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Engineering » Biomedical Engineering » "Progress in Molecular and Environmental Bioengineering - From Analysis and Modeling to Technology Applications", book edited by Angelo Carpi, ISBN 978-953-307-268-5, Published: August 1, 2011 under CC BY-NC-SA 3.0 license. © The Author(s).

Chapter 26

Improving Biosurfactant Recovery from Pseudomonas aeruginosa Fermentation

By Salwa Mohd Salleh, Nur Asshifa Md Noh and Ahmad Ramli Mohd Yahya
DOI: 10.5772/23395

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Schematic figure of modified bioreactor with integrated foam recycler system
Figure 1. Schematic figure of modified bioreactor with integrated foam recycler system
Time profile of cell dry weight of P. aeruginosa USM AR-2 at different aeration rates
Figure 2. Time profile of cell dry weight of P. aeruginosa USM AR-2 at different aeration rates
Time profile of rhamnolipid concentration produced by P. aeruginosa USM AR-2 at different aeration rates
Figure 3. Time profile of rhamnolipid concentration produced by P. aeruginosa USM AR-2 at different aeration rates
Time profile of cell growth during batch fermentation agitated at 500 rpm under an aeration rate of 0.5 vvm
Figure 4. Time profile of cell growth during batch fermentation agitated at 500 rpm under an aeration rate of 0.5 vvm
Time profile of rhamnolipid concentration during batch fermentation agitated at 500 rpm under an aeration rate of 0.5 vvm
Figure 5. Time profile of rhamnolipid concentration during batch fermentation agitated at 500 rpm under an aeration rate of 0.5 vvm

Improving Biosurfactant Recovery fromPseudomonas aeruginosa Fermentation

Salwa Mohd Salleh1, Nur Asshifa Md Noh and Ahmad Ramli Mohd Yahya

1. Introduction

Surface active agents or surfactants or are amphiphilic compounds that are chemically synthesized which can greatly reduce the surface tension of a liquid. They are widely used industrially for various purposes such as detergents, wetting agents, foaming agents, emulsifiers, dispersants, lubricants and penetrants (Mulligan & Gibbs, 1993). To date, a large majority of surfactants used are chemically synthesized including alkylbenzene sulfonates (detergents) and lauryl sulfate (foaming agent) (Mukherjee et al., 2006). These synthetic surfactants have been used in the oil industries to aid the clean up of oil spills, rapidly removing large amounts of oil from the ocean/soil surface (Banat, 1995). However, much like the oil they remove, these compounds exhibit poor biodegradability, are toxic to the environment and consequently, have limited applications.

In recent years, environmental compatibility and biodegradability have become increasingly important factors in the selection of industrial chemicals (Banat, 1995). For this reason, natural biosurfactants appear as a promising candidate to replace or reduce the usage of chemically synthesized surfactants. Biosurfactants are surface active biomolecules produced by a variety of microorganisms such as bacteria, yeast and fungi. As with surfactants, they too are amphipathic molecules, comprising hydrophilic and hydrophobic domains. The simultaneous existence of these domains provides biosurfactants the ability to partition themselves at the interphases between different fluid phases (Banat et al., 2000). They show similar capability of reducing the surface and interfacial tensions using the same mechanisms as the synthetic surfactants. Owing to their unique characteristics which include lower toxicity, higher biodegradability, environmental compatibility and stable activity at extreme pH, salinity and temperature, biosurfactants have gained attention and importance in various fields (Maier, 2003; Mullican et al., 2005).

1.1. Downstream processes

In general, biosurfactants are still unable to compete with the synthetic surfactants for commercial purposes due to their high production and recovery costs. As reported by Mukherjee et al., (2006), three main factors that hinder the commercialization of biosurfactant are: i) the high cost of raw materials; ii) the high recovery and purification costs; and iii) the low yields in the production processes. Thus, in order to reduce the production cost of biosurfactants and to increase the efficiency of biosurfactant production, several techniques and approaches have been adopted worldwide. Inexpensive alternative substrates, optimized culture conditions in bioreactor operations, cost-effective recovery processes and strain improvements have been investigated to enhance biosurfactant yields (Chen et al., 2006; Deleu and Paquot, 2004; Joshi et al., 2008; Yeh et al., 2006).

