Temporal Changes in Environmental Characteristics and Diversity of Net Phytoplankton in a Freshwater Lake

Temporal changes in the species composition, seasonal abundance, and diversity of net phytoplankton (NPP) were investigated in relation to some environmental characteristics of the water and sediment of Lake Krishnasayer, an ancient man-made shallow freshwater lake, located at Burdwan, India, between January and December 2003. In all, 43 species and 7 genera were identified from the weekly samples taken from a 1 x 1 x 1-m water column at sites I and II. The most abundant taxa were Cyanophyta (34.8%-37.8%) and Bacillariophyta (34.2%-34.3%), whilst Euglenophyta was the least abundant (4%-5.3%). The relationships (r) were significant (P < 0.05) and positive between water temperature and abundance of Euglenophyta, Secchi transparency, and Chlorophyta and Bacillariophyta, dissolved oxygen and Chlorophyta, dissolved chloride, and Cyanophyta and Euglenophyta, phosphate-phosphorus and Cyanophyta, and organic carbon and Bacillariophyta. In contrast, the relationships (r) were significant (P < 0.05), but inverse between water temperature and abundance of Bacillariophyta, Secchi transparency and Euglenophyta, dissolved chloride and Bacillariophyta, nitrate-nitrogen and Euglenophyta, and organic carbon and Euglenophyta. Furthermore, regression coefficients (b) indicated a significant (P < 0.05) positive relationship between Secchi transparency and overall NPP abundance, and a significant (P < 0.05) inverse relationship between silica and overall NPP abundance. The diversity indicated high values with peaks in species abundance in March, May, and September at site I, and in May, September, and November at site II. The seasonal abundance and frequency of occurrence for a few dominant species of Cyanophyta (e.g., Anabaena circinalis, Nostoc carneum, Oscillatoria formosa, Rivularia haematitis, and Spirula subsalsa), Chlorophyta (e.g., Spirogyra communis, Ulothrix tenerrima, and Zygnema pectinum), Euglenophyta (e.g., Euglena viridis), and Bacillariophyta (e.g., Cyclotella glomerata, Navicula capitata, Nitzschia acicularis, and Pinnularia major) in the surface water of this lake were 3.3%-5.5%, respectively.

Temporal Changes in Environmental Characteristics and Diversity of Net Phytoplankton in a Freshwater Lake

Temporal changes in the species composition, seasonal abundance, and diversity of net phytoplankton (NPP) were investigated in relation to some environmental characteristics of the water and sediment of Lake Krishnasayer, an ancient man-made shallow freshwater lake, located at Burdwan, India, between January and December 2003. In all, 43 species and 7 genera were identified from the weekly samples taken from a 1 x 1 x 1-m water column at sites I and II. The most abundant taxa were Cyanophyta (34.8%-37.8%) and Bacillariophyta (34.2%-34.3%), whilst Euglenophyta was the least abundant (4%-5.3%). The relationships (r) were significant (P < 0.05) and positive between water temperature and abundance of Euglenophyta, Secchi transparency, and Chlorophyta and Bacillariophyta, dissolved oxygen and Chlorophyta, dissolved chloride, and Cyanophyta and Euglenophyta, phosphate-phosphorus and Cyanophyta, and organic carbon and Bacillariophyta. In contrast, the relationships (r) were significant (P < 0.05), but inverse between water temperature and abundance of Bacillariophyta, Secchi transparency and Euglenophyta, dissolved chloride and Bacillariophyta, nitrate-nitrogen and Euglenophyta, and organic carbon and Euglenophyta. Furthermore, regression coefficients (b) indicated a significant (P < 0.05) positive relationship between Secchi transparency and overall NPP abundance, and a significant (P < 0.05) inverse relationship between silica and overall NPP abundance. The diversity indicated high values with peaks in species abundance in March, May, and September at site I, and in May, September, and November at site II. The seasonal abundance and frequency of occurrence for a few dominant species of Cyanophyta (e.g., Anabaena circinalis, Nostoc carneum, Oscillatoria formosa, Rivularia haematitis, and Spirula subsalsa), Chlorophyta (e.g., Spirogyra communis, Ulothrix tenerrima, and Zygnema pectinum), Euglenophyta (e.g., Euglena viridis), and Bacillariophyta (e.g., Cyclotella glomerata, Navicula capitata, Nitzschia acicularis, and Pinnularia major) in the surface water of this lake were 3.3%-5.5%, respectively.

