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Soil carbon in the Red River Valley: towards
precision quantification and modeling
JOSE PABLO CASTRO, CALEY GASCH, PAULO FLORES,
PETER ODUOR, ERIK HANSON, MINGAO YUAN
NORTH DAKOTA STATE UNIVERSITY
CO2 CH4
CaCO3
CO
Short-mid
term
Long
term
Goal
To quantify in a precise and accurate way
the soil carbon stocks of nine farms located
in the Red River Valley using PrecisionAg
tools, GIS, remote sensing and deep
learning methods.
Electromagnetic
induction
Multispectral
photogrammetry
Annual
yield
datasets
Sampling
design
Sampling
design
Soil sampling
40 samples per farm
6 depths
2 repetitions
0-4 inches
4-8 inches
8-12 inches
12-24 inches
24-36 inches
36-48 inches
40 samples* 6 depths* 2 repetitions* 9 farms = 4320 samples
Yield sampling
Lab Analysis
Independent variables (X)
X1 = Band 1 Blue UAV (Average of four flights)
X2 = Band 2 Green UAV (Average of four flights)
X3 = Band 3 Red UAV (Average of four flights)
X4 = Band 4 NIR1 (Average of four flights)
X5 = Band 5 NIR2 (Average of four flights)
X6 = Band 6 NIR2 (Average of two flights)
X7 = Enhanced Natural Difference Vegetation Index UAV (Average of four flights)
X8 = Green Natural Difference Vegetation Index UAV (Average of four flights)
X9 = GSAVI Green Salinity Vegetation Index UAV (Average of four flights)
X10 = Natural Difference Reflectance Enhanced UAV (Average of four flights)
X11 = Natural Difference Vegetation Index UAV (Average of four flights)
X12 = Optimized Salinity Vegetation Index UAV (Average of two flights)
X13 = Salinity and Vegetation Index UAV (Average of four flights)
X14 = VSEC_D (Apparent electrical conductivity (0-30 cm depth)
X15 = VSEC_S (Apparent electrical conductivity (0-90 cm depth)
X16 = DEM RTK (Digital elevation model)
X17 = Relative yield 1
X18 = Relative yield 2
X19 = Depth
X20 = Longitude
X21 = Latitude
Dependent variables (Y)
• Y1 = Total carbon in soil
• Y2 = Inorganic carbon in soil
• Y3 = Organic carbon in soil
• Y4 = Bulk density
Database
Thiessen polygons Kriging
Target Training Size Test Size Best model AdjR2 R2 RMSE
Samples
for
training
Y1 = TC 0.8 0.2 GradientBoostingRegressor 0.38 0.5 0.48 32
Y1 = TC 0.6 0.4 HistGradientBoostingRegressor 0.4 0.5 0.5
24
Y1 = TC 0.4 0.6 HistGradientBoostingRegressor 0.37 0.4 0.52
16
Y1 = TC 0.2 0.8 RandomForestRegressor 0.15 0.2 0.59 8
Y1 = TC 0.01 0.99 LGBMRegressor -0.03 0 0.67 1
Y2 = IC 0.8 0.2 GradientBoostingRegressor 0.74 0.8 0.46 32
Y2 = IC 0.6 0.4 HistGradientBoostingRegressor 0.74 0.8 0.47
24
Y2 = IC 0.4 0.6 GradientBoostingRegressor 0.71 0.7 0.52 16
Y2 = IC 0.2 0.8 HistGradientBoostingRegressor 0.66 0.7 0.56
8
Y2 = IC 0.01 0.99 XGBRegressor 0.54 0.6 0.66 1
Y3 = OC 0.8 0.2 GradientBoostingRegressor 0.86 0.9 0.31 32
Y3 = OC 0.6 0.4 GradientBoostingRegressor 0.88 0.9 0.3 24
Y3 = OC 0.4 0.6 LGBMRegressor 0.88 0.9 0.29 16
Y3 = OC 0.2 0.8 HistGradientBoostingRegressor 0.83 0.8 0.35
8
Y3 = OC 0.01 0.99 AdaBoostRegressor 0.7 0.7 0.48 1
Conclusion
Soil organic and inorganic carbon stocks can be predicted using precision ag tools, GIS, remote
sensing, and deep learning models with determination’s coefficients around 0.8. Traditional
methods as Thiessen polygons or Kriging does not achieve more than 0.2-0.4.
An accuracy and precise quantification of carbon in the soil allows farmers to negotiate better
contracts for carbon sequestration and at the same time allows to the companies to have a
better control of where they are investing the money.
