International Journal of Scientific & Engineering Research, Volume 4, Issue 4, April ISSN

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International Journal of Scientific & Engineering Research, Volume 4, Issue 4, April-2013 1083 Parasitic distribution in relation to gender, season and length of fish hosts in Shallabugh wetland. Ibraq Khurshid Fayaz Ahmad and Tariq Ahmad Department of Zoology, University of Kashmir, Srinagar-190 006, Kashmir Abstract kibraq@yahoo.com Parasitism is of great interest to the ecologists because it poses great problem in the growth of the fish hosts. With the aim to evaluate the relationship between the infection levels, length of fish host, gender and season, the present study was undertaken on Shallabugh wetland for a period of one year from August 2011 to July 2012. This Wetland consists of larger area of riverine marshes and shallow fresh water with associated reed-beds on the floodplains of river Jhelum. The Wetland together with marshes is fed by the Anchar Lake and local runoff. The average depth of the water varies from 0.3 to 2.0 meters. The Wetland supports a locally important fishery and reed harvesting Industry, which provides excellent opportunities for sport Hunting. During the study period, 342 fish specimens belonging to the genus Schizothorax were examined from three collection sites in the wetland. The collection sites were inlet (where the anchar lake meets the Shallabugh wetland), middle of the Shallabugh wetland and third is the outlet ( where the shallabugh wetland meets river jhelum). Out of 342 specimens120 were taken from inlet, 113 from middle and 109 from outlet. A total of 106 specimens were infected (52 at inlet, 25 at middle and 29 at outlet) showing the intra wetland variations of 43.33% (inlet), 22.12% (middle) and 26.6% (outlet). Our results show that the prevalence of infection increased significantly with increase in the length of host.(r = 0.968). Season wise distribution also showed the +ve correlation (chi-square = 43.560), (p = 0.001) and furthermore the gender showed the ve correlation with the prevalence of infection as the male and female host specimens were equally prone to the helminth infection. Key words: Fish; Parasite; Helminth; Schizothorax spp,.wetland; Kashmir. Introduction About 46 sps. of helminths are reported as parasites of fresh water fishes of Kashmir as far the knowledge of the author is conserned. They belong to four groups, cestodes (6sps.), trematodes (20sps.), nematodes (5sps.) and acanthocephala (15sps.). These helminth parasites may infect several hosts from different families (Poulin 1992). In

International Journal of Scientific & Engineering Research, Volume 4, Issue 4, April-2013 1084 the past researchers have studied some of the ecological aspects of the helminth parasites in this region like season influencing the helminth parasites (Chishti et al., 2000 ; Zargar et al.,2012). However previous studies have not used the holistic approach to ascertain the effect of various factors which influence infection level of helminth parasites in the Kashmir Himalayas. In order to unravel the effect of various factors like seasonality, gender, length of the host, we carried out the investigation in Shallabugh Wetland. Hypothesis It was predicted that gender, seasonality and length could affect the helminth infection. Material and method 3.1 Study site: Shallabugh wetland is 16 km northwest of Srinagar and measures about 12 square kilometres. The Wetland consists of larger area of riverine marshes and shallow fresh water with associated reed-beds on the floodplains of river Jhelum. The Wetland together with marshes is fed by the Anchar Lake and local runoff. The average depth of the water varies from 0.3 to 2.0 meters. The Wetland supports a locally important fishery and reed harvesting Industry, which provides excellent opportunities for sport Hunting. 3.2 Host and parasite collection The present study was carried out between August 2011 to July 2012. In total 342 (143 S. plagiostomus, 55 S. curvifrons, 77 S. esocinus, 67 S. labiatus) individuals of Schizothorax species were examined. Fishes were caught by local fisherman using nets. Further investigation was carried out in the laboratory,where total length, standard length, body weight and gender for each was determined. Biometrical indices like length weight relationship was calculated by Lecren s (1951) method (W = al b ) and conditional factor by Fulton s index (K= W/L 3 X10 5 ). Fish collected from Shallabugh wetland were immediately dissected and some fishes were kept alive in aquarium for short period of time (upto 2hr).so that they remain fresh for parasitological investigation. Gills, intestine were carefully removed soon after the death of fish and kept in a petridish containing normal saline (0.85%NaCl). For studying the micro distribution of some helminth parasites like

