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J Ind Microbiol Biotechnol (2009) 36:269–274
DOI 10.1007/s10295-008-0495-6

 ORIGINAL PAPER



Microalgae as a raw material for biofuels production
Luisa Gouveia · Ana Cristina Oliveira




Received: 1 August 2008 / Accepted: 14 October 2008 / Published online: 4 November 2008
© Society for Industrial Microbiology 2008


Abstract Biofuels demand is unquestionable in order to                increase (»50%) in oil quantity. If the purpose is to
reduce gaseous emissions (fossil CO2, nitrogen and sulfur             produce biodiesel only from one species, Scenedesmus
oxides) and their purported greenhouse, climatic changes              obliquus presents the most adequate fatty acid proWle,
and global warming eVects, to face the frequent oil supply            namely in terms of linolenic and other polyunsaturated fatty
crises, as a way to help non-fossil fuel producer countries to        acids. However, the microalgae Neochloris oleabundans,
reduce energy dependence, contributing to security of sup-            Nannochloropsis sp. and Dunaliella tertiolecta can also be
ply, promoting environmental sustainability and meeting               used if associated with other microalgal oils and/or vegeta-
the EU target of at least of 10% biofuels in the transport            ble oils.
sector by 2020. Biodiesel is usually produced from oleagi-
nous crops, such as rapeseed, soybean, sunXower and palm.             Keywords Neochloris oleoabundans · Scenedesmus
However, the use of microalgae can be a suitable alterna-             obliquus · Nannochloropsis sp. · Dunaliella tertiolecta ·
tive feedstock for next generation biofuels because certain           Lipids · Biofuels · Biodiesel
species contain high amounts of oil, which could be
extracted, processed and reWned into transportation fuels,
using currently available technology; they have fast growth           Introduction
rate, permit the use of non-arable land and non-potable
water, use far less water and do not displace food crops cul-         Finding suYcient supplies of clean energy for the future is
tures; their production is not seasonal and they can be har-          one of society’s most daunting challenges and is intimately
vested daily. The screening of microalgae (Chlorella                  linked with global stability, economic prosperity, and qual-
vulgaris, Spirulina maxima, Nannochloropsis sp., Neochl-              ity of life.
oris oleabundans, Scenedesmus obliquus and Dunaliella                    Fuels represent around 70% of the total global energy
tertiolecta) was done in order to choose the best one(s), in          requirements, particularly in transportation, manufacturing
terms of quantity and quality as oil source for biofuel pro-          and domestic heating. Electricity only accounts at present
duction. Neochloris oleabundans (fresh water microalga)               for 30% of global energy consumption.
and Nannochloropsis sp. (marine microalga) proved to be                  In the European Union (EU), the transport sector is
suitable as raw materials for biofuel production, due to their        responsible for almost one quarter of greenhouse gas emis-
high oil content (29.0 and 28.7%, respectively). Both mic-            sions [15] and it is, therefore, essential to Wnd ways of
roalgae, when grown under nitrogen shortage, show a great             reducing emissions. Vehicles must be cleaner and more fuel
                                                                      eYcient and the use of biofuels can also play an important
                                                                      role in avoiding the excessive dependence on fossil fuels
L. Gouveia (&) · A. C. Oliveira                                       and ensuring security of supply, in promoting environmen-
Departamento de Energias Renováveis,                                  tal sustainability and meeting the target of at least of 10%
Instituto Nacional de Engenharia,
                                                                      by 2020 for biofuels in the transport sector. Biodiesel fuel
Tecnologia e Inovação, Estrada do Paço do Lumiar,
22, 1649-038 Lisbon, Portugal                                         has received considerable attention in recent years, as it is
e-mail: luisa.gouveia@ineti.pt                                        made from non-toxic, biodegradable and renewable

                                                                                                                        123
270                                                                                     J Ind Microbiol Biotechnol (2009) 36:269–274