___

  • Amarsinghe PB & Vijverberg J (2002). Primary production in a tropical reservoir in Sri Lanka. Hydrobiologia 487: 85-93.
  • Bailey-Watts AE (1982). The composition and abundance of phytoplankton in Loch Leven (Scotland) 1977-1979 and a comparison with the succession in earlier years. Int Rev Ges Hydrobiol Hydrogr 67: 1-25.
  • Calijuri MC, Dos Santos ACA & Jati S (2002). Temporal changes in the phytoplankton community structure in a tropical and eutrophic reservoir (Barra Bonita, S.P. – Brazil). Journal of Plankton Research 24: 617-634.
  • Carmichael W (1981). The water environment. Algal Toxins and Health. New York: Plenum Press, pp. 225.
  • Çetin AK (2000). Phytoplankton of Gölbaflı Lake (Adıyaman, Turkey) and their seasonal variations. International Journal on Algae 2: 87-96.
  • Chattopadhyay B (1997). “Barddhamaner Agragatite Raj Paribarer Bhumika” (The role of the King in the progress of Barddhaman). Paschim Banga (West Bengal), Burdwan Dist. No. 1403. Calcutta, Dept. of Information and Culture, Govt. of West Bengal, 175- 179.
  • Chhatwal GR, Mehera MC, Satake M, Katyal T, Latyal M & Nagahiro T (1996). Environmental Analysis (Air, Water and Soil). New Delhi: Anmol Publications Pvt. Ltd., pp. 204.
  • Clesceri LS, Greeenberg AE & Eaton AD (eds.) (1998). Standard Methods for the Examination of Water and Wastewater. 20thed. Washington D.C., American Public Health Assoc., American Water Works Assoc., & Water Environment Fed., 2:1-90, 4:52- 160,10:1-28 pp.
  • Cox FJ (1996). Identification of Freshwater Diatoms from Live Material. London: Chapman & Hall.
  • Das SM & Upadhya JC (1979). Studies on qualitative and quantitative fluctuations of plankton in two lakes Nainital & Bhimtal, India. Acta Hydrobiol 21: 9-17.
  • George MG (1966). Comparative plankton ecology of five fresh tanks in Delhi. Hydrobiologia 27: 81-108.
  • George MG (1969). Seasonal trends in physico-chemical factors and plankton of freshwater pond and their role in fish culture. Hydrobiologia 33: 145-160.
  • Gibson CE, Wu Y & Pinkerton D (1995). Substance budgets of an upland catchment: the significance of atmospheric phosphorus inputs. Freshwat Biol 33: 385-392.
  • Harper DM, Adams C & Mavuti K (1995). The aquatic plant communities of the lake Naivasha Wetland, Kenya: pattern, dynamics and conservation. Wetlands Ecol Manage 3: 111-123.
  • Hegde GR (1990). Limnological studies on two fish tanks of Dharwad, Karnataka. Recent Trends in Limnology 1-4: 263-269.
  • Hirose M, Nishibe Y, Ueki M & Nakano S (2003). Seasonal changes in the abundance of autotrophic picoplankton and some environmental factors in hypereutrophic Furuike pond. Aquatic Ecology 37: 37-43.
  • Hubble DS & Harper DM (2002). Nutrient control of phytoplankton production in Lake Naivasha, Kenya. Hydrobiologia 488: 99-105.
  • Khan AA & Siddiqui AQ (1977). Seasonal changes in limnology of perennial fish pond at Aligarh. Indian J Fish 21: 463-478.
  • Krammer K & Lange-Bertalot H (1991). Bacillariophyceae. Süsswasser- flora von Mitteleuropas, Band 2/3, 3. Teil: centraes, Fragilariaceae, Eunotiaceae, P.1-576. Stuttgart: Gustav Fischer Verlag.
  • Maeda H, Kawai A & Tilzer M (1992). The water bloom of cyanobacterial picoplankton in Lake Biwa, Japan. Hydrobiologia 248: 93-103.
  • Melack JM (1979). Temporal variability of phytoplankton in tropical lakes. Oeocologia 44: 1-7.
  • Parker BC & Hatcher RF (1974). Enrichment of surface freshwater microlayer with algae. J Phycol 10: 185.
  • Pentecost A (1998). Phosphorus fractionation in the sediments of Malham Tarn, North Yorkshire. Field Studies 9: 337-342.
  • Rawson DS (1956). Algae indicators of tropical lake type. Limnol Oceanogr 1: 18-31.
  • Scheffer M (1998). Ecology of Shallow Lakes. London: Chapman & Hall, pp. 357.
  • Simpson EH (1949). Measurement of diversity. Nature 163: 688.
  • Singh S (1990). High altitude limnology and its scope in India. Recent Trends in Limnology 1-4: 113-127.
  • Solorzano L & Sharp JH (1980). Determination of total dissolved nitrogen in natural-waters. Limnol Oceanogr 25: 751-754.
  • Squires MM & Lesack LFW (2002). Water transparency and nutrients as controls on phytoplankton along a flood-frequency gradient among lakes of the Mackenzie Delta, Western Canadian Arctic. Can J Fish Aquat Sci 59: 1339-1349.
  • Sreenivasan A (1974). Limnological features of a tropical impoundment, Bhavanisagar Reservoir, India. Int Rev Ges Hydrobiol 53: 327- 342.
  • Stockner JG & Shortreed KS (1988). Response of Anabaena and synechococcus to manipulation of nitrogen: phosphorus ratio in a lake fertilization experiment. Limnol Oceanogr 33: 1348-1361.
  • Talling JF (1993). Comparative seasonal changes, and inter-annual variability and stability, in a 26-year record to total phytoplankton biomass in four English lake basins. Hydrobiologia 268: 65-98.
  • Talling JF & Parker JE (2002). Seasonal dynamics of phytoplankton and phytobenthos, and associated chemical interactions, in a shallow upland lake (Malham Tarn, Northern England). Hydrobiologia 487: 167-181.
  • Watson SB, McCauley E & Downing JA (1997). Patterns in phytoplankton taxonomic composition across temperate lakes of differing nutrient status. Limnol Oceanogr 42: 487-495.
  • Wehr JD & Sheath RG (2003). Freshwater Algae of North America. San Diego, CA: Academic Press.
  • Wetzel RG & Likens GE (1991). Limnological Analyses (2nded.). New York: Springer-Verlag, pp. 391.
  • Zar JH (1996). Biostatistical Analysis (3rded.). New Jersey: Prentice Hall, pp. 918.
Turkish Journal of Botany-Cover
  • ISSN: 1300-008X
  • Yayın Aralığı: Yılda 6 Sayı
  • Yayıncı: TÜBİTAK