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1860797960242069504
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INTELEK Repository
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Online Access
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https://intelek.unisza.edu.my/intelek/pages/search.php?search=!collection407072
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2024-08-29 09:27:48
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Restricted Document
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15096
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UniSZA
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[1] P. Read, T. Fernandes, Management of environmental impacts of marine aquaculture in Europe, Aquaculture 226 (2003) 139–163. [2] R.H. Piedrahita, Reducing the potential environmental impact of tank aquaculture effluents through intensification and recirculation, Aquaculture 226 (2003) 35–44. [3] S.H. Sugiura, D.D. Marchant, T. Wigins, R.P. Ferraris, Effluent profile of commercially used low-phosphorus fish feeds, Environ. Pollut. 140 (2006) 95–101. [4] B. Eikebrokk, R. Piedrahita, Y. Ulgenes, Rates of fish waste production and effluent discharge from a recirculating system (BIOFISH) under commercial conditions, Aquacult. Res. 26 (1995) 589–599. [5] D.E. Brune, G. Schwartz, A.G. Eversole, J.A. Collier, T.E. Schwedler, Intensification of pond aquaculture and high rate photosynthetic systems, Aquacult. Eng. 28 (2003) 65–86. [6] D.M. Smith, M.A. Burford, S.J. Tabrett, S.J. Irvin, L. Ward, The effect of feeding frequency on water quality and growth of the black tiger shrimp (Penaeus monodon), Aquaculture 207 (2002) 125–136. [7] E.S. Thoman, E.D. Ingall, D.A. Davis, C.R. Arnold, A nitrogen budget for a closed, recirculating mariculture system, Aquacult. Eng. 24 (2001) 195–211. [8] A.Q. Siddiqui, A.H. Al-Harbi, Nutrient budget in tanks with different stocking densities of hybrid tilapia, Aquaculture 170 (1999) 245–252. [9] A.V. Suresh, L.C. Kwei, Effect of stocking density on water quality and production of red tilapia in a recirculating water system, Aquacult. Eng. 11 (1992) 1–22. [10] M.D. Krom, A. Neori, A total nitrogen budget for an experimental intensive fishpond with circularly moving seawater, Aquaculture 83 (1989) 345–358. [11] P.A. Azevedo, C.L. Podemski, R.H. Hesslein, S.E.M. Kasian, D.L. Findlay, D.P. Bureau, Estimation of waste outputs by a rainbow trout cage farm using a nutritional approach and monitoring of lake water quality, Aquaculture 311 (2011) 175–186. [12] M. Bermudes, B. Glencross, K. Austen, W. Hawkins, The effects of temperature and size on the growth, energy budget and waste outputs of barramundi (Lates calcarifer), Aquaculture 306 (2010) 160–166. [13] J.E. Rakocy, D.S. Bailey, R.C. Shultz, E.S. Thoman, Update on tilapia and vegetable production in the UVI aquaponics system, New Dimensions on Farmed Tilapia: Proceedings of the Sixth International Symposium on Tilapia in Aqua-culture, Manila, Philippines, 2004, pp. 676–690. [14] O. Schneider, V. Sereti, E.H. Eding, J.A.J. Verreth, Analysis of nutrient flows in integrated intensive aquaculture systems, Aquacult. Eng. 32(2005) (2005) 379–401. [15] Y.F. Lin, S.R. Jing, D.Y. Lee, Y.F. Chang, Y.M. Chen, K.C. Shih, Performance of a constructed wetland treating intensive shrimp aquaculture wastewater under high hydraulic loading rate, Environ. Pollut. 134 (2005) 411–442. [16] J. Blamire, E-Learning for Quantitative Analysis-Kjeldahl Method, 2003. Available from: http://www.brooklyn.cuny. edu/bc/ahp/SDKC/Chem/SD_KjeldahlMethod.html. [17] N.J. Thiex, H. Manson, S. Anderson, J.A. Persson, Determination of crude protein in animal feed, forage, grain, and oilseeds by using block digestion with a copper catalyst and steam distillation into boric acid: Collaborative study, J. AOAC Int. 85 (2002) 309–317. [18] T.M. Losordo, M.P. Masser, H. Westers, System carrying capacity and flow estimation. in: M.B. Timmons, T.M. Losordo, (Eds.), Aquaculture Water Reuse Systems: Engineering Design and Management, Develop. Aquacul. Fish. Sci. 27 (1994) 9–60. [19] J.E. Huguenin, J. Colt, Design and Operating Guide for Aquaculture Seawater Systems, Elsevier, Amsterdam, 1989. [20] R.H. Piedrahita, Reducing the potential environmental impact of tank aqua-culture effluents through intensification and recirculation, Aquaculture 226 (2003) 35–44. [21] E. Papatryphon, J. Petit, H.M.G. Van der Werf, S.J. Kaushik, K. Claver, Nutrient-balance modelling as a tool for environmental management in aquaculture: The case of trout farming in France, Environ. Manage. 35 (2005) 161–174. [22] J.A. Brandes, A.H. Devol, Isotopic fractionation of oxygen and nitrogen in coastal marine sediments, Geochim. Cosmochim. Acta 61 (1997) 1798–1801. [23] Y. Tal, J.E.M. Watts, S.B. Schreier, K.R. Sowers, H.J. Schreier, Characterization of the microbial community and nitrogen transformation processes associated with moving bed bioreactors in a closed recirculated mariculture system, Aquaculture 215 (2003) 187–202. [24] Y. Suzuki, T. Maruyama, H. Numata, H. Sato, M. Asakawa, Performance of a closed recirculating system with foam separation, nitrification and denitrification units for intensive culture of eel: Toward zero emission, Aquacult. Eng. 29 (2003) 165–182.
