Thessaly master plan- WWF presentation_18.04.24.pdf
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UAS based soil moisture monitoring
1. 1
UAS Based Soil Moisture Downscaling Using
Random Forest Regression Model
โข Ruodan Zhuang1, Salvatore Manfreda2, Yijian Zeng3, Nunzio Romano2, Eyal Ben Dor4,
Antonino Maltese5, Paolo Nasta2, Nicolas Francos4, Fulvio Capodici5, Antonio
Paruta5, Giuseppe Ciraolo5, Brigitta Szabรณ6, Jรกnos Mรฉszรกros6, George P. Petropoulos7,
Lijie Zhang8, and Zhongbo Su3,9
โข 1 University of Basilicata, Italy; 2 University of Naples Federico II, Napoli, Italy; 3 University of Twente, The
Netherlands; 4 Tel Aviv University, Israel; 5 University of Palermo, Italy; 6 Centre for Agricultural Research, Hungary; 7
Technical University of Crete, Greece; 8 Forschungszentrum Jรผlich, Germany; 9 School of Water and Environment,
Changโan University, China
4. 4
2. In-situ Rainfall data
โข k is an empirical factor to
indicate the decay effect from
the rainfall (0.85 and 0.98 )
โข Pt-i is the precipitation value
at ith days before day of t
Antecedent Precipitation Index
6. 6
3. Random Forest Regression Model:
Two Steps Downscaling
c) 16cm & 1km resolution DEM
a) Flowchart of RF regression model
b) Two steps downscaling
7. 7
3. RF Regression Model:
Coarse Resolution (1km & 30m) Data
Datasets (Sensor) Variables Spatial resolution Temporal resolution Duration
Sentinel-1 C-SAR
Surface soil moisture
(SSM)
1km Daily 2015-2019
MODIS
Land surface
temperature (LST)
1km Daily 2015-2019
MODIS
Normalized difference
vegetation (NDVI)
1km
10 days 2015-2019
SRTM
Digital Elevation Model
(DEM)
30m / /
LANDSAT-8 RED, GREEN BANDS 30m 16 days 2015-2019
LANDSAT-8 TIR BANDS 30m 16 days 2015-2019
8. 8
3. RF Regression Model: MODEL I
1kmโ30m
Feature: API, Importance: 0.56
LST, Importance: 0.27
NDVI, Importance: 0.10
DEM, Importance: 0.07
RMSE: 11.17 [saturation degree]
r2: 0.84
Pearson correlation coefficient: 0.91
a) RF Regression Model I Test Results
b) Evaluation of the Estimated SM Time Series
SM
SM
9. 9
3. RF Regression Model: MODEL II
30mโ16cm
a) RF Regression Model II Test Results b) Validation of the Estimated SM c) Estimated SM map (14-June-2019)
30m Soil moisture
10. 10
3. 5year average map of 30m predicted SSM
5year-average 30m SSM (30km*30km) MFC2 and SoilNet
MFC2
DEM 30km*30km
13. 13
4. Scaling characteristics: Variances Time series
1km sentinel SSM product Predicted 30m SSM product
Same Area: 30km*30km
14. 14
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169. https://doi.org/10.1177/0263276419851846
โช Bauer-Marschallinger, B., Paulik, C., Hochstรถger, S., Mistelbauer, T., Modanesi, S., Ciabatta, L., โฆ Wagner, W. (2018). Soil moisture
from fusion of scatterometer and SAR: Closing the scale gap with temporal filtering. Remote Sensing, 10(7), 1030.
https://doi.org/10.3390/rs10071030
โช Manfreda, S., McCabe, M. F., Miller, P. E., Lucas, R., Madrigal, V. P., Mallinis, G., โฆ Toth, B. (2018). On the use of unmanned aerial
systems for environmental monitoring. Remote Sensing, 10(4), 641. https://doi.org/10.3390/rs10040641
โช McCabe, M. F., Rodell, M., Alsdorf, D. E., Miralles, D. G., Uijlenhoet, R., Wagner, W., โฆ Wood, E. F. (2017). The future of Earth
observation in hydrology. Hydrology and Earth System Sciences, 21(7), 3879โ3914. https://doi.org/10.5194/hess-21-3879-2017
โช Nasta, P., Bogena, H. R., Sica, B., Weuthen, A., Vereecken, H., & Romano, N. (2020). Integrating Invasive and Non-invasive
Monitoring Sensors to Detect Field-Scale Soil Hydrological Behavior. Frontiers in Water, 2(September).
