Master IB Biology A4.2: Conservation of biodiversity with notes created by examiners and strictly aligned with the syllabus.
A4.2.1 Biodiversity as the variety of life in all its forms, levels and combinations
A4.2.2 Comparisons between current number of species on Earth and past levels of biodiversity
A4.2.3 Causes of anthropogenic species extinction
A4.2.4 Causes of ecosystem loss
Biodiversity is the variety of living organisms, biological systems and heritable variation found in an area or on Earth as a whole. Notice what that definition does: it goes beyond just “number of species”. Biodiversity exists at several levels of biological organization.
Ecosystem diversity is the variety of ecosystems in a region, differing in their physical conditions, communities and ecological processes. A coral reef, a peat swamp forest, a temperate grassland and a mangrove forest are not just different scenery. Each one has its own abiotic conditions, food webs and cycling of matter.
Species diversity is the variety of species in a community or region, usually considering both how many species are present and how evenly individuals are distributed among them. So, a forest with 100 tree species has more species diversity than a plantation of one tree species, even if the total number of individual trees is the same.
Genetic diversity is the variety of alleles and genotypes within a species or population. Students often forget this level. A species reduced to a few surviving individuals may still exist, but it may have lost much of the variation needed for resistance to disease, adaptation to environmental change and avoidance of inbreeding.
A global map of land vertebrate diversity shows a striking pattern: diversity is not spread evenly across Earth. It is generally highest in tropical regions near the equator and lower toward the poles. That matters for conservation, because decisions are spatial. Losing a hectare of habitat in one place may remove far more species than losing a hectare somewhere else.

The key link is that life is unified by shared features — cells, DNA, genetic code, metabolism and evolution by natural selection — while variation diversifies life at every scale. DNA sequence variation can produce protein variation. Variation among individuals can produce population-level adaptation; variation among species produces different niches in communities; and variation among ecosystems produces the biosphere’s enormous range of habitats.
Variation also helps communities stay stable. If several species perform similar ecological roles, the loss or decline of one may be partly buffered by others. If genetic variation is high within a population, some individuals are more likely to survive a new disease, pollutant or climate stress. Diversity is not just a catalogue of “interesting organisms”; it is part of how living systems persist through change.
Species discovery means finding, naming and describing species so other scientists can recognize them. Around two million species have been formally described, but that doesn’t mean only two million species exist. Many insects, fungi, protists, deep-sea organisms and microorganisms are still poorly sampled.
For eukaryotes, estimates of the total number of species often reach the millions. The figures vary because scientists use different methods. For prokaryotes, the uncertainty is even greater: many cannot be cultured easily, and defining a bacterial “species” is less straightforward than defining many animal or plant species.
Fossil evidence means preserved material or traces of past organisms, used to infer the history of life. Fossils don’t provide a complete list of all species that ever lived. Soft-bodied organisms, small organisms and organisms from habitats with poor preservation are under-represented. Even so, fossils do show broad trends.
The fossil record shows five previous mass extinctions, each followed by long periods when biodiversity increased again as new groups evolved and diversified. Since the last major mass extinction, at the end of the Cretaceous period, biodiversity has had tens of millions of years to build up. The best fossil evidence suggests that more species are alive today than at any previous time in Earth’s history.

Classification means arranging organisms into groups based on shared characteristics or evolutionary relationships. It works as pattern recognition: scientists compare evidence for similarities, differences and ancestry patterns.
The same observations can sometimes be sorted in different defensible ways. Splitters are taxonomists who recognize more separate species within a group by emphasizing differences between populations. Lumpers are taxonomists who recognize fewer species by emphasizing similarities and combining populations into broader species. Neither label automatically means “right” or “wrong”; the question is which evidence is being given more weight.
DNA sequencing has often encouraged splitting, since populations that look similar may be genetically distinct and reproductively isolated. Older classifications based mainly on appearance sometimes encouraged lumping. So, in biology, strong evidence is rarely just one observation. It is a pattern supported by multiple methods, open to checking and revision.

