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Pretreatmentofmicroalgalbiomassforenhancedrecovery/extractionofreducingsugarsandproteins
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HanyangUniversity
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ArizonaStateUniversity
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Byong-HunJeon
HanyangUniversity
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ORIGINAL PAPER
Pretreatment of microalgal biomass for enhancedrecovery/extraction of reducing sugars and proteins
Marwa M. Eldalatony1 • Akhil N. Kabra3 • Jae-Hoon Hwang2 • Sanjay P. Govindwar3 •
Ki-Hyun Kim4• Hoo Kim1
• Byong-Hun Jeon1
Received: 3 August 2015 /Accepted: 19 October 2015
� Springer-Verlag Berlin Heidelberg 2015
Abstract Microalgae species including Chlamydomonas
mexicana, Micractinium reisseri, Scenedesmus obliquus
and Tribonema aequale were cultivated in batch cultures,
and their biochemical composition was determined.
C. mexicana showed the highest carbohydrate content of
52.6 % and was selected for further study. Sonication
pretreatment under optimum conditions (at 40 kHz,
2.2 Kw, 50 �C for 15 min) released 74 ± 2.7 mg g-1 of
total reducing sugars (TRS) of dry cell weight, while the
combined sonication and enzymatic hydrolysis treatment
enhanced the TRS yield by fourfold (280.5 ± 4.9 mg g-1).
The optimal ratio of enzyme [E]:substrate [S] for maxi-
mum TRS yield was [1]:[5] at 50 �C and pH 5. Combined
sonication and hydrolysis treatment released 7.3 %
(27.1 ± 0.9 mg g-1) soluble protein of dry cell weight,
and further fermentation of the dissolved carbohydrate
fraction enhanced the soluble protein content up to 56 %
(228.4 mg g-1) of total protein content. Scanning and
transmission electron microscopic analyses indicated that
microalgae cells were significantly disrupted by the com-
bined sonication and enzyme hydrolysis treatment. This
study indicates that pretreatment and subsequent fermen-
tation of the microalgal biomass enhance the recovery of
carbohydrates and proteins which can be used as feedstocks
for generation of biofuels.
Keywords Sonication � Enzymatic hydrolysis �Fermentation � Biofuel � Chlamydomonas mexicana � Totalreducing sugars
Introduction
Bioethanol, a promising biofuel that can substitute gaso-
line in combustion engines [1], has been produced at
commercial scale via fermentation of different carbohy-
drate-rich feedstocks such as sugarcane and corn (first
generation) and waste lignocellulose biomass (second
generation) [2, 3]. However, research on the microalgal
cellulosic based material (third generation) has gained
much attention as they have lacked lignin and can accu-
mulate large quantities of carbohydrates [4]. The main
challenge in bioethanol production from microalgal bio-
mass is to efficiently release fermentable sugars from
microalgal cells [5, 6].
The conversion of native cellulose from the microalgae
biomass to fermentable sugar is extremely slow, since the
cellulosic material is well protected by the cell matrix [7].
Pretreatment of the biomass enhances the rate of hydrolysis
to fermentable sugar as it increases the surface area,
enhances the sugar solubility, improves the substrate
digestibility and weakens the cell wall for enzymes to be
accessible [8, 9]. Several methods for algal cell disruption
including alkaline or acid reagents, bead beating, micro-
wave (220–1100 W/60 min), osmotic shock (with NaCl),
high-pressure homogenization and autoclaving (at 121 �C)
& Byong-Hun Jeon
1 Department of Natural Resources and Environmental
Engineering, Hanyang University, Seoul 133-791,
South Korea
2 Swette Center for Environmental Biotechnology,
The Biodesign Institute at Arizona State University,
P.O. Box 875701, Tempe, AZ 85287-5701, USA
3 Department of Biochemistry, Shivaji University, Vidyanagar,
Kolhapur, Maharashtra 416004, India
4 Department of Civil and Environmental Engineering,
Hanyang University, Seoul 133-791, South Korea
123
Bioprocess Biosyst Eng
DOI 10.1007/s00449-015-1493-5
have been evaluated [10–13], but such methods are eco-
nomically infeasible as they require high temperatures and
addition of beads or chemicals [14]. Alternatively, ultra-
sonication technique has been considered as an emerging
technology with the potential to reduce reaction time and
chemical loading, and the capacity to modify the surface
structure of biomass with beneficial effects on the sac-
charification process [15]. Sonication has been extensively
used for cell lysis and homogenization, and has been
considered as a cost-effective pretreatment for disrupting
the rigid cell envelopes of microalgae [16, 17], but it has a
low efficiency to accumulate carbohydrates residues for
bioethanol production compared to enzymatic hydrolysis
[18]. Enzymatic hydrolysis has been reported as an effi-
cient method for the hydrolysis of microalgal cell wall [19,
20] and has been considered advantageous over acid
hydrolysis because of its higher selectivity and production
of low toxic hydrolysates compared to acid hydrolysis [21].
