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3.6 SOUTHWEST FLORIDA/BIG CYPRESS BASIN
Sub-Region 5
Index of Southwest
Florida/Big Cypress Basin Restoration Projects
Southwest/Big Cypress |
Project ID # |
PPM |
Lead Organization |
Start |
Finish |
Financial
Requirement |
Appropriated to Date |
Page |
Additional
Water Conveyance Structures Under Tamiami Trail |
SW01 |
Hibbard |
DOT |
1998 |
2002 |
4,355,000 |
0 |
262 |
Seminole
Tribe Water Conservation Project for Big Cypress Reservation |
SW03 |
Tepper |
Seminoles |
1998 |
2005 |
70,053,000 |
0 |
264 |
Belle
Meade Land Acquisition |
SW04 |
Boler |
FDEP |
1997 |
1999 |
33,726,136 |
10,916,425 |
266 |
Big
Cypress National Preserve Addition |
SW05 |
Hibbard |
NPS |
1998 |
2001 |
30,320,000 |
18,520,000 |
267 |
Big
Cypress National Preserve Mineral Rights |
SW06 |
Hibbard |
NPS |
|
|
0 |
0 |
268 |
Big
Cypress National Preserve Private Inholdings |
SW07 |
Hibbard |
NPS |
On
going |
2001 |
165,261,364 |
154,561,364 |
269 |
Corkscrew
Regional Ecosystem Watershed |
SW08 |
Rinaldi |
SFWMD |
1995 |
2002 |
47,530,000 |
36,810,000 |
270 |
Fakahatchee
Strand Land Acquisition Project |
SW09 |
Boler |
FDEP |
1997 |
1999 |
23,310,945 |
19,044,116 |
271 |
Southern
Golden Gate Estates Hydrological Restoration |
SW10 |
Kuester |
FDEP |
1998 |
2005 |
53,760,000 |
38,560,000 |
272 |
Land
Adjacent to Dade County Training Jetport |
SW11 |
Hibbard |
NPS |
|
|
0 |
0 |
274 |
Southern
CREW Project Addition/Imperial River Flowways |
SW12 |
Merriam |
SFWMD |
1997 |
2001 |
30,484,000 |
2,500,000 |
275 |
Twelve
Mile Slough |
SW13 |
Rinaldi |
SFWMD |
1998 |
2001 |
3,300,000 |
3,300,000 |
277 |
Seminole
Tribe Best Management Practices for the Big Cypress Reservation |
SW14 |
Tepper
|
Seminoles |
1998 |
2001 |
4,013,000 |
0 |
278 |
Seminole
Tribe Exotic Species Removal |
SW15 |
Tepper |
Seminoles |
1998 |
2010 |
988,000 |
76,000 |
279 |
Picayune
Strand State Forest Exotic Species Management |
SW16 |
Folks |
FDACS |
1998 |
2010 |
24,914,000 |
0 |
280 |
Assimilative
Capacity for Phosphorus of C&SF Canals on the Big Cypress Reservation |
SW17 |
Tepper |
Seminoles |
1997 |
2004 |
400,000 |
100,000 |
281 |
Forested
Wetland Nutrient Uptake Research |
SW18 |
Tepper |
Seminoles |
1998 |
2004 |
400,000 |
110,000 |
282 |
Impacts
of Sludge Deposition on Phosphorus Levels on the Big Cypress Reservation |
SW19 |
Tepper |
Seminoles |
1998 |
1998 |
30,000 |
0 |
283 |
Melaleuca
Control (Critical) on Big Cypress National Preserve |
SW20 |
Hibbard |
NPS |
1998 |
2005 |
1,400,000 |
700,000 |
284 |
Characterization
of the geologic framework of the subsurface coarse sand zone and its influence on Florida
Bay |
SW21 |
Scott |
FDEP |
1997 |
2000 |
1,500,000 |
0 |
285 |
Subsurface
Sand Body Investigation (Sunniland) |
SW22 |
Scott |
FDEP |
1996 |
1997 |
10,000 |
10,000 |
286 |
Southwest
Surficial Aquifer System Investigation |
SW23 |
Scott |
