Sentinel-2 satellite preview of Geneva-region, captured on 2025-11-29 from an altitude of approximately 786 km.
Rapid urbanization and climate change are placing unprecedented stress on cities worldwide. As built-up areas expand and green spaces decline, urban heat islands intensify, air quality deteriorates, and residents face increased health risks. Understanding the spatial distribution of vegetation and development is essential for evidence-based urban planning, climate adaptation, and public health protection. This analysis quantifies the current balance between green cover and built-up surfaces in Geneva-region, identifies thermal vulnerability hotspots, and provides actionable recommendations for enhancing urban forestry and green infrastructure.
The NDVI statistics for the Geneva-region reveal critical insights into the current state of its green cover. The mean NDVI value of 0.108, with a median of 0.064, indicates a relatively low vegetation cover across the region. The standard deviation of 0.127 suggests variability in vegetation density. Spatially, the NDVI color map shows that areas with higher NDVI values (indicating denser vegetation) are scattered, with most regions exhibiting lower NDVI values. This pattern suggests that Geneva-region's green cover is not uniformly distributed, with certain areas having significantly denser vegetation compared to others. The 10th percentile value of -0.011 and the 90th percentile of 0.298 further indicate the disparity in vegetation density across the region. These numbers underscore the need for targeted greening efforts in areas with lower NDVI values to enhance overall green cover and ecological balance.
Analyzing the NDBI statistics provides insights into the urbanization patterns within the Geneva-region. The mean NDBI value of 0.011, coupled with a median of 0.015, suggests a relatively low level of built-up intensity across the region. However, the standard deviation of 0.131 indicates significant variability in urbanization, with certain areas exhibiting much higher built-up intensity. The NDBI color map highlights these high built-up zones, which are primarily concentrated in specific urban areas. The 10th percentile value of -0.124 and the 90th percentile of 0.144 further illustrate the disparity in built-up intensity. These findings suggest that while the overall built-up intensity is low, there are pockets of high urbanization pressure that may require attention to manage development sustainably.
NDVI Color Visualization
NDVI Greyscale (Index Values)
NDBI Color Visualization
NDBI Greyscale (Index Values)
Beyond NDVI and NDBI, three complementary indices provide deeper insights into vegetation health and water presence:
EVI improves on NDVI by correcting for atmospheric conditions and canopy background noise. It is more sensitive in areas with dense vegetation, making it useful for monitoring forest health and identifying vegetation stress that NDVI might miss.
EVI Color Visualization
EVI Greyscale (Index Values)
MNDWI enhances water body detection by using green and shortwave infrared bands. It is more effective than NDWI at separating water features from built-up areas, making it ideal for mapping urban water bodies like lakes, rivers, and reservoirs.
MNDWI Color Visualization
MNDWI Greyscale (Index Values)
NDMI measures vegetation water content by comparing near-infrared and shortwave infrared reflectance. Higher values indicate well-hydrated vegetation, while lower values suggest drought stress. This index is valuable for assessing irrigation effectiveness and identifying areas at risk of vegetation die-off.
NDMI Color Visualization
NDMI Greyscale (Index Values)
The NDVI-NDBI difference analysis provides a nuanced understanding of the balance between vegetation and built-up areas in the Geneva-region. The mean difference of 0.097, with a standard deviation of 0.225, indicates a slight overall dominance of vegetation over built-up areas. However, the difference bins reveal a more detailed picture. The majority of the region (66.25%) falls within the bin ranging from -0.589 to 0.116, indicating a near balance between vegetation and built-up areas. Areas with a positive difference (indicating vegetation dominance) account for 31.97% (bin from 0.116 to 0.821) and 1.74% (bin from 0.821 to 1.526), while areas with a negative difference (indicating built-up dominance) account for 0.04% (bin from -1.295 to -0.589) and 0.003% (bin from -2.0 to -1.295). The difference map and legend illustrate these patterns spatially, with different colors representing varying balances between vegetation and built-up areas. This analysis highlights the importance of maintaining a healthy balance to mitigate urban heat island effects and promote ecological sustainability.
