estimating benefits of hydrologic restoration and freshwater … · 2014. 9. 17. · estimating...
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Estimating Benefits of Hydrologic Restoration and Freshwater
Introduction Projects in Coastal Wetlands
Ron Boustany USDA/Natural Resources Conservation Service
Lafayette, LA
CEER 2014
Area
(Spa
tial)
Time (Temporal)
Progradation Degradation
Delta Cycle
High River Influence High O2 High Mineral/Sediment High Nutrient Availability Low Plant Competition Mineral Soils High Bulk Density Geologically Driven
Low River Influence Low O2 Low Mineral/Sediment Low Nutrient Availability High Plant Competition Organic Soils Low Bulk Density Biologically Driven
Based on O’Neil 1949, Gosselink 1984, Sasser 1994, Swarzenski et al. 2008
Input > Output
Input = Output
Input < Output
+1.0%
+0.5%
+0.25%
-0.25%
-0.5%
TIME
AREA
Annual Land Change Rates
0%
-1.0%
Prograding (Land Gain)
Degrading (Land Loss)
Input > Output
Input = Output
Input < Output
+2.0%
-2.0%
Inputs = organic + mineral accretion; Ouputs = subsidence + erosion + SLR
Organic Fraction
Mineral Fraction
Wetland Soil Nutrients
Plant Production
Sediment
Export
(-)
(-) (+)
(+)
(-)
(+)
Salinity
NSED2 Model: Calculates a benefit from nutrient and sediment introduction. SPROD2 Model: Calculates benefit from reduction in salinity.
Nutrients In situ Organic Production
Organic soil fraction
Export Denitrification
Burial (Immobilization)
Decomposition Export
Salinity Reduction
Sediment Mineral soil
fraction
Export
SPROD2
NSED2
Gosselink et al. 1984
Patterns Consistency Predictability Model “remarkably constant”
* Nyman et al. 1990, Hatton et al. 1983 ** Faulkner and Poach 1996
About 0.026 g cm-3 organic carbon in all soils
32.5%
16.3%
10.0%
3.0%0.08
0.160.24
0.835
0
0.1
0.2
0.3
0.4
0.5
0.6
0.7
0.8
0.9
0.0%
5.0%
10.0%
15.0%
20.0%
25.0%
30.0%
35.0%
Fresh/Intermediate Brackish Saline New Delta
% Organic C Bulk Density
Bulk Density = 0.16 g cm-3 (Brackish Marsh)
% Organic = 16.25% Organic Fraction = BD * % Organic Organic Fraction = 0.16 * 0.1625 = 0.026 g cm-3
Production Rate (PR) = 2653 g m-2 y-1
= 0.2653 g cm-2 y-1
= 0.2653 g cm-3 y-1 (at 1 cm depth) % of Production in BD = (Organic Fraction)/(PR) (0.16 g cm-3)*(0.1625) ÷ (0.2653 g cm-3) = 9.8%
1 cm
Organic Fraction Calculation (NSED2 & SPROD2)
0.00
0.10
0.20
0.30
0.40
0.50
0.60
0.70
0.80
0.90
1.00
1 2 3 4 5 6 7 8 9 1011121314151617181920212223242526272829303132333435Salinity (ppt)
% Maximum Productivity
Fresh
Intermediate
Brackish
Saline
Reproduced from Snedden and Swenson 2012
Central Terrebonne Freshwater Enhancement Project (TE-66)
Project Area – 48,446 acres 19,421 acres wetland 29,025 acres water
Loss Rate = -0.46%/y
(89.3 acres/y)
Problem: Expanded breach in historic ridge that allows for more direct transfer of higher saline gulf marine waters to penetrate deep into the upper Central Terrebonne fresh and intermediate marshes. Goals: Reestablish historic hydrologic and salinity conditions by reducing the intrusion of gulf marine waters via the Grand Pass into the Central Terrebonne marshes. Solution: Construction of rock barge bay in pass to reduce 900 ft wide x 37 ft deep opening by 90% to 150 ft x 16 ft. Model: SPROD2 (STELLA 10.0.4)
SPROD2 Model – Calculates the benefits of salinity reduction from freshwater introduction and/or structural features
Module 1- Salinity Dilution Box Model Calculates the percent difference in salinity with the project.
