The effect on growth of Chlamydomonas reinhardtii of flue gas from a power plant based on waste combustion
© Mortensen and Gislerød; licensee Springer 2014
Received: 16 December 2013
Accepted: 23 May 2014
Published: 18 June 2014
Flue gases from a power plant based on waste combustion were tested as a carbon dioxide (CO2) source for growing Chlamydomonas reinhardtii. To achieve recognition as an environmentally friendly hydrogen production method, waste gases should be used to grow this hydrogen-producing microalgae. The algae were grown in undiluted flue gas containing 11.4±0.2% CO2 by volume, in diluted flue gas containing 6.7±0.1% or 2.5±0.0% CO2, and in pure liquid CO2 at a concentration of 2.7±0.2%. The NOx concentration was 45±16 mg m-3, the SO2 concentration was 36±19 mg m-3, the HCl concentration 4.1±1.0 mg m-3 and the O2 concentration 7.9±0.2% in the undiluted flue gas. Undiluted flue gas reduced the dry weight production by around 20-25% when grown at a photon flux density (PFD) of 300 μmol m-2 s-1 artificial light and at 24 or 33°C, compared with the other treatments. A less negative effect was found at the highest flue gas concentration when the algae were grown at 75 μmol m-2 s-1 PFD. Growing the algae outdoors at a day length of 12.5 h and a temperature of around 24°C, the dry weight production was higher (about 15%) in the 2.6% CO2 flue gas treatment compared with all other treatments. Reducing the light level by 30% through shading did not affect the dry weight production. Calculated on aerial basis the productivity reached approximately 70 g m-2 day-1 in the 300 μmol m-2 s-1 PFD treatment (corresponding to 25 mol m-2 day-1) and approximately 17 g m-2 day-1 in the 75μmol m-2 s-1 PFD treatment (corresponding to 6.5 mol m-2 day-1). The outdoor production reached around 14 g m-2 day-1. It was concluded that the negative effect of the undiluted flue gas was attributable to the high CO2 concentration and not to the other pollutants.
The single-celled green alga Chlamydomonas reinhardtii is known to produce hydrogen when starved of sulphur under anaerobic conditions (Skjånes et al. ; Nguyen et al. ; Geier et al. ). At present, conventional hydrogen production is energy-intensive, and more environmentally friendly production based on biological processes is therefore of great interest (Jo et al. ). Today, the atmospheric CO2 concentration of about 400 μmol mol-1 strongly limits the algal growth, and additional CO2 gas has to be supplied throughout the production phase (Geier et al. ). Waste CO2 from industrial flue gases should be used in order to make the production environmentally friendly. This will also contribute to reducing CO2 emissions that are important to the environment (IPCC ). Several studies have been carried out on the effect of flue gases on the growth of microalgae (Douskova et al. ; Kastanek et al. ; Borkenstein et al. ). Chlamydomonas reinhardtii seems to have been little studied, however (see review by van den Hende et al. ). Flue gases contain pollutants such as NOx and SO2 that can reach harmful levels depending on the species (van den Hende et al. ). However, few studies have devoted attention to whether the harmful effects depend on environmental factors such as irradiance level and temperature. In tomato plants, it is known that susceptibility to NOx is much higher in low-light as opposed to high-light conditions (Mortensen ). For microalgae, and particularly for C. reinhardtii, little is known about the modifying effects of climate factors. Therefore, in this work the effect of flue gas was studied on C. reinhardtii at different levels of artificial light and in outdoor conditions with and without shade, as well as at two temperature levels.
Material and methods
Chlamydomonas reinhardtii strain SAG 34.89 from SAG (Göttingen, Germany) obtained from the NIVA culture collection, Norway, was used in the experiments. The algae were stored on Petri dishes covered with TAP medium 1.5% agar (Gorman and Levine ). The algae were grown in the high-salt Sueoka medium (Sueoka ). Sodium bicarbonate was used in the medium to buffer the culture at 10 mM. The microalgae were grown in 1.0 l clear plastic bottles (80 mm inner and 82 mm outer diameter) filled with 0.85 l of growing medium (filled up to 17 cm). Tubes with these dimensions have a volume of approximately 60 l per m2 surface area when placed closely together, as the bottles were in the present experiments. The light was supplied by cool white fluorescence tubes (Osram L58W/840) 24 h day-1 placed about 10 cm in front of the row of bottles. The photon flux density (PFD) of the artificial light was measured by a LI-COR Model Li-250 instrument with quantum sensor (400-700 nm). The light was supplied from one side and was measured at the surface of the bottles. However, inside the culture the light level strongly decreased from the light exposed side to the opposite side of the bottles, as well as with increasing cell concentration during growth. Typically, the light level decreased by about 70% through the 8.0 cm diameter bottle at start of the experiment and by more than 99.9% at the end of the experiment, due to the increase in the algae concentration.
