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International Journal of Pharmaceutical Science Invention
ISSN (Online): 2319 – 6718, ISSN (Print): 2319 – 670X
www.ijpsi.org Volume 2 Issue 12 ‖ December 2013 ‖ PP.38-42

Klebsilla: In Drinking Water
Deepesh Kumar*, Shrutikirti , Kaushal Kumari
Deptt. Of Microbiology, Subharti Medical College, Meerut-250004, U.P
S.V.B.P Hospital, LLRM Medical College, Meerut – 250004,U.P
ABSTRACT: A total of 116 drinking water samples from Government hand pump (32 samples), Municipal
tap water (58 samples) and Water cooler (26 samples) collected aseptically in sterilized container. Over a
period of nine month September to May 2012.Most probable number (MPN) test was done to detect the
coliforms in drinking water samples. Percentage occurrence of the isolates was Klebsiella spp. (15%), along
with Pseudomonas aeruginosa (25%), Escherichia coli (28%). The pH of the water samples ranged from 5.9 to
7.45, temperature ranged from 26.58ºC to 30.13ºC. Therefore the need for the provision of reliable potable
water to the local dwellers by government is highly recommended to prevent health hazards.

KEYWORDS: Drinking water sample, MPN count, Coliforms
I.

INTRODUCTION

Water is the most abundant chemical in the human body and plays a central role in the regulation of
nutrient transport, toxic waste removal, thermal regulation and digestion, organ functioning and metabolic
activities. However, if water is fecally polluted it spreads diseases in consumers to a great number of people[1].
World health organization estimated in 2000 assessment that there are four billion cases of diarrhea each year in
addition to millions to other cases of illness associated with the lack of access of clean water [2]. It is well
established that infectious diseases are transmitted primarily through water supplies contaminated with human
and animal excreta particularly faeces[3].Out breaks of water borne diseases continue to occur throughout the
world but are especially serious in developing countries[4-5]. The human pathogens that present serious risk of
disease whenever present in drinking water include Salmonella species, Shigella species, pathogenic
Escherichia coli, Vibrio cholerae, Yersinia entercolitica, Campylobacter species, various viruses such as
Hepatitis A, Hepatitis E, Rota virus and parasites such as Entamoeba histolytica and Giardia species and so
on[5-7].Public and environmental health protection requires safe drinking water, which means that it must be
free of pathogenic bacteria.

II.

CHARACTERISTICS

Klebsiella spp. is Gram-negative, nonmotile, usually encapsulated rod-shaped bacteria, belonging to
the family Enterobacteriaceae [8-9].These bacteria produce lysine decarboxylase but not ornithine
decarboxylase and are generally positive in the Voges-Proskauer test. Members of the Enterobacteriaceae family
are generally facultatively anaerobic, and range from 0.3 to 1.0 mm in width and 0.6 to 6.0 mm in length
[9]. Klebsiella spp. often occurs in mucoid colonies [8-9]. The genus consists of 77 capsular antigens (K
antigens), leading to different serogroups.

III.

EPIDEMIOLOGY

Klebsiella spp. occur worldwide, particularly in tropical and subtropical regions, and are ubiquitous,
including forest environments, vegetation soil, water, and mucosal membranes of host species[8]. Although they
are common pathogens for community-acquired pneumonias and bacteremias, the majority of the infections are
nosocomial (hospital-acquired; ~56% of all Klebsiella infections).Klebsiella spp. are considered endemic in
neonatal wards and nosocomial outbreaks, particularly in neonatal wards, are common. Adult males are more
susceptible to infection with Klebsiella spp. than adult females [8]. however, Klebsiella spp. demonstrate higher
colonization rates among neonates that may survive up to months as compared to a few days to weeks in adults.
Risk of infection and carriage rates of Klebsiella spp. increases with increase in duration of stay within a
hospital; 11% to 42% increase in carriage rate within 14 days of hospitalization according to one study [8].
Infection and carriage rates also increase with antimicrobial use; this usually leads to the development of
extended-spectrum beta-lactamase (ESBLs) which provide resistance against antibiotics [8-11].K.
pneumoniae is most pathogenic to humans among all Klebsiella spp.,followedby K.oxytoca.
K.ozaenae and K.rhinoscleromatis cause specific diseases in humans [11]. K.granulomatis and K. variicola have
also been identified as being pathogenic to humans. K. singaporensis is still very novel and its pathogenicity to
humans has yet to be determined. Although, the number of infections is lower than some other pathogens,
infections by Klebsiella spp. demonstrate substantial morbidity and mortality. K. pneumoniae occurs in the
nasopharynx and intestinal tract of humans, as a saprophyte [11]. It is one of the leading causes of community-

