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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 31 - Annual population estimates of Southern Elephant Seals at Macquarie Island

  Index - Description | Data | Custodian evaluation | Related resources | Parameters

Southern Elephant seal. Lusitania Bay, Macqurie Island (AAD Photo 62/ B2) by Christo Baars, 1995
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Indicator Definition Count of all adult females, fully weaned pups and dead pups hauled out on, or
close to, the day of maximum cow numbers, set for October 15.


Responsible
Organisation
organisation logo
Australian Antarctic Division (details)
Custodians
HARRY BURTON
harry.burton@aad.gov.au
INVESTIGATOR
TECHNICAL CONTACT
Australian Antarctic Division
203 Channel Highway
Kingston
Tasmania 7050
Australia
Ph +61 3 6232 3339
ROSEMARY GALES
rgales@dpiwe.tas.gov.au
INVESTIGATOR
Parks and Wildlife Service
DEPARTMENT OF PRIMARY INDUSTRY,
WATER AND ENVIRONMENT
GPO BOX 44A
Hobart
Tasmania 7001
Australia
Ph +61 3 6233 3865
Theme Area Biodiversity
Indicator Type Condition   
Criteria the
Indicator Satisfies
The following 14 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
12. Where possible and appropriate, facilitate community involvement
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 Yearly measurements
Monitoring Location Macquarie Island (details)  

Geographic Coverage is

    Latitude (-54.7 to -54.6)
    Longitude (158.8 to 158.9)

Rationale For Indicator Selection Elephant seals from Macquarie Island are long distance foragers who can
utilise the Southern Ocean both west as far as Heard Island and east as far as
the Ross Sea. Thus their populations reflect foraging conditions across a vast
area.


The slow decline in their numbers (-2.3% annually from 1988-1993) suggests
that their ocean foraging has been more difficult in recent decades.
Furthermore, interactions with humans are negligible due to the absence of
significant overlap in their diet with commercial fisheries. This suggests
that changes in "natural" ocean conditions may have altered aspects of prey
availability. It is clear that seal numbers are changing in response to ocean
conditions but at the moment these conditions cannot be specified.


Design and Strategy For Indicator Monitoring Program Spatial Scale: Five beaches on Macquarie Island (lat540 37' 59.9" S,
long 1580 52' 59.9" E): North Head to Aurora Point; Aurora Point to Caroline
Cove; Garden Cove to Sandy Bay; Sandy Bay to Waterfall Bay; Waterfall Bay to
Hurd Point.


Frequency: Annual census on 15th October


Measurement Technique: Monitoring the Southern Elephant Seal population on
Macquarie island requires a one day whole island adult female census on
October 15 and a daily count of cow numbers, fully weaned pups and dead pups
on the west and east isthmus beaches throughout October.


Daily cow counts during October, along the isthmus beaches close to the
Station, provide data to identify exactly the day of maximum numbers. The
isthmus counts are recorded under the long-established (since 1950) harem
names. Daily counts allow adjustment to the census totals if the day of
maximum numbers of cows ashore happens to fall on either side of October 15.
Personnel need to be dispersed around the island by October 15 so that all
beaches are counted for seals on that day. This has been achieved successfully
for the last 15 years.


On the day of maximum haul out (around 15th October) the only Elephant seals
present are cows, their young pups and adult males. The three classes can be
readily distinguished and counted accurately. Lactating pups are not counted,
their numbers are provided by the cow count on a 1:1 proportion. The combined
count of cows, fully weaned pups and dead pups provides an index of pup
production.


The count of any group is made until there is agreement between counts to
better than +/- 5%. Thus there is always a double count as a minimum; the
number of counts can reach double figures when a large group is enumerated.
The largest single group on Macquarie Island is that at West Razorback with
>1,000 cows; Multiple counts are always required there.


Research Issues Much research has been done already to acquire demographic data so that
population models can be produced. Thus there will be predicted population
sizes for elephant seals on Macquarie Island in 2002 onwards and the annual
censuses will allow these predictions to be tested against the actual numbers.
The censuses are also a check on the population status of this endangered
species.


Data

Timespan: 1988 to 2008.
Number of data points: 36.

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.



Macquarie Island: Number of breeding females - Full census


Macquarie Island: Number of breeding females - Partial census


Data Quality, Interpretation and
Analysis of Indicator Data
Two different methodologies have been employed to collect these data. From 1988 to 2004 a full census of all colonies on the island were conducted each year between the 13th and 17th of October - details of which are presented below. From 2005 onwards, owing to diminishing resources, a decision was made to only census a representative sample of the southern elephant seal colonies on the island. 5 colonies were selected as being representative of the whole island. Further information about this &partial& census can be found in a word document available for download from the URL given below.

