Oceanographic measurements were conducted in the Subantarctic Zone south of Tasmania in September 1997. 5 sediment trap moorings were deployed, and a total of 10 CTD vertical profiles were taken. Over 90 Niskin bottle water samples were collected for the measurement of salinity and nutrients (phosphate, nitrate+nitrite, silicate). The fields in this dataset are: oceanography ship station number date start time bottom time finish time cruise start position bottom position finish position maximum position bottom depth pressure temperature (T-90) salinity sigma-T specific volume anomaly geopotential anomaly dissolved oxygen fluorescence photosynthetically active radiation

This file contains a report of biological field work undertaken in the Casey region during 1976. It includes work done on seals and seabirds. The hard copy of the log has been archived by the Australian Antarctic Division library.

Taken from sections of the report: This report has been prepared as a supplement to the 1997/98 Survey Report by John Hyslop and contains solely comments and recommendations as seen from the perspective of the volunteer survey student. It is hoped this report may be of some use in the future planning and operation of Surveying and Mapping expeditions to Antarctica. The report has been divided according to each area visited and discusses the work achieved and highlights any possible improvements either in the actual surveys undertaken or the execution of the program as a whole. Typical issues include helicopter operations, aerial photography, the oblique mount, collaboration with other field parties, transportation and so on. VOYAGE SOUTH The voyage south provided the ideal opportunity to begin the detailed planning of the work to come. Flight planning for the photography was started and locations for photo control throughout the offshore islands at Mawson were determined. It was important to prioritize which work was to be undertaken first throughout the offshore islands at Mawson. This was to ensure the most important work was completed before the sea ice deteriorated and prevented travel on quads. The voyage to Mawson went via Casey where the surveyors were required to undertake a small amount of work during the stop over. Ice conditions prevented the Aurora reaching Casey. John and I were unable to make it to Casey due to the long fly off and limited time. Ian Sutherland (Station Leader at Casey) informed us that snow conditions over the station would have prevented most survey work anyway. This was the perfect example that survey work in Antarctica is totally dependent on current weather conditions in addition to the 'A' factor. This highlighted the fact that all plans for work in the Antarctic are required to be 'dynamic' and hence the various priorities listed in the brief were appreciated. It was quite frustrating spending close to 4 weeks on the Aurora before arriving on the continent and beginning the work proper. The frustration culminated in the problem with the Aurora's rudder and expeditioners being told we may be returning to Australia even though we were within fly-off distance to Mawson.

Sediment Recruitment Experiment 4 (SRE4) was a large, long term (5 year) field experiment run at Casey Station (from 2001 to 2006) testing the effects of 4 different hydrocarbons on marine sediment ecosystems. Four different types of hydrocarbons were individually mixed with defaunated marine sediments and deployed in trays on the seabed at O'Brien Bay-1. Trays were collected after deployment periods of 5 weeks, 56 weeks, 62 weeks, 2 years and 5 years. In addition there was a bioturbation treatment using the burrowing urchin Abatus (at 56 weeks only). Samples were collected from 4 replicate trays of each treatment at each sampling time. Analyses were done of sediment hydrocarbon chemistry, microbial communities, meiofaunal communities, macrofaunal communities and diatom communities. The hydrocarbon treatments were: a synthetic Mobil lubricating oil; the same Mobil lubricating oil after 125? hours use in a vehicle engine; a Fuchs synthetic lubricating oil marketed as highly biodegradable; and Special Antarctic Blend diesel fuel (SAB). A control uncontaminated sediment treatment was used for comparison.

This GIS dataset contains bird data from 1998/99 field work in the Windmill Islands by Jonny Stark and Jeroen Creuwels. The locations are Frazier Islands, Ardery Island and Casey station. Polygon data represents the extents of flying bird nesting areas and adelie penguin colonies. Point data represents flying bird nest locations.

These data tables were scanned by Fiona Gleadow. The data relate to diving petrels (Pelecanoides) from Heard Island, and generally appear to be measurements of body parts (weight, wing, tail, beak, tarsus, toe) on males and females, as well as measurements of eggs (weight, length and width).

This dataset contains the underway data collected during the Aurora Australis Voyage 2 2001-02. This voyage went to Casey and Macquarie Island, leaving from and returning to Hobart. Underway (meteorological, fluorometer and thermosalinograph) data are available online via the Australian Antarctic Division Data Centre web page (or via the Related URL given below). For further information, see the Marine Science Support Data Quality Report at the Related URL below.

An occupancy survey on 26 January 2012 found 1 island (70166) along the coast between 111 degrees 00'E - 111 degrees 10'E had populations of breeding Adelie penguins. The survey was conducted from a fixed wing aircraft and oblique aerial photographs were taken of the occupied site. The aerial photographs were geo-referenced to the coastline shapefile from the Landsat Image Mosaic of Antarctica (LIMA, tile E158) and the boundaries of penguin colonies were digitised from the geo-referenced photos with not intentional buffer. Note the quality of the aerial photos was poor and so the resultant boundary mapping will not be very accurate. Also in the Balaena Islands there is a historic record from the 50s of penguins nesting on Thompson Islet (70166). When aerial photos were taken of this island penguins could not be detected. Please refer to the Seabird Conservation Team Data Sharing Policy for use, acknowledgement and availability of data prior to downloading data.

