Impacts of gold mine waste disposal on a tropical pelagic ecosystem.

We used a comparative approach to investigate the impact of the disposal of gold mine tailings into the ocean near the Lihir mine (Niolam Island, Papua New Guinea). We found abundance and diversity of zooplankton, micronekton and pelagic fish to be similar or higher in the mine region compared to the reference site. We also found relatively high trace metal concentrations in lower trophic level groups, especially zooplankton, near the mine discharge, but few differences in tissue concentrations of micronekton, baitfish and pelagic fish between the two regions. Biomagnification of some trace metals by micronekton, and of mercury by fish was evident in both regions. We conclude that ocean mine waste disposal at Niolam Island has a local impact on the smaller and less mobile pelagic communities in terms of trace metal concentrations, but has little effect on the abundance and biodiversity of the local food web.

A rapid radiochemical bacterial bioassay to evaluate copper toxicity in freshwaters.

A rapid, highly sensitive bacterial bioassay to determine copper toxicity in freshwaters was developed based on the inhibition of cellular assimilation of radiolabeled glucose. The test used a copper-sensitive bacterium isolated from a freshwater stream. Employing sensitive radiochemical techniques enabled environmentally relevant concentrations of the test bacterium (10(5) cells mL(-1)) and a short incubation period (4 hours) to be used, which minimized the potential for changes in copper speciation during the test. The 4-hour median effective concentration (EC(50)) for inorganic copper at pH 7.5 in synthetic freshwater was 0.6 microg L(-1) (95% confidence limits 0.4 to 1.0 microg L(-1)). This compared well with chronic growth inhibition of this bacterium in minimal medium (48-hour EC(50) of 0.9 microg L(-1) [95% confidence limits 0.7 to 1.0 microg L(-1)]). MINEQL + software (Environmental Research Software) was used to calculate copper (II) ion concentrations in synthetic freshwater at pH 7.5, giving an EC(50) value of pCu(2+) 8.8. However, using nitrilotriacetic acid metal-ion buffers (Cu-NTA), 50% inhibition occurred at a pCu(2+) of 9.7, suggesting this bacterium was markedly more inhibited by copper in these Cu(2+)-buffered solutions. This may indicate that the Cu-NTA species was contributing to toxicity. The radiochemical bioassay was evaluated further using freshwater samples from both copper-impacted and pristine environments. Measured EC(50) values ranged from 3.4 to 34.0 microg L(-1)inorganic copper and were strongly correlated with dissolved organic carbon (DOC) concentrations (r = 0.88, p < 0.05).

Hardness corrections for copper are inappropriate for protecting sensitive freshwater biota.

Toxicity testing using a freshwater alga (Chlorella sp.), a bacterium (Erwinnia sp.) and a cladoceran (Ceriodaphnia cf. dubia) exposed to copper in synthetic and natural freshwaters of varying hardness (44-375 mg CaCO3/l), with constant alkalinity, pH and dissolved organic carbon concentration, demonstrated negligible hardness effects in the pH range 6.1-7.8. Therefore, the use of a generic hardness-correction algorithm, developed as part of national water quality guidelines for protecting freshwater biota, is not recommended for assessing the toxicity of copper to these, and other, sensitive freshwater species. Use of the algorithm for these sensitive species will be underprotective because the calculated concentrations of copper in water that cause a toxic effect will be higher.

Dissolved trace metal distributions in Port Jackson estuary (Sydney Harbour), Australia.

Concentrations of dissolved metals (Cd, Cu, Ni, Mn and Zn) were determined for summer and winter, under low-flow conditions in Port Jackson, a microtidal, well-mixed estuary in south-east Australia. Mean concentrations of Cd (0.04+/-0.02 microg/l), Ni (0.86+/-0.40 microg/l), Mn (20.0+/-25 microg/l) and Zn (6.47+/-2.0 microg/l) were below water quality guidelines. Concentrations of Cu (1.68+/-0.37 microg/l), however, slightly exceeded recommended values. Dissolved Ni and Mn behaved mostly conservatively, whereas Cd, Cu and Zn showed mid-estuarine maxima. Peaks in Cd, Cu and Zn concentrations were located in the upper estuary, independent of the salinity and suspended particulate matter loading, and were consistent with anthropogenic inputs of metals in the estuary. Concentrations of dissolved Cu were highest in summer, whereas concentrations of Cd, Ni and Mn were significantly lower in summer than winter (P< or =0.05). The increase in temperature and biological activity during summer explained the seasonal variation. The sequence of log K(d) values (20-30 salinity) was Mn>Zn>Cu>Ni. These results give unique information concerning the contemporaneous distribution of dissolved trace metals in the Port Jackson estuary and they provide a data set against which the long-term contamination may be assessed.

An evaluation of potential interferences in a fluorimetric assay for the rapid detection of thermotolerant coliforms in sewage.

A 1-h fluorimetric assay of beta-D-galactosidase activity was evaluated for determining thermotolerant coliforms (TTC) in sewage samples. Above TTC concentrations of 2.3 x 103 colony-forming units (cfu) 100 ml-1, the assay response was related to TTC concentration. However, below this concentration, a large background signal was observed which was independent of TTC concentration. A separation scheme involving various filtration treatments and additions of a beta-D-galactosidase inhibitor was devised and used to quantify the sources of this anomalous assay response. The interferences encountered were largely due to the presence in sewage of non-specific cell-free enzymes or other cell-free substances that were capable of hydrolysing the fluorogenic substrate. Despite this apparent limitation, the fluorimetric enzyme assay has potential as an 'early warning' indicator of treatment process failure and gross sewage contamination and leakage in situations where TTC concentrations exceed 2.3 x 103 cfu 100 ml-1

Sample storage artifacts affecting the measurement of dissolved copper in sulfidic waters.

