Wildlife conservation

Wildlife conservation refers to the practice of protecting wild species and their habitats in order to maintain healthy wildlife species or populations and to restore, protect or enhance natural ecosystems. Major threats to wildlife include habitat destruction/degradation/fragmentation, overexploitation, poaching, pollution and climate change. The IUCN estimates that 27,000 species of the ones assessed are at risk for extinction. Expanding to all existing species, a 2019 UN report on biodiversity put this estimate even higher at a million species. It's also being acknowledged that an increasing number of ecosystems on Earth containing endangered species are disappearing. To address these issues, there have been both national and international governmental efforts to preserve Earth's wildlife. Prominent conservation agreements include the 1973 Convention on International Trade in Endangered Species of Wild Fauna and Flora (CITES) and the 1992 Convention on Biological Diversity (CBD).[1][2] There are also numerous nongovernmental organizations (NGO's) dedicated to conservation such as the Nature Conservancy, World Wildlife Fund, and Conservation International.

Ankeny Wildlife Refuge in Oregon.

Threats to wildlife

A forest burned for agriculture in southern Mexico.

Habitat destruction

Habitat destruction decreases the number of places wildlife can live in. Habitat fragmentation breaks up a continuous tract of habitat, often dividing large wildlife populations into several smaller ones.[3] Human-caused habitat loss and fragmentation are primary drivers of species declines and extinctions. Key examples of human-induced habitat loss include deforestation, agricultural expansion, and urbanization. Habitat destruction and fragmentation can increase the vulnerability of wildlife populations by reducing the space and resources available to them and by increasing the likelihood of conflict with humans. Moreover, destruction and fragmentation create smaller habitats. Smaller habitats support smaller populations, and smaller populations are more likely to go extinct.[4]

Overexploitation

Overexploitation is the harvesting of animals and plants at a rate that's faster than the species's ability to recover. While often associated with Overfishing, overexploitation can apply to many groups including mammals, birds, amphibians, reptiles, and plants.[5] The danger of overexploitation is that if too many individuals of a species are taken, then the species may not recover.[6] For example, overfishing of top marine predatory fish like tuna and salmon over the past century has led to a decline in fish sizes as well as fish numbers.[3]

Confiscated animal pelts from the illegal wildlife trade.

Poaching

Poaching for illegal wildlife trading is a major threat to certain species, particularly endangered ones whose status makes them economically valuable.[7] Such species include many large mammals like African elephants, tigers, and rhinoceros. [traded for their tusks, skins, and horns respectively].[7][8] Less well-known targets of poaching include the harvest of protected plants and animals for souvenirs, food, skins, pets, and more; Because poachers tend to target threatened and endangered species, poaching causes already small populations to decline even further.

Culling

Culling is the deliberate and selective killing of wildlife by governments for various purposes. An example of this is shark culling, in which "shark control" programs in Queensland and New South Wales (in Australia) have killed thousands of sharks, as well as turtles, dolphins, whales, and other marine life.[9][10][11] The Queensland "shark control" program alone has killed about 50,000 sharks — it has also killed more than 84,000 marine animals.[12][9] There are also examples of population culling in the United States, such as bison in Montana and swans, geese, and deer in New York and other places.[13][14]

Aerial view of the BP Deepwater Horizon oil spill in 2010.

Pollution

A wide range of pollutants negatively impact wildlife health. For some pollutants, simple exposure is enough to do damage (e.g. pesticides). For others, its through inhaling (e.g. air pollutants) or ingesting it (e.g. toxic metals). Pollutants affect different species in different ways so a pollutant that is bad for one might not affect another.

  • Air pollutants: Most air pollutants come from burning fossil fuels and industrial emissions. These have direct and indirect effects on the health of wildlife and their ecosystems. For example, high levels of sulfur oxides (SOx) can damage plants and stunt their growth.[15] Sulfur oxides also contribute to acid rain, harming both terrestrial and aquatic ecosystems. Other air pollutants like smog, ground-level ozone, and particulate matter decrease air quality.
  • Heavy metals: Heavy metals like arsenic, lead, and mercury naturally occur at low levels in the environment, but when ingested in high doses, can cause organ damage and cancer.[16] How toxic they are depends on the exact metal, how much was ingested, and the animal that ingested it. Human activities such as mining, smelting, burning fossil fuels, and various industrial processes have contributed to the rise in heavy metal levels in the environment.
  • Toxic chemicals: There are many sources of toxic chemical pollution including industrial wastewater, oil spills, and pesticides. There's a wide range of toxic chemicals so there's also a wide range of negative health effects. For example, synthetic pesticides and certain industrial chemicals are persistent organic pollutants. These pollutants are long-lived and can cause cancer, reproductive disorders, immune system problems, and nervous system problems.[17]

