FINFISH SEED RESOURCES OF ADYAR ESTUARY AND KOVALAM BACKWATER AROUND MADRAS, INDIA * Central Marine Fisheries Research Institute, Cochin-6%1 03 ]

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J. mar. biol. Ass. India, 1991, 33 (1 & 2) : 59-68 FINFISH SEED RESOURCES OF ADYAR ESTUARY AND KOVALAM BACKWATER AROUND MADRAS, INDIA * P. NAMMALWAR, G. MOHANRAJ**, S. KANDASAMY AND A. C. SEKHAR Central Marine Fisheries Research Institute, Cochin-6%1 03 ] ABSTRACT A survey of the seasonal and specieswise distribution and abundance of finfish seed resources of Adyar Estuary and Kovalam Backwater around Madras was carried out from January 1984 to December 1986. Adyar Estuary was found to be the potentially good ground forfinfishseed collection. The seasonal and percentage composition of seeds of the cultivablefishesmugil cephalus, Liza macrolepis, Liza parsia, Liza tade and Liza cimnesius and Chanos chanos from the estuary and backwater have been assessed. Stray occurrence of other cultivablefinfishseed such as Sillago spp., Sigams spp., Etroplus spp. and Epinephelus spp. were also recorded. Among the grey mullets, Uie striped mullet Mi^il cephalus occurred only from December to March whereas the fry and fingerlings of other grey mullet species occurred throughout the year. The peak season for milkfish seed occurrence was from May to July and November-December being the secondary season. The fry andfingerlingsof the striped mullet Mugil cephalus of the length ranging 15-79 mm were collected predominantly between November and February. Those of the other grey mullet species of the length ranging 15-54 mm occurred throughout the year. In the case of milkfish, 20-59 mm size range was dominant during the peak season. A brief account on the fry andfingerlingsof other finfishes has been presented. The magnitude of seed availability is correlated with the hydrological conditions of Adyar Estuary and Kovalam Backwater. Ecological significance of the results is discussed. INTRODUCTION resources survey of cultivable finfishes in the estuaries and backwaters for locating potential IN RECENT years, there has been a growing eas of their availability and the relative interest in aquaculture throughout the world abundance in diflferent seasons (Tampi. 1968 < to increase the fish production mainly in Qasim, 1975). coastal waters, backwaters and estuaries. Tn the absence of any standard technology for the ^here are about seven estuaries and one mass production of marine finfish seed by backwater along the Madras Coast. They are induced breeding, collection of seed from the puijcat, Ennore, Adyar, Cooum, Kovalam, natural environment is the only major source Edayur. Sadras and Palar. Many workers at present. This necessitated intensive seed ^.^^ surveyed the abundance of finfish seed resources from Adyar Estuary and Kovalam * Presented at the ' Symposium on Tropical Marine Rackwater rrhackn nnh flannnathj IQ/IO Living Resources' held by the Marine Biological «ackwater (.cnacko and Uanapathi. 1949 Association of India at Cochin from January 12-16, Chacko et al., 1954; Evangeline, 1968 ^'**- Evangeline et al., 1969; Evangeline and **Present Address: Madras Research Centre of CnHVinkar 107> RncA ^t ^i tq^o. Central Marine Fisheries Research Institute, 141, =>ucmakar. ly/^, Hose et al.. 1978, Marshalls Road, Egmore, Madras-600 0O8, Nammalwar, 1986). However, it may be

