Standard methods for the examination of water and sewageAmerican Public Health Association. Laboratory Section
Science
Standard methods for the examination of water and sewage
American Public Health Association. Laboratory Section
Sewage -- Analysis; Water -- Analysis
The procedure to this point must be carried out in the field, but after
the acid has been added and the stopper replaced there is no further
change, and the rest of the test may be performed within a few hours, as
convenient. Transfer 200 cc. of the contents of the bottle to a flask
and titrate with N/40 sodium thiosulfate, using a few cubic centimeters
of the starch solution as indicator toward the end of the titration. Do
not add the starch solution until the color has become faint yellow, and
titrate until the blue color disappears.
The use of potassium permanganate is made necessary by high nitrite or
organic matter. The procedure outlined must be followed in all work on
sewage and partly purified effluents or seriously polluted streams or
samples whose nitrite nitrogen exceeds 0.1 part per million. In testing
other samples the procedure may be shortened by beginning with the
addition of the manganous sulfate solution and proceeding from that
point as outlined, except that only 1 cc. of alkaline potassium iodide
need be added.
_Calculation of Results._—Oxygen shall be reported in parts per million
by weight. It is sometimes convenient to know the number of cubic
centimeters per liter of the gas at 0°C. temperature and 760 mm.
pressure and also to know the percentage which the amount of gas present
is of the maximum amount capable of being dissolved by distilled water
at the same temperature and pressure. If 200 cc. of the sample is taken
the number of cubic centimeters of N/40 thiosulfate used is equal to
parts per million of oxygen. Corrections for volume of reagents added
amount to less than 3 per cent and are not justified except in work of
unusual precision. To obtain the result in cubic centimeters per liter
multiply the number of cubic centimeters of thiosulfate used by 0.698.
To obtain the result in percentage of saturation divide the number of
cubic centimeters of thiosulfate by the figure in Table 14 opposite the
temperature of the water and under the proper chlorine figure. The last
column of Table 14 permits interpolation for intermediate chlorine
values. At elevations differing considerably from mean sea level and for
accurate work attention must be given to barometric pressure, the normal
pressure in the region being preferable to the specific pressure at the
time of sampling. The term “saturation” refers to a condition of
equilibrium between the solution and an oxygen pressure in the
atmosphere corresponding to 158.8 millimeters, or approximately
one-fifth atmosphere. The true saturation or equilibrium between the
solution and pure oxygen is nearly five times this value, and
consequently values in excess of 100 per cent saturation frequently
occur in the presence of oxygen-forming plants.
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