Marine

Marine ecosystems that form the marine environment are the largest habitats on Earth for a diversified group of organisms. The biotic community of marine envi­ronments is dominated by microalgae. They are among the largest primary pro­ducers of biomass in the marine environment and are common inhabitants of the tidal and intertidal areas of the marine ecosystem. These algae exhibit a character­istic geographical distribution pattern under the influence of several environmen­tal factors (Vijayaraghavan and Kaur, 1997). Nevertheless, the coastal ecosystem in the marine environment is very complex where all organisms exist in mutual dependency. Although considerable attention has been paid to distribution, abun­dance, growth, culture, biochemical constituents, by-products, and bioactivity of marine algae in different parts of the world (Faulkner, 1984), information is avail­able on the microbes, planktonic and faunal associates of marine algae, and the impact of various environmental factors on their distribution. The algal biotope with its morphological diversity is considered important in providing food, living space, and refuge, and offers a variety of potential habitats for the faunal spe­cies, including planktonic forms. A detailed investigation is therefore necessary to understand the actual nature of the association between algae and other forms to appreciate the potential importance of this interaction in the marine ecosystem. Steele (1988) described the “heuristic projection,” which illustrates the scales of importance in monitoring pelagic components of the ecological unit. The large marine ecosystem (LME) approach defines a spatial domain based on ecological principles and, thereby, provides a basis for focused temporal and spatial scientific research and monitoring efforts in support of management aimed at the long-term productivity and sustainability of marine habitats and resources. The plankton of LMEs can be studied by deploying Continuous Plankton Recorder (CPR) sys­tems (Glover, 1967) through commercial vessels. Advanced plankton recorders can be installed with sensors for intense recording of temperature, salinity, chlo­rophyll, nitrate/nitrite, petroleum hydrocarbons, light, bioluminescence, and pri­mary productivity (UNESCO, 1992; Williams, 1993), which will help monitor the changes in phytoplankton composition, dominance, and long-standing changes in the physical and nutrient characteristics of the LME. In addition, longer-term changes in relation to the biofeedback of the plankton community toward adverse climate may also be clearly understood (Hayes et al., 1993; Jossi and Goulet, 1993; Williams, 1993).

The phytoplankton community includes 5,000 marine species of unicellular algae and has a broad diversity of cell size (mostly in the range of 1 to 100 pm), morphology, physiology, and biochemical composition (Margalef, 1978). All phy­toplankton species are capable of photosynthesis, and many have the capacity for rapid cell division and population growth—up to four doublings per day. The popu­lation dynamics of the phytoplankton can be interpreted as responses to changes in the individual processes that regulate the biomass (total quantity, in measures such as carbon, nitrogen, or chlorophyll concentration), species composition, and spatial distribution of the phytoplankton population. Phytoplankton have a wide distribution in all habitats of the marine environment and play a major role in the food chain of an aquatic ecosystem. Some of the phytoplankton species also act as bio-indicators, reflecting changes in the environment. Different hydrobiological parameters, such as pH, temperature, salinity, alkalinity, nutrient concentration, solar radiation, etc., determine species composition, diversity, succession, and abundance of phytoplank­ton (Perumal et al., 1999; Redekar and Wagh, 2000a, b). Remarkable changes in the irradiance toward phytoplankton could occur due to changing seasonal, diurnal cycles and weather conditions. Diatoms are the significant and often dominant con­stituent of benthic microalgal communities in estuarine and shallow coastal regions (Sullivan, 1999).

The taxonomy of the most common species with reliable distributional informa­tion and records will allow for the design of ecological role models incorporating the effects of climatic parameters, which would be very useful in predicting shifts in distribution due to climatic changes.

REFERENCES

Baker, G. C., Beebee, T. J.C., and Ragan, M. A. (1999). Prototheca richardsi, a pathogen of anuran larvae, is related to a clade of protistan parasites near the animal-fungal diver­gence. Microbiology, 145: 1777-1784.

