Southern Appalachian grass balds: The role of keystone megaherbivores. Pages 215-223 in: R. P. Eckerlin, editor. Proceedings of the Appalachian Biogeography Symposium, Virginia Museum of Natural History Special Publication Number 7.
This guide was authored by: Timothy G. Howard
Information for this guide was last updated on: April 29, 2019
Please cite this page as:
New York Natural Heritage Program. 2019. Online Conservation Guide for Rocky summit grassland. Available from: https://guides.nynhp.org/rocky-summit-grassland/. Accessed November 16, 2019.