Sweetgum (Liquidambar styraciflua) is aptly named - the resin from the tree was used as a chewing gum by several Native American tribes. The Cherokee, Choctaw, Koasati, and Rappahannock would knock a piece of bark from the sweetgum tree, causing resin to flow from the tree. The sap hardened after a week and was collected for chewing gum.
There are an estimated 10 to 30 extant occurrences statewide. A few documented occurrences have good viability, but none of these are in excellent condition. A few are protected on public land or private conservation land. This community has a very limited statewide distribution that is primarily concentrated on Staten Island where there are several small, good quality examples. The current trend of this community is probably stable for occurrences on public land and private conservation land, or declining slightly elsewhere due to moderate threats that include alteration of the natural hydrology, development, and invasive species.
The number and acreage of red maple-sweetgum swamps in New York have probably declined slightly, or remained stable, in recent decades as a result of wetland protection regulations. Since World War II, urbanization has emerged as the predominant force impacting wetlands in most parts of the region (Golet et al. 1993).
The number and acreage of red maple-sweetgum swamps in New York have probably declined substantially from historical numbers likely correlated with agricultural and other development. The principal causes of wetland loss in the Northeast prior to mid-1800s include conversion of wetlands to agriculture, the construction of impoundments for hydropower and water supply, and the cutting of swamp timber for lumber, fence posts, and fuel wood (Golet et al. 1993). Extensive historical extirpation of red maple-sweetgum swamps has been cited by Stevens (1992). More wetlands are being drained and filled for development as undeveloped uplands in the metropolitan New York City area have become very scarce. Reportedly, no old-growth examples remain north of Richmond County (Stevens 1992).
Red maple-sweetgum swamps are threatened by development in the surrounding landscape and its assocaited run-off (e.g., residential, commercial, roads, utility ROWs, golf courses, etc.), habitat alteration (e.g., excessive logging, ditching, pollution), and recreational overuse (e.g., hiking trails, ATVs, trash dumping, illegal fires). Alteration to the natural hydrological regime is also a threat to this community (e.g., impoundments, blocked culverts). Several red maple-sweetgum swamps are threatened by invasive species, such as tree-of-heaven (Ailanthus altissima), barberry (Berberis thunbergii), Oriental bittersweet (Celastrus orbiculatus), Japanese honeysuckle (Lonicera japonica), multiflora rose (Rosa multiflora), garlic mustard (Alliaria petiolata), purple loosestrife (Lythrum salicaria), and reedgrass (Phragmites australis).Conversion of wetlands for agriculture was a major cause of inland wetland loss in many areas of the Northeast historically, and it is still an important factor today, most notably in New York (Golet et al. 1993).
Where practical, establish and maintain a natural wetland buffer to reduce storm-water, pollution, and nutrient run-off, while simultaneously capturing sediments before they reach the wetland. Buffer width should take into account the erodibility of the surrounding soils, slope steepness, and current land use. Wetlands protected under Article 24 are known as New York State "regulated" wetlands. The regulated area includes the wetlands themselves, as well as a protective buffer or "adjacent area" extending 100 feet landward of the wetland boundary (NYS DEC 1995). If possible, minimize the number and size of impervious surfaces in the surrounding landscape. Avoid habitat alteration within the wetland and surrounding landscape. For example, roads and trails should be routed around wetlands, and should not pass through the buffer area. If the wetland must be crossed, then bridges and boardwalks are preferred over filling. Restore past impacts, such as removing obsolete impoundments and ditches in order to restore the natural hydrology. Prevent the spread of invasive exotic species into the wetland through appropriate direct management, and by minimizing potential dispersal corridors, such as roads.
When considering road construction and other development activities minimize actions that will change what water carries and how water travels to this community, both on the surface and underground. Water traveling over-the-ground as run-off usually carries an abundance of silt, clay, and other particulates during (and often after) a construction project. While still suspended in the water, these particulates make it difficult for aquatic animals to find food; after settling to the bottom of the wetland, these particulates bury small plants and animals and alter the natural functions of the community in many other ways. Thus, road construction and development activities near this community type should strive to minimize particulate-laden run-off into this community. Water traveling on the ground or seeping through the ground also carries dissolved minerals and chemicals. Road salt, for example, is becoming an increasing problem both to natural communities and as a contaminant in household wells. Fertilizers, detergents, and other chemicals that increase the nutrient levels in wetlands cause algae blooms and eventually an oxygen-depleted environment where few animals can live. Herbicides and pesticides often travel far from where they are applied and have lasting effects on the quality of the natural community. So, road construction and other development activities should strive to consider: 1. how water moves through the ground, 2. the types of dissolved substances these development activities may release, and 3. how to minimize the potential for these dissolved substances to reach this natural community.
Continue searching for large sites in good condition (A- to AB-ranked).
Research the hydrologic regime of red maple-sweetgum swamps and determine what unique soil characteristics support this community. Assess examples (e.g., Arshamonaque) that are dominated by swamp white oak (Quercus bicolor), swamp cottonwood (Populus heterophylla), and pin oak (Quercus palustris) that have little or no red maple or sweetgum and determine if this is a new community type.
This community is apparently concentrated in the western half of Staten Island (Richmond County) with a few examples extending north to the Hudson Highlands in Westchester and Rockland counties. Red maple-sweetgum swamps were probably historically present in very small patches farther east in Queens, Kings, and Nassau Counties. It was also likely to have been present historically in Bronx and New York Counties.