Baker, G. C., Gaffar, S., Cowan, D. A., and Suharto, A. R. (2001). Bacterial community analysis of Indonesian hot springs. FEMS Microbiology Letters, 200: 103-109.

Cardozo, K. H., Guaratini, T., Barros, M. P., et al. (2007). Metabolites from algae with economical impact. Comparative Biochemistry and Physiology — Part C: Toxicology & Pharmacology, 146: 60-78.

Faulker, D. J. (1984). Marine natural products: Metabolites of marine algae and herbivorous marine mollusks. Natural Products Report, 1: 251-280.

Fontaneto, D., Herniou, E. A., Boschetti, C., Caprioll, M., Melone, G., Ricci, C., and Barraclough, T. G. (2007). Independently evolving species in asexual bdelloid rotifers. PLoS Biology, 5: 914-921.

Glover, R. S. (1967). The Continuous Plankton Recorder Survey of the North Atlantic. Symposia of the Zoological Society of London, 19: 189-210.

Guschina, I. A., and Harwood, J. L. (2006). Lipids and lipid metabolism in eukaryotic alga. Progress in Lipid Research, 45: 160-186.

Harvey, J. B.J., and Goff, L. J.A. (2006). A reassessment of species boundaries in Cystoseira and Halidrys (Phaeophyceae, Fucales) along the North American west coast. Journal of Phycology, 42: 707-720.

Hayes, G. C., Carr, M. R., and Taylor, A. H. (1993). The relationship between Gulf Stream position and copepod abundance derived from the Continuous Plankton Recorder survey: Separating the biological signal from sampling noise. Journal of Plankton Research, 15: 1359-1373.

Jossi, J. W., and Goulet, J. R. (1993). Zooplankton trends: U. S. north-east shelf ecosystem and adjacent regions differ from north-east Atlantic and North Sea, ICES. Journal of Marine Science, 50: 303-313.

Khan, S. A., Rashmi, M. Z., Hussain, Prasad, S., and Banerje, U. C. (2009). Prospects of bio­diesel production from microalgae in India. Renewable and Sustainable Energy Reviews, 13(9): 2361-2372.

Lilly, E. L., Halanych, K. M., and Anderson, D. M. (2007). Species boundaries and global bioge­ography of the Alexandrium tamarense complex (Dinophyceae). Journal of Phycology, 43: 1329-1338.

Margalef, R. (1978). Life forms of phytoplankton as survival alternatives in an unstable envi­ronment. Oceanologica Acta, 1: 493-509.

Mclnnery, J. O., Wilkinson, M., Patching, J. W., Embley, T. M., and Powell, R. (1995). Recovery and phylogenetic analysis of novel archaeal rRNA sequences from deep sea deposit feeder. Applied and Environmental Microbiology, 61: 1646-1648.

Monaghan, M. T., Balke, M., Gregory, T. R., and Vogler, A. P. (2005). DNA-based species delineation in tropical beetles using mitochondrial and nuclear markers. Philosophical Transactions of the Royal Society B Biological Sciences, 360: 1925-1933.

Olmos, J., Paniagua, J., and Contreras, R. (2000). Molecular identification of Dunaliella sp. utilizing the 18S rDNA gene. Letters Applied Microbiology, 30: 80-84.

Olsen, G. J., Lane, D. J., Ginovannani, S. J., Peace, N. R., and Stahl, D. A. (1986). Microbial ecology and evolution: A ribosomal RNA approach. Annual Review of Microbiology, 40: 337-365.

Perumal, P., Sampathkumar, P., and Karuppasamy, P. K. (1999). Studies on bloom farming species of phytoplankton in the Velar Estuary, south east coast of India. Indian Journal of Marine Science, 28: 400-401.

