Achieving the Best Yield in Glycolipid Biosurfactant Preparation by Selecting the Proper...
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Journal of Surfactants andDetergents ISSN 1097-3958 J Surfact DetergDOI 10.1007/s11743-013-1520-y
Achieving the Best Yield in GlycolipidBiosurfactant Preparation by Selecting theProper Carbon/Nitrogen Ratio
Rashmi Rekha Saikia, HemenDeka, Debahuti Goswami, JiumoniLahkar, Siddhartha Narayan Borah,Kaustuvmani Patowary, Plabita Baruah,et al.
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ORIGINAL ARTICLE
Achieving the Best Yield in Glycolipid Biosurfactant Preparationby Selecting the Proper Carbon/Nitrogen Ratio
Rashmi Rekha Saikia • Hemen Deka • Debahuti Goswami •
Jiumoni Lahkar • Siddhartha Narayan Borah •
Kaustuvmani Patowary • Plabita Baruah • Suresh Deka
Received: 28 February 2013 / Accepted: 31 July 2013
� AOCS 2013
Abstract Pseudomonas aeruginosa RS29, the native
biosurfactant-producing strain isolated from the oil fields
of Assam, India was used to investigate the influence of the
carbon nitrogen ratio on production of the biosurfactant.
The biosurfactant producing ability of the strain was
measured based on surface tension (ST) reduction of the
culture medium and the emulsification (E24) index. Pro-
duction was greatly influenced by the sources of nitrogen
and carbon as well as the carbon to nitrogen (C/N) ratio.
Sodium nitrate was the best nitrogen source and the water
miscible carbon source, glycerol was observed as the best
carbon source for maximum biosurfactant production. The
C/N ratio 12.5 allowed the maximum production of bio-
surfactant by the RS29 strain. At this C/N ratio, 55 % ST of
the culture medium was reduced by the produced biosur-
factant. Concentrations of crude and rhamnolipid biosur-
factant obtained at this particular C/N ratio were 5.6 and
0.8 g/l respectively. The RS29 strain was novel as it was
able to produce a sufficient amount of biosurfactant uti-
lizing a much lower amount of the water miscible carbon
source, glycerol. Extraction of the biosurfactant by a
chloroform–methanol (2:1) mixture was the best method to
obtain the highest biosurfactant from the culture medium of
the strain. The biosurfactant was confirmed as a mixture of
mono and di-rhamnolipid congeners, Rha–C10–C10–CH3
being the most abundant one. The biosurfactant was a good
foaming and emulsifying agent.
Keywords Pseudomonas aeruginosa � C/N ratio �Biosurfactant � Rhamnolipid
Introduction
Biosurfactants have received more and more attention in
recent years due to various biological functions and prop-
erties. They have potentials in commercial applications like
in food, in microbiological, pharmaceutical and biomedical
industries, as bio-control agents in agricultural applications
and in health and beauty products for the cosmetic indus-
tries [1–6]. Biosurfactants are environmentally friendly in
nature. When compared to synthetic surfactants, they have
several advantages, including high biodegradability, low
toxicity, low irritancy, and compatibility with human skin
[7, 8] and they are superior to their synthetic counterparts.
The type, quality and quantity of biosurfactants pro-
duced are influenced by the changes in the environmental
conditions [9]. Since the highest activities of microbes can
be attained under suitable environmental conditions; hence
optimization of these conditions is a vital step to achieve
maximum production of biosurfactant. Feeling the need of
these compounds, many studies have been conducted at
present to ensure the production of biosurfactant by
microorganisms [10–12]. But the main challenge with the
production of biosurfactants for commercial applications is
the high production cost. Because of the production cost,
biosurfactants cannot compete economically with the
chemically synthesized ones [13]. Therefore, the present
study was conducted with the aim of obtaining maximum
Electronic supplementary material The online version of thisarticle (doi:10.1007/s11743-013-1520-y) contains supplementarymaterial, which is available to authorized users.
R. R. Saikia � H. Deka � D. Goswami � J. Lahkar �S. N. Borah � K. Patowary � P. Baruah � S. Deka (&)
Environmental Biotechnology Laboratory, Life Sciences
Division, Institute of Advanced Study in Science and
Technology (IASST), Paschim Boragaon,
Guwahati 781035, Assam, India
e-mail: [email protected]; [email protected]
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DOI 10.1007/s11743-013-1520-y
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biosurfactant production with the native isolate, Pseudo-
monas aeruginosa RS29 by selecting proper carbon and
nitrogen sources. Detailed investigation was also carried
out to select the best C/N ratio to attain the highest pro-
duction of biosurfactant. The most efficient method was
selected to extract maximum amount of biosurfactant from
the culture media. The biosurfactant produced was further
investigated to characterize it for its composition and
activity.
