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U.S. Department of the Interior
U.S. Geological Survey
FS-146-96

Ecosystem History: Terrestrial and Fresh-water Ecosystems of Southern Florida

Introduction | Reconstruction of Ancient Communities | Vegetation along a Nutrient Gradient: Water Conservation Area 2A | Anticipated Schedule | Summary

Introduction

Plant and animal communities of the historic Everglades have undergone striking changes over the last few decades, including declines in wading bird populations, invasion by exotic (non-native) plant and animal species, and areal expansion of cattails into sawgrass marshes. Many of these changes have been attributed to human activities in the region, and efforts are underway to restore the Everglades to a more pristine state.

Restoration plans include alteration of the present levee and canal system that controls water flow throughout southern Florida and changes in agricultural and land development activities. However, can we be sure that the observed changes are related to human practices rather than representing an extreme in the natural variability of the system? This question should be answered before changing current land-use practices to alleviate environmental concerns. To address this question, it is necessary to look at patterns of floral and faunal change over the last century as well as over the last few millennia.

This project aims to reconstruct floral and faunal composition at selected time intervals throughout southern Florida to determine: 1) detailed biotic changes over the last 150 years; 2) the natural range of biotic variability over the last few thousand years; and 3) determine whether any cause-and-effect relationships exist between biotic and environmental changes. Such questions are being addressed by scientists in the South Florida Initiative of the Ecosystem Program at the U.S. Geological Survey.

Planned Products

Reconstruction of Ancient Communities

A series of surface samples and shallow cores are being collected from sites throughout southern Florida for analysis of pollen and spores, mollusks, foraminifers, ostracodes, diatoms, and any other biotic elements present, as well as for radiometric dating, charcoal, and other geochemical analyses. Age control for the last 150 years is provided by analysis of the radioisotope lead-210(210Pb) from each sample; radiocarbon (14C) dating is used on samples in the middle and basal parts of the cores to date sediments too old to be dated using lead-210.

Pollen preserved in the cores provide a proxy record of vegetational patterns throughout the history of the site. Because pollen typically is transported from the source plant before being incorporated into sediments, it provides a record of the regional vegetation rather than just the vegetation growing at a site, and this is useful in interpreting broad patterns of vegetational distribution. However, the percent abundance of pollen in a sample is not directly related to the abundance of its source plant in the standing vegetation, because plants differ in pollination method and produce different quantities of pollen. To cite one example, a wind-pollinated species such as pine releases much more pollen into the atmosphere (and, ultimately, into the sediment) than an insect-pollinated plant. To correct for such biases, it is useful to analyze pollen from surface (modern) samples to determine what pollen assemblages are characteristic of different vegetation types. For this project, surface samples have been collected from 23 sites in WCA 2 and 3 and from the mangrove fringe along Florida Bay. Statistical comparison of downcore assemblages with these modern assemblages allows identification of modern analogs for the downcore assemblages and, therefore, interpretation of standing vegetation throughout the history of the site.

Vegetation along a Nutrient Gradient: Water Conservation Area 2A

Cattails are native to the Everglades, typically occurring in small stands throughout the region. Disturbances, such as increased water depths associated with soil subsidence and fires, tend to favor colonization by cattails. They also are very opportunistic in utilizing increased nutrient levels, particularly phosphorus, and the relative contribution of each of these factors to their increased abundance in key regions needs to be ascertained. Cattails are particularly abundant along the canals and levees in the Water Conservation Areas, forming single species stands that are visible on satellite photographs. Along the Hillsboro Canal, between WCA 1 and WCA 2A, cattails began to dominate vegetation shortly after construction of WCA 2A in the 1960s, probably in response to the deeper water levels and disturbance resulting from construction of the Water Conservation Area. In the 1980s, the area covered by cattail stands doubled, expanding southward into the sawgrass marshes.

A nutrient gradient exists from the Hillsboro Canal south into WCA 2A, and a series of monitoring stations have been installed along this gradient. Cores have been collected at several of these stations to document the floral, faunal, and fire history of the sites, and pollen data from two of the stations are presented below. At site F1, <2 km from the canal, highconcentrations of phosphorus and other nutrients are present, grading down to normal nutrient levels at site U3, approximately 13 km from the canal. Pollen assemblages and radioisotopes (210Pb and 14C) have been analyzed from these cores to compare both long-term and recent temporal and spatial vegetational trends and to determine whether any changes or differences are attributable to documented environmental change.

Site F1 - Cattail Site

Pollen assemblages from site F1 document several noteworthy changes through time in vegetational composition. From about 1,100 years before present until the early 1900s, marsh and slough vegetation, including sawgrass, water lily, and arrowhead, were the dominant elements of the pollen assemblages. In the early 1900s, pollen of the pigweed family doubled in abundance, completely dominating the assemblage. Since 1960, cattail pollen abundance has increased five-fold from 3% to 15%. The shift from the original marsh and slough vegetation to a weedy type of vegetation, represented by pollen of the pigweed family, coincides approximately with construction of the Hillsboro Canal in the early 1900s and associated disturbance of the original vegetation. The initial increase in abundance of cattail pollen at about 1960 occurred at about the same time as construction of WCA 2A; subsequent disturbances and addition of nutrients may have served to maintain and expand the area covered by cattails.

Site U3 - Pristine Site

Site U3 is pristine in terms of nutrient content but has undergone a great deal of physical disturbance associated with scientific investigations. The peat accumulation rate is much lower at this site (0.083 cm/yr as compared to 0.173 cm/yr at site F1). Pollen assemblages from this site generally resemble the pre-1900 patterns at site F1. Cattail pollen is present in low abundances throughout the core, and pigweed pollen abundance is similar to that in pre-1900 samples at site F1. Also, patterns of sawgrass, water lily, and arrowhead abundance mirror those of site F1. Apparently, site U3 is distant enough from the canal that disturbances associated with its construction did not alter the vegetation. The primary difference from site F1 is the higher abundance of aster (daisy) pollen in the upper 10 cm at site U3. Analysis of surface samples from the area should provide new evidence on the distribution and abundance of aster pollen throughout the region, enabling a better interpretation of the unusually high abundance of the pollen at site U3.

Anticipated Schedule

  1. Collect cores in Taylor Slough and Buttonwood Embankment.
  2. Produce reports on vegetational history from sites in Water Conservation Area 2A and Taylor Creek. Produce report on modern pollen assemblages; correlate pollen record with standing vegetation.
  3. Complete coring in Buttonwood Embankment and begin coring in new regions of interest.
  4. Produce reports on cores from Taylor Slough and Big Cypress.
  5. Complete analyses of cores; synthesize data to produce regional overview of vegetational changes. Develop vegetational reconstructions for selected time intervals over the last 150 years.

Summary

Pollen assemblages document the normal variability of the vegetation over the last millennium and suggest that some changes over the last 150 years are beyond the bounds of normal variability. The patterns and timing of vegetational change established throughout southern Florida will provide critical information for calibration of models designed to predict vegetational response to future environmental change and will help to determine whether past changes were caused by human activities or whether they represent a normal element of community variation.


For more information contact:

Debra A. Willard
U.S. Geological Survey
926A National Center
Reston, VA 20192
(703) 648-5320
Email: dwillard@usgs.gov

Related information:

SOFIA Project: Ecosystem History: Terrestrial and Fresh-water Ecosystems of Southern Florida



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Last updated: 03 November, 2004 @ 03:04 PM(TJE)