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publications > poster > modeling manatee response to restoration

Modeling Manatee Response to Restoration in the Ten Thousand Islands and Everglades National Park

photograph of a manatee Bradley M. Stith, James P. Reid, and Susan M. Butler

U. S. Geological Survey, Florida Integrated Science Center, Sirenia Project, Gainesville, FL, USA
Email contact: Bradley_Stith@usgs.gov

Presented at the First National Conference on Ecosystem Restoration (NCER), December 6-10, 2004, Orlando, Florida

Research Questions

How will manatees respond to hydrologic restoration in the Ten Thousand Islands and Everglades region?

How do manatees currently use the resources in this region, prior to restoration?

Aerial Surveys
  • Two types of aerial surveys are flown over the Ten Thousand Island study area to collect information on the distribution and abundance of manatees.
  • Parallel strip transects (green lines below) are flown 8 times in the summer following protocols by Miller et al. (1998). Two observers in the plane independently record the location, activity and number of manatees observed in each group.
  • Distribution surveys (yellow line below) are flown monthly following an irregular predefined path across the mainland waterways, the mangrove islands, and offshore bays.
image showing flight paths of aerial surveys
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photograph of plane flying over water
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Satellite Telemetry
  • Satellite telemetry is used to document the movements of individual manatees over time.
  • A total of 26 manatees (8 males, 18 females) were captured and radio-tagged at Port of the Islands, Collier County, Florida through December 2003.
  • Most tagged manatees were fitted with Argos transmitters, providing approximately four location fixes per 24-hour period.
  • GPS tags were used periodically to provide much more accurate locations than the Argos data (approx. 30 m vs. >150 m) every 15-30 minutes, but the battery life was much shorter (8 weeks vs. 6 months).
  • A total of 17,753 high quality Argos fixes over 6,157 tracking days were recorded from 26 tagged manatees (see map below).
photograph of scientists working with a tagged manatee
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image showing recorded tracking locations
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Key Manatee Behavior

Manatees show different winter migratory strategies, including moving south, moving north, or remaining in the same area all year.

Manatees show regular movement patterns between offshore feeding areas and freshwater sites.

Seasonal Movements
  • Manatees captured in the study area showed variation in migratory behavior. Most tagged animals (16 of 26) overwintered near their capture site.
  • Four of 26 animals moved south to Whitewater Bay during cold events (see below).
  • Four of 26 animals moved north to power plants in Fort Myers or Tampa.
Anna:
  06Jan02 - 25Jan02
  20Dec02 - 08Feb03

Mitzie:
  20Dec02 - 08Jan03

Tipper:
  11Dec02 - 08Feb03

Surfer:
  26Nov00 - 09Feb01

image showing seasonal movement of manatees
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Interzone Movements
All tagged manatees make regular movements between offshore seagrass beds and inland sites that provide access to freshwater.
image showing tagged manatee movement
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graph showing tagged manatee movement
Surfer - August 2000
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Transition Probabilities
To model interzone movements, telemetry data is formatted as mark-recapture data and coded for different ecological zones. The example below shows 8 weeks of "resightings" for one tagged manatee: Offshore (S), Travel (T), Inland (I), or no data (0).

TSSSSSTSSSSSTT000000000000TTTTTTST0TTT0TSSSSSTTTSSII0T0S 1;
SSS0SSSSS0SSSST000STSS0SSSTSSSSSS00I0SSSSSSSTS0I0SSS00SS 1;
S0TTSTS0I000SSSTSTTSSSST0000SSSTSSTSS00I0S0SSSSSSSSSS0II 1;
I0SSSSSS0S0SS0II00BBSTSSSTT0S00SS0T0SSSSS0I0BTSSSSSSS000 1;

Multistate modeling (Lebreton & Pradel 2002) is used to analyze these data and provide movement probabilities between zones. This approach also provides a framework for testing hypotheses as competing models, and for analyzing covariates that may influence movement.


Model Structure

Variation in manatee behavior is readily captured in an individual-based model.

Manatee movement and home range can be modeled on a network data structure.

Manatee response to restoration can be modeled as reinforcement learning.

Home Ranges as Networks
  • Manatees have large home ranges, but use a limited proportion of the habitat available to them.
  • They avoid water deeper than 2-3 meters except when traveling. They also avoid shallow water that is not near deeper water, perhaps as a means of avoiding stranding and predation.
  • Network data structures efficiently describe manatee movement pathways and home ranges (see map below).
  • GPS data provides information on movement rates (see graph below) that is directly incorporated into the model.
image showing manatee movement pathways and home ranges
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Surfer - August 2000
graph of manatee movement rates
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Reinforcement Learning
  • Simulated manatees learn which pathways provide reliable assess to freshwater by positive or negative reinforcement as they choose among alternative pathways.
  • The Rescorla-Wagner model is a simple, field tested method of modeling reinforcement.

delta symbolVn = C (VMax - Vi)

Where V is the strength of association (between a node of the network and the availability of freshwater ),and C is a constant for the individual's rate of conditioning (learning).

Movement as a Monte Carlo Markov Chain process
Transition probabilities obtained from the Multistate model are used to simulate the movement of manatees among ecological zones as a markov chain process.


Model Issues

How should hydrology be modeled?

How can the model be validated?

Hydrology component
  • Water quality data is available from a number of monitoring stations in the study area (see graph below).
  • Salinity and water temperature can be modeled along the network used by the manatees.
  • Ideally, an estuarine hydrology model (e.g. TIME) would be linked to the manatee model.
  • As a surrogate for the hydrology model, we are using simple empirical models along the network to simulate changes in hydrology.
graph showing salinity measurements from 3 monitoring stations
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graph of salinity versus distance from weir
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Model Validation
  • Comparison of aerial survey distribution data with snap-shots of simulated population (see graph below from aerial distributional survey).
  • Comparison of real and simulated coarse-scale seasonal home range estimates.
  • Comparison of real and simulated fine-scale foraging movements.
  • Face validation by biologists viewing real-time map displays.
  • Comparison of population trend analysis based on transect surveys and demographic modeling.

graph from aerial distributional survey
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Literature Cited
Miller, K.E., B.B. Ackerman, L.W. Lefebvre, and K.B. Clifton. 1998. An evaluation of strip-transect aerial survey methods for monitoring manatee populations in Florida. Wildlife Society Bulletin 26(3):561-570.

Lebreton, J.D. and R. Pradel. 2002. Multistate recapture models: modelling incomplete individual histories. J. Applied Statistics 29: 353-369.

Acknowledgements: This research is a cooperative effort with federal, state, and private partners, including: Everglades National Park, U. S. Fish and Wildlife Service, Big Cypress National Preserve, Rookery Bay National Estuarine Research Reserve, Florida Fish and Wildlife Conservation Commission, Collier Co. Department of Environmental Services, and Mote Marine Laboratory.

United States Geological Survey logo United States Fish and Wildlife Service logo


Related information:

SOFIA Project: Predicting Effects of Hydrologic Restoration on Manatees along the Southwest Coast of Florida



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