Experimental Procedures
Materials
Pseudomonas aeruginosa RS29, isolated from crude oil
contaminated soil was used for the present study [14].
Cultures were grown in 500-ml conical flasks containing
100 ml mineral medium with the composition (g/l):
NH4NO3 (2.0), KCl (0.1), KH2PO4 (0.5), K2HPO4 (1.0),
CaCl2 (0.01), MgSO4�7H2O (0.5), FeSO4�7H2O (0.01),
yeast extract (0.1) and 10 ml of trace element solution
containing (g/l): H3BO3 (0.26), CuSO4�5H2O (0.5),
MnSO4�H2O (0.5), (NH4)6Mo7O24�4H2O (0.06) and
ZnSO4�7H2O (0.7). Glycerol (2 % v/v) was used as the sole
carbon source. All chemicals were purchased from Merck
(Mumbai, India). The pH of the medium was adjusted to
7.0 ± 0.5 and the flasks were kept in a shaking incubator
(Orbitek Ljeil) at 37.5 �C and 150 rpm for 4 days. The ST
measurement(s) was carried out in a K11 tensiometer
(Kruss, Germany) using the plate method.
Methods
Investigation of Nitrogen Sources
The nitrogen sources investigated in the study were
ammonium nitrate, ammonium chloride, ammonium sul-
fate, sodium nitrate and potassium nitrate. The nitrogen
salts were added to the mineral medium containing glyc-
erol as the sole carbon source at 0.2 % (w/v) concentration.
A control without any extra nitrogen salt was also studied.
Optical density (OD) at 600 nm, E24 index and critical
micelle dilution (CMD) were measured along with the
measurement of ST. OD was measured with a Shimadzu
UV-1800 UV-spectrophotometer.
The E24 index of the produced biosurfactant was mea-
sured by mixing 3 ml of whole bacterial culture with an
equal volume of n-hexadecane. The mixture was vortexed
at high speed for 2 min and left undisturbed for 24 h. The
E24 index is used to measure the emulsification ability of
biosurfactants and expressed as below [15, 16]
Percentage of height of emulsified layer mmð ÞTotal height of the liquid column mmð Þ
The CMD is defined as the solubility of a surfactant in
an aqueous phase and is commonly used to measure the
efficiency of a surfactant [17]. CMD-1 and CMD-2 were
determined by measuring the ST values of the cell free
culture broth (CFCB) diluted 10- and 100-times with
distilled water [18]. The CFCB was obtained by
centrifuging a 48-h old culture of the strain grown in the
mineral medium with glycerol at 10,0009g for 20 min at
4 �C.
Effect of Carbon Sources
Water miscible and immiscible carbon sources were
investigated for their ability to support growth and bio-
surfactant production of the strain. The carbon sources used
in the study were glucose, glycerol, mannitol, n-hexadec-
ane and olive oil. These were added at the 2 % level to the
mineral medium amended with the best nitrogen source.
The inoculated mineral medium was incubated in a rotary
shaker at 37.5 �C with 150 rpm for 4 days and the ST was
measured every day. OD, E24 index and CMD were
recorded for each of the carbon sources. A control without
any carbon source was also studied in the investigation.
Influence of the C/N Ratio
The C/N ratio is a vital factor influencing the performance
of biosurfactant production [19, 20]. Hence, in the present
study various C/N ratios were investigated to select the
optimum one for maximum biosurfactant production.
Carbon and nitrogen sources used in the study were the
best ones selected from the above studies. The investigated
C/N ratios were 2.5, 7.5, 12.5, 17.5 and 22.5. These were
prepared by keeping the nitrogen source concentration
constant (2 g/l) and changing the concentration of the
carbon source (5, 15, 25, 35, 45 g/l). The cultures were
allowed to grow in a rotary shaker at 150 rpm at 37.5 �C.
Growth of biomass was measured by the UV-spectropho-
tometer. Production of biosurfactant was measured to
select the best C/N ratio along with the measurement of ST.
Quantification of the biosurfactant was performed as
described by Saikia et al. [14]. The produced biosurfactant
was characterized biochemically as well as by LC–MS
analysis which has been described later on.
Extraction and Purification of the Biosurfactant
Three methods were investigated to select the best one for
extraction of the biosurfactant produced by the RS29 strain.