Extinction means the permanent loss of all living individuals of a species. Extinctions have always happened. They do not necessarily reduce biodiversity over long periods if speciation balances them. The problem now is the speed of loss: many present-day extinctions are anthropogenic, meaning caused directly or indirectly by human activity.
In this topic, keep the focus on the causes of the current sixth mass extinction, rather than the asteroid impacts, volcanism or long-term climate shifts linked with earlier mass extinctions.
Over-exploitation is the removal of organisms from a population faster than reproduction can replace them. This includes hunting, fishing, logging and harvesting plants for food, medicine or trade. Large animals that reproduce slowly are especially vulnerable.
Habitat destruction means removing or severely altering the place where a species normally lives and obtains resources. Agriculture, settlement, roads, mining and logging can push a population below the size needed for survival.
Invasive alien species are non-native organisms introduced by humans that spread and harm native species or ecosystems. They may cause extinction through predation, competition, disease transmission or hybridization with native relatives.
Pollution is the release of substances or energy into the environment at levels that harm organisms or ecological processes. Pesticides, heavy metals, oil, plastics, excess nutrients and pharmaceutical residues can all reduce survival or reproduction.
Rapid climate change is human-driven change in long-term temperature, rainfall, seasonality or extreme events, happening faster than some species can adapt or migrate. Species restricted to islands, mountains, polar regions or isolated reefs have few escape routes.

The North Island giant moa, Dinornis novaezealandiae, shows the loss of terrestrial megafauna well. It was a huge flightless bird from New Zealand. After human settlement, hunting pressure and associated habitat change led to the extinction of moa species within a short historical period. Its size did not protect it; slow-breeding large animals are often easy to overexploit.
The Caribbean monk seal, Neomonachus tropicalis, is a marine extinction case. It lived in the Caribbean Sea and Gulf of Mexico. Humans killed it for oil and meat, disturbed breeding sites and competed with it for fish. The species was last reliably seen in the twentieth century and is now extinct. This example helps because students sometimes assume extinction is mainly a land problem. Marine mammals can disappear too.
For a familiar regional case, use a species that has gone extinct from your own country or local area if your class has one. A widely taught example is the thylacine, Thylacinus cynocephalus, which disappeared from Tasmania after hunting, government bounties, habitat change and conflict with livestock farming. The key skill is to link the extinction to named human pressures, rather than just saying that the species “died out”.
Comparison of three anthropogenic extinction case studies and their main human causes.
| Case study | Habitat / group | Main human causes | Extinction outcome |
|---|---|---|---|
| North Island giant moa (Dinornis novaezealandiae) | New Zealand; terrestrial megafauna | Hunting by humans; associated habitat change | Moa species became extinct within a short historical period after human settlement |
| Caribbean monk seal (Neomonachus tropicalis) | Caribbean Sea and Gulf of Mexico; marine mammal | Killing for oil and meat; disturbance of breeding sites; competition for fish | Extinct; last reliable sightings were in the twentieth century |
| Thylacine (Thylacinus cynocephalus) | Tasmania; regional land mammal | Hunting and government bounties; habitat change; conflict with livestock farming | Extinct; disappeared from Tasmania after multiple human pressures |
When writing about organisms, either the common name or the scientific name is acceptable, provided the organism is clear. Scientific names help when common names vary between countries.
An ecosystem is a biological system made of a community of organisms interacting with each other and with the physical environment. Ecosystem loss happens when an ecosystem disappears or functionally collapses, so its characteristic community, abiotic conditions and ecological processes no longer persist.
Loss can be direct, such as a forest being cleared for agriculture. It can also be indirect, for example when water flow, salinity, nutrient level or climate changes beyond the tolerance of key organisms. A keystone species is a species with a disproportionately large effect on community structure compared with its abundance. Remove one, and much wider ecosystem change can follow.
The causes studied here should be directly or indirectly anthropogenic. The main ones are:

Mixed dipterocarp forest is a tropical rainforest ecosystem dominated by many tree species from the family Dipterocarpaceae. In Southeast Asia, these forests can contain very high tree diversity and large amounts of valuable timber.
Most loss comes from logging, conversion to oil palm plantations and wider land-use change. Lowland forest on deep peat is especially vulnerable: drainage lets peat decompose, releasing carbon dioxide and making the land more fire-prone. Once the forest structure, soil water level and species composition have changed, the original ecosystem is not simply “waiting to grow back”.

