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Applied and Environmental Microbiology, October 2001, p. 4908-4913, Vol. 67, No. 10
0099-2240/01/$04.00+0 DOI: 10.1128/AEM.67.10.4908-4913.2001
Copyright © 2001, American Society for Microbiology. All rights reserved.
Evidence for Detachment of Indigenous Bacteria from
Aquifer Sediment in Response to Arrival of Injected Bacteria
W. P.
Johnson,1,*
P.
Zhang,1
P. M.
Gardner,1
M. E.
Fuller,2 and
M. F.
DeFlaun2
Department of Geology and Geophysics,
University of Utah, Salt Lake City, Utah
84112,1 and Envirogen, Inc.,
Lawrenceville, New Jersey 086482
Received 11 May 2001/Accepted 4 July 2001
 |
ABSTRACT |
Two bacterial strains isolated from the aquifer underlying Oyster,
Va., were recently injected into the aquifer and monitored using
ferrographic capture, a high-resolution immunomagnetic technique. Injected cells were enumerated on the basis of a vital fluorescence stain, whereas total cell numbers (stained target cells plus unstained target and antigenically similar indigenous bacteria) were identified by cell outlines emanating from fluorophore-conjugated antibodies to
the two target strains. The arrival of injected bacteria at the
majority of monitored sampling ports was accompanied by simultaneous temporary increases in unstained cell counts that outnumbered the
injected bacteria by 2- to 100-fold. The origin and mechanism of
appearance of the unstained cells are considered.
 |
TEXT |
Little is known about the
hydrodynamic environment experienced by bacteria attached to sediment
grain surfaces in groundwater aquifers. Laboratory studies of other
colloidal materials have determined that hydrodynamic interactions
between mobile and attached colloids prevent the attachment of mobile
colloids within a given distance of attached colloids, an effect known
as hydrodynamic scattering (1) or the shadow effect
(9). Force balance calculations also indicate that
hydrodynamic interactions between mobile and attached colloids can be
expected to result in enhanced detachment of attached colloids, even
for dilute solutions (2, 3). This report describes field
data that indicate that hydrodynamic interactions between mobile and
attached bacteria may indeed be relevant to bacterial transport in groundwater.
The experiments were performed at the U.S. Department of Energy
Natural and Accelerated Bioremediation (NABIR) South Oyster (SO) field
site, in Oyster, Va., on the southern Delmarva Peninsula. The SO and
Narrow Channel (NC) focus areas are two locations at the site where
flow cells to study bacterial transport have been installed. The flow
cells at both sites are bordered on the down-gradient end by
groundwater extraction wells used to set up a steady-state flow field
prior to injection experiments. Within each flow cell are 24 custom-made multilevel samplers (MLS) (8), each possessing 12 sampling ports vertically spaced approximately 30 cm apart within
the lower 3 m of the shallow sandy aquifer. The MLS designs and
flow cell installation at the two focus areas are described in further
detail elsewhere (8).
Two bacterial strains were used in this study. DA001 is an aerobic,
adhesion-deficient variant of an isolate originally obtained from the
NC focus area and has been identified as a Comamonas sp.
OY-107 is a facultative iron-reducing bacterium of the genus Acidovorax that was naturally adhesion deficient when it was
isolated from the SO site. DA001 and OY-107 are gram-negative rods
approximately 1.2 by 0.6 µm and 1.9 by 1.0 µm in size,
respectively. The organisms were grown at Envirogen, Inc., on acetate
(NC experiment) or lactate (SO experiment) using standard fermentation
procedures and were harvested by centrifugation (6,
7). The injected DA001 and OY-107 cells were labeled using the
green fluorescent vital stain 5- (and 6)-carboxyfluorescein
diacetate, succinimidyl ester (CFDA/SE), and the red fluorescent vital
stain 5- (and 6)-carboxytetramethylrhodamine succinimidyl
ester (TAMRA/SE) as described elsewhere (6, 7). Examination of the stained cells via epifluorescence microscopy and
flow cytometry showed that at most 1 to 5% of the population of cells
were not visibly fluorescent after the staining procedure (6,
7; Fuller et al., unpublished).