Three different solvent systems were used in these three
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methods. The solvent systems were acetone, chloroform–
methanol and ethyl acetate.
In the first method, the culture broth was centrifuged at
10,0009g for 20 min to remove the cells from the medium.
The clear supernatant served as the source of the crude
biosurfactant. The biosurfactant was recovered from the
CFCB by cold acetone precipitation as described by Pruthi
and Cameotra [21]. The pH of the biosurfactant-containing
CFCB was adjusted to pH 11 and three volumes of chilled
acetone was added to that. It was then allowed to stand for
10 h at 4 �C to eliminate secondary metabolites by pre-
cipitation. The precipitate was collected by centrifugation
and evaporated to dryness to remove residual acetone. In
the second method, biosurfactants from the CFCB was
extracted by a chloroform–methanol (2:1) mixture three
times. The combined extracts were then transferred to a
round-bottom flask connected to a rotary evaporator. The
concentration process was continued at 40 �C until a yel-
lowish-brown colored viscous and consistent extract was
obtained. The crude biosurfactant was then dried and
weighed. In the third method, CFCB was heated at 110 �C
for 10 min to deproteinize it. After cooling, it was acidified
to pH 3.0 by the addition of 2 N HCl. Biosurfactants were
extracted continuously with ethyl acetate at room temper-
ature. The mixture was shaken vigorously and then left
static so that the organic phase got separated from the
aqueous phase. The organic phase was then transferred to a
rotary evaporator and a viscous honey-colored biosurfac-
tant was recovered after solvent evaporation at 40 �C under
reduced pressure. Quantification of the pure biosurfactant
was carried out by a specific method of Chandrasekaran
and Bemiller [22].
Purification of the biosurfactant was performed by liquid
column chromatography according to previous literature
[23] with slight modifications. The crude biosurfactant
(1 g) was dissolved in 5 ml of chloroform and subjected to
a silica gel 60 chromatography column (26 9 3.3 cm)
equilibrated with chloroform. The loaded column was
washed with chloroform and chloroform–methanol mobile
phases were applied as; 50:3 v/v (300 ml), 50:5 v/v
(200 ml) and 50:50 v/v (100 ml) at a flow rate of 1 ml/min.
Fractions of 15 ml were collected and biosurfactant present
in the fractions were detected (ST measurement). Finally,
chloroform–methanol (50:50 v/v) was applied to remove
any remaining biosurfactant from the column. The bio-
surfactant-containing fractions were combined and dried in
a rotary evaporator at 40 �C.
Characterization of Biosurfactant
The purified biosurfactant was analyzed by thin layer
chromatography (TLC). The biosurfactant was dissolved in
a chloroform–methanol (9:1) mixture at a concentration of
10 mg/ml [24]. For analysis, 2 ll of the sample was spotted
onto the silica gel (G60: Merck, Germany) plates. After
drying the sample for 5 min, the plates were developed in
chloroform:methanol:acetic acid:water (25:15:4:2 v/v/v/v)
at room temperature. The chromatogram was sprayed with
a-naphthol reagent followed by concentrated sulfuric acid.
The biosurfactant was separated and identified by LC
coupled to MS using an Agilent 6410 Triple Quad LC–MS
system. The purified sample was dissolved in methanol and
2 ll of the sample was injected into a Zorbax C18 column
(2.1 9 50 mm). The LC flow rate was 0.2 ml/min. An
acetonitrile/water gradient with 0.01 % formic acid was
used (10–90 %) as the mobile phase. ESI–MS was per-
formed in positive mode and analyzed using Agilent
software.
Activity Assay
Foaming
For measuring foaming activity, the flask containing a
2-day old culture of the strain was hand shaken for 2 min
and the stability of the foam was monitored by observing it
for 48 h.
Emulsification
Emulsification activity of the produced biosurfactant was
measured as described previously for the E24 index. Six
immiscible solvents namely, n-hexadecane, hexane, olive
oil, crude oil, diesel and coconut oil were used to observe
the emulsification activity of the biosurfactant.
Oil Displacement
Oil displacement is a method used to determine efficiency
of a given biosurfactant by evaluating the diameter of the
clear zone formed after the addition of surfactant-con-
taining solution on an oil–water interphase. The test is also
used as a preliminary method for identification of biosur-
factant producing strains. Oil displacement activity is
directly proportional to the concentration of the biosur-
factant in the solution [25]. For this assay, 50 ll of crude
oil was added to the surface of 40 ml of distilled water in a
petri dish (15 cm) to form a thin oil layer. Then, 25 ll of
culture broth was gently placed on the centre of the oil
layer. A control plate was also studied where instead of
culture broth only distilled water was placed on the oil
layer. The oil displacement area (ODA) was calculated as-
ODA ¼ 22=7 radius2� �
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Statistical Analysis
Studies were carried out three times with three replications
each and the results represented are the means ± standard
deviations (SD). One way ANOVA was conducted to see
the significance of production of biosurfactant as well as its
extraction from culture media.
