SPAWNING HABITAT AND BIOMASS ESTIMATION OF ANCHOVY (Engraulis encrasicolus, L.) IN BOKA KOTORSKA BAY

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Stud. Mar., 25(1): 83-100 UDK: 597.553.1+639.2.053 (262.3) SPAWNING HABITAT AND BIOMASS ESTIMATION OF ANCHOVY (Engraulis encrasicolus, L.) IN BOKA KOTORSKA BAY Mandić Milica 1, Đurović Mirko 1 and Regner Slobodan 2 1 Institute of marine biology, P.O. Box 69 85330 Kotor, Montenegro 2 Institute of multidisciplinary studies, Belgrade, Serbia E-mail: mamilica@ac.me ABSTRACT In the present study, daily egg production method (DEPM) was used to estimate spawning stock biomass (SSB) of anchovy (Egraulis encrasicolus, L.) in the Boka Kotorska Bay. DEPM surveys were carried out in July 2006, April 2007, and August 2007. Data from CalVet net egg together with reproductive parameters of adult specimens from purse seine nets were used for this assessment. Estimated spawning stock biomass was 1336.97 t. in July 2006, 1013.57 in April 2007, and 1030.59 tons in August 2007. Key words: Engraulis encrasicolus, Daily Egg Production Method, SSB, Boka Kotorska Bay 83

Mandić, M. et al. INTRODUCTION Anchovy (Engraulis encrasicolus, L.) is one of the economically most important Mediterranean small pelagic species with very wide distribution all over the Adriatic Sea. It is found all over the Mediterranean and the Black sea. Anchovy approaches the coast in spring when the temperature rises, and reaches sexual maturity at the end of the first year of life. Reproductive period of anchovy in the Adriatic Sea lasts from spring to autumn, usually from April to October, and sometimes from March to November (Zavodnik, 1970; Merker & Vujošević, 1972; Regner, 1972, 1985, Piccinetti et al., 1979). Main spawning area of anchovy is in the eutrophic waters of the western part of the shallow northern Adriatic and along the Italian coast to the peninsula of Gargano (Regner, 1996). Anchovy stock assessment using eggs and/or larvae surveys are based on the fact that the number of eggs produced by the fish population during the spawning season is proportional, to some extent, to the weight of the mature part of population (Beverton & Holt, 1957). The first attempt of stock assessment using egg survey in the Adriatic Sea was made by Štirn (1969) who estimated anchovy stock biomass in the northern Adriatic Sea. After late 70 s sampling methods were standardized and number of surveys was performed mostly in northern and central Adriatic (Piccinetti et al., 1979, 1980, 1981; Regner et al., 1983; Regner, S. 1985, Dulčić & Cetinić, 1993). In southern Adriatic Sea, DEPM was applied for the first time in June- July of 1993 in the south-western part of Adriatic sea (Casavola et al., 1996), while in 1999 the same method was applied also in southern Adriatic, in the area near Bari (Italy) (Melià et al., 2002). 84

SPAWNING HABITAT AND BIOMASS ESTIMATION OF ANCHOVY In Montenegrin continental shelf DEP method was applied for the first time in August of 2005 in the scope of AdriaMed project. The aim of this paper is to give information about spawning stock biomass of anchovy, in one of the ecologically most sensitive areas of Montenegrin coast. MATERIAL AND METHODS Three ichthyoplankton surveys were carried out in July 2006, April 2007, and August 2007. Plankton samples were taken with PairOVET (modified CalVet) plankton net on 18 stations in the Bay (Figure 1, Table 1). Diameters of net cylinders were 25 cm each, and the total mouth area was 0.098 m 2, with mesh size of 0.160 mm. Net was towed vertically at a speed of 0.5 m*sec -1, from the depth of 5 m above the bottom, as the maximal depth in the Bay is 60 m. Temperature and salinity were measured from the sea surface to the maximal depth attained. Plankton material was preserved immediately on board in 2.5% solution of buffered formaldehyde. Anchovy eggs were counted, staged and aged after methodology developed by Regner, (1985) in the laboratory of the Institute of Marine Biology, Kotor, and data were further processed using the Surfer Golden Software 8 and applying the kriging interpolation method. 85

