Investigation on Diversity, Distribution and Periodicity of Fungi in Shanthi Sagar Lake of Davangere District, Karnataka, India

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Sengupta, M. and Dalwani, R. (Editors). 2008 Proceedings of Taal 2007: The 12th World Lake Conference: 2009-2013 Investigation on Diversity, Distribution and Periodicity of Fungi in Shanthi Sagar Lake of Davangere District, Karnataka, India Rajanaika, Prasad. D and Ramlingappa Department of Applied Botany, Kuvempu University, Shankaraghatta - 577 451, Karnataka, India E-mail: Rajump.nayak@gmail.com ABSTRACT Fresh water lake ecosystem is an ideal home for the increased biological activity of diversified microbes. Shanti Sagar is one of the biggest fresh water lake in Karnataka situated in Davangere district of Karnataka. The lake comes under tropical climatic conditions. An investigation was conducted on this lake to study the fungal composition, their diversity, distribution and periodicity for two years. For comprehensive study four sampling stations were identified in the lake, from this stations water samples and decaying plant materials were collected at monthly intervals, then, they were subjected to the laboratory analysis, Isolation of fungi has done from the water and decaying plant material by following suitable isolation methods viz, Bating and Incubation methods. Totally 2 species of fungi were isolated and identified, which were belongs to two main fungal groups viz, Aquatic and Aero aquatic fungi. Totally 12 major aquatic fungal species were recorded which includes, Achlya debaryana, Achlya orion, Allomyces arbuscular, Allomyces anamalus, Achlya recurva, Achlya prolifera, Aphanomyces laevis, Pythium debarianum, Pythium elangatum, Saprolegnia ferax, Saprolegnia parasitica, and Saprolegnia terrestries. Totally 14 major aero aquatic fungal species were isolated and identified, which includes, Alternaria alternata, Aspergillus flavus, Aspergillus fumigatus, Aspergillus niger, Chaetomium globosum, cladosporides, Fusarium solani, Fusarium equisiti, Fusarium oxysporum, Fusarium semitectum, Penicillium citrinum, Rhizopus nigricans, Trichoderma harzianum, and Trichoderma viride. The percent occurrence, distribution and periodicity of aquatic fungi and aero aquatic depends on the physico-chemical factors of the water and also they varies from one season to another season. Keywords: Aquatic fungi, Aero aquatic fungi, Fresh water bodies and Lake ecosystem. INTRODUCTION Ecology of water fungi has not attained the degree of prominence as the ecology of soil fungi. The qualitative composition of the fungal population in water is now becoming fairly well known. Heterotrophic organisms are usually present in natural water in direct proportion to the physico-chemical nature of aquatic environment. A wide variety of aquatic fungi such as chytridiomycetes, Saprolegniales and peronosporales are found in fresh water. Till 1942, whatever information available it was mainly concerned to oosporic phycomycetes or water molds which till then were regarded as true water fungal flora. In 1942, Ingold reported a distinctive and abundant flora of conidial fungi as aquatic hypomycetes. In the same time, Glen-Bott (1951) recognized another assemblage of aquatic hypomycetes as aero aquatic fungi with the mycelium in submerged decaying leaves. Cooke (191, 193) divided the fungi encountered in fresh water in to two principal groups, The Hydro fungi which require the presence of water to complete their life cycle and geo-fungi or typical soil fungi which were not specially adopted to aquatic existence, but they might be found in water because of adequate supply of nutrients, these were regarded as Facultative aquatic fungi. Fresh water bodies receives various category of waste materials, many of them are organic in nature. These organic wastes are easily degraded by microbes like fungi and bacteria, naturally present in river water. Hunter (1975) studied the water molds and their role in the degradation of wastes in the river great Ouse and its tributaries. The various wastes accumulated in the water bodies creates several problems and are responsible to kill aquatic fungi, which are useful for the bio-degradation process. Thompstone and Dix (1985) Identified 25 isolates of Achlya and Saprolegnia sp. Singh (1982) studied the distribution, occurrence and cellulose decomposition of the five species of aquatic hypomycetes. With this reason the investigation on diversity distribution and periodicity of fungi of Shanthi sagar lake of Davangere district, Karnataka, India was considered for the present investigation. In the present study, the diversity,

Distribution and periodicity of aquatic fungi has been made. MATERIALS AND METHODS To study the distribution and occurrence of aquatic fungi of shanthi sagar lake, water and organic waste material s like twigs, decaying aquatic plant parts were collected from lake. Water is collected from 2 liters plastic cans and plant materials were collected in polythene bags of 1kg capacity from the identified stations at monthly intervals from February 2005 to January 2007. Isolation of fungi was carried out by following isolation techniques viz, Incubation and bating techniques in the laboratory. In incubation method, decaying leaf litter, aquatic plant parts, woody materials were collected from the lake. The materials were broken into small pieces and incubated on wet blotters in petriplates, The materials along with petriplates were kept in the incubator under laboratory condition (22+ 2º temperature) for about 8 days. In bating method, sterilized broken pulses and pieces of blotter papers were used as fungal bates. The known quantity of water was taken in the sterilized petriplates, then broken pulses and paper pieces of blotter paper were added. The plated materials along with petriplates were kept for incubation under laboratory conditions (22+2º temperature) for about 7 to 8 days, at the end of the incubation period the colonized fungi were found on the incubated materials. Identification and characterization of fungi were made as per the key and monographs. Culturing of few aquatic and extra-aquatic was done in the laboratory on cornmeal and potato dextrose agar media. Calculation of total and individual fungal occurrence were made at the end. All calculation were made in terms of percentage by following simple formula. Number of samples in which fungi appeared Total number of samples plated The individual fungal occurrence of each fungal species was calculated by using following simple formula. RESULTS AND DISCUSSION 100 Individual fungal species that appeared in the samples Total number of colonies of all fungi in the samples 100 The detailed study with regard to the distribution, periodicity and percentage of occurrence of different groups of fungi occurred in four identified stations in Shanthi Sagar Lake has been discussed below. There are four different sample collection stations (Station-I, Station-II, Station-III, Station-IV) were identified in the lake based on the extent of pollution and Anthropogenic activities. The distribution of aquatic fungi and extra aquatic fungi of all four stations were discussed below. From all the four sampling station, a total of 2 species belongs to 13 genera of both aquatic and extra aquatic fungi were isolated. Out of 2 species, 12 species belongs to aquatic phycomycetes, species belongs to Ascomycetes, 2 species belongs to Zygomycetes and 11 species belongs to Deuteromycetes. Totally 12 species of aquatic fungi belonging to 7 genera are encountered in all the four stations, which includes: Achlya debaryana, A. Orion, A. prolifera, A. recurva, Allomyces arbuscular, A. anamalus, Aphonomyces laevis, Pythium elangatum, P. debarianum,saprolegnia ferax, S. parasitica and S. terrestries. The two yearly average percentage of distribution of individual fungi summarized