Appendix 3 - Individual FY96 Project Reports

In overview NOAA's Florida Bay Science Program has had three overall objectives: improving our physical understanding of Florida Bay (three projects); characterizing the Bay ecosystem and recent changes (five projects); and two projects that address anthropogenic pollution. The full FY96 project reports submitted are given verbatim below under their respective themes.

Improving our physical understanding and/or modeling of Florida Bay's interconnection and dependence upon regional oceanographic and meteorological processes are the general goals of three of the individual projects. They represent the NOAA contribution to a larger Interagency effort attempting to develop, initialize and run in operational mode a Bay Circulation model which is in turn part of the still larger effort to develop, initialize and run in operational mode a coupled oceanographic, hydrological and atmospheric model of the South Florida penninsula.

1) "Regional Boundary Conditions for Florida Bay"
F. Aikman III, W. O'Connor and G. Mellor.

The project goal is to provide accurate physical (water levels, currents,temperature and salinity) boundary condition information to modelers and investigators working in the South Florida region and in Florida Bay. The total water level is probably the single most important parameter for any hydrodynamic modeling effort in Florida Bay, thus we are initially focusing on providing this, coordinating as closely as possible with the Corps of Engineers modeling effort in Florida Bay. To this end the Princeton Ocean Model (POM) is being applied for the Gulf of Mexico/Caribbean (GOM) region to provide this information, based on atmospheric and tidal forcing of a barotropic (two-dimensional; vertically integrated) version of the POM. Work to date can be summarized as follows:

We proposed to answer the following four questions:


  1. Are methyl mercury concentrations in carnivorous fish (red drum, spotted seatrout, and gray snapper) from Florida Bay now higher than concentrations in other Florida and U.S. regions?
  2. Do methyl mercury concentrations in these intermediate carnivores vary spatially in the Bay in a pattern that can be used to infer sources of elevated methyl mercury inputs?
  3. Are methyl mercury concentrations in food web organisms supporting these intermediate carnivores consistent with both the inferred sources and the measured concentrations in the intermediate carnivores?
  4. Are top predator species potentially at risk of bioaccumulating excessive methyl mercury concentrations through consumption of lower trophic level organisms in Florida Bay?

Initial work has targeted mercury analysis in forage fish (bay anchovies and silver jennies) that are the main prey of some the intermediate and top predators. It is hypothesized that if Everglades' freshwater runoff is an important source of methyl mercury to Florida Bay, then fish captured from areas nearest the Taylor Slough and Canal 111 inputs would contain the highest concentrations of methyl mercury.

Field and Lab Work: Initial field sampling targeted food web organisms from eastern Florida Bay, the area of greatest concern for mercury enrichment. Samples were collected by 3.4 m otter trawl during five minute tows, sorted on deck, placed in ziplock bags, iced until returned to the laboratory where they were frozen until analysis. Water temperature and salinity and position (GPS) were measured at time of sampling. Total mercury analysis in tissues was performed by cold vapor atomic absorption on individual fish rather than composites with QC results that were within the criteria recommended in EPA, 1995).. Bay anchovies (Anchoa mitchelli) were analyzed whole while silver jennies (Eucinostomus gula) were homogenized and subsampled.

Results: Mercury concentrations in bay anchovies from eastern Florida Bay were surprisingly high. Mean concentrations ranged from 0.055 µg Hg/g wet weight at the Crab Keys site, most distant from the Everglades to 0.271 µg Hg/g at the Eagle Key site near Little Madeira Bay. These concentrations are of the same magnitude (0.177 to 0.422 µg Hg/g wet weight) as bay anchovies collected from a mercury contaminated Superfund site at Lavaca Bay, Texas. They are higher than concentrations found in a similar sized forage fish, Gambusia sp., from within the Everglades drainage (Water Control Areas) where highest mercury concentrations are also found in largemouth bass and wading birds (Stober et al., 1995). This suggests that predators on anchovies in eastern Florida Bay could bioaccumulate concentrations of mercury high enough to be of concern.

If we assume an approximate biomagnification factor for methyl mercury of about four between prey and predator fish (current modeling effort), intermediate carnivores such as spotted seatrout feeding on anchovies would be predicted to contain between 0.22 and 1.08 µg Hg/g wet weight. This is similar to the range 0.38 to 1.70 µg Hg/g wet weight reported for spotted seatrout in eastern Florida Bay (Strom and Graves, 1995).

Existence of lower Hg concentrations in anchovies at the site most distant from the Everglades suggests a possible spatial gradient which will require further sampling for confirmation.

Silver Jennies (mojarra) from only four sites have been analyzed for mercury, as yet. The three sites nearest the Everglades have marginally higher mean Hg concentrations (0.110, 0.120, 0.123 µg Hg/g) than the more distant site (0.092 µg Hg/g). Analysis of existing samples and others scheduled for collection should allow us to determine if mercury concentrations in mojarra and in rainwater killifish (the other dominant forage fish) are as high as in bay anchovies. If not, then the reported shift over the past dozen years to anchovies as the dominant forage fish in Florida Bay (Hoss et al., 1996) could translate to an increase in mercury concentrations in fish such as spotted seatrout which feed preferentially on anchovies. Thus, the recent reports of elevated mercury concentrations in certain recreational sized fish in eastern Florida Bay could be follow from ecological shifts in the food web of Florida Bay, independent of any possible historical changes in mercury inputs

Ongoing Work: Collection of intermediate carnivorous fish (spotted seatrout, gray snapper, and red drum) for mercury analysis is being done through a cooperative arrangement with Robert Brock of the National Park Service. These angler-caught fish will also be analyzed for growth and reproductive condition as indicators of changing environmental condition in Florida Bay (Elledge and Brock, 1995). Growth data will be of direct use in modeling the mercury bioaccumulation in these fish which requires bioenergetic estimates of growth and feeding for calibration.