Fu et al. [22] reported a higher conversion yield (80 %) of
polysaccharides to fermentable sugars using enzymatic
hydrolysis [23, 24]. Carbohydrases have been used for
extraction of plant proteins at neutral and slightly basic pH
levels [25]. Microalgal soluble proteins after carbohydrate
fermentation process can be used for higher alcohol pro-
duction, which make the overall process cost effective with
increased utilization of the microalgal biomass towards
bioenergy [26].
The main objective of this work was to maximize the
release of reducing sugars and protein. A combined soni-
cation and enzymatic hydrolysis treatment was conducted.
Sonication with respect to temperature and time, and
enzymatic hydrolysis for [E]:[S] ratio, temperature and pH
were optimized. Dissolved protein concentration was
monitored during the sonication and enzymatic hydrolysis
treatments. Fermentation process was also evaluated for the
release of soluble proteins. Scanning electron microscope
(SEM) and transmission electron microscope (TEM)
analysis were used to observe the cell integrity after the
pretreatments.
Materials and methods
Cultivation of different microalgae strains
Chlamydomonas mexicana (YSL008), Micractinium reis-
seri (YSL004), Scenedesmus obliquus (YSL014) and Tri-
bonema aequale (YSR021) were isolated from an effluent
of a municipal wastewater treatment plant (Wonju, Water
Supply and Drainage Center, South Korea) and were sub-
mitted to the GenBank under accession numbers of
FR751193, FR751188, FR751171 and FR751201, respec-
tively. The molecular identification of the strains was
performed following the earlier protocol [27]. Microalgae
were cultivated in 5 L Erlenmeyer flasks with 4 L working
volume of Bold’s Basal Medium [28]. Cultures were kept
under white fluorescent light illumination at 60 lmol
photon m-2 s-1 and 26 ± 2 �C for 20 days. Cultures were
mixed using a magnetic stir plate and sparged with sterile
air (0.2 lm filters) at a flow rate of 0.6 L min-1.
Biochemical characterization of microalgae strains
The carbohydrate concentration was determined using
phenol–sulfuric acid method [29]. 10 mg was reacted with
5 mL of sulfuric acid and 1 mL of phenol (5 %) in a water
bath. The mixtures were incubated for 5 min at 90 �C, thenthe absorbance measurements (490 nm) were compared to
a standard curve based on glucose. The concentration of
individual sugars was determined using an ICS-5000 bio-
liquid chromatography (Dionex, USA) with CarboPac PA1
column [30]. Lowry method was used to determine the
protein content in the microalgae strains using bovine
serum albumin (BSA) as a standard protein substrate [31].
Amino acids were analyzed after acid hydrolysis of the
samples with 0.02 N HCl at 110 �C for 22 h. Wako (019-
08393) amino acids mixture standard solution, type H was
used as a standard solution. Ammonia content was also
presented as it comes from the degradation of some amino
acids (e.g., glutamine, asparagine) during acid hydrolysis
[32].
Optimization of sonication pretreatment
The microalgal biomass (C. mexicana) was harvested at the
end of the exponential phase using a centrifuge (Hanil
science industrial, 3000 rpm for 10 min), and was soni-
cated for 15, 30, 45 and 60 min at 30, 40 and 50 �C in a
sonicator (Branson 8510-DTH sonicator, Danbury, Con-
necticut, USA) at a constant frequency of 40 kHz with
maximum power output of 2.2 Kw [16]. At selected time
intervals, a 1.5 mL sample was withdrawn, filtered (syringe
filter, PES Membrane, 0.22 lm, 25 mm) and used for TRS
and protein analysis using microplate reader (Infinite M200
PRO Microplate Reader, NanoQuant from Tecan).
