HOME JOURNALS CONTACT

Trends in Applied Sciences Research

Year: 2014 | Volume: 9 | Issue: 2 | Page No.: 93-102
DOI: 10.17311/tasr.2014.93.102
Production of Spirulina platensis Biomass Using Digested Vinasse as Cultivation Medium
Budiyono , Iqbal Syaichurrozi, Siswo Sumardiono and Setia Budi Sasongko

Abstract: Spirulina platensis is one of the potential food sources in the future. Many authors have investigated the potential of wastewater as cultivation medium for microalgae, but utilization digested vinasse as cultivation medium has not reported yet. The purpose of this study was to investigate the potential of digested vinasse as cultivation medium for Spirulina platensis. Digested vinasse contained 30,250 mg L-1 Chemical Oxygen Demand (COD), 11,343.75 mg L-1 total carbon, 688.2 mg L-1 total N, 219.9 mg L-1 PO4-3-P. Cultivation was done in batch system at room temperature using erlenmeyer and using TL lamp as light source. Optical Density (OD) of culture was measured using spectrophotometry UV-VIS at wave length (λ) 680 nm every day. The results showed that the addition of digested vinasse more than 0.8% v/v (242 mg L-1 COD content) caused growth rate of S. platensis very slowly. Presence of organic compounds in medium reduced the production of photosynthetic pigment so that it hampered the rate of photosynthesis. Besides that, phenolic compounds contained in digested vinasse could damage the membrane cell of S. platensis. The maximum growth rates at digested vinasse addition of 0.0 (without addition); 0.8; 1.6; 2.4; 3.2; 4.0; 4.8 were 0.168; 0.143; 0.073; 0.044; 0.042; 0.030; 0.005 day-1, respectively. Utilization of nutrients in digested vinasse could reduce 50% of the synthetic nutrient need. Medium which had Carbon:Nitrogen:Phosphorus (C:N:P) ratio of 60.5:6.2:1 was the best medium to cultivate S. platensis with maximum growth rate of 0.220 day-1.

Fulltext PDF Fulltext HTML

How to cite this article
Budiyono , Iqbal Syaichurrozi, Siswo Sumardiono and Setia Budi Sasongko, 2014. Production of Spirulina platensis Biomass Using Digested Vinasse as Cultivation Medium. Trends in Applied Sciences Research, 9: 93-102.

Keywords: Biomass, cultivation, digested vinasse and Spirulina platensis

INTRODUCTION

Cultivation of Spirulina has many advantages compared to that of other microalgaes. Production of Spirulina biomass rate is faster than that of some others. Spirulina has so big biomass size that it easy to harvest and Spirulina can live in extreme conditions (very alkaline) with pH range of 8-11 (Desmorieux and Decaen, 2005; Richmond, 1988). According to Kozlenko and Henson (1998), Spirulina is one of the potential food sources because 1 acre of Spirulina can produce 20 times as many proteins as 1 acre soybean or corn. Spirulina contains high level of protein in range of 60-71% of dry weight and 65% higher than other natural foods. Fat contents in Spirulina have range of 6-7% and the most of that are unsaturated fats (Tietze, 2004; Spolaore et al., 2006).

Microalgae can be applied on wider field of technology. It not only produces biomass that can be used as food and energy source but also can be used to reduce COD content, nitrogen-phosphorus, heavy metals of wastewater. COD, N and P contained in wastewater are utilized by microalgae as nutritional source to grow. From an economic perspective, the culturing microalgae in wastewater can reduce the cost of synthetic nutrient need (Hadiyanto and Hartanto, 2012) cultivated Spirulina sp. in medium which contained POME (Palm Oil Mil Effluent). Spirulina sp. could thrive with 20% concentration of POME and 50% reduction in synthetic nutrient need. Duangsri and Satirapipathkul (2011) reported that Spirulina sp. could grow well in medium brine wastewater. Cheunbarn and Peerapornpisal (2010) reported that medium cultivation that contained 10% swine wastewater treatment effluent, 8 g L-1 NaHCO3 and 1.5 g L-1 NaNO3 caused the most maximum growth rate of S. platensis. Andrade and Costa (2007) conducted cultivation of S. platensis using molasses. Concentration of molasses 0.75 g L-1 caused the most maximum biomass production of S. platensis compared to that of molasses 0.25 and 0.5 g L-1.

