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Allen Thompson, University of Missouri
Claire Baffaut, USDA-ARS, CSWQ Columbia, MO
Sapana Lohani, University of Missouri
SVI: How does it work?
Soil Vulnerability Index for Risk
Classification
Background
SVI system:
• Similar classification to Land Capability Class
• For cultivated land only
o Includes managed hayland, pastureland and known CRP uses
o Original intent for use at field scale
• Locally relevant with measureable difference between Classes
o Actual distinction between Low compared to Moderate, etc.
• Assumes no conservation practice in place
Three Important Driving Factors
Related to Threshold Values
• Statistically tested against output from CEAP APEX simulations
o SSURGO/gSSURGO soil properties using soil map unit components for
NRI points in Ohio and Tennessee River basins
o At least a 75% match between output from APEX classification and soil
properties
o Hydrologic Soil Group (A, B, C, D)
o Soil Erodibility (RUSLE2 K-factor)
o Slope Categories
Risk Categories
• Classified into Four Risk Categories
oLow
oModerate
oModerately High
oHigh
Thresholds for Soil Runoff Risk
• Lower threshold limit: 2 tons/ac sediment loss
(without conservation practices)
o (based on researcher’s experience as acceptable limit)
• Sediment loss < 2 tons/ac
classified as Low
• Results from Highly Erodible Lands (HEL) indicated 90% of HEL points
had sediment loss > 8 tons/ac (based on NRCS technical guides)
• Sediment loss > 8 tons/ac
 classified as High
• Breakpoint for other two classes at mid point (5 tons/ac)
Summary Soil Runoff Risks
Risk Category Sediment loss threshold
Low < 2 tons/ac
Moderate 2 to 5 tons/ac
Moderately High 5 to 8 tons/ac
High > 8 tons/ac
Thresholds for Leaching
• Considered percolation volume (PRK)
• Considered NO3-N in percolation (PRKN)
• Considered in reverse order to runoff results
(i.e. low runoff infers high percolation)
• No Practice scenario generally applied > =1.8 times more
N than crop required
Settled on percolation volume PRK under no
practice scenario. Use of N was too variable.
Thresholds for Leaching (cont.)
• Established High threshold of 200 mm percolation
o Used Hyd group A, slopes ≤ 2% and coarse textured soil
o Verified that 75% of those soils had > 200 mm percolation
o Nearly half of the remaining 25% soils had hay in rotation
• (thus likely reduced leaching rates)
o 200 mm percolation ~ 25% of average annual precipitation for
Upper Mississippi region
Thresholds for Leaching (cont.)
• Established Low threshold of 50 mm percolation
o Used Hyd group D, moderately fine and fine textured soils
(>35% clay in surface layer)
• No restrictions due to slope
o (if flat and low leaching then definitely Low)
o 85% had < 50 mm leaching
o 75% had < 30 mm leaching
• Selected 50mm leaching value
o Represents 1/4th of High threshold as was used for runoff risk
• Breakpoint for other two classes at midpoint (125 mm)
Summary Leaching Risks
Risk Category Percolation Threshold
Low < 50 mm
Moderate 50 to 125 mm
Moderately High 125 to 200 mm
High > 200 mm
Additional Factors
• Used Recursive Partitioning procedure to develop:
o K-factor breaks (soil erodibility, RUSLE2)
o Slope factor breaks
o For leaching, if soil drained, risk class increased by two
categories (no distinction between surface or subsurface)
Slide 12
Soil Runoff Potential
Hydrologic Group Slope K-factor Risk Class
A All All Low
B <4 All Low
B 4 to 6 <0.32 Moderate
B 4 to 6 All Moderately High
B >6 All High
C <2 All Low
C 2 to 6 <0.28 Moderate
C 2 to 6 >0.28 Moderately High
C >6 All High
D <2 <0.28 Low
D <2 >0.28 Moderate
D 2 to 4 All Moderately High
D >4 All High
Slide 13
Hydrologic
Group
Slope K-factor Risk Class
A <=12 all High
A >12 all Moderately High
B <3 <0.24 High
B >=3 & <=12 <0.24 Moderately High
B All other B All other B Moderate
C Moderate
D Low
Soil Leaching Potential
Note: Hyd Group C & D High risk class
if Organic Soils
Sites used for SVI evaluation
Summary
• SVI originally designed for field use
• Cultivated land only
• Assumes no conservation practice in place
• Divided into four risk classes
• Classifications for Soil Runoff and Leaching
Funding provided for this project by
USDA-NRCS and USDA-ARS.

