Can We Teach AI to See the World the Way Animals Do?

New paper proposes using deep learning to collect richer ecological data, with the aim of better predicting how ecological communities change.

For decades, ecology has been very good at explaining the past. We can look at a collapsed fishery, a vanished pollinator population, or a coral reef bleaching event and piece together, after the fact, what went wrong. What ecology has struggled to do, and what it needs to get better at, is predicting these changes before they happen.

Conservation policymakers don’t just need to understand why an ecosystem collapsed last year. They need to know what will happen if we build a road through a forest, dam a river, or let a new pesticide into widespread use, before those decisions are made, not after the damage is done.

A new method paper by C. J. M. Musters and Geert R. de Snoo of Leiden University, published in Individual-based Ecology, explores whether combining deep learning with this individual-based framework could offer a way forward. They propose: closing the prediction gap requires not just better data, but an entirely different kind of data – and possibly, machines that sense the world the way animals do. 

Why Predicting Ecosystems Is So Hard

Ecological communities are dazzlingly complex. Every organism in a habitat is constantly responding to its environment and to every other organism around it, like competing for food, avoiding predators, seeking mates, adjusting behavior with the seasons. Traditional ecology often simplifies this complexity by grouping organisms into species-level categories. 

Ecosystem illustration
Example of an ecosystem. Credit to goodstudio via Canva.

Musters and de Snoo point to the work of ecologist John Lawton, who argued that this kind of unpredictability is strongest at “intermediate” scales – not in small populations of a single species, not across whole biomes, but somewhere in between. The authors define this middle ground as spaces of roughly 1 to 1,000,000 km² over 10 to 100 years. Unhelpfully, that’s also roughly the scale at which conservation decisions actually get made. 

Organism-based Ecology or Individual-based Ecology takes a different starting point. Instead of assuming species behave as uniform units, it treats individual organisms as the fundamental actors whose actions and interactions generate the patterns we see in ecosystems. That’s a more realistic picture – but also a far more complicated one. Communities become vast networks of individual organisms, each constantly gathering and responding to information from their surroundings and from each other. 

Where Deep Learning Comes In 

 Binary code
Binary codes. Credit to RDGraphics via Canva.

Deep learning (DL), the technology behind everything from image recognition to language models, is extraordinarily good at finding patterns in complex data. In principle, DL combined with organism-based ecology, the study of how individual organisms behave and interact, could be used to build models that predict how a community will shift as conditions change.

However, deep learning is only as good as the data you feed it, and the data ecology currently collects wasn’t designed with this goal in mind.

Traditional ecological datasets tend to record outcomes: population counts, species distributions, migration patterns. What they largely fail to capture is something more fundamental – the raw sensory information that organisms actually use to make decisions. A bird doesn’t respond to “average temperature over the season.” It responds to what it can see, smell, hear, and feel, moment to moment, in its environment.

Schematic
Flow diagram of the first three time-steps of a Recurrent Neural Network to predict changes in the state of community.  Credit to Musters & de Snoo GR, 2026.

If deep learning models are going to predict how organisms actually behave and interact, the authors argue, they need training data that reflects what the organisms themselves are sensing rather than just retrospective statistics ecologists usually collect. 

Building “Artificial Sense Organs” for Ecology

To generate that new kind of data, Musters and de Snoo propose building sensory instruments that mimic the sense organs of the organisms themselves – broad-spectrum devices that continuously and non-invasively record the same signals animals, plants, fungi, and microbes use to make decisions. Paired with existing tools like camera traps, biologging, satellite imagery, and environmental DNA sampling, this could generate the rich, organism-centered datasets that deep learning models actually need. 

A Call for Caution

Deep Learning models are black boxes, even when their predictions are accurate, it’s often unclear why. Models trained on incomplete or biased data can generate ecologically impossible results, like population sizes that go negative. 

