FR | EN
SCROLL

Published on January 17, 2026

EVOLUTION OF BIODIVERSITY IN EUROPE

By Analyse

Support Analyse

FOREWORD

This article aims to provide key insights into the evolution of biodiversity in Europe through data-driven analysis.

It is structured into four chapters: definitions and context derived from [1–7], the evolution of species diversity based on data from [8], the monitoring of a biological indicator reflecting the state of biodiversity using data from [9, 10], and the evolution of forest ecosystems, studied using data from [11–14].

DEFINITIONS AND CONTEXT

To address the notion of biodiversity, it is necessary to define what life is.

In the broadest biological sense, one proposal [1] describes a living organism as a dissipative structure capable of autocatalysis, homeostasis, and learning.

A structure is described as dissipative if it maintains an ordered state by drawing energy from its environment. A tornado, for instance, may be regarded as a non-living dissipative structure.

Autocatalysis, for its part, is the capacity for growth and reproduction, as seen in the case of fire.

Homeostasis allows for the maintenance of an internal balance despite external disturbances. Termite mounds, for instance, exhibit homeostatic properties through the self-regulation of their internal temperature.

Learning is a means to increase its chances of survival through the storage and exploitation of information about its environment. Inert materials like sand piles exhibit physical memory, as their spatial configuration encodes the history of the most recent impact.

It is the combination of all these properties that defines a living organism. But how do these theoretical criteria apply to life on Earth?

It contains proteins responsible for all cellular tasks. By consuming energy, these proteins ensure the cell's survival (dissipative function), growth and reproduction (autocatalysis), and the maintenance of internal balance, especially during external disturbances (homeostasis). The cell also contains DNA, which stores the genetic information necessary for learning.

A living organism on Earth thus possesses all of these properties. But where does the diversity of life come from?

The mechanism of biological evolution, through reproduction and genetic mutations, has generated a morphological, anatomical, and behavioural diversity of all living beings.

Today, phylogenetic classification criteria allow individuals to be separated into groups. A clade (phylogenetic group) contains an ancestor and all its descendants. The basic unit of this classification is the species, which thus groups together all individuals capable of interbreeding and producing viable and fertile offspring.

The diagram represents a simplified and truncated version of the phylogenetic tree of life from LUCA (Last Universal Common Ancestor) to the three kingdoms Animalia, Plantae, and Fungi. All living organisms are descended from LUCA, which is estimated to have existed over 3 billion years ago. The age of LUCA is estimated at more than 3 billion years.
The tree begins by dividing into 3 domains: Bacteria, Archaea, and Eukaryota, all of which possess at least one cell. Eukaryotes are distinguished by the presence of a cell nucleus, and Archaea are distinguished from Bacteria by their DNA transcription mechanism. The last common ancestor of eukaryotes is estimated at more than 1.6 billion years.
The clade Eukaryota divides into 6 super-groups. The group Opisthokonta is characterized by the presence of a single posterior flagellum used for cell movement, as is the case for spermatozoa.
The Opisthokonta branch groups Animalia and Fungi, while Archaeplastida contains the Plantae kingdom; humans are thus phylogenetically closer to fungi than to plants.

But then, what is biodiversity?

Biodiversity refers to the diversity of ecosystems, that of the communities of species living within them, the diversity between and within species, and the diversity of the interactions between these different elements. This study relies on indicators to assess the evolution of biodiversity over time.

The first indicator is the estimated number of living species, which is a subject of debate among biologists, the number having evolved significantly since the advent of genetics, varying today between 10 million and 1 trillion [2–7].

The estimation of the number of living species on Earth and the associated uncertainty are presented in this graph for the 3 domains of life. The statistical uncertainty represents an interval within which the true value is likely to be found; the smaller this interval, the more precise the measurement.
The group Eukaryota here includes only animals, fungi, and plants. Among eukaryotes (organisms whose cells possess a nucleus), the estimated number varies between 8 million [7] and 170 million [2].
Only a portion of living species is described and named by taxonomists, representing around 2.17 million species [8], or 7% for eukaryotes.
Among these described species within eukaryotes, 8% are assessed by the International Union for Conservation of Nature (IUCN).

