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                Geotechnical News • December 2012
              
            
            
              
                www.geotechnicalnews.com
              
            
            
              for Hydrogeological Site Assessment
            
            
              (HSA) [3] for technical assistance of
            
            
              the Qualified Person (QP), P.Eng. or
            
            
              P.Geo.
            
            
              The PTTW’s objective is to imple-
            
            
              ment the MOE’s water management
            
            
              policy for fair sharing, conservation
            
            
              and sustainable use of Ontario water
            
            
              resources without water allocation but
            
            
              preventing unacceptable interferences.
            
            
              The PTTW hydrogeological study and
            
            
              application are based on six principles
            
            
              listed on Table 1. Included in these
            
            
              six principles is incorporation of the
            
            
              precautionary principles summarized
            
            
              on Table 2.
            
            
              
                Ground water flow principles
              
            
            
              
                and equations
              
            
            
              The water in soils (porous media)
            
            
              exists in three forms of adsorbed
            
            
              (hydroscopic or pellicular), capil-
            
            
              lary (or matric) and gravitational (or
            
            
              free). The free or gravitational water
            
            
              in soils is usually referred to as the
            
            
              ground water. The ground water bod-
            
            
              ies can exist in perched condition in
            
            
              sand seams/lenses within silty/clayey
            
            
              soils and in regional condition within
            
            
              aquifers (in sand and gravel, confined
            
            
              or unconfined) that may be separated
            
            
              by aquitards (clayey soils).
            
            
              The ground water flow varies with
            
            
              space, time, boundary conditions,
            
            
              medium (soil or rock) properties and
            
            
              behaviour as well as the fluid (perme-
            
            
              ant) temperature, density and viscos-
            
            
              ity. The ground water flow types
            
            
              in relation to time can be steady or
            
            
              transient; in relation to space uniform
            
            
              or varied and in relation to the driving
            
            
              force laminar or turbulent. The driving
            
            
              force or free energy for ground water
            
            
              flow can be expressed in terms of
            
            
              “potential” (Ф: free energy per unit
            
            
              mass of fluid) or “total head” (h: free
            
            
              energy per unit weight of fluid), or
            
            
              “pressure” (p = free energy per unit
            
            
              volume of fluid).
            
            
              The laminar ground water flow in
            
            
              saturated soils is usually analyzed by
            
            
              Darcy’s law which is based on linear
            
            
              relationship between the rate of flow
            
            
              and the driving forces. It is important
            
            
              to note that Darcy’s law is valid as
            
            
              long as the Reynold’s number based
            
            
              on an average grain size does not
            
            
              exceed some value between 1 and 10
            
            
              which is indicative of linear laminar
            
            
              flow. The ground water flow in frac-
            
            
              tured rock mass is usually nonlinear.
            
            
              The Reynold’s number for flow
            
            
              through porous media is:
            
            
              Where
            
            
              r
            
            
              and
            
            
              m
            
            
              are the fluid density
            
            
              and viscosity,
            
            
              
                v
              
            
            
              is kinematic viscos-
            
            
              ity, v is specific discharge, and d is a
            
            
              representative length dimension for
            
            
              the porous medium, variously taken
            
            
              as a mean pore dimension, a mean
            
            
              grain diameter, or some function of the
            
            
              square foot of the permeability K.
            
            
              The most commonly encountered Dar-
            
            
              cian ground water flow equation is
            
            
              Q = 
            
            
              KiA 
            
            
              (2)
            
            
              Where Q is the flow rate L
            
            
              3
            
            
              /T); i is the
            
            
              hydraulic gradient (dimensionless); A
            
            
              is the total cross-sectional area of flow
            
            
              (L
            
            
              2
            
            
              ); and K is the constant of propor-
            
            
              tionality (L/T), which is termed the
            
            
              hydraulic conductivity; or
            
            
              q  =  
            
            
              Ki 
            
            
              (3)
            
            
              v  =  
            
            
              Ki/n 
            
            
              (4)
            
            
              Where q is the specific discharge or
            
            
              flux and v is the average linear veloc-
            
            
              ity of the flow in a porous medium
            
            
              with a volumetric porosity of n.
            
            
              The “specific yield” (Y
            
            
              s
            
            
              ) of a porous
            
            
              medium is the drainable water and the
            
            
              “specific retention” (R
            
            
              s
            
            
              ) is the undrain-
            
            
              able water. The porosity of a saturated
            
            
              soil n, which is a function of void ratio
            
            
              
                Table 1. Permit-To-Take Water Principles
              
            
            
              1
            
            
              Ecological approach
            
            
              2
            
            
              Prevention and resolution of unacceptable interferences
            
            
              3
            
            
              Adaptive management for better response to the evolving
            
            
              environmental conditions
            
            
              4
            
            
              Addressing cumulative impacts of water takings
            
            
              5
            
            
              Incorporation of precautionary principles (Table 2); and
            
            
              6
            
            
              Promotion of the public and local agency involvement
            
            
              
                Table 2. Precautionary Principles
              
            
            
              1
            
            
              Demonstrate that all aspects of the project have been examined and planned
            
            
              in a careful and precautionary manner in order to ensure that they do not
            
            
              cause serious or irreversible damage to the environment and/or the health of
            
            
              current or future human generations
            
            
              2
            
            
              Outline and justify the assumptions made about the effects of all aspects of
            
            
              the project and the approaches to minimize these effects
            
            
              3
            
            
              Evaluate and compare alternative means of carrying out the Project in
            
            
              light of risk avoidance, adaptive management capacity and preparation for
            
            
              surprise
            
            
              4
            
            
              Demonstrate that in designing and operating the project, priority has been
            
            
              and will be given to strategies that avoid the creation of adverse effects
            
            
              5
            
            
              Provide that contingency plans explicitly address worst-case scenarios and
            
            
              include risk assessments and evaluations of the degree of uncertainty
            
            
              6
            
            
              Identify and propose follow-up and monitoring activities, particularly in
            
            
              areas where scientific uncertainty exists in the prediction of effects; and
            
            
              7
            
            
              Present public views on the acceptability of all of the above
            
            
              Re
            
            
              =
            
            
              
                pvd
              
            
            
              
                u or vd
              
            
            
              
                v
              
            
            
              (1)