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Introduction
The need to clarify water




Colloids – impart color and turbidity
to water – aesthetical acceptability



11/10/13

Aesthetics and health

Microbes are colloids too
water treatment

1
COAGULATION &
FLOCCULATION









11/10/13

Removal of colloidal
substances from water
Potable water requirements
health, aesthetics, economic

Colloids
Size of colloids - light waves
Brownian motion
Stability of colloids

water treatment

2
What is Coagulation?
 Coagulation is the destabilization of colloids by addition of
chemicals that neutralize the negative charges
 The chemicals are known as coagulants, usually higher valence
cationic salts (Al3+, Fe3+ etc.)
 Coagulation is essentially a chemical process

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--- -- --- - - --- -- -- -water treatment

3
What is Flocculation?
Flocculation is the agglomeration of destabilized particles into
a large size particles known as flocs which can be effectively removed
by sedimentation or flotation.

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4
Coagulation aim

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5
Why coagulation and flocculation?
Various sizes of particles in raw water

Type
Type

Settling velocity
Settling velocity

10
10

Pebble
Pebble

0.73 m/s
0.73 m/s

1
1

Course sand
Course sand

0.23 m/s
0.23 m/s

0.1
0.1

Fine sand
Fine sand

0.6 m/min
0.6 m/min

0.01
0.01

Silt
Silt

8.6 m/d
8.6 m/d

0.0001 (10 micron)
0.0001 (10 micron)

Large colloids
Large colloids

0.3 m/y
0.3 m/y

0.000001 (1 nano)
0.000001 (1 nano)

Small colloids
Small colloids

3 m/million y
3 m/million y

GravIty settlIng

Particle diameter (mm)
Particle diameter (mm)

Colloids – so small: gravity settling not possible
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6
Colloid Stability
Colloid
H 2O

 Colloids have a net negative surface charge
 Electrostatic force prevents them from agglomeration

---Colloid - A

Repulsion

---Colloid - B

 Brownian motion keeps the colloids in suspension
 Impossible to remove colloids by gravity settling
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7
Colloidal interaction

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8
Charge reduction

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9
Colloid Destabilization




Positively charges ions (Na+, Mg2+, Al3+,
Fe3+ etc.) neutralize the colloidal negative
charges and thus destabilize them.



11/10/13

Colloids can be destabilized by charge
neutralization

With destabilization, colloids aggregate in
size and start to settle

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10
Force analysis on colloids

The integral of the
combined forces is
the energy barrier
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11
Flocculation aids

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Floc formation with polymers

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13
Jar Tests
 The jar test – a laboratory procedure to determine the optimum pH
and the optimum coagulant dose
 A jar test simulates the coagulation and flocculation processes

Determination of optimum pH
 Fill the jars with raw water sample
(500 or 1000 mL) – usually 6 jars
 Adjust pH of the jars while mixing
using H2SO4 or NaOH/lime
(pH: 5.0; 5.5; 6.0; 6.5; 7.0; 7.5)
 Add same dose of the selected
coagulant (alum or iron) to each jar
(Coagulant dose: 5 or 10 mg/L)
11/10/13

water treatment

Jar Test
14
Jar Tests – determining optimum pH


Rapid mix each jar at 100 to 150 rpm for 1 minute. The rapid mix
helps to disperse the coagulant throughout each container

Reduce the stirring speed to 25 to 30 rpm
and continue mixing for 15 to 20 mins
This slower mixing speed helps
promote floc formation by
enhancing particle collisions,
which lead to larger flocs




Turn off the mixers and allow
flocs to settle for 30 to 45 mins



Measure the final residual
turbidity in each jar



Jar Test set-up

Plot residual turbidity against pH
11/10/13

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15
Jar Tests – optimum pH
Optimum pH: 6.3

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Optimum coagulant dose
 Repeat all the previous steps
 This time adjust pH of all jars at
optimum (6.3 found from first test)
while mixing using H2SO4 or
NaOH/lime
 Add different doses of the selected
coagulant (alum or iron) to each jar
(Coagulant dose: 5; 7; 10; 12; 15; 20 mg/L)
 Rapid mix each jar at 100 to 150 rpm for 1 minute. The rapid
mix helps to disperse the coagulant throughout each container
 Reduce the stirring speed to 25 to 30 rpm for 15 to 20 mins
11/10/13

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17
Optimum coagulant dose
 Turn off the mixers and allow flocs to settle for 30 to 45 mins
 Then measure the final residual turbidity in each jar
 Plot residual turbidity
against coagulant dose

