Harvest_Yellow-spotted River Turtle_Peru

Affiliation
IIED
Type of wild species covered by the record
Wild species used in its natural habitat
Stage of the value chain covered by the record
Unknown/not recorded
Record Source
Scientific publication (e.g., journal articles and book chapters independently peer-reviewed)

Assessing Ecological and Social Dimensions of Success in a Community-based Sustainable Turtle Harvest Program in the Peruvian Amazon

Unknown/not recorded
Is the species endemic HIDE
No
Population Status
Unknown/not recorded
Formal international protection in place
International Level
National Level
Unknown/not recorded
Threats/Pressures impacting the conservation of the species
Population Trend
Unknown/not recorded
Sub-national Level
Unknown/not recorded
Name
Emma Hemmerlé
Scientific Name
Podocnemis unifilis
Common Name(s)
Yellow-Spotted River Turtle
Taricaya
Yellow-head Sideneck
Type of Use
Extractive (i.e., the entire organism or parts of the organism are removed from its environment)
If extractive, for the target species, is this use
Non-Lethal
Does this use involve take/extraction of
Only parts or products of the organism (e.g., feathers, leaves, branches, eggs, nuts)
Details of parts/products taken

eggs/hatchlings;
non lethal when destined to the pet trade; lethal when destined to local consumption.

Are specific characteristics/traits being targeted?
Unknown/not recorded
Purpose of Use
Basic subsistence (meeting day to day essential needs)
What is the trend in the level of offtake within the period covered by this record?
Additional Details (if available)

Poachers often engage in tense confrontations with members of organized groups and with park rangers. In some cases, offenders are armed and refuse to recognize the authority of members of organized groups as monitors of their managed sectors. Although park rangers hold more legal authority to report offenders to the local police (located in the towns), the mitigation of illicit activity is complicated by the low number of park rangers distributed throughout ranger stations in the reserve.

Provide Details of resource rights regime where relevant

In this study, we focus on a CBCRM program in the Peruvian Amazon that allows for the legal harvest and trade of an IUCN-designated Vulnerable freshwater turtle spe- cies, Podocnemis unifilis.
The governing bodies of the protected areas under Peru’s Ministry of the Environment approve contracts (management plans) in which local people in groups of approximately ten individuals apply to take part in the management activities with the incentive to legally harvest and commercialize a quota of the managed eggs and hatchlings.
The third phase, which began in 2013 and is still operating as of 2019, increased the percentage of hatchlings that community members were allowed to harvest to 40%.

Geographic Location
Country
Peru
Sub region/state
Amazonas - Pacaya- Samiria National Reserve
Local people (e.g., individuals, communities, co-operatives)
National / local private sector
International private sector
Is the use part of a strategy to generate conservation incentives, to finance conservation, or to improve tolerance/stewardship?
Yes
Is there evidence that the use is affecting the conservation status of the species? HIDE
Yes – use is negatively affecting the status (e.g., population is declining; extraction effort is increasing)
Is there evidence that the use is affecting natural selection?
Unknown/not recorded
Is there evidence that the use is affecting poaching of illegal wildlife trade?
Unknown/not reported

Rangers and community members in Pacaya Basin per- ceive a trend of growth in the managed P. unifilis popula- tion since the implementation of the program, yet this perception may diverge from our ecological understanding of the system under current acceptable harvest
We identified eight ecological indicators from the interviews, with the most widely stated indicators of population growth being the perceived abundance of indi- viduals seen basking in Pacaya (58% of respondents), the perceived increases in the population because of increases in the number of nests translocated each year (38%), and perceived increases in the population due to the yearly increase in hatchlings released into the water (35%).

but By 2012, the perceived success of the program resulted in an increase in the allowed harvest quota of hatchlings from 20 to 40% per year during Phase 3 (2013–2017). Results from the PVAs (population viability analyses) given the best-available site- and species-specific data revealed that under the current harvest rates (40% of hatchlings per year), the P. unifilis population will continue to decrease over time (84% probability of extinction after 30 years), and an (unknown) additional (illicit) harvest pressure of 100 adults per year increases the probability of extinction to 98% after 30 years

Is there any evidence that this use of the species is having a knock-on effect on the status of non-target species
Yes, it is having a positive effect (e.g., reduced competition, reduced risk of hybridization)
Unknown/not recorded
Yes, considered unsustainable
Additional Details (if available)

Organized groups also contribute to the re-nesting, protection, and release of P. expansa (“Charapa”), but this turtle species is not commercialized.

