Chemical Engineering Journal 164 (2010) 85–91
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Chemical Engineering Journal
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Effect of freeze/thaw conditions, polyelectrolyte addition, and sludge loading on
sludge electro-dewatering process
Pham-Anh Tuan
a,∗
, M. Sillanpää
a,b
a
University of Eastern Finland, Laboratory of Applied Environmental Chemistry, Patteristonkatu 1, FI-50100 Mikkeli, Finland
b
LUT Technology, Lappeenranta University of Technology, Patteristonkatu 1, FI-50100 Mikkeli, Finland
article info
Article history:
Received 14 December 2009
Received in revised form 11 August 2010
Accepted 12 August 2010
Keywords:
Electro-dewatering
Electro-osmosis
Freeze/thaw conditions
Polyelectrolyte addition
Sludge
abstract
Laboratory scale pressure-driven electro-dewatering reactor was set up to study the effect of polyelec-
trolyte addition and freeze/thaw conditions on solid content in the final sludge cake at different sludge
loading rates. An increase in freezing temperature and extended natural freezing periods resulted in a
significant increase in sludge dewatering ability. However, dry solid (DS) content in the final sludge cake
after electro-dewatering was similar (39.3–41.5%) regardless the experimental strategies. The reduction
in sludge loading rate from 20 to 3 kg DS/m
2
resulted in the increase in DS content of the final sludge
cake (35.8–48.7%) using both, the polyelectrolyte addition and freezing condition sludge samples. During
electro-dewatering using sludge amended with polymers, the DS content in the final sludge cake by the
anode and the cathode was similar or a bit higher at the cathode either at high sludge loading or using
high amount of polymers. It was found that polymer addition had a negative effect on the electro-osmotic
flow.
© 2010 Elsevier B.V. All rights reserved.
1. Introduction
The most important disadvantage of aerobic municipal wastew-
ater treatment is the generation of large amounts of waste sludge.
Original biological sludge from wastewater treatment plant such
as activated sludge and anaerobically digested sludge are well
known to have a poor dewaterability. It is known that freeze/thaw
conditioning is a highly effective sludge dewatering technique.
The main principle of this technique is that during freezing, ice
crystals grow incorporating water molecules [1,2]. Because the
structure of ice crystals is highly organized and symmetrical, it
cannot accommodate any additional atoms or molecules. Each ice
crystal continues to grow as long as there are water molecules
available. All other impurities and solid particles are forced to the
boundaries of the ice crystal where they become compressed or
dehydrated. This technique changes sludge floc into a compacted
form, reduces sludge bound water content and makes sludge more
apt for settling and filtration [3]. In general, sludge freezing at
slow freezing rates shows better dewaterability than fast freezing.
Nonetheless, it has been reported that even fast freezing signifi-
cantly improves sludge dewaterability [4]. Ormeci and Vesilind [2]
who studied freeze/thaw conditioning effect on alum and activated
sludge, concluded that freeze/thaw conditioning effectively dewa-
∗
Corresponding author. Tel.: +358 40 355 3404; fax: +358 15 333 6013.
E-mail addresses: tuan.pham@uef.fi (P.-A. Tuan),
mika.sillanpaa@lut.fi (M. Sillanpää).
tered alum and activated sludge, however, alum sludge was likely
to freeze/thaw better than activated sludge due to its low dissolved
ion and organic matter content. High concentrations of dissolved
ions and organic material present in activated sludge promote par-
ticle entrapment during freezing and decrease the effectiveness of
freeze/thaw conditioning. Alum sludge ice crystals predominantly
grow in columns, whereas activated sludge ice crystals grow in
dendrite [5]. The addition of dissolved solids (NaCl) to alum sludge
changes ice crystals growth from columnar to dendrite. Because the
dendrite ice crystals are formed at the ice/water interface, sludge
particles are trapped in the ice front, resulting in a decrease in
sludge dewaterability. The freeze/thaw conditioning does not only
increase the sludge dewaterability but also reduces pathogenic
microorganisms in sludge [6]. It is also considered as a low-cost
sludge treatment technique at moderate to cold climates [7].
Electrically assisted treatments have gained popularity in envi-
ronmental engineering in recent years [8–13]. Electro-dewatering
method, when low level electric field is applied to the sludge cake
to induce the migration of water, has been reported to significantly
reduce water content in the final sludge cake [14,15]. However,
the effectiveness of electro-dewatering process strongly depends
on electric field strength and the contact time [16–18]. Moreover,
an increase in voltage application subsequently results in reduced
water content in the final sludge cake as reported by numerous
researchers [14,19–21]. During electro-dewatering process, sludge
type and alkalinity plays an important role in water removal rate
and the final dry solid (DS) content of the sludge cake [22]. The
effect of different types of polyelectrolyte and doses on electro-
1385-8947/$ – see front matter © 2010 Elsevier B.V. All rights reserved.
doi:10.1016/j.cej.2010.08.028