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FULL LENGTH ARTICLE
Evaluation of the potential for some isolated
microalgae to produce biodiesel
Eman A. Mahmoud a,*, Laila A. Farahat a
, Zeinab K. Abdel Aziz b
,
Nesreen A. Fatthallah a
, Rawheya A. Salah El Din b
a
Egyptian Petroleum Research Institute, Processes Development Department, Petroleum Biotechnology Lab, Egypt
b
Al-Azhar University (Girls Branch), Faculty of Science, Botany and Microbiology Department, Egypt
Received 17 August 2014; accepted 26 October 2014
Available online 13 April 2015
KEYWORDS
Biodiesel;
Lipid;
Microalgae
Abstract The energy and the world food crises have ignited interest in algal culture for making
biodiesel, bioethanol, biobutanol and other biofuels using the land that is not suitable for
agriculture. Algal fuel is an alternative to fossil fuel that uses algae as its source of natural deposits.
Microalgal lipids are the oils of the future for sustainable biodiesel production. One of the most
important roles in obtaining oil from microalgae is the choice of species. A total of fifteen microal-
gal isolates, obtained from brackish and fresh waters, were assayed at the laboratory for their ability
to high biomass productivity and lipid content. Only three microalgae were selected as the most
potent isolates for biomass and lipid production. They have been identified as Chlorella vulgaris,
Scenedesmus quadri and Trachelomonas oblonga. All of them were cultivated on BG11 media and
harvested by centrifugation. The dry weight of the three isolates was recorded as 1.23, 1.09 and
0.9 g/l while the lipid contents were 37%, 34% and 29%, respectively which can be considered a
promising biomass production and lipid content.
ª 2015 The Authors. Production and hosting by Elsevier B.V. on behalf of Egyptian Petroleum Research
Institute. This is an open access article under the CC BY-NC-ND license (http://creativecommons.org/
licenses/by-nc-nd/4.0/).
1. Introduction
Depletion of world petroleum reserves and the impact of
environmental pollution by increasing exhaust emissions have
led to the search for suitable alternative fuels for diesel engines
[1]. Biodiesel is an alternative to diesel fuel, which is produced
from oils via transesterification. Currently, it is being recog-
nized as a green and alternative renewable diesel fuel that
has attracted vast interest from researchers, governments,
and local and international traders [2]. It is nontoxic,
biodegradable and has the potential to replace the conven-
tional diesel fuel. Presently, biodiesel is produced from different
crops, such as, soybean, rapeseed, sunflower, palm, coconut,
jatropha, karanja, used fried oil and animal fats [3]. There will
be certain limitations in the use of these oils as alternate fuels
because of its food demand, life span, lower yield, higher land
usage and higher price inter alia [4]. It is necessary to search for
non food based alternate feedstocks for biodiesel production.
Selection of biodiesel feedstock is based on higher yields, short
duration, lower production cost and less land usage. Among
various biodiesel feedstocks, the microalgae oil has the
* Corresponding author.
E-mail address: Em_micro81@yahoo.com (E.A. Mahmoud).
Peer review under responsibility of Egyptian Petroleum Research
Institute.
Egyptian Journal of Petroleum (2015) 24, 97–101
HOSTED BY
Egyptian Petroleum Research Institute
Egyptian Journal of Petroleum
www.elsevier.com/locate/egyjp
www.sciencedirect.com
http://dx.doi.org/10.1016/j.ejpe.2015.02.010
1110-0621 ª 2015 The Authors. Production and hosting by Elsevier B.V. on behalf of Egyptian Petroleum Research Institute.
This is an open access article under the CC BY-NC-ND license (http://creativecommons.org/licenses/by-nc-nd/4.0/).
potential to replace the conventional diesel fuel. Microalgae
have been suggested as a potential feedstock for fuel produc-
tion because of a number of advantages, including higher
photosynthetic efficiency, higher biomass production, and
higher growth rates, as compared to other energy crops [5].
The interest in microalgae for oil production is due to the high
lipid content of many species, and also to the fact that lipid
synthesis, especially of the non-polar triacylglycerols (TAGs),
which are the best substrate to produce biodiesel, can be
modulated by varying growth conditions. Biodiesel production
from microalgal biomass is a sequential process that consists of
the cultivation, harvest, oil extraction, and conversion of
algal lipids into advanced biofuels [4]. A key consideration is
the choice of algal strain. The growth characteristics and
composition of microalgae are known to significantly depend
on the cultivation conditions. There are four major types of
cultivation conditions for microalgae: photoautotrophic,
heterotrophic, mixotrophic and photoheterotrophic cultiva-
tion [6]. Phototrophic cultivation occurs when the microalgae
use light, such as sunlight, as the energy source, and inorganic
carbon (e.g., carbon dioxide) as the carbon source to form
chemical energy through photosynthesis [5]. This is the most
commonly used cultivation condition for microalgae growth
[7,8]. Harvesting of microalgae is seen as one of the major
challenges of using microalgae for the production of biodiesel.
