adsorption characteristics of cellulase and β-glucosidase on avicel, pretreated sugarcane bagasse,...
TRANSCRIPT
This article has been accepted for publication and undergone full peer review but has not been through the copyediting,
typesetting, pagination and proofreading process, which may lead to differences between this version and the Version of
Record. Please cite this article as doi: 10.1002/bab.1307.
This article is protected by copyright. All rights reserved. 1
Adsorption Characteristics of Cellulase and β-glucosidase on Avicel, Pretreated
Sugarcane Bagasse and Lignin
Daniele Longo Machado1, João Moreira Neto
1*, José Geraldo da Cruz Pradella
2, Antonio
Bonomi1,2
, Sarita Cândida Rabelo2, Aline Carvalho da Costa
1
1Laboratory of Fermentative and Enzymatic Process Engineering, School of Chemical
Engineering, University of Campinas, Campinas, SP, Brazil
2 Laboratório Nacional de Ciência e Tecnologia do Bioetanol (CTBE) – CTBE/CNPEM,
Campinas, SP, Brazil
Adsorption of Cellulase on Sugarcane Bagasse
*Address for correspondence: João Moreira Neto, Laboratory of Fermentative and Enzymatic
Process Engineering, School of Chemical Engineering, University of Campinas, Zip code:
13083-852, Campinas, SP, Brazil. Tel:+55-19-3521-3959; fax:+55-19- 3521-3965
e-mail: [email protected]
This article is protected by copyright. All rights reserved. 2
Abstract
Although adsorption is an essential step in the enzymatic hydrolysis of lignocellulosic
materials, literature reports controversial results in relation to the adsorption of the cellulolitic
enzymes on different biomasses/pretreatments, which difficults the description of this
phenomenon in hydrolysis mathematical models. In this work, the adsorption of these
enzymes on Avicel and sugarcane bagasse pretreated by the hydrothermal (HB) and
organosolv (OB) methods was evaluated. The results have shown no significant adsorption of
β-glucosidase on Avicel or HB. Increasing solids concentration from 5% (w/v) to 10% (w/v)
had no impact on the adsorption of cellulase on the different biomasses if stirring rates were
high enough (>100 rpm for Avicel and >150 rpm for BH and BO). Adsorption equilibrium
time was low for Avicel (10 minutes) when compared to the lignocellulosic materials (120
minutes). Adsorption isotherms determined at 4 and 50ºC have shown that for Avicel there
was a decrease in the maximum adsorption capacity (Emax) with the temperature increase,
while for HB increasing temperature increased Emax. Also, Emax increased with lignin content
in the material. Adsorption studies of cellulase on lignin left after enzymatic digestion of HB
shows lower but significant adsorption capacity (Emax=11.92 ± 0.76 mg/g).
Keywords: adsorption kinetics, cellulase, enzymatic hydrolysis, Langmuir isotherm, sugarcane
bagasse, β-glucosidase
Abbreviations: HB, hydrothermal bagasse; OB, organosolv bagasse; HPLC, high-performance
liquid chromatography; IL, isolated lignin; CTBE/CNPEM, Brazilian Bioethanol Science and
Technology Laboratory; FPU, Filter Paper Units; CBU, Cellobiose Units.
This article is protected by copyright. All rights reserved. 3
1. Introduction
Cellulase adsorption on the substrate and the formation of the enzyme-substrate complex are
considered critical steps in the enzymatic hydrolysis of cellulose [1]. Thus, an adequate
description of the adsorption step is indispensable to construct an accurate hydrolysis
mathematical model. Many hypotheses have been made to include the adsorption step in
mathematical models, but most of them have not been experimentally proven and there are
contradicting assumptions in different models.
Most works assume that the adsorption equilibrium time is fast (≤ 90 min) compared to the
hydrolysis time course (>24h) [2, 3]. However, many of the studies use pure cellulose as
substrate and adsorption kinetics have been shown to be influenced by the biomass
characteristics and pretreatment [4]. Zheng [5] has shown that the adsorption equilibrium
time of cellulase on sulfuric acid pretreated wild ryegrass is long (8 h), which points to the
need for experimental studies for different biomasses/pretreatments.
Among the most extensively studied aspects of the enzymatic hydrolysis of cellulose in the
last years is the decrease in yield at high solids loading. Wang et al. [6] concluded that the
decreased yield was caused by a decline in the adsorption capacity of cellulase at high
substrate concentrations. These authors have found that even when a fixed substrate/enzyme
ratio was maintained, there was a decrease in the mass of adsorbed enzymes per mass of
substrate when solids loads were changed from 1% to 5% (w/v, based on cellulose) and
determined different adsorption isotherms for different substrate concentrations. The
isotherms determination, however, must have been influenced by mass transfer limitations,
especially considering that the experiments were performed at a very low stirring rate (40
rpm).
