Carbohydrate Polymers 148 (2016) 69–77
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Carbohydrate Polymers
journal homepage: www.elsevier.com/locate/carbpol
Nanofibrillated cellulose from tobacco industry wastes
Glaiton Tuzzin, Marcelo Godinho, Aline Dettmer
∗
, Ademir José Zattera
Engineering of Processes and Technologies Post-Graduate Program, University of Caxias do Sul, Caxias do Sul, Rio Grande do Sul, Brazil
a r t i c l e i n f o
Article history:
Received 4 February 2016
Received in revised form 6 April 2016
Accepted 9 April 2016
Available online 12 April 2016
Keywords:
Tobacco
Waste
Steam explosion
Nanocellulose
a b s t r a c t
Tobacco stems waste underwent steam explosion pulping for nanofibrillated cellulose (NFC) production.
In order to obtain NFC hydrogels, the pulp obtained by steam explosion was bleached and refined in
a grinder employing specific energy of up to 5067 kWh/t. Eucalyptus kraft pulp was processed under
the same conditions to produce NFC hydrogels, later used in order to compare with NFC hydrogels from
tobacco stems waste. According to statistical analysis, the optimum tobacco stems pulping condition was
obtained with a severity index of log 3.0 and active alkali of 16.25%. These conditions allowed obtaining
a bleached pulp with Schopper Riegler degree of 46. Electronic microscopy with field emission showed a
higher presence of nanofibers in the tobacco stems pulp than in commercial eucalyptus kraft pulp, both
after refining. Thermal analysis indicated that tobacco stems pulp degrade at lower temperatures than
eucalyptus kraft pulp. FTIR analysis did not indicate chemical bonding differences between the two pulps.
© 2016 Elsevier Ltd. All rights reserved.
1. Introduction
The demographic and economic expansion has been demand-
ing higher amounts of natural resources worldwide. Hence, waste
generation grows and becomes a threat to ecological equilibrium
and to human survival.
Tobacco industry employs tobacco leaves for cigarette and cigar
production (Peˇ sevski et al., 2010). According to data of the Brazilian
Association of Tobacco Growers, Brazil produced 607 thousand tons
of tobacco in the 2015/16 harvest. About 4% of the tobacco leaves
processed become a waste, which is basically constituted of tobacco
stems (leaves midribs) and dust from processing.
Tobacco stems correspond to about 20% of the total leaves
weight (Browne, 1990) and present a higher cellulose content
(up to 23%) than the leaf lamina (Leffingwell, 2001; Wakeham &
Silberman, 1966). Since cellulose confers an unpleasant taste when
burnt, tobacco stems are not directly used in cigar and cigarette
production (Leffingwell, 2001). In order to allow tobacco stem use,
it is laminated and turned into reconstituted tobacco, to which
flavorings and humectants are added (Browne, 1990). However,
reconstituted tobacco is only used in low quality cigarette, thus
not consuming all the waste produced (Peˇ sevski et al., 2010).
Tobacco stalks, in their turn, are directly disposed on the land
used for tobacco cultivation. They can have up to 40% of cellulose
∗
Corresponding author at: Rua Francisco Getúlio Vargas, 1130, Caxias do Sul,
95070-560 Rio Grande do Sul, Brazil.
E-mail address: alinedettmer@gmail.com (A. Dettmer).
content in weight, which makes it an interesting raw material for
papermaking or for the production of other cellulose derivatives
(Shakhes et al., 2011; Agrupis, Maekawa, & Suzuki, 2000).
Among all the cellulose derivatives, one has been attract-
ing particular interest: nanocellulose. Some advantages of this
new material, which is obtained from renewable sources, is its
high area/volume ratio, high Young’s modulus, its capability of
being biodegraded, and its nontoxic characteristics (Flauzino Neto,
Silvério, Dantas, & Pasquinia, 2013). Nanocellulose can also be
obtained from agricultural wastes like pineapple leaves (Cherian,
Leão, Souza, Pothan, & Kottaisamy, 2010), banana tree stalk (Deepa
et al., 2011), wheat straw (Kaushik & Singh, 2011), rice husk (Kalita
et al., 2015), and pinecone (Rambabu, Panthapulakkal, Sain, & Dalai,
2016). Nanocellulose may be applied in nanocomposites, in elec-
tronic devices, in cosmetic products, and in membranes, among
others (Eichhorn et al., 2010).
Different processes may be used to produce nanocellulose. Acid
hydrolysis produces nanocrystalline cellulose—NCC (Klemm et al.,
2011; Johar, Ahmad, & Dufresne, 2012). Bacterial nanocellulose
(BNC) is produced from sugar consumption by bacteria of the genus
Gluconacetobacter (Dufresne, 2013; Klemm et al., 2011). Although
both processes present high yields, NCC production generates high
amounts of wastewater and BNC production is expensive (Klemm
et al., 2011).
In 1979, researchers at the ITT Rayonnier developed a mechan-
ical process that enables nanofibers production from sulfite pulp
employing high-pressure homogenizers. This material, known as
microfibrillated cellulose (MFC) or nanofibrillated cellulose (NFC),
displays a gel-like behavior. However, this process of obtaining
http://dx.doi.org/10.1016/j.carbpol.2016.04.045
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