Nitrogen Balance of Intensive Snakehead Fish Culture in Earthen Ponds under Different Water Exchange Frequencies: a Case Study of Ang Thong Fisheries and Processing Cooperative
Keywords:
nitrogen balance, water exchange, intensive culture system, snakehead fishAbstract
Background and Objectives : An intensive snakehead fish culture in earthen ponds in Ang Thong province are reared without any aeration system. Waste accumulation occurs according to the culture period. Therefore, the water must be exchanged with different volumes and frequencies. The discharged effluent is usually high in nitrogen compounds, especially ammonia and nitrate. These affected the water quality in natural water resources and the environment. Due to the lack of information on the optimal water exchange frequency for fish growth, in this study, the effect of 3 different water exchange frequencies on the total yield of snakehead fish and nitrogen balance changes in intensive snakehead fish culture in earthen ponds with different water exchange frequencies were studied.
Methodology: The completely randomized design consisted of 3 treatments, which were 3 systems of water exchange frequencies: Treatment 1, snakehead fish farming system with water exchange once a week (T1); Treatment 2, twice a week (T2); and Treatment 3, three times a week (T3). Each treatment contained 3 replicates. The experimental units were 1 rai (1,600 m2) earthen ponds, filled with water at 150 cm depth and a total water volume of 2,400 m3. The fish with an average initial weight (±SD) of 5.01 ± 0.87- 5.47 ± 0.69 g were stocked at the density of 10,000 fish/pond (6.25 fish/m2). The data of total fish weight and total feed were recorded. Water quality, sediment, and total nitrogen in feed, water, fish and sediment were analyzed; the data obtained were then used to calculate the nitrogen budget.
Main Results : The result showed that the average final total fish weight (±SD) of T2 (water exchange 2 times/week) (9,000.00 ± 17.65 kg) and T3 (water exchange 3 times/week) (9,137.00 ± 11.25 kg) had significantly higher yield (p<0.05) than that of T1 (water exchange 1 time/week) (8,600.00 ± 15.14 kg). There was no statistically significant difference (p>0.05) in the total feed used in fish rearing in all three treatments. In addition, the average feed conversion ratio (FCR) in T2 (1.536 ± 0.001) and T3 (1.500 ± 0.001) were significantly lower (p<0.05) than that of T1 (1.603 ± 0.002). The nitrogen budget in snakehead fish culture with three different management systems showed that the nitrogen sources were fish feed, sediment and water, respectively. The main source of nitrogen in the fish ponds was fish feed. The percentages of nitrogen in T1 from water, sediment, and fish feed were 4.1 ± 1.12, 12.7 ± 2.61 and 83.2 ± 4.17%, respectively. Whereas in T2, the nitrogen from water, sediment, and fish feed were 5.7 ± 1.04, 14.0 ± 1.00 and 80.3 ± 2.18%, respectively. As well as, in T3, the nitrogen from water, sediment, and fish feed were 5.2 ± 1.32, 13.8 ± 2.15 and 81.0 ± 1.83%, respectively. The source of nitrogen from water filled into the ponds, was found to be that T2 and T3 had significantly higher (p<0.05) nitrogen percentages than T1, while there were no significant differences (p>0.05) among the nitrogen percentages from the sediment in all 3 treatments. As for the nitrogen from fish feed, T1 had a significantly higher (p<0.05) percentage of nitrogen than those of T2 and T 3. For nitrogen loss from the fish ponds, there was accumulation in fish, sediment, effluent, and others that was non-detected. The main loss of nitrogen from the fish ponds of all 3 treatments was accumulation in fish. As in T1, the nitrogen loss from effluent, fish, sediment and others were 22.1±2.83, 35.0±2.12, 30.1±3.61 and 12.8±3.80 %, respectively. For T2, the nitrogen loss from effluent, fish, sediment and others were 19.5 ± 2.33, 35.2±2.44, 28.6±1.65 and 16.7 ± 4.33 %, respectively. In addition, in T3 the nitrogen loss from effluent, fish, sediment and others were 17.8 ± 4.02, 38.4 ± 3.17, 27.4 ± 1.78 and 16.4 ± 4.12 %, respectively. Nitrogen loss from fish ponds by accumulation in effluent, it was found that in T1, the percentage of nitrogen loss was significantly higher (p<0.05) than those of T2 and T3. The same results were found in nitrogen loss by accumulation in sediment and others. On the other hand, by accumulation in fish, the nitrogen loss of T3 was significantly higher (p<0.05) than those of T1 and T2.