SPROD2 Salinity/Production Model
1:10 PM Wed, Jul 09, 2014
Untitled
Page 1
0.00 8100.00 16200.00 24300.00 32400.00
Hours
1:
1:
1:
2:
2:
2:
-1
2
5
0
15
30
1: Tide Level 2: Tide Sal
1
11
12 2
2
2
1:18 PM Wed, Jul 09, 2014
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Page 1
0.00 8100.00 16200.00 24300.00 32400.00
Hours
1:
1:
1:
2:
2:
2:
3:
3:
3:
0
15
30
-2
-1
1
1: Tide Sal 2: Salinity 3: Percent Salinity Diff
1
1
1
12 22
2
3 3 3 3
Module 2 – Marsh production factor calculator Calculates the percent difference in production within each marsh zone.
SPROD2 Salinity/Production Model
1:36 PM Wed, Jul 09, 2014
Untitled
Page 10.00 8100.00 16200.00 24300.00 32400.00
Hours
1:
1:
1:
2:
2:
2:
0
15
30
-1
0
1
1: B Init Sal 2: B Diff%
1
1
1
1
2 2 2 2
Example of brackish marsh results.
Module 3-Land Change Calculators Calculates the acres of land benefit within each marsh zone based upon the increase in organic production from salinity reduction.
SPROD2 Salinity/Production Model
1:40 PM Wed, Jul 09, 2014
Untitled
Page 1
0.00 8100.00 16200.00 24300.00 32400.00
Hours
1:
1:
1:
2:
2:
2:
3:
3:
3:
4:
4:
4:
-0.02
-0.004
0.012
0
15
30
1: I Acres 2: B Acres 3: S Acres 4: Salinity
1 1 1 122
2 23 3 3 3
4
4
44
Annual Land Loss Reduction Percent Calculator
Annual Net Change Calculator
SPROD2 Salinity/Production Model
14.3% reduction in land loss rate
Land Loss Spreadsheet
233 net acres in 20 yrs 1:10 PM Wed, Jul 09, 2014
Untitled
Page 1
0.00 8100.00 16200.00 24300.00 32400.00
Hours
1:
1:
1:
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2:
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4:
19090
19295
19500
0
0
0
0
10
20
1: FWOP 2: FWP 3: ANNUAL LLR PERCENT 4: ANNUAL NET CHANGE
1
1
1
1
2
2
2
2
3
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3
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4
4
4
4
Cameron-Creole Freshwater Introduction Project (CS-49)
Project Area = 22,240 acres 7,659 acres wetland 14,581 acres water
Loss Rate = -0.76%/y
(58.2 acres/y)
Problem: Experiencing increased tidal exchange, saltwater intrusion, and reduced freshwater retention associated with the Calcasieu Ship Channel and the GIWW. Also recently impacted by hurricanes. Goals: The project would restore the function, value, and sustainability to approximately 22,247 acres of marsh and open water. Solution: Construction of ten 48-inch culverts in the bank of the GIWW to establish freshwater flow from the GIWW into the Cameron-Creole marshes. Model: NSED2 (STELLA 10.0.4)
NSED2 Nutrient/Sediment Model
NSED2 Nutrient/Sediment Model
Nutrient Module: calculates the acres of benefit from increase in nutrients.
NSED2 Nutrient/Sediment Model
Sediment Module: calculates the acres of benefit from increase in sediments.
Annual Net Change and Land Loss Reduction Percent Calculators
NSED2 Nutrient/Sediment Model Marsh Fill Calculator
156 net acres in 20 yrs
Conclusions
• Desktop modeling has allowed us to quantify benefits of introducing nutrients, sediments and lowering salinities in a way that allows equitable comparison to all project types.
• By quantifying the benefits of nutrient, sediment and salinity reduction, we are able to provide estimates of cost/benefit to allow decision makers to make more informed decisions in selecting projects for funding.
Questions?
Weeds or Organic Production?