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and taking into account all source waters, this area of fresher
water would extend along the mainland shoreline to the isthmus bounding the southern end of Barnes Sound.
When considering questions related to water management
and freshwater flows from the mainland, the focus within these
regions shifts westward to water and habitats nearest the coast
that provide the most sensitive indicators of bay conditions.
For the purposes of this report, the focus for development of
targets to assist in the estimation of water for the protection of
fish and wildlife is placed on two areas: the Coastal Mangrove
Zone (CMZ) on the mainland of Biscayne National Park, and
the Western Bay Zone (WBZ), including the seagrass bottom,
which occurs in the western portion of the South Bay Section
(Fig. 3).
Western Bay Zone Target Area. RECOVER has developed
a performance indicator (SE-6) for CERP restoration efforts
in Southern Biscayne Bay that describes indicator organisms,
salinity conditions, and the “nearshore” area in which the performance measure will be applied. The area defined in SE-6
has lost historical oyster (Crassostrea virginica) colonies and
no longer sustains red drum (Sciaenops ocellatus), a species
that could be restored if habitat conditions were made suitable. Performance measure SE-6 defines “nearshore” as 250 m
from shore during the dry season and 500 m from shore during the wet season (Fig. 3). The definition of these longitudinal
bands of estuarine habitat is based on a simple consideration
of a volume of water entering the bay edge as uniform flow;
Ecological and Hydrologic Targets for Western Biscayne National Park 5
however, there is no analysis in the performance measure that
explains why 250 and 500 m were chosen as target areas.
Because the characteristics of the benthic community
depend on bottom type, we chose to use existing, but stable,
physical characteristics of the bay bottom to assist in the
definition of a target area for restoration. Based on benthic
mapping and evaluation of abundance and distribution of
benthic community types, the ecology of Biscayne Bay, as a
whole, is dominated by the soft bottom (approximately 64%
of the bottom) and hard bottom (17%) benthic communities
(NOAA 1996). Soft bottom, shallow areas promote seagrass
communities, whereas hard bottom areas, which occur where
sediment is non-existent or very thin over a rocky substrate,
are characterized by soft corals (i.e., sea fans), sponges, and
isolated coral colonies.
Examination of geological maps of the bay bottom shows
that areas affected by freshwater inflows along the coast of
Biscayne National Park comprise a zone of soft bottom seagrass habitat that extends from Turkey Point to about 1,000
m offshore at Convoy Point to some 6,500 m offshore at the
northern mainland boundary of the park (Fig. 3). The northern sector of this zone is a mix of both soft and hard bottom
communities. This zone is bounded by the CMZ at the western shore of central and southern Biscayne Bay and by an area
of hard bottom that occupies the Middle Bay Zone to the
east. This WBZ historically received freshwater flow through
coastal marshes and creeks, and groundwater recharge that
correlated with the wet and dry seasons.
The bottom type and location of the WBZ, relative to historical freshwater inflows, define a target area of 10,000 acres
of functional, seagrass-based estuarine habitat in Biscayne
National Park. In contrast, the RECOVER dry season target
of 250 m from shore covers about 1,600 acres, or only 16%
of functional estuarine habitat that could be restored. The
RECOVER wet season target of 500 m from shore covers
about 3,200 acres, or less than 1/3 of the estuarine habitat that
could be restored. It is our understanding that RECOVER
may consider revising SE-6 in response to the considerations
discussed here.
Our description of desired conditions and the analyses
of ecological and hydrologic targets in the WBZ focus on
this 10,000 acre area of submerged aquatic vegetation (SAV)
habitat at the western edge of Central and South Bay, within
Biscayne National Park. Currently, freshwater is delivered
through canal structures along the coast. The water deliveries should be stabilized by linking volumes and timing with
natural coastal marsh hydroperiods and estuarine salinities.
This change would reestablish high quality nursery habitat for
important fish and invertebrates in a band of soft bottom/SAV
habitat from the northern boundary of Biscayne National
Park south to Turkey Point (Fig. 3).
Florida Turnpike
6 South Florida Naturai Resources Center Technical Series (2006:1)
Submerged aquatic
vegetation
Hard bottom
Eastern extent of Coastal
Mangrove Zone
250 meter buffer
500 meter buffer
Bay Zone borders
Area Enlarged
Atlantic
Ocean
Legend
S-20F
Barnes
Sound
Point
Biscayne
Bay
Key
Biscayne
Safety Valve
Figure 3. RECOVER performance measure focus areas and alternative Western Bay Zone focus area based on submerged aquatic vegetation on the bay bottom.
Ecological and Hydrologic Targets for Western Biscayne National Park 7
ECOLOGICAL TARGETS FOR BISCAYNE
NATIONAL PARK
Historical Conditions
Coastal Mangrove Zone. What we now call the Coastal Mangrove Zone was formerly composed of freshwater