FDEP |
1997 |
1998 |
60,000 |
60,000 |
287 |
Henderson
Creek/Belle Meade Restoration Project |
SW24 |
Haner |
FDEP |
1997 |
2002 |
5,140,000 |
3,940,000 |
288 |
Lake
Trafford Restoration |
SW26 |
Boler |
FDEP |
1998 |
2002 |
8,243,000 |
43,000 |
290 |
Estero
Bay Land Acquisition Program |
SW28 |
Boler |
FDEP |
1985 |
end |
20,784,050 |
7,973,750 |
292 |
Lake
Park Restoration Project |
SW29 |
Boler |
FDEP |
1997 |
2003 |
5,000,000 |
2,541,000 |
293 |
Town
Of Ft. Myers Beach Storm Water Retrofit Program |
SW30 |
Boler |
FDEP |
1998 |
2000 |
120,000 |
0 |
294 |
Rookery
Bay Land Acquisition Project |
SW31 |
Boler |
FDEP |
1997 |
1999 |
38,826,750 |
31,355,418 |
295 |
Collier
Seminole Resource Management/Acquisition Project |
SW33 |
Henry |
FPS |
1998 |
2000 |
808,000 |
404,000 |
296 |
Fakahatchee
Strand State Preserve Exotic Removal Project |
SW34 |
Toppin |
FDEP |
1998 |
2001 |
200,000 |
0 |
298 |
Estero
Bay Aquatic Preserve and Buffer Reserve Enhancement and Exotic Removal Project |
SW35 |
Stafford |
FDEP |
1998 |
2001 |
1,365,000 |
50,842 |
299 |
Long-term
Study of Fire Regimes in Pineland and Associated Cypress Wetlands |
SW36 |
Snyder |
USGS/BRD |
1994 |
2002 |
660,000 |
282,000 |
300 |
Strand
Structure and Productivity of Short-hydroperiod Graminoid Wetlands |
SW37 |
Snyder |
USGS/BRD |
1999 |
2002 |
470,000 |
0 |
301 |
Aquatic
Animal Dynamics in Big Cypress Habitats |
SW38 |
Loftus |
USGS/BRD |
1999 |
2004 |
210,000 |
0 |
302 |
Seminole
Critical Project for the West side of the Big Cypress Water Conservation Project |
SW39 |
Tepper |
Seminoles |
1998 |
2002 |
45,198,000 |
0 |
303 |
Plant
Biodiversity of Big Cypress National Preserve |
SW40 |
Snyder |
USGS/BRD |
1998 |
2000 |
48,000 |
48,000 |
305 |
Hydrologic
Reconnaissance of the gray limestone aquifer of South Florida |
SW41 |
Reese |
USGS/BRD |
1996 |
1999 |
817,000 |
323,600 |
306 |
Stratigraphy
and hydrogeology of the surficial aquifer system of Southwest Florida |
SW43 |
Wardlaw |
USGS |
1996 |
1999 |
939,177 |
635,050 |
307 |
Okaloacoochee
Slough |
SW44 |
Rinaldi |
SFWMD |
1998 |
2001 |
20,352,060 |
20,352,060 |
308 |
Southwest
Florida Water Management Model and Natural System Model |
SW50 |
Merriam |
USFWS |
2000 |
2005 |
2,000,000 |
0 |
309 |
Conservation
Easements for Multi-Species Recovery and Water Quality Maintenance |
SW51 |
Eller |
USFWS |
1999 |
2008 |
50,700,000 |
0 |
310 |
Subtotal Southwest/Big Cypress: |
|
|
|
|
|
697,696,482 |
353,216,625 |
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ECOLOGICAL SETTING:
The Southwest Florida/Big Cypress Basin (SW/BCB) extends north from
Everglades National Park (ENP) to the Caloosahatchee River watershed, and east from the
Gulf of Mexico to the L-4 and L-28 canal systems and Lostmans Slough. It includes southern
Lee and Hendry, all of Collier, and small portions of western Broward and Dade, and
northwestern Monroe counties.
