Tourism_Yellow Eyed Penguin_New Zealand

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)

Behavioural consequences of human disturbance on subantarctic Yellow-eyed Penguins Megadyptes antipodes

Decreasing
Is the species endemic HIDE
Yes
Population Status
Uncommon and only found within narrow areas of distribution
Unknown/not recorded
National Level
Unknown/not recorded
Population Trend
Unknown/not recorded
Sub-national Level
Unknown/not recorded
Additional Details (if available)

By-catch mortality in the commercial gillnet fisheries is thought have driven significant declines over the past two decades, both on predator-free islands, such as Whenua Hou, and along the mainland coast; . Modelling has found a likely correlation between changing sea surface temperature and penguin vital rates, whereby productivity and survival are projected to decline under predicted climate change (Mattern et al. 2017). This has been seen in the Boulder Beach colony, where changes in SST have been found to account for 33% of the population fluctuations (Mattern et al. 2017). Human disturbance, particularly from unregulated tourists at breeding areas, negatively affects energy budgets, fledgling weight and probability of survival (McClung et al. 2004; Ellenberg et al. 2007, 2009, 2013), with human to penguin distance being a predictor of the likelihood of defensive behaviour;

Name
Emma Hemmerlé
Scientific Name
Megadyptes antipodes
Common Name(s)
Yellow-eyed Penguin
Type of Use
Non-Extractive
Are specific characteristics/traits being targeted?
Unknown/not recorded
Purpose of Use
Recreational
What is the main end use for any living organisms, parts or products taken/extracted?
What is the trend in the level of offtake within the period covered by this record?
Additional Details (if available)

The current minimum approach guideline for all wildlife there is a distance of 5 m, yet the appropriateness of this has never been scientifically validated.
On Enderby Island, tourists approached to a median minimum distance of 27 m, where the probability of disturbance is 0.65, and 39% of tourists approached to a minimum distance of < 21 m, where the probability of disturbance is > 0.87

Geographic Location
Country
New Zealand
Sub region/state
Auckland Archipelago
Name
Enderby Island
Site Description

Enderby Island, Auckland Island archipelago (50°29′45′′S 166°17′44′′E)
We collected all behavioural data at Penguin Alley, a section of Sandy Bay, Enderby Island, that is frequently used by penguins transiting to and from their nests and tourists arriving/departing and setting off/returning from walks on the island;

National external (individual, groups. e.g., hunters, anglers, photographers, tourists)
International external (individual, groups. e.g., hunters, anglers, photographers, tourists)
If more than one box ticked, please provide more details

tourists are the primary users

Is the use part of a strategy to generate conservation incentives, to finance conservation, or to improve tolerance/stewardship?
Unknown/not recorded
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
Is there any evidence that this use of the species is having a knock-on effect on the status of non-target species
Unknown/not recorded
Unknown/not recorded
Details of assessment carried out

As tourist visitation is infrequent and at low levels on Enderby Island, these penguins may not have had the opportunity to become habituated to humans. However, the lack of habituation by Yellow-eyed Penguins on mainland New Zealand (where the level of tourism is much higher and continuous year-round) indicates that habituation to tourism may not be possible.

Has a valuation of financial flows from this use at the site/national/international level been recorded
No
Contribution to GDP
Unknown/not recorded
Medicine/healthcare
Training/Skills
Land/Resource Rights
Decision Making
Social Cohesion
Conflict- people
Conflict- wildlife
Climate Change
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
Present
Support from Government
Present
Abundant population of target species
Absent
Biological characteristics of target species
Present
Establishment and implementation of species and/or area management plan
Absent
Source Reference(s)

French, R. , Muller, C. G., Chilvers, B. L., & Battley, P. (2019). Behavioural consequences of human disturbance on subantarctic Yellow-eyed Penguins Megadyptes antipodes. Bird Conservation International, 29(2), 277–290. Cambridge University Press.

Human presence caused a significant drop in the probability of a successful transit to or from their nest, and significantly increased the time penguins spent alert and decreased the time spent preening. Modelling showed the distance from a human to a penguin is a significant predictor of the likelihood of a bird displaying disturbance behaviour, with the current minimum approach guideline of 5 m not sufficient for preventing disturbance. Unregulated tourism has been shown to decrease juvenile survival in their first year as a result of lower fledging weights, affecting population recruitment (McClung et al. 2004).

Threats/pressures impacting the species at the scale of this record
Who is involved in the use?
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
Other
Lack of habituation to human disturbance;
Other
Human Intrusions and disturbances
No assessment recorded
No assessment has been recorded
Country reference