Journal of
Ecology and The Natural Environment

  • Abbreviation: J. Ecol. Nat. Environ.
  • Language: English
  • ISSN: 2006-9847
  • DOI: 10.5897/JENE
  • Start Year: 2009
  • Published Articles: 356

Full Length Research Paper

Abundance and diversity of major cultivable fungal flora of River Jhelum in Kashmir Himalaya

Furqana Fayaz
  • Furqana Fayaz
  • Department of Environmental Science, University of Kashmir, 190006, India.
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Azra N. Kamili
  • Azra N. Kamili
  • Centre of Research for Development, University of Kashmir, 190006, India.
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Bisma Zahoor Hafiz
  • Bisma Zahoor Hafiz
  • Department of Environmental Science, University of Kashmir, 190006, India, Centre of Research for Development, University of Kashmir, 190006, India.
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Imran Khan
  • Imran Khan
  • Department of Environmental Science, University of Kashmir, 190006, India, Centre of Research for Development, University of Kashmir, 190006, India.
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Gowhar Hamid Dar
  • Gowhar Hamid Dar
  • Department of Environmental Science, University of Kashmir, 190006, India, Centre of Research for Development, University of Kashmir, 190006, India.
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  •  Received: 02 December 2014
  •  Accepted: 19 December 2014
  •  Published: 30 January 2015

 ABSTRACT

The present work was carried out in the in river Jhelum of Kashmir Himalaya to assess the density and diversity of fungal flora, to isolate and identify the fungi from the water along with some physical parameters like pH and temperature which was carried out between June-November, 2011 at four sites differing from each other markedly in terms of biotic and abiotic factors. During the study, a variety of fungal strains were isolated and identified from the water of river at the four sites. The highest viable count of fungi was observed at site III with a cfu/ml of 3.6 x 102 in the month of July and the lowest viable count at site IV with a cfu/ml of 2.7×102 in the month of November. Among most dominant of the isolate identified 20% were Aspergillus spp. followed by 4% Pencillium spp. and 4% Candida spp. Comparative analysis of different types of colonies found at the four sites during the study indicates that the fungal density was dominant in the month of July.

 

Key words: River Jhelum, fungi, Aspergillus spp., Pencillium spp., and Candida spp.


 INTRODUCTION

The valley of Kashmir is a lacustrine basin with an average altitude of 1585 m a.s.l. Both the valley and its surrounding mountains are home to a large number of aquatic habitats like lakes, ponds, streams, rivers and wetlands. It is estimated that 6% of the land area of Jammu and Kashmir is under aquatic habitats (Zutshi and Gopal, 2000). Water is essential to sustain life, and without it life becomes impossible, it is an indispensable commodity, which should be easily accessible, adequate in quantity, free of contamination, safe, affordable and available throughout the year in order to sustain life (Al Khatib and Salah, 2003). Fungi are among the most diverse groups of living organisms on earth, though inadequately studied worldwide (Grover et al., 2007). Aquatic fungi play a crucial role in the freshwater ecosystem in nutrient cycling by breaking down leaves and woody substrates and also as symbionts (Barlocher and Kendrick, 1981). Physical chemical factors of ecosystem play important role on the growth, multiplication, distribution and seasonal periodicity of aquatic fungi (Park, 1972). Fungi belong to the kingdom Eumycota. This kingdom comprises five phyla namely Ascomycota, Basidiomycota, Zygomycota, Chytridiomycota, and Glomeromycota (Kirk et al., 2001; Schußler et al., 2001). Penicillium species have been frequently recovered from water in the various studies performed. Several of the species in genus Penicillium and Aspergillus are known to produce mycotoxins in other substrates, such as food and beverages (Moreau, 1979; Pitt and Hocking, 1999) and detection of aflatoxins produced by A. flavus in water from a cold water storage tank was demonstrated by Paterson et al. (1997). Predominant fungal genera and species in treated and untreated water are: Aspergillus, Cladosporium, Epicoccum, Penicillium, Trichoderma, Arthrinium phaeospermum, A. flavus, C. cladosporioides, Fusarium culmorum, Mucor hiemalis and Trichoderma harzianum (Kinsey et al., 1999). Many other fungal genera isolated from Danube river water in Europe include: Mortierella, Absidia, Rhizopus, Acremonium, Beauveria, Doratomyces, Monilia, Rhizopus arrhizus, Acremonium strictum, Fusarium oxysporum and Stemphyllium botryosum (Tothova, 1999). What governs the distribution of freshwater fungi is difficult to determine, although some species appear to be more common either in temperate or tropical regions (Shearer et al., 2007; Raja et al., 2009).
 
