THE SPECIES COMPOSmON, ABUNDANCE AND THE DISTRIBUTION OF SEAGRASS COMMUNITIES IN PUTTALAM LAGOON

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Vidyodaya J. Sci., (1991) Vol. 3 No.2, pp. 93-102 THE SPECIES COMPOSmON, ABUNDANCE AND THE DISTRIBUTION OF SEAGRASS COMMUNITIES IN PUTTALAM LAGOON P. M. A. JAYASURIYA National Aquatic Resources Agency Crow Island Mattakuliya, Colombo IS Abstract The species composition, abundance and the distribution of different seagrass beds of Puttalam lagoon have been investigated. Eight species belonging to six genera were recorded during the investigation i.e., Enhalus acroida (I. F..)Royle Thalassia hemprichif (Ehrenb.) Aschers., HaIodule uninervis (Forsk.) Aschers in Bossiser, Syringodium isoetifolium (Aschers.) Dandy, Cymodocea rotundata Ehernb. et Hempr. ex Aschers., Cymodocea serrulata(r. Br.) Aschers, and Magnus, Halophila ovalis (R. Br.) Hook. F. and Halophila decipiens Ostenfeld. Two varieties of (narrow and wide) were also recorded during this investigation. The distribution pattern of the different species of seagrass beds showed a close association with different salinity values of the lagoon. It was found that the narrow variety of covered 75 % of the potential areas of the lagoon. It was also observed that, Cymodocea serrulata and play a major role as substrata lor many important epiphytic forms of macro and micro algae. It was also discussed thai traditionalfishing methods prevailing in this lagoon show til great threat to the 'survival of the seagrass communities.' Key words ; composition, abundance, distribution of seagrasses; Puttalam 1. Introduction The seagrass communities are the most conspicuous and widespread biotypes in the shallow marine environment. They form extensive animal spawning grounds and habitats; additionally grass blades can be lucrative substrates for plant and epiphytes as well as being a direct food source for gracing animals such as sea urchins, manatees, turtles and some fishes (Odum, 1974). Their elaborate rhizome and root systems trap and stabilize the sediments. Tlierefore seagrass beds are an important part of neritic and estuarine systems (Wood et al, 1969). There is very little information on seagrass communities of Sri Lanka, (Abeywickrema, 1986; De Silva & Ranathunga, 1987). Abeywickrema (Pers. comm.) and Samarakoon, 1988 has recorded 9 genera of seagrasses with 12 species in Sri Lanka. A recent study was done to map out the distribution 'of various species of seagrasses in Negombo lagoon by De Silva and Ranathunga (1987).

94 Seagrasses of Puttalam Lagoon Puttalam lagoon is one of the largest lagoons in Sri Lanka which covers an area of 237 km2 and provides large shallow areas which are favourable for the growth of searrass communities. No work has been done on types, distribution or ecology of seagrass beds of Puttalam lagoon except for Salm (1981) who has indicated the location of the seagrass beds in Kokkilai lagoon, Puttalam and Dutch Bay, Jaffna and Mannar districts as well as Negombo lagoon. Seagrass communities of Puttalam lagoon play a major role in various aspects such as providing food for one of the most endangered species of marine mammals (dugong) (Colin and Bertram, 1970; Jones, 1980) and providing breeding and nursery grounds for fish and shrimps, and act as one of the major substratum for the growth of Graci/aria edulis which is a commercially important seaweed species. They also serve as sheltered refuges and perhaps feeding areas for a number of juvenile pelagic fish in the lagoon. Therefore it is very useful to study the extents and the types of seagrass communities in this lagoon. The main objectives of this study are to find out the different seagrass species, abundance and their distribution pattern in this lagoon. 2. Materials and Methods This study was carried out in September to December in 1989. The total seagrass beds of the lagoon was covered by walking, snorkling and using a boat with a grab sampler in deeper areas. The seagrass communities were studied along transects (Tl, - TI4,) perpendiculer to the coast line. Transects were selected in such a way that as many different communities and habitats as possible could be investigated. The transects extended from the shore to the low water level and continued until only very similar communities were observed. Five to six one square meter quadrat samples were taken along each transect and the number of different seagrass species in each of them were counted. Extent and the distribution of the different communities were mapped and the abundance of dominant species were noted. 3. Results Eight species belonging to six genera were recorded from the Puttalam lagoon during the present survey. The species Cymodocca rotundata was recorded for the first time in Sri Lanka. Out of 9 genera of seagrasses recorded for Sri Lanka only six were found in the Puttalam lagoon Two variations of (narrow and wide leaves) were also found during this survey. Fig. 1 (a-i) shows the following varieties of seagrass species.

