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COMMUNITY STRUCTURE OF PHYTOPLANKTON IN
SAMPALOC LAKE,
SAN PABLO CITY, LAGUNA
HAIZEL ANNE T. DE ASIS AND JAHZEEL ZUBIAGA
DEPARTMENT OF BIOLOGY
POLYTECHNIC UNIVERSITY OF THE PHILIPPINES
Phytoplankton
roup of minute autotrophic
organism
loats in the water surface of
rivers and lake
rowth of Phytoplankton is affected by
Eutrophication
Allow algae bloom on the surface
Low dissolved oxygen in bottom waters
death of oxygen-dependent organism
Fish and invertebrate mortality
(Round, 1981)
Phytoplankton
ampaloc Lake:
utrophic Area
‱ Commercialization
‱ human effluents
‱ illegal fish pens
‱ crowded fish cages
SAMPALOC LAKE
educing Fish cages
 characterization of the phytoplankton
community be done in Sampaloc Lake
determine the trophic status of the lake’s
water by identifying indicator species
present in the study site.
STATEMENT OF THE PROBLEM
e determined the structural diversity of the
phytoplankton in Sampaloc Lake Laguna
correlate the diversity of phytoplankton with existing
environmental factors
identified and classified the phytoplankton present
compare the phytoplankton diversity in each designated
OBJECTIVES OF THE STUDY
Station
Physico – chemical
Parameters
Biological Parameters
Horizontal Hauling-Littoral Zone
Vertical Hauling-Limnetic ZonepH
Tur
b
T° DO
Correlation Analysis
Preservation
Concentration
Identification Counting
Diversity Indices
(Dominance, Abundance, Shannon,
Simpson , Evenness and Richness)
Methodology
Temperature and pH
Dissolved Oxygen
Transparency
Vertical Hauling
Horizontal Hauling
Station
Physico – chemical
Parameters
Biological Parameters
Horizontal Hauling-Littoral Zone
Vertical Hauling-Limnetic ZonepH
Tur
b
T° DO
Correlation Analysis
Preservation
Concentration
Identification Counting
Diversity Indices
(Dominance, Abundance, Shannon,
Simpson , Evenness and Richness)
Methodology
Plankton Net
Haemocytometer
Station
Physico – chemical
Parameters
Biological Parameters
Horizontal Hauling-Littoral Zone
Vertical Hauling-Limnetic ZonepH
Tur
b
T° DO
Correlation Analysis
Preservation
Concentration
Identification Counting
Diversity Indices
(Dominance, Abundance, Shannon,
Simpson, Evenness and Richness)
Methodology
ESULTS
ND
values are reported as mean ± Standard Error (s/√n)
*values with the same letters are not significantly different at α= 0.05
 
