Review of Anticipated Benefits in 1995 Water Regulation Schedule - - PowerPoint PPT Presentation

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Review of Anticipated Benefits in 1995 Water Regulation Schedule - - PowerPoint PPT Presentation

Review of Anticipated Benefits in 1995 Water Regulation Schedule for Water Conservation Area 1 Dr. Laura A. Brandt USFWS Team Leader, Joint Ecological Modeling Lab November 14, 2006 TOC Meeting Nov 14, 2006 TOC L.A. Brandt Review of


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SLIDE 1

Nov 14, 2006 TOC L.A. Brandt

Review of Anticipated Benefits in 1995 Water Regulation Schedule for Water Conservation Area 1

  • Dr. Laura A. Brandt

USFWS Team Leader, Joint Ecological Modeling Lab November 14, 2006 TOC Meeting

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SLIDE 2

Nov 14, 2006 TOC L.A. Brandt

Review of Environmental Assessment

  • Describe the ecological rationale for the

proposed changes as they relate to the stated purposes

  • Describe the hydrological and ecological

measures that could be used and the expectations for them if the anticipated benefits were achieved

  • Describe, where possible, what has been

achieved

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SLIDE 3

Nov 14, 2006 TOC L.A. Brandt

Summary

  • The water regulation schedule for WCA-1

was changed in 1995 to make conditions in the Refuge interior wetter- particularly in the north- for the benefit habitat and wildlife

Wet Prairie

Shrub

Tree Island Tree Island Wet Prairie

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SLIDE 4

Nov 14, 2006 TOC L.A. Brandt

Summary (cont.)

  • The change to the 1995 water regulation

schedule has resulted in many of the anticipated hydrological benefits

  • Generally there are:

– Higher water levels – Longer hydroperiods – Lower frequency of dry-outs

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SLIDE 5

Nov 14, 2006 TOC L.A. Brandt

Summary (cont.)

  • In most cases it has not been confirmed

that the hydrological changes have resulted in the desired ecological changes

  • It is likely that some ecological benefits

have occurred

  • However, under recent management, it is

still too dry in the north and too wet in the south

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SLIDE 6

Nov 14, 2006 TOC L.A. Brandt

Summary (cont.)

  • It also is likely that there have been some

unintended ecological consequences

– Deeper depths and longer hydroperiods in the south – Reduction in variability in hydroperiod and depths

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SLIDE 7

Nov 14, 2006 TOC L.A. Brandt

Summary (cont.)

  • Creating “optimal” conditions for the

Refuge interior will require creative solutions that take advantage of natural variability

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SLIDE 8

Nov 14, 2006 TOC L.A. Brandt

Background

  • Water Conservation

Area 1 is a part of A.R.M. Loxahatchee NWR

  • Established as one of

5 WCAs for flood protection, water supply, wildlife habitat

  • Water is managed

under a water regulation schedule

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SLIDE 9

Nov 14, 2006 TOC L.A. Brandt

Background (cont.)

  • There have been four water regulation

schedules for WCA-1

  • The current water regulation schedule has

been in effect since 1995

  • Changes to the water regulation schedule

have been made at the request of FWS to improve conditions for wildlife

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SLIDE 10

Nov 14, 2006 TOC L.A. Brandt From Richardson et al. 1990

Elevation and Water Level Gauges

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SLIDE 11

Nov 14, 2006 TOC L.A. Brandt

10 11 12 13 14 15 16 17 18 J F M A M J J A S O N D Month Elevation Feet NGVD ZONE A1 [1975-1994] ZONE A2[1975-1994] ZONE B [1975-1994] ZONE C [1975-1994]

1975-1994 WCA-1 Water Regulation Schedule

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SLIDE 12

Nov 14, 2006 TOC L.A. Brandt

10 11 12 13 14 15 16 17 18 J F M A M J J A S O N D Month Elevation Feet -NGVD ZONE A1 [1995-2005] ZONE A2 [1995-2005] ZONE B [1995-2005] ZONE C [1995-2005]

1995-present WCA-1 Water Regulation Schedule

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SLIDE 13

Nov 14, 2006 TOC L.A. Brandt

Summary of Changes From 1975 to 1995 Water Regulation Schedule for WCA-1

  • Raised floor from 11 to 14 feet NGVD
  • Raised the top of Zone B from 15.35 to

