Monitoring Green Infrastructure for Natural Water Retention Using Copernicus Global Land Products

Nature-based solutions are increasingly relevant tools for spatial and environmental planning, climate change adaptation (CCA), and disaster risk reduction (DRR). For this reason, a wide range of institutions, governments, and financial bodies are currently promoting the use of green infrastructure (GI) as an alternative or a complement to traditional grey infrastructure. A considerable amount of research already certifies the benefits and multi-functionality of GI: natural water retention measures (NWRMs), as GIs related specifically to the water sector are also known, are, for instance, a key instrument for the prevention and mitigation of extreme phenomena, such as floods and droughts. However, there are persisting difficulties in locating and identifying GI and one of the most promising solutions to this issue, the use of satellite-based data products, is hampered by a lack of well-grounded knowledge, experiences, and tools. To bridge this gap, we performed a review of the Copernicus Global Land Service (CGLS) products, which consist of freely-available bio-geophysical indices covering the globe at mid-to-low spatial resolutions. Specifically, we focused on vegetation and energy indices, examining previous research works that made use of them and evaluating their current quality, aiming to define their potential for studying GI and especially NWRMs related to agriculture, forest, and hydro-morphology. NWRM benefits are also considered in the analysis, namely: (i) NWRM biophysical impacts (BPs), (ii) ecosystem services delivered by NWRMs (ESs), and (iii) policy objectives (POs) expressed by European Directives that NWRMs can help to achieve. The results of this study are meant to assist GI users in employing CGLS products and ease their decision-making process. Based on previous research experiences and the quality of the currently available versions, this analysis provides useful tools to identify which indices can be used to study several types of NWRMs, assess their benefits, and prioritize the most suitable ones.

[1]  S. Stehman,et al.  Validation of the 2008 MODIS-MCD45 global burned area product using stratified random sampling , 2014 .

[2]  Gérard Dedieu,et al.  Assessment of an Operational System for Crop Type Map Production Using High Temporal and Spatial Resolution Satellite Optical Imagery , 2015, Remote. Sens..

[3]  J. Pekel,et al.  High-resolution mapping of global surface water and its long-term changes , 2016, Nature.

[4]  Frédéric Baret,et al.  GEOV1: LAI and FAPAR essential climate variables and FCOVER global time series capitalizing over existing products. Part1: Principles of development and production , 2013 .

[5]  Stephan Pauleit,et al.  Planning multifunctional green infrastructure for compact cities: What is the state of practice? , 2017, Ecological Indicators.

[6]  Baofeng Su,et al.  Significant Remote Sensing Vegetation Indices: A Review of Developments and Applications , 2017, J. Sensors.

[7]  Andrea Taramelli,et al.  Earth Observation for Maritime Spatial Planning: Measuring, Observing and Modeling Marine Environment to Assess Potential Aquaculture Sites , 2016 .

[8]  M. Suškevičs Legitimate planning processes or informed decisions? Exploring public officials' rationales for participation in regional green infrastructure planning in Estonia , 2019, Environmental Policy and Governance.

[9]  Sandra C. Freitas,et al.  Land surface temperature from multiple geostationary satellites , 2013 .

[10]  P. Strosser,et al.  A guide to support the selection, design and implementation of Natural Water Retention Measures in Europe. Capturing the multiple benefits of nature-based solutions , 2015 .

[11]  H. Laudon,et al.  Cost of riparian buffer zones: A comparison of hydrologically adapted site‐specific riparian buffers with traditional fixed widths , 2016 .

[12]  Jane Elith,et al.  Green Infrastructure Design Based on Spatial Conservation Prioritization and Modeling of Biodiversity Features and Ecosystem Services , 2015, Environmental Management.

[13]  R. Lafortezza,et al.  Transitional path to the adoption of nature-based solutions , 2019, Land Use Policy.

[14]  Bernhard Geiger,et al.  Land Surface Albedo Derived on a Daily Basis From Meteosat Second Generation Observations , 2008, IEEE Transactions on Geoscience and Remote Sensing.

[15]  Stefan Schindler,et al.  Multifunctionality of floodplain landscapes: relating management options to ecosystem services , 2014, Landscape Ecology.

[16]  Diego González-Aguilera,et al.  HidroMap: A New Tool for Irrigation Monitoring and Management Using Free Satellite Imagery , 2018, ISPRS Int. J. Geo Inf..

[17]  J. Monteith SOLAR RADIATION AND PRODUCTIVITY IN TROPICAL ECOSYSTEMS , 1972 .

[18]  F. Kogan Remote sensing of weather impacts on vegetation in non-homogeneous areas , 1990 .

[19]  COMMUNICATION FROM THE COMMISSION TO THE EUROPEAN PARLIAMENT, THE COUNCIL, THE EUROPEAN ECONOMIC AND SOCIAL COMMITTEE AND THE COMMITTEE OF THE REGIONS , 2008 .

[20]  Andrea Taramelli,et al.  Global MODIS Fraction of Green Vegetation Cover for Monitoring Abrupt and Gradual Vegetation Changes , 2018, Remote. Sens..

[21]  W. Wagner,et al.  A Method for Estimating Soil Moisture from ERS Scatterometer and Soil Data , 1999 .

[22]  Martina Artmann,et al.  How smart growth and green infrastructure can mutually support each other — A conceptual framework for compact and green cities , 2017, Ecological Indicators.

