fbpx
Wikipedia

Decline in amphibian populations

Since the 1980s, decreases in amphibian populations, including population decline and localized mass extinctions, have been observed in locations all over the world. This type of biodiversity loss is known as one of the most critical threats to global biodiversity. The possible causes include habitat destruction and modification, diseases, exploitation, pollution, pesticide use, introduced species, and ultraviolet-B radiation (UV-B). However, many of the causes of amphibian declines are still poorly understood, and the topic is currently a subject of ongoing research.

The Golden toad of Monteverde, Costa Rica, was among the first casualties of amphibian declines. Formerly abundant, it was last seen in 1989.

Modeling results found that the current extinction rate of amphibians could be 211 times greater than the background extinction rate. This estimate even goes up to 25,000–45,000 times if endangered species are also included in the computation.[1]

Scientists began observing reduced populations of several European amphibian species already in the 1950s. Nevertheless, awareness of the phenomenon as a global problem and its subsequent classification as a modern-day mass extinction only dates from the 1980s. By 1993, more than 500 species of frogs and salamanders on all five continents were in decline.

Observations edit

 
The distribution of 2,873 globally threatened amphibian species.[2]

In the past three decades, declines in populations of amphibians (the class of organisms that includes frogs, toads, salamanders, newts, and caecilians) have occurred worldwide. In 2004, the results were published of the first worldwide assessment of amphibian populations, the Global Amphibian Assessment. This found that 32% of species were globally threatened, at least 43% were experiencing some form of population decrease, and that between 9 and 122 species have become extinct since 1980.[3] As of 2010, the IUCN Red List, which incorporates the Global Amphibian Assessment and subsequent updates, lists 650 amphibian species as "Critically Endangered", and 35 as "Extinct".[4] Despite the high risk this group faces, recent evidence suggests the public is growing largely indifferent to this and other environmental problems, posing serious problems for conservationists and environmental workers alike.[5]

Declines in amphibian populations were first widely recognized in the late 1980s[citation needed], when a large gathering of herpetologists reported noticing declines in populations in amphibians across the globe.[6] Among these species, the Golden toad (Bufo periglenes) endemic to Monteverde, Costa Rica, featured prominently. It was the subject of scientific research until populations suddenly crashed in 1987 and it had disappeared completely by 1989.[7] Other species at Monteverde, including the Monteverde Harlequin Frog (Atelopus varius), also disappeared at the same time. Because these species were located in the pristine Monteverde Cloud Forest Reserve, and these extinctions could not be related to local human activities, they raised particular concern among biologists.[8]

Many scientists believe that amphibians serve as "canaries in a coal mine", and that declines in amphibian populations and species indicate that other groups of animals and plants will soon be at risk.[9]

Initial skepticism edit

When amphibian declines were first presented as a conservation issue in the late 1980s, some scientists remained unconvinced of the reality and gravity of the conservation issue.[10] Some biologists argued that populations of most organisms, amphibians included, naturally vary through time. They argued that the lack of long-term data on amphibian populations made it difficult to determine whether the anecdotal declines reported by biologists were worth the (often limited) time and money of conservation efforts.[citation needed]

However, since this initial skepticism, biologists have come to a consensus that declines in amphibian populations are a real and severe threat to biodiversity.[3] This consensus emerged with an increase in the number of studies that monitored amphibian populations, direct observation of mass mortality in pristine sites that lacked apparent cause, and an awareness that declines in amphibian populations are truly global in nature.[11]

Causes edit

Habitat loss, disease and climate change are thought to be responsible for the drastic decline in populations in recent years.[12]

Declines have been particularly intense in the western United States, Central America, South America, eastern Australia and Fiji (although cases of amphibian extinctions have appeared worldwide). While human activities are causing a loss of much of the world's biodiversity, amphibians appear to be suffering much greater effects than other classes of organism. Because amphibians generally have a two-staged life cycle consisting of both aquatic (larvae) and terrestrial (adult) phases, they are sensitive to both terrestrial and aquatic environmental effects. Because their skins are highly permeable, they may be more susceptible to toxins in the environment than other organisms such as birds or mammals.[9]

Numerous potential explanations for amphibian declines have been proposed. Most or all of these causes have been associated with some population declines, so each cause is likely to affect in certain circumstances but not others. Many of the causes of amphibian declines are well understood, and appear to affect other groups of organisms as well as amphibians. These causes include habitat modification and fragmentation, introduced predators or competitors, introduced species, pollution, pesticide use, or over-harvesting. However, many amphibian declines or extinctions have occurred in pristine habitats where the above effects are not likely to occur. The causes of these declines are complex, but many can be attributed to emerging diseases, climate change, increased ultraviolet-B radiation, or long-distance transmission of chemical contaminants by wind.

Artificial lighting has been suggested as another potential cause. Insects are attracted to lights making them scarcer within the amphibian habitats.[13][14]

Habitat modification edit

Habitat modification or destruction is one of the most dramatic issues affecting amphibian species worldwide. As amphibians generally need aquatic and terrestrial habitats to survive, threats to either habitat can affect populations. Hence, amphibians may be more vulnerable to habitat modification than organisms that only require one habitat type. Large scale climate changes may further be modifying aquatic habitats, preventing amphibians from spawning altogether.[15]

Habitat fragmentation edit

Habitat fragmentation occurs when habitats are isolated by habitat modification, such as when a small area of forest is completely surrounded by agricultural fields. Small populations that survive within such fragments are often susceptible to inbreeding, genetic drift, or extinction due to small fluctuations in the environment. [16]

Disease edit

Research from 2007 and 2018 indicated that the reemergence of varieties of chytrid fungi may account for a substantial fraction of the overall decline.[17][18][19]

A number of diseases have been related to mass die-offs or declines in populations of amphibians, including "red-leg" disease (Aeromonas hydrophila), Ranavirus (family Iridoviridae), Anuraperkinsus, and chytridiomycosis. It is not entirely clear why these diseases have suddenly begun to affect amphibian populations, but some evidence suggests that these diseases may have been spread by humans, or may be more virulent when combined with other environmental factors.[20]

Trematodes edit

 
Trematode cyst-infected Pacific Tree Frog (Hyla regilla) with supernumerary limbs, from La Pine, Deschutes County, Oregon, 1998–9. This 'category I' deformity (polymelia) is believed to be caused by the trematode cyst infection. The cartilage is stained blue and calcified bones in red.

There is considerable evidence that parasitic trematode platyhelminths (a type of fluke) have contributed to developmental abnormalities and population declines of amphibians in some regions.[21] These trematodes of the genus Ribeiroia have a complex life cycle with three host species. The first host includes a number of species of aquatic snails. The early larval stages of the trematodes then are transmitted into aquatic tadpoles, where the metacercariae (larvae) encyst in developing limb buds. These encysted life stages produce developmental abnormalities in post-metamorphic frogs, including additional or missing limbs.[6] These abnormalities increase frog predation by aquatic birds, the final host of the trematode.