Optimization of enzymatic hydrolysis pretreatment
Cellulase from Trichoderma reesei ATCC 26921 was
purchased from Sigma-Aldrich, as a lyophilized powder
with concentration C1 Unit per mg of solid, and was used
for hydrolyzing C. mexicana biomass. One unit of cellulase
liberates 1.0 lmol of glucose from cellulose (substrate) in
1 h at pH 5.0 and temperature 37 �C [24]. The enzyme
cellulase was dissolved in sterile de-ionized (DI) water in
the presence of 0.15 % polyhexamethylene biguanide
Bioprocess Biosyst Eng
123
(PHMB) at 5 mg mL-1 concentration before the experi-
ments. PHMB was used as a disinfectant and antiseptic
agent. Hydrolysis of sonicated microalgae biomass was
performed in a 50 mM Sodium Acetate Buffer solution.
The sonicated biomass was incubated with the enzyme
solution at different [E]:[S] ratios (1:25, 1:10 and 1:5), pH
(3–6) and temperatures (20–60 �C). Each hydrolysis pro-
cess was conducted at a working volume of 50 mL in a
100-mL shake flask. The flasks were sealed with rubber
stoppers equipped with needles for CO2 emitting and
placed in a shaking water bath (HS-SHWB-30, Hansol
Tech) for 24 h at 120 rpm. At selected time intervals, a
1.5 mL sample was withdrawn and immediately heated for
5 min in a boiling water bath to terminate the enzymatic
reaction. The hydrolysis mixture was centrifuged at 1300g
for 10 min to remove the solid matter. The supernatants
were used to monitor the total reducing sugar [29, 33], and
the degree of hydrolysis was calculated using following
Eq. [20]:
Hydrolysis yield ¼ TRS concentration ðg=LÞInitial concentration ðg/L) of substrate� 100 %
Release of soluble proteins during fermentation
Fermentation of the dissolved carbohydrate fraction (TRS)
released due to the pretreatments (sonication and enzy-
matic hydrolysis) was processed using Saccharomyces
cerevisiae YPH499 [Meyen ex E.C. Hansen (ATCC�
204679TM)]. Released protein fraction from the microalgal
biomass during the carbohydrate fermentation process was
monitored. S. cerevisiae was cultivated using yeast extract,
peptone, and dextrose (YPD) medium for 2–3 days. The
yeast biomass was harvested, washed and adjusted to 10 g/
L for inoculation in the fermentation rector. The pH of the
untreated, sonicated, and sonicated-hydrolyzed microalgal
cells was adjusted to 5 using 1 N HCl/KOH before yeast
inoculation. The fermentation experiments were performed
in triplicate using 250 mL serum bottles with a working
volume of 150 mL. The headspace of each bottle was
flushed with N2 gas for 15 min to provide an anaerobic
environment and then sealed tightly with a butyl rubber
stopper and aluminum crimp. The bottles were placed in a
shaking water bath (HS-SHWB-30, Hansol Tech) at 37 �Cand 120 rpm for 3 days. During carbohydrate fermentation,
the dissolved protein concentration was monitored. A
separate reactor containing yeast only was operated as a
control, and the protein concentration observed in the
control reactor was subtracted from the values obtained
from the reactor containing yeast ? algae to determine the
amount of proteins from algae only.
Scanning and transmission electron microscopic
examination
The structure of untreated, sonicated, and sonicated-hy-
drolyzed microalgal cells was observed with low-vacuum
scanning electron microscope (LV-SEM, S-3500N, Hita-
chi) and transmission electron microscope (TEM, Leo
912A 8B OMEGA EF-TEM, Carl Zeiss, Germany) at
120 keV electron energy emission. The microalgae cell
suspension was fixed using 4 % glutaraldehyde in 0.1 M
cacodylate buffer (pH 7.4), then post-fixed in 1 % OsO4
with 0.1 M cacodylate buffer for 1 h and rinsed with 0.1 M
cacodylate buffer. The cells were pelleted, fixed in glu-
taraldehyde, dehydrated in a series of Et-OH solutions and
embedded in EPON resin. The polymerized blocks were
anaerobically sectioned on a microtome and thin sections
were mounted on copper grids coated with Formvar and
carbon for TEM analysis [15, 16].
