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Habitat ecology of zygopteran (Odonata) nymphs in certain water bodies of Madhya Pradesh PDF

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, HABITAT ECOLOGY OF ZYGOPTERAN (ODONATA) NYMPHS IN CERTAIN WATER BODIES OF MADHYA PRADESH 1 S. Kaushik, S. Sharma, M.N. Saxena and D.N. Saksena2 The distribution ofzygopteran (Odonata) nymphs and theirassociation with macrophytes in certain clean and polluted water bodies of Madhya Pradesh have been described. 16 species of zygopteran insects were identified on the basis of last instar nymphal stages. Neurobasis chinensis chinensis andPseudagrion spencei m were found at higher altitude (1067 above msl) and Copera marginipes, Ischnura delicata, /. rufostigma m Pseudagrion laidlawi and Rhodischnura nursei were observed at lower altitudes (205 to 318 above msl). Copera marginipes Ischnura rufostigma, Lestes praemorsa, Neurobasis chinensis chinensis, Pseudagrion , laidlawi P. spencei, Rhinocypha unimaculata and Rhodischnura nursei preferred lotic waters. Neurobasis , chinensis chinensis and Pseudagrion spencei inhabited acidic waters. Copera marginipes and Rhinocypha unimaculata were found in association with Vallisneria spiralis and Eichhornia crassipes respectively and Ischnura rufostigma along with decaying vegetation. Other species had no specific preference for the macro- phytes. Thezygopteran nymphs thus were found from clear to polluted waters atvarious altitudes in association with a variety of habitats. Introduction MaterialandMethods Various lentic and loticwaterbodies.atPach- Most of the lakes in the world and many marhi, Reewa, Morena and Gwalior, situated at other aquatic systems are shallow and thus likely m altitudes of 1067, 318, 300 and 205 above msl to offer sites for submerged macrophylic com- respectively inMadhya Pradesh, were selected for munities (Wetzel 1975). Such aquatic macro- the study. phytes may contribute considerably to the produc- Zygopteran nymphs were collected with the tivity of the water body and provide suitable help of ‘D’ frame net made of nylon cloth (mesh places for hiding, breeding, egg laying, size 80/sq. cm). The nymphs after segregation anchorage, rich oxygen supply and also the food were preserved in 90% alcohol with a few drops supply for all groups of aquatic insects (Krcekcr of glycerin. Identification of these nymphs was 1939, Andrews and Hasler 1943, Cover and Har- based on the characteristics oflast instar nymphal rel 1978, Das and Bisht 1979 and Pandit et al. stages as suggested by Fraser (1957). Water 1985). temperature, dissolved oxygen, pH and chloride The insect and macrophyte communities in were also recorded immediately after collection an aquatic ecosystem remain interdependent of water samples at the sites as per the standard ecologically (Pandit et al. 1985) and therefore, a methods ofAPHA(1975). Macrophytes were also great interest inaquatic insects with regard to their collected along the sampling station and habit and habitat in relation to the environment 5% preserved in formalin. has been shown during recent years (McGaha The range of physico-chemical charac- 1952, Krull 1970, Soszka 1975a, Rosenberg 1986 teristics, distribution of zygopteran nymphs and and Kaushik et al 1990). Observations on the their association with macrophytes have been distribution, habit and habitat of zygopteran given in Tables 1, 2 and 3 respectively. (Odonata) nymphs from various water bodies of Madhya Pradesh in relation to their physico- Results and Discussion chemical characteristics are presented here. The physico-chemical characteristics and abundance of macrophytes influence the distribu- Accepted September 1989. tion of aquatic communities including insects 2 School of Studies in Zoology, Jiwaji University, (Pandit et al. 1985, Kaushik et al. 1990). Out of Gwalior 474 Oil. 1 HABITAT ECOLOGY