In the data graphs displayed below, the &Full Census& graph present data collected between 1988 and 2004 using the full census method. The &Partial Census& graph present data from 1988 onwards using the partial census method - for the period 1988-2004, the figures for the 5 colonies used in the partial census have been obtained from the full census data.

Full Census Method:

Female Elephant seals haul-out to pup on island beaches according to a very regular pattern (Gaussian or Normal distribution) and timetable (peak haul-out between 13 and 17 October). They group together in &harems& with a few associated dominant males and are readily counted due to their obvious locations on open beaches and their lack of movement once ashore and having pupped. Thus counts of females can be made accurately to within +/- 5%.

The counts of the adult females (cows), fully weaned pups and dead pups are summed daily, and separately, through October for the west and east isthmus beaches. These totals represent the time distribution of numbers of cows ashore for each of these beaches. Corrections to the census totals are made in two stages:

Firstly, Gaussian curves are fitted to these distributions by least-squares calculations. From the equation to the curve for the west isthmus, the day of maximum numbers is determined as the calculated mean day. If the day of maximum numbers is not October 15, then the total for October 15 is increased by the proportional difference between it and the peak total of the fitted curve.

Secondly, the totals of the numbers for each of the five island zones counted on October 15 are increased to numbers predicted for the actual day of maximum cows ashore. This is done by transforming the fitted curve for the west isthmus into daily values of the proportion of cows present, from 1 (which is the number of cows at the peak of the curve) to fractions for each day on either side of the peak. Then the zone totals are divided by the fraction appropriate for their number of days delayed. This is done because the island beaches are grouped into five zones (see figure in instructions) which have characteristic day delays in their elephant seal cow numbers reaching a maximum with respect to the west isthmus area.

These delays are given in days:
ZONE- DAYS (delay from calc. peak day, west Isthmus)
North Head to Aurora Point - 0
Aurora Point to Caroline Cove - 3
Garden Cove to Sandy Bay - 2
Sandy Bay to Waterfall Bay - 3
Waterfall Bay to Hurd Point - 5

The total for the census is the sum of all these five adjusted zone totals.


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 These data are publicly available for download from the URL given below.
A copy of the word document describing the census methodology adopted in 2005 is also available for download from the URL given below.

Custodian Evaluation
Date entered Evaluation
15-Apr-2002 The data to date show that the number of breeding cows on Macquarie Island have been declining at ~1.2% per year for the last decade. This indicates that the large ocean environment that the seals forage in (the whole Southern Ocean between M.I. and Antarctica and west to Heard Is and east to the Ross Sea) is becoming less and less suitable for foraging by Southern Elephant Seals. It seems likely that present changes in ocean circulation in this huge area have resulted in reductions of plankton stocks to squid and myctophid fish (the major prey groups of Southern Elephant Seals) in accessible foraging areas for the seals compared to previous decades. There has been no appreciable and current competition between Southern Elephant Seals and fisheries in the Southern Ocean to date. Thus the seal decrease is attributable to "natural causes" as above.

11-Nov-2002
Condition scale - 4 - fair condition

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

    Metadata SOE_elephant_seals - Annual population estimates of Southern Elephant Seals at Macquarie Island from censuses made annually on October 15th.
    Project 2265 - Factors controlling the population status of the southern elephant seal Mirounga leonina at Macquarie Island
    Scientific Bibliography 17287 - Hindell, M.A., Burton, H.R. (1987) Past and Present Status of the Southern Elephant Seal (Mirounga leonina) at Macquarie Island. Journal of Zoology 213. pp 365-380.
    SOE Indicator 27 - Regional populations of Adelie penguins in the vicinity of Casey, Davis and Mawson.
    SOE Indicator 28 - Standard demographic parameters for Adelie penguins at Mawson
    SOE Indicator 29 - Breeding population of the Southern Giant Petrel at Heard Island, the McDonald Islands and within the AAT
    SOE Indicator 31 - Annual population estimates of Southern Elephant Seals at Macquarie Island
    SOE Indicator 32 - Fecundity and pup growth in fur seal colonies on Macquarie Island
    SOE Indicator 33 - Annual catch in tonnes of marine species harvested in Australian Antarctic and sub-Antarctic waters
    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 26 - Mirounga leonina Southern Elephant Seal
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 females - Full census (properties)
Number of breeding females - Partial census (properties)
The following parameters and/or sensor notes are from the metadata record.

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


Related URL's
http://data.aad.gov.au/aadc/portal/download_file.cfm?file_id=2308
Download page for Australian Antarctic Data Centre