It research project is at 40% development. It is expected to be 100% complete in the next three
years.
Acknowledgment
This research is based upon work supported by the U.S. Department of Agriculture, Agricultural
Research Service, under agreement No. 58-6064-8-023.
Thanks to NDSU research specialist Joel Bell and undergraduate student Mike McKenna for their
hard work in the field of this project.
References
Lin Yang, Yanyan Cai, Lei Zhang, Mao Guo, Anqi Li, Chenghu Zhou. (2021) A deep learning method to predict soil organic
carbon content at a regional scale using satellite-based phenology variables, International Journal of Applied Earth
Observation and Geoinformation, Volume 102, 2021, 102428, ISSN 1569-8432,
https://doi.org/10.1016/j.jag.2021.102428.
Omosalewa Odebiri, Onisimo Mutanga, John Odindi (2022) Deep learning-based national scale soil organic carbon
mapping with Sentinel-3 data, Geoderma, Volume 411, 2022, 115695, ISSN 0016-7061,
https://doi.org/10.1016/j.geoderma.2022.115695.
Qian Liu, Li He, Long Guo, Mengdi Wang, Dongping Deng, Pin Lv, Ran Wang, Zhongfu Jia, Zhongwen Hu, Guofeng Wu,
Tiezhu Shi. (2022) Digital mapping of soil organic carbon density using newly developed bare soil spectral indices and
deep neural network, CATENA, Volume 219, 2022, 106603, ISSN 0341-8162,
https://doi.org/10.1016/j.catena.2022.106603.
Seyed Roohollah Mousavi, Fereydoon Sarmadian, Mahmoud Omid, Patrick Bogaert (2022) Three-dimensional mapping
of soil organic carbon using soil and environmental covariates in an arid and semi-arid region of Iran, Measurement,
Volume 201, 2022, 111706, ISSN 0263-2241, https://doi.org/10.1016/j.measurement.2022.111706.
Wei-chun Zhang, He-shuang Wan, Ming-hou Zhou, Wei Wu, Hong-bin Liu, Soil total and organic carbon mapping and
uncertainty analysis using machine learning techniques, Ecological Indicators, Volume 143, 2022, 109420, ISSN 1470-
160X, https://doi.org/10.1016/j.ecolind.2022.109420.

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NDGeospatialSummit2022 - Soil carbon in the Red River Valley: towards precision quantification and modeling

  • 1. Soil carbon in the Red River Valley: towards precision quantification and modeling JOSE PABLO CASTRO, CALEY GASCH, PAULO FLORES, PETER ODUOR, ERIK HANSON, MINGAO YUAN NORTH DAKOTA STATE UNIVERSITY
  • 2.
  • 3.
  • 5.
  • 6.
  • 7.
  • 8.
  • 10.
  • 11.
  • 12. Goal To quantify in a precise and accurate way the soil carbon stocks of nine farms located in the Red River Valley using PrecisionAg tools, GIS, remote sensing and deep learning methods.
  • 18. Soil sampling 40 samples per farm 6 depths 2 repetitions 0-4 inches 4-8 inches 8-12 inches 12-24 inches 24-36 inches 36-48 inches 40 samples* 6 depths* 2 repetitions* 9 farms = 4320 samples
  • 21. Independent variables (X) X1 = Band 1 Blue UAV (Average of four flights) X2 = Band 2 Green UAV (Average of four flights) X3 = Band 3 Red UAV (Average of four flights) X4 = Band 4 NIR1 (Average of four flights) X5 = Band 5 NIR2 (Average of four flights) X6 = Band 6 NIR2 (Average of two flights) X7 = Enhanced Natural Difference Vegetation Index UAV (Average of four flights) X8 = Green Natural Difference Vegetation Index UAV (Average of four flights) X9 = GSAVI Green Salinity Vegetation Index UAV (Average of four flights) X10 = Natural Difference Reflectance Enhanced UAV (Average of four flights) X11 = Natural Difference Vegetation Index UAV (Average of four flights) X12 = Optimized Salinity Vegetation Index UAV (Average of two flights) X13 = Salinity and Vegetation Index UAV (Average of four flights) X14 = VSEC_D (Apparent electrical conductivity (0-30 cm depth) X15 = VSEC_S (Apparent electrical conductivity (0-90 cm depth) X16 = DEM RTK (Digital elevation model) X17 = Relative yield 1 X18 = Relative yield 2 X19 = Depth X20 = Longitude X21 = Latitude Dependent variables (Y) • Y1 = Total carbon in soil • Y2 = Inorganic carbon in soil • Y3 = Organic carbon in soil • Y4 = Bulk density Database
  • 22.
