Journal of Biotechnology 162 (2012) 415–421
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Journal of Biotechnology
jou rn al hom epage: www.elsevier.com/locate/jbiotec
Fractionation of sulphite spent liquor for biochemical processing using ion
exchange resins
D.L.A. Fernandes, C.M. Silva, A.M.R.B. Xavier, D.V. Evtuguin
∗
CICECO, Department of Chemistry, University of Aveiro, 3810-193 Aveiro, Portugal
a r t i c l e i n f o
Article history:
Received 4 January 2012
Received in revised form 9 March 2012
Accepted 15 March 2012
Available online 23 March 2012
Keywords:
Sulphite spent liquor
Lignosulphonates
Sugars
Fermentation
Ion exchange resin
Bioethanol
a b s t r a c t
Sulphite spent liquor (SSL) is a side product from acidic sulphite pulping of wood, which organic coun-
terpart is composed mainly by lignosulphonates (LS) and sugars. The last are a prominent substrate for
the bioprocessing although a previous purification step is necessary to eliminate microbial inhibitors.
In this study a fractionation of hardwood SSL (HSSL) has been accomplished employing ion exchange
resins in order to separate sugars fraction from concomitant inhibitors: LS, acetic acid, furan derivatives,
phenolics, acetic acid and excess of inorganic salts. The fractionation of HSSL has been carried out using
two fixed-bed ion exchangers in series (cationic + anionic). The first cation exchange column packed with
Dowex 50WX2 resin was able to eliminate free cations and partially separate sugars from high molecu-
lar weight LS and furan derivatives. The second anion exchange column packed with Amberlite IRA-96
sorbed remaining LS, phenolics and acetic acid. Overall, the series arrangement under investigation has
removed 99.99% of Mg
2+
, 99.0% of Ca
2+
, 99.6% of LS, and 100% of acetic acid, whereas the yield of recovered
sugars was at least 72% of their total amount in HSSL.
© 2012 Elsevier B.V. All rights reserved.
1. Introduction
The world is facing a reduction of global fossil fuels resources,
while energy requirements are progressively growing up. Alter-
natives to produce fuel and chemicals from non-fossil feedstocks
are attracting considerable interest around the world, in order
to answer such needs and minimizing environmental impacts
(Alvarado-Morales et al., 2009; Brehmer et al., 2009; Gonzalez-
Garcia et al., 2009; Mussatto et al., 2010; Sannigrahi et al., 2010).
Bioethanol is an attractive biofuel, since it can be easily pro-
duced in large scale for blending with gasoline or to be used
as pure “green” fuel. Bioethanol can be generated from different
renewable raw materials containing simple sugars, starch or more
complex substrates as lignocellulose (Balat, 2011; Balat et al., 2008;
Chen and Qiu, 2010; Gonzalez-Garcia et al., 2009; Mussatto et al.,
2010).
In last years, numerous studies has been focused towards
biotechnological strategies for the production of the so called “sec-
ond generation” biofuels, utilizing, for instance, forestry wastes
(Balat, 2011; Chen and Qiu, 2010), residual agricultural biomass
(Huang et al., 2009; Nigam, 2001b; Zanichelli et al., 2007), and
industrial wastes (Guimarães et al., 2010; Xavier et al., 2010). This
kind of materials avoid social disturbance, since do not compete
with food crops causing the rise of food prices such as sucrose
∗
Corresponding author. Tel.: +351 234 401 526; fax: +351 234 380084.
E-mail address: Dmitrye@ua.pt (D.V. Evtuguin).
or grains used for the “first generation” bioethanol fermentation
(Alvarado-Morales et al., 2009; Bacovsky et al., 2010; Xavier et al.,
2010).
The production of bioethanol from non-food staff is an emerging
challenge in the area. Sulphite spent liquors (SSLs) are side prod-
ucts from acidic sulphite pulping of wood, and are normally burned
to recover energy and the inorganic base (Casey, 1980; Fernandes
et al., 2012). SSLs are produced in large amounts, about 90 billion
litres annually worldwide (Lawford and Rousseau, 1993). In partic-
ular, approximately 1 million tons of bleached sulphite eucalyptus
pulp is produced per year, and 8–10 m
3
of hardwood sulphite spent
liquors (HSSL) are produced per ton of pulp (Lawford and Rousseau,
1993; Marques et al., 2009a).
The major components of SSLs are lignosulphonates (LS) and
sugars, which are recognized valuable by-products for the produc-
tion of added value products (Hocking, 1997; Plank, 2004; Goheen,
1971). With regard to bioethanol, SSL exhibits advantages over
common lignocellulosic materials, because during the wood pulp-
ing step a series of monomeric sugars are released, thus avoiding
complex industrial hydrolysis processes (Fernandes et al., 2012).
However, SSL contains several low- and high-molecular weight fer-
mentation inhibitors, namely LS, acetic acid, phenolics and high
levels of cationic species, that require a previous detoxification step
(Xavier et al., 2010). Hence, the separation and purification of the
sugars fraction of HSSL are needed to provide an adequate substrate
stream for bioconversion into ethanol. Ion exchange chromatogra-
phy is frequently used as a separation tool in bioprocessing (Cramer
and Holstein, 2011).
0168-1656/$ – see front matter © 2012 Elsevier B.V. All rights reserved.
doi:10.1016/j.jbiotec.2012.03.013