Results and Discussion
Investigation of Nitrogen Sources
Application of various nitrogen sources in the culture
media revealed that maximum reduction of ST (55.5 and
55.3 %) was achieved while sodium nitrate and potassium
nitrate were used as nitrogen sources respectively
(Table 1). This might be because of nitrogen salts being
less available from these two salts. Since nitrate first
undergoes dissimilatory nitrate reduction to ammonium
and then assimilation by glutamine-glutamate metabolism;
assimilation of nitrate as a nitrogen source is so slow that it
would simulate a condition of limiting nitrogen [26, 27]. It
had been reported that nitrogen limitation enhances bio-
surfactant production [28]. Ammonium nitrate also showed
significant reduction of ST (54.05 %). ST reduction for
ammonium chloride and ammonium sulfate (13 and
12.71 % respectively) was not prominent as compared to
the other nitrogen sources and the control (40.03 %).
Maximum bacterial growth was observed in an ammo-
nium nitrate-containing mineral medium and for the rest of
the four nitrogen sources almost equal growth was recor-
ded. The lowest bacterial growth was observed in the case
of the control (Table 1). Ammonium nitrate-supplemented
medium supported the growth of the strain more than the
synthesis of biosurfactant by it. Though ammonium sulfate
and ammonium chloride also supported bacterial growth
but synthesis of biosurfactant was very poor in the cases of
these two salts.
The control also showed results. This may be because of
the bacterial utilization of yeast extract present in the
medium in which the strain grew, reduced ST and showed
an E24 index of 50 %. The E24 index was at a maximum
and almost similar for sodium nitrate (80 %) and potassium
nitrate (79 %) followed by ammonium nitrate (72 %). The
minimum was observed for ammonium chloride and
ammonium sulfate (36 % for both) (Table 1).
CMD-1 and CMD-2 were also lowest (27.2 and
40.0 mN/m respectively) for sodium nitrate-supplemented
media followed by potassium nitrate (Table 1). The results
showed little change in efficiency after diluting the sample
100 times. It suggested that a sufficient amount of biosur-
factant was present in the culture medium, and thus its
surface activity was retained even at such a high dilution.
These values are appreciably better than the CMD-1 and
CMD-2 values reported for P. aeruginosa MTCC8165
(29.9 ± 1.0 and 46.5 ± 0.90 respectively), P. aeruginosa
MTCC7815 (36.2 ± 0.35 and 58.1 ± 0.53 respectively),
P. aeruginosa MTCC7812 (48.1 ± 0.46 and 62.6 ± 1.43
respectively) and P. aeruginosa MTCC7814 (38.4 ± 0.64
and 59.8 ± 0.25 respectively) [29].
Carbon Sources
Investigation of water-miscible and immiscible carbon
sources revealed that glycerol was the best carbon source
for maximum biosurfactant production. The strain showed
a 50.46 % reduction in ST when glycerol was used as the
carbon source. In glucose- and mannitol-containing media,
45.16 and 45.31 % ST reductions were achieved respec-
tively. Growth of the strain on olive oil resulted in a
24.86 % decrease in ST and a poor result was recorded for
n-hexadecane (1.9 %) and the control (1.20) (Table 2).
