Our flora focus today is on a plant called Knieskern's beaked rush, or Rhynchosproa knieskernii. (Hereafter referred to as R. knieskernii). I've chosen to focus on a species that has a global distribution consisting of: New Jersey. That's right. It grows only in New Jersey. No where else in the world. The information below is based on 1993 population figures; since then, a number of populations caused by human disturbance have been noted.
US Fish & Wildlife will be instituting a Recovery Workshop this summer for this plant and an Adopt a Knieskern's Population program.
Rhynchospora knieskernii was first discovered by Peter D. Knieskern, M.D., in Ocean County, New Jersey in 1843 (Stone 1911). Dr. Knieskern originally labeled specimens of the plant as Rhynchospora grayana. However, a description of the species was not published until John Carey did so in 1847 (Carey 1847), renaming the species in honor of Dr. Knieskern.
Photo
R. knieskernii is a perennial sedge (or sometimes annual if growing conditions are adverse), usually under 40 cm, occasionally up to 60 cm. It is not rhizotomous. Here is the technical description: It is characterized by spikelets along the length of the stem. The achene (seed) has 6 bristles, retrorsely barbed, somewhere between half as long as the achene to about the same length as the achene, and the tubercule is triangular, and about half the length of the achene. USFWS suggests that the bristles may assist in animal dispersal. (1993) Achene is yellow brown in the center and darker around the edges. It fruits late July until frost. It is an obligate hydrophyte, meaning that it requires a certain amount of wetlands to persist. It was federally listed as threatened on July 18, 1991.
R. knieskernii is endemic to the New Jersey Pine Barrens, known from 5 counties.
* Monmouth
* Atlantic
* Burlington
* Camden
* Ocean
Natureserv lists its occurances within two watersheds: Mullica-Toms River and Great Egg Harbor.
Two extirpated populations are known from Delaware. It has not been documented in Delaware since 1875; possibly this plant was collected in New Jersey and mislabeled as to its origin.
Natureserv reports 52 known locations, 38 of which are extant (existing). They seem to break down into two categories:
* Naturally occurring populations
* Anthrogenic populations
Naturally occurring populations: Populations that are naturally occurring are generally found in wet bog iron areas, or over clay deposits, often adjacent to slow moving streams, pitch pine lowland swales, and pine barrens savannahs (USFWS 1992). Characteristic of these sites is early succession, low soil productivity, high acidity, frequency of fire, and a ground water influenced, constantly fluctuating water regime. Approximately six of the known populations are naturally occurring. The constant erosion and fire frequency inflicted on the area from the fluctuating water regime naturally maintain the ecosystem. (stochastic events)
Anthrogenic populations: Roughly 32 of these populations are anthrogenic, a result of artificial disturbance:
* Railroad, roadside, or powerline right of ways
* Inactive sand and clay pits (sand, clay and gravel mining, borrow pit excavation) that hold water, ephemeral ponds of a sort
* Cranberry bog construction
These sites often have an underlying clay lens more so than a bog iron deposit. Again, sites typically have fluctuating water regimes as well as various combinations of sand, clay, bog ore, gravel, and peat (e.g., sandy clay, gravelly sand with clay inclusions and traces of bog iron (Kolaga and Schuyler 1993); clayey sand mixed with gravel, peaty sand (Gordon 1993); and sandy peat (New Jersey Heritage Program 1991).
Reasons for rarity:
Intrinsic:
* An ecospecialist: R. knieskernii is a poor competitor. Succession is the antithesis of this species; it requires natural disturbances such as fire or flood scouring, or anthrogenic disturbances, such as Right of way maintenance, occasional ORV use, etc. Of the 38 extant sites referenced by USFWS in 1993, 19 are said to be undergo habitat succession that could eliminate those populations.
* Physiological factors: an eco-specialist, an obligate, narrow hydrophyte
* Temporal: a neoendemic: Neoendemics are found frequently in geologically youthful habitats, and often their rarity is partly a function of their youth - in some cases these plants have not had time to expand their range from their point of origin to their climatic and geological limits. (Fiedler) Endemic species must rely exclusively for their long-term viability and continued existence on the management of the geographical area to which they are restricted.
* Stochastic events necessary to promote habitat conducive for R. knieskernii: fire, erosion, flood scouring, etc.
* Edaphic factors: only somewhat so; naturally occurring populations tend to favor particular soil types with bog iron substrate; anthrogenic populations seem to have more flexibility as to soil type and often have an underlying clay lens.
R. knieskernii is both an endemic and habitat restricted, both characteristic traits of rarity in the Pine barrens.
Anthropogenic:
* Habitat loss/degradation
* Roadside grading, sand & gravel operation
* Development
* Recreational uses
* Change in hydrology
* Fire suppression—may have eliminated or altered a component of the ecosystem that naturally maintained habitat for this species
Threats: Vulnerable to roadside grading, sand & gravel operations, habitat succession, development, & recreational pressures.
What you can do: Private landowners with Knieskern's beaked-rush on their property can help protect the species by preventing people from picking or digging the plant and by contacting the U.S. Fish and Wildlife Service to develop a protection and managient strategy for the property. If you find plants that appear to be Knieskern's beaked-rush, carefully note their location and, if possible, photograph the plant. Please do not remove the plant! Notify the U.S. Fish and Wildlife Service and your State's Natural Heritage Program (USFW).
Sources
Fiedler, Peggy. Rarity in Vascular Plants. (from CNPS Inventory, 6th Edition, 2001)
http://www.cnps.org/programs/Rare_Plant/inventory/rarity.htm
Flora of North America
http://www.efloras.org/florataxon.aspx?flora_id=1&taxon_id=242357898
NatureServ
http://www.natureserve.org/explorer/servlet/NatureServe?searchName=Rhynchospora+knieskernii
NJ Natural Heritage Database
http://www.state.nj.us/dep/parksandforests/natural/heritage/
USFW Recovery Plan
http://ecos.fws.gov/docs/recovery_plans/1993/930929b.pdf
USFW Species Account:
http://endangered.fws.gov/i/q/saq6q.html
W3 Tropicos
http://mobot.mobot.org/cgi-bin/search_pick?name=Rhynchospora+knieskernii
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