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The effect on growth of Chlamydomonas reinhardtii of flue gas from a power plant based on waste combustion
Flue gases from a power plant based on waste combustion were tested as a carbon dioxide (CO(2)) 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 a...
Autores principales: | , |
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Formato: | Online Artículo Texto |
Lenguaje: | English |
Publicado: |
Springer
2014
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Materias: | |
Acceso en línea: | https://www.ncbi.nlm.nih.gov/pmc/articles/PMC4230831/ https://www.ncbi.nlm.nih.gov/pubmed/25401062 http://dx.doi.org/10.1186/s13568-014-0049-4 |
Sumario: | Flue gases from a power plant based on waste combustion were tested as a carbon dioxide (CO(2)) 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% CO(2) by volume, in diluted flue gas containing 6.7±0.1% or 2.5±0.0% CO(2), and in pure liquid CO(2) at a concentration of 2.7±0.2%. The NO(x) concentration was 45±16 mg m(-3), the SO(2) concentration was 36±19 mg m(-3), the HCl concentration 4.1±1.0 mg m(-3) and the O(2) 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% CO(2) 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 CO(2) concentration and not to the other pollutants. |
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