Details of assessment carried out

Rangers and community members in Pacaya Basin per- ceive a trend of growth in the managed P. unifilis popula- tion since the implementation of the program, yet this perception may diverge from our ecological understanding of the system under current acceptable harvest
We identified eight ecological indicators from the interviews, with the most widely stated indicators of population growth being the perceived abundance of indi- viduals seen basking in Pacaya (58% of respondents), the perceived increases in the population because of increases in the number of nests translocated each year (38%), and perceived increases in the population due to the yearly increase in hatchlings released into the water (35%).

but By 2012, the perceived success of the program resulted in an increase in the allowed harvest quota of hatchlings from 20 to 40% per year during Phase 3 (2013–2017). Results from the PVAs (population viability analyses) given the best-available site- and species-specific data revealed that under the current harvest rates (40% of hatchlings per year), the P. unifilis population will continue to decrease over time (84% probability of extinction after 30 years), and an (unknown) additional (illicit) harvest pressure of 100 adults per year increases the probability of extinction to 98% after 30 years;
, respon- dents’ perceptions of a trend of growth are in contrast to our findings of a possible declining population trend under current management. The aforementioned finding highlights the importance of a mixed natural and social sciences approach in elucidating how social understanding and ecological understanding of a system may converge and diverge.

Has a valuation of financial flows from this use at the site/national/international level been recorded
No
Contribution to GDP
Unknown/not recorded
Training/Skills
Land/Resource Rights
Decision Making
Social Cohesion
Conflict- people
Conflict- wildlife
Climate Change

Tensions arise between group members, who may illicitly harvest resources, and park rangers, who are confronted with the decision to engage in disciplinary action and potentially disrupt social relation- ships.

Other Socio-Economic Impacts

Purchasing power --> “In the past, I could not even afford to buy an old pot. Now I can purchase more expensive things, and [now] I have a house.”

Safety --> "a quarter of respondents noted the dangerous nature of the work, including difficult travel terrain, expo- sure to predators and poachers, and adverse weather conditions"

Has any assessment of socio-economic sustainability been recorded
Yes, considered unsustainable
Details of assessment

Significant vulnerabilities exist for system sustainability, notably the recent decrease in foreign demand for the traded resource, and hence the recent decrease in values of hatchlings.

Has the use of the species been recorded as resulting in changes to human health in this record?
Unknown/not recorded
Has the species in use been noted as being of particular disease risk to humans?
Unknown/not recorded
Has the use of the species resulted in changes to animal welfare in this record?
Unknown/not recorded
Are there particular practices which have increased the risk to human or animal health or welfare in the use of this species?
Unknown/not recorded
Does the use of this species increase susceptibility to pathogen spread?
Unknown/not recorded
Unknown/not recorded
Strong community governance/institutions/rights for wildlife management
Absent
Supportive policy and legislative framework
Absent
Adequate capacity to implement and enforce governance arrangements
Absent
Support from NGOs
Absent
Support from Government
Absent
High financial returns from use
Absent
Abundant population of target species
Absent
Biological characteristics of target species
Absent
Capacity building of community
Absent
Establishment and implementation of species and/or area management plan
Absent
Effective private sector approach engagement through certification
Absent
Good benefit-sharing mechanism
Absent
Good Market Strategies
Absent
Source Reference(s)

Rivera, C.J., Macey, S.K., Blair, M.E. et al. Assessing Ecological and Social Dimensions of Success in a Community-based Sustainable Harvest Program. Environmental Management 67, 731–746 (2021). https://doi.org/10.1007/s00267-021-01425-6

members of local groups were allowed to harvest and directly consume and trade non viable eggs during the first phase of the program (1994–2007) in exchange for the protection of nests and the release of hatchlings into the water

Rangers and community members in Pacaya Basin per- ceive a trend of growth in the managed P. unifilis popula- tion since the implementation of the program, yet this perception may diverge from our ecological understanding of the system under current acceptable harvest
We identified eight ecological indicators from the interviews, with the most widely stated indicators of population growth being the perceived abundance of indi- viduals seen basking in Pacaya (58% of respondents), the perceived increases in the population because of increases in the number of nests translocated each year (38%), and perceived increases in the population due to the yearly increase in hatchlings released into the water (35%).

but By 2012, the perceived success of the program resulted in an increase in the allowed harvest quota of hatchlings from 20 to 40% per year during Phase 3 (2013–2017). Results from the PVAs (population viability analyses) given the best-available site- and species-specific data revealed that under the current harvest rates (40% of hatchlings per year), the P. unifilis population will continue to decrease over time (84% probability of extinction after 30 years), and an (unknown) additional (illicit) harvest pressure of 100 adults per year increases the probability of extinction to 98% after 30 years
, respon- dents’ perceptions of a trend of growth are in contrast to our findings of a possible declining population trend under current management. The aforementioned finding highlights the importance of a mixed natural and social sciences approach in elucidating how social understanding and ecological understanding of a system may converge and diverge.

Who is involved in the use?
Additional details of specific groups

The range of ages of the respondents was 24–62.

Is there any gender/age specificity in the various roles
Unknown/not recorded
How many of these local jobs accure to the following categories?
How many people outside the local area are employed
Is there any evidence of other economic benefits associated with this use beyond direct income and jobs
Unknown/Not recorded
Scale of Assessment
IUCN National Red List Category
IUCN Global Red List Category
Green Status Global Category
Yearly Financial Flows
Country reference