Climate change

Humans are responsible for present-day climate change currently changing Earth's environmental conditions. It's related to some of the aforementioned threats to wildlife like habitat destruction and pollution. Rising temperatures, melting ice sheets, changes in precipitation patterns, severe droughts, more frequent heat waves, storm intensification, and rising sea levels are some of the effects of climate change.[18] Phenomena like droughts, heatwaves, intense storms, and rising sea levels, directly lead to habitat destruction. Meanwhile, a warming climate, fluctuating precipitation, and changing weather patterns will impact species ranges. Overall, the effects of climate change increase stress on ecosystems, and species unable to cope with rapidly changing conditions will go extinct.[19] While modern climate change is caused by humans, past climate change events occurred naturally and have led to extinctions.

Species conservation

Leatherback sea turtle (Dermochelys coriacea)

It's estimated that, because of human activities, current species extinction rates are about 1000 times greater than the background extinction rate (the 'normal' extinction rate that occurs without additional influence) .[20] According to the IUCN, out of all species assessed, over 27,000 are at risk of extinction and should be under conservation.[21] Of these, 25% are mammals, 14% are birds, and 40% are amphibians.[21] However, because not all species have been assessed, these numbers could be even higher. A 2019 UN report assessing global biodiversity extrapolated IUCN data to all species and estimated that 1 million species worldwide could face extinction.[22][23] Yet, because resources are limited, sometimes it's not possible to give all species that need conservation due consideration. Deciding which species to conserve is a function of how close to extinction a species is, whether the species is crucial to the ecosystem it resides in, and how much we care about it.

Leatherback sea turtle

The leatherback sea turtle (Dermochelys coriacea) is the largest turtle in the world, is the only turtle without a hard shell, and is endangered.[24] It is found throughout the central Pacific and Atlantic Oceans but several of its populations are in decline across the globe (though not all). The leatherback sea turtle faces numerous threats including being caught as bycatch, harvest of its eggs, loss of nesting habitats, and marine pollution.[24] In the US where the leatherback is listed under the Endangered Species Act, measures to protect it include reducing bycatch captures through fishing gear modifications, monitoring and protecting its habitat (both nesting beaches and in the ocean), and reducing damage from marine pollution.[25] There is currently an international effort to protect the leatherback sea turtle.[24]

Habitat conservation

Red-cockaded woodpecker (Picoides borealis)

Habitat conservation is the practice of protecting a habitat in order to protect the species within it.[3] This is sometimes preferable to focusing on a single species especially if the species in question has very specific habitat requirements or lives in a habitat with many other endangered species. The latter is often true of species living in biodiversity hotspots, which are areas of the world with an exceptionally high concentration of endemic species (species found nowhere else in the world).[26] Many of these hotspots are in the tropics, mainly tropical forests like the Amazon. Habitat conservation is usually carried out by setting aside protected areas like national parks or nature reserves. Even when an area isn't made into a park or reserve, it can still be monitored and maintained.

Red-cockaded woodpecker

The red-cockaded woodpecker (Picoides borealis) is an endangered bird in the southeastern US.[27] It only lives in longleaf pine savannas which are maintained by wildfires in mature pine forests. Today, it is a rare habitat (as fires have become rare and many pine forests have been cut down for agriculture) and is commonly found on land occupied by US military bases, where pine forests are kept for military training purposes and occasional bombings (also for training) set fires that maintain pine savannas.[3] Woodpeckers live in tree cavities they excavate in the trunk. In an effort to increase woodpecker numbers, artificial cavities (essentially birdhouses planted within tree trunks) were installed to give woodpeckers a place to live. An active effort is made by the US military and workers to maintain this rare habitat used by red-cockaded woodpeckers.

Conservation genetics

Florida panther (Puma concolor coryi)

Conservation genetics studies genetic phenomena that impact the conservation of a species. Most conservation efforts focus on ensuring population growth but genetic diversity also greatly affect species survival. High genetic diversity increases survival because it means greater capacity to adapt to future environmental changes.[4] Meanwhile, effects associated with low genetic diversity, such as inbreeding depression and loss of diversity from genetic drift, often decrease species survival by reducing the species' capacity to adapt or by increasing the frequency of genetic problems. Though not always the case, certain species are under threat because they have very low genetic diversity. As such, the best conservation action would be to restore their genetic diversity.