Most of the adsorption isotherms of cellulase on biomass in the literature are determined at
4ºC to avoid the hydrolysis reaction [4, 7-9]. However, adsorption is strongly influenced by
This article is protected by copyright. All rights reserved. 4
temperature [10] and hydrolysis occurs at 50ºC, thus if the isotherm is to be used in a
mathematical model it should be determined at this temperature. Maurer et al. [11] proposed
the addition of high glucose concentrations (at least 100 times higher than the enzyme
concentration) to inhibit the hydrolysis reaction in adsorptions studies at high temperatures.
Another controversial aspect in enzymatic hydrolysis models is the unproductive adsorption
of β-glucosidase on lignin. Haven e Jorgensen [12] concluded that adsorption characteristics
are different for different β-glucosidase preparations. In the experimental conditions used in
their work, while β-glucosidase from Aspergillus niger (Novozym 188) did not adsorb on
lignin or on biomass, Cellic® CTec2 β-glucosidase adsorbed significantly, although its
catalytic activity was retained. Even so, many mathematical models in the literature consider
a reduction in the specific hydrolysis rate of cellobiose due to unproductive adsorption of β-
glucosidase on lignin [13-15]. As the adsorption of this enzyme on lignin depends on the
enzyme preparation as well as the biomass and pretreatment, experimental studies are
necessary for specific combinations of enzyme/biomass/pretreatment.
In this work the adsorption of cellulase (Celluclast 1.5 L by Novozyme, Sigma-Aldrich) and
β-glucosidase (Novozym 188, Sigma-Aldrich) was evaluated on Avicel and sugarcane
bagasse pretreated by the hydrothermal (HB) and organosolv (OB) methods. The different
materials were chosen to evaluate the difference in adsorption characteristics in
microcrystalline cellulose (Avicel) and lignocellulosic biomasses with high (Hydrothermal
bagasse) and low (Organosolv bagasse) lignin contents. The adsorption of β-glucosidase on
the biomass with higher lignin content (HB) and the influence of solids concentration and
stirring on the adsorption of cellulase on the three materials were evaluated. Experiments
were performed to calculate the adsorption equilibrium time for the three materials and
isotherms were determined at 4 and 50ºC. Also, adsorption equilibrium time and adsorption
isotherms of cellulase on lignin isolated after hydrolysis of HB were determined. Langmuir
This article is protected by copyright. All rights reserved. 5
isotherms were chosen because they represent simple mechanistic models that can be
employed to compare the kinetic properties of various enzyme-cellulose systems [18].
They are extensively used and provide a good fit to the data of cellulase adsorption on
lignocellulosic biomass in most cases presented by many authors [4, 9, 16, 17]. However,
some assumptions must be taken into consideration for the use of the Langmuir
isotherm, as the reversibility of adsorption, the interactions between non-adsorbed
species, the homogeneity of binding sites and the uniform composition between the
adsorbed cellulases [19].
2. Materials and Methods
2.1. Substrate
The substrate used in all experiments was fresh sugarcane bagasse (Saccharum officinarum)
submitted to hydrothermal (HB) and organosolv (OB) pretreatment and microcrystalline
cellulose (Avicel PH101, nominal particle size 50µm) obtained from Sigma-Aldrich. Bagasse
was provided by the sugar plant “Usina Tarumã” from Raizen group, located in Tarumã, São
Paulo, Brazil, from the same mechanical harvest (2011/12) and resulting from the last milling
after juice extraction. It was dried at room conditions for 4 days, ground in a cutting mill
(Pulverisette 19, Fritsch), subsequently sieved using a 0.5 mm sieve and stored in sealed
plastic bags.
2.2. Enzymes
The enzymes used were cellulase from Trichoderma reesei (Celluclast 1.5 L by Novozyme,
Sigma-Aldrich) and β-glucosidase from Aspergillus niger (Novozym 188, Sigma-Aldrich).
2.3. Pretreatment of lignocellulosic biomass
Two different pretreatments (hydrothermal and organosolv) were separately applied to
sugarcane bagasse. Both pretreatments were conducted at the Brazilian Bioethanol Science
This article is protected by copyright. All rights reserved. 6
and Technology Laboratory (CTBE/CNPEM) according to previously determined conditions
[20, 21].
The hydrothermal pretreatment was performed at 190 °C for 10 min in an alloy reactor C-276
(Parr, model 4554). 300 g of previously ground bagasse (particle size < 0.5 mm) were added
to the reactor with 3 L of distilled water and solid-liquid ratio of 1:10 (w/v). After
pretreatment, the biomass was washed to neutral pH for removal of the soluble compounds.
Analysis of structural carbohydrates, lignin and ash were performed according to Sluiter et al.
[22-24] and Hyman et al. [25]. The composition of the hydrothermal sugarcane bagasse (HB)
was 61.07 ± 0.97 % cellulose, 2.10 ± 0.06 % hemicelluloses, 31.97 ± 0.05 % lignin and 6.44
± 0.06 % ash.
