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8/13/2019 Chapter 8-Filtration (56 P)
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PART III. CASE STUDIES
Chapter 8. Filt ration
1
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Characteristics
1) Filtration used for removal of suspended and colloidal solids.
Coa-Floc-Sed followed by filtration
Direct filtration
Direct filtration of high solids
2) Porous media captures solids and transports water.
Solid: suspended vs. dissolved?
Capture dissolved solids?
3) Filtration is primary a physical process but chemicals can be added to improve
performance.
2
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3
10-3um, < colloids < 1 um
1 um < suspended solids < 103um
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Characteristics
4) Two phase process: Solids removal during filtration followed by solids removal
(backwashing).
5) Because it is a two phase process, filtration is typically discontinuous but some
filters are designed to simultaneous filtration and backwashing. Alternatively, you can
design several filtration units in parallel.
- Membrane filtration or separation is excluded in this chapter.
4
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General Classif ication of f ilters According to the Types of Media
1)Single Medium Filters
-One type of medium
-Typically sand or crushed anthracite coal
2) Dual-media filters
-Two types of media
-Typically crushed anthracite and sand
3) Multimedia filters
-Three types of media
-Typically crushed anthracite, sand, and garnet
5
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General Classification of Filters According to Filtration Principles
1) Granular medium filtration.
- Rapid sand filters
2) Surface filtration
- Micro-screens- Vacuum filters/Pre-coat filters
- Slow sand filters
6
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Desired characteristics of the Perfect filter
1)2)
3)
4)
5)
6)
7
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Definition sketch for length of filtration run.
8
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Granular Medium Filtration (Rapid Sand Filtration (vs. slow sand fil tration))
Classification
1) Flow direction
- Downflow
- Upflow
- Biflow
9
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10
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Granular Medium Filtration
Classification
2) Types of Filtering Materials & Filter Configurations.
12
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Classification
3) Driving Force
-Gravity
-Pressure
13
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Classification
4) Flow Control
14
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Classification
5) Backwash/Surface Wash
15Operation of conventional downflow, granular-medium, gravity-flow filter
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16
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17
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18Removal of Suspended Particulate Matter with a Granular Filter
Straining
Sedimentationor inertial impaction
Interception
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19
Removal of Suspended Particulate Matter with a Granular Filter
Adhesion
Flocculation
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20
Solids Removal in Depth Filtration
It is important to realize that particles that contact the media surface must attach or
bond to the surface, with the exception of particles removed by straining. The
bonding forces in filtration are the same as those on coagulation and flocculation:
van der Waals forces. It is also possible that particles will be sheared off or detach
from the media, but reattach deeper in the filter.
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== .CoeffUniformityUC
Grain size and distribution
Effective size = D10
However, grain shape is also an important factor in calculating filtration headlosses and
bed expansion during bachwashing.
22
D10
If D10and CU are small, ??? (vice
versa)
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grainsandofareasurfaceactual
deqwithspherevolumeequalofareasurfaceDefine sphericity, =
Grain density: affects mostly ??
Grain hardness: affects mostly ??
23
In the absence of determining dequse the mean diameter between sieves as an
approximation of deq.
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==volumebedTotal
volumeVoidPorosityBedFixed
hrmhrm
mton
AreaSurface
FlowmediaofrateFiltration /
)(, 2
3
=
=
24
, head-loss but water quality
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25
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26
day
ftgalFiltrationSand
/180m
7.5m/hr
hr/m7.5m
hrL/m7500
min/3,
3
23
2
2
=
=
=
=
watertonorm
population
personperL
3000,500
000,000,1
500
)176176(5353
2778180
000,500 2
ftftormm
mrequiredareaFiltration
=
==
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Hydraulics of depth fi ltration flow
27
Darcys Law Laminar flow
Divided by A
KSX
hKqAQ =
==/
Darcys law can be applied for the hydraulics to estimate how much water can be
transported away from the site
Darcys law: a phenomenologically derived constitutive equation that describes the
flow of a fluid through a porous medium.
