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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
Dissertation Stage - II
2
Aim
• EXPLORING THE POTENTIAL OF HALOTOLERANT BACTERIA IN THE DEGRADATION OF DISSOLVED
AMMONIA FROM AQUACULTURE FARM.
3
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.
4
Results
5
Bacteria isolation
6
 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)
Bacterial growth analysis
7
• 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
• Figure showing bacterial growth for S1A, S1B,
S1C, S4A, S4B, and S4C ( From aquaculture farm)
• Every bacterial culture showed significant growth
in provided conditions.
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.
9
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
• 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.
Nitrite estimation
11
0
1
2
3
4
5
6
7
SK09 ASK29 S1A
Conc.(uM)
• Figure showing nitrite production by SK09, ASK 29 and S1A
Nitrate estimation
12
• Figure showing nitrate production by SK09 and S1A
Overall study on Bacterial strain
13
• Figure showing the correlation in different physico
chemical character for S1A
14
• Figure showing the correlation in different physico
chemical character for SK09
Comparison between bacterial culture on the basis observed traits
SK09 (SKCC)
• less
• 41%
• 1uM
• 1.3uM
• 3.02mg/L
S1A (Aquaculture farm)
• more
• 42%
• 5.7uM
• 2.82uM
• 0.63mg/L
15
• Characterstics
• Growth
• Ammonium degradation
• Nitrite production
• Nitrate production
• Oxygen consumption
Bacterial identification
16
• Gram staining for S1A under 100X magnification oil immersion
Biochemical Test
Carbohydrates S1A Carbohydrates S1A Carbohydrates S1A
Lactose + Salicin + Sodium gluconate -
Xylose + Dulcitol - Glycerol +
Maltose + Inositol - alpha-methy-D-mannoside -
Fructose + Sorbitol + Xylitol -
Dextrose + Mannitol + ONPG +
Galactose - Adonitol - Esculine hudrolysis +
Raffinose + Arabitol - D- Arabinose -
trehalose + Erythritol - Citrate utilization -
Melibiose + alpha-methy-D-glucose - malonate utilization -
Sucrose + Rhamnose - Sorbose -
L-Arabinose + Cellobiose + Melezitose -
Mannose + Inulin +
17
Scanning electron microscopy
18
• Figure showing SEM image of S1A at different magnification i.e.5000X and 7000X respectively
• The size of bacteria found to be 2.640um.
16S rRNA sequencing
• >S1A
AACCTGCCTGTAAGACTGGGATAACTTCGGGAAACCGAAGCTAATACCGGATAGGATCTTCTCCTTCATGGGAGATGATT
GAAAGATGGTTTCGGCTATCACTTACAGATGGGCCCGCGGTGCATTAGCTAGTTGGTGAGGTAACGGCTCACCAAGGCA
ACGATGCATAGCCGACCTGAGAGGGTGATCGGCCACACTGGGACTGAGACACGGCCCAGACTCCTACGGGAGGCAGCA
GTAGGGAATCTTCCGCAATGGACGAAAGTCTGACGGAGCAACGCCGCGTGAGTGATGAAGGCTTTCGGGTCGTAAAAC
TCTGTTGTTAGGGAAGAACAAGTATGAGAGTAACTGCTCGTACCTTGACGGTACCTAACCAGAAAGCCACGGCTAACTAC
GTGCCAGCAGCCGCGGTAATACGTAGGTGCAAGCGTTATCCGGAATTATTGGGCGTAAAGCGCGCGCAGGCGGTTTCTTA
AGTCTGATGTGAAAGCCCACGGCTCAACCGTGGAGGGTCATTGGAAACTGGGGAACTTGAGTGCAGAAGAGAAAAGC
GGAATTCCACGTGTAGCGGTGAAATGCGTAGAGATGTGGAGGAACACCAGTGGCGAAGGCGGCTTTTTGGTCTGTAACT
GACGCTGAGGCGCGAAAGCGTGGGGAGCAAACAGGATTAGATACCCTGGTAGTCCACGCCGTAAACGATGAGTGCTAA
GTGTTAGAGGGTTTCCGCCCTTTAGTGCTGCAGCTAACGCATTAAGCACTCCGCCTGGGGAGTACGGTCGCAAGACTGAA
ACTCAAAGGAATTGACGGGGGCCCGCACAAGCGGTGGAGCATGTGGTTTAATTCGAAGCAACGCGAAGAACCTTACCA
