Species reintroduction

Species reintroduction is the deliberate release of a species into the wild, from captivity or other areas where the animal survives.[1] A species that needs reintroduction is usually one whose existence has become threatened or endangered in the wild. However, reintroduction of a species can also be for pest control. For example, wolves being reintroduced to a wild area because of an overpopulation of elk or deer. Because reintroduction may involve returning native species to localities where they had been extirpated, some prefer the term "reestablishment".[1]

Reintroduction has been practiced for many years.[2]

Principles of reintroduction

Reintroduction and translocation are both important tools for population and species management. Translocation moves wild-caught animals from one natural location to another, while reintroduction moves captive-born animals into their natural historical range.[3] "Much of the behavioral research required to obtain reproduction will also be critical for reintroduction, which depends on the development of behaviorally competent individuals. More behavioral research to select the best candidates and prepare them for the very different challenges that await them in nature will be essential also. Behaviorists will again play a crucial role in post-release monitoring to determine the behavioral deficiencies that limit the success of reintroductions. There may be no other conservation action where the skills of behavioral researchers are more essential than reintroduction."[4] In situ conservation means "on site". In-situ conservation is the conservation of species diversity within normal and natural habitats and ecosystems. The challenge in using in-situ methods is to expand our vision of protected areas to include multiple use and extractive reserves to develop new models for conservation. In-Situ conservation uses innovative proposals such as damaged ecosystems to preserve rare, endangered, and threatened species and to expand the range of options available for economic development.[5] Ex-situ conservation means literally, "off-site conservation". It is the process of protecting an endangered species of plant or animal outside of its natural habitat. Capturing and relocating part of a population from a threatened habitat and placing it in a new location where it may have a better chance of survival is one example. Ex-situ conservation should only be used when In-Situ conservation cannot.[2]

Education

Zoos are one of the most conventional methods of ex-situ conservation. Depending on their size and location, zoos receive between a few tens of thousands to several million visitors annually. Zoos provide education to the public about the many endangered species and explain the factors contributing the threats they face in their native habitats.[6] Through ex-situ conservation methods they provide protected specimens for breeding and reintroduction into the wild. It has been suggested that this method should be used only when necessary and when In-Situ conservation is not possible.[2]

Successes and failures

Reintroduction biology is new and continues to be a work in progress. Although there is still no general and broadly accepted definition of reintroduction success, it has been proposed that the criteria widely used to assess the conservation status of endangered taxa, such as the IUCN Red List criteria, should be used to asses reintroduction success. [7] In other words, successful reintroduction programs should yield viable and self-sustainable populations on the long-term. The IUCN/SSC Re-introduction Specialist Group & Environment Agency, in their 2011 Global Re-introduction Perspectives, compiled reintroduction case studies from around the world.[8] 184 case studies were reported on a range of species which included invertebrates, fish, amphibians, reptiles, birds, mammals, and plants. Assessments from all of the studies included goals, success indicators, project summary, major difficulties faced, major lessons learned, and success of project with reasons for success or failure. The Siberian tiger population has rebounded from 40 individuals in the 1940s to around 500 in 2007. The Siberian tiger population is now the largest un-fragmented tiger population in the world.[9] Yet, a high proportion of translocations and reintroductions have not been successful in establishing viable populations[3] Black footed ferrets in North America have also been a highly successful reintroduced species. Husbandry techniques were refined and the first successful captive breeding occurred in 1987. For this species, disease management in captivity is paramount and strict protocols are followed. Genetic management is closely monitored and ferrets are bred using a mean-kinship strategy which provides genetic diversity when bred in captivity.[8] To prepare them for reintroduction into their new "wild" habitat, captive-born ferrets are placed in outdoor pens, simulating quasi-natural conditions with dirt burrows and live prey. Ferrets that receive pre-release conditioning in outdoor pens prior to release have demonstrated 10-fold higher survival rates in the wild than ferrets that receive no pre-release exposure. Ferrets are typically released in the fall during their natural dispersal and kits (young of the year) are the primary candidates.[8]

