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Mortality and Survival of the Himalayan Mahseer Tor Putitora in a Regulated Section of the River Ganga Between Rishikesh and Haridwar PDF

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Preview Mortality and Survival of the Himalayan Mahseer Tor Putitora in a Regulated Section of the River Ganga Between Rishikesh and Haridwar

MORTALITYAND SURVIVALOFTHEHIMALAYANMAHSEER TOR PUTITORA IN A REGULATED SECTION OF THE RIVER GANGA BETWEENRISHIKESH ANDHARIDWAR 1 J.P.BhattandP.Nautiyal2 Key words: Himalayan Mahseer, Torputitora, mortality rate, survival rate, river Ganga Studieswere conducted to assessthe mortalityand survival ratesofthe Himalayan Mahseer Tor putitora in the foothills section ofthe Ganga 285-290 m above msl (29° 56’ N lat., 78° 10’ E long.), where the river has been extensively regulated through two barrages and an array of canals for hydropower generation, irrigation and recreation. The mortality and survival rates of samplesmeasuring 14.5 to98 cmin lengthwereobservedtobe0.414and0.586(pooledsample), 0.348 and 0.652 (1993-94), 0.487 and 0.513 (1994-95), 0.499 and 0.501 (male) and 0.381 and 0.619(female)respectively, inthe 1+to9+age-groupfishes. Theweightedmortalityandsurvival rateswere0.323 and 0.67(pooled sample),0.346 and 0.654(1993-94), 0.47 and 0.53 (1994-95), 0.436and0.564(males)and0.467and0.567(females)respectively,whileinstantaneousmortality ratewas0.589, 0.53, 0.693, 0.855 and 0.555 in the pooled sample, 1993-94, 1994-95, malesand femalesrespectively. Mortality was high in the higherage groups in captivity. Introduction of T. putitora is not available in India and in Garhwal region. The age composition of the stock, the relative strength ofdifferent age groups and the MaterialandMethods maximum life span are, within certain limits, speciescharacteristic.Fisheswithshortlifecycle, Fishing mortality rates were estimated with a population which consists ofonly a few from commercial landings from the foothills age groups, are adapted to living under section ofthe Ganga near Ajeetpur, a riverside conditions ofvery high and variable mortality. villagelocateddownstreamofHaridwar.Thefish On the other hand, species which form samples were taken randomly from the fish populations containing many age groups and contractor at Ajeetpur or from the Raiwala fish with late mortality are adapted to living under market (where fish is supplied from Ajeetpur). conditions of a relatively stable food supply, Fish samples were given an abdominal incision negligible annual fluctuation in the mortality of and preserved in 10% formalin. In the case of mature individuals, and little effect ofpredator large fishes, length and weight was recorded on fishes. Ifasubstantialpartofapopulationshould the spot and scales were collected. die, its replacement is slow and this is reflected The age of the samples was determined in the age composition which is a function of with the help of key scales (Bagenal 1978) replacement, growthanddeath(Nikolsky 1976). obtainedfromthebaseofdorsalandpectoralfins Smith(1983)andWankowskietal. (1988) fromfishesmeasuring 14.5to98cm. Preliminary studied the mortality rates in Nemcidactylus screening indicatedthatthenumberofringswas macropterus but information on the mortality similar in the dorsal and pectoral scales. Thus , only dorsal fin region scales were selected. To 'AcceptedJune, 1997 determinethe age, thescaleswere analysedwith ^DepartmentofZoology,H.N.B.GarhwalUniversity, Srinagar246174.UttarPradesh. a Carl Zeiss Jena Documeter. The number of 70 JOURNAL. BOMBAY NATURAL HISTORY SOCIETY. 