Theresa M. Possley Nelson, PE Aaron S. Ruesch Michelle Hu - - PowerPoint PPT Presentation

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Theresa M. Possley Nelson, PE Aaron S. Ruesch Michelle Hu - - PowerPoint PPT Presentation

Theresa M. Possley Nelson, PE Aaron S. Ruesch Michelle Hu Wisconsin Department of Natural Resources SWAT Conference Purdue University October 16, 2015 Water quality in Wisconsin EVAAL Tillage estimations TMDL = Total Maximum


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Theresa M. Possley Nelson, PE Aaron S. Ruesch Michelle Hu

Wisconsin Department of Natural Resources

SWAT Conference Purdue University October 16, 2015

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 Water quality in Wisconsin  EVAAL  Tillage estimations

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 TMDL = Total Maximum Daily Load  Established under the Clean Water Act  The maximum amount of a pollutant that a

waterbody can receive and still safely meet water quality standards

Impaired Waters

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Does not meet water quality standards

Current Pollutant Load

Total Maximum Daily Load

Meets water quality standards

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Total Phosphorus (lbs/acre/year)

0.0-0.3 1.1-1.6 0.8-1.1 0.6-0.8 0.3-0.6

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  • 23 square miles
  • 187 farms
  • 1,129 fields

?

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LiDAR Crop Data Soils

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 Erosion Vulnerability Assessment for

Agricultural Lands

 GIS-based model  Vulnerability to erosion and nutrient export  Deprioritizes internally draining areas

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 Sheet and rill erosion

𝐵 = 𝑆𝐿(𝑀𝑇)𝐷𝑄

Constant tant Constant tant

𝐵 = 𝐿(𝑀𝑇)𝐷

SS SSUR URGO GO soil ils DEM Cr Cropla land nd data la layer

  • Rainfall erosivity
  • Soil erodibility
  • Slope/Slope-Length
  • Cover factor
  • Practice Factor
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Eleva vatio tion n (feet)

1000 650 5 5 5 feet

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http://nassgeodata.gmu.edu/CropScape/

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Corn Soybean Corn Corn Soybean C-C-S-C-C, C-S-C-S-C, S-C-C-S-C, C-C-C-C-S, S-S-S-S-C = Cash

sh Grain in Rotat

  • tation

ion

2012 12 2011 11 2010 10 2009 09 2008 08

RU RUSLE LE2 2 -> Ro Rotat ational ional C F C Fac actor tor

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10 meter resolution http://datagateway.nrcs.usda.gov/

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 Potential for gully erosion

SPI = 𝑔(slope, catchment area)

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 Areas that do not contribute to surface waters

Depression (sink) on the landscape

Vs VR

Stream

VR

R > V

VS

𝑾𝒕 ≥ 𝑾𝒔, 𝑱𝒐𝒖𝒇𝒔𝒐𝒃𝒎𝒎𝒛 𝒆𝒔𝒃𝒋𝒐𝒇𝒆 𝑾𝒕 < 𝑾𝒔, 𝑶𝒑𝒖 𝒋𝒐𝒖𝒇𝒔𝒐𝒃𝒎𝒎𝒛 𝒆𝒔𝒃𝒋𝒐𝒇𝒆

10-yr, 24-hr

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 Areas that do not contribute to surface waters

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Low Medium High

USLE SPI NC Areas Erosion Vulnerability Prioritization

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 Documents  Tutorial Data  ArcToolbox http://dnr.wi.gov/topic/nonpoint/evaal.html

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 Counties, consultants, NGOs for watershed

planning

  • > 15 counties

 9 key element & TMDL implementation plans  Land and water resource management plans  Lake management planning  Adaptive management/water quality trading

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 We can’t model what we don’t know

  • Tillage
  • Manure application
  • Soil P
  • BMPs

 Erosion must be driving factor  Does not account for delivery factors or tile

drainage

 Cannot “target”, rather “prioritize”

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 Currently assuming high or low C factor  Use Landsat satellite imagery  Calculate Normalized Difference Tillage Index

(NDTI) values and correlate to residue cover and associated tillage type

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 Landsat 7 & 8  Normalized Difference Tillage Index  NDTI = (band5 – band7) / (band5 + band7) “Remote Sensing Of Crop Residue Cover Using Multi-temporal Landsat Imagery”

  • B. Zheng - 2012
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 NDTI is positively correlated with crop residue

cover and green vegetation

Brian Gelder, Iowa State

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“Remote Sensing Of Crop Residue Cover Using Multi-temporal Landsat Imagery”

  • B. Zheng - 2012

Intensive sive Tillage No T Till

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 Obtain imagery throughout spring planting

season

 Preprocessing: remove obscured pixels  Calcualte minNDTI

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 Link known tillage practices and crop residue

percentages to spectral signatures

 Annual data collection  Includes

  • Crop type
  • Tillage type
  • Percent residue
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y = 0.1118x + 0.0212 R² = 0.8648

0.02 0.04 0.06 0.08 0.1 0.12 0.14 0.16 0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8 0.9 1

minNDTI nNDTI % % Crop

  • p Resi

sidue ue Cover er

Marathon County minNDTI 2012 Linear (Marathon County minNDTI 2012)

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Moldboard (0-15%) (16-75%) No Till (76-100%) 0.0001 – 0.0380 0.0380 – 0.0771 0.0771 – 0.2999 2012 minNDTI Tillage Type (%CRC)

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High C factor NDTI C factor

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Always Prioritized Never Prioritized NDTI Prioritized High C Prioritized

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 Landsat

  • Data gaps
  • Clouds
  • Timing/availability
  • Soil moisture impacts

 Validation data  Computing time/power

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 EVAAL uses readily available data to assess

erosion vulnerability; can be used to prioritize watershed efforts

 NDTI is positively correlated to crop residue

coverage; can be used to infer tillage

 EVAAL results can be improved using satellite

derived tillage information

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Theresa M. Possley Nelson, PE (608) 266-7037 Theresa.Nelson@wisconsin.gov dnrwaterqualitymodeling@wisconsin.gov