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Remote Sensing
  • Editorial
  • Open Access

12 May 2022

Editorial for Special Issue: “New Insights into Ecosystem Monitoring Using Geospatial Techniques”

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1
Italian National Institute for Environmental Protection and Research (ISPRA), Via Vitaliano Brancati 48, 00144 Roma, Italy
2
IHCantabria—Instituto de Hidráulica Ambiental, Universidad de Cantabria, PCTCAN, C/Isabel Torres 15, 39011 Santander, Spain
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Department of Geography, Simon Fraser University, 8888 University Drive, Burnaby, BC V5A 1S6, Canada
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Laboratory LETG-Brest, Géomer, UMR 6554 CNRS, IUEM UBO, 29200 Brest, France
This article belongs to the Special Issue New Insights into Ecosystem Monitoring Using Geospatial Techniques

1. Introduction

Recent global-scale environmental issues from climate change to biodiversity loss are generating an intense social pressure on the scientific community [1]. A growing need for information on environmental topics with appropriate reliability and suitable spatial scalability (from local to global analysis and vice versa) is spreading among societies [2].
The availability of huge amounts of environmental data allows the use of advanced analytic techniques that can provide useful information from a variety of large datasets, including those observing and measuring the ecosystem processes in response to environmental drivers [3]. A multidisciplinary approach, including artificial intelligence, big data analytics, and ecological modelling, is highly recommended to interpret ecological processes and identify adequate solutions for the environmental issues of the Anthropocene [4]. However, the use of big data today generated by different sources represents a big challenge, from detailed analysis on specific topics or geographic areas to issues at wider scales and over broader timescales [5].
Earth Observation (EO) data acquired by satellite sensors offer new opportunities for the ecology sciences and are revolutionizing the methodologies applied, from experimental/theoretical to computational science [6], projecting big data from space in the mainstream of ecological analysis.
It is therefore easily foreseeable that, in the next decades, new technologies will affect the activities on ecosystem survey, mapping, and monitoring, opening a new era. The reasons are first linked to the requirements of global, continental, and national policies on the environment sustainability, such as those stated in the 2030 Agenda for Sustainable Development, that gave a new stimulus to improve ecological research in this direction [7,8]. The increasing demand from national institutions for updated information to monitor ecosystems and detect their changes in time and space plays a crucial role in demonstrating mapping products as an essential tool for biodiversity assessments [9]. Indeed, in the light of “Biological Diversity” concept (see Convention on Biological Diversity: https://www.cbd.int/convention/text/ (accessed on 1 May 2022)), habitats are cardinal pieces for quantitative estimations of biodiversity at local and global scales. They are basic units of ecosystems and biomes identified by abiotic environmental factors, such as climate, geomorphology, pedology, as well as by plant species composition (i.e., vegetation units) [10].
In this direction, this Special Issue aims to compile research papers dealing with both methodologies of remote sensing and implementation of research results to facilitate the environmental monitoring, using geospatial techniques, in several ecosystems (e.g., wetland, coastal, estuarine, forest, shrubland, and alpine grasslands) or for land use and land cover (LULC) changes analysis. Altogether, in this Special Issue, nine papers are published, and the results obtained are implemented along two continents, using remote sensing platforms such as Landsat (i.e., 5TM, 7ETM+ and 8OLI), Sentinel (2A/2B MSI), World-View, and SPOT 5 imageries or hyperspectral imagery from proximal sensors by airborne vehicles (i.e., helicopter). Among the methods used to process the remotely sensed data, the increasing focus on the use of machine learning algorithm models such as Random Forests (RF), Support Vector Machine (SVM), Linear Regression (LR), Convolutional Neural Network (CNN), and Deep Learning (DL) classifier is noteworthy. In Table 1, the key message of all published papers is summarized. More detailed information on each article published in this Special Issue is given below in order of the publication date.
Table 1. Topics and main findings covered in the Special Issue on “New Insights into Ecosystem Monitoring Using Geospatial Techniques”.

