Speckled alder (Alnus incana ssp. rugosa) is a nitrogen-fixing shrub that has been found to increase the concentration of inorganic nitrogen in the surface waters of the Adirondacks. Native Americans used speckled alder in combination with bloodroot, wild plum, and red osier dogwood (Cornus sericea) to make a scarlet dye for porcupine quill embroidery. Inuit people and settlers extracted a dark dye from the bark for tanning and staining hides. The bark was boiled to make medicinal teas for treating rheumatism and was also applied to wounds as a poultice to reducing bleeding and swelling.
There are several thousand shrub swamps statewide. Some documented occurrences have good viability and many are protected on public land or private conservation land. This community has statewide distribution, and includes a few large, high 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 and invasive species.
The number and acreage of shrub swamps in New York have probably remained stable in recent decades as a result of wetland protection regulations. There may be a few cases where this community has increased as a result of abandoned agriculture land.
The number and acreage of shrub swamps in New York have substantially declined (50-75%) from historical numbers likely correlated to the alteration to the natural hydrology and to direct destruction, especially near urban areas.
Shrub swamps are threatened by development and its associated run-off (e.g., agriculture, residential, roads/bridges), habitat alteration (e.g., pollution, nutrient loading, excessive logging in adjacent uplands), and recreational overuse (e.g., trash dumping, motor boating). Alteration to the natural hydrological regime is also a threat to this community (e.g., impoundments, blocked culverts, beaver). Several shrub swamps are threatened by invasive species, such as purple loosestrife (Lythrum salicaria), reedgrass (Phragmites australis), and frog-bit (Hydrocharis morsus-ranae).
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 ideally 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 runoff 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 system, they 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 algal blooms and eventually an oxygen-depleted environment in which 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.
Survey for occurrences statewide to advance documentation and classification of shrub swamps. A statewide review of shrub swamps is desirable. Continue searching for large sites in good condition (A- to AB-ranked).
Research composition of shrub swamps statewide in order to characterize variations. Collect sufficient plot data to support the recognition of several distinct shrub swamp types based on composition and by ecoregion (e.g., Alnus spp. dominant, Cephalanthus occidentalis dominant, Cornus spp. dominant, Salix spp. dominant, etc.).
Widespread throughout the state, including the coastal areas and represented by different regional variants. Alder-dominated swamps are widespread throughout the northern Appalachian portion of the northern third of New York and probably extend south as small patches in the lower New England and Great Lakes areas.
This physiognomically broadly-defined community is likely to be widespread worldwide. Examples with the greatest biotic affinities to New York occurrences are suspected to span north to southern Canada, west to Minnesota, southwest to Indiana and Tennessee, southeast to Georgia, and northeast to Nova Scotia.
A shrub swamp is an inland wetland dominated by tall shrubs that occurs along the shore of a lake or river; in a wet depression or valley not associated with lakes; or as a transition zone between a marsh, fen, or bog and a swamp or upland community. The substrate is usually mineral soil or muck. This is a very broadly defined type that includes several distinct communities and many intermediates. In northern New York many shrub swamps are dominated by alder (Alnus incana ssp. rugosa); these swamps are sometimes called alder thickets. A swamp dominated by red osier dogwood (Cornus sericea), silky dogwood (C. amomum), and willows (Salix spp.) may be called a shrub carr. Along the shores of some lakes and ponds there is a distinct zone dominated by waterwillows (Decodon verticillatus) and/or buttonbush (Cephalanthus occidentalis) which can sometimes fill a shallow basin. Birds that may be found in shrub swamps include both common species such as common yellowthroat (Geothlypis trichas) and swamp sparrow (Melospiza georgiana) and rare species such as the American bittern (Botaurus lentiginosus).
Shrub swamps are very common and quite variable. They may be codominated by a mixture of species or be a near-monoculture of a single dominant shrub species. Characteristic shrubs include meadowsweet (Spiraea alba var. latifolia), steeplebush (Spiraea tomentosa), gray dogwood (Cornus racemosa), swamp azalea (Rhododendron viscosum), highbush blueberry (Vaccinium corymbosum), maleberry (Lyonia ligustrina), smooth alder (Alnus serrulata), spicebush (Lindera benzoin), willows (Salix bebbiana, S. discolor, S. lucida, S. petiolaris), wild raisin (Viburnum nudum var. cassinoides), and arrowwood (Viburnum dentatum var. lucidum).
Known examples of this community have been found at elevations between 95 feet and 1,900 feet.
The best time to view the diversity of plants in a shrub swamp is in the summer, from June to August. Many dogwood species (Cornus spp.) begin to bloom as early as May, but most other characteristic shrubs, including meadowsweet (Spiraea alba), buttonbush (Cephalanthus occidentalis), and sweet pepperbush (Clethra alnifolia) bloom from June or July through August.
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.
Alnus serrulata (smooth alder)
Alnus incana ssp. rugosa (speckled alder)
Cephalanthus occidentalis (buttonbush)
Clethra alnifolia (coastal sweet-pepperbush)
Cornus sericea (red-osier dogwood)
Alnus incana ssp. rugosa (speckled alder)
Cephalanthus occidentalis (buttonbush)
Ilex laevigata (smooth winterberry)
Vitis aestivalis (summer grape)
Bidens cernua (nodding beggar-ticks)
Carex torta (twisted sedge)
Decodon verticillatus (water-willow)
Persicaria arifolia (halberd-leaved tear-thumb)
Phalaris arundinacea (reed canary grass)
Typha angustifolia (narrow-leaved cat-tail)
Lemna minor (common duckweed)
This figure helps visualize the structure and "look" or "feel" of a typical Shrub 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%.
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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.
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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.
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.
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This guide was authored by: Gregory J. Edinger
Information for this guide was last updated on: June 10, 2019
Please cite this page as:
New York Natural Heritage Program. 2019. Online Conservation Guide for Shrub swamp. Available from: https://guides.nynhp.org/shrub-swamp/. Accessed November 19, 2019.