The Lake Okeechobee Water Quality Model (LOWQM) Enhancements, Calibration, Validation and Analysis

Abstract The Lake Okeechobee Water Quality Model (LOWQM) was enhanced to more accurately simulate sediment-water phosphorus (P) dynamics by separating the organic P (OP) into four classes (readily degradable, moderately degradable, non-degradable and dissolved), and to more accurately simulate algal dynamics by representing the phytoplankton community with the three distinct major algal groups (cyanobacteria, diatoms and green algae) observed in the lake. The model was calibrated and validated to observed water column nutrient data, sediment nutrient measurements and biovolume data for cyanobacteria, diatoms, and green algae. Model predictions were consistent with experimental observations and indicated that net sediment inorganic P (IP) loads were twice the external TP loads and net sediment inorganic nitrogen (IN) loads were 0.64 times the external total N loads. However, because of organic nutrient and algal settling the lake sediments are an overall nutrient sink. Sensitivity analysis indicated that total algal carbon, algal groups and chlorophyll a were very sensitive to changing algal parameters, parameters affecting light, temperature and supply of IP to the water column. Nutrients were less sensitive for two reasons: 1) algae represent a small fraction of the total nutrient mass, 2) the large pools of sediment nutrients, with long turnover times, buffer changes in the water column. Sensitivity analysis pointed to three potential management options to improve lake water quality: dredging, chemical treatment of sediments and external load reduction. These options were previously considered in a large sediment management feasibility study, which concluded that the last option-load reduction-was the most viable.

[1]  A. J. Mehta,et al.  Shallow Stratigraphy of Lake Okeechobee, Florida: A Preliminary Reconnaissance , 1994 .

[2]  K. Havens,et al.  Hurricane Effects on a Shallow Lake Ecosystem and Its Response to a Controlled Manipulation of Water Level , 2001, TheScientificWorldJournal.

[3]  C. Schelske,et al.  Assessment of nutrient effects and nutrient limitation in Lake Okeechobee , 1989 .

[4]  T. Auer,et al.  Phosphorus diagenesis in lake sediments: investigations using fractionation techniques , 1995 .

[5]  V. J. Bierman,et al.  A preliminary modeling analysis of water quality in Lake Okeechobee, Florida : diagnostic and sensitivity analyses , 1995 .

[6]  D. W. Schults,et al.  Summer internal phosphorus supplies in Shagawa Lake, Minnesota , 1981 .

[7]  K. Havens,et al.  Rapid ecological changes in a large suptropical lake undergoing cultural eutrophication , 1996 .

[8]  Thomas L. Crisman,et al.  Relationships between light availability, chlorophyll a, and tripton in a large, shallow subtropical lake , 1995 .

[9]  James J. Fitzpatrick,et al.  Water Quality Analysis Simulation Program (WASP) , 1900 .

[10]  R. Thomann,et al.  Principles of surface water quality modeling and control , 1987 .

[11]  P. Heuberger,et al.  Calibration of process-oriented models , 1995 .

[12]  P. Brezonik,et al.  Modern and historic accumulation rates of phosphorus in Lake Okeechobee, Florida , 1998 .

[13]  P. Moore,et al.  Phosphorus Flux between Sediment and Overlying Water in Lake Okeechobee, Florida: Spatial and Temporal Variations , 1998 .

[14]  K. Havens,et al.  Seasonal and Spatial Variation in Algal Bloom Frequencies in Lake Okeechobee, Florida, U.S.A. , 1994 .

[15]  V. J. Bierman,et al.  Modeling of phytoplankton in Saginaw Bay. I: Calibration phase , 1986 .

[16]  V. J. Bierman,et al.  A preliminary modeling analysis of water quality in Lake Okeechobee, Florida: Calibration results , 1995 .

[17]  David M. Soballe,et al.  Wind-related Limnological Variation in Lake Okeechobee, Florida , 1990 .

[18]  Kinjiro Kajiura,et al.  5. A Model of the Bottom Boundary Layer in Water Waves , 1968 .

[19]  B. Boudreau A kinetic model for microbic organic-matter decomposition in marine sediments , 1992 .

[20]  K. Havens,et al.  The Phosphorus Mass Balance of Lake Okeechobee, Florida: Implications for Eutrophication Management , 2005 .

[21]  Paul V. Zimba,et al.  Spatial and temporal variability of trophic state parameters in a shallow subtropical lake (Lake Okeechobee, Florida, USA) , 1993 .

[22]  Tim A. Wool,et al.  A SEDIMENT RESUSPENSION AND WATER QUALITY MODEL OF LAKE OKEECHOBEE 1 , 1997 .

[23]  G. Premazzi,et al.  Delay in Lake Recovery Caused by Internal Loading , 1991 .

[24]  Richard R. Horner,et al.  Declining lake sediment phosphorus release and oxygen deficit following wastewater diversion , 1986 .

[25]  V. J. Bierman,et al.  Modeling of Phytoplankton in Saginaw Bay: II. Post-Audit Phase , 1986 .

[26]  Smriti Mishra Advances in Limnology , 2002 .

[27]  K. Havens,et al.  A Critical Evaluation of Phosphorus Management Goals for Lake Okeechobee, Florida, USA , 1997 .

[28]  C. T. Haan,et al.  Impact of Uncertain Knowledge of Model Parameters on Estimated Runoff and Phosphorus Loads in the Lake Okeechobee Basin , 1996 .

[29]  R. T. James,et al.  Long-Term Changes in the Sediment Chemistry of a Large Shallow Subtropical Lake , 2001 .

[30]  Z. Ji,et al.  Calibration and verification of a spectral wind–wave model for Lake Okeechobee , 2001 .

[31]  K. Reddy,et al.  Forms and distribution of inorganic phosphorus in sediments of two shallow eutrophic lakes in Florida , 1995, Hydrobiologia.

[32]  R. R. Strathmann,et al.  ESTIMATING THE ORGANIC CARBON CONTENT OF PHYTOPLANKTON FROM CELL VOLUME OR PLASMA VOLUME1 , 1967 .

[33]  K. R. Reddy,et al.  Role of Eh and pH on Phosphorus Geochemistry in Sediments of Lake Okeechobee, Florida. , 1994, Journal of environmental quality.

[34]  K. Jin,et al.  Application of three-dimensional hydrodynamic model for lake Okeechobee , 2000 .

[35]  James J. Fitzpatrick,et al.  Chesapeake Bay Sediment Flux Model , 1993 .

[36]  James L. Martin,et al.  THE WATER QUALITY ANALYSIS SIMULATION PROGRAM, WASP5 PART A: MODEL DOCUMENTATION , 1993 .

[37]  R. Berner,et al.  The role of sedimentary organic matter in bacterial sulfate reduction: The G model tested1 , 1984 .

[38]  D. V. Molen,et al.  Application of SWITCH, a model for sediment-water exchange of nutrients, to Lake Veluwe in The Netherlands , 1993, Hydrobiologia.