https://doi.org/10.3389/frwa.2020.00026
โช Paruta, A., Ciraolo, G., Capodici, F., Manfreda, S., Sasso, S. F. D., Zhuang, R., โฆ Maltese, A. (2020). A Geostatistical Approach to Map
Near-Surface Soil Moisture Through Hyperspatial Resolution Thermal Inertia. IEEE Transactions on Geoscience and Remote Sensing,
1โ18. https://doi.org/10.1109/TGRS.2020.3019200
โช Peng, J., Loew, A., Merlin, O., & Verhoest, N. E. C. (2017). A review of spatial downscaling of satellite remotely sensed soil moisture.
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โช Romano, N., Nasta, P., Bogena, H., De Vita, P., Stellato, L., & Vereecken, H. (2018). Monitoring Hydrological Processes for Land and
Water Resources Management in a Mediterranean Ecosystem: The Alento River Catchment Observatory. Vadose Zone Journal, 17(1),
180042. https://doi.org/10.2136/vzj2018.03.0042
โช Tmuลกiฤ, G., Manfreda, S., Aasen, H., James, M. R., Gonรงalves, G., Ben-Dor, E., โฆ McCabe, M. F. (2020). Current practices in UAS-
based environmental monitoring. Remote Sensing, 12(6). https://doi.org/10.3390/rs12061001
โช Wang, S., Garcia, M., Ibrom, A., Jakobsen, J., Kรถppl, C. J., Mallick, K., โฆ Bauer-Gottwein, P. (2018). Mapping root-zone soil moisture
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Reference
15. Appendix 1: LANDSAT-8: From TIR to LST
โข STEP 1:
๐น๐๐ถ =
๐๐ท๐๐ผ โ ๐๐ท๐๐ผ๐
๐๐ท๐๐ผ๐ฃ + ๐๐ท๐๐ผ๐
NDVI values of full vegetation cover and
bare soil.
โข STEP 2:
Land surface emissivity ๐ retrieval:
๐๐ ๐น๐๐ถ = 0 โ ๐
= 0.979 โ 0.046 โ ๐๐๐๐๐4
๐๐ 0 < ๐น๐๐ถ < 1 โ ๐
= 0.971(1 โ ๐น๐๐ถ) + 0.987 โ ๐น๐๐ถ
๐๐ ๐น๐๐ถ = 1 โ ๐ = 0.99
โข STEP 3
๐๐ = [
๐2
๐ ln{
๐1
๐5[
[๐(
๐1
(๐
๐2
๐ ) โ 1
) + (1 โ ๐)๐ฟ๐] โ (1 โ ๐)๐ฟ๐
๐
]
+ 1}
โข ๐ฟ๐ is the down-welling atmospheric radiance.
โข ๐ is the effective band wavelength,
โข T is the brightness temperature (K),
โข ๐1 = 1.19104 ร 108
๐๐๐4
๐โ2
๐ ๐โ1
โข ๐2 = 14387.7๐๐๐พ
โข K1=774.8853
โข K2=1321.0789
โข ๐ is the land surface emissivity.
15
16. Appendix 2: Example map of LST
16
Presence of clouds may limit the extents of
the higher resolution LST maps
lst1: 1km MODIS LST (averaged of 13:30 and 01:30)
lst2: 30m LANDSAT LST (daytime)
17. Appendix 3: Example map of NDVI
โข LANDSAT8 Band 4 (red) & 5 (Nir) (Top of atmosphere reflectance)โ Atmosphere correction (bottom of
atmosphere reflectance) โ NDVI ori โ Interpolation (with limit)โ S-G filter โ NDVI (30m)
โข MODIS 1km NDVI โ S-G filter
17
NDVI
ndvi1: 1km MODIS NDVI
ndvi2: 30m LANDSAT NDVI