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Australian Antarctic Data Centre

SIMR - (State of Environment)

State of Environment

System for Indicator Management and Reporting - an on-line State of Environment system for the Antarctic.

Indicator 27 - Regional populations of Adelie penguins in the vicinity of Casey, Davis and Mawson.

  Index - Description | Custodian evaluation | Related resources | Parameters

Adelie colony near Casey (AAD Photo 1063/ B4) by B. Greenstreet, 1984/85
Print indicator

Indicator Definition Breeding populations of Adilie penguins at Davis, Mawson and Casey
(including Shirley Island and Whitney Point).


Responsible
Organisation
organisation logo
Australian Antarctic Division (details)
Custodians
ERIC WOEHLER
eric.woehler@aad.gov.au
INVESTIGATOR
TECHNICAL CONTACT
Australian Antarctic Division
203 Channel Highway
Kingston
Tasmania 7050
Australia
Ph +61 3 6232 3376
Theme Area Biodiversity
Indicator Type Condition   
Criteria the
Indicator Satisfies
The following 13 out of 15 criteria
1. Serve as a robust indicator of environmental change
2. Reflect a fundamental or highly-valued aspect of the environment or an important environmental issue
3. Be either national in scope or applicable to regional environmental issues of national significance
4. Provide an early warning of potential problems
5. Be capable of being monitored to provide statistically verifiable and reproducible data that shows trends over time and, preferably, apply to a broad range of environmental regions
6. Be scientifically credible
7. Be easy to understand
8. Be monitored with relative ease
9. Be cost-effective
10. Have relevance to policy and management needs
11. Contribute to monitoring of progress towards implementing commitments in nationally important environmental policies
13. Contribute to the fulfillment of reporting obligations under international agreements
15. Where possible and appropriate, be consistent and comparable with other countries’ and state and territory indicators
For details of indicators, see the State of Environment Bibliography entries 16336 and 16337
Date Input
Monitoring Location Shirley Island (details)   Rookery Island 6 (details)   Rookery Island 2 (details)   Whitney Point (details)   Rookery Island (details)   Rookery Island 9 (details)   Rookery Island 5 (details)   Béchervaise Island (details)   Giganteus Island (details)   Verner Island (details)   Any Named places

Geographic Coverage is

    Latitude (-70.0 to -50.0)
    Longitude (50.0 to 110.0)

Rationale For Indicator Selection The breeding population of Adilie penguins is related to resource
availability (nesting space and food), behavioural mechanisms
(immigration/emigration and breeding effort/success) in addition to climate
change and human impacts (fisheries, tourism, pollution, disturbance).
Monitoring these colonies and interpretation of the data provides
information on changes in the Antarctic ecosystem.


Design and Strategy For Indicator Monitoring Program Spatial scale: Colonies near Australian Stations -
Casey (lat 660 16' 54.5" S, long 1100 31' 39.4" E)
Davis (lat 680 34' 35.8" S, long 770 58' 02.6" E)
Mawson (lat 670 36' 09.7" S, long 620 52' 25.7" E)


All colonies on -
Shirley Island (lat 660 16' 55.9" S, long 1100 29' 17.9" E) and
Whitney Point (lat 660 15' 08.6" S, long 1100 31' 40.1" E)


Frequency: Annual surveys at Shirley Island and Whitney Point. Other
colonies every 2-3 years, depending on logistical constraints.


Measurement technique: Each colony is visited and all breeding birds are
counted from the ground by two or three personnel performing replicate counts.
Supplementary census data are obtained from oblique ground and aerial
photographs. All breeding adults in a colony are counted.


Considerations regarding disturbance associated with census visits are also
incorporated into monitoring strategies. The lack of annual census data for
some colonies does not reduce the value of these long-term monitoring
programmes.


Research Issues Adilie Penguin populations throughout East Antarctica have shown
sustained, long-term increases for the past 30 or more years; in contrast,
populations elsewhere around the Antarctic and on the Antarctic Peninsula have
exhibited decreases or no clear long-term trends (Woehler et al. 2001).
Greater coverage of colonies throughout the AAT would provide a more accurate
estimate of the total annual breeding population in East Antarctica. In
addition to basic inventory requirements, data on the population trends would
contribute to a better understanding of the role of Adilie penguins in
the Antarctic ecosystem, and provide managers with feedback or management
strategies.


Data

Timespan: 1959/60 to 2002/03.
Number of data points: 54.

To view or download any of the data, you must be logged into the Data Centre Portal. If you return to this indicator, you will find a Search Data link that will allow you to view or extract the data for this indicator.

Number of breeding pairs. Use the search data option to select data within particular areas.

Rookery Islands (details)




Kista Strait Islands (details)




Shirley Island (details)




Whitney Point (details)




Data Quality, Interpretation and
Analysis of Indicator Data
Censuses of breeding adults are performed and long term trends are determined. Integration with other long term datasets is currently underway through international collaborations, allowing for comparisons among sites at regional and ecosystem scales.

Some analyses and their interpretations have been published (see references), and current analyses will examine population data as they are compiled.


Data Usage Constraints Please follow instructions listed in the citation reference provided at the URL below when using these data.
Data Distribution
DATA OFFICER AADC
metadata@aad.gov.au
Australian Antarctic Division
203 Channel Highway
Kingston
Tasmania 7050
Australia
Ph +61 3 6232 3244
Data Access Constraints Some data are published, others are in press and/or under analyses. Contact data compiler for access and use (Dr Eric J Woehler, AAD).


Custodian Evaluation
Date entered Evaluation
23-May-2002 Adelie penguin populations in East Antarctica are presently showing long-term (30-50 year) increases at regional scales. While some populations show inter-annual variability, regional populations (for example, the Mawson coastline) are increasing in the longer term. For the Casey region, the total breeding population has more than trebled since the early 1960s. Similar long-term increases have been reported by French researchers for Adelie Land.

