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Ecological Modeling
I have used a variety of modeling frameworks over a range of scales
to investigate ecological relationships of estuarine and marine systems.
IBM Modeling:
Individual-based model of the feeding behavior of predators foraging in
a complex food environment.
- Currie WJS and KMD Cuddington. The Importance of Patchy Distributions
for Predator Foraging Success: Zooplankton in a Multifractal Field.
Nutrient Loading to Estuaries:
CLUE: is a generalized model of nutrient loading into New England coastal
embayments as determined by land-use. CLUE is a process-based, empirical
model in which the relationships among its important variables are derived
from independent observations. It represents the best synthesis of how
the various components of land use, nitrogen loading, and ecosystem response
fit together. The nitrogen loading model was developed and tested originally
in Waquoit Bay on Cape Cod, but has successfully estimated nitrogen inputs
into estuaries, as determined by field measurements and other supporting
data. This provides an estimate of the amount of nitrogen entering the
receiving waters either as a mass loading value or a concentration. Estuary
size and the tidally induced flushing rate determine the amount of nitrogen
available for biological uptake in the estuary.
The ecosystem response model takes output from the nitrogen loading model
and estimates the levels of four key indicators of estuarine habitat quality
in response to the nitrogen loading: algal blooms, eelgrass, susceptibility
to low dissolved oxygen conditions, and fish populations. Water column
chlorophyll concentration is calculated based on relationships of algal
productivity to nitrogen availability, light, temperature, mixing, and
grazing by herbivores. The model estimates susceptibility to anoxia by
calculating the number of days that oxygen demand is likely to exceed
supply, based on average light incidence, temperature, and modeled system
respiration. For a given embayment, the ecosystem response model estimates
the areal extent and density of eelgrass under pristine and eutrophic
conditions, using such factors as light availability, temperature, and
water depth. Finally, the model estimates finfish abundance and diversity
as a function of eelgrass density.
- Currie WJS and JN Kremer. The CLUE model: A generalized model for
the investigation and management of shallow estuarine eutrophication
EcoHAB:
Harmful Algal Blooms (HABs) of the dinoflagellate Karenia brevis
Davis (formerly Gymnodinium breve) routinely affect the Gulf coast
of Florida and account for a significant portion of the yearly production
of the region. HABs of Karenia brevis have resulted in closures
of shellfishing due to Neurotoxic Shellfish Poisoning (NSP), and fish
and marine mammal kills. The vital tourist industry requires immediate
cleanup of beaches fouled by significant fish kills reaching 100 kg /
meter of coastline and costing millions of dollars.
Extremely clear water, low nutrients, and a resultant low phytoplankton
biomass typify waters of this region. Though tropical oligotrophic waters
are not typical environments for dense growths of algae, episodic blooms
have been documented back to the 1700's. This is in part due to the specifics
of K. brevis physiology, which grows at extremely low light levels,
has high nutrient uptake rates, and utilizes both inorganic and organic
nitrogen. These dinoflagellates are active swimmers (1 m hr-1) capable
of vertical migration, with known positively phototrophic, weakly negatively
geostrophic behavior. While significant progress has been made documenting
the toxin production and growth physiology of K. brevis, these are almost
exclusively laboratory-based studies. Little research has yet been done
using field-based measurements of Florida HAB initiation, growth and dissipation.
A variety of triggers have been suggested to account for the bloom initiation
including Saharan dust events, growth of nitrogen-fixing cyanobacteria,
and upwelling on the continental shelf. We use a straightforward modeling
approach with very little site specificity, a simple imbedded biological
model parameterized with Karenia brevis physiology capable of simulating
the gross features of both the initiation and spread of a bloom off Florida.
This ecological model is coupled to ROMS, the Regional Ocean Modeling
System, a sophisticated, open-source physical oceanographic model ideally
suited for the simulation of upwelling systems to investigate the possibility
of wind-induced upwelling as the initiator of HABs off Florida.
- Currie WJS, Lewis CV, Powell TM. Upwelling events initiate harmful
algal blooms of Karenia brevis on the West Florida Shelf - a
modeling study.
Relevant Publications:
- Howard C. Berg. 1983. Random walks in biology. Princeton Univ. Press,
142p.
- D. L. DeAngelis. 1992. Dynamics of Nutrient Cycling and Food Webs.
Kluwer Academic Publishers, 288 p
- DeAngelis DL, Gross GL (1992) Individual-based models and approaches
in ecology: Populations, communities and ecosystems. Chapman and Hall,
Inc, New York
- L. Edelstein-Keshet. 1988. Mathematical Models in Biology. McGraw-Hill,
608p
- Nicholas J. Gotelli. 2001. A primer of ecology. Sinauer, 206 p., 3nd
Ed.,
- William S. C. Gurney and Roger M. Nisbet. Ecological Dynamics. Oxford
Univ. Press, 352p
- Hassell MP (1978) The dynamics of arthropod predator-prey systems.
Princeton University Press, Princeton
- Kareiva, P. 1990. Population dynamics in spatially complex environments:
theory and data. Phil. Trans. R. Soc. Lond. B 330:175-190.
- Sharon E. Kingsland. Modeling Nature. 1995. The Univ. of Chicago Press,
2nd Ed
- Roger M. Nisbet and William S. C. Gurney. 1982. Modelling Fluctuating
Populations. Wiley, 379p
- David C. Schneider. 2003. Quantitative Ecology: Spatial and Temporal
Scaling. Academic Press, 395p
- Peter Yodzis. 1998. Introduction to theoretical ecology. New York
(etc.): Harper & Row, 384 p
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