Cultivation of microalgae using digested vinasse has not reported yet. In author’s previous research, authors treated vinasse, bottom product of distillation in bioethanol industry, using anaerobic digester. Thus, vinasse that had been processed using anaerobic digester was called digested vinasse. Digested vinasse contained a number of nutrients such as COD, total of nitrogen and PO4-3P. These contents could be utilized as nutritional source by microalgae.

The objectives of this study were to investigate the effect of addition digested vinasse to growth rate of S. platensis and pH culture and to know the best percentage reduction of synthetic nutrients.

MATERIALS AND METHODS

Microalgae and digested vinasse: Microalgae used was Spirulina platensis obtained from the collection of C-BIORE (Center of Biomass and Renewable Energy), University of Diponegoro, Indonesia. Culture of S. platensis that had OD680 value~0.6 was used as inoculum. Digested vinasse was obtained from variable in author’s previous research that produced the most of total biogas. Digested vinasse used in this study contained 30,250 mg L-1 COD; 11,343.75 mg L-1 total Carbon; 688.2 mg L-1 total Nitrogen; 219.9 P-PO4-3. In addition, pH condition of digested vinasse used in this study was 6.7.

Experimental set up: Synthetic medium used was cultivation medium for S. platensis developed by Hadiyanto and Hartanto (2012) with nutrients: 1 g L-1 NaHCO3 (purity 98%), 0.05 g L-1 urea (46% N content), 10 ppm TSP (45% P2O5 content). S. platensis could grow optimally at room temperature, so cultivation was done at room temperature. Artificial light as light source was obtained from tube light (TL) lamp 18 watt placed with distance of 10-15 cm from culture. Initial pH culture was adjusted 9.0 using HCl 1 M or NaOH 1 M.

Experimental design
Scenario I: Cultivation medium with total volume 1 L was operated in batch system using erlenmeyer. Digested vinasse was added into media with variety in concentration of 0, 0.8, 1.6, 2.4, 3.2, 4.0, 4.8% v/v medium. Inoculum of S. platensis 10% v/v was added into medium. In this scenario, all of cultures were added synthetic nutrients 100% (1 g L-1 NaHCO3 (purity 98%), 0.05 g L-1 urea (46% N content), 10 ppm TSP (45% P2O5 content)) (Table 1). Initial pH for all cultures was adjusted 9.0.

Table 1: Composition of digested vinasse, tap water, inoculum and synthetic nutrient in cultivation mediums

Scenario II: Addition of digested vinasse concentration in medium that had the best growth rate of S. platensis from scenario I, was used in this scenario. Then, it was combined with addition of synthetic nutrients of 100, 75, 50, 25, 0% (Table 1). Initial pH for all culture was adjusted 9.0.

Experimental procedures: Cultivation was done using erlenmeyer in 13-20 days. Optical density of all variables was measured two times by using spectrophotometry UV-VIS at λ 680 nm every day. Value of pH medium was measured by using pH meter every day. The results of investigation were used to calculate the growth rate, growth curve and pH profile curve:

Remarks: μ, growth rate (day-1); ODi, Optical density at ti; OD0, Optical density at t0; ti, cultivated time I; t0, cultivated time 0.

RESULTS AND DISCUSSION

Effect of addition of digested vinasse (Scenario I): The results showed that the higher the concentration of digested vinasse was added into medium, the slower S. platensis grow in medium (Fig. 1). In media I (without addition of digested vinasse), S. platensis thrived from beginning of cultivation until 14th day, then decreased until ending of cultivation with the highest OD680 1.126. While in media II, S. platensis biomass reached the highest OD680 at 16th day with value of 1.070 (Table 2). In the addition of digested vinasse more than 0.8% v/v, S. platensis needed a very long time to adapt, 8 days in medium III, 9 days in medium IV, 11 days in medium V, 11 days in medium VI and 14 days in medium VII (Fig. 1). The length of adaptation due to the high concentration of COD added into medium. Travieso et al. (1996) stated that microalgae could grow well and set aside maximum of COD 88% when medium contained 250 mg L-1 COD concentration of settled piggery wastewater from variety ranges of COD between 250-1,100 mg L-1. The results of this study were consisted with that of Travieso et al. (1996), where the addition of digested vinasse 242 mg L-1 COD (medium I) caused growth of S. platensis better than the addition of digested vinasse more than 242 mg L-1 COD (medium III-VII).

