Page 119 - Fundamentals of Water Treatment Unit Processes : Physical, Chemical, and Biological
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74                             Fundamentals of Water Treatment Unit Processes: Physical, Chemical, and Biological



                   ^ m ¼ 0.2 h  1                                     tipped in favor of advection; convection seemed to
                  K m ¼ 6mg=L                                         be more associated with heat.]
                  Y ¼ 0.31 kg cells synthesized=kg substrate degraded  CSTR: (1) A common acronym for ‘‘completely stirred tank
                                              3
                           2
                    ¼ 31.4 m media surface area=m bulk volume         reactor.’’ (2) A ‘‘complete-mix’’ reactor is also a

                                  2
                  X ¼ 1.0 kg cells=m media surface area               CSTR.
                  porosity, P ¼ 0.40.                          Detention time: The residence time of a fluid in a volume of
                Let design variables be:                              some kind in which the hypothetical ‘‘plug’’ flow
                  depth of the filter, D ¼ 2.0 m                       occurs.
                                        2          3           Diffusion: Molecular transport by random motion of mol-
                  HLR ¼ Q=A ¼ 5.0 gpm=ft ¼ 3.395 10  m=s and
                  recall,   v ¼ HLR=P                                 ecules. Fick’s first law describes the transport rate.
                                                               Dispersion: The ‘‘spread’’ of a substance in flow. In porous
                Operating conditions are:
                                                                      media flow and in turbulent flow, the mechanism is a
                  S 0 ¼ 200 mg BOD=L, and
                                                                      statistical variation of velocity about the mean
                  S(2.0 m) ¼ 30 mg BOD=L
                                                                      advective velocity. In flow through basins, ‘‘short
                [Note that S(2.0) is a nomenclature adopted here that  circuiting’’ causes a portion of the flow to reach the
                means the effluent concentration is at 2.0 m depth in the  end of the basin sooner than the ‘‘plug-flow’’ vel-
                filter.]                                               ocity. At the same time, a portion of the flow will
                (a) Assume steady state conditions and determine a    exchange mass with dead zones of the basin which
                    ‘‘calibration’’ coefficient, K for the model. The  will cause a long tail on a dispersion curve. A dye
                    value for K is determined by trial and error and is  test or a salt test is used commonly as a means to
                    the value selected when the calculated S(2.0) equals  evaluate dispersion. Intuitively, if 100 molecules are
                    30 mg=L (the assumed actual effluent concentration).  transported to a point in front of or behind the mean
                (b) Assume a flow variation over a 24 h period (use    flow due to a statistical mechanism the same statis-
                    sinusoidal variation if you wish), and determine the  tics are applicable to those 100 molecules in the new
                    S(2.0 m) versus t.                                position. In the next ‘‘step’’ some of the 100 will be
             4.9 Global Atmosphere as a Reactor                       behind the average and some will be ahead.
                Suppose that a gas (any gas) is emitted by various surface  Fick’s first law: The mathematical relation in which flux
                sources. Let the gas be nonreactive in the atmosphere, but  density of a given substance is proportional to the
                will dissolve in water (in accordance with Henry’s law).  concentration gradient.
                If the atmosphere has a uniform concentration of the gas  Finite difference equation: The expression of a differential
                        3
                at x kg=m , estimate the number of years for the atmos-  equation in terms of infinitesimal differences, that is,
                phere to purge itself to a concentration 0.05 fraction of  DC, Dt, DZ,
                the original concentration. [Hint: The rate of contact with  Fit: The relationship between a ‘‘form’’ and its ‘‘context.’’
                water surfaces is probably rate limiting.] As a second  Flow net: Analysis method for ‘‘irrotational flow’’ and is
                aspect of the problem, consider the complexity of the  applicable to turbulent flow where viscosity is not a
                movement of air masses and the assumption of homo-    major influence and to ground water flow for cases in
                geneity (i.e., complete mix is only a first approximation).  which R   1 (which is usual). The flow net is
            4.10 Global Atmosphere as a Reactor with Carbon           comprised of streamlines and potential lines (or sur-
                Dioxide                                               faces) and is unique for a particular set of ‘‘boundary
                Suppose that the gas in the previous problem is carbon  conditions.’’
                dioxide. Develop a rough global model of a carbon  Flux: Rate of transport of mass (or heat) across a boundary
                balance.                                              (kg=s)
                                                               Flux density: Rate of transport of mass (or heat) across a
                                                                                                2
                                                                      boundary per unit area (kg=s=m )
            GLOSSARY
                                                               Form: The kind of design synthesized that may or may not
            Advection: The transport of molecules or mass by a fluid flow  ‘‘fit’’ the ‘‘context’’ at hand.
                   with such flow responding to a pressure gradient.  Gaussian: The probability curve that is ‘‘normal’’ in shape,
            Appropriate fit: A ‘‘form’’ that relates to a given ‘‘context’’  that is, bell-shaped; it may be the outcome of meas-
                   in an appropriate manner.                          urements of a given random variable.
            Biofilm: Bacteria film that adheres to a surface.    Homogeneous reactor volume: The part of a reactor in
            Contactor: A reactor in which reaction occurs.            which the contaminant of interest, for example, A
            Context: The situation or setting that comprises the basis for  has a constant concentration from point to point
                   a design.                                          within the volume. It is important to designate
            Convection: The movement of a fluid under a pressure gra-  because the materials balance relation is valid
                   dient (see advection). [In this text, convection was  only for a homogeneous volume. A ‘‘complete-
                   used initially and then was replaced with ‘‘advec-  mix’’ activated sludge reactor could approach this
                   tion’’; in splitting hairs to decide, the scales were  homogeneity. A plug-flow reactor does not, by
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