Science and Nature

Amphibians, a unique group of vertebrates containing > 7000 known species, are threatened worldwide. A recent assessment of the entire group (iucnredlist.org/amphibians) found that nearly one-third (32%) of the world’s amphibian species are threatened, representing 1,856 species. Amphibians have existed on earth for over 300 million years, yet in just the last two decades there have been an alarming number of extinctions, nearly 168 species are believed to have gone extinct and at least 2,469 (43%) more have populations that are declining. This indicates that the number of extinct and threatened species will probably continue to rise (Stuart et al. 2004).

Amphibian diversity is highest in the tropics and Brazil has the most described species at 932 species. By contrast, the United States is nearly the same size as Brazil but has 297 species (as of Feb 13, 2013).

II. Map of Global Declines

Declines have occured around the world, the areas that have suffered the most declines include Central America, the Caribbean, and Australia.

III. Why Are Amphibian Populations Declining?

Clearly, the most important factor leading to amphibian population declines is habitat destruction. When forests are cleared it is no surprise that species that once lived there disappear. What is alarming is that there are many cases where the habitat is protected and amphibians are still disappearing. The causes for recent amphibian declines are many, but an emerging disease called chytridiomycosis and global climate change are thought the be the biggest threats to amphibians. Chytridiomycosis is a disease caused by the fungal chytrid pathogen Batrachochytrium dendrobatidis. This pathogen is associated with the global loss of hundreds of species of amphibians and represents a spectacular loss of biodiversity, some say the worst in recorded history.
In the table below we break down all of the hypothesized factors and the links provide more detailed information for each one. Some factors are obviously shared with other types of endangered species on our planet and are part of to the worldwide biodiversity crisis such as habitat destruction, alteration and fragmentation (Fisher and Shaffer 1996, Davidson et al. 2001, Marsh and Trenham 2001), introduced species (Vredenburg 2004, Kats and Ferrer 2003) andover-exploitation (Jennings and Hayes 1985, Lannoo et al. 1994). For these threats, we have a pretty good understanding of the ecological mechanisms underlying declines (Collins and Storfer 2003). However, amphibians have also declined in relatively ‘pristine’ and protected environments (Wake 1991, Crump et al. 1992, Lips 2000). These more complex and elusive mechanisms include climate change (Pounds et al. 1999, Kiesecker et al. 2001, Carey and Alexander 2003), increased UV-B radiation, chemical contaminants (Hayes et al. 2002, Blaustein et al. 2003), emerging infectious diseases (Daszak et al. 2003; see AmphibiaWeb's global distribution map of chytrid) and deformities (or malformations). The underlying mechanisms behind these factors are complex and they may be working synergistically with more straight forward factors, such as habitat destruction and introduced species, to exacerbate declines (Kiesecker et al. 2001, Blaustein and Kiesecker 2002). Researchers are finding that there is not a single overarching cause for global declines, instead all of these factors are threatening amphibian populations and the threat tends to vary depending on the location. If we are going to prevent further extinctions, research must move forward quickly and be used effectively in management by governments and non-governmental organizations around the world.

IV. Factors Involved in Amphibian Declines

Table 1. Probable and confirmed factors causing amphibian declines (modified from Table 1 in Young et al. 2001).

FACTOR	PROCESS(ES)
Habitat destruction, alteration and Fragmentation	Roads, introduced species, or other factors separate remaining populations of amphibians from each other.
Introduced Species	Non-native species prey on or compete with native amphibians.
Over-Exploitation	Amphibians are removed form the wild and sold internationally as food, as pets, or for medicinal and biological supply markets
Climate Change	Amphibians are extremely sensitive to small changes in temperature and moisture. Changes in global weather patterns (e.g. El Niño events or global warming) can alter breeding behavior, affect reproductive success, decrease immune functions and increase amphibian sensitivity to chemical contaminants.
UV-B Radiation	Levels of UV-B radiation in the atmosphere have risen significantly over the past few decades. Researchers have found that UV-B radiation can kill amphibians directly, cause sublethal effects such as slowed growth rates and immune dysfunction, and work synergistically with contaminants, pathogens and climate change.
Chemical Contaminants	Chemical stressors (e.g., pesticides, heavy metals, acidification and nitrogen based fertilizers) can have lethal, sublethal, direct or indirect effects on amphibians. These effects may include death, decreased growth rates, developmental and behavioral abnormalities, decreased reproductive success, weakened immune systems and/or hermaphroditism.
Disease	New diseases (such as chytridiomycosis) or higher susceptibility to existing diseases leads to deaths of adults and larvae.
Deformities	There has been a recent and widespread increase of deformities (or malformations) in natural populations of amphibians; this is now perceived as a major environmental problem.
Synergisms	Multiple factors can act together to cause mortality or sublethal effects.

V. Possible Solutions: WHAT CAN BE DONE TO SAVE AMPHIBIANS?

The Global Amphibian Assessment has created an AMPHIBIAN ACTION CONSERVATION PLAN (pdf).

Table 2. Here are some other ways to reverse or ameliorate Amphibian Declines:

SOLUTION	PROCESS(ES)
Captive Breeding	Captive breeding progams for endangered species are being carried out in zoos.
Reintroductions	Reintroduction programs place amphibians back into wild habitats in the hope that new populations can be established.
Non-native Species Removal	Introduced species are being removed where they threaten native species.