Microalgae that store lipids have low densities and are found
in suspension making separation difficult. Large scale extrac-
tion procedures for microalgal lipids are complex and still in
the developmental stage [9]. Microalgal oil can be extracted
chemically or mechanically, similar to other oleaginous
biomass. Usually physical extraction requires an additional
chemical as a solvent to enhance the extraction process. The
most popular solvents include hexane or chloroform and
alcohol. The combination of polar and non-polar solvents
enhances the extraction of both polar and non-polar lipids.
Crude microalgal oil is especially high in viscosity, thus requir-
ing conversion to lower molecular weight constituents in the
form of fatty acid alkyl esters. Transesterification converts
raw microalgal lipid (triacylglycerols/free fatty acids) into
renewable, non-toxic and biodegradable biodiesel for direct
consumption by unmodified diesel engines [9]. This research
is an attempt to grow and develop different microalgal strains
having promising dry weight and lipid content to produce
valuable biodiesel.
2. Materials and methods
2.1. Samples: Collection and analysis
Water samples used to isolate microalgae were collected asep-
tically from sites that appeared to contain algal bloom. About
eight different water samples were collected from different
locations in Egypt, four of them from Giza Governorate at dif-
ferent sites in Mariotya symbolized as (Pm, Spm, Dpm and
Cm), one from Sharqawia canal in Qaliubia Governorate
(Scq) and one from Canal water in Qaliubia (Ck). Another
sample was collected from Cairo Governorate Kupri El kuba
(Gk) and also one from Ain Elsira (As). Samples were gath-
ered from about a diameter of 10 cm under the water surface
and placed in sterile plastic bags, then transported to the lab-
oratory within 24 h of collection.
2.2. Physical and chemical analyses of water samples
The Physical and chemical properties of the water samples
were determined at Central Lab, Egyptian Petroleum
Research Institute. Anions and cations were determined
according to ASTM D-4327 and 6919, respectively using an
ion chromatography. The instrument used was Dionex IC
model ICS 1100 equipped with high capacity columns (AS9
and CS12) for anions and cations respectively, TDS was deter-
mined according to ASTM D-1888.pH was determined
according to ASTM D-1293 using a digital pH meter model
metler Toledo-Seven Go. Alkaline species (CO3, OH, HCO3)
were measured according to ASTM D-3875. Calculations were
done using Alkalinity calculator Ver. 2.10 (USGS).
2.3. Isolation, purification and identification of microalgae
Ten ml of water sample was transferred to a 500 ml conical
flask containing 250 ml of sterilized BG 11 medium [10]. The
flasks were incubated on a rotary orbital shaker at 150 rpm
under continuous illumination using white fluorescent light
at intensities of 3000 Lux for three weeks. Every two days,
the flasks were examined for algal growth using an optical
microscope. Subcultures were made by inoculating 50 ll of cul-
ture solution onto Petri plates containing the same isolation
media solidified with 1.5% (w/v) of bacteriological agar. The
purity of the culture was confirmed by repeated plating, also
by repeated observation under a microscope. The obtained iso-
lates were identified microscopically according to Prescott [11].
2.4. Determination of microalgae growth
After the Microalgal cultivation on BG11 medium under the
previous conditions, the microalgae growth was determined
by measuring optical density at a wavelength of 685 nm [12]
(denoted as OD 685) using a spectrophotometer (model jen-
way 6300, Eu). The dry cell weight (DCW) of microalgae bio-
mass was also obtained by filtering 50 ml of aliquots of culture
through a cellulose acetate membrane filter (0.45 lm pore size,
47 mm in diameter). Each loaded filter was dried at 105 °C
until the stability of weight is reached. The dry weight of the
blank filter was subtracted from that of the loaded filter to
obtain the microalgae dry cell weight.
2.5. Lipid extraction and fatty acid analyses
The total lipids were extracted from the fresh microalgal bio-
mass using a slightly modified method of Bligh and Dyer
[13]. In brief, 50 ml of microalgae culture was harvested by
centrifugation at 10,000 rpm for 5 min, re-suspended in 1 ml
of distilled water. After drying the samples using oven, the
samples were extracted using a mixture of chloroform: metha-
nol (1:1. v/v). The mixtures were transferred into a separating
funnel and shaken for 5 min, an additional portion of chloro-
form (the same volume) was added and the extraction mixture
was shaken again for 5 min. To separate the chloroform and
aqueous methanol layers, a same volume of water was added
and then centrifuged at 10,000 rpm for 10 min. The chloro-
form layer was gently removed from the bottom, and a second
extraction was performed. The chloroform portions were
98 E.A. Mahmoud et al.
collected and washed with 5 ml of 5% NaCl solution and
evaporated in an oven at 50 °C to dryness. Thereafter, the
weight of the crude lipid obtained from each sample was mea-
sured gravimetrically.