The organosolv pretreatment was performed in the same reactor. 300 g of ground bagasse
with 3L water/ethanol solution (1:1 v/v) and solid-liquid ratio of 1:10 (w/v) were added to the
reactor. The reaction occurred in 150 minutes at a temperature of 190 °C. The pretreated
bagasse was washed with a solution of 1 % (w/v) of sodium hydroxide to solubilize the
residual lignin from the fibers. After washing with sodium hydroxide, the biomass was
washed to neutral pH for removal of the soluble compounds. The composition analysis
methodology was the same used in the hydrothermal pretreated bagasse. The composition of
the organosolv sugarcane bagasse (OB) was 86.91 ± 0.40 % cellulose, 6.63 ± 0.25 %
hemicelluloses, 4.42 ± 0.27 % lignin and 3.75 ± 0.11 % ash.
2.4. Preparation of isolated lignin samples
Lignin was obtained by hydrolyzing HB samples for 96 hours. The samples were incubated
in citrate buffer (50 mM, pH 4.8) supplemented with 0.02% sodium azide per gram of
biomass and 15 FPU of cellulase/g bagasse and 25 CBU of β-glucosidase/g bagasse at 50 °C
with stirring in an orbital shaker at 150 rpm. The enzymatic hydrolysis was conducted at 3%
bagasse (w/v) loading in a 300 mL reaction mixture in a 1 L Erlenmeyer flask. Before the
This article is protected by copyright. All rights reserved. 7
addition of cellulase and β-glucosidase, the mixture of substrate and buffer was pre-heated in
an incubator shaker to the temperature of 50°C for 60 min to allow the substrate to disperse
uniformly in the buffer. After hydrolysis, in order to separate the liquid phase from the
solid phase, the residual material (lignin residue) of the hydrolysis was filtered through
a sieve with pore size 400 mesh (<0.0015 in) and subsequently washed with water.
Desorption of the proteins bound to the residual substrate (the solid phase) after hydrolysis
was carried out according to previously described conditions [26]. After washing the residual
substrate, 300 mL of citrate buffer (50 mM, pH 5.3) containing 0.5% Tween 80 (v/v) was
added to the lignin residue. The Erlenmeyer flasks were incubated for 2 h at 44 °C in an
orbital shaker at 150 rpm. After this period, the suspension was sonicated at 40 kHz for 60
min in a USC-2800 ultrasonic water bath (Unique, Brazil). Then, the materials were washed
3 times with distilled water and dried at room temperature. The lignin content of the isolated
lignin (IL) sample was 78.12 ± 0.02 %.
2.5. Enzyme activity assays
Cellulase activity was determined as filter paper units per milliliter (FPU/mL), as
recommended by the International Union of Pure and Applied Chemistry [27, 28], using
filter paper (Whatman No. 1) as substrate. The enzymatic reaction was performed at
50ºC, for 60 min at pH 4.8. The quantification of sugars released in the medium was
performed by the DNS method described by Miller [29] and Bazán [30].
β-glucosidase activity was determined using a solution of cellobiose 15 mmol/L and
expressed in units per milliliter (CBU/mL) [31]. For quantification of glucose released, the
enzymatic Glucose GOD-PAP method was used, as described by Henry [32]. Enzyme
activity was 87.74 FPU/mL for cellulase and 617.33 CBU/mL for β-glucosidase.
2.6. Cellulase adsorption kinetics and adsorption isotherm
This article is protected by copyright. All rights reserved. 8
Cellulase adsorption kinetics was performed on Avicel, HB, OB and IL in 125 mL
Erlenmeyer flasks with 50 mM citrate buffer (pH 4.8) supplemented with 0.02% of sodium
azide per gram of biomass at different substrate concentrations (5% or 10% w/v). In order to
inhibit hydrolysis reaction in the assays performed at 50ºC, D-(+)-glucose (Sigma-Aldrich)
was added to the aqueous enzyme solution. Glucose is an inhibitor of cellulase, preventing
hydrolytic activity and complexation with the cellulose substrate. According to Maurer et al.
[11] glucose inhibition of the active site of cellulase does not affect the sorption properties,
apparently because the binding domain primarily controls adsorption. The concentration of
glucose in the reaction medium was kept 250 times greater than the protein concentration
used (4 mg/g of substrate).
The flasks were incubated in an air bath shaker (MA 832, Marconi, Brazil) at 50 °C for 1 h
before addition of the enzymes. Five stirring speeds (40, 100, 150, 200 and 250 rpm) were
tested. The flasks were removed at different time intervals during the incubation. The
supernatant from each flask was collected, centrifuged (NT 810 Novatecnica, Brazil) at 25 ºC
(2122 g, 5 min) and filtered using a hydrophilic PTFE membrane with a pore size of 0.45
µm. The protein content of the supernatant was determined using Bradford method [33].
Cellulase adsorption isotherm experiments were conducted by varying the concentration of
cellulase protein (0.1–4.5 mg/mL) added to a constant substrate concentration of 5% (w/v) at
a stirring rate of 150 rpm in 50 mM citrate buffer (pH 4.8) at 4 °C and 50 °C for the
adsorption equilibrium time determined for each substrate. The mass of protein in the
supernatant was determined as free cellulase in solution. The mass of cellulase bound to the
substrate was calculated by subtraction the mass of free protein in solution from the mass of
initial total protein. For the experiments at 50 ºC glucose was added to inhibit hydrolysis in a
cellulase-glucose ratio of 1:100 (w/w).
