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Tuesday Plenary Panel - Tomer
1. Overview of the
Agricultural Conservation Planning Framework-
Database, Concept, and GIS Toolbox
for Watershed Planning
Mark Tomer
USDA-ARS
National Laboratory for Agriculture and the Environment
Ames Iowa
2. Some questions
• How many HUC-12 watersheds are there in the Ohio and
upper Mississippi river basins?
• 11,198
• How many farm fields are there in Iowa?
• 708,884
• How do we improve water quality across all Midwestern
landscapes?
• We certainly need to prioritize among fields and watersheds,
but then we must address them collaboratively, one
watershed and one field at a time.
• How to be consistent across the Midwest in this effort?
• With consistent and well detailed data that are analyzed and
presented in a way to help local planners and landowners
make good decisions for resource improvement.
3. • gSSURGO 10m rasters
• MUAggAtt
• VALU1
• Horizon
• Texture
• Parent Material
Soils Data
3
7. Any broad-based approach to watershed
planning must recognize:
• That each watershed is unique;
• That each farm is unique and that farmers must each
be included as equal partners in planning process;
• That nutrient reduction goals can only be met by a
mix of practices placed within fields and below field
edges; and,
• That the need to protect and improve the health of
our soil resource is paramount to maximize crop
production and to protect water quality.
7
8. Concept for Agricultural Conservation Planning Framework (ACPF):
A CONSERVATION PYRAMID FOR AGRICULTURAL WATERSHEDS
8(Tomer et al., 2013)
9. AVOID and CONTROL : Improve soil health within cropped fields to avoid and control pollutant losses by-
Protecting soils from erosion with zero or minimum tillage;
Limiting excess nutrients through rates and timing of fertilizer and manure applications;
Building soil organic matter and rejuvenating compacted soils with intensified crop rotations
IN FIELDS:
Place water control /
filter practices
BELOW FIELDS
Place water
detention / nutrient
removal practices
RIPARIAN ZONE
Place/design
practices for
ecosystem function
and nutrient removal
Agricultural Conservation Planning Framework to improve water quality in agricultural watersheds
CONTROL, TRAP,
and/or TREAT
TILE DRAINAGE SURFACE RUNOFF
9
Yes No
H A B C
M B C
L C
Close to stream?
Slopesteepness
Yes No
H CZ MSB SSG
M MSB MSB SSG
L DRV DRV SBS
Shallow water table?
Runoffdelivery
Runoff Risk Assessment:
Prioritize fields where
multiple erosion control
practices are most needed
Riparian Assessment:
Identify riparian function
by stream reach
Assessments for prioritization
and design of practices
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10. Nutrient removal wetlandsTwo-stage drainage ditch
Denitrifying bioreactors
Practices for Reducing Nitrate Loads from Tile Drainage
Controlled drainage
18. Channel Network
Contributing Area > 1 HA
Shallow Water Table Zone
0 0.40.2 Miles
2. Shallow Water Table
1. Local Runoff
Riparian Analysis
N
19. Channel Network
Contributing Area > 1 HA
Shallow Water Table Zone
Riparian Analysis Polygon
0 0.40.2 Miles
2. Shallow Water Table
3. Riparian Analysis Polygons
1. Local Runoff
Riparian Analysis
N
20. Channel Network
Contributing Area > 1 HA
Shallow Water Table Zone
Riparian Analysis Polygon
0 0.40.2 Miles
2. Shallow Water Table
3. Riparian Analysis Polygons
Critical Zone
Multi Species Buffer
Stiff Stemmed Grasses
Deep Rooted Vegetation
Stream Bank Stabilization
Riparian Function
4. Riparian Function
1. Local Runoff
Riparian Analysis
N
22. AVOID and CONTROL : Improve soil health within cropped fields to avoid and control pollutant losses by-
Protecting soils from erosion with zero or minimum tillage;
Limiting excess nutrients through rates and timing of fertilizer and manure applications;
Building soil organic matter and rejuvenating compacted soils with intensified crop rotations
Controlled Drainage
where slopes are least
Bioreactors
or small wetlands constructed
above field-tile outlets
Re-Saturated Buffers
Yes No
H A B C
M B C
L C
Close to stream?
Slopesteepness
Yes No
H CZ MSB SSG
M MSB MSB SSG
L DRV DRV SBS
Shallow water table?
