Research article
Electrochemical treatment of biologically pre-treated dairy
wastewater using dimensionally stable anodes
Vlasia Markou
a
, Maria-Christina Kontogianni
a
, Zacharias Frontistis
a, *
,
Athanasia G. Tekerlekopoulou
b
, Alexandros Katsaounis
a
, Dimitris Vayenas
a, c
a
Department of Chemical Engineering, University of Patras, Caratheodory 1, GR-26504 Patras, Greece
b
Department of Environmental & Natural Resources Management, University of Patras, Agrinio, Greece
c
Institute of Chemical Engineering Sciences, Foundation for Research and Technology, PO Box 1414, GR-26504 Patras, Greece
article info
Article history:
Received 8 May 2017
Received in revised form
21 June 2017
Accepted 17 July 2017
Keywords:
Dairy
Wastewater
Electrochemical
Dimensionally stable anodes
abstract
In this work, electrochemical oxidation of aerobically pre-treated dairy wastewaters using IrO
2
-Pt coated
dimensionally stable anodes was investigated. It was found that IrO
2
/Ti electrode outperforming Pt/Ti
and IrO
2
-Pt/Ti at lower current densities, while Pt/Ti achieved better efficiency at higher current density.
Among the different parameters which were studied, the current density was the most crucial for the
efficiency of the process. A current density of 100 mA/cm
2
led to almost complete removal of 3700 mg/L
COD after 360 min of treatment using IrO
2
/Ti electrode and 0.2 M of sodium chloride while complete
decolorization was achieved in less than 60 min. Electrolytes also found to significantly affect the process.
More specific, the use of sodium chloride instead of sodium sulfate enhanced both COD and color
removal due to the formation of active chlorine species. The effect of temperature was relative low; the
process was favourable at elevated temperatures while increasing COD loading resulted in a decrease of
COD and color removal.
© 2017 Elsevier Ltd. All rights reserved.
1. Introduction
Since ancient times the consumption of dairy products consti-
tutes an important part of human nutrition. In recent years, due to
the intensification of the dairy industry the management of dairy
effluents has become a major problem since dairy wastewaters can
be a significant threat, mostly for the aquatic environment
(Carvalho et al., 2013; Prazeres et al., 2012). Consequently, there is a
significant need to improve the management and treatment of
dairy effluents in order to reduce environmental problems and to
ensure the economic viability of this essential agricultural industry.
(Sarkar et al., 2006).
Several research groups have studied the biological treatment of
dairy wastewater, either under aerobic condition (Bumbac et al.,
2015; Tatoulis et al., 2015) or anaerobic conditions (Venetsaneas
et al., 2009; Demirel et al., 2005) with the simultaneous produc-
tion of hydrogen and methane. However, even though biological
processes may lead to a significant reduction of the organic
material, usually they fail to meet the limits settled by environ-
mental legislations for the disposal of effluents into the environ-
ment. Therefore, the combination of biological treatment with
other treatment processes such as constructed wetlands (Sultana
et al., 2016) and intermittent sand filters (Healy et al., 2007) have
been proposed in literature.
At the same time, a considerable research on agro-industrial
wastewaters treatment using physical processes like membrane
technology, mainly reverse osmosis and nanofiltration (Su arez and
Riera, 2015; Vourch et al., 2008; L aszl o et al., 2007) or adsorption
(Kushwaha et al., 2010) has been carried out. Nevertheless, the
main drawback of the physical processes is the fact that they
transfer the problem from one phase to another resulting in the
necessity either of the further concentrated solution treatment
(Perez et al., 2010), or the regeneration of the adsorption material
(Ehrenmann et al., 2011).
Advanced Oxidation Processes (AOPs) is a family of technologies
based on the in situ production of highly reactive radicals. Among
various AOPs most studies related to dairy wastewaters have been
conducted with Fenton, photo Fenton and electro Fenton like re-
actions (Davarnejad and Nikseresht, 2016; Loures et al., 2014;
Prazeres et al., 2013; Vlyssides et al., 2013), photocatalysis (Lamas
* Corresponding author.
E-mail address: zfrontistis@chemeng.upatras.gr (Z. Frontistis).
Contents lists available at ScienceDirect
Journal of Environmental Management
journal homepage: www.elsevier.com/locate/jenvman
http://dx.doi.org/10.1016/j.jenvman.2017.07.046
0301-4797/© 2017 Elsevier Ltd. All rights reserved.
Journal of Environmental Management 202 (2017) 217e224