Great Lakes Wooded Dune and Swale
Summary
This system is found in nearly 100 occurrences throughout the Great Lakes shorelines of the United States and Canada. It consists of a foredune, followed by a series of low to high dunes (uplands) and swales (wetlands). The system is often best developed where post-glacial streams entered an embayment and provide a dependable sand source. The combination of along-shore currents, waves, and winds form foredunes along the shoreline. The foredunes of most dune-and-swale complexes are commonly 1-2 m high, with Ammophila breviligulata, Calamovilfa longifolia, Salix serissima, Salix cordata, and Populus balsamifera most common. The swale immediately behind the foredune is influenced by short-term variation in lake levels and can be partially or occasionally completely filled by dune sands following major storm events. Species common to this first swale include Juncus arcticus ssp. littoralis, Juncus pelocarpus, Juncus nodosus, Eleocharis acicularis, and Schoenoplectus americanus. Occasionally, such swales may contain lake-influenced, calcareous sands and may contain moderately alkaline indicators.
A low dune field with more advanced plant succession often follows the first open dunes and swales. Pinus banksiana, Pinus strobus, and Pinus resinosa often form a scattered overstory canopy, while Juniperus communis, Juniperus horizontalis, Arctostaphylos uva-ursi, and Koeleria macrantha form a scattered ground layer. Following the dune-field zone, both dunes and swales are typically forested. Moist swales are often forested, and soil organic material has often begun to accumulate. Thuja occidentalis, Alnus incana, Salix spp., and Acer rubrum dominate the partial overstory canopy and understory. In contrast to the dry or moist swales, wetter swales (where standing water is present through most of the year) may be dominated by Carices, such as Carex aquatilis and Carex stricta. Forested beach ridges, with soils of medium to course sand, tend to be dominated by species common to dry-mesic and mesic northern forest. Complexes located in embayments protected from prevailing winds tend to be formed entirely of low, water-lain beach ridges. As a result, even the beach ridges within these complexes support wetland vegetation.
Six major subtypes of Great Lakes Dune and Swale were described for Michigan, including the Lake Superior high dune type, the Lake Superior low dune type, the North Lake Michigan high dune type, Northern Lake Huron-Lake Michigan low dune type, the Southern Lake Huron type, and the Northern Great Lakes low dune type. These subtypes represent patterns of floristic variation resulting from latitude and sand dune/beach ridge characteristics that constrain floristic and structural attributes. High dune types may support predominantly upland vegetation, while low dune types may support predominantly wetland vegetation.
Source: NatureServe Explorer
Vegetation
The foredunes of most dune-and-swale complexes are commonly 1-2 m high, with Ammophila breviligulata, Calamovilfa longifolia, Salix serissima, Salix cordata, and Populus balsamifera most common. The swale immediately behind the foredune is influenced by short-term variation in lake levels and can be partially or occasionally completely filled by dune sands following major storm events. Species common to this first swale include Juncus arcticus ssp. littoralis (= Juncus balticus), Juncus pelocarpus, Juncus nodosus, Eleocharis acicularis, and Schoenoplectus americanus (= Scirpus americanus). Occasionally, such swales may contain lake-influenced, calcareous sands, and the shallow swale may contain moderately alkaline indicators, such as Cladium mariscoides, Myrica gale, Dasiphora fruticosa ssp. floribunda (= Pentaphylloides floribunda), and others.
A low dune field with more advanced plant succession often follows the first open dunes and swales. Pinus banksiana, Pinus strobus, and Pinus resinosa often form a scattered overstory canopy, while Juniperus communis, Juniperus horizontalis, Arctostaphylos uva-ursi, and Koeleria macrantha form a scattered ground layer.
Following the dune-field zone, both dunes and swales are typically forested. Moist swales are often forested, and soil organic material has often begun to accumulate. Thuja occidentalis, Alnus incana, Salix spp., and Acer rubrum dominate the partial overstory canopy and understory. In contrast to the dry or moist swales, wetter swales (where standing water is present through most of the year) may be dominated by Carices, such as Carex aquatilis and Carex stricta.
