A multidisciplinary research team, funded by the U.S. Department of En
ergy (DOE) Subsurface Science Program, initiated a field-scale bacteri
al transport study in a sandy aquifer on the coastal plain of Virginia
in 1994. The purpose of the study was to evaluate the relative import
ance of hydrogeological and geochemical heterogeneity in controlling b
acterial transport. Extensive geophysical and geochemical characteriza
tion of the site was accomplished using intact cores obtained during t
he construction of the flow field and in a nearby sand pit exposure of
the sedimentary facies found in the flow field. Geophysical technique
s, including ground penetrating radar and cross borehole tomography, w
ere used to relate the depositional environment of the sand pit to the
flow field as well as to produce a 3-dimensional depiction of the flo
w field to be used in modeling the site and the results of the injecti
on experiments. The 30 m long flow cell consists of ground water produ
ction and injection wells, a tracer injection well, and 10 multilevel
samplers screened every half meter from 4.0 to 10.5 m below ground sur
face, The organization that owns the field site required that only nat
ive microorganisms be introduced at the site, therefore, the injected
bacterial strain was isolated from the indigenous community in the aqu
ifer. Candidate strains were selected by a protocol that enriched for
phenotypes of low adhesion and non-clinical antibiotic resistance whic
h could be used to detect the organism on selective media. The bacteri
a were selected for low adhesion to site sediments so that they might
be readily transported through the aquifer. For the field injection ex
periment detection and quantitation of the strain chosen by this scree
ning process, PL2W31, was accomplished by isotopically enriching the c
ells with [C-13]glucose. Forced gradient conservative (Br-) tracer tes
ts were performed immediately prior to the bacterial injection experim
ent to provide a measure of non-reactive transport through the aquifer
. The non-reactive tracer test indicated the presence of hydrogeologic
al heterogeneities at the site that caused differential breakthrough o
f the tracer. Results from the bacterial transport experiment indicate
that bacteria traveled the length of the Row field (4 m), but that th
e majority of the biomass injected was retained in the sediments betwe
en the injection well and the first multilevel sampler at 0.5 m. Preli
minary bacterial transport models indicate that the observed behavior
could be accounted for by the presence of two subpopulations within a
single bacterial strain with differing transport properties.