resources, and provides environmental beneWts, since its        Table 2 Lipid content of some microalgae (% dry matter) (adapted
use leads to a decrease in the harmful emissions of carbon      from [3, 18, 21, 23, 26, 33, 35, 38])
monoxide, hydrocarbons and particulate matter and to the        Species                                                Lipids
elimination of SOx emissions, with a consequent decrease
in the greenhouse eVect, in line with the Kyoto Protocol        Scenedesmus obliquus                                   11–22/35–55
agreement. Biodiesel is usually produced from oleaginous        Scenedesmus dimorphus                                  6–7/16–40
crops, such as rapeseed, soybean, sunXower and from palm,       Chlorella vulgaris                                     14–40/56
through a chemical transesteriWcation process of their oils     Chlorella emersonii                                    63
with short chain alcohols, mainly methanol [1, 2, 19, 30].      Chlorella protothecoides                               23/55
   However, the use of microalgae can be a suitable alter-      Chlorella sorokiana                                    22
native because algae are the most eYcient biological pro-       Chlorella minutissima                                  57
ducer of oil on the planet and a versatile biomass source       Dunaliella bioculata                                   8
and may soon be one of the Earth’s most important renew-        Dunaliella salina                                      14–20
able fuel crops [6], due to the higher photosynthetic           Neochloris oleoabundans                                35–65
eYciency, higher biomass productivities, a faster growth        Spirulina maxima                                       4–9
rate than higher plants (which is also important in the
screening step), highest CO2 Wxation and O2 production,
growing in liquid medium which can be handled easily, can       biodiesel production with high oxidation stability [11, 16, 24,
be grown in variable climates and non-arable land includ-       25]. The physical and fuel properties of biodiesel from micro-
ing marginal areas unsuitable for agricultural purposes (e.g.   algal oil in general (e.g. density, viscosity, acid value, heating
desert and seashore lands), in non-potable water or even as     value, etc.), are comparable to those of fuel diesel [23, 27].
a waste treatment purpose, use far less water than tradi-          Key technical challenges include identifying the strains
tional crops and do not displace food crop cultures; their      with the highest growth rates and oil content with adequate
production is not seasonal and can be harvested daily [6–8].    composition, which were the aim of this work. Oil extrac-
   As a matter of fact, average biodiesel production yield      tion procedure was selected and the fatty acid proWle
from microalgae can be 10 to 20 times higher than the yield     analyzed for all microalgae tested. The oil was also charac-
obtained from oleaginous seeds and/or vegetable oils [7,        terized in terms of its iodine value, a parameter that must be
34] (Table 1).                                                  considered if biodiesel production is the purpose.
   Some microalgae have high oil content (Table 2) and
can be induced to produce higher concentration of lipids
(e.g. low nitrogen media, Fe3+concentration and light inten-    Materials and methods
sity) [18, 21, 28, 32, 35].
   The ability of algae to Wx CO2 can also be an interesting    Microalgae production
method of removing gases from power plants, and thus can
be used to reduce greenhouse gases with a higher produc-        The microalgae used in this study were Chlorella vulgaris
tion microalgal biomass and consequently higher biodiesel       (INETI 58), Spirulina maxima (LB 2342), Nannochloropsis
yield [22, 39]. Algal biomass production systems can be         sp., Neochloris oleabundans (UTEX # 1185, USA), Scene-
easily adapted to various levels of operational and techno-     desmus obliquus (FCTU Coimbra) and Dunaliella tertio-
logical skills; some microalgae have also a convenient fatty    lecta (IPIMAR). The microalgae were cultivated in
acids proWle and an unsaponiWable fraction allowing a           appropriate growth medium [37]. All the microalgae tested
                                                                were initially grown in airlift bioreactors and then in poly-
                                                                ethylene bags with bubbling air under low lighting condi-
Table 1 Comparison of some
sources of biodiesel [7]
                                 Crop               Oil yield   tions (150 E m¡2 s¡1), at the optimal temperature for each
                                                    (L ha¡1)    microalga (indoors), and Wnally in outdoor raceways agi-
                                 Corn                   172     tated by paddle wheels, during 4 months (May–August).
                                 Soybean                446     For N. oleabundans and Nannochloropsis sp. growth was
                                 Canola               1,190     also performed under N-starvation during 5 days, after
                                 Jatropha             1,892     removing culture medium (initially NaNO3 = 0.25 g L¡1
                                 Coconut              2,689
                                                                and KNO3 = 0.2 g L¡1 as N-sources for N. oleabundans
                                 Palm                 5,950
                                                                and Nannochloropsis, respectively) by centrifugation and
                                                                re-inoculating it in N-deWcient medium. Microalgal
                                 Microalgaea        136,900
a
    70% oil (by wt) in biomass                                  biomass harvesting was processed without Xocculation by
b
                                 Microalgaeb         58,700
    30% oil (by wt) in biomass                                  simply removing agitation and concentrating by centrifugation


123
J Ind Microbiol Biotechnol (2009) 36:269–274                                                                                               271


(Beckman Avanti, J-25I (small volumes) and Alfa-Laval                    Iodine value
LAPX202 (big volumes)) and freeze-dried.
                                                                         Oils from microalgae were characterized in terms of iodine
Growth evaluation                                                        value according to the European Standard EN 14111 [13].

