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STA & Reservoir Performance Measures for the Everglades Restudy

Comparisons of ECP with Restudy Alternatives

03/30/02

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This page presents comparisons of STA/reservoir mass balances between the ECP design and Restudy alternatives.   ECP design values are given for three conditions:
  • Historical - Water Year 1979-1988 inflows to WCA's used to derive STA inflow volumes and loads.
  • ECP(1)   - Water Year 1979-1988 values used in ECP design (historical values, after adjustment for STA construction & BMP's (25% load reduction, 20% runoff volume reduction))
  • ECP(2) - ECP design values, adjusted further to consider BMP makeup water and implementation of the Interim Action Plan (IAP) over the 1979-1988 period.  50% of BMP makeup water is assumed to be treated in STA-34 and the remainder is treated in the source basin STA's.  Over 1979-1988, approximately 14% of EAA runoff was backpumped to Lake Okeechobee.  In recent years, backpump volume has decreased to ~4%.     Assuming that this condition prevails in the future, the adjustment for IAP causes in increase in the runoff pumped south to the STA's.  The volume of new regulatory release from the Lake under this plan is reduced relative to ECP(1) to offset IAP runoff, so that the total plan meets the ~28% EFA target for flow increase relative to the WY 1979-1988 period.

Restudy values are given for the 2050 base condition (50Base) and each alternative (ALT-A,B,C,D,D13R).  Sources which are not treated by the ECP (urban water supply deliveries, discharges from Acme Drainage District) are not considered in these comparisons.

Detailed results by STA are given in attached tables for each design period (1965-1995, WY 1979-1988) and each BMP performance assumption (25%, 51%).  

Another set of tables summarizes total project inflows by source (EAA runoff, lake release, etc.) and total project outflows by location (WCA-1, WCA-2A, etc..) for each design period and BMP assumption.

Differences in the predicted STA outflow volumes between the ECP design and Restudy alternatives can be partially attributed to differences in the areal water budget terms for the STA's (rainfall, evapotranspiration, and seepage).  The following table compares ECP design with 50Base values (area-weighted mean over all STAs) for Water Years 1979-1988:

STA Areal Water Balance Terms (inches/yr)

ECP

50base

Diff.

Precipitation

48.5

49.9

1.4

Evapotranspiration

45.3

57.2

11.9

Seepage In

0

2.0

2.0

Seepage Out

0

4.9

4.9

Net

3.2

-10.3

-13.5

Higher evapotranspiration rates in the Restudy simulations (57.2 vs. 45.3 in/yr)are primarily responsible for differences in the net water budget terms.   Applied over the 39,918-acre total STA surface area, the net areal flow difference of -13.5 inches/year amounts to a net flow difference of -44.5 kac-ft/yr.   This means that for the same inflow volumes, the Restudy assumptions (inherent in the SFWMM) would predict 44.5 kac-ft/yr less outflow, as compared ECP assumptions.   This difference amounts to ~4% of the historical inflow to the WCA's (1075 kac-ft/yr), which was used as a basis for calculating the 28% flow increase required by the Everglades Forever Act.   Thus, if the EFA target were adjusted to account for differences in areal fluxes (principally, ET), the target would be 24% instead of 28%.    Actual ET rates may fall somewhere between the ECP (45.3 in/yr) and 50Base (57.2 in/yr)  values.  Measured ET rates in the Everglades Nutrient Removal Project were 47.5 in/yr (Dec 1, 1995 - Nov 30, 1996) and 49.6 in/yr (Dec 1, 1996 - Nov 30, 1997)  (SFWMD, Everglades Nutrient Removal Project 1996 and 1997 Monitoring Reports).   

The following table compares ECP design with 50Base values for STA inflow volumes over Water Years 1979-1988:

STA Inflow Sources (kac-ft/yr)

ECP(1)

ECP(2)

50Base

EAA Runoff

666.4

744.7

720.9

Lake Release

257.6

364.9

269.6

C139

114.5

114.5

112.8

298

24.9

24.9

19.3

C51W

105.4

105.4

117.4

STA Net

10.6

10.6

-34.2

Total

1179.4

1365.0

1205.8

Percent Increase *

10%

27%

12%

* Percent Increase relative to historical WCA inflow of 1075 kac-ft/yr.

The volume of C51W runoff captured under the 50Base run (117.4 kac-ft/yr) is 11% higher than that captured under the ECP plans (105.4 kac-ft/yr).  Otherwise, differences in lake release and net areal fluxes account for most of the differences between the ECP designs and the 50Base run.