Results of CMD-1 (10- times dilution) and CMD-2 (100-
times dilution) also showed that the best results were
obtained with glycerol as the carbon source followed by
mannitol. The values of CMD-1 and CMD-2 of the bio-
surfactant-containing cell-free medium with glycerol as the
Table 1 Effect of nitrogen source on ST reduction, CMD-1, CMD-2, E24 index and OD600 after 48 h of growth of P. aeruginosa RS29 in
mineral medium
Nitrogen source ST (0 h)
(mN/m)
ST (48 h)
(mN/m)
ST reduction
(%)
CMD-1
(mN/m)
CMD-2
(mN/m)
E24 index
(%)
OD600
Control (without nitrogen source) 60.2 ± 0.23 36.1 ± 0.20 40.03 ± 0.90 49.7 ± 0.16 60.0 ± 0.23 50 ± 0.30 1.39 ± 1.0
Ammonium nitrate 59.2 ± 0.11 27.2 ± 1.0 54.05 ± 1.0 28.7 ± 0.90 42.4 ± 1.0 72 ± 0.25 3.87 ± 1.5
Ammonium chloride 60.0 ± 0.15 52.2 ± 1.20 13.00 ± 0.88 58.8 ± 0.36 59.5 ± 0.49 36 ± 0.35 2.12 ± 0.98
Ammonium sulfate 59.0 ± 0.20 51.5 ± 0.80 12.71 ± 0.89 58.2 ± 0.40 59.7 ± 0.82 36 ± 0.18 2.06 ± 1.2
Sodium nitrate 59.1 ± 0.10 26.3 ± 0.89 55.50 ± 0.20 27.2 ± 0.30 40.0 ± 0.86 80 ± 0.40 2.36 ± 0.86
Potassium nitrate 59.1 ± 0.23 26.4 ± 1.30 55.33 ± 0.12 27.4 ± 0.94 41.2 ± 0.25 79 ± 0.32 2.28 ± 1.15
Results represented are the means ± SD of three independent experiments with three replicates each
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carbon source were 27.2 and 40.0 mN/m respectively,
similar to those mentioned in the case of sodium nitrate.
The E24 index was also maximum for glycerol (80 %).
This was followed by mannitol with E24 index 68 %. The
E24 indexes for olive oil, glucose, n-hexadecane and
control were 67, 60, 55 and 29 % respectively (Table 2).
The maximum OD was observed in the glycerol-containing
medium (Table 2). The results suggest that the RS29 strain
can show its maximum activity in glycerol-containing
media. It was reported that the most of the identified bio-
surfactants are synthesized by microorganisms grown on
water-immiscible hydrocarbons. These compounds are
expensive which in turn raise the overall cost of the process
[30]. Though the literature shows the potentials of n-
hexadecane [31] and vegetable oils [32] as good substrates
for biosurfactant production by Pseudomonas sp., but the
RS29 strain performed better in glycerol rather than the
water-immiscible ones. Similar results have been reported
in the literature [33]. Since costs of water-immiscible
carbon sources are more than water-miscible ones, utili-
zation of glycerol for biosurfactant production is more
economic.
Influence of the C/N Ratio
The C/N ratio is very influential in biosurfactant production
[19, 20] and the optimum value of this ratio can vary
depending on the strain used and the carbon source [34].
Investigation of the influence of the C/N ratio on biosur-
factant production revealed that 12.5 was the optimum
ratio for maximum growth of biomass and biosurfactant
production by the RS29 strain (Fig. 1). An increase in the
C/N ratio from 2.5 to 12.5 resulted in an increase in the
growth of bacterial biomass and production of biosurfac-
tant. Further increases in the C/N ratio reduced the pro-
duction as well as the growth of biomass of the strain. The
highest ST reduction was obtained (55 %) at the C/N ratio
of 12.5 (Table 3). The maximum amount of crude biosur-
factant 5.6 g/l (0.8 g/l rhamnolipid) was obtained at the
C/N ratio of 12.5 (Fig. 1). Differences between crude and
rhamnolipid biosurfactant contents in the culture medium
are in agreement with the literature reporting extraction of
13.35 g/l crude biosurfactant from a 72-h old culture of
Pseudomonas aeruginosa in a palm oil medium with
2.91 g/l rhamnolipid biosurfactant [12]. Growth of biomass
of the strain was also very good at this C/N ratio. It was
reported that a lower C/N ratio was favorable for biosur-
factant production by P. fluorescens Migula 1895-DSMZ
[16]. For P. aeruginosa EM1, Wu et al. [34] observed an
optimum C/N ratio of 26 when glucose was used as a
carbon source and a C/N ratio of 52 when glycerol was
used. They obtained 4.9 g/l biosurfactant using glycerol as
the substrate. Santa Anna et al. [35] demonstrated maxi-
mum production of 0.69 g/l rhamnolipid with the best
tensoactive characteristics (48 % decrease in ST) with
glycerol, a carbon source easily assimilated at a C/N ratio
of 22.8. Rashedi et al. [36] reported that the best biosur-
factant production of 0.69 g/l was obtained with glycerol
and sodium nitrate at a C/N ratio of 55. Therefore, it is
clear that the RS29 strain is better than these strains in
terms of maximum production of biosurfactant at low
amounts of carbon substrate. As it is known that limited
nitrogen enhances production of biosurfactant [28]; keep-
ing the nitrogen content constant if the highest biosurfac-
tant production can be obtained at a low C/N ratio, it shows
that the bacterium is utilizing a lower amount of substrate
for the production of biosurfactant. This is economically
viable.