Growth parameters such as optical density (OD) (540 nm)
(Hitachi U-2000) and ash free dry weight (AFDW) (What-                   Results and discussion
man GF/C 45 m) were measured three times a week.
                                                                         Microalgal biomass maximum concentration reached by all
Oil extraction                                                           microalgae ranged between 2 g L¡1 (Neochloris oleabun-
                                                                         dans and Scenedesmus obliquus in polyethylene bags) and
Oil extraction from microalgal biomass was performed in a                3.6 g L¡1 (Dunnaliella in polyethylene bags) (Table 3)
Soxhlet apparatus using n-hexane as solvent with sample                  according to other authors [17, 29, 36]. Average concentra-
pre-treatment (propanol) after cell disruption by sonication             tion and productivities were similar for all microalgae tested
during 20 min. These conditions were established after                   ranging from 1.0–2.6 to 0.1–0.2 g L¡1 day¡1, respectively.
selection from a wide range of procedures and by compari-                   The results of extraction methods, from a previous study,
son with the results obtained with the Bligh and Dyer                    indicated that the best procedure is Soxhlet with n-hexane
extraction method [5].                                                   as a solvent. In terms of pre-treatment, propanol has a posi-
                                                                         tive eVect on oil extraction (results not shown). For micro-
Oil characterization                                                     algal cell disruption, the ultrasonic method is more eYcient
                                                                         than vortex and homogeneizer.
Fatty acid composition                                                      The tested microalgae strains revealed similar average,
                                                                         maximum biomass concentration and productivities
To determine the fatty acid composition of each raw mate-                (Table 3) and it can be seen that Nannochloropsis sp. and
rial, oil samples (»150 mg) (in duplicate) were chemically               Neochloris oleabundans are the strains with the highest oil
derivatized using the borum triXuoride method described in               content, in agreement with literature [7, 29, 35].
the EN ISO 5509 [12]. The organic phase obtained was                        Fatty acid proWle was determined for all microalgae and
analyzed by gaseous chromatography using a CP-3800 GC                    the results are presented in Table 4. All microalgal lipids
(Varian, USA) equipped with 30 m DB-WAX (J&W, Agi-                       are mainly composed of unsaturated fatty acids (50–65%)
lent) capillary column (0.25 mm of internal diameter and                 and a signiWcant percentage of palmitic acid (C16:0) was
0.25 m of Wlm thickness). Injector (split 1:100) and detec-              also present (17–40%). Among the unsaturated fatty acids
tor (Xame ionization) temperatures were kept constant at                 special attention should be taken to the linolenic (C18:3)
250°C. The oven temperature program started at 180°C for                 and polyunsaturated (¸4 double bonds) contents, due to the
5 min, increased at 4°C min¡1 until 220°C, and kept con-                 EN 14214 [14] that speciWes a limit of 12 and 1%, respec-
stant at this temperature for 25 min. Carrier gas, He, was               tively, for a quality biodiesel. As can be seen from Table 4,
kept at a constant rate of 1 mL min¡1. Fatty acid composi-               only the oils extracted from S. obliquus and Nannochlorop-
tion was calculated as percentage of the total fatty acids               sis sp. present linolenic acid contents within speciWcations.
present in the sample, determined from the peak areas.                   The oil of S. obliquus also has a lower polyunsaturated fatty




Table 3 Microalgal biomass average concentration, biomass maximum concentration, productivities and microalgal biomass oil content
                       Average biomass                      Maximum biomass                       Productivities                 Oil content
                       concentration (g L¡1)                concentration (g L¡1)                 (g L¡1 day¡1)                  (%) (AFDW)

Sp                     2.0                                  3.1                                   0.21                            4.1
Cv                     1.5                                  3.0                                   0.18                            5.1
Sc                     0.9                                  2.0                                   0.09                           17.7
Dt                     2.6                                  3.6                                   0.12                           16.7
Nanno                  1.6                                  2.5                                   0.09                           28.7
Neo                    1.5                                  2.0                                   0.09                           29.0
Sp, Spirulina maxima; Cv, Chlorella vulgaris; Sc, Scenedesmus obliquus; Dt, Dunaliella tertiolecta; Nanno, Nannochloropsis sp.; Neo, Neochloris
oleabundans


                                                                                                                                   123
272                                                                                              J Ind Microbiol Biotechnol (2009) 36:269–274


Table 4 Main fatty acids present in Spirulina maxima (Sp), Chlorella vulgaris (Cv), Scenedesmus obliquus (Sc), Dunaliella tertiolecta (Dt), Nan-
nochloropsis sp. (Nanno) and Neochloris oleabundans (Neo) oil extracts
Fatty acid        Sp (% w w¡1)           Cv (% w w¡1)        Sc (% w w¡1)         Dt (% w w¡1)         Nanno (% w w¡1)         Neo (% w w¡1)

14:0                0.34                 3.07                 1.48                 0.47                 7.16                    0.43
16:0              40.16                  25.07               21.78                17.70                23.35                   19.35
16:1                9.19                 5.25                 5.95                 0.88                26.87                    1.85
16:2                n.d.                 n.d.                 3.96                 3.03                 0.39                    1.74
16:3                0.42                 1.27                 0.68                 1.24                 0.48                    0.96
16:4                0.16                 4.06                 0.43                10.56                 n.d.                    7.24
18:0                1.18                 0.63                 0.45                 n.d.                 0.45                    0.98
18:1                5.43                 12.64               17.93                 4.87                13.20                   20.29
18:2              17.89                  7.19                21.74                12.37                 1.21                   12.99
18:3              18.32                  19.05                3.76                30.19                 n.d.                   17.43
18:4                0.08                 n.d.                 0.21                 n.d.                 n.d.                    2.10
20:0                0.06                 0.09                 n.d.                 n.d.                 n.d.                    n.d.
20:1                n.d.                 0.93                 n.d.                 n.d.                 n.d.                    n.d.
20:2                0.48                 n.d.                 n.d.                 n.d.                 n.d.                    n.d.
20:3                n.d.                 0.83                 n.d.                 n.d.                 n.d.                    n.d.
20:4                n.d.                 0.23                 n.d.                 n.d.                 2.74                    n.d.
20:5                n.d.                 0.46                 n.d.                 n.d.                14.31                    n.d.
Saturated         41.74                  28.56               23.71                18.17                30.96                   20.76
Unsaturated       51.97                  51.91               54.66                63.14                59.20                   64.60



