Assessment of E. coli in sediments of an urban watershed
Demaria, A.1, M. Mikesell1,
and L.Yustik2
1Environmental Consulting
& Technology, Inc. MI, U.S.A.2
Macomb County Office of Public Works, MI. U.S.A.
Abstract
The Bear Creek
drainage district, located in Oakland and Macomb Counties in southeast
Michigan, encompasses 19 square miles of concentrated residential,
commercial and industrial development. The drainage district is
served by 29 smaller county drains that are tributary to Bear Creek.
The goal of the current work in the district is to identify and
eliminate sources of E. coli contamination in the Creek.
The first step is to identify sources of E. coli entering the watercourse
through systematic sampling and testing of the Bear Creek and its
tributaries.
The water quality data collected in Bear Creek indicates that the
E. coli levels increase during wet weather. The cause of this
increase is likely caused by (i) sewage entering the storm drains,
(ii) bacteria washed off the land surface into drainage systems
with the storm water, and/or (iii) re-suspension of bacteria associated
with sediments deposited in the collection system.
Four of the large drains that contribute to Bear Creek pass under
a major road through inverted siphons. Sediments accumulate in the
siphons, which are continuously under water. It was postulated that
these sediments serve as a source for bacteria. A diver was contracted
by Macomb County Public Works Office to sample the sediments that
have accumulated in each siphon. The results of the sampling indicated
that high levels of bacteria - in some cases over 2,000,000 cfu/100g
- exist in the sediments.
Sediment samples were also collected at ten locations
in the open portion of Bear Creek. A hand auger was used to collect
two samples from a depth of 8-12" of sediment from each location.
Samples were divided according to sediment type and placed into
separate containers. Typically the upper layer was comprised of
sand and gravel, while the bottom layer was silt or clay. E.
coli levels in the upper layer averaged over 60,000 cfu/100
g, while the lower layer contained an average of about 27,000 cfu/100
g.