P. M. A. Jayasuriya 9S (ti) (c t (ft (II Fig I. (0- I) wogros. species 101104 In tile Punobm Lagoon. Fig. (a-i) seagrass species found in the Putta1arn Lagoon.

96 Seagrasses.of Puttalam Lagoon Fig. 2. Map of Puttalam lagoonshowing the location of the 14 Transects (T -1)

P. M. A. Jayusurlya 97 f 0) (b) C c) Enholus oerold ThaJass/o hemprlchll Holodule unlnerv(s Cd) fe) Syringodlum Isoetlfonum Cymodoc:eo rofundafa (g) (Il) HaIopfIIIo!!!!!! Fig. 3. (a)-(f) Distribution of eight seagrass species in the puttalam lgo.oan

.8 Seagrasses of Puttalam. Lagoon Table 1 Distribution of seagrasses found along the transects in the west coast of Puttalam lagoon. Station Area Seagrass species Transect T 1 Kalpitiya (north western region) Cymodocea serrulata Cymodocea rotundata Halophila ovalis Halophila deceplens Syringodium isoetlfolium T 2 T 3 T 4 TS T 6 Kuringipitiya (north western region) Palliwasalthurai (north western region) Kandakuda (north western region) Etalai (south western region) Noracholai (south western region) Halophila ovalis Syringodium isoetifolium Cymodocea serrulata Halophila ovalis Cymodocea serrulata Halophila ovalis Cymodocea serrulata Cymodocea serrulata Cymodocea rotundata Halophile ovalis Cymodocea rotundata T 7 Mampuri (souch western region) Halodule uninervis

P. M. A. Jayasuriya 99 Table II Distribution of seagrasses found along the transects in the east coast of Puttalam lagoon. Station Area Seagrass species Transect T8 Palavi (south eastern region) Halophila ova/is T9 Puttalam Halophila ovalis (south eastern region) T]O Seguwantive Halophila ovalis (north eastern region) Ha/odu/a uninervis Cymodocea rotundata TI] Ambalama Halophila ovalis (north eastern region) T]2 Moongil Aru Halophila ovalis (north eastern region) Thalassia hemprichit T13 Eluwankulama Halophila ovalis (north eastern region) Kara:3tve Comodocea serrulata T]4 (north eastern region) Halophila decepiens Table m Percentage abundance of ditr:lrennt sea grass species found in four different areas of the lagoon. Species EMa- Thalas- Ha/o- Halo- Syrinco- Cymodo- Cymodo- Halo- Halo- Ius sia dale dule dium cea cea phila phila acroi- hempri- uninervis uninervis isoetifo- rotun- serru- ova- deceou- Area des chii (narrow (wide /ium data lata lis ebs variety) variety} % % % % % % % % North 42 ]6 6 2 4 2 ]4 8 6 Western South 33 59 2 5 Western North 22 15 ]5 4 8 6 8 20 2 Eastern South 25 18 38 S 5 6 Eastem

too Seagrasses of Putta/am Lagoon 1. Enholus acroides 2. 3. (narrow variety) 4. (wide variety) 5. Siringodium isoetifolium 6. Cymodocea rotundata 7. Cymodocea serrulata 8. Halophila ovalis.. 9. Halophila decipiens. Fig. l-a Fig. I-b Fig. l-c Fig. i-a Fig. I-e Fig. I-f. Fig. I-g Fig. I-h Fig. I-I Fig. 2 shows the map of the lagoon and the location of 14 transects. Fig. 3 a-h show the distribution of different seagrass beds in the Puttalam lagoon. Table I and 1I give the different seagrass species along the transects in the western and eastern parts of the lagoon respectively. Table III gives the percentage abundance of different seagrass species found in four different areas of the lagoon. 4. Discussion: Out of the eight species of seagrasses found in the Puttalam lagoon Halophila ovalis,, and Cymodocea serrulata are the most common. The density of the other three spades Cymodocea rotundata, Halophila decipiens and Syringodium isoetifolium are fairly low compared to the others. The distribution pattern of these eight species (Fig. 1 a-h) is influenced by the nature of the habitat and physico chemical parameters of the lagoon. The salinity level of the water in the eastern part of the lagoon is fairly low (around 30-35 ppt) compared to the western part since several fresh water inlets fallon to the eastern side of the lagoon. The salinity level in the south western part of the lagoon is considerably high (45 to 50 ppt). The salt pans of the National Salt Corporation are also situated in this area. narrow-leaf variety seems to have a high range of salinity tolerance as it is found in the south western part and in the eastern part of the lagoon (Fig. lc). This species appears to be the most common seagrass in the survey areas. According to the topography survey that has been carried out by Perera and Siriwardana (1982), extensive areas of the Puttalam lagoon showed soft muddy bottoms. The Halodule species is mostly confined to these areas by its rhizome mat with an extensive network of horizontal axis. The wide-leaf variety of seems to be confined to the relatively deeper areas from 1 m to 1.5 m in depth.. The wide-leaf variety of Halodule uninervis is comparatively low in abundance. Both varieties of forms 60 % of the seagrass communities in the south western areas (Table III)..

