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Risk and Benefits of Translocation for
conservation goal (A Term Paper on EES 603 Biodiversity
Conservation and Restoration )
PRESENTED BY
Nikesh Kathayat
M.Sc. Forestry Second
Semester
FoF, Hetauda Campus
Submitted To
Evaluation Committee
FACULTY OF FORESTRY
HETAUDA CAMPUS
AGRICULTURE AND FORESTRY
INTRODUCTION
• Movement of living organisms from one area
with free release in another (IUCN 1987).
• Categorization of Translocation (IUCN 1987):
1. Introduction: Not known to have existed
previously
2. Reintroduction: Released from which it has
disappeared
3. Restocking: Added to existing population
Source : The Kantipur Pos
STATUS
Blackbuck
• Reintroduction effort in nepal dates back to 1977
• 8 blackbucks from Khairapur to Baghaura phanta in Bardia NP
• 28 blackbucks were reintroduced in Hirapur Phanta in Shuklaphanta National Park
Rhino
• 13 rhinos were reintroduced from Chitwan National Park to Bardia National Park in
1986.
• Since 1986, a total of 100 rhinos have been translocated to BaNP and Sh.NP
Wild water buffalo
• 15 wild water buffalo were translocated to Chitwan National park in 2017
Gharial
• Gharial conservation breeding centre first batch of 50 captive
bred gharials released in Narayani in 1981.
• Since then 1246 gharials released to different river systems
Swamp deer
• Altogether 7 swamp deer translocated in Padampur block in the
eastern sector of the chitwan national park from shuklaphanta
national park
Vulture
• In 2017, reintroduction of the captive-bred endangered vulture
carried out for the first time.
• Further releases of captive-bred vultures are also planned.
Source: WWF, 2017
CRITERIA FOR EVALUATING TRANSLOCATION PROJECTS
(SOURCE: Perez I et al., 2012)
Benefits of Translocation
Translocation has a number of other important benefits:
• Provide opportunities for more in-depth scientific research.
• Reintroduction (via translocation) aims to restore a habitat to its natural state
• Establish a healthy, genetically diverse, self-sustaining population
• Add genetic diversity to an existing population.
RISK CONSEQUENCE MITIGATION
Outbreeding
depression
Decreased fitness of offspring from
crosses
Evaluate in preliminary crosses,
compensate through higher numbers;
Obtain genetic data
Replacement of
recipient genetic
background
Loss of uniqueness, local
adaptability
Restrict donor numbers to minimize
impact if considered a threa
Disease transmission Spread of disease could have
disastrous consequences
Ensure only healthy material is
translocated; If appropriate,
quarantine prior to release
Inbreeding and
genetic load
Loss of genetic diversity, decreased
fitness, increased extinction risk
Increase potential for gene flow;
controlled crossing strategy to
minimize inbreeding
Environmental change
in remnant population
Loss of evolvability, increased
extinction risk
Consider other translocation sites;
Consider captive breeding as
insurance
Source: Weeks et al.
SIMPLE RISK-ASSESSMENT FRAMEWORK FOR
TRANSLOCATIONS
CONCLUSION
• Most powerful tools for biodiversity conservation, as habitat loss, introduced
species, disease epidemics and climate change
• Should only be attempted when a suitable unoccupied habitat exists.
• Provide an insurance mechanism for populations to adapt to future conditions
• However, risks need to be weighed carefully on a case-by-case basis.
• And Extensive post-translocation monitoring required to ensure normal
growth
REFERENCES
• Armstrong DP and Seddon PJ. 2008. Directions in reintroduction biology. Trends Ecol
Evol 23: 20–25.
• Bajomi B , Pullin AS , Stewart GB , et al. 2010. Bias and dispersal in the animal
reintroduction literature. Oryx 44: 358–65.
• IUCN (International Union for Conservation of Nature). 1987. IUCN position statement
on translocation of living organisms: introductions, reintroductions and re-stocking. Gland,
Switzerland: IUCN.
• IUCN (International Union for Conservation of Nature). 1998. IUCN guidelines for re-
introductions. Gland, Switzerland, and Cambridge, UK: IUCN.