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38 | P a g e
Klebsilla: In Drinking Water
acquired pneumonia. It is important cause of primary liver abscess and of microbial fascial space infections
among diabetic patients in Asia, predominantly in Taiwan [8]. It is commonly isolated from infections of burns
and human bites. Recently, it has become an increasing cause of chronic diarrhoea in HIV infected adults in
Africa. K. pnuemoniae and K. oxytoca are important causative agents of community-acquired meningitis and
brain abscesses in Asia, predominantly in Taiwan. According to some reports, Klebsiella spp. is responsible for
16 to 43% of central nervous system (CNS) infections and brain abscesses. Environmental strains of K.
pneumoniae have been shown to be equally virulent as clinical strains; however, whether this is true or not for
othe rKlebsiella spp. has yet to be determined [12].

IV. PATHOGENICITY:
Klebsiella spp. has been identified as important common pathogens for nosocomial pneumonia (7 to
14% of all cases), septicaemia (4 to 15%), and urinary tract infection (UTIs; 6 to 17%), wound infections (2 to
4%), intensive care unit (ICU) infections (4 to 17%), and neonatal septicaemias (3 to 20%). Klebsiella spp. can
also cause bacteremias and hepatic infections, and have been isolated from a number of unusual infections,
including endocarditis, primary gas-containing mediastinal abscess, peritonitis, acute cholecystitis, crepitant
myonecrosis, pyomyositis, necrotizing fasciitis, psoas muscle abscess, fascial space infections of the head and
neck, and septic arthritis.They are also important opportunistic pathogens, particularly among the
immunocompromised. Pathogenicity factors of Klebsiella spp. include adhesins, siderophores, capsular
polysaccharides (CPLs), cell surface lipopolysaccharides (LPSs), and toxins, each of which plays a specific role
in the pathogenesis of these species. Depending on the type of infection and the mode of infectivity, cells
of Klebsiella spp. may adhere and attack upper respiratory tract epithelial cells, cells in gastrointestinal tract,
endothelial cells, or uroepithelial cells, followed by colonization of mucosal membranes. Common underlying
conditions include alcoholism, diabetes mellitus, chronic liver disease (cirrhosis), chronic renal failure, cancer,
transplants, burns, and/or use of catheters [8].
V. MATERIALS AND METHODS:
A total of 116 drinking water samples were collected from each source according WHO guidelines for
drinking water quality assessment [13], over a period of nine month September to May 2012.
VI. SAMPLE COLLECTION:
About 200ml water samples from Government hand pump, water cooler and Municipal tap water were
collected, labeled and transported to the laboratory for bacteriological analysis.
VII. BACTERIOLOGICAL ANALYSIS:
Bacteriological analysis was carried out for indicator organisms i.e. total and fecal coliform (E.coli) by
most probable number (MPN) method 9,10..Ten tubes of MacConkeys broth (Hi media Pvt. Ltd Mumbai)
arranged in two rows with a 100 ml blood culture bottle. First row containing 10 ml double strength
MacConkeys broth was inoculated with 10 ml of water sample and 50 ml double strength MacConky broth was
inoculated with 50ml of water sample. Second row containing 1 ml single strength MacConkeys broth medium
was inoculated with 1 ml water sample respectively. Were incubated in an incubator at 44°C for 24h. After
incubation, the number of bottles in which lactose fermentation with acid and gas production has occurred was
counted. Finally, by referring to probability table (Macrady table-2) the MPN of coliform in 100 ml water
sample was been estimated (Cheesbrough, 2006). Analysis is usually performed using culture and biochemical
test also.
VIII.

