Angelidaki, Irini

Galanidis, S.

Holdt, Susan Løvstad

Margarido Pargana, Alexandre

Online Research Database In Technology

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Downloaded from orbit.dtu.dk on: Dec 20, 2017Green macroalgae for biomitigation of nutrients, purification of biogas and energyproductionHoldt, Susan Løvstad; Galanidis, S.; Margarido Pargana, Alexandre; Angelidaki, IriniPublication date:2012Document VersionPublisher's PDF, also known as Version of recordLink back to DTU OrbitCitation (APA):Holdt, S. L., Galanidis, S., Margarido Pargana, A., & Angelidaki, I. (2012). Green macroalgae for biomitigation ofnutrients, purification of biogas and energy production. Poster session presented at ALGER 2012, Bodø,Norway.DTU Environment, Department of Environmental Engineering,  Technical University of Denmark, Miljøvej, Building 113, 2800 Kgs. Lyngby, DENMARK    Day 21 Day 7 The green macroalgae Ulva lactuca and Ulvaria splendens are two species particularly interesting in a algal biorefinery concept including biofuel production in Denmark and Greenland, respectively. The possibility of using digested pig manure (DPM) as nutrient source for the cultivation of the two species was investigated, and the macroalgae were also used as substrate for anaerobic thermophilic digestion with DPM as inoculum. Half the algal fronds were washed with fresh water in order to investigate the effect of sea salt in the anaerobic digestion.  In addition, biogas was investigated as carbon source for algal biomass production.  Diluted DPM was suitable as nutrient source. However, growth rate 27% lower (0.16 d-1) than the maximum achieved (0.22 d-1 with NO3- culture medium (F/2)). Ulva lactuca had higher growth rates compared to U. splendens (p<0.05). The specific growth rates of U. lactuca were not significantly different when using diluted DPM or standard medium (F/2), both with biogas  Abstract Holdt SL*, Galanidis S, Pargana AM, Angelidaki I (*corresponding author: suho@env.dtu.dk)   Determine the growth rate of U.lactuca and U.splendens cultivated under different nutrient regimes.   Investigate digested pig manure (DPM) as nutrient source candidate for algal growth.  Investigate biogas as a carbon source for cultivation of U. lactuca  Quantify the biogas potential production of  U. lactuca and U. splendens.  Investigate the possible inhibition of the biogas process, by the marine sea salt contained in the superficial seawater present on the algal fronds. The algal biorefinery concept Aims Results  High growth rates  (0.22 d-1 with NO3- culture medium) and high yields (10 x corn yield).   U. lactuca had higher growth rates for all treatments compared to U.splendens (p<0.05).  Diluted DPM was suitable as nutrient source, however growth rate 27% lower (0.16 d-1) than the maximum achieved (Figure 1).  No significant difference in specific growth rates of U. lactuca when using diluted DPM or standard medium (F/2), both with biogas and CO2 as bubbled gas (Figure 2).   Both U. splendens and U.lactuca could be used for biogas production with a yield of approx.  0.2 L-CH4/gVS. The CH4 yields were 21-29% higher when the macroalgae was washed.   The Na+ and K+ concentrations of < 1 g/L  should not be inhibiting the biogas process (Figure 3).  Conclusions Photos: Ulva lactuca Figure 3: Average methane production of U.lactuca and U.splendens digested under batch thermophilic conditions. Fresh refers to washed and salt to non-washed samples prior to incubation. Different letters represent results of significant difference (p<0.05)  Figure 1: Specific growth rates of U.lactuca and U.splendens cultivated under different nutrient regimes corresponding to 12.35mgN/L. U. splendens died after 4days of cultivation in NO-3. Different letters represent results of significant difference (n=3, p<0.05)  Figure 4: The algal biorefinery concept: Algal biomass cultivated and harvested are utilized for several extracted high value-added products, and biomass waste are converted to biofuels. Waste effluent from biofuel processes, such as digested pig manure are rich in nutrients and may be used for crop or algal cultivation. Flue gas may be recycled as carbon source for algal cultivation. Biogas may be purified when sparged through algal cultivation system. Materials