DC.
Identity
Unique IDELEMENT_GLOBAL.2.144987
Element CodePDSAX0P060
Record TypeSPECIES
ClassificationSpecies
Classification StatusStandard
Name CategoryVascular Plant
Endemicendemic to a single nation
KingdomPlantae
PhylumAnthophyta
ClassDicotyledoneae
OrderCelastrales
FamilyCelastraceae
GenusParnassia
Other Common Nameslargeleaf grass of Parnassus (EN)
Concept ReferenceKartesz, J.T. 1994. A synonymized checklist of the vascular flora of the United States, Canada, and Greenland. 2nd edition. 2 vols. Timber Press, Portland, OR.
Conservation Status
Rank Method Rank calculation - Biotics v2
Review Date2025-04-30
Change Date2025-04-30
Edition Date2025-04-24
Edition AuthorsWeakley (1994), rev. L. Morse (1998, 2000), rev. C. Nordman (2025).
Threat ImpactHigh
Range Extent200,000-2,500,000 square km (about 80,000-1,000,000 square miles)
Number of Occurrences81 to >300
Rank ReasonsLargeleaf Grass-of-Parnassus (Parnassia grandifolia) occurs in the eastern United States, in the Appalachians, Interior Low Plateau, Interior Highlands and widely disjunct areas of the Coastal Plain. It occurs in scattered locations from Virginia and West Virginia, west to Missouri and eastern Texas, and occurs disjunct in the Florida Panhandle, Florida Peninsula, and southeastern North Carolina. It is a perennial plant with round leaves and white flowers which occurs in wetlands, especially with calcareous seepage. It is rare across its range except it is considered just uncommon in Arkansas and Missouri, it is estimated there are more than 150 occurrences. It is known from the Apalachicola, De Soto (on Camp Shelby), Kisatchie, Mark Twain, Pisgah, Ocala, and Ozark National Forests, and from some state parks, natural areas, nature preserves, and wildlife management areas. It is threatened by filling and other impacts to wetlands, land-use conversion and habitat fragmentation, such as from road construction and residential or commercial development. Intensive forest management practices (such as skidder or logging road crossings, herbicide or mechanical site preparation), canopy closure from competing shrubs, invasive exotic grasses such as Arthraxon hispidus, Microstegium vimineum, Schedonorus arundincaeus and rooting by feral hogs are also threats.
Range Extent CommentsLargeleaf Grass-of-Parnassus (Parnassia grandifolia) occurs in the eastern United States, in the Appalachians, Interior Low Plateau, Interior Highlands and widely disjunct areas in the Coastal Plain. It occurs in scattered locations from Virginia and West Virginia, west to Missouri, Arkansas, southeastern Oklahoma, eastern Texas, Louisiana, southern Mississippi, and is disjunct in the Florida Panhandle, Florida Peninsula, and southeastern North Carolina. It is rare across its range except it is considered just uncommon (not rare) in the Interior Highlands of Missouri and Arkansas (Gentry et al. 2013, FNA 2016, FNAI 2025, GBIF 2025, John Logan, pers. comm., 1993, MacRoberts et al. 1997, Weakley and Southeastern Flora Team 2025). Range extent was estimated to be about 1,140,000 square kilometers, using herbarium specimens, photo-based observations, and NatureServe Network occurrence data collected between 1994 and 2025 (GBIF 2025, iNaturalist 2025, NatureServe 2025, RARECAT 2025, SEINet 2025).
Occurrences CommentsBy applying a 1 km separation distance to herbarium specimens, photo-based observations, and NatureServe Network occurrence data documented between 1994 and 2025, it is estimated that there are 150 or more occurrences of Parnassia grandifolia, rangewide (GBIF 2025, iNaturalist 2025, NatureServe 2025, RARECAT 2025, SEINet 2025). It is considered rare throughout its range and just uncommon (not rare) in the Interior Highlands of Missouri and Arkansas (Weakley and Southeastern Flora Team 2025). There have been over 100 locations reported for this species in Arkansas (John Logan, pers. comm., 1993).
Threat Impact CommentsParnassia grandifolia is rare wherever it occurs east of the Mississippi River, making it especially threatened by filling and other impacts to wetlands, land-use conversion and habitat fragmentation (Southern Appalachian Species Viability Project 2002), this may be from impacts of road construction and residential or commercial development. Intensive forest management practices (such as skidder or logging road crossings, herbicide or mechanical site preparation) could irreparably damage the fragile wetland habitat of this species. Canopy closure from competing shrubs, invasive exotic grasses which may invade wetlands such as Arthraxon hispidus, Microstegium vimineum, Schedonorus arundincaeus and rooting by feral hogs are threats (NatureServe 2025).