Modern Insect Extinctions, the Neglected Majority

Most extinctions estimated to have occurred in the historical past, or predicted to occur in the future, are of insects. Despite this, the study of insect extinctions has been neglected. Only 70 modern insect extinctions have been documented, although thousands are estimated to have occurred. By focusing on some of the 70 documented extinctions as case studies, I considered ways in which insect extinctions may differ from those of other taxa. These case studies suggested that two types of extinction might be common for insects but rare for other taxa: extinction of narrow habitat specialists and coextinctions of affiliates with the extinctions of their hosts. Importantly, both of these forms of extinction are often ignored by conservation programs focused on vertebrates and plants. Anecdotal evidence and recent simulations suggest that many insect extinctions may have already occurred because of loss of narrow habitat specialists from restricted habitats and the loss of hosts. If we are serious about insect conservation, we need to spend more time and money documenting such extinctions. To neglect such extinctions is to ignore the majority of species that are or were in need of conservation.

[1]  D. Bellwood,et al.  The contribution of small individuals to density–body size relationships , 2003, Oecologia.

[2]  F. Howarth Environmental Impacts of Classical Biological Control , 1991 .

[3]  D. Yeates,et al.  Patterns and levels of endemism in the Australian Wet Tropics rainforest: evidence from flightless insects , 2002 .

[4]  W. Mccafferty Status of some historically unfamiliar American mayflies (Ephemeroptera) , 2001 .

[5]  P. Goldstein Systematic collection data in North American invertebrate conservation and monitoring programmes , 2004 .

[6]  S. Kellert Values and Perceptions of Invertebrates , 1993 .

[7]  K. Gaston,et al.  A critical assessment of the form of the interspecific relationship between abundance and body size in animals , 1997 .

[8]  R. Redak Arthropods and Multispecies Habitat Conservation Plans: Are We Missing Something? , 2000, Environmental management.

[9]  Thomas M. Brooks,et al.  Relative risk of extinction of passerine birds on continents and islands , 1999, Nature.

[10]  P. Lesica,et al.  Should We Use Pesticides to Conserve Rare Plants? , 2000 .

[11]  N. Stork,et al.  Extinction or 'co-extinction' rates? , 1993, Nature.

[12]  D. Pearson,et al.  World‐Wide Species Richness Patterns of Tiger Beetles (Coleoptera: Cicindelidae): Indicator Taxon for Biodiversity and Conservation Studies , 1992 .

[13]  P. Raven,et al.  Biodiversity: Extinction by numbers , 2000, Nature.

[14]  O. Phillips,et al.  Extinction risk from climate change , 2004, Nature.

[15]  R. Adams,et al.  PIGEON LICE DOWN UNDER: TAXONOMY OF AUSTRALIAN CAMPANULOTES (PHTHIRAPTERA: PHILOPTERIDAE), WITH A DESCRIPTION OF C. DURDENI N. SP , 2000, The Journal of parasitology.

[16]  L. P. Koh,et al.  Co‐Extinctions of Tropical Butterflies and their Hostplants , 2004 .

[17]  S. Beissinger,et al.  Limitations of Captive Breeding in Endangered Species Recovery , 1996 .

[18]  M. Mckinney High Rates of Extinction and Threat in Poorly Studied Taxa , 1999 .

[19]  Andrew F. G. Bourke,et al.  The influence of sociality on the conservation biology of social insects , 2001 .

[20]  J. Sprent Parasites lost? , 1992, International journal for parasitology.

[21]  V. Novotný,et al.  Arthropod Monitoring for Fine-Scale Habitat Analysis: A Case Study of the El Segundo Sand Dunes , 2000, Environmental management.

[22]  J. Lockwood TAXONOMIC STATUS OF THE ROCKY MOUNTAIN LOCUST: MORPHOMETRIC COMPARISONS OF MELANOPLUS SPRETUS (WALSH) WITH SOLITARY AND MIGRATORY MELANOPLUS SANGUINIPES (F.) , 1989, The Canadian Entomologist.

[23]  Lian Pin Koh,et al.  Species Coextinctions and the Biodiversity Crisis , 2004, Science.

[24]  J. Shogren,et al.  Is the Tasmanian tiger extinct? A biological–economic re-evaluation , 2003 .

[25]  E. Williams,et al.  Parasite Conservation and the Black‐Footed Ferret Recovery Program , 1998 .

[26]  C. Kremen,et al.  A null model for species richness gradients: bounded range overlap of butterflies and other rainforest endemics in Madagascar , 1999 .

[27]  D. Rentz A new and apparently extinct katydid from Antioch sand dunes , 1977 .

[28]  D. A. Windsor Equal Rights for Parasites , 1995, Perspectives in biology and medicine.

[29]  D. Priddel,et al.  Rediscovery of the ‘extinct’ Lord Howe Island stick-insect (Dryococelus australis (Montrouzier)) (Phasmatodea) and recommendations for its conservation , 2003, Biodiversity & Conservation.

[30]  F. Seow-Choen Stick and leaf insect (Phasmida: Insecta) biodiversity in the Nature Reserves of Singapore , 1997 .

[31]  J. Lockwood,et al.  A solution for the sudden and unexplained extinction of the Rocky Mountain grasshopper (Orthoptera: Acrididae). , 1990 .

[32]  J. Elkinton,et al.  Effects of a Biological Control Introduction on Three Nontarget Native Species of Saturniid Moths , 2000, Conservation biology : the journal of the Society for Conservation Biology.

[33]  J. Thomas,et al.  Complexity of species conservation in managed habitats: interaction betweenMaculinea butterflies and their ant hosts , 1992, Biodiversity & Conservation.

[34]  J Memmott,et al.  Infiltration of a Hawaiian Community by Introduced Biological Control Agents , 2001, Science.

[35]  J. Pérez,et al.  A new species of Felicola (Phthiraptera: Trichodectidae) from the endangered Iberian lynx: another reason to ensure its survival , 2001, Biodiversity & Conservation.