Efficient downstream processing techniques are required to minimize the overall production costs of any biotechnological products, including biosurfactants. Moreover, approximately 60% of the total biosurfactant production expenditure is from the downstream processes. Thus, it is prudent to recover and purify the biosurfactants in a cost-effective manner as this will contribute significantly in minimizing the total cost of production. In most reported studies, biosurfactants are recovered from the culture media using a combination of several techniques such as precipitation, centrifugation and solvent extraction (Desai and Desai, 1993). However, the solvents that are generally used for biosurfactant recovery, such as methanol, chloroform, acetone and dichloromethane are air-polluting, costly and toxic to environment.

1.2. Foam fractionation

Foam fractionation has drawn the most attention for the recovery of surface active molecules as this technique offers high effectiveness and requires a low cost of operation. It was originally proposed by Leonard and Lemlich in 1965 and has recently been practiced by a number of researchers (Davis et al., 2001; Chen et al., 2006a; Chen et al., 2006b; Sarachat et al., 2010). In this technique, foam is allowed to overflow from the bioreactor through a fractionation column, resulting in a highly concentrated product. To date, due to the outstanding features of this technique, such as high effectiveness, high purity of product, low space requirements and environmentally friendly, there are a number of reports that presented foam fractionation as one of the most proficient methods in biosurfactant recovery (Chen et al., 2006a; Davis et al., 2001; Noah et al., 2002; Sarachat et al., 2010).

The present study focused on the production and recovery of a biosurfactant produced by Pseudomonas aeruginosa isolated from local crude oil sample. This bacterium was found to produce rhamnolipid, a glycolipid-type of biosurfactant. The study was initiated with the cultivation of Pseudomonas aeruginosa USMAR-2 in a bioreactor, followed by the simultaneous recovery of rhamnolipid. This resulted in a process with a combined rhamnolipid production and recovery. An integrated foam recycler was employed to fractionate the foam produced and recycle the froth containing biosurfactant into the reactor. Several parameters were manipulated including aeration and agitation rate to improve the rhamnolipid recovery efficiency and productivity. The main objective in this study is to use the foaming problem as a key to purify and concentrate the rhamnolipid by recovering the overflowing foam from the modified bioreactor.

2. Methodology

2.1. Foam fractionation

Batch cultivation was carried out in 3.0 L bioreactor (Bioflo 115, New Brunswick, USA), integrated with a foam fractionation system for the primary rhamnolipid recovery. The foam fractionation system consisted of two main parts: i) a 3.0 L bioreactor and ii) a foam recycler system (Figure 1). The foam recycler system was equipped with a foam collector vessel (500 mL flask) and a foam recycler pump. The rapid stirring and aeration supplied during the fermentation ensured excessive foam and the overflowed foam was allowed to flow out of the bioreactor through an integrated foam tube. The resulting foamate was directed into the foam collector vessel and was continuously recycled into the bioreactor using the foam recycler pump until the rhamnolipid concentration in the foam remained constant. The foamate containing the concentrated product can be directly used for a suitable application or can be further purified should a higher concentration of rhamnolipid be required.


Figure 1.

Schematic figure of modified bioreactor with integrated foam recycler system

2.2. Aeration and agitation rate

The agitation speed and the aeration rate were manipulated throughout the study by setting the desired parameter values in the bioreactor controller, Biocommand OPC Version 1.30 (New Brunswick Scientific, USA).

2.3. Rhamnolipid recovery (%) and rhamnolipid enrichment

The formulas used to calculate the rhamnolipid recovery and enrichment in foam fractionation are as follows:

  1. Rhamnolipid recovery:

(%)=rhamnolipidconcentrationinfoamate(rhamnolipidconcentrationinfoamate+rhamnolipid concentration in culture when foaming ceases)x100
  1. Rhamnolipid enrichment:


3. Results and discussion

In a normal bioprocess practice, foam formation is avoided at all costs as it will cause several problems, such as stripping of product, nutrients and cells into the foam. In most fermentation systems, the excessive foam can be controlled chemically or mechanically. The addition of chemical antifoams can often suppress a highly foaming culture. However, this technique will raise the cost of cultivation and lower its productivity as the antifoam (usually a surface tension lowering substance) can be costly and its presence may reduce the oxygen transfer rate and the nutrient uptake (Davis et al., 2001). Moreover, antifoam often works upon addition, but the foam build-up will soon ensue as the fermentation progresses. On the other hand, mechanical foam breakers or any mechanical devices are only applicable for a moderately foaming culture as this technique can cause high energy consumption (Heinzle et al., 2006).