Mandić, M. et al. Figure 1: Geographical position of Montenegro and Boka Kotorska Bay (Investigated stations 1-18) Adult samples were collected by purse seine nets from commercial catches. On July 22 nd 2006 total of 48 specimens were collected, from which 18 females and 30 males. Next sampling was performed on April 13 th 2007 (24 females and 21 males) and last sampling was done on July 29 th 2007 when total of 43 specimens were analyzed, from which 23 females and 20 males. Adult individuals were processed immediately after catch in order to get the best values of reproductive parameters. Total length (TL) and weight and gonad free weight of anchovy females was measured, extracted ovaries weighed and thereafter preserved in 10% solution of buffered formaldehyde for histological analysis of ovaries. 86

SPAWNING HABITAT AND BIOMASS ESTIMATION OF ANCHOVY Table 1: Geographical position of investigated stations in Boka Kotorska Bay STATION COORDINATES º N º E Degrees Minutes Seconds Degrees Minutes Seconds DEPTH (m) DEPTH OF SAMPL ING (m) 1. Kotor Bay 42 25 82 18 46 11 19 14 2. Kotor Bay 42 28 49 18 45 0 34 29 3. Kotor Bay 42 29 3 18 45 73 29 24 4. Kotor Bay 42 28 79 18 42 52 45 40 5. Risan Bay 42 29 77 18 41 0 30 25 6. Risan Bay 42 29 49 18 39 85 20 15 7. Risan Bay 42 30 49 18 41 50 18 13 8. Verige 42 28 57 18 41 50 44 39 9. Tivat Bay 42 25 76 18 40 11 37 32 10. Tivat Bay 42 25 22 18 41 69 20 15 11. Verige 42 27 12 18 40 82 37 32 12. Tivat Bay 42 25 67 18 37 86 41 36 13. Kumbor Strate 14. Herceg Novi Bay 42 25 88 18 35 86 36 31 42 26 26 18 32 72 42 37 15. Topla 42 26 84 18 31 43 12 7 16. Herceg Novi Bay 17. Herceg Novi Bay 18. Cape Mirišta 42 24 89 18 32 53 40 35 42 23 62 18 33 13 57 52 42 23 57 18 34 22 50 45 87

Mandić, M. et al. Anchovy eggs were classified under ten developmental stages (Regner, 1985). Temperature of the sea surface was used for calculation of developmental time from fertilization to hatching (in days). The following function (1) was used for all estimates of developmental times of anchovy eggs since 1979 (Regner, 1985): D 4.914322 0.257451 T 1 / 1.012896 1 e (1) where D is developmental time of eggs in days, and T is the temperature in C. Numbers of eggs were adjusted as a number of individuals per unit of the surface (1m²) using the function given by Tanaka (1973). DEPM (Daily Egg production Method) is the method developed by Coastal research division of the Southwest Fisheries Center, La Jolla (SWFC, California). Method is based on ichthyoplankton investigation for estimating spawning stock biomass (SSB) of batch spawners with indeterminate annual fecundity, in particular Clupeidae and Engraulidae families.. It was developed in the late 1970 s and since then, it has been applied to a variety of small pelagic stocks. Application of this method requires knowledge of the boundaries of the spawning areas. model: The spawning stock biomass estimation is based on Parker s (1980) E B k * Frb * f * R (2) 88

SPAWNING HABITAT AND BIOMASS ESTIMATION OF ANCHOVY Where: B = spawning biomass in metric tons; E = number of eggs produced per day over the surveyed area (daily production); k = conversion factor from grams to metric tons; F rb = relative batch fecundity; f = spawning frequency; R = sex ratio (fraction of mature females by weight). Spawning frequency (fraction of mature females spawning per day was estimated using postovulatory follicles (POF s) method (Hunter & Macewicz 1985). Determination of spawning frequency (f) by this method is based on frequency of females which have postovulatory follicles (POF s) compared to all sample of mature females (Hunter & Macewicz, 1985). Spawning frequency is determinated by number of D-1 POF s (those postovulatory follicles that appear between the 19 and 28 h after spawning). Those follicles are shrunken and have few folds, and less irregular form than new POF s. Lumen is reduced and may contain some granular material (Fig 2). In order to determinate exact day of the spawning by POF s, morphology was examined in detail. 89

