Page 196 - Soil and water contamination, 2nd edition
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Systems and models                                                    183

                   lake (one store ) with a drain that discharges excess water as function of the lake volume: the
                   water discharge (flux) is proportional to the water volume in the lake:

                    Q     k  V                                                         (10.1)
                     out
                                                     3
                                                                            -1
                                                        -1
                   where  Q   = discharge from the lake [L  T ],  k  =  rate constant [T ], and  V = water
                          out
                                     3
                   volume in the lake [L ]. Note that in this feedback  mechanism, the rate of change of the
                   store , determined by Q , is controlled by the state  of the store itself (V). Given a constant
                                      out
                   inflow into the lake, the reservoir system evolves to a condition of steady state  or dynamic
                   equilibrium , which means that the inputs  and outputs  are in balance, so that the state of the
                   system (water level) does not change. If an additional amount of water is instantaneously
                   added to the reservoir, the system tends to return to a state with a constant inflow and
                   outflow. By definition, the response time  of the system is defined as 1/k, which corresponds
                   to the time needed to reduce the difference between the actual value and the steady state
                   value by 63 percent.
                      In contrast, a  positive feedback  mechanism exacerbates some initial change from the

                   steady state , leading to a ‘blow-up’ condition. For example, if in the same reservoir a crack
                   or hole occurs in the dam, the eroding power of the outflowing water enlarges the gap, so
                   the water discharge through the hole increases rapidly. It is only a matter of time before the
                   whole dam collapses. Eventually, when the reservoir is nearly empty the negative feedback
                   mechanism takes over, so a new steady state  condition is reached for which the outflow
                   rate equals the inflow. The fact that the Earth has had water and an atmosphere for a very
                   long time suggests that our Earth system is dominated by negative feedback  mechanisms.
                   Nevertheless, positive feedback mechanisms may be very important, since they have the
                   potential to bring about dramatic changes.
                      If we consider the hydrological cycle  at the global scale , we may assume a closed system ,
                   i.e. a system that only exchanges energy with its surroundings; water does not enter or leave
                   the Earth system. The global hydrological cycle (see Figure 3.1) is driven by solar energy that
                   powers the evaporation  and translocation by wind. The evaporated water is returned to the
                   Earth’s surface by precipitation, some of which falls on land. In most areas, more water enters
                   the land via precipitation than leaves it by evaporation. If the water is not temporarily stored
                   on the soil surface in the form of snow and ice, part of the excess water is discharged directly
                   into streams and lakes via overland flow . The rest infiltrates the soil and percolates to the
                   groundwater, which also ultimately discharges into surface waters. Rivers are the main routes
                   transporting water from land to sea.
                      Although the global hydrological cycle  may be looked upon as a closed system , the water
                   cycle is often investigated at the smaller scale  of a local groundwater system or single drainage
                   basin. The drainage basin as a hydrological unit can be envisaged as an open system receiving

                   mass (in the form of water) and energy from the weather over the basin and losing them
                   by evaporation  and water discharge through the basin outlet. Therefore, the drainage basin
                   provides a useful framework for studying the phenomena related to the transport and fate of
                   contaminants.
                      Groundwater transports chemicals that are produced by internal weathering  and
                   dissolution  reactions or delivered to the soil surface via atmospheric deposition  (e.g. acid
                   rain ) or anthropogenic immissions (e.g. application of manure , fertiliser, and pesticides  in
                   agriculture). River water transports materials produced by erosion  processes on hill slopes
                   and river banks and by internal production of organic matter , as well as dissolved ions
                   originating from natural or anthropogenic sources. The fine fraction of sediments, which
                   consists mainly of clay minerals  and organic matter, is particularly able to bind various
                   chemicals; this fraction is therefore considered to be a very important vector for transporting
                   nutrients and a large variety of contaminants, including heavy metals  and organic pollutants.










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