Additional intermediate carnivore fish are being collected as part of the Fisheries-Independent Monitoring program of the Florida Department of Environmental Protection in Florida Bay (Colvocoresses and McMichael, 1995). Duplicate fillet samples from the same fish will be analyzed for mercury by the two groups as a quality assurance measure. We will also analyze smaller individuals of the three carnivore species as part of bioaccumulation modeling. We expect to acquire, for mercury analysis, additional samples of the forage fish from this program whose array of 31 stations covers most of Florida Bay, including stations from each of the targeted sampling zones.

Mercury analyses of other teleost and invertebrate food web organisms from eastern Florida Bay are underway. This data will provide possible corroborating evidence of spatial gradients of mercury in the Bay, provide inputs to mercury bioaccumulation modeling useful in prediction, and perhaps allow us to infer the relative importance of benthic and pelagic environments as proximate sources of mercury to higher trophic level biota.

Colvocoresses, J.A. and R. H. McMichael Jr. 1995. Marine fisheries-independent monitoring program. Abstract presented at Florida Bay Science Conference: A report by principal investigators. Gainesville FL October 17-18, 1995. pp.203-206.


Elledge, D.M. and R.J. Brock. 1995. Age, growth, mortality, fecundity, and RNA-DNA analysis of spotted seatrout, Cynoscion nebulosus, in Florida Bay. Abstract presented at Florida Bay Science Conference: A report by principal investigators. Gainesville FL October 17 18, 1995. pp. 207-208.


EPA, 1995. Guidance for Assessing Chemical Contaminant Data for Use in Fish Advisories. Vol. 1: Fish Sampling and Analysis. Second Edition. EPA Office of Water EPA 823-R-95-007.


Hoss, D.E., G.A. Thayer, A.B. Powell, P.A. Tester, and M. B. Robblee. 1996. Assesment of trophic structure and responses of fish and shellfish to changes in habitat in Florida Bay. progress report submitted to the NOAA Florida Bay Project and Everglades National Park. August 1996.


Stober, Q.J., R.D. Jones, and D.J.Scheidt. 1995. Ultra trace level mercury in the Everglades ecosystem, a multi-media canal pilot study. Water, Air, and Soil Pollution. 80:991-1001.


Strom, D.G. and G.A. Graves. 1995. A comparison of mercury in estuarine fish: lorida Bay and Indian River Lagoon. Ecosystem Management Report. Florida Department of Environmental Protection, Southeast District Ambient Water Quality Section, Port St. Lucie. FL. October 1995. 34 pp.


The NOAA Florida Bay Program has also funded essential non-research items:


12) "Data Management and Administration"
M. Crane

The NOAA research program in Florida Bay has a significant data gathering mission plus an agreement with the other agencies to share that information. There are three major areas of data administration to report.

  1. The first area is internal data support to the NOAA researchers. An internal tracking system was developed to monitor the samples with detailed inventory data. This was maintained in the NOAA Florida Bay Sample Tracking Spread Sheet for each investigator that collects samples in the field. Each investigator submits station location, date, time and type of samples. The file contains over 900 unique samples or stations. A second support item in this internal support area is the assessment that a regional data support facility is required to process the data from NOAA investigators. A NOAA Florida Bay Data Operations Facility is planned for FY1997. A proposal was forwarded to NESDIS and NODC for funding a regional coastal data support facility in Miami as part of the NOAA Florida Bay data plan.

  2. The second area is external data coordination. The "Florida Bay" Program ManaqementCouncil created a Florida Bay Data Administration Council in response to an item noted it the 1995 Boesch report. A NOAA Florida Bay Data Administrator was named for NOAA and Mr. Crane was named as chairman of the new Florida Bay Data Administration Council. Two action items were addressed to this Data Council - one is creating a WEB site for research projects and the second was assisting the NOS/FMRI monitoring data base effort. A new WEB site for the Project Tracking and Indexing System was established on the US Army Corps of Engineers server in Jacksonville.. All FB research projects will be identified and loaded onto the site. Providing support to the ORCA/FMRI monitoring data base system was initiated in Sept 1996.


  3. The third area is the administrative support for data items to the NOAA Florida Bay Management Team. A master list of Florida Bay contacts was maintained as a spread sheet file. A roster of contacts that are associated with the NOAA research program in Florida Bay has been updated through out the year. This administrative support extended to Working Group and Task Force support also. Mr. Crane participated in the Public Information and Education Subgroup activities concerning the data and information topics. In addition NOAA provides liaison member to the Office of the Executive Director, SFERTF. Mr. Crane worked with the staff of the OED at the Florida International University campus office and participated in the development of the Integrated Financial Plan document that was published on August 15, 1996. As the NOAA Data Administrator for the Florida Bay Program, Mr. Crane advised the Management Team of future action items. One of them is the meta data commitments related to the data. FGDC meta data format agreed as the standard for future meta base files.