Table 5 Microalgal iodine values                                          such as nitrogen limitation, and high Fe3+ concentration and
                     Sc            Dt            Nanno          Neo
                                                                          light intensity.
                                                                              To reduce microalgal biomass overall production costs,
Iodine value         69            121           52             102       the biomass cake remaining after oil has been extracted can
Sc, Scenedesmus obliquus; Dt, Dunaliella tertiolecta; Nanno, Nanno-       be used as fertilizer or feed, can undergo anaerobic fermen-
chloropsis sp.; Neo, Neochloris oleabundans                               tation to obtain biogas and/or a pyrolysis process, or to
                                                                          extract high value chemical compounds (bioreWnery con-
acid content than the value referred by the European stan-                cept) [7, 8, 10, 27]. Ran and Spada [27] suggest that to
dard. However, all the analyzed microalgae oils may be                    make plants accessible to small producers, such as agricul-
used for good quality biodiesel if associated with other oils,            tural farms, in the near future, could integrate this concept
or without restrictions as raw material for other biofuels                in order to obtain biofuels, electricity and feed for live-
production processes.                                                     stock.
   The oils obtained from the microalgae with higher oil                      The global biodiesel market is estimated to reach 37 bil-
content were characterized in terms of iodine value                       lion gallons by 2016, growing at an average annual growth
(Table 5). The obtained results meet the biodiesel quality                of 42%, being Europe the major biodiesel market for the
speciWcations (<120 gI2/100 g) [13] which makes these                     next decade or so, closely followed by US market [31]. In
microalgae oils competitive with some vegetable oils tradi-               order to meet these rapid expansion in biodiesel production
tionally used for biodiesel production as soy or sunXower,                capacity, observed not only in develop countries but also in
that usually present iodine values higher than 120.                       developing countries such as China, Brasil, Argentina,
   Neochloris oleabundans cultivated under nitrogen short-                Indonesia and Malaysia, other oil sources, especially non-
age, after 5 days of nitrogen starvation (results not shown),             edible oils, need to be explored [20]. Microalgae seems to
showed a fatty acid content increase of »50% with no sig-                 be the only source of renewable biodiesel that has the
niWcant change in fatty acid proWle indicating this is a high             potential to completely displace petroleum-derived trans-
potential microalga for biofuel production purposes. These                port fuels without the controversial argument “food for
results are in agreement with other studies, see, e.g. Illman             fuel” and to reach the 2003 Biofuels Directive target,
et al. [18], Liu et al. [21], RudolW et al. [28], Solovchenco             achieving more than a 35% minimum greenhouse gas sav-
et al. [32], and Tornabene et al.[35] that reported an                    ings (this value represents the diminishing impact of oleag-
increase of oil content as a response of stress conditions,               inous crops including the land use change) [7–9]. Some


123
J Ind Microbiol Biotechnol (2009) 36:269–274                                                                                              273