Two experiments were carried out indoor with artificial light, while a third experiment was carried out outdoor in daylight. The daylight was measured by a Delta-T Devices PAR sensor (cosine corrected within ±5% up to 70° incidence). The temperature was controlled by placing the bottles with the microalgae culture in water baths controlled by aquarium heaters. A circulation pump ensured a homogenous temperature in the water baths. The temperature was measured by cupper-constantan thermocouples. The CO2 concentration was measured by a Vaisala CO2 transmitter (Type GMT221, range 0-5%). The CO2 concentration as well as the temperatures and the daylight PAR were recorded as hourly means by a Campbell CR10X logger with an AM25T thermocouple multiplexer. In addition a Vaisala GMP instrument was used to measure the CO2 concentrations between 0 and 20%, and the measurements were recorded as hourly means.
The flue gas
Mean concentrations (±SD) of different pollutants as measured in the different flue gas concentrations
NOx (mg m-3)
SO2 (mg m-3)
HCl (mg m-3)
CO (mg m-3)
TOC (mg m-3)
*Hg (μg m-3)
*HF (mg m-3)
*Dioxins (ng m-3)
+Ni+Pb+Sb+V (mg m-3)
Flue gas from the chimney was sucked by pumps through two 100 l plastic tubs connected in series for condensation of water vapour. The microalgae were grown in undiluted flue gas (11.4% CO2) or mixed with fresh air in a constant ratio using air pumps (Resun ACO-008A) to yield 6.7% and 2.5% CO2, respectively (Figure 1, Table 1). One CO2 concentration (2.66±0.16%) was established by mixing pure CO2 (food quality) from bottles with fresh air. The CO2 gas flow was determined by a capillary with a defined resistance, while the gas pressure was defined by the height of a water column. In this way, a very accurate CO2 flow could be added to a constant rate of fresh air supplied by air pumps (Resun ACO-001, ACO-004).
The different gas mixtures were bubbled through plastic tubes with 0.3 cm inner diameter to the bottom of the bottles at a rate of approximately 100 l h-1. All treatments in all experiments included three parallel bottles containing 0.85 l of culture. Three independent experiments (including a total of 60 bottles) were carried out during the same time period, all of which started with the same algae concentration of 0.20 g dry weight per litre culture. This concentration was established by adding algae from a start culture. Two of the experiments were conducted indoor with artificial lighting while the third was conducted outdoor in daylight.
Dissolved CO2 in the growth medium
The microalgae were grown at the three flue gas concentrations and one concentration with pure CO2 from bottles (Figure 1, Table 1). Two photon flux densities (PFD) were continuously applied, 75 and 300 μmol m-2 s-1, corresponding to 6.5 and 25.9 mol m-2 day-1 PAR, respectively. Two rows of twelve bottles with algae culture were placed closely adjacent to each other in a water bath. One row along one side of the water bath was exposed to 300 μmol m-2 s-1 PFD, and the other row along the opposite side was exposed to 75 μmol m-2s-1 PFD. A black sheet across the water bath eliminated any light pollution between the two light treatments. The water bath was made of transparent plexiglass, and one and four fluorescent tubes placed 10-15 cm from the bottles (outside the water bath) produced the low and high PFD, respectively. The temperature was 33±2°C. The dry weight (mg l-1 culture), pH and O2 concentration in the culture were measured after three and five days, and the production per m2 and day was calculated using the vertical projected area of the bottles.
The same flue gas and pure CO2 gas treatments were applied in this experiment as in Experiment 1. In this experiment a PFD of 300 μmol m-2 s-1 given continuously was used. The temperature was 19±2°C during the first day, and was thereafter increased to 24±2°C. The temperature was controlled as in Experiment 1. Twelve bottles were included in the experiment, and the dry weight concentration and pH were measured four and five days after the start.
The dry weight was measured by vacuum filtering 10 or 20 ml of culture through a 90 mm filter (Whatman GF/B, cat. No. 1821-090) and drying it in an oven for four hours at 100°C. No pore size of this filter is given, however, all algal cells remained on the filter since no colouration of the filtered water was observed. The data were analysed using the SAS-GLM procedure (SAS institute Inc., Cary, USA) based on the bottles as replicates (n=3).