60 P. NAMMALWAR AND OTHERS noted that these assessment of finfish seed resources have been made only for limited periods and no attempt was made on the seasonal and specieswise abundance of finfish seed. The estuaries at Madras do not remain in constant continuity with the sea throughout the year. They are cut off from the open sea for a period ranging from 6 to 9 months. It has been reported that the long shore drift on the open coast frequently closes the river mouth. As a result, acute sullage problems arise in most of the coastal rivers where a minor portion of the untreated sewage and industrial wastes is allowed to flow into the river system. Therefore, it is reasonable to expect severe oscillations in the physio-chemical characteristics of the coastal ecosystem. If the fluctuations in the abiotic regime is detrimental to the biotic components, then there may be related changes in the abundance of fish seed resources. On this basis, an attempt has b"?en made to relate the fish seed abundance with the condition of the river mouth whether open or closed, with the hope that such an integrated survey would provide information for formulating guidelines for effective utilization of natural estuarine resources. The present survey was carried out on the seasonal and specieswise abundance of finfish seed resources of Adyar Estuary and Kovalam Backwater of Madras area. ADYAR KOVALAM 13' i3\ 13 15' NNORE 1^ 0 12' 4B' The authors are grateful to Dr. P. S. B. R. James, Director, Central Marine Fisheites Research Institute, Cochin for his keen interest and encouragement during this period of investigation. Thanks are due to Shri V. Rengacharilu for the analysis of environmental conditions. MATERIAL AND METHODS The survey was carried out from January 1984 to December 1986 in Adyar Estuary (13 01' N-80 17'E) and Kovalam Backwater (I2''49' N - 80 15' E) (Fig. 1). A nylon drag net MAMAULAPURAM PUDUPm-TNAM sa I CM =.4 MILES "7^ Fig, 1. Location of Adyar Estuary and Kovalam Backwater around Madras,

(4 X 3 X 1 m) of the mesh size 5 mm was used. Based on the operational time, volume of water filtered, the area covered, the number of fry and fingerlings per net/hr was estimated. Fortnightly collections were made in the early morning. A minimum of six hauls, three in high tide and three in low tide were made. The hauls made during high tides and low HNFISH SEED RESOURCES AROUND MADRAS computed. Fry and fingerlings belonging to the primary cultivable species of mullets such as Mugil cephalus, Liza macrolepis, Liza parsia, Liza tade, Liza cunnesius and milkfish Chanos chanos. silverwhiting Sillago sihama, rabbitfish Siganus spp., pearl spot Etroplus suratensis and perch Epinephelus spp. were sorted out for their numerical abundance. Hydrological characteristics of the water such as temperature, salinity, dissolved oxygen. ph and water transparency were recorded from Adyar Estuary and Kovalam Backwater. 6l RESULTS r M A M AS 0 n a Fig. 2. Seasonal abundance of marinefinfishseed in Adyar Estuary and Kovalam Backwater from January 1984 to December 1986. tides in a month were treated separately and the average number of seed per haul/hr vras In Adyar Estuary The average monthly abimdance of total finfish seed in Adyar Estuary during January, 1984 to December, 1986 is given in Fig. 2. It may be observed from the results that milkfish seed contributed maximum numbers, during September (958 nos/net/hr). In order to study the distribution pattern of varioxis size groups of fry andfingerlingsof grey mullets, they were assorted with various size groups with an length interval of 5 mm. The percentage of each size group of various grey mullet species in the collections over the period 1984-86 is analysed (Fig. 3). Grey mullet species L. macrolepis, L. parsia, L. tade and L. cunnesius occurred throughout the year whereas M. cephalus were found only from December to March. An analysis of the size frequency distribution pattern indicates that in a given month one or two size groups were represented well, while the rest were poorly represented. The fry and fingerlings of mullets M. cephalus showed the dominance of the size group 15-19, 40-44, 45-49 nun during November, December and January, the length range 15-79 mm being collected predominantly during November-February. The other mullet species L. macrolepis, L. parsia, L. tade and

62 P. NAMMALWAR AND OTHBRS L. cmnesius of the length range of 15-54 mm occurred throughout the year. Fry and fingerlings of milkfish Chanos chanos in Adyar Estuary were observed from April to June being the major season and from October to November the secondary season. The abundance was high (676 nos/ The fry and fingerlings of other groups like Allanetta spp. Genes spp., Ambassis spp., Lutianus spp., Elops spp., Therapon spp., Caranx spp., Sphyraenaspp., Tackysurus spp., Thryssa spp., Rhynchorhamphus spp., occaried in meagre numbers in most part of the survey period. 30 1388 60 40 zo 1985 S«4 I ao 60 40 20 Fig. 3. M 1984 m M i ADYAR ESTUARY _. Mugil cephaluslj Liza macrolepismt Liza cunnesius\^ Liza partial M M J J A S Liza fade OH Chanos chanos 9 Other fishes^sl Percentage occurrence of marine ftnflsh seed in Adyar Estuary from January 1984 to December 1986. net/hr) in the month of April and June, when milkfish of 20-44 mm size was dominant. Fry and fingerlings of pearlspot Etroplus suratensis and silverwhiting Sillago sihama were recorded in high numbers from August-November in Adyar Estuary, N In Kovalam Backwater Kovalam Backwater is located 35 km south of Madras and runs parallel to the sea coast. It is connected with the sea about a kilometre from Kovalam Village. During the northeast monsoon period flood waters collected from

