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Fluvial metal transport near sources of acid mine-drainage: Relationships of soluble, suspended and deposited metal

Published online by Cambridge University Press:  05 July 2018

Stephen Boult*
Affiliation:
Department of Geography, Manchester University, M13 9PL, UK

Abstract

The Afon Goch (Anglesey, UK) is a short (12 km source to estuary) stream highly contaminated by acid mine drainage (AMD) throughout its length, due to past-mining at the head of the stream. Metal distribution is strongly controlled by the pH, which increases downstream particularly at confluences with two unpolluted tributaries. A pH increase causes precipitation of metals, primarily Fe as hydroxide, thus altering the transport of the metal load, potentially allowing storage of metal within the river as deposited material. However, further work suggests that the controls on whether metal can behave non-conservatively, and therefore the controls on metal distribution, are more complicated than being purely pH dependent. This is because much of the Fe load, even at the low pH at the head of the stream, is not soluble Fe3+ but colloidal Fe hydroxide. Consequently, coagulation is a requisite intermediate step between precipitation and potential for settling. It is possible that in reaches of the stream away from tributary confluences, the process of coagulation is the predominant influence on metal distribution. Furthermore, because much of the metal load in the water column is very fine, its deposition results in a sediment in which the metals can be intimately associated with a biofilm at the sediment/water interface. Such associations change both deposition and erosion characteristics of the sediment and have implications for subsequent diagenesis and mineral morphology.

Type
Geochemistry
Copyright
Copyright © The Mineralogical Society of Great Britain and Ireland 1996

