Sabine Duquesne

Management and remediation of contaminated sites at Casey Station, Antarctica

The Protocol on Environmental Protection to the Antarctic Treaty requires that past and present work sites be cleaned up unless removal would result in greater adverse environmental impact than leaving the contaminant in its existing location. In the early 1990s Australia began the documentation of contaminated sites associated with its research stations, which resulted in an extensive record of contamination at abandoned stations and waste-disposal sites. Currently the technical capability to remediate these sites does not exist because of environmental challenges that are unique to the cold regions. Investigations indicate that clean-up operations in the past have proceeded without adequate precautions and without effective monitoring. To address these problems, three research priorities have been identified to assist meeting international and national obligations to clean up these sites. They are: understanding contaminant mobilisation processes; development of ecological risk assessment for use in monitoring and setting priorities; and development of clean-up and remediation procedures. This study provides sufficient information to guide the completion of a clean-up at Casey Station and to indicate how other similar sites should be managed. The next stage is to develop the theory into an operational plan to include detailed protocols for clean-up, monitoring, site remediation, and management of the waste stream from site to final repository. To achieve this, the Australian Antarctic Division has established a contaminated sites taskforce to facilitate the transition from research and development of techniques to implementation of suitable clean-up options.

Pesticides in Sediments From Queensland Irrigation Channels and Drains

Abstract Pesticide concentration in sediment from irrigation areas can provide information required to assess exposure and fate of these chemicals in freshwater ecosystems and their likely impacts to the marine environment. In this study, 103 sediment samples collected from irrigation channels and drains in 11 agricultural areas of Queensland were analysed for a series of past and presently used pesticides including various organochlorines, synthetic pyrethroids, benzoyl ureas, triazines and organophosphates. The most often detected compounds were endosulphans (α, β and/or endosulphan sulphate) which were detectable in 78 of the 103 samples and levels ranged from below the limit of quantification (0.1 ng g−1 dw) up to 840 ng g−1 dw. DDT and its metabolites were the second most often detected pesticide investigated (74 of the 103 samples) with concentrations up to 240 ng g−1 dw of ∑DDTs. Mean ∑endosulphan and ∑DDT concentrations were 1–2 orders of magnitude higher in sediments from the irrigation areas which are dominated by cotton cultivation compared to those which are dominated by sugarcane cultivation. In contrast to these insecticides, the herbicides diuron, atrazine and ametryn were the compounds which were most often detected in sediments from irrigation drains in sugarcane areas with maximum concentrations in areas of 120, 70 and 130 ng g−1 dw, respectively. In particular during flood events, when light is limiting, transport of these photosynthesis inhibiting herbicides from the sugarcane cultivation areas to the marine environment may result in additional stress of marine plants.

Effects of contaminants in the Antarctic environment — potential of the gammarid amphipod crustacean Paramorea walkeri as a biological indicator for Antarctic ecosystems based on toxicity and bioacccumulation of copper and cadmium

This study provides information on LC(50) toxicity tests and bioaccumulation of heavy metals in the nearshore Antarctic gammarid, Paramorea walkeri. The 4 day LC(50) values were 970 µg/l for copper and 670 µg/l for cadmium. Net uptake rates and bioconcentration factors of these elements were determined under laboratory conditions. After 12 days of exposure to 30 µg/l, the net uptake rates were 5.2 and 0.78 µg/g per day and the bioconcentration factors were 2080 and 311 for copper and cadmium, respectively. The body concentrations of copper were significantly correlated with the concentrations of this element in the water. Accumulation of copper and cadmium continued for the entire exposure suggesting that heavy metals concentrations were not regulated to constant concentrations in the body. Using literature data about two compartments (water-animal) first-order kinetic models, a very good agreement was found between body concentrations observed after exposure and model predicted. Exposure of P. walkeri to mixtures of copper and cadmium showed that accumulation of these elements can be assessed by addition of results obtained from single exposure, with only a small degree of uncertainty. The study provides information on the sensitivity of one Antarctic species towards contaminants, and the results were compared with data of similar species from lower latitudes. An important finding is that sensitivity to toxic chemicals and toxicokinetic parameters in the species investigated are comparable with those of non-polar species. The characteristics of bioaccumulation demonstrate that P. walkeri is a circumpolar species with the potential to be a standard biological indicator for use in monitoring programmes of Antarctic nearshore ecosystems. The use of model prediction provide further support to utilise these organisms for biomonitoring.