Also, models trained largely on data from wealthy, well-studied regions could embed cultural assumptions that don’t transfer elsewhere. The authors offer a vivid example, Black-tailed Godwits are cherished in the Netherlands but considered agricultural pests in parts of West Africa, where they feed on rice rather than soil invertebrates. Applying a European-trained model globally, without care, risks a kind of “unintentional colonialism” in conservation decision-making. 

In their method paper, the authors are clear, that the models they describe don’t exist yet, and that building them will require new instruments, new interdisciplinary collaboration between ecologists and ethologists, and  critically explicit, published testing of where these models work and where they don’t. What they’re offering instead is a roadmap, by starting small, building sensory prototypes, training experimental models on well-studied plots, and rigorously checking every prediction against reality before trusting it with real conservation decisions. 

Whether “artificial sense organs” turn out to be the right way to get there remains to be seen. But the underlying challenge – teaching machines to understand ecosystems well enough to predict their future – is one of the more important questions facing conservation science today. 

Original source:

Musters CJM, de Snoo GR (2026) Challenges and opportunities for Artificial Intelligence for predicting changes in ecological communities. Individual-based Ecology 2: e199762. https://doi.org/10.3897/ibe.2.199762 

GBIF Marks 25 Years of FAIR Biodiversity Data, Now Spanning 70 Countries and 3.8 Billion Records

As GBIF marks 25 years and 3.8 billion records across 70 countries, a new overview looks ahead – tackling data gaps to shape the next quarter-century.

Digital biodiversity data has come a long way. Twenty-five years ago, the Global Biodiversity Information Facility (GBIF) launched with 21 founding countries and a simple but ambitious goal: make the world’s biodiversity data freely and openly available to anyone, anywhere.

Today, GBIF’s network includes 70 participating countries, along with data providers across more than 120 countries, offering open access to over 3.8 billion biodiversity data records. This milestone is explored in a new overview article published in the Biodiversity Data Journal, which traces GBIF’s trajectory over the past quarter-century and the challenges that remain as it looks ahead.

GBIF Executive Secretary Dr. Joe Miller remarked:

As GBIF celebrates its 25th anniversary, I’m very proud to serve as Executive Secretary of the organisation and to have contributed to this milestone publication. Detailing the history of GBIF both as an infrastructure and a global network, the article pays tribute to all the people involved in the network throughout a quarter century—be they staff, participants, nodes, volunteers, data publishers or data users. It represents the past, present and future of GBIF. I believe the paper will help strengthen our network and its capacity to respond to biodiversity data needs both now and in the future.

GBIF was established in 2001, following a proposal from the Organisation for Economic Cooperation and Development’s Megascience Forum which concluded that “an international mechanism is needed to make biodiversity data and information accessible worldwide”.

The call came in response to a problem facing the international community after the 1992 Rio Earth Summit: the world’s biodiversity knowledge was scattered across a small number of institutions, concentrated in wealthy countries, with no shared way to bring it together in support of the newly signed Convention on Biological Diversity.

Now, a quarter-century later, GBIF has become the foundational infrastructure for biodiversity science and policy worldwide.

A Growing Global Network

Biodiversity data in GBIF
Annual biodiversity data made available through the Global Biodiversity Information Facility as of July 2026. Credit to GBIF.

GBIF’s work is carried out through a distributed network of 47 voting country participants and 42 organisational participants, each represented by a national or thematic “node” that mobilises data, builds local capacity, and connects biodiversity communities to GBIF’s infrastructure. More than 2,700 institutions, including museums, universities, government agencies, citizen science platforms, and a growing number of private-sector organisations, have published data through the network, with new publishers joining at a rate of more than two every three days, totalling nearly 3500 organisations involved.

key numerical metrics of the Global Biodiversity Information Facility
Infographic summary of key numerical metrics of the Global Biodiversity Information Facility as of August 2026. See dynamic metrics at GBIF.org and at https://www.gbif.org/analytics/global.