OF ZYGOPTERAN NYMPHS 401 Table 1 RANGE OFTOLERANCE OFPHYSICO-CHEMICALCHARACTERISTICS INVARIOUS ZYGOPTERANNYMPHS Name ofthe species Altitude (m) Water colour Water Dissolved pH Chloride above mean temperature oxygen (mg/1) sea level (°C) (mg/1) Neurobasis chinensis 1067 Clear 16-24 8.1-11.9 6.0-6.7 19-23 Rhinocypha unimaculata 318-1067 Clear-greenish 24-29 9.5-11.2 6.7-8.0 20-75 Agriocnemispygmaea 205-1067 Clear-blackish 16-24 5.7-11.9 6.0-8.3 23-120 Ceriagrion coromandelianum 205-1067 Clear-greenish 16-29 8.1-11.9 6.0-8.3 23-114 Enallagmaparvum 205-1067 Greenish-blackish 22-26 5.7-10.1 6.0-8. 69-120 Ischnura delicata 205-318 Greenish 21-29 7.4-10.1 7.2-8.2 30-114 I. senegalensis 205-1067 Greenish-blackish 24-30 5.1-10.0 6.0-8.2 74-597 I. rufostigma 300 Greenish 22-24 7.4-10.1 1.2-1.5 69-74 Pseudagrion rubriceps 205-1067 Clear-blackish 16-30 5.1-11.9 6.0-8.3 23-597 P. laidlawi 300-318 Greenish 22-29 8.4-11.2 7.2-8.0 69-88 P. spencei 1067 Clear 24 8.1-9.5 6.5-6.7 19-20 Rhodischnura nursei 300 Greenish 22-24 7.4-10.1 1.2-1.5 69-74 Lestespraemorsapraemorsa 300-1067 Clear-greenish 16-24 8.4-11.9 6.0-7.8 23-74 Copera marginipes 300-318 Greenish 23-29 9.5-11.2 7.9-8.0 75-88 — the water bodies selected Big fall, A—psara and thus decreased pH. These findings are in vihar, Patthar chata and Matsya sarovar the agreement with Irwin and Stevenson (1951). The waterwas comparatively cleanand clearwhilethe alkaline nature (pH 7.2 to 8.3) of water bodies at water in Beehar, Bichhiya, Saank, Asaun, Kuari Rewa, Morena, and Gwalior may be due to ionic rivers and Ganga sagar tank was turbid and light composition and greater photosynthetic activity green in colour due to the growth of of algae (Goel et al. 1986). phytoplankton. Lotus pool, Vivek nagar pond, Chlorides occur naturally in all types of Chandanpura pond and Moti mahal tank were waters. The most important sources ofchloride in pollutedby domestic and municipal wastes, while natural waters are from sewage discharge and J.C. Mill pond received cotton mill effluents. industrial waste and the salts of sodium, potas- Temperature and dissolved oxygen in en- sium and calcium. The lowest chloride value (19 vironments have great bearing on both terrestrial mg/1) was recorded in Patthar chata while the and aquatic communities. Water temperature and highest (597 mg/1) was found in J.C. Mill pond, dissolved oxygen were found to show a wide indicating organic pollution (Table 1). Sharma et range ofvariation in the waterbodies selected for al. (1978) have also reported that increased the study. Highest water temperature and lowest chloride concentration of water is indicative of dissolved oxygenwas measured inJ.C. Mill pond pollution. while lowest temperature and highest dissolved 16 species of zygoptera were identified, out oxygen was observed in Big fall waters. of which 12 species belonging to Coenagriidae Hydrogen ion concentration of natural and 1 species each to Lestidae, Agriidae, Platyc- waters is another important environmental factor. nemididae and Chlorocyphidae were recorded Itsvariations are linked, among othercauses, with from various water bodies in Madhya Pradesh the species compositionand life processes ofcon- (Table 2). The distribution of zygopteran insects stituent biological communities (Jhingran 1982). with regard to altitude indicates that Neurobasis The nature of all water bodies at Pachmarhi was chinensis chinensis and Pseudagrion spencei found to be slightly acidic. It may be due to the were recorded in hilly areas ofPachmarhi located presence of decaying vegetation. This decaying at an altitude of 1067 m, while Copera mar- CO vegetation increased the concentration of 2 ginipes Ischnura delicata I. rufostigma , , , JOURNAL, BOMBAY NATURAL HIST SOCIETY. Vol. SB 402 * (0 O«Jtt * * *1111 + 11 + 111 CcOQAD I O * * lll + + ll + lll I l «>0 * 2 * + II + III + III 3 ! I cfl W 13 CS * * es i 1 I I I t I I °C + 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 *s 5 * o* + + + Ov 1 ! I I I I I I I I I I I iJ £ •c * + ll + ll + + ll a o\ | l l I I 3 I a +I++I cC> 00 + + II + + 00* | | I I i o > •e * + + + c^ t I I I I I I cfl efl IIIIII++SI C/5 * + + VO I I ++ •c | I I I I I I I I I I I I I * 3*- + II + + II + III | | I I I 1e3S ^* + a> ^-» e I I I I I I I ! I I I I I I •8C*1 ^ •S 2 eS lllllillll * + + + I 1 l I I £ I + + 8.5 I I I ! I I I I I I cu-a Si ^25 Tf r a> S£< g " 2 3 J- 1 J’O § Ox a w . M«3 £2 « fj <sw 13 . ii 3 5 > ^ W •oa *u22 ««II<S0 .