Since no substantial work has been carried out regarding the current understanding and distribution of fungal flora in the Jhelum River. Therefore the objective of this study was to focus on the isolation and identification of the fungal flora from this important river.


 MATERIALS AND METHODS

Study area and study sites
 
Jhelum, the major waterway of Kashmir, originates from the spring Verinag located in the foot of  a spur of the Pir Panjal Mountains in the district Anantnag from where a number of tributaries join the Jhelum and make it navigable from Khannabal to Wular Lake. The river runs a course of 203 km through the valley and the hydrology of River Jhelum is largely controlled by snowmelt in spring season and heavy rains from June to September. A total of four study sites (Figure 1) markedly different in respect of geographical and demographical features were selected for the sampling. These sites were characterized by having the moderate human population on both the banks along with the agricultural fields:
 
 
Site I: It was near Marval, Pampore lying between geographical coordinates 33? 58’ 45.4” N and 74? 54’ 16.5” E with an elevation of 1601 m. a.s.l. This site was located about 32 km from the main city centre (Lal chowk). On both sides of the bank the land was used for agricultural purposes and was bordered with residential hamlets around. The average depth of river at this site was about 1.6 m.
 
Site II: It was located (about 1.2 km from the city centre) at Zero bridge in Srinagar city lying between the geographical coordinates of 34? 4’ 9.2” N and 74? 50’ 20.88” E and having an elevation of 1582 m. a.s.l. At this stretch of the River, Jhelum congested human population and commercial activities takes place along the both sides of the banks. All along its course from Marval to Srinagar the river receives significant quantities of domestic wastes from human settlements and army cantonment areas. The average depth at this site was about 2 m.
 
Site III: This site was located about 10 km from main city centre at Qamarwari in Srinagar city lying between the geographical coordinates of 34? 05’ 35.9” N  and 74? 46’ 45.4” E and having an elevation of 1579 m. a.s.l. At this site both commercial and residential activities take place along both sides of river, which directly release the sewage and other solid wastes directly into the river. The average depth at this site was about 1.2 m.
 
Site IV: This site was located at Tengpora about 26 km from the main city centre lying between the geographical coordinates of 74? 43’ 11” E and 34? 7’47.1” N and having an elevation of 1577 m. a.s.l. This stretch of River Jhelum was characterized by moderate human population on both the banks along with the vegetable cultivation. Human interference like emission of domestic sewage, washing of clothes and other activities usually takes place at this particular site.
 
Laboratory analysis
 
Surface water samples were collected aseptically in pre-sterilized bottle on the monthly basis from June to November, 2011. During the present study Rose Bengal Agar media was used for isolation of Water fungi. At the end of the incubation period, the percentage frequency and percentage contribution of the fungal flora was calculated (Hogg and Hudson, 1966).
 
Dilution plate method
 
The water samples were mixed with sterile distilled water and a series of dilutions were made. From the dilutions, 0.1 ml inoculums was poured onto Rose Bengal agar and incubated at 28±2°C for 1 week to assess the growth of colonies (Waksman, 1922; Warcup, 1950; Bandh et al., 2011; Dar et al., 2013). The number of colonies counted was expressed as (colony forming units) cfu/ml and were calculated by using the formula:
 
Cfu/ml=n×d
 
Where, n= number of colonies; d = dilution factor = 1/dilution.
 
Identification of the fungal isolates was done upto genera level using standard fungal identification key of Barnett and Hunter (1999), Khulbe (2001).