2.5.1. Fatty acid analysis
The fatty acid profile of the extracted oil sample of all species
was determined by converting the fatty acids in the oil to fatty
acid methyl esters (FAMEs). The FAME composition was
determined using a Gas-Chromatography (GC) with a split
automatic injector and silica capillary column DB-5 (length:
60 m; ID: 0.32 mm.). Details of the procedure have been
described according to Lepage and Roy (1986 and 1988)
[14,15]. Helium was used as carrier gas at a flow rate of
1 ml/min. The column was held at 150 °C for 1 min and
ramped to 240 °C at a rate of 30 °C/min, and it was then held
at 240 °C for 30 min. Standards were used to give rise to well
individualized peaks that allow the identification of the fatty
acid composition.
3. Results and discussion
3.1. Samples, collection and analysis
Microalgae are ubiquitous organisms present in all existing
earth ecosystems, not only aquatic, but also terrestrial,
representing a large variety of species living in a wide range
of environmental conditions [16]. The physical and chemical
properties results of eight water samples from different sites
were determined at Central Lab, Egyptian Petroleum
Research Institute which are shown in Table 1.
The concentration of dissolved solids (TDS) in stream
water is important because it determines the flow of water in
and out of the cells of aquatic organisms. Aforesaid output
data showed the variation of TDS results which revealed the
difference of water sample nature, for example, the high
TDS value for AS, GK, PM, SPM and DPM samples means
that it is brackish water, while its value for SCQ, CM and
CK samples reflects the fresh nature of the sample. Also, we
noticed the variation of nitrate and phosphate percentages
from sample to another which affected the Microalgal isolates,
types and characterization. Concentrations of nitrogen com-
pounds in the culture media can regulate a degree of intra-
cellular lipid/triglyceride accumulations [17–19].
3.2. Isolation, purification and identification of microalgae
In our study, more than twenty-eight isolates were isolated
from the collected water samples but only fifteen axenic
microalgae isolates were selected and sub-cultured on slants
on its specific isolation media (BG11) and kept in a refrigerator
for further investigation due to their purity. According to mor-
phological examination under a microscope based on cell
shapes, fifteen microalgal isolates were identified as, Chlorella
vulgaris Pm, Scenedesmus quadricauda Scq, Microcystis aerugi-
nosa Spm, Chlorella sp.Spm3, Chlorella sp.Spm5, M. aerugi-
nosa Dpm Chlorella sp. Cm, Chlorella sp. Ck, Trachelomonas
oblonga Ck, M. aeruginosa Ck, Haematococcus pluvialis Gk,
M. aeruginosa As, Chlorella sp. Scq, M. aeruginosa Gk,
Chlorella sp. Dpm, respectively.
N.B: The symbol after algal name refereed to the isolation
place.
3.3. Biomass and lipid content
One of the most important decisions in obtaining oil from
microalgae is the choice of species. Accordingly; all the fifteen
purified strains were screened for their lipid content and mass
productivity (Figs. 1 and 2). Among all isolates, C. vulgaris
Pm, S. quadricauda Scq and T. oblonga Ck were the most
potent isolates. The dry weight of the three isolates were
recorded as 1.23, 1.09 and 0.9 g/l while the lipid contents were
37%, 34% and 29%, respectively which can be considered a
promising biomass production and lipid content. Rodolfi
et al. (2009) and Reda et al. (2011) recorded that lipid content
of fresh water microalgae was nearly 20% [19,20]. Several
microalgae species can be induced to accumulate substantial
lipid quantities to obtain high oil yields. However, some differ-
ences exist among various species, and even within the same
genus [21]. From Figs. 1 and 2, it can be clearly observed that,
some isolates may be similar to T. oblonga or slightly more in
dry weight and lipid content but this strain was selected
because of its behavior stability.
3.4. Growth rate of microalgal strains
Under suitable conditions and sufficient nutrients, microalgae
can richly grow. Usually, they double their biomass within
Table 1 Physical and chemical properties of the collected water samples.
Water sample AS CK CM DPM GK PM SCQ SPM
Analysis
Physical properties
Total dissolved solids (TDS) mg/l 8493 856 948 5387 7678 1280 355 4993.2
pH @ 25° C 8.3 7.58 8.3 7.47 7.77 8.16 8.06 8.33
Salinity mg/l 3839.6 491.7 288.8 2197.8 5933.4 478.5 105.3 1793.6
Hardness mg/l 2822.1 321.7 327 1376.9 2410.7 510.6 177.3 1376.9
Chemical properties (mg/l)
Nitrate 0.34 5.3 1.36° 0.358 Nil 0.22 Nil 0.358
Phosphate 0.02 0.61 0.77 0.06 0.04 1 0.2 0.08
Chloride 2327 298 175 1332 3596 290 63.8 1087
Sodium 1472 110.4 135.19 1194 1803 155 35.56 1046
Magnesium 217.8 34.89 17.59 96.6 221.25 43.12 11.72 96.6
Biodiesel production ability assessment of microalgae 99
3.5 h or 24 h during the exponential growth phase [22]. The
pure growth rate differed among the examined microalgal spe-
cies (Fig. 3). Algal growth is directly affected by the availabil-
ity of nutrients, light, the stability of pH, and temperature [23].