 
Pacific Tree Frog with limb malformation induced by Ribeiroia ondatrae

A study showed that high levels of nutrients used in farming and ranching activities fuel parasite infections that have caused frog deformities in ponds and lakes across North America. The study showed increased levels of nitrogen and phosphorus cause sharp hikes in the abundance of trematodes, and that the parasites subsequently form cysts in the developing limbs of tadpoles causing missing limbs, extra limbs and other severe malformations including five or six extra or even no limbs.[22]

Pollution and chemical contaminants edit

There is evidence of chemical pollutants causing frog developmental deformities (extra limbs, or malformed eyes).[23][24] Pollutants have varying effects on frogs. Some alter the central nervous system; others cause a disruption in the production and secretion of hormones. Experimental studies have also shown that exposure to commonly used herbicides such as glyphosate (Tradename Roundup) or insecticides such as malathion or carbaryl greatly increase mortality of tadpoles.[25] Additional studies have indicated that terrestrial adult stages of amphibians are also susceptible to non-active ingredients in Roundup, particularly POEA, which is a surfactant.[26] Although sex reversal in some species of frogs occur naturally in pristine environments, certain estrogen-like pollutants can forcibly induce these changes.[27] In a study conducted in a laboratory at Uppsala University in Sweden, more than 50% of frogs exposed to levels of estrogen-like pollutants existing in natural bodies of water in Europe and the United States became females. Tadpoles exposed even to the weakest concentration of estrogen were twice as likely to become females while almost all of the control group given the heaviest dose became female.[28]

While most pesticide effects are likely to be local and restricted to areas near agriculture, there is evidence from the Sierra Nevada mountains of the western United States that pesticides are traveling long distances into pristine areas, including Yosemite National Park in California.[29]

Some recent evidence points to ozone as a possible contributing factor to the worldwide decline of amphibians.[30]

Ozone depletion, ultraviolet radiation and cloud cover edit

Like many other organisms, increasing ultraviolet-B (UVB) radiation due to stratospheric ozone depletion and other factors may harm the DNA of amphibians, particularly their eggs.[31][32] The amount of damage depends upon the life stage, the species type and other environmental parameters. Salamanders and frogs that produce less photolyase, an enzyme that counteracts DNA damage from UVB, are more susceptible to the effects of loss of the ozone layer. Exposure to ultraviolet radiation may not kill a particular species or life stage but may cause sublethal damage.

More than three dozen species of amphibians have been studied, with severe effects reported in more than 40 publications in peer-reviewed journals representing authors from North America, Europe and Australia. Experimental enclosure approaches to determine UVB effects on egg stages have been criticized; for example, egg masses were placed at water depths much shallower than is typical for natural oviposition sites. While UVB radiation is an important stressor for amphibians,[33] its effect on the egg stage may have been overstated.[34]

Anthropogenic climate change has likely exerted a major effect on amphibian declines. For example, in the Monteverde Cloud Forest, a series of unusually warm years led to the mass disappearances of the Monteverde Harlequin frog and the Golden Toad.[35] An increased level of cloud cover, a result of geoengineering[citation needed] and global warming, which has warmed the nights and cooled daytime temperatures, has been blamed for facilitating the growth and proliferation of the fungus Batrachochytrium dendrobatidis (the causative agent of the fungal infection chytridiomycosis).

 
An adult male Ecnomiohyla rabborum in the Atlanta Botanical Garden, a species ravaged by Batrachochytrium dendrobatidis in its native habitat. It was the last known surviving member of its species, and with its death on Sept 28, 2016, the species is believed to be extinct.[36][37]

Although the immediate cause of the die offs was the chytrid, climate change played a pivotal role in the extinctions. Researchers included this subtle connection in their inclusive climate-linked epidemic hypothesis, which acknowledged climatic change as a key factor in amphibian extinctions both in Costa Rica and elsewhere.[38]

New evidence has shown global warming to also be capable of directly degrading toads' body condition and survivorship.[39] Additionally, the phenomenon often colludes with landscape alteration, pollution, and species invasions to effect amphibian extinctions.[40]

Introduced predators edit

Non-native predators and competitors have also been found to affect the viability of frogs in their habitats. The mountain yellow-legged frog which typically inhabits the Sierra Nevada lakes have seen a decline in numbers due to stocking of non-native fish (trout) for recreational fishing. The developing tadpoles and froglets fall prey to the fish in large numbers. This interference in the frog's three-year metamorphosis is causing a decline that is manifest throughout their ecosystem.[41]

Increased noise levels edit

Frogs and toads are highly vocal, and their reproductive behaviour often involves the use of vocalizations. There have been suggestions that increased noise levels caused by human activities may be contributing to their declines. In a study in Thailand, increased ambient noise levels were shown to decrease calling in some species and to cause an increase in others.[42] This has, however, not been shown to be a cause for the widespread decline.

Symptoms of stressed populations edit

Amphibian populations in the beginning stages of decline often exhibit a number of signs, which may potentially be used to identify at-risk segments in conservation efforts. One such sign is developmental instability, which has been proven as evidence of environmental stress.[43] This environmental stress can potentially raise susceptibility to diseases such as chytridiomycosis, and thus lead to amphibian declines. In a study conducted in Queensland, Australia, for example, populations of two amphibian species, Litoria nannotis and Litoria genimaculata, were found to exhibit far greater levels of limb asymmetry in pre-decline years than in control years, the latter of which preceded die offs by an average of 16 years.[citation needed] Learning to identify such signals in the critical period before population declines occur might greatly improve conservation efforts.

Conservation measures edit

The first response to reports of declining amphibian populations was the formation of the Declining Amphibian Population Task Force (DAPTF) in 1990. DAPTF led efforts for increased amphibian population monitoring in order to establish the extent of the problem, and established working groups to look at different issues.[44][45] Results were communicated through the newsletter Froglog.

Much of this research went into the production of the first Global Amphibian Assessment (GAA), which was published in 2004 and assessed every known amphibian species against the IUCN Red List criteria. This found that approximately one third of amphibian species were threatened with extinction.[46] As a result of these shocking findings an Amphibian Conservation Summit was held in 2005, because it was considered "morally irresponsible to document amphibian declines and extinctions without also designing and promoting a response to this global crisis".[47]

Outputs from the Amphibian Conservation Summit included the first Amphibian Conservation Action Plan (ACAP)[47] and to merge the DAPTF and the Global Amphibian Specialist Group into the IUCN SSC Amphibian Specialist Group (ASG).[44] The ACAP established the elements required to respond to the crisis, including priority actions on a variety of thematic areas. The ASG is a global volunteer network of dedicated experts who work to provide the scientific foundation for effective amphibian conservation action around the world.

The ACAP (Gascon et al 2007), concerned that time and capability were short, recommended that all relevant species be immediately incorporated into ex situ breeding programs.[48] On 16 February 2007, scientists worldwide met in Atlanta, U.S., to form a group called the Amphibian Ark to help save more than 6,000 species of amphibians from disappearing by starting captive breeding programmes.[49] Overall between the call to action in 2007 and 2019 there has been a 57% increase in number of breeding programs, or 77 additional species.[48]

Areas with noticed frog extinctions, like Australia, have few policies that have been created to prevent the extinction of these species. However, local initiatives have been placed where conscious efforts to decrease global warming will also turn into a conscious effort towards saving the frogs. In South America, where there is also an increased decline of amphibian populations, there is no set policy to try to save frogs. Some suggestions would include getting entire governments to place a set of rules and institutions as a source of guidelines that local governments have to abide by.[50][51]

A critical issue is how to design protected areas for amphibians which will provide suitable conditions for their survival. Conservation efforts through the use of protected areas have shown to generally be a temporary solution to population decline and extinction because the amphibians become inbred.[52] It is crucial for most amphibians to maintain a high level of genetic variation through large and more diverse environments.