$&0 2Ud«1 ia ^ 2 c '7|1 ’t3fi s~aQe<$ -•.gv533 ''l52l3'a? 0S»«yiS5-+0;•S0VS2v6«J0 d?2v«,=3«56(5i0"-«Qga3H If-£2I60if”l2.r^l--eV<s6o23r0-lsSq-s§|l1^f_P01082o3«2u 1&£§ogsg1.SsI3&? <c^j<*aaH. ^J«sCxSoUiCO.H*o-Is*I 8L eao ^< dSee J 6« ‘C *C C « -« I | d G PQ c4 1-1 C/5 Ph << Ph 4?0> HABITAT ECOLOGY OF ZYGOPTERAN NYMPHS 403 « g | ,3 O 15 "a . vO i I I I I I I I ! I I I I I as - -I g 8 o vn + + + ^. <u I I I I I I 1 ! I I s 5 *« ? 8 O <^3 i I I I I 1 I ! I I I I <3 2 IS. !§ 8 co 8 jo 1 I ! I t I I I I 1 I I I I ^ vo *o n + + CnL,' I I I I I I I I c'S v. S K c 6C J3 2 2 + + + + + + •C a I 1 I I I I O g NYMPHS *o. <o + + + + I I I l | 1 I I I I I s' ~a 1 ^°: .2 + ZYGOPTERAN ON •$> I I I I I I I I I I I I I o § & + + AND oo I I •2 CO 6o’"l '5 •£3 •§ aO>h + + 0g « t/i I I I ! I I I I I I I MACROPHYTES d «2 0) a n; OF Nd>-> VO I + 1+ +I + I I 1 + 1 I + I a56co’“i>• ^ «o 1 -2 VO + + I I I I ! I I I I I ! I I ASSOCIATION 8 B c sO &C 'C + + + + 60 I I I I I I CO ^ 1 s£8 SHOWING ^ I+l a CO + + + I I I I I I I .5 . 2a dw, + ^H 8 2 I I I I I I I 1 I I I I I I O u 2 J- = «2| + + I I I I I I I I I I -I I -T|l ^ •1 a 4c>o <!> Oh 1o0 ><0 „8{I, _do § . "r '_CCooOl, u§s 5a 'aV5./: "§oa •§8r ^-55SJ.atOa§o>.~I^3aatgo lCwSL•, 5£S>o '•~SC«sS?o -.«632ac co. -OoVOCd-C.Sh ^5 "25a “s§Ka a>aI3 §cs i^| "t53jf--j-^SS2 82*" ^O©n•"g§g COOd>CX>) "^H<aIQsO^s• -.?2512?, 404 JOURNAL, BOMBAY NATURAL HIST SOCIETY, Vol. 88 Pseudagiron laidlawi and Rhodischnura nursei teran nymphs with different species of macro- m m were observed at an altitude of 205 to 318 phytes has been shown in Table 3. Ceriagrion only. coromandelianum Ischnura senegalensis and , Agriocnemis pygmaea, Ceriagrion Pseudagrion rubriceps have been found in as- coromandelianum Enallagmaparvum Ischnura sociation with at least 10 species of macrophytes , , senegalensis Lestes praemorsa praemorsa without any specific preference. Copera mar- , , Pseudagrion rubriceps and Rhinocypha ginipes andRhinocypha unimaculata have strong unimaculata were widely distributed from higher affinity for Vallisneria spiralis and Eichhornia to lower altitudes. crassipes respectively, whileIschnura rufostigma Copera marginipes Ischnura rufostigma was always found along with decaying vegeta- , , Lestes praemorsa praemorsa Neurobasis tion. However, Rhinocypha unimaculata and , chinensis chinensis Pseudagrion laidlawi P. Ceriagrioncoromandelianum were also observed , , spencei Rhinocypha unimaculata and clingingto rocks andalgal growthinwaterrespec- , Rhodischnura nursei indicated their preference tively. for lotic water, while other species were present Odonatan nymphs are believed to inhabit in both lotic as well as lentic waters. clean waters with sufficient oxygen (Tonapi Pseudagrion rubricepswas observed inboth 1980). This is, however, not true in the present clean and polluted waters and thus accepted a study. The zygopteran nymphs have been ob- wide range of water temperature and chloride served from clean to polluted waters and were concentration (Table 1). Ischnura senegalensis found to prefera variety ofmacrophytic habitat as was found in waters with high concentration of has been suggested by Roback (1974), Hynes chloride. Hynes (1974), Roback (1974) and Perry (1974) and Perry (1981). (1981) have also reported similar observations Acknowledgements regarding the tolerance