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Contaminants on Australia's North West Shelf: sources, impacts, pathways and effects.
Specific objectives of the contaminants component of the North West Shelf Joint Environmental Management Study were to: Establish an inventory of contaminant inputs (nutrients and toxicants) from all known point and diffuse sources; Review the pathways, fates and bioavailability of the contaminants of concern in the water, sediments and biota; Establish environmental quality criteria to assess environmental health and provide early indications of environmental degradation; and For the contaminants of concern, collate and evaluate the applicability of available toxicological data, and if necessary develop acute and chronic toxicity data using local marine indicator species. The North West Shelf (NWS) has been subject to inputs of contaminants (toxicants and nutrients) from a variety of point and diffuse sources over the last 35 years. The various types of contaminants behave differently and can have different effects depending on their loads to, and concentrations in, the environment. Effective environmental management relies on an understanding of the types and quantities of wastes discharged, the sources of those discharges and their environmental consequences viewed individually and from a cumulative perspective, and considering both acute and chronic effects. An electronic database of annual loadings of point source contaminants discharged into NWS waters has been compiled for the period 1985 to 2001. The contaminants include toxicants such as heavy metals and petroleum compounds and nutrients such as nitrogen. Concentrations of heavy metals in the waters surrounding the offshore petroleum facilities were lower than the highest level of protection specified in the ANZECC & ARMCANZ (2000) guidelines. There are significant discharges of heavy metals from the Parker Point Power Station where the annual loads in 2000 range from 252 kg/yr for cadmium to 8 145 kg/yr for zinc. There appears to be no data on the concentration levels of these metals in the waters or the sediments surrounding the discharge sites. In 2000, 12 million tonnes of produced formation water containing 214 tonnes of oil was discharged from nine offshore petroleum facilities. This compares with an estimated 3,300 tonnes of oil naturally seeping into NWS waters. Few studies of the fates and effects of petroleum-based compounds have been undertaken on the NWS. These studies report no acute effects, but suggest that chronic and sub-lethal effects on marine plankton and bacteria have occurred in the vicinity of some of the production platforms. Concentrations of the antifouling chemical, tributyltin (TBT), were found in coastal waters of the Dampier Archipelago to be at levels ranging from 0.003 to 0.025 μg/L. In chapter 3 we review what is known about fates, pathways and potential bioavailability for the key contaminants of concern identified as part of the contaminants inventory and the review of toxicological data (chapter 4). These contaminants were identified as: six metals; barium, cadmium, chromium, copper, lead, mercury and zinc; one organometalloid: tributyltin (TBT); one nutrient: nitrogen; a waste stream; produced formation waters (PFW); and hydrocarbons (oil). The results of the water quality study indicate that the coastal waters of the North West Shelf are generally of very high quality. The concentrations of metals were low by world standards, with localised elevations of some metals adjacent to industrial centres and ports. No organic chemicals were detected. The reporting limits were well below the guideline trigger values recommended in ANZECC & ARMCANZ (2000) for a very high level of ecological protection for the five organics for which guideline values were available. The findings of this study suggest that ANZECC & ARMCANZ (2000) 99% species protection guidelines are relevant to the region for all metals analysed, except cobalt, for which the 95% species protection guideline is recommended for u
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Environmental sampling in the coastal waters of south eastern Tasmania
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Comprehensive baseline environmental data for Storm Bay in south eastern Tasmania were required to inform the salmonid industry regarding site selection, to provide background environmental data before large-scale farming commences, and to support the development of a scientifically relevant and cost-effective environmental monitoring program. Storm Bay is a large deep bay that receives freshwater inflow from the River Derwent on its north-western boundary and exchanges water with Frederick Henry Bay on its north-eastern boundary. The eastern and western boundaries are defined by the Tasman Peninsula and Bruny Island, respectively, and the southern boundary connects with the Tasman Sea. This area is a mixing zone between the River Derwent outflow and oceanic waters. The oceanography in Storm Bay is complex and is characterized by considerable fluctuations in temperature, salinity and nutrients on variable temporal and spatial scales. This is due to the southerly extension of warm nutrient-depleted sub-tropical waters transported via the