Mandić, M. et al. Figure 2: Histological slide of gonad (POF s) Relative batch fecundity was calculated as a number of eggs produced per unit of female weight (ovary-free weight). It was calculated based on a random sample in which we found two hydrated females. Spawning frequency was calculated using average value of measurements that were done during 2005 and 2008 for biomass estimates of anchovy in Montenegrin continental shelf. RESULTS AND DISCUSSION The distribution and abundance of anchovy eggs are presented in Figures 3, 4, and 5. During the cruise in July 2006, six centers of intensive spawning were observed (stations 2, 4, 8, 10, 11 and 14). In April 2007, also six centers of intensive spawning were found at stations 2, 3, 4, 8, 9 and 11, while the highest abundance was found inside the Bay of Kotor at station 2. In August of 2007 five centers of intensive spawning were found (at stations 1,2,6,9, and 10). 90

SPAWNING HABITAT AND BIOMASS ESTIMATION OF ANCHOVY Figure 3: Distribution of anchovy eggs in July of 2006 (N/ m 2 *day -1 ) Figure 4: Distribution of anchovy eggs in April of 2007 (N/ m 2 *day -1 ) 91

Mandić, M. et al. Figure 5: Distribution of anchovy eggs in August of 2007 (N/m 2 *day -1 ) km 2. Total surface of surveyed area in the Boka Kotorska Bay was 87.334 Estimates of anchovy s gonad free spawning biomass, using Parker s (1980) equation for all investigated seasons is shown in Tables 2-7. Table 2: Summary of parameters used and estimates of anchovy spawning biomass (July 2006) Total surveyed area (km 2 ) 87.334 Daily egg production (N eggs/m 2 * day -1 ) 117.97 Total egg daily egg production in positive area 9.9E+09 Sex ratio 0.389 Spawning frequency (histological, POF) 0.053 Relative batch fecundity (N of eggs per gram of weight) 359.9 Spawning biomass (tons), postovulatory follicles (POF) 1336.97 92

SPAWNING HABITAT AND BIOMASS ESTIMATION OF ANCHOVY Table 3: Anchovy biomass divided by bays (July 2006) Surface of the bay (km 2 ) Biomass (tons) Kotor Bay 16.262 582.216 Risan Bay 8.005 82.472 Tivat Bay 34.439 555.872 Hercegnovi Bay 28.628 116.414 Table 4: Summary of parameters used and estimates of anchovy spawning biomass (April 2007) Total surveyed area (km 2 ) 87.334 Daily egg production (N eggs/m 2 * day -1 ) 109.48 Total egg daily egg production in positive area 8.9E+09 Sex ratio 0.462 Spawning frequency (histological, POF) 0.053 Relative batch fecundity (N of eggs per gram of weight) 359.9 Spawning biomass (tons), postovulatory follicles (POF) 1013.573 Table 5: Anchovy biomass divided by bays (April 2007) Surface of the bay (km 2 ) Biomass (tons) Kotor Bay 16.262 593.2626 Risan Bay 8.005 40.426 Tivat Bay 34.439 306.687 Hercegnovi Bay 28.628 73.196 Table 6: Summary of parameters used and estimates of anchovy spawning biomass (August 2007) Total surveyed area (km 2 ) 87.334 Daily egg production (N eggs/m 2 * day -1 ) 99.19 Total egg daily egg production in positive area 9.5E+09 Sex ratio 0.483 Spawning frequency (histological, POF) 0.053 Relative batch fecundity (N of eggs per gram of weight) 359.9 Spawning biomass (tons), postovulatory follicles (POF) 1030.589 93