 


 RESULTS AND DISCUSSION

The study was carried out between in four months June-November, 2011 and a total of 40 isolates were obtained during the study. The results of isolation and enumeration are indicated in Table 1. The isolates were identified on the basis of difference in some morphological features like colony appearance, elevation, margin, condia colour and reverse colour of the colonies. The colony appearance ranged from circular, irregular and filamentous. The margin varied from entire filamentous, undulate and lobate.  There was also considerable difference in the colour of colonies (dark green, sea green, yellowish white, cream white etc.). The individual colony count of different fungal isolates reveals that isolate type F23 was having the highest number of colonies (n=48) at site I followed by F6, F33, F30 and others. The colony count of isolate F23 was highest (n=24) in the month of July at site 2, isolate F33 had the highest number of colonies (n=38) followed by F30, F23 and others. The colony count of isolate F33 was highest (n=21) in the month of July at site 3, isolate F23 had the highest number of colonies (n=40) followed by F33, F4, F3 and others, and the colony count of isolate F23 and F33 was highest (n=22) in the month of July. At site 4, isolate F23 was had the highest number of colonies (n=40) followed by F33, F8, F5 and others. The colony count of isolate F23 was highest (n=22) in the month of July.  The total colony count given indicates that isolate F23 had the highest total colony count (n=156) for all months followed by isolate F33 (n=119). The total monthly fungal population (Cfu/ml) was also recorded for all four months as indicated in Table 2 and the data recorded reveals that the   
 
 
 
maximum population during July was 3.6×102 for site 3 and least for site 1 (1.1×102) in November as shown in Table 3. The diameter of the identified species was recorded and ranged from 1.5 to 1.63 cm; the elevation of these species included flat, raised, convex and filamentous. The margin included filamentous entire convex undulate and entire. The colour of the colonies on both upper and reverse sides varied from cream, white, yellow, pink etc. Aspergillus sp. contributed 20% followed by Pencillium sp. (4%) and Candida (5%) as shown in Figure 2.
 
 
 
The results obtained regarding the Aspergillus and Penicillium species during the study are in agreement with the study of Kellerman and McBeth (1912) who mentioned that the species of genus Aspergillus and Pencillium are found in polluted lake waters and act as cellulose decomposer. These genera have also been reported frequently from the drain waters with maximum densities during high pollution (Khulbe and Durgapal, 1994). Candida spp. obtained during the study was found to be pathogenic to humans which are a concern but these species can thus act as good indicators of water pollution (Cooke, 1954). The data recorded for water indicates higher temperature during July and lower during November (Table 3). The fungal load also shows decreasing trend from June to November. The higher temperature in July may be the reason for better growth of fungal population. Similar results were suggested by Bock (1956) and Dar et al. (2013), who reported optimum temperature for growth fungi bacteria has to be between 15?C and 31?C thus confirming the results obtained during the study. The maximum fungal population in July may possibly be due to more feasible temperature and increase in organic matter (Khulbe and Durgapal, 1992). Increase of fungi indicates increasing organic loading in water (APHA, 1998). During our study in the month of November, fungal population was minimum which may be attributed to the low temperature. These results are in agreement with the study of Khulbe and Durgapal (1992) who in his studies on Naintal Lake, has reported that fungal population was maximum in August during high temperature while it was lowest in the month of January when temperature was relatively low.


 CONCLUSION

From the study, it may be concluded that Aspergillus sp. and Pencillium sp. were present at all four sites during the study while as Candida sp. was found at site I in October and November. However, the Site III, on the River Jhelum showed the highest density of cultivable fungal population.


 CONFLICT OF INTERESTS

The author(s) declare there is no conflict of interests.



 REFERENCES

Al Khatib IA, Salah S (2003). Bacteriological and chemical quality of swimming pools water in developing countries, a case study in the west bank of Palestine. Int. J. Environ. Res. 13:17-22.

 

APHA (1998) Standard Methods for Examination of Water and Wastewater. 20th edition. American Public Health Association, Washington D.C.

 

 

Bandh SA, Kamili AN, Ganai BA (2011). Identification of some Penicillium species by traditional approach of morphological observation and culture. Afr. J. Microbial. Res. 5(21):3493-3496.

 

 

Barlocher F, Kendrick B (1981). Role of aquatic hyphomycetes in the trophic structure of streams, In: Wicklow DT, Carroll GC, eds.The fungal community: its organization and role in the ecosystem, New York: Marcel Dekker. pp. 743-760.

 

 

Barnett HL, Hunter BB (1999). Illustrated Genera of Imperfect Fungi (fourth ed.). APS Press, St. Paul, Minnesota, USA, 218 pp.

