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OPTIMIZATION OF IMMOBILIZED ALGAL CULTIVATION IN AQUACULTURE WASTEWATER

Algal concentration

6.9 OPTIMIZATION OF IMMOBILIZED ALGAL CULTIVATION IN AQUACULTURE WASTEWATER

Based on the experiments of the present work, the optimal immobilized conditions for algal cultivation depend on the purpose of the cultivation. The optimal initial algal concentration, bead concentration, and bead size for nutrient removal and algal growth are different. If the purpose of the cultivation is to treat aquaculture wastewater and achieve high nutrient removal,

the optimal initial algal concentration, beads to culture medium ratio, and bead size seem to be 5.1  105 cells/bead, 1:10.7, and 3.4 mm. If the purpose of the cultivation is to produce algal biomass for the production of high-value algae-based compounds and achieve high algal growth, the optimal initial algal concentration, beads to culture medium ratio, and bead size seem to be 1.2  105 or 2.3  105 cells/bead, 1:5.4, and 4.7 mm. If both high nutrient removal and algal growth are desired, the parameters could be adjusted somewhere between the optimal values for nutrient removal and algal growth.

7. CONCLUSIONS

Microalga S. quadricauda was able to successfully grow and remove nutrients in the course of the cultivation in aquaculture wastewater, which implies that the algal species holds potential to be utilized in the aquaculture wastewater treatment. Immobilization was observed to improve the nutrient removal from aquaculture wastewater. However, assimilation by algae was not the only nutrient removal mechanism in the bead treatment, since nutrients were also removed via bacterial assimilation, adsorption to alginate, phosphorus precipitation, and ammonia volatilization. Algal growth on the other hand was not enhanced in immobilized cultivation, and the leakage of cells from the beads to the culture medium was common in the treatments with immobilized algae. Neither nutrient removal nor algal growth was observed to benefit from the addition of Mg into the beads. Of the initial algal concentrations, beads to culture medium ratios, and bead sizes that were tested in the experiments, 5.1  105 cells/bead, 1:10.7, and 3.4 mm seem to be optimal for nutrient removal from aquaculture wastewater in 4.5-day cultivation and 1.2  105 or 2.3  105 cells/bead, 1:5.4, and 4.7 mm for algal growth in 6-day cultivation.

However, the results obtained in the experiments are only directional estimates for various reasons. First of all, in many of the experiments, especially the ones investigating the nutrient removal, the differences between the treatments were small, and the statistical significance between the treatments could not be determined due to low sample size. In addition, some of the conducted measurements (ammonia concentration and cell counts) were not performed precisely according to the instructions, which reduces the accuracy of the results. The experiments investigating bead concentration and bead size had also issues in their experimental set-up and consequently the results of these experiments are influenced not only by the differences in the investigated parameter but also by the differences in the initial algal concentration.

Overall, immobilization seems to be an interesting technique to ease algal cultivation and harvesting. However, more research is still needed especially on large scale before immobilized algae can be applied for aquaculture wastewater treatment. In the future research it is highly important to carefully plan the experiments in advance to assure that solely the investigated parameter is causing differences in the results, and that the sample size is large enough to allow the statistical analysis of the results.

REFERENCES

Abdel Hameed M.S. 2007. Effect of algal density in bead, bead size and bead concentrations on wastewater nutrient removal. African Journal of Biotechnology 6: 1185-1191.

Aishvarya V., Jena J., Pradhan N., Panda P.K., and Sukla L.B. 2015. Microalgae: cultivation and application. In: Sukla L.B., Pradhan N., Panda S., and Mishra B.K. (eds.). Environmental Microbial Biotechnology, Soil Biology 45, p. 289-311. Springer International Publishing, Switzerland.

Andersen R.A. 2013. The microalgal cell. In: Richmond A. and Hu Q. (eds.). Handbook of Microalgal Culture: Applied Phycology and Biotechnology, 2. edition, p. 3-20. John Wiley &

sons, New Delhi.

BRAND. 2013. General Catalog 900, p.253. Germany.

Cao L., Wang W., Yang Y., Yang C., Yuan Z., Xiong S., and Diana J. 2007. Environmental impact of aquaculture and countermeasures to aquaculture pollution in China. Environmental Science and Pollution Research 14: 452-462.

Castine S.A., McKinnon A.D., Paul N.A., Trott L.A., and de Nys R. 2013. Wastewater treatment for land-based aquaculture: improvements and value-adding alternatives in model systems from Australia. Aquaculture Environment Interactions 4: 285-300.

Chen Y.C. 2001. Immobilized microalga Scenedesmus quadricauda (Chlorophyta, Chlorococcales) for long-term storage and for application for water quality control in fish culture. Aquaculture 195: 71-80.

Chen Y.C. 2003. Immobilized Isochrysis galbana (Haptophyta) for long-term storage and applications for feed and water quality control in clam (Meretrix lusoria) cultures. Journal of Applied Phycology 15: 439-444.

Chevalier P. and de la Noüe J. 1985. Efficiency of immobilized hyperconcentrated algae for ammonium and orthophosphate removal from wastewaters. Biotechnology Letters 7: 395-400.

Cripps S.J. and Bergheim A. 2000. Solids management and removal for intensive land-based aquaculture production systems. Aquacultural Engineering 22: 33-56.