Fig. 1(a-b): The effect of addition of digested vinasse to (a) Growth curve of S. platensis and (b) Profile pH medium

Table 2: The effect of addition of digested vinasse to maximum growth rate (μmax ), optical density (OD) and maximum time (tOD) (Scenario I)
COD: Chemical Oxygen Demand; C:N:P: Carbon:Nitrogen:Phosphorus; OD 680max: Maximum optical density reached at λ 680 nm; tOD 680 max: Time at OD 680680 reached; μmax: Maximum growth rate reached at OD 680max and tOD 680 max

The addition of high concentration of COD caused dark color and turbidity which were high in medium, so the penetration of light into medium was small. This phenomenon disrupted photosynthetic activity of S. platensis. Cheunbarn and Peerapornpisal (2010) stated that S. platensis could not thrive in medium which contained high organic substances because that could affect dark color and turbidity. Thus, the photosynthetic rate of S. platensis was slowly. Hadiyanto and Hartanto (2012) confirmed that the dark color as an effect of presence of wastewater caused decreasing in the intensity of light into medium so that the process of photosynthesis was impaired.

In media I and II, pH increased from the beginning of cultivation until 12th day with the highest pH were 10.3 and 10.2, respectively (Fig. 1). The increasing of pH was caused by presence of sodium bicarbonate (NaHCO3) in medium. Sodium bicarbonate was dissolved into Na+ and HCO3¯ (bicarbonate ion). Na+ was used as micro nutrient by S. platensis while HCO3- was converted in form CO2 and OH¯ with help of enzyme carbonic anhydrase (Reuter and Muller, 1993; Jaiswal et al., 2005; Badger et al., 1994). CO2 formed was utilized as carbon source for photosynthesis. Ion OH¯ accumulated in medium caused alkaline in pH (Richmond and Grobbelaar, 1986; Grobbelaar, 2004; De Morais and Costa, 2007).

The increasing in pH was related with photosynthetic activity, where the higher the rate of photosynthetic activity, the higher the pH medium (Andrade and Costa, 2007). The maximum pH value indicated that chlorophyll a concentration of S. platensis was maximum and growth phase of S. platensis no longer sustained and reached death phase (Kim et al., 2007). In Fig. 1, S. platensis reached the point of death on the 14th day and 16th day respectively in medium I and II after it reached the highest pH at 12th day.

While in medium III-VII, pH decreased at first time of cultivation and then went up. This phenomenon might be caused by activity of bacteria in medium. The more concentration of digested vinasse were added, the more amount of bacteria was contained in medium. Based on principle that was proposed by Oswald et al. (1957), at beginning of cultivation oxidation bacteria in medium converted organic compounds of wastewater into CO2 via respiration. CO2 formed reacted with water to form carbonate, so medium to be acidic. Then, carbonate was used by S. platensis for photosynthetic process and released OH¯, so pH medium gradually increased.

Besides activity of bacterial oxidation might participate in the system, S. platensis also utilized organic carbon as source of carbon to produce CO2 through respiration. This growth was called heterotrophic growth, whereby energy and carbon source derived from organic carbon such as glucose. Carbon dioxide formed caused acidic in pH medium. Furthermore, S. platensis used CO2 for photosynthesis. This growth was called photoautotrophic growth which utilized light as primary energy source and carbon dioxide as primary carbon source. Because of photoautotrophic growth, pH medium was gradually increased. Photoautotrophic and heterotrophic processes that took place simultaneously in cell were called mixotrophic growth (Marquez et al., 1993).

Ogbonna and Tanaka (1998) stated that addition of organic carbon would reduce the production of photosynthetic pigments, so rate of photosynthesis was slowly. Carbon dioxide was the main of carbon source needed in photosynthesis. In this study, carbon dioxide was obtained from NaHCO3. The more digested vinasse was added into medium, the more slowly rate of photosynthesis went on in system (Fig. 1).

Production of biomassa in media I and II declined after 14th dan 16th, respectively. This declined phase was called death phase because a lot of algal cells were death. This phase was occurred due to the age old culture and the limitation of light and energy supply. Membran cell of S. platensis broke (lysis), so organic materials in cell were out and dissolved into medium (Fogg and Thake, 1987). This phenomenon might cause decreasing in pH medium. This could be shown in Fig. 1, growth of S. platensis decreased and pH of medium decreased too.