Mawson Coast breeding populations (Woehler et al., 1989):

Giganteus Island: The breeding population increased between 1972-73 and 1981-82, and then decreased to less then that of 1972-73 in 1988-89.

Verner Island: The breeding population at Verner Island has shown a long-term (15-year) decrease. This decrease is approaching 40% between 1972-73 and 1988-89.

Rookery Island: The population increased between 1972-73 and 1981-82, and remained stable between 1981-82 and 1988-89.

Rookery Island 2: The breeding population increased between 1972-73 and 1981-82, and then decreased to less then that of 1972-73 in 1988-89.

Rookery Island 5: The data indicate a relatively stable population between 1972-73 and 1981-82, and a slight decrease to 1988-89.

Rookery Island 6: As with Rookery Island 2, the population increased between 1972-73 and 1981-82, and has since declined. The photographic coverage in 1981-82 is incomplete, with only 90% of the island photographed. Colonies were larger in 1981-82 than 1988-89.

Rookery Island 9: The population increased between 1972-73 and 1981-82, and remained stable between 1981-82 and 1988-89.

Casey region breeding populations:

Shirley Island: The breeding population has not changed significantly since 1968. Large inter-annual variations in breeding population size are evident.

Whitney Point: The breeding population at Whitney Point has more than quadrupled between 1959 and 1995. This increase is reflected both in an increase in the populations of existing colonies and in the formation of new colonies.

Reference

Woehler, E.J., Johnstone, G.W. and Burton, H.R. (1989) The distribution and abundance of Adelie penguins, Pygoscelis adeliae, in the Mawson area and at the Rookery Islands (Specially Protected Area 2), 1981 and 1988. ANARE Research Notes 71, Antarctic Division, Australia.



7-Nov-2002
Condition scale - 6

1 - the environment degraded to the point where rehabilitation is impossible
0 1 2 3 4 5 6 7
7 - the environment is pristine, in perfect condition, no anthropogenic influences

State of Knowledge scale - 6

1 - Poor
0 1 2 3 4 5 6 7
7 - Excellent

For definitions of the Scale categories, consult the Explanation of the Status Categories

Related resources

    Database/Application Biodiversity - SCAR EBA program
    Metadata SOE_seabird_candidate_sp_AP - Annual population counts at selected Adélie Penguin colonies within the AAT
    Project 94 - Aerial Photographic Census of Adelie Penguins in the Casey Region 1990/91
    Project 2264 - Population monitoring of Adelie penguins
    Scientific Bibliography 17295 - Martin, M.R., Johnstone, G.W. & Woehler, E.J. (1990) Increased numbers of Adelie Penguins Pygoscelis adeliae breeding near Casey, Wilkes Land, East Antarctica. Corella 14, 119-122.
    Scientific Bibliography 17296 - Woehler, E.J. (1990) The distribution of seabird biomass in the Australian Antarctic Territory: Implications for conservation Environmental Conservation 17, 256-261.
    Scientific Bibliography 17297 - Woehler, E.J. & Johnstone, G.W. (1991) Status and conservation of the seabirds of the Australian Antarctic Territory In: Seabird status and conservation: a supplement. ed.Croxall, J.P., ICBP Technical Publication 11, 279-308.
    Scientific Bibliography 17298 - Woehler, E.J., Slip, D.J., Robertson, L.M., Fullagar, P.J. & Burton, H.R. (1991) The distribution, abundance and status of Adilie Penguins Pygoscelis adeliae at the Windmill Islands, Wilkes Land, Antarctica Marine Ornithology 19, 1-18.
    Scientific Bibliography 17299 - Woehler, E.J. (1993) Antarctic seabirds: their status and conservation in the AAT. RAOU Conservation Statement 9, 8pp.
    Scientific Bibliography 17300 - Woehler, E.J., Penney, R.L., Creet, S.M. & Burton, H.R. (1994) Impacts of human visitors on breeding success and long-term population trends in Adilie Penguins at Casey, Antarctica Polar Biology 14, 269-274.
    SOE Indicator 31 - Annual population estimates of Southern Elephant Seals at Macquarie Island
    SOE Indicator 33 - Annual catch in tonnes of marine species harvested in Australian Antarctic and sub-Antarctic waters
    SOE Indicator 34 - Sea bird egg contamination
    SOE Indicator 36 - Numbers of species protected at various levels of conservation status
    SOE Indicator 37 - Species and numbers of species killed, taken or interfered with or disturbed in the Antarctic and the sub-Antarctic for the purpose of scientific research
    SOE Indicator 45 - Monthly collections of marine debris from Sandell Bay beach on Macquarie Island (categories and mass)
    Taxonomy 1086 - Pygoscelis adeliae Adelie Penguin
Parameters
The properties link can be used to view details of the parameters measured for this indicator.

Parameter NameUnit of measure Properties
Number of breeding pairs (properties)
The following parameters and/or sensor notes are from the metadata record.

Parameters -
EARTH SCIENCE > BIOLOGICAL CLASSIFICATION > ANIMALS/VERTEBRATES > BIRDS
EARTH SCIENCE > BIOSPHERE > ECOLOGICAL DYNAMICS > COMMUNITY DYNAMICS
EARTH SCIENCE > BIOSPHERE > ECOLOGICAL DYNAMICS > SPECIES/POPULATION INTERACTIONS
EARTH SCIENCE > BIOSPHERE > ECOLOGICAL DYNAMICS > SPECIES/POPULATION INTERACTIONS
EARTH SCIENCE > BIOSPHERE > ECOLOGICAL DYNAMICS > SPECIES/POPULATION INTERACTIONS