Many factors can attribute to the success or failure of a reintroduction. Predators, food, pathogens, competitors, and weather can all affect a reintroduced population's ability to grow, survive, and reproduce. Animals raised in captivity may experience stress during captivity or translocation, which can weaken their immune systems.[10] The IUCN reintroduction guidelines emphasize the need for an assessment of the availability of suitable habitat as a key component of reintroduction planning.[11] Poor assessment of the release site can increase the chances that the species will reject the site and perhaps move to a less suitable environment. This can decrease the species fitness and thus decrease chances for survival.[10] They state that restoration of the original habitat and amelioration of causes of extinction must be explored and considered as essential conditions for these projects. Unfortunately, the monitoring period that should follow re introductions often remains neglected.[12]

Improving research techniques

A cooperative approach to reintroduction by ecologists and biologists could improve research techniques. For both preparation and monitoring of reintroductions, increasing contacts between academic population biologists and wildlife managers is encouraged within the Survival Species Commission and the IUCN. The IUCN states that a re-introduction requires a multidisciplinary approach involving a team of persons drawn from a variety of backgrounds.[11] A survey by Wolf et al. in 1998 indicated that 64% of reintroduction projects have used subjective opinion to assess habitat quality.[10] This means that most reintroduction evaluation has been based on human anecdotal evidence and not enough has been based on statistical findings. Seddon et al. (2007) suggest that researchers contemplating future reintroductions should specify goals, overall ecological purpose, and inherent technical and biological limitations of a given reintroduction, and planning and evaluation processes should incorporate both experimental and modeling approaches.[2]

Monitoring the health of individuals, as well as the survival, is important; both before and after the reintroduction. Intervention may be necessary if the situation proves unfavorable.[11] Population dynamics models that integrate demographic parameters and behavioral data recorded in the field can lead to simulations and tests of a priori hypotheses. Using previous results to design further decisions and experiments is a central concept of adaptive management. In other words, learning by doing can help in future projects. Population ecologists should therefore collaborate with biologists, ecologists, and wildlife management to improve reintroduction programs.[5]

Survival skills

It may be very hard to reintroduce species into the wild, even if their natural habitats were restored. Survival techniques, which are normally passed from parents to offspring during parenting, are lost. The genetics of the species is saved, but the natural memetics of the species is not.

Beginning in the 1980s, biologists have learned that many mammals and birds need to learn a lot to survive in the wild. Thus, reintroduction programmes have to be planned carefully, ensuring that the animals have the necessary survival skills. Biologists must also study the animals after the reintroduction to learn whether the animals are surviving and breeding, what effects the reintroduction has on the ecosystem, and how to improve the process.

Still, a vast number of animals may need to be reintroduced into the wild to be sure that enough of them learn how to survive. For instance, in reintroducing houbara bustards into the wild in the United Arab Emirates, more than 5,000 birds per year are used.[2][13]

Re-introduction Specialist Group (RSG)

The RSG is a network of specialists whose aim is to combat the ongoing and massive loss of biodiversity by using re-introductions as a responsible tool for the management and restoration of biodiversity. It does this by actively developing and promoting sound inter-disciplinary scientific information, policy, and practice to establish viable wild populations in their natural habitats. The role of the RSG is to promote the re-establishment of viable populations in the wild of animals and plants. The need for this role was felt due to the increased demand from re-introduction practitioners, the global conservation community and increase in re-introduction projects worldwide.

Increasing numbers of animal and plant species are becoming rare, or even extinct in the wild. In an attempt to re-establish populations, species can – in some instances – be re-introduced into an area, either through translocation from existing wild populations, or by re-introducing captive-bred animals or artificially propagated plants.

United Kingdom

Ongoing or successful programs

Reserva CIBE

Planned or proposed programs

Other countries

Planned or proposed programmes

Lion reintroduction sites in India

Ongoing or successful programs

Africa

Asia

Arabian oryx (Oryx leucoryx)