the surrounding areas constitute the backwater proper and there is no river connection. This backwater extends to a distance of about 20 km. The survey area covered extends for about 5 kms from the bar mouth of the backwater. PINFISH SEED RESOURCES AROUND MADRAS 63 to August and fingerlings of L. parsia and L. fade from September to December were collected. The occurrence of fry and fingerlings of milkfish was abundant during June (3600 nos/net/hr) and September (4.500 nos/ net/ hr) in Kovalam Backwater. The abimdance of marine finfish seed was The size frequency distribution of fry and maximum during June (5650 nos/net/hr) and fingerlings of grey mullets revealed that in a eo 1386 so LJL 1985 M I to s i ^ ao Ml I 0 1984 60 40 20 M M J.A A S 0 KOVALAM BACKWATER. g^ nrai Mugil ctphalus L l LiiQ macrolepis H Liza cunntsius'^ Lkoporsio^ fade m Chonos chanos BB Otimr fishes Gu Fig. 4. Percentage occurrence of marine finfish seed in Kovaiam Backwater from January 1984 to December 1986. minimiun during Janxiary (86 nos/net/hr). given month only two or three size groups may Significant fluctuations in abundance was be well represented (Fig. 4). The fry and recorded in the rest of the months. fingerlings of mullets M. cephalns of size 25-29 and 60-64 mm were dominant during November Fry (10-40 mm) and fingerlings (50-70 mm) and December, L. macrolepis, L. parsia and of L. macrolepis and L. cunnesius from January L. cunnesius of the leiigth range of 15-54 mm

64 P. NAMMALWAR AND OTHERS occurred throughout the y<ar. In the case of November. The occurrence of 15-75 mm L. tade, the fry and fingerlings of size 20-24 length range was high during May-August and 70-74 mm occurred from September to and of 40-75 mm during October-November. December. c c: JO I 2 -J 1 I 1 U -I 1 I I I I i_j I 1 I 1 1 I I I I ' 3-8 li 2 ^ ' -J I 4_I I I I t I I I 1 ' ' ' ' d ' I I t I I ' ' 28 24 I 16 o 6 i _I ' ' '! L J I 1 I I I I I I J I I 1 1 I I I I I I ' I I I I ' "^32 ojo 26 ' 1 I I I I I I I I 1 1 ] I I I I ] I I I I I I I I I I I L. J M M J S N J M M J S N J M M J S N 1964 /S85 see ADYAR ESTUARY Fig. 5. Hydrological conditions of Adyar Estuary from January 1984 to December 1986. The fry and fingerlings of Chanos chanos Stray number of fry and fingerlings of occurred from May-August and October- Etroplus suratensis, Sillago sihama, Epinephelus

FINFISH SEED RESOURCES AROUND MADRAS 65 tauvina and Siganus spp. occurred during the spp., Nematalosa nasus. Allanetta spp., period of study. Fry (30-45 mm) of 5^. sihama Lutianus Johnii, Therapon jarbua, Caranx spp., and fingerlings (75-130 mm) of E. suratensis Tachysums spp.. Rhynchorhamphus spp, and and E. tauvina were met with only during Leiognathus spp. were also found in large July and September. numbers during the present investigation. I I I I i L. _L I I I 1 U _J U_J I 1 1 L- j m M J 5 N J M M J S N J M M J S W 34 7585 me KOVALAM BACKWATER Fig. 6. Hydrological conditions of Kovalam Backwater from January 1984 to December 1986. Fry, fingerlings and juveniles of the Premonsoon, monsoon and postmonsoon commercially important fishes such as Ambassis months recorded higher number of yoimg commersoni, Ehps saurus, Thyrssa spp., Gerres ones of these groups. 5