time around the end of 2009 or in early 2010 is when small,               7. Chisti Y (2007) Biodiesel from microalgae. Biotechnol Adv
commercial-scale algae-based systems for biodiesel pro-                      25:294–306. doi:10.1016/j.biotechadv.2007.02.001
                                                                          8. Chisti Y (2008) Biodiesel from microalgae beats bioethanol.
duction are likely to start entering the mainstream [4]. US                  Trends Biotechnol 26:126–131. doi:10.1016/j.tibtech.2007. 12.002
and EU may realize their visions to replace up to 20% of                  9. Cockerill S, Martin C (2008) Are biofuels sustainable? The EU
transports fuels by 2020 by using environmentally and eco-                   perspective. Biotechnol Biofuels 1:9. doi:10.1186/1754-6834-1-9
nomically sustainable biofuels from algae [4].                           10. Danielo O (2005) An algae-based fuel. Biofuture 255:1–4
                                                                         11. Dote Y, Sawayama S, Inoue S, Minowa T, Yokoyama S (1994)
                                                                             Recovery of liquid fuel from hydrocarbon-rich microalgae by ther-
                                                                             mochemical liquefaction. Fuel 73:1855–1857. doi:10.1016/0016-
Conclusions                                                                  2361(94)90211-9
                                                                         12. European Standard EN 5509 (2000) Animal and vegetable fats and
                                                                             oils—preparation of methyl esters of fatty acids
Microalgal biodiesel is technically feasible and to be eco-              13. European Standard EN 14111 (2003) Fat and oil derivatives—
nomic competitive with petrodiesel, microalgal production,                   fatty acid methyl esters (FAME)—determination of iodine value
harvesting and extraction must be optimized, as well as                  14. European Standard EN 14214 (2004) Automotive fuels—fatty
improvements to algal biology through genetic and meta-                      acid methyl esters (FAME) for diesel engines—requirements and
                                                                             test methods
bolic engineering. The use of the bioreWnery concept and                 15. Eurostat (2007) Online database of the European Union, 2920
advances in photobioreactor engineering will further lower                   Luxembourg. http://epp.eurostat.ec.europa.eu. Accessed 8 May
the cost of production.                                                      2007
   From the microalgae tested in this work, Neochloris ole-              16. Ginzburg BZ (1993) Liquid fuel (oil) from halophilic algae: a
                                                                             renewable source of non-polluting energy. Renew Energy 3:249–
abundans and Nannochloropsis sp. proved to be suitable as                    252. doi:10.1016/0960-1481(93)90031-B
raw materials for biofuels production, due to their high oil             17. Hu Q, Guterman H, Richmond A (1996) A Xat inclined modular
content (29.0 and 28.7%, respectively). They are fresh                       photobioreactor for outdoor mass cultivation of photoautotrophs.
water and marine microalgae, respectively, which enlarge                     Biotechnol      Bioeng     51:51–60     10.1002/(SICI)1097-0290
                                                                             (19960705)51:1<;51::AID-BIT6>;3.0.CO;2-#
the environmental cultivation possibilities and do not com-              18. Illman AM, Scragg AH, Shales SW (2000) Increase in Chlorella
pete with food crops.                                                        strains caloriWc values when grown in low nitrogen medium.
   Both microalgae, when grown under N-deWcient culture                      Enzyme Microb Technol 27:631–635. doi:10.1016/S0141-0229
medium, show a great increase in oil quantity (e.g. Neochl-                  (00)00266-0
                                                                         19. Lang X, Dalai AK, Bakhshi NN, Reaney MJ, Hertz PB (2001)
oris oleabundans can reach 56%, results not shown).                          Preparation and characterization of bio-diesels from various bio-
   If the purpose is to produce biodiesel from one algal spe-                oils. Bioresour Technol 8:53–62. doi:10.1016/S0960-8524(01)
cies, Scenedesmus obliquus presents the most adequate fatty                  00051-7
acid proWle, namely in terms of linolenic and polyunsatu-                20. Li Q, Du W, Liu D (2008) Perspectives of microbial oils for
                                                                             biodiesel production. Appl Microbiol Biotechnol 80:749–756.
rated fatty acids. However, Neochloris oleabundans, Nanno-                   doi:10.1007/s00253-008-1625-9
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associated with other microalgae oils and/or vegetable oils.                 accumulation in Chlorella vulgaris. Bioresour Technol 99:4717–
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Acknowledgments The authors would like to acknowledge Doutora            22. Maeda K, Owada M, Kimura N, Omata K, Karube J (1995) CO2
Narcisa Bandarra from IPIMAR for the fatty acid analysis and also            Wxation from the Xue gas on coal—red thermal power plant by
Mrs. Ana Melo and Mr. Roberto Medeiros for the experimental work.            microalgae. Energy Convers Manage 36:717–720. doi:10.1016/
                                                                             0196-8904(95)00105-M
                                                                         23. Miao X, Wu Q (2006) Biodiesel production from heterotrophic
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123

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Microalgae as a Raw Material For Biofuels Production

