• Tidak ada hasil yang ditemukan

CHAPTER 6: Aeration pre-treatment

6.5 CONCLUSIONS

also decreases. Therefore, the optimum air flow rate is approximately 4 L min-1 L-1 urine, after which the marginal increase in cost outweighs the marginal decrease in operating time. At an air flow rate of 4 L min-1 L-1 urine, the air bubbling would cost $0.65 m-3 and would require an operating time of approximately 7.6 hours.

Air vs. CO2 enriched gas

Figure 6-7B compares the cost and operating time for different CO2 concentrations at optimum operating conditions. Whilst the required operating time is significantly decreased by increasing the CO2 concentration, the cost is 2.35 times more when compared to air bubbling. As CO2 costs $ 0.97 per kg (Air Liquide, Cape Town), even if CO2 is 100% efficient, approximately 1.3 kg of CO2 is required per m3 of urine resulting in a minimum cost of $1.27 m-3 urine, which is double the cost of air bubbling.

Further information regarding how flow rate and operating time impact the costing for CO2 can be found in Figure C-8. An additional advantage of air bubbling to remove excess calcium is that it can be used to sequester CO2 directly from the atmosphere (Aguilar, 2012). The cost of the power requirements for air bubbling would require the break-even sales price ($ 1.57 L-1) of the niche fertilizer product to be increased by 0.2%, based on the economic analysis conducted by Chipako and Randall (2020a).

Figure 6-7: Cost and operating time as a function of air flow rate varying from 1 to 10 L min-1 L-1 (A), cost and operating time as a function of CO2 concentration for the most cost-efficient flow rate (B).

It was determined that the rate of CO2 dissolution is the key process controlling the pH of the solution, and ultimately the calcium is removed as solid CaCO3. At low flow rates, CO2 dissolution was the rate- limiting step whilst at high flow rates and/or high CO2 concentrations, the fast pH decrease limited the precipitation of CaCO3.

It was also shown that even though the pH of the solution had dropped below the threshold pH for enzymatic urea hydrolysis to occur (<11), no urea hydrolysis was detected, most likely because the urease-producing bacteria had been inhibited at the high initial pH values (>12.5) and the reaction time was too fast.

Through simulations, it was shown that after pre-treatment with air bubbling, 85% of the water could be removed from the urine before CaCO3 scaling would be detected. However, the exact nature of membrane scaling for the proposed process needs to be investigated further experimentally and in a full-scale RO system.

The cost of using air enriched with CO2 was more than double compared to using an air blower. Whilst using higher concentrations of CO2 resulted in a significant decrease in operating time, it did not justify the overall operating cost. The optimum operating condition was determined to be an air flow rate of 4 L min-1 L-1 urine and an operating time of 7.6 hours. At these conditions, 95% of the calcium could be removed for a cost of $0.65 m-3 (R11 m-3). This represents only 0.2% of the break-even sales price ($1.57/ R27 L-1) of a liquid fertilizer product that could be produced in a RO system.

REFERENCES

Aguilar, M.J. 2012. Urine as a CO2 absorbent. Journal of Hazardous Materials 213-214, 502-504.

Altiner, M. 2018. Influences of CO2 Bubbling Types on Preparation of Calcite Nanoparticles by Carbonation Process. Periodica Polytechnica Chemical Engineering 62(2), 209-214.

Bang, J.-H., Jang, Y.N., Kim, W., Song, K.S., Jeon, C.W., Chae, S.C., Lee, S.-W., Park, S.-J. and Lee, M.G. 2011. Precipitation of calcium carbonate by carbon dioxide microbubbles. Chemical engineering journal 174(1), 413-420.

Brison, A. 2016. Understanding the processes involved during the stabilization of urine with calcium hydroxide, MSc. Thesis. ETH Zürich Zürich

Callahan, B.P., Yuan, Y. and Wolfenden, R. 2005. The Burden Borne by Urease. Journal of the American Chemical Society 127(31), 10828-10829.

Campos, J.C., Moura, D., Costa, A.P., Yokoyama, L., Araujo, F.V.d.F., Cammarota, M.C. and Cardillo, L. 2013. Evaluation of pH, alkalinity and temperature during air stripping process for ammonia removal from landfill leachate. Journal of Environmental Science and Health, Part A 48(9), 1105-1113.

Chipako, T. and Randall, D. 2020. Investigating the feasibility and logistics of a decentralized urine treatment and resource recovery system. Journal of Water Process Engineering 37, 101383.