2.7. β-glucosidase adsorption kinetics
This article is protected by copyright. All rights reserved. 9
β-glucosidase adsorption kinetics was performed on HB in 125 mL Erlenmeyer flasks with
50 mM citrate buffer (pH 4.8) supplemented with 0.02% of sodium azide per gram of
biomass at 5% and 10% (w/v) substrate concentrations. After adding 2 mg protein/g
substrate, the flasks were incubated in an air bath shaker at 50°C and 150 rpm. The
supernatant from each flask was collected, centrifuged and filtered. The protein content of the
supernatant was determined using Bradford method [33].
2.8. HPLC Analysis
Liquid samples from composition analysis of bagasse were analysed by high performance
liquid chromatography (Model 1260 Infinity Agilent Technologies HPLC with refractive
index detector IR and UV-Vis DAD). All samples were filtered using a GS cellulose ester
membrane with a pore size of 0.22 µm (Millipore) before analysis to remove solid particles.
Analysis of sugars and acetic acid were performed using an Aminex HPX- 87H column at
35°C. The mobile phase used was a solution of H2SO4 at pH 2.6 prepared with ultra pure
water (Milli- Q) with a flow rate of 0.6 ml/min. The compounds separated in the stationary
phase were monitored with a refractive index detector at 30° C for 20 min. Quantification of
furfural and hydroxymethylfurfural were performed in a Nova-Pak C18 column (Waters Co.,
Milford, MA) at 30°C, the mobile phase was a solution of acetonitrile /water (1:8 with 1%
acetic acid) previously filtered and degassed, with a flow of 0.8 ml/min. The separated
compounds were monitored by an UV-Vis detector at 280 nm and run time of 8 min.
3. Results and discussion
3.1. Effect of stirring and solids concentration on the kinetics of cellulase adsorption
Figure 1 shows the adsorption kinetics of 4 mg cellulase/g substrate (5.5 FPU/g substrate) on
Avicel and pretreated sugarcane bagasse (HB and OB) at 10% (w/v) solids concentration for
stirring rates varying from 40 to 250 rpm. Statistical analysis using Tukey’s multiple
comparison test (p<0.05) has shown that the adsorption of cellulase on Avicel is lower at 40
This article is protected by copyright. All rights reserved. 10
rpm (2.80 0.22 mg/g Avicel, Figure 1a) and that the adsorption is similar for the assays
performed with stirring rates higher than 100 rpm (3.76 0.16 mg/g Avicel).
For the lignocellulosic substrates (HB and OB), the adsorption was statistically similar for
stirring rates higher than 150 rpm, 3.75 0.01 mg/g HB and 3.85 0.03 mg/g OB, from
Figures 1b and 1c, respectively. At 40 rpm the adsorption was of 3.33 0.02 mg/g HB and
3.25 0.05 mg/g OB and at 100 rpm 3.35 0,01 mg/g HB and 3.46 0.01 mg/g OB.
These data suggest that enzymatic hydrolysis should be performed at stirring rates higher
than 100 rpm for Avicel and higher than 150 rpm for the lignocellulosic materials (HB and
OB) in order to avoid the influence of mass transfer limitations. The lower stirring rate
required for Avicel in comparison to HB and OB may be caused by structural differences in
the materials, but also by particle size. The particle size of the Avicel used in the experiments
was approximately 50 μm, while HB and OB had particle sizes <0.5 mm.
Figures 2 shows the profiles of adsorbed cellulase/g substrate at 5% and 10% (m/v) substrate
concentrations and varying stirring rates (100, 150 and 200 rpm) for Avicel, HB and OB,
respectively.
It can be noticed from Figures 2a, b and c that the adsorption equilibrium time for cellulase
on Avicel is fast, around 10 minutes for all the conditions studied. From Figures 2d, e, f and
2g, h, i it can be seen that the adsorption of cellulases on HB and OB is fast for the first 30
min and then gets slower as it approaches equilibrium, which is reached in approximately 2 h.
The majority of the studies in the literature claim that the concentration of adsorbed cellulase
gets constant in times ≤ 90 min [2, 3, 9, 34]; other studies suggest that 30 min are enough [17,
35, 36]. In this work the adsorption equilibrium time determined for Avicel was the same as
the calculated in the work of Kumar and Wyman [4] and the value was much smaller than the
determined for the pretreated biomasses (HB and OB).
This article is protected by copyright. All rights reserved. 11
Figures 2a, b and c show that the profiles of cellulase adsorption were similar at solids
concentrations of 5 and 10% (w/v) at stirring rates of 100 rpm and higher. Wang et al. [6]
claimed that the adsorption of cellulase on Avicel (mg cellulase/g Avicel) was higher at a
solid concentration of 1% (w/v) than at 5% (w/v) and concluded that cellulase adsorption on
Avicel was influenced by solids loadings. The authors, however, worked with a low stirring
rate of 40 rpm and mass transfer limitations probably influenced their results.
