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Patterns in surface water                                             369

                   product  of calcium  carbonate  (calcite ) to be exceeded. As a result, the calcium carbonate
                   precipitates and starts settling out of the water column to the lake bed sediments .  This
                   process is illustrated by Figure 18.23, which shows the seasonal variation in the composition
                   of settling particles collected at 40 m depth in  Lake Zurich, Switzerland, from April to
                   October 1989 (Wieland et al., 2001).  Lake Zurich is a pre-alpine hard-water lake along the
                   northern rim of the  Alps. The lake is approximately 29 km long and 2.5 km wide and its
                   maximum depth is 137 m. Most of the suspended particulate matter  at the sampling location
                   is autochthonously produced, since the riverine input of allochthonous sediment  is effectively
                   trapped in the upstream sections of the lake. The particles are mainly comprised of calcium
                   carbonate, organic matter , iron  oxyhydroxides , and residual material, which contains silica
                   and aluminosilicates. In June, the calcium carbonate content of the suspended particles
                   increases dramatically from less than 30 percent to approximately 95 percent (Figure 18.23).
                   The precipitation of calcium carbonate also increases the total mass flux towards the lake
                   bottom by a factor of two to four. In September and October, the calcium carbonate content
                   gradually declines to the spring levels.



                   18.5  FURTHER READING ON CONTAMINANTS IN SURFACE WATER

                   •  Miller, J.R. and Orbock Miller, S.M., 2007,  Contaminated rivers: A geomorphological-
                      geochemical approach to site assessment and remediation, (Dordrecht NL: Springer).
                   •  Westrich, B. and Förstner, U. (Eds.), 2007, Sediment dynamics and pollutant mobility in
                      rivers: An interdisciplinary approach, (Berlin: Springer).
                   •  Plate, E.J. and Zehe, E. (Eds.), 2008, Hydrologie und Stoffdynamik kleiner Einzugsgebiete:
                      Prozesse und Modelle, (in German), (Stuttgart: Schweizerbart).


                   EXERCISES

                   1. Explain briefly:
                      a.   why the nitrate concentration in river water increases downstream of a wastewater
                         discharge;
                      b.  why the chloride concentration in streams decreases during a storm event;
                      c.  why relatively large amounts of groundwater are entrained during runoff events;
                      d.   why hysteresis occurs in the relationship between river discharge and suspended solids
                         concentrations during single flood events;
                      e.  why the phosphate concentration in rivers decreases during summer;
                      f.  why calcium carbonate precipitation occurs in hard water lakes during summer.

                   2.  Explain the role of hydrological events for the export of contaminants from catchments.

                   3.  Describe the timing of the peak or trough concentration relative to peak discharge for:
                      a.  positive, clockwise Q–C response;
                      b.  negative, clockwise Q–C response;
                      c.  positive, anti-clockwise Q–C response;
                      d.  negative, anti clockwise Q–C response.

                   4.  a.  Give a definition of concentration rating curves.
                      b.   Describe how the coefficient  a in Equation (18.1) differs between catchments on
                         intensively weathered rocks and catchments on bare unweathered rock.










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