Runoffdelivery
Design Types for Riparian Buffers:
CZ Critical Zone -sensitive sites
MSB Multi-Species Buffer
SSG Stiff-Stemmed Grasses
DRV Deep-Rooted Vegetation
SBS Stream Bank Stability
Grassed Waterways where
gullies may form
Contour Filter Strips,
Terraces, Conservation Cover
where slopes are steep
Ditch design: Two-Stage Ditches;
novel practices for detention /
diversion of tile drainage
Runoff Risk Assessment:
Prioritize fields where
multiple erosion control
practices are most needed
Riparian Assessment:
Identify riparian function
by stream reach
Surface Intake Filters or
Restored Wetlands where
depressions occur
IN FIELDS:
Place water control /
filter practices
BELOW FIELDS
Place water
detention / nutrient
removal practices
RIPARIAN ZONE
Place/design
practices for
ecosystem function
and nutrient removal
Perennial crops, & novel
practices to intercept flows
where soils stay wet
Downstream/ In-stream: River restoration
(e.g., pool-riffle structures, re-meandering,
oxbow rehabilitation)
Process for conservation planning to improve water quality in agricultural watersheds using precision technologies
DATA REQUIRED: LiDAR-based digital elevation model, Soil survey, Field boundaries, Land use
CONTROL, TRAP,
and/or TREAT
TILE DRAINAGE SURFACE RUNOFF
Assessments for prioritization
and design of practices
Water detention using impoundments of varying designs
Nutrient Removal
Wetlands
Sediment Detention Basins
Farm Ponds
APPLICATION: Scenario Development/
stakeholder feedback/ implement/ monitor/ adapt 22
23. Nutrient Removal Wetlands
Wetland Pool Area
Wetland Buffer
Drainage Areas
Resaturated Buffers
Resat. Buffer Opportunities
Cover Crops
Cover Crops Fields
Stream Network
Stream Network
Wetland Pool Area
Wetland Buffer
Drainage Areas
Cover Crops
Cover Crop Fields
Controlled Drainage
Drainage Mgmt Opportunities
Stream Network
Stream Network
Nutrient Removal Wetlands
Conservation Planning Scenario
Lime CreekBeaver Creek
0 21 Kilometers 23
24. 0
50
100
150
200
250
300
350
400
0.0 0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8
Croplandtakenfromproductionbyscenario
(ha)
Average nutrient removal efficiency needed among all
scenario practices to achieve 40% reduction for watershed
Included
Excluded
0
50
100
150
200
250
300
350
400
0.0 0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8
Croplandtakenfromproductionbyscenario
(ha)
Average nutrient removal efficiency needed among all
scenario practices to achieve 40% reduction for watershed
66-100%
0-33%
0
50
100
150
200
250
300
0.0 0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8
Croplandtakenfromproductionbyscenario
(ha)
Average nutrient removal efficiency needed among all
scenario practices to achieve 40% reduction for watershed
Included
Excluded
0
50
100
150
200
250
300
0.0 0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8
Croplandtakenfromproductionbyscenario
(ha)
Average nutrient removal efficiency needed among all
scenario practices to achieve 40% reduction for watershed
66-100%
0-33%
Average nutrient removal efficiency required among all practices in scenario to achieve 40% reduction
Areaofcroplandtakenoutofproductionunderscenario(ha)
WetlandsWetlands
Cover
crops
Cover
crops
Beaver Creek Lime Creek
25. Types of practices sited by the ACPF
• Drainage water management
• Surface intake treatments (e.g., blind inlets)
• Grassed waterways
• Contour filter strips/terraces
• Water/sediment control basins
• Nutrient removal wetlands
• Riparian buffers – functional opportunities
• To be added: saturated buffers, bioreactors, two stage
ditches
• However, users are encouraged to identify unique features
that present conservation challenges and/or opportunities
(e.g. springs, gravel pits, sinkholes, depressions)
26. ACPF Summary: see http://northcentralwater.org/acpf/
• Aim is to develop a customized planning resource for HUC12
watersheds. Input data are widely available in the Midwest.
• Addresses tile drainage and runoff pathways, while stressing the
importance of soil health for conservation success.
• Suggests possible beneficial locations for different types of
practices placed in fields, at field edges, and in riparian zones.
Well known and new types of practices can be included.
• Planning alternatives can be developed and ranked without
additional input data.
• No recommendations are made. Results provide a planning
resource, not a plan. Actual watershed planning is inherently a
local consultative process involving landowners.
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27. Thanks to:
Sarah Porter, USDA-ARS
David James, USDA-ARS
Kathy Boomer, The Nature Conservancy
Eileen McLellan, Environmental Defense Fund
Support: NRCS Conservation Innovation Grant
awarded to the Environmental Defense Fund
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