A Case Study in Lake Management Issues

47
Ed Dunne, Ph.D, Division of Environmental Sciences, SJRWMD P.O. Box 1429, Palatka, FL 32178; Email: [email protected] ; ph: 386-329- 4227 A Case Study in Lake Management Issues

description

A Case Study in Lake Management Issues. Ed Dunne, Ph.D , Division of Environmental Sciences, SJRWMD P.O. Box 1429, Palatka, FL 32178; Email: [email protected] ; ph: 386-329-4227. Overview. Issues in lake management Approach to lake restoration/enhancement Lake Apopka and historical sketch - PowerPoint PPT Presentation

Transcript of A Case Study in Lake Management Issues

Page 1: A Case Study in Lake Management Issues

Ed Dunne, Ph.D, Division of Environmental Sciences, SJRWMDP.O. Box 1429, Palatka, FL 32178; Email: [email protected]; ph: 386-329-4227

A Case Study in Lake Management

Issues

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Issues in lake management Approach to lake restoration/enhancement Lake Apopka and historical sketch Time series of:

basin changes and nutrient loading Nutrient budgets and water quality trends

Total P, Chl a, Transparency, TSS Management practices

Within watershed, within lake Lake Improvements

Accessing lake data Water levels and water quality

Overview

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Water Management Districts in Florida

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18 Counties in the Districts

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Ten Major Watersheds

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Good waters

10%

90%

Lakes, Reservoirs, and Ponds

Good WatersImpaired Waters

Source:http://iaspub.epa.gov/waters10/attains_state.control?p_state=FL#total_assessed_waters

Florida 2010Lakes, Reservoirs, and Ponds 2010

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Lakes, Reservoirs, and Ponds 2010:Causes of impairment

Mercury26%

Nutrients27%Iron

10%

DO11%

Alkalinity2%

Turbidity12%

pH6%

Ammonia5%

Source: http://iaspub.epa.gov/waters10/attains_state.control?p_state=FL#total_assessed_waters

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Multipronged approach to deal with impairment

Restoration/Enhancement

Reduce nutrient load to the lake

Cost effective nutrient program to: Remove Reduce

Source ControlWithin Watershed

Mitigate LossWithin Lake

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Controlling and Mitigating Eutrophication

Reduce P loading

Lower P concentration & plankton

Increase water transparency

Increase SAV

Increase game fish Time

Improved Ecosystem Health

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Multipronged approach to lake improvement

Lake water quality

Water levels

Restoring

Wetlands

Storm water

Acquiring land

TMDLControl of

Hydrilla

Planting littoral zone

Marsh Flow-Way

Shad Harvest

Within Watershed

Within Lake

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Lake Apopka

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A lake and it’s watershed

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Lake ApopkaHistorical timeline: 1880s-

2010s 1880s Land around the lake $0.25/acre 1890s Apopka Beauclair Canal 1920s Sewage, wastewater, hurricanes (6-8ft) 1940s Muck farms on NS, lake levee, hurricanes, blooms, <

SAV 1950s Water control structures on ABC 1960s Fish kills, pesticide use by agriculture 1970s State/federal restoration, bacterial disease, bass failing,

4 fish camps 1980s Tower Chemical, fish kill, Apopka and SWIM Acts, no fish

camps, pilot projects initiated, $15 million land purchase

1990s FOLA, MFW pilot project, shad harvest, Act ’96 (P criterion), $100 million land purchase, bird die

off 2000s TMDL, MOU, MFW, reflooded 5,000 acres of NSRA 2010s Bird list = 346 sp., MFW, shad, BMAP projects, reflooded

10,000 acres, > SAV

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Time series:Basin changes, P

loading, and water quality

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Sources: Lake Apopka External Nutrient Budget 1989-2002; Schelske et al., 2005.