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4839-01-FH02-FPBSM-14-00328.pdf
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https://intelek.unisza.edu.my/intelek/pages/view.php?ref=15096
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15096 https://intelek.unisza.edu.my/intelek/pages/view.php?ref=15096 https://intelek.unisza.edu.my/intelek/pages/search.php?search=!collection407072 Restricted Document Article Journal application/pdf Adobe Acrobat Pro DC 20 Paper Capture Plug-in with ClearScan 11 1.6 Adobe Acrobat Pro DC 20.6.20042 2024-08-29 09:27:48 4839-01-FH02-FPBSM-14-00328.pdf UniSZA Private Access Nitrogen budget and effluent nitrogen components in aquaponics recirculation system Desalination and Water Treatment In this study, the dynamics of nitrogen through aquaponics recirculation system was examined by developing a nitrogen budget. The model evaluated total ammonia nitrogen (TAN) production and removal in biofilters, identifying and quantifying the fate of nitrate nitrogen (NO 3 -N) and determining the system maximum carrying capacity. Of the nitrogen input into the culture tank via feed, 83.8% was recovered from different pool: 39.4% as fish flesh (harvested), 2.1% as mortalities, 34.7% as dissolved inorganic forms of nitrogen and 7.6% as total organic nitrogen. The remaining 16.2% of nitrogen unaccounted for likely was lost as nitrogen gas due to passive denitrification and as volatization of ammonia. Average TAN in the culture tanks was 2.08 mg/L. Under current condition, system loading with fish biomass at average of 68.5% of the maximum predicted. The hydroponic troughs removal efficiency averaged 60.4% TAN per pass. From TAN production, 88% was removed in hydroponic troughs, 11% by passive nitrification and 1% by water exchange. Under conditions of reusing treated effluent with residual TAN, the hydroponic troughs work normally, while TAN in the systems did not increase noticeably. 52 6 744-752 [1] P. Read, T. Fernandes, Management of environmental impacts of marine aquaculture in Europe, Aquaculture 226 (2003) 139–163. [2] R.H. Piedrahita, Reducing the potential environmental impact of tank aquaculture effluents through intensification and recirculation, Aquaculture 226 (2003) 35–44. [3] S.H. Sugiura, D.D. Marchant, T. Wigins, R.P. Ferraris, Effluent profile of commercially used low-phosphorus fish feeds, Environ. Pollut. 140 (2006) 95–101. [4] B. Eikebrokk, R. Piedrahita, Y. Ulgenes, Rates of fish waste production and effluent discharge from a recirculating system (BIOFISH) under commercial conditions, Aquacult. Res. 26 (1995) 589–599. [5] D.E. Brune, G. Schwartz, A.G. Eversole, J.A. Collier, T.E. Schwedler, Intensification of pond aquaculture and high rate photosynthetic systems, Aquacult. Eng. 28 (2003) 65–86. [6] D.M. Smith, M.A. Burford, S.J. Tabrett, S.J. Irvin, L. Ward, The effect of feeding frequency on water quality and growth of the black tiger shrimp (Penaeus monodon), Aquaculture 207 (2002) 125–136. [7] E.S. Thoman, E.D. Ingall, D.A. Davis, C.R. Arnold, A nitrogen budget for a closed, recirculating mariculture system, Aquacult. Eng. 24 (2001) 195–211. [8] A.Q. Siddiqui, A.H. Al-Harbi, Nutrient budget in tanks with different stocking densities of hybrid tilapia, Aquaculture 170 (1999) 245–252. [9] A.V. Suresh, L.C. Kwei, Effect of stocking density on water quality and production of red tilapia in a recirculating water system, Aquacult. Eng. 11 (1992) 1–22. [10] M.D. Krom, A. Neori, A total nitrogen budget for an experimental intensive fishpond with circularly moving seawater, Aquaculture 83 (1989) 345–358. [11] P.A. Azevedo, C.L. Podemski, R.H. Hesslein, S.E.M. Kasian, D.L. Findlay, D.P. Bureau, Estimation of waste outputs by a rainbow trout cage farm using a nutritional approach and monitoring of lake water quality, Aquaculture 311 (2011) 175–186. [12] M. Bermudes, B. Glencross, K. Austen, W. Hawkins, The effects of temperature and size on the growth, energy budget and waste outputs of barramundi (Lates calcarifer), Aquaculture 306 (2010) 160–166. [13] J.E. Rakocy, D.S. Bailey, R.C. Shultz, E.S. Thoman, Update on tilapia and vegetable production in the UVI aquaponics system, New Dimensions on Farmed Tilapia: Proceedings of the Sixth International Symposium on Tilapia in Aqua-culture, Manila, Philippines, 2004, pp. 676–690. [14] O. Schneider, V. Sereti, E.H. Eding, J.A.J. Verreth, Analysis of nutrient flows in integrated intensive aquaculture systems, Aquacult. Eng. 32(2005) (2005) 379–401. [15] Y.F. Lin, S.R. Jing, D.Y. Lee, Y.F. Chang, Y.M. Chen, K.C. Shih, Performance of a constructed wetland treating intensive shrimp aquaculture wastewater under high hydraulic loading rate, Environ. Pollut. 