Part of ECO-02 — Biodiversity & Conservation

Threats Summary: HIPPO Framework and Extinction Cascade

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The Five Faces of Biodiversity Loss: The HIPPO Framework

The ongoing sixth mass extinction event — the first in Earth's history to be driven entirely by a single species — can be understood through the HIPPO framework, which identifies five interacting causes of biodiversity loss.

Habitat loss and fragmentation (H) is the single most important cause, affecting approximately 86% of all terrestrial threatened species. Tropical rainforests have been reduced from covering 14% of Earth's land surface to approximately 6% through deforestation for agriculture, urbanisation, logging, and infrastructure. Beyond outright destruction, habitat fragmentation isolates populations in island-like patches surrounded by hostile matrices of agricultural and urban land. Fragmented populations suffer the edge effect (altered microclimate and species composition at boundaries), reduced immigration, increased inbreeding, and eventual extinction vortex dynamics when populations fall below their minimum viable population size.

Invasive alien species (I) represent the second major driver and the leading cause of island extinctions. The introduction of the Nile perch (Lates niloticus) into Lake Victoria in the 1950s illustrates the catastrophic potential: it drove hundreds of endemic cichlid fish to extinction through a combination of direct predation and exacerbation of eutrophication-related habitat degradation. In India, Lantana camara (a South American ornamental shrub), Eichhornia crassipes (water hyacinth, the "terror of Bengal"), and Parthenium hysterophorus (Congress grass) have invaded forests, wetlands, and roadsides, outcompeting native vegetation and reducing habitat quality for native wildlife.

Population growth and overexploitation (P) — the direct killing of species faster than their reproductive rates — has driven several iconic extinctions. Steller's sea cow, discovered in 1741, was extinct by 1768 — hunted to extinction in just 27 years by sailors harvesting its meat and oil. The passenger pigeon, once numbering 3–5 billion individuals and filling entire forests, was commercially hunted to extinction by 1914. These examples demonstrate that even the most abundant species are not safe from overexploitation.

Pollution (P) operates more subtly but pervasively. Pesticide biomagnification is the classic example: DDT entering food chains at low concentrations (0.003 ppm in phytoplankton) accumulates through successive trophic levels to reach ~25 ppm in raptors, causing eggshell thinning through disruption of calcium metabolism. This drove eagle, peregrine falcon, and brown pelican populations to near-extinction before DDT bans allowed recovery. Industrial effluents, plastics, excess fertilisers causing eutrophication, and oil spills all contribute to biodiversity loss across aquatic and terrestrial ecosystems.

Co-extinction (O) multiplies total extinction numbers by cascading losses through networks of ecological dependencies. When a host plant goes extinct, its specialised herbivores, pollinators, and seed dispersers may follow. When a top predator disappears, its prey species can explode in abundance, then crash as resources are depleted. Fig trees and their specific fig wasps share an obligate mutualism: each species can only reproduce with the help of the other, so if either goes extinct, the other automatically follows.

These five HIPPO causes rarely act in isolation. Lake Victoria's cichlid disaster involved invasive species (Nile perch), habitat degradation through eutrophication (pollution), and co-extinction cascades. The passenger pigeon faced both overexploitation and habitat loss simultaneously. Understanding the synergistic interaction of HIPPO drivers is essential for designing effective conservation interventions.

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