The effect of different CO 2 concentrations supplied by flue gas (Fl) and one concentration supplied by pure liquid CO 2 gas (C) on pH, O 2 concentration in the culture and dry weight concentration (n=3, ±SE) after 3 and 5 days of C. reinhardtii grown at 75 and 300 μmol m -2 s -1 PFD
Mean dry weight production
Day 0 - 3
Dry w. (mg l-1)
Dry w. (mg l-1)
F-value and significance level:
CO2 x PFD
The effect of different CO 2 concentrations supplied by flue gas (Fl) and one concentration supplied by pure liquid CO 2 gas (C) on pH and dry weight concentration (n=3, ±SE) after 4 and 5 days of C. reinhardtii grown at 300 μmol m -2 s -1 PFD
Dry weight increase
Dry w. (mg l-1)
Dry w. (mg l-1)
F-value and significance level:
The effect of different CO 2 concentrations supplied by flue gas (Fl) and one concentration supplied by pure liquid CO 2 gas (C) on pH and dry weight concentration (n=3, ±SE) after four days of C. reinhardtii grown in daylight or 70% daylight (shaded)
Dry weight increase
Dry w. (mg l-1)
F-value and significance level:
CO2 x Light
The undiluted flue gas containing 11.4% CO2 caused a decrease in the dry weight production compared with lower flue gas concentrations (2.5 and 6.7%). This was particularly the case when the dry weight production was very high (up to 70-80 g m-2 day-1), obtained at 300 μmol m-2 s-1 PFD continuously applied (25.9 mol m-2 day-1 PAR). In low-light conditions, (continuously 75 μmol m-2 s-1 PFD or 6.5 mol m-2 day-1 PAR) or in sunny daylight with a day length of 12.5 h (17.2 mol m-2 day-1 PAR) when the growth rate was much lower, less or no negative effect was found of the undiluted flue gas. The question was whether the negative effect was related to the high CO2 concentration itself or to the accompanying air pollutants. Separate measurements indicated that the dissolved CO2 concentration in the culture with undiluted flue gas might be about 400 mg l-1 as compared with about 150 mg l-1 in diluted flue gas with a concentration of 2.5% CO2. This is far below the saturating level of CO2 in water that is about 1500 mg l-1 at 23°C and 1200 mg l-1 at 33°C. The present pollutant levels of NOx and SO2 below about 50 mg m-3 in the flue gas seldom seem to cause growth reduction in microalgae (Matsumoto et al. ; Douskova et al. ; van den Hende et al. ; Farrelly et al. ; Jiang et al. ). Other flue gas compounds such as CO, HCl, HF and heavy metals such as Hg have received little attention so far (van den Hende et al. ). Probably the concentrations in the present flue gas were so low that they would have no effect on the growth. However, microalgae possess very high metal uptake capacities and accumulation in the cells will therefore take place (de-Bashan and Bashan ). High CO2 concentrations (18-19%) from pure liquid CO2 gas, however, have recently been found to decrease the dry weight production in the same C. reinhardtii strain (Mortensen and Gislerød ). Fischer et al. () showed that cells of the same species were more susceptible to high-light stress under high CO2 concentrations than under low concentrations. In the present study, however, the negative effect of the high concentrations seemed to be more related to a high growth rate than to high-light conditions. It can also be noted that the maximum dry weight concentration reached in the algae culture in the flue gas decreased to the same extent (in percentage) as the dry weight production, indicating higher respiration or lower photosynthetic activity in the algae. The negative effect of the 11.4% flue gas in the present experiment was in contrast to the stimulating effect of flue gas, probably due to lower O2 content, found in some studies on microalgae (Vance and Spalding ; Douskova et al. ; Kliphuis et al. ). Growing Chlorella sp. at 2-20% CO2 (v/v) simulating flue gas from biogas gave the same effect as growing the algae in food grade CO2 at the same concentrations (Douskova et al. ). The environmental conditions could play a role here, and they might also be the reason for the positive effect of the moderate flue gas concentration with 2.5% CO2 in the present experiment in daylight.
The production at low-level light 24 h day-1 (6.5 mol m-2 day-1 PAR) was at the same level (around 14 g m-2 da-1) as at about a three times higher PAR in daylight, which demonstrates the limitation of the algae as regards utilising the high irradiance level. The productivity in daylight was typical of outdoor production systems and the high productivity was typical of controlled environmental conditions in laboratories (Grobbelaar ). The light use efficiency in the present study was found to be the same in the range 75-300 μmol m-2 s-1 PFD. If we assume that all daylight above 300 μmol m-2 s-1 PFD has a value of 300 μmol m-2 s-1, the mean PFD of the daylight will decrease from 199 to about 90 μmol m-2 s-1 or 7.8 mol m-2 day-1 PAR. This level is comparable to the low-light level with artificial light applied 24 h day-1. In addition to the constraint caused by light saturation, the presence of a dark period is known to decrease algae growth much more than would be expected from the reduction in PAR (Jacob-Lopez et al. ). This means that long day lengths and lower maximum irradiance levels at high latitudes would be beneficial for algae production during the summer months. However, short days and low PAR during large parts of the year make the production of algae impractical in such locations. Growing C. reinhardtii with the aim of using it to produce hydrogen should be based on using daylight in combination with flue gas in order to ensure a positive energy balance (Lam et al. ). However, large-scale systems that can utilise the high irradiance levels of daylight much better than today (Slegers et al. ) are a prerequisite for future energy-efficient hydrogen production using microalgae. Flue gas is an important CO2 source. However, while care should be taken to ensure a CO2 concentration that is optimal, the presence of pollutants in the flue gas in today’s industrial emissions seems to be less of a problem in relation to the growth of the algae.
The authors thank ‘Borregaard Waste to Energy’ with Jørgen Karlsen and staff in Sarpsborg for their hospitality, excellent assistance and for providing the records of the flue gas measurements. This work was done as a part of the project ‘Use of solar energy for CO2 capture, algae cultivation and hydrogen production’ headed by Dr Stig Borgvang (Bioforsk). It was financed by the Research Council of Norway.
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