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www.sciencevision.org Sci Vis Vol 14 Issue No 1 January-March 2014 Research Note ISSN (print) 0975-6175 ISSN (online) 2229-6026

Preliminary assessment on water quality and biodiversity in and around in southern ,

Lalmuansangi and H. Lalramnghinglova*

Department of Environmental Science, , 796004, India

Received 12 January 2014 | Revised 13 March 2014 | Accepted 17 March 2014

ABSTRACT

The present study was conducted during March to September 2013 at Palak Dil, the largest lake in Mizoram, which is located between 92°52’-92°55’E longitude and 22°10’-22°13’N latitude in the remote part of Mara Autonomous District Council in the southern part of Mizoram near the bor- der of Indo-Burma hotspots region. The Palak Dil is a nationally recognized natural lake and the catchment area is approximately 18.5 sq km and the total water body is around 1.5 sq km only. The water quality, viz. temperature, pH, total dissolved solids, electrical conductivity, acidity, alka- linity, dissolved oxygen, biological oxygen demand, carbon dioxide, total hardness, chloride, nitrate, phosphate and iron were analyzed and found that all the parameters are within the standard limits given by various scientific agencies, but the water is not pure as expected. This can be accrued to the developmental works that were undergoing around the lake. Study on biodiversity was carried out by field enumeration, collection and identification of the flora and fauna. It was observed that the ecosystem in which birds and animals living there is gradually degrading due to anthropogenic activity and developmental works.

Key words: Assessment; water quality; biodiversity; Palak Dil; Mizoram.

INTRODUCTION munities are highly dynamic as they are located at the interface of terrestrial and aquatic ecosys- Lakes are one of the important natural wet- tem. The species richness and the biodiversity in lands. Wetlands are the transitional zones that such area are quite high, as they offer special occupy the intermediate position between dry habitat for many macrophytes, planktons, inver- land and open water. They encompass diverse tebrates, and vertebrates. The richness is mainly and heterogeneous habitat ranging from rivers attributed to the spatial heterogeneity, that is, flood plains and rain fed lakes to swamp, estuar- the greater the number of niches the greater is ies, and salt marshes.1Generally, wetlands com- the opportunity for successful invasion by spe- cies. Due to developmental activities and needs Corresponding author: Lalramnghinglova for human consumption, the ecology of wet- Phone: +91-9436144392 lands is depleting in different ways. Mizoram is E-mail: [email protected]

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Lalmuansangi and Lalramnghinglova

one of the north-eastern States of India having a is unique and pristine in nature and situated in a total geographical area of 21,081 sq km with a remote part of the Mara Autonomous District small population of 1,091,014, the density being Council in in the international 52 per sq km.2 Developmental works that were border of Indo-Burma hotspots region and falls going-on can severely affect the ecological as- under the Palak Wildlife Sanctuary of Mizoram pects of the wetland. Palak Dil is a small but a (Fig. 1). The distance from Aizawl is 390 km to recognized national wetland in Mizoram. Lakes the south and 97 km from Saiha, the district are locally called “Dil”. There are just a few headquarters. The catchment area is approxi- such „Dil‟ which scattered here and there, but mately 18.5 sq km and the total water body is they are tiny pools or marshy depressions, such around 1.5 sq km. The Mara community called as, Rengdil (0.6 sq km radius), Rungdil (0.75 sq the lake as “Pala Tipo”. Pala Tipo is the only km radius), Diltlang (0.5 sq km radius), natural lake in Mizoram and is fairly rich in Hmawngbu (0.7 sq km radius) and Tamdil (0.8 flora and fauna. The lake lies in between sq km radius).3 and Tokalo villages; and the Tokalo Village Council (the grass root governance institution) is MATERIALS AND METHODS responsible for regulating the use of the lake as well as the land and forests surrounding it. Be- Study site yond the lake and towards Myanmar lie large swathes of forests that are exposed to very lim- Palak Dil is located between 92°52‟- 92°55‟E ited and low intensity local use. longitude and 22°10‟-22°13‟N latitude. The lake Water quality

The water samples were taken from five sam- pling sites, viz., Site-1 (East), Site-2 (North), Site-

Figure 1. Location map of Palak Dil. Figure 2. Photograph of Palak Dil.