RESULT AND OBSERVATION

A total of 116 drinking water samples were tested by MPN method. Out of which,
Total drinking water sample collected from Municipal Tap Water = 58 (50%)
Total drinking water sample collected from Government Hand Pump = 32 (28%).
Total drinking water sample collected from Water cooler = 26 (22%).
After determinant of MPN number of positive sample, for organism identification do the culture & biochemical
test.

IX.

CULTURE

From the 1 ml tube (single strength) of positive test, a loop full specimen was taken
the MacConkey agar plate and incubate at 370 C overnight.

X.

and streaked into

INTERPRETATION

A mixed growth of either dry lactose fermenting, mucoid lactose fermenting and non-lactose
fermenting growth appeared after the incubation (figure.1).
For Specification, the colonies were subcultured on other individual MacConkey agar plate from primary plate
and incubate at 370C overnight.

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39 | P a g e
Klebsilla: In Drinking Water
After the incubation a pure, heavy growth was on MacConkey agar plate (figure. 2).

XI.

BIOCHEMICAL TEST

For species identification the biochemical (IMViC) test as per WHO guideline was performed.
TABLE: 1 - Biochemical characterization.
Organism

MR

Escherichia coli
+
Klebsiella
+
Pseudomonas sp.
−
VP: Voges-Proskauer, MR: Methyl Red.

VP

Indole

Urease

Citrate

−
−
−

+
−
−

−
+
−

−
+
+

TABLE: 2 - Profile of Positive Sample (n=116).

Source of Water
Positivity
Organism
Escherichia coli
Klebsiella Sp.
Pseudomonas Sp.
Mix Sample

Municipal
Tap
Water
58

Municipal
Hand
Pump
32

20
8
12

5
-

Water
Cooler

Total No.

26

116

1
1
15
1

21
9
20
13

TABLE: 3 - Profile of Mix Sample (n=13) with reference to sample no.

No. of
Sample

Escherichia coli,
Klebsiella Sp.,
Pseudomonas Sp.

Organism
Escherichia
coli, Klebsiella
Sp.

3
5
4
1

+
-

+
-

www.ijpsi.org

Escherichia
coli,
Pseudomonas
Sp.
+
-

Klebsiella Sp.,
Pseudomonas
Sp.
+

40 | P a g e
Klebsilla: In Drinking Water
TABLE: 4 - Profile of total positive sample (n=116)
Source of
water sample

No. of
Sample
collected

No. of
Unsatisfactory
sample (%)

Municipal Tap
Water

58
(50%)

40
(69%)

Government
Hand Pump

32
(27.59%)
26
(22.42%)

5
(15.62%)
18
(70%)
63
(54.31%)

Organism grown

Water Cooler
Total

116

XII.

Escherichia
coli

Pseudomonas
Sp.

Klebsiella
Sp.