A recent study [2] includes in its calculation cryptic species (those with the same morphology but distinct genetically) and host-specific species. Each insect species would thus host, on average, one unique associated mite species, and both would each be associated with a unique nematode species.

Plants [3] represent only a small fraction of the diversity across the three kingdoms, as shown in the graph below.
Vertebrates — the clade that includes the species Homo sapiens — are estimated to represent only 0.1% of the species in the Animal kingdom [7], as shown here.

To study the evolution of biodiversity, a first step consists of looking at the diversity of known species.

EVOLUTION OF SPECIES DIVERSITY

To measure the evolution of species diversity, the IUCN [8] assesses a portion (approximately 8% as shown previously) of the described species, monitoring the evolution of their population.

It assigns each assessed species an extinction risk level, ranging from Extinct in the Wild (EW - score: 5), Critically Endangered (CR - score: 4), Endangered (EN - score: 3), Vulnerable (VU - score: 2), Near Threatened (NT - score: 1), Data Deficient (DD) to Least Concern (LC - score: 0).

The risk level is based on criteria including the evolution of the geographic distribution, of the size of the population, and the estimation of the probability of extinction.

The measurements presented in the figure below indicate the proportion of threatened (classified as CR, EN, VU) or extinct (EW) species — and the associated uncertainty — among the assessed species within a given taxonomic family globally.
This metric provides an overview of the current extinction risk level for species assessed by the IUCN worldwide.
Of all assessed species, on average 28% are threatened with extinction, as shown by the orange dotted line in the figure.

To measure the change in this risk, the IUCN constructs the Red List Index (RLI) defined as: $$ \text{RLI} = 1 - \frac{\sum{\text{S}}}{\text{N} \times \text{S}_{\text{EW}}} $$ where S is the species score, N is the number of species assessed, and SEW is the maximum score (SEW=5). The closer the index is to 1, the greater the survival probability of the species.

The graph illustrates the evolution of the RLI in Europe and the associated 95% uncertainty. A 95% confidence interval corresponds to a 5% margin of error.
The species conservation index is declining, and this trend has accelerated since the late 20th century.
The evolution of the RLI globally is presented in pink for comparison. The index is therefore more favorable to species survival in Europe than worldwide.
Nevertheless, a similar declining dynamic has been observed since 1998, reaching 0.84 in Europe and 0.73 globally in 2020.

Thus, IUCN data point to an accelerating decline in biodiversity, both in Europe and worldwide.

A change of scale allows verification of this trend through the study of a species group whose properties make them a key biological indicator: butterflies.

MONITORING OF A BIOLOGICAL INDICATOR

More than half of the described species in the world are insects [8]. They contribute significantly to global biodiversity and provide numerous ecosystem services that help preserve it, such as pollination.

Many European Union (EU) indicators are related to gene or species diversity but do not directly capture the state of biodiversity. Certain characteristics make butterflies a key biological indicator.

They have a short, fragile lifespan and are thus highly and rapidly sensitive to environmental changes. Their wide array of colours and forms make them popular and more easily identifiable than other insect species. Finally, they represent a broad diversity of insect species.

For these reasons, amongst others, butterflies have benefited from rich documentation derived from numerous observation studies. Along with birds and bats, they are the only groups for which harmonised data are available across Europe.

Measurement campaigns since 1991 have made it possible to obtain standardised data [9] by following the protocol below: the observer follows a path (transect) of 0.2 to 3 km at a constant speed, whilst counting and identifying butterflies present in a 5-metres wide corridor around them.

More than 6000 butterfly observation sites across Europe have provided this data since 1991. These are used by the European Butterfly Monitoring Scheme (eBMS) to monitor the evolution of butterfly populations and will be presented in this work.