• Weeks RA, SGRO CM, Young A. 2011. Assessing the benefits and risks of translocations
in changing environments: a genetic perspective
RISK AND BENEFITS OF WILDLIFE TRANSLOCATION

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RISK AND BENEFITS OF WILDLIFE TRANSLOCATION

  • 1. Risk and Benefits of Translocation for conservation goal (A Term Paper on EES 603 Biodiversity Conservation and Restoration ) PRESENTED BY Nikesh Kathayat M.Sc. Forestry Second Semester FoF, Hetauda Campus Submitted To Evaluation Committee FACULTY OF FORESTRY HETAUDA CAMPUS AGRICULTURE AND FORESTRY
  • 2. INTRODUCTION • Movement of living organisms from one area with free release in another (IUCN 1987). • Categorization of Translocation (IUCN 1987): 1. Introduction: Not known to have existed previously 2. Reintroduction: Released from which it has disappeared 3. Restocking: Added to existing population Source : The Kantipur Pos
  • 3. STATUS Blackbuck • Reintroduction effort in nepal dates back to 1977 • 8 blackbucks from Khairapur to Baghaura phanta in Bardia NP • 28 blackbucks were reintroduced in Hirapur Phanta in Shuklaphanta National Park Rhino • 13 rhinos were reintroduced from Chitwan National Park to Bardia National Park in 1986. • Since 1986, a total of 100 rhinos have been translocated to BaNP and Sh.NP Wild water buffalo • 15 wild water buffalo were translocated to Chitwan National park in 2017
  • 4. Gharial • Gharial conservation breeding centre first batch of 50 captive bred gharials released in Narayani in 1981. • Since then 1246 gharials released to different river systems Swamp deer • Altogether 7 swamp deer translocated in Padampur block in the eastern sector of the chitwan national park from shuklaphanta national park Vulture • In 2017, reintroduction of the captive-bred endangered vulture carried out for the first time. • Further releases of captive-bred vultures are also planned. Source: WWF, 2017
  • 5. CRITERIA FOR EVALUATING TRANSLOCATION PROJECTS (SOURCE: Perez I et al., 2012)
  • 6. Benefits of Translocation Translocation has a number of other important benefits: • Provide opportunities for more in-depth scientific research. • Reintroduction (via translocation) aims to restore a habitat to its natural state • Establish a healthy, genetically diverse, self-sustaining population • Add genetic diversity to an existing population.
  • 7. RISK CONSEQUENCE MITIGATION Outbreeding depression Decreased fitness of offspring from crosses Evaluate in preliminary crosses, compensate through higher numbers; Obtain genetic data Replacement of recipient genetic background Loss of uniqueness, local adaptability Restrict donor numbers to minimize impact if considered a threa Disease transmission Spread of disease could have disastrous consequences Ensure only healthy material is translocated; If appropriate, quarantine prior to release Inbreeding and genetic load Loss of genetic diversity, decreased fitness, increased extinction risk Increase potential for gene flow; controlled crossing strategy to minimize inbreeding Environmental change in remnant population Loss of evolvability, increased extinction risk Consider other translocation sites; Consider captive breeding as insurance Source: Weeks et al.
  • 8. SIMPLE RISK-ASSESSMENT FRAMEWORK FOR TRANSLOCATIONS
  • 9. CONCLUSION • Most powerful tools for biodiversity conservation, as habitat loss, introduced species, disease epidemics and climate change • Should only be attempted when a suitable unoccupied habitat exists. • Provide an insurance mechanism for populations to adapt to future conditions • However, risks need to be weighed carefully on a case-by-case basis. • And Extensive post-translocation monitoring required to ensure normal growth
  • 10. REFERENCES • Armstrong DP and Seddon PJ. 2008. Directions in reintroduction biology. Trends Ecol Evol 23: 20–25. • Bajomi B , Pullin AS , Stewart GB , et al. 2010. Bias and dispersal in the animal reintroduction literature. Oryx 44: 358–65. • IUCN (International Union for Conservation of Nature). 1987. IUCN position statement on translocation of living organisms: introductions, reintroductions and re-stocking. Gland, Switzerland: IUCN. • IUCN (International Union for Conservation of Nature). 1998. IUCN guidelines for re- introductions. Gland, Switzerland, and Cambridge, UK: IUCN. • Weeks RA, SGRO CM, Young A. 2011. Assessing the benefits and risks of translocations in changing environments: a genetic perspective