66 P. NAMMALWAR AND OTHERS HYDROLOOICAL CONDITIONS Temperature, salinity, dissolved oxygen, ph and water transparency were monitored from January 1984 to December 1986. Salinity The salinity fluctuation was significant, and ranged from 9.88 % to 45.6%<,. Peak sabnity (45.6 %o) was in September and minimxmi salinity (9.88%) in November. Adyar Estuary Temperature Temperature ranged between 26.0 C and 32.6 C. The maximum during May (32.6''C) and minimum (26.0 C) during December were recorded. Salinity Salinity ranged from 4.24 % to 36.56%o; Peak salinity (30.56%J was recorded during October and low salinity (4.24 %o) during January. Dissolved oxygen The dissolved oxygen content of the water ranged from 0.91 ml/1 to 4.78 ml/1. Maximum DO content of 4,78 mi/1 was observed during April and the minimum of 0.91 ml/1 during July. In general DO content of the water during high tide period was higher. ph The annual variation in ph ranged from 6.5 to 8.6. Maximum ph was 8.6 in October and minimum (6.5) in November. Water transparency The secchi disc depth which was used as a measure of transparency of the water ranged from 23 in January to 57 cm in March. Kovalam Backwater Temperature The temperature ranged from 25.2 C to 34.2 C. The maximiun temperature of 32.5''C was recorded during March and minimum during December, the value being 25.2 Cj The annual pattern of temperature is bimodal. Dissolved oxygen The dissolved oxygen content ranged from 2.92 ml/1 (July) to 5.36 ml/1 (May). ph There was no significant variation in the ph and it ranged from 7.79 (December) to 8.60 (May). Water transparency Maximum transparency (85 cm) was observed during September and low (35 cm) during November. DISCUSSION The results of the present study have brought to light the existence of potentially good grounds in Adyar Estuary and Kovalam Backwater for the cultivable marine finfish seed exploitation along the Madras Coast. Based on the relative abundance of the seed, it may be stated that Adyar Estuary could be considered to be rich for grey mullet assemblage. The tidal pools of Kovalam Backwater were found to be potential areas for milkfish seed. Investigations on the seed resources, hydrobiology and fisheries of Adyar Estuary and Kovalam Backwater have been carried out by many earlier workers (Chacko and Ganapathi. 1949; Chacko et al, 1954; Evangeline, 1968; Evangeline et al. 1969; Evangeline and Sudhakar, 1972; Bose et al. 1978 ; Nammalwar, 1986). They have reported a maximum occurrence of about 35 to 40% for grey mullet seed among the fish seed resources in these estuary and backwater. In the present study however, grey mullets accomplish 50 to 55% of fish seed resources. Evaagoliae et al. (1969), while commeatiog

on the occurrence of mullet seed, drew attention to the role of the formation of sand bar at the mouths of the river. They emphasized that the abundance of fish seed within the estuary is governed by the length of time for which the river mouth was in continuity with the open sea coast. During the present study the bar mouths of Adyar and Kovalam Backwater were found naturally in an open condition for a period of about 7 to 8 months. It is evident that the increase in the abundance of fish seed resource now reported on, may primarily be due to the open condition of the bar mouth of the estuary over a longer period facilitating the entry of seed during most months of the year. Thus, the opening of the bar mouth is an important factor for the abundant marine finflsh seeds, besides recuperation of the river during the high tide period. Therefore, every effort must be made to maintain an year round continuity of the estuary and backwaters with the sea in order to maintain a sustained augmentation offish seed resources. While the seed of grey mullets Liza macrolepis, Liza parsia, Liza tade and Liza cunnesius occurred throughout the year with two peak seasons, October to December and April to Jime that of Mugil cephalus occurred only from December to March. It is known that the seed of grey mullets migrate into the estuarine and backwater regions soon after spawning (Panikkar and Aiyar. 1939; Jacob and Krishnamurthy, 1948; Rengaswamy, 1980). In both Adyar Estuary and Kovalam Backwater, the peak abundance of grey mullet seed coincided with the peak spawning seasons of mullets suggesting thereby that the regulatory function of the estuarine mouth during these peak spawning seasons would increase seed abimdance of grey mullets in these estuarine PINFISH SEED RESOURCES AROUND MADRAS 67 and backwater areas. Surveillance work carried out by the Tamil Nadu Public works Department in keeping the bar mouth open and the concomitant increase in marine finfish seed yield, as reported in the present study, may be taken as an initial promise of high degree of success that can be achieved in this direction if such a coordinated environmental maxiagement of the coastal estuarine system is carried out. It has been observed in the present study that seed measuring 15-54 mm length occurred almost throughout the year giving a positive indication for commercial exploitation. Relatively, more abundant occurrence of milkfish of the size 20-59 mm dominated as also of other marine finfish seed, during May-July deserves special mention. Further, it may be observed that there was consistency in the seasonal abundance and size range for different species of finfish met within Adyar Estuary and Kovalam Backwater during the present study. However, there are greater possibilities for the exploitation of finfish seed over a major part of the year. It may be seen from the present study that in Adyar Estuary and Kovalam Backwater both the extremes of salinity and temperature conditions are met with. For instance, during December, January, March and September, minimum and maximum salinity and temperature recorded were 4.24-45.60 %o and 25.2 C - 34.2 C respectively. Physiological adaption of the grey mullets and milkfish to cope with the extreme salinity and temperature variations are yet another factor for their successful colonization in estuarine and backwater habitat (Kutty 1967 ; Nammalwar, 1982). However, the oxygen regime present in the estuary and backwater impose some limitations for the abxindance of mullets. During the present study, it was found that a huge oxygen deficit was registered (0.91 ml/1) in Adyar Estuary. If the dissolved oxygen level in Adyar Estuary and Kovalam Backwater is maintained above 2 ml/1 the future prospects of grey mullets and milkfish culture could be improved. This could only be achieved if the bar mouth of the estuary could be kept open.

