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Quantitative Study on Microbial Pollution of River ... - GANGAPEDIA

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♦ It should affect the quality <strong>of</strong> water — (i) before<br />

drains from city discharge; (ii) inside city; and (iii) after<br />

the river leaves the city.<br />

SAMPLE SAMPLE COLLECTION<br />

COLLECTION<br />

Sample collecti<strong>on</strong> is a very important part <strong>of</strong> river study<br />

because c<strong>on</strong>clusi<strong>on</strong>s drawn are based <strong>on</strong>ly <strong>on</strong> the testing<br />

<strong>of</strong> collected samples. The purpose <strong>of</strong> taking samples is<br />

to obtain informati<strong>on</strong>, which in some way typifies the<br />

aquatic system from which samples are drawn 12 . Grab<br />

Sampling procedure was adopted as recommended by<br />

Standard Method for microbiological analysis. Samples<br />

were collected during lean seas<strong>on</strong>, <strong>on</strong> m<strong>on</strong>thly basis, for<br />

a period <strong>of</strong> four m<strong>on</strong>ths from March 2004 to June 2004.<br />

Three sets <strong>of</strong> water samples, from each sampling locati<strong>on</strong><br />

and for every sampling date, were collected for this study.<br />

(i) Water samples for microbiological examinati<strong>on</strong>,<br />

other than Helminth eggs, for BOD and COD<br />

determinati<strong>on</strong> were collected in n<strong>on</strong>-reactive<br />

borosilicate glass bottles <strong>of</strong> 500 ml capacity each that<br />

had been cleansed and rinsed carefully, given a final<br />

rinse with distilled water and sterilized. Samples were<br />

taken from the river by holding the bottle near its base<br />

in the hand and plunging it, neck downward, below<br />

the surface. Then turning the bottle until neck points<br />

slightly upward and mouth is directed toward the<br />

current. The sampling bottle was not filled up to the<br />

brim and 20 mm to 30 mm space was left for effective<br />

shaking <strong>of</strong> the bottle 13 .<br />

(ii) Water samples for Helminth eggs were collected in<br />

Table able 1 1 1 Summary Summary <strong>of</strong> <strong>of</strong> analytic analytic methods methods and and observed observed values<br />

values<br />

n<strong>on</strong>-reactive plastic bottles <strong>of</strong> 5 l capacity, which had<br />

been cleansed and finally rinsed with distilled water 14 .<br />

(iii) Water samples for DO determinati<strong>on</strong> were<br />

collected in BOD bottles (n<strong>on</strong>-reactive borosilicate<br />

glass bottles <strong>of</strong> 300 ml capacity). The DO was fixed by<br />

standard procedure Onsite, just after collecti<strong>on</strong> 13 .<br />

SAMPLE SAMPLE PRESER PRESERVATION<br />

PRESER TION TION AND AND STORAGE<br />

STORAGE<br />

Microbiological analysis <strong>of</strong> water samples was started<br />

as so<strong>on</strong> as possible after collecti<strong>on</strong> to avoid unpredictable<br />

changes in the microbial populati<strong>on</strong> 15 . As the samples<br />

cannot be processed within 1 h after collecti<strong>on</strong>, therefore<br />

for most accurate results, samples were brought in iced<br />

insulated c<strong>on</strong>tainer, during transport from Delhi to IIT<br />

Roorkee laboratory.<br />

ANAL ANALYSIS ANAL YSIS OF OF SAMPLES<br />

SAMPLES<br />

The Samples were analyzed in accordance with the<br />

standard methods. The techniques, instruments and<br />

principles involved in arriving at different parameters<br />

are tabulated in Table 1.<br />

RESUL RESULTS RESUL RESULTS<br />

TS<br />

The variati<strong>on</strong> in water quality parameters determined<br />

through the analysis <strong>on</strong> site and in laboratory at Indian<br />

Institute <strong>of</strong> Technology, Roorkee (India) were reported<br />

in Table 1. The l<strong>on</strong>gitudinal pr<strong>of</strong>ile <strong>of</strong> various microbial<br />

parameters is shown in Figure 2. The L<strong>on</strong>gitudinal<br />

pr<strong>of</strong>iles <strong>of</strong> BOD, COD and DO values were shown in<br />

Figure 3.<br />

Parameters Parameters Principle Principle Principle<br />

Instruments/ Instruments/ technique technique used used<br />

Observed Observed values values<br />

values<br />

Minimum Minimum Maximum Maximum Maximum Average verage<br />

Temperature, °C Metric Thermometer 19 36 28<br />

pH Metric Digital pH meter 7 9.2 7.5<br />

TDS, mg/l Metric Digital TDS meter 190 700 460<br />

Turbidity, NTU Nephelometric Digital Turbidity Meter 3.6 52.0 32.1<br />

DO, mg/l Volumetric Modified Winkler’s method<br />

BOD, mg/l Volumetric Winkler’s method, incubati<strong>on</strong> for 3 days<br />

COD, mg/l Closed Reflux, colorimetric Hach COD system (DR/ 4000 U<br />

TC, MPN/100 ml MPN index Lauryl tryptose broth, incubati<strong>on</strong><br />

FC, MPN/100 ml MPN index EC Medium, incubati<strong>on</strong> temperature<br />

HPC, CFU/ml Total plate count Pour plate method, plate count agar,<br />

Coliphages, per ml Equati<strong>on</strong>s (APHA 9211 D 3) Inte-relati<strong>on</strong>ship<br />

Titrant — N/40 Na 2 S 2 O 3 Ind — starch 0.0 8.2 1.5<br />

at 27°C (IS : 3025 part 4, 1993) 3.0 52.0 34.2<br />

spectrophotometer) set at λ = 600 nm 6.0 120.0 75.5<br />

temperature 35 ± 0.5°C for 24 h to 48 h 2.1E04 4.3E07 9.3E06<br />

44.5 ± 0.2°C for 24 ± 2 h 3.9E03 3.9 E 07 4.6 E 06<br />

incubati<strong>on</strong> temperature 35°C for 48 h,<br />

digital col<strong>on</strong>y counter 2.4E03 1.5E06 2.6E05<br />

between TC and coliphages, FC<br />

Helminth eggs, Microscopic count Modified Bailenger method,<br />

and coliphages 5.2E03 9.0E08 1.2E08<br />

per ml centrifuge (1000 g), compound microscope 5 38 23<br />

58 IE(I) Journal–EN

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