The Aral Sea was once one of the world’s largest lakes. During the twentieth century, rivers that fed it were diverted for irrigation. The lake shrank, salinity rose dramatically, and its fish and invertebrate communities collapsed. This is ecosystem loss caused by water diversion, not by direct hunting of the species involved.
Where possible, add a local ecosystem-loss case — for example, a drained wetland, cleared woodland, converted grassland, polluted river or reclaimed coastal habitat. Strong case studies name the ecosystem, identify the human driver, and explain the mechanism of collapse.
A biodiversity crisis means an unusually rapid loss of species, genetic diversity and ecosystems across many regions. That claim needs evidence behind it, not just a few dramatic examples.
Useful evidence can come from IPBES reports and from reliable biodiversity surveys in many habitats around the world. IPBES is an intergovernmental science-policy body that assesses evidence on biodiversity and ecosystem services for governments and the public.
Surveys can measure population size, species range, area of habitat, ecosystem degradation, number of threatened species, genetic diversity, species richness and species evenness. Species richness is the number of species present in a sample or area. Species evenness is the similarity in the abundances of the species present. A site with ten species, each represented by similar numbers of individuals, is more even than a site where one species dominates and the other nine are rare.
A single survey shows what was present at one time. On its own, it cannot prove a decline. To show change, surveys must be repeated using comparable methods: the same site boundaries, similar search effort, similar season, similar time of day where relevant, and consistent identification methods.

For example, researchers might walk a fixed transect each year to count butterflies. They might also use quadrats repeatedly to record plant species in a grassland. Remote sensing can monitor ecosystem area and degradation too, such as forest loss, burning or conversion to agriculture.

A commonly used diversity measure is Simpson’s reciprocal index: D = N(N − 1) / Σn(n − 1), where D is the reciprocal diversity index (dimensionless), N is the total number of organisms of all species in the sample (organisms, a dimensionless count) and n is the number of organisms of one species in the sample (organisms, a dimensionless count). Values are higher when richness is high and individuals are spread more evenly among species.
Citizen science is scientific data collection or analysis carried out by members of the public, usually following a shared protocol. It can be extremely valuable because many observers can collect data over huge areas and long time periods. Bird counts, butterfly transects and species-recording apps can reveal changes that a small research team could not monitor alone.
There are methodological concerns as well. Citizen observers may vary in expertise, sampling effort may be uneven, popular sites may be over-recorded, and absence of a record does not always mean absence of a species. Good citizen-science projects reduce these problems with training, validation, photographs, expert checking, standardized protocols and transparent databases.
To be verifiable, evidence usually needs to come from a published source, ideally peer-reviewed. Peer review is evaluation of scientific work by other specialists before publication, so that methods, analysis and conclusions can be checked. Strong evidence in biology is repeatable, methodologically clear, open to scrutiny and consistent across independent sources.
The current biodiversity crisis has intensified as human activity has grown in scale. Human population growth is the increase in the number of humans alive over time; it raises total demand for food, water, energy, land, transport and materials.
Population growth doesn’t act by itself. Its impact depends on consumption, technology, governance and inequality. Even so, a larger population usually puts more pressure on land and ecosystems unless resource use changes sharply.