The Biodiversity Data Journal itself is one example of this network in action, as it operates its own GBIF-hosted data portal – one of more than 20 such portals across Pensoft-published journals – providing direct access to hundreds of datasets and hundreds of thousands of occurrence records drawn from the journal’s publications.

Data Supporting Science and Policy

GBIF data mediation
The universe of GBIF data mediation.

GBIF-mediated data now underpin an average of eight new peer-reviewed research papers per day, and have contributed to more than 15,000 publications to date, spanning fields from climate change and food security to public health and invasive species management. An independent 2023 assessment estimated that GBIF generates roughly €12 in societal benefit for every €1 invested, with researcher time savings alone valued at €35 million annually.

The organisation’s impact also extends deeply into international policy. GBIF-mediated data support multiple indicators under the Kunming-Montreal Global Biodiversity Framework, inform assessments by the International Union for Conservation of Nature (IUCN) and the Intergovernmental Science-Policy Platform on Biodiversity and Ecosystem Services (IPBES), and are increasingly used by the private sector to meet emerging nature-related disclosure requirements.

Adapting to New Kinds of Data

Over 25 years, GBIF has continually expanded to accommodate new sources of biodiversity data – from digitised natural history specimens and citizen science observations to DNA-based records and, most recently, structured survey and monitoring data designed to support large-scale biodiversity tracking. In 2026, GBIF adopted the Catalogue of Life as its taxonomic backbone, the result of a multi-year collaboration to build shared infrastructure for reconciling species names across datasets.

Persistent Gaps Remain

key events of GBIF

A timeline of key events in the history of the Global Biodiversity Information Facility. Credit to Miller et al., 2026.

Despite this growth, GBIF recognises that several significant challenges remain. The global loss of biodiversity continues to be described as a crisis in major international assessments, even as the data infrastructure has improved. And the data itself continues to reflect long-standing imbalances – regions with high biodiversity, particularly in the Global South, remain underrepresented, while well-studied, charismatic groups such as birds are overrepresented compared to less visible taxa; furthermore, many marine species and hard-to-identify cryptic habitats and organisms remain inadequately documented.

Closing these gaps was part of the original motivation for creating GBIF a quarter-century ago, and it remains valid today. GBIF’s own assessment is that the network cannot resolve these asymmetries alone, doing so will depend on broader shifts in global scientific funding, data culture, and capacity, alongside GBIF’s continued efforts to expand its Participant network and to diversify the types of data it can mobilise.

An additional, ongoing challenge is data heterogeneity and data quality, because GBIF indexes data, rather than directly vetting every record, it relies on its network of data publishers to maintain quality at source, and on users to report issues – a distributed model that keeps the network scalable but is not without friction.

Looking Ahead

capacity development at GBIF.
Capacity development across the Global Biodiversity Information Facility community.  Credit to Miller et al., 2026.

Guided by its 2023–2027 Strategic Framework, GBIF is prioritising continued growth of its Participant network, expanded support for survey and monitoring data, and deeper integration of DNA-derived biodiversity records – all aimed at closing longstanding geographic and taxonomic gaps in digital biodiversity data worldwide.

Original source:

Miller J, Mandeville C, Schigel D, Gamboa Martinez J, Nielsen AM, Sheldon S, Hahn A, Raymond M, Bundgaard-Jensen S, Bagard Laursen M, Copas K, Blissett M, Høfft M, Méndez Hernández F, Noesgaard D, Rodrigues A, Russell L, Stjernegaard Jeppesen T, Elkjær Ørum-Kristensen A, Grosjean M, Waller J, Podolskiy M, Goodson H, Novakovikj S, Frøslev T, Ingenloff K, Sørensen Nilsson A, Svenningsen C, van der Meijden D, Suen A, Hakan Uzun A, Vaskova M, Nielsen C, Marentes Herrera E, Schaldemose Reibke N, Robertson T (2026) The Global Biodiversity Information Facility at 25. Biodiversity Data Journal 14: e208528. https://doi.org/10.3897/BDJ.14.e208528