The simultaneous rhamnolipid production and primary recovery using the foam fractionation system developed in this work was able to address the foaming problem associated with rhamnolipid production without the addition of an antifoam agent. As reported by Yeh et al., (2006), the biosurfactant product preferentially distributed into the foam fraction, resulting in a higher concentration of biosurfactants in the foam. Consequently, this approach gave a concentrated biosurfactant product while at the same time, alleviated the foaming problem.

3.1. Effect of different aeration rate

Besides establishing a bioreactor design that can control foaming and recover the product, the other interest in this work is to study the effect of aeration and agitation speed towards rhamnolipid production and foam formation. These two parameters are highly correlated with the oxygen transfer efficiency in the bioreactor (Davis et al., 2001, Yeh et al., 2006). Thus, the effect of the aeration rate towards rhamnolipid production was investigated by fixing the stirrer speed at 400 rpm. As indicated in Figure 2, the cell dry weight of P. aeruginosa was 6.96 g/L when the aeration rate was set at 1.0 vvm. A similar fermentation run, aerated at 0.5 vvm gave a cell dry weight of 5.88 g/L. Interestingly, as depicted in Figure 3, the rhamnolipid concentrations obtained with both aeration rates (0.5 vvm and 1.0 vvm) were not significantly different, 1.15 g/L and 1.41 g/L, respectively. Thus, 0.5 vvm was used in subsequent experiments (Table 1). However, fixing the agitation rate at 400 rpm with either 0.5 vvm or 1.0 vvm resulted in no overflowing foam. It is tempting to speculate that a higher agitation speed is needed to enhance the foam formation. Thus, it is essential to find a suitable agitation rate, leading to a condition that is favorable for foam formation while maintaining a high rhamnolipid concentration.

3.2. Effect of different agitation rates with foam recycler system

Yeh and co-workers (2006) reported that efficient mass transfer and sufficient oxygen supply played major roles in rhamnolipid production. The influence of agitation rates in enhancing rhamnolipid yield and productivity was further investigated. The highest rhamnolipid concentration in the foamate (2.93 g/L) was achieved using the foam recycler system, with the bioreactor aerated at 0.5 vvm and agitated at 500 rpm. As shown in Figure


Figure 2.

Time profile of cell dry weight of P. aeruginosa USM AR-2 at different aeration rates


Figure 3.

Time profile of rhamnolipid concentration produced by P. aeruginosa USM AR-2 at different aeration rates

5, the highest concentration of rhamnolipid was detected from the recycled foam, not from the culture broth. This finding provides valuable information regarding the rhamnolipid enrichment and recovery process as summarized in Table 1, confirming that rhamnolipid was being concentrated in the foam.

Thus, this approach would be beneficial for subsequent downstream processes, providing an alternative source for rhamnolipid recovery as it was recovered from the froth rather than the spent broth. In addition, it presents a significant process cost reduction since the foamate is much smaller in volume relative to the spent broth. Rhamnolipid productivity in the foam recycler system was double the value of that in the conventional cultivation. In particular, the foam recycler system improved rhamnolipid production but did not contribute much to the growth of P. aeruginosa USM AR-2 in the cultivation system. The highest biomass densities for both conventional and foam recycler system remained similar (Figure 4). However, when the conventional cultivation was employed, approximately 50% of the culture broth was stripped from the vessel as a result of severe foaming during cultivation. It was assumed that this contributed to the lower concentration of rhamnolipid (1.15 g/L) as indicated in Figure 5. As summarized in Table 2, rhamnolipid production in the modified bioreactor from this work is highly competitive when compared with the findings from relevant studies done by several researchers (Table 2).

Cultivation conditionYield a Productivity b Rhamnolipid enrichmentRhamnolipid recovery (%)Remarks
Aeration rate (vvm)Agitation rate (rpm)Foam recycler system
1.04000.2030.015--No overflow foam
0.54000.1960.012--No overflow foam
0.5500-0.1440.014--50 % of culture broth was loss
0.55000.2330.0281.8965.40Overflowed foam was recycled

Table 1.

the yield of rhamnolipid on biomass (g g-1)b volumetric production rate (g L-1 h-1)Summary of results obtained in an integrated bioreactor for the production of rhamnolipid produced by P. aeruginosa USM AR-2

Direct utilization of the foam produced can be applied in many fields, such as in bioremediation where the foam can be used to flush contaminated soils. For example, in a study conducted by Mulligan & Wang, 2006, the feasibility of rhamnolipid foam to enhance the remediation of heavy metals in contaminated soils was evaluated.


Figure 4.

Time profile of cell growth during batch fermentation agitated at 500 rpm under an aeration rate of 0.5 vvm


Figure 5.