International Journal of Scientific & Engineering Research, Volume 4, Issue 4, April-2013 1085 Diplozoon, Pomphorhynchus, the methodology of Turgut et al. (2006) and Geets et al (1997) were adopted. 3.3 Experimental Design Three collection sites were selected for collection in Shallabugh wetland. One site is where the Anchar Lake meets the Shallabugh Wetland (inlet), second is the middle of Shallabugh Wetland and the third is the sangam (outlet). 3.4 Data Analysis Pearsons correlation was used to asses association between different physic chemical features and helminth infection. Chisquare analysis was also used for calculating the prevalence of helminth infection and the relation between length and infection rate. 4. Results and discussion 4.1 Intra wetland variations The results showed a significant difference between study sites in Shallabugh wetland (p=0.008). The prevalence was significantly higher at highly polluted site (prevalence = 45.8; p < 0.05) in comparison to eutrophic site (prevalence = 22.01; p < 0.05) in Shallabugh wetland (table 1). Table:1 Intra wetland variations of parasitic infection in Shallabugh Wetland Inlet Middle Outlet Total no. examined 120 113 109 No. infected 52 25 29 Prevalence 43.33 22.12 26.6 No. of parasites 123 82 54 Mean intensity 2.36 3.28 1.87 P = 0.032 Data showed the significant intra wetland variation in prevalence of helminth infection in fish hosts. Significantly low mean intensity at the polluted and hyper eutrophic site in Shallabugh wetland could be due to negative impact of contaminants on helminths itself and thus decreased intensity. It also seems that helminths show antagonistic response to combined effect of pollutant and eutrophication at this site. 4.2 Effect of month and season on the infection The monthly prevalence showed insignificant differences (p > 0.05), whereas seasons showed significant differences in prevalence (Table 2; p < 0.05). Clear

International Journal of Scientific & Engineering Research, Volume 4, Issue 4, April-2013 1086 seasonal trend was observed in Shallabugh Wetland with maximum infection level during summer months and least in winter months. The prevalence among different seasons when compared statistically revealed significant differences (p < 0.05). Table: 2 Season wise prevalence of helminth infection in fish hosts Season No. examined Positive Prevalence % Spring 85 17 20 Summer 84 43 51.19 Autumn 95 36 37.89 Winter 78 10 12.8 Total 342 106 30.99 Chi-square = 43.560 p-value = 0.001 The results showed significant seasonality in the helminth infection in Shallabugh wetland. The seasonality in our study is in conformity with the results of Yufa and Tingbao (2011) who concluded that the helminth species like monogenean showed seasonal alterations associated with environmental changes. The abrupt increase in helminth infection from winter in Shallabugh wetland could be due to increased duration of life of the infective larva, thereby assisting the transfer of helminth infection like Diplozoon infection from fish to fish (Chubb, 1979). 4.3 influence of gender and condition factor on the level of infection In all the three study sites males and females are equally susceptible to infection (p < 0.005; Table 3). Table 7. Gender Wise prevalence of Helminth parasites in Fishes Host Gender No. Examined +ve Prevalence (%) P.value S. plagiostomus M 83 15 (18.0) 0.32 F 60 16 (26.6) S. labiatus M 42 14 (33.33) 0.7 F 25 7 (28)

International Journal of Scientific & Engineering Research, Volume 4, Issue 4, April-2013 1087 S.esocinu M 42 16 (38.09) 0.87 F 31 11 (35.4) S.curvifrons M 41 13 (31.7) 0.53 F 58 14 (24.13) The present study showed insignificant relationship between gender and helminth infection, which is in accordance to the studies done by Peerzada and Chishti, (1999), who reported similar rates of infection in both the sexes. Condition coefficient was found to be lower in infected fish than in uninfected fish in Shallabugh wetland. It may be due to the fact that parasites decrease the immune system of the hosts, which may lead to decreased growth of fish. Decreased growth may lead to decrease in condition coefficient (Khan and Thulin, 1991; Poulin, 1992). Parasites may also alter the physiological as well as reproductive functions of hosts. This may also lead to decreased growth of fish (Le Cren, 1951). It has been reported previously that condition factor tend to be higher due to higher food quality and availability (Polacik et al., 2009; Ondrackova et al., 2009). 4.4 Prevalence, mean intensity in relation to length of host Prevalence and mean intensity showed the +ve correlation with the length of host (p > 0.005; table 4). Table 4.4 Prevalence, mean intensity in relation to length of host length No.examined No. infected No.of parasites Prevalence Mean intensity 10.5-15.5 79 10 22 12.65 2.2 15.5-20.5 87 28 64 32.18 2.28 20.5-25.5 84 30 76 35.71 2.5 25.5-30.5 92 38 97 41.30 2.4 Total 342 106 259 30.46 2.44 This depicts that with increase in the host length the no. of parasites also increase. 5. Conclusions and suggestions