The Grassland Butterfly Indicator (GBI) is constructed from the observations of 17 common butterfly species across the 27 EU member states [9].

The graph illustrates the evolution of the GBI between 1991 and 2023 and the associated uncertainty.
The indicator measures the abundance of grassland butterfly species; it starts at 100% in the first year of measurement and ends at 50% in 2023, thus revealing a halving of grassland butterfly populations across the EU since 1991.
This translates to a rapid decline in biodiversity over the same period in European grassland ecosystems.
In the Netherlands, a pioneering country in butterfly observation, data [10] has been collected since 1890 in the three main habitat types: grasslands, forests, and heathlands.
The orange curve illustrates the decline of the multi-species index of butterfly distribution in the Netherlands since 1890. A decline in species distribution in space is a sign of a greater decline in population abundance.
A 68% decrease in butterfly distribution between 1890 and 2017 is observed in the Netherlands. All habitat types are affected.
The shifting baseline syndrome consists of assuming that a system's state of equilibrium is the one that was measured first.
The risk is to bias the perception of historical biodiversity loss, as in this example, by focusing on recent evolution and assuming that the system's reference state corresponds to the study's first measurement, here in 1991.
However if EU butterflies followed a trend similar to that in the Netherlands during the 20th Century, the total decline in the abundance of EU grassland butterflies from 1890 to 2023 would reach above 80%.

How to explain this decline ?

One of the predominant factors is habitat loss for grassland butterflies. This stems primarily from agricultural intensification, which involves using fertilizers and pesticides in monocultures to artificially maximize production. Nitrogen deposition, used to fertilize the soil, contaminates and transforms ecosystems [9].

A series of warmer and drier summers due to climate change is causing an additional decline. The protection of remaining semi-natural grasslands, the reversal of the habitat fragmentation trend, and the transformation of intensive agricultural practices can contribute to restoring grassland biodiversity and allowing for the benefits of its ecosystem services.

To complement this study, another type of ecosystem can be examined. It covers a large part of Europe and has evolved throughout the Holocene—the current interglacial period—under a climate favorable to its development: the forest ecosystem.

EVOLUTION OF FOREST ECOSYSTEMS

A forest ecosystem is a system composed of a physical environment with trees, communities of plant, animal, fungal, and microbial species, and all the interactions amongst these organisms and with their environment.

Forests provide numerous ecosystem services, such as the production of renewable material, the storage of CO2, soil protection, and the development of biodiversity, amongst others.

In this work, the study of the evolution of forest ecosystems in Europe begins with the observation of forest cover changes [11]. This study is based on field measurements taken during National Forest Inventory (NFI) campaigns, which survey the area of EU countries to measure the size, number of species, age, and volume of trees.

This graph illustrates its increase in Europe since 1990, reaching 227 million hectares, or 34.8% of Europe's land area, in 2020 [11].
The rate of forest area expansion is decreasing, falling from +0.3% per year over the period 1990–2020 to +0.2% for 2010-2020.
Using wood consumption data, forest growth estimates, and forest age structure, a reconstruction of forest management since 1600 has been carried out [12].
An increase in forest cover is observed from 1850 as illustrated by the dotted line. This increase stems mainly from the introduction of conifers, which have gone from a proportion of 29% to 56% of the total forest area since 1600 [12].
However, a decline in forest cover is observed between 1600 and 1850. This is reflected in the evolution of the area of unmanaged forests — which decreases mainly in Scandinavian countries — falling from 30% to 17% of the European forest area [12].
To avoid the shifting baseline syndrome, it can be useful to take a step back on the evolution of forest cover in Europe. This is possible thanks to palynology, i.e., the study of fossils containing pollen grains.
A study [13] is based on the idea that pollen samples with similar compositions have a similar natural environment.
Thus, by associating fossil samples with the closest modern samples — for which certain environmental parameters are known — it is possible to measure the evolution of forest cover. This evolution is illustrated in the graph below, produced using data from [13].
The significant increase in forest cover observed at the beginning of the Holocene — the interglacial period spanning the last 12,000 years — is attributed to the transition to a post-glacial climate with rising temperatures and humidity [13].
These new parameters caused transformations in forests which became denser, and scattered woodlands replaced tundras — plant formations in cold climate zones. Forest cover reached a plateau between -6500 and -4000 coinciding with the maximum development of temperate forests composed of conifers and broadleaves.
Two phases of decline followed this period, both attributed to human pressures; the first from -4000 coincides with an estimate of the beginning of the Neolithic period in the British Isles [13], characterized by sedentarisation and the development of agriculture.
The second phase of decline corresponds to an acceleration, observed from 500, particularly visible in Eastern Europe.

