Iron-ore tailings filled in a soil column were leached daily with deionized water at various pH 5, 6, 7, 8 and 9) for 50 days. There was a continuous decline in conductivity of all leachates during the study. The final conductivity values of all leachates were significantly lower (P < 0.001) than the initial values. Final pH values were all in the range 8.2-8.3. The lower pH treatments resulted in high leachate concentrations of magnesium, manganese, iron, lead, and zinc. Sodium, potassium and calcium concentrations were similar for all treatments.
Allen, S.E., Grimshaw, H.H., Parkinson, J.A. & Quarmby, C. (1974), Chemical Analysis of Ecological Materials, Blackwell, Oxford.
2.
Davis, S.C. (1961), Mineralogy of the Ma On Shan Iron Mine, Hong Kong , Economics and Geology, 56(3), 592—602.
3.
Down, C.C. & Stocks, J. (1977), Environmental problems of tailings disposal, Mining Magazine, 135(7), 25-33.
4.
Klei, H.E., Sundstrom, D. & Sweency, C. (1981), Metal leaching from sewage slude ash, BioCycle, May/June, 41-43.
5.
Wong, M.H. & Lai, K.K. (1982), Application of activated sludge for improving iron-ore tailings, Reclamation and Revegetation Research, 1, 83-97.
6.
Wong, M.H. & Lai, M.W. (1977), An ecological survey of the heavy metal contamination of the edible clam Paphia spp. on the iron-ore tailings of Tolo Harbour, Hong Kong, Hydrobiologia, 56(3), 265-272.
7.
Wong, M.H. & Tam, F.Y. (1977), Soil and vegetation contamination by iron-ore tailings, Environmental Pollution, 14, 241-254.
8.
Wong, M.H., Chan, K.C. & Choy, C.K. (1978), The effect of the iron-ore tailings on the coastal environment of Tolo Harbour, Hong Kong, Environmental Research , 15, 342-356.
9.
Wong, M.H., Chan, K.Y., Kwan, S.H. & Mo, C.F. (1979), Metal contents of the two marine algae found on the iron-ore tailings, Marine PollutionBulletin, 10(2), 56-59.