The community range is centered in the Mid-Atlantic Coast Ecoregion, but extends into the North Atlantic Coast Ecoregion, and includes New York, New Jersey, Pennsylvania, Delaware, Maryland, Virginia, and possibly North Carolina. It may extend farther north along the coast of Connecticut (Bray 1915).
Sweetgum (Liquidambar styraciflua) is often the dominant tree or may be codominant with red maple (Acer rubrum). The shrub layer is usually fairly well-developed. Characteristic shrubs are sweet pepperbush (Clethra alnifolia), swamp azalea (Rhododendron viscosum), arrowwood (Viburnum dentatum var. lucidum), spicebush (Lindera benzoin), highbush blueberry (Vaccinium corymbosum), black chokeberry (Aronia melanocarpa) and possibly fetterbush (Leucothoe racemosa). The herbaceous layer is often dominated by ferns, including netted chain fern (Woodwardia areolata), cinnamon fern (Osmunda cinnamomea), and sensitive fern (Onoclea sensibilis). Characteristic herbs include lizard's-tail (Saururus cernuus), Canada mayflower (Maianthemum canadense), jumpseed (Persicaria virginiana), skunk cabbage (Symplocarpus foetidus) and jewelweed (Impatiens capensis).
Red maple-sweetgum swamps occur on somewhat poorly drained seasonally wet flats, usually on somewhat acidic gleyed to mottled clay loam or sandy loam. Red maple-sweetgum swamps often occur as a mosaic with upland forest communities. Sweetgum (Liquidambar styraciflua) is often the dominant tree or may be codominant with red maple (Acer rubrum).
Known examples of this community have been found at elevations between 8 feet and 190 feet.
The community vegetation is at its peak during midsummer; at this time ferns, sedges, and herbs can be readily observed and identified. Striking seasonal leaf color can be enjoyed in the fall.
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.
Liquidambar styraciflua (sweet-gum)
Nyssa sylvatica (black-gum, sour-gum)
Populus heterophylla (swamp cottonwood)
Quercus bicolor (swamp white oak)
Quercus palustris (pin oak)
Clethra alnifolia (coastal sweet-pepperbush)
Ilex verticillata (common winterberry)
Lindera benzoin (spicebush)
Ulmus americana (American elm)
Rhododendron viscosum (swamp azalea)
Parthenocissus quinquefolia (Virginia-creeper)
Smilax rotundifolia (common greenbrier)
Impatiens capensis (spotted jewelweed, spotted touch-me-not)
Onoclea sensibilis (sensitive fern)
Saururus cernuus (lizard's-tail)
Symplocarpus foetidus (skunk-cabbage)
This figure helps visualize the structure and "look" or "feel" of a typical Red Maple-Sweetgum Swamp. 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%.
Bray, W.L. 1915. The development of the vegetation of New York State. New York State College of Forestry, Tech. Publ. No. 3, Syracuse, NY.
Breden, T.F., Y. Alger, K. Strakosch Walz, and A.G. Windisch. 2001. Classification of Vegetation Communities of New Jersey: Second Iteration. Association for Biodiversity Information and New Jersey Natural Heritage Program, Office of Natural Lands Management, Division of Parks and Forestry, NJ Department of Environmental Protection. Trenton, NJ.
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.
Greller, A.M. 2000. Mixed hardwood swamp forest on rolling uplands near Lake Success on Long Island. The Quarterly Newsletter of the Long Island Botanical Society. 10(2):18-20.
Greller, Andrew M. 1977. A classification of mature forests on Long Island, New York. Bull. Torrey Bot. Club 140 (4):376-382.
Grossman, D. H., K. Lemon Goodin, and C. L. Reuss, editors. 1994. Rare plant communities of the conterminous United States: An initial survey. The Nature Conservancy. Arlington, VA. 620 pp.
New York Natural Heritage Program. 2019. New York Natural Heritage Program Databases. Albany, NY.
New York State Department of Environmental Conservation. 1995. Freshwater Wetlands: Delineation Manual. July 1995. New York State Department of Environmental Conservation. Division of Fish, Wildlife, and Marine Resources. Bureau of Habitat. Albany, NY.
Rheinhardt, R., D. Whigham, H. Khan, and M. Brinson. 2000. Vegetation of headwater wetlands in the Inner Coastal Plain of Virginia and Maryland. Castanea 65(1):21-35.
Robichaud, B. and M.F. Buell. 1973. Vegetation of New Jersey: A study of landscape diversity. Rutgers Univ. Press. New Brunswick, NJ. 340 pp.
Sneddon, L., M. Anderson and K. Metzler. 1996. Community alliances and elements of the eastern region. Second draft. Unpublished report. The Nature Conservancy, Eastern Region Conservation Science, Boston, MA. April 11. 234 pp.
Stevens, G. 1992. Assessment of wetland delineation on the Great Sweet-gum Swamp Site, Village of Scarsdale, NY. Unpublished report. Hudsonia Ltd. Annandale, NY. June 30. 12 pp.
This guide was authored by: Jennifer Garrett
Information for this guide was last updated on: March 23, 2017
Please cite this page as:
New York Natural Heritage Program. 2019. Online Conservation Guide for Red maple-sweetgum swamp. Available from: https://guides.nynhp.org/red-maple-sweetgum-swamp/. Accessed November 14, 2019.