GGTCTTGACATCCTCTGACAACTCTAGAGATAGAGCGTTCCCCTTCGGGGGACAGAGTGACAGGTGGTGCATGGTTGTCG
TCAGCTCGTGTCGTGAGATGTTGGGTTAAGTCCCGCAACGAGCGCAACCCTTGATCTTAGTTGCCAGCATTTAGTTGGGC
ACTCTAAGGTGACTGCCGGTGACAAACCGGAGGAAGGTGGGGATGACGTCAAATCATCATGCCCCTTATGACCTGGGCT
ACACACGTGCTACAATGGATGGTACAAAGGGCTGCAAGACCGCGAGGTCAAGCCAATCCCATAAAACCATTCTCAGTTCG
GATTGTAGCCTGCAACTCGCCTACATGAAGCTGGAATCGCTAGTATCGCGGATCAGCATGCCGCGGTGAATACGTTCCCGG
GCCTTGTACACACCGCCCGTCACACCACGAGAGTTT GTAACACCC
19
Evolutionary relativeness.
20
• Closest neighbours to S1A
22
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.
23
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.
24
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 .
25
References
• Arciero, D.M. and Hooper, A.B. (1993) Hydroxylamine oxidoreductase from
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.
• Bock, E., Koops, H.-P., Harms, H. and Ahlers, B. (1991). The biochemistry of nitrifying organisms in variations of
Autotrophic Life Academic Press, London, pp. 171- 200.
• D. N. Miller and R. L. Smith (2009). “Microbial characterization of nitrification in a shallow, nitrogen-contaminated
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
Scientific Publications, Oxford. 172 pp.
26
• 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.
27
Thank you
28
29

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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. 3
  • 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. 4
  • 6. Bacteria isolation 6  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 7 • 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. 9 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.
  • 11. Nitrite estimation 11 0 1 2 3 4 5 6 7 SK09 ASK29 S1A Conc.(uM) • Figure showing nitrite production by SK09, ASK 29 and S1A
  • 12. Nitrate estimation 12 • Figure showing nitrate production by SK09 and S1A
  • 13. Overall study on Bacterial strain 13 • Figure showing the correlation in different physico chemical character for S1A
  • 14. 14 • Figure showing the correlation in different physico chemical character for SK09
  • 15. Comparison between bacterial culture on the basis observed traits SK09 (SKCC) • less • 41% • 1uM • 1.3uM • 3.02mg/L S1A (Aquaculture farm) • more • 42% • 5.7uM • 2.82uM • 0.63mg/L 15 • Characterstics • Growth • Ammonium degradation • Nitrite production • Nitrate production • Oxygen consumption
  • 16. Bacterial identification 16 • Gram staining for S1A under 100X magnification oil immersion
  • 17. Biochemical Test Carbohydrates S1A Carbohydrates S1A Carbohydrates S1A Lactose + Salicin + Sodium gluconate - Xylose + Dulcitol - Glycerol + Maltose + Inositol - alpha-methy-D-mannoside - Fructose + Sorbitol + Xylitol - Dextrose + Mannitol + ONPG + Galactose - Adonitol - Esculine hudrolysis + Raffinose + Arabitol - D- Arabinose - trehalose + Erythritol - Citrate utilization - Melibiose + alpha-methy-D-glucose - malonate utilization - Sucrose + Rhamnose - Sorbose - L-Arabinose + Cellobiose + Melezitose - Mannose + Inulin + 17
  • 18. Scanning electron microscopy 18 • Figure showing SEM image of S1A at different magnification i.e.5000X and 7000X respectively • The size of bacteria found to be 2.640um.
