LUNULARIA -features, morphology, anatomy ,reproduction etc.
Dissertation Work- Hari mohan at Goa university
1. Exploring the potential of halotolerant bacteria in the degradation of
dissolved ammonia from aquaculture farm
Hari Mohan Jha
MB0515
Under supervision of
Prof. Savita Kerkar
Dept. of Biotechnology, Goa university
3. Aim
• EXPLORING THE POTENTIAL OF HALOTOLERANT BACTERIA IN THE DEGRADATION OF DISSOLVED
AMMONIA FROM AQUACULTURE FARM.
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4. Objectives
• Isolation of ammonia utilizing bacteria from aquaculture pond.
• Screening of bacteria for ammonia oxidizing activity.
• Determining the effects of the Ammonia Oxidizing Bacteria (AOB) on the concentration
of inorganic nutrients and physico-chemical parameters.
• Partial Identification of the AOB.
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6. Bacteria isolation
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Sample collected from Site 1 (S1A, S1B,
S1C) and Site 4 (S4A, S4B, S4C)
• Water sample was collected from Dr. Rivonkar Aquaculture
Farm (15.4602° N,73.8950° E)
7. Bacterial growth analysis
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• Figure showing bacterial culture growth for
SK0116 to SK1016 (SKCC).
• No significant growth observed in SK0116,
SK0216, SK0316, SK0416, SK0516.
• SK0616, SK0716, SK0916, SK0816 showed
maximum growth within allotted period of
time.
• Figure showing bacterial growth for SK1116, SK1216,
SK1316, SK1416, SK1716, ASK9, ASK35, ASK11,
ASK29, ASK186
0
0.2
0.4
0.6
0.8
SK1116 SK1216 SK1316 SK1416 SK1716 ASK9 ASK35 ASK11 ASK29 ASK186
Opticaldensity
Bacterial culture
Bacterial Growth
2 Days 4 Days 6 Days
]o
8. 8
• Figure showing bacterial growth for S1A, S1B,
S1C, S4A, S4B, and S4C ( From aquaculture farm)
• Every bacterial culture showed significant growth
in provided conditions.
9. Analysis for Ammonium degradation
• Figure showing ammonium concentration at
interval of 2days for first 10 bacterial culture
from SKCC.
• SK0916 showed only ammonium degradation
i.e. 41% , whereas SK1016, SK0816 showed
increased then degradation in ammonium
concentration.
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0
20
40
60
80
100
120
140
160
180
200
Control SK0116 SK0216 SK0316 SK0416 SK0516 SK0616 SK0716 SK0916 SK1016 SK0816
Conc(mg/L)
Culture
Day 2 Day 4 Day 6
10. •
10
• Figure showing ammonium concentration at
interval of 2days for next 10 culture.
• ASK29 showed only ammonium degradation
0
20
40
60
80
100
120
SK1116 SK1216 SK1316 SK1416 SK1716 ASK9 ASK35 ASK11 ASK29 ASK186
AmmoniumConc.(mg/L)
Bacterial culture
2Days 4Days 6Days
• Figure showing ammonium concentration at interval
of 2days for aquaculture isolates.
• S1A showed significant ammonium degradation i.e.
42% in six days interval.
18. Scanning electron microscopy
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• Figure showing SEM image of S1A at different magnification i.e.5000X and 7000X respectively
• The size of bacteria found to be 2.640um.
23. Summary
• The project work focused on the potential application of halotolerant bacteria for degradation of
dissolved ammonia.
• Halotolerant Bacteria from an aquaculture farm were isolated and hypersaline bacteria from SKCC
were used for the study.
• The farm and saltern bacteria were screened for Ammonium oxidization activity.
• Ammonia Oxidising Bacteria (AOB) were further analysed for its effect on different
physiochemical parameters and nutrients.
• The best ammonia oxidising bacteria were selected based on its potential to degrade dissolved
ammonia and oxygen utilisation.
• The bacteria S1A showed similarity with Bacillus aryabhattai (99.85%), Bacillus
megaterium (99.7%) and Bacillus flexus (98.86%) based on 16S rRNA sequencing, phylogenetic
analysis, morphological and biochemical characteristics.
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24. Conclusion
• The halotolerant bacteria S1A isolated from aquaculture farm showed ammonium oxidizing
activity which could be explored further as a bioremidiator of Ammonia from aquaculture farm.
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25. Acknowledgement
I would like to thank
• Department of Biotechnology , New Delhi
• HOD Dept. of Biotechnology and My Guide Prof. Savita kerkar
• All faculty members Usha Ma’am, Barros Ma’am, Ghadi Sir, Abhishek Sir, Gautam Sir
• Samantha Ma’am and all Research scholar of our Dept.
• Non teaching staff
• My classmates , my juniors and our seniors .
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26. References
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Nitrosomonas europaea is a multimer of an octa-heme subunit.J.Biol.Chem.268, 14645-14654.
• A.Dapena, J. L. Campos, A. Mosquera, and R. Mendez,( 2006) “Anammox process for nitrogen removal from
anaerobically digested fish canning effluents,” Water Sci. Technol, vol. 53, pp. 265-74
• Altschul, S. F., Madden, T. L., Schaeffer, A. A., Zhang, J., Zhang, Z., Miller, W. & Lipman, D. J. (1997). Gapped BLAST and
PSI‐BLAST: a new generation of protein database search programs. Nucleic Acids Res 25, 3389‐3402.
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Autotrophic Life Academic Press, London, pp. 171- 200.
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aquifer, Cape Cod, Massachusetts and detection of a novel cluster associated with nitrifying Betaproteobacteria,” J
Contam Hydrol, vol. 103, pp. 182-93.
• Ehrich, S., Behrens, D., Lebedeva, E., Ludwig, W. and Bock, E. (1995) A new obligately chemolithoautotrophic, nitrite-
oxidizing bacterium, Nitrospira moscoviensis sp. nov and its phylogenetic relationship.Arch.Microbiol.164, 16-23.
• Eigner, U.and Bock, E. (1972) Synthesis and breakdown of polyphosphate fraction in cells of Nitrobacter
winogradskyi.Arch.Mikrobiol.81, 367-378.
• Felsenstein J. (1985). Confidence limits on phylogenies: An approach using the bootstrap. Evolution 39:783-791
• Golterman (H.L.) & Clymo (R.S.). (1969). — Chemical Analysis of Fresh Waters. In IBP Handbook No 8. Blackwell
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27. • Tamura K, Stecher G, Peterson D, Filipski A, and Kumar S (2013) MEGA6: Molecular Evolutionary Genetics
Analysis version 6.0. Molecular Biology and Evolution:30 2725-2729
• Wood PM. (1986). Nitrification as a bacterial energy source. See Ref. 141a, pp.39–62
• Zart, D.and Bock, E. (1998) High rate of aerobic nitrification and denitrification by
Nitrosomonas eutropha grown in a fermentor with complete biomass retention in the presence of gaseous
NO2 or NO. Arch.Microbiol.169, 282-286.
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