Page 243 - Soil and water contamination, 2nd edition
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230                                                  Soil and Water Contamination
                                               2    . 0  90
                        th
                       4  iteration:  L     . 3  99  tanh     . 3  99 tanh(  . 1  554 )    . 3  99  . 0  914    . 3  65
                                   w
                                                  . 3  64
                                               2    . 0  90
                        th
                       5  iteration:  L     . 3  99  tanh     . 3  99 tanh(  . 1  549 )    . 3  99  . 0  914    . 3  65 m
                                   w
                                                  . 3  65
                                th
                       After the 5  iteration with  L  = 3.65 m, we have achieved convergence. Now, the
                                               w
                       amplitude of the wave motion at the lake bottom A  is calculated using Equation (12.10):
                                                              b
                                   . 0  224         . 0  224   . 0  224
                       A                                                . 0  050  m
                        b
                           2  sinh( 2  . 0  90  . 3 /  65 )  2  sinh(  . 1  549 )  2  . 2  247
                       The maximum water velocity at the lake bottom due to wave motion is then estimated
                       using Equation (12.3):
                                  . 0  224    1                  1
                       u  , b  max                        . 0  440     . 0  196 m s -1
                                 . 1  60  sinh  2 (  . 0  90  . 3 /  65 )  . 2  247
                       The friction coefficient is calculated using Equation (12.9) (note that K  = D90 = 70 μm
                                                                              n
                             -6
                       = 70·10  m):
                                        . 0  75
                                     6
                                70  10                . 0  75       3         3
                       C     4 . 0           4 . 0  . 0  0014     4 . 0  2 . 7  10     9 . 2  10
                         f
                                  . 0  050
                       Finally, calculate the bottom shear stress τ  using Equation (12.2):

                                                       b
                                             2
                            1000  9 . 2  10  3  . 0  196    . 0  111 N m -2
                        b
                       As the bottom shear stress  is slightly larger than the critical shear stress  for erosion  and
                                               -2
                       deposition, which is 0.10 N m , some of the bottom sediment  is resuspended  into the
                       water column.
                    12.4  SEDIMENT DEPOSITION
                    If the shear stress  at the soil–water interface is less then the critical value τ , the sediment
                                                                               b,d
                    in the water column settles and the net sediment flux  J   (see Equation 12.1) becomes a
                                                                  s
                    deposition flux, which can be formulated as:
                    J     w  C                                                        (12.11)
                     d     s  b
                                                -2
                                                  -1
                    where J  = sedimentation  flux [M L  T ], α = a delay factor [-], w  = the maximum settling
                          d                                             s
                                                              -1
                    velocity of the suspended sediment  when τ  = 0 [L T ], and C  = the suspended sediment
                                                      b               b
                                                                 -3
                    concentration just above the soil–water interface [M L ]. If the variation in suspended
                    sediment concentration over the vertical profile is small (this holds for turbulent streams),
                    the vertically averaged concentration (C) can be adopted for C . Note that in this case the
                                                                      b
                    removal of sediment from the water column follows  first-order kinetics (combine Equation
                    12.11 (C  = C) with the transport Equation 12.1). If only sedimentation is considered, then
                           b
                    the differential equation becomes:
                     C     J s    w s
                                    C                                                 (12.12)
                      t    H     H





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