The region provides significant habitat for many threatened and
endangered species and species of special concern, including the American bald eagle,
Florida panther, woodstork, snail kite, snowy plover, Florida sandhill crane, red-cockaded
woodpecker, Big Cypress fox squirrel, Florida black bear, alligator, limpkin, Everglades
mink, crocodile, Loggerhead sea turtle, West Indian manatee, snook, jewfish, gopher
tortoise, Eastern indigo snake, many species of wading birds and migratory shore birds and
songbirds.
The slash pine forests of southwest Florida have been identified as an
endangered ecosystem. This sub-region, along with the western Greater Okeechobee
sub-region, may have the State's greatest acreage of hydric pine flatwoods, which have
significant ecological and hydrological value. Plant species diversity is high, with over
900 species, including 85 protected species. At least 21 Federal and State listed animal
species are supported by the flatwoods communities important to groundwater recharge.
The sub-region also encompasses tremendous acreages of ecologically
valuable wetlands. Big Cypress National Preserve (BCNP) and its Addition Lands, is
approximately 728,000 acres of swamplands. It is dominated by seasonally flooded cypress
savannas and freshwater marshes interspersed with islands of slash pine and mixed hardwood
hammocks. The BCNP is about one-third covered with cypress trees, mostly dwarf pond
cypress. The few remaining giant bald cypresses, escapees of the lumber era, may be
600-700 years old.
Fakahatchee Strand, over 74,000 acres in size, is the center of native
U.S. orchid species diversity. The Corkscrew Regional Ecosystem Watershed (CREW) is more
than 58,000 acres of mostly functional wetlands. It supports North America's largest
nesting colony of endangered wood storks and largest remaining stand of virgin bald
cypress. Within CREW is the 1,500-acre Lake Trafford, the largest freshwater lake in the
region. Lake Trafford supports significant bass and other fish, invertebrate, and bird
populations. The CREW provides habitat for about 75 protected plant and animal species, as
well as having significant hydrologic importance by conveying water to the Florida Panther
National Wildlife Refuge (NWR), Fakahatchee Strand State Preserve, Rookery Bay, and Estero
Bay Aquatic Preserve and Buffer Reserve watersheds. Okaloacoochee Slough encompasses
approximately 140,000 acres of mostly priority 1 habitat for Florida panthers. Other
significant wetland areas lie within the Big Cypress Area of Critical State Concern
(ACSC); Belle Meade and Southern Golden Gate land acquisition projects; Picayune Strand
State Forest; the Florida Panther and 10,000 Islands National Wildlife Refuges; and
Collier-Seminole State Park.
The coastal areas in this subregion are characterized by mangrove
dominated estuaries with salt marsh habitats occurring landward of the mangrove zone. They
generally provide a rich and abundant fish and shellfish nursery, as well as supporting
bottlenose dolphin, the endangered West Indian Manatee, and an abundance of wading and
shore bird species. Seagrasses, oyster bars, and mudflats are common benthic habitats.
Beaches and dunes provide critical nesting habitat for many species of protected migratory
shore birds and the threatened Loggerhead sea turtle. Important protected beach/dune and
estuarine areas include Delnor-Wiggins Pass and Barefoot Beach State Recreation Areas;
Estero Bay Aquatic Preserve and Buffer Reserve, Rookery Bay Aquatic Preserve and National
Estuarine Research Reserve, the Ten Thousand Islands Aquatic Preserve and National
Wildlife Refuge; the Estero Bay Tributaries and the Wiggins Pass/Cocohatchee Estuary
Outstanding Florida Waters (OFW), and the Little Estero, Caxambas, and Big Marco Critical
Wildlife Areas.