Figures 2d, e and f show the profiles of cellulase adsorption on HB (5% and 10%, w/v). It
can be seen that when the stirring rate was 100 rpm, mass transfer limitations took place and
the adsorption profiles were different for the different solids loadings. The maximum
adsorption capacity was higher at 5% (w/v) solids (3.94 0.01 mg/g HB) than at 10% (w/v)
solids (3.36 0.01 mg de celulase/g HB). For stirring rates of 150 rpm and higher the
adsorption profiles were similar, which shows that once mass transfer limitations are
eliminated, the adsorption is not dependent on the solids concentration. The same behavior is
shown in Figures 2g, h and i for cellulase adsorption on OB, at stirring rates of 150 rpm up
there was no influence of solids loading on the adsorption profiles.
Ouyang et al. [37] concluded that the adsorption of cellulases on bagasse produced by
traditional sulfite pulping processing was influenced by substrate concentration and was
higher at low solids concentrations (4% w/v) than at high solids concentrations (8% w/v).
The stirring rate used in this study, however, as well as in the work of Wang et al. [6], was
low, of 100 rpm, and probably the authors also confounded an effect of mass transfer
limitation with the influence of solids loading on the adsorption stage. Therefore, it can be
concluded that stirring rates in enzymatic hydrolysis of biomass should be high enough to
avoid mass transfer limitations and in this case the mass of cellulase adsorbed by mass of
substrate is not dependent on the substrate concentration.
3.2. Adsorption of β-glucosidade on pretreated bagasse
This article is protected by copyright. All rights reserved. 12
Many works have concluded that the adsorption of β-glucosidade on pure cellulose (Avicel)
is negligible [5, 38-40]. The same was found in preliminary experiments performed in this
work (data not shown).
Assuming that β-glucosidade does not adsorb on cellulose, only the kinetics of adsorption of
this enzyme on HB, the biomass with the highest lignin content (31.97%), was evaluated.
The stirring rate used in this study was set high enough (150 rpm) to avoid mass
transfer effects as previously described in the section 3.1. Figure 3 shows the supernatant
β-glucosidade concentration after 2 mg enzyme/g substrate were added to solutions
containing 5 and 10% (w/v) of HB, corresponding to concentrations of 0.1 and 0.2 mg β-
glucosidade/mL, respectively. It can be seen that β-glucosidade concentrations were
practically constant, indicating that there was no adsorption of the enzyme on the substrate.
Some studies report significant adsorption of β-glucosidases on lignocellulosic materials [8,
39, 41, 42]. Lu et al., [43] claimed that this is an unexpected behaviour as β-glucosidades do
not have cellulose binding domain (CBD) and thus have low affinity for lignocellulosic
substrates. Berlin et al. [44] found that β-glucosidade had low affinity for isolated lignin-rich
residues. The controversy must be due to the different enzyme sources, substrates and
pretreatments used in the different works, as suggested by Haven e Jorgensen [12]. These
authors found that β-glucosidase from Aspergillus niger (Novozym 188), the same enzyme
used in the present work, did not adsorb on lignin or on biomass, corroborating the present
results.
3.3. Adsorption isotherms of cellulase on Avicel and pretreated sugarcane bagasse (HB
and OB)
The contact time between enzyme and substrate in the adsorption isotherm studies was fixed
a little higher than the previously calculated adsorption equilibrium time for each substrate in
order to make sure that equilibrium was attained. Also stirring rate was set high enough (150
This article is protected by copyright. All rights reserved. 13
rpm) to avoid mass transfer effects as previously described. The contact time for Avicel was
fixed at 30 min and for pretreated bagasse (HB and OB) at 3h. Experimental data were
adjusted to the Langmuir isotherm (Equation 1) using the software OriginPro 8.0 (OriginLab,
Northampton, MA, USA).
fp
fp
adEK
EKEE
1
max (1)
In Equation 1 Ead is the amount of adsorbed enzyme (mg enzyme/g substrate); Emax is the
maximum adsorption capacity (mg enzyme/g substrate); Ef is the free enzyme concentration
(mg enzyme/mL) and Kp is the equilibrium constant (mL/mg enzyme).
It can be seen from Figure 4, which shows the adsorption isotherms for all the substrates, that
the Lagmuir isotherm adjusted the experimental data accurately. Table 1 shows the values of
maximum adsorption capacity (Emax) and of the equilibrium constant (Kp) for all the
isotherms.
The parameters for Avicel at 4 ºC and 50 ºC (Emax= 42.09 ± 1.78 mg/g Avicel and Emax=17.46
± 0.85 mg/g Avicel, respectively) are in the same order of magnitude of results previously
reported [6, 9, 35] and these authors also reported a decrease in Emax as temperature increases.
This behavior is expected in processes described by the Langmuir model [9].
For the hydrothermal bagasse (HB), however, Emax increased from of 15.81± 0.58 mg/g BH
at 4 ºC to 36.93 ± 2.73 mg/g BH at 50 ºC. An increase of the maximum adsorption capacity
with temperature was found by Zheng et al. [9] when studying the adsorption of cellulases on
lignin isolated from lignocellulosic materials submitted to different pretreatments.