Transport of DA001 at the NC focus area was examined in an experiment
performed during October 1999, whereas simultaneous transport of DA001
and OY-107 was examined at the SO focus area during August 2000. One
week prior to injection at each site, a forced hydraulic gradient was
established by withdrawing groundwater at the down-gradient wells in
order to achieve an average site pore water velocity of 1 m
day
1 through the flow cells. The NC injection
solution was composed of 90% CFDA/SE-stained DA001 cells and 10%
13C-labeled unstained DA001 cells, with a total
concentration of 108 cells
ml
1. The 13C-labeled
cells are relevant to this report insofar as this fraction of the
injected cell suspension was unstained. For the SO field experiment,
all of the DA001 and OY-107 cells (5 × 107
cells ml
1 each) were internally stained with
TAMRA/SE and CFDA/SE, respectively; no 13C
labeling was performed. Both field experiments were done with an
injection system that preserved the groundwater chemistry (6, 8). Sampling infrastructure and sampling protocols used at the
NC and SO focus areas are described in detail elsewhere (6, 8). The samples were preserved in the field (1% [vol/vol]
formaldehyde) and shipped on ice to the University of Utah.
For the ferrographic capture analyses, polyclonal rabbit antibodies
(Rockland Immunochemicals, Inc., Gilbertsville, Pa.) raised to whole
cells of the target bacterial strains were used to tether goat
anti-rabbit-coated paramagnetic beads (50-nm diameter; Miltenyi Biotec,
Auburn, Calif.) to the surface of the target cells following sample
collection. The bacterium-bead suspension was then introduced into a
Bio-Ferrograph (Guilfoyle, Inc, Belmont, Mass.), which deposited the
magnetically tagged bacteria onto a small area of a glass substratum.
The bacteria were then enumerated under an epifluorescence microscope.
Further details are given elsewhere (8, 11, 12).
Aliquots of the anti-DA001 and anti-OY-107 antibodies were conjugated
to a green fluorophore, fluorescein isothiocyanate (FITC), used in
parallel analyses to allow the enumeration of unstained cells of target
and antigenically similar strains that may have been captured. The
FITC-conjugated antibodies provided fluorescent outlines of all
captured cells (hereafter referred to as total cell counts), whereas
the nonconjugated antibodies were not fluorescent. Hence, when the
nonconjugated antibodies were used in the analyses, only the stained
(injected) cells were visible (hereafter referred to as injected cell
counts). Examples of stained and FITC-outlined bacterial images are
given in the report of Zhang et al. (12). The number of
unstained bacteria (unstained target and antigenically similar
bacteria) in each sample was determined as the difference between the
total and the injected cell counts.
As stated above, the NC injection solution contained 10%
13C-labeled DA001 cells and 90% CFDA/SE-stained
DA001 cells. Also, for both experiments, a conservative maximum of 5%
of the injected cells that underwent the staining procedure may not
have been rendered internally fluorescent (6, 7; Fuller et
al., unpublished). To account for this initial unstained fraction of
the injected cells, a specified fraction of the injected cell counts
was subtracted from the difference between the total and the injected
cell counts. The specified fractions were 15% for NC samples (10%
13C labeled plus 5% inefficiently stained) and
10% for SO samples (5% inefficiently stained plus 5% conservative addition).
Standards for stained DA001 cells and stained OY-107 cells (~100
cells ml
1 mixed in NC artificial
groundwater, stored in plastic centrifuge tubes, and
refrigerated at 4°C) were analyzed every 10 samples to monitor
analytical error. For samples targeting the CFDA-stained bacteria,
analyses for total cell counts (injected cells plus unstained
target and antigenically similar cells) and injected cell counts were
performed separately, since the FITC-conjugated antibody and the
CFDA/SE stain fluoresced at similar wavelengths. For samples targeting
the TAMRA/SE-stained bacteria, total and injected cell counts targeting
DA001 were determined together (using the FITC-conjugated antibody),
since the FITC-conjugated anti-DA001 antibody and the TAMRA/SE stain
fluoresced at different wavelengths.