Basin Land Use Changes

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Major Former Farm Areas

Source: Lake Apopka External Nutrient Budget 1989-2010

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Source: Lake Apopka External Nutrient Budget 1989-2010

Basin Land Use Changes

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0.000

0.100

0.200

0.300

0.400

0.500

0.600

0.700

0.800

1900 1910 1920 1930 1940 1950 1960 1970 1980 1990 2000 2010

Phosphorus Loading to Lake Apopka 1900-2002

Measured

Estimated from literature

Load

ing

g m

-2 y

r-1

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Year 20092007200520032001199919971995199319911989

0.7

0.6

0.5

0.4

0.3

0.2

0.1

0.0Tota

l pho

spho

rus

Load

ing

to L

ake

Apop

ka g

/m2

TMDL

Apopka SpringSHPMWGPCFJohns LakeBasin RunoffRainfallFarm Pumps

Phosphorus Loading to Lake Apopka 1989-2010

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0

0.1

0.2

0.3

0.4

1987 1991 1995 1999 2003 2007 2011

Tota

l Pho

spho

rus

mg/

L

Year

Lake Apopka Total P (Annual, Monthly)

Target P 0.055 mg/L

Total Phosphorus (P) (mg/L)

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Total Phosphorus (P) (mg/L)

63.50

64.50

65.50

66.50

67.50

0.00

0.05

0.10

0.15

0.20

0.25

0.30

1987 1991 1995 1999 2003 2007 2011

Lake

Sta

ge f

t N

GVD

192

9

Tota

l Pho

spho

rus

mg/

L

Year

Lake ApopkaTotal P (Annual)

Lake Stage (Annual)

Target P 0.055 mg/L

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63.50

64.50

65.50

66.50

67.50

0

20

40

60

1987 1990 1993 1996 1999 2002 2005 2008 2011

Lake

Sta

ge f

t N

GVD

Tota

l Pho

spho

rus

met

ric to

ns

Year

Lake Apopka Total P Mass (Annual)Lake Stage (Annual)

P Mass at Target P Conc

and Mean Stage

Total P (metric tons) and Stage

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R² = 0.9106

0

40

80

120

0 100 200 300

Chlo

roph

yll

a ug

/L

Total Phosphorus ug/L

Lake Apopka, annual mean values1989 - 2010

Relationship between chl. a and total P

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0

50

100

150

200

1987 1991 1995 1999 2003 2007 2011

Chl

orop

hyll

ug/L

Year

Lake Apopka Chlorophyll (Annual, Monthly)

Chlorophyll a (µg/L)

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63.50

64.50

65.50

66.50

67.50

0

40

80

120

1987 1991 1995 1999 2003 2007 2011

Lake

Sta

ge ft

NG

VD 1

929

Chl

orop

hyll

aug

/L

Year

Lake Apopka Chlorophyll (Annual)Lake Stage (Annual)

Chlorophyll a (µg/L)

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Relationship between TSS and chl. a

R² = 0.7064

0

40

80

120

0 50 100 150

TSS

mg/

L

Chlorophyll a ug/L

Lake Apopka, annual mean values1989 - 2010

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0

40

80

120

160

200

1987 1990 1993 1996 1999 2002 2005 2008 2011

TSS

mg/

L

Year

Lake Apopka TSS (Annual, Monthly)

Total Suspended Solids (mg/L)

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63.50

64.50

65.50

66.50

67.50

0

4000

8000

12000

16000

20000

24000

1987 1990 1993 1996 1999 2002 2005 2008 2011

Lake

Sta

ge f

t N

GVD

Tota

l sus

pend

ed s

olid

s m

etric

tons

Year

Lake Apopka TSS (Annual)Lake Stage (Annual)

Total Suspended Solids (mg/L)

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0

0.1

0.2

0.3

0.4

0.5

1987 1991 1995 1999 2003 2007 2011

Tran

spar

ency

m

Year

Lake Apopka Secchi Transparency (Annual, Monthly)

Secchi depth (meters)

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63.50

64.50

65.50

66.50

67.50

0

0.1

0.2

0.3

0.4

0.5

1987 1991 1995 1999 2003 2007 2011

Lake

Sta

ge ft

NG

VD 1

929

Tran

spar

ency

m

Year

Lake Apopka Secchi Depth (Annual)Lake Stage (Annual)