96(1) APR. 1999 MORTALITYAND SURVIVAL OF THE HIMALAYAN MAHSEER IN THE RIVER GANGA annuli in each key scale was recorded. Annulus recordedas0.586.Relativelyhighersurvivalrate formation was determined by the criteria wasrecordedinthe 1993-94yearsample(0.652) suggested by Bagenal (1978) and adopted by as compared with 1994-95 year sample (0.513). Nautiyal (1990). According to him, a zone of The weighted mortality rate was found to be closely spaced ridges is followed by a zone of 0.346, 0.47 and 0.323 for the 1993-94, 1994-95 widely spaced ridges. The annulus is usually and pooled year samples, respectively. The consideredtobeattheouterborderoftheclosely weightedsurvivalrateswere0.65, 0.53 and0.67 spaced ridges. for 1993-94, 1994-95 andpooledsamples(Table The mortality and survival rates were 1). determined by the age frequency method Mortality rate was observed to be 0.499 (Rounseefell and Everhart 1985), using the for males and 0.381 for females. The survival following equations. rates were recorded as 0.501 and 0.619 in The annual mortality rate (r) = (1-s) or male and female, respectively. Weighted (1-e 8) where 5 (rate ofsurvival) was computed mortalityrateswerefoundtobe0.436and0.467, in the following manner: whilesurvivalrateswere0.564and0.567inmale and female respectively. The instantaneous n-1 n mortality rate was 0.855 in male and 0.555 in [ I log f(y) ] - [ Ilog f(y) ] female (Table 1). y=x y =x - 1 The 1+ and 2+ age groups showed zero mortality rates in the year class sample 1993- 94, male and female. Zero mortality was also where f(y) =age frequency at any age (y) observed in the 3+ age group during 1994-95. The instantaneous mortality rate (8) was Low mortality and higher survival rates were computedas follows: observedinthe lowerage classes (3+, 4+) while higher mortality and lower survival rates were 8 = l°gI0(l/s) (l/logIOe) = loge (1/1-r) seen in the higher age groups (8+, 9+; Table 2). where l/log = 2.303 10e Discussion Observations Studies indicate that information on the The rates obtained for the year-class various aspects of population structure is samples 1993-94 and 1994-95 were 0.348 and important for managing natural populations, 0.487 respectively. The mortality rate for the especiallycommerciallyexploitedfishstock.The pooled data (1993-1995) was 0.414 (Table 1). age structure, like other parameters of the The survival rate for the pooled data was population, may change from time to time. Table1 COMPUTATIONOFMORTALITYANDSURVIVALRATESINTORPUTITORA FOR DIFFERENTYEARSANDSEXES Parameters 1styear(1993-94) 2ndyear(1994-95) Pooledsamples Male Female Instantaneousmortalityrate 0.530 0.693 0.589 0.855 0.555 Mortalityrate 0.348 0.487 0.414 0.499 0.381 Survivalrate 0.652 0.513 0.586 0.501 0.619 Weightedmortalityrate 0.346 0.470 0.323 0.436 0.467 Weightedsurvivalrate 0.654 0.530 0.677 0.564 0.567 JOURNAL BOMBAY NATURAL HISTORY SOCIETY, 96(1), APR. 1999 71 , 4 1 MORTALITYAND SURVIVAL OF THE HIMALAYAN MAHSEER IN THE RIVER GANGA Table2 COMPUTATIONOFMORTALITYANDSURVIVALRATESOFTORPUTITORA INTHEPOOLEDSAMPLES A B C D E F G H Age(y) Freq.(f) logf logf(y)-f(y-l) Dtimes (1-D) Antilog weighted (2.303) (DX-'Jf) byf(y) 1 14 1.146 2 62 1.792 3 58 1.763 -0.029 0.066 0.971 0.935 -0.220 4 43 1.633 -0.130 0.299 0.870 0.741 -0.851 5 20 1.301 -0.332 0.764 0.668 0.465 -1.484 6 11 1.041 -0.260 0.598 0.74 0.549 -0.860 7 8 0.903 -0.138 0.317 0.862 0.727 -0.389 8 3 0.447 -0.456 1.050 0.544 0.349 -0.642 9 1 000 -0.447 1.029 0.533 0.341 000 Total 223 1.792 4.123 5.188 4.107 4.446/26. (Mean) (0.256) (0.589) (0.741) (0.586) =0.169 Instantaneousmortalityrate(5)=0.589 Weightedsurvivalrate/s(w)=0.677 Mortalityrate(r)=0.41 Weightedmortalityrater(w):=0.323 Survivalrate(s)=0.586 1-0. 