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3 (West), Site-4 (South) and Site-5 at the centre ume which was raised by construction of 1m of the lake every two months from March- Sep- high retention wall above the natural water vol- tember 2013. The American Public Health ume during rainy season which decreases the Agency (APHA) 1998 was employed for analyz- ion concentration in the water. The same reason ing the water quality.4 All the water samples was found with the results of TDS which de- were tested in the field by Hanna Soil & Water creases from March to September. Acidity was Analysis Kit, except iron and biological oxygen found to be lowest in May-June. Dissolved oxy- demand which were tested in the laboratory of gen was almost same during the sampling pe- PHE Department, Saiha. riod, but the reading was low rather than ex- pected. However, all the parameters were found Biodiversity within the standard limits given by World Health Organization. Biodiversity was studied by field investiga- tion, collection and identification of the flora Biodiversity and fauna during the study period. Plant collec- tion and processing was done using standard Biodiversity was studied by field investiga- methods given by Bridson and Forman,5 Jain tion, collection and identification of the flora and Rao6 and Womersly7. Zoological specimens and fauna during the study period. were identified with the help from Department of Zoology, Mizoram University, Aizawl, and Flora Zoological Survey of India, Kolkata. The lake is bounded by tropical evergreen RESULTS AND DISCUSSION mixed with moist deciduous forests. The flora in and around the Palak Dil was reported by Lal- Water quality ramnghinglova et al.8 The dominant and emer- gent species is Dipterocarpus retusus. The highly The water sample collected from five differ- valued timber yielding species include Diptero- ent sampling sites were analyzed by using port- carpus turbinatus, Terminalia myriocarpus, Gmelina able Hanna Water Testing Kit for the physico- orborea; ethno-medicinal plants include Bombax chemical properties of water, viz. temperature, insigne, Carralia brachiata, Dendroxnide sinuata, pH, electrical conductivity (EC). Total dissolved Anacolosa cresipes, Bacauria sapida, Psychotria calo- solids (TDS), acidity, alkalinity, carbon dioxide, carpa and Buettneria aspera, Pasderia foetida, Mi-

(CO2) dissolved oxygen (DO), biological oxygen kania micrantha among climbers; and, Trapa demand (BOD), total hardness, nitrate, phos- natans var. bisinosa, Hydrilla and tall reeds among phate, chloride and iron. All the water samples macrophytes. The common plant species are were tested at the field itself except iron biologi- presented in Table 2-5. cal oxygen demand for want of appropriate equipments but were tested in the laboratory. Fauna The average reading taken from all the sites dur- ing March–September 2013 is presented in Ta- Robertson,9 a Scottist naturalist reported the ble 1, and histograms showing the physical and avifauna of Palak Dil in 2006. The list of birds chemical parameters in Fig. 3 and 4. include Buceros bicornis, Anthracoceros albirostis, Temperature decreases from April due to A.malabaricus, Garullex leucoluphus, Polyplectron change in season and decrease in surface tem- bicalcaratum, Trachybaptus ruficollis, Gallus gallus, perature. There was a slight decrease in pH and Ardeo grayii, Porphrycio porphyrio, and Upupa alkalinity possibly due to increase in water vol- epops. Migratory birds used to visit this place;

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Table 1. Water quality of Palak Dil (April- September 2013). n=5. Months Parameters March– May– July– April June Sep Temperature °C 32 30.2 29.4 pH 8.0 8.3 6.5 Electrical Conductivity 70 77 57 TDS ppm 51.03 39 28 Acidity mg/l 2 1 2 Alkalinity mg/l 8 6 4 Carbon dioxide 2 4 4 Figure 3. Graph showing physical parameters. Dissolved 5.8 5.2 5.6 oxygen Biological 3.4 3 3 oxygen demand Total hardness 6 8 8 Nitrate mg/l >47 >47 >47 Iron mg/l 1 1 1 Chloride 8 10 10 Phosphate 0.42 0.46 0.44

Figure 4. Graph representing chemical parameters.

