Kanapaha Prairie
Rapid Ecological Project Assessment
Draft Date:
Matrix Score: 7.18 of 9.44
Size: 4,435 acres
Number of parcels: 115
Number of owners: 87
Number of Buildings: 74
Location/Description:
The 4,435 acre Kanapaha Prairie
Project (KAN) is located west of
The Alachua County Ecological Inventory Project, also known as the KBN Study (KBN) ranked the Kanapaha Prairie Project 9th of 47 projects evaluated in the county, and categorized it as an above average project. The purpose of the KBN Study was to identify, inventory, map, describe, and evaluate the most significant natural biological communities, both upland and wetland, that remain in private ownership in Alachua County and make recommendations for protecting these natural resources (KBN 1996).
The KBN Study
summarized the
Protecting Water Resources:
The entire Kanapaha Prairie Project is located in the unconfined Aquifer Zone of Alachua County. This is a region of low and flat terrain where porous sands overlie the Floridan Aquifer System. “These porous sands comprise an area of high aquifer recharge and allow pollutants direct access to the aquifer” (Macesich 1988). The St. John’s River Water Management Districts Aquifer Recharge Map for Alachua County shows that 100% of the site falls in an area of high aquifer recharge, which is defined as 12 inches or more of recharge to the Floridan aquifer per year.
After the 1998 El Nino rainfall resulted in flooding of some residences, the regulatory flood elevation was re-evaluated by the Alachua County Engineer. The regulatory flood elevation was changed from 58 feet to 63 feet above sea level, pending a future Federal Emergency Management Agency (FEMA) re-evaluation. Based on 63 feet, approximately 60% of the total acreage is either wetlands or falls in the regulatory flood elevation.
Another result of the flooding in this area was the acquisition of a Wetland Reserve Program Conservation Easement over most of Levy Prairie, located in the Barr Hammock-Levy Prairie Project. Once this wetland is restored, it will allow storage of storm water in the Levy Prairie area and reduce the risk of flooding in Kanapaha Prairie.
“Kanapaha Prairie is a karst basin
with an outflow to the sink in the NW corner of the basin {Pearson Sink}, where
the water flows into the Floridan Aquifer.
This basin is itself the outflow area for
Protecting Natural
Communities and Landscapes:
Natural Communities
Sandhill
Xeric Hammock
Prairie Hammock
Wet Prairie
Basin Marsh
Depression Marsh
Flatwoods/
Other
Rough Pasture
Improved Pasture
Low Impact Development
Old Field Pine
Row Crops
The above list of natural
communities is from the KBN Study and staff observations. The ecological quality of
the natural communities range from fair to good.
The Project site is adjacent to the
Alachua County Forever (ACF) Barr Hammock-Levy Prairie Project.
Seventy-nine percent of the project
site is within the Florida Ecological Greenways Network (FEGN), in the priority
5 project area known as Paynes Prairie-Goethe. This FEGN project is one of
three highest priority projects in
The Paynes Prairie-Goethe FEGN
project is a part of the connection from
The connection between the
Eighty-three percent of the site falls within FNAI’s Habitat Conservation Priorities. Approximately 64% of the project area is a priority 4 and 19% is a priority 5. FNAI’s Habitat Conservation Priorities prioritize places on the landscape that would protect both the greatest number of rare species and those species with the greatest conservation need (FNAI, June 2001).