East Australian Current (EAC) down the east coast of Tasmania over summer, whilst the south and south-west coasts are influenced by cooler, nutrient-rich sub-Antarctic waters from the south and the Leeuwin Current from the north-west (Buchanan et al. 2014). The current project arose in response to the salmon aquaculture industry recognising the need for increased scientific knowledge to support ecologically sustainable development of Atlantic salmon (Salmo salar) farming operations in south-eastern Tasmania, particularly expansion into Storm Bay. The information provided will assist salmon companies to manage their operations in Storm Bay under varying environmental conditions. Our research has also provided the opportunity to investigate changes in water quality over a quarter of a century, as CSIRO investigated seasonal and inter-annual variability in chemical and biological parameters in Storm Bay during 1985-89. We sampled at the same “master station” in Storm Bay as CSIRO and used similar procedures where possible. Five sites were sampled monthly in Storm Bay for over five years from November 2009 to April 2015, except on rare occasions when weather conditions were unsuitable, and bimonthly at times in 2013 when external funding was not available. Site 1 was located at the mouth of the Derwent estuary and the entrance to Storm Bay, site 2 was in the same location as the ‘master site’ of a CSIRO study in 1985-88, site 3 was furthest offshore and provided the most information on oceanic currents influencing the bay, while sites 5 and 6 were requested by the salmon aquaculture industry as potential sites for expansion of salmon farming. Site 4 was further offshore and monitoring at this site was discontinued after three months because of insufficient time to collect samples from all sites in one day. An additional site, 9, at the entrance to Frederick Henry Bay was included from 18 July 2011 at the request of the Marine Farming Branch, Department of Primary Industries, Parks, Water and Environment (DPIPWE), to provide information on water quality coming from Frederick Henry Bay. Adjacent to, and largely unaffected by the River Derwent, Frederick Henry Bay is a large marine embayment with limited freshwater input from the Coal River at its northern boundary. See child records linked to this parent record for specific context and methodologies for each of the monitoring variables (phytoplankton, zooplankton, chlorophyll, pigment, nutrients, oceanography).
Southern Surveyor Voyage SS 05/2007 - Voyage of discovery - Sediments of the deep continental shelf and slope in Australia's "North West Region"
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The overall aims were to provide data on the distribution of deep seabed habitats and fauna that are amenable to scientific hypothesis testing, can be immediately applied to marine resource management processes, and that enable strategic development of tools and techniques for understanding the processes that maintain deep sea biodiversity. This work was to support the process of NWR Estate inventory and management performance assessment by providing interpreted benthic habitat maps, faunal inventories, distribution maps and conservation values. Data will be collected at scientific reference sites from potential MPA areas that can be re-visited for monitoring purposes in the future. Sampling along environmental gradients (geographic range and depth) in this section of Australia's coast will also provide the opportunity to evaluate biogeographic hypotheses. Further refinement of predictive methods for identifying seabed habitat types, initially developed in temperate and cool-temperate environments, will be enabled by data collection from this tropical location in Australia. We intended to highlight the importance of this underlying science as a modern "Voyage of Discovery" given the likely significance of the findings in terms of Australia's biodiversity and its biogeography and evolution. (From Voyage Plan). Sediment samples were divided into two samples: an elutrition sample for macroinvertebrates that was sent to Robin Wilson at MV for analysis and a sediment sample to be analysed by Geoscience Australia.
해양수산부 해양방사성물질 제주연안 삼중수소 신속분석결과
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우리나라 제주연안(10개정점)에 대해 방사성물질이 어느 정도로 분포하고 있는지 일반분석(증류법) 결과를 제공합니다.
Transport and dispersal of selected pollutants in the terrestrial and nearshore marine environments, Casey Station
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Metadata record for data from ASAC Project 2179 See the link below for public details on this project. Taken from a progress report of the project written in 1998: 60 terrestrial sediments have been taken from Wilkes and Thala Valley tip, with control sites at Robinsons Ridge and Jacks Donga. 50 marine sediments have been taken from the bay offshore from Thala Valley tip. 116 fresh and marine waters have been taken from the fresh water stream flowing through the Thala Valley tip, the tip/sea interface, and the nearshore marine offshore from Thala Valley tip and control sites. Formal integration of these data into a GIS is underway. These data have not been archived until 2012, hence the only data available were sourced from publications arising from the project.