Page 351 - Soil and water contamination, 2nd edition
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338                                                  Soil and Water Contamination



























                      6642          100 km

                    Figure 18.1  General water circulation pattern in Lake Michigan,  USA.
                    affected by variations in wind speed and direction, the shape of the lake, inflowing streams,
                    variations in water density and, particularly in very large lakes, by the Coriolis force caused
                    by the rotation of the Earth (Hemond and Fechner-Levy, 2000). In the northern hemisphere,
                    the Coriolis force deflects surface currents to the right; in the southern hemisphere it deflects
                    them to the left. Figure 18.1 shows the general water circulation in Lake Michigan , USA, as
                    an example of a complex pattern of water movement in large lakes produced by variability of
                    winds, complex lake geometry, and the Coriolis force.
                       Because rivers  are long, shallow and narrow water bodies, it is commonly assumed that
                    dissolved and particulate matter  is uniformly mixed across the cross-sectional area of the
                    channel. Therefore, rivers are usually considered as one-dimensional objects. Only in river
                    studies at the local scale , for example in the case of transverse mixing of point discharges
                    within the river channel or dispersal of sediment  and associated contaminants over
                    floodplains , is the second or even third dimension  taken into consideration. Obviously, lakes
                    are much wider than rivers, so in most lake studies, the second lateral dimension is also taken
                    into account. Furthermore, in deep lakes, where vertical variation of the physico-chemical
                    properties of lake becomes important, the third (vertical) dimension is also considered.


                    18.2  SPATIAL VARIATION IN RIVER WATER COMPOSITION

                    18.2.1  Effects of diffuse source s

                    It has long been recognised that besides direct point source  discharges, contaminant
                    transport in and from catchments is controlled by climate,  geology, topography, and diffuse
                    anthropogenic inputs (see e.g. Dillon and Kirchner, 1975; Grobler and Silberbauer, 1985;
                    Qu  et al., 1993; De Caritat, 1996; McKee  et al., 2001). In pristine rivers , the transport
                    of substances is largely determined by the interrelated geochemical composition and
                    weathering  rate of the bedrock, which can be traced back to geology and climate factors,










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