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Science of Water : Concepts and Applications

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Environmental Biomonitoring, Sampling, <strong>and</strong> Testing 281<br />

2. Sample procedure:<br />

A. Keep the sample bottle unopened after sterilization until the sample is to be collected.<br />

B. Remove the bottle stopper <strong>and</strong> hood or cap as one unit. Do not touch or contaminate<br />

the cap or the neck <strong>of</strong> the bottle.<br />

C. Submerge the sample bottle in the water to be sampled.<br />

D. Fill the sample bottle approximately three quarters full, but not less than 100 mL.<br />

E. Aseptically replace the stopper or cap on the bottle.<br />

F. Record the date, time, <strong>and</strong> location <strong>of</strong> sampling, as well as the sampler’s name <strong>and</strong> any<br />

other descriptive information pertaining to the sample.<br />

3. Sample preservation <strong>and</strong> storage—examination <strong>of</strong> bacteriological water samples should<br />

be performed immediately after collection. If testing cannot be started within one hour<br />

<strong>of</strong> sampling, the sample should be iced or refrigerated at 4°C or less. The maximum recommended<br />

holding time for fecal coliform samples from wastewater is 6 h. The storage<br />

temperature <strong>and</strong> holding time should be recorded as part <strong>of</strong> the test data.<br />

Multiple Tube Fermentation Technique<br />

The multiple fermentation technique for fecal coliform testing is useful in determining the fecal<br />

coliform density in most water, solid, or semisolid samples. Wastewater testing normally requires<br />

use <strong>of</strong> the presumptive <strong>and</strong> confi rming test procedures. It is recognized as the method <strong>of</strong> choice for<br />

any sample that may be controversial (enforcement related). The technique is based on the most<br />

probable number <strong>of</strong> bacteria present in a sample that produces gas in a series <strong>of</strong> fermentation tubes<br />

with various volumes <strong>of</strong> diluted sample. The MPN is obtained from charts based on statistical studies<br />

<strong>of</strong> known concentrations <strong>of</strong> bacteria.<br />

The technique utilizes a two-step incubation procedure. The sample dilutions are fi rst incubated<br />

in lauryl (sulfonate) tryptose broth for 24–48 h (presumptive test). Positive samples are then<br />

transferred to EC broth <strong>and</strong> incubated for an additional 24 h (confi rming test). Positive samples<br />

from this second incubation are used to statistically determine the MPN from the appropriate<br />

reference chart.<br />

A single media, 24-h procedure is also acceptable. In this procedure, sample dilutions are inoculated<br />

in A-1 media <strong>and</strong> are incubated for 3 h at 35°C, then incubated the remaining 20 h at 44.5°C.<br />

Positive samples from these inoculations are then used to statistically determine the MPN value<br />

from the appropriate chart.<br />

Fecal Coliform MPN Presumptive Test Procedure<br />

1. Prepare dilutions <strong>and</strong> inoculate fi ve fermentation tubes for each dilution.<br />

2. Cap all tubes, <strong>and</strong> transfer to incubator.<br />

3. Incubate 24 + 2 h at 35 ± 0.5°C.<br />

4. Examine tubes for gas.<br />

A. Gas present = Positive test—transfer<br />

B. No gas = Continue incubation<br />

5. Incubate total time 48 ± 3 h at 35 ± 0.5°C<br />

6. Examine tubes for gas.<br />

A. Gas present = Positive test—transfer<br />

B. No gas = Negative test<br />

√ Note: Keep in mind that the fecal coliform MPN confi rming procedure using A-1 broth test<br />

is used to determine the MPN/100 mL. The MPN procedure for fecal coliform determinations<br />

requires a minimum <strong>of</strong> three dilutions with fi ve tubes/dilution.<br />

Calculation <strong>of</strong> Most Probable Number (MPN)/100 mL<br />

The calculation <strong>of</strong> the MPN test results requires selection <strong>of</strong> a valid series <strong>of</strong> three consecutive<br />

dilutions. The number <strong>of</strong> positive tubes in each <strong>of</strong> the three selected dilution inoculations is used<br />

to determine the MPN/100 mL. In selecting the dilution inoculations to be used in the calculation,

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