CLDynamicLandCover
Authors/Creators
- 1. Facultad de Ingeniería y Ciencias, Universidad Adolfo Ibañez
-
2.
Center for Climate and Resilience Research
-
3.
Data Observatory Foundation
- 4. Doctorado en Ciencias de Recursos Naturales, Universidad de la Frontera
- 5. Department of Civil Engineering, Faculty of Engineering and Sciences, Universidad de la Frontera
Description
| Description | |
|---|---|
| Dataset | CLDynamicLandCover |
| Resolution | 30 m |
| Area | Central Chile (latitudes -31.61° to -43.50°; southern Coquimbo – southern Los Lagos) |
| Years covered | 1990, 1999, 2004, 2009, 2013, 2018 |
| Temporal resolution | Five-year intervals |
| Development | Semi-automatic algorithm, initially for south-central Chile, later expanded |
| Data sources | Landsat (spectral reflectivity), SRTM (topography), auxiliary cartographic info |
| Training data | 15 land cover classes, photointerpreted & georeferenced in 2018 |
| Feature selection | Machine learning algorithms + expert criteria |
| Accuracy | Overall accuracy: 0.894–0.950; Kappa: 0.877–0.943 |
Abstract
The CLDynamicLandCover is a 30 m spatial resolution dynamic land use dataset for Central Chile, covering latitudes -31.61 to -43.50. It provides land cover maps on a five-year scale from 1990 to 2018, created by a semi-automatic algorithm initially developed for the coastal sector of south-central Chile. This method was later expanded to cover areas from the southern Coquimbo region to the southern Los Lagos region.
The dataset uses a supervised classification approach with satellite data (Landsat and SRTM) to represent reflectivity and topography, and auxiliary cartographic information. It includes training points for 15 land cover classes, photointerpreted and georeferenced in 2018, to create a spectral signature for each class. Predictive variables are selected using machine learning algorithms and expert criteria.
The 2018 endmember is used to estimate the Jeffries-Matusita Distance for points from other years (1990, 1999, 2004, 2009, 2013), determining whether a pixel's land cover class changed or remained constant. A separability cutoff threshold optimizes class discrimination between years. Points below the threshold are retained (indicating no change), and those above are eliminated (indicating change). These points train a Random Forest classification model to generate land cover maps for each year.
Land trajectories were corrected based on ecological transitions and economic cost criteria, with a new classification for harvested plantations. The product shows high accuracy, with values ranging from 0.894 to 0.950 and Kappa coefficients from 0.877 to 0.943 across the years.
Resumen
El CLDynamicLandCover es un conjunto de datos dinámico de uso del suelo con una resolución espacial de 30 m para Chile Central, que cubre las latitudes -31.61 a -43.50. Proporciona mapas de cobertura de suelo en intervalos de cinco años entre 1990 y 2018, creados mediante un algoritmo semiautomático desarrollado inicialmente para el sector costero del centro-sur de Chile. Posteriormente, este método se amplió para cubrir áreas desde el sur de la región de Coquimbo hasta el sur de la región de Los Lagos.
El conjunto de datos utiliza un enfoque de clasificación supervisada con información satelital (Landsat y SRTM) para representar la reflectancia y la topografía, complementado con información cartográfica auxiliar. Incluye puntos de entrenamiento para 15 clases de cobertura de suelo, fotointerpretados y georreferenciados en 2018, con el fin de generar una firma espectral para cada clase. Las variables predictoras fueron seleccionadas mediante algoritmos de aprendizaje automático y criterios de expertos.
Se usa la Distancia Jeffries-Matusita de 2018 para los puntos de otros años (1990, 1999, 2004, 2009, 2013), determinando si la clase de cobertura de un píxel cambió o se mantuvo constante. Un umbral de separabilidad optimiza la discriminación de clases entre años: los puntos bajo el umbral se conservan (sin cambio) y los puntos sobre el umbral se eliminan (cambio). Estos puntos entrenan un modelo de clasificación Random Forest para generar los mapas de cobertura de cada año.
Las trayectorias de cambio de cobertura fueron corregidas en base a transiciones ecológicas y criterios de costo económico, incorporando además una nueva clasificación para las plantaciones cosechadas. El producto muestra una alta precisión, con valores que van desde 0.894 a 0.950 y coeficientes Kappa entre 0.877 y 0.943 a lo largo de los distintos años.