According to Zheng et al. [9] and Pareek et al. [8] the protein adsorption in lignin-rich
substrates might be due to hydrophobic interactions between lignin and cellulase. An
increasing temperature would alter protein molecular structures and expose more
hydrophobic regions to the sur7roundings, therefore leading an increase in lignin
This article is protected by copyright. All rights reserved. 14
adsorption capacity.
A comparison of the values of Emax for the three substrates (Table 1) shows that the
maximum adsorption capacity seems to be higher for biomasses with higher lignin content.
For Avicel, pure cellulose, Emax was 17.41 ± 0.85 mg/g Avicel; for OB, with 4.42% of lignin,
Emax was 29.40 ± 1.20 mg/g OB and for HB, with 31.97% of lignin, Emax was 36.93 ± 2.73
mg/g HB. The maximum enzyme concentration used in the isotherm experiments was 4.5
mg/mL, equivalent to 90 mg of protein/g of biomass.
Other authors have found that more cellulase is adsorbed on materials with higher lignin
content [16, 43]. Heiss-Blanquet et al. [34], however, found that less cellulase was adsorbed
on wheat straw submitted to organosolv pretreatment than on the same biomass submitted to
steam explosion, even though the organosolv pretreated wheat straw had the lowest lignin
content.
The parameter Kp of the Langmuir isotherm was not interpreted in this work. For
purified proteins the inverse of Kp (1/Kp) is a measure of the affinity of the protein for
the substrate. As the cellulolytic complex used in this work is composed by several
proteins, this parameter has no physical meaning [45].
3.4. Cellulase adsorption on lignin
The adsorption of cellulase on lignin has been evaluated in many works [7, 9, 17, 42, 46, 47].
These authors suggest that cellulases from Trichoderma reesei adsorb unproductively on
lignin. Studies suggest that the cellulase interactions with lignin may be through electrostatic
bonds [44, 47], hydrophobic bonds [48] and hydrogen bonds [49]. The unproductive
adsorption of the cellulolytic enzymes on lignin decreases hydrolysis yields and demands for
higher enzymes dosages to enhance the efficiency of the process, leading to higher costs [46,
50].
This article is protected by copyright. All rights reserved. 15
The adsorption kinetics of cellulase on isolated lignin (IL) (the residue of enzymatic
hydrolysis of HB, 78.12 ± 0.02 % of lignin) can be seen in Figure 5a, which shows that the
adsorption equilibrium time is around 1h for this biomass. Zheng et al. [9] evaluated the
adsorption of cellulases on lignin isolated from different biomasses and pretreatments
(diluted acid and steam explosion pretreated wheat straw and steam explosion pretreated rice
straw). They found that the adsorption equilibrium time was 1h at 4 ºC and 12h at 50 ºC, a
result very different from this work.
The maximum mass of cellulase adsorbed was 2.75 ± 0.03 mg/ g IL when 4 mg enzyme/g
biomass were added. When compared with the values obtained for HB (Figure 3 d, e and f)
and OB (Figure 3 g, h and i), around 3.75 mg/g de bagasse, it can be seen that the adsorption
on lignin is lower than on biomass, but significant.
Figure 5b shows the Langmuir isotherm for the adsorption of cellulases on lignin and the
estimated parameters are shown in Table 1. The maximum adsorption capacity (Emax=11. 92
± 0.76 mg/g LI) obtained in this work is similar to the obtained by Zheng et al. [9]. Although
the adjusted value of Emax was 22 mg/g IL in their work, this value was extrapolated, as the
maximum experimental values obtained were around 15 mg/g IL, even for the higher enzyme
concentrations considered (2 mg/mL at 1% solids, equivalent to 200 mg/g IL; a much higher
value than the 90 mg enzyme/g IL used in the present work).
Analyzing Table 1 it can be concluded that the isolated lignin presented lower adsorption
capacity when compared to the other substrates. The maximum adsorption capacity of the IL
was 1.5 times lower than of Avicel, 2 times lower than of OB and 3 times lower than HB,
which suggest that cellulases have higher affinity for cellulosic/lignocellulosic substrates than
for lignin. Palonen et al. [7] and Seo et al. [42] also have found that cellulases have higher
affinity for cellulose than for isolated lignin at 4ºC. Pareek et al. [8] and Li et al. [17],
This article is protected by copyright. All rights reserved. 16
however, concluded that isolated lignin adsorbed more cellulases than the pretreated biomass
and Avicel at 4 ºC.