Under similar environmental conditions, the average specific
growth rates of 5.728 and 5.525 were found for S. quadricauda
Scq and T. oblonga Ck respectively at 680 nm after 29 day
incubation compared with 11.721 for C. vulgaris Pm. This
result indicates that, C. vulgaris Pm, S. quadricauda Scq and
T. oblonga Ck strains were suitable for high-density cultures.
3.5. Fatty acid composition
Fatty acid compositions determine biodiesel properties, owing
to the chemical features of fatty acids, such as carbon chain
length and unsaturation extent. Therefore, fatty acid profiles
for the most potent strains were determined (Table 2). The
most important unsaturated fatty acids present in microalgal
Figure 1 Dry weight of the fifteen microalgal isolates.
Figure 2 Lipid content of the fifteen microalgal isolates.
Figure 3 Growth curve of the three most potent microalgal strains.
Table 2 Fatty acid profile (% of total FAMEs) (Saturated
and unsaturated fatty acids) of three most potent microalgal
strains.
Fatty acids Chlorella
vulgaris
Scenedesmus
quadricauda
Trachelomonas
oblonga
C12:0 1.95 3.9 2.78
C14:0 1.88 1.76 1.49
C14:1 ND ND 2.48
C16:0 10.35 22.02 15.86
C16:1 10.75 3.77 10.37
C16:2 7.27 ND ND
C17:0 12.94 2.11 12.35
C17:1 ND 1.8 1.03
C18:0 6.53 4.84 4.67
C18:1 6.80 25.97 8.42
C18:2 26.28 15.25 30.00
C18:3 10.45 12.05 8.02
C20:0 2.21 ND ND
Saturated 35.85 34.67 37.16
Unsaturated 61.53 58.83 52.31
Total even
carbon
84.44 89.6 76.1
ND: Undetectable.
100 E.A. Mahmoud et al.
strains are, palmitoleic acid (C16:1), oleic acid (C18:1), lenoleic
acid (C18:2) and linolenic (C18:3). These results comply with
Knothe, 2008 who said that oleic acid, palmitoleic and palmitic
acid were recognized as the most common fatty acids con-
tained in microalgal lipid [24]. Oleic acid was found in the high
concentration which reached to 25.97% for S. quadricauda
Scq, and lenoleic acid was high in T. oblonga Ck reaching up
to 30.00%. Palmitoleic acid, oleic acid, lenoleic acid and lino-
lenic acid were found in all algal species. Oils with high oleic
acid contents have been reported to have a reasonable balance
of fuel, including its ignition quality, combustion heat, cold fil-
ter plugging point (CFPP), oxidative stability, viscosity, and
lubricity, which are determined by the structure of its fatty
esters component [25,24]. Therefore, among the tested microal-
gal species, S. quadricauda Scq showed the highest oleic acid
content, making it the most suitable for the production of
good quality biodiesel.
4. Conclusions
The total lipid content and net biomass productivity in
microalgae vary greatly from one species to another although
they belong to the same algal group. So, it is very important to
screen microalgal strains before the selection of the suitable
strain for the application. Three strains from 15 microalgal iso-
lates were selected due to their high lipid content, mass produc-
tion and ease of cultivation; they are C. vulgaris Pm, S.
quadricauda Scq and T. oblonga Ck. The composition of fatty
acids in the studied species was mainly C12:0, C16:0, C16:1,
C18:1, C18:2 and C18:3. The results of this study indicate that
the naturally isolated microalgae C. vulgaris Pm, S. quadri-
cauda Scq and T. oblonga Ck are valuable candidates for use
in biodiesel production.