  • 1. J Ind Microbiol Biotechnol (2009) 36:269–274 DOI 10.1007/s10295-008-0495-6 ORIGINAL PAPER Microalgae as a raw material for biofuels production Luisa Gouveia · Ana Cristina Oliveira Received: 1 August 2008 / Accepted: 14 October 2008 / Published online: 4 November 2008 © Society for Industrial Microbiology 2008 Abstract Biofuels demand is unquestionable in order to increase (»50%) in oil quantity. If the purpose is to reduce gaseous emissions (fossil CO2, nitrogen and sulfur produce biodiesel only from one species, Scenedesmus oxides) and their purported greenhouse, climatic changes obliquus presents the most adequate fatty acid proWle, and global warming eVects, to face the frequent oil supply namely in terms of linolenic and other polyunsaturated fatty crises, as a way to help non-fossil fuel producer countries to acids. However, the microalgae Neochloris oleabundans, reduce energy dependence, contributing to security of sup- Nannochloropsis sp. and Dunaliella tertiolecta can also be ply, promoting environmental sustainability and meeting used if associated with other microalgal oils and/or vegeta- the EU target of at least of 10% biofuels in the transport ble oils. sector by 2020. Biodiesel is usually produced from oleagi- nous crops, such as rapeseed, soybean, sunXower and palm. Keywords Neochloris oleoabundans · Scenedesmus However, the use of microalgae can be a suitable alterna- obliquus · Nannochloropsis sp. · Dunaliella tertiolecta · tive feedstock for next generation biofuels because certain Lipids · Biofuels · Biodiesel species contain high amounts of oil, which could be extracted, processed and reWned into transportation fuels, using currently available technology; they have fast growth Introduction rate, permit the use of non-arable land and non-potable water, use far less water and do not displace food crops cul- Finding suYcient supplies of clean energy for the future is tures; their production is not seasonal and they can be har- one of society’s most daunting challenges and is intimately vested daily. The screening of microalgae (Chlorella linked with global stability, economic prosperity, and qual- vulgaris, Spirulina maxima, Nannochloropsis sp., Neochl- ity of life. oris oleabundans, Scenedesmus obliquus and Dunaliella Fuels represent around 70% of the total global energy tertiolecta) was done in order to choose the best one(s), in requirements, particularly in transportation, manufacturing terms of quantity and quality as oil source for biofuel pro- and domestic heating. Electricity only accounts at present duction. Neochloris oleabundans (fresh water microalga) for 30% of global energy consumption. and Nannochloropsis sp. (marine microalga) proved to be In the European Union (EU), the transport sector is suitable as raw materials for biofuel production, due to their responsible for almost one quarter of greenhouse gas emis- high oil content (29.0 and 28.7%, respectively). Both mic- sions [15] and it is, therefore, essential to Wnd ways of roalgae, when grown under nitrogen shortage, show a great reducing emissions. Vehicles must be cleaner and more fuel eYcient and the use of biofuels can also play an important role in avoiding the excessive dependence on fossil fuels L. Gouveia (&) · A. C. Oliveira and ensuring security of supply, in promoting environmen- Departamento de Energias Renováveis, tal sustainability and meeting the target of at least of 10% Instituto Nacional de Engenharia, by 2020 for biofuels in the transport sector. Biodiesel fuel Tecnologia e Inovação, Estrada do Paço do Lumiar, 22, 1649-038 Lisbon, Portugal has received considerable attention in recent years, as it is e-mail: luisa.gouveia@ineti.pt made from non-toxic, biodegradable and renewable 123
  • 2. 270 J Ind Microbiol Biotechnol (2009) 36:269–274 resources, and provides environmental beneWts, since its Table 2 Lipid content of some microalgae (% dry matter) (adapted use leads to a decrease in the harmful emissions of carbon from [3, 18, 21, 23, 26, 33, 35, 38]) monoxide, hydrocarbons and particulate matter and to the Species Lipids elimination of SOx emissions, with a consequent decrease in the greenhouse eVect, in line with the Kyoto Protocol Scenedesmus obliquus 11–22/35–55 agreement. Biodiesel is usually produced from oleaginous Scenedesmus dimorphus 6–7/16–40 crops, such as rapeseed, soybean, sunXower and from palm, Chlorella vulgaris 14–40/56 through a chemical transesteriWcation process of their oils Chlorella emersonii 63 with short chain alcohols, mainly methanol [1, 2, 19, 30]. Chlorella protothecoides 23/55 However, the use of microalgae can be a suitable alter- Chlorella sorokiana 22 native because algae are the most eYcient biological pro- Chlorella minutissima 57 ducer of oil on the planet and a versatile biomass source Dunaliella bioculata 8 and may soon be one of the Earth’s most important renew- Dunaliella salina 14–20 able fuel crops [6], due to the higher photosynthetic Neochloris oleoabundans 35–65 eYciency, higher biomass productivities, a faster growth Spirulina maxima 4–9 rate than higher plants (which is also important in the screening step), highest CO2 Wxation and O2 production, growing in liquid medium which can be handled easily, can biodiesel production with high oxidation stability [11, 16, 24, be grown in variable climates and non-arable land includ- 25]. The physical and fuel properties of biodiesel from micro- ing marginal areas unsuitable for agricultural purposes (e.g. algal