Florida panther

The Florida panther is a subspecies of puma (specifically Puma concolor coryi) that resides in the state of Florida and is currently endangered.[28] Historically, the Florida panther's range covered the entire southeastern US. In the early 1990s, only a single population with 20-25 individuals were left. The population had very low genetic diversity, was highly inbred, and suffered from several genetic issues including kinked tails, cardiac defects, and low fertility.[4] In 1995, 8 female Texas pumas were introduced to the Florida population. The goal was to increase genetic diversity by introducing genes from a different, unrelated puma population. By 2007, the Florida panther population had tripled and offspring between Florida and Texas individuals had higher fertility and less genetic problems. In 2015, the US Fish and Wildlife Service estimated there were 230 adult Florida panthers and in 2017, there were signs that the population's range was expanding within Florida.[28]

Conservation methods

Wildlife population monitoring

Non-invasive monitoring of dhole is crucial for knowledge about its conservation status. More research is needed in chinese wilderness.

Monitoring of wildlife populations is an important part of conservation because it allows managers to gather information about the status of threatened species and to measure the effectiveness of management strategies. Monitoring can be local, regional, or range-wide, and can include one or many distinct populations. Metrics commonly gathered during monitoring include population numbers, geographic distribution, and genetic diversity, although many other metrics may be used.

Monitoring methods can be categorized as either "direct" or "indirect". Direct methods rely on directly seeing or hearing the animals, whereas indirect methods rely on "signs" that indicate the animals are present. For terrestrial vertebrates, common direct monitoring methods include direct observation, mark-recapture, transects, and variable plot surveys. Indirect methods include track stations, fecal counts, food removal, open or closed burrow-opening counts, burrow counts, runaway counts, knockdown cards, snow tracks, or responses to audio calls.[29]

For large, terrestrial vertebrates, a popular method is to use camera traps for population estimation along with mark-recapture techniques. This method has been used successfully with tigers, black bears, and numerous other species.[30][31] Trail cameras can be triggered remotely and automatically via sound, infrared sensors, etc. Computer vision-based animal individual re-identification methods have been developed to automate such sight-resight calculations.[32][33] Mark-recapture methods are also used with genetic data from non-invasive hair or fecal samples.[34] Such information can be analyzed independently or in conjunction with photographic methods to get a more complete picture of population viability.

Government involvement

In the US, the Endangered Species Act of 1973 was passed to protect US species deemed in danger of extinction.[35] The concern at the time was that the country was losing species that were scientifically, culturally, and educationally important. In the same year, the Convention on International Trade in Endangered Species of Fauna and Flora (CITES) was passed as part of an international agreement to prevent the global trade of endangered wildlife.[1] In 1980, the World Conservation Strategy was developed by the IUCN with help from the UN Environmental Programme, World Wildlife Fund, UN Food and Agricultural Organization, and UNESCO.[36] Its purpose was to promote the conservation of living resources important to humans. In 1992, the Convention on Biological Diversity (CBD) was agreed on at the UN Conference on Environment and Development (often called the Rio Earth Summit) as an international accord to protect the Earth's biological resources and diversity.[2]

According to the National Wildlife Federation, wildlife conservation in the US gets a majority of its funding through appropriations from the federal budget, annual federal and state grants, and financial efforts from programs such as the Conservation Reserve Program, Wetlands Reserve Program and Wildlife Habitat Incentives Program.[37][38] A substantial amount of funding comes from the sale of hunting/fishing licenses, game tags, stamps, and excise taxes from the purchase of hunting equipment and ammunition.[39]

Non-government involvement

In the late 1980s, as the public became dissatisfied with government environmental conservation efforts, people began supporting private sector conservation efforts which included several non-governmental organizations (NGOs) .[40] Seeing this rise in support for NGOs, the U.S. Congress made amendments to the Foreign Assistance Act in 1979 and 1986 “earmarking U.S. Agency for International Development (USAID) funds for [biodiversity]”.[40] From 1990 till now, environmental conservation NGOs have become increasingly more focused on the political and economic impact of USAID funds dispersed for preserving the environment and its natural resources.[41] After the terrorist attacks on 9/11 and the start of former President Bush's War on Terror, maintaining and improving the quality of the environment and its natural resources became a “priority” to “prevent international tensions” according to the Legislation on Foreign Relations Through 2002[41] and section 117 of the 1961 Foreign Assistance Act.[41]