  • 24.
  • 25. Target Training Size Test Size Best model AdjR2 R2 RMSE Samples for training Y1 = TC 0.8 0.2 GradientBoostingRegressor 0.38 0.5 0.48 32 Y1 = TC 0.6 0.4 HistGradientBoostingRegressor 0.4 0.5 0.5 24 Y1 = TC 0.4 0.6 HistGradientBoostingRegressor 0.37 0.4 0.52 16 Y1 = TC 0.2 0.8 RandomForestRegressor 0.15 0.2 0.59 8 Y1 = TC 0.01 0.99 LGBMRegressor -0.03 0 0.67 1 Y2 = IC 0.8 0.2 GradientBoostingRegressor 0.74 0.8 0.46 32 Y2 = IC 0.6 0.4 HistGradientBoostingRegressor 0.74 0.8 0.47 24 Y2 = IC 0.4 0.6 GradientBoostingRegressor 0.71 0.7 0.52 16 Y2 = IC 0.2 0.8 HistGradientBoostingRegressor 0.66 0.7 0.56 8 Y2 = IC 0.01 0.99 XGBRegressor 0.54 0.6 0.66 1 Y3 = OC 0.8 0.2 GradientBoostingRegressor 0.86 0.9 0.31 32 Y3 = OC 0.6 0.4 GradientBoostingRegressor 0.88 0.9 0.3 24 Y3 = OC 0.4 0.6 LGBMRegressor 0.88 0.9 0.29 16 Y3 = OC 0.2 0.8 HistGradientBoostingRegressor 0.83 0.8 0.35 8 Y3 = OC 0.01 0.99 AdaBoostRegressor 0.7 0.7 0.48 1
  • 26.
  • 27. Conclusion Soil organic and inorganic carbon stocks can be predicted using precision ag tools, GIS, remote sensing, and deep learning models with determination’s coefficients around 0.8. Traditional methods as Thiessen polygons or Kriging does not achieve more than 0.2-0.4. An accuracy and precise quantification of carbon in the soil allows farmers to negotiate better contracts for carbon sequestration and at the same time allows to the companies to have a better control of where they are investing the money. It research project is at 40% development. It is expected to be 100% complete in the next three years.
  • 28. Acknowledgment This research is based upon work supported by the U.S. Department of Agriculture, Agricultural Research Service, under agreement No. 58-6064-8-023. Thanks to NDSU research specialist Joel Bell and undergraduate student Mike McKenna for their hard work in the field of this project.
  • 29. References Lin Yang, Yanyan Cai, Lei Zhang, Mao Guo, Anqi Li, Chenghu Zhou. (2021) A deep learning method to predict soil organic carbon content at a regional scale using satellite-based phenology variables, International Journal of Applied Earth Observation and Geoinformation, Volume 102, 2021, 102428, ISSN 1569-8432, https://doi.org/10.1016/j.jag.2021.102428. Omosalewa Odebiri, Onisimo Mutanga, John Odindi (2022) Deep learning-based national scale soil organic carbon mapping with Sentinel-3 data, Geoderma, Volume 411, 2022, 115695, ISSN 0016-7061, https://doi.org/10.1016/j.geoderma.2022.115695. Qian Liu, Li He, Long Guo, Mengdi Wang, Dongping Deng, Pin Lv, Ran Wang, Zhongfu Jia, Zhongwen Hu, Guofeng Wu, Tiezhu Shi. (2022) Digital mapping of soil organic carbon density using newly developed bare soil spectral indices and deep neural network, CATENA, Volume 219, 2022, 106603, ISSN 0341-8162, https://doi.org/10.1016/j.catena.2022.106603. Seyed Roohollah Mousavi, Fereydoon Sarmadian, Mahmoud Omid, Patrick Bogaert (2022) Three-dimensional mapping of soil organic carbon using soil and environmental covariates in an arid and semi-arid region of Iran, Measurement, Volume 201, 2022, 111706, ISSN 0263-2241, https://doi.org/10.1016/j.measurement.2022.111706. Wei-chun Zhang, He-shuang Wan, Ming-hou Zhou, Wei Wu, Hong-bin Liu, Soil total and organic carbon mapping and uncertainty analysis using machine learning techniques, Ecological Indicators, Volume 143, 2022, 109420, ISSN 1470- 160X, https://doi.org/10.1016/j.ecolind.2022.109420.