Triplicate analyses were performed using ferrographic capture of
serially diluted stained DA001 standards with nominal concentrations of
5,000, 500, 50, and 5 cells ml
1, which yielded
cell counts of 5,500 ± 800, 620 ± 30, 60 ± 11, and
11 ± 2 cells ml
1. The
corresponding analytical errors were 15, 5, 20, and 22%, respectively.
Blank samples showed values ranging from 0 to 6 cells
ml
1, causing the sample with the lowest
concentration to be significantly overestimated. A quantitation limit
of 20 cells ml
1 was therefore used in this
study, and cell counts of less than 20 cells
ml
1 were considered negligible. This degree of
resolution is unparalleled by other bacterial tracking techniques
(4, 6, 8).
Equivalent cell counts were obtained repeatedly over a month-long
period using the FITC-conjugated and nonconjugated antibodies and
refrigerated (4°C) standards (3,500 cells/ml) in NC groundwater and
NC artificial groundwater, with and without preservation with 1%
formaldehyde. The results also indicated that the internal stain was
stable for at least 1 month and that cell lysis and growth were not
significant under storage conditions. Triplicate recoveries from
standards of 570 cells ml
1 (DA001) and of 800 cells ml
1 (OY-107), analyzed separately and as
a mixture, showed no cross-reactivity of the antibodies to the two strains.
The number of cells captured by the FITC-conjugated anti-DA001 antibody
was low (<50 cells ml
1) across the NC site
prior to the arrival of injected cells (initial samples) (Fig.
1A). Unstained cell counts (unstained
target and antigenically similar cells) became significant during the
breakthrough of injected DA001 (difference between total and injected
cell counts after subtraction of 15% of the injected cell count) (Fig. 1A). During the breakthrough of injected DA001, unstained cell counts
in well M3 were relatively constant, ranging between 1,000 and 2,000 cells ml
1, despite order-of-magnitude
changes in injected DA001 counts (Fig. 1A). Well B3 exhibited two
pulses of injected DA001 (Fig. 1B). During the period between 25 and 42 days, unstained cell counts (600 to 800 cells
ml
1) were much higher than injected DA001
counts, by as much as a factor of 100. No unstained bacteria
accompanied the second pulse of injected DA001 in well B3. These
results indicate that unstained cell counts were not proportional to
injected DA001 counts during breakthrough at the NC site.

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FIG. 1.
Breakthrough at the NC focus area of injected DA001
(using nonconjugated anti-DA001 antibody [Abs]) and total cells
(injected DA001 plus unstained DA001 and antigenically similar cells
recovered using FITC-conjugated anti-DA001 antibody) in wells M3 and
B3. Unstained cell counts are shown as gray bars after
subtraction of 15% of the injected cell counts from the difference
between total and injected cell counts.
|
|
Examples of cell breakthrough during the SO focus area experiment are
shown for MLS 12 port 4 (Fig. 2) and MLS
24 port 6 (Fig. 3). Prior to the
breakthrough of injected cells, insignificant total cell counts
determined by ferrographic capture were observed for the SO site (early
times in Fig. 2 and 3), corroborating plate counts for the same
samples. Breakthrough of the two injected strains was similar, with
three low-concentration breakthrough pulses of DA001 (Fig. 2A) and
OY-107 (Fig. 2B) in MLS 12 port 4 and two low-concentration
breakthrough pulses of DA001 (Fig. 3A) and OY-107 (Fig. 3B) in MLS 24 port 6. Associated with the breakthrough of the injected cells were
pulses of unstained cells (difference between total and injected cell
counts after subtraction of 10% of the injected cell count). Unstained
cell counts were up to ninefold higher than injected cell counts (e.g.,
analyses with anti-DA001 antibody at 1.5 days in MLS 12 port 4) (Fig.
