Hydro-Meteorological Landslide Inventory for Sustainable Urban Management in a Coastal Region of Brazil
Abstract
1. Introduction
2. Materials and Methods
2.1. Data and Test Site
2.1.1. Landslide Data Gathering
- The systematic collection and mapping of landslide occurrences from institutional and local civil defence reports, verified news articles, and previous research, all covering the period from 1988 to 2025 for the cities of Cubatão, Guarujá, Santos, and São Vicente. These records provided fundamental information including date, location, and descriptive accounts of each event (Table 1);
- Field validation that was conducted through targeted site visits and UAV-based assessments to verify event locations, characterise slope conditions, and fill data gaps. Ten areas were selected based on accessibility and visited across the study region, including scars from the 2020 event. Additionally, validation in Cubatão leveraged prior fieldwork from [46], while the consistent UAV-based assessments conducted by the Civil Defence of Santos provided high-accuracy data for recent events, significantly reducing the need for extensive field surveys;
- The spatial verification and adjustment of event locations using QGIS, based on address records, fieldwork validation, and the interpretation of high-resolution satellite imagery via PlanetScope and Google Earth Pro’s time series. The adjustment was performed on a 1:25.000 map scale.
2.1.2. Rainfall and Soil Moisture Network
2.1.3. Geoenvironmental Parameters
- Watersheds and slope units: Watershed boundaries and slope units were derived from a 5 m resolution contour lines from a Digital Elevation Model (DEM) produced using data from the Brazilian Geological Survey database using the r.watershed algorithm in GRASS GIS, providing a detailed representation of topographic variability across the study area. The delineation allowed for the assignment of each landslide to its respective hydrological unit and slope compartment;
- Slope type classification: Slopes were preliminarily classified as “unmodified” or “anthropogenically modified” based on human-induced alterations, using field observations, urban mapping, and high-resolution imagery interpretation. This classification is crucial for differentiating between areas affected by direct anthropogenic interventions and those retaining their natural characteristics, especially in densely urbanised regions where human-induced changes are a key landslide trigger, such as in Hong Kong and Chongqing [16,41,50];
- Lithological map: A lithological map was integrated into the inventory, associating each event with its geological substrate and soil behaviour related to different rainfall and soil moisture thresholds. Lithological information was available at different cartographic scales: 1:50,000 [44] for the municipalities of Cubatão, Santos, and São Vicente, and 1:250,000 [51] for Guarujá. The difference in map scale was considered a source of spatial uncertainty in the lithology parameter attribution;
- Land use and land cover map: Obtained from MapBiomas Collection 9 (2023) [52], which provides annual, multi-temporal, and 30 m resolution land cover and land use classifications across Brazil derived from Landsat imagery. It enabled the assessment of anthropogenic modifications and land cover patterns in the study area.
2.2. Inventory Compilation
2.2.1. Data Preprocessing
- 1.
- Geographic confidence classification
- 2.
- Temporal confidence classification
- 3.
- Slope modification classification criteria
- 4.
- Soil moisture sensors and satellite data agreement
- Mean Bias Error (MBE): The mean bias error quantifies the systematic difference between the satellite and in situ measurements, indicating whether the satellite product consistently overestimates or underestimates soil moisture values relative to ground truth. Positive values denote overestimation, while negative values indicate underestimation;
- Root Mean Square Error (RMSE) and Mean Absolute Error (MAE): These metrics describe the overall and average discrepancies, respectively, between the satellite and ground-based measurements. The RMSE gives greater weight to larger errors due to its squared term, while the MAE represents the mean of absolute differences, providing an intuitive average error magnitude;
- Pearson Correlation Coefficient (r): The Pearson correlation coefficient was used to measure the strength and direction of the linear relationship between the two datasets. A threshold of r ≥ 0.30 was adopted as the minimum acceptable level of linear association for reliable agreement at each station and sensor depth;
- Coefficient of Variation Difference (CV_diff): This metric captures the relative difference in variability (as a percentage of the mean) between the satellite-derived and in situ soil moisture datasets. A CV_diff below 20% was set as the threshold to ensure that the relative spread of values remains comparable across both data sources, an essential check given the different observational natures of the two datasets.