oil in general (e.g. density, viscosity, acid value, heating desert and seashore lands), in non-potable water or even as value, etc.), are comparable to those of fuel diesel [23, 27]. a waste treatment purpose, use far less water than tradi- Key technical challenges include identifying the strains tional crops and do not displace food crop cultures; their with the highest growth rates and oil content with adequate production is not seasonal and can be harvested daily [6–8]. composition, which were the aim of this work. Oil extrac- As a matter of fact, average biodiesel production yield tion procedure was selected and the fatty acid proWle from microalgae can be 10 to 20 times higher than the yield analyzed for all microalgae tested. The oil was also charac- obtained from oleaginous seeds and/or vegetable oils [7, terized in terms of its iodine value, a parameter that must be 34] (Table 1). considered if biodiesel production is the purpose. Some microalgae have high oil content (Table 2) and can be induced to produce higher concentration of lipids (e.g. low nitrogen media, Fe3+concentration and light inten- Materials and methods sity) [18, 21, 28, 32, 35]. The ability of algae to Wx CO2 can also be an interesting Microalgae production method of removing gases from power plants, and thus can be used to reduce greenhouse gases with a higher produc- The microalgae used in this study were Chlorella vulgaris tion microalgal biomass and consequently higher biodiesel (INETI 58), Spirulina maxima (LB 2342), Nannochloropsis yield [22, 39]. Algal biomass production systems can be sp., Neochloris oleabundans (UTEX # 1185, USA), Scene- easily adapted to various levels of operational and techno- desmus obliquus (FCTU Coimbra) and Dunaliella tertio- logical skills; some microalgae have also a convenient fatty lecta (IPIMAR). The microalgae were cultivated in acids proWle and an unsaponiWable fraction allowing a appropriate growth medium [37]. All the microalgae tested were initially grown in airlift bioreactors and then in poly- ethylene bags with bubbling air under low lighting condi- Table 1 Comparison of some sources of biodiesel [7] Crop Oil yield tions (150 E m¡2 s¡1), at the optimal temperature for each (L ha¡1) microalga (indoors), and Wnally in outdoor raceways agi- Corn 172 tated by paddle wheels, during 4 months (May–August). Soybean 446 For N. oleabundans and Nannochloropsis sp. growth was Canola 1,190 also performed under N-starvation during 5 days, after Jatropha 1,892 removing culture medium (initially NaNO3 = 0.25 g L¡1 Coconut 2,689 and KNO3 = 0.2 g L¡1 as N-sources for N. oleabundans Palm 5,950 and Nannochloropsis, respectively) by centrifugation and re-inoculating it in N-deWcient medium. Microalgal Microalgaea 136,900 a 70% oil (by wt) in biomass biomass harvesting was processed without Xocculation by b Microalgaeb 58,700 30% oil (by wt) in biomass simply removing agitation and concentrating by centrifugation 123
  • 3. J Ind Microbiol Biotechnol (2009) 36:269–274 271 (Beckman Avanti, J-25I (small volumes) and Alfa-Laval Iodine value LAPX202 (big volumes)) and freeze-dried. Oils from microalgae were characterized in terms of iodine Growth evaluation value according to the European Standard EN 14111 [13]. Growth parameters such as optical density (OD) (540 nm) (Hitachi U-2000) and ash free dry weight (AFDW) (What- Results and discussion man GF/C 45 m) were measured three times a week. Microalgal biomass maximum concentration reached by all Oil extraction microalgae ranged between 2 g L¡1 (Neochloris oleabun- dans and Scenedesmus obliquus in polyethylene bags) and Oil extraction from microalgal biomass was performed in a 3.6 g L¡1 (Dunnaliella in polyethylene bags) (Table 3) Soxhlet apparatus using n-hexane as solvent with sample according to other authors [17, 29, 36]. Average concentra- pre-treatment (propanol) after cell disruption by sonication tion and productivities were similar for all microalgae tested during 20 min. These conditions were established after ranging from 1.0–2.6 to 0.1–0.2 g L¡1 day¡1, respectively. selection from a wide range of procedures and by compari- The results of extraction methods, from a previous study, son with the results obtained with the Bligh and Dyer indicated that the best procedure is Soxhlet with n-hexane extraction method [5]. as a solvent. In terms of pre-treatment, propanol has a posi- tive eVect on oil extraction (results not shown). For micro- Oil characterization algal cell disruption, the ultrasonic method is more eYcient than vortex and homogeneizer. Fatty acid composition The tested microalgae strains revealed similar average, maximum biomass concentration and productivities To determine the fatty acid composition of each raw mate- (Table 3) and it can be seen that Nannochloropsis sp. and rial, oil samples (»150 mg) (in duplicate) were chemically Neochloris oleabundans are the strains with the highest oil derivatized using the borum triXuoride method described in content, in agreement with literature [7, 29, 35]. the EN ISO 5509 [12]. The organic phase obtained was Fatty acid proWle was determined for all microalgae and analyzed by gaseous chromatography using a CP-3800 GC the results are presented in Table 4. All microalgal lipids (Varian, USA) equipped with 30 m DB-WAX (J&W, Agi- are mainly composed of unsaturated fatty acids (50–65%) lent) capillary column (0.25 mm of internal diameter and and a signiWcant percentage of palmitic acid (C16:0) was 0.25 m of