Skip to main content

Advertisement

Log in

On-line estimation of O2 production, CO2 uptake, and growth kinetics of microalgal cultures in a gas-tight photobioreactor

  • Published:
Journal of Applied Phycology Aims and scope Submit manuscript

Abstract

Growth of the green algae Chlamydomonas reinhardtii and Chlorella sp. in batch cultures was investigated in a novel gas-tight photobioreactor, in which CO2, H2, and N2 were titrated into the gas phase to control medium pH, dissolved oxygen partial pressure, and headspace pressure, respectively. The exit gas from the reactor was circulated through a loop of tubing and re-introduced into the culture. CO2 uptake was estimated from the addition of CO2 as acidic titrant and O2 evolution was estimated from titration by H2, which was used to reduce O2 over a Pd catalyst. The photosynthetic quotient, PQ, was estimated as the ratio between O2 evolution and CO2 up-take rates. NH4 +, NO2 , or NO3 was the final cell density limiting nutrient. Cultures of both algae were, in general, characterised by a nitrogen sufficient growth phase followed by a nitrogen depleted phase in which starch was the major product. The estimated PQ values were dependent on the level of oxidation of the nitrogen source. The PQ was 1 with NH4 + as the nitrogen source and 1.3 when NO3 was the nitrogen source. In cultures grown on all nitrogen sources, the PQ value approached 1 when the nitrogen source was depleted and starch synthesis became dominant, to further increase towards 1.3 over a period of 3–4 days. This latter increase in PQ, which was indicative of production of reduced compounds like lipids, correlated with a simultaneous increase in the degree of reduction of the biomass. When using the titrations of CO2 and H2 into the reactor headspace to estimate the up-take of CO2, the production of O2, and the PQ, the rate of biomass production could be followed, the stoichiometrical composition of the produced algal biomass could be estimated, and different growth phases could be identified.

This is a preview of subscription content, log in via an institution to check access.

Access this article

Price excludes VAT (USA)
Tax calculation will be finalised during checkout.

Instant access to the full article PDF.

Figure 1
Figure 2
Figure 3
Figure 4

Similar content being viewed by others

References

  • Arvola L (1981) Spectrophotometric determination of chlorophyll a and phaopigments in ethanol extraction. Ann Bot Fenn 8:221–227

    Google Scholar 

  • Atkins PW (1980) Physical chemistry. Oxford University Press, Oxford

    Google Scholar 

  • Ball SG (2002) The intrinsic pathway of starch biosynthesis and degradation in the monocellular alga Chlamydomonas reinhardtii. Aust J Chem 55:49–59

    Article  CAS  Google Scholar 

  • Behrens PW, Sicotte VJ, Delente J (1994) Microalgae as a source of stable isotopically labelled compounds. J Appl Phycol 6:113–121

    Article  CAS  Google Scholar 

  • Coleman LW, Rosen BH, Schwartzbach SD (1988) Preferential loss of chloroplast proteins in nitrogen deficient Euglena. Plant Cell Physiol 29:1007-1014

    CAS  Google Scholar 

  • Delente JJ, Behrens PW, Hoeksema SD (1992) Closed photobioreactor and method of use. United States Patent 5,151,347

  • Eriksen NT, Iversen JJL (1995) On-line determination of pigment composition and biomass in cultures of microalgae. Biotechnol Tech 9:49–54

    Article  CAS  Google Scholar 

  • Eriksen NT, Geest T, Iversen JJL (1996) Phototrophic growth in the lumostat: a photo-bioreactor with on-line optimization of light intensity. J Appl Phycol 8:345–352

    Article  CAS  Google Scholar 

  • Galván A, Quesada A, Fernández E (1996) Nitrate and nitrite are transported by different specific transport systems and by a bispecific transporter in Chlamydomonas reinhardtii. J Biol Chem 271:2088–2092

    Article  PubMed  Google Scholar 

  • Geankopolis CJ (1978) Transport processes and unit operations. Allyn and Bacon, Boston

    Google Scholar 

  • Kalacheva GS, Zhila NO, Volova TG (2002) Lipid and hydrocarbon compositions of a collection strain and a wild sample of the green microalga Botryococcus. Aquat Ecol 36:317-330

    Article  CAS  Google Scholar 

  • Liu X, Gong JK, Collins AW, Grove LJ, Seyler JW (2001) Theoretical study of carbon dioxide coordination in palladium complexes. Appl Organomet Chem 15:95–98

    Article  Google Scholar 

  • Molina Grima E, Pérez JAS, Camacho FC, Medina AR, Giménez AG, Alonso DL (1995) The productivity of polyunsaturaated fatty acids by microalgae: from strain selection to product purification. Process Biochem 30:711–719

    Article  CAS  Google Scholar 

  • Navarro MT, Guerra E, Fernández E, Galván A (2000) Nitrite reductase mutants as an approach to understanding nitrate assimilation in Chlamydomonas reinhardtii. Plant Physiol 122:283–289