Mandić, M. et al. Table 7: Anchovy biomass divided by bays (August 2007) Surface of the bay (km 2 ) Biomass (tons) Kotor Bay 16.262 153.782 Risan Bay 8.005 71.487 Tivat Bay 34.439 695.657 Herceg Novi 28.628 Bay 109.661 Based on the average number of anchovy eggs per m 2 94 per day in separate bays (Kotor Bay, Risan Bay, Tivat Bay and Herceg Novi Bay), biomass was estimated separately for each bay. Although, it is clear that one can not draw a clear line between the bays, however, the following table shows the values of anchovy biomass in all bays in order to compare the results. The distribution of anchovy eggs is under the significant influence of environmental conditions (especially of temperature and salinity) as well as several other oceanographic conditions like sea currents, river runoffs, mixing, nutrients etc. These factors have a strong influence upon adult population, particularly upon place and timing of their reproduction. High abundance of anchovy eggs cannot be related only to the favorable values of temperature and salinity, but to the combination of several environmental and biological factors (Marano, 2001). River run offs have strong influence on spawning and survival rate of early life stages and recruitment of anchovy (Lloret et al., 2004). Abundance of anchovy eggs was calculated as a number of individuals per m 2 per day of the sea surface for comparing results with earlier investigations (Merker & Vujošević, 1972). Also, daily production of anchovy eggs was calculated in order to determine daily intensity of spawning. Although the main spawning areas are in accordance with earlier investigations (Merker, 1972), the abundance is different. Namely, Merker (1972) found eggs in April just at several stations, with the main spawning area

SPAWNING HABITAT AND BIOMASS ESTIMATION OF ANCHOVY in the Bay of Tivat (73 eggs/m²), while the main spawning season was in June and July (max. 376 eggs/m²), in the central part of the Bay of Kotor. This kind of distribution of anchovy eggs (with main spawning areas in bays of Kotor and Tivat, Figs. 4.5 and 6) could be explained by the facts that, beside very favourable values of temperature and salinity, these bays are eutrophic and represent favourable spawning and nursery areas for anchovy. High abundance of anchovy eggs in April could be also explained by high value of nutrients and mixing of water column as a whole. Investigation of length frequencies of anchovy, which is part of the national project from 2004, shows that in Boka Kotorska Bay live mostly young anchovies. So, it can be concluded that after reaching first sexual maturity, young anchovies spawn in the bay and after spawning season goes towards the open waters were continues its life cycle. Our data are in very good accordance with data from Zrmanja river (Sinovčić, G. and Zorica, B., 2006) where is the similar situation as in the Boka Kotorska Bay. Those data prove that juvenile anchovies spawn in the Bay, while adult anchovies spawn in the open part of the Adriatic Sea. Those investigations deny earlier assumptions that adults came inshore to spawn. (Fage,1935 ; Merker and Vujosevic, 1972). Results of spawning biomass of anchovy in Boka Kotorska Bay shows relative stable biomass level during tree investigated seasons, what points to relatively stable ecological conditions in the Boka Kotorska Bay. Having in mind that there are no long-term ichthyoplankton studies in the South Adriatic Sea, this investigation, which was continued after several decades of intermission, shows that the Boka Kotorska Bay is an important spawning area of anchovy. 95

Mandić, M. et al. Despite their importance, studies dealing with larval fish distribution and abundance in the south Adriatic (as well as on fish eggs) are very scarce. Based on data obtained by the estimated biomass by DEP method MSY (Maximal Sustainable Yield) could be determined, or the maximum amount of fish that may be caught without compromising the dynamics of natural populations. Acknowledgements The present study was part of the Project named: Research of ichthyoplankton and juvenile sardine (Sardina pilchardus, Walb.) and anchovy (Engraulis encrasicolus, L.) in Boka Kotorska Bay which was supported by the Ministry of Science of Montenegro. 96