32

8

15

-

5

-

1

16

2

33
(28.44%)

29
(25%)

17
(14.65%)

DISCUUSION

According to the WHO, The lack of safe water supply and of adequate means of sanitation is blamed
for as much as 80% of all diseases in developing countries. Sewage containing human excreta is the most
dangerous material that pollutes water. The most important microbial diseases transmitted through water are
Typhoid fever, Amoebic dysentery, bacillary dysentery, Cholera, Poliomyelitis and Infectious hepatitis [14].
The samples received from hostel over head tank showed mixed contamination of Pseudomonas aeruginosa
and Escherichia coli. However when the sample was again received from the same site after treatment showed
contamination with Pseudomonas aeruginosa only. The bacteriological examination of drinking water by MPN
method is a sensitive method to assess its quality though it does not detect contamination with protozoa, virus
and fungi. Enumeration of Escherichia coli forms has been recommended by the Indian council of medical
research and has been the main method adopted by many workers [15].
This could be due to mixing of sewage water with drinking water as a result of leakage in the pipeline.
A regular monitoring of the water quality for improvement not only prevents disease and hazards but also
checks the water resources from going further polluted
The conservation of water sources is very important to provide safe water as far as possible, water sources must
be protected from contamination by human and animal waste which can contain a variety of Bacterial, Viral,
Protozoan and Helminthic Parasites.
The control of drinking water quality in distribution networks remain a major challenge. The protection
of sources, treatment and distribution management are all critical strategies in maintaining and improving water
supply.

REFERENCES
[1]
[2]
[3]
[4]
[5]
[6]
[7]
[8]
[9]

[10]
[11]
[12]

[13]

Nakade D.B., Assessment of bacteriological quality of water in Kolhapur city of Maharashtra,India.Int. Res.j.Enviromental Sci.
ISSSN 2319-1414 vol.2 (2), 63-65, February 2013.
WHO, 2000 global water supply and sanitation assessment 2000 report.
WHO, guidelines for drinking water quality. Vol.1, Geneva, World Health Organisation. 1993, pp. 1- 29.
Manja KS, Maurva MS, Ran KM. A simple field test for the detection of faecal pollution in drinking water. Bull. WHO.,
1982;60:797-801.
Emde KME, Mao H, Finch GR. Detection ad occurrence of water borne bacterial and viral pathogens. Water Environ. Ret,,
1992:64:641-47.
Geldreich EL. Water borne pathogens invasions: A case for water quality protection in distribution. Proceedings of American
Water Works Association. Water Quality Technology Conference, 1992: pp. 1-18.
Joklik WK, Willett HP, Amos DB, ct al, Ziusser Microbiology. 20th Ed., Norwalk; Appleton and Lange, 1992, pp. 393-400,
Janda, J. M., & Abbott, S. L. (2006). The Genera Klebsiella and Raoultella.The Enterobacteria (2nd ed., pp. 115-129).
Washington, USA: ASM Press.
Abbott, S. L. (2007). Klebsiella, Enterobacter, Citrobacter, Serratia, Plesiomonas, and Other Enterobacteriaceae. In P. R. Murray,
E. J. Baron, J. H. Jorgensen, M. L. Landry & M. A. Pfaller (Eds.), Manual of Clinical Microbiology (9th ed., pp. 698-711).
Washington, USA: ASM Press.
Euzéby, J. P. (2010). List of Bacterial Names with Standing in Nomenclature. Int. J. Syst. Bacteriol., 47, 13 July, 2010. Retrieved
from http://www.bacterio.cict.fr/m/micrococcus.html
Podschun, R., & Ullmann, U. (1998). Klebsiella spp. as nosocomial pathogens: epidemiology, taxonomy, typing methods, and
pathogenicity factors. Clinical Microbiology Reviews, 11(4), 589-603.
Podschun, R., Pietsch, S., Holler, C., & Ullmann, U. (2001). Incidence of Klebsiella species in surface waters and their
expression of virulence factors. Applied and Environmental Microbiology, 67(7), 3325-3327. doi:10.1128/AEM.67.7.33253327.2001
Guideline manual for drinking water quality monitoring and assessment: 2nd edition

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41 | P a g e
Klebsilla: In Drinking Water
[14]
[15]

Geldreich, the Bacteriology of Water. Chapter 15: in Leslie Collier, Albert Balows, Max Sussman editors. Topley Wilson’s
Microbiology and Microbial Infections 9th ed, London, hodder Arnold; 2005, p351-363.
Indian Council of Medical Research. Manual of Methods for the Examination of Water Sewage of Industrial Wastes. ICMR
Special Reports, series no 47, 1953.