  • 19. 16S rRNA sequencing • >S1A AACCTGCCTGTAAGACTGGGATAACTTCGGGAAACCGAAGCTAATACCGGATAGGATCTTCTCCTTCATGGGAGATGATT GAAAGATGGTTTCGGCTATCACTTACAGATGGGCCCGCGGTGCATTAGCTAGTTGGTGAGGTAACGGCTCACCAAGGCA ACGATGCATAGCCGACCTGAGAGGGTGATCGGCCACACTGGGACTGAGACACGGCCCAGACTCCTACGGGAGGCAGCA GTAGGGAATCTTCCGCAATGGACGAAAGTCTGACGGAGCAACGCCGCGTGAGTGATGAAGGCTTTCGGGTCGTAAAAC TCTGTTGTTAGGGAAGAACAAGTATGAGAGTAACTGCTCGTACCTTGACGGTACCTAACCAGAAAGCCACGGCTAACTAC GTGCCAGCAGCCGCGGTAATACGTAGGTGCAAGCGTTATCCGGAATTATTGGGCGTAAAGCGCGCGCAGGCGGTTTCTTA AGTCTGATGTGAAAGCCCACGGCTCAACCGTGGAGGGTCATTGGAAACTGGGGAACTTGAGTGCAGAAGAGAAAAGC GGAATTCCACGTGTAGCGGTGAAATGCGTAGAGATGTGGAGGAACACCAGTGGCGAAGGCGGCTTTTTGGTCTGTAACT GACGCTGAGGCGCGAAAGCGTGGGGAGCAAACAGGATTAGATACCCTGGTAGTCCACGCCGTAAACGATGAGTGCTAA GTGTTAGAGGGTTTCCGCCCTTTAGTGCTGCAGCTAACGCATTAAGCACTCCGCCTGGGGAGTACGGTCGCAAGACTGAA ACTCAAAGGAATTGACGGGGGCCCGCACAAGCGGTGGAGCATGTGGTTTAATTCGAAGCAACGCGAAGAACCTTACCA GGTCTTGACATCCTCTGACAACTCTAGAGATAGAGCGTTCCCCTTCGGGGGACAGAGTGACAGGTGGTGCATGGTTGTCG TCAGCTCGTGTCGTGAGATGTTGGGTTAAGTCCCGCAACGAGCGCAACCCTTGATCTTAGTTGCCAGCATTTAGTTGGGC ACTCTAAGGTGACTGCCGGTGACAAACCGGAGGAAGGTGGGGATGACGTCAAATCATCATGCCCCTTATGACCTGGGCT ACACACGTGCTACAATGGATGGTACAAAGGGCTGCAAGACCGCGAGGTCAAGCCAATCCCATAAAACCATTCTCAGTTCG GATTGTAGCCTGCAACTCGCCTACATGAAGCTGGAATCGCTAGTATCGCGGATCAGCATGCCGCGGTGAATACGTTCCCGG GCCTTGTACACACCGCCCGTCACACCACGAGAGTTT GTAACACCC 19
  • 21.
  • 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. 23
  • 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. 24
  • 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 . 25
  • 26. References • Arciero, D.M. and Hooper, A.B. (1993) Hydroxylamine oxidoreductase from 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. • Bock, E., Koops, H.-P., Harms, H. and Ahlers, B. (1991). The biochemistry of nitrifying organisms in variations of Autotrophic Life Academic Press, London, pp. 171- 200. • D. N. Miller and R. L. Smith (2009). “Microbial characterization of nitrification in a shallow, nitrogen-contaminated 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 Scientific Publications, Oxford. 172 pp. 26
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