Extraction and Characterization of the Biosurfactant
Use of a chloroform–methanol (2:1) solvent system was the
best method to extract the maximum amount of biosur-
factant from the culture media. As seen in Table 4, the
maximum biosurfactant amount was obtained from the
culture media when it was extracted with a mixture of
chloroform and methanol at a 2:1 ratio. The biosurfactant
sample produced two purple colored spots on the TLC
plates after spraying with a-naphthol and sulfuric acid.
Spot 1 with an Rf (retardation factor) value equal to
Table 2 Effect of carbon source on ST reduction, CMD-1, CMD-2, E24 index and OD600 after 48 h of growth of P. aeruginosa RS29 in
mineral medium
Carbon source ST (0 h)
(mN/m)
ST(48 h)
(mN/m)
ST reduction
(%)
CMD-1
(mN/m)
CMD-2
(mN/m)
E24 index
(%)
OD600
Control (without carbon source) 51.4 ± 1.0 50.8 ± 0.90 1.20 ± 0.90 68.7 ± 1.1 71.4 ± 1.13 29 ± 1.0 0.785 ± 1.0
Glucose 51.6 ± 0.98 28.3 ± 1.0 45.16 ± 1.0 32.7 ± 0.90 61.4 ± 1.0 60 ± 1.20 2.305 ± 1.5
Mannitol 50.1 ± 1.20 27.4 ± 1.20 45.31 ± 0.88 28.8 ± 0.86 41.5 ± 0.99 68 ± 0.95 2.415 ± 0.98
Glycerol 54.1 ± 0.99 26.8 ± 0.80 50.46 ± 0.89 27.2 ± 1.0 40.0 ± 0.86 80 ± 1.10 3.20 ± 1.20
Olive oil 34.6 ± 1.10 26.0 ± 0.89 24.86 ± 1.20 30.6 ± 1.2 37.5 ± 1.0 67 ± 1.20 2.80 ± 0.86
n-Hexadecane 46.8 ± 0.87 45.9 ± 1.30 1.90 ± 1.12 62.3 ± 0.94 71.5 ± 1.10 55 ± 1.0 1.18 ± 1.15
Values are presented as means ± SD of three independent experiments with three replicates each
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0.42 ± 0.04 and spot 2 with an Rf value equal to
0.78 ± 0.28. This indicated that the biosurfactant sample
was composed of congeners with one and two sugar mol-
ecules influencing the movement of the molecules on the
TLC plate. This is in agreement with Guerra-Santos et al.
[37] who described the production of active compounds by
Pseudomonas aeruginosa on TLC, with the same solvent
system. They obtained Rf values of 0.4 and 0.8 for di- and
mono-rhamnolipid respectively.
As described in the Materials and Methods section, the
MS spectra were acquired in positive ion modes to confirm
the structural assignment of the quasi-molecular ions. The
RS29 strain produced several congeners with M.W. rang-
ing from 334 to 735. Comparison of mass spectra ions with
the available literature [38, 39] revealed the identity of the
congeners which are presented along with their abundance
in Table 5.
Analysis of biochemical as well as spectrometric data of
the biosurfactant revealed the rhamnolipid nature of it. The
rhamnolipid nature of the biosurfactant produced by RS29
is in agreement with previous works reporting production
of rhamnolipid type of biosurfactant by Pseudomonas sp.
[40–42]. Predominance of C10 fatty acids in the rhamn-
olipid biosurfactant was also stated by Thaniyavarn et al.
[12] with the pseudo-molecular ion at m/z 103 as the base
peak of the GC–MS spectrum for Pseudomonas aeruginosa
A41. Arino et al. [43] reported production of C10 fatty acids
as the main component of rhamnolipid biosurfactant by
Pseudomonas aeruginosa GL1 with production of some
amount of C8, C12:1 and C12 fatty acids. LC–MS charac-
terization (Fig. 2) of the produced biosurfactant showed
that the extracted rhamnolipid was a mixture of different
congeners having mono and di-rhamnose groups and with
pseudomolecular ion (m/z) ranging from 334 to 735.
Among the congeners, the predominant one was found to
be Rha–C10–C10–CH3 while the next more abundant con-
gener was Rha–Rha–C8 (Table 5). It was also clear from
the analysis that more mono-rhamnolipid congeners were
present in the biosurfactant than the di-rhamnolipid ones.