Table 1. Physico-chemical Parameters of Sampaloc Lake (November 2010).
Parameters Station Average
1 2 3 4 5
Temperature (0
C) 28.23±0.04 a
27.82±0.03a
27.61±0.02a
25.86±1.11a
27.14±0.02a
27.33±0.24
pH 8.35±0.05abc
8.32±0.05abc
8.36±0.03ac
8.43±0.05b
8.27±0.09c
8.35±0.05
Transparency(in.) 28.50±1.32ab
38.58±5.30a
34.72±7.50a
30.02±7.59a
20.08±0.19b
30.38±0.57
DO(mg/L) 8.75±0.05a
9.06±0.02ab
9.32±0.02ab
10.22±.08b
9.29±0.05a
9.33±0.04
DIVISION CHLOROPHYTA
Spirogyra sp.
Stigeoclonium sp.
Staurastrum sp. Green Algae 1
Pediastrum sp. Protoccoccus sp.
DIVISION BACILLARIOPHYTA
Amphora sp. Berkeleya sp. Cyclotella sp. Coscinodiscus sp. Thallossiosira sp.
Pinnularia sp.Odontella sp.Nitzchia sp.Navicula sp.Melosira sp.Mastoglia sp.
DIVISION CYANOPHYTA
COMPOSITION OF PHYTOPLANKTON
COMMUNITY
he algal composition of Sampaloc Lake was represented by three major groups
namely:
‱ Bacillariophyta (diatom)
‱ Chlorophyta (green-algae) and
‱ Cyanophyta (blue-green algae)
which comprises twenty (20) taxa. The genera were distributed into 6
genera of green algae, 11 genera of diatoms and 3 genera of blue-green algae.
Taxa Abundance Mean RA(%)
Rf (%)1 2 3 4 5
Chlorophyta
1. Pediastrum sp. 76 0 0 0 116 131.20 0.180126253 40
2. Protoccocus sp. 0 0 0 139 0 139.00 0.190834979 20
3. Spirogyra sp. 182 8 0 0 0 44.40 0.06095736 40
4. Stigeoclonium sp.
5. Staurastrum sp.
6. Green algae 1
0
0
8
369
0
0
0
58
0
0
0
0
0
0
0
369.00
58.00
1.60
0.506605087
0.079628984
0.002196662
20
20
20
Bacillariophyta
7. Amphora sp. 0 0 0 0 152 152.00 0.208682854 20
8. Berkeleya sp. 0 0 0 0 3 3.00 0.004118741 20
9. Cosinodiscus sp. 3 0 1768 0 0 1768.60 2.428134842 40
10. Cyclotella sp. 245 240 104 328 53 774.00 1.06263506 100
11. Mastoglia sp. 0 0 0 0 18 18.00 0.024712443 20
12. Melosira sp. 2326 1374 859 902 12104 15704.20 21.56050842 100
13. Navicula sp. 48 0 33 5 0 47.60 0.065350683 60
14. Pinnularia sp. 3 0 0 0 0 0.60 0.000823748 20
15. Odontela sp. 0 0 0 0 1152 1152.00 1.581596369 20
16. Nitzcha sp. 35 10 13 0 73 103.00 0.141410092 80
17. Thalossiosira sp. 0 96 0 0 0 96.00 0.131799697 20
Cyanophyta
18. Lyngbya sp. 0 0 0 0 1323 1323.00 1.81636458 20
19. Oscillatoria sp. 533 78 0 0 0 184.60 0.253439835 40
20. Merismopedia sp. 0 116 46510 0 4242 50868.00 69.83736467 60
72937.8
 
Table 2. Community comparison of phytoplankton in different station.
Melosira sp.
Cyclotella sp.
Figure.3 Distribution of the major phytoplankton taxa in
Sampaloc Lake (November 2010).
 
(S) (d) (H’) (1-D) (E) (D)  
 
 
1 10 0.048 a
1.113 a
0.516 a
0.305 a
1.104 a
 
2 8 0.398 a
1.302 a
0.601 a
0.409 a
1.033 a
 
3 7 0.890 a
0.274 a
0.110 a
0.188 a
0.555 a
 
4 4 0.498 a
0.871 a
0.502 a
0.597 a
0.415 a
 
5 9 0.453 a
1.092 a
0.547 a
0.298 a
0.912 a
 
 
Average 20 0.534 0.973 0.446 0.132 1.680
Station Diversity Indices
*values are reported as mean ± Standard Error (s/√n)
*values with the same letters are not significantly different at α= 0.05
Table 3. Community Characteristics of Phytoplankton in Sampaloc Lake (November, 2011)
Characterization of Phytoplankton Community
SUMMARY, CONCLUSION AND
RECOMMENDATION
Based on the results the following conclusions were figure out:
‱the phytoplankton community in Sampaloc Lake was distributed
to 3 major groups namely Division Chlorophyta, Bacillariophyta
and Cyanophyta ;
‱a total of 20 taxa were present in Sampaloc Lake and
dominated by Melosira sp. and
‱Sampaloc Lake is exhibiting eutrophic condition based on the
presence of bioindicator groups.
Upon completion of the study, the following are
recommended:
‱the trophic state of Sampaloc Lake be verified
using other chemical analyses ;
‱continuous monitoring of the lake be done to
improve the trophic condition of the lake and
‱use SEM (scanning electron microscope) in
identification of the phytoplankton at species level.