Statistical analysis
All experiments were conducted in triplicates and the data
were presented as the mean ± standard error mean (SEM).
One-way analysis of variance (ANOVA) followed by
Tukey’s multiple comparison test was used to examine the
difference among individual treatment and optimum con-
dition. GraphPad Prism version 5.0 for Windows (Graph-
Pad Software, Inc., USA) was used for all statistical
analysis and difference in the variables was considered
significant at the P\ 0.05 of confidence.
Results and discussion
Biochemical characterization
Carbohydrate quantification showed that C. mexicana
possessed the highest carbohydrate content of dry cell
weight (52.6 %) compared to T. aequale (47.72 %),
S. obliquus (41.4 %) and M. reisseri (20.23 %), and was
selected for further investigation. The carbohydrate frac-
tion of C. mexicana was divided into glucose (63.67 %),
mannose (24.33 %), galactose (8.66 %) and glucosamine
(3.34 %) (Fig. 1). Protein content of C. mexicana, T. ae-
quale, S. obliquus and M. reisseri was 37.40, 46.04, 25.50
and 43.72 % of dry biomass, respectively. Recently, pro-
teins have also gained much attention for generation of
higher alcohols. Huo et al. [34] modified the Escherichia
coli cells through metabolic engineering such that they can
de-aminate algal protein hydrolysates, enabling the cells to
convert proteins into C4 and C5 alcohols with 56 % the-
oretical yield. The target strain (C. mexicana) showed
37.4 % protein content which was further subjected to
Bioprocess Biosyst Eng
123
amino acid analysis. Leucine (Leu.), Asparagine (Asp.),
Glutamine (Gln.), Alanine (Ala.), Glycine (Gly.), Thre-
onine (Thr.) and Valine (Val.) accounted higher percentage
which represent *64 % of total amino acids (Fig. 1).
Threonine, glycine and valine have been reported to be the
major fermentable amino acids which can be converted
into (iso)butanol [35]. Protein and amino acid analysis will
give a preface for our future studies on protein
fermentation.
Optimization of sonication treatment
Sonication process as a pretreatment method for TRS
production was optimized with respect to temperature (30,
40 and 50 �C) and time (15, 30, 45 and 60 min). TRS
concentration increased with increasing sonication tem-
perature from 30 to 50 �C (Fig. 2), indicating a significant
influence of temperature on the TRS production. TRS
obtained at 50 �C were significantly different (*P\ 0.05)
than TRS produced at 30 and 40 �C. A slight increase in
TRS was observed from 15 to 60 min at 50 �C. Consid-ering the time and energy consumed, we selected 50 �Cand 15 min as optimum sonication conditions, which
released 14 % TRS of total carbohydrate. Jeon et al. [15]
reported that 32.4 % of dissolved carbohydrate was
released after sonication of microalgal biomass. Sonication
treatment involves the transmission of sonic waves through
the microalgal culture. The waves create a series of micro
bubbles cavitation, which impart kinetic energy into cell
surface, leading to the disintegration of the cell wall and
release of the intracellular carbohydrates into the exocel-
lular medium [14]. Sonication treatment in this study
enhanced the sugar solubility, but it showed a low effi-
ciency to release the carbohydrates residues. Pretreatment
of microalgae promotes the disintegration of polysaccha-
ride complexes which increases the availability of substrate
for enzymatic hydrolysis, facilitating the subsequent fer-
mentation process [36]. Therefore, enzyme hydrolysis of
the microalgal biomass was performed after sonication
treatment to enhance the TRS production as it offers higher
yield and selectivity, and mild operating conditions than
acid hydrolysis.