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2 allen thompson -svi how does it work presentation final

  • 1. Allen Thompson, University of Missouri Claire Baffaut, USDA-ARS, CSWQ Columbia, MO Sapana Lohani, University of Missouri SVI: How does it work? Soil Vulnerability Index for Risk Classification
  • 2. Background SVI system: • Similar classification to Land Capability Class • For cultivated land only o Includes managed hayland, pastureland and known CRP uses o Original intent for use at field scale • Locally relevant with measureable difference between Classes o Actual distinction between Low compared to Moderate, etc. • Assumes no conservation practice in place
  • 3. Three Important Driving Factors Related to Threshold Values • Statistically tested against output from CEAP APEX simulations o SSURGO/gSSURGO soil properties using soil map unit components for NRI points in Ohio and Tennessee River basins o At least a 75% match between output from APEX classification and soil properties o Hydrologic Soil Group (A, B, C, D) o Soil Erodibility (RUSLE2 K-factor) o Slope Categories
  • 4. Risk Categories • Classified into Four Risk Categories oLow oModerate oModerately High oHigh
  • 5. Thresholds for Soil Runoff Risk • Lower threshold limit: 2 tons/ac sediment loss (without conservation practices) o (based on researcher’s experience as acceptable limit) • Sediment loss < 2 tons/ac classified as Low • Results from Highly Erodible Lands (HEL) indicated 90% of HEL points had sediment loss > 8 tons/ac (based on NRCS technical guides) • Sediment loss > 8 tons/ac  classified as High • Breakpoint for other two classes at mid point (5 tons/ac)
  • 6. Summary Soil Runoff Risks Risk Category Sediment loss threshold Low < 2 tons/ac Moderate 2 to 5 tons/ac Moderately High 5 to 8 tons/ac High > 8 tons/ac
  • 7. Thresholds for Leaching • Considered percolation volume (PRK) • Considered NO3-N in percolation (PRKN) • Considered in reverse order to runoff results (i.e. low runoff infers high percolation) • No Practice scenario generally applied > =1.8 times more N than crop required Settled on percolation volume PRK under no practice scenario. Use of N was too variable.
  • 8. Thresholds for Leaching (cont.) • Established High threshold of 200 mm percolation o Used Hyd group A, slopes ≤ 2% and coarse textured soil o Verified that 75% of those soils had > 200 mm percolation o Nearly half of the remaining 25% soils had hay in rotation • (thus likely reduced leaching rates) o 200 mm percolation ~ 25% of average annual precipitation for Upper Mississippi region
  • 9. Thresholds for Leaching (cont.) • Established Low threshold of 50 mm percolation o Used Hyd group D, moderately fine and fine textured soils (>35% clay in surface layer) • No restrictions due to slope o (if flat and low leaching then definitely Low) o 85% had < 50 mm leaching o 75% had < 30 mm leaching • Selected 50mm leaching value o Represents 1/4th of High threshold as was used for runoff risk • Breakpoint for other two classes at midpoint (125 mm)
  • 10. Summary Leaching Risks Risk Category Percolation Threshold Low < 50 mm Moderate 50 to 125 mm Moderately High 125 to 200 mm High > 200 mm
  • 11. Additional Factors • Used Recursive Partitioning procedure to develop: o K-factor breaks (soil erodibility, RUSLE2) o Slope factor breaks o For leaching, if soil drained, risk class increased by two categories (no distinction between surface or subsurface)
  • 12. Slide 12 Soil Runoff Potential Hydrologic Group Slope K-factor Risk Class A All All Low B <4 All Low B 4 to 6 <0.32 Moderate B 4 to 6 All Moderately High B >6 All High C <2 All Low C 2 to 6 <0.28 Moderate C 2 to 6 >0.28 Moderately High C >6 All High D <2 <0.28 Low D <2 >0.28 Moderate D 2 to 4 All Moderately High D >4 All High
  • 13. Slide 13 Hydrologic Group Slope K-factor Risk Class A <=12 all High A >12 all Moderately High B <3 <0.24 High B >=3 & <=12 <0.24 Moderately High B All other B All other B Moderate C Moderate D Low Soil Leaching Potential Note: Hyd Group C & D High risk class if Organic Soils
  • 14. Sites used for SVI evaluation
  • 15. Summary • SVI originally designed for field use • Cultivated land only • Assumes no conservation practice in place • Divided into four risk classes • Classifications for Soil Runoff and Leaching
  • 16. Funding provided for this project by USDA-NRCS and USDA-ARS.

Notes de l'éditeur

  1. Basically Lee’s original slide.
  2. Added color to correspond to SVI cultivated cropland classes as mapped in FY2015 web services – basically Lee’s original slide