Tuesday Plenary Panel - Tomer
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Transcript of Tuesday Plenary Panel - Tomer
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 EnvironmentAmes Iowa
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.
• gSSURGO 10m rasters• MUAggAtt• VALU1• Horizon• Texture• Parent Material
Soils Data
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FBndID Acres isAG GenLU CropRotatn CropSumry CCCount MixCountF070801050202_10 105.9 1 Corn/Soybeans BCBCBC C3B3 0:6 0:6F070801050202_8 109.0 1 C/S with Continuous Corn BCBCCC C4B2 2:6 2:6F070801050202_50 94.8 1 Continuous Corn CCCCCC C6 5:6 0:6F070801050202_62 41.9 1 Pasture PPPPPP P6 0:6 6:6F070801050202_282 35.5 1 Conservation Rotation PPPCBC C2B1P3 0:6 3:6
maj07 pct07 maj08 pct08 maj09 pct09 maj10 pct10 maj11 pct11 maj12 pct12… 5 94 1 93 5 92 1 94 5 93 1 99… 5 74 1 82 5 74 1 91 1 82 1 91… 1 84 1 93 1 84 1 96 1 97 1 99… 181 68 181 66 181 45 181 51 171 43 171 74… 181 74 181 32 181 46 1 76 5 80 1 87
Land Use Data• 2007-2012 NASS CDL• Sequence of major crops• Individual-field dominant crop• Dominant crop percent of field• Rule-based crop rotation• Continuous corn count
4
5
Terrain Data
Flow Accumulation
Slope
• LiDAR-derived digital elevation model• 3m horizontal resolution• Hydrologically enforced
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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.
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Concept for Agricultural Conservation Planning Framework (ACPF):A CONSERVATION PYRAMID FOR AGRICULTURAL WATERSHEDS
8(Tomer et al., 2013)
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 ZONEPlace/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
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Yes No
H A B C
M B C
L C
Close to stream?
Slop
e st
eepn
ess
Yes No
H CZ MSB SSG
M MSB MSB SSG
L DRV DRV SBS
Shallow water table?
Runo
ff de
liver
y
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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Nutrient removal wetlandsTwo-stage drainage ditch
Denitrifying bioreactors
Practices for Reducing Nitrate Loads from Tile Drainage
Controlled drainage
Controlled Drainage where slopes are least
Photo by IDALS-DSC
Nutrient interception wetlands
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Grassed waterwaysContour filter strips
Conservation cover
Practices to Manage Runoff & Water Quality
Sediment detention basins
Water/Sediment Control Basins to detain runoff/sediment
Grassed Waterways to slow concentrated flows
Potential Riparian Functions Depend on Landscape Attributes and May Be Achieved at Varying Buffer Widths
Schultz et al., 2009
Channel Network
Contributing Area > 1 HA
0 0.40.2 Miles
1. Local Runoff
Riparian Analysis
N
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
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
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
Across watershed: Nutrient/manure management, Cover Crops, No-tillage or strip tillage
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?
Slop
e st
eepn
ess
Yes No
H CZ MSB SSG
M MSB MSB SSG
L DRV DRV SBS
Shallow water table?
Runo
ff de
liver
y
Design Types for Riparian Buffers:CZ Critical Zone -sensitive sitesMSB Multi-Species BufferSSG Stiff-Stemmed GrassesDRV Deep-Rooted VegetationSBS 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 ZONEPlace/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 technologiesDATA 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 BasinsFarm Ponds
APPLICATION: Scenario Development/ stakeholder feedback/ implement/ monitor/ adapt 22
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 ScenarioLime CreekBeaver Creek
0 21 Kilometers 23
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
Crop
land
tak
en f
rom
pro
ducti
on b
y sc
enar
io
(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
Crop
land
tak
en f
rom
pro
ducti
on b
y sc
enar
io
(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
Crop
land
take
n fr
om p
rodu
ction
by
scen
ario
(h
a)
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
Crop
land
tak
en f
rom
pro
ducti
on b
y sc
enar
io
(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
Area
of c
ropl
and
take
n ou
t of p
rodu
ction
und
er s
cena
rio (h
a)
WetlandsWetlands
Covercrops
Covercrops
Beaver Creek Lime Creek
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)
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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Thanks to:Sarah Porter, USDA-ARSDavid James, USDA-ARS
Kathy Boomer, The Nature ConservancyEileen McLellan, Environmental Defense Fund
Support: NRCS Conservation Innovation Grantawarded to the Environmental Defense Fund
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