- 5.
- Assembling the hydro-meteorological landslide inventory
- Looks up for stations with at least min_records of 20 days of valid rain data in the 30 days before the landslide date;
- Tries first stations in the same city with that data count;
- Falls back to the nearest station, ignoring city but still meeting data count;
- If none meet the threshold, it falls back to the nearest station regardless of data count.
2.2.2. Time Resolution-Based Datasets
- Daily resolution model: The first set of models examined the role of cumulative rainfall and antecedent soil moisture at a daily resolution. Events with exact dates only (T3), enabling only daily summary variables;
- Finer resolution: Events with precise timestamps or approximate time periods within the day (T1 and T2), allowing for the extraction of finer temporal scale hydro-meteorological variables.
2.2.3. Rainfall Data Featuring Engineering and Completeness
- Cumulative rainfall totals over 1, 3, 7, 14, and 30 days;
- Moving maximum rainfall intensities at 10 min, 30 min, 1 h, 3 h, 6 h, and 12 h intervals;
- Antecedent soil moisture conditions via daily, 3-day, and 7-day averages and maxima;
- is the completeness percentage for station i in month j;
- is the number of unique records observed in month j for station i;
- is the total expected number of records for that month (either number of hours for Cemaden network or number of days for EMAE and SABESP stations).
2.3. Inventory Analysis and Web Application
- (i)
- Temporal and spatial distribution assessments, analysing annual, decadal, and monthly landslide frequencies and their geographic distribution across municipalities. Temporal confidence and geographical accuracy classifications were summarised to appraise dataset quality;
- (ii)
- Seasonal trends analysis, comparing monthly landslide occurrences with regional average rainfall to identify peak activity periods and confirm wet season patterns typical of the tropical coastal region;
- (iii)
- Hydro-meteorological data completeness evaluation, calculating the percentage of expected rainfall and soil moisture records retrieved per monitoring station and month, using the completeness metric from Section 2.1.3. Heatmaps illustrated spatial and temporal monitoring gaps;
- (iv)
- Soil moisture data validation and bias correction, comparing ERA5-Land reanalysis soil moisture against in situ sensor data. Performance was assessed via Pearson’s correlation, the Mean Absolute Error (MAE), and the coefficient of variation difference (CV_diff) to identify suitable stations and depths for correction.
- (i)
- Interactive visualisation of individual landslide events alongside antecedent rainfall and soil moisture conditions;
- (ii)
- Filtering and querying by temporal, spatial, geomorphological, and confidence parameters;
- (iii)
- Operational and research support, offering municipal agencies, researchers, and planners a platform to assess landslide hazard contexts in near real time or retrospectively.
3. Results
3.1. Landslide Inventory Overview
3.1.1. Landslide Inventory with Date (LID)
3.1.2. Landslide Inventory with Time (LIT)
3.1.3. Temporal Distribution
3.2. Field Validation and Landslide Characterisation
3.3. Geoenvironmental Characterisation
3.4. Rainfall and Soil Moisture Conditions
3.4.1. Monthly Landslide Frequency and Seasonal Trends
3.4.2. Rainfall and Soil Moisture Data Completeness
3.4.3. Soil Moisture Data Validation and Gap Filling
3.5. Application Records and Visualisation
- datetime_brazil: Date and time of record in Brazilian local time;
- rain_mm_24 h, rain_mm_48 h, rain_mm_72 h: Cumulative rainfall totals in millimetres over the preceding 24, 48, and 72 h, respectively;
- geo_confidence: Geographical confidence classification (G1–G3) indicating locational accuracy of the landslide record;
- temporal_confidence: Temporal confidence classification (T1–T3) indicating date/time accuracy of the landslide occurrence;
- city: Municipality name;
- address: Street address of the landslide site;
- neighbourhood: Local neighbourhood or district name;
- latitude, longitude: Geographical coordinates of the landslide site in decimal degrees;
- slope_type: Slope category where the landslide occurred (e.g., cut, natural, or fill);
- landslide_id: Unique identifier for each landslide record;
- landslide_occurred: Boolean flag indicating if a landslide occurred (1) or not (0);
- ws_id: Watershed identification code where the landslide site is located;
- lulc: Land use and land cover classification of the landslide site;
- rainfall_station_code: Code identifying the associated rainfall monitoring station;
- sm_station_code: Code identifying the associated soil moisture station;
- sm_l1–sm_l6: Soil moisture values (%) at six soil depth layers, varying 0.5 m amongst each one, ranging from 0.5 m to 3 m.