Education of local people to protect amphibians is crucial, along with legislation for local protection and limiting the use of toxic chemicals, including some fertilizers and pesticides in sensitive amphibian areas.[53]

See also edit

References edit

  1. ^ McCallum, M. L. (2007). (PDF). Journal of Herpetology. 41 (3): 483–491. doi:10.1670/0022-1511(2007)41[483:ADOECD]2.0.CO;2. S2CID 30162903. Archived from the original (PDF) on 2008-12-17.
  2. ^ Jennifer A. Luedtke; Janice Chanson; Kelsey Neam; et al. (4 October 2023). "Ongoing declines for the world's amphibians in the face of emerging threats" (PDF). Nature. 622 (7982): 308–314. doi:10.1038/S41586-023-06578-4. ISSN 1476-4687. Wikidata Q123056982.
  3. ^ a b Stuart, Simon N.; Chanson, Janice S.; Cox, Neil A.; Young, Bruce E.; Rodrigues, Ana S. L.; Fischman, Debra L.; Waller, Robert W. (3 December 2004). "Status and Trends of Amphibian Declines and Extinctions Worldwide". Science. 306 (5702): 1783–1786. Bibcode:2004Sci...306.1783S. CiteSeerX 10.1.1.225.9620. doi:10.1126/science.1103538. PMID 15486254. S2CID 86238651.
  4. ^ "IUCN Red List - Search Results". IUCN Red List of Threatened Species. Version 2010.3. IUCN. Retrieved September 8, 2010.
  5. ^ McCallum, M.L.; Bury, G.W. (2013). "Google search patterns suggest declining interest in the environment". Biodiversity and Conservation. 22 (6–7): 1355–1367. doi:10.1007/s10531-013-0476-6. S2CID 15593201.
  6. ^ a b Blaustein, A.R.; Wake, D.B. (1990). "Declining amphibian populations: a global phenomenon?". Trends in Ecology and Evolution. 5 (7): 203–204. doi:10.1016/0169-5347(90)90129-2.
  7. ^ Crump, M.L.; Hensley, F.R.; Clark, K.I. (1992). "Apparent decline of the golden toad: Underground or extinct?". Copeia. 1992 (2): 413–420. doi:10.2307/1446201. JSTOR 1446201.
  8. ^ J. Alan Pounds; Martha L. Crump (1994). "Amphibian Declines and Climate Disturbance: The Case of the Golden Toad and the Harlequin Frog". Conservation Biology. 8 (1): 72–85. doi:10.1046/j.1523-1739.1994.08010072.x. S2CID 53330451.
  9. ^ a b Science Daily (October 15, 2004), Amphibians in dramatic decline: Study finds nearly one third of species threatened with extinction. Sciencedaily.com. Retrieved on September 18, 2007.
  10. ^ Pechmann, J.H.K.; Scott, D.E.; Semlitsch, R.D.; Caldwell, J.P.; Vitt, L.J.; Gibbons, J.W. (1991). "Declining amphibian populations: the problem of separating human impacts from natural fluctuations". Science. 253 (5022): 892–895. Bibcode:1991Sci...253..892P. doi:10.1126/science.253.5022.892. PMID 17751826. S2CID 27171692.
  11. ^ Houlahan, J.E.; Findlay, C.S.; Schmidt, B.R.; Meyer, A.H.; Kuzmin, S.L. (2000). "Quantitative evidence for global amphibian population declines". Nature. 404 (6779): 752–758. Bibcode:2000Natur.404..752H. doi:10.1038/35008052. PMID 10783886. S2CID 4393392.
  12. ^ "Conservation International - Amphibians". Retrieved 8 August 2012.
  13. ^ Eisenbeis, G., 2006. Artificial night lighting and insects: Attraction of insects to streetlamps in a rural setting in Germany. In C. Rich & T. Longcore (eds), Ecological Consequences of Artificial Night Lighting. Island Press: 281-304.
  14. ^ Baker, B.J.; Richardson, J.M.L. (2006). "The effect of artificial light on male breeding-season behaviour in green frogs, Rana clamitans melanota". Canadian Journal of Zoology. 84 (10): 1528–1532. doi:10.1139/z06-142.
  15. ^ "Climate link to amphibian decline". BBC News. 2008-10-27. Retrieved 2010-05-01.
  16. ^ Knozowski, P.; Górski, A.; Stawicka, A. M.; Nowakowski, J. J. (2022-12-31). "Long-term changes in the diversity of amphibian communities inhabiting small water bodies in the urban area of Olsztyn (NE Poland)". The European Zoological Journal. 89 (1): 791–812. doi:10.1080/24750263.2022.2087773.
  17. ^ Kriger, Kerry M.; Hero, Jean‐Marc (26 July 2007). "The chytrid fungus Batrachochytrium dendrobatidis is non‐randomly distributed across amphibian breeding habitats". Diversity and Distributions. 13 (6): 781–788. doi:10.1111/j.1472-4642.2007.00394.x. S2CID 85857635. Batrachochytrium dendrobatidis has been implicated as the causative agent of mass moralities, population declines, and the extinctions of stream‐breeding amphibian species worldwide.
  18. ^ Retallick, Richard W. R.; Miera, Verma (2007). "Strain differences in the amphibian chytrid Batrachochytrium dendrobatidis and non-permanent, sub-lethal effects of infection" (PDF). Diseases of Aquatic Organisms. 75 (3): 201–207. doi:10.3354/dao075201. PMID 17629114. The chytrid fungus Batrachochytrium dendrobatidis (Bd) is likely the cause of numerous recent amphibian population declines worldwide.
  19. ^ O’Hanlon, Simon J; et al. (2018). "Recent Asian origin of chytrid fungi causing global amphibian declines". Science. 360 (6389): 621–627. Bibcode:2018Sci...360..621O. doi:10.1126/science.aar1965. PMC 6311102. PMID 29748278.
  20. ^ Daszak, Peter; Lee Berger; Andrew A. Cunningham; Alex D. Hyatt; D. Earl Green; Rick Speare (1999). "Emerging Infectious Diseases and Amphibian Population Declines". Emerging Infectious Diseases. 5 (6): 735–48. doi:10.3201/eid0506.990601. PMC 2640803. PMID 10603206.
  21. ^ Johnson, P.T.J.; Chase, J.M. (2004). "Parasites in the food web: linking amphibian malformations and aquatic eutrophication". Ecology Letters. 7 (7): 521–526. doi:10.1111/j.1461-0248.2004.00610.x.
  22. ^ Johnson PTJ; Jonathan M. Chase; Katherine L. Dosch; Richard B. Hartson; Jackson A. Gross; Don J. Larson; Daniel R. Sutherland; Stephen R. Carpenter (2007). "Aquatic eutrophication promotes pathogenic infection in amphibians". PNAS. 104 (40): 15781–15786. Bibcode:2007PNAS..10415781J. doi:10.1073/pnas.0707763104. PMC 2000446. PMID 17893332.
  23. ^ Blaustein, Andrew R; Pieter TJ Johnson (2003). (PDF). Front. Ecol. Environ. 1 (2): 87–94. doi:10.1890/1540-9295(2003)001[0087:TCODA]2.0.CO;2. ISSN 1540-9295. Archived from the original (PDF) on 2013-10-29.
