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ISSN No:-2456-2165
The method of analysing water to estimate the numbers Sanitary analysis of drinking water: This was done by
of bacteria present in it and, if needed, to find out what sort of multiple tube fermentation method or multiple tube method
bacteria they are is called Bacteriological analysis of water. It (MPN).It the most commonly used test for the analysis of
indicates the biological quality of water. It is a microbiological microbiological quality of water samples. The test is primarily
analytical procedure which make use ofwater samplesto used to detect coliforms, which are indicator organisms for
determine the most probable number of microoragnisms in it faecal contamination. They make up 10% of intestinal
and draws inference from the results regarding the potability microflora of most animals. The test has three stages namely
of the water. The procedure is routinely used to confirm the presumptive, confirmed, and complete test. MacConkey broth
safety of water for human use. (which is the media used) tubes are incubated with water
samples and the MPN index of the sample is calculated. The
Kuttanad being below the sea level receive the flood complete test follows by inoculation of EMB agar plate,
waters of the river systems like Periyar, Muvattupuzha, Nutrient agar plate and MacConkey broth and preparation of a
Meenachil, Pampa and Achenkovil, all originating from gram stain slide from nutrient agar (NA) slant, is used to
Western Ghats mountain ranges which receives south west establish that Coliform bacteria are present in the sample. The
and north east monsoonal rains. These rivers along with their complete process including the confirmed and complete test
tributaries traverses Kuttanad wetlands and Vembanad Lake requires at least 3 days for incubation.
before ending in the Arabian Sea. The organic matter
transported and deposited here contributes to the uniqueness Isolation of Vibrio from samples of drinking water: For
of the Kuttanadan ecosystem in addition to its location near Vibrio species isolation, 250mL of water sample were filtered
equator, equitable temperature regime, high rainfall and high through 0.22 μm membranes. Membranes were aseptically
solar radiation throughout the year. Most of the Kuttanad area transferred in 225 mL of alkaline peptone water (APW).
remain waterlogged almost throughout the year and are Incubate the sample mixture at 35°C. After 6-8 hour
subjected to flood during the rainy season. incubation, transfer a loopful from the surface pellicle of APW
culture to the surface of a dried TCBS (Thiosulfate Citrate
The present study is about to find the water quality of Bile Salts Sucrose agar) plate and streak in a manner that will
Kuttanad area after the flood that affected Kerala in 2018. yield isolated colonies. Incubate TCBS plates at 35°C for18-
Mostly the parts of lower Kuttanad was severely affected by 24 hours. Examine the TCBS plates for Vibrio colonies.
the flood. The contamination of the drinking water source Vibrio cholerae colonies appear large, smooth, yellow and
increase which are mainly well water in those areas. slightly flattened with opaque centres and translucent
Microbiological analysis was conducted for the identification periphery and Vibrio parahaemolyticus appears as round,
and enumeration of coliform bacteria. Tests were also opaque, green or bluish colonies 2-3mm in diameter.
conducted for the detection and isolation of Vibrio and
Salmonella species. Isolation of Salmonella from drinking water: For
Salmonella spp. isolation, 250mL water was filtered through
II. METHODOLOGY the 0.22 μm pore-sized membrane until it became occluded.
Membranes were aseptically transferred to homogenized
Sampling area: Kuttanad is a highly complex, dynamic and mixture of 225mL buffered peptone water (BPW). Incubate
unique rice growing agro-climatic tract of Kerala lying 0.5 to the sample mixture at 35°C for 24 hours. Transfer 0.1ml to
2.5 m below Mean Sea Level (MSL). It extends between 10ml of Rappaport-Vassiliadis (RV) medium. Mix well.
North latitudes 9 0 8‟ and 9 0 52‟ and East longitudes 760 19‟ Incubate RV medium at 42°C for 24 hours in a water bath.
and 760 44‟, comprises the area of 54 revenue villages spread Mix and streak a loopful of growth from RV medium on
over Alappuzha, Kottayam and Pathanamthitta districts. The Xylose Lysine Deoxycholate (XLD) agar. Incubate plates at
total geographic area of the region is 1100km. Kuttanad is 35°C for 24 hours. Examine all the plates for presence of
bordered by Kaduthuruthy- Vaikom road in the north, Salmonella colonies - Pink colonies with or without black
Kaduthuruthy - Kottayam -Mavelikkara railway line in the centres.