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Phytoplankton

  • 1. COMMUNITY STRUCTURE OF PHYTOPLANKTON IN SAMPALOC LAKE, SAN PABLO CITY, LAGUNA HAIZEL ANNE T. DE ASIS AND JAHZEEL ZUBIAGA DEPARTMENT OF BIOLOGY POLYTECHNIC UNIVERSITY OF THE PHILIPPINES
  • 2. Phytoplankton roup of minute autotrophic organism loats in the water surface of rivers and lake
  • 3. rowth of Phytoplankton is affected by Eutrophication Allow algae bloom on the surface Low dissolved oxygen in bottom waters death of oxygen-dependent organism Fish and invertebrate mortality (Round, 1981) Phytoplankton
  • 4. ampaloc Lake: utrophic Area ‱ Commercialization ‱ human effluents ‱ illegal fish pens ‱ crowded fish cages SAMPALOC LAKE
  • 5. educing Fish cages  characterization of the phytoplankton community be done in Sampaloc Lake determine the trophic status of the lake’s water by identifying indicator species present in the study site. STATEMENT OF THE PROBLEM
  • 6. e determined the structural diversity of the phytoplankton in Sampaloc Lake Laguna correlate the diversity of phytoplankton with existing environmental factors identified and classified the phytoplankton present compare the phytoplankton diversity in each designated OBJECTIVES OF THE STUDY
  • 7. Station Physico – chemical Parameters Biological Parameters Horizontal Hauling-Littoral Zone Vertical Hauling-Limnetic ZonepH Tur b T° DO Correlation Analysis Preservation Concentration Identification Counting Diversity Indices (Dominance, Abundance, Shannon, Simpson , Evenness and Richness) Methodology
  • 8. Temperature and pH Dissolved Oxygen Transparency
  • 10. Station Physico – chemical Parameters Biological Parameters Horizontal Hauling-Littoral Zone Vertical Hauling-Limnetic ZonepH Tur b T° DO Correlation Analysis Preservation Concentration Identification Counting Diversity Indices (Dominance, Abundance, Shannon, Simpson , Evenness and Richness) Methodology
  • 12. Station Physico – chemical Parameters Biological Parameters Horizontal Hauling-Littoral Zone Vertical Hauling-Limnetic ZonepH Tur b T° DO Correlation Analysis Preservation Concentration Identification Counting Diversity Indices (Dominance, Abundance, Shannon, Simpson, Evenness and Richness) Methodology
  • 14. values are reported as mean ± Standard Error (s/√n) *values with the same letters are not significantly different at α= 0.05   Table 1. Physico-chemical Parameters of Sampaloc Lake (November 2010). Parameters Station Average 1 2 3 4 5 Temperature (0 C) 28.23±0.04 a 27.82±0.03a 27.61±0.02a 25.86±1.11a 27.14±0.02a 27.33±0.24 pH 8.35±0.05abc 8.32±0.05abc 8.36±0.03ac 8.43±0.05b 8.27±0.09c 8.35±0.05 Transparency(in.) 28.50±1.32ab 38.58±5.30a 34.72±7.50a 30.02±7.59a 20.08±0.19b 30.38±0.57 DO(mg/L) 8.75±0.05a 9.06±0.02ab 9.32±0.02ab 10.22±.08b 9.29±0.05a 9.33±0.04
  • 15. DIVISION CHLOROPHYTA Spirogyra sp. Stigeoclonium sp. Staurastrum sp. Green Algae 1 Pediastrum sp. Protoccoccus sp.
  • 16. DIVISION BACILLARIOPHYTA Amphora sp. Berkeleya sp. Cyclotella sp. Coscinodiscus sp. Thallossiosira sp. Pinnularia sp.Odontella sp.Nitzchia sp.Navicula sp.Melosira sp.Mastoglia sp.
