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

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GROUNDWATER FLUX<br />

<strong>ground<strong>water</strong></strong> is a significant contributor. <strong>The</strong> values for Zn and Ni are in a similar range to<br />

those derived from the baseflow and riverbed piezometer data (Table 8.1) but the mass flux <strong>of</strong><br />

Cr is considerably higher than the 0.03-0.1 kgd -1 calculated from the riverbed data. This<br />

suggests either a significant <strong>ground<strong>water</strong></strong> source not detected in the riverbed sampling or that<br />

Cr enters as a <strong>surface</strong> <strong>water</strong> or pipe end discharge either in dissolved or particulate form.<br />

As discussed in the previous chapter, the possibility exists that acidic <strong>ground<strong>water</strong></strong> discharge<br />

may mobilise contaminants from within the metal rich riverbed sediments. <strong>The</strong> mass loading<br />

appears to be low enough not to have a significant adverse <strong>impact</strong> on the overall <strong>surface</strong> <strong>water</strong><br />

quality under current conditions. For example, the maximum mass flux for zinc <strong>of</strong> 5 kgd -1 , if<br />

added to a typical dry weather flow <strong>of</strong> 166 Mld -1 at Perry Barr would produce a rise in<br />

concentration <strong>of</strong> only 0.03 mgl -1 . <strong>The</strong> study <strong>of</strong> mass flux has so far focussed on a general<br />

contaminant contribution across the study reach. It would be beneficial to consider the<br />

possible contributions from some <strong>of</strong> the individual contaminant plumes identified and to<br />

assess whether any remediation is worth attempting on an individual plume basis.<br />

8.4 Mass flux from individual contaminant plumes.<br />

<strong>The</strong> calculation <strong>of</strong> mass flux from a discharging <strong>ground<strong>water</strong></strong> plume requires specific<br />

information on:<br />

• the spatial extent <strong>of</strong> the plume discharge area;<br />

• the distribution <strong>of</strong> contaminant concentration values within the plume;<br />

• the spatial distribution <strong>of</strong> <strong>ground<strong>water</strong></strong> discharge rates to the <strong>surface</strong> <strong>water</strong> mixing zone<br />

across the plume;<br />

• the <strong>impact</strong> <strong>of</strong> retardation processes such as sorption on the mass flux;<br />

335

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