68 P. NAMMALWAR AND OTHERS REFERENCES BosE, V. C, V. VENKATESAN AND D. SUNDARARAJAN 1978. Prawn seed resources of Adyar Estuary at Madras. Proc. Natl. Symp. Shrimp farming. Central Institute of Fisheries Education, Bombay, p. 1-50. CHACXO, P. I. AND S. V. GANAPATHI 1949. Some observations on the Adyar River with special reference to its hydrological conditions. Indian Geogr. Journ., 24: 3549. CHACKO, P. I., R. SRINIVASAN, R. GEORGE, S. KRISHNAMURTHY AND R. GANESAN 1954. A study of the hydrobiology and fisheries of the Adyar Estuary with special reference to conservation. Contr. Freshwat. Fish. Biol. Stn. Madras, 11: 1-23. EVANGELINE, G. 1968. Trend in the fisheries of Adyar Estuary from April 1963 to March 1965. Madras J. Fish., 4 : 1-19. P. MOHANAKRISHNAN AND K. R. SEETHA- LAKSHMI 1969. A preliminarj; hydrobiological survey of certain estuaries in the Cfaingleput District, Madras State. Madras J. Fish., 5 : 1-16. AND K. SUDHAKAR 1972. On the recruitment of prawn postlarvae in the Adyar Estuary. Proc. Sem. Maricul. Mechanised fishing, Madras. pp. 39-41. JACOB, K. AND B. KRISHNAMURTHY 1948. Breeding and feeding habits of mullet (Mugil) in Ennore Creek. J. Bombay nat. Hist. Soc., 47: 455457. KuTTY, M. N. 1967. Physiological studies in relation to fisheries. Souvenir. 20th Anniversary, Central Marine Fisheries Research Institute, Mandapam Camp., pp. 117-120. NAMMALWAR, P. 1982. Some aspects of ecophysiology and biological concerns of the estuarine mullet Liza macrolepis (Smith) with reference to heavy metals pollution. Ph.D. Thesis. Univ. Madras, 266 pp. 1986. Survey of prawn and fish seed resources from the estuaries aroimd Madras. Proc. National. Symp. Estuarine Biology, Annamalai University (Unpublished). PANIKKAR, N. K. AND R. G. AIYAR 1939. Observations on breeding in brackishwater animals of Madras. Proc. Indian. Acad. Sci. B.,9: 343-364. QASIM, S. Z. 1975 Aquaculture : Its potential and scope in India. Proc. Indian Nat. Sci. Acad., 5: 397-420. RANGASWAMY, C. 1980. Age and growth of economic brackishwater fishes of Pulicat Lake. Summer Institute in Brackishwater culture and Capture fisheries, Barrackpore, pp. 1-7. TAMPI, P. R. S. 1968. Cultivable marine fish fry resources from brackishwater environments. Symp. Living Resources of the seas around India. CMFRI, pp. 390-399.