The maximum growth rate (μmax) of S. platensis on each medium could be seen in Table 2. The greater the concentration of digested vinasse, the smaller the maximum growth rate. Media II, with the addition of the smallest concentration of digested vinasse (0.8% v/v or 242 mg L-1 COD), had the highest μmax of the others (medium III-VII). However, medium II had less μmax than media I (without digested vinasse addition) although medium II had more time of exponential phase than medium I. That was caused by dark color and turbidity medium that reduced penetration of light into medium. Richmond (1988) confirmed that organic carbon and light were two important factors that influenced the growth of mixotrophic microalgae.

Effect of variation of synthetic nutrient addition (Scenario II): After cultivation in 13 days, maximum growth rate on each medium was shown in Table 3. Maximum growth rate in media A, B, D, E had almost the same value, there was 0.163-0.169 day-1, while medium C had maximum growth rate of 0.220 day-1. This result was caused by availability of optimum number of nutrients in medium. Phang and Ong (1988) reported that the ideal C:N:P ratio for microalgal cultivation was 56:9:1. Medium C with C:N:P ratio of 60.5:6.2:1 gave the best results compared to C:N:P ratio of the other mediums. From Table 3, C:N:P ratio of medium C was the closest to the ideal C:N:P ratio proposed by Phang and Ong (1988). However, after 9th day of cultivation, the growth rate S. platensis in medium C decreased. Phenol in vinasse that was not degraded during the anaerobic processing might cause decreasing in growth rate of S. platensis.

OD 680max on media A and B were too low (below 0.6). OD value that can be used as inoculum was at least 0.5-0.6. Besides that, biomass in media A and B were yet to be harvested because it was just little. Meanwhile, media C, D, E had OD 680max that was eligible as inoculum. The higher synthetic nutrients were added in medium, the higher OD 680max and tOD 680 max (Table 3). These results showed that the utilization of digested vinasse could not replace all of synthetic nutrient need. Medium A (without synthetic nutrients) had the smallest OD 680max and μmax because availability ratio of carbon, nitrogen and phosphorus was not optimal.

Medium C had the highest μmax that was achieved at 9th day of cultivation. S. platensis could grow quickly in medium C until 9th day of cultivation then decreased till the end of cultivation. This phenomenon was caused by nutrient that was needed by S. platensis, that already exhausted absorbed in the first 8 days. While in medium D and E, S. platensis could grow up to 2th and 13th day.

Table 3: The effect of addition of digested vinasse to maximum growth rate (μmax ), optical density (OD) and maximum time (tOD) (Scenario II)
COD: Chemical Oxygen Demand; C:N:P: Carbon:Nitrogen:Phosphorus; OD 680max: Maximum optical density reached at λ 680 nm; tOD 680 max: Time at OD 680680 reached; μmax: Maximum growth rate reached at OD 680max and tOD 680 max

Fig. 2(a-b): The effect of variation of synthetic nutrient addition to (a) Growth curve of S. platensis and (b) Profile pH medium

Synthetic nutrient was very important as source of nutrition beside nutrient from digested vinasse. These indicated that autotrophic character of S. platensis was more than heterotrophic character if there were a number of inorganic carbon source (NaHCO3) in medium.

pH of media A, B, C and D decreased at beginning of cultivation. While medium E, pH went up from beginning to end cultivation (Fig. 2). Decreasing in pH was caused by the lower availability of bicarbonate in medium A, B, C, D than that in medium E. Bicarbonate in medium was dissolved into CO2 and OH¯ during cultivation. Accumulation of OH- caused increasing in pH (Richmond and Grobbelaar, 1986; Grobbelaar, 2004; De Morais and Costa, 2007). Besides that, decreasing in pH could be caused by mixotrophic growth which utilized organic carbon (such as organic acid, acetic acid, sugar and glycerol) as carbon source via respiration (Borowitzka, 1998; Kawaguchi, 1980; Fogg, 1975; Ogbonna et al., 2000; Wood et al., 1999). Respiratory activity produced CO2 that caused pH medium low. In medium E, pH rose at the early cultivation because photosynthesis process was more dominant than respiration process.

The results of this study were much better than the results of study reported by Hadiyanto and Hartanto (2012) whereby medium of cultivation that contained 20% v/v POME and 50% synthetic nutrients gave the best growth rate of Spirulina platensis (0.142 day-1). Meanwhile in this study, medium C, with addition of the same synthetic nutrients (50%) and 0.8% v/v digested vinasse had growth rate of 0.220 day-1. In addition, the results of this study were better than the results of study conducted by Andrade and Costa (2007) whereby maximum growth rate of S. platensis was 0.147 day-1 in medium which contained 0.25 g L-1 molasses.