Time profile of rhamnolipid concentration during batch fermentation agitated at 500 rpm under an aeration rate of 0.5 vvm


Table 2.

Comparison of foam fractionation for biosurfactant recovery from this work with other studies

4. Conclusion

At the end of this experiment, 2.93 g/L rhamnolipid was successfully obtained from the foam collected. The suitable agitation rate is very important to maintain the homogeneity of the medium and bacterial cells in the bioreactor. Using this combination (500 rpm and 0.5 vvm), a uniform distribution of the gas phase and sufficient gas-liquid mass transfer was achieved. With the foam recycler system, the foam was successfully fractionated and yielded a much higher rhamnolipid concentration. Severe foam formation was kept under control throughout the cultivation without the addition of an antifoam agent. Further research is needed to improve the system, namely to enhance the production where the other modes of cultivation (fed-batch or continuous) can be explored.


The authors gratefully acknowledge the financial support for this work in the form of the Postgraduate Incentive Grant, University Sains Malaysia (USM) and the National Science Fellowship, Ministry of Science, Technology and Innovation, Malaysia (MOSTI). All equipment and facilities are provided by USM.


1 - I. M. Banat, 1995 A review: Biosurfactant production and possible uses in microbial enhanced oil recovery and oil pollution remediation. Bioresource Technology, 51 1-12.
2 - I. M. Banat, R. S. Makkar, S. S. Cameotra, 2000 Potential commercial application of microbial surfactants. Applied Microbiology Biotechnology, 53 495-508.
3 - C. Y. Chen, S. C. Baker, R. C. Darton, 2006a Continuous production of biosurfactant with foam fractionation. Journal of Chemical Technology and Biotechnology, 81 1915-1922.
4 - C. Y. Chen, S. C. Baker, R. C. Darton, 2006b Batch production of biosurfactant with foam fractionation. Journal of Chemical Technology and Biotechnology, 81 1923-1931.
5 - D. A. Davis, H. C. Lynch, J. Varley, 2001 The application of foaming for the recovery of surfactin from Bacillus subtilis ATCC 21332 cultures. Enzyme Technology, 28 346-354.
6 - M. Deleu, M. Paquot, 2004 From renewable vegetables resources to microorganisms: New Trends in Surfactants. Comptes Rendus Chimie, 7 641-646.
7 - J. D. Desai, A. J. Desai, 1993 Production of biosurfactants. In: Kosaric N, (ed) Biosurfactants. New York: Marcel Dekker. 65 97 .
8 - E. Heinzle, A. Biwer, C. Cooney, 2006 Development of Sustainable Bioprocess, In: Development of Sustainable Bioprocess, 32 57 , John Wiley & Sons Ltd, 978-0-470-01559-9, England.
9 - S. Joshi, C. Bharucha, S. Jha, S. Yadav, A. Nerurkar, A. J. Desai, 2008 Bioresource Technology, 99 195-199.
10 - R. M. Maier, 2003 Biosurfactant: evolution and diversity in bacteria. Advanced Applied Microbiology, 52 101-121.
11 - S. Mukherjee, P. Das, R. Sen, 2006 Towards commercial production of microbial surfactants. Trends in biotechnology. 24 11 509-515.
12 - C. N. Mullican, 2005 Environmental applications for biosurfactants. Environmental Pollution. 133 183-198.
13 - C. N. Mulligan, B. F. Gibbs, 1993 Factors influencing the economics of biosurfactants. In: Kosaric, N. (ed.). Biosurfactants Production, Properties and Applications. New York: Marcel Dekker, Inc. 329 371 .
14 - C. N. Mulligan, S. Wang, 2006 Remediation of a heavy metal-contaminated soil by rhamnolipid foam. Engineering Geology, 86 75-81.
15 - K. S. Noah, S. L. Fox, D. F. Bruhn, 2002 Development of continuous surfactin production from potato process effluent by Bacillus subtilis in an airlift reactor. Applied Biochemistry Biotechnology. 100 803-813.
16 - T. Sarachat, O. Pornsunthorntawee, S. Chadavej, R. Rujiravanit, 2010 Purification and concentration of rhamnolipid biosurfactant produced by pseudomonas aeruginosa SP4 using foam fractionation. Bioresource Technology. 101 324-330.
17 - M. S. Yeh, Y. H. Wei, J. S. Chang, 2006 Bioreactor design for enhanced carrier-assisted surfactin production with Bacillus subtilis. Process Biochemistry, 41 1799-1805.