Cruz I., Bashan Y., Hernàndes-Carmona G., and L.E. de-Bashan. 2013. Biological deterioration of alginate beads containing immobilized microalgae and bacteria during tertiary wastewater treatment. Applied Microbiology and Biotechnology 97: 9847-9858.

de-Bashan L.E. and Bashan Y. 2010. Immobilized microalgae for removal of pollutants: review of practical aspects. Bioresource Technology 101: 1611-1627.

Delrue F., Álvares-Días P.D., Fon-Sing S., Fleury G., and Sassi J.F. 2016. The environmental biorefinery: using microalgae to remediate wastewater, a win-win paradigm. Energies 9: 132-150.

Dos Santos M.M., Moreno-Garrido I., Gonçalves F., Soares A.M.V.M., and Ribeiro R. 2002.

An in situ bioassay for estuarine environments using the microalga Phaeodactylum tricornutum. Environmental Toxicology and Chemistry 21: 567-574.

FAO. 2018. The State of World Fisheries and Aquaculture 2018 - Meeting the sustainable development goals. Rome. Licence: CC BY-NC-SA 3.0 IGO.

HACH. 2019a. Nitrate, Cadmium Reduction Method 8039. Water Analysis Handbook.

https://www.hach.com/wah. Accessed 4.8.2020.

HACH. 2019b. Nitrite, Diazotization LR Method 8507. Water Analysis Handbook.

https://www.hach.com/wah. Accessed 4.8.2020.

HACH. 2017a. Nitrogen, Ammonia-Nessler Method 8038. Water Analysis Handbook.

https://www.hach.com/wah. Accessed 4.8.2020.

HACH. 2017b. Phosphorus, Reactive (Orthophosphate), PhosVer 3 (Ascorbic Acid) Method 8048. Water Analysis Handbook.

https://www.hach.com/wah. Accessed 4.8.2020.

Kathijotes N., Alam L., and Kontou A. 2015. Aquaculture, coastal pollution and the environment. In: Mustafa S. and Shapawi R. (eds.). Aquaculture Ecosystems: Adaptability and Sustainability, p. 139-163. John Wiley & Sons, Pondicherry.

Lam M.K. and Lee K.T. 2012. Immobilization as a feasible method to simplify the separation of microalgae from water for biodiesel production. Chemical Engineering Journal 191: 263-268.

Lee H., Jeong D., Im S.J., and Jang A. 2020. Optimization of alginate bead size immobilized with Chlorella vulgaris and Chlamydomonas reinhardtii for nutrient removal. Bioresource Technology 302: 1-5.

Lee Y.K., Chen W., Shen H., Han D., Li Y., Jones H.D.T., Timlin J.A., and Hu Q. 2013. Basic culturing and analytical measurement techniques. In: Richmond A. and Hu Q. (eds.). Handbook of Microalgal Culture: Applied Phycology and Biotechnology, 2. edition, p. 3-20. John Wiley

& sons, New Delhi.

Mollamohammada S., Aly Hassan A., and Dahab M. 2020. Nitrate removal from groundwater using immobilized heterotrophic algae. Water, Air & Soil Pollution 231: 1-13.

Mongirdas V., Žibienė G., and Žibas A. 2017. Waste and its characterization in closed recirculating aquaculture systems – a review. Journal of Water Security 3: 1-8.

Moreno-Garrido I. 2008. Microalgae immobilization: current techniques and uses. Bioresource Technology 99: 3949-3964.

Oluwole O.R., Tobin C.M., Banjo T.T., Efunwoye O.O., and Awoyemi S.O. 2019. The use of immobilized microalgal bead concentrations in the removal of ammonium nitrogen from synthetic wastewater. Nigerian Journal of Biotechnology 36: 171-176.

Pires J.C.M., Alvim-Ferraz M.C.M., Martins F.G., and Simões M. 2013. Wastewater treatment to enhance the economic viability of microalgae culture. Environmental Science and Pollution Research 20: 5096-5105.

Shubert E. and Gärtner G. 2015. Nonmotile coccoid and colonial green algae. In: Wehr J.D., Sheath R.G., and Kociolek J.P. (eds.). Freshwater Algae of North America: Ecology and Classification, 2. edition, p. 315-373. Academic Press, USA.

Tam N.F.Y. and Wong Y.S. 2000. Effect of immobilized microalgal bead concentrations on wastewater nutrient removal. Environmental Pollution 107: 145-151.

Tam N.F.Y., Lau P.S., and Wong Y.S. 1994. Wastewater inorganic N and P removal by Chlorella vulgaris. Water Science and Technology 30: 369-374.

Tepe Y. and Aydin Temel F. 2018. Treatment of effluents from fish and shrimp aquaculture in constructed wetlands. In: Stefanakis A.I. (ed.) Constructed Wetlands for Industrial Wastewater Treatment, p. 105-125. John Wiley & Sons, Chennai.

Tränkner M., Tavakol E., and Jákli B. 2018. Functioning of potassium and magnesium in photosynthesis, photosynthate translocation and photoprotection. Physiologia Plantarum 163:

414-431.

Turcios A.E. and Papenbrock J. 2014. Sustainable treatment of aquaculture effluents – What can we learn from the past for the future? Sustainability 6: 836-856.

Wang P., Li Z., Bai J., Lang Y., and Hu H. 2016. Optimization of microalgal bead preparation with Scenedesmus obliquus for both nutrient removal and lipid production. Ecological Engineering 92: 236-242.

Whitton R., Le Mével A., Pidou M., Ometto F., Villa R., and Jefferson B. 2016. Influence of microalgal N and P composition on wastewater nutrient remediation. Water Research 91: 371-378.