CE 260 2013 - Lecture 21- Wastewater Treatment Problems

download CE 260 2013 - Lecture 21- Wastewater Treatment Problems

of 10

Transcript of CE 260 2013 - Lecture 21- Wastewater Treatment Problems

  • 7/30/2019 CE 260 2013 - Lecture 21- Wastewater Treatment Problems

    1/10

    WasteWater Treatment Processes: Example

    Problems

    CE 260 Lecture 19

    05/31/2013

    http://find/
  • 7/30/2019 CE 260 2013 - Lecture 21- Wastewater Treatment Problems

    2/10

    Primary Clarifier

    30000 people, 0.5m3 / persone / day. Design a conventional

    primary clarifier to have a 2hrs detention time and a 40m/doverflow rate and a high-rate clarifier with a 1500m/d overflow.What are the dimension of the conventional vs high rate?

    http://find/
  • 7/30/2019 CE 260 2013 - Lecture 21- Wastewater Treatment Problems

    3/10

    Primary Clarifier

    A = Q/v = 375m2

    diameter=

    (4A

    pi

    ) = 22m

    depth=QA

    = 15000237524

    = 3.3m

    high rate: A=Qv

    = 15000/1500 = 10m2

    http://find/
  • 7/30/2019 CE 260 2013 - Lecture 21- Wastewater Treatment Problems

    4/10

    Secondary treatment: Pond problem

    http://find/
  • 7/30/2019 CE 260 2013 - Lecture 21- Wastewater Treatment Problems

    5/10

    Secondary treatment: Pond problem

    Mass balance:dX

    dt =QX0 QXf

    +Vr

    Insert the Monod expression for the rate r, with also a die off ofthe bacteria, and consider the steady state:

    dX

    dt = QX0

    QX + V

    (

    kmaxXS

    Ks + S

    kdX) = 0

    Considering X0 = 0, simplify by Q:

    X +V

    Q (

    kmaxXS

    Ks +

    S kdX) = 0

    Factor X out and consider = VQ

    :

    X((kmaxS

    Ks + S kd)) = 0

    http://find/http://goback/
  • 7/30/2019 CE 260 2013 - Lecture 21- Wastewater Treatment Problems

    6/10

    This is true if:

    X((kmaxS

    Ks + S kd)) = 0

    for any X. Solving for S gives:

    S =Ks(1 + kd)

    kmax 1 kd

    Note that S, the amount of BOD (or equivalently of organicmatter) in the system does not depend on the input concentration

    but only on microbiological information (and residence time)!

    http://find/
  • 7/30/2019 CE 260 2013 - Lecture 21- Wastewater Treatment Problems

    7/10

    The same approach leads to an expression for X, the microbeconcentration:

    dS

    dt= QS0 QS V (

    kXS

    Ks + S) = 0

    Note that k is the substrate utilisation rate here (hence the minussign), not the microbial population growth rate

    (kmaxintheslidesabove).Again, eliminating Q and solving for X gives:

    X =(Ks + S)(S0 S)

    kS

    Using design values (table 6E2 in Nazaroff) for Ks = 60,kd = 0.06 and kmax = 3 yields S=6.9mg/L. With k=5 and S thatwe just calculated, we obtain X=43mg/L.

    http://find/
  • 7/30/2019 CE 260 2013 - Lecture 21- Wastewater Treatment Problems

    8/10

    Secondary treatment: Pond performance

    Matlab code to plot S and X as a function of.

    1 S=@(Ks,kd,tau,km,Y) ...

    Ks.*(1+kd.*tau)./(km*Y.*tau(1+kd.*tau));2

    3

    X=@(Sin,S,tau,Y,k) ...((SinS)./tau).*((Y.*tau)./(1+k.*tau));

    4

    5 Ks=60;kd=0.05;km=3;k=5;Y=0.6;Sin=200;

    6

    7 tau=0.1:0.1:10;

    8

    9 Sresult=S(Ks,kd,tau,km,Y);

    10 Xresult=X(Sin,Sresult,tau,Y,kd);

    http://find/http://goback/
  • 7/30/2019 CE 260 2013 - Lecture 21- Wastewater Treatment Problems

    9/10

    Secondary treatment: Pond performance

    Matlab code to plot S and X as a function of(continued).

    1

    2 figure

    3 plot(tau,Sresult,'linewidth',2);

    4 hold on

    5 plot(tau,Xresult,'r','linewidth',2)

    6

    7 set(gca,'ylim',[0 100],'xlim',[1 ...

    10],'box','off','linewidth',2)

    8 set(gcf,'color','w')

    9

    10 xlabel('Residence Time (days)')

    11 ylabel('Concentration (mg/L)')

    12 legend({'Substrate';'Bacteria'})

    http://find/
  • 7/30/2019 CE 260 2013 - Lecture 21- Wastewater Treatment Problems

    10/10

    Secondary treatment: Pond performance

    Note that the bacterial concentration decreases as the residencetime increases in this case because of the die off parameter. Thatswhy for an activated sludge reactor, we recirculate some of themass to maintain an optimal concentration. Similar mass balanceapproach can be used to derive expressions for a complete

    activatedd sludge reactor (see Nazaroff pp 349 to 352 for this).

    http://find/