Optimization of enzymatic hydrolysis treatment
Effect of [E]:[S] ratio
Sonication treatment resulted in partial disintegration of
microalgal biomass, making the polysaccharides more
amenable to enzymatic hydrolysis. The optimization of
enzymatic hydrolysis (cellulase form T. reesei) conditions
with respect to [E]:[S] ratio, temperature and pH has been
described in Fig. 3. The TRS level increased along with
hydrolysis time up to 24 h producing higher simple fer-
mentable sugars (Fig. 3a). Comparative short duration
(24 h) for optimum release of fermentable sugars than
previous studies (50–80 h) [37–39] offers the advantages
of eliminating contamination, reducing inhibition effects
and making the process economically feasible. The TRS
yields after enzymatic hydrolysis of sonicated algal
Fig. 1 Amino acid profile and sugar composition of Chlamydomonas
mexicana. Results are expressed as percentage of each sugar/amino
acid [Leucine (Leu.), Asparagine (Asp.), Glutamine (Gln.), Alanine
(Ala.), Glycine (Gly.), Threonine (Thr.), Valine (Val.), Proline (Pro.),
Phenylalanine (Phe.), Lysine (Lys.), Arginine (Arg.), Serine (Ser.),
Isoleucine (Ile), Cystine (Cys.), Histidine (His.) and Methionine
(Met.)] and represent the real recovery of amino acid after analysis.
Concentration of Ammonia (NH3) corresponds to nitrogen recovery
from some free amino acids destroyed during acid hydrolysis
Fig. 2 Effect of sonication conditions (temperatures and time) on
TRS production. The amount of TRS obtained at 50 �C was
significantly different than TRS obtained at 30 and 40 �C (*P\ 0.05)
Bioprocess Biosyst Eng
123
biomass at various [E]:[S] ratios increased linearly with
increases in incubation period from 0 to 24 h showing a
maximum TRS yield (150 mg g-1) at the ratio [1]:[5]. TRS
produced at [1]:[5] was significantly different
(***P\ 0.0001) as compared to TRS produced at [1]:[10]
and [1]:[25]. The TRS concentration was decreased at
higher [E]:[S] ratios (1:10 and 1:25), which can be attrib-
uted to increased substrates’ viscosity, leading to inefficient
hydrolysis [24, 40]. High viscosity increases the contents of
insoluble materials, which hinders the efficiency of enzyme
to hydrolyze the substrates, and causes an end-product
inhibition and mass transfer limitations within the reaction
mixture, leading to a low TRS yield [41].
Effect of temperature
Temperature is a variable that has a significant effect on
enzyme activity. The hydrolysis of C. mexicana was car-
ried out at different temperatures ranging from 20 to 60 �Cwith the optimum [E]:[S] ratio (1:5) and pH 5. As illus-
trated in Fig. 3b, the TRS yield for 24 h ascended with an
increase in temperature from 20 to 50 �C and then des-
cended with a further increase in temperature to 60 �C. Theoptimum enzymatic hydrolysis temperature was 50 �C,reflecting the highest TRS yield of 280.5 mg g-1 after 24 h
of hydrolysis. The amount of TRS obtained at 50 �C was
significantly different (***P\ 0.0001) than TRS produced
at 20, 30, 40 and 60 �C. The optimum temperature for the
enzymatic hydrolysis of different cellulosic biomass has
also been reported to be 50 �C [19, 39, 42]. An increase in
the temperature affects the kinetic energy of enzymatic
reactions, which increases the frequency of collision
between the substrate and the active sites of an enzyme.
Such a thermal agitation may lead to denaturation of
enzymes, thereby reducing the availability of active sites
[43]. This explains the low TRS yield observed at high
temperature (60 �C) compared to the optimum temperature
(50 �C). Kim et al. [44] reported that over-dehydration of
TRS was incurred on exposure to high temperature,
resulting in the formation of by-products such as 5-Hy-
droxymethylfurfural, levulinic acid, formic acid and char.
Effect of pH
The effect of pHs (3–6) on the hydrolysis of C. mexicana
was investigated using optimum [E]:[S] ratio (1:5) and
temperature (50 �C) (Fig. 3c). The increase in medium pH
from 3 to 5 increased the TRS yield from 140 to
274 mg g-1 after 24 h of hydrolysis. The highest enzyme
activity was observed at pH 5, resulting in the release of
52.1 % TRS of total carbohydrates after 24 h of hydrolysis.