Two congeners having unsaturated fatty acids (Rha–C12:2
and Rha–C10–C14:1) were also found in the rhamnolipid
mixture. This is in agreement with results reported earlier
[39]. They have reported both mono- and di-rhamnolipid
congeners from Pseudomonas aeruginosa 47T2 with the
pseudomolecular ion (m/z) ranging from 475 to 703. Rha–
Rha–C8–C10, Rha–C10–C8, Rha–C8–C10, Rha–Rha–C8–
C12:1, Rha–Rha–C10–C10, Rha–Rha–C10–C12:1, Rha–C10–
0
1
2
3
4
5
6
7
2.5 7.5 12.5 17.5 22.5
C/N ratio
Rh
amn
ose
co
nte
nt
(g/l)
C
rud
e b
iosu
rfac
tan
t (g
/l)
0
1
2
3
4
5
6
Bio
mas
s (g
/l)
Rhamnose content Biomass Crude biosurfactant
Fig. 1 Effect of the C/N ratio on the growth of bacteria and
production of biosurfactant in a mineral medium containing glycerol
and sodium nitrate as carbon and nitrogen sources respectively. Bars
indicate standard deviations
Table 3 Rhamnolipid quantification and ST measurement of 48-h
old culture of P. aeruginosa RS29 on glycerol at different C/N
conditions
C/N ratio Rhamnolipid (g/l) ST reduction (%)
2.5 0.49 ± 0.20* 53 ± 0.42
7.5 0.59 ± 0.16* 53 ± 0.38
12.5 0.80 ± 0.18* 55 ± 0.29
17.5 0.60 ± 0.24* 51 ± 0.45
22.5 0.58 ± 0.22* 48 ± 0.32
Values are presented as means ± SD of three independent experi-
ments with three replicates each. Significance of difference:
* p \ 0.05
Table 4 Extraction of biosurfactant using three different methods
Method Biosurfactant extracted (g/l)
Acetone precipitation 4.4 ± 1.9
Extraction by chloroform–methanol 5.6 ± 1.3*
Extraction using ethyl acetate 4.8 ± 1.5
Results are presented as means ± SD of three independent experi-
ments with three replicates each. * p \ 0.05 and * p \ 0.01
Table 5 Identification and characterization of major rhamnolipid
congeners using LC–ESI–MS and their abundance in percent in the
produced biosurfactant
m/z Structural analogue Abundance (%)
476.5 Rha–C10–C8 or Rha–C8–C10 11.9
358.2 Rha–C12:2 10.05
334.41 Rha–C10 5.15
616.7 Rha–C14–C14 5.23
664.82 Rha–Rha–C10–C10–CH3 11.12
678.84 Rha–Rha–C12–C10 3.38
518.7 Rha–C10–C10–CH3 31.86
452.49 Rha–Rha–C8 12.04
558.74 Rha–C10–C14:1 3.12
734.95 Rha–Rha–C14–C12 or Rha–Rha–C12–C14 1.36
594.69 Rha–Rha–C8–C8 4.79
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C10, Rha–Rha–C10–C12, Rha–Rha–C12–C10, Rha–C10–
C12:1, Rha–C12:1–C10, Rha–Rha–C12:1–C12, Rha–Rha–C10–
C14:1, Rha–C10–C12, Rha–C12–C10 were the reported
identified congeners with Rha–Rha–C10–C10 being the
most abundant one.
Activity Assay
The biosurfactant-containing culture supernatant showed
good foaming stability. The foam produced was stable for
48 h indicating prospects of the produced biosurfactant as a
good foaming agent for industrial purposes.
The biosurfactant also showed very good emulsification
activity when tested with various immiscible substrates. As
seen in Table 6, biosurfactant-containing culture media
could emulsify all the tested substrates, namely n-hexa-
decane, hexane, olive oil, crude oil, diesel and coconut oil
which are highly immiscible in water. But the highest E24
index was recorded with crude oil. The recorded E24 with
crude oil was 100 % (Table 6). This was followed by the
E24 index with n-hexadecane of 80 %. Olive oil, diesel and
coconut oil showed approximately equal E24 index.
Lowest E24 index was recorded for hexane (60 %).
The ODA of the biosurfactant was found to be 132.67 cm2
(Fig. 3). According to Thaniyavarn et al. [44], the diameter
of the clearing zone on the oil surface correlates to surfactant
activity. For pure biosurfactant, there is a linear correlation
between the quantity of the surfactant and the clearing zone
diameter. The larger the size, the higher the activity of a
surfactant is. In the control plate where instead of culture
broth only distilled water was used a clear zone did not form.
