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1
Using Geospatial Tools to Identify
Critical Nutrient Source Areas and
Agricultural BMP Implementation
Priorities
Presentation by: Louise Heyming
Grand River Conservation Authority
Cambridge, Ontario, Canada
2
Project Objectives
1) Demonstrate how a high resolution digital
elevation model (DEM) and advanced GIS
techniques can be used to determine nutrient
source areas
2) Demonstrate how the identified nutrient
source areas can be used to target agricultural
best management practices (BMPs)
3
The Grand River Watershed
4
80 year history of water
management planning
Shared responsibility
Successful collaboration
Building on existing data,
knowledge and
accomplishments
Finding practical ‘best
value’ solutions
A long history of water management
2014
5
Water Management Plan Goals
Ensure sustainable water supplies
for communities, economies
and ecosystems
Improve water quality to improve
river health and reduce the river’s
impact on Lake Erie
Reduce flood damage potential
Increase resiliency
to deal with climate change
6
Phosphorus Loads
Priority watersheds were
identified through the
Water Management Plan
Highest P
concentrations occur
during spring from non-
point sources
Point sources dominate
in summer
(Adapted from GRCA 2006)
7
Identifying Nutrient Source Areas
Terrain Analysis Approach
Gully Erosion
RUSLE-FAC Approach
Sheet Erosion
Identify Priority Areas Identify Priority Areas
High Priority Areas for BMPs
8
Pilot Study Area – Firella Creek
The Upper Nith River Sub-
basin was identified as a
significant contributor of
nutrients and sediment in
the Water Management
Plan
 Firella Creek study
area covers
approximately 32
km2 and is located
within the Upper Nith
Sub-basin
Lake Erie
9
DEM Development
Stereo Project Creation:
Aerial Data
 Scans
 Camera Files
 Orientation Files
 Control Files
10
DEM Development
Source: www.planar3d.com
Large Scale 3D
Vector Hydrology
Creation:
11
DEM Development
Pixel-Auto Correlation (PAC) Point Collection:
12
Final Firella Creek DEM
13
Terrain Analysis Approach
Digital Elevation Model
Slope Raster
Stream Power Index Raster
Flow Accumulation Raster
Stream Power Index
measures the erosive power
of flowing water, identifies
areas of potential gully
erosion
Approach adapted from (Galzki, Birr and Mulla 2011)
14
Terrain Analysis Approach
Stream Power Index (SPI)
High SPI values
represent the likely
overland flow paths
during a storm event
– the potential gullies
15
Stream Power Index (SPI) Signatures
Terrain Analysis Approach
SPI Value Percentile
-0.540 75.00%
-0.079 80.00%
0.460 85.00%
1.135 90.00%
2.214 95.00%
A path of high SPI
values that flow into
observed surface
hydrology
16
Terrain Analysis Approach
Field Verification
SPI Signatures - 95th Percentile
Correctly
Identified
Incorrect Identification
False Positive Thick Vegetation Other
9/10 (90%) 0/10 (0%) 1/10 (10%) 0/10 (0%)
17
Terrain Analysis Approach
Stream Power Index
Signatures
Stream Power Index
Signature Catchment Areas
18
Priority Areas using Terrain Analysis
19
RUSLE - FAC Approach
A = R * K * L * S * C * P
Average annual soil loss – Potential sheet erosion
(tonnes/hectare/year)
RUSLE–FAC = Revised Universal Soil Loss Equation – For Application in Canada
20
Priority Areas using RUSLE - FAC
21
Priority Nutrient Source Areas
Priority Nutrient Source Areas - High Values
SPI – High Catchments
RUSLE-FAC -High Values
22
Current Extension Program Approach
Technical assistance and
financial incentives to all
farmers
Work with those farmers who
come forward (i.e. they know
they have an erosion issue)
Financial incentives are
offered for both structures
and conservation practices
All erosion control projects
are offered the same incentive
structure
Photo: C. Heibert
23
Mapping Objectives
Identify most vulnerable
areas
Apply BMPs best suited to
issue (gully and/or sheet
erosion)
Target outreach and
financial incentives
(location, incentive level)
Photo: A. Loeffler
24
At the Farm Scale
25
At the Farm Scale
26
At the Farm Scale
27
Early Results
Increase in requests
for technical
assistance to design
erosion control system
Requests for mapping
outside our pilot study
area
Photo: A. Loeffler
28
Future Applications
Internal CA use:
 Identify priority subwatersheds (best value
solutions)
 Connect issues to BMPs (structures vs
cropping practices)
 Identify potential water quality monitoring
sites.