This finding was in agreement with the results reported by
Ingesson et al. [41], where the optimum glucose concen-
tration was observed at a pH ranging from 4.5 to 5.0. The
present results showed that TRS yield dropped drastically
with the subsequent increase in pH to 6. TRS obtained at
pH 5 were significantly different (***P\ 0.0001) than
TRS produced at pHs of 3, 4 and 6). Deflection of pH from
the optimum value affects the electrostatic bonding
between the enzyme and substrate during the hydrolysis
process [24]. The enzyme undergoes conformational
changes on disruption of their charge, making the active
site no longer suitable to catalyze the hydrolysis reactions
[43, 45].
Fig. 3 Effect of different enzyme [E]:substrate [S] ratios (condition:
pH 5 and 37 �C) (a), different temperatures (condition: ratio [1]:[5]
and pH 5) (b), and different pHs (condition: ratio [1]:[5] and
50 �C) (c), on TRS production by enzymatic hydrolysis. TRS
produced at [1]:[5], 50 �C and pH 5, were significantly different
than TRS obtained under other conditions (***P\ 0.0001)
Bioprocess Biosyst Eng
123
A comparison of the results reported in previous studies
with the results of this study for TRS production from algae
by enzymatic hydrolysis is shown in Table 1. Various
enzymes alone or in combination have been used to
hydrolyze the microalgae cells for maximizing the TRS
production. The TRS yield ranged from 120 to
327.2 mg g-1 biomass (Table 1). The variation might be
due to the differences in enzyme type and concentration,
pH value, temperature and microalgae species.
Release of protein during pretreatment
and subsequent fermentation
Utilization of the released proteins for higher alcohol
production will render the overall process cost effective by
increasing the recovery of bioenergy from microalgae
biomass. Dissolved protein concentration of C. mexicana
was monitored during optimization of sonication and
enzymatic hydrolysis treatments for maximizing the TRS
yield. Sonication treatment at 50 �C for 15 min liberated
2.3 mg protein g-1 biomass. Woods et al. [49] reported
that ultrasonication of the green filamentous algae (Cla-
dophora) resulted in 0.7 mg mL-1 protein yield. The
combined sonication and enzymatic hydrolysis treatment
increased the dissolved protein concentration up to
27.1 ± 0.9 mg g-1 biomass (Fig. 4). Carbohydrases attack
the carbohydrate components of the cell wall, decreasing
the cell wall integrity and increasing the liberation of the
intracellular protein pool [50].
Fermentation of microalgal carbohydrates for bioethanol
production leads to a simultaneous release of 56 %
(228.4 mg g-1) protein fraction under the combined
sonication and hydrolysis treatment. The amount of proteins
released during the fermentation of combined sonicated-
hydrolyzed biomass was significantly different as compared
to proteins liberated from untreated and sonicated alone
(***P\ 0.0001). The dissolved protein concentration was
increased up to 51.6, 108 and 228.5 mg g-1 during fer-
mentation of the untreated, sonicated, and sonicated-hy-
drolyzed microalgae biomass, respectively (Fig. 5).
Scanning and transmission electron microscopic
examinations
Scanning and transmission electron microscopes were used
to observe the cell integrity after the pretreatments. Scan-
ning electron microscopy (SEM) analysis revealed ultra-
Fig. 4 Concentration of dissolved protein released during combined
sonication and enzymatic hydrolysis
Table 1 Comparison of the results reported in previous studies with the results of this study for TRS production from algae by enzymatic
hydrolysis
Enzyme pH Temp �C Substrate Total reducing sugar (TRS)
yield
References
Pectinase (p4716) 4 35 Teraselmis suecica 400.0 mg (g biomass)-1 [46]
Cellulase (C1 U/mg) 4.8 40 Chlorococum humicola 64.2 % (w/w) [24]
Novozyme 188 (263 CBU/g) ? Celluclast 1.5 L
(798 EGU/g)
4.8 50 Eucheuma cottonii 327.2 mg (g biomass)-1 [20]
Cellulase (C1 U/mg) 5 50 Chlamydomonas
mexicana
280.5 mg (g biomass)-1 This study
Cellulase (22119) 4.8 45 Ulva fasciata 206.0 mg (g biomass)-1 [47]
Cellulase (10 U/g) ? b-glucosidase (5 U/g) 5 30 Parthenium
hysterophorus
187.4 mg (g biomass)-1 [23]
Novozyme 188 (263 CBU/g) ? Celluclast 1.5 L
(798 EGU/g)
4.5 55 Nannochloropsis
gaditana
129 mg (g biomass)-1 [1]
Cellulase (50 FPU/g) ? b-glucosidase (250 CBU/g) 4.8 50 Sargassum sp. 120 mg (g biomass)-1 [42]
Cellulase (20 FPU/g) ? b-glucosidase (60 U/g) 5 50 Gracilaria verrucosa 870 mg (g cellulose)-1 [39]
(Celluclast 1.5 L, Novoprime B957), ?