Europe

North America

Oceania

South America

See also

References

  1. 1 2 Campbell-Palmer, R.; Rosell, F. (2010). "Conservation of the Eurasian beaver Castor fiber: an olfactory perspective". Mammal Review. 40 (4): 293–312. doi:10.1111/j.1365-2907.2010.00165.x.
  2. 1 2 3 4 5 6 Seddon; Armstrong, DP; Maloney, RF (2007). "Developing the Science of Reintroduction Biology". Conservation Biology. 21 (2): 303–312. doi:10.1111/j.1523-1739.2006.00627.x. PMID 17391180.
  3. 1 2 Kleiman, D. G. (1989). "Reintroduction of captive mammals for conservation. Guidelines for reintroducing endangered species into the wild". BioScience. 39 (3): 152–161. doi:10.2307/1311025.
  4. Swaisgood, Ronald R (November 2004) Retrieved May 8, 2012 from http://www.animalbehavior.org/ABSConservation/ConservationBehaviorist/
  5. 1 2 BGCI: The global network. Retrieved April 30, 2012 from http://www.bgci.org/ourwork/Ecosystems/
  6. The Role of Zoos and Aquaria of the World in Conservation. Retrieved April 30, 2012 from http://www.americanzoos.info/Home/World%20Zoo%20Conservation%20Strategy.pdf
  7. Robert, A.; Colas, B.; Guigon, I.; Kerbiriou, C.; Mihoub, J.B.; Saint-Jalme, M.; Sarrazin, F. (2015). "Defining reintroduction success using IUCN criteria for threatened species: a demographic assessment". Animal Conservation. 18 (5): 397–406. doi:10.1111/acv.12188.
  8. 1 2 3 Soorae, P. S. (ed.) (2011). Global Re-introduction Perspectives: 2011.More case studies from around the globe. Gland, Switzerland: IUCN/SSC Re-introduction Specialist Group and Abu Dhabi, UAE: Environment Agency-Abu Dhabi. xiv + 250 pp.SBN: 978-2-8317-1432-5 www.iucnsscrsg.org
  9. Rietbergen, Jennifer Building a Sustainable Future WWF International 2008
  10. 1 2 3 Stamps, J.A.; Swaisgood, R.R (2007). "Someplace like home: Experience, Habitat selection and Conservation Biology". Applied Animal Behaviour Science. 102 (3–4): 392–409. doi:10.1016/j.applanim.2006.05.038.
  11. 1 2 3 Prepared by the SSC Re-introduction Specialist Group (May 1995) IUCN/SSC Guidelines for Re-Introductions http://www.iucnsscrsg.org
  12. Sarrazin, F. Barbault, R. (November 1996). Reintroduction: Challenges and Lessons for Basic Ecology Elsevier Science Volume 11 No. 11
  13. "Houbara bustard reintroduced into the wild".
  14. Monbiot, George (2013-10-18). "Why are Britain's conservation groups so lacking in ambition?". The Guardian. ISSN 0261-3077. Retrieved 2016-04-17.
  15. "Ladybird Spider- Eresus cinnaberinus".
  16. Red squirrel conservation, squirrel ecology and grey squirrel management
  17. "Big Cat Swap Raises Questions". Institute for War and Peace Reporting. 19 May 2010. Retrieved 30 October 2015.
  18. Arabian Oryx.gov.sa, [Monitoring of Arabian oryx at reintroduction sites "Monitoring of Arabian oryx at reintroduction sites"].
  19. Haaretz,"Jerusalem Zoo Oryx Moving to the Arava", 1 March 2007.
  20. See Borneo Orangutan Survival
  21. Teva.org.il, "Nubian Ibex".
  22. IUCN Red List, "Equus ferus ssp. przewalskii".
  23. http://www.ynetnews.com/articles/0,7340,L-4291551,00.html
  24. http://www.int-res.com/articles/esr2014/23/n023p159.pdf
  25. Groff C., Bragalanti N., Rizzoli R., Zanghellini P. (editors), "2012 Bear Report, Forestry and Wildlife Department of the Autonomous Province of Trento", 2013.
  26. Koelewijn H.P., "The reintroduction of the otter", 2012.
  27. News - Department of the Environment, Heritage & Local Government
  28. Black-Footed Ferret, "Reintroduction".
  29. "Threatened and Endangered Species in Washington: 2012 Annual Report" (PDF).
  30. Yellowstone National Park, "Wolf Reintroduction Changes Ecosystem", 21 June 2011.
  31. "British Virgin Islands: Flamingo Reintroduction to Anegada - The Conservation Agency". The Conservation Agency. Retrieved 2016-04-12.

Further reading

This article is issued from Wikipedia - version of the 11/30/2016. The text is available under the Creative Commons Attribution/Share Alike but additional terms may apply for the media files.