2A). It should be noted that the error bars are smaller than the
symbols for total cell counts obtained with anti-OY-107 antibody
between days 1 and 2 (Fig. 2B). Some breakthrough pulses of injected
bacteria did not show an accompanying pulse of unstained bacteria,
e.g., cell counts obtained with anti-OY-107 antibody at 5.5 days in MLS
24 port 6 (Fig. 3B). Furthermore, some wells showed no unstained cells
at any time during the breakthrough of injected cells, e.g., MLS 8 port
4 (Fig. 4). Although the difference
between total and injected cell counts slightly exceeded the 10%
tolerance used for SO samples at 4.5 days in Fig. 4, the difference in
this instance is not sufficient to be convincingly indicative of
unstained bacteria beyond those present in the injected solution.

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FIG. 2.
Breakthrough at SO focus area MLS 12 port 4 (S12/P4) of
injected DA001 (using nonconjugated anti-DA001 antibody [Abs]) and
total cells (using FITC-conjugated anti-DA001 antibody) and injected
OY-107 (using nonconjugated anti-OY-107 antibody) and total cells
(using FITC-conjugated anti-OY-107 antibody). Unstained cell counts are
presented as gray bars after subtraction of 10% of the injected cell
counts from the difference between total and injected cell counts.
Long-term data are shown in the inset graphs. Error bars show standard
deviations.
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FIG. 3.
Breakthrough at SO focus area MLS 24/port 6 (S24/P6) of
injected DA001 (using nonconjugated anti-DA001 antibody [Abs]) and
total cells (using FITC-conjugated anti-DA001 antibody) and injected
OY-107 (using nonconjugated anti-OY-107 antibody) and total cells
(using FITC-conjugated anti-OY-107 antibody). Unstained cell counts are
presented as gray bars after subtraction of 10% of the injected cell
counts from the difference between total and injected cell counts.
Long-term data are shown in the inset graphs. Error bars show standard
deviations.
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FIG. 4.
Breakthrough at SO focus area MLS 8/port 4 (S8/P4) of
injected DA001 (using nonconjugated anti-DA001 antibody [Abs]) and
total cells (using FITC-conjugated anti-DA001 antibody). Unstained cell
counts are presented as a gray bar after subtraction of 10% of the
injected cell counts from the difference between total and injected
cell counts.
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|
Longer-term breakthrough of the two strains in the same MLS ports as
those described above (shown in the insets in Fig. 2 and 3) indicated
that above a certain injected cell concentration, unstained cells were
not detectable as the difference between total and injected cell
counts. Unstained cell counts at about 4.5 days in inset Fig. 2A and
about 8 days in inset Fig. 3A were associated with near-unity ratios of
total to injected cell counts and so were close to unstained cell
counts expected to exist within the injected population. The absence of
a significant number of unstained cells at higher injected cell counts
(higher than about 30,000 cells/ml) indicates that the capturable
unstained cells were limited in number.
The results clearly indicate that prior to the breakthrough of injected
cells the counts of unstained cells were negligible, whereas unstained
cell counts greatly increased simultaneously with the breakthrough of
injected cells, to values that often exceeded the injected cell counts.
There are several potential origins of these unstained cells, including
the injected bacterial population and the bacterial population
indigenous to the aquifer (not injected). Assuming that
unstained cells originated from the injected cell population,
their appearance at concentrations outnumbering injected cell
concentrations (by as much as a factor of 100) requires mechanisms to
selectively concentrate unstained cells relative to stained cells
during transport. Potential mechanisms include growth of injected cells
(with lack of stain transfer to daughter cells), loss of stain from
injected cells during transport, and less adhesion of unstained
relative to stained cells. Cell division was insignificant for stored
samples monitored over a 1-month period, as described above.