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Biodiesel production ability assessment of microalgae 101

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Evaluation

  • 1. FULL LENGTH ARTICLE Evaluation of the potential for some isolated microalgae to produce biodiesel Eman A. Mahmoud a,*, Laila A. Farahat a , Zeinab K. Abdel Aziz b , Nesreen A. Fatthallah a , Rawheya A. Salah El Din b a Egyptian Petroleum Research Institute, Processes Development Department, Petroleum Biotechnology Lab, Egypt b Al-Azhar University (Girls Branch), Faculty of Science, Botany and Microbiology Department, Egypt Received 17 August 2014; accepted 26 October 2014 Available online 13 April 2015 KEYWORDS Biodiesel; Lipid; Microalgae Abstract The energy and the world food crises have ignited interest in algal culture for making biodiesel, bioethanol, biobutanol and other biofuels using the land that is not suitable for agriculture. Algal fuel is an alternative to fossil fuel that uses algae as its source of natural deposits. Microalgal lipids are the oils of the future for sustainable biodiesel production. One of the most important roles in obtaining oil from microalgae is the choice of species. A total of fifteen microal- gal isolates, obtained from brackish and fresh waters, were assayed at the laboratory for their ability to high biomass productivity and lipid content. Only three microalgae were selected as the most potent isolates for biomass and lipid production. They have been identified as Chlorella vulgaris, Scenedesmus quadri and Trachelomonas oblonga. All of them were cultivated on BG11 media and harvested by centrifugation. The dry weight of the three isolates was recorded as 1.23, 1.09 and 0.9 g/l while the lipid contents were 37%, 34% and 29%, respectively which can be considered a promising biomass production and lipid content. ª 2015 The Authors. Production and hosting by Elsevier B.V. on behalf of Egyptian Petroleum Research Institute. This is an open access article under the CC BY-NC-ND license (http://creativecommons.org/ licenses/by-nc-nd/4.0/). 1. Introduction Depletion of world petroleum reserves and the impact of environmental pollution by increasing exhaust emissions have led to the search for suitable alternative fuels for diesel engines [1]. Biodiesel is an alternative to diesel fuel, which is produced from oils via transesterification. Currently, it is being recog- nized as a green and alternative renewable diesel fuel that has attracted vast interest from researchers, governments, and local and international traders [2]. It is nontoxic, biodegradable and has the potential to replace the conven- tional diesel fuel. Presently, biodiesel is produced from different crops, such as, soybean, rapeseed, sunflower, palm, coconut, jatropha, karanja, used fried oil and animal fats [3]. There will be certain limitations in the use of these oils as alternate fuels because of its food demand, life span, lower yield, higher land usage and higher price inter alia [4]. It is necessary to search for non food based alternate feedstocks for biodiesel production. Selection of biodiesel feedstock is based on higher yields, short duration, lower production cost and less land usage. Among various biodiesel feedstocks, the microalgae oil has the * Corresponding author. E-mail address: Em_micro81@yahoo.com (E.A. Mahmoud). Peer review under responsibility of Egyptian Petroleum Research Institute. Egyptian Journal of Petroleum (2015) 24, 97–101 HOSTED BY Egyptian Petroleum Research Institute Egyptian Journal of Petroleum www.elsevier.com/locate/egyjp www.sciencedirect.com http://dx.doi.org/10.1016/j.ejpe.2015.02.010 1110-0621 ª 2015 The Authors. Production and hosting by Elsevier B.V. on behalf of Egyptian Petroleum Research Institute. This is an open access article under the CC BY-NC-ND license (http://creativecommons.org/licenses/by-nc-nd/4.0/).
  • 2. potential to replace the conventional diesel fuel. Microalgae have been suggested as a potential feedstock for fuel produc- tion because of a number of advantages, including higher photosynthetic efficiency, higher biomass production, and higher growth rates, as compared to other energy crops [5]. The interest in microalgae for oil production is due to the high lipid content of many species, and also to the fact that lipid synthesis, especially of the non-polar triacylglycerols (TAGs), which are the best substrate to produce biodiesel, can be modulated by varying growth conditions. Biodiesel production from microalgal biomass is a sequential process that consists of the cultivation, harvest, oil extraction, and conversion of algal lipids into advanced biofuels [4]. A key consideration is the choice of algal strain. The growth characteristics and composition of microalgae are known to significantly depend on the cultivation conditions. There are four major types of cultivation conditions for microalgae: photoautotrophic, heterotrophic, mixotrophic and photoheterotrophic cultiva- tion [6]. Phototrophic cultivation occurs when the microalgae use light, such as sunlight, as the energy source, and inorganic carbon (e.g., carbon dioxide) as the carbon source to form chemical energy through photosynthesis [5]. This is the most commonly used cultivation condition for microalgae growth [7,8]. Harvesting of microalgae is seen as one of the major challenges of using microalgae for the production of biodiesel. Microalgae that store lipids have low densities and are found in suspension making separation difficult. Large scale extrac- tion procedures for microalgal lipids are complex and still in the developmental stage [9]. Microalgal oil can be extracted chemically or mechanically, similar to other oleaginous biomass. Usually physical extraction requires an additional chemical as a solvent to enhance the extraction process. The most popular solvents include hexane or chloroform and alcohol. The combination of polar and non-polar solvents enhances the extraction of both polar and non-polar lipids. Crude microalgal oil is especially high in viscosity, thus requir- ing conversion to lower molecular weight constituents in the form of fatty acid alkyl esters. Transesterification converts raw microalgal lipid (triacylglycerols/free fatty acids) into renewable, non-toxic and biodegradable biodiesel for direct consumption by unmodified diesel engines [9]. This research is an attempt to grow and develop different microalgal strains having promising dry weight and lipid content to produce valuable biodiesel. 