4. Discussion
4.1. Strengths and Limitations of the Inventory
4.2. Gaps Addressed in Brazil and International Landslide Data Practices
4.3. Comparison to International Inventories and Highlights
4.4. Potential Applications
- Operational LEWSs; the subset of landslides with T1/T2 times and G1/G2 locations can be used for threshold definition and the validation of rainfall and soil moisture-based warnings, which is a critical gap in current Brazilian systems, which largely rely on rainfall-only thresholds with limited empirical landslide occurrence data for calibration;
- Empirical and physical modelling, by supporting hydro-meteorological correlation studies and landslide susceptibility mapping and offering calibrated inputs for models requiring precise temporal and spatial landslide data, a method applied effectively in regions such as Italy (e.g., [42]);
- The inventory also holds operational and scientific value for climate-related landslide monitoring, given its long temporal coverage of rain gauges and landslides coupled with the integration of rainfall and soil moisture information. The observed seasonal patterns and rainfall–landslide relationships enable further assessments of potential shifts in landslide seasonality and frequency under changing climatic conditions. Additionally, the inventory’s structure facilitates data-driven susceptibility and hazard modelling initiatives in urbanised, landslide-prone regions, providing robust, confidence-classified data for probabilistic or machine learning-based approaches;
- Public policy and civil defence planning; by identifying municipalities and decades with data gaps, the inventory guides future monitoring investments and risk management priorities. In addition to enhancing public transparency and facilitating access for decision-makers, the BrazInv application is structured to support its integration into municipal contingency planning protocols. Its design also enables use in public risk communication campaigns, fostering citizen education and the participatory mapping of landslide hazards. Hence, we highly encourage continuous investment in the current network to maintain and even amplify it for more accurate landslide forecasting.
4.5. Transferability of the Framework
5. Conclusions
- (i)
- Compilation of 2534 landslide records systematically classified by spatial (G1–G3) and temporal (T1–T3) confidence, enabling transparent data precision assessment;
- (ii)
- Demonstration that UAV field validation markedly improves locational accuracy and typological consistency, especially in complex terrain;
- (iii)
- Integration of soil moisture data, highlighting its potential for operational early warning while identifying the limitations of satellite-derived products without local calibration in tropical coastal environments;
- (iv)
- Identification of spatial and temporal reporting gaps, informing future monitoring and data management priorities;
- (v)
- Development of a prototype of a publicly accessible platform to showcase BrazInv, promoting transparency and usability for both research and risk management.
- (i)
- Confidence classifications significantly enhance inventory reliability for both research and early warning applications, though precise temporal data remains challenging;
- (ii)
- Multi-source integration combined with UAV validation is essential for producing detailed and robust inventories in urbanised tropical regions;
- (iii)
- Soil moisture data can complement rainfall-based warnings, but requires local calibration to be operationally effective when using satellite reanalysis estimation;
- (iv)
- Persistent data gaps and biases highlight the need for systematic, standardised landslide documentation at municipal and national levels;
- (v)
- The methodology and framework are transferable worldwide and provide a model for other Brazilian regions and similar international contexts.