Amyloglucosidase (300L)
5.5 55 Dunaliella tertiolecta
LB999
42.0 % (w/w) [48]
Bioprocess Biosyst Eng
123
structural changes in C. mexicana during sonication and
enzymatic hydrolysis. As shown in Fig. 6a, the surface of
untreated sample was smooth and continuous. The soni-
cated samples showed partially ruptured cell wall (Fig. 6b),
while enzymatic hydrolysis increased the rupturing of cell
wall. The cell wall of sonicated-hydrolyzed cells appeared
to be thinner after enzymatic hydrolysis, indicating the
release of carbohydrate constituents of cell wall into the
medium (Fig. 6c).
Transmission electron microscope (TEM) images
showed that algae cells were lysed to a greater extent by
enzymatic hydrolysis compared to sonication (Fig. 6). The
nucleus materials in the nucleus membrane were clearly
visible and well defined for the untreated algae (Fig. 6d).
The nucleus materials in the sonicated microalgae (Fig. 6e)
were less spread throughout the cell interior compared to
enzymatic hydrolyzed microalgal cells where some of the
nucleus materials were spread outside the cell and were
accumulated within the algal periplasm because of the
complete lysis of the nucleus membrane. Enzymatic
hydrolysis altered the morphology of the microalgae cells,
which is in agreement with a previous study [48]. The TEM
micrographs of untreated C. mexicana showed well-defined
shapes with typical smooth surfaces and the outline of a
regular cell wall (Fig. 6d). The cell wall was disintegrated
after hydrolysis with the release of cell wall-associated
carbohydrates and proteins into the exo-cellular medium
(Fig. 6f). This finding confirmed the disintegration of the
samples’ cellulosic structure due to the enzymatic con-
version of cellulose to its constituent sugars [19].
Fig. 5 Effect of carbohydrate fermentation on protein release of
untreated, sonicated and combined sonicated-hydrolyzed microalgal
biomass. (Condition; 37 �C, 120 rpm for 3 days). Values are a mean
of three experiments ± SEM. The amount of proteins released during
the fermentation of sonicated-hydrolyzed biomass was significantly
different compared to untreated and sonicated treatment biomass
(***P\ 0.0001)
Fig. 6 SEM and TEM images showing the destruction of the cell
wall on the microalgae surfaces and in periplasm. SEM images of
untreated (a), SEM images of sonication treated (b), SEM images of
sonication and enzyme hydrolysis treated (c), TEM images of
untreated (d), TEM images of sonication treated (e), and TEM
images of sonication and enzyme hydrolysis treated (f), Chlamy-
domonas mexicana cells after 24 h of hydrolysis under optimized
conditions
Bioprocess Biosyst Eng
123
Conclusion
The combined sonication and enzymatic hydrolysis pre-
treatment of microalgae C. mexicana enhanced the release
of TRS and dissolved protein fractions up to 53 and 7 %
compared to sonication alone (14 and 2.3 %), respectively.
Fermentation of the TRS fraction enhanced the dissolved
protein fraction up to 56 %. SEM and TEM analyses
confirmed the complete cell distraction by combined son-
ication and enzyme hydrolysis treatment. These results
demonstrate that the combined sonication and enzymatic
hydrolysis pretreatment enhances the conversion of
microalgae biomass to soluble sugar, and subsequent fer-
mentation of the sugar residues significantly increases the
release of microalgal proteins. Such approach will render
the algae-based biofuel technology cost effective by
increasing the conversion of microalgae biomass to feed-
stocks (TRS and protein) for bioalcohol production.
Acknowledgments This work was supported by the Mid-career
Researchers Program (the National Research Foundation of Korea,
2013069183).
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