Forested beach ridges, with soils of medium to course sand, tend to be dominated by species common to dry-mesic and mesic northern forest. Soil moisture conditions appear to change dramatically with slight elevational changes and are reflected in the development of soil organic material and changing plant species. On higher, drier ridges, soils often have less than 3 cm of organic material. Pinus resinosa, Pinus strobus, and Quercus rubra are often codominant, while Betula papyrifera, Populus grandidentata, Abies balsamea, and Acer rubrum are subdominant or understory species. Pteridium aquilinum, Gaylussacia baccata, Vaccinium myrtilloides, Cornus canadensis, and Gaultheria procumbens occur in the shrub and ground layers.
Complexes located in embayments protected from prevailing winds tend to be formed entirely of low, water-lain beach ridges. As a result, even the beach ridges within these complexes support wetland vegetation.
Source: NatureServe Explorer
Environment
The system consists of a foredune, followed by a series of low to high dunes (uplands) and swales (wetlands). The system is often best developed where post-glacial streams entered an embayment and provide a dependable sand source. The combination of along-shore currents, waves, and winds form foredunes along the shoreline. With gradual long-term drops in water level, combined with post-glacial uplifting of the earth's crust, these low dunes gradually rise above the direct influence of the lakes, and new foredunes replace them. Over several thousand years, a series of ridges and swales is created. For most complexes, the flow of surface streams and groundwater maintain the wet conditions in the swales. With time, plant succession has proceeded to the point where the beach ridges are now forested while the wet swales are either forested or open wetlands. Along the Lake Superior shoreline, where post-glacial uplift is greatest, many of the complexes consist primarily of dry, forested swales. The dunes and swales differs depending on fetch and the amount of sediment available. The influence of Great Lakes water-level fluctuations is probably limited to the first few swales inland from the shoreline. For most of the complexes, the water occupying the swales comes from streams flowing from the adjacent uplands or from groundwater seepage.
Source: NatureServe Explorer
Dynamics
Foredune and immediate back dune areas are influenced by active dune processes of wind-caused "blowouts" and subsequent restabilization. Forested beach ridges may support fire regimes characteristic of similar upland forest systems outside of these complexes. Due to lakeshore proximity, heavy winds and resultant windthrow are common in forested ridges. Great Lakes water-level fluctuations likely influence water levels in swales closest to the shoreline, if at all. The hydrology of interdunal swales is driven largely by lateral flow through the porous beach ridges. Older swales (farthest from current lakeshores) in larger complexes support peat-forming bogs.
Source: NatureServe Explorer
Distribution
This system occurs throughout the Great Lakes shorelines of the United States and Canada. In Pennsylvania, this is only on Presque Isle.
Source: NatureServe Explorer
Ecologically Associated Plant Species
Plant species that characterize this ecosystem type, organized by vegetation stratum. These are species ecologically associated with the ecosystem, not confirmed present in any specific area.
Tree canopy
Abies balsamea, Acer rubrum, Betula papyrifera, Juniperus communis, Pinus banksiana, Pinus resinosa, Pinus strobus, Populus balsamifera, Populus grandidentata, Quercus rubra, Thuja occidentalis
Shrub/sapling (tall & short)
Alnus incana, Dasiphora fruticosa ssp. floribunda, Gaylussacia baccata, Myrica gale, Salix cordata, Salix serissima, Vaccinium myrtilloides
Short shrub/sapling
Arctostaphylos uva-ursi, Gaultheria procumbens, Juniperus horizontalis
Herb (field)
Ammophila breviligulata, Botrychium michiganense, Calamovilfa longifolia, Carex aquatilis, Carex stricta, Cladium mariscoides, Cornus canadensis, Eleocharis acicularis, Iris lacustris, Juncus balticus var. littoralis, Juncus nodosus, Juncus pelocarpus, Koeleria macrantha, Lycopodiella margueritiae, Lycopodiella subappressa, Oligoneuron houghtonii, Pteridium aquilinum, Schoenoplectus americanus
Source: NatureServe Ecological System assessment
Ecologically Associated Animals (14)
Animal species ecologically associated with this ecosystem type based on NatureServe assessment. These are species whose habitat requirements overlap with this ecosystem, not confirmed present in any specific roadless area.
