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USEPA
Information Collection Requirements rule for the collection and
analysis of samples for protozoa and enteric viruses (U.S.
Environmental Protection Agency, 1995a, 1995b). Indicator
bacteria samples were collected and analyzed by the USGS
according to procedures described in Myers and Wilde (1997).
In addition to the above microbiological species, samples were
collected and analyzed for chemical constituents, such as
nutrients, total organic carbon, and tritium, that may serve as
indicators of possible surface contamination of the aquifer. All
chemical analyses were done by USGS laboratories in Arvada,
Colorado, or Ocala, Florida. Onsite analysis of specific
conductance, pH, temperature, dissolved oxygen, and alkalinity
were done at each PWS well according to procedures described by
Wilde and Radtke (1997).
Preliminary Results
Results from the first round of enteric virus, coliphage, and
fecal indicator bacteria sample collection are shown in figure 4.
Of the 109 PWS wells sampled, 86 showed no presence of
microbiological contamination. However, human enteric viruses
were present in 9 of the 109 PWS wells at densities near the
lower level of analytical detection. Contrary to what might be
expected, most of the enteric virus contamination was observed
outside the areas characterized as primary and secondary karst.
Coliphage were observed in samples collected from 9 of the 109
wells--1 of which was a control site located in the Mississippi
Alluvial Plain. Coliphage and enteric viruses were present in two
wells located near the northern boundary of the Ozark Plateau
aquifer system along the Missouri River. Fecal indicator bacteria

Virus sampling equipment and
public-water-supply well.
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Ozark and St. Francois aquifers. In addition, four PWS wells
were selected as control sites. Two of the control sites are
located in western Missouri where the Ozark aquifer is confined
by the Ozark confining unit, the Springfield Plateau aquifer, and
the Western Interior Plains confining system, and two are located
in the Mississippi Alluvial Plain of southeastern Missouri (fig.
2).
Only community wells-municipal, PWS district, subdivision, and
mobile home park-constructed in the last 15 years were

Forested land use in the Ozark Plateaus.
Photo courtesy of S.R. Femmer,
U.S. Geological Survey.

Agricultural land use in the Ozark
Plateaus.
Photo courtesy of B.J. Smith,
U.S. Geological Survey.
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considered. This study was designed to eliminate type of well
construction as a variable for microbiological contamination so
that interpretation could be limited to hydrogeology and land
use. Well-selection criteria were based on availability of well
construction and completion records (well and casing depth, size,
and type), well operation and maintenance history, current usage,
and geology. Finally, an attempt was made to obtain fairly even
areal and vertical coverage in the aquifer and to represent the
different land uses in the Ozark Plateaus.
Sample Collection and Analysis
The first round of sampling was completed in July 1997.
Samples from each PWS well were analyzed for the following
microbiological species-total human enteric viruses,
male-specific and somatic coliphage, and fecal indicator bacteria
[fecal coliform, Escherichia coli (E. coli), and fecal
streptococci]. Coliphage are viruses that attack E. coli and are
being studied as possible indicators of the presence of human
enteric viruses. The enteric virus and coliphage samples were
collected by the USGS at the selected wells. Samples represent
untreated water from the aquifer. Enteric virus and coliphage
samples were analyzed by the University of New England in
Biddeford, Maine, according to procedures described in the
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