15.75 feet

  • Raised the bottom of Zone A from 17.0 to

17.5 feet and from 15.75 up to 17.5 feet from early July to mid-September

  • Added provisions for preceding inflows

under certain conditions of water supply delivery

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SLIDE 14

Nov 14, 2006 TOC L.A. Brandt

Anticipated Benefits of 1995 Water Regulation Schedule for WCA-1

  • 1. Allow higher water levels during wet years in the northern portion of the

Refuge

  • 2. Increase the hydroperiod of interior marshes of the Refuge such that dry-out

does not occur on an annual basis

  • 3. Increase the proportion of the interior marsh of the Refuge that serves as

nursery areas for aquatic organisms

  • 4. Improve the timing of winter stage drawdown in the Refuge to benefit

wading bird

  • 5. Restore conditions in the Refuge similar to those found when the areas was

used by snail kites for nesting

  • 6. Allow for the storage of a greater quantity of water within the C&SF system

during wet and normal rainfall years

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SLIDE 15

Nov 14, 2006 TOC L.A. Brandt

  • 1. Allow higher water levels during wet years

in the northern portion of the Refuge

  • Reverse the trend of

invasion of sawgrass by brush and conversion of wet prairie to sawgrass

5 10 15 20 25 30 35 40 45 Slough Wet Prairie Sawgrass Brush Other Vegetation class Percent of Refuge interior Overall percent from Hagenbuck et

  • al. 1974

Overall percent from Richardson et

  • al. 1990 without

tree islands

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SLIDE 16

Nov 14, 2006 TOC L.A. Brandt

Wet Prairie Shrub Tree Island

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SLIDE 17

Nov 14, 2006 TOC L.A. Brandt

Tree Island Wet Prairie

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SLIDE 18

Nov 14, 2006 TOC L.A. Brandt

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SLIDE 19

Nov 14, 2006 TOC L.A. Brandt

  • 1. (cont.) Allow higher water levels during

wet years in the northern portion of the Refuge

  • Bring 20,000 ac of

marsh in the northern quarter of the Refuge back into productive marsh condition

  • Avoid yearly dry-outs
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SLIDE 20

Nov 14, 2006 TOC L.A. Brandt

  • 2. Increase the hydroperiod of interior

marshes of the Refuge such that dry-

  • ut does not occur on an annual basis
  • Have larger populations of aquatic
  • rganisms
  • Increase protection against drought by

having greater year round water storage

  • Avoid yearly dry-outs
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SLIDE 21

Nov 14, 2006 TOC L.A. Brandt

  • 3. Increase the proportion of the

interior marsh of the Refuge that serves as nursery areas for aquatic organisms

  • Increase aquatic productivity
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SLIDE 22

Nov 14, 2006 TOC L.A. Brandt

  • 4. Improve the timing of winter stage

drawdown in the Refuge to benefit wading birds

  • Provide foraging and

nesting conditions for wading birds from January-June

  • Slower spring

recession rate would benefit wood storks and other wading birds

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SLIDE 23

Nov 14, 2006 TOC L.A. Brandt

  • 5. Restore conditions in the Refuge similar

to those found when the areas was used by snail kites for nesting

  • Provide habitat

suitable for snail kite nesting

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SLIDE 24

Nov 14, 2006 TOC L.A. Brandt

  • 6. Allow for the storage of a greater

quantity of water within the C&SF system during wet and normal rainfall years

  • Avoid yearly dry-outs
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SLIDE 25

Nov 14, 2006 TOC L.A. Brandt

Hydrological Measures

  • Average monthly stage at 1-7 and 1-8C
  • Percentage of April-June period when

water depth was >0.325 feet

  • Average yearly hydroperiod at 1-7 (15.0),

15.5, and 16.0 feet

  • Average spring (March-June) hydroperiod

at 1-7, 15.5, and 16.0 feet

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SLIDE 26

Nov 14, 2006 TOC L.A. Brandt

Hydrological Measures (cont.)

  • Number of years when stage went below ground

(dry-out) at 1-7, 15.5, and 16.0 feet

  • Number of years between dry-outs
  • Percentage of years when there was at least 3

years between dry-outs

0.2 0.4 0.6 0.8 1 Slough Wet Prairie Sawgrass Brush/Shrub Vegetation class Relative elevation from slough (feet)

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SLIDE 27

Nov 14, 2006 TOC L.A. Brandt

Hydrological Measures (cont.)