Culmination of Low-Dose Pesticide Effects

Pesticides applied in agriculture can affect the structure and function of nontarget populations at lower doses and for longer timespans than predicted by the current risk assessment frameworks. We identified a mechanism for this observation. The populations of an aquatic invertebrate (Culex pipiens) exposed over several generations to repeated pulses of low concentrations of the neonicotinoid insecticide (thiacloprid) continuously declined and did not recover in the presence of a less sensitive competing species (Daphnia magna). By contrast, in the absence of a competitor, insecticide effects on the more sensitive species were only observed at concentrations 1 order of magnitude higher, and the species recovered more rapidly after a contamination event. The underlying processes are experimentally identified and reconstructed using a simulation model. We conclude that repeated toxicant pulse of populations that are challenged with interspecific competition may result in a multigenerational culmination of low-dose effects.

Long-term signal of population disturbance after pulse exposure to an insecticide : Rapid recovery of abundance, persistent alteration of structure

Little is known about the effect of pulse exposure to toxicants on populations when density regulation is present. Yet, for a more realistic risk assessment, it is necessary to include effect and recovery at the population level. Here, we investigate the long-term and delayed effects as well as the subsequent recovery of populations of Daphnia magna. A 24-h pulse of the pyrethroid fenvalerate reduced the abundance at a concentration of 1.0 microg/L and higher. However, abundance recovered and reached control levels after one to two generation times (GTs) following reproduction of surviving individuals (GT = 8 d, from birth until first reproduction). At high concentrations above the acute median lethal concentration (3.2 micorg/L), abundance initially decreased even more strongly but was then elevated compared to control values for an extended period of time. Population structure (size distribution) was affected at lower concentrations than abundance (> 0.8 microg/L). In addition, the alteration of population structure lasted for a long time, so that control levels were approached only after approximately six or seven GTs. Our results show that pulse exposure to toxicants may lead to a long-term alteration of population structure even at sublethal concentrations. Possible mechanisms that sustain the effects of toxicants may be delayed life-history effects on the individual level and elevated competition because of altered population structure on the population level.

Linking feeding activity and maturation of Daphnia magna following short‐term exposure to fenvalerate

Feeding activity and maturation were investigated in Daphnia magna exposed to fenvalerate for 24 h. The feeding activity was monitored by measuring filtration rates and 15N-traced food assimilation. Exposure resulted in individuals with reduced feeding activity and smaller body size at concentrations of 0.3 microg/L or greater as well as delayed maturation at concentrations of 0.61microg/L or greater. Filtration rates recovered within 2 d of the exposure, but long-term effects of reduced feeding activity, such as growth retardation, occurred. Because D. magna needs to reach a minimum size to mature, growth retardation may explain the observed delay in maturity. The proposed causal relationships suggest that exposure to fenvalerate reduces feeding activity, resulting in growth retardation, which leads to delayed maturity. In cases of exposure to such toxicants, the monitoring of feeding activity may predict long-term effects on population parameters.

Biological monitoring of heavy-metal contamination in coastal waters off Casey Station, Windmill Islands, East Antarctica

Abstract. Heavy-metal concentrations were determined in tissues of different species of benthic invertebrates collected in the Casey region (Australian Antarctic Territory) where an old waste-disposal tip site is a source of contamination. The species studied included the bivalve Laternula elliptica, starfish Notasteriasarmata, heart urchins Abatusnimrodi and A. ingens and gammaridean amphipod Paramoerawalkeri. The specimens were collected at both reference and contaminated locations where lead was the priority element and copper was the next most important in terms of increased concentrations. The strong association between a gradient of contamination and concentrations in all species tested indicates that they are reflecting well the environmental changes, and that they appear as appropriate biological indicators of heavy-metal contamination. Aspects of the biology of species with different functional roles in the marine ecosystem are discussed in relation to their suitability for wider use in Antarctic monitoring programmes. For example, in terms of heavy-metal bioaccumulation, the bivalve appears as the most sensitive species to detect contamination; the starfish provides information on the transfer of metals through the food web while the heart urchin and gammarid give indications of the spatial and temporal patterns of the environmental contamination. The information gathered about processes of contaminant uptake and partitioning among different tissues and species could be used in later studies to investigate the behaviour and the source of contaminants.