The combined overlay image of NDVI and NDBI provides a comprehensive view of the spatial distribution of vegetation and built-up areas in the Geneva-region. By examining this overlay, patterns emerge that show where vegetation and built-up areas coexist or dominate. This visualization helps identify areas where green spaces are integrated within urban environments and highlights regions where either vegetation or built-up areas are more prevalent. Understanding these patterns is crucial for urban planning and ecological management, as it allows for the identification of opportunities to enhance green infrastructure within urban settings.
NDVI-NDBI Difference Map (Green = vegetation-dominated; Red = built-up-dominated)
Combined NDVI-NDBI Overlay
The heat risk distribution, as analyzed through the urban heat index bins, reveals critical insights into the thermal landscape of the Geneva-region. The mean urban heat index of -0.097, with a standard deviation of 0.225, indicates a generally low heat risk across the region. However, the bins data shows that 66.25% of the region falls within the bin ranging from -0.116 to 0.589, suggesting a moderate heat risk. High-risk zones, where NDBI > NDVI, account for 31.97% (bin from -0.821 to -0.116) and 1.33% (bin from -1.526 to -0.821), indicating areas with significant urban heat island effects. These high-risk zones are primarily located in densely built-up areas, as shown in the heat index map. The implications for the urban heat island effect are significant, with potential impacts on public health, energy consumption, and overall urban livability. Addressing these high-risk zones through greening initiatives and urban planning strategies is essential to mitigate heat-related risks.
Urban Heat Index Map (Red = high risk zones)
The interactive map below shows the exact geographical bounds of this satellite analysis. The colored overlay represents the NDVI coverage area overlaid on OpenStreetMap. You can zoom and pan to explore how the analysis boundaries align with streets, neighborhoods, and landmarks in Geneva-region.
Note: The analysis boundaries may extend beyond administrative city limits as they represent the satellite image crop captured on 2025-11-29. This ensures complete coverage of the urban area and surrounding regions for comprehensive vegetation and heat risk assessment.
Urban forests and green spaces are critical infrastructure for healthy, livable cities. Trees and vegetation reduce air pollution, lower urban temperatures through shade and evapotranspiration, manage stormwater, support biodiversity, and improve mental health and well-being. As cities grow denser and climate change intensifies heat events, monitoring and protecting urban green cover becomes essential for public health and environmental resilience.
Satellite remote sensing provides objective, repeatable measurements of vegetation health and urban development patterns across entire metropolitan areas. The Normalized Difference Vegetation Index (NDVI) quantifies photosynthetic activity and green cover, while the Normalized Difference Built-up Index (NDBI) identifies impervious surfaces and development intensity. Together, these indices reveal the changing balance between nature and urban growth—and highlight where intervention is most needed.
NDVI (Normalized Difference Vegetation Index) measures the difference between near-infrared light (strongly reflected by healthy vegetation) and red light (absorbed by chlorophyll). Values range from -1 to +1, with higher values indicating denser, healthier vegetation. Typical ranges: 0.6-0.9 = dense forest; 0.3-0.6 = moderate vegetation; 0.1-0.3 = sparse vegetation; <0.1 = bare soil or built-up areas.
NDBI (Normalized Difference Built-up Index) uses shortwave infrared and near-infrared bands to identify constructed surfaces. Positive values indicate built-up areas (roads, buildings, concrete), while negative values suggest natural or vegetated land. When NDBI exceeds NDVI in an area, it signals high development intensity and elevated urban heat island risk.
Our Mission: We want this research dataset brief to be Simple, Authentic, and Repeatable.
Urban Green Cover and Heat Risk Assessment
This dataset was created to help anyone understand how vegetation and green cover in this region is changing over time. It brings together processed satellite data, simple calculations, and a few observations that give the bigger picture.
At I Hug Trees, we believe that Geospatial Satellite imagery and processed data should be accessible to everyone. While grounded in scientific principles, outputs are presented in accessible formats so that technical imagery and calculations resonate with ordinary people and communities. Because only when it is relatable, can it tell clear stories about our greenery and urban life: shaping how we live, how we breathe, and how we cope with rising heat.
This dataset tries to make that easier. Whether you are a researcher, policy maker, student or just curious about the environment, these numbers and images help you see trends that are not obvious at first glance.
Basic Preprocessing:
It is important to get the right tile from the Sentinel-2 database for imagery processing. The browser feature from the Copernicus Data Space Ecosystem helped us identify the correct tile, its bounds, and the subset coordinates needed for extraction. It is always essential to double-check the preview image to verify that the fetched tile truly corresponds to the target region.