for a wide range of physico-chemical characteristics of water by This article is dedicated to the late Prof. J. speciesofIschnura.Neurobasischinensischinen- B__ahadur, the then Head of S•chool of Studies in sis andPseudagrion spencei were collected from Zoology, and Rector, Jiwaji University, Gwalior. hilly lotic waters with slightly acidic pH and low We are grateful to him for providing necessary We concentration of chlorides (Table 1). laboratory facilities. are also thankful to the Since macrophytes provide food and shelter U.G.C. for financial assistance and to Dr J.P. to many macroinvertebrate communities inwater, Kaushik, School of Studies in Botany, for iden- the formerhavebeen found to harbourzygopteran tification of macrophytes. nymphs also. The association of various zygop- References Andrews, J.D. & Hasler, A.D. (1943): Fluctuations in the R. Zool. Soc. N.S.W.HandbookNo. 12. & animal populations ofthelittoral zone in lake Nendota. Goel, A.K., Khatarkar, S.D., Kulkarni, A.Y. TrtvedI, Trans. Wis.Acad. Sci.ArtsLet. 35: 175-185. R.K. (1986): Limnological studies ofa few freshwater Apha(1975): Standardmethods for theexamination ofwater, bodies in South Western Maharashtra with special ref- sewage and industrial waste. (14th ed.). American erence to their chemistry and phytoplankton. Indian Public Health Association, New York. Poll. Res. 5(2): 79-84. & Cover, E.C. Harrel, R.C. (1978): Sequence of coloniza- Hynes, H.B.N. (1974): The biology ofpollutedwaters. Univ. tion, diversity, biomass and productivity of macro-in- Toronto Press, Toronto. & vertebratesonartificialsubstrates ina freshwatercanal. Irwin, W.H. Stevenson, J.H. (1951): Physicochemical Hydrobiologia 59: 81-95. nature of clay turbidity with special reference to & Das, S.M. Bisht, R.S. (1979): Ecology ofsome hemiptera clarification and productivity of impoundmentwaters. and Coleoptera of Kumaun lakes. Ind. J. Ecol. 6(1): OklaAgr. Mech. Coll. Bull. 48: 1-54. 35-40. Jhingran, V.G. (1982): FishandFisheriesofIndia. Hindustan A Fraser, F.C. (1957): reclassification ofthe order Odonata. Publishing Corporation (India), Delhi. HABITAT ECOLOGY OF ZYGOPTERAN NYMPHS 405 & Kaushik, S., Sharma, S., Saxena, M.N. Saksena, D.N. Roback, S. (1974): Insects. In: Pollutional Eology of fresh (1990): Habitatecology ofAnisopterannymphs in cer- water invertebrates (Eds.) C.W. Hartand S.L.H. Fuller. tainwaterbodies ofMadhyaPradesh. ActaHydrochim. Academic Press, NewYork. hydrobiol. 18(4): 443-447. Rosenberg, M. D. (1986): Importance of insects in environ- A Krecker, F.H. (1939): comparative study of the animal mental impact assessment. Environmental Manage- population of certain submerged aquatic plants. Ecol- ment10(6): 773-783. & ogy20: 553-562. Sharma, K.P., Goel, P.K. Gopal, B. (1978): Limnological Krull,J.N. (1970): Aquaticplantmicroinvertebrateassocia- studies of polluted fresh water I. Physico-chemical tions and water fowl. J. WildlifeManage. 34(4): 707- characteristics. Int.J. Ecol. Environ. Sci. 4: 89-105. 718. Soszka, G.J. (1975a): The invertebrates on submerged mac- McGaha,YJ. (1952): Thelimnological relationsofinsectsof rophytes in three Masurian lakes. Ekol. Poll. 23 (3): certainaquaticfloweringplants. Trans.Am.Microscop. 371-391. Soc. 71(4): 355-381. Soszka, G.J. (1975b): Ecological relations between inver- & Pandit, A.K., Pandit, S.N. Kaul, V. (1985): Ecological tebratesandsubmergedmacrophytesinthelakelittoral. relations betweeninvertebrates andsubmerged macro- Ekol. Poll. 23(3): 393-415. phytes in two Himalayan lakes.Poll. Res. 4(2): 53-58. Tonapi,G.T. (1980): FreshwateranimalsofIndia. Oxfordand Perry,T.E. (1981): Dragonfliesand damselflies(Odonata) of IBH Publishing Co., New Delhi. theGrandriversystem,NortheasternOhio, 1974-1978. Wetzel, R.G. (1975): Limnology. W.B. Saunders, Philadel- OhioJ. Sci. 81(3): 125-131. phia.

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