The ECP design and Restudy runs also differ with respect to STA bypass predictions.   The ECP design treats all EAA runoff in the WY 1979-1988 period.    Predicted bypass volumes for the 50Base run and each Restudy alternative are summarized below:

STA Bypass Flows (kac-ft/yr),  Water Years 1979-1988
50Base Alt-A Alt-B Alt-C Alt-D Alt-D13R

STA-2

23.3

6.1

9.5

9.4

9.3

9.3

STA-34

0.0

14.7

22.6

22.9

23.1

22.9

STA-5

0.0

0.0

0.0

0.0

0.0

0.0

Total

23.3

20.8

32.0

32.2

32.4

32.2

The following table compares bypass volumes for the 1965-1995 period:

STA Bypass Flows (kac-ft/yr), Cal. Years 1965-1995

50Base

Alt-A

Alt-B

Alt-C

Alt-D

Alt-D13R

STA-2

21.1

4.4

7.9

7.8

7.6

7.8

STA-34

0.0

19.9

27.7

27.7

28.0

27.8

STA-5

0.3

0.4

0.4

0.3

0.4

0.4

Total

21.4

24.6

36.0

35.8

36.0

35.9

As distinguished from the ECP design, the Restudy alternatives predict frequent bypass events for STA-2 during the WY 1979-1988 period.  Under the 50Base run, it is possible that these bypasses reflect peak flows which were historically backpumped to Lake Okeechobee and were not considered in the ECP design.  With the Restudy Alternatives, STA-2 bypass volumes decrease while STA-34 bypass volumes increase.  The mass-balance comparisions indicate that IAP flows would have a larger impact in total inflows to STA-2 and STA-34 than on inflows to other STA's (compare ECP(1) vs. ECP(2) inflows).   Further investigation of the SFWMM simulation algorithm for STA's is needed to determine whether STA bypass volumes predicted by the SFWMM should be a real concern from a design perspective.

All Restudy runs assume that the second portion of STA-6 is not constructed and that runoff from the C-139 Annex is not treated in the ECP.  Although there is a possiblity that the second unit will not be constructed (depending upon observed performance of STA-5 and the first portion of STA-6), current plans call for construction of both units.  If this occurs, a portion of the runoff from C-139 will be treated in STA-6 and the overloading of STA-5 predicted for all restudy alternatives will be alleviated to some extent.

Figures & Discussion (Water Year 1979-1988, BMP Performance = 25%):

Tables:

Period of Record 65-95 65-95 79-88 79-88
BMP Performance 25% 51% 25% 51%
Mass Balance Comparisons X X X X
Project Inflow & Outflow Summaries X X X X

STA & Reservoir Inflows vs. Source

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in2_w.gif (9663 bytes)

These charts compare the sources of flow and load to STA's and reservoirs.   All values are for WY 1979-1988 and a BMP performance assumption of 25%.  Restudy Alternatives A-D13R treat additional lake water by capturing a portion of the EAA runoff in the first storage reservoir (Talisman) and later releasing most of it for irrigation purposes.   This increases capacity for lake releases in the other storage reservoirs and STA-34.

STA & Reservoir Inflows vs. Plan

xcwca.gif (9032 bytes)

in2_w.gif (9663 bytes)

These charts compare the sources of flow and load to STA's and reservoirs.   All values are for WY 1979-1988 and a BMP performance assumption of 25%.  Restudy Alternatives A-D13R capture additional lake water in the EAA storage reservoirs.   A portion of the EAA runoff is captured in the first EAA storage reservoir (Talisman) and used to help meet EAA irrigation demand.  

STA & Reservoir Outflows vs. Location & Plan

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out2_w.gif (8319 bytes)

These charts show STA and reservoir outflow volumes and loads as a function of location and plan.  Values are for WY 1979-1988.   Outflows include STA outflows and high-flow bypasses.   The major distinction between the ECP and Restudy alternatives is that the latter includes outflow to the EAA from the EAA storage reservoirs to help meet irrigation demand.

STA Outflow Concentrations vs. Location

out2_c.gif (10118 bytes)

These charts show the flow-weighted-mean concentrations of total phosphorus in the combined discharges from the STA's to each WCA, Rotenberger, Holeyland, and all (WCA/R/HL).  Results are for Water Years 1979-1988 and 25% BMP performance.   Concentrations reflect STA outflows and high-flow bypass.

STA & Reservoir Outflows to WCA's, Holeyland, & Rotenberger

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out2_w.gif (8319 bytes)

out2_c.gif (10118 bytes)

This charts show the flow, load, and concentration in combined discharges from the STA's to the WCA's, Holeyland, & Rotenberger Tract for Water-Years 1979-1988 and 25% BMP performance.  The combined discharges include outflows from treatment areas and high-flow bypass.

STA & Reservoir Performance Measures

http://www.wwwalker.net/restudy/ecp_res.htm      Updated:  03/30/02