Source: NatureServe Ecological System assessment
At-Risk Species Associated with this Ecosystem (9)
Species with conservation concern that are ecologically associated with this ecosystem type. G-Rank indicates global conservation status: G1 (critically imperiled) through G5 (secure). ESA status indicates U.S. Endangered Species Act listing.
Source: NatureServe Ecological System assessment
Component Associations (11)
Plant community associations that occur within this ecological system. Associations are the finest level of the U.S. National Vegetation Classification (USNVC) and describe specific, repeating assemblages of plant species. Each association represents a distinct community type that may be found where this ecosystem occurs.
| Name | G-Rank | |
|---|
| Ammophila breviligulata - (Schizachyrium scoparium) Grassland | G4 | NatureServe |
| Chamaedaphne calyculata - Myrica gale / Carex lasiocarpa Fen | G4 | NatureServe |
| Dasiphora fruticosa / Cladium mariscoides - Juncus arcticus ssp. littoralis - (Rhynchospora capillacea) Wet Meadow | G3 | NatureServe |
| Hudsonia tomentosa Dune Dwarf-shrubland | GNR | NatureServe |
| Juniperus horizontalis - Arctostaphylos uva-ursi - Juniperus communis Dune Dwarf-shrubland | G3 | NatureServe |
| Pinus banksiana - Pinus resinosa - Pinus strobus Dune Forest | G3 | NatureServe |
| Pinus banksiana - (Pinus resinosa) - Pinus strobus / Juniperus horizontalis Wooded Grassland | G2 | NatureServe |
| Populus deltoides - (Juniperus virginiana) Dune Woodland | G1 | NatureServe |
| Prunus pumila - (Ptelea trifoliata) Dune Shrubland | G2 | NatureServe |
| Thuja occidentalis - Fraxinus nigra Swamp | GNR | NatureServe |
| Thuja occidentalis - (Picea mariana, Abies balsamea) / Alnus incana Swamp | G4 | NatureServe |
State Conservation Ranks (7)
Subnational conservation status ranks (S-ranks) assigned by Natural Heritage Programs in each state where this ecosystem occurs. S1 indicates critically imperiled at the state level, S2 imperiled, S3 vulnerable, S4 apparently secure, and S5 secure. An ecosystem may be globally secure but imperiled in specific states at the edge of its range.
| State | S-Rank |
|---|
| IL | SNR |
| IN | SNR |
| MI | SNR |
| MN | SNR |
| NY | SNR |
| PA | SNR |
| WI | SNR |
Methodology and Data Sources
Ecosystem classification: Ecosystems are classified using the LANDFIRE 2024 Existing Vegetation Type (EVT) layer, mapped to NatureServe Terrestrial Ecological Systems via a curated crosswalk. Each EVT is linked to the USNVC (U.S. National Vegetation Classification) hierarchy through pixel-level co-occurrence analysis of LANDFIRE EVT and NatureServe IVC Group rasters across all roadless areas.
Vegetation coverage: Coverage percentages and hectares are derived from zonal statistics of the LANDFIRE 2024 EVT raster intersected with roadless area boundaries.
Ecosystem narratives and community species: Sourced from the NatureServe Explorer API, representing professional ecological assessments of vegetation composition, environmental setting, dynamics, threats, and characteristic species assemblages.
IVC hierarchy: The International Vegetation Classification hierarchy is sourced from the USNVC v3.0 Catalog, providing the full classification from Biome through Association levels.
Component associations: Plant community associations listed as components of each NatureServe Ecological System. Association data from the NatureServe Explorer API.
State ranks: Conservation status ranks assigned by NatureServe member programs in each state where the ecosystem occurs.