Table 2. Common tree species in and around Palak Dil. Scientific name Family Local name Albizzia procera Roxburgh Mimosaceae Kangtek Artocarpus chaplasha Roxburgh Moraceae Tatkawng Artocarpus lakoocha Roxburgh Moraceae Theitat Chukrasia tabularis Anthony Juss Melaiceae Zawng-tei Dipterocarpus retusus Blume Dipterocarpaceae Thingsen Dipterocarpus turbinatus Gaertn C.F Dipterocarpaceae Lawngthing Dendrocnide sinuate Blume Urtacaceae Thakpui Duabanga grandiflora (DC.) Walpers Sonneratiaceae Zuang Ficus sp. Moraceae Hmawng Gmelina arborea Roxburgh Verbenaceae Thlanvawng Haematocarpus validus Miers Menispermaceae Theichhungsen Lagerstromia speciousus Persoon Lythraceae Thlado Mesua ferrae Linneus Clusiaceae Herhse Michelia champaca Linneus Magnoliaceae Ngiau Schima wallichii Choisy, J.D Theaceae Khiang Terminalia myriocarpa Van Heurck & Mueller Argoviencis Combrateceae Char Tetrameles nudiflora R. Br. Datiscaceae Thingdawl Toona ciliate Roemer, M.J Meliaceae Teipui Willughbeia edulis Roxburgh Apocyanaceae Vuakdup

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Table 3. Climbers and herbs. Scientific name Family Local name Bacaura ramniflora Loureiro Euphorbiaceae Pangkai Clerodendrum infortunatum Linnaeus Verbanaceae Phuihnamchhia Cheilocostus speciousus C.Specht Costaceae Sumbul Homalomena aromatic Schott Araceae Anchiri Mikania micrantha Kunth Compositae Japanhlo Pandanus pseudofoetidus Martelli Pandanaceae Ramlakhuihthei Phrygnium placentarium Blume Marantaceae

Table 4. Cane species. Scientific name Family Local name Arenga pinnata Merrill Arecaceae Thangtung Bambusa tulda Roxburgh Poaceae Rawthing Borassus flabellifer Linnaeus Arecaceae Siallu Calamus erectus Roxburgh Arecaceae Thilthek Calamus flagellum Griffith,W. Reptiles Palmae HruipuiFamily Calamus tenuis Roxburgh Arecaceae Thilte Calotes vesicolor Agamidae Caryota mitis Loureiro Arecaceae Meihle Chrysopelea ornate Culubridae Caryota urens Loureiro Arecaceae Tum Cosymbotus patyrus Gekkonidae Daemonorops jenkinsiana Griffith,W. Arecaceae Raichhawk Draco maculates Agamidae Dendrocalamus longispathus Kurz, W.S Poaceae Rawnal Hemidactylus frenatus Gekkonidae Salaca secunda Griffith,W. Arecaceae Hruitung H. garnoti Gekkonidae Manouria emys Testunidae Table 5. Aqua flora. Ptychozoon lionotum Gekkonidae Scientific name PtyctolaemusFamily gularis LocalAgamidae name Eichhornea sp. PythonPontederiaceae reticulates DumparBoidae Hedychuim Gracile Roxburgh RamphotyphlopsZingiberaceae braninus TyphopidaeAichhia Lasia spinosa Thw. RhapdophisAraceae subminiatus ZawngzangColubridae c.cf.alticristastaus Table 6. The common animals of Palak Wildlife Sanctuary. Varanus bengalensis Scinidae Reptiles Family Birds Calotes vesicolor Agamidae Anthraceros alborosthris Bucerotidae Chrysopelea ornate Culubridae Buceros bicornis Burcerotidae Cosymbotus patyrus Gekkonidae Ceyx erithacus Alcenidae Draco maculates Agamidae Cyprinus sps. Cyprinidae Hemidactylus frenatus Gekkonidae Cuculus sp. Cuculidae H. garnoti Gekkonidae Dendrocygna janica Dendrocygnidae Manouria emys Testunidae Gallinula chloropus Podicipitidae Ptychozoon lionotum Gekkonidae Gallus gallus Phasianidae Ptyctolaemus gularis Agamidae G. chloropus ralidae Python reticulates Boidae Loriculus vernalis Psittacidae Ramphotyphlops braninus Typhopidae Meglaima viren Meglaimidae Rhapdophis subminiatus Colubridae Nyctyornis athertoni Meropidae c.cf.alticristastaus Picus chlorophis Picidae Varanus bengalensis Scinidae Podiceps ruficollis Podicipitidae Birds Polyoectron bicalcaratum Phasiandae Anthraceros alborosthris Bucerotidae Common Animals species Buceros bicornis Burcerotidae Berylmys boversi Muridae 43Ceyx erithacus ScienceAlcenidae Vision © 2014 MAS.Callosciurus All rights reserved erythracus Sciuridae Cyprinus sps. Cyprinidae Capricornis rubidus Bovidae Cuculus sp. Cuculidae Hoolock gibbon Hylobatidae Dendrocygna janica Dendrocygnidae Macaca spp. Cercopithecidea Gallinula chloropus Podicipitidae Muntiacus vaginalis Cervidae Gallus gallus Phasianidae Pardofelis marmolata Felidae G. chloropus ralidae Prionai bengalensis Felidae Loriculus vernalis Psittacidae Rusa unicolor Cervidae Meglaima viren Meglaimidae Ratufa bicolor Sciuridae Nyctyornis athertoni Meropidae Sus scrofa Elephantidae Picus chlorophis Picidae Tamiops mmacclellandi Sciuridae Podiceps ruficollis Podicipitidae Polyoectron bicalcaratum Phasiandae Common Animals species Berylmys boversi Muridae Callosciurus erythracus Sciuridae Capricornis rubidus Bovidae Hoolock gibbon Hylobatidae Macaca spp. Cercopithecidea Muntiacus vaginalis Cervidae Pardofelis marmolata Felidae Prionai bengalensis Felidae Rusa unicolor Cervidae Ratufa bicolor Sciuridae Sus scrofa Elephantidae Tamiops mmacclellandi Sciuridae