Next, we used an AWS Lambda environment for the bounds-discovery phase. This step involved fetching band data from the Microsoft Planetary Computer for dates where cloud cover was below 30% within the past 60 days. Once the acquisition date met this condition, we moved to AWS EC2 server scripts written in Python to download raw band data and process them into COGs (Cloud Optimised GeoTIFFs) along with additional indices.
These processed COGs and index outputs are then used for image displays, NDVI interpretation, and HTML digest features published on our platform. All indices raw value outputs are in JSON files for easy repeatable processing. We currently run this workflow on a quarterly schedule for each identified region.
Cloud Masking:
This dataset uses Sentinel-2's Scene Classification Layer (SCL) to remove pixels affected by clouds, shadows, haze, and saturation. Only surface-clear classes are kept, ensuring that the vegetation indices are calculated from clean, reliable pixels. The masking is applied at the pixel level, meaning every index (NDVI, EVI, etc.) is computed only on valid areas after stripping away noisy regions. This results in more trustworthy COGs, cleaner previews, and more meaningful temporal comparisons.
Calculation Formulas Used:
NDVI = (NIR − Red) ÷ (NIR + Red)EVI = 2.5 × (NIR − Red) ÷ (NIR + 6×Red − 7.5×Blue + 1)NDWI = (Green − NIR) ÷ (Green + NIR)NDBI = (SWIR1 − NIR) ÷ (SWIR1 + NIR)Tools Used:
Data Source: Microsoft Planetary Computer (Sentinel-2 L2A), rasterio, GDAL
Computation: Python 3, NumPy, SciPy, Pillow, Rasterio, rio-cogeo
AWS Pipeline: Lambda (triggers), EC2 (processing), S3 (storage), Bedrock (AI summaries)
Mapping: Leaflet.js, tile layers served from S3
Automation: Python boto3, Cron (EC2 quarterly jobs)
The dataset includes metadata.json with satellite tile information, various index outputs
(NDVI, EVI, NDWI, NDBI, MNDWI, NDMI), and statistical summaries. Please find the detailed list of files
available for download in the Download Data & Maps section below.
You can explore the NDVI trends, plug the json file into your favourite tool, build visualisations, or compare it with earlier datasets. It's created to be flexible.
AI helped speed up some parts of the work, like spotting unusual patterns, creating brief insights, and checking for inconsistencies. All metadata and bin-statistics JSON files were loaded and parsed into structured dictionaries, ensuring the AI receives clean, context-rich inputs for stable summarisation and interpretation.
Please refer to the How to Cite This Analysis section below for citation guidelines. This dataset is licensed under Creative Commons Attribution 4.0 International (CC BY 4.0).
For any questions, collaborations, or clarifications, feel free to reach out at: nature@ihugtrees.org
Images were processed using Python with the pystac-client and rasterio
libraries. Cloud masking was applied using the QA60 scene classification layer. Statistics
were computed using rasterio zonal statistics and exported as JSON for
analysis. All geospatial outputs are provided as Cloud-Optimized GeoTIFFs (COGs) for
efficient web access and GIS integration.
Yaragarla, R. (2025). Urban Green Cover & Heat Risk Assessment: Geneva-region. I Hug Trees. Retrieved from https://ihugtrees.org/data-analytics/sentinel-ndvi/Geneva-region/2025/12/04/digest.html
Satellite data: Copernicus Sentinel-2 (ESA), processed via Microsoft Planetary Computer.
@misc{ihugtrees_urban_geneva-region_2025,
author = {Yaragarla, Ramkumar},
title = {Urban Green Cover \& Heat Risk Assessment: Geneva-region},
year = {2025},
publisher = {I Hug Trees},
url = {https://ihugtrees.org/data-analytics/sentinel-ndvi/Geneva-region/2025/12/04/digest.html},
note = {Satellite data: Copernicus Sentinel-2}
}
This analysis and associated datasets are licensed under Creative Commons Attribution 4.0 International (CC BY 4.0). You are free to share and adapt this work with appropriate attribution.
If using Microsoft Planetary Computer data, please cite: microsoft/PlanetaryComputer (2022)
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