Conclusions : The intensive culture of snakehead fish in earthen ponds with three different water exchange frequencies showed that the fish in T2 and T3 (the water exchange 2 and 3 times/week) had significantly (p<0.05) higher final total fish weight and lower feed conversion ratio than that of the fish in T1. The main source of nitrogen in the fish ponds was from the fish feed, which had an average nitrogen content (±SD) of between 80.3 ± 2.18 and 83.2 ± 4.17%. In addition, the main nitrogen loss from the fish ponds was the fish, which had an average nitrogen content (±SD) of between 35.0 ± 2.12 and 38.4 ± 3.1%. The optimal water exchange frequencies for an intensive snakehead fish culture in earthen ponds were twice a week.
References
Adhikari, S., Sahu, B. C., Mahapatra, A. S., & Dey, L. (2014). Nutrient budgets and effluent characteristics in giant freshwater prawn (Macrobrachium rosenbergii) culture ponds. Bulletin of environmental contamination and toxicology, 92, 509-513. doi.org/10.1007/s00128-014-1227-4.
Ajiboye, A. O., Awogbade, A. A., & Babalola, O. A. (2015). Effects of water exchange on water quality parameters, nutrient utilization and growth of African catfish (Clarias gariepinus). International Journal of Livestock Production, 6(5), 57-60. doi.org/10.5897/IJLP2015.0256.
AOAC. (2000). Official methods of analysis of the Association of Official Analytical Chemists. 17th ed. Association of Official Analytical Chemists & Association of Official Agricultural Chemists. USA: Association of Official Analytical Chemists.
Barbieri, E., & Doi, S. A. (2012). Acute toxicity of ammonia on juvenile cobia (Rachycentron canadum, Linnaeus, 1766) according to the salinity. Aquaculture International, 20(2), 373-382. doi.org/10.1007/s10499-011-9467-3.
Casillas-Hernández, R., Magallón-Barajas, F., Portillo-Clarck, G., & Páez-Osuna, F. (2006). Nutrient mass balances in semi-intensive shrimp ponds from Sonora, Mexico using two feeding strategies: Trays and mechanical dispersal. Aquaculture, 258(1-4), 289-298. doi.org/10.1016/j.aquaculture.2006.03.027.
Chiquito-Contreras, R. G., Hernandez-Adame, L., Alvarado-Castillo, G., Martínez-Hernández, M. D. J., Sánchez-Viveros, G., Chiquito-Contreras, C. J., & Hernandez-Montiel, L. G. (2022). Aquaculture—production system and waste management for agriculture fertilization—A review. Sustainability, 14(12), 7257. doi.org/10.3390/su14127257.
Dalbem Barbosa, A. P., Kosten, S., Muniz, C. C., & Oliveira-Junior, E. S. (2024). From feed to fish-nutrients’ fate in aquaculture systems. Applied Sciences, 14(14), 6056. doi.org/10.3390/app14146056.
Dauda, A. B., Ajadi, A., Bashir, Z., & Ikpe, J. (2022). Frequency of water change on growth performance, nutrient utilization and liver histology of Nile Tilapia (Oreochromis niloticus, Linnaeus, 1758). Asian journal of fisheries and aquatic research. Pg, 16(2), 42-50. doi.org/10.9734/AJFAR/2022/v16i230370.
David, F. S., Proença, D. C., & Valenti, W. C. (2017). Nitrogen budget in integrated aquaculture systems with Nile tilapia and Amazon River prawn. Aquaculture International, 25(5), 1733-1746. doi.org/10.1007/s10499-017-0145-y.
Deka, K., Bordoloi, D., Khound, A. J, Bharali, M. J., & Chelleng, R. (2022). A review on aeration process and different types of aerators used in various aquaculture systems. International Journal of Current Microbiology and Applied Sciences, 11(6), 353-358. doi.org/10.20546/ijcmas.2022.1106.039.
Golder, T. I. (2022). Waste production in aquaculture. Modern Approaches in Chemical and Biological Sciences, 122-128. doi.org/10.31674/book.2022macbs.015.