Notes
Technical info
| ID | Class Name | Description | RGB Code |
| 1 | Water bodies and channels |
Natural and artificial inland water bodies. Lakes, lagoons, waterholes and wide/accumulation sectors of rivers and streams. Includes agricultural and mining reservoirs/ponds. | 0, 92, 230 |
| 2 | Beachs, dunes and sandbanks |
Coastal and riverine beaches and dunes; inland in abandoned and/or transported dunes, sandbanks in clogged rivers and other sandy sectors at altitude. | 255, 235, 190 |
| 3 | Mediterranean sclerophyll Native Forest | Mediterranean sclerophyll forest sectors with mature native trees and dense thickets (woody plants greater than two meters in height), or with a coverage of over 80% withr espect to the Landsat grid. | 56, 168, 0 |
| 4 | Temperate Native Forest | Temperate forested sectors with mature native trees (woody plants greater than three meters in height), or with a coverage over 90% with respect to Landsat grid. | 38, 115, 0 |
| 5 | Broad leaf plantation | Forest plantations of exotic broad leaf species (mainly Eucalyptus sp.) | 255, 0, 197 |
| 6 | Fruit trees | Fruit tree plantations (fruit growing). Class generated from training points obtained from the fruit tree cadastre (vineyards, avocado, citrus, grapefruit, etc). | 200, 0, 0 |
| 7 | Glacier and snow | Snow-covered surfaces and eternal ice. | 255, 255, 255 |
| 8 | Riparian vegetation | Flooded surfaces (permanent and seasonal) covered with vegetation, adjacent to watercourses, bodies of water and water outcrops. | 0, 255, 197 |
| 9 | Shrub and bush vegetation |
Sectors covered with woody plants less than 3 meters high. Canopy projection covering from 5% to 80% with respect to Landsat grid. | 255, 120, 0 |
| 10 | Pynophyte plantation | Forest plantations of exotic acriculate and imbricate/scaly/spiral-eaved species (mainly Pinus radiata). | 115, 40, 0 |
| 11 | Grasslands, pastures and annual crops | Annual natural (un-managed) grasslands and pastures and annual irrigated and rained (non-fruit) agricultural crops. Herbaceous cover with high seasonal variation in early spring vs. late summer. | 255, 255, 0 |
| 12 | Meadows and evergreen grasslands | Managed and unmanaged evergreen grasslands and pastures. More common in southern Chile, associated with animal grazing areas. Herbaceous cover with low seasonal variation in early spring vs. late summer. | 50, 230, 0 |
| 13 | Bare soil and non-vegetated areas | Decapitated soils, excavations, landfills, roads and mine stockpiles, rocky outcrops, faults, landslides and rock slides and sectors above the altitudinal limit of vegetation. | 199, 215, 158 |
| 14 | Peatland | Soils covered by peatlands. | 104, 104, 104 |
| 15 | Impermeable surface | Surfaces covered with impervious human infrastructure: Buildings, paved roads, housing and industrial sectors. | 0, 0, 0 |
| 16 | Harvested plantation | Estimated harvested areas of tree plantations | 186, 85, 211 |
Files
Figure_1.png
Files
(763.5 MB)
| Name | Size | |
|---|---|---|
|
md5:9d629d9f7126e2e16fbc492924f7d40e
|
89.9 MB | Preview Download |
|
md5:5439379acf1f770d928adffe892f9e44
|
130.5 MB | Preview Download |
|
md5:76a58a33863a019e194865381297d3c2
|
131.6 MB | Preview Download |
|
md5:7785c2a221907b4447b953773801363a
|
133.3 MB | Preview Download |
|
md5:0eacd4cccf879ebdd817141f41c87344
|
135.7 MB | Preview Download |
|
md5:1f128323f09c618a44067c3b4b8d06d2
|
139.2 MB | Preview Download |
|
md5:cc4ad1b6977e88313c335ebed569cbd5
|
2.6 MB | Preview Download |
|
md5:ada0377429c6c78d417b60cee3178f2e
|
653.4 kB | Preview Download |
Additional details
References
- Zhao, Y., Feng, D., Yu, L., Wang, X., Chen, Y., Bai, Y. & Gong, P. (2016). Detailed dynamic land cover mapping of Chile: Accuracy improvement by integrating multi-temporal data. Remote Sensing of Environment, 183, 170- 185