Estimation of Inputs to Florida Bay

Inputs from Florida Keys - Runoff

July 1998

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Introduction    |     Methods    |   Results   |   Potential Refinements

Introduction

This section develops estimates of flows and nutrient loads in stormwater runoff and wastewater from the Florida Keys.  The methodology and assumptions are derived primarily from the draft Water Quality Protection Program for the Florida Keys National Marine Sanctuary (USEPA, 1993).

Methods

Based upon the availability of land use data summaries, estimates are derived for three source areas (Upper, Middle, and Lower Keys), as shown below:

map_keys.gif (24553 bytes)

Most of the Lower Keys region is outside of the model domain.  Calculations are driven by estimated 2010 land uses in each region (USEPA, 1993):

Single

Multi-

Region

Family

Family

Commercial

Open

Total

Description

Lower Keys

2951

689

4337

22151

30128

Bahia Honda --> Key West

Middle Keys

2037

510

1467

4446

8460

Marathon --> Windley

Upper Keys

3391

1212

1135

17017

22755

Plantation --> Largo

Total

8379

2411

6939

43614

61343

The following equations are used to estimate total runoff volumes and loads from each region:

Vijn    =   Fjn    Sumk  [  Pi   Ajk    Rk  ]

Lijpn    =    Fjn    Sumk  [   Pi   Ajk    Rk   Cpk   ]   Kp

where,

Vijn    =   total runoff volume for month i, region j, & water body n (bay or reef)
Fjn = fraction of runoff from region j discharged to water body n
Sumk = sum over land uses
P = precipitation in month i
Ajk  = area of region j with land use k
Rk = runoff coefficient for land use k
Lijpn = load for month i, region j, water quality component p, & water body n
Ckp = runoff concentration for land use k and component p
Kp = load attenuation factor for water quality component k

Runoff volumes are calculated using a constant surface runoff coefficient (runoff/rainfall) for each land use category.  Runoff volumes are multiplied by assumed runoff concentrations for each land use category to estimate runoff loads.  Factors to account for attenuation of runoff loads between points of generation and points of inflow to the Bay or Reef are included in the estimation procedure.  Attenuation reflects losses in transport (lack of direct connection between impervious source areas and points of discharge to Bay or Reef)  and runoff BMP's (swales, detention/retention areas).    Transport losses of phosphorus, nitrogen, and suspended solids are estimated using average removal efficiencies reported by USEPA (1993b) for infiltration BMP's and assuming that such BMP's (or equivalent transport losses) are applied to 50% of the source areas in each region.  While estimation of transport losses is difficult, ignoring them altogether would over-estimate loads reaching the bay or reef.  Partitioning of nutrient species and estimates of other water quality components are derived using a framework which is similar to that used in estimating loads from the Florida mainland.  Finally, coefficients to reflect the destination of runoff loads (Bay vs. Reef) are included; current estimates assume a 50/50 split between bay and reef discharges in each region.

Calculations are performed on a monthly basis between October 1985 and December 1997 using a rainfall time series for the Keys region obtained from the National Climatic Data Center (Florida Region 7).  This data set is described in a separate section of this report.

Results

Input values and results are listed in the attached tables:

The output file contains a monthly average flow (m3/sec) and flow-weighted-mean concentration (ppm) for each water-quality component, for each month between October 1985 and December 1997, and for 6 inflow points (discharges to bay & reef from 3 areas).  An excel workbook will be provided to generate output files for alternative sets of assumptions.

Potential Refinements

The following tasks would provide refined estimates of runoff volumes and loads from the Keys:

  • Incorporate revised estimates of land use & runoff concentrations being developed by USEPA & SFWMD.
  • Compile current land use data aggregated on smaller spatial scales
  • Inventory permitted stormwater discharges, BMP's, & site-specific water quality data (SFWMD Dept. of Regulation)
  • Compile & review other stormwater studies conducted in the Keys (e.g., LaPointe, 1995)
  • Review of land use distributions and drainage facilities to evaluate potential transport losses and estimate split between bay and reef discharges
  • Use spatially-distributed rainfall estimates derived from the ENP marine monitoring network
  • Apply a more detailed urban runoff simulation model

Such efforts may be justified if the Bay water quality model is found to be sensitivite to runoff loads.

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http://www.wwwalker.net/flabay/keys_run.htm     Updated:  03/30/02