Microalgal growth could be hampered by the presence of phenol in medium. Some authors reported that Chlorella sp., S. obliquus and Spirulina maxima could not grow by using phenol as carbon source (Semple and Cain, 1997; Klekner and Kosaric, 1992; Scragg, 2006) added that Chlorella vulgaris and Chlorella VT-1 also could not thrive in medium containing phenol compounds. Phenol in medium damaged the structure of membrane cell (Leonard and Lindley, 1999). Digested vinasse used in this study might contain phenolic compounds.

CONCLUSION

Medium that contained 0.8% v/v digested vinasse (242 mg L-1 COD) was the best medium to grow S. platensis. Inhibition of growth was caused by presence of organic compound in medium so medium became dark and turbidity that caused slowly penetration of light into medium. Besides that, organic compounds in medium reduced production of photosynthetic pigments so rate of photosynthesis was very slowly. Combination of 0.8% v/v digested vinasse and 50% synthetic nutrient (medium C) gave the most satisfactory result which was the largest growth rate value of 0.220 day-1. Medium C had ideal C:N:P ratio which was 60.5:6.2:1.

ACKNOWLEDGMENT

The authors thank to Indonesian Ministry of Higher Education for financial support via Hibah Kompetensi Program year 2012.

REFERENCES

  • Andrade, M.R. and J.A.V. Costa, 2007. Mixotrophic cultivation of microalga Spirulina platensis using molasses as organic substrate. Aquaculture, 264: 130-134.
    CrossRef    


  • Badger, M.R., K. Palmqvist and J.W. Yu, 1994. Measurement of CO2 and HCO3- fluxes in cyanobacteria and microalgae during steady-state photosynthesis. Physiol. Plant., 90: 529-536.
    CrossRef    


  • Borowitzka, M.A., 1998. Limits to Growth. In: Wastewater Treatment with Algae, Wong, Y.S. and N.F.Y. Tam (Eds.). Springer-Verlag, New York, USA., ISBN-13: 9783540633631, pp: 203-226


  • Cheunbarn, S. and Y. Peerapornpisal, 2010. Cultivation of Spirulina platensis using anaerobically swine wastewater treatment effluent. Int. J. Agric. Biol., 12: 586-590.


  • Kim, C.J., Y.H. Jung and H.M. Oh, 2007. Factors indicating culture status during cultivation of Spirulina (Arthrospira) platensis. J. Microbil., 45: 122-127.
    PubMed    


  • Desmorieux, H. and N. Decaen, 2005. Convective drying of spirulina in thin layer. J. Food Eng., 66: 497-503.
    CrossRef    Direct Link    


  • De Morais, M.G. and J.A.V. Costa, 2007. Biofixation of carbon dioxide by Spirulina sp. and Scenedesmus obliquus cultivated in a three-stage serial tubular photobioreactor. J. Biotechnol., 129: 439-445.
    CrossRef    


  • Duangsri, P. and C. Satirapipathkul, 2011. Spirulina sp. production in brine wastewater from pickle factory. Proceedings of the International Conference on Bioscience, Biochemistry and Bioinformatics, February 26-28, 2011, Singapore, pp: 415-418.


  • Fogg, G.E., 1975. Algal Cultures and Phytoplankton Ecology. 2nd Edn., The University of Wisconsin Press, Wisconsin, USA., ISBN-13: 9780299067601, Pages: 175


  • Fogg, G.E. and B. Thake, 1987. Algal Cultures and Phytoplankton Ecology. 3rd Edn., The University of Wisconsin Press, USA., ISBN-13: 9780299105600, Pages: 269


  • Grobbelaar, J.U., 2004. Algal Nutrition: Mineral Nutrition. In: Handbook of Microalgal Culture: Biotechnology and Applied Phycology, Richmond, A., (Ed.). Chapter 6, Blackwell Publishing Ltd., Oxford, UK., ISBN-13: 9780632059539, pp: 97-115


  • Hadiyanto, M.M.A.N. and G.D. Hartanto, 2012. Enhancement of biomass production from Spirulina sp cultivated in POME medium. Proceedings of the International Conference on Chemical and Material Engineering, September 12-13, 2012, Semarang Indonesia, pp: 1-6.


