Industrial waters are clarified to remove turbidity and
color from the effluent streams in the textile, paper and other polluting industries.
The dictionary meaning of a coagulant is "an agent that induces curdling
or congealing. In a water treatment, what it is a chemical that will remove color
and turbidity present in raw water in the form of flocs. Coagulants neutralize the repulsive electrical charges
(typically negative) surrounding particles allowing them to "stick
together" creating clumps or flocks. Flocculants facilitate the
agglomeration or aggregation of the coagulated particles to form larger
floccules and thereby hasten gravitational settling. Some coagulants serve a
dual purpose of both coagulation and flocculation in that they create large flocks
that readily settle.
In waste water treatment, coagulation and flocculation are
employed to separate suspended solids from water. Although the terms
coagulation and flocculation are often used interchangeably, or the single term
"flocculation" is used to describe both; they are, in fact, two
distinct processes. Knowing their differences can lead to a better
understanding of the clarification and dewatering operations of wastewater treatment.
Finely dispersed solids (colloids) suspended in wastewaters are stabilized by
negative electric charges on their surfaces, causing them to repel each other.
Since this prevents these charged particles from colliding to form larger
masses, called flocks, they do not settle. To assist in the removal of
colloidal particles from suspension, chemical coagulation and flocculation are
required. These processes, usually done in sequence, are a combination of
physical and chemical procedures. Chemicals are mixed with wastewater to
promote the aggregation of the suspended solids in to particles large enough to
settle or be removed.
Coagulation is the destabilization of colloids by neutralizing the
forces that keep them apart. Cationic coagulants provide positive electric
charges to reduce the negative charge (zeta potential) of the colloids. As a
result, the particles collide to form larger particles (flocks).Coagulation,
thus, implies formation of smaller compact aggregates. Rapid mixing is required
to disperse the coagulant throughout the liquid.
Care must be taken not to overdose the coagulants as this
can cause a complete charge reversal and restabilize the colloid complex.
Effluents are heterogeneous in nature. Chemical coagulation
is an important unit process in water treatment for the removal of turbidity.
Its application in water treatment is followed by sedimentation and
filteration. Various types of coagulants are being used to condition water
before sedimentation and filteration. The most widely used coagulants are:
v
Aluminum
sulphate{Alum }
v
Poly aluminum
chloride {PAC}
v
Ferrous sulphate
v
Sodium Aluminate
v
Silicon
Derivatives
v
Lime
v
Synthetic
Organic Polymers
Currently Alum and PAC are most extensively used in water
treatment .When brought in contact with water, they form positively charged
aluminium hydroxide floc which agglomerates the negatively charged clays, slit,
bacteria, algae organic matters etc causing them to settle down. The sludge
formation in alum and PAC is very high. Also it suffers from high disposal cost
making the treatment non user friendly. suffer from a serious draw back
Synthetic polymers are now increasingly being used as polymeric coagulants for
water treatment. Commercial polymeric coagulants are highly charged cationic products. Cationic polymeric coagulants /flocculants contain positively charged groups such as
amino {- NH3 +}, Imino {- CH2 NH2 + - CH2} or quaternary amino {- + NR4}. Although
a number of poly sulphonium and poly phosponium compounds have been reported,
quadrivalenrt nitrogen is the charged site in all commercial cationic polymeric
coagulants at the present time. Cationicity derives from the quadrivalent
nitrogen, either via protonation of primary, secondary or tertiary amines or
via generation of quaternary nitrogen groupings. Coagulants of this latter
types are referred to as Poly quats. Cationicity of the quaternary nitrogen is
independent of Ph, although, other parts of the polymer molecule may exhibit
sensitivity to Ph, such as hydrolysis of ester linkages. Cationicity dependent
on protonation, however, is a function of Ph .With out getting enmeshed in
details of polymer- surface interactions, the gross effects of Ph on effective
cationicity can be obtained from colloid titration behavior of the polymer at
fixed levels of Ph.