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References

Austin, B. (1988) Methods in Aquatic Bacteriology. New York, John Wiley.Google Scholar
Bird, S.C. (1987) The effect of hydrological factors on trace metal contamination in the River Tawe South Wales. Environ. Pollut., 45, 87124.CrossRefGoogle Scholar
Boult, S. (1994) Transport of metals in a stream heavily contaminated by acid mine-drainage, (unpublished PhD thesis, Manchester University, Department of Geology).Google Scholar
Boult, S. and Curtis, C.D. (1994) The predictability of metal flux in a stream heavily polluted by acid mine drainage. In Trace Substances, Environment and Health(Cothern, C.R., ed.) 227-36. Science Reviews, Northwood UK.Google Scholar
Boult, S., Collins, D.N., White, K.N. and Curtis, C.D. (1994) Heavy metal transport in a stream heavily contaminated by acid mine-drainage The Afon Goch, Anglesey, UK. Env. Poll., 84, 279–84.CrossRefGoogle Scholar
Bradley, S.B. and Lewin, J. (1982) Transport of heavy metals on suspended solids under high flow conditions in a mineralized region of Wales. Environ. Pollut. Ser. B., 4, 257–67.CrossRefGoogle Scholar
Carpenter, R.H. and Hayes, W.B. (1980) Annual accretion of Fe-Mn oxides and certain associated metals in a stream environment. Chemical Geology, 29, 249–59.CrossRefGoogle Scholar
Chapman, B.M., Jones, D.R. and Jung, R.F. (1983) Processes controlling metal ion attenuation in acid mine drainage streams. Geochim. Cosmochim. Acta, 47, 1957-73.CrossRefGoogle Scholar
Church, M.A., MacLean, D.G. and Walcott, J.F. (1987) Bed load sampling and analysis. In Sediment Transport in Gravel Bed Rivers. (Thorne, C.R., Bathurst, J.C. and Hey, R.D., eds.) 4379. Wiley, Chichester.Google Scholar
Costerton, J.W., Marrie, T.J. and Cheng, K.J. (1985) Phenomena of bacterial adhesion. In Bacterial adhesion.(Savage, D.C. and Fletcher, M., eds.) 9. New York, Plenum Press.Google Scholar
de Boer, P.L. (1981) Mechanical effects of microorganisms on intertidal bedform migration. Sedimentology, 28, 129–32.CrossRefGoogle Scholar
Geesey, G.G (1982) Microbial exopolymers. ASM News, 48, 914.Google Scholar
Grimshaw, D.L., Lewin, J. and Fuge, R. (1976) Seasonal and short-term variations in the concentration and supply of dissolved zinc to aquatic environments. Environ. Pollut., 11, 17.CrossRefGoogle Scholar
Johnson, N. (1995) Effects on Biofilm Ecology of Trace Metal Contamination.Unpublished PhD thesis, Manchester University, Biological Sciences.Google Scholar
Kennedy, V.C., Zellweger, G.W. and Jones, B.F. (1974) Filter pore size effects on the analysis of Al, Fe, Mn and Ti in water. Water Resources Research, 10(4), 785-90.CrossRefGoogle Scholar
Kinniment, S.L. and Wimpenny, J.W.T. (1992) Measurement of the distribution of adenylate charge across a biofilm. Applied Environmental Microbiology, 58, 1629–33.CrossRefGoogle Scholar
Leenaers, H. (1989) The transport of heavy metals during flood events in the polluted River Geul (the Netherlands). Hydrological Processes, 3, 325–8.CrossRefGoogle Scholar
Lion, L.W., Shuler, M.L., Hsieh, K.M. and Ghiorse, W.C. (1988) Trace metal interactions with microbial biofilms. CRC Crit. Rev. Environ. Con., 17, 273306.CrossRefGoogle Scholar
MacAskie, L.E. and Dean, A.C.R. (1987) Use of immobilised biofilm for U and Pu removal. Enz. Microbiol. TechnoL, 9, 2.CrossRefGoogle Scholar
Marchesi, J.R., Russell, N.J., White, G.F. and House, W.A. (1991) Effects of surfactant adsorption and bio-degradability on the distribution of bacteria between sediments and water. Applied Environmental Microbiology, 57, 2507–13.CrossRefGoogle Scholar
McKnight, D.M. and Bencala, K.E. (1989) Reactive iron transport in an acidic mountain stream in Summit County, Colorado: a hydrologic perspective. Geochim. Cosmochim. Acta, 53, 2225–34.CrossRefGoogle Scholar
NRA (1993) Constructed Wetlands to Ameliorate Metal- rich Mine Waters.R & D notel02. National Rivers Authority, Bristol.Google Scholar
Parkman, R. (1994) Sedimentary Geochemistry of an Estuary Polluted by Acid Mine Drainage.Un published PhD thesis, Manchester University, Geology Department.Google Scholar
Patterson, D.M. (1989) Short-term changes in the erodibility of intertidal cohesive sediments related to the migratory behaviour of epipelic diatoms. Limnol. Oceanogr., 34(1), 223-34.CrossRefGoogle Scholar
Rouxhet, P.G. (1991) Interfacial interactions with micro-organisms. Biofouling, 4, 151–61.CrossRefGoogle Scholar
Schultze-Lam, S. Thompson, J.B. and Beveridge, T. (1993). Metal ion immobilization by bacterial surfaces in freshwater environments. Water Poll. Res. J. Canada, 28, 5181.CrossRefGoogle Scholar
Stumm, W. and Morgan, J. J. (1981) Aquatic Chemistry. Wiley, New York.Google Scholar
Uhlinger, D.J. and White, D.C. (1983) Relationship between physiological status and formation of EPS. Applied Environmental microbiology, 45, 6470.CrossRefGoogle Scholar
Walling, D.E. and Webb, B.W. (1986) Solutes in river systems. In Solute Processes.(S. Trudgill, ed.) John Wiley, Chichester, 175260.Google Scholar
Walling, D.E. and Webb, B.W. (1988) The reliability of rating curve estimates of suspended sedimennt yield: some further comments. International Association of Hydrological Sciences Publication, 174, 337–50.Google Scholar
Walton, K.C. and Johnson, D.B. (1992) Microbiological and chemical characteristics of an acidic stream draining a disused copper mine. Env. Poll., 76, 169—75.CrossRefGoogle Scholar
Yordanov, R. (1994) The Chironomid Population of Stream Sediments Heavily Contaminated by acid Mine Drainage. Unpublished MSc. thesis, Manchester University, Biological Sciences.Google Scholar