FNAI Under-represented Natural
Communities occur on 50% of the project site. Thirty one percent of the
site is upland hammock, 18% is pine flatwoods and 1% is sandhill. Under-represented Natural Communities are
those natural community types that were inadequately represented on
conservation lands in
PROTECTING PLANT AND
ANIMAL SPECIES:
Common Name Endemic/ Large Fed/State FCREPA/FNAI
Noted Observed
Home-Range Status Designation
Amphibians
Eastern
Tiger Salamander -/- -/- SU/S3 SM N
Gopher
Frog -/- -/SSC T/S3 SM C
Striped
Newt -/- -/- R/S2S3 SM
American
Alligator -/- T/SSC -/S4 SM C
Eastern
Diamondback Rattlesnake -/- -/- -/S3 SM C
Eastern
Indigo Snake -/- T/T SSC/S3 SM,N P
Gopher
Tortoise -/- -/SSC T/S3 F,N N
Peninsula
Mole Skink -/- -/- -/- SM
Southern
Hognose Snake P
Short-tailed
Snake X/- -/T T/S3 SM N
Spotted
Turtle -/- -/- R/S3? SM N
Birds
Black-Crowned
Night Heron -/- -/- SSC/S3? SM
Black
Rail -/- -/- R/S3 SM
Great
Egret -/- -/- SSC/S4 SM
Least
Bittern -/- -/- SSC/S4 SM
Little
Blue Heron -/- -/SSC SSC/S4 SM
Osprey -/- -/- T/S3S4 SM
Snowy
Egret -/- -/SSC SSC/S3 SM
Southeastern
American Kestrel -/- -/T T/S3 F,N
Southern
Bald Eagle -/L T/T T/S3 F,N,K
White
Ibis -/- -/SSC SSC/S4 SM
Wild
Turkey -/L F
Wood
Stork -/- E/E E/S2 SM
Bobcat -/L -/- -/- F
Northern
Yellow Bat -/- -/- SU/- SM
River
Otter -/- -/- -/- SM
X= Endemic, L=species with large home ranges according to the Closing the Gaps in Florida’s Wildlife Habitat System, S= observed by Alachua Co. EPD staff and/or an LCB subcommittee member, SM= documented on the Species Models maps created by the Florida Fish and Wildlife Conservation Commission, F= Focal species used for the most detailed analyses in the Closing the Gaps in Florida’s Wildlife Habitat Conservation System, Florida Game and Fresh Water Fish Commission, 1994, N= Florida Natural Areas Inventory Element Occurrence, P= potential for species based on habitat types, K=documented in the Alachua County Ecological Inventory Project.
Information in the “Observed” column was provided by local experts. David Auth, Ph.D. provided the information on amphibians and reptiles. This data was based on a series of maps made by Dr. Auth using location of capture of specimens in museums of the United States dating back to before 1900, and to a lesser extent, to visual sightings by Dr. Auth and other professional biologists. “P”=Present, indicates at least one museum record or visual sighting of the species in the project area. “C”=Close, indicates a museum record or visual sighting within one mile of the project border. “N”=Not Present and Not Close, indicates all map records for the species lie outside the one mile limit.
Exotic
plants found on this property include: exotic bamboos (both runners and
clumpers), goldenrain tree, Chinese tallow, coral ardisia, Boston fern, and
Chinese privet (KBN 1996). Air potato is present on a
portion of the site also.
About 14% of the KAN Project area is made up of Sandhill Crane Strategic Habitat Conservation Areas. Strategic Habitat Conservation Areas were developed by the Florida Fish and Wildlife Conservation Commission (FFWCC). They are private lands containing habitats critical to the continued survival of populations of inadequately protected plants and animals (Cox et al. 2000). These lands are essential to providing some of state’s rarest animals, plants, and natural communities with the land base necessary to sustain populations into the future (Cox et al.1994).
Fifty percent of the site is within Regional Biodiversity Hotspots. The purpose of the Regional Biodiversity Hot Spots maps, also developed by FFWCC, is to “convey more detailed information on the known locations of as many components of biological diversity as possible, regardless of whether or not they fall within proposed Strategic Habitat Conservation Areas, to help meet the need for conservation information at regional and local levels” (Cox et al. 1994).
The
The FFWCC bald eagle nest data shows two bald eagle nests on the project site and two others within two miles of the project site.
