Page 424 - The Engineering Guide to LEED-New Construction Sustainable Construction for Engineers
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384    Cha pte r  T e n


             flow rate we are interested in determining. The direct rainfall flow into the BMP has
             been estimated in Eqs. (10.2.3) and (10.2.4) as the rainfall rate times the surface area
             of the BMP, and both the soil infiltration flow out (exfiltration) and the evaporation
             loss have been estimated by some sort of areal soil/subsurface infiltration rate and
             some sort of areal evaporation rate (see also Chap. 3 for evapotranspiration rates).
             The flow from the upslope areas can be estimated by Eq. (10.2.5), using the following
             variables:

             A        Land area upslope of BMP that drains into it (length squared, usually acres)
               up
             C      Average stormwater runoff coefficient of land surface upslope of BMP
               up
             This results in Eq. (10.2.6).

                 Q = C IA     upslope rational method runoff estimate contribution   (10.2.6)
                   up  up  up
                 By using these equations, many different situations can be modeled. For the first scenario,
             assume that it is raining at a constant rainfall rate I, that the only flows in are from upslope
             runoff and the rain, that there is negligible evaporation, and that there was no water initially
             stored in the BMP. The equations can be used to estimate the time it might take to start runoff
             out of the BMP (which is essentially the time to fill the storage volume during which the
             runoff out of the BMP is zero) if the flows in are greater than the infiltration rate.


                t = S      /[C IA + I(A  ) − F(A  )]  time to fill in fi rst scenario   (10.2.7)
                    fi ll  BMP  up  up  BMP     BMP
                 Now, assume that the storage volume S   has filled and the rain continues. The
                                                   BMP
             equations can also be used to estimate the steady-state runoff out of this BMP. In this
             case, the outlet for the flow out is above the storage volume height, a common condition
             in many cases. If there are multiple outlets, then the equations will need to be solved for
             each stage of storage within the BMP.

               Q   = C IA + I(A  ) − F(A  )  steady-state flow out in second scenario   (10.2.8)

                 out  up  up  BMP     BMP
                 The main way to model the stormwater mass balance around any BMP is to first
             make a simplified sketch of the system, labeling potential flows in and out and internal
             items such as storage as in Fig. 10.2.1. Then the initial conditions are used along with
             Eqs. (10.2.3) and (10.2.4) to model the system. For solutions, the equations are further
             simplified by allowing negligible flows to be neglected for the model and by using
             accepted models and parameters such as the rational method or soil infiltration rates to
             substitute for many of the variables.


             Pollutant Mass Balances
             The mass balance of pollutants around a BMP can be modeled by using the box model
             in the stormwater mass balance model and including the concentration of the pollutant
             in each flow, or within the BMP, using the following definitions:
             C        Average concentration of a pollutant in a BMP
               PBMP
             C        Average concentration of a pollutant infiltrating into ground
               PF
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