This metadata record contains the results from bioassays conducted to show the response of larval Antarctic Sterechinus neumayeri sea urchins to contamination from combinations if IFO 180 fuel and the fuel dispersant Slickgone NS. AAS project 4142. Experiments used an intermediate grade Fuel Oil (IFO 180) and an internationally approved fuel dispersant, Slickgone NS, produced by Dasic International LTD. Treatments included a physically dispersed treatment of IFO 180 only, a chemically dispersed treatment of IFO 180 treated with Slickgone NS and a Slickgone NS only treatment to determine the toxicity of the dispersant. Treatments were experimentally mixed using a magnetic stirrer to combine treatment substances and filtered seawater (FSW) in temperature-controlled cabinets at 0oC to create a Water Accommodated Fraction (WAF). WAFs were produced in 2 L and 5 L glass aspirator bottles following the methods of Singer, Aurand et al. (2000) with adaptations by Barron and Ka'aihue (2003) and Kostzakoulakis (chemistry section, project 4142) stirring for 42 h with a settling time of 6 h. WAF treatments used concentrations of 100%, 50%, 20% and 10%, CEWAF and dispersant only treatments used concentrations of 10%, 5%, 1% and 0.1%. Toxicity tests were conducted in temperature-controlled cabinets at 0 oC using uncapped, forty-millilitre glass headspace vials, each containing 15.5 ml of test solution and 0.5 ml of embryo suspension. Fertilisation methods followed standard procedures for Sterechinus neumayeri. Two tests were conducted to determine the effect of a single pollution event (test 1) compared with a recurring repeated pulse pollution event (test 2). Test 1 required no water changes, while test 2 required renewal of the test treatments on a 4-day basis. Three endpoints were used, un-hatched blastula (48 h to 48.5 h) to represent the embryonic phase, gastrula (10 d) and 4-armed pluteus (16 d to 18 d). At the termination of each endpoint, 1 ml of 10% buffered formalin was added to each relevant vial and recapped. At the conclusion of the experiments, preserved embryos were observed under a dissecting microscope to determine the number of normal, abnormal and unfertilised embryos relative to controls. Samples for analysis of total petroleum hydrocarbon content were taken throughout the 2 experiments to determine the actual concentrations to which embryos and larvae were exposed. The measured concentrations were integrated following the methods of Payne et al. (2014) to obtain a profile of hydrocarbon content over each test period. Two spreadsheets are included in this metadata record detailing survival data and results of hydrocarbon analysis. The survival data file includes test condition details on the first tab, with data for tests 1 and 2 on the second and third tabs. Test treatment and concentration are listed on the left of each data block and count categories are defined in the top left panel. Development stage, date preserved and age of organism is defined for each data block, representing the three endpoints included in the experiments: unhatched blastula, gastrula and 4-armed pluteus. The hydrocarbon analysis, TPH (total petroleum hydrocarbon) file details chemical analysis results produced by K. Kotzakoulais at Macquarie University as part of project 4142. Row terminology explanations are as follows: TPH metadata Test name- indicates the tested species Exp number-indicates whether the data belongs to test 1 or test 2 Water change- details the identification of the sample in relation to the 4-day water change regime. Start samples represent the beginning of the experiment. Pre samples are taken at the end of the corresponding 4-day period, before the water is changed. 'Post' samples are taken of newly made test solutions. The chronological order of sampling is therefore: Start, pre4d, post4d, pre8d, post 8d etc. Only 'pre' samples were taken for test 1, as there were no water changes. less than C9 - greater than C28- Hydrocarbon content of samples was broken down into four compound size classes detailed for each analysis. Contamination- contamination was detected in samples, the source of contamination remains unclear, however it was established that contamination occurred during the sampling process and therefore did not come into contact with organisms. Contamination was therefore excluded from calculations. The hydrocarbon content of 0.1% dilutions was unable to be reliably analysed due to accuracy of the equipment and interfering contamination. Control data indicates spot checks to confirm the presence or absence of fuel. Very small amounts of hydrocarbons were detected as lighter fuel components evaporated and dissolved into control water within the cabinet. These very small amounts are negligible. Abnormality metadata Tab 1 details test conditions Tab 2 'Test 1' includes the data for test 1 Tab 2 'Test 2' includes the data for test 2. All observational categories are defined within the spreadsheet.

Adelie colony boundaries at Bechervaise Island were mapped by Matthew Pauza on the 21 Dec 2016. Subcolonies were mapped by circumnavigating the perimeter on foot while carrying a Garmin GPS (Etrex30) to record the track. When mapping the perimeter of the subcolonies a buffer distance of approximately 2.5 meters was maintained between the mapper and the breeding birds. This buffer distance was reduced by .5m to between 2m in the final shapefiles. Please refer to the Seabird Conservation Team Data Sharing Policy for use, acknowledgement and availability of data prior to downloading data.