www.ijpsi.org

42 | P a g e

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International Journal of Pharmaceutical Science Invention (IJPSI)

  • 1. International Journal of Pharmaceutical Science Invention ISSN (Online): 2319 – 6718, ISSN (Print): 2319 – 670X www.ijpsi.org Volume 2 Issue 12 ‖ December 2013 ‖ PP.38-42 Klebsilla: In Drinking Water Deepesh Kumar*, Shrutikirti , Kaushal Kumari Deptt. Of Microbiology, Subharti Medical College, Meerut-250004, U.P S.V.B.P Hospital, LLRM Medical College, Meerut – 250004,U.P ABSTRACT: A total of 116 drinking water samples from Government hand pump (32 samples), Municipal tap water (58 samples) and Water cooler (26 samples) collected aseptically in sterilized container. Over a period of nine month September to May 2012.Most probable number (MPN) test was done to detect the coliforms in drinking water samples. Percentage occurrence of the isolates was Klebsiella spp. (15%), along with Pseudomonas aeruginosa (25%), Escherichia coli (28%). The pH of the water samples ranged from 5.9 to 7.45, temperature ranged from 26.58ºC to 30.13ºC. Therefore the need for the provision of reliable potable water to the local dwellers by government is highly recommended to prevent health hazards. KEYWORDS: Drinking water sample, MPN count, Coliforms I. INTRODUCTION Water is the most abundant chemical in the human body and plays a central role in the regulation of nutrient transport, toxic waste removal, thermal regulation and digestion, organ functioning and metabolic activities. However, if water is fecally polluted it spreads diseases in consumers to a great number of people[1]. World health organization estimated in 2000 assessment that there are four billion cases of diarrhea each year in addition to millions to other cases of illness associated with the lack of access of clean water [2]. It is well established that infectious diseases are transmitted primarily through water supplies contaminated with human and animal excreta particularly faeces[3].Out breaks of water borne diseases continue to occur throughout the world but are especially serious in developing countries[4-5]. The human pathogens that present serious risk of disease whenever present in drinking water include Salmonella species, Shigella species, pathogenic Escherichia coli, Vibrio cholerae, Yersinia entercolitica, Campylobacter species, various viruses such as Hepatitis A, Hepatitis E, Rota virus and parasites such as Entamoeba histolytica and Giardia species and so on[5-7].Public and environmental health protection requires safe drinking water, which means that it must be free of pathogenic bacteria. II. CHARACTERISTICS Klebsiella spp. is Gram-negative, nonmotile, usually encapsulated rod-shaped bacteria, belonging to the family Enterobacteriaceae [8-9].These bacteria produce lysine decarboxylase but not ornithine decarboxylase and are generally positive in the Voges-Proskauer test. Members of the Enterobacteriaceae family are generally facultatively anaerobic, and range from 0.3 to 1.0 mm in width and 0.6 to 6.0 mm in length [9]. Klebsiella spp. often occurs in mucoid colonies [8-9]. The genus consists of 77 capsular antigens (K antigens), leading to different serogroups. III. EPIDEMIOLOGY Klebsiella spp. occur worldwide, particularly in tropical and subtropical regions, and are ubiquitous, including forest environments, vegetation soil, water, and mucosal membranes of host species[8]. Although they are common pathogens for community-acquired pneumonias and bacteremias, the majority of the infections are nosocomial (hospital-acquired; ~56% of all Klebsiella infections).Klebsiella spp. are considered endemic in neonatal wards and nosocomial outbreaks, particularly in neonatal wards, are common. Adult males are more susceptible to infection with Klebsiella spp. than adult females [8]. however, Klebsiella