http://en.wikipedia.org/wiki/File:Darcy%27s_Law.png8/13/2019 Chapter 8-Filtration (56 P)
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KSX
hKq =
=
Darcys Law
q = hydraulic flux, or velocity of flow (apparent velocity, Va), m/d
K = permeability coefficient or hydraulic conductivity, m/d
h = head-loss (or pressure drop)
X = distance where the head-loss occurs
S = hydraulic gradient, m/m
28
Laminar flow in Circular Pipes (Void Space)
VD
L
gVD
L
hL 22 3232
==
L
hgDV L
32
2
=
weightspecificg==
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KSX
hKq =
=
29
Laminar flow in Circular Pipes (Void Space)
VD
L
ghL 232
=
What happens in Circular Pipes (Channel) with
Medium
?????32 2VD
L
ghL
=
http://en.wikipedia.org/wiki/File:Darcy%27s_Law.png8/13/2019 Chapter 8-Filtration (56 P)
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Apply the equation now to flow through porous media.
Consider media is composed of spheres and voids.
= Porosity
T
V=
V= Void volumeT= Total volume
30
L32
hgDV L
2
a
=
Face velocity = Vapparent= Va
Va=V
V = average velocity through pores
dP,4
dA,
P
AR
2
H =
==
Relating D to the hydraulic radius, RH
For a pipe flowing full D=4RH
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L32
hgDV L
2
a
=
Relating D to the hydraulic radius, RH
For voids & spheres
spheresofareasurface
volumevoid
AR
R
LA
LR
LA
LP
LAR
S
VH =
=
=
=
=
244
244
2
TV =
( )== 1
TVTS
= 1S
T
31
S
SH
AR
=
1
SV
=
1
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( )L
hR
gV LHa
24
32
=L
hR
g LH
2
2
=
( )
2
2
3
12
=
S
SLa
ALhgV
( )a
S
SL LV
A
g
h
2
3
212
=
6,
3
2 S
SS
ddA
==
SS
S
dV
ASdefine 6
==
For non-sphereseqd
S
6=
32
S
SH
AR
=
1
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( ) LVd
)'S(1
g
2h a2
S
2
3
2
L
=
S' = 6 for spheres
Finally
This is essentially the Fair- Hatch eq.
In AWWA it is called the Kozeny equation.
33
seqs
s
d
S
dV
AS
'6===
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( )g
V
d
L1fh
2a
3
=
dVNwhere
NVfbut a
a
== ReRe
641
Other equations developed f rom theoretical considerationsCarmen Kozeny based on Darcy-Weisbach
34
( )LV
d
)'S(1
g
2h a2
S
2
3
2
L
=
Friction factor
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35
Headloss Equations Summary
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( ) ( ) 23223
2
Vd
L
e
e1
g
75.1V
d
L
e
e1
g150h
+
=
( ) ( ) ( ) 23223
2
Vdeq
L
e
e1
g
88.274.1V
deq
L
e
e1
g150h
+
=
( )V
d
L
e
e1
g180h
223
2
=
( )V
deq
L
e
e1
g180h
223
2
=
Headloss Equations Summary
Carmen Kozeny M&E
Ergun AWWA
Kozeny AWWA
Fair-Hatch M&E
36
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BGD FFF =
Backwashing Hydraulics (Recall Chapter 7 for Particle Settling)
When particles are completely fluidize; i.e. no particles are touching (Discrete)
( ) PWSsp
wPD gV
AC = 2
2
Vb = Backwash velocity m/s
37
DBGT FFFF =0
eeL ,
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Backwashing Hydraulics
( )2
22
2
22
2
22
1
2 b
spb
wPDb
b
spwPDPWS
sp
wPD V
VVAC
V
VVACg
VAC ===
Vb = Backwash velocity m/s
38
eeL ,
(e) = Correction factor to relate backwash velocity to
the discrete particle settling velocity, Vsp
PWSe
b
wPDb
spb
wPD
gVV
ACV
VVAC )()(
22
2
2
22
==
)()( 2 eb
sp
V
V=
B k hi H d li
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Backwashing Hydraulics
( ) ( ) PWSeb
wPD gV
AC = 2
2
( )
=
P
P
WD
WPsp
AC
g2V
Recall V For a sphere (Chapter 7)
39
laminar.,.24
1
Re
Re ei
N
CNfor D