  • Jaiswal, P., R. Prasanna and A.K. Kashyap, 2005. Modulation of carbonic anhydrase activity in two nitrogen fixing cyanobacteria, Nostoc calcicola and Anabaena sp. J. Plant Physiol., 162: 1087-1094.
    CrossRef    


  • Kawaguchi, K., 1980. Microalgae Production Systems in Asia. In: Algae Biomass Production and Use, Shelef, G. and C.J. Soeder (Eds.). Elsevier/North Holland Biomedical Press, Amsterdam, pp: 25-33


  • Klekner, V. and N. Kosaric, 1992. Degradation of phenols by algae. Environ. Technol., 13: 493-501.
    CrossRef    


  • Kozlenko, R. and R.H. Henson, 1998. Spirulina latest scientific research: Effects on the AIDS virus, cancer and the immune system. http://www.thebody.com/cgi-bin/bbs/showflat.php?Board=treatment&Number=204588.


  • Richmond, A., 1988. Spirulina. In: Micro-Agal Biotechnology, Borowitzka, M.A. and L.J. Borowitzka (Eds.). Cambridge University Press, Cambridge, UK., ISBN-13: 9780521323499


  • Leonard, D. and N.D. Lindley, 1999. Growth of Ralstonia eutropha on inhibitory concentrations of phenol: Diminished growth can be attributed to hydrophobic perturbation of phenol hydroxylase activity. Enzyme Microb. Technol., 25: 271-277.
    CrossRef    


  • Marquez, F.J., K. Sasaki, T. Kakizono, N. Nishio and S. Nagai, 1993. Growth characteristics of Spirulina platensis in mixotrophic and heterotrophic conditions. J. Ferment. Bioeng., 76: 408-410.
    CrossRef    Direct Link    


  • Ogbonna, J.C. and H.C. Tanaka, 1998. Cyclic autotrophic/heterotrophic cultivation of photosynthetic cells: A method of achieving continuous cell growth under light/dark cycles. Bioresour. Technol., 65: 62-72.
    CrossRef    


  • Ogbonna, J.C., H. Yoshizawa and H. Tanaka, 2000. Treatment of high strength organic wastewater by a mixed culture of photosynthetic microorganisms. J. Applied Phycol., 12: 277-284.
    CrossRef    


  • Oswald, W.J. and H.B. Gotaas, 1957. Photosynthesis in sewage treatment. Trans. Am. Soc. Civil Eng., 122: 73-105.
    Direct Link    


  • Phang, S.M. and K.C. Ong, 1988. Algal biomass production in digested palm oil mill effluent. Biol. Wastes, 25: 177-191.
    CrossRef    


  • Reuter, W. and C. Muller, 1993. New trends in photobiology: Adaptation of the photosynthetic apparatus of cyanobacteria to light and CO2. J. Photochem. Photobiol. B: Biol., 21: 3-27.
    CrossRef    


  • Richmond, A. and J.U. Grobbelaar, 1986. Factors affecting the output rate of Spirulina platensis with reference to mass cultivation. Biomass, 10: 253-264.
    CrossRef    


  • Scragg, A.H., 2006. The effect of phenol on the growth of Chlorella vulgaris and Chlorella VT-1. Enzyme Microb. Technol., 39: 796-799.
    CrossRef    


  • Semple, K.T. and R.B. Cain, 1997. Degradation of phenol and its methylated homologues by Ochromonas danica. FEMS Microbiol. Lett., 152: 133-139.
    CrossRef    


  • Spolaore, P., C. Joannis-Cassan, E. Duran and A. Isambert, 2006. Commercial applications of microalgae. J. Biosci. Bioeng., 101: 87-96.
    CrossRef    PubMed    Direct Link    


  • Tietze, H.W., 2004. Spirulina Micro Food Macro Blessing. 4th Edn., Harald Tietze Publishing, Australia


  • Travieso, L., F. Benitez, P. Weiland, E. Sanchez, R. Dupeyron and A.R. Dominguez, 1996. Experiments on immobilization of microalgae for nutrient removal in wastewater treatments. Bioresour. Technol., 55: 181-186.
    CrossRef    


  • Wood, B.J.B., P.H.K. Grimson, J.B. German and M. Turner, 1999. Photoheterotrophy in the production of phytoplankton organisms. J. Biotechnol., 70: 175-183.
    CrossRef    Direct Link    

  • © Science Alert. All Rights Reserved