Reptiles Family Calotes vesicolor Agamidae Chrysopelea ornate Culubridae Cosymbotus patyrus Gekkonidae Draco maculates Agamidae Hemidactylus frenatus Gekkonidae H. garnoti Gekkonidae Manouria emys Testunidae Ptychozoon lionotum Gekkonidae Ptyctolaemus gularis Agamidae Python reticulates Boidae Ramphotyphlops braninus Typhopidae Rhapdophis subminiatus Colubridae c.cf.alticristastaus Varanus bengalensis Scinidae Birds Anthraceros alborosthris Bucerotidae Buceros bicornis Burcerotidae Ceyx erithacus Alcenidae Cyprinus sps. Cyprinidae Cuculus sp. Cuculidae Dendrocygna janica Dendrocygnidae Gallinula chloropus Podicipitidae Gallus gallus Phasianidae G. chloropus ralidae Loriculus vernalis Psittacidae Meglaima viren Meglaimidae Nyctyornis athertoni Meropidae Picus chlorophis PicidaeLalmuansangi and Lalramnghinglova Podiceps ruficollis Podicipitidae Polyoectron bicalcaratum Phasiandae Common Animals species halt their visitations. This leaves the area Berylmys boversi Muridae marshy where Eichhornea crasipes grows on it. Callosciurus erythracus Sciuridae The area is very odorous and makes the water Capricornis rubidus Bovidae very dirty. The pathways, rest house and view- Hoolock gibbon Hylobatidae points that were made near the lake also pollute Macaca spp. Cercopithecidea the water. Apart from the terrestrial vegetation, Muntiacus vaginalis Cervidae aquatic plants mainly hydrophytes are floating Pardofelis marmolata Felidae on the lake surface. These hydrophytes played a Prionai bengalensis Felidae significant role in the lake ecology, since the Rusa unicolor Cervidae roots of these species (Trapa natans var. bipinosa) Ratufa bicolor Sciuridae acts as purifier of water, thus preventing the wa- Sus scrofa Elephantidae ter from ferruginous. Alien species of fish intro- Tamiops mmacclellandi Sciuridae duced to the lake competes with the indigenous species. The indigenous species losses their over 70 species of birds were recorded from the chance of survival, so, they are almost extinct area during a three day IBA survey,10 while the from the lake. A couple and a calf of wild ele- presence of 136 species of avifauna and 42 spe- phants that were survived in 2003 no longer ex- cies of mammals including rare and threatened ists in the sanctuary in 2013. Human-induced primates like the Phayre‟s leaf monkey alteration of the ecosystems disrupt the ecologi- (Trachypithecus obscurus phayrei) and the Western cal balance. In situ biological conservation and hoolock gibbon (Hoolock hoolock hoolock).11 Rep- eco-restoration is paramount important and tiles such as snakes and lizards and amphibians need of the hour before it further deteriorates the were found near the lake. A variety of fish exists wetland, biodiversity and bio-aesthetic value. in the lake, some of which were locally found, The present investigation provides a prelimi- others being introduced. The lake is abounding nary data which laid upon a base line data for with reeds, fishes and few crabs. Bear, tiger, monitoring the water quality and the biodiver- deer, wild pig are common animals. In sity of the sanctuary. Mizoram, Palak Dil is the only abode of aquatic birds, with the wild duck of few species. Com- SUGGESTIONS AND RECOMMENDATIONS mon animals are presented in Table 6. 1) The most important thing is to lower the CONCLUSIONS water level and try to restore the original ecosystem by nature conservation and re- Palak Dil has a unique feature of biodiversity introduction processes. richness which differs from a survey conducted 2) Construction of alternative approach route by Lalramnghinglova in 2003 and 2006 that the to Miepu and Tokalo villages through lake losses its value as the water quality and bio- Border Development Works is recom- diversity are degraded. The water quality was mended with prior consent by giving expected to be very pure but it was found that awareness to the local people. the water quality is degrading due to develop- 3) Replacement of exotic fish species by re- mental works and human interventions. Migra- introduction of indigenous fish species. tory birds which lodged on Ficus trees growing 4) Rest House is very near from the lake; in the lake which were died because of raising human sound and music played by stu- up of the water volume which submerged the dent- visitors will surely chase away the Ficus trees retarded the visits of migratory birds. animals, so it should be prohibited. More research is needed to see that if this is the 5) Settlements, if any be made, at least half a keystone species for migratory birds that may kilometer away from the lake is desirable