2. Materials and methods 2.1. Samples: Collection and analysis Water samples used to isolate microalgae were collected asep- tically from sites that appeared to contain algal bloom. About eight different water samples were collected from different locations in Egypt, four of them from Giza Governorate at dif- ferent sites in Mariotya symbolized as (Pm, Spm, Dpm and Cm), one from Sharqawia canal in Qaliubia Governorate (Scq) and one from Canal water in Qaliubia (Ck). Another sample was collected from Cairo Governorate Kupri El kuba (Gk) and also one from Ain Elsira (As). Samples were gath- ered from about a diameter of 10 cm under the water surface and placed in sterile plastic bags, then transported to the lab- oratory within 24 h of collection. 2.2. Physical and chemical analyses of water samples The Physical and chemical properties of the water samples were determined at Central Lab, Egyptian Petroleum Research Institute. Anions and cations were determined according to ASTM D-4327 and 6919, respectively using an ion chromatography. The instrument used was Dionex IC model ICS 1100 equipped with high capacity columns (AS9 and CS12) for anions and cations respectively, TDS was deter- mined according to ASTM D-1888.pH was determined according to ASTM D-1293 using a digital pH meter model metler Toledo-Seven Go. Alkaline species (CO3, OH, HCO3) were measured according to ASTM D-3875. Calculations were done using Alkalinity calculator Ver. 2.10 (USGS). 2.3. Isolation, purification and identification of microalgae Ten ml of water sample was transferred to a 500 ml conical flask containing 250 ml of sterilized BG 11 medium [10]. The flasks were incubated on a rotary orbital shaker at 150 rpm under continuous illumination using white fluorescent light at intensities of 3000 Lux for three weeks. Every two days, the flasks were examined for algal growth using an optical microscope. Subcultures were made by inoculating 50 ll of cul- ture solution onto Petri plates containing the same isolation media solidified with 1.5% (w/v) of bacteriological agar. The purity of the culture was confirmed by repeated plating, also by repeated observation under a microscope. The obtained iso- lates were identified microscopically according to Prescott [11]. 2.4. Determination of microalgae growth After the Microalgal cultivation on BG11 medium under the previous conditions, the microalgae growth was determined by measuring optical density at a wavelength of 685 nm [12] (denoted as OD 685) using a spectrophotometer (model jen- way 6300, Eu). The dry cell weight (DCW) of microalgae bio- mass was also obtained by filtering 50 ml of aliquots of culture through a cellulose acetate membrane filter (0.45 lm pore size, 47 mm in diameter). Each loaded filter was dried at 105 °C until the stability of weight is reached. The dry weight of the blank filter was subtracted from that of the loaded filter to obtain the microalgae dry cell weight. 2.5. Lipid extraction and fatty acid analyses The total lipids were extracted from the fresh microalgal bio- mass using a slightly modified method of Bligh and Dyer [13]. In brief, 50 ml of microalgae culture was harvested by centrifugation at 10,000 rpm for 5 min, re-suspended in 1 ml of distilled water. After drying the samples using oven, the samples were extracted using a mixture of chloroform: metha- nol (1:1. v/v). The mixtures were transferred into a separating funnel and shaken for 5 min, an additional portion of chloro- form (the same volume) was added and the extraction mixture was shaken again for 5 min. To separate the chloroform and aqueous methanol layers, a same volume of water was added and then centrifuged at 10,000 rpm for 10 min. The chloro- form layer was gently removed from the bottom, and a second extraction was performed. The chloroform portions were 98 E.A. Mahmoud et al.
  • 3. collected and washed with 5 ml of 5% NaCl solution and evaporated in an oven at 50 °C to dryness. Thereafter, the weight of the crude lipid obtained from each sample was mea- sured gravimetrically. 2.5.1. Fatty acid analysis The fatty acid profile of the extracted oil sample of all species was determined by converting the fatty acids in the oil to fatty acid methyl esters (FAMEs). The FAME composition was determined using a Gas-Chromatography (GC) with a split automatic injector and silica capillary column DB-5 (length: 60 m; ID: 0.32 mm.). Details of the procedure have been described according to Lepage and Roy (1986 and 1988) [14,15]. Helium was used as carrier gas at a flow rate of 1 ml/min. The column was held at 150 °C for 1 min and ramped to 240 °C at a rate of 30 °C/min, and it was then held at 240 °C for 30 min. Standards were used to give rise to well individualized peaks that allow the identification of the fatty acid composition. 