WBF2026-672, updated on 10 Mar 2026
https://doi.org/10.5194/wbf2026-672
World Biodiversity Forum 2026
© Author(s) 2026. This work is distributed under
the Creative Commons Attribution 4.0 License.
Oral | Tuesday, 16 Jun, 09:30–09:45 (CEST)| Room Jakobshorn
Opportunities and challenges for near-term ecological forecasting with biodiversity and EO data
Patrícia Singh1,2, Billur Bektas3,4, Sanne Evers5, Erola Fenollosa6, Gerbrand Koren7, Sruthi Krishna Moorthy Parvathi6, Sean Pang6, Maria Paniw5, Damien Robert8, Ghjulia Sialelli9,10, Jasper Slingsby11, Rachael Thornley6, Emma L Underwood12, Jan Dirk Wegner8, and Wanben Wu13
Patrícia Singh et al.
  • 1Department of Botany and Zoology, Masaryk University, Brno, Czechia (patadurcanova@gmail.com)
  • 2Institute for Biochemistry and Biology, University of Potsdam, Potsdam, Germany (patadurcanova@gmail.com)
  • 3Department of Environmental Systems Science, ETH Zurich, Zürich, Switzerland (billur.bektas@usys.ethz.ch)
  • 4Institute of Integrative Biology, ETH Zurich, Zurich, Switzerland (billur.bektas@usys.ethz.ch)
  • 5Department of Conservation Biology and Global Change, Doñana Biological Sation, Sevilla, Spain (sanne.m.evers@gmail.com)
  • 6Department of Biology, University of Oxford, Oxford, United Kingdom (erola.fenollosaromani@biology.ox.ac.uk)
  • 7Copernicus Institute of Sustainable Development, Utrecht University, Utrecht, Netherlands (g.b.koren@uu.nl)
  • 8Department of Mathematical Modeling and Machine Learning, University of Zurich, Zurich, Switzerland (damien.robert@uzh.ch)
  • 9Photogrammetry and Remote Sensing, ETH Zurich, Zurich, Switzerland (gsialelli@ethz.ch)
  • 10ETH AI Center, ETH Zurich, Zurich, Switzerland (gsialelli@ethz.ch)
  • 11Department of Biological Sciences, University of Cape Town, Cape Town, South Africa (jasper.slingsby@uct.ac.za)
  • 12Department of Geography, Geology and the Environment, Kingston University London, London, United Kingdom (emma.underwood@kingston.ac.uk)
  • 13Department of Biology, Aarhus University, Aarhus, Denmark (wanben.wu@bio.au.dk)

Near-term ecological forecasting offers a powerful early-warning system for ecological change, enabling proactive and adaptive management. Yet the ability to generate accurate, real-time forecasts remains limited. Although ecological monitoring and retrospective analyses have advanced rapidly, forecasting is still constrained by the scarcity of biodiversity datasets that provide frequent and standardized observations from the same locations.

Global biodiversity aggregators—such as the Global Biodiversity Information Facility and the Ocean Biodiversity Information System—and their sources provide invaluable broad-scale information, but their records are typically opportunistic and infrequently revisited, making them better suited to retrospective analyses than to near-term forecasting. Closing this gap requires collaboration with local data providers (e.g., national parks, protected areas, long-term monitoring networks) and the development of coordinated, open-access biodiversity monitoring infrastructures across larger spatial scales. Initiatives such as the Global Ecosystem Research Infrastructure, the Group on Earth Observations Biodiversity Observation Network and BioTime represent important but still underutilized foundations.

Earth observation (EO) data can help bridge several of these limitations by offering spatially synchronized measurements, high temporal resolution, and near-real-time environmental information. However, EO alone cannot generate ecological predictions. The most promising path forward lies in integrating frequently updated biodiversity observations with real-time EO indicators to build automated, transferable, and scalable forecasting pipelines. Cloud-based EO platforms (e.g., Google Earth Engine, WEkEO, CREODIAS) enable reproducible environmental data processing, while modern automation tools (e.g., GitHub Actions, Cron jobs) make continuous model updating feasible. Interactive, user-centred dashboards then provide accessible pathways for communicating forecasts.

Despite progress, challenges persist: biodiversity monitoring remains spatially uneven, temporal resolution is often insufficient, and forecasting systems lack standardized validation frameworks, robust uncertainty communication, and sustained software engineering support. Overcoming these barriers requires interoperable infrastructures that integrate biodiversity monitoring, EO processing, automated forecasting, and forecast dissemination.

Building such systems—grounded in INSPIRE and FAIR data principles—is essential for achieving the near-term ecological forecasting capacity needed to meet global policy commitments, including the Kunming–Montreal Global Biodiversity Framework and the Sustainable Development Goals. Strengthening the connections among local biodiversity monitoring, EO-derived indicators, and automated forecasting pipelines will substantially enhance our ability to anticipate ecological change and deliver timely, evidence-based guidance for conservation and resilience planning.

How to cite: Singh, P., Bektas, B., Evers, S., Fenollosa, E., Koren, G., Moorthy Parvathi, S. K., Pang, S., Paniw, M., Robert, D., Sialelli, G., Slingsby, J., Thornley, R., Underwood, E. L., Wegner, J. D., and Wu, W.: Opportunities and challenges for near-term ecological forecasting with biodiversity and EO data, World Biodiversity Forum 2026, Davos, Switzerland, 14–19 Jun 2026, WBF2026-672, https://doi.org/10.5194/wbf2026-672, 2026.