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                                                         Groundwater quality and contaminant hydrogeology  219





































                   Fig. 6.12 Behaviour of organic contaminants in groundwater. The chlorinated solvent contaminant shown in (a) has a density greater than
                   water (a dense non-aqueous phase liquid or DNAPL) and so sinks to the base of the aquifer. Here, transport of the DNAPL is controlled by
                   the slope of the base of the aquifer, while the dissolved aqueous phase moves in the direction of groundwater flow. The hydrocarbon
                   contaminant shown in (b) has a density less than water (a light non-aqueous phase liquid or LNAPL) and so floats on the water table. In this
                   case, transport of the LNAPL is controlled by the slope of the water table, while the dissolved aqueous phase moves in the direction of
                   groundwater flow.




                   similar manner to chlorinated solvents except, as  oil table will rest directly on the water table. In the
                   shown in the Fig. 6.12b, by reason of their density,  case of a thick zone of mobile LNAPL, the water
                   they float on the water table. The aromatic BTEX  table may be depressed by the weight of the LNAPL
                   compounds, benzene, toluene, ethylbenzene and  (Fig. 6.12b). The mobile LNAPL can migrate in the
                   xylene, are released in significant amounts by petro-  vadose zone, following the slope of the water table,
                   leum and can be transported by groundwater in the  while the dissolved components can disperse with the
                   aqueous phase. When spilled at the land surface, oil  advecting groundwater. The residual LNAPL phase
                   will migrate vertically in the vadose zone under the  in the vadose zone can partition into the vapour
                   influence of gravity and capillary forces, in an ana-  phase as well as the water phase, with the degree of
                   logous manner to water, until it reaches the top of   partitioning dependent on the relative volatility of
                   the capillary fringe. Much of the LNAPL will be left  the hydrocarbon and its solubility in water. In frac-
                   trapped in the vadose zone, but on reaching the   tured rocks, LNAPL will typically resist migration
                   capillary fringe the LNAPL will accumulate and   below the water table but where there is sufficient
                   an ‘oil table’ will develop. As the weight of LNAPL  weight, LNAPL can penetrate below the water table
                   increases, the capillary fringe will become thinner  to a limited extent when the pressure exerted by the
                   until mobile or ‘free’ product accumulates. Eventually,  LNAPL exceeds the displacement pressure of the
                   the capillary fringe may disappear completely and the  water in the fractures (Fig. 6.14b).
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