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exist at some level satisfactory to water managers, citizens and scientists. |
Appendix E Tables E-1 to E-6 list the various alternatives considered for use for |
each of the six sub-regions, with values established on a scale of 0-5 for by bestprofessional-judgment by the two principal scientists writing this report: Greg |
Braun and Roy R. "Robin" Lewis III, combined with knowledge derived from the |
reviewed literature, and comments by interviewees to the principal scientists. |
Each potential approach was rated on a scale of 0-5, and the six values were then |
added together for a final score. The minimum score could therefore be 0, and |
the maximum 30. Each of these final totaled values is listed in summary in Table |
5. The highest scores are highlighted. For one region, Central Biscayne Bay, two |
possible approaches are tied with the same score, 22. Since the valued ecosystem |
components and the chosen indicator species are the same for this region, this |
does not impact the choice of approach. |
Table 6 is modified from Table 5 to now include a subjective rating by the |
principal scientists of the currently existing strength of scientific data support for |
a particular recommended approach. On a rating scale of 0-5, 0 is pure conjecture |
with no data support, 3 is moderate data support, and 5 is very strong data |
support. For most of the recommended approaches, the current scientific data |
base to support a specific quantitative MFL is low to moderate. As noted by |
Browder et al. (2001), "(D)evelopment of the information and modeling tools |
necessary to link water management, salinity envelopes, and biological |
performance measures is still in their early stages with respect to Biscayne |
Bay...thus far it has not been possible to translate changes in freshwater flow into |
terms meaningful to the Bay ecosystem in more than a general sense." |
The highest rated approaches, strength of scientific data support for that |
approach and recommended contingency plan for each region are listed below. |
Table 6 |
Comparison of the Relative Strength of Scientific Support for the |
Different MFL Approaches for Each Sub-region |
Oleta River |
Snake Creek |
Northern |
Biscayne Bay |
Miami River |
Gov't Cut |
Central |
Biscayne Bay |
South-Central |
Biscayne Bay |
Southern |
Biscayne Bay |
2 2 4 |
Relative Strength of |
Scientific Support (0-5) 2 3 2 |
Soil Characteristics |
Requirement for preferred |
fish communities |
Food Web Support |
Sub-Region |
Pre-development Scenario |
Valued Ecosystem |
Component(s) |
Community Index |
Indicator Species |
POTENTIAL APPROACHES |
Presence/Absence/Vitality |
of Preferred Habitats |
Ecological Preservation |
22 22 |
17 |
14 8 |
17 |
21 |
12 |
15 |
16 |
22 15 |
6 |
18 18 16 |
22 |
17 |
14 |
14 |
12 |
12 |
12 12 6 |
5 |
12 20 |
12 |
12 |
12 |
6 |
15 11 |
5 |
22 16 |
13 |
26 |
10 |
5 |
15 |
12 |
5 |
10 |
Shaded bocks indicate the recommended approach for each sub-region, based on it receiving the highest ranking. |
It is important to note that these values represent a composite of multiple factors (see Appendix E). |
12 |
15 |
5 |
10 |
12 |
12 12 |
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