El Fil, H. and Manzola, A. 2003. Decarbonation of geothermal waters by seeding with aragonite crystals coupled with air bubbling. Applied geochemistry 18(8), 1137-1148.

Franks, R., Bartels, C. and Nagghappan, L. 2009. Performance of a reverse osmosis system when reclaiming high pH-high temperature wastewater. American Water Works Association Membrane Technology Conference. Memphis, USA, 15-18 March. 1-16.

Hasson, D., Segev, R., Lisitsin, D., Liberman, B. and Semiat, R. 2011. High recovery brackish water desalination process devoid of precipitation chemicals. Desalination 283, 80-88.

Haynes, W.M., Lide, D.R. and Bruno, T.J. 2016. CRC handbook of chemistry and physics, 95th edition, CRC Press, Florida, USA.

Kazmierczak, T., Tomson, M. and Nancollas, G. 1982. Crystal growth of calcium carbonate. A controlled composition kinetic study. The Journal of Physical Chemistry 86(1), 103-107.

Lisitsin, D., Hasson, D. and Semiat, R. 2008. The potential of CO2 stripping for pretreating brackish and wastewater desalination feeds. Desalination 222(1-3), 50-58.

Millero, F.J., Graham, T.B., Huang, F., Bustos-Serrano, H. and Pierrot, D. 2006. Dissociation constants of carbonic acid in seawater as a function of salinity and temperature. Marine Chemistry 100(1- 2), 80-94.

Mitsoyannis, E. and Saravacos, G.D. 1977. Precipitation of calcium carbonate on reverse osmosis membranes. Desalination 21(3), 235-240.

OLI Systems Inc. 2022. OLI Stream Analyzer, version 11.0, OLI Systems Inc, New Jersey, USA.

Putnam, D.F. 1971 Composition and concentrative properties of human urine, p. 112, NASA, Washington, D.C.

Rahardianto, A., McCool, B.C. and Cohen, Y. 2008. Reverse osmosis desalting of inland brackish water of high gypsum scaling propensity: kinetics and mitigation of membrane mineral scaling.

Environmental science & technology 42(12), 4292-4297.

Randall, D.G., Krähenbühl, M., Köpping, I., Larsen, T.A. and Udert, K.M. 2016. A novel approach for stabilizing fresh urine by calcium hydroxide addition. Water Research 95, 361-369.

Reichert, P. 1994. AQUASIM-A tool for simulation and data analysis of aquatic systems. Water Science and Technology 30(2), 21.

Rektorschek, M., Weeks, D., Sachs, G. and Melchers, K. 1998. Influence of pH on metabolism and urease activity of Helicobacter pylori. Gastroenterology 115(3), 628-641.

Sierra, E., Acién, F., Fernández, J., García, J., González, C. and Molina, E. 2008. Characterization of a flat plate photobioreactor for the production of microalgae. Chemical Engineering Journal 138(1-3), 136-147.

Siva, T., Muralidharan, S., Sathiyanarayanan, S., Manikandan, E. and Jayachandran, M. 2017.

Enhanced polymer induced precipitation of polymorphous in calcium carbonate: calcite aragonite vaterite phases. Journal of Inorganic and Organometallic Polymers and Materials 27(3), 770-778.

Song, Y., Weidler, P.G., Berg, U., Nüesch, R. and Donnert, D. 2006. Calcite-seeded crystallization of calcium phosphate for phosphorus recovery. Chemosphere 63(2), 236-243.

Stumm, W. and Morgan, J.J. (1996) Aquatic chemistry: chemical equilibria and rates in natural waters, John Wiley & Sons, New York.

Touati, K., Cherif, H., Kammoun, N., Jendoubi, M. and Elfil, H. 2018. Inhibition of calcium carbonate scaling by precipitation using secondary nucleation coupled to degassing with atmospheric air.

Journal of water process engineering 22, 258-264.

Udert, K. 2002. The fate of phosphorus and nitrogen in source-separated urine, PhD thesis. Swiss Federal Institute of Technology, Zurich, Switzerland.

Udert, K.M., Larsen, T.A. and Gujer, W. 2003. Estimating the precipitation potential in urine- collecting systems. Water Research 37(11), 2667-2677.

Velts, O., Uibu, M., Kallas, J. and Kuusik, R. 2011. CO2 mineral trapping: Modeling of calcium carbonate precipitation in a semi-batch reactor. Energy Procedia 4, 771-778.

Warner, R.C. 1942. The kinetics of the hydrolysis of urea and of arginine. Journal of Biological Chemistry 142(2), 705-723.