Sample preservation and storage procedures (acidification with HNO(3) and storage in plastic bottles) normally employed prior to the determination of dissolved Cu in sulfidic waters were compared with sample preservation involving the initial oxidation of sulfide with H(2)O(2) or S(2)O(5)(2-) followed by acidification. Acidification alone was demonstrated to be inadequate and resulted in a significant underestimation of dissolved Cu (losses ranging from 50% to >90%). Similar losses were observed in both polyethylene and Teflon storage bottles. Experiments suggest that losses of copper occur following sample acidification owing to the formation of stable copper sulfide phases which adsorb onto container surfaces. It is therefore recommended that an oxidative pretreatment step is carried out prior to the acidification of porewaters collected for metal analysis. The results of this study suggest that much of the previous data reporting dissolved Cu concentrations in sulfidic waters and porewaters may be in error.

Beta-D-galactosidase activity of viable, non-culturable coliform bacteria in marine waters.

The beta-D-galactosidase activity of viable but non-culturable (vnc) Escherichia coli cells in seawater was investigated using a rapid fluorimetric enzyme assay. Results from microcosm studies showed that loss of culturability did not necessarily result in loss of the ability to produce the galactosidase enzyme. Even when no culturable cells were detected, a positive enzyme assay response was observed and the activity of the inducible enzyme over time more closely reflected the number of vnc cells present.

Possible interference of lactose-fermenting marine vibrios in coliform beta-D-galactosidase assays.

An investigation into possible interferences in beta-D-galactosidase-based assays for coliform bacteria in marine waters was carried out. A rapid instrumental fluorescence assay for beta-D-galactosidase activity, using 4-methylumbelliferyl-beta-D-galactoside as a substrate, was used to investigate activities of this enzyme in non-coliform bacterial isolates from coastal waters. Only 2% of isolates showed slight enzyme activity after a 1-h incubation period at 44.5 degrees C. At a lower incubation temperature of 20 degrees C, 51% and 94% of the isolates showed some enzyme activity within 6 h and 48 h, respectively. Fifty-nine out of 67 of these isolates were identified as Vibrio species. A lac+ strain of Vibrio vulnificus was found to produce beta-D-galactosidase which caused significant false-positive reactions in the Colilert-Marine Water assay when present at concentrations of 10 cfu ml-1 or greater. This interference could be overcome by addition of the vibriostatic agent O/129. The high fluorescence of this reagent, however, precluded the simultaneous determination of Escherichia coli in the Colilert test and also its use in instrumental fluorescence assays. It was concluded that in assays employing high temperatures and short incubation times, Vibrio species are unlikely to cause significant interferences.

Plant and algal interference in bacterial beta-D-galactosidase and beta-D-glucuronidase assays.

Several commonly occurring freshwater and marine plants and algae were screened for beta-D-galactosidase and beta-D-glucuronidase activities by using a 60-min enzyme assay based on the hydrolysis by these enzymes of 4-methylumbelliferyl-beta-D-galactoside and 4-methylumbelliferyl- beta-glucuronide, respectively. All freshwater plant extracts tested showed beta-D-galactosidase activity several at relatively high levels, and a number also showed beta-D-glucuronidase activity. A number of the macroalgae showed no activity of either enzyme, but those showing beta-D-galactosidase activity also showed beta-D-glucuronidase activity. The majority of microalgae showed some beta-D-galactosidase activity, but few showed beta-D-glucuronidase activity. Further studies, using the commercial Colilert test and the marine water formulation of Colilert, revealed that 2 of 11 of the microalgal species and several of the plant extracts tested caused positive reactions. It was concluded that several plant extracts and algae could significantly interfere with the detection of coliform bacteria and Escherichia coli with the use of rapid assays, on the basis of their production of beta-D-galactosidase and beta-D-glucuronidase, respectively. The significance of the plant and algal interferences in tests such as Colilert is dependent on the levels of enzymes released under natural conditions, the dilution which they may undergo, and the numbers of algal cells present. This also applies to interferences in rapid enzyme assays.(ABSTRACT TRUNCATED AT 250 WORDS)

Determination of organotins in natural waters by toluene extraction and graphite furnace AAS.

The determination of tributyltin in natural waters by extraction into toluene and graphite-furnace AAS measurement of tin has been investigated. The effect of pH on the extraction of mono-, di- and tributyltin and triphenyltin has been examined and the optimum conditions for the estimation of tributyltin assessed. The AAS performance is greatly improved by using furnace tubes pretreated by soaking in sodium tungstate solution. Such pretreatment is essential if low detection limits are to be attained. Extraction of the tributyltin from aqueous media resulted in a marked signal enhancement (irrespective of the type of furnace tube), which varied according to the nature of the aqueous solution. The enhancement is believed to result from water in the toluene extract activating the tube surface. Methods for the estimation of tributyltin in waters, appropriate for screening samples as part of routine monitoring programmes, are described. With a 1-litre sample, a limit of detection of approximately 4 ng/l. was attained for tin. The relative standard deviation of six replicate analyses of sea-water containing 170 ng/l. tin (present as tributyltin) was 1.5%.