spp. demonstrate higher colonization rates among neonates that may survive up to months as compared to a few days to weeks in adults. Risk of infection and carriage rates of Klebsiella spp. increases with increase in duration of stay within a hospital; 11% to 42% increase in carriage rate within 14 days of hospitalization according to one study [8]. Infection and carriage rates also increase with antimicrobial use; this usually leads to the development of extended-spectrum beta-lactamase (ESBLs) which provide resistance against antibiotics [8-11].K. pneumoniae is most pathogenic to humans among all Klebsiella spp.,followedby K.oxytoca. K.ozaenae and K.rhinoscleromatis cause specific diseases in humans [11]. K.granulomatis and K. variicola have also been identified as being pathogenic to humans. K. singaporensis is still very novel and its pathogenicity to humans has yet to be determined. Although, the number of infections is lower than some other pathogens, infections by Klebsiella spp. demonstrate substantial morbidity and mortality. K. pneumoniae occurs in the nasopharynx and intestinal tract of humans, as a saprophyte [11]. It is one of the leading causes of community- www.ijpsi.org 38 | P a g e
  • 2. Klebsilla: In Drinking Water acquired pneumonia. It is important cause of primary liver abscess and of microbial fascial space infections among diabetic patients in Asia, predominantly in Taiwan [8]. It is commonly isolated from infections of burns and human bites. Recently, it has become an increasing cause of chronic diarrhoea in HIV infected adults in Africa. K. pnuemoniae and K. oxytoca are important causative agents of community-acquired meningitis and brain abscesses in Asia, predominantly in Taiwan. According to some reports, Klebsiella spp. is responsible for 16 to 43% of central nervous system (CNS) infections and brain abscesses. Environmental strains of K. pneumoniae have been shown to be equally virulent as clinical strains; however, whether this is true or not for othe rKlebsiella spp. has yet to be determined [12]. IV. PATHOGENICITY: Klebsiella spp. has been identified as important common pathogens for nosocomial pneumonia (7 to 14% of all cases), septicaemia (4 to 15%), and urinary tract infection (UTIs; 6 to 17%), wound infections (2 to 4%), intensive care unit (ICU) infections (4 to 17%), and neonatal septicaemias (3 to 20%). Klebsiella spp. can also cause bacteremias and hepatic infections, and have been isolated from a number of unusual infections, including endocarditis, primary gas-containing mediastinal abscess, peritonitis, acute cholecystitis, crepitant myonecrosis, pyomyositis, necrotizing fasciitis, psoas muscle abscess, fascial space infections of the head and neck, and septic arthritis.They are also important opportunistic pathogens, particularly among the immunocompromised. Pathogenicity factors of Klebsiella spp. include adhesins, siderophores, capsular polysaccharides (CPLs), cell surface lipopolysaccharides (LPSs), and toxins, each of which plays a specific role in the pathogenesis of these species. Depending on the type of infection and the mode of infectivity, cells of Klebsiella spp. may adhere and attack upper respiratory tract epithelial cells, cells in gastrointestinal tract, endothelial cells, or uroepithelial cells, followed by colonization of mucosal membranes. Common underlying conditions include alcoholism, diabetes mellitus, chronic liver disease (cirrhosis), chronic renal failure, cancer, transplants, burns, and/or use of catheters [8]. V. MATERIALS AND METHODS: A total of 116 drinking water samples were collected from each source according WHO guidelines for drinking water quality assessment [13], over a period of nine month September to May 2012. VI. SAMPLE COLLECTION: About 200ml water samples from Government hand pump, water cooler and Municipal tap water were collected, labeled