Submitted:
17 April 2024
Posted:
19 April 2024
Read the latest preprint version here
Abstract
Keywords:
1. Introduction
1.1. Climate Change, Disasters and Farming
1.2. Disaster Risk Management
1.3. Provision of Insurance for Small Farmers
2. Materials and Methods
2.1. The Study Area
2.2. Data Sources
2.2.1. Earth Observation (EO) Imagery
2.2.2. Digital Elevation Models (DEMs) and Geomorphometrics
2.2.3. Mobile Phone Photos
2.3. Data Analysis
2.3.1. Terrain: DEM Geomorphometrics
- Slope steepness: Slope Gradient (SG) shows the change occurring in elevation between each pixel of the DEM and its neighbors. Flat surfaces are characterized by low values while a steep relief is indicated by the higher values [35]. The direction of slope, known as the Slope Aspect, was also mapped because some slopes receive more rainfall as they face towards the dominant direction of winds during the wetter seasons of the year.
- Topographic Position Index (TPI), showing landform types: This is a geomorphological measure that classifies landforms into 10 types: canyons and deeply-incised valleys, mid-slope drainage, upland drainage, U-shaped valleys, plains, foot slopes, upper slopes, local ridges, mid-slope ridges, and high ridges [34,36].
- Topographic Wetness Index (TWI): This measure determines the slope of a given field in order to estimate soil moisture and surface saturation of that area. A high TWI value refers to accumulation of moist, surface saturation or alluvial deposits [37,38]. A low TWI value indicates susceptibility to soil erosion, whereas a high TWI values indicates an area with limited moisture [34,39,40].
2.3.2. Vegetation Mapping and Monitoring
- Vegetation detection with satellite imagery: Sentinel-2 and PlanetScope imagery were used to discriminate between vegetation and areas of bare soil in the study areas. The production of land cover types through machine learning predictive modelling informed our parametric insurance model and helped in price-setting as detailed later in this paper. This was done using a Random Forest (RF) machine learning classification algorithm [41]. A high prediction accuracy and high tolerance to outliers and noise are of the main advantages of RFs [41]. In addition, it estimates correlation between covariates and dependent variables by evaluating the relative importance of covariates [42]. RF classification was applied to cloud-free Sentinel-2 imagery, based on training samples, to discriminate land cover types.
- Normalized Difference Vegetation Index (NDVI): NDVI “is the primary vegetation index for monitoring crop conditions” [12]. It is widely-used due to its ability to measure photosynthesis activity and, thus, correlate with vegetation density and vitality [43,44]. NDVI is derived from satellite imagery in the visible and near-infra-red (VNIR) parts of the electromagnetic spectrum. NDVI derived from imagery of the Moderate Resolution Imaging Spectroradiometer (MODIS: 250m pixels) can be used for assessing vegetation dynamics during the past 20 years because archive of MODIS NDVI data extends back to 2000 [45]. NDVI has been at the center of calculations pertaining food insecurity whenever EO is adopted in order to spot anomalies in growth of crops [12]. In their study, Bégué, Madec [12] conducted spatio-temporal analysis of NDVI performance in West Africa. Impacts of extreme weather events, thus, could be evaluated based on NDVI values before, during and after each disaster.
2.3.3. Time-Series Analysis
2.3.4. Deep Learning (DL)
3. Results
3.1. Terrain and Infrastructure Risks
3.2. Indices and Predictions: Climate and Vegetation Over Time
3.3. Deep Learning and Mobile Phone Photos of Crops
4. Discussion
4.1. Parametric Insurance Model
- Actuarial rate tables - premiums, reserves, cash values and dividends.