[23]  C. Albergel,et al.  From near-surface to root-zone soil moisture using an exponential filter: an assessment of the method based on in-situ observations and model simulations , 2008 .

[24]  J. C. Taylor,et al.  Real-time vegetation monitoring with NOAA-AVHRR in Southern Africa for wildlife management and food security assessment , 1998 .

[25]  L. Boschetti Modis collection 5.1 burned area product - mcd45. User’s guide version 3.0.1 , 2013 .

[26]  Andrea Taramelli,et al.  A Hybrid Power Law Approach for Spatial and Temporal Pattern Analysis of Salt Marsh Evolution , 2017, Journal of Coastal Research.

[27]  J. Pereira,et al.  Vegetation burning in the year 2000: Global burned area estimates from SPOT VEGETATION data , 2004 .

[28]  Brian E. Robinson,et al.  Using ecosystem service trade‐offs to inform water conservation policies and management practices , 2016 .

[29]  J. A. Schell,et al.  Monitoring vegetation systems in the great plains with ERTS , 1973 .

[30]  Emily Wheeler,et al.  Ecosystems as infrastructure , 2017 .

[31]  S. Stehman,et al.  Stratification and sample allocation for reference burned area data , 2017 .

[32]  Hector Nieto,et al.  Evapotranspiration estimates derived using thermal-based satellite remote sensing and data fusion for irrigation management in California vineyards , 2018, Irrigation Science.

[33]  Sindy Sterckx,et al.  Evaluation of the SPOT/VEGETATION Collection 3 reprocessed dataset: Surface reflectances and NDVI , 2017 .

[34]  M. Lennon,et al.  Green infrastructure and planning policy: a critical assessment , 2015 .

[35]  Nicolás Velásquez Girón,et al.  Evaluation of existing relations between convective systems and extreme events in tropical catchments of the Andean region , 2020 .

[36]  Emily Nicholson,et al.  The role of satellite remote sensing in structured ecosystem risk assessments. , 2018, The Science of the total environment.

[37]  Marc Padilla,et al.  Assessing the Temporal Stability of the Accuracy of a Time Series of Burned Area Products , 2014, Remote. Sens..

[38]  Clement Atzberger,et al.  First Experience with Sentinel-2 Data for Crop and Tree Species Classifications in Central Europe , 2016, Remote. Sens..

[39]  F. Baret,et al.  GEOV1: LAI, FAPAR essential climate variables and FCOVER global time series capitalizing over existing products. Part 2: Validation and intercomparison with reference products , 2013 .

[40]  M. Pérez-Soba,et al.  Mainstreaming ecosystem services into EU policy , 2013 .

[41]  S. Stehman,et al.  Comparing the accuracies of remote sensing global burned area products using stratified random sampling and estimation , 2015 .

[42]  L. Fusaro,et al.  Regulating Ecosystem Services and Green Infrastructure: assessment of Urban Heat Island effect mitigation in the municipality of Rome, Italy , 2019, Ecological Modelling.

[43]  B. Grizzetti,et al.  Mapping ecosystem services for policy support and decision making in the European Union , 2012 .

[44]  Richard C. Thompson,et al.  From ocean sprawl to blue-green infrastructure – A UK perspective on an issue of global significance , 2019, Environmental Science & Policy.

[45]  Urban green indicators: a tool to estimate the sustainability of our cities , 2019, International Journal of Design & Nature and Ecodynamics.

[46]  C. Polce,et al.  Spatial alternatives for Green Infrastructure planning across the EU: An ecosystem service perspective , 2018 .

[47]  E. J. Cilliers,et al.  Reflecting on Green Infrastructure and Spatial Planning in Africa: The Complexities, Perceptions, and Way Forward , 2019, Sustainability.

[48]  S. W. Maier,et al.  Estimating the area of stubble burning from the number of active fires detected by satellite , 2007 .

[49]  A. Huete,et al.  A review of vegetation indices , 1995 .

[50]  Virgilio Hermoso,et al.  Designing a network of green infrastructure to enhance the conservation value of protected areas and maintain ecosystem services. , 2019, The Science of the total environment.

[51]  John W. Jones,et al.  Satellite remote sensing estimation of river discharge: Application to the Yukon River Alaska , 2018, Journal of Hydrology.

[52]  Jean-Louis Roujean,et al.  Comparing Operational MSG/SEVIRI Land Surface Albedo Products From Land SAF With Ground Measurements and MODIS , 2010, IEEE Transactions on Geoscience and Remote Sensing.

[53]  Wolfgang Jentner,et al.  Visualization and Visual Analytic Techniques for Patterns , 2019, Studies in Big Data.

[54]  F. Kogan Operational Space Technology for Global Vegetation Assessment , 2001 .

[55]  David Hernández-López,et al.  Scalable pixel-based crop classification combining Sentinel-2 and Landsat-8 data time series: Case study of the Duero river basin , 2019, Agricultural Systems.

[56]  J. Grégoire,et al.  A new, global, multi‐annual (2000–2007) burnt area product at 1 km resolution , 2008 .

[57]  Frédéric Baret,et al.  Near Real-Time Vegetation Monitoring at Global Scale , 2014, IEEE Journal of Selected Topics in Applied Earth Observations and Remote Sensing.