and methods Natural populations of Ulva lactuca and Ulvaria splendens were collected at Danish and Greenlandic shores, respectively, and cultivated in 300 mL aerated seawater enriched with with NO-3 (F/2), NH+4 (standard algal medium) and diluted (1:200) digested pig manure (mainly NH+4) as nitrogen source corresponding to 12.35 mg N/L. Light was provided 24 hours daily with intensity of 48µmolphotons/s/m2 temperature of 15°C, salinity 13 ppt (U. lactuca) and 35 ppt (U. splendens) and experiment duration was 21 d. Another experiment was setup with U. lactuca using the same variables but sparging with CO2 or biogas. CO2 was added using an electronic valve connected to the gas bubble allowing a puls of 1 min at intervals of 1 hour. Biogas (artificial mixture of 30% CO2, 30% nitrogen (N2), and 40% methane (CH4) was added at a rate of 5 mL/min in pulses of 15 min with intervals of 45 min, using a peristaltic pump connected to a bag reservoir. A buffer (1% of K2HPO4 1M solution) was added to media to prevent pH changes below pH6. Buffer (K2HPO4) was added in all treatments except control (- buffer). For experiments of biogas potential 550 mL bottles were used with organic loading of 1, 2, and 4 g VS/L macerated algal biomass (U. lactuca  and U. splendens; washed with fresh water or left with sea water on surface), water and inoculated with digested pig manure (DPM) to volume of 200 mL. The biogas was measured by GC after  34 days.  Ulva lactuca and Ulvaria splendens could both be cultivated on diluted DPM as growth medium, and experiments with U.lactuca showed that sparged biogas was suitable for cultivation. The biogas potentials are comparable to other well-known feedstocks incl. Manure. Higher biogas potentials were reached in the washed U.splendens. This species natural habitat in Greenland and in the experimental setup were remarkably more saline. Green macroalgae for biomitigation of nutrients,  purification of biogas and energy production Day 1 Dilution of digested pig manure 187154214151050100150200250Washed Non-WashedmL CH4/ g VSU. lactuca U. fuscaU. lactuca U. splendens a b c c n=6 n=6 n=5 n=3 Ulva lactuca Ulvaria splendens Digested pig manure a b c d e Ulva lactuca  Specific growth rate (d-1) 0.15 0.16 0.17 0.18 0.19 0.20 biogas + F/2 biogas + DPM CO2 + DPM CO2 + F/2 control (- buffer) control (buffer) Figure 2: Specific growth rates of U.lactuca cultivated under different nutrient regimes (corresponding to 12.35mgN/L) and sparging of CO2 or biogas as carbon source.. Buffer (K2HPO4) was added in all treatments except control (- buffer). Error bars represent standard errors (n=3). Funded by: Indian Department of Biotechnology (DBT) and Danish Council for Strategic Research (DSF) [09-067601] and CO2 as bubbled gas. Both species could be used for biogas production with a yield of approx.  0.2 L-CH4/gVS. The CH4 yields were 21-29% higher when the macroalgae was washed, removing salt on surface (p<0.05).  Especially, the biogas yield from U. splendens, growing under more saline conditions, benefited from this treatment. These results suggest that CO2 from biogas and biogas effluents can be used for respectively carbon and nutrients supply for cultivation of algae, which can further be used for possible extraction of high added value products and bioenergy. This will, in addition to algal biomass, result in purification of nutrient rich waste waters, and purification of biogas. This study showed the two green macroalgae as promising candidates for future algal biorefineries. These results suggest that CO2 from biogas and biogas effluents can be used for respectively carbon and nutrients supply for cultivation of algae, which can further be used for possible extraction of high added value products and bioenergy. This will, in addition to algal biomass, result in purification of nutrient rich waste waters, and purification of biogas. Further studies are needed to describe the process of biogas purification. 0 0.05 0.10 0.15 0.20 0.25 

Green macroalgae for biomitigation of nutrients, purification of biogas and energy production

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Green macroalgae for biomitigation of nutrients, purification of biogas and energy production

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