LINKAGE TO THE TOTAL SYSTEM:
Water from the basin flows south and southwest to provide freshwater
for the estuaries along the southwest coast, including the Ten Thousand Islands National
Wildlife Refuge and Aquatic Preserve, Rookery Bay National Estuarine Research Reserve and
Aquatic Preserve, southwestern Everglades National Park (ENP), and indirectly to Florida
Bay. The basin also provides water for several southwest Florida communities. Ecological
connections between Everglades National Park and the Big Cypress basin are evident,
resulting in similar concerns and scientific needs for both sub-regions. The extensive,
contiguous areas are distinguished by the large proportion of officially designated
wilderness area (in ENP) and by Federal ownership for controlled-use purposes of most of
the southern and eastern portion of the BCNP. Development impacts in the remainder of the
subregion have a direct effect on ecosystem health within the Everglades basin.
ECOSYSTEM ISSUES AND RESTORATION OBJECTIVES:
Southwest Florida is undergoing tremendous development pressure and has
had the highest growth rate in Florida during the last ten years. During the 1950s-1970s,
several large-scale residential developments along with major road and drainage projects
were constructed throughout the region, causing loss of both wetland and upland habitat,
lowering of the water table, and impacts to the region's rivers and estuaries.
Incorporated cities include Naples, Ft. Myers Beach, Marco Island and Everglades City.
Rapidly developing areas include northern Collier County, northern Golden Gate Estates,
Estero, Immokalee, and Bonita Springs.
Recent plans for expanding the Southwest International Airport and
constructing Florida Gulf Coast University has spurred development pressure to new levels.
Agriculture is a major industry in the area, especially citrus and winter vegetables.
Until recently, conversion of natural lands to agriculture occurred at an even greater
rate than residential and commercial development in some areas of the basin. There is
concern about potential effects on plants, wildlife, and their habitats and on surface and
ground water quality and quantity. Some citrus development projections estimate that up to
50% of available Florida panther habitat in the Immokalee Rise area may be lost. Citrus
also uses more water per acre than any other type of agriculture, except plant nurseries.
There is concern over the potential impacts for water table drawdown.
Construction of the Tamiami Trail in 1928, the first east-west road
across the basin, altered the natural timing and distribution of surface water flow. Since
then, other residential road and canal systems have altered natural freshwater sheetflow
patterns to the estuaries, resulting in increased rates of runoff and substantial point
loads of contaminants. As a result, salinity patterns have changed, the estuarine nursery
value for fish and shellfish has decreased, fisheries and seagrass abundance have been
reduced, and nutrient loading has increased. One of the most significant examples of this
was the development of Golden Gate Estates in the 1950s, which includes approximately 200
square miles of road and drainage canal development in wetlands east of Naples. This
project continues to cause drawdown of the water table, impacts to wildlife habitat,
increased fire, and unnatural discharges of large volumes of freshwater into the Ten
Thousand Islands estuary.
Water quality in the urban estuaries continues to decline as a result
of non-point source discharges. Nutrient and turbidity levels are on the rise in the
estuaries, and concentrations of heavy metals indicative of polluting conditions
(including cadmium, lead, copper and zinc) are found in the sediments. Fresh water systems
have suffered a swell. The once sandy substrate of Lake Trafford, which had supported
important submerged aquatic vegetation, is now buried under 7 million cubic yards of muck
caused by nutrient-rich runoff and chemical aquatic weed control practices. The high
biochemical oxygen demand of the muck causes periodic massive fish kills in the lake.
Water quality within the BCNP is generally considered to be good to excellent. However,
runoff from citrus and other farming operations upstream of the BCNP has long been a
concern. Indian lands of the Miccosukee and Seminole Tribes, an important component of the
basin, receive surface water that is contaminated with high concentrations of nitrogen,
phosphorus, heavy metals, and other pollutants. These pollutants are generally attributed
to intensive upstream agricultural development and other anthropogenic activities.