134 (2005) 411–442. [16] J. Blamire, E-Learning for Quantitative Analysis-Kjeldahl Method, 2003. Available from: http://www.brooklyn.cuny. edu/bc/ahp/SDKC/Chem/SD_KjeldahlMethod.html. [17] N.J. Thiex, H. Manson, S. Anderson, J.A. Persson, Determination of crude protein in animal feed, forage, grain, and oilseeds by using block digestion with a copper catalyst and steam distillation into boric acid: Collaborative study, J. AOAC Int. 85 (2002) 309–317. [18] T.M. Losordo, M.P. Masser, H. Westers, System carrying capacity and flow estimation. in: M.B. Timmons, T.M. Losordo, (Eds.), Aquaculture Water Reuse Systems: Engineering Design and Management, Develop. Aquacul. Fish. Sci. 27 (1994) 9–60. [19] J.E. Huguenin, J. Colt, Design and Operating Guide for Aquaculture Seawater Systems, Elsevier, Amsterdam, 1989. [20] R.H. Piedrahita, Reducing the potential environmental impact of tank aqua-culture effluents through intensification and recirculation, Aquaculture 226 (2003) 35–44. [21] E. Papatryphon, J. Petit, H.M.G. Van der Werf, S.J. Kaushik, K. Claver, Nutrient-balance modelling as a tool for environmental management in aquaculture: The case of trout farming in France, Environ. Manage. 35 (2005) 161–174. [22] J.A. Brandes, A.H. Devol, Isotopic fractionation of oxygen and nitrogen in coastal marine sediments, Geochim. Cosmochim. Acta 61 (1997) 1798–1801. [23] Y. Tal, J.E.M. Watts, S.B. Schreier, K.R. Sowers, H.J. Schreier, Characterization of the microbial community and nitrogen transformation processes associated with moving bed bioreactors in a closed recirculated mariculture system, Aquaculture 215 (2003) 187–202. [24] Y. Suzuki, T. Maruyama, H. Numata, H. Sato, M. Asakawa, Performance of a closed recirculating system with foam separation, nitrification and denitrification units for intensive culture of eel: Toward zero emission, Aquacult. Eng. 29 (2003) 165–182.
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| spellingShingle |
Nitrogen budget and effluent nitrogen components in aquaponics recirculation system
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| summary |
In this study, the dynamics of nitrogen through aquaponics recirculation system was examined by developing a nitrogen budget. The model evaluated total ammonia nitrogen (TAN) production and removal in biofilters, identifying and quantifying the fate of nitrate nitrogen (NO 3 -N) and determining the system maximum carrying capacity. Of the nitrogen input into the culture tank via feed, 83.8% was recovered from different pool: 39.4% as fish flesh (harvested), 2.1% as mortalities, 34.7% as dissolved inorganic forms of nitrogen and 7.6% as total organic nitrogen. The remaining 16.2% of nitrogen unaccounted for likely was lost as nitrogen gas due to passive denitrification and as volatization of ammonia. Average TAN in the culture tanks was 2.08 mg/L. Under current condition, system loading with fish biomass at average of 68.5% of the maximum predicted. The hydroponic troughs removal efficiency averaged 60.4% TAN per pass. From TAN production, 88% was removed in hydroponic troughs, 11% by passive nitrification and 1% by water exchange. Under conditions of reusing treated effluent with residual TAN, the hydroponic troughs work normally, while TAN in the systems did not increase noticeably.
|
| title |
Nitrogen budget and effluent nitrogen components in aquaponics recirculation system
|
| title_full |
Nitrogen budget and effluent nitrogen components in aquaponics recirculation system
|
| title_fullStr |
Nitrogen budget and effluent nitrogen components in aquaponics recirculation system
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| title_full_unstemmed |
Nitrogen budget and effluent nitrogen components in aquaponics recirculation system
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| title_short |
Nitrogen budget and effluent nitrogen components in aquaponics recirculation system
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| title_sort |
nitrogen budget and effluent nitrogen components in aquaponics recirculation system
|