and transported to the laboratory for bacteriological analysis. VII. BACTERIOLOGICAL ANALYSIS: Bacteriological analysis was carried out for indicator organisms i.e. total and fecal coliform (E.coli) by most probable number (MPN) method 9,10..Ten tubes of MacConkeys broth (Hi media Pvt. Ltd Mumbai) arranged in two rows with a 100 ml blood culture bottle. First row containing 10 ml double strength MacConkeys broth was inoculated with 10 ml of water sample and 50 ml double strength MacConky broth was inoculated with 50ml of water sample. Second row containing 1 ml single strength MacConkeys broth medium was inoculated with 1 ml water sample respectively. Were incubated in an incubator at 44°C for 24h. After incubation, the number of bottles in which lactose fermentation with acid and gas production has occurred was counted. Finally, by referring to probability table (Macrady table-2) the MPN of coliform in 100 ml water sample was been estimated (Cheesbrough, 2006). Analysis is usually performed using culture and biochemical test also. VIII. RESULT AND OBSERVATION A total of 116 drinking water samples were tested by MPN method. Out of which, Total drinking water sample collected from Municipal Tap Water = 58 (50%) Total drinking water sample collected from Government Hand Pump = 32 (28%). Total drinking water sample collected from Water cooler = 26 (22%). After determinant of MPN number of positive sample, for organism identification do the culture & biochemical test. IX. CULTURE From the 1 ml tube (single strength) of positive test, a loop full specimen was taken the MacConkey agar plate and incubate at 370 C overnight. X. and streaked into INTERPRETATION A mixed growth of either dry lactose fermenting, mucoid lactose fermenting and non-lactose fermenting growth appeared after the incubation (figure.1). For Specification, the colonies were subcultured on other individual MacConkey agar plate from primary plate and incubate at 370C overnight. www.ijpsi.org 39 | P a g e
  • 3. Klebsilla: In Drinking Water After the incubation a pure, heavy growth was on MacConkey agar plate (figure. 2). XI. BIOCHEMICAL TEST For species identification the biochemical (IMViC) test as per WHO guideline was performed. TABLE: 1 - Biochemical characterization. Organism MR Escherichia coli + Klebsiella + Pseudomonas sp. − VP: Voges-Proskauer, MR: Methyl Red. VP Indole Urease Citrate − − − + − − − + − − + + TABLE: 2 - Profile of Positive Sample (n=116). Source of Water Positivity Organism Escherichia coli Klebsiella Sp. Pseudomonas Sp. Mix Sample Municipal Tap Water 58 Municipal Hand Pump 32 20 8 12 5 - Water Cooler Total No. 26 116 1 1 15 1 21 9 20 13 TABLE: 3 - Profile of Mix Sample (n=13) with reference to sample no. No. of Sample Escherichia coli, Klebsiella Sp., Pseudomonas Sp. Organism Escherichia coli, Klebsiella Sp. 3 5 4 1 + - + - www.ijpsi.org Escherichia coli, Pseudomonas Sp. + - Klebsiella Sp., Pseudomonas Sp. + 40 | P a g e
  • 4. Klebsilla: In Drinking Water TABLE: 4 - Profile of total positive sample (n=116) Source of water sample No. of Sample collected No. of Unsatisfactory sample (%) Municipal Tap Water 58 (50%) 40 (69%) Government Hand Pump 32 (27.59%) 26 (22.42%) 5 (15.62%) 18 (70%) 63 (54.31%) Organism grown Water Cooler Total 116 XII. Escherichia coli Pseudomonas Sp. Klebsiella Sp. 32 8 15 - 5 - 1 16 2 33 (28.44%) 29 (25%) 17 (14.65%) DISCUUSION According to the WHO, The lack of safe water supply and of adequate means of sanitation is blamed for as much as 80% of all diseases in developing countries. Sewage containing human excreta is the most dangerous material that pollutes water. The most important microbial diseases transmitted through water are Typhoid fever, Amoebic dysentery, bacillary dysentery, Cholera, Poliomyelitis and Infectious hepatitis [14]. The samples received from hostel over head tank showed