  24. ^ Burkhart, James G.; Gerald Ankley; Heidi Bell; et al. (2000). "Strategies for assessing the implications of malformed frogs for environmental health". Environmental Health Perspectives. 108 (1): 83–90. doi:10.1289/ehp.0010883. JSTOR 3454299. PMC 1637865. PMID 10620528. Associated workshop held on December 4-5, 1997.
  25. ^ Relyea, R.A. (2004). "The impact of insecticides and herbicides on the biodiversity and productivity of aquatic communities". Ecological Applications. 15 (2): 618–627. doi:10.1890/03-5342.
  26. ^ Relyea, R.A. (2005). "The lethal impact of Roundup on aquatic and terrestrial amphibians". Ecological Applications. 15 (4): 1118–1124. doi:10.1890/04-1291.
  27. ^ . National Geographic. Archived from the original on February 20, 2021.
  28. ^ . Yahoo! News. 2007. Archived from the original on March 2, 2007. Retrieved 2007-03-01.
  29. ^ Grossi, Mark (24 July 2001). . The Fresno Bee. Archived from the original on June 18, 2007. Retrieved 2008-10-02.
  30. ^ Dohm, M.R.; et al. (2005). "Effects of ozone exposure on nonspecific phagocytic capacity of pulmonary macrophages from an amphibian, Bufo marinus". Environmental Toxicology and Chemistry. 24 (1): 205–210. doi:10.1897/04-040r.1. PMID 15683185. S2CID 6574504.
  31. ^ Andrew R. Blaustein; Joseph M. Kiesecker; Douglas P. Chivers; Robert G. Anthony (November 1995). "Ambient UV-B radiation causes deformities in amphibian embryos". PNAS. Vol. 92. pp. 11049–11052. doi:10.1073/pnas.92.24.11049. PMID 9391095.
  32. ^ Belden, Lisa K.; Blaustein, Andrew R. (2002). "Population differences in sensitivity to UV-b radiation for larval long-toed salamanders" (PDF). Ecology. 83 (6): 1586–1590. doi:10.1890/0012-9658(2002)083[1586:PDISTU]2.0.CO;2. ISSN 0012-9658.
  33. ^ Bancroft, B.A.; et al. (2007). "Effects of UVB radiation on marine and freshwater organisms: a synthesis through meta-analysis". Ecology Letters. 10 (4): 332–345. doi:10.1111/j.1461-0248.2007.01022.x. PMID 17355571.
  34. ^ Licht, LE (2003). "Shedding Light on Ultraviolet Radiation and Amphibian Embryos". BioScience. 53 (6): 551–561. doi:10.1641/0006-3568(2003)053[0551:sloura]2.0.co;2.
  35. ^ Alan Pounds, J.; Bustamante, Martín R.; Coloma, Luis A.; Consuegra, Jamie A.; Fogden, Michael P. L.; Foster, Pru N.; La Marca, Enrique; Masters, Karen L.; Merino-Viteri, Andrés; Puschendorf, Robert; Ron, Santiago R.; Sánchez-Azofeifa, G. Arturo; Still, Christopher J.; Young, Bruce E. (2006). "Widespread amphibian extinctions from epidemic disease driven by global warming" (PDF). Nature. 439 (7073): 161–167. Bibcode:2006Natur.439..161A. doi:10.1038/nature04246. PMID 16407945. S2CID 4430672.
  36. ^ Messenger, Stephen (2016-09-30). "Last Frog Of His Kind Dies Alone". The Dodo. Retrieved 30 September 2016.
  37. ^ Zoo Atlanta (February 17, 2012). . Atlanta Fulton County Zoo. Archived from the original on May 24, 2012. Retrieved March 12, 2012.
  38. ^ Pounds, J. Alan; Bustamante, Martín R.; Coloma, Luis A.; Consuegra, Jamie A.; Fogden, Michael P. L.; Foster, Pru N.; La Marca, Enrique; Masters, Karen L.; Merino-Viteri, Andrés; Puschendorf, Robert; Ron, Santiago R.; Sánchez-Azofeifa, G. Arturo; Still, Christopher J.; Young, Bruce E. (2007). "Global warming and amphibian losses; The proximate cause of frog declines? (Reply)". Nature. 447 (7144): E5–E6. Bibcode:2007Natur.447....5P. doi:10.1038/nature05942. S2CID 4372607.
  39. ^ Reading, C. J. (2006). (PDF). Oecologia. 151 (1): 125–131. doi:10.1007/s00442-006-0558-1. PMID 17024381. S2CID 24832716. Archived from the original (PDF) on 2014-02-02. Retrieved 2014-01-21.
  40. ^ Pounds, J. Alan; Puschendorf, Robert (2004). "Ecology: Clouded Futures (News & Views)". Nature. 427 (6970): 107–109. doi:10.1038/427107a. PMID 14712258. S2CID 877425.
  41. ^ Knapp, R. A.; Matthews, K. R. (2000). "Non-native fish introductions and the decline of the mountain yellow-legged frog from within protected areas". Conservation Biology. 14 (2): 428–438. doi:10.1046/j.1523-1739.2000.99099.x. S2CID 51734566.
  42. ^ Sun, Jennifer W.C.; Narins, Peter M. (2005). "Anthropogenic sounds differentially affect amphibian call rate" (PDF). Biological Conservation. 121 (3): 419–427. doi:10.1016/j.biocon.2004.05.017.
  43. ^ Alford, Ross A.; Bradfield, Kay S.; Richards, Stephen J. (2007). "Ecology: Global warming and amphibian losses" (PDF). Nature. 447 (7144): E3–E4. Bibcode:2007Natur.447....3A. doi:10.1038/nature05940. PMID 17538571. S2CID 4412404.
  44. ^ a b P. J. Bishop, A. Angulo, J. P. Lewis, Robin D. Moore, G. B. Rabb and J. Garcia Moreno, « The Amphibian Extinction Crisis - what will it take to put the action into the Amphibian Conservation Action Plan? », S.A.P.I.EN.S [Online], 5.2 | 2012, Online since 12 August 2012, connection on 09 April 2019. URL : http://journals.openedition.org/sapiens/1406
  45. ^ Alastair Campbell, ed. (1999). (PDF). Environment Australia. ISBN 0-642-54656-8. OCLC 44894378. Archived from the original (PDF) on 2011-11-14.
  46. ^ Stuart et al (2004) Status and Trends of Amphibian Declines and Extinctions Worldwide. Science. Vol. 306, Issue 5702, pp. 1783-1786. doi:10.1126/science.1103538
  47. ^ a b Gascon, Claude; Collins, James P.; Moore, Robin D.; Church, Don R.; McKay, Jeanne E.; Mendelson III, Joseph R., eds. (2007). Amphibian Conservation Action Plan. Gland/Cambridge: IUCN SSC Amphibian Specialist Group. S2CID 87645483.
  48. ^ a b Silla, Aimee J.; Byrne, Phillip G. (2019-02-15). "The Role of Reproductive Technologies in Amphibian Conservation Breeding Programs". Annual Review of Animal Biosciences. 7 (1). Annual Reviews: 499–519. doi:10.1146/annurev-animal-020518-115056. ISSN 2165-8102. PMID 30359086. S2CID 53098666.
  49. ^ . 2007. Archived from the original on 2015-10-18. Retrieved 2007-02-22.
  50. ^ "Amphibian Conservation Alliance". from the original on 29 September 2023.
  51. ^ [1][dead link]
  52. ^ Crump, M. (2002). Amphibians, Reptiles, and their Conservation. North Haven, CT: Linnet Books. ISBN 9780208025111.
  53. ^ Halliday, Adler (2008). The New Encyclopedia of Reptiles and Amphibians (2 ed.). Online: Oxford University Press. ISBN 9780198525073.