169=0.831 adapting to change in the environmental and haddock. According to Gulland (1978), the conditions. The data on age structure can also mortality varies continuously with age. It is be used to draw inferences on the health ofthe usually more convenient and more reliable, population, its mortality and survival rates within an acceptable approximation, to consider (Nikolsky 1976, Bagenal 1978 and Rounseefell that fishing mortality changes abruptly, being and Everhart 1985). zero on the pre-recruits below a certain age and In our study, survival rates were found to constant from a given age upwards. be higher than the mortality rates. Relatively Itwasconcludedthatmortalityincaptivity higher annual mortality and lower survivalrates increased with age. Tandon and Johal (1996) were found in males (0.499, 0.501) than in stated that increase in mortality between females (0.381, 0.619). In the Atlantic salmon particular age classes is due to substantial also, this difference has been reported by increase in the exploitation rate. According to Nikolsky(1980).Healsostatedthateachspecies Ricker(1962)andGulland(1975),thevariations has a definite mortality rate. A species with a inthepercentagemortalitybetweendifferentage shortlife cycle exhibits arelatively higherdeath classes are due to the available stock, shifting of rate thanone with a long cycle and late maturity year class, and probably also due to sampling such as the Himalayan mahseer. error.RounseefellandEverhart(1985)statedthat We reiterate thatthe numbers ofa species weightedvaluesdonotdepartfarfromthevalues before the harvestable size are not a true index computedbytheconventionalmethods,although for the calculation of mortality/survival rates it may be an advantage to weight when the because the fish at this size/age are vulnerable samples are small. to fishing gear. Similar results (high mortality Acknowledgement in higher age classes and low mortality in the lowerageclasses)werealsoobtainedbyTandon The authors are grateful to the Ministry of and Johal (1996) in C. mirigala and L. rohita Environment and Forests, Govt, of India, New fromGobindsagar,andbyGraham(1956)incod Delhi, for financial assistance. 72 JOURNAL BOMBAY NATURAL HISTORY SOCIETY, 96(1) APR. 1999 MORTALITYAND SURVIVAL OF THE HIMALAYAN MAHSEER IN THE RIVER GANGA References Bagenal, T. (1978): Methods for Assessment ofFish Bishen Singh Mahendra Pal Singh, Dehradun. India Production in Freshwaters. Blackwell Scientific andOttoKoeltzSciencePublishers,W. Germany: 1- Publications,Oxford,pp365. 323. Graham,M.(1956):SeaFisheries:Theirinvestigationsin Ricker,W.E.(1969):Effectofsize-selectivemortalityand theUnitedKingdom. EdwardArnoldPublishersLtd., sampling bias on estimation of growth, mortality, London:487. production and yield. J: Fish. Res. Board Can.. 26: Gulland,J.A. (1975): Manualofmethodsforfishstock 479-541. assessment Pt. 1. Fish population analysis. FAO Rounseefell, G.A. & W.H. Everhart (1985): Fishery manualsinfisheriesscience.No4FRS/n4 154. Science, Its MethodsandApplications. International Gulland,J.A.(1978):Fishing,fishandfoodproduction. BooksandPeriodicalsSupplyService,NewDelhi: 1- InEcologyofFresh WaterFish Production(ed. S.D. 444. Gerking), pp 381-402. Blackwell Scientific Smith,D.C.(1983):Annualtotalmortalityandpopulation Publications,Oxford. structure of Jakss morwong (Nemadactylus Nautiyal,P.(1990):NaturalhistoryofGarhwalHimalayan macropterus Bloch and Schneider) in eastern Mahseer:Growthrateandagecompositioninrelation Australianwaters.Aust. J. Mar. FreshwaterRes. 34: to fishery, feeding and breeding ecology. Proc. 2nd 253-260. Asian FisheriesForum. Tokyo, (eds. R. Hirano & I. Tandon, K.K. & M.S. Johal(1996): AgeandGrowth in Hanyu.):769-772. IndianFreshwaterFishes.NarendraPublishingHouse, Nikolsky,G.V.(1976):TheEcologyofFishes.Academic NewDelhi: 1-232. Press,LondonInc.3-352. Wankowski, J.W.J., E. Hyduke, & S. Willium (1988): Nikolsky, G.V.(1980): Theory of Fish Population Populationagestructureandnatural mortalityratesof DynamicsastheBiologicalBackgroundforRational Jakssmorwong{Nemadactylusmacroptems)ineastern Exploitationand ManagementofFisheryResources. BassStrait,Australia.Fisheriesresearch6:317-336. JOURNAL, BOMBAY NATURAL HISTORYSOCIETY. 96(1). APR. 1999 73

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