Page 119 - Materials Chemistry, Second Edition
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102       Practical Design Calculations for Groundwater and Soil Remediation



               (d)  Use Equation (3.33) to find the retardation factor:
                           b ρ  K p  (1.6)(1.275)
                    R =+       =+            =  6.10 forbenzene
                                1
                       1
                            φ          0.4
                           b ρ  K p  (1.6)(0.32)
                    R =+       =+            =  2.28 for 1,2-DCA
                       1
                                 1
                            φ          0.4
                           b ρ  K p  (1.6)(717)
                    R =+       =+           =  2,869 forpyrene
                                 1
                       1
                            φ         0.4
              Discussion:
              Pyrene is very hydrophobic with a large K  value, and its retardation
                                                    p
                factor is much larger than those of benzene and 1,2-DCA.


           3.5.4   Migration of Dissolved Plume

           The retardation factor relates the plume migration velocity to the ground-
           water seepage velocity as


                                    R =  V s  or  V p =  V s              (3.34)
                                       V p          R

           where V  is the groundwater seepage velocity and V  is the velocity of the dis-
                   s
                                                        p
           solved plume. When the value of R is equal to unity (for inert compounds),
           the compound will move at the same speed as the groundwater flow without
           any “retardation.” When R = 2, for example, the COC will move at half of the
           groundwater flow velocity.

           Example 3.20:   Migration Speed of Dissolved Plume in Groundwater

           The aquifer underneath a site is impacted by several organic compounds
           including benzene, 1,2-dichloroethane (DCA), and pyrene. A recent ground-
           water monitoring in September 2013 indicated that 1,2-DCA and benzene
           have traveled 250 m and 20 m downgradient, respectively, while no pyrene
           compounds were detected in the downgradient wells.
             Estimate the time when the leachates first entered the aquifer. The follow-
           ing data were obtained from the site assessment:

              •  Effective aquifer porosity = 0.40
              •  Aquifer hydraulic conductivity = 30 m/day
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