Pons, J., Barraclough, T. G., Gomez-Zurita, J., et al. (2006). Sequence-based species delimita­tion for the DNA taxonomy of undescribed insects. Systematic Biology, 55: 595-609.

Rajkumar, R. (2010). Environment Impact Assessment of Mass Cultivation of Kappaphycus alvarezii (Doty) Doty ex Silva along the Coast of Palk Bay, Tamil Nadu and the Potential of Bacillus megaterium RRM2 Isolated from the Alga for its Proteolytic Activity. Ph. D. dissertation, University of Madras, India.

Redekar, P. D., and Wagh, A. B. (2000a). Growth of fouling diatoms from the Zuari Estuary, Goa (west coast of India) under different salinities in the laboratory. Seaweed Research and Utilisation, 22(1&2): 121-124.

Redekar, P. D., and Wagh, A. B. (2000b). Relationship of fouling diatoms number and chlorophyll value from Zuari Estuary, Goa (west coast of India). Seaweed Research and Utilisation, 22(1&2): 173-181.

Steele, J. H. (1988). Scale selection for biodynamic theories. In Rothschild, B. J. (Ed.), Toward a Theory on Biological-Physical Interactions in the World Ocean, NATO AS1 Series C: Mathematical and Physical Sciences, Vol. 239, pp. 513-526. Dordrecht: Kluwer Academic Publishers.

Sullivan, M. J. (1999). Applied diatom studies in estuaries and shallow coastal environments. In The Diatoms: Application for the Environmental and Earth Sciences. E. F. Stoermer and J. P. Smol (Eds.), London: Cambridge University Press, pp. 334-351.

Templeton, A. R., Crandall, K. A., and Sing, C. F. (1992). A cladistic analysis of phenotypic associations with haplotypes inferred from restriction endonuclease mapping and sequencing data. III. Cladogram estimation. Genetics, 132: 619-633.

UNESCO (United Nations Educational, Scientific and Cultural Organization). (1992). Monitoring the Health of the Oceans: Defining the Role of the Continuous Plankton Recorder in Global Ecosystems Studies. The Intergovernmental Oceanographic Commission and The Sir Alister Hardy Foundation for Ocean Science. IOC/INF-869, SC — 92MS-8.

Van Waasbergen, L. G., Balkwill, D. I., Crockers, F. H., Bjornstad, B. N., and Miller, R. V. (2000). Genetic diversity among Arthrobacter species collected across a heteroge­neous series of terrestrial deep-subsurface sediments as determined on the basis of 16S rRNA and re cA ngene sequence. Applied and Environmental Microbiology, 66: 3454-3463.

Vanormelingen, P., Hegewald, E., Braband, A., Kitschke, M., Friedl, T., Sabbe, K., and Vyverman, W. (2007). The systematics of a small spineless Desmodesmus taxon, D. costatogranulatus (Sphaeropleales, Chlorophyceae), based on ITS2 rDNA sequence analyses and cell wall morphology. Journal of Phycology, 43: 378-396.

Vijayaraghavan, M. R., and Kaur. (1997). Brown Algae Structure, Ultra Structure and Reproduction. New Delhi, India: APH Publishing Corporation.

Wiens, J. J. (2007). Species delimitation: new approaches for discovering diversity. Systematic Biology, 56: 875-878.

Wiens, J. J., and Penkrot, T. A. (2002). Delimiting species using DNA and morphological varia­tion and discordant species limits in spiny lizards (Sceloporus). Systematic Biology, 51: 69-91.

Williams, R. (1993). Evaluation of new techniques for monitoring and assessing the health of large marine ecosystems. In Rapport, D. (Ed.), NATO Advanced Research Workshop Evaluating and Monitoring the Health of Large-Scale Ecosystems. Berlin: Springer-Verlag.

Zhang, A. B., Sikes, D. S., Muster, C., and Li, S. Q. (2008). Inferring species membership using DNA sequences with back-propagation neural networks. Systematic Biology, 57: 202-215.