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

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GROUNDWATER FLUX<br />

An estimate <strong>of</strong> mass loading from rainfall run-<strong>of</strong>f may be calculated for the unconfined<br />

aquifer using a <strong>surface</strong> area <strong>of</strong> 1.063 x 10 8 m 2 and an average recharge from rainfall <strong>of</strong><br />

0.00036 md -1 . This does not include the recharge <strong>of</strong> 0.00033 md -1 estimated to come from<br />

other sources such as leaking <strong>water</strong> mains (Section 6.4.2.2). <strong>The</strong> estimate <strong>of</strong> pollutant mass<br />

flux from industry is based on a land use <strong>of</strong> 20% in the industrial/commercial category<br />

(Thomas, 2001). <strong>The</strong> estimated <strong>ground<strong>water</strong></strong> mass flux to the river for Cl was 1,271 tonnes<br />

per year -1 (Table 8.1) which may be compared with an atmospheric loading (residential ro<strong>of</strong><br />

top run-<strong>of</strong>f) to the aquifer <strong>of</strong> 71 ty -1 . A combined estimate <strong>of</strong> Cl mass flux for <strong>urban</strong> and<br />

industrial recharge to the aquifer was ~ 1,700 ty -1 . In addition to this an average amount <strong>of</strong><br />

8,781 ty -1 <strong>of</strong> NaCl ( 5,326 ty -1 as Cl) is applied in the Birmingham area during winter road<br />

salting (Jenkins, 1995). <strong>The</strong> estimated <strong>ground<strong>water</strong></strong> mass flux to the river for SO4 was 1,904<br />

ty -1 and for NO3 515 ty -1 compared with an atmospheric loading to the aquifer <strong>of</strong> 85 and 87 ty -<br />

1 respectively. <strong>The</strong> combined estimate for <strong>urban</strong> and industrial recharge to the aquifer for NO3<br />

was 219 ty -1 . This compares with estimates by Ford (1994) for the atmospheric fallout on the<br />

Birmingham area for SO4 <strong>of</strong> 275 ty -1 and for NO3 160 ty -1 .<strong>The</strong> fluxes to the river are<br />

considerably higher than the contributions from run-<strong>of</strong>f suggesting considerable input from<br />

other sources such as leaking sewers and <strong>water</strong> mains, contaminated land and mineral<br />

dissolution.<br />

<strong>The</strong> mass flux <strong>of</strong> the chlorinated solvents to the river is limited despite the large mass<br />

estimated to be resident in the aquifer (Rivett, 1989). For TCE a total mass flux <strong>of</strong> 95 kgy -1<br />

equates to 65 litres, ~1/3 <strong>of</strong> a drum, and for TCA 82 kgy -1 equates to 61 litres, ~1/3 drum, and<br />

PCE 2 kgy -1 equates to 1.2 litres, ~ 1 lemonade bottle. Calculations from the sampling <strong>of</strong><br />

abstraction wells indicated loss <strong>of</strong> TCE from the aquifer <strong>of</strong> 1,500 kgy -1 (1987) and 160 kgy -<br />

1 (1990) (Taylor et al.,1999). <strong>The</strong> lower value in 1990 was the result <strong>of</strong> the more restricted<br />

324

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