External links edit

  • IUCN Red List - Amphibians 2014-07-01 at the Wayback Machine – assesses the current status of amphibian species worldwide (incorporates the Global Amphibian Assessment)
  • AmphibiaWeb – provides background information on amphibian declines.
  • Weedicide induced feminization
  • at Queensland Frog Society

decline, amphibian, populations, since, 1980s, decreases, amphibian, populations, including, population, decline, localized, mass, extinctions, have, been, observed, locations, over, world, this, type, biodiversity, loss, known, most, critical, threats, global. Since the 1980s decreases in amphibian populations including population decline and localized mass extinctions have been observed in locations all over the world This type of biodiversity loss is known as one of the most critical threats to global biodiversity The possible causes include habitat destruction and modification diseases exploitation pollution pesticide use introduced species and ultraviolet B radiation UV B However many of the causes of amphibian declines are still poorly understood and the topic is currently a subject of ongoing research The Golden toad of Monteverde Costa Rica was among the first casualties of amphibian declines Formerly abundant it was last seen in 1989 Modeling results found that the current extinction rate of amphibians could be 211 times greater than the background extinction rate This estimate even goes up to 25 000 45 000 times if endangered species are also included in the computation 1 Scientists began observing reduced populations of several European amphibian species already in the 1950s Nevertheless awareness of the phenomenon as a global problem and its subsequent classification as a modern day mass extinction only dates from the 1980s By 1993 more than 500 species of frogs and salamanders on all five continents were in decline Contents 1 Observations 1 1 Initial skepticism 2 Causes 2 1 Habitat modification 2 2 Habitat fragmentation 2 3 Disease 2 3 1 Trematodes 2 4 Pollution and chemical contaminants 2 5 Ozone depletion ultraviolet radiation and cloud cover 2 6 Introduced predators 2 7 Increased noise levels 3 Symptoms of stressed populations 4 Conservation measures 5 See also 6 References 7 External linksObservations edit nbsp The distribution of 2 873 globally threatened amphibian species 2 In the past three decades declines in populations of amphibians the class of organisms that includes frogs toads salamanders newts and caecilians have occurred worldwide In 2004 the results were published of the first worldwide assessment of amphibian populations the Global Amphibian Assessment This found that 32 of species were globally threatened at least 43 were experiencing some form of population decrease and that between 9 and 122 species have become extinct since 1980 3 As of 2010 update the IUCN Red List which incorporates the Global Amphibian Assessment and subsequent updates lists 650 amphibian species as Critically Endangered and 35 as Extinct 4 Despite the high risk this group faces recent evidence suggests the public is growing largely indifferent to this and other environmental problems posing serious problems for conservationists and environmental workers alike 5 Declines in amphibian populations were first widely recognized in the late 1980s citation needed when a large gathering of herpetologists reported noticing declines in populations in amphibians across the globe 6 Among these species the Golden toad Bufo periglenes endemic to Monteverde Costa Rica featured prominently It was the subject of scientific research until populations suddenly crashed in 1987 and it had disappeared completely by 1989 7 Other species at Monteverde including the Monteverde Harlequin Frog Atelopus varius also disappeared at the same time Because these species were located in the pristine Monteverde Cloud Forest Reserve and these extinctions could not be related to local human activities they raised particular concern among biologists 8 Many scientists believe that amphibians serve as canaries in a coal mine and that declines in amphibian populations and species indicate that other groups of animals and plants will soon be at risk 9 Initial skepticism edit When amphibian declines were first presented as a conservation issue in the late 1980s some scientists remained unconvinced of the reality and gravity of the conservation issue 10 Some biologists argued that populations of most organisms amphibians included naturally vary through time They argued that the lack of long term data on amphibian populations made it difficult to determine whether the anecdotal declines reported by biologists were worth the often limited time and money of conservation efforts citation needed However since this initial skepticism biologists have come to a consensus that declines in amphibian populations are a real and severe threat to biodiversity 3 This consensus emerged with an increase in the number of studies that monitored amphibian populations direct observation of mass mortality in pristine sites that lacked apparent cause and an awareness that declines in amphibian populations are truly global in nature 11 Causes editHabitat loss disease and climate change are thought to be responsible for the drastic decline in populations in recent years 12 Declines have been particularly intense in the western United States Central America South America eastern Australia and Fiji although cases of amphibian extinctions have appeared worldwide While human activities are causing a loss of much of the world s biodiversity amphibians appear to be suffering much greater effects than other classes of organism Because amphibians generally have a two staged life cycle consisting of both aquatic larvae and terrestrial adult phases they are sensitive to both terrestrial and aquatic environmental effects Because their skins are highly permeable they may be more susceptible to toxins in the environment than other organisms such as birds or mammals 9 Numerous potential explanations for amphibian declines have been proposed Most or all of these causes have been associated with some population declines so each cause is likely to affect in certain circumstances but not others Many of the causes of amphibian declines are well understood and appear to affect other groups of organisms as well as amphibians These causes include habitat modification and fragmentation introduced predators or competitors introduced species pollution pesticide use or over harvesting However many amphibian declines or extinctions have occurred in pristine habitats where the above effects are not likely to occur The causes of these declines are complex but many can be attributed to emerging diseases climate change increased ultraviolet B radiation or long distance transmission of chemical contaminants by wind Artificial lighting has been suggested as another potential cause Insects are attracted to lights making them scarcer within the amphibian habitats 13 14 Habitat modification edit Main article Habitat destruction Habitat modification or destruction is one of the most dramatic issues affecting amphibian species worldwide As amphibians generally need aquatic and terrestrial habitats to survive threats to either habitat can affect populations Hence amphibians may be more vulnerable to habitat modification than organisms that only require one habitat type Large scale climate changes may further be modifying aquatic habitats preventing amphibians from spawning altogether 15 Habitat fragmentation edit Main article Habitat fragmentation Habitat fragmentation occurs when habitats are isolated by habitat modification such as when a small area of forest is completely surrounded by agricultural fields Small populations that survive within such fragments are often