- Interest rates
- Loading rates, expense charges, and policy fees
- Date bands and face amount bands
- Premium calculation rules
- Billing and collection rules
- Underwriting rules
4.1.1. Insurance Claim Verification
4.1.2. Automated Decision Making
4.2. Impact
4.2.1. Applications of EO for Finance and Insurance Services
4.2.2. Moral Hazard and Information Asymmetry
4.2.3. Digital Divide and Data Poverty
4.2.4. Sustainability
4.2.5. Policy Making
4.3. Limitations
4.3.1. Technological Challenges
4.3.2. Data Challenges
4.4. Recommendations
4.5. Future Agenda
4.5.1. Wider Coverage
4.5.2. Multiple Data Sources
5. Conclusions
Author Contributions
Funding
Institutional Review Board Statement
Informed Consent Statement
Data Availability Statement
Acknowledgments
Conflicts of Interest
Appendix A. Natural Hazards in Dosquebradas Colombia 1998-2020 (compiled from IDEAM online database)
| Disaster | Start Date | End Date | |
| 1 | Drought | 1998-01-01 | 1999-01-01 |
| 2 | Flood | 1999-01-10 | 1999-05-19 |
| 3 | Earthquake | 1999-01-25 | 1999-01-26 |
| 4 | Flood | 1999-10-28 | 1999-12-31 |
| 5 | Flood | 2000-05-18 | 2000-05-24 |
| 6 | Wildfire | 2001-08-01 | 2001-09-01 |
| 7 | Drought | 2002-01-01 | 2003-01-01 |
| 8 | Flood | 2002-04-24 | 2002-04-29 |
| 9 | Flood | 2003-08-01 | 2003-12-01 |
| 10 | Flood | 2004-01-01 | 2004-06-28 |
| 11 | Drought | 2004-01-01 | 2005-01-01 |
| 12 | Flood | 2005-04-12 | 2005-05-07 |
| 13 | Flood | 2005-09-15 | 2005-11-17 |
| 14 | Flood | 2006-01-01 | 2006-04-27 |
| 15 | Drought | 2006-01-01 | 2007-01-01 |
| 16 | Flood | 2007-10-20 | 2007-10-26 |
| 17 | Flood | 2008-01-01 | 2008-05-19 |
| 18 | Flood | 2008-11-16 | 2009-01-12 |
| 19 | Drought | 2009-01-01 | 2010-01-01 |
| 20 | Wildfire | 2010-01-01 | 2010-04-06 |
| 21 | Flood | 2010-10-30 | 2011-01-12 |
| 22 | Flood | 2011-02-10 | 2011-06-05 |
| 23 | Flood | 2011-09-01 | 2011-12-31 |
| 24 | Flood | 2012-03-15 | 2012-05-14 |
| 25 | Earthquake | 2013-02-09 | 2013-02-09 |
| 26 | Flood | 2013-09-15 | 2013-12-01 |
| 27 | Drought | 2015-08-01 | 2016-02-01 |
| 28 | Storm | 2016-09-20 | 2016-09-23 |
| 29 | Flood | 2017-03-17 | 2017-05-16 |
| 30 | Flood | 2017-12-01 | 2018-01-07 |
| 31 | Drought | 2018-01-01 | 2020-01-01 |
| 32 | Flood | 2019-02-20 | 2019-02-26 |
| 33 | Flood | 2020-06-10 | 2020-07-10 |
Appendix B. Datasets analyzed in Google Earth Engine
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| Dataset | Type | Pixel size (m) | Derived Indices | Data Provider |
|---|---|---|---|---|
| ALOS PALSAR (L-band radar) |
Digital Elevation Model (DEM) |
12.5 |
Landform types, Slope steepness, Floodplains, Topographic wetness |
https://search.asf.alaska.edu/#/ |
|
MODIS |
VIR imagery |
250 |
NDVI (vegetation photosynthesis) |
https://modis.gsfc.nasa.gov/data/ |
|
Sentinel-2 MultiSpectral Instrument L2A |
VIR imagery |
10 |
NDVI: vegetation photosynthesis, bare ground, crop type. |
https://earth.esa.int/web/sentinel/user-guides/sentinel-2-msi/product-types/level-2a |
|
PlanetScope |
VNIR imagery |
3.8 |
https://www.planet.com/products/planet-imagery/ |
|
|
Geological maps |
GIS - 1:100,000 |
1000 |
Geology Land cover type |
http://www.ideam.gov.co/ |
| OpenStreetMap | Open Source topography | Variable to 1:10k scale | Topography: Drainage, Roads, Bridges, Buildings |
https://www.openstreetmap.org/#map=13/4.8540/-75.7178&layers=C |
|
Google Earth Pro |
Maps & archive EO imagery |
0.3 -30 |
Digital Globe & Map with 3D visualisation of terrain |
https://www.google.com/intl/en_uk/earth/versions/ |
|
Google Earth Engine (GEE) |
Archive EO imagery |
10 -500 |
Search engine & data analysis platform |
https://code.earthengine.google.com/ |
| Metric | Score |
|---|---|
| Accuracy | 0.8473 |
| Precision | 0.8917 |
| Sensitivity (recall) | 0.9175 |
| F1-score | 0.9044 |
| Specificity | 0.7947 |
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