P. M. A. Jayasuriya 101 Halophila ovalis is also widely spread in the survey areas except in the south western region. This has been observed at depths between 0.5 and 1.5 m. This species is found in areas of muddy substrates. However the density of this species is very low in all four regions of the lagoons and the percentage abundance did not exceed 20%. Halophila decipiens is also found in very low quantities and this species is confined only to the north western region of the lagoon. beds were always found in deeper areas such as I to 2 meters depth. The abundance of in the north western and north eastern areas were higher than those of the other species (Table III). It was also observed that the leaf blades of Enhalus provide substrata for a large number of micro and macro algae such as Lorencia sp., Hypnea sp. and Acanthophora species. By providing suitable substrata for these photosynthetic organisms, the total primary productivity of the seagrass habitat is substantially increased. These epiphytes form an essential part of the complex food webs that exists in a seagrass community. and serrulata are also found to be very common except inthe Seguwantive area and the south western area. The low abundance of these two species at Seguwantive area may be due to the low salinities prevailing in this area because of the fresh water inlets. Both species have been observed to grow from low water level to a depth of 1.5 meters with a salinity range of 35 to 45 ppt. These two species act as a major substratum for Gracilaria edulis which is a commercially important seaweed species.. Cymodocea rotundata is found in all parts of the lagoon but in low abundance (Fig. I g). This species is mostly found mixed with. It also grows in little deeper areas such as I to 2 meters of depth. Syringodium isoetifolium is found only in the nothern part of the lagoon (Fig. 3 d) and this may be due to its less tolerant character for different habitats. This species is also found in very low abundance compared to other species. 5. Conclusion Eight species belonging to six genera were recorded during this investigation. Cymodocea rotundata was recorded for the first time in Sri Lanka. The distribution pattern of the different species of sea grass beds showed a close association with different salinity values of the lagoon. Traditional fishing methods prevailing in this lagoon show a great threat to the survival of the sea grass communities. 6. Acknowledgements: I am thankful to Mr. Andrew Saternius and Mr. Wasantha Bandara for their assistance in collection of data.

102 Seagrasses of Puttalam Lagoon Rererences : 1. Abeywickrema, B.A. 1986. History of the mangroves and seagrass studies in Sri Lanka. Paper presented at the "workshop on the research needs for aquatic ecosystems of Sri Lanka (coral reefs, estuaries, seagrass beds, mangroves, lagoons and wetlands and associated aspects of nature and wild life conservation)." Abstracts of papers published by the National Aquatic Resources Agency (NARA TECH ABS (86-1), Colombo 2. Colin, and Bertram, K. 1970. The dugongs of Ceylon. Loris 12 (1): 53-55. 3. De Silva, M. W. R. N. and Ranathunga, R. A. S. 1987. Seagrass beds of the Negombo lagoon. Natural resources, Energy and science Authority of Sri Lanka, (NARESA/ EN/85/1). 4. Jones, S. 1980. The dugong or the so-called mermaid, Dugong dugong (Muller) of the Indo-Sri Lanka waters problem of research and conservation. Spolia Zeylanica. 3S (1&2): 223-260. 5. Odum, H. T. 1974. Tropical marine meadows. P. 442-487 in Odum, H. T., Copeland, B. J. and McMahan, E. A., eds. Coastal Ecological systems of the United States. Vo\. 1 Conservation Foundation, Washington, D.C. 6. Perera, W. K. T. and Siriwardana, P. P. G. S. N. 1982, Topography of Puttalam lagoon. J. Inland Fish. Vo\. 1. December 1982 pp. 97-104. 7. Salm, R. V. 1981. India and Pakistan: Description, Use and Management. In U.S. Fish and Wild Life service. 8. Wood E. J. F. Odum W. E. and Zieman, J.C. 1969. Influence of seagrasses on the productivity of coastal lagoons Contribution 1117, University of Miami, Resenstiel school of Marine and atmospheric sciences. Lagunas Coasteras, U. N. symposio. Mem- Intern. Lagunas Coasteras. UNAM-UNESCO. Nov. 28-30: 495-502