This time, only recent data, from 2005 to 2015, are available for Europe. These allow illustrating a 1% decrease over this period in the proportion of forests formed by only a single tree species.

The proportion of forests with between 2 and 5 species has increased by more than 1%, while that of forests with more than 6 species has remained stable in comparison.

The diversity of forests according to the number of tree species in Europe in 2015 is illustrated in the graph below.
Despite a recent stability in tree species diversity, one-third of forests are composed of a single tree species. Furthermore, 5% of tree species continue to be threatened.

More than half of the growing stock volume — total volume of living trees — in 2020 is composed of spruce or pine.

This large increase in the share of conifers in forests in Europe is mainly attributed to the interest in their rapid growth, and thus wood productivity in the short term.

Annual growth over the last 30 years of the growing stock volume of broadleaves of +1.6% against +1.2% for conifers has been observed, thus illustrating the better long-term yield of broadleaved or mixed forests.

On the other hand, the forest bird population indicator is stable since 1980, with a slight increase observed since 2010.

While forest area is increasing in Europe, and certain forest biodiversity indicators are stable, the growth of growing stock volume is slowing down each year [11].

Indeed, it appears that damages — mainly due to wind, bark beetles, and fire — suffered by forests in Europe have increased significantly since 1950 [14] as illustrated in the graph below.
The annual volume of damages is equivalent to 0.23% of the standing volume over the period 1950–2000, compared to 0.27% for the period 2001–2019, an increase of 17%.
In addition, damage over the entire study period represents 16% of the harvested wood.
Past forest exploitation choices, with the development of monocultures, and climate change, reinforce the fragilities and disturbances observed in European forests.

By increasing tree mortality, these factors reduce the duration of carbon storage in living biomass and in soils. Yet, the absorption and storage of CO2 by forests is equivalent to 10% of EU emissions, thus helping to combat climate change [14].

Other indicators testify to the fragility of European forests, such as defoliation — leaf loss — which is increasing for 4/5th of trees. Another fragility stems from the age structure of trees with 3/4 of forests considered even-aged i.e. belonging to the same age class.

Climate change, by causing droughts and soil desiccation, contributes to further weakening trees.

In summary, despite a recent increase in area, European forests have lost diversity as a result of past management choices. This has created vulnerabilities, making them more sensitive to increasingly frequent external disturbances.

CONCLUSION

The full extent of biodiversity remains unknown and expands as it is studied. Despite this, substantial knowledge for certain species groups, such as vertebrates or plants, allows for the monitoring of their evolution. Genetics has enabled the reconstruction of the Tree of Life where all species are classified. Nearly one-third of the described and assessed species are threatened with extinction. Indeed, a rapid decline in the species conservation index is observed. It indicates a threat to species diversity in Europe and globally.

The example of European grassland ecosystems is used to substantiate this observation. Through the butterfly index, a halving of grassland butterfly populations is observed between 1990 and 2023. A study in the Netherlands provides an order of magnitude of the losses likely experienced by butterfly populations in Europe in the 20th century, bringing the total decline in European grassland butterflies to a level above 80%.

