B. Sawyer et al., BACTERIAL AEROSOL EMISSION RATES FROM MUNICIPAL WASTE-WATER AERATION TANKS, Applied and environmental microbiology, 59(10), 1993, pp. 3183-3186
In this report we describe the results of a study conducted to determi
ne the rates of bacterial aerosol emission from the surfaces of the ae
ration tanks of the Metropolitan Water Reclamation District of Greater
Chicago John E. Egan Water Reclamation Plant. This study was accompli
shed by conducting test runs in which Andersen six-stage viable sample
rs were used to collect bacterial aerosol samples inside a walled towe
r positioned above an aeration tank liquid surface at the John E. Egan
Water Reclamation Plant. The samples were analyzed for standard plate
counts (SPC), total coliforms (TC), fecal coliforms, and fecal strept
ococci. Two methods of calculation were used to estimate the bacterial
emission rate. The first method was a conventional stack emission rat
e calculation method in which the measured air concentration of bacter
ia was multiplied by the air flow rate emanating from the aeration tan
ks. The second method was a more empirical method in which an attempt
was made to measure all of the bacteria emanating from an isolated are
a (0.37 m2) of the aeration tank surface over time. The data from six
test runs were used to determine bacterial emission rates by both calc
ulation methods. As determined by the conventional calculation method,
the average SPC emission rate was 1.61 SPC/m2/s (range, 0.66 to 2.65
SPC/m2/s). As determined by the empirical calculation method, the aver
age SPC emission rate was 2.18 SPC/m2/s (range, 1.25 to 2.66 SPC/m2/s)
. For TC, the average emission rate was 0.20 TC/m2/S (range, 0.02 to 0
.40 TC/m2/S) when the conventional calculation method was used and 0.2
7 TC/m2/s (range, 0.04 to 0.53 TC/m2/s) when the empirical calculation
method was used. The fecal coliforms and fecal streptococci both had
emission rates that were much lower than the SPC and TC emission rates
. Our estimates of bacterial source strength emission rates should be
useful in any future dispersion modeling work performed at this or any
other water reclamation plant in which the activated sludge process i
s used.