Copper bioavailability and amelioration of toxicity in Macquarie Harbour, Tasmania, Australia

The 100-year operation of the Mount Lyell Mining and Railway Company Limited's copper mine in Queenstown, Australia, has resulted in the deposition of over 100 million cubic metres of mine tailings, smelter slag and topsoil into the King River and Macquarie Harbour. A preliminary risk assessment, together with chemical mea- surements of dissolved copper, ASV-labile copper, copper complexing capacity and resin-adsorbed copper, sug- gested that copper in mid-salinity harbour waters was potentially bioavailable. However, toxicity tests based on inhibition of microalgal (Nitzschia closterium) growth showed that copper in these waters was not toxic, even though labile copper concentrations (6-24 mg L -1 ) exceeded the concentration of lowest observable effect for algae of 5 mg L -1 . Measurements of intracellular and membrane-bound copper confirmed that cell division was not affected because copper was not taken up intracellularly. Amelioration of copper toxicity was due to binding of dis- solved organic matter and/or other metals at the cell membrane, preventing copper binding and uptake. An under- standing of the mechanism of copper toxicity and its amelioration is vital to assessing various clean-up options for the harbour.

[1]  J. Rijstenbil,et al.  Copper and zinc in estuarine water: Chemical speciation in relation to bioavailability to the marine planktonic diatom Ditylum Brightwellii , 1992 .

[2]  E. Grill,et al.  An ion-exchange procedure for quantifying biologically active copper in sea water , 1986 .

[3]  Duane A. Benoit,et al.  The effects of water chemistry on the toxicity of copper to fathead minnows , 1996 .

[4]  G.R.W. Denton,et al.  The Influence of Temperature and Salinity Upon the Acute Toxicity of Heavy Metals to the Banana Prawn (Penaeus merguiensis de Man) , 1982 .

[5]  T. Florence,et al.  A novel adsorbent for the determination of the toxic fraction of copper in natural waters , 1987 .

[6]  J. Meador THE INTERACTION OF PH, DISSOLVED ORGANIC CARBON, AND TOTAL COPPER IN THE DETERMINATION OF IONIC COPPER AND TOXICITY , 1991 .

[7]  J. Allison,et al.  MINTEQA2/PRODEFA2, a geochemical assessment model for environmental systems: Version 3. 0 user's manual , 1991 .

[8]  P. Nichols,et al.  Chemistry of trace elements, humic substances and sedimentary organic matter in Macquarie Harbour, Tasmania , 1991 .

[9]  J. Giesy,et al.  Copper speciation in soft, acid, humic waters: Effects on copper bioaccumulation by and toxicity to simocephalus serrulatus (Daphnidae) , 1983 .

[10]  J. Stauber,et al.  Interactions of copper and manganese: A mechanism by which manganese alleviates copper toxicity to the marine diatom, Nitzschia closterium (Ehrenberg) W. Smith , 1985 .

[11]  M. Twiss,et al.  Accumulation of natural organic matter on the surfaces of living cells: implications for the interaction of toxic solutes with aquatic biota , 1997 .

[12]  J. Stauber,et al.  The influence of iron on copper toxicity to the marine diatom, Nitzschia closterium (ehrenberg) W. Smith , 1985 .

[13]  D. Turner,et al.  Metal speciation and bioavailability in aquatic systems , 1995 .

[14]  P. Campbell,et al.  Decreased toxicity of Al to Juvenile Atlantic salmon (Salmo salar) in acidic soft water containing natural organic matter: A test of the free‐ion model , 1997 .

[15]  M. Gardner,et al.  An evaluation of voltammetric titration procedures for the determination of trace metal complexation in natural waters by use of computers simulation , 1988 .

[16]  J. Stauber,et al.  Mechanism of toxicity of ionic copper and copper complexes to algae , 1987 .

[17]  M. Twiss,et al.  Influences of Natural Dissolved Organic Matter on the Interaction of Aluminum with the MicroalgaChlorella: A Test of the Free-Ion Model of Trace Metal Toxicity , 1996 .

[18]  M. Ahsanullah,et al.  Toxicity assessment of waters from Macquarie Harbour, western Tasmania, using algae, invertebrates and fish , 1996 .