east, Mavelikkara - Haripad - Thottapally road in the south
and Thottapally -Alappuzha - Thaneermukkom road in the Biochemical tests:The following tests were done for the
west. Thirty samples from different Taluks of Kuttanad were partial characterization of E.coli, Salmonella andVibrio
selected for this study. species isolated from the water samples: Carbohydrate
fermentation tests,Indole test,Methyl Red (MR)-Voges
Key
+ = Positive -ve = Negative A+G= acid and gas ND = Not determined
production
The 2018 Kerala flood was among the most severely Tubes were looked for acid and gas production. The
affected floods of the state. Almost lasting for about two number of tubes with acid and gas production for each volume
weeks, the flood affected the economic and ecological strata. of water added were noted and the most probable number of
Wide range of destruction was followed by the flood. The total coliforms were calculated according to the standardized
flood water contained organic and inorganic waste products in probability table for all samples of water and the results
large quantities. The flood water all along with the waste was obtained were compared to the interpretation table. Of the 30
deposited in the low-lying areas of the state. Kuttanad around water samples obtained from the different Taluks of Kuttanad;
4-10ft below sea level was among the major places that were samples from five places had shown MPN index ≥1100 for
affected. Being thickly populated and a major contributor to total coliforms per 100mL which make up 16.67% of the total
the state’s food crop production Kuttanad faced immense samples analysed. Among these five places, water from
stress all throughout. All the topographical factors contributed Champakulam had shown the highest MPN index ie., 1.1x105
to the increase of contamination of water resources of the per 100 ml of sample. Followed by water samples from places
Kuttanad area. such as Kannady, Kavalam, Pullangady, and Narakathara. All
the above places except Narakathara showed the presence of
Sanitary analysis of drinking water of different Taluks in E.coli. Among the samples analysed 30% of the samples
the Kuttanad area where flood was severely affected was showed MPN index from 460-150.
carried out by multiple tube fermentation method (MPN). 30
samples were collected from different Taluks of Kuttanad and E.coli was detected in 9 samples viz.smaples from
was transported to the laboratory and processed within 24 Champakulam, Kannady, Kavalam, Pullangady, Kulipura,
hours of collection. Further samples were analysed for the Pallikuttumma, Edathua, Valady, and Kumaramkary, which
detection and isolation of Vibrio and Salmonella species. constitute 30% of the whole samples. These samples on
Water borne diseases such as cholera, salmonellosis etc. were culturing on the differential media; EMB (Eosin Methylene
expected in post flood period. Blue) agar showed colonies with green metallic sheen and
other characters of E.coli. (fig 1)
ACKNOWLEDGMENT
REFERENCES
[1]. Atif M. El-Naggar, Soaad A. Mahmoud and Safaa I.
Tayel. Bioaccumulation of Some Heavy Metals and
Histopathological Alterations in Liver ofOreochromis
niloticus in Relation to Water Quality at Different
Localities alongthe River Nile, Egypt
[2]. Byamukama, D., R.L. Mach, F. Kansiime, M. Manafi
and A.H. Farnleitner: Discrimination efficacy of faecal
pollution detection in different aquatic habitats of a high
altitude tropical estuary, using presumptive
coliforms,Escherichia coli and Clostridium perfringens
spores. Appl. Environ.Microbiol., 71, 65-71 (2005).
[3]. Ehsan Humayun, Aqsa Bibi, Atif Ur Rehman, Sajjad
Ahmad, Nodia Shujaat (April 2015). Isolation and
identification of Coliform bacteria from drinking water
sources of Hazara region. Department of Biochemistry,
Hazara University Garden Campus Manshera, KPK,
Pakistan.
[4]. Geldreich, E.E. 1976 Faecal coliform and faecal
streptococcus density relationships in
[5]. Goel, P. K.; Bhosale, P. M. Studies on the river
Panchganga at Kolhapur with special reference to human
impact on water quality. In: TRIPATHY, G.; PANDEY,
G. C. (Eds.). Current topics in environmental sciences.
[S.l.]: ABD Publishers, 2001. p. 108-122.
[6]. Leclerc, H., Mossel, D.A.A., Edberg, S.C. and Struijik,
C.B. (2001). Advances in the bacteriology of the
coliform group: their suitability as markers of microbial
water safety.Annu.Rev.Microbial., 55: 2001-234
[7]. Maier, R., Pepper, I., and Gerba, C.(2000).
Environmental microbiology. Orlando, Florida:
Academic Press