    Article  PubMed  CAS  Google Scholar 

  • Nowakowski R, Grzeszczak P, Dús R (2002) AFM studies of the catalytic reaction of hydrogen with oxygen on thin Pd and Pt films under pressure ∼101 kPa. Surf Sci 507–510:813–818

    Article  Google Scholar 

  • Redfield AC, Ketchum BH, Richards FA (1963) The influence of organisms on the composition of sea-water. In: Hill MN (ed) The sea: ideas and observations on progress in the study of the seas. Wiley, New York, pp 26–77

    Google Scholar 

  • Rexach J, Llamas A, Fernandéz E, Galván A (2002) The activity of the high-affinity nitrate transport system I (NRT2;1, NAR2) is responsible for the efficient signalling of nitrate assimilation genes in Chlamydomonas reinhardtii. Planta 215:606–611

    Article  PubMed  CAS  Google Scholar 

  • Rexach J, Montero B, Fernández E, Galván A (1999) Differential regulation of the high affinity nitrite transport systems III and IV in Chlamydomonas reinhardtii. J Biol Chem 274:27801–27806

    Article  PubMed  CAS  Google Scholar 

  • Richardson K, Beardall J, Raven JA (1983) Adaptation of unicellular algae to irradiance: An analysis of strategies. New Phytol 93:157–191

    Article  Google Scholar 

  • Rigano VDM, Vona V, Cargagna S, Esposito S, Carillo P, Rigano C (2000) Effects of sulfate-starvation and re-supply on growth, NH4 + uptake and starch metabolism in Chlorella sorokiniana. Aust J Plant Physiol 27:335–342

    Article  Google Scholar 

  • Roels JA (1980) Applications of macroscopic principles to microbial metabolism. Biotechnol Bioeng 22:2457–2514

    Article  CAS  Google Scholar 

  • Starr RC (1978) The culture collection of algae at The University of Texas at Austin. J Phycol 14:47–100

    Article  Google Scholar 

  • Stenholm H, Song S, Eriksen NT, Iversen JJL (1998) Indirect estimation of poly-ß-hydroxybutyric acid by cell carbon analysis. Biotechnol Techn 12:451–454

    Article  CAS  Google Scholar 

  • Stumm W, Morgan JJ (1995) Aquatic chemistry. Wiley, New York

    Google Scholar 

  • Zhila NO, Kalacheva GS, Volova TG (2005) Effect if nitrogen limitation on the growth and lipid composition of the green alga Botryococcus braunii Kütz IPPAS H-252. Russ J Plant Physiol 52:357–365

    Article  CAS  Google Scholar 

  • Zittelli GC, Lavista F, Bastianini A, Rodolfi L, Vincenzini M, Tredici MR (1999) Production of eicosapentaenoic acid by Nannochloropsis sp. cultures in outdoor tubular photobioreactors. J Biotechnol 70:299–312

    Article  Google Scholar 

Download references

Acknowledgments

We thank Dr. Niels Iversen for help measuring nitrogen sources, Lars Jørgensen, DB Lab, for carrying out the biomass elemental composition analysis, and Gunnar Andersen for technical assistance.

Author information

Authors and Affiliations

Authors

Corresponding author

Correspondence to Niels Thomas Eriksen.

Appendix

Appendix

Distribution of CO2 in gas tight photobioreactor

To account for the effect of uptake of the nitrogen source on the total content of inorganic carbon in the photobioreactor, the distribution of inorganic carbon between the Pd catalyst, the gas phase, and the liquid medium was calculated. Since batch cultures were grown over relative long periods of time (200–300 h), the calculations were based on pseudo-steady-state conditions

$$ CO_{{2,Pd}} \leftrightarrows CO_{{2,gas}} \leftrightarrows H_{2} CO^{ * }_{{3aq}} \leftrightarrows HCO^{ - }_{{3aq}} + H^{ + }_{{aq}} \leftrightarrows CO^{{2 - }}_{{3aq}} + 2H^{ + }_{{aq}} $$
(A1)

The total amount of inorganic carbon in the photobioreactor, \( m_{{C_{i} }} \) was the sum of all pools of inorganic carbon present in the system as described in Eq. A1

$$ m_{{C_{i} }}=m_{{H_{2} CO^{*}_{3} ,aq}} + m_{{HCO^{,}_{3} ,aq}} + m_{{CO^{{2 - }}_{3} ,aq}} + m_{{CO_{2} ,gas}} + m_{{CO_{2} ,Pd}} $$
(A2)

where \( m_{{H_{2} CO^{*}_{3} ,aq}} ,\,m_{{HCO^{ - }_{3} ,aq}} \),and \( m_{{CO^{{2 - }}_{3} ,aq}} \) are the amounts of dissolved H2CO3 (including dissolved CO2), HCO3 , and CO3 2−, respectively, \( m_{{CO_{2} ,gas}} \) is the total amount of CO2 in the gas phase, and \( m_{{CO_{2} ,Pd}} \) is the total amount of CO2 adsorbed to the Pd catalyst.