Communication tool:
 Engage landowners to raise awareness.
Program delivery level:
 Tailor financial incentives to improve
chances of target farms participating.
Erosion control structure design
 DEM will help facilitate design work
Photo: L Heyming
29
Thank you
Ontario Ministry of the Environment & Climate Change
Grand River Conservation Authority
Ontario Ministry of Agriculture, Food & Rural Affairs
Regional Municipality of Waterloo
Agriculture & Agri-Food Canada
Environment Canada
This Project has received funding support from the Government of Ontario. Such support does not indicate endorsement by the Government of Ontario of the contents of this material.
30
References
Galzki, J. C., et al. "Identifying critical agricultural areas with three-meter LiDAR elevation data
for precision conservation." Journal of Soil and Water Conservation 66.6 (2011): 423-430.

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Using Novel Geospatial Tools and Approaches for Identifying Critical Nutrient Source - heyming

  • 1. 1 Using Geospatial Tools to Identify Critical Nutrient Source Areas and Agricultural BMP Implementation Priorities Presentation by: Louise Heyming Grand River Conservation Authority Cambridge, Ontario, Canada
  • 2. 2 Project Objectives 1) Demonstrate how a high resolution digital elevation model (DEM) and advanced GIS techniques can be used to determine nutrient source areas 2) Demonstrate how the identified nutrient source areas can be used to target agricultural best management practices (BMPs)
  • 3. 3 The Grand River Watershed
  • 4. 4 80 year history of water management planning Shared responsibility Successful collaboration Building on existing data, knowledge and accomplishments Finding practical ‘best value’ solutions A long history of water management 2014
  • 5. 5 Water Management Plan Goals Ensure sustainable water supplies for communities, economies and ecosystems Improve water quality to improve river health and reduce the river’s impact on Lake Erie Reduce flood damage potential Increase resiliency to deal with climate change
  • 6. 6 Phosphorus Loads Priority watersheds were identified through the Water Management Plan Highest P concentrations occur during spring from non- point sources Point sources dominate in summer (Adapted from GRCA 2006)
  • 7. 7 Identifying Nutrient Source Areas Terrain Analysis Approach Gully Erosion RUSLE-FAC Approach Sheet Erosion Identify Priority Areas Identify Priority Areas High Priority Areas for BMPs
  • 8. 8 Pilot Study Area – Firella Creek The Upper Nith River Sub- basin was identified as a significant contributor of nutrients and sediment in the Water Management Plan  Firella Creek study area covers approximately 32 km2 and is located within the Upper Nith Sub-basin Lake Erie
  • 9. 9 DEM Development Stereo Project Creation: Aerial Data  Scans  Camera Files  Orientation Files  Control Files
  • 10. 10 DEM Development Source: www.planar3d.com Large Scale 3D Vector Hydrology Creation:
  • 13. 13 Terrain Analysis Approach Digital Elevation Model Slope Raster Stream Power Index Raster Flow Accumulation Raster Stream Power Index measures the erosive power of flowing water, identifies areas of potential gully erosion Approach adapted from (Galzki, Birr and Mulla 2011)
  • 14. 14 Terrain Analysis Approach Stream Power Index (SPI) High SPI values represent the likely overland flow paths during a storm event – the potential gullies
  • 15. 15 Stream Power Index (SPI) Signatures Terrain Analysis Approach SPI Value Percentile -0.540 75.00% -0.079 80.00% 0.460 85.00% 1.135 90.00% 2.214 95.00% A path of high SPI values that flow into observed surface hydrology