This pollution has resulted in contaminated fish and wildlife, which
tribal members consume as part of their traditional subsistence hunting and fishing
lifestyle, and significant economic and recreational fisheries and ecotourism for
urban/rural communities. The pollution has resulted in conversion of wetlands to areas
lacking the natural plant and animal diversity of the past. The subsurface strata
contribute nutrients to the groundwater affecting the surface flora and fauna. Subsurface
investigations are needed to provide the required data to understand the subsurface
stratigraphy and its groundwater impacts to the South Florida Ecosystem.
Vegetation in conservation areas of the Big Cypress Basin has not been
substantially altered compared to other sub-regions, but is threatened by the invasion of
a variety of exotic plants. Melaleuca, in particular, now occupies about 6% of the BCNP
and resists control efforts. This and other invasive species may lower the water table and
hasten extinction of native species. Non-native fishes have colonized natural and
disturbed habitats during the past three decades. Documented impacts include predation,
nest-site competition, and habitat disturbance. Without strict border controls, relevant
legislation, and support from the nursery industry, more exotic species will invade with
unknown ecological consequences.
Continued loss of floral and faunal diversity from upland communities
is of great concern. Though issues of biodiversity are frequently discussed in relation to
wetlands, many of the known and imminently threatened losses of species in the basin
appear to be associated with uplands.
Slash pine forest ecosystem acreage in Southwest Florida declined 88%
from 1900-1989. Large acreages of hydric pine flatwoods have been lost to logging,
development, and agriculture activities. Habitat destruction from residential and
commercial development continues. Agricultural conversion has abated, but there are many
large permits pending. Approximately 130,000 acres of citrus exist, with approximately
500,000 acres currently permitted. Melaleuca and other invasive exotic plants are a
serious ecological problem.
Principal threats to survival of the Florida panther are habitat loss,
automobile traffic, and inbreeding. Survival of Florida's state mammal is dependent on
stabilizing the extant population, genetic restoration, and reintroduction elsewhere in
its historic range. With the exception of the well-studied panther, black bear, and
white-tailed deer, there is only limited information on the biology or population ecology
of most native mammals. In addition, the ecological consequences of an expanding
population of feral pigs have not been measured.
The total number of wading birds nesting in the Big Cypress and
Everglades Basins has declined by more than 95% from peak estimates of nesting birds in
the 1930s. Impacts of altered hydropatterns include (1) reduced number of birds attempting
to nest, (2) relocated colonies, (3) changed timing of nesting, and (4) fewer years of
successful nesting.
Several initiatives with public and private interests have formed to
address the problems associated with the intense development pressure being experienced in
this environmentally sensitive region. Some of these include the Southwest Issues Group of
the Governors Commission for a Sustainable South Florida, Southwest Coast Ecosystem
Management Team, Estero Bay Agency for Bay Management, Southwest Focus Group, Panther and
Private Lands team, Lake Trafford Restoration Task Force, Southern Golden Gate Technical
Committee, Big Cypress Basin Science Steering Committee, Greenways and Trails, and others.
RESTORATION OBJECTIVES:
The restoration objectives of critical importance for Sub-region 5 have
been identified by the Working Group and are listed as follows:
- Restoration of more natural distribution, timing and quantities of
fresh water into the coastal estuaries.
- Improvement to water quality by addressing point source and non-point source discharges.
- Restoration of degraded habitat, and minimization of further habitat loss.
- Protection of flood plains from further development to minimize needs for additional
drainage projects.
- Improvement of aquifer recharge, and protection of ground water from pollutant loading,
saltwater intrusion.
- Promotion of best management practices to agriculture, development, local governments,
and the general public.
- Protection, buffering, and management of existing public lands.
RESTORATION PROJECTS:
Important restoration projects in progress or proposed for the
Sub-region are identified on the following pages:
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