International Journal of Scientific & Engineering Research, Volume 4, Issue 4, April-2013 1088 In summary, intra lake variation, season, condition factor and microhabitat seem to have a significant impact on the helminth infection. It also seems from the data that eutrophic and hypertrophic habitats were favourable for helminths. It is suggested that more field and in vitro studies need to be carried out to know the joint impact of pollution and eutrophication on the helminth infection. Present study will pave the way for future studies on different ecological aspects of helminth parasites in this region as well as in similar climatic regions of the world. Furthermore we need to unravel the specific factors which have major impact on the occurrence of helminths in this region. Helminths in particular should be integrated with bio monitoring programmes, as these parasites can provide supplementary information on pollution. It is also suggested that helminths in general should be analysed for accumulation capability of different contaminants under experimental conditions in order to validate the role of helminth parasites in environmental monitoring. References:- American Public Health Association,Washington, DC (1998). Standard methods for the examination of water and wastewater, 20th ed. Amer-ican Public Health Association, the American Water Works Association and the Water Environment Federation, 1220 pp. Baggea, A. M and Valtonen, E. T (1996). Experimental study on the influence of paper and pulp mill effluent on the gill parasite communities of roach (Rutilus rutilus). Parasitology 112: 499 508. Beer, S. A and German, S. M(1993). Ecological prerequisites of worsening of the cercariosis situation in cities of Russia (Moscow region as an example). Parazitologiya 27: 441 449 Bhat, S. A., Rather, S. A and Pandit, A. K.(2001). Impact of effluents from Sheri- Kashmir Institute of Medical Sciences (SKIMS), Soura on Anchar Lake. J. Res. Dev. 1: 30 37. Blanar, C. A., Munkittrick, K. R.., Houlahan, J., Mac Latchy, D. L and Marcogliese, D. J(2009). Pollution and parasitism in aquatic animals: a meta-analysis of effect size. Aquat. Toxicol. 93:1 80. Bush, A.O., Lafferty, K. D., Lotz, J. M and Shostak, A.W (1997). Parasitology meets ecology on its own terms: Margolis et al. revisited. J. Parasitol. 83: 575 583. Chubb, J. C (1979). Seasonal occurrence of helminths in freshwater fishes. Part II. Trematoda. Adv. Parasitol. 17: 141 313.

