ARIES for PEOPLE Explorer
The ARIES for PEOPLE Explorer is a web-based application built on the k.LAB Integrated Modelling Platform. The application has access to all information (data and models) available on the Integrated Modelling network, and provides a dedicated user interface to allow to the pilot countries to easily access and test the output of the PEOPLE-EA project, funded by the European Space Agency, and developed by the ARIES team (BC3) in collaboration with the VITO team and using the OpenEO (Open Earth Observations) platform.
At the top of the menu on the left side of the screen, you can specify the geographic area and temporal and spatial scale.
Select the year(s) for your analysis. If data are missing for a specific year of interest, ARIES automatically fills gaps using the closest available year's data
(To be confirmed given the behaviour of OpenEO UDP) |
I. Single-year analysis (uncheck the box)
II. Multi-year analysis - showing change over time (check the box)
The People EA deliverables section contains the list of the variables, in the current state of development of the project, that can be observed by simply clicking on the variable's box.
This action will trigger the model(s) underlying the variable(s) selected, in case more variables are selected, the computational flow is continuous and after the whole workflow to compute and a variable is completed, the system moves to the next tasks in the queue of computation. The models to be computed follow the order of selection of the user.
Most of the variables are modeled from different datasets, so time of computation should be similar, but in case one shares inputs used in a previous computation, those are not re-calculated, thus you should expect the additional output to be computed in less time.
There are 3 main outputs of the condition accounts:
Ecosystem Typology Group | Ecosystem Typology Class | Typology class description | Variable | Variable description and link to dataset or DOI | Spatial Resolution | Spatial Extent | Temporal resolution/ coverage |
---|---|---|---|---|---|---|---|
A. Abiotic ecosystem characteristics | A.1 Physical state | Physical descriptors of the abiotic components of the ecosystem (e.g. Soil structure, impervious surface, water availability) | A1.1 Normalized Difference Water Index | GEE MODIS Terra Daily NDWI The Normalized Difference Water Index (NDWI) is sensitive to changes in liquid water content of vegetation canopies. It is derived from the Near-IR band and a second IR band, ≈1.24μm when available and the nearest available IR band otherwise. It ranges in value from -1.0 to 1.0. See Gao (1996) for details. This product is generated from the MODIS/006/MOD09GA surface reflectance composites. | 500m | Global | Daily 2000-2023 |
A.2 Chemical state | Chemical composition of the abiotic ecosystem compartments (e.g. Soil nutrient concentration, air and water quality) | A2.1 Soil Organic Carbon | 2003 OCTOP: Topsoil Organic Carbon Content for Europe - Organic carbon content in the first 30 cm of soil | 1km | Europe | 2003 | |
2014 LUCAS: Topsoil Soil Organic Carbon (LUCAS) for EU25 - Organic carbon content in the first 30 cm of soil | 500m | Europe | 2014 | ||||
B. Biotic ecosystem characteristics | B.1 Compositional state | Composition/diversity of the ecological communities at a given location and time (e.g. Presence/abundance of key species, species richness, genetic diversity, presence of threatened species, diversity/abundance of relevant species groups) | B1.1 Threatened Forest Bird Species diversity | Population trend of bird species: datasets from Article 12, Birds Directive 2009/147/EC reporting (2008-2012) | 5km? | Europe | 2000 and 2008 |
B.2 Structural state | Aggregate properties (e.g. mass, density) of the whole ecosystem or its main biotic components (e.g. Total biomass, canopy coverage, annual maximum NDVI, Vegetation density, habitat structure, food chain and trophic levels) | B2.1 Leaf Area Index | Copernicus leaf area index The LAI quantifies the thickness of the vegetation cover and it's recognized as an Essential Climate Variable (ECV) by the Global Climate Observing System (GCOS). | 300m | Global | 2014 to present | |
1km | Global | 1999 to present | |||||
B2.2 Tree cover density | Copernicus HRL tree cover density layer It offers high-resolution information on the percentage of tree cover in a given area | 100m | Europe | 2012, 2015, 2018 | |||
B.3 Functional state | Summary statistics (e.g. frequency, intensity) of the biological, chemical, and physical interactions between the main ecosystem compartments (e.g. Primary productivity, community age, distribution frequency, decomposition processes) | B3.1 Net Primary Production | Dry Matter Productivity and Net Primary Production The ecosystem Net Primary Production (NPP) represents the net growth rate of the vegetation(excluding autotrophic respiration), expressed in kilograms of production per hectare per day (gC/m²/day). It is a proportion of Gross Primary Production and it's directly related to ecosystem Dry Matter Productivity, expressed in kgNPP/ha/day. | 300m | Global | 2014 to 2020 | |
1km | Global | 1999 to 2020 | |||||
B3.2 Drought Severity | Self-calibrating Palmer Drought Severity Index (scPDSI): The scPDSI metric was introduced by Wells et al. (2004), who gave detailed information about its calculation. The scPDSI is a variant of the original PDSI of Palmer (1965), with the aim to make results from different climate regimes more comparable. As with the PDSI, the scPDSI is calculated from a time series of precipitation and temperature, together with fixed parameters related to the soil/surface characteristics at each location. https://crudata.uea.ac.uk/cru/data/drought/#global | 0,5 degree | Global | Annual / 1998 to 2018 | |||
B3.3 Green index | |||||||
B3.4 Drought Severity (2nd variable) | Combined drought indicator (v3) - A combination of spatial patterns of precipitation, soil moisture, and greenness vegetation anomalies, the CDI identifies areas at risk of agricultural drought. | 5 km | Europe | 10 day observations 2012-2023 | |||
B3.5 Normalized Difference Vegetation Index | https://land.copernicus.eu/global/products/ndvi The Normalized Difference Vegetation Index (NDVI) is an indicator of the greenness of the biomes. | 300m | Global | 3 day observations 2020 to present | |||
1km | Global | 3 day observations 1998 to 2020 | |||||
B3.6 Burned severity | |||||||
B3.7 Fire occurrence | |||||||
C. Landscape level characteristics | C.1 Landscape and seascape at coarse scale | Metrics describing mosaics of ecosystem types at coarse (such as landscape and seascape) spatial scale (e.g. Landscape diversity, connectivity, fragmentation, ecosystem type mosaics) | C1.1 Forest Fragmentation | Relative Magnitude of Fragmentation (RMF) Global remote-sensing data product (i.e. the 27-year annual ESA CCI land cover maps which can be categorized as an EBV ‘Ecosystem Distribution’) | 300m | Global | Annual 1992-2020 |
C1.2 Forest Connectivity | Generated using GUIDOS toolbox and Corine landcover daatset - Methodology | 100m | Europe | 2000, 2006, 2012, 2018 | |||
C1.3 Landscape Naturalness | Generated using GUIDOS toolbox and Corine landcover daatset - Methodology | 100m | Europe | 2000, 2006, 2012, 2018 |
Each variable is scaled between 0 and 1, with values getting closer to 1 as the forest conditions improve.