Secchi depth (meters)

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Some management practices to help improve the lake

Within lakeWithin watershed

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Reflooding Ag. lands back to Wetlands

RESULTS 2000 Initial flooding of Duda Sub-East 680 acres 2011 Flooding to date about 10,000 acres

Phased ApproachEnvironmental Site Assessments, Risk AssessmentBA, BO, biota monitoring during floodingPrior to flooding:Field prep., which included soil amendment (3,000 ha; $2.5 m)Remediation to reduce OCP - deep ploughing (1,620 ha; $9.6

m)

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2000

Phased Approach to Flooding

Maps produced by P. Bowen

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2005

Phased Approach to Flooding

Maps produced by P. Bowen

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2010

Phased Approach to Flooding

Maps produced by P. Bowen

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2011

Phased Approach to Flooding

9,870 acres flooded

Maps produced by P. Bowen

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Gizzard Shad Harvest on Lake Apopka 1993 - 2010

RESULTS 450-500 mT/yr of fish

harvested P removal in fish = 2-3

mT/yr

GOALSRemove P in fish bodies Reduce recycling of P caused

by bottom feedingReduce turbidity caused by

bottom disturbance

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Gizzard Shad Harvest on Lake Apopka 1993 - 2010

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Marsh Flow-way 2003 - 2010

REMOVAL RESULTS TP: 2 mT, 28%, 0.8 g m-2 yr-1

TSS: 4,000 mT, 91%, 1,300 g m-2 yr-1 TN: 80 mT, 22%, 26 g m-2 yr-1

GOALSMaximize P removal from the

lake Provide wetland habitat

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-1

4

9

14

19

-1

0

1

2

3

4

5

6

7

2001 2003 2005 2007 2009 2011

Tota

l P re

mov

ed m

etri

c to

nsMarsh Flow-Way Total Phosphorus Removal

November 2003 through December 2010

Efficiency = 28%

Cum

ulat

ive

tota

l P re

mov

ed m

etric

ton

s

Total Phosphorus

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0

5,000

10,000

15,000

20,000

25,000

30,000

35,000

0

1,000

2,000

3,000

4,000

5,000

6,000

7,000

2001 2003 2005 2007 2009 2011

Cum

ulat

ive

solid

s re

mov

ed m

etrc

tons

Solid

s re

mov

ed m

etri

c to

ns

Marsh Flow-Way Total Suspended Solids Removal

November 2003 through December 2010

Efficiency = 91%

Total Suspended Solids

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0

100

200

300

400

500

600

700

0

25

50

75

100

125

150

2001 2003 2005 2007 2009 2011

Cum

ulat

ive

TN r

emov

ed m

etric

ton

s

TN r

emov

ed m

etri

c to

ns

Marsh Flow-Way Total Nitrogen Removal

November 2003 through December 2010

Efficiency = 22%

Total Nitrogen

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Evidence for Lake Improvement

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0.000

0.100

0.200

0.300

1987 1991 1995 1999 2003 2007 2011

Tota

l Pho

spho

rus

mg/

L

Year

Lake Apopka Total P (Annual)

Target P 0.055 mg/L

Pre Post

Pre = period used to measure baseline loading for TMDL development (Magley, 2003)Post = period to include years with both normal and low lake stages

Total Phosphorus (P) (mg/L)

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Changes in Lake ApopkaConcentrations & Loads

Parameter Units Comparison periodPre (‘89-’94) Post (‘03-’10)

Change

TP loading mT/yr 64 26 -59%

TP mg/L 0.21 0.11 -45%

Chl a µg/L 99 63 -37%

Secchi m 0.21 0.33 56%

TSS mg/L 86 67 -22%

TP mT 43 19 -55%

TSS mT 17,533 10,927 -38%

TN mT 1,112 715 -36%

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Year Area (acres)1997 2.92000 6.22003 02006 13.62008 02009 13.52011 50

Changes in areal coverage of Vallisneria americana along Lake Apopka shoreline

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Accessing lake data

http://floridaswater.com/