Science Vision © 2014 MAS. All rights reserved 44 Preliminary assessment on water quality and biodiversity in and around Palak Dil

to avoid discrimination to the animals. 3. Personal communication of Lalramnghinglova H (2013). 6) Many on-going developmental works de- Presentation on Biodiversity conservation: overview, Aug. grade the environment, pollute the water 29, 2013. quality and disturb the unique biodiver- 4. Anonymous (1998). Standard methods for the examination of water and waste waters. (20th edition) American Public sity. So, preserving the lake and its area in Health Association, Washington DC. its natural entity would be most desirable and attractive to the visitors to fetch earn- 5. Bridson R & Forman L (1999). The Herbarium Handbook (3rd ed.). Royal Boani Gardens, Kew, p. 334. ings. 6. Jain SK & Rao RR (1977). Handbook of Field and Herbarium 7) Engagement of local tourist guides can Methods. Today & Tomorrow’s Printers and Publishers, generate better income than the disastrous New Delhi, p. 157. socio-economic ruin of the retaining wall 7. Womersley J S (1981). Plant Collection and Herbarium Devel- of the lake. opment - A Manual. FAO Plant Production and Protec- 8) If development works must go on, na- tion Paper 33, Rome, p. 137. tional eco-tourism norms should be fol- 8. Lalramnghinglova H, Lalnuntluanga & Jha LK (2006). A lowed, keeping in mind the future genera- survey report of Ngengpui and Palak Dil in the southern tions; and try to manage with least de- part of Mizoram. Indian Forester,132, 1282–1291. struction of the natural beauty. 9. Robertson A (1995-96). Report on a field trip to 9) Clearance of the peripheral region of the Mizoram, List of birds species observed, submitted to the lake beyond 2 m is not advocated. Environment & Forest, , Ai- zawl, pp.1–20. 10. Birand A & Pawar S (2001). A survey of birds in North- EFERENCES R east India. Final Report, Center for Ecological Research and Conservation, Mysore, India. 1. Wetzel RG (2006). Limnology: Lake and River ecosystems (Third Edition). Academic Press, Santiago, California. 11. Roy D & Choudhury S (2007). Prioritisation of biodiver- sity rich sites in the State of Meghalaya. In: Setting Biodiver- 2. Anonymous (2012). Statistical Handbook Mizoram. Direc- sity Conservation Priorities for India: Vol. 1 & 2. torate of Economics & Statistics, Mizoram:Aizawl, p.1.

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