4. Conclusions
The results of the present work show that the adsorption of β-glucosidase from A. niger
on Avicel and bagasse pretreated by both methods (HB and OB) was negligible, which
shows that mathematical models describing the hydrolysis of these substrates should not
consider the reduction of the specific rate of cellobiose hydrolysis due to unproductive
adsorption when β-glucosidase from A. niger is used. The adsorption equilibrium time
determined for Avicel (10 min) was much lower than that of the pretreated biomasses
(2h). In addition, the results obtained show that solids concentration up to 10% (w/v) do
not influence the adsorption kinetics at sufficiently high stirring rates (>100 rpm for
Avicel, >150 rpm for pretreated bagasse). The Langmuir isotherm adjusted well the
adsorption data at 4 and 50 ºC. The adjusted parameters at 50 ºC were very different
from the parameters at 4 °C. Therefore, if the isotherms are to be used in hydrolysis
mathematical models, they must be determined in the temperature in which hydrolysis
occurs (50 ºC). The adsorption experimental data have shown that the adsorption of
cellulase is higher for materials with high lignin contents and that this enzyme has
higher affinity for cellulose than for lignin, although the adsorption in lignin is
significant.
5. Acknowledgements
The authors acknowledge Fundação de Amparo à Pesquisa do Estado de São Paulo
(FAPESP) process number 2011/02743-5, Conselho Nacional de Desenvolvimento Científico
e Tecnológico (CNPq) for financial support, and the sugar plant “Usina Tarumã” from Raizen
group, located in Tarumã, São Paulo, Brazil for the supply of sugarcane bagasse.
This article is protected by copyright. All rights reserved. 17
6. References
[1] Gan, Q., Allen, S. J. and Taylor, G. (2003) Process Biochem. 38, 1003-1018.
[2] Boussaid, A. and Saddler, J. N. (1999) Enzyme Microb Tech. 24, 138–143.
[3] Kim, D. W., Jang, Y. H. and Jeong, Y. K. (1998) Biotechnol Appl Bioc. 27, 97–102.
[4] Kumar, R. and Wyman, C. E. (2009) Biotechnol Bioeng. 103, 252–267.
[5] Zheng, Y. (2007) Kinetic modeling of enzymatic saccharification and particleboard
characteristics of saline biomass. PhD thesis, University of California, Davis, USA.
[6] Wang, W., Kang, L., Wei, H., Arora, R, A. and Lee, Y. Y. (2011) Appl Biochem Biotech.
164, 1139-1149.
[7] Palonen, H., Tjerneld, F., Zacchi, G., Tenkanen, M. (2004) J Biotechnol. 107, 65-72.
[8] Pareek, N., Gillgren, T. and Jönsson, L. (2013) Bioresource Technol. 148, 70-77.
[9] Zheng, Y., Zhang, S., Miaoa, S., Su, Z. and Wang, P. (2013) J Biotechnol. 166, 135-143.
[10] Kaya, F., Heitmann JR, J. A. and Joyce, T. W. (1994) J Biotechnol. 36, 1-10.
[11] Maurer, S. A., Bedbrook, C. N., and Radke, C. J. (2012) Ind Eng Chem Res. 51, 11389-
11400.
[12] Haven, M. Ø. and Jørgensen, H. (2013) Biotechnol Biofuels, 6:165.
[13] Philippidis, G. P. and Hatzis, C. (1997) Biotechnol Prog. 13, 222-231.
[14] Zheng, Y., Pan, Z., Zhang, R. and Jenkins, B. M. (2009) Biotechnol Bioeng. 102, 1558-
1569b.
[15] Moreira Neto, J., Garcia, D. R., Rueda, S. M. G., Costa, A. C. (2013) Bioprocess Biosyst
Eng. 36, 1579-1590.
[16] Qi, B., Chen, X., Su, Y. and Wan, Y. (2011) Bioresource Technol. 102, 2881-2889.
[17] Li, J., Li, S., Fan, C. and Yan, Z. (2012) Colloid Surface B. 89, 203-210.
[18] Zhang, Y. H. P. and Lynd, L. R. (2004) Biotechnol. Bioeng., 88, 797–824.
This article is protected by copyright. All rights reserved. 18
[19] Bansal, P., Hall, M., Realff, M. J., Lee, J. H. and Bommarius, A. S. (2009) Biotechnol.
Advances, 27, 833–848.
[20] Driemeier, C., Pimenta, M. T. B., Rocha, G. J. M., Oliveira, M., Mello, D. B., Maziero,
P. and Gonçalves, A. R. (2011) Cellulose, 18, 1509-1519.
[21] Christofoletti, G. B. (2010) Estudo dos efeitos de etapas de pré-tratamento na hidrólise
ácida de bagaço de cana-de-açúcar. Master thesis, University of São Paulo, São Carlos,
Brazil.
[22] Sluiter, A., Ruiz, R., Scarlata, C., Sluiter, J. and Templeton, D. (2005a) National
Renewable Energy Laboratory (NREL), 1-12.
[23] Sluiter, A., Hames, B., Ruiz, R., Scarlata, C., Sluiter, J. and Templeton, D. (2005b)
National Renewable Energy Laboratory (NREL), 1-8.
[24] Sluiter, A., Hames, B., Ruiz, R., Scarlata, C., Sluiter, J. and Templeton, D., Crocker, D.
(2008) National Renewable Energy Laboratory (NREL), 1-16.
