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The impact of urban groundwater upon surface water - eTheses ...

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CONCLUSIONS<br />

<strong>surface</strong>-<strong>water</strong> quality by diluting sewage effluent and industrial pipe discharges. <strong>The</strong> <strong>impact</strong><br />

<strong>of</strong> the <strong>ground<strong>water</strong></strong> on the river was found to be scale dependent. High concentration<br />

contaminant plumes were observed within the riverbed which may have a localised <strong>impact</strong> on<br />

the ecology, but the large dilution within the river limited the <strong>impact</strong> on the overall <strong>surface</strong>-<br />

<strong>water</strong> quality. <strong>The</strong>re is some evidence that natural attenuation within the aquifer and/or the<br />

riverbed limits the quantity <strong>of</strong> organic and inorganic contaminants entering the river by the<br />

<strong>ground<strong>water</strong></strong> pathway.<br />

Objective 2. To investigate the physical and chemical processes controlling contaminant flux<br />

across the <strong>ground<strong>water</strong></strong>/<strong>surface</strong> <strong>water</strong> interface.<br />

Surface <strong>water</strong> was observed to penetrate the riverbed and mix with the <strong>ground<strong>water</strong></strong> in the<br />

hyporheic zone to depths <strong>of</strong> up to 60 cm . Rapid changes in pH, Eh and dissolved oxygen<br />

content occurred across the <strong>ground<strong>water</strong></strong>/<strong>surface</strong> <strong>water</strong> interface leading to precipitation or<br />

sorption <strong>of</strong> some inorganic contaminants, probably to iron oxyhydroxide grain coatings.<br />

Zonation <strong>of</strong> some processes occurred within the interface over a limited (tens <strong>of</strong> centimetres)<br />

vertical extent. Dissolved oxygen levels were generally lower in the riverbed than the<br />

<strong>ground<strong>water</strong></strong> or <strong>surface</strong> <strong>water</strong>, probably due to microbial activity, and there was evidence <strong>of</strong><br />

nitrate and sulphate reduction in some localities from both the <strong>ground<strong>water</strong></strong> and the <strong>surface</strong><br />

<strong>water</strong>. <strong>The</strong>re was no conclusive pro<strong>of</strong> <strong>of</strong> the biodegradation <strong>of</strong> organic contaminants such as<br />

chlorinated solvents within the riverbed, but the presence <strong>of</strong> daughter compounds indicated<br />

that biodegradation <strong>of</strong> PCE/TCE had occurred at least somewhere in the <strong>ground<strong>water</strong></strong> system.<br />

Natural attenuation within the riverbed does not occur in all situations and may be limited by<br />

rapid rates <strong>of</strong> <strong>ground<strong>water</strong></strong> discharge through the more permeable bed sediments.<br />

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