Metal accumulation in the clam Tridacna crocea under natural and experimental conditions

Clams (Tridacna crocea) were collected from three sites in the Torres Strait along a transect from the mouth of the heavily polluted Fly River towards the south. The concentrations of Cu, Cd and Zn in different organs of the clams were determined and, with the exception of Cd levels in the gills and mantle, were found to decrease with increasing distance from the river outfall. The levels of metals in the clam tissues, however, fall within a similar range of values found in control clams collected from Orpheus Island. In addition, the rates of metal bioaccumulation in clams were studied under laboratory conditions. Experiments carried out with either Cd (0.20 mg/l) or Cu (0.06 mg/l) in seawater revealed a linear uptake of metal throughout the experimental period in different clam organs. The highest accumulation rates were found in the kidney and the lowest in the muscle. The accumulation rate of Cd was higher in the mantle than in the gills, whereas the inverse was found for Cu. Cu treatment resulted in significant expulsion of the symbiotic zooxanthellae from the mantle, a recognized stress response. In clams collected from the wild, the concentration of renal metal-binding proteins (metallothionein-like proteins) increased with the levels of total metal in the kidneys, and indirectly reflected the environmental levels.

Biochemical, metabolic, and behavioural responses and recovery of Daphnia magna after exposure to an organophosphate

The responses of various suborganismal and organismal endpoints of Daphnia magna to pulse exposure to sublethal levels of the organophosphate paraoxon-methyl were compared. The changes and recovery of biochemical, metabolic, and behavioural variables, as well as physiological responses, were observed. The cholinesterase (ChE), filtration, and swimming activities were all affected in a concentration-dependent manner, and these effects reached significance at concentrations of 1.0, 1.5, and 0.7 microg L(-1), respectively. The levels of these variables recovered significantly after detoxification for 24h in clean medium. ChE and swimming activities were affected significantly by lower concentrations of paraoxon-methyl than filtration activity, which had the same threshold as the physiological responses ((15)N abundance and body size). This study showed that among the parameters studied, swimming activity was the most sensitive, whereas changes in filtration activity had the most significant physiological consequences, and were therefore important in terms of effects propagation to the population level.

Effects of the organophosphate paraoxon-methyl on survival and reproduction of Daphnia magna : Importance of exposure duration and recovery

The aim of this study was to determine the influence of exposure duration (1 h, 24 h, continuous) to paraoxon-methyl on the magnitude of lethal and sublethal effects, the shape of the concentration-response relationships and the recovery processes in Daphnia magna. Survival was more severely reduced in the continuous than in the pulse exposure regimes. The lethal concentrations (3d median lethal concentration [LC50] values) were 233, 2.33, and 1.14 microg/L after 1-h, 24-h, and continuous exposure, respectively. The shapes of the concentration-response relationships for survival were significantly different after 1 h of exposure than after 24-h and continuous exposure. Indeed, the slopes of the curves defined by the ratios LC90/LC10 (ratio of 90 and 10% lethal concentrations) were 100, 1.74, and 1.97 for 1-h, 24-h, and continuous exposure, respectively. The large difference between 1 h and longer durations of exposure shows that the population is partially affected (10-90%) over a much broader range of concentrations when exposure is short. Negative effects on reproductive outputs occurred mostly at concentrations affecting partly the survival and therefore also over a broad range of concentrations after 1 h of exposure. However, these effects were only transient in the pulse exposure regimes as individual performances recovered. By contrast, reproductive outputs of survivors exposed continuously remained impaired. These results suggest that a refined risk assessment should consider exposure duration because it influences the magnitude of effects and recovery.