mixed contamination of Pseudomonas aeruginosa and Escherichia coli. However when the sample was again received from the same site after treatment showed contamination with Pseudomonas aeruginosa only. The bacteriological examination of drinking water by MPN method is a sensitive method to assess its quality though it does not detect contamination with protozoa, virus and fungi. Enumeration of Escherichia coli forms has been recommended by the Indian council of medical research and has been the main method adopted by many workers [15]. This could be due to mixing of sewage water with drinking water as a result of leakage in the pipeline. A regular monitoring of the water quality for improvement not only prevents disease and hazards but also checks the water resources from going further polluted The conservation of water sources is very important to provide safe water as far as possible, water sources must be protected from contamination by human and animal waste which can contain a variety of Bacterial, Viral, Protozoan and Helminthic Parasites. The control of drinking water quality in distribution networks remain a major challenge. The protection of sources, treatment and distribution management are all critical strategies in maintaining and improving water supply. REFERENCES [1] [2] [3] [4] [5] [6] [7] [8] [9] [10] [11] [12] [13] Nakade D.B., Assessment of bacteriological quality of water in Kolhapur city of Maharashtra,India.Int. Res.j.Enviromental Sci. ISSSN 2319-1414 vol.2 (2), 63-65, February 2013. WHO, 2000 global water supply and sanitation assessment 2000 report. WHO, guidelines for drinking water quality. Vol.1, Geneva, World Health Organisation. 1993, pp. 1- 29. Manja KS, Maurva MS, Ran KM. A simple field test for the detection of faecal pollution in drinking water. Bull. WHO., 1982;60:797-801. Emde KME, Mao H, Finch GR. Detection ad occurrence of water borne bacterial and viral pathogens. Water Environ. Ret,, 1992:64:641-47. Geldreich EL. Water borne pathogens invasions: A case for water quality protection in distribution. Proceedings of American Water Works Association. Water Quality Technology Conference, 1992: pp. 1-18. Joklik WK, Willett HP, Amos DB, ct al, Ziusser Microbiology. 20th Ed., Norwalk; Appleton and Lange, 1992, pp. 393-400, Janda, J. M., & Abbott, S. L. (2006). The Genera Klebsiella and Raoultella.The Enterobacteria (2nd ed., pp. 115-129). Washington, USA: ASM Press. Abbott, S. L. (2007). Klebsiella, Enterobacter, Citrobacter, Serratia, Plesiomonas, and Other Enterobacteriaceae. In P. R. Murray, E. J. Baron, J. H. Jorgensen, M. L. Landry & M. A. Pfaller (Eds.), Manual of Clinical Microbiology (9th ed., pp. 698-711). Washington, USA: ASM Press. Euzéby, J. P. (2010). List of Bacterial Names with Standing in Nomenclature. Int. J. Syst. Bacteriol., 47, 13 July, 2010. Retrieved from http://www.bacterio.cict.fr/m/micrococcus.html Podschun, R., & Ullmann, U. (1998). Klebsiella spp. as nosocomial pathogens: epidemiology, taxonomy, typing methods, and pathogenicity factors. Clinical Microbiology Reviews, 11(4), 589-603. Podschun, R., Pietsch, S., Holler, C., & Ullmann, U. (2001). Incidence of Klebsiella species in surface waters and their expression of virulence factors. Applied and Environmental Microbiology, 67(7), 3325-3327. doi:10.1128/AEM.67.7.33253327.2001 Guideline manual for drinking water quality monitoring and assessment: 2nd edition www.ijpsi.org 41 | P a g e
  • 5. Klebsilla: In Drinking Water [14] [15] Geldreich, the Bacteriology of Water. Chapter 15: in Leslie Collier, Albert Balows, Max Sussman editors. Topley Wilson’s Microbiology and Microbial Infections 9th ed, London, hodder Arnold; 2005, p351-363. Indian Council of Medical Research. Manual of Methods for the Examination of Water Sewage of Industrial Wastes. ICMR Special Reports, series no 47, 1953. www.ijpsi.org 42 | P a g e