in the Table-I. The isolated species of extra Aquatic fungi from all the four station belongs to three fungal classes like Deuteromycetes, Ascomycetes and zygomycetes, they comprise about 8 genera and 14 species and includes Alternaria alternata, Aspergillus flavus, A. fumigatus, A. niger, Chaetomium globosum, cladosporides,fusarium oxysporum, F. solani, F.equisiti, F. semitectum, Penicillium citrinum, Rhizopus nigricans, Trichoderma viride and T. harzianum. The two yearly average percentage of distribution of extra aquatic fungi has been given in the Table-3. The data obtained from the analysis regarding distribution of aquatic fungi and extra aquatic fungi of all the four stations reveals that, maximum percentage of fungal distribution was recorded in the station I, when compared to other three stations (station-ii, station III and station -IV). The higher fungal incidence that, occurred in station-i is because of unpolluted nature of water and less anthropogenic activities encountered in that station. Where as the lowest percent distribution of aquatic and extra aquatic fungi was recorded in the station-iii. This is due to the polluted nature of the water and increased anthropogenic activities in that station(table-1 and 3). 2010

Seasonal variation of aquatic and extra aquatic fungi of all the four station were recorded in the Table- 2 and 4. The data obtained during the present investigation reveals the maximum fungal distribution was recorded during the monsoon period followed by pre-monsoon periods in all the four stations. But comparatively less percentage of fungal incidences was recorded during post monsoon period (Table-2 and 4). The occurrence of maximum percentage of aquatic and extra aquatic fungi during monsoon period is probably due to the occurrence of low temperature, high organic load and low ph of the water. Table-1: Percentage of distribution of aquatic fungi in different stations of Shanthi Sagar Lake Station-I Station-II 1 Achlya debaryana 33.9 30.5 32.5 22.7 19.15 20.9 2 Achlya orion 2.2 18. 22.4 13. 15.8 14.7 3 Allomyces arbuscular 1.8 14.7 15.75 10.8 9.5 10.15 4 Allomyces anamalus 14.0 15. 14.8 8.0 9. 8.8 5 Achlya recurva 5.3 4.5 4.9 4.0 3.5 3.7 Achlya prolifera.9 7.8 7.3 4.7 3.8 4.2 7 Aphanomyces laevis 11.4 10.3 10.8 11.0 10. 10.8 8 Pythium elangatum 25.7 21.8 23.7 19.4 1.5 17.9 9 Pythium debarianum 33.1 30.7 31.9 18.2 1.8 17.5 10 Saprolegnia ferax 23.2 21.0 22.1 14.3 12.5 13.4 11 Saprolegnia parasitica 1.7 14. 15. 10.2 9.8 10.0 12 Saprolegnia terrestries 10.5 7.8 9.15.9 5.8.35 Station -III Station-IV 1 Achlya debaryana 20.5 1. 18.5 20. 23.5 23.05 2 Achlya orion 14.5 17.2 15.58 1.85 15.0 15.9 3 Allomyces arbuscular 10.9 10.03 10.4 13.2 1.3 14.75 4 Allomyces anamalus 8.2 7. 7.9 12.43 14.2 13.31 5 Achlya recurva 5.2 4. 4.9 5.0 5.5 5.25 Achlya prolifera 4.23 3.5 3.85 5.2.1 3.8 7 Aphanomyces laevis 11.2 10.9 11.08 10.5 11.3 10.9 8 Pythium elangatum 17.4 15.2 1.3 21.2 20.0 20. 9 Pythium debarianum 1.8 17. 17.2 18.3 1.7 17.5 10 Saprolegnia ferax 12. 10.5 11.5 14.3 12.5 13.2 11 Saprolegnia parasitica 10.1 9.2 9. 10. 11.5 11.05 12 Saprolegnia terrestries.7 4.35 5.5 8.0 7.5 7.7 Table2: Seasonal average values of distribution of aquatic fungi in different stations of Shanthi sagar lake Station-I Station-II Station -III Station-IV Species of Fungi No. PM M PO-M PM M PO-M PM M PO-M PM M PO-M 1 Achlya debaryana 30.5 42.0 29.4 20.5 28.2 19. 19.0 24.0 18.5 24.3 25. 18.0 2 Achlya orion 27.3 31. 19.7 12.4 18.0 10.5 15.5 1.2 14.0 1.3 19.05 15.2 3 Achlya prolifera.9 10.5.5 5.0 8.8 4.5 5.2.3 2.3 5.2 7.1 3.8 4 Achlya recurva 4.5 7. 4.0 3.5.0 2.5 3.0 5.9 2.0.0 7.5 4.5 5 Allomyces arbuscular 1.5 18.4 15.5 10. 11.3 10.5 10.5 12.8 9.5 12.0 15.8 11.0 Allomyces anamalus 12.7 18.3 11.0 7.2 10.5.5 8.2 9.0 7.5 13.3 13.5 10.5 7 Aphanomyces laevis 12.2 19.5 10.5 10.5 12.5 10.0 11.3 13.0 9.5 10.3 11.5 9.8 8 Pythium elangatum 25. 29.0 22.5 22.3 23.5 22.9 21. 19.3 11.5 23.5 25. 14.5 9 Pythium debarianum 31.0 38.0 30.5 18.3 19.5 17.0 1. 18.5 15.5 20.0 22.5 12. 10 Saprolegnia ferax 23.0 2.3 20.5 13.5 17.0 12.4 12.0 15.2 10. 13.5 1.0 12. 11 Saprolegnia parasitica 15.2 18.5 1. 10.5 11.8 8.5 9.8 12. 7.9 11.5 11.0 9.5 12 Saprolegnia terrestries 10.5 12.3 8.7.8 9.5.5.0 8.5 5.0 8. 9.1.5 PM-Pre monsoon, M- Monsoon, PO-M- Post monsoon 2011