This allows each indicator to represent in a consistent way the information coming from the variables, which in their original values have different ranges but also different interpretation of such values, and not always higher value are associated to better conditions (e.g. if we look at variable like Drought Severity or Forest Fragmentation, the higher the value, the worse the forests conditions).
There are 7 indicators available in the application:
These areas are used to identify forest considered in good health, so as to define the upper reference values of that variable. Forests considered in good conditions (the upper reference areas) must meet the following criteria:
Such criteria are observed based on the information of the following datasets:
Results are obtained combining the following inputs by using, as consistently as possible, the year 2000 as the reference year, with exception of the information on the Tree-cover density, whose earliest observation is in the year 2012.
Whenever a forest lacks to meet any of the listed criteria, it was not considered as an area of reference for good condition.
European forests have been initially categorized based on their landcover forest class, as per the Corine dataset, which distinguishes 4 types of forest:
Such categories of forest were also combined with the information on the European bioregion zones, used to define 11 bioregions over:
The Scandinavian Alpine zone was differentiate from the rest of the Alpine bioregion for its characteristics, and covers the forest in the Scandinavian mountains on the border between Norway and Sweden.
The combination of landcover forests and bioregions results in 44 forest types, following the definition of Maes, J., Bruzón, A.G., Barredo, J.I. et al. Accounting for forest condition in Europe based on an international statistical standard. Nat Commun 14, 3723 (2023).- https://doi.org/10.1038/s41467-023-39434-0
The following datsets were used to obtain this information:
The percentile computed define the thresholds used to rescale the observed variables values into indicators ranging from 0 to 1.
Xi = (Xobserved - XLowerReference) / (XUpperReference - XLowerReference)
This section shows the most relevant spatial inputs and outputs in the account(s) run by the user
(e.g., in the case of ecosystem extent, the most relevant outputs are land cover and ecosystem type data).
The last section stores all tables and maps produced in that session, so that the user can download them in a zipped file (of Excel spreadsheets or GeoTIFFs) before leaving the application.
In the upper left corner of the application, there is a section dedicated to SEEA-relevant indicators.
This section includes selected indicators from the Sustainable Development Goals (SDGs) and the Convention on Biology Diversity (CBD) Post-2020 Biodiversity Indicators, which have been added to the application.
Once it is opened, a drop-down menu shows the list of available indicators.
Those selected by the user are added in the ARIES for SEEA panel as if they were an additional standard SEEA EA account
Aspects of the user interface change once you begin to run an accounting model:
The third tab available once a model has run is the Dataflow view
This shows a diagram that visually summarize each model component and how those were combined to obtain the final result(s). Clicking on an individual rectangle provides details about the dataset, algorithm, etc. used at each step of the model.This subsection explains how ARIES spatializes tabular national statistical data and aggregates it through spatial modelling, using crop provisioning as an example. The problem can be framed as follows:
The method implemented follows:
(1): Production table (reference)
(2): Production data from statistical aggregates (in reference year)
(3): Crop production map (spatial data in reference year)
(4): Production data from any year
Note that 2 and 4 must come from to the same data source (apply the same methodology), in order to generate spatialized crop production in time series.
The models only estimates the reallocation of such production, the biophysical production comes from statistical aggregate
This approach assumes crop extent to be constant (based on spatial data for the reference year), with only crop yield (tons produced per hectare) changing over time - an assumption we know to be false, but that a lack of time series spatial data based on subnational crop production forces us to accept, for now. Increases or decreases in production are thus spread across the whole country, rather than for that specific (but unknown) areas. The approach can be improved significantly with:
While most of the functions needed to compile SEEA accounts are available through ARIES for SEEA interface, the normal functionalities of the ARIES Explorer remain available through the search bar.
This sections shows how to query them.
Context:
Zoom in (by clicking on the ) and out (
). This can be useful when selecting your context using map boundaries (entire rectangle shown in the interface) or administrative regions or river basins, which change as a user zooms and pans the map.
Additional features that will be made available in future releases of ARIES for SEEA include:
Need to add a final page with an about section where we acknowledge EU funding.
May be also add a contact (email address) such as support@integratedmodelling.org