  • 16. 16 Terrain Analysis Approach Field Verification SPI Signatures - 95th Percentile Correctly Identified Incorrect Identification False Positive Thick Vegetation Other 9/10 (90%) 0/10 (0%) 1/10 (10%) 0/10 (0%)
  • 17. 17 Terrain Analysis Approach Stream Power Index Signatures Stream Power Index Signature Catchment Areas
  • 18. 18 Priority Areas using Terrain Analysis
  • 19. 19 RUSLE - FAC Approach A = R * K * L * S * C * P Average annual soil loss – Potential sheet erosion (tonnes/hectare/year) RUSLE–FAC = Revised Universal Soil Loss Equation – For Application in Canada
  • 20. 20 Priority Areas using RUSLE - FAC
  • 21. 21 Priority Nutrient Source Areas Priority Nutrient Source Areas - High Values SPI – High Catchments RUSLE-FAC -High Values
  • 22. 22 Current Extension Program Approach Technical assistance and financial incentives to all farmers Work with those farmers who come forward (i.e. they know they have an erosion issue) Financial incentives are offered for both structures and conservation practices All erosion control projects are offered the same incentive structure Photo: C. Heibert
  • 23. 23 Mapping Objectives Identify most vulnerable areas Apply BMPs best suited to issue (gully and/or sheet erosion) Target outreach and financial incentives (location, incentive level) Photo: A. Loeffler
  • 24. 24 At the Farm Scale
  • 25. 25 At the Farm Scale
  • 26. 26 At the Farm Scale
  • 27. 27 Early Results Increase in requests for technical assistance to design erosion control system Requests for mapping outside our pilot study area Photo: A. Loeffler
  • 28. 28 Future Applications Internal CA use:  Identify priority subwatersheds (best value solutions)  Connect issues to BMPs (structures vs cropping practices)  Identify potential water quality monitoring sites. Communication tool:  Engage landowners to raise awareness. Program delivery level:  Tailor financial incentives to improve chances of target farms participating. Erosion control structure design  DEM will help facilitate design work Photo: L Heyming
  • 29. 29 Thank you Ontario Ministry of the Environment & Climate Change Grand River Conservation Authority Ontario Ministry of Agriculture, Food & Rural Affairs Regional Municipality of Waterloo Agriculture & Agri-Food Canada Environment Canada This Project has received funding support from the Government of Ontario. Such support does not indicate endorsement by the Government of Ontario of the contents of this material.
  • 30. 30 References Galzki, J. C., et al. "Identifying critical agricultural areas with three-meter LiDAR elevation data for precision conservation." Journal of Soil and Water Conservation 66.6 (2011): 423-430.

Editor's Notes

  1. The Grand River Watershed is the largest Canadian watershed flowing into Lake Erie. From the headwaters to the lake is appoximately 300 kms or 186 miles. The Grand River watershed is home to nearly 1million residents. 80% of the population live in a few urban centres. 70% of the watershed is in agricultural production. Production here is a dominated by variations of a corn, bean, cereals with some forage and specialty crops. The watershed is also home to many livestock operations.
  2. digitizing 3D vector hydrology across the watershed. Drainage features were digitized as polygon and line features. Each vertex has an XYZ value.
  3. The result is a 1m cell size DEM with hydrology enforced.
  4. SPI = (Flow Accumulation) x (Slope)
  5. Having identified the areas at greatest risk for gulley erosion, we wanted to further understand the average annual soil loss potential from sheet erosion. The RUSLE FAC approach was used to estimate Potential long term average annual soil loss in (tonnes per hectare per year) This was done using best available data. Where possible we incorporated RUSLE2 values. (for K and R)
  6. .