Gross, A., Boyd, C. E., & Wood, C. W. (2000). Nitrogen transformations and balance in channel catfish ponds. Aquacultural Engineering, 24(1), 1-14. doi.org/10.1016/S0144-8609(00)00062-5.
Herath, S. S., & Satoh, S. (2022). Environmental impacts of nitrogen and phosphorus from aquaculture. In Feed and Feeding Practices in Aquaculture (pp. 427-444). Woodhead Publishing. doi.org/10.1016/B978-0-12-821598-2.00010-2.
Ho, K. Y., & Ho, Y. Y. (2004). Nitrogen dynamics and growing of shrimp (Fenneropenaeus chinensis) in the high density aquaculture ponds. Korean Journal of Fisheries and Aquatic Sciences, 37(1), 24-32. doi.org/10.5657/kfas.2004.37.1.024.
Is-haak, J., Koydon, S., Iampichai, Y., & Ngamphongsai, C. (2022). Effects of ammonia, temperature and their interaction on oxygen consumption rate of Asian seabass (Lates calcarifer) juveniles. Agriculture and Natural Resources, 56(5), 917-924. doi.org/10.34044/j.anres.2022.56.5.06.
Jiao, Y., Zhao, H., Li, Z., Tang, X., Li, Y., Chen, S., Zhu, Z., Wang, T., Strokal, M., & Kroeze, C. (2022). Nitrogen budgets for freshwater aquaculture and mariculture in a large tropical island–a case study for Hainan Island 1998–2018. Marine Environmental Research, 177, 105642. doi.org/10.1016/j.marenvres.2022.105642.
Jiménez-Montealegre, R., Verdegem, M. C. J., Van Dam, A., & Verreth, J. A. J. (2002). Conceptualization and validation of a dynamic model for the simulation of nitrogen transformations and fluxes in fish ponds. Ecological modelling, 147(2), 123-152. doi.org/10.1016/S0304-3800(01)00403-3.
Jørgensen, B.B. (1977) Bacterial sulfate reduction within reduced microniches of oxidized marine sediments. Mar Biol 41, 7–17. doi.org/10.1007/BF00390576.
Kajimura, M., Takimoto, K., & Takimoto, A. (2023). Acute toxicity of ammonia and nitrite to Siamese fighting fish (Betta splendens). BMC Zoology, 8, 25. doi.org/10.1186/s40850-023-00188-3.
Kim, J. H., Kang, Y. J., & Lee, K. M. (2022). Effects of nitrite exposure on the hematological properties, antioxidant and stress responses of juvenile Hybrid Groupers, Epinephelus lanceolatus♂× Epinephelus fuscoguttatus♀. Antioxidants, 11(3), 545. doi.org/10.3390/antiox11030545.
Koschorreck, M. (2005). Nitrogen turnover in drying sediments of an Amazon floodplain lake. Microbial ecology, 49(4), 567-577. doi.org/10.1007/s00248-004-0087-6.
Liu, B., Zhang, K., Wang, G., & He, X. (2023). A Study on nitrogen and phosphorus budgets in a polyculture system of Oreochromis niloticus, Aristichthys nobilis, and Cherax quadricarinatus. Water, 15(15), 2699. doi.org/10.3390/w15152699.
Nhan, D. K., Verdegem, M. C., Milstein, A., & Verreth, J. A. (2008). Water and nutrient budgets of ponds in integrated agriculture-aquaculture systems in the Mekong Delta, Vietnam. Aquaculture Research, 39(11), 1216-1228. doi.org/10.1111/j.1365-2109.2008.01986.x.
Phan, L. T., Bui, T. M., Nguyen, T. T. T., Gooley, G. J., Ingram, B. A., Nguyen, H. V., Nguyen, P. T. , & De Silva, S. S. (2009). Current status of farming practices of striped catfish, Pangasianodon hypophthalmus in the Mekong Delta, Vietnam. Aquaculture, 296(3-4), 227-236. doi.org/10.1016/j.aquaculture.2009.08.017.