susceptible to inbreeding genetic drift or extinction due to small fluctuations in the environment 16 Disease edit Research from 2007 and 2018 indicated that the reemergence of varieties of chytrid fungi may account for a substantial fraction of the overall decline 17 18 19 A number of diseases have been related to mass die offs or declines in populations of amphibians including red leg disease Aeromonas hydrophila Ranavirus family Iridoviridae Anuraperkinsus and chytridiomycosis It is not entirely clear why these diseases have suddenly begun to affect amphibian populations but some evidence suggests that these diseases may have been spread by humans or may be more virulent when combined with other environmental factors 20 Trematodes edit Further information Ribeiroia nbsp Trematode cyst infected Pacific Tree Frog Hyla regilla with supernumerary limbs from La Pine Deschutes County Oregon 1998 9 This category I deformity polymelia is believed to be caused by the trematode cyst infection The cartilage is stained blue and calcified bones in red There is considerable evidence that parasitic trematode platyhelminths a type of fluke have contributed to developmental abnormalities and population declines of amphibians in some regions 21 These trematodes of the genus Ribeiroia have a complex life cycle with three host species The first host includes a number of species of aquatic snails The early larval stages of the trematodes then are transmitted into aquatic tadpoles where the metacercariae larvae encyst in developing limb buds These encysted life stages produce developmental abnormalities in post metamorphic frogs including additional or missing limbs 6 These abnormalities increase frog predation by aquatic birds the final host of the trematode nbsp Pacific Tree Frog with limb malformation induced by Ribeiroia ondatraeA study showed that high levels of nutrients used in farming and ranching activities fuel parasite infections that have caused frog deformities in ponds and lakes across North America The study showed increased levels of nitrogen and phosphorus cause sharp hikes in the abundance of trematodes and that the parasites subsequently form cysts in the developing limbs of tadpoles causing missing limbs extra limbs and other severe malformations including five or six extra or even no limbs 22 Pollution and chemical contaminants edit There is evidence of chemical pollutants causing frog developmental deformities extra limbs or malformed eyes 23 24 Pollutants have varying effects on frogs Some alter the central nervous system others cause a disruption in the production and secretion of hormones Experimental studies have also shown that exposure to commonly used herbicides such as glyphosate Tradename Roundup or insecticides such as malathion or carbaryl greatly increase mortality of tadpoles 25 Additional studies have indicated that terrestrial adult stages of amphibians are also susceptible to non active ingredients in Roundup particularly POEA which is a surfactant 26 Although sex reversal in some species of frogs occur naturally in pristine environments certain estrogen like pollutants can forcibly induce these changes 27 In a study conducted in a laboratory at Uppsala University in Sweden more than 50 of frogs exposed to levels of estrogen like pollutants existing in natural bodies of water in Europe and the United States became females Tadpoles exposed even to the weakest concentration of estrogen were twice as likely to become females while almost all of the control group given the heaviest dose became female 28 While most pesticide effects are likely to be local and restricted to areas near agriculture there is evidence from the Sierra Nevada mountains of the western United States that pesticides are traveling long distances into pristine areas including Yosemite National Park in California 29 Some recent evidence points to ozone as a possible contributing factor to the worldwide decline of amphibians 30 Ozone depletion ultraviolet radiation and cloud cover edit See also Climate change Like many other organisms increasing ultraviolet B UVB radiation due to stratospheric ozone depletion and other factors may harm the DNA of amphibians particularly their eggs 31 32 The amount of damage depends upon the life stage the species type and other environmental parameters Salamanders and frogs that produce less photolyase an enzyme that counteracts DNA damage from UVB are more susceptible to the effects of loss of the ozone layer Exposure to ultraviolet radiation may not kill a particular species or life stage but may cause sublethal damage More than three dozen species of amphibians have been studied with severe effects reported in more than 40 publications in peer reviewed journals representing authors from North America Europe and Australia Experimental enclosure approaches to determine UVB effects on egg stages have been criticized for example egg masses were placed at water depths much shallower than is typical for natural oviposition sites While UVB radiation is an important stressor for amphibians 33 its effect on the egg stage may have been overstated 34 Anthropogenic climate change has likely exerted a major effect on amphibian declines For example in the Monteverde Cloud Forest a series of unusually warm years led to the mass disappearances of the Monteverde Harlequin frog and the Golden Toad 35 An increased level of cloud cover a result of geoengineering citation needed and global warming which has warmed the nights and cooled daytime temperatures has been blamed for facilitating the growth and proliferation of the fungus Batrachochytrium dendrobatidis the causative agent of the fungal infection chytridiomycosis nbsp An adult male Ecnomiohyla rabborum in the Atlanta Botanical Garden a species ravaged by Batrachochytrium dendrobatidis in its native habitat It was the last known surviving member of its species and with its death on Sept 28 2016 the species is believed to be extinct 36 37 Although the immediate cause of the die offs was the chytrid climate change played a pivotal role in the extinctions Researchers included this subtle connection in their inclusive climate linked epidemic hypothesis which acknowledged climatic change as a key factor in amphibian extinctions both in Costa Rica and elsewhere 38 New evidence has shown global warming to also be capable of directly degrading toads body condition and survivorship 39 Additionally the phenomenon often colludes with landscape alteration pollution and species invasions to effect amphibian extinctions 40 Introduced predators edit Main article Introduced species Non native predators and competitors have also been found to affect the viability of frogs in their habitats The mountain yellow legged frog which typically inhabits the Sierra Nevada lakes have seen a decline in numbers due to stocking of non native fish trout for recreational fishing The developing tadpoles and froglets fall prey to the fish in large numbers This interference in the frog s three year metamorphosis is causing a decline that is manifest throughout their ecosystem 41 Increased noise levels edit Frogs and toads are highly vocal and their reproductive behaviour often involves the use of vocalizations There have been suggestions that increased noise levels caused by human activities may be contributing to their declines In a study in Thailand increased ambient noise levels were shown to decrease calling in some species and to cause an increase in others 42 This has however not been shown to be a cause for the widespread decline Symptoms of stressed populations editAmphibian populations in the beginning stages of decline often exhibit a number of signs which may potentially be used to identify at risk segments in conservation efforts One such sign is developmental instability