Non-governmental organizations

Many NGOs exist to actively promote, or be involved with, wildlife conservation:

See also

References

  1. "What is CITES?". CITES: Convention on International Trade in Endangered Species of Wild Fauna dn Flora. Retrieved 2019-05-13.
  2. "History of the Convention". Convention on Biological Diversity. Retrieved 2019-05-13.
  3. Cain, Michael L.; Bowman, William D.; Hacker, Sally D. (2013). Ecology (3rd ed.). Sunderland, Massachusetts, U.S.A.: Sinauer Associates. ISBN 9780878939084. OCLC 868150915.
  4. Frankham, Richard; Ballou, Jonathan D.; Ralls, Katherine; Eldridge, Mark D. B.; Dudash, Michele R.; Fenstar, Charles B.; Lacy, Robert C.; Sunnucks, Paul (2017). Genetic Management of Fragmented Animal and Plant Populations. New York, NY: Oxford University Press. ISBN 9780198783398.
  5. "Overexploitation". National Wildlife Federation. Retrieved 2019-05-12.
  6. "Overexploitation". The Environmental Literacy Council. Retrieved 2019-05-12.
  7. "Illegal Wildlife Trade". U.S. Fish and Wildlife Service. Retrieved 2019-04-14.
  8. "Illegal Wildlife Trade- Overview". World Wildlife Fund. Retrieved 2019-04-14.
  9. Mitchell, Thom (2015-11-20). "Queensland's Shark Control Program Has Snagged 84,000 Animals". Action for Dolphins. Retrieved 2019-01-04.
  10. https://web.archive.org/web/20181002102324/https://www.marineconservation.org.au/pages/shark-culling.html "Shark Culling". marineconservation.org.au. Archived from the original on 2018-10-02. Retrieved January 4, 2019.
  11. https://hsi.org.au/blog/2016/12/08/shark-nets-death-traps-for-marine-animals/ Archived 2018-10-02 at the Wayback Machine Morris, Jessica (December 8, 2016). "Shark Nets – Death Traps For Marine Animals". hsi.org.au. Retrieved January 4, 2019.
  12. https://www.news.com.au/technology/science/animals/aussie-shark-population-is-staggering-decline/news-story/49e910c828b6e2b735d1c68e6b2c956e Aussie Shark Population In Staggering Decline. NewsComAu. 14 December 2018. Retrieved September 4, 2019.
  13. James, Will (2014-03-06). "Killing Wildlife: The Pros and Cons of Culling Animals". National Geographic. National Geographic. Retrieved 7 March 2019.
  14. Hadidian, John (Dec 5, 2015). "Wildlife in U.S. Cities: Managing Unwanted Animals". Animals. 5 (4): 1092–1113. doi:10.3390/ani5040401. PMC 4693205. PMID 26569317.
  15. "Sulfur Dioxide Basics". US EPA. 2016-06-02. Retrieved 2019-05-12.
  16. Tchounwou, Paul B.; Yedjou, Clement G.; Patlolla, Anita K.; Sutton, Dwayne J. (2012), Luch, Andreas (ed.), "Heavy Metal Toxicity and the Environment", Molecular, Clinical and Environmental Toxicology, Springer Basel, 101, pp. 133–164, doi:10.1007/978-3-7643-8340-4_6, ISBN 9783764383398, PMC 4144270, PMID 22945569
  17. "Persistent organic pollutants (POPs)". World Health Organization. Retrieved 2019-05-12.
  18. "The Effects of Climate Change". NASA Climate Change: Vital Signs of the Planet. Retrieved 2019-05-13.
  19. Dawson, T. P.; Jackson, S. T.; House, J. I.; Prentice, I. C.; Mace, G. M. (2011-04-01). "Beyond Predictions: Biodiversity Conservation in a Changing Climate". Science. 332 (6025): 53–58. Bibcode:2011Sci...332...53D. doi:10.1126/science.1200303. ISSN 0036-8075. PMID 21454781. S2CID 40618973.
  20. Pimm, S. L.; Jenkins, C. N.; Abell, R.; Brooks, T. M.; Gittleman, J. L.; Joppa, L. N.; Raven, P. H.; Roberts, C. M.; Sexton, J. O. (2014-05-30). "The biodiversity of species and their rates of extinction, distribution, and protection". Science. 344 (6187): 1246752. doi:10.1126/science.1246752. ISSN 0036-8075. PMID 24876501. S2CID 206552746.