  • 18. COMPOSITION OF PHYTOPLANKTON COMMUNITY he algal composition of Sampaloc Lake was represented by three major groups namely: ‱ Bacillariophyta (diatom) ‱ Chlorophyta (green-algae) and ‱ Cyanophyta (blue-green algae) which comprises twenty (20) taxa. The genera were distributed into 6 genera of green algae, 11 genera of diatoms and 3 genera of blue-green algae.
  • 19. Taxa Abundance Mean RA(%) Rf (%)1 2 3 4 5 Chlorophyta 1. Pediastrum sp. 76 0 0 0 116 131.20 0.180126253 40 2. Protoccocus sp. 0 0 0 139 0 139.00 0.190834979 20 3. Spirogyra sp. 182 8 0 0 0 44.40 0.06095736 40 4. Stigeoclonium sp. 5. Staurastrum sp. 6. Green algae 1 0 0 8 369 0 0 0 58 0 0 0 0 0 0 0 369.00 58.00 1.60 0.506605087 0.079628984 0.002196662 20 20 20 Bacillariophyta 7. Amphora sp. 0 0 0 0 152 152.00 0.208682854 20 8. Berkeleya sp. 0 0 0 0 3 3.00 0.004118741 20 9. Cosinodiscus sp. 3 0 1768 0 0 1768.60 2.428134842 40 10. Cyclotella sp. 245 240 104 328 53 774.00 1.06263506 100 11. Mastoglia sp. 0 0 0 0 18 18.00 0.024712443 20 12. Melosira sp. 2326 1374 859 902 12104 15704.20 21.56050842 100 13. Navicula sp. 48 0 33 5 0 47.60 0.065350683 60 14. Pinnularia sp. 3 0 0 0 0 0.60 0.000823748 20 15. Odontela sp. 0 0 0 0 1152 1152.00 1.581596369 20 16. Nitzcha sp. 35 10 13 0 73 103.00 0.141410092 80 17. Thalossiosira sp. 0 96 0 0 0 96.00 0.131799697 20 Cyanophyta 18. Lyngbya sp. 0 0 0 0 1323 1323.00 1.81636458 20 19. Oscillatoria sp. 533 78 0 0 0 184.60 0.253439835 40 20. Merismopedia sp. 0 116 46510 0 4242 50868.00 69.83736467 60 72937.8   Table 2. Community comparison of phytoplankton in different station.
  • 21. Figure.3 Distribution of the major phytoplankton taxa in Sampaloc Lake (November 2010).
  • 22.   (S) (d) (H’) (1-D) (E) (D)       1 10 0.048 a 1.113 a 0.516 a 0.305 a 1.104 a   2 8 0.398 a 1.302 a 0.601 a 0.409 a 1.033 a   3 7 0.890 a 0.274 a 0.110 a 0.188 a 0.555 a   4 4 0.498 a 0.871 a 0.502 a 0.597 a 0.415 a   5 9 0.453 a 1.092 a 0.547 a 0.298 a 0.912 a     Average 20 0.534 0.973 0.446 0.132 1.680 Station Diversity Indices *values are reported as mean ± Standard Error (s/√n) *values with the same letters are not significantly different at α= 0.05 Table 3. Community Characteristics of Phytoplankton in Sampaloc Lake (November, 2011) Characterization of Phytoplankton Community
  • 23. SUMMARY, CONCLUSION AND RECOMMENDATION Based on the results the following conclusions were figure out: ‱the phytoplankton community in Sampaloc Lake was distributed to 3 major groups namely Division Chlorophyta, Bacillariophyta and Cyanophyta ; ‱a total of 20 taxa were present in Sampaloc Lake and dominated by Melosira sp. and ‱Sampaloc Lake is exhibiting eutrophic condition based on the presence of bioindicator groups.
  • 24. Upon completion of the study, the following are recommended: ‱the trophic state of Sampaloc Lake be verified using other chemical analyses ; ‱continuous monitoring of the lake be done to improve the trophic condition of the lake and ‱use SEM (scanning electron microscope) in identification of the phytoplankton at species level.

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  1. Hanap nun cambridge microscope