Northern Tallgrass Prairie

EVT 7420
CES205.686GNRHerbGrassland
Summary
This system is found primarily in the Northern Tallgrass ecoregion ranging along the Red River basin in Minnesota and the Dakotas to Lake Manitoba in Canada. It constitutes the northernmost extension of the "true" prairies. Similar to Central Tallgrass Prairie (CES205.683), this system is dominated by tallgrass species such as Andropogon gerardii, Sorghastrum nutans, and Panicum virgatum. However, the soils in this region are not as rich nor deep, the growing season length and precipitation are less, and thus this system does not have as much species diversity as grasslands to the south. This system is often found on well-drained, drier soils and can grade into Eastern Great Plains Tallgrass Aspen Parkland (CES205.688) to the north and east. Grazing and fire influenced this system historically. Much of this system has been converted to agriculture with very few unaltered and highly fragmented examples remaining.
Source: NatureServe Explorer
Dynamics
Fire plays an important role in the maintenance of this prairie system (Curtis 1959, Vogl 1964, Anderson 1990b). Fire promotes seed production and flowering necessary for plant regeneration. Because environmental conditions are suitable for tree growth, without recurrent fire (every 2-10 years), succession to forest or woodland will occur rapidly (Minnesota DNR 2005b). From Landfire BpS: Frequent fires impacted this prairie system every 1-3 years, maintaining grass and forb vegetation. Fire could occur throughout the year with larger, less frequent fires occurring during the dormant season and smaller, more frequent fires occurring during the growing season. Native American burning, essential to maintaining the eastern tallgrass prairie, was bimodal in distribution, peaking in April and October with lightning ignition occurring primarily during July and August (Higgins 1986).

Bison grazing as a major disturbance was likely much more limited than prairies further west. Elk probably contributed to the impact of grazing and browsing as well, but it is assumed that the total contributions of these two species was still considerably less than to the west. The elk may have contributed to the reduction of young woody saplings invading prairie adjacent to protected woody areas. Prior to European settlement, episodic grazing by large, native mammals was common and encouraged the persistence of several native grass and forb species (Minnesota DNR 2005b). Insect and small mammal herbivory impacts composition and dominance. From Landfire BpS: Bison, with peripheral help from grasshoppers, elk, antelope and a myriad of smaller animals made herbivory one of the dominating factors of the northern tallgrass prairie (Severson and Sieg 2006). With estimates of 30-60 million bison in the Northern Great Plains (Isenberg 2000), herbivory by large mammals also was a significant disturbance to the grasslands. Bison herbivory occurred in a mob-grazing or flash-grazing method, with extensive herds migrating across the prairie as they graze. Modern rotational grazing systems simulate this by resting areas after intensive grazing. Elk, too, may have played an important role than generally believed, particularly in the eastern portion of the zone. Whether bison or elk, large mammals preferentially grazed recently burned sites.
Source: NatureServe Explorer
Threats
The northern tallgrass system has been significantly transformed since European settlement largely into an agricultural landscape. Remaining patches are highly fragmented. Woodland acreage has increased appreciably due to fire suppression, extirpation of native grazers, and human disturbance. Many areas that were not cultivated are subject to intensive grazing which has resulted in most native species being replaced by introduced ones (Minnesota DNR 2005b). Without heavy intervention and intense management and restoration efforts, it is highly unlikely that many remaining northern tallgrass prairie patches will be self-sustaining or persist over time (Koper et al. 2010).
Source: NatureServe Explorer
Distribution
Found primarily in the Northern Tallgrass ecoregion ranging along the Red River basin in Minnesota and the Dakotas to Lake Manitoba in Canada.
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.

Herb (field)

Andropogon gerardi, Hesperostipa spartea, Lithospermum canescens, Panicum virgatum, Schizachyrium scoparium, Sorghastrum nutans, Zizia aptera
Source: NatureServe Ecological System assessment
Ecologically Associated Animals (11)

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.

Mammals (5)

Common NameScientific NameG-Rank
Plains Pocket GopherGeomys bursariusG5
Thirteen-lined Ground SquirrelIctidomys tridecemlineatusG5
Prairie VoleMicrotus ochrogasterG5
Franklin's Ground SquirrelPoliocitellus frankliniiG5
Western Harvest MouseReithrodontomys megalotisG5

Reptiles (2)

Common NameScientific NameG-Rank
Prairie SkinkPlestiodon septentrionalisG5
Plains GartersnakeThamnophis radixG5

Butterflies & Moths (3)

Common NameScientific NameG-Rank
Regal FritillaryArgynnis idaliaG3?
Dakota SkipperHesperia dacotaeG2
Poweshiek SkipperlingOarisma poweshiekG1

Other (1)

Common NameScientific NameG-Rank
Meadow VoleMicrotus pennsylvanicusG5
Source: NatureServe Ecological System assessment
At-Risk Species Associated with this Ecosystem (3)

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
Regal FritillaryArgynnis idaliaG3?--
Dakota SkipperHesperia dacotaeG2Threatened
Poweshiek SkipperlingOarisma poweshiekG1Endangered
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
Andropogon gerardii - Hesperostipa spartea - Sporobolus heterolepis GrasslandG2 NatureServe
Andropogon gerardii - (Panicum virgatum) - Muhlenbergia richardsonis Wet MeadowG3 NatureServe
Carex prairea - Schoenoplectus pungens - Rhynchospora capillacea FenG2 NatureServe
Populus tremuloides - Quercus macrocarpa - Andropogon gerardii Brush GrasslandG2 NatureServe
Schizachyrium scoparium - Bouteloua curtipendula - Hesperostipa spartea - (Pascopyrum smithii) GrasslandG3 NatureServe
Schizachyrium scoparium - Bouteloua curtipendula Loess Mixedgrass GrasslandG3 NatureServe
State Conservation Ranks (4)

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
IASNR
MNSNR
NDSNR
SDSNR
Roadless Areas (5)

Inventoried Roadless Areas where this ecosystem is present, identified from LANDFIRE 2024 Existing Vegetation Type spatial analysis. Coverage indicates the proportion of each area occupied by this ecosystem type.

North Dakota (5)

AreaForestCoverageHectares
DelamereDakota Prairie Grasslands37.1%762.57
DurlerDakota Prairie Grasslands29.6%1,491.48
VenloDakota Prairie Grasslands28.2%606.15
SheyenneDakota Prairie Grasslands24.6%1,444.86
McleodDakota Prairie Grasslands21.4%790.83
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.