2. Overview of Contributions

The follow is the synthesis of results obtained in each paper published in the SI “New Insights into Ecosystem Monitoring Using Geospatial Techniques”.
G. Hernández-Romero et al. [11] introduced a study aiming at applying an RS framework useful to identify suitable locations related to the conservation and restoration of natural forests in hillslopes and riparian areas. The combination of information about LULC dynamics, wetland distribution, and erosion processes has allowed establishing an innovative spatially explicit RS-based workflow that allows addressing potential ecological and hydrological problems of wetlands in mountainous environments by using nature-based solutions related to forest ecosystems.
Mapping species-specific chlorophyll content in a heterogeneous grassland using high-spatial resolution hyperspectral images was investigated in a study by B. Lu et al. [12]. This research aimed to better retrieve vegetation chlorophyll content of different species. Overall, the utilization of species-specific models is recommended for mapping vegetation properties in heterogeneous ecosystems.
The research of G. Xie et al. [13] was aimed to study multiannual changes in LCLU in the Crozon Peninsula, an area that has mainly been marked by conversion between three types of LCLU, i.e., cropland, urban, and vegetation, in recent years, especially from 2007 to 2018. The challenge of this research was to deal with multiannual changes of a coastal area with different shapes and patterns by combining machine learning methods with PCC. Although high classification accuracy was observed, several uncertainties and limitations persisted, such as misclassification: classifications were based on images with different spatial resolutions, cloud-free satellite images during the growing season. Hence, some recommendations can be made for further studies, such as applying more vegetation indices or using hyperspectral images and exploring the synthetic-aperture radar images.
The goal of the study of J. C. Bernier et al. [14] was to provide a comprehensive analysis of recent landscape-scale changes along the northern Chandeleur Islands using a consistent dataset and methodology to better understand temporal and spatial variability in barrier response to natural and anthropogenic disturbances over the past few decades. The results presented in this study demonstrate that automated thresholding algorithms can be applied to multiple spectral indices derived from medium-resolution Landsat satellite imagery to rapidly delineate land-cover classes and barrier-island extents at the landscape scale.
In K. Mikula et al. [15], it was presented that the NaturaSat software aims to integrate image-processing knowledge and various techniques together with vegetation science, into one multipurpose tool that is designed for performing facilities for all the requirements of habitat exploration in one place. The results obtained show that NaturaSat software implements new powerful tools, such as the semi-automatic and automatic segmentation RS imageries methods and natural numerical networks. It is robust enough for vegetation scientists and nature conservationists to accurately extract target units’ borders, even at the habitat level.
With the introduction of high-resolution satellite imagery with frequent return intervals, satellite-derived wetland shoreline data could provide the same spatial and temporal detail as other sources of data, including field-based Global Positioning System (GPS) or aerial imagery-derived shoreline data, but gain greater spatial coverage and reduce the cost of shoreline monitoring by either replacing GPS field surveys or reducing the necessity of survey frequency. K. E. L. Smith et al. [16] showed the results of a semi-automated procedure to map wetland shorelines from WV imageries and compared them to contemporaneous shoreline data from GPS and digitized aerial imagery for study sites at the Grand Bay National Estuarine Research Reserve, Moss Point, MS, USA. The availability of high-resolution satellite imagery and new developments in rapid image analysis techniques can help fill the data gap and provide critical information for coastal wetland monitoring programs.
In T. Chernenkova et al. [17], the aim of the study published was to perform a vegetation mapping and to identify coniferous forests dynamics in the central Russian Plain at the edge of large metropolis influence (case study in Moscow). This study is based on both field and remote sensing data. The results obtained will contribute to the development of plans for sustainable management and conservation of forest biodiversity under different management scenarios.
A novel approach for a spatially explicit habitat mapping of forest in Italy using a supervised machine learning model and the combination of a vegetation dataset, high resolution EO data, and environmental variables was presented by E. Agrillo et al. [18]. The obtained results could be useful for monitoring the spatial patterns of ecosystems in space and time. The approach presented will allow an information technology procedure to be sped up with annual or seasonal updating, depending on the extension of the study area and the monitoring objectives. The obtained procedures could be applied on several environmental data in order to cyclically and promptly repeat spatial analysis to detect changes in space and time in support of ecosystem conservation issues, especially to evaluate the impact of illegal actions (e.g., forest harvesting) or natural hazards (e.g., destructive storms or other natural disasters) on habitat distribution.
N. Alessi et al. [19] presented a fuzzy classification of terrestrial ecosystems in a mountain environment. Using different remotely sensed indices, the authors use an unsupervised clustering to implement a temporal comparison among clustered pixels. The obtained clusters were assigned to terrestrial ecosystems based on ground observation of vegetation. The study reports an increase in the forested area to the detriment of grassland, and an expansion of ice-free area due to the retreat of the mountain glacier. The presented approach allows monitoring terrestrial ecosystems in space and time based on their characteristic spectral signal.
All the above-mentioned studies confirm the great potential of using geospatial techniques for ecosystem monitoring. We hope that the results and findings shown here will encourage further research and the land managers of the importance and benefits of better integration of remote sensing data on operational monitoring and surveillance of ecosystems.

Author Contributions

Conceptualization, E.A.; writing—review and editing, E.A., N.A., J.M.Á.-M., L.C., F.F., B.L., S.N., M.Š. and K.E.L.S. All authors have read and agreed to the published version of the manuscript.

Funding

This research received no external funding.

Data Availability Statement

Not applicable.

Acknowledgments

As the Guest Editors, we would like to thank all the authors who accepted the challenge to share their research results and ideas in this Special Issue. Special thanks to all anonymous reviewers involved in the SI and helped the authors to improve their manuscripts. Thanks also to the editorial staff of Remote Sensing for supporting the idea of this SI. Furthermore, special thanks to Vladimir Maksimović for helping to spread the message and pressing us to publish during the COVID-19 pandemic.

Conflicts of Interest

The authors declare no conflict of interest.

References

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