Tambekar and Gadakh [45] isolated biosurfactant-producing
bacterial strains from petroleum-contaminated soil and
reported two Pseudomonas aeruginosa strains. Investigation
revealed that the strain isolated from garage soil showed
38.47 cm2 and the strain isolated from soil of petrol pump
showed 0.79 cm2 ODA. The isolated Pseudomonas aeru-
ginosa PDKT2 from used engine oil-contaminated soil
reported an oil displacement area of 2.5 cm2 [46]. Techaoei
et al. [47] isolated a Pseudomonas aeruginosa strain
SCMU106 from garage site which showed an oil
Fig. 2 LC chromatogram of the
column purified biosurfactant
extracted with chloroform–
methanol
Table 6 E24 indexes of the
produced biosurfactant with
various substrates
Results are presented as
means ± SD of three
independent experiments with
three replicates each
Solvent Height of the
emulsified layer (cm)
Total height
of the liquid (cm)
E24 index (%)
n-hexadecane 4.16 ± 0.15 5.2 ± 0.10 80 ± 0.14
Hexane 2.52 ± 0.14 4.2 ± 0.12 60 ± 0.13
Olive oil 3.36 ± 0.12 4.8 ± 0.11 70 ± 0.10
Crude oil 5.0 ± 0.0 5.0 ± 0.09 100 ± 0.06
Diesel 3.7 ± 0.11 5.3 ± 0.09 70.5 ± 0.10
Coconut oil 3.5 ± 0.11 5.2 ± 0.10 69 ± 0.11
Fig. 3 Oil displacement activity of the biosurfactant-containing
culture broth
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displacement area of 9.83 and 11.17 cm2 while NH4NO3 and
KNO3 were used as nitrogen sources respectively. The above
discussions revealed that the biosurfactant produced by the
isolated RS29 strain showed excellent activity in terms of the
oil displacement area when sodium nitrate was used as the
nitrogen source.
Conclusion
The yield of biosurfactant is absolutely dependent on the
sources of nitrogen and carbon in the culture medium.
Moreover, the C/N ratio has a great influence on the pro-
duction of biosurfactant. In our study, the RS29 strain was
able to produce the highest amount of biosurfactant at a
very low substrate concentration, demonstrating the effi-
ciency of the strain on glycerol. Obtaining the maximum
amount of biosurfactant from culture media is also
dependent on the extraction procedure used for the pur-
pose. The strain has great practical potential to be used as
an emulsifying and foaming agent.
Acknowledgments We thank the Director of the Institute of
Advanced Study in Science and Technology (IASST), Guwahati, for
providing us with laboratory facilities to carry out the research work.
The corresponding author gratefully acknowledges the Department of
Biotechnology (DBT) from the government of India, for the project
grant (DBT project No. BT/PR 9795/BCE/08/590/2007). We also
thank Mr S Dey, Biotech Park, Assam, India for his assistance in LC–
MS analysis.
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Author Biographies
Rashmi Rekha Saikia is a scientist of the Institute of Advanced
Study in Science and Technology (IASST), Guwahati, India. Her
scientific interests include production of surfactants of microbial
origin and virulence property of the surfactant producing microbes,
application of biosurfactants in petroleum industries such as for the
recovery of hydrocarbons from refinery sludge, bioremediation of
contaminated soil etc.
Hemen Deka is a research associate of IASST, India. His research
interests include biowaste management and currently he is working
on the development of plant–microbe consortia for remediation of
contaminated soil.
Debahuti Goswami is a senior research fellow at IASST, India. She
is presently involved in production enhancement of biosurfactants and
their application for crop disease control.
Jiumoni Lahkar is a research fellow at IASST, India. Currently she
is carrying out research on application of biosurfactants for crop
improvement.
Siddhartha Narayan Borah is a research fellow at IASST, India. He
is pursuing research in the area of plant diseases and the possible
application of biosurfactants for disease control.
Kaustuvmani Patowary is a research fellow at IASST, India.
Presently he is working on high molecular weight polycyclic aromatic
hydrocarbon (PAH) remediation by application of biosurfactant
producing bacteria.
Plabita Baruah is a research fellow at IASST, India. She is presently
working on phyto-remediation of hydrocarbon contaminated soil by
herbs like Cyperus brevifolius.
Suresh Deka is a professor in the Life Sciences Division of IASST,
India. His research interests include bioremediation of contaminated
soil with plants and microbes, degradation of heavy metals, applica-
tion of biosurfactants in agriculture and the petroleum industries.
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