  21. "The IUCN Red List of Threatened Species". IUCN Red List of Threatened Species. Retrieved 2019-04-15.
  22. "UN Report: Nature's Dangerous Decline 'Unprecedented'; Species Extinction Rates 'Accelerating'". United Nations Sustainable Development. 2019-05-06. Retrieved 2019-05-22.
  23. Diaz, Sandra; Settele, Josef; Brondizio, Eduardo (2019-05-06). "Summary for policymakers of the global assessment report on biodiversity and ecosystem services of the Intergovernmental Science-Policy Platform on Biodiversity and Ecosystem Services" (PDF). ipbes. Retrieved 2019-05-22.
  24. "Leatherback Turtle". NOAA Fisheries. Retrieved 2019-06-06.
  25. BUSH, HAL BERNTON AND EVAN. "Pacific sea turtles likely to go extinct under Trump administration policy, lawsuit argues". The Sacramento Bee. ISSN 0890-5738. Retrieved 2019-06-12.
  26. Kent, Jennifer; Gustavo A. B. da Fonseca; Mittermeier, Cristina G.; Mittermeier, Russell A.; Myers, Norman (2000). "Biodiversity hotspots for conservation priorities". Nature. 403 (6772): 853–858. Bibcode:2000Natur.403..853M. doi:10.1038/35002501. ISSN 1476-4687. PMID 10706275. S2CID 4414279.
  27. "Red-Cockaded Woodpecker". U.S. Fish and Wildlife Service. 2016-12-19. Retrieved 2019-06-06.
  28. "Florida Panther". www.fws.gov. 2018-01-11. Retrieved 2019-05-28.
  29. Witmer, Gary (2005). "Wildlife population monitoring: some practical considerations". Wildlife Research. 32 (3): 259–263. doi:10.1071/WR04003.
  30. Karanth, K. Ullas; Nichols, James D., eds. (2017). Methods For Monitoring Tiger And Prey Populations | SpringerLink (PDF). doi:10.1007/978-981-10-5436-5. ISBN 978-981-10-5435-8. S2CID 33402538.
  31. Molina, Santiago; Fuller, Angela K.; Morin, Dana J.; Royle, J. Andrew (May 2017). "Use of spatial capture–recapture to estimate density of Andean bears in northern Ecuador". Ursus. 28 (1): 117–126. doi:10.2192/URSU-D-16-00030.1. ISSN 1537-6176. S2CID 89925949.
  32. Schneider, Stefan; Taylor, Graham W.; Kremer, Stefan C. (2020). Similarity Learning Networks for Animal Individual Re-Identification - Beyond the Capabilities of a Human Observer. IEEE. doi:10.1109/wacvw50321.2020.9096925. ISBN 978-1-7281-7162-3.
  33. Wang, Le; Ding, Rizhi; Zhai, Yuanhao; Zhang, Qilin; Tang, Wei; Zheng, Nanning; Hua, Gang (2021). "Giant Panda Identification" (PDF). IEEE Transactions on Image Processing. Institute of Electrical and Electronics Engineers (IEEE). doi:10.1109/tip.2021.3055627. ISSN 1057-7149.
  34. Robinson, Stacie; Waits, Lisette; Martin, Ian (2009-06-03). "Estimating abundance of American black bears using DNA-based capture–mark–recapture models". Ursus. 20: 1–11. doi:10.2192/08GR022R.1. S2CID 84690450.
  35. "Endangered Species Act | Overview". U.S. Fish & Wildlife Service. 2018-12-11. Retrieved 2019-06-06.
  36. "World Conservation Strategy" (PDF). Retrieved 2011-05-01.
  37. "Securing Funds for Conservation". National Wildlife Federation. www.nwf.org. Retrieved 2018-12-25.
  38. "Farm Bill". National Wildlife Federation. www.nwf.org. Retrieved 2018-12-25.
  39. Service, U.S. Fish and Wildlife. "Fish and Wildlife Service". www.fws.gov. Retrieved 2016-01-21.
  40. Meyer, Carrie A. (1993). "Environmental NGOs in Ecuador: An Economic Analysis of Institutional Change". The Journal of Developing Areas. 27 (2): 191–210. JSTOR 4192201. PMID 12286336.
  41. "The Foreign Assistance Act of 1961, as amended" (PDF). Retrieved 2011-05-01.
  42. "About Us - Learn More About The Nature Conservancy". Nature.org. 2011-02-23. Retrieved 2011-05-01.
  43. "WWF in Brief". World Wildlife Fund. Retrieved 2011-05-01.
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