With respect to forests, a positive trend is observed in the recent evolution of forest area; however, the perspective of its evolution since the start of the Holocene shifts the view on the influence of humans on forest ecosystems. Indeed, at their peak extent, before the effect of human pressures took hold, forests exceeded 60% of Europe’s area while they represent around one-third today.

The recent evolution of forests attests to a relatively stable diversity; however, over the last few centuries, a strong increase in the proportion of conifers has been observed, reaching more than half of the growing stock. Forest management has often relied on planting monocultures, which have permanently transformed Europe's forest ecosystems. These changes have weakened forest resilience and volume growth; forests are less diverse in terms of tree species—with one-third consisting of a single species—and lack age diversity. Ecosystem services provided by forests, such as CO2 storage, have also been diminished. These fragile forests now face more violent disturbances caused by wind, drought, and bark beetles, all of which are exacerbated by climate change.

The observed signals are consistent with a general decline in biodiversity in Europe. The factors causing this decline are linked to habitat loss and production intensification practices, compounded by pressures related to climate change.

BIBLIOGRAPHY

[1] Stuart Bartlett and David Louapre. Provenance of life : Chemical autonomous agents surviving through associative learning. Physical Review E, 106 :034401, 2022. DOI

[2] Xin Li and John J. Wiens. Estimating global biodiversity : The role of cryptic insect species. Systematic Biology, 72 :391–403, 2023. DOI

[3] Royal Botanic Gardens Kew. State of the World’s Plants and Fungi 2024. Royal Botanic Gardens Kew, 2024. DOI

[4] LPSN. List of Prokaryotic Names with Standing in Nomenclature. URL. Consulté 11/2025.

[5] Stelios Louca and Michael Doebeli. The number of species on earth and the global rate of speciation. Ecology Letters, 22 :1819–1828, 2019. DOI

[6] Kenneth J. Locey and Jay T. Lennon. Scaling laws predict global microbial diversity. Proceedings of the National Academy of Sciences (PNAS), 113 :5970–5975, 2016. DOI

[7] Camilo Mora, Derek P. Tittensor, Sina Adl, Alastair G. B. Simpson, and Boris Worm. How many species are there on earth and in the ocean ? PLoS Biology, 9 :e1001127, 2011. DOI

[8] International Union for Conservation of Nature (IUCN). The IUCN Red List of Threatened Species. Version 2025-2. Summary Statistics (Figure 2). URL. Consulté 11/2025.

[9] Chris van Swaay et al. EU grassland butterfly index 1991-2023 technical report, September 2025. DOI

[10] Arco Van Strien et al. Over a century of data reveal more than 80% decline in butterflies in the netherlands. Biological Conservation, 234 :116–122, July 2019. DOI

[11] FOREST EUROPE. State of Europe’s Forests 2020 (SoEF 2020). Liaison Unit, Bratislava, Bratislava, 2020. Rapport préparé pour la Conférence ministérielle pour la protection des forêts en Europe. DOI

[12] M. J. McGrath, S. Luyssaert, P. Meyfroidt, J. O. Kaplan, M. Bürgi, Y. Chen, K. Erb, U. Gimmi, D. McInerney, K. Naudts, J. Otto, F. Pasztor, J. Ryder, M.-J. Schelhaas, and A. Valade. Reconstructing european forest management from 1600 to 2010. Biogeosciences, 12 :4291–4316, 2015. DOI

[13] M. Zanon, B. A. S. Davis, L. Marquer, S. Brewer, and J. O. Kaplan. European forest cover during the past 12,000 years : A palynological reconstruction based on modern analogs and remote sensing. Frontiers in Plant Science (Front Plant Sci), 9 :253, Mar 2018. DOI

[14] Marco Patacca et al. Significant increase in natural disturbance impacts on european forests since 1950. Global Change Biology, 29 :1359–1376, 12 2022. DOI

Thank you for watching this video. This work is part of a broader project aimed at developing a scientific, data-driven approach to information. To enable the continuation of this work independently, the funding relies on your support via the Tipeee platform; the link is provided in the description. Thank you for your support!