New England Coastal Heathland and Grassland

EVT 7399Northern Atlantic Coastal Plain Grassland
CES203.895GNRHerbGrassland
Summary
Sandplain grasslands and heathlands of the southern New England / New York coast are areas of graminoid- and shrub-dominated vegetation maintained by periodic fire or other disturbance, as well as exposure to maritime influences. Developing on acidic, nutrient-poor, and very well-drained soils within a few kilometers of the ocean, they may occur as heathlands, grasslands, or support a patchwork of grass and shrub vegetation. Characteristic species include Gaylussacia baccata, Arctostaphylos uva-ursi, Corema conradii, Amelanchier nantucketensis, Hudsonia ericoides, Hudsonia tomentosa, Vaccinium angustifolium, Deschampsia flexuosa, Schizachyrium scoparium, and Carex pensylvanica. They provide habitat for several rare or uncommon forbs including Liatris scariosa var. novae-angliae and Agalinis acuta. They are important habitat for several bird and other animal species including the short-eared owl and regal fritillary, and (along with brushy plains and woodlands) provided habitat for the extinct heath hen.
Source: NatureServe Explorer
Vegetation
Characteristic species include Gaylussacia baccata, Arctostaphylos uva-ursi, Corema conradii, Amelanchier nantucketensis, Hudsonia ericoides, Hudsonia tomentosa, Vaccinium angustifolium, Deschampsia flexuosa, Schizachyrium scoparium, and Carex pensylvanica. They provide habitat for several rare or uncommon forbs including Liatris scariosa var. novae-angliae and Agalinis acuta.
Source: NatureServe Explorer
Environment
Sandplain grasslands and heathlands of the southern New England / New York coast are areas of graminoid- and shrub-dominated vegetation maintained by extreme conditions and periodic fire or other disturbance. Developing on acidic, nutrient-poor, and very well-drained soils, they may occur as heathlands, grasslands, or support a patchwork of grass and shrub vegetation.
Source: NatureServe Explorer
Dynamics
The largely exposed locations experience extreme variations in temperature and moisture, and the sandy, nutrient-poor soils contribute to prevention of establishment of woody vegetation. Coastal occurrences maintain their open nature with the stress and killing of woody plant tissue caused by high winds, desiccation, and salt spray. Examples that developed in slight depressions are also maintained by frost that persists longer into the growing season (MNHESP 2010a, 2010b). Prior to European settlement, this system is believed to have occurred as small patches in limited areas near the coast (Motzkin and Foster 2002); there may also have been patches in the vicinity of Native American settlements, based on the prevalence of charcoal in some palynological cores (Dunwiddie 1989). Presettlement grasslands appear to have been more likely on portions of Long Island (Hempstead Plains and Montauk) and Martha's Vineyard than on Nantucket, Block Island, or Cape Cod (Motzkin and Foster 2002). This native vegetation is often confused with similar semi-natural grasslands and heathlands characterized by a mixture of native and exotic species developed as a result of agriculture; some natural occurrences may have resulted as expansions of original native vegetation. They have increased in extent and largely post-date land clearing following European settlement (Foster et al. 2002). In addition, some heathlands may have developed on severely disturbed soils following the abandonment of agriculture and grazing (Motzkin and Foster 2002). Efforts to reverse the conversion of these heathlands and grasslands to tall shrublands or woodlands have generally used a mixture of prescribed fire and mowing, and less commonly grazing.
Source: NatureServe Explorer
Threats
Hempstead Plains grasslands, once an extensive native grassland, have been reduced by 99% of their original extent. Other maritime grasslands and heathlands have been considerably reduced in extent as well, largely as a result of development and agriculture. Current threats include development, isolation from larger natural systems, loss of connectivity to other natural systems, invasive species encroachment (e.g., Lespedeza cuneata, Artemisia vulgaris, Anthoxanthum odoratum, Celastrus orbiculata, Lonicera morrowii, Centaurea biebersteinii (= Centaurea maculosa)), and fire suppression. Major threats to maritime heathlands include development and use of four-wheel drive vehicle and impacts of off-road vehicle use (NYNHP 2013f). Examples of this system in New England were naturally small but are threatened by fragmentation or outright destruction by development, off-road vehicle traffic, and incursion by non-native species. Examples in the maritime zone are also threatened by heightened storm intensity, sea-level rise, and erosion.
Source: NatureServe Explorer
Distribution
This system is endemic to a small area ranging from the southern New York coastline north to Cape Cod, Massachusetts.
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.

Shrub/sapling (tall & short)

Amelanchier nantucketensis, Gaylussacia baccata

Short shrub/sapling

Arctostaphylos uva-ursi, Corema conradii, Hudsonia ericoides, Hudsonia tomentosa, Vaccinium angustifolium

Herb (field)

Agalinis acuta, Avenella flexuosa, Carex pensylvanica, Liatris novae-angliae var. novae-angliae, Schizachyrium scoparium
Source: NatureServe Ecological System assessment
Ecologically Associated Animals (3)

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.

Birds (1)

Common NameScientific NameG-Rank
Short-eared OwlAsio flammeusG5

Butterflies & Moths (2)

Common NameScientific NameG-Rank
a dart mothAbagrotis nefasciaG4
Regal FritillaryArgynnis idaliaG3?
Source: NatureServe Ecological System assessment
At-Risk Species Associated with this Ecosystem (4)

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.

Common NameScientific NameG-RankESA Status
Sandplain GerardiaAgalinis acutaG1QEndangered
Nantucket ShadbushAmelanchier nantucketensisG3Q--
Regal FritillaryArgynnis idaliaG3?--
Northern BlazingstarLiatris novae-angliae var. novae-angliaeG4T3--
Source: NatureServe Ecological System assessment
Component Associations (6)

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.

NameG-Rank
Amelanchier canadensis - Viburnum spp. - Morella pensylvanica Scrub ForestGNR NatureServe
Gaylussacia baccata - Vaccinium angustifolium - Arctostaphylos uva-ursi / Schizachyrium littorale Dwarf-shrublandG3 NatureServe
Morella pensylvanica / Schizachyrium littorale - Danthonia spicata Shrub GrasslandG2 NatureServe
Pinus rigida / Quercus ilicifolia / Morella pensylvanica WoodlandG3 NatureServe
Quercus stellata - Sassafras albidum / Smilax glauca WoodlandGNR NatureServe
Schizachyrium scoparium - Sorghastrum nutans - Hypoxis hirsuta - Baptisia tinctoria GrasslandG1 NatureServe
State Conservation Ranks (3)

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.

StateS-Rank
MASNR
NYSNR
RISNR
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.