VI. Literature Cited

Alford, R. A., and S. J. Richards. 1999. Global amphibian declines: A problem in applied ecology. Pages 133-165 in Annual Review of Ecology and Systematics. Annual Reviews, Palo Alto.
Blaustein, A. R., and J. M. Kiesecker. 2002. Complexity in conservation: Lessons from the global decline of amphibian populations. Ecology Letters 5:597-608.
Blaustein, A. R., J. M. Romansic, J. M. Kiesecker, and A. C. Hatch. 2003. Ultraviolet radiation, toxic chemicals and amphibian population declines. Diversity & Distributions [print] 9:123-140.
Blaustein, A. R., and D. B. Wake. 1990. Declining amphibian populations - a global phenomenon. Trends in Ecology & Evolution 5:203-204.
Carey, C., and M. A. Alexander. 2003. Climate change and amphibian declines: is there a link? Diversity and Distributions 9:111-121.
Collins, J. P., and A. Storfer. 2003. Global amphibian declines: Sorting the hypotheses. Diversity & Distributions [print] 9:89-98.
Crump, M. L., F. R. Hensley, and K. L. Clark. 1992. Apparent decline of the Golden Toad: underground or extinct? Copeia 1992:413-420.
Daszak, P., A. A. Cunningham, and A. D. Hyatt. 2003. Infectious disease and amphibian population declines. Diversity & Distributions [print] 9:141-150.
Davidson, C., H. B. Shaffer, and M. R. Jennings. 2001. Declines of the California red-legged frog: Climate, UV-B, habitat, and pesticides hypotheses. Ecological Applications 11:464-479.
Fisher, R. N., and H. B. Shaffer. 1996. The decline of amphibians in California's Great Central Valley. Conservation Biology 10:1387-1397.
Hayes, T. B., A. Collins, M. Lee, M. Mendoza, N. Noriega, A. A. Stuart, and A. Vonk. 2002. Hermaphroditic, demasculinized frogs after exposure to the herbicide atrazine at low ecologically relevant doses. Proceedings of the National Academy of Sciences of the United States of America 99:5476-5480.
Houlahan, J. E., C. S. Findlay, B. R. Schmidt, A. H. Meyer, and S. L. Kuzmin. 2000. Quantitative evidence for global amphibian population declines. Nature 404:752-755.
Jennings, M. R., and M. P. Hayes. 1985. Pre-1900 overharvest of California [USA] red-legged frogs (Rana aurora draytonii): The inducement for bullfrog (Rana catesbeiana) introduction. Herpetologica 41:94-103.
Kats, L. B., and R. P. Ferrer. 2003. Alien predators and amphibian declines: Review of two decades of science and the transition to conservation. Diversity & Distributions [print] 9:99-110.
Kiesecker, J. M., A. R. Blaustein, and L. K. Belden. 2001. Complex causes of amphibian population declines. Nature 410:681-684.
Lannoo, M. J., K. Lang, T. Waltz, and G. S. Phillips. 1994. An altered amphibian assemblage: Dickinson County, Iowa, 70 years after Frank Blanchard's survey. American Midland Naturalist 131:311-319.
Lips, K. R. 2000. Decline of a tropical amphibian fauna. in 166th National Meeting of the American Association for the Advancement of Science (AAAS) and Science Innovation Exposition., Washington, D.C., USA, February 17-22, 2000.
Marsh, D. M., and P. C. Trenham. 2001. Metapopulation dynamics and amphibian conservation. Conservation Biology 15:40-49.
Pounds, A., M. Fogden, and J. Campbell. 1999. Biological response to climate change on a tropical mountain. Nature 398:611-614.
Stuart, S., Chanson, J. S., Cox, N. A., Young, B. E., Rodrigues, A. S. L., Fishman, D. L. and Waller, R. W. 2004. Status and trends of amphibian declines and extinctions worldwide. - Science 306: 1783-1786.
Vredenburg, V. T. 2004. Reversing introduced species effects: Experimental removal of introduced fish leads to rapid recovery of declining frog. Proceedings of the National Academy of Sciences 101(20):7646-7650.
Wake, D. B. 1991. Declining amphibian populations. Science 253:860.
Young, B. E., K. R. Lips, J. K. Reaser, R. Ibanez, A. W. Salas, J. R. Cedeno, L. A. Coloma, S. Ron, E. La Marca, J. R. Meyer, A. Munoz, F. Bolanos, G. Chaves, and D. Romo. 2001. Population declines and priorities for amphibian conservation in Latin America. Conservation Biology 15:1213-1223.

Source

Literature citations edited by John Wilkinson (johnjwilkinson at hotmail), May 14, 2008.

VII. Recent Scientific Publications

AmphibiaWeb maintains a list of recent scientific publications on amphibian declines and amphibian conservation.This list is compiled and updated monthly by Professor Tim Halliday (formerly DAPTF International Director) (t.r.halliday@open.ac.uk).

Magnolias are prized worldwide for their flowers and forms. Growing as large shrubs or trees, they produce showy, fragrant flowers that are white, pink, red, purple or yellow. Some forms are evergreen with glossy and leathery leaves and some evergreen types have buds, stems and undersides of leaves that are covered with attractive gold to copper to brown felt-like hairs. There are more than 200 species of Magnolia native to temperate, subtropical and tropical areas of southeastern Asia, eastern North America, Central America, the Caribbean and parts of South America. Many are now grown worldwide because of their beautiful flowers, shape and form.