Table-3: Percentage of distribution of Extra Aquatic fungi in different stations of Shanthi Sagar Lake Station-I Station-II % % 1 Alternaria alternata 18.0 1.5 17.25 10.0 9.2 9. 2 Aspergillus flavus 39.5 3.3 37.9 19. 22. 21.1 3 Aspergillus fumigatus 34.0 32.5 33.25 20.3 21.4 20.8 4 Aspergillus niger 38. 39.5 39.05 25.0 22.5 23.75 5 Chaetomium globosum 13.0 10. 11.8 8.5 5.7 7.1 ladosporoides 17.8 13.5 15. 5.7 5.0 5.3 7 Fusarium equisiti 2. 23.7 25.15 20.3 18.4 19.3 8 Fusarium oxysporum 30. 31.4 31.0 22.3 21.5 21.9 9 Fusarium semitectum 32.3 30.5 31.4 27.3 22. 24.9 10 Fusarium solani 28. 2.5 27.5 19.0 1.2 17. 11 Penicillium citrinum 1.8 15.0 15.9 10.1 12.0 11.08 12 Rhizopus nigricans 17.5 14. 1.05 10.8 7.5 9.15 13 Trichoderma viride 15.5 14.0 14.7 8.1 8.5 8.3 14 Trichoderma harzianum 15.5 18. 17.05 805.8 7. Station -III Station-IV 1 Alternaria alternata 10.0 8. 9.3 13.0 14.7 13.8 2 Aspergillus flavus 20.5 23.3 21.9 23.5 22.7 23.1 3 Aspergillus fumigatus 17.0 1.7 1.8 18.3 20.8 19.5 4 Aspergillus niger 21.5 22.4 21.95 19.4 2.0 22.7 5 Chaetomium globosum 7. 7.0 7.3 10.1 9.8 9.9 ladosporoides 4.5 4.9 4.7 11.8 9. 10.7 7 Fusarium equisiti 18. 1.5 17.5 19.1 1.5 17.8 8 Fusarium oxysporum 19.3 18.8 19.09 24.0 22. 23.3 9 Fusarium semitectum 19.0 20.3 19. 22.3 18.0 20.15 10 Fusarium solani 18.0 15.4 1.7 19.5 17.5 18.5 11 Penicillium citrinum 10.0 11.5 10.7 13.8 14.5 14.15 12 Rhizopus nigricans 11.0 8.0 9.5 13.5 11. 12.5 13 Trichoderma viride 7.3.5.9 9.03 10.5 9.7 14 Trichoderma harzianum 8.5.2 7.3 11.0 8.5 9.7 Table-4: Seasonal average values of distribution of Extra Aquatic fungi in different stations of Shanthi Sagar Lake Station-I Station-II Station -III Station-IV Species of Fungi No. PM M PO-M PM M PO-M PM M PO-M PM M PO-M 1 Alternaria alternata 35.4 39.2 18. 2.3 29.2 12. 21.4 23.5 14. 2.3 27.4 19. 2 Aspergillus flavus 3.2 38.3 21.0 20.5 21.2 15.4 19. 20.3 13.3 22.5 31.4 19.5 3 Aspergillus fumigatus 37.4 38.3 27.2 23.4 25.5 13.4 19.9 21.3 11.2 20.7 22.0 13. 4 Aspergillus niger 39. 42.2 29.0 20.2 25. 17.05 19.2 21.03 15.0 23.2 2.4 20.5 5 Chaetomium globosum 13.5 1.0 9.5 7.5 12.0.0.5 11.0 5.3 9.5 14.5.5 cladosporoides 18.1 19.4 12.0 12.5 14.5 9.0 11.4 13.3.5 12.0 15.5 8.0 7 Fusarium solani 18. 23.4 13.1 10.5 12. 8.5 10.5 12.0 7.5 13.4 1. 10. 8 Fusarium equisiti 25. 31.8 19.5 20.5 23. 1. 20. 21.5 15. 18.4 23.5 11.7 9 Fusarium oxysporum 3.05 40.2 21.7 20. 2.4 18.2 21.8 23. 13.4 20.5 25.5 18.4 10 Fusarium semitectum 29. 35.4 22.5 19. 21.15 17.09 21.85 23.8 10.7 20.2 23.05 1505 11 Penicillium citrinum 18.0 19.0 13.5 12.4 12.5.7 11.8 12.5 7.5 14.5 15.0 12.7 12 Rhizopus nigricans 17.5 21.0 14.0 12. 13.5 7.5 11. 14.7 8.8 13.4 14.5 13.0 13 Trichoderma harzianum 1. 18.2 12.5 9.0 10.5.5 8.5 10.0 7.15 12.2 12. 9.9 14 Trichoderma Viride 14.5 18.5 13.5 7.5 10.0.5.0 12.5 4. 8.5 11. 7.0 2012

PM-Pre monsoon, M- Monsoon, PO-M- Post monsoon REFERENCES Cooke, W.B. 191. Pollution effect on the fungus population of a stream. Journal of Ecology. 42: 1-18. Cooke, W.B. 193 A laboratory guide to fungi in polluted waters, sewage and sewage treatment systems. V.S. Dept. Health Education and Welfare, Cincinnat. Hunter, R.E. 1975. Water molds of the great river Ouse and its tributaries. Trans. British Journal of Mycological Society. 5: 101-108. Ingold, C. T. 1942. Aquatic Hypomycetes of decaying alder leaves. Trans. British Journal of Mycological Society. 2: 104-105. Singh, N. 1982. Cellulose decomposition by some tropical aquatic Hypomycetes. Trans. British Mycological Society. 79(3) : 50-51 Thompstone, A. and Dix, N.J. 1985. Cellulose activity in the Saprolegniaceae Trans. British Mycological Society. 85: 31-3. 2013