[25] Hyman, D., Sluiter, A., Crocker, D., Johnson, D., Sluiter, J., Black, S. and Scarlata, C.
(2007) National Renewable Energy Laboratory (NREL), 1-13.
[26] Pribowo, A., Arantes, V. and Saddler, J. N. (2012) Enzyme Microb Tech. 50, 195-203.
[27] Ghose, T. K. (1987) Pure Appl Chem. 59, 257-268.
[28] Adney, B. and Baker, J. (1996) Chemical analysis and testing task laboratory analytical
procedure. LAP-006.
[29] Miller, G. L. (1959) Anal. Chem., 31, 426-428.
[30] Bazán, Juan Heraldo Viloche.(1993) Estudo de produção enzimática da dextrana clínica.
phD thesis, University of Campinas, Campinas, Brazil.
[31] Wood, T. M. and Bhat, K. M, in: Wood, W. A and Kellog, S. T., Eds. (1988) Methods in
enzymology, Academic Press, San Diego, Canada, 160, pp. 87-116.
[32] Henry, R. J., Cannon, D. C., Winkelman, J. (1974) Clinical chemistry principles and
This article is protected by copyright. All rights reserved. 19
techniques, 2 ed. Harper and Row Publishers Inc. N.Y. p. 1288.
[33] Bradford, M. M. (1976) Anal Biochem. 72, 248-254.
[34] Heiss-Blanquet, S., Zheng, D., Lopes Ferreira, N, Lapierre, C, and Baumberger, S.
(2011) Bioresource Technol. 102, 5938-5946.
[35] Kim, D. W., Jeong, Y. K. and Lee, J. K. (1994) Enzyme Microb Tech.16, 649-58.
[36] Singh, A., Kumar, P. K. R. and Schugerl, K. (1991) J Biotechnol. 18, 205-212.
[37] Ouyang, J., et al. (2013) Bioresource Technol. 146, 288-293.
[38] Ooshima, H., Sakata, M., Harano, Y. (1983) Biotechnol Bioeng. 25, 3103-3114.
[39] Zheng, Y., Pan, Z., Zhang, R., Wang, D. Jenkins, B. (2008) Appl Biochem Biotech. 146,
231-248.
[40] Zhu, Z., Sathitsuksanoh, N., Vinzant, T., et al. (2009) Biotechnol Bioeng. 103, 715-724.
[41] Yang, B. and Wyman, C. E. (2006) Biotechnol Bioeng. 94, 611-617.
[42] Seo, D., Fujita, H. and Sakoda, A. (2011) Adsorption, 17, 813-822.
[43] Lu, Y. P., Yang, B., Gregg, D., Saddler, J. N. and Mansfield. S. D. (2002) Appl Biochem
Biotech. 98, 641-654.
[44] Berlin, A., Balakshin, M., Gilkes, N. Kadla, J., Maximenko, V., Kubo, S. and Saddler, J.
(2006) J Biotechnol. 125, 198-209.
[45] Bresolin, I. T. L., Borsoi-Ribeiro, M., Caro, J. R., Santos, F. P., Castro, M. P. and
Bueno, S. M. A. (2009). J. Chromatogr. B. 877, 17-23.
[46] Börjesson, J., Peterson, R., Tjerneld, F. (2007) Enzyme Microb Tech. 40, 754-762.
[47] Lou, H., Wanga, M., Lai, H, Lin, X., Zhou, M., Yang, D. and Qiu, X. (2013)
Bioresource Technol. 146, 478-484.
[48] Eriksson, T., Börjesson, J. and TJerneld, F. (2002) Enzyme Microb Tech. 31, 353-364.
[49] Sewalt, V. J. H., Glasser, W. G., Beauchemin, K. A. (1997) J Agr Food Chem. 45, 1823-
1828.
[50] Zhu, J. Y and Zhuang, X. S. (2012) Prog Energ Combust. 38, 583-598.
This article is protected by copyright. All rights reserved. 20
Table 1- Maximum adsorption capacity (Emax) and equilibrium constant (Kp) in the
adsorption of cellulases on Avicel and hydrothermal (HB) and organosolv (OB) pretreated
bagasse adjusted to the Langmuir isotherm (Equation 1).
Substrate Temperature (°C) Emax (mg/g) Kp (mL/mg) R2
Avicel 4 42.09 ± 1.78 4.23 ± 0.71 0.95
Avicel 50 17.41 ± 0.85 4.46 ± 0.87 0.96
HB 4 15.81 ± 0.58 9.26 ± 2.10 0.95
HB 50 36.93 ± 2.73 1.28 ± 0.25 0.96
OB 50 29.40 ± 1.204 2.68 ± 0.40 0.97
IL 50 11.92 ± 0.76 13.27 ± 6.29 0.87
This article is protected by copyright. All rights reserved. 21
Figure 1
This article is protected by copyright. All rights reserved. 22
Figure 2
This article is protected by copyright. All rights reserved. 23
Figure 3
This article is protected by copyright. All rights reserved. 24
Figure 4
This article is protected by copyright. All rights reserved. 25
Figure 5