 

 

Bock KJ (1956). Zurokologic and systematic saprophttischer wasserpilze ausdem. Silberse bei Bremerhaven. Veroff instt. Messeresforch. Bremerchii. 4:25-44.

 

 

Cooke CW (1954). Pliocene Echinoids from Okinawa. Geological Survey Professional Papers 264, 45-53. page(s): 47; pl. 11

 

 

Dar GH, Bandh SA, Kamili AN, Nazir R, Bhat RA (2013). Comparative Analysis of Different Types of Bacterial Colonies from the Soils of Yusmarg Forest, Kashmir valley India. Ecologia Balkanica 5(1):31-35.

 

 

Grover R, Sharma KP, Kumar P, Kumar S (2007). Response of fungal community in the unpolluted and polluted (textile and distillery wastes) habitats. J. Environ. Sci. Eng. 49(2):93-98.

 

 

Hogg B, Hudson HJ (1966). Microfungi of the leaves of Fagus sylvatica The microfungal succession. Trans. Br. Mycol. Soc. 49:185-192.
Crossref

 

 

Kellerman KE, McBeth IG (1912). The fermentation of cellulose. ZBI Bakt I Abs. 34:485-494.

 

 

Khulbe RD (2001). A manual of aquatic fungi (Chytridiomycetes and Oomycetes) Delhi, Daya, p. 255.

 

 

Khulbe RD, Drugapal A (1994). Sewage mycoflora in relation to pollutants in Nainital, Kumaun Himalaya. Pollut. Res. 13(1):53-58.

 

 

Khulbe RD, Durgapal A (1992). Population dynamics of Geo fungi in a polluted fresh water body at National Kuamaun Himalays, Deptt of Botany, Kumaun University. Pollut. Res. 24:180-187.

 

 

Kinsey GC, Paterson RR, Kelley J (1999). Methods for the determination of filamentous fungi in treated and untreated waters. J. Appl. Microbiol. 85:214S-224S.
Crossref

 

 

Kirk PM, Cannon PF, David JC, Stalpers JA (2001). Ainsworth & Bisby's Dictionary of the fungi, 9th edn. CAB International, Wallingford.

 

 

Moreau C (1979). Moulds, Toxins and Food, 2nd edn. John Wiley & Sons, New York.

 

 

Park DE (1972). On the ecology of heterotrophic microorganisms in freshwater. Trans. Br. Mycol. Soc. 58:291-299.
Crossref

 

 

Paterson RRM, Kelley J, Gallagher M, (1997) Natural occurrence of aflatoxins and Aspergillus flavus (Link) in water. Lett. Appl. Microbiol. 25:435-436.
Crossref

 

 

Pitt JI, Hocking AD (1999). Fungi and Food Spoilage, 2nd edn. Aspen Publishers, Gaithersburg, MD.

 

 

Raja HA, Schmit JP, Shearer CA (2009). Latitudinal, habitat andsubstrate distribution patterns of freshwater ascomycetes in theFlorida Peninsula. Biodivers. Conserv. 18:419-455.
Crossref

 

 

Schußler A, Schwarzott D, Walker C (2001). A new fungal phylum, theGlomeromycota: phylogeny and evolution. Mycol. Res. 105:1413-1421.s

 

 

Shearer CA, Descals E, Kohlmeyer B, Kohlmeyer J, Marvanova L, Padgett D, Porter D, Raja HA, Schmidt JP, Thornton HA, Voglymayr H (2007). Fungal biodiversity in aquatic habitats. Biodivers. Conserv. 16:49-67.
Crossref

 

 

Tothova L (1999) Occurrence of microscopic fungi in the Slovak section of the Danube River. Biologia 54:379-385.

 

 

Waksman SSA (1922). A method of counting the number of fungi in the soil. J. Bacteriol. 7:339-341.

 

 

Warcup JH (1950). The soil plate method for isolation of fungi from soil. Nature 166:117-118.
Crossref

 

 

Zutshi DP, Gopal B (2000). State of Biodiversity in Lakes and Wetlands of Kashmir valley. In: Environment, Biodiversity and Conservation, Khan, M.A. and S. Farooq (Eds.). APH Publishing Corporation, New Delhi, India, ISBN-13: 9788176481649, pp. 51-67.

 

 




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