International Journal of Scientific & Engineering Research, Volume 4, Issue 4, April-2013 1089 Chishti, M. Z. and Bakshi, S. (2000). On Rhabdhochona guptii n. sp. From the intestines of Cyprinus carpio spicularis, a fresh water fish from Hokarsar (wetland) in Kashmir. Indian Journal of Parasitology, 14(1): 45-49. Fellis, K.J and Esch, G.W (2004). Community structure and seasonal dynamics of helminth parasites in Lepomis cyanellus and L. macrochirus from Charlie s Pond, North Carolina, host size and species as determinants of community structure. J. Parasitol. 90: 41 49. Holmes, J. C(1972). Site selection by parasitic helminths: interspecific interactions, site segregation, and their importance to the develop-ment of helminth communities. Can. J. Zool. 51: 333 347. Ibraq khurshid and fayaz ahmad ( 2012). Gastro-intestinal helminth infection in fishes relative to season from Shallabugh wetland.int. J. Rec. Sci. Res., 3(4): 270-272. Kennedy, C. R and Watt, R. J., 1994. The decline and natural recovery of an unmanaged coarse fishery in relation to changes in land use and atten-dant eutrophication. In: Cowx, I.G. (Ed.), Rehabilitation of Freshwater Fisheries. Blackwell Scientific, Oxford, pp. 366 375. Khan, R. A and Thulin, J (1991). Influence of pollution on parasites of aquatic animals. Adv. Parasitol. 30: 201 238. Lafferty, K. D and Kuris, A. M (1999). How environmental stress affects the impacts of parasites. Limnol. Oceanogr. 44: 925 931. Lafferty, K. D and Kuris, A. M (2005). Parasitism and environmental distur-bances. In: Thomas, F., Guégan, J.F., Renaud, F. (Eds.), Parasitism and Ecosystems., pp. 113 123. Le Cren, E.D (1951). The length weight relationship and seasonal cycle in gonadal weight and condition in the perch. Perca fluviatilus. J. Anim. Ecol. 20: 201 219. Marcogliese, D. J (2001). Implications of climate change for parasitism of animals in the aquatic environment. Can. J. Zool. 79: 1331 1352. Margolis, L., Esch, G.W., Holmes, J. C., Kuris, A.M and Schad, G. A (1982). The use of ecological terms in parasitology (report Bush et al. Parasite Ecology and Terminology 583 of an adhoc committee of the American Society of Parasitologists). J. Parasitol. 68: 131 133.

International Journal of Scientific & Engineering Research, Volume 4, Issue 4, April-2013 1090 Mu noz, G and Randhawa, H. S (2011). Monthly variation in the parasite communities of the intertidal fish Scartichthys viridis (Blenniidae) from central Chile: are there seasonal patterns? Parasitol. Res. 109: 53 62. Pandit, A. K., Yousuf, A. R (2002). Trophic status of Kashmir Himalayan lakes as depicted by water chemistry. J. Res. Dev. 2, 0972 5407. Peerzada, M. Y. and chishti, M. Z (1999). Ecological studies on helminth parasites infecting snowfed stream fishes of Kashmir: Acanthocephala (Neoechinorhynchus: Neoechinorhynchidae). 5th National Seminar on Fish and their Environment. 26-28 July. Department of Zoology, University of Kashmir, Srinagar, 190006, India. Polacik, M., Janac, M., Jurajda, P., Adamek, Z., Ondrackova, M., Trichkova, T and Vassilev, M (2009). Invasive gobies in the Danube: invasion success facilitated by availability and selection of superior food resources. Ecol. Freshw. Fish 8: 640 649. Poulin, R (1992). Toxic pollution and parasitism in freshwater fish. Para-sitol. Today 8: 58 60. Rohde, K (1979). A critical evaluation of intrinsic and extrinsic factors responsible for niche restriction in parasites. Am. Nat. 114: 648 671. Rohde, K (1981). Niche width of parasites in species rich and species-poor communities. Experientia 37: 359 361. Souza, W. P and Grosholz, E. D (1991). The influence of habitat structure on the transmission of parasites. In: Bell, S. S., Mc Coy, E. D., Mushinsky, H. R. (Eds.), Habitat Structure: The Physical Arrangement of Objects in Space., pp. 300 324. Turgut, E., Shinn, A., Wootten, R and (2006). Spatial distribution of Dactylogyrus (Monogenan) on the Gills of the Host. Turk. J. Fish Aquat. Sci. 6: 93 98. Williams, H and Jones, A (1994). Parasitic Worms of Fish. Taylor & Francis Ltd, p. 593. Yufa, L and Tingbao, Y (2011). Seasonal patterns in the community of gill monogeneans on wild versus cultured orange-spotted grouper, Epinephelus coioides Hamilton, 1822 in Daya Bay, South China Sea. Aquac. Res., 1 11. Zargar, U. R., Yousuf, A. R., Chishti, M. Z., Ahmed, F., Bashir, H and Ahmed, F ( 2012). Effects of water quality and trophic status on helminth infec-tions in

International Journal of Scientific & Engineering Research, Volume 4, Issue 4, April-2013 1091 the cyprinid fish, Schizothorax niger Heckel, 1838 from three lakes in the Kashmir Himalayas. J. Helminthol. 86: 70 76.