Furthermore, the lack of significant cell division during transport in
the field was indicated by close corroboration of injected DA001 cell
counts by culture plating (with identification based on unique colony
morphology), ferrographic capture, 13C
analyses, direct counting, and flow cytometry (8). Loss
of stain was negligible for both CFDA/SE and TAMRA/SE in
refrigerated (4°C), preserved (1% formaldehyde) samples monitored
over a month-long period (this study). Furthermore, loss of stain
during transport in the field was negligible, as indicated by flow
cytometric analyses of groundwater samples, which showed that the
per-cell fluorescence of CDFA/SE-stained DA001 did not change over a
period of more than 100 days in the aquifer at NC (6, 13).
Equivalent adhesion of stained and unstained cells during transport has
been shown with standard adhesion assays (5) and with
50-cm cores (7.2 cm in diameter) packed with NC site sediment
(interstitial velocity, 1 m day
1)
(4). Our results indicate that selective concentration of unstained cells during transport by the above mechanisms did not occur
to an extent that could explain the appearance of unstained cells at
concentrations far higher than the injected cell concentrations. However, even assuming that selective concentration of unstained cells
occurred during transport, it is difficult to explain the observed
temporal variations in unstained cell concentrations, that is, the
ephemeral pulse of unstained cells that was not detectable at higher
injected cell concentrations. In order to explain the observed
breakthrough behavior, selective concentration of unstained cells would
need to have occurred exclusively on the low-concentration fringes of
the injected bacterial plume, a possibility that cannot be
discounted but that seems unlikely.
Considering the possibility that unstained cells originated from the
cell population indigenous to the aquifer (not injected), potential
mechanisms of appearance include growth or detachment in response to
breakthrough of the injected bacterial plume. Increased shear forces
cannot explain the observations, since forced-gradient conditions were
imposed at least 1 week prior to injection. Appearance due to growth
seems unlikely, since no lag time was observed between the appearance
of the unstained cells and the breakthrough of the injected bacteria.
The progression of breakthrough in well B3 during the NC experiment
(Fig. 1) and in MLS 12 port 4 at the SO focus area (Fig. 2) indicates
that the highest ratios of unstained to injected cell concentrations
were associated with the earliest pulses of injected cells, whereas
subsequent pulses of similar concentrations of injected cells produced
lower relative unstained cell counts. This observation is consistent
with detachment from sediment of a limited population of weakly
attached cells in response to breakthrough of the injected bacterial
plume. Detachment could have occurred due to a number of mechanisms,
including slight shifts in groundwater chemistry (reviewed in reference
10) or hydrodynamic interactions with mobile injected
bacteria (2, 3), among others. Since no significant
changes in groundwater pH, ionic strength, or dissolved oxygen
accompanied the breakthrough of injected cells, it is plausible that
the appearance of unstained cells represented detachment in response to
hydrodynamic or other interactions with the injected bacteria.
 |
ACKNOWLEDGMENTS |
This work was funded by the U.S. Department of Energy (DOE)
Natural and Accelerated Bioremediation Research Program
(NABIR)
Acceleration Element (grant DE-FG03-99ER62820/A000).
We acknowledge the leadership of Frank Wobber. The long-term sampling
efforts of Keun-Hyung Choi and Leslie Ball and the excellent work of
David Stone in sample analyses also deserve heartfelt thanks and
praise. Access to the field site was granted by The Nature Conservancy,
Virginia Coast Reserve.
 |
FOOTNOTES |
*
Corresponding author. Mailing address: Department of
Geology and Geophysics, 135 South, 1460 East, University of Utah, Salt Lake City, UT 84112. Phone: (801) 581-5033. Fax: (801) 581-7065. E-mail: wjohnson{at}mines.utah.edu.
 |
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Applied and Environmental Microbiology, October 2001, p. 4908-4913, Vol. 67, No. 10
0099-2240/01/$04.00+0 DOI: 10.1128/AEM.67.10.4908-4913.2001
Copyright © 2001, American Society for Microbiology. All rights reserved.
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