which has been proven as evidence of environmental stress 43 This environmental stress can potentially raise susceptibility to diseases such as chytridiomycosis and thus lead to amphibian declines In a study conducted in Queensland Australia for example populations of two amphibian species Litoria nannotis and Litoria genimaculata were found to exhibit far greater levels of limb asymmetry in pre decline years than in control years the latter of which preceded die offs by an average of 16 years citation needed Learning to identify such signals in the critical period before population declines occur might greatly improve conservation efforts Conservation measures editSee also Amphibian Ark The first response to reports of declining amphibian populations was the formation of the Declining Amphibian Population Task Force DAPTF in 1990 DAPTF led efforts for increased amphibian population monitoring in order to establish the extent of the problem and established working groups to look at different issues 44 45 Results were communicated through the newsletter Froglog Much of this research went into the production of the first Global Amphibian Assessment GAA which was published in 2004 and assessed every known amphibian species against the IUCN Red List criteria This found that approximately one third of amphibian species were threatened with extinction 46 As a result of these shocking findings an Amphibian Conservation Summit was held in 2005 because it was considered morally irresponsible to document amphibian declines and extinctions without also designing and promoting a response to this global crisis 47 Outputs from the Amphibian Conservation Summit included the first Amphibian Conservation Action Plan ACAP 47 and to merge the DAPTF and the Global Amphibian Specialist Group into the IUCN SSC Amphibian Specialist Group ASG 44 The ACAP established the elements required to respond to the crisis including priority actions on a variety of thematic areas The ASG is a global volunteer network of dedicated experts who work to provide the scientific foundation for effective amphibian conservation action around the world The ACAP Gascon et al 2007 concerned that time and capability were short recommended that all relevant species be immediately incorporated into ex situ breeding programs 48 On 16 February 2007 scientists worldwide met in Atlanta U S to form a group called the Amphibian Ark to help save more than 6 000 species of amphibians from disappearing by starting captive breeding programmes 49 Overall between the call to action in 2007 and 2019 there has been a 57 increase in number of breeding programs or 77 additional species 48 Areas with noticed frog extinctions like Australia have few policies that have been created to prevent the extinction of these species However local initiatives have been placed where conscious efforts to decrease global warming will also turn into a conscious effort towards saving the frogs In South America where there is also an increased decline of amphibian populations there is no set policy to try to save frogs Some suggestions would include getting entire governments to place a set of rules and institutions as a source of guidelines that local governments have to abide by 50 51 A critical issue is how to design protected areas for amphibians which will provide suitable conditions for their survival Conservation efforts through the use of protected areas have shown to generally be a temporary solution to population decline and extinction because the amphibians become inbred 52 It is crucial for most amphibians to maintain a high level of genetic variation through large and more diverse environments Education of local people to protect amphibians is crucial along with legislation for local protection and limiting the use of toxic chemicals including some fertilizers and pesticides in sensitive amphibian areas 53 See also edit nbsp Amphibians portalEffects of pesticides on amphibians Holocene extinction Colony collapse disorder Decline in insect populations White nose syndrome The Sixth Extinction book Racing Extinction film References edit McCallum M L 2007 Amphibian Decline or Extinction Current Declines Dwarf Background Extinction Rate PDF Journal of Herpetology 41 3 483 491 doi 10 1670 0022 1511 2007 41 483 ADOECD 2 0 CO 2 S2CID 30162903 Archived from the original PDF on 2008 12 17 Jennifer A Luedtke Janice Chanson Kelsey Neam et al 4 October 2023 Ongoing declines for the world s amphibians in the face of emerging threats PDF Nature 622 7982 308 314 doi 10 1038 S41586 023 06578 4 ISSN 1476 4687 Wikidata Q123056982 a b Stuart Simon N Chanson Janice S Cox Neil A Young Bruce E Rodrigues Ana S L Fischman Debra L Waller Robert W 3 December 2004 Status and Trends of Amphibian Declines and Extinctions Worldwide Science 306 5702 1783 1786 Bibcode 2004Sci 306 1783S CiteSeerX 10 1 1 225 9620 doi 10 1126 science 1103538 PMID 15486254 S2CID 86238651 IUCN Red List Search Results IUCN Red List of Threatened Species Version 2010 3 IUCN Retrieved September 8 2010 McCallum M L Bury G W 2013 Google search patterns suggest declining interest in the environment Biodiversity and Conservation 22 6 7 1355 1367 doi 10 1007 s10531 013 0476 6 S2CID 15593201 a b Blaustein A R Wake D B 1990 Declining amphibian populations a global phenomenon Trends in Ecology and Evolution 5 7 203 204 doi 10 1016 0169 5347 90 90129 2 Crump M L Hensley F R Clark K I 1992 Apparent decline of the golden toad Underground or extinct Copeia 1992 2 413 420 doi 10 2307 1446201 JSTOR 1446201 J Alan Pounds Martha L Crump 1994 Amphibian Declines and Climate Disturbance The Case of the Golden Toad and the Harlequin Frog Conservation Biology 8 1 72 85 doi 10 1046 j 1523 1739 1994 08010072 x S2CID 53330451 a b Science Daily October 15 2004 Amphibians in dramatic decline Study finds nearly one third of species threatened with extinction Sciencedaily com Retrieved on September 18 2007 Pechmann J H K Scott D E Semlitsch R D Caldwell J P Vitt L J Gibbons J W 1991 Declining amphibian populations the problem of separating human impacts from natural fluctuations Science 253 5022 892 895 Bibcode 1991Sci 253 892P doi 10 1126 science 253 5022 892 PMID 17751826 S2CID 27171692 Houlahan J E Findlay C S Schmidt B R Meyer A H Kuzmin S L 2000 Quantitative evidence for global amphibian population declines Nature 404 6779 752 758 Bibcode 2000Natur 404 752H doi 10 1038 35008052 PMID 10783886 S2CID 4393392 Conservation International Amphibians Retrieved 8 August 2012 Eisenbeis G 2006 Artificial night lighting and insects Attraction of insects to streetlamps in a rural setting in Germany In C Rich amp T Longcore eds Ecological Consequences of Artificial Night Lighting Island Press 281 304 Baker B J Richardson J M L 2006 The effect of artificial light on male breeding season behaviour in green frogs Rana clamitans melanota Canadian Journal of Zoology 84 10 1528 1532 doi 10 1139 z06 142 Climate link to amphibian decline BBC News 2008 10 27 Retrieved 2010 05 01 Knozowski P Gorski A Stawicka A M Nowakowski J J 2022 12 31 Long term changes in the diversity of amphibian communities inhabiting small water bodies in the urban area of Olsztyn NE Poland The European Zoological Journal 89 1 791 812 doi 10 1080 24750263 2022 2087773 Kriger Kerry M Hero Jean Marc 26 July 2007 The chytrid fungus Batrachochytrium dendrobatidis is non randomly distributed across amphibian breeding habitats Diversity and Distributions 13 6 781 788 doi 10 1111 j 1472 4642 2007 00394 x S2CID 85857635 Batrachochytrium dendrobatidis has been implicated as the causative agent of mass moralities population declines and the extinctions of stream breeding amphibian species worldwide Retallick Richard W R Miera Verma 2007 Strain differences in the amphibian chytrid Batrachochytrium dendrobatidis and