Phu, T. Q., Hang, B. T. B., Tuong, D. D., Anna, V. G., Kaneko, T., Phuong, N. T., & Huong, D. T. T. (2022). Effects of size and nitrite exposure on respiration, oxygen partitioning, and growth of obligate air-breathing fish Channa striata. Fisheries Science, 88, 149–159.doi.org/10.1007/s12562-021-01562-1.
Qin, J., Fast, A.W. , & Kai, A.T. (1997), Tolerance of snakehead Channa striatus to ammonia at different pH. Journal of the World Aquaculture Society, 28, 87-90. doi.org/10.1111/j.1749-7345.1997.tb00965.x.
Rutegwa, M., Potužák, J., Hejzlar, J., & Drozd, B. (2019). Carbon metabolism and nutrient balance in a hypereutrophic semi-intensive fishpond. Knowledge & Management of Aquatic Ecosystems, (420), 49. doi.org/10.1051/kmae/2019043.
Sahu, B. C., Adhikari, S., Mahapatra, A. S., & Dey, L. (2013). Carbon, nitrogen, and phosphorus budget in scampi (Macrobrachium rosenbergii) culture ponds. Environmental monitoring and assessment, 185, 10157-10166. doi.org/10.1007/s10661-013-3320-2.
Sahu, B. C., Adhikari, S., Mahapatra, A. S., & Dey, L. (2015). Nitrogen, phosphorus, and carbon budgets in polyculture ponds of Indian major carps and giant freshwater prawn in Orissa State, India. Journal of applied aquaculture, 27(4), 365-376. doi.org/10.1080/10454438.2015.1115320.
Sampantamit, T., Ho, L., Lachat, C., Sutummawong, N., Sorgeloos, P., & Goethals, P. (2020). Aquaculture production and its environmental sustainability in Thailand: Challenges and potential solutions. Sustainability, 12(5), 2010. doi.org/10.3390/su12052010.
Saraswathy, R., Muralidhar, M., Kailasam, M., Ravichandran, P., Gupta, B. P., Krishnani, K. K., Ponniah, A. G., Sundaray, J. K., Panigrahi, A., & Nagavel, A. (2013). Effect of stocking density on soil, water quality and nitrogen budget in Penaeus monodon (Fabricius, 798) culture under zero water exchange system. Aquaculture Research, 44(10), 1578-1588. doi.org/10.1111/j.1365-2109.2012.03165.x.
Shen, C., Cao, S., Mohsen, M., Li, X. S., Wang, L., Lu, K. L., Zhang, C.X., & Song, K. (2024). Effects of chronic nitrite exposure on hematological parameters, oxidative stress and apoptosis in spotted seabass (Lateolabrax maculatus) reared at high temperature. Aquaculture Reports, 35, 102022. doi.org/10.1016/j.aqrep.2024.102022.
Shiu, N., Guo, H., & Kim, Y. (2024). Heated aeration for nitrite-oxidizing bacteria (NOB) control in anammox-integrated membrane-aerated biofilm reactors (MABR). Environments, 11(7), 155.
doi.org/10.1080/10454438.2015.1115320.
Siddiqui, A. Q., & Al-Harbi, A. H. (1999). Nutrient budgets in tanks with different stocking densities of hybrid tilapia. Aquaculture, 170(3-4), 245-252. doi.org/10.1016/S0044-8486(98)00421-9.
Thakur, D. P., & Lin, C. K. (2003). Water quality and nutrient budget in closed shrimp (Penaeus monodon) culture systems. Aquacultural engineering, 27(3), 159-176. doi.org/10.1016/S0144-8609(02)00055-9.
Yan, Y., Zhou, J., Du, C., Yang, Q., Huang, J., Wang, Z., Xu, J., & Zhang, M. (2024). Relationship between nitrogen dynamics and key microbial nitrogen-cycling genes in an intensive freshwater aquaculture pond. Microorganisms, 12(2), 266. doi.org/10.3390/ microorganisms12020266.

Downloads
Published
How to Cite
Issue
Section
License
Copyright (c) 2025 Faculty of Science, Burapha University

This work is licensed under a Creative Commons Attribution-NonCommercial-NoDerivatives 4.0 International License.
Burapha Science Journal is licensed under a Creative Commons Attribution-NonCommercial-NoDerivatives 4.0 International (CC BY-NC-ND 4.0) licence, unless otherwise stated. Please read our Policies page for more information