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Archer et al. 2014
Pollinator ecology is geographically biased toward wealthy temperate nations; nearly half of all data comes from 5 countries.
This undermines global models and hides declines in Africa/Asia.
Consequences: unknown stressors, economic vulnerability, and taxonomic gaps.
Calls for global collaboration, low‑cost protocols, citizen science.
Díaz & Malhi 2022
Biodiversity' includes within-species, between-species and ecosystem diversity, with intrinsic, instrumental and relational values.
Decline accelerated since 1950.
Díaz et al. 2019
~1 million species threatened
60–70% of land altered.
Proposes five changes: incentives, cross-sector action, precaution, resilience, stronger environmental law.
Newbold et al. 2015
Species richness declines up to 76%.
Biotic homogenisation spreading; agriculture creates human-dominated assemblages.
Even low-emission pathways cause land conversion impacts
Land-use is dominant driver.
Tilman et al. 2017
Sub-Saharan Africa, South America and SE Asia face highest future risks.
Solutions: close yield gaps, shift diets, conservation-focused trade; could reduce extinction risk by 50%.
Wiens & Saban 2025a
Genus-level extinctions rare and declining: only 102 genera lost in 500 years, mostly island endemics.
Extinction patterns do not match species-level claims; warns against exaggeration while affirming biodiversity loss is still serious.
Wiens & Saban 2025b
Critiques 'sixth mass extinction' framing
Definitions inconsistent, rates extrapolated incorrectly
Sees island losses (more likely) as indicative of global contexts
Biodiversity crisis is real but not a mass extinction under strict criteria.
Carvalheiro et al. 2025
Brazil holds 10% of global bee diversity yet faces massive knowledge shortfalls
>50% of Brazil has zero bee records.
Functional, phylogenetic and abundance data critically lacking.
Collen et al. 2016
IUCN Red List is often misunderstood: not a conservation priority list but a risk assessment tool.
Uses comparable criteria across taxa.
Rarity ≠ high risk.
Misuse leads to inflated or downplayed extinction claims.
Cowie et al. 2022
Invertebrates excluded from most assessments; molluscs reveal far higher extinction rates.
Authors estimate ~13% of species extinct since 1500 (vs 0.04% Red List).
Many extinctions undocumented
Cowie et al. 2025
Extinction denial undermines policy
Many species unassessed by IUCN Red List, making true extinction rates higher.
Island losses remain globally important
Ellis et al. 2012
Human activity has increased local plant richness in 69% of landscapes via introductions > extinctions.
Novel assemblages form, but native species decline and homogenisation increases.
Lindenmayer et al. 2013
Monitoring without action leads to 'monitoring to extinction'; adaptive management needed
Predefined thresholds should trigger interventions
Example: Great Glider species collapse in Australia despite clear warning signs.
Jaureguiberry et al. 2022
Global analysis identifies land/sea-use change as dominant driver across biodiversity dimensions; exploitation second.
Pollution, climate and invasives also key.
Drivers interact; climate-only solutions insufficient.