Achieving Social and
Human Values:
Approximately 53% of the KAN project falls in either a priority 2 or 3 Natural Resource-based Recreation Area, Knight, et al. 2000, and approximately 79% is within a priority 5 Ecological Greenway. The Natural Resource-based Recreation map was developed by FNAI in collaboration with DEP, FFWCC and DOF. The recreation potential of a site depends on available road access, presence of a water body or beach, proximity to urban areas, and size of the site. “These criteria were applied to Potential Natural Areas delineated by FNAI using aerial photography and revised using the 1995 Water Management District land cover data. Sites were ranked by recreation potential” (Knight, et al. 2000).
The
Management Issues:
The
“The ever increasing residential development is gradually reducing both the size and the quality of the habitats. In addition, people and people’s pets and fencing are increasing the stress and mortality suffered by many of the wild animals. The prairie and sandhill habitats were at the small end of the viability spectrum for use by sandhill cranes, fox squirrels, indigo snakes, and some other species ten years ago. The size of available habitat has been significantly reduced since then and this process is continuing at an increased rate today. It may already be too late, even if development could be stopped where it is now, to be able to manage a viable ecosystem here for these species. This is not to say the situation is hopeless. If development stopped now, or in the near future, and the homeowners here cooperated in a effort to improve and maintain habitat for wildlife, most of the wildlife species now present in the hammock, prairie, marsh and lake habitats could be maintained” (KBN 1996).
Economic Acquisition
Issues:
There are 115 parcels and 87 ownerships in the 4,435 acre Kanapaha Prairie Project. The property appraiser shows 74 buildings on their parcel data.
The project site falls within
unincorporated
One ownership, Kanapaha Ranch, makes
up 1,122 acres or 25% of the project acreage.
The Alachua County Property Appraisers 2002 Just Value or land value for
the entire project is $ 9,366,700 or $2,112/ acre. The ACPA’s total value
(Just, Miscellaneous and Buildings) for the project area is $16,105,000 or 3,632/acre. These figures are for comparative purposes
between nominated properties, and are not necessarily an accurate reflection of
the true cost of the property if acquired by the Alachua County Forever
Program.
The 1,122 acre Kanapaha Ranch Tracts
(07399-009-000, 07399-000-000, 07398-000-000, 07354-000-000, 07353-000-000) and
make up the majority of the prairie and a portion of the oak hammock
surrounding the south side of the prairie and are the keystone parcels for the
project.
Once the
actual prairie is acquired, the 264 acre
These are as follows:
Pearson Sink:
Hough 41.02
ac 07352-000-000
Kistner 50.04
ac 07353-019-000
Dunlap 38.81
ac 07353-017-001
Lamor III& Lamor 51.55
ac 07353-016-000
Connection to Barr Hammock Levy Prairie
Lane 16.22
ac 07354-001-000
20.39
ac 07354-022-000
49.65
ac 07397-004-006
38.39
ac 07398-016-000
2.86
ac 07354-004-001
Griffen 20.01
ac 07398-003-000
Mitchell 9.89
ac 07398-001-000
Campbell/Thompson 10.89 ac 07398-002-000
Waters 20.57
ac 07354-023-000
Other:
While there are no Florida Master Site file listed archeological or cultural sites within the project area, there are eight sites listed in the Division of Historic Preservation’s Master Site File within one mile of the Kanapaha Prairie Project site.
Literature Citations
Aucott, W. 1988. Water Resources Investigation Report
88-4057. USGS.
Cox, J., R. Kautz, M. MacLaughlin, and T. Gilbert.
1994. Closing the Gaps in
Cox, J. and R. Kautz. 2000. Habitat Conservation Needs of
Rare and Imperiled Wildlife in
Hoctor, T.S., J. Teisinger, M.G. Carr., P.C, Zwick. 2002.
Identification of Critical Linkages Within the
Knight, G., A. Knight, and J. Oetting. 2000. Florida Forever
Conservation Needs Assessment Summary Report to the Florida Forever Advisory
council.
KBN, A Golder Associates Company. 1996.
Macesich, M. 1988.
Geologic Interpretation of the Aquifer Pollution Potential in