Wlm thickness). Injector (split 1:100) and detec- also present (17–40%). Among the unsaturated fatty acids tor (Xame ionization) temperatures were kept constant at special attention should be taken to the linolenic (C18:3) 250°C. The oven temperature program started at 180°C for and polyunsaturated (¸4 double bonds) contents, due to the 5 min, increased at 4°C min¡1 until 220°C, and kept con- EN 14214 [14] that speciWes a limit of 12 and 1%, respec- stant at this temperature for 25 min. Carrier gas, He, was tively, for a quality biodiesel. As can be seen from Table 4, kept at a constant rate of 1 mL min¡1. Fatty acid composi- only the oils extracted from S. obliquus and Nannochlorop- tion was calculated as percentage of the total fatty acids sis sp. present linolenic acid contents within speciWcations. present in the sample, determined from the peak areas. The oil of S. obliquus also has a lower polyunsaturated fatty Table 3 Microalgal biomass average concentration, biomass maximum concentration, productivities and microalgal biomass oil content Average biomass Maximum biomass Productivities Oil content concentration (g L¡1) concentration (g L¡1) (g L¡1 day¡1) (%) (AFDW) Sp 2.0 3.1 0.21 4.1 Cv 1.5 3.0 0.18 5.1 Sc 0.9 2.0 0.09 17.7 Dt 2.6 3.6 0.12 16.7 Nanno 1.6 2.5 0.09 28.7 Neo 1.5 2.0 0.09 29.0 Sp, Spirulina maxima; Cv, Chlorella vulgaris; Sc, Scenedesmus obliquus; Dt, Dunaliella tertiolecta; Nanno, Nannochloropsis sp.; Neo, Neochloris oleabundans 123
  • 4. 272 J Ind Microbiol Biotechnol (2009) 36:269–274 Table 4 Main fatty acids present in Spirulina maxima (Sp), Chlorella vulgaris (Cv), Scenedesmus obliquus (Sc), Dunaliella tertiolecta (Dt), Nan- nochloropsis sp. (Nanno) and Neochloris oleabundans (Neo) oil extracts Fatty acid Sp (% w w¡1) Cv (% w w¡1) Sc (% w w¡1) Dt (% w w¡1) Nanno (% w w¡1) Neo (% w w¡1) 14:0 0.34 3.07 1.48 0.47 7.16 0.43 16:0 40.16 25.07 21.78 17.70 23.35 19.35 16:1 9.19 5.25 5.95 0.88 26.87 1.85 16:2 n.d. n.d. 3.96 3.03 0.39 1.74 16:3 0.42 1.27 0.68 1.24 0.48 0.96 16:4 0.16 4.06 0.43 10.56 n.d. 7.24 18:0 1.18 0.63 0.45 n.d. 0.45 0.98 18:1 5.43 12.64 17.93 4.87 13.20 20.29 18:2 17.89 7.19 21.74 12.37 1.21 12.99 18:3 18.32 19.05 3.76 30.19 n.d. 17.43 18:4 0.08 n.d. 0.21 n.d. n.d. 2.10 20:0 0.06 0.09 n.d. n.d. n.d. n.d. 20:1 n.d. 0.93 n.d. n.d. n.d. n.d. 20:2 0.48 n.d. n.d. n.d. n.d. n.d. 20:3 n.d. 0.83 n.d. n.d. n.d. n.d. 20:4 n.d. 0.23 n.d. n.d. 2.74 n.d. 20:5 n.d. 0.46 n.d. n.d. 14.31 n.d. Saturated 41.74 28.56 23.71 18.17 30.96 20.76 Unsaturated 51.97 51.91 54.66 63.14 59.20 64.60 Table 5 Microalgal iodine values such as nitrogen limitation, and high Fe3+ concentration and Sc Dt Nanno Neo light intensity. To reduce microalgal biomass overall production costs, Iodine value 69 121 52 102 the biomass cake remaining after oil has been extracted can Sc, Scenedesmus obliquus; Dt, Dunaliella tertiolecta; Nanno, Nanno- be used as fertilizer or feed, can undergo anaerobic fermen- chloropsis sp.; Neo, Neochloris oleabundans tation to obtain biogas and/or a pyrolysis process, or to extract high value chemical compounds (bioreWnery con- acid content than the value referred by the European stan- cept) [7, 8, 10, 27]. Ran and Spada [27] suggest that to dard. However, all the analyzed microalgae oils may be make plants accessible to small producers, such as agricul- used for good quality biodiesel if associated with other oils, tural farms, in the near future, could integrate this concept or without restrictions as raw material for other biofuels in order to obtain biofuels, electricity and feed for live- production processes. stock. The oils obtained from the microalgae with higher oil The global biodiesel market is estimated to reach 37 bil- content were characterized in terms of iodine value lion gallons by 2016, growing at an average annual growth (Table 5). The obtained results meet the biodiesel quality of 42%, being Europe the major biodiesel market for the speciWcations (<120 gI2/100 g) [13] which makes these next decade or so, closely followed by US market [31]. In microalgae oils competitive with some vegetable oils tradi- order to meet these rapid expansion in biodiesel production tionally used for biodiesel production as soy or sunXower, capacity, observed not only in develop countries but also in that usually present iodine values higher than 120. developing countries such as China, Brasil, Argentina, Neochloris oleabundans cultivated under nitrogen short- Indonesia and Malaysia, other oil sources, especially non- age, after 5 days of nitrogen starvation (results not shown), edible oils, need to be explored [20]. Microalgae seems to showed a fatty acid content increase of »50% with no sig- be the only source of renewable biodiesel that has the niWcant change in fatty acid proWle indicating this is a high potential to completely displace petroleum-derived trans- potential microalga for biofuel production purposes. These port fuels without the controversial argument “food for results are in agreement with other studies, see, e.g. Illman fuel” and to reach the 2003 Biofuels Directive target, et al. [18], Liu et al. [21], RudolW et al. [28], Solovchenco achieving more than a 35% minimum greenhouse gas sav- et al. [32], and Tornabene et al.[35] that reported an ings (this value represents the diminishing impact of oleag- increase of oil content as a response of stress conditions, inous crops including the land use change) [7–9]. Some 123
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