Author Contributions
Funding
Data Availability Statement
Acknowledgments
Conflicts of Interest
References
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Source | Date Range | Observations |
---|---|---|
São Paulo State Geological Institute (IG) | 1990–2018 | Data from the whole state, includes news reporting, local civil defence data, and more |
Santos Municipal Civil Defence | 2014–2023 | Local data, occurrences recorded when called upon by society |
Cubatão Municipal Civil Defence | 1998–2024 | Local data, occurrences recorded when called upon by society |
Gathered by the author from news reporting | Scattered | Information completion conducted by the author according to the news, such as landslide time/period |
Data Type | Dataset | Time Range | Temporal Resolution | Source |
---|---|---|---|---|
Rainfall | Manual rain gauge | 1940–present | Daily | ANA 1 |
Manual rain gauge | 1940–present | Every 3 hrs | SABESP 2 | |
Automatic rain gauge | 2015–present | 10 min | CEMADEN 3 | |
CHIRPS satellite estimate | 1981–present | Daily | Climate Hazards Center | |
IMERG satellite estimate | 2000–present | 30 min | NASA 4 | |
Soil moisture | Automatic in situ geosensor network | 2019–present | 10 min | CEMADEN |
Era5-Land reanalysis | 1981–present | Hourly | Copernicus |
Geographic Confidence Class | Code | Description |
---|---|---|
High | G1 | Known point; precisely mapped via high-resolution imagery, remote sensing, GPS, field survey, or precise report |
Medium | G2 | Approximate location from address and number of the house or geocoding |
Low | G3 | Estimated based on indirect info from any other source |
Temporal Confidence Class | Code | Description |
---|---|---|
High | T1 | Precise time of occurrence available (recorded hour and minutes) |
Medium | T2 | Approximate period of the day available (morning, afternoon, night, dawn) 1 |
Low | T3 | Date is known or approximate date information available |
Category | Time Range | Assigned Time for Events Without Known Time |
---|---|---|
Dawn | 00:00–05:59 | Events reported as occurring at dawn were assigned 00:00 |
Morning | 06:00–13:59 | Events reported as occurring in the morning were assigned 06:00 |
Afternoon | 14:00–18:59 | Events reported as occurring in the afternoon were assigned 14:00 |
Night | 19:00–23:59 | Events reported as occurring at night were assigned 19:00 |
Date only | YYYY-MM-DD | Events reported with a specific date but no time information were assigned to the day before |
Inventory | Location | Time Frame | Rainfall Data Linked | Confidence Classification | Soil Moisture Data Linked | Public Availability |
---|---|---|---|---|---|---|
BrazInv | Baixada Santista (Brazil) | 1988–2024 | Yes | Geographical and temporal | Yes | Partially open |
ITALICA [24,25] | Italy | 1996–2021 | Yes | Geographical and temporal | No | Open access |
Italian IFFI Inventory [58] | Italy | Historical–present | No | No | No | Open access |
NASA Global Landslide Catalog (GLC) [59,60] | Global | 2007–present | No | No | No | Open access |
USGS Landslide Inventory [61] | USA | Historical–present | No | Geographical | No | Open access |
British Geological Survey (BGS) [62,63] | United Kingdom | Historical–present | Yes 1 | No | No | Open access |
New Zealand National Landslide DB [64] | New Zealand | Historical–present | No | No | No | Open access |
São Paulo State IG Inventory | São Paulo State (Brazil) | Historical–present | No | No | No | Open access |
Nicaragua Landslide Database [65] | Nicaragua | 1826–2003 | Yes | No | No | Limited |
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Hader, P.R.P.; Horta, I.T.L.G.; da Silva do Valle, V.A.; Irigaray, C. Hydro-Meteorological Landslide Inventory for Sustainable Urban Management in a Coastal Region of Brazil. Sustainability 2025, 17, 7487. https://doi.org/10.3390/su17167487
Hader PRP, Horta ITLG, da Silva do Valle VA, Irigaray C. Hydro-Meteorological Landslide Inventory for Sustainable Urban Management in a Coastal Region of Brazil. Sustainability. 2025; 17(16):7487. https://doi.org/10.3390/su17167487
Chicago/Turabian StyleHader, Paulo Rodolpho Pereira, Isabela Taici Lopes Gonçalves Horta, Victor Arroyo da Silva do Valle, and Clemente Irigaray. 2025. "Hydro-Meteorological Landslide Inventory for Sustainable Urban Management in a Coastal Region of Brazil" Sustainability 17, no. 16: 7487. https://doi.org/10.3390/su17167487
APA StyleHader, P. R. P., Horta, I. T. L. G., da Silva do Valle, V. A., & Irigaray, C. (2025). Hydro-Meteorological Landslide Inventory for Sustainable Urban Management in a Coastal Region of Brazil. Sustainability, 17(16), 7487. https://doi.org/10.3390/su17167487