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Bog Asphodel

Photo taken by
Michael Hogan
Fine Art Photography of
Southern New Jersey
Narthecium americanum (Bog asphodel)
Narthecium americanum Ker-Gawl. Yellow asphodel
Abama american (Ker-Gawl.) Morong
Abama montan Small
Nartheciumossifragum var. americanum (Ker-Gawl.) Gray
TAXONOMY
Like many species, Bog Asphodel has undergone taxonomic review and
taxonomic changes. It was known as Abama
Americana and Abama Montana. Our
species was also considered to be a variety of the European and western Asian
Narthecium ossifragrum (var. americanum).
It resembles the other three species of Narthecium, but is
geographically separated from them as they are from each other. Other than
the European and western Asian N. ossifragum, N.
californicum is found in Oregon
and California and N. asiaticum is found in Asia. Narthecium
americanum is generally smaller in size, with smaller structural features
than the other species. Some researchers believe that there is some
justification for only recognizing one worldwide species.
Due to the recent research on plant families, Narthecium will
probably be taken out of the Lily family in future flora manuals. The lily
family is now being split up into many families (over 30). Narthecium
is considered to be in the Nartheciaceae with Aletris (colic root) and Lophiola
(goldencrest).
NJ NATURAL HERITAGE PROGRAM
The Nature Heritage Program states that the recorded range for N.
americanum is New Jersey, Delaware,
North Carolina, and South
Carolina. Two historical occurences
in Delaware. One historical
occurrence occurs in both North Carolina
and South Carolina. In New
Jersey, there are numerous locations.
DESCRIPTION OF PLANT
This species is a perennial rhizomatous herb with linear equitant basal
leaves and an erect stem terminated by a raceme of yellow flowers. The plants
can be up to 50 cm tall from stout horizontal rhizomes. The flower consists
of three petals and three sepals all yellow and linear up to 9 mm long. The
stamens are densely hairy with filiform filaments. The ovary is tapering to
the style with a small 3-lobed stigma. The fruits are long pointed
reddish-brown capsules up to 14 mm long. Seeds are numerous and narrowly
elliptic with elongate filiform tails at each end.
HABITAT
Stone describes the habitat as moist savannas or broad, wet sandy bogs
along streams. Jim Stasz stated that plants often
grow in quaking bog mats associated with spring seeps. The plant also grows
on firm wet substrates that are generally free of standing water but may be
periodically flooded for short periods of time. Populations often border
white cedar swamps and sometimes are in openings of such swamps. Associated
with N. americanum are: Oclemena nemoralis (Ait.) Greene Bog
Nodding-Aster, Calamagrostis pickeringii Gray Pickering’s Reed Grass, Calamovilfa brevipilis
(Torr.) Scribn. Pine
Barren Sand-Reed, Juncus caesariensis Coville New
Jersey Rush, Lophiola aurea
Ker-Gawl. Goldencrest, Muhlenbergia torreyana
(J.A. Schultes) A.S. Hitchc.
New Jersey Muhly, Platanthera integra (Nutt.) Gray ex Beck Yellow Fringeless
Orchid, Pogonia ophioglossoides (L.) Ker-Gawl. Snake-Mouth Orchid, Rhynchospora
oligantha Gray Feather-Bristle Beak Sedge, Schizaea pusilla Pursh Little Curly-Grass Fern, Triantha
racemosea (Walt.) Small Coastal False Asphodel, and many species of Sphagnum moss.
BIOLOGY/ECOLOGY
This species in New Jersey
flowers in June and July. Seed production is high and although seeds
germinate readily, seedlings are rarely encountered in the field.
Reproduction of N. americanum is primarily vegetative from rhizomes.
The rhizomes can form an extensive turf.
Water movement may be one of the characteristics that Bog Asphodel depends
on. It is not found in places where water movement is minimal or stagnant.
The plant may be an indicator of flushed habitats. Flooding or continuous
surface saturation however may eradicate the plant. Stone stated that Bog
Asphodel is one of those species which are exterminated by cranberry culture.
Shading of habitats inhibits flowering of N. americanum.
POPULATION QUALITY
Numerous populations with high EO quality occur in the pinelands. A few
sites have been eliminated by conversion to commercial cranberry bogs and at
least one population by residential development. Some populations are
non-flowering due to shading or due to changes in the hydrology of the site.
THREATS
The greatest threat is disruption of the water regime. Making the habitat
wetter or drier will affect it. Flooding by beaver, commercial cranberry
growers, and damming streams for recreational use are just some of the uses
that can lower or raise water levels and cause the plant problems. Habitat
destruction as related to development is a threat to sites near the periphery
of the pinelands. Trampling by all-terrain vehicles is a potential problem.
MONITORING
Populations should be evaluated every two or three years. Non-flowering
populations need more study to determine what controls flowering. More
information is needed about its tolerance to fire and logging. And what
effect does succession have on its survival?
MANAGEMENT
Watersheds are critical to the protection of this species. Disruptions of
the water regime will eliminate it.
Note: Most of this information was taken from the Element Stewardship
Abstract that is available on the internet at http://www.nj.gov/dep/parksandforest/natural/heritage/textfiles/nartham.txt
Prepared by Bill Olson
Botanical Consultant
Howell, New Jersey 07731
Email Bill Olson
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Title Design by Elayne A.
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