non permanent sub lethal effects of infection PDF Diseases of Aquatic Organisms 75 3 201 207 doi 10 3354 dao075201 PMID 17629114 The chytrid fungus Batrachochytrium dendrobatidis Bd is likely the cause of numerous recent amphibian population declines worldwide O Hanlon Simon J et al 2018 Recent Asian origin of chytrid fungi causing global amphibian declines Science 360 6389 621 627 Bibcode 2018Sci 360 621O doi 10 1126 science aar1965 PMC 6311102 PMID 29748278 Daszak Peter Lee Berger Andrew A Cunningham Alex D Hyatt D Earl Green Rick Speare 1999 Emerging Infectious Diseases and Amphibian Population Declines Emerging Infectious Diseases 5 6 735 48 doi 10 3201 eid0506 990601 PMC 2640803 PMID 10603206 Johnson P T J Chase J M 2004 Parasites in the food web linking amphibian malformations and aquatic eutrophication Ecology Letters 7 7 521 526 doi 10 1111 j 1461 0248 2004 00610 x Johnson PTJ Jonathan M Chase Katherine L Dosch Richard B Hartson Jackson A Gross Don J Larson Daniel R Sutherland Stephen R Carpenter 2007 Aquatic eutrophication promotes pathogenic infection in amphibians PNAS 104 40 15781 15786 Bibcode 2007PNAS 10415781J doi 10 1073 pnas 0707763104 PMC 2000446 PMID 17893332 Blaustein Andrew R Pieter TJ Johnson 2003 The complexity of deformed amphibians PDF Front Ecol Environ 1 2 87 94 doi 10 1890 1540 9295 2003 001 0087 TCODA 2 0 CO 2 ISSN 1540 9295 Archived from the original PDF on 2013 10 29 Burkhart James G Gerald Ankley Heidi Bell et al 2000 Strategies for assessing the implications of malformed frogs for environmental health Environmental Health Perspectives 108 1 83 90 doi 10 1289 ehp 0010883 JSTOR 3454299 PMC 1637865 PMID 10620528 Associated workshop held on December 4 5 1997 Relyea R A 2004 The impact of insecticides and herbicides on the biodiversity and productivity of aquatic communities Ecological Applications 15 2 618 627 doi 10 1890 03 5342 Relyea R A 2005 The lethal impact of Roundup on aquatic and terrestrial amphibians Ecological Applications 15 4 1118 1124 doi 10 1890 04 1291 Healthy frogs can mysteriously reverse their sex National Geographic Archived from the original on February 20 2021 Pollutants change he frogs into she frogs Yahoo News 2007 Archived from the original on March 2 2007 Retrieved 2007 03 01 Grossi Mark 24 July 2001 Sierra Frogs Fall Silent The Fresno Bee Archived from the original on June 18 2007 Retrieved 2008 10 02 Dohm M R et al 2005 Effects of ozone exposure on nonspecific phagocytic capacity of pulmonary macrophages from an amphibian Bufo marinus Environmental Toxicology and Chemistry 24 1 205 210 doi 10 1897 04 040r 1 PMID 15683185 S2CID 6574504 Andrew R Blaustein Joseph M Kiesecker Douglas P Chivers Robert G Anthony November 1995 Ambient UV B radiation causes deformities in amphibian embryos PNAS Vol 92 pp 11049 11052 doi 10 1073 pnas 92 24 11049 PMID 9391095 Belden Lisa K Blaustein Andrew R 2002 Population differences in sensitivity to UV b radiation for larval long toed salamanders PDF Ecology 83 6 1586 1590 doi 10 1890 0012 9658 2002 083 1586 PDISTU 2 0 CO 2 ISSN 0012 9658 Bancroft B A et al 2007 Effects of UVB radiation on marine and freshwater organisms a synthesis through meta analysis Ecology Letters 10 4 332 345 doi 10 1111 j 1461 0248 2007 01022 x PMID 17355571 Licht LE 2003 Shedding Light on Ultraviolet Radiation and Amphibian Embryos BioScience 53 6 551 561 doi 10 1641 0006 3568 2003 053 0551 sloura 2 0 co 2 Alan Pounds J Bustamante Martin R Coloma Luis A Consuegra Jamie A Fogden Michael P L Foster Pru N La Marca Enrique Masters Karen L Merino Viteri Andres Puschendorf Robert Ron Santiago R Sanchez Azofeifa G Arturo Still Christopher J Young Bruce E 2006 Widespread amphibian extinctions from epidemic disease driven by global warming PDF Nature 439 7073 161 167 Bibcode 2006Natur 439 161A doi 10 1038 nature04246 PMID 16407945 S2CID 4430672 Messenger Stephen 2016 09 30 Last Frog Of His Kind Dies Alone The Dodo Retrieved 30 September 2016 Zoo Atlanta February 17 2012 It s Leap Year Remember the Rabbs tree frog Atlanta Fulton County Zoo Archived from the original on May 24 2012 Retrieved March 12 2012 Pounds J Alan Bustamante Martin R Coloma Luis A Consuegra Jamie A Fogden Michael P L Foster Pru N La Marca Enrique Masters Karen L Merino Viteri Andres Puschendorf Robert Ron Santiago R Sanchez Azofeifa G Arturo Still Christopher J Young Bruce E 2007 Global warming and amphibian losses The proximate cause of frog declines Reply Nature 447 7144 E5 E6 Bibcode 2007Natur 447 5P doi 10 1038 nature05942 S2CID 4372607 Reading C J 2006 Linking global warming to amphibian declines through its effects on female body condition and survivorship PDF Oecologia 151 1 125 131 doi 10 1007 s00442 006 0558 1 PMID 17024381 S2CID 24832716 Archived from the original PDF on 2014 02 02 Retrieved 2014 01 21 Pounds J Alan Puschendorf Robert 2004 Ecology Clouded Futures News amp Views Nature 427 6970 107 109 doi 10 1038 427107a PMID 14712258 S2CID 877425 Knapp R A Matthews K R 2000 Non native fish introductions and the decline of the mountain yellow legged frog from within protected areas Conservation Biology 14 2 428 438 doi 10 1046 j 1523 1739 2000 99099 x S2CID 51734566 Sun Jennifer W C Narins Peter M 2005 Anthropogenic sounds differentially affect amphibian call rate PDF Biological Conservation 121 3 419 427 doi 10 1016 j biocon 2004 05 017 Alford Ross A Bradfield Kay S Richards Stephen J 2007 Ecology Global warming and amphibian losses PDF Nature 447 7144 E3 E4 Bibcode 2007Natur 447 3A doi 10 1038 nature05940 PMID 17538571 S2CID 4412404 a b P J Bishop A Angulo J P Lewis Robin D Moore G B Rabb and J Garcia Moreno The Amphibian Extinction Crisis what will it take to put the action into the Amphibian Conservation Action Plan S A P I EN S Online 5 2 2012 Online since 12 August 2012 connection on 09 April 2019 URL http journals openedition org sapiens 1406 Alastair Campbell ed 1999 Declines and disappearances of Australian frogs PDF Environment Australia ISBN 0 642 54656 8 OCLC 44894378 Archived from the original PDF on 2011 11 14 Stuart et al 2004 Status and Trends of Amphibian Declines and Extinctions Worldwide Science Vol 306 Issue 5702 pp 1783 1786 doi 10 1126 science 1103538 a b Gascon Claude Collins James P Moore Robin D Church Don R McKay Jeanne E Mendelson III Joseph R eds 2007 Amphibian Conservation Action Plan Gland Cambridge IUCN SSC Amphibian Specialist Group S2CID 87645483 a b Silla Aimee J Byrne Phillip G 2019 02 15 The Role of Reproductive Technologies in Amphibian Conservation Breeding Programs Annual Review of Animal Biosciences 7 1 Annual Reviews 499 519 doi 10 1146 annurev animal 020518 115056 ISSN 2165 8102 PMID 30359086 S2CID 53098666 Bid to save frogs from killer goes worldwide 2007 Archived from the original on 2015 10 18 Retrieved 2007 02 22 Amphibian Conservation Alliance Archived from the original on 29 September 2023 1 dead link Crump M 2002 Amphibians Reptiles and their Conservation North Haven CT Linnet Books ISBN 9780208025111 Halliday Adler 2008 The New Encyclopedia of Reptiles and Amphibians 2 ed Online Oxford University Press ISBN 9780198525073 External links editFrogWeb Amphibian Declines amp Malformations IUCN Red List Amphibians Archived 2014 07 01 at the Wayback Machine assesses the current status of amphibian species worldwide incorporates the Global Amphibian Assessment AmphibiaWeb provides background information on amphibian declines Reptile Amphibian amp Pesticide RAP Database Weedicide induced feminization Photos of Sick Frogs at Queensland Frog Society Retrieved from https en wikipedia org w index php title Decline in amphibian populations amp oldid 1215691752, wikipedia, wiki, book, books, library,

article

, read, download, free, free download, mp3, video, mp4, 3gp, jpg, jpeg, gif, png, picture, music, song, movie, book, game, games.