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VALUED ECOSYSTEM COMPONENTS |
SFWMD (2002d) defines valued ecosystem components (VEC's) as “…a species, |
community, or set of environmental conditions and associated biological |
communities that is considered to be critical for maintaining the integrity…” of a |
given estuarine ecosystem. |
VEC's represent the full suite of plant and animal communities, individual |
species, substrate characteristics (hardbottom, softbottom), and water quality |
conditions (salinity zones, dissolved oxygen zones, etc.) that when taken together |
or individually are valued for aesthetics, commercial or recreational fisheries |
values, or heritage values. Once these are listed as they are in Section 6 above, the |
question is which of these, or components of each, may have higher or lower |
"values", and which are indeed sensitive to freshwater inputs to the estuary. |
Mangroves for example are VEC's for all the estuaries in the southern half of |
Florida, but are relatively insensitive to salinity changes over a very wide range |
since they are facultative halophytes not obligate halophytes. That is they can |
grow in totally fresh water, or survive in interstitial salinities as high as 55 psu |
for red mangroves and 90 psu for black mangroves. The American oyster, on the |
other hand is an obligate marine organism, but cannot persist in any numbers to |
Potential Alternative Approaches for MFL Development for Biscayne Bay |
Freshwater Flow and Ecological Relationships in Biscayne Bay 5-9 |
form an oyster bar unless very specific salinity and bottom characteristics are |
present. |
INDICATOR SPECIES |
SFWMD (2002d) defines an indicator species as one where a change in |
abundance, distribution or condition can be related to flow or salinity. Criteria |
for selection may include commercial, recreational or aesthetic value, ecological |
importance, and whether it is a listed species or an endemic species. |
Starting with the full suite of VEC's for Biscayne Bay, Table 4 was prepared and |
lists potential indicator species for minimum flows and levels, based upon their |
occurrence in Biscayne Bay, life history, review general estuarine literature and |
specific literature on Biscayne Bay, interviews and personal communications. |
Sources of information include Serafy et al (1997) who collected 95 taxa of fish |
from the Bay, Serafy et al (2003) who extended this work to mangrove fringed |
shorelines in the central, south-central and southern portions of the Bay, and |
Alleman (personal communication) who has prepared a draft table of species |
salinity relationships in the Bay that lists twelve species of fish, three |
invertebrates, wading birds as a group, and two species of seagrasses. Ault et al. |
(2001) reported via visual census or creel survey data, and collected a total of 325 |
species of fish and macroinvertebrates from 77 families within Biscayne National |
Park. Thorhaug et al (2001) lists two marine mammals, eight marine or estuarine |
reptiles, thirteen coastal birds, two fish, twenty-nine corals and ten marine plants |
as listed marine or estuarine species of concern in the Bay. Diatoms appear to be |
a sensitive indicator of both existing salinities and historic salinities (Ross et al., |
2002, Gaiser and Wachnicka 2003) and are included as a group. Alleman et al. |
(1995) specifically cite the diamondback terrapin (Malaclemys terrapin), the |
mangrove water snake (Nerodia fasciata compressicauda), and the American |
crocodile (Crocodylus acutus) as important potential indicator species for |
freshwater inputs to the Bay. |
From the information provided in this table it is apparent that not all the species |
considered occur throughout the entire Bay. For a species to be considered for |
use as an indicator species for a particular portion of the Bay, it must occur there, |
or have occurred there in the recent past and have some reasonable chance of |
returning in sufficient numbers to persist there if it is to be considered. Thus the |
American crocodile can be considered for portions of the Bay, but not all, since it |
is not reported for all parts of the Bay and is not likely to occur in some parts of |
the Bay except very rarely. |
Table 4 |
Potential indicator species for freshwater minimum flows and levels |
establishment in Biscayne Bay. |
5-10 |
Potential Indicator Sub-region |
Scientific Name Common Name Snake Cr & |
Oleta R. |
North Miami |
River |
Central South |
Central |
S |
PLANTS (Microphytes – diatoms) *** |
SSS |
PLANTS (Macrophytes) |
Avicennia germinans Black mangrove * S ** S * S * S |
Cladium jamaicense Sawgrass * S |
Conocarpus erecta Buttonwood * |
Distichilis spicata Saltgrass * |
Eleocharis cellulosa Spikerush * SS |
Halophila decipiens Paddle grass * |
Halophila englemanii Stargrass |
Halophila johnsonii Johnson's |
seagrass |
* * * |
Halodule wrightii Shoal grass * * * * * |
Juncus roemerianus Black needlerush * |
Laguncularia racemosa White mangrove * ** * * |
Rhizophora mangle Red mangrove * S ** S * S ** S |
Ruppia maritima Wigeon grass * * *SSS |
Spartina spartinae Cordgrass |
Syringodium filiforme Manatee grass * * * * * * |
Thalassia testudinum Turtle grass * * ** ** |
ANIMALS |
Invertebrates |
Callinectes sapidus Blue crab |
Crassostrea virginica American oyster * * |
Farfantepenaeus duorarum Pink shrimp ***SSS ***SSS |
Limulus polyphemus Horseshoe crab |
Menippe mercenaria Stone crab |
Mixed spp of benthic |
macroinvertebrates, |
(epifauna & infauna) |
* * * ** * |
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