3. Results and discussion 3.1. Samples, collection and analysis Microalgae are ubiquitous organisms present in all existing earth ecosystems, not only aquatic, but also terrestrial, representing a large variety of species living in a wide range of environmental conditions [16]. The physical and chemical properties results of eight water samples from different sites were determined at Central Lab, Egyptian Petroleum Research Institute which are shown in Table 1. The concentration of dissolved solids (TDS) in stream water is important because it determines the flow of water in and out of the cells of aquatic organisms. Aforesaid output data showed the variation of TDS results which revealed the difference of water sample nature, for example, the high TDS value for AS, GK, PM, SPM and DPM samples means that it is brackish water, while its value for SCQ, CM and CK samples reflects the fresh nature of the sample. Also, we noticed the variation of nitrate and phosphate percentages from sample to another which affected the Microalgal isolates, types and characterization. Concentrations of nitrogen com- pounds in the culture media can regulate a degree of intra- cellular lipid/triglyceride accumulations [17–19]. 3.2. Isolation, purification and identification of microalgae In our study, more than twenty-eight isolates were isolated from the collected water samples but only fifteen axenic microalgae isolates were selected and sub-cultured on slants on its specific isolation media (BG11) and kept in a refrigerator for further investigation due to their purity. According to mor- phological examination under a microscope based on cell shapes, fifteen microalgal isolates were identified as, Chlorella vulgaris Pm, Scenedesmus quadricauda Scq, Microcystis aerugi- nosa Spm, Chlorella sp.Spm3, Chlorella sp.Spm5, M. aerugi- nosa Dpm Chlorella sp. Cm, Chlorella sp. Ck, Trachelomonas oblonga Ck, M. aeruginosa Ck, Haematococcus pluvialis Gk, M. aeruginosa As, Chlorella sp. Scq, M. aeruginosa Gk, Chlorella sp. Dpm, respectively. N.B: The symbol after algal name refereed to the isolation place. 3.3. Biomass and lipid content One of the most important decisions in obtaining oil from microalgae is the choice of species. Accordingly; all the fifteen purified strains were screened for their lipid content and mass productivity (Figs. 1 and 2). Among all isolates, C. vulgaris Pm, S. quadricauda Scq and T. oblonga Ck were the most potent isolates. The dry weight of the three isolates were recorded as 1.23, 1.09 and 0.9 g/l while the lipid contents were 37%, 34% and 29%, respectively which can be considered a promising biomass production and lipid content. Rodolfi et al. (2009) and Reda et al. (2011) recorded that lipid content of fresh water microalgae was nearly 20% [19,20]. Several microalgae species can be induced to accumulate substantial lipid quantities to obtain high oil yields. However, some differ- ences exist among various species, and even within the same genus [21]. From Figs. 1 and 2, it can be clearly observed that, some isolates may be similar to T. oblonga or slightly more in dry weight and lipid content but this strain was selected because of its behavior stability. 3.4. Growth rate of microalgal strains Under suitable conditions and sufficient nutrients, microalgae can richly grow. Usually, they double their biomass within Table 1 Physical and chemical properties of the collected water samples. Water sample AS CK CM DPM GK PM SCQ SPM Analysis Physical properties Total dissolved solids (TDS) mg/l 8493 856 948 5387 7678 1280 355 4993.2 pH @ 25° C 8.3 7.58 8.3 7.47 7.77 8.16 8.06 8.33 Salinity mg/l 3839.6 491.7 288.8 2197.8 5933.4 478.5 105.3 1793.6 Hardness mg/l 2822.1 321.7 327 1376.9 2410.7 510.6 177.3 1376.9 Chemical properties (mg/l) Nitrate 0.34 5.3 1.36° 0.358 Nil 0.22 Nil 0.358 Phosphate 0.02 0.61 0.77 0.06 0.04 1 0.2 0.08 Chloride 2327 298 175 1332 3596 290 63.8 1087 Sodium 1472 110.4 135.19 1194 1803 155 35.56 1046 Magnesium 217.8 34.89 17.59 96.6 221.25 43.12 11.72 96.6 Biodiesel production ability assessment of microalgae 99
  • 4. 3.5 h or 24 h during the exponential growth phase [22]. The pure growth rate differed among the examined microalgal spe- cies (Fig. 3). Algal growth is directly affected by the availabil- ity of nutrients, light, the stability of pH, and temperature [23]. Under similar environmental conditions, the average specific growth rates of 5.728 and 5.525 were found for S. quadricauda Scq and T. oblonga Ck respectively at 680 nm after 29 day incubation compared with 11.721 for C. vulgaris Pm. This result indicates that, C. vulgaris Pm, S. quadricauda Scq and T. oblonga Ck strains were suitable for high-density cultures. 3.5. Fatty acid composition Fatty acid compositions determine biodiesel properties, owing to the chemical features of fatty acids, such as carbon chain length and unsaturation extent. Therefore, fatty acid profiles for the most potent strains were determined (Table 2). The most important unsaturated fatty acids present in microalgal Figure 1 Dry weight of the fifteen microalgal isolates. Figure 2 Lipid content of the fifteen microalgal isolates. Figure 3 Growth curve of the three most potent microalgal strains. Table 2 Fatty acid profile (% of total FAMEs) (Saturated and unsaturated fatty acids) of three most potent microalgal strains. Fatty acids Chlorella vulgaris Scenedesmus quadricauda Trachelomonas oblonga C12:0 1.95 3.9 2.78 C14:0 1.88 1.76 1.49 C14:1 ND ND 2.48 C16:0 10.35 22.02 15.86 C16:1 10.75 3.77 10.37 C16:2 7.27 ND ND C17:0 12.94 2.11 12.35 C17:1 ND 1.8 1.03 C18:0 6.53 4.84 4.67 C18:1 6.80 25.97 8.42 C18:2 26.28 15.25 30.00 C18:3 10.45 12.05 8.02 C20:0 2.21 ND ND Saturated 35.85 34.67 37.16 Unsaturated 61.53 58.83 52.31 Total even carbon 84.44 89.6 76.1 ND: Undetectable. 100 E.A. Mahmoud et al.