SPAWNING HABITAT AND BIOMASS ESTIMATION OF ANCHOVY REFERENCES Beverton, R. J. H. & Holt, S. J. (1957): On the Dynamics of Exploited Fish Populations, Fishery Investigations Series II Volume XIX, Ministry of Agriculture, Fisheries and Food. U.K. 533 p. Casavola, N., Marano, G. & Rizzi E. (1996): Batch fecundity of Engraulis encrasicolus L. in the southwestern Adriatic Sea. Sci. Mar., 60 (2-3): 369-377 p. Dulčić, J & Cetinić, P. (1993): Estimate of spawning biomass of anchovy, Engraulis encrasicolus, in the eastern part of Adriatic from 1989 to 1990 by means of egg surveys. Acta Ichthyol. Piscat. Vol XXIII, fasc 2: 67-76 p. Fage, L. (1935). La ponte et les races locales de l'anchois de la Mediterranee (Engraulis encrasicolus L. ) Rapp. Proc. Verb. Reun. Commn. Int Explor. Scient. Mer. Mediterr. 10: 67-71 p. Hunter, J. R. & Macewicz, B., J. (1980): Sexual maturity, batch fecundity, spawning frequency, and temporal pattern of spawning for the northern anchovy, Engraulis mordax, during the 1979 spawning season. Rep. Calif. Ocean. Fish. Invest., 21: 139-149 p. Lloret, J., Palomera, I., Salat, J. & Sole, I. (2004): Impact of freshwater input and wind on landings of anchovy (Engraulis encrasicolus) and sardine (Sardina pilchardus) in shelf waters surrounding the Ebre (Ebro) River delta (north-werstern Mediterranean). Fish. Oceanogr. 13: 2, 102-110p. Melià, P., Casavola, N. & Gatto, M. (2002): Estimating Daily Egg Production of European Anchovy in the Adriatic Sea: A Critical Appraisal. Mar. Ecol., 23. Supl. 1, 272-279 p. 97

Mandić, M. et al. Merker, K. (1971): Some preliminary observation on findings of spawning areas of sardine (Sardina pilchardus WALB.) in South Adriatic area.(in Montenegrin). Studia Marina, No 5, pp 61-74. Hydrobiologia 612: 185-199 p. Merker, K. & Vujosevic, M. (1972): Density and distribution of anchovy (Engraulis encrasicolus L.) eggs in the Bay of Boka Kotorska (in Serbo-Croatian). Poljoprivreda i šumarstvo, 18: 15-27 p. Parker, K. (1980): A direct method for estimating northern anchovy, Engraulis mordax, spawning biomass. Fish.Bull.U.S. 78:541 544 p. Piccinetti, C., Regner, S. & Specchi, M. (1979): Estimation du stock d anchois (Engraulis encrasicolus L.) de la haute et moyenne Adriatique. Inv. Pesc., 43 (1): 69-81 p. Piccinetti, C., Regner, S. & Specchi, M. (1980): Etat du stock d anchois et de sardine en Adriatique. FAO Fish. Rep., 239: 43-52 p. Piccinetti, C., Regner, S. & Specchi, M. (1981): Estimation preliminaire de la production maximale d anchois et de sardine en Adriatique. FAO Fish. Rep., 253: 155-158 p. Regner, S. (1972): Contribution to the study of the ecology of the planktonic phase in the life history of the anchovy, Engraulis encrasicolus (Linnaeus, 1758), in the central Adriatic. Acta Adriat., 14 (9):40 p. Regner, S., Piccinetti, C. & Specchi, M. (1983): Estimate of spawning biomass of sardine in the Northern and Central Adriatic from 1979 to 1882 by means of egg surveys. FAO Fish. Rep., 290:223-232 p. Regner, S. (1985): Ecology of planktonic stages of the anchovy, Engraulis encrasicolus (Linnaeus, 1758), in the central Adriatic. Acta Adriat., 26(1), Series Monographiae, 1: 1-113. 98

SPAWNING HABITAT AND BIOMASS ESTIMATION OF ANCHOVY Regner, S. (1996): Effects of environmental changes on early stages and reproduction of anchovy in the Adriatic Sea. Sci. Mar., 60 (Supl.2): 167-177 p. Sinovčić, G and B. Zorica (2006): Reproductive cycle and minimal length at sexual maturity of Engraulis encrasicolus (L.) in the Zrmanja River estuary (Adriatic Sea, Croatia). Est., Coast. Shelf. Sci. 69: 439-448 p. Štirn, J. (1969): Pelagial severnega Jadrana. Razprave- Dissertationes, 12(2): 92 p. Tanaka, S. (1973): Stock Assessment by means of ichthyoplankton surveys. FAO Fish. Tech. Rap., 122: 33-51 p. Zavodnik, D. (1970): Comparative data on the spawning of sardine (Sardina pilchardus Walb.), sprat (Sprattus sprattus L.) and anchovy (Engraulis encrasicholus L.) in the North Adriatic. Ichthyologia, 2: 171-178 p. 99