At pH 7.5, CO3 2− constituted only in the order of 0.1% of the total dissolved inorganic carbon, and the amounts of inorganic carbon in the different pools described in Eqs. A1 and A2 were essentially controlled by the concentration of HCO3 in the growth medium. Since 1 mol of H+ was consumed for each mol of NO3 or NO2 taken up by the cells, these protons were regenerated by addition of CO2, which dissolved as HCO3 and resulted in an equimolar increase of [HCO3 ]. For each mol of NH4 + taken up, 1 mol of H+ was produced, and with NH4 + as the nitrogen source, less CO2 than taken up photosynthetically were therefore added to the photobioreactor resulting in an equimolar decrease of [HCO3 ]. The amount of dissolved HCO3 was therefore estimated by

$$m_{{HCO^{ - }_{3} .aq}}={\left( {{\left[ {HCO^{1}_{3} } \right]}_{{t_{0} }} \pm \Delta N} \right)} \cdot V_{L} $$
(A3)

where ΔN is the total decrease in concentration of the nitrogen source due to consumption by the algae, and V L is the volume of the liquid medium.

The amount of dissolved H2CO3 * in the growth medium was described by

$$ m_{{H_{2} CO^{*}_{{_{3} }} ,aq}}={\left( {\frac{{{\left[ {HCO^{ - }_{3} } \right]} \cdot {\left[ {H^{ + } } \right]}}} {{K_{1} }}} \right)} \cdot V_{L} $$
(A4)

where K 1 is the equilibrium constant between H2CO3 * and HCO3 + H+ (10−6.3 M, Stumm and Morgan 1995). The amount of dissolved CO3 2− is described by

$$ m_{{CO^{{2 - }}_{3} ,aq}}={\left( {\frac{{K_{2} \cdot {\left[ {HCO^{ - }_{3} } \right]}}} {{{\left[ {H^{ + } } \right]}_{{t_{0} }} }}} \right)} \cdot V_{L} $$
(A5)

where K 2 is the equilibrium constant between HCO3 and CO3 2− + H+ (10−10.3 M, Stumm and Morgan 1995).

The relationship between the partial pressure of CO2 in the headspace, \( p_{{CO_{2} }} \) and the concentration of H2CO3 * in the medium was described by Henry’s law

$$p_{{CO_{2} }}=K_{H} \cdot {\left[ {H_{2} CO^{ * }_{3} } \right]} $$
(A6)

where K H is Henry’s constant (3.0 • 103 kPa M−1, Atkins 1980). The total amount of CO2 in the headspace was calculated from \(p_{{CO_{2} }} \) using the gas law

$$ m_{{CO_{2} ,gas}}=\frac{{p_{{CO_{2} }} \cdot V_{G} }} {{R \cdot T}} $$
(A7)

where V G is the volume of the gas in the headspace and the closed gas loop, R is the gas constant, and T is the absolute temperature.

The amount of CO2 reversibly adsorbed onto the Pd catalyst was described by a Langmuir binding isotherm

$$ m_{{CO_{2} ,Pd}}=\frac{{c_{{CO_{2} ,Pd,\max }} \cdot W_{{Pd}} \cdot p_{{CO_{2} ,gas}} }} {{a + p_{{CO_{2} ,gas}} }} $$
(A8)

where \( c_{{CO_{2} ,Pd,\max }} \) is the maximal surface-cover of CO2 on the Pd catalyst (60 μmol g−1), W Pd is the mass of Pd catalyst in the catalytic column (25 g), and a is the half saturation constant (2.1 kPa). The parameters, \( c_{{CO_{2} ,Pd,\max }} \) and a were estimated by measuring the increase of partial pressure after adding known amounts of CO2 to a closed chamber containing the Pd catalyst.

If the nitrogen uptake is measured or modelled, it is now possible to calculate the relationship between the overall change in total inorganic carbon content and nitrogen content in the photobioreactor, \( \frac{{\Delta m_{{C_{i} }} }} {{\Delta N \cdot V_{L} }} \)

$$\frac{{\Delta m_{{C_{i} }} }}{{\Delta N \cdot V_{L} }}=\frac{{m_{{C_{i} }} - m_{{C_{i} t_{0} }} }}{{{\left( {N - N_{{t_{0} }} } \right)} \cdot V_{L} }} $$
(A9)

With NO3 and NO2 as nitrogen sources, \( \frac{{\Delta m_{{C_{i} }} }} {{\Delta N \cdot V_{L} }} \) is negative. With NH4 + as nitrogen source, \( \frac{{\Delta m_{{C_{i} }} }} {{\Delta N \cdot V_{L} }} \) is positive. In the experiments described in this paper, ΔN was estimated from Eq. 13.

Rights and permissions

Reprints and permissions

About this article

Cite this article

Eriksen, N.T., Riisgård, F.K., Gunther, W.S. et al. On-line estimation of O2 production, CO2 uptake, and growth kinetics of microalgal cultures in a gas-tight photobioreactor. J Appl Phycol 19, 161–174 (2007). https://doi.org/10.1007/s10811-006-9122-y

Download citation

  • Received:

  • Accepted:

  • Published:

  • Issue Date:

  • DOI: https://doi.org/10.1007/s10811-006-9122-y

Key words

Navigation