  • 5. strains are, palmitoleic acid (C16:1), oleic acid (C18:1), lenoleic acid (C18:2) and linolenic (C18:3). These results comply with Knothe, 2008 who said that oleic acid, palmitoleic and palmitic acid were recognized as the most common fatty acids con- tained in microalgal lipid [24]. Oleic acid was found in the high concentration which reached to 25.97% for S. quadricauda Scq, and lenoleic acid was high in T. oblonga Ck reaching up to 30.00%. Palmitoleic acid, oleic acid, lenoleic acid and lino- lenic acid were found in all algal species. Oils with high oleic acid contents have been reported to have a reasonable balance of fuel, including its ignition quality, combustion heat, cold fil- ter plugging point (CFPP), oxidative stability, viscosity, and lubricity, which are determined by the structure of its fatty esters component [25,24]. Therefore, among the tested microal- gal species, S. quadricauda Scq showed the highest oleic acid content, making it the most suitable for the production of good quality biodiesel. 4. Conclusions The total lipid content and net biomass productivity in microalgae vary greatly from one species to another although they belong to the same algal group. So, it is very important to screen microalgal strains before the selection of the suitable strain for the application. Three strains from 15 microalgal iso- lates were selected due to their high lipid content, mass produc- tion and ease of cultivation; they are C. vulgaris Pm, S. quadricauda Scq and T. oblonga Ck. The composition of fatty acids in the studied species was mainly C12:0, C16:0, C16:1, C18:1, C18:2 and C18:3. The results of this study indicate that the naturally isolated microalgae C. vulgaris Pm, S. quadri- cauda Scq and T. oblonga Ck are valuable candidates for use in biodiesel production. References [1] Y. Sahin, Energy Educ. Sci. Technol. A 26 (2011) 129–142. [2] A. Demirbas, Energy Convers. Manage. 50 (2009) 14–34. [3] S.A. Khan, Rashmi, M.Z. Hussain, S. Prasad, U.C. Banerjee, Renew. Sustain. Energy Rev 13 (2009) 2361–2372. [4] T.M. Mata, A.A. Martins, N.S. Caetano, Renew. Sustain. Energy Rev 14 (2010) 217–232. [5] GuanHua Huang, Feng Chen, Dong Wei, XueWu Zhang, Gu Chen, Appl. Energy 87 (2010) 38–46. [6] K. Chojnacka, F.J. Marquez-Rocha, Biotechnology 3 (2004) 21–34. [7] L. Gouveia, A.E. Marques, T.L. da Silva, A. Reis, J. Ind. Microb. Biotechnol. 36 (2009) 821–826. [8] C. Yoo, S.Y. Jun, J.Y. Lee, C.Y. Ahn, H.M. Oh, Bioresour. Technol. 101 (2010) S71–S74. [9] I. Rawat, R. Ranjith Kumar, T. Mutanda, F. Bux, Appl. Energy 88 (2011) 3411–3424. [10] B. Wang, A. Zarka, A. Trebst, S. Boussiba, J. Phycol. 39 (2003) 1116–1124. [11] G.W. Prescott, Algae of the Western Great Lakes Area, Fifth ed., W.M.C. Brown Publishers, Dubuque, Iowa, 1973. [12] L. Wang, M. Min, Y. Li, P. Chen, Y. Chen, Y. Liu, Y. Wang, R. Ruan, Appl. Biochem. Biotechnol. 162 (4) (2009) 1174–1186. [13] E.G. Bligh, W.J. Dyer, Can. J. Biochem. Physiol. 37 (1959) 911– 917. [14] G. Lepage, C.C. Roy, J. Lipid Res. 27 (1986) 114–120. [15] G. Lepage, C.C. Roy, J. Lipid Res. 29 (1988) 227–234. [16] E.B. Sydney, T.E. da Silva, A. Tokarski, A.C. Novak, J.C. deCarvalho, A.L. Woiciecohwski, et al, Appl. Energy (2010) 11–24, doi: 1016/j.apenergy. [17] M. Limonet, S. Saffroy, F. Maujean, M. Linder, S. Delaunay, Process Biochem. 42 (2007) 700–703. [18] J. Pruvost, G. Van Vooren, G. Cogne, J. Legrand, Bioresour. Technol. 100 (2009) 5988–5995. [19] L. Rodolfi, G.C. Zittelli, N. Bassi, G. Padovani, N. Biondi, G. Bonini, M.R. Tredici, Biotechnol. Bioeng. 102 (2009) 100–112. [20] A.I. Reda, J.H. Abou-Shanab, C. Yunchul, M. Booki, J. Byong- Hun, Appl. Energy (2011). [21] F.X. Malcata, Trend Biotechnol. 29 (2011) 542–549. [22] Y. Chisti, Biotechnol. Adv. 25 (2007) 294–306. [23] L. Wang, L. Yecong, P. Chen, M. Min, Y. Chen, J. Zhu, et al, Bioresour. Technol. 101 (2010) 2623–2628. [24] G. Knothe, Energy Fuels 22 (2008) 1358–1364. [25] S. Stournas, E. Lois, A. Serdari, J. Am. Oil Chem. Soc. 472 (1995) 433. Biodiesel production ability assessment of microalgae 101