Optimum coagulant dose: 12.5 mg/L

The coagulant dose with
the lowest residual
turbidity will be the
optimum coagulant dose
11/10/13

water treatment

Coagulant Dose mg/L

18
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19
•

Hydraulic Jump: Hydraulic Jump creates turbulence and
thus help better mixing.
Coagulant
•

In-line flash mixing

•

Mechanical mixing
Back mix impeller

flat-blade impeller

Inflow
Chemical
feeding

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Chemical
feeding

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Inflow

20
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21
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22
Chemical
feeding

Inflow

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23
11/10/13

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24
 Relative coagulating power
Na+ = 1;
Al3+ > 1000;

Mg2+ = 30
Fe3+ > 1000

 Typical coagulants
Aluminum sulfate: Al2(SO4)3.14 H2O
Iron salt- Ferric sulfate:

Fe2(SO4)3

Iron salt- Ferric chloride: Fe2Cl3
Polyaluminum chloride (PAC): Al2(OH)3Cl3
11/10/13

water treatment

25
Aluminum Chemistry
With alum addition, what happens to water pH?
Al2(SO4)3.14 H2O ⇔ 2Al(OH)3↓+ 8H2O + 3H2SO4-2
1 mole of alum consumes 6 moles of bicarbonate (HCO3-)
Al2(SO4)3.14 H2O + 6HCO3- ⇔ 2Al(OH)3↓+ 6CO2 + 14H2O + 3SO4-2
If alkalinity is not enough, pH will reduce greatly
Lime or sodium carbonate may be needed to neutralize the acid.
(Optimum pH: 5.5 – 6.5)
11/10/13

water treatment

26
Alkalinity calculation
If 200 mg/L of alum to be added to achieve complete coagulation.
How much alkalinity is consumed in mg/L as CaCO3?
Al2(SO4)3.14 H2O + 6HCO3- ⇔ 2Al(OH)3↓+ 6CO2 + 14H2O + 3SO4-2
594 mg

366 mg

594 mg alum consumes

366 mg HCO3-

200 mg alum will consume

(366/594) x 200 mg HCO3= 123 mg HCO3-

Alkalinity in mg/L as CaCO3

= 123 x (50/61)
= 101 mg/L as CaCO3

11/10/13

water treatment

27
COAGULANT AIDS
Other substances than
coagulants used:
- Clay minerals
- Silicates
- Polymers

Polymers are often
either anionic or
cationic to aid
coagulation.
Polymers also
reinforce flocs
11/10/13

water treatment

28
FLOCCULATION
Flocculation - agglomeration of colloids by collisions to form separable flocs
Examples - milk, blood, seawater

Mechanisms - perikinetic, collisions from Brownian motion
- orthokinetic, induced collisions through stirring

Orthokinetic flocculation
Velocity gradient, relative movement between colloids in a fluid body
RMS velocity gradient

Camp No. Gt

11/10/13

Typical 2x 104 - 105

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29
Typical layout of a water treatment plant

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30
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31
Slide 13 of 27

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32
Design of Flocculator (Slow & Gentle mixing)
Flocculators are designed mainly to provide enough interparticle
contacts to achieve particles agglomeration so that they can be
effectively removed by sedimentation or flotation
Transport Mechanisms
• Brownian motion: for relatively small particles
which follow random motion and collide with
other particles (perikinetic motion)
• Differential settling: Particles with different
settling velocities in the vertical alignment collide
when one overtakes the other (orthokinetic motion)

11/10/13

water treatment

33
Mechanical Flocculator

Transverse paddle

L

11/10/13

H

Cross flow Flocculator (sectional view)

W

Plan (top view)
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34
Hydraulic Flocculation
•

L

Horizontally baffled tank

The water flows horizontally.
The baffle walls help to create
turbulence and thus facilitate mixing

W
Plan view (horizontal flow)

•

Vertically baffled tank

The water flows vertically. The baffle
walls help to create turbulence and thus
facilitate mixing

H
L

Isometric View (vertical flow)
11/10/13

water treatment

35
Hydraulic Flocculation

http://www.environmental-center.com/magazine/iwa/jws/art4.pdf
11/10/13

water treatment

36
Hydraulic flocculators

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water treatment

37
Hydraulic flocculators: simple technology

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38
Hydraulic Flocculation: Pipe

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39
Hydraulic Flocculation: Pipe

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40
Hydraulic Flocculation:Large stirrers

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41
Mechanical flocculators

11/10/13

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42
Mecahnical flocculators

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43
Mechanical flocculators

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44
Another mechanical
flocculator

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45
Differential settling flocculation

Slide 26 of 27

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Flocculators integrated with settling

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47
Flocculators integrated with settling

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48
Flocculators both sides of settling

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49
Flocculator perforated wall (in background)

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Coagulation