EO BALTIC PLATFORM FOR GOVERNMENTAL SERVICES (EO-BALP) Reference nr. ESA AO/1-11741/23/I-NB ��ESA Contract No. 4000142702/23/I-NB
Forest Monitoring Application
06.02.2025
Agenda
10:30 - 10:45 Introduction of the EO-BALP Project and the Forest Monitoring Application
10:45 - 11:10 Demo of the Forest Monitoring Application
11:10 - 11:20 Accomplished accuracies of the forest data
Q&A session
GeoHub Platform
Forest Monitoring Application, beta version
Scenario 1: �Automated clear-cut monitoring system in the Baltics
Register
Review the plot analysis
1) current status (0-30%; 30-70%; 70-100%)
2) forest area (%, ha)
3) damaged area (%, ha)
4) previous monitoring date
5) change since last monitoring time
Upload forest plots with attributes and edit them in the web app if needed
Evaluate the area using various spatial data (all Baltics)
Download the result in GeoJSON and CSV formats
Scenario 2: �Automated forest health risk monitoring �(clear-cuts, windfalls, fires, pests, illnesses, increased moisture, etc.)�
Specify forest plots for analysis or send as shapefile to info@forestradar.com
Evaluate the area using various spatial data (all Baltics)
Receive risk areas in the app after the end of the vegetation season
Specify the time period of the analysis (year)
Register
Download the result in GeoJSON and CSV formats
Forest Monitoring - Layers (orthophoto map)
Forest Monitoring - Layers (satellite map)
Forest Monitoring - Layers (forest health)
Evaluate and download result (GeoJSON and CSV formats)�
Cadastre map
Topographic map
CSV file to easy copy and paste coordinates in other map apps
Layers
Bookmarks
The application saves your settings and map areas before closing.
Demo of the Forest Monitoring Application
EO BALTIC PLATFORM FOR GOVERNMENTAL SERVICES (EO-BALP) Reference nr. ESA AO/1-11741/23/I-NB ��ESA Contract No. 4000142702/23/I-NB
Acomplished accuracies of the forest data
06.02.2025
Data layers
Green: tree cover detected
Transparent: no tree cover
Accuracy was evaluated for masks based on summer images of Estonia using CHM of 2023 at stand level
Tree cover class according to CHM | Number of forest stands | Detected as non-forest | Detected as forest |
0-5% | 2055 | 2005 (97.6%) | 50 |
6-10% | 2258 | 2160 (96%) | 98 |
11-20% | 2199 | 1780 (81%) | 419 |
21-40% | 2081 | 919 | 1162 (56%) |
41-60% | 2554 | 118 | 2436 (95%) |
61-80% | 9200 | 6 | 9194 (99.9%) |
81-100% | 43660 | 0 | 43660 (100%) |
🟩At tree canopy cover between 10 and 40% there will always be high detection uncertainty due to the reflectivity characteristics of the background ground cover
Tree cover class according to CHM | Number of forest stands | True Positive | True Negative | False Positive | False Negative |
0-5% | 2055 | - | 97.6% | 2.4% | - |
6-10% | 2258 | - | 96.0% | 4.3% | - |
11-20% | 2199 | | | | |
21-40% | 2081 | | | | |
41-60% | 2554 | 95% | - | - | 4.6% |
61-80% | 9200 | 99.9% | - | - | 0.06% |
81-100% | 43660 | 100% | - | - | 0% |
🟩At tree canopy cover lower than 10% and higher than 40%, detection accuracy is above 95%
🟩The smallest tree canopy cover that can be detected at pixel level with sufficient confidence is 40% per 900m2
🟩It should be noted that due to mixed pixel, illumination and co-registration errors, the average offset between the S2 result boundaries and the CHM boundaries is approximately 9 meters
🟩Results obtained in autumn and winter can have lower accuracy than those obtained in summer/spring (no snow)as well as for images with haze/fog
2. Damaged tree crown masks: data layers
2. Damaged tree crown masks: data layers
2. Damaged tree crown masks: accuracy
🟩 62 forest stands checked: 52 conform, 10 false positives mostly due to cutting acitivities
🟩After introducing context evaluation number of false positives reduced from 16% to 5%
2. Damaged tree crown masks: accuracy
🟩 Sattelite images and machine learning provides regular information over vast areas