  • Timing of initiation of spring recession
  • Spring recession rate
  • Average yearly water storage
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SLIDE 28

Nov 14, 2006 TOC L.A. Brandt

13.50 14.50 15.50 16.50 17.50

Jan Feb Mar Apr May Jun Jul Aug Sept Oct Nov Dec Month

Stage 1-8C (feet NGVD) Average monthly stage 1-8C 1975-1994 Average monthly stage at 1-8C 1995-2005

13.5 14.5 15.5 16.5 17.5 Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec Month Stage 1-7 (feet NGVD) Average monthly stage 1-7 1975-1994 Average monthly stage 1-7 1995-2005

Average monthly stage difference 0.85 feet. Range 0.63 to 1.34 feet Average monthly stage difference 0.38 feet. Range 0.26 to 0.60 feet.

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SLIDE 29

Nov 14, 2006 TOC L.A. Brandt

25 50 75 100 15.0 15.5 16.0 Elevation (feet NGVD) Average yearly Hydroperiod (%) 2 4 6 8 10 12 Months Mean 1975-1995 Mean 1995-2005

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SLIDE 30

Nov 14, 2006 TOC L.A. Brandt

Elevation (feet NGVD) Percentage of years 1975-1994 when there was at least three years between dry outs Percentage of years 1995-2005 when there was at least three years between dry outs Ecologically different? 15.0 45% 64% Yes 15.5 20% 55% Yes 16.0 0% 0% No

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SLIDE 31

Nov 14, 2006 TOC L.A. Brandt

Ecological Measures

  • Acres of sawgrass, brush, and wet prairie

in 1975, 1995, 2005

  • Acres of each vegetation type converted to

a different vegetation type

  • Density and distribution of aquatic
  • rganisms (fish and apple snails)
  • Number and spatial extent of wading birds

foraging in the Refuge from January-June

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SLIDE 32

Nov 14, 2006 TOC L.A. Brandt

Ecological Measures (cont.)

  • Number of wading bird nests
  • Number of successful wading bird nests
  • Frequency of “good” nesting years for

wading birds

  • Frequency of snail kite nesting
  • Number of successful snail kite nests per

year

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SLIDE 33

Nov 14, 2006 TOC L.A. Brandt

Hydrological Change Likely to Result in Ecological Change?

Hydrological Measure Anticipated Benefit Ecological Indicator Overall 15.0 ft 15.5 ft 16.0 ft Average Monthly Stage 1, 5 Vegetation Y Y M # years when stage went below ground 1, 2, 5 Vegetation, fish, snail kites N Y N Average yearly hydroperiod 2, 5 Vegetation, snail kites N M Y Average spring (Mar-Jun) hydroperiod 2, 5 Vegetation, snail kites N M Y # years between dry-outs 3, 5, 6 Vegetation, fish, snail kites Y Y N % years with at least 3 years between dry-outs 3 Fish Y Y N % of time in Apr-Jun depth >0.325 ft 3, 5 Apple snails, snail kites M Y N Timing of spring recession 4 Wading birds Y Recession rate 4 Wading birds ?

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SLIDE 34

Nov 14, 2006 TOC L.A. Brandt

Summary

  • The change to the 1995 water regulation

schedule has resulted in many of the anticipated hydrological benefits

  • Generally there are:

– Higher water levels – Longer hydroperiods – Lower frequency of dry-outs

slide-35
SLIDE 35

Nov 14, 2006 TOC L.A. Brandt

Summary (cont.)

  • In most cases it has not been confirmed

that the hydrological changes have resulted in the desired ecological changes

  • It is likely that some ecological benefits

have occurred

  • However, under recent management, it is

still too dry in the north and too wet in the south

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SLIDE 36

Nov 14, 2006 TOC L.A. Brandt

Summary (cont.)

  • It also is likely that there have been some

unintended ecological consequences

– Deeper depths and longer hydroperiods in the south – Reduction in variability in hydroperiod and depths

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SLIDE 37

Nov 14, 2006 TOC L.A. Brandt

Recommendations

  • Take advantage of new water level

gauges in North and South

  • Work within the current schedule in an

adaptive management approach (e.g., set up ways to explicitly learn while managing)

  • Establish ecological monitoring to follow

changes

  • Set up timelines for evaluation and

modification of operations

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SLIDE 38

Nov 14, 2006 TOC L.A. Brandt

Key internal influences on water management

  • T&E species and habitat (snail kite and

wood stork)

  • Tree islands
  • Wading birds
  • Apple snails
  • Alligators
  • Exotics
  • Fire
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SLIDE 39

Nov 14, 2006 TOC L.A. Brandt

Summary (cont.)

  • Creating “optimal” conditions for the

Refuge interior will require creative solutions that take advantage of natural variability