Several interacting causes drive the current crisis:

These causes often strengthen each other. Roads that fragment a forest make it easier for hunters to enter, leave it more vulnerable to invasive species, and expose it to drying and fire. Climate change can add further stress by shifting temperature and rainfall beyond the range to which species are adapted.
The present situation is often called the sixth mass extinction because extinction rates are far above background rates and many groups are declining at the same time. Earlier mass extinctions were caused by non-human geological or astronomical events; this one is largely caused by human choices, so prevention and reduction are possible.
Conservation means protecting and managing biodiversity to reduce extinction risk and keep ecosystems functioning. Species don’t all face the same threats, so no single method works for every case. A plant with viable seeds, a migratory bird, a coral reef and a large carnivore all need different measures.

In situ conservation conserves species within their natural habitats. It protects organisms while they are still interacting with their usual abiotic environment, food sources, competitors, predators, mutualists and pathogens. This is usually the preferred approach because it keeps whole ecological relationships intact, rather than saving isolated individuals on their own.
Protected areas include national parks, marine reserves, wildlife refuges and community-managed forests. A line on a map, though, rarely does the job by itself. Nature reserve management means active intervention in a protected area to maintain biodiversity and ecological function. It may include anti-poaching patrols, control of invasive species, habitat burning or grazing regimes, reintroduction of locally extinct species, predator management, visitor control and monitoring.
Rewilding is the restoration of a degraded ecosystem toward a more self-sustaining state by re-establishing natural processes and, where suitable, missing species. It isn’t just planting a few trees. The aim is to let ecological interactions take on more of the work over time.
Reclamation is the recovery of degraded land or water so that it can support a functioning ecosystem again. Examples include restoring wetlands by raising water levels, reconnecting rivers to floodplains, removing pollutants, replanting native vegetation and reducing erosion.
These approaches link to the question about stability. Ecological communities with more variation in species, genes and niches often have more ways to absorb disturbance. By restoring habitat structure and species interactions, conservation can increase resilience, although recovery may take decades and may not recreate the original ecosystem exactly.
Ex situ conservation conserves species outside their natural habitats. Zoos can breed endangered animals, botanic gardens can propagate endangered plants, and carefully managed programmes may later return individuals to suitable habitat.
There are limits. Captive populations can lose genetic diversity, adapt to captivity, or fail to learn natural behaviours. Ex situ conservation also does not protect the original ecosystem. Use it when wild survival is currently unsafe, when numbers are extremely low, or when a backup population is needed.
Germ plasm is living reproductive or genetic material that can be used to produce new individuals. Seed banks store seeds at low temperature and low moisture to maintain viability. Tissue banks, sperm banks and egg storage can preserve genetic material from animals and plants. This is valuable, but it is a backup, not a substitute for conserving living ecosystems.

Conservation resources are limited, so conservationists have to make hard choices. The EDGE of Existence programme offers one way to set priorities: it combines evolutionary uniqueness with extinction risk.
A clade is a group of organisms made of a common ancestor and all its descendants. Evolutionarily distinct describes a species with few close living relatives, so it represents a long, separate branch of evolutionary history. Globally endangered describes a species at high risk of extinction across its whole natural range, not just rare in one country.
EDGE species are species that are both evolutionarily distinct and globally endangered. The reasoning is straightforward: if one is lost, Earth loses a species, along with a large amount of unique evolutionary history.

Prioritization uses science, but science alone doesn’t decide it. Choosing which species “should” receive money and protection carries ethical, environmental, political, social, cultural and economic implications.
Different groups may value different goals. Some focus on preventing the most likely extinctions; others aim to preserve maximum phylogenetic diversity, protect keystone species, conserve culturally significant species, support ecosystem services, or help species in regions with fewer conservation resources. These aims can clash. For that reason, prioritization needs open debate, rather than the pretence that there is one automatic answer.
Taxonomy can shape conservation too. If a rare population is classified as a separate species, it may receive more attention and legal protection than if it is treated as a subspecies or local population. This links back to classification as pattern recognition: the way we classify biodiversity can influence how society protects it.
One final link: diversity matters at every level. EDGE focuses on deep evolutionary diversity; reserve management often focuses on ecosystem diversity; breeding programmes focus heavily on genetic diversity. Good conservation tries to keep all three in view.