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Journal of Bacteriology, July 2000, p. 3809-3815, Vol. 182, No. 13
0021-9193/00/$04.00+0
Copyright © 2000, American Society for Microbiology. All rights reserved.
Physical Morphology and Surface Properties of
Unsaturated Pseudomonas putida Biofilms
Ilene D.
Auerbach,1,2
Cody
Sorensen,2
Helen G.
Hansma,2 and
Patricia
A.
Holden1,*
Donald Bren School of Environmental Science
and Management1 and Department of
Physics,2 University of California, Santa
Barbara, California 93106
Received 10 January 2000/Accepted 2 April 2000
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ABSTRACT |
Unsaturated biofilms of Pseudomonas putida, i.e.,
biofilms grown in humid air, were analyzed by atomic force microscopy
to determine surface morphology, roughness, and adhesion forces in the
outer and basal cell layers of fresh and desiccated biofilms. Desiccated biofilms were equilibrated with a 75.5% relative humidity atmosphere, which is far below the relative humidity of 98 to 99% at
which these biofilms were cultured. In sharp contrast to the effects of
drying on biofilms grown in fluid, we observed that drying caused
little change in morphology, roughness, or adhesion forces in these
unsaturated biofilms. Surface roughness for moist and dry biofilms
increased approximately linearly with increasing scan sizes. This
indicated that the divides between bacteria contributed more to overall
roughness than did extracellular polymeric substances (EPS) on
individual bacteria. The EPS formed higher-order structures we termed
mesostructures. These mesostructures are much larger than the discrete
polymers of glycolipids and proteins that have been previously
characterized on the outer surface of these gram-negative bacteria.
 |
INTRODUCTION |
Bacteria in the environment and in
vivo frequently live as biofilms where cells are embedded in a matrix
of bacterially produced extracellular polymeric substances (EPS)
(7, 10). Biofilms occur extensively in aquatic systems,
where they are implicated in industrial concerns such as biofouling and
corrosion (21), and where they are also implicated in drug
resistance (17) and dental caries (37). In waste
treatment systems such as trickling filters, wet biofilms are studied
for their roles in catalyzing pollutant transformations
(58). Generally, the morphologies of biofilms that occur in
aquatic systems are mushroom-like (11) with stalked
EPS-encapsulated cells growing from the substratum and channels for
fluid flow (54) around and through the stalks (11). This well-characterized structure of aquatic biofilms is now understood to facilitate cell-cell communication
(12).
In the absence of fluid flow, however, such as in soil systems (8,
19), in food, or on plant leaf surfaces (38), biofilms may appear as patchy films or dense microcolonies. These biofilms are
unsaturated; i.e., they grow in an environment that is only transiently
wet. From continuously wet to mostly dry environments, biofilms
probably show a range of morphologies that are environment dependent.
Correspondingly, the view of biofilms from studying aquatic systems may
be only a window to the variety of morphological and functional forms
that biofilms may take.
The immediate purpose of this work was to build upon earlier work
regarding mass transfer characteristics (31) of unsaturated Pseudomonas putida biofilms by examining physical
characteristics at the air-biofilm interface that could contribute to
high overall mass transfer resistance for substances diffusing through
unsaturated biofilms. In aquatic systems, channels in the biofilm
matrix act as conduits for nutrient resupply and waste removal
(54). In unsaturated systems, however, air-biofilm
interphase mass transfer and diffusion within the biofilm matrix are
the primary mechanisms for mass delivery (31). Our
perspective is that just as mass transfer studies and confocal
microscopy of aquatic biofilms have facilitated a relatively
sophisticated understanding of biofilm structure in aquatic systems, a
better understanding of unsaturated biofilm structure and function can
be facilitated through combined mass transfer and morphological
studies. We regard investigation of the air-biofilm interface as one
step to understanding mass transfer-related characteristics of dense
biofilms that occur in unsaturated systems. In response, the work
reported here was to characterize the roughness, force characteristics,
and morphology of the unsaturated biofilm-air interface. To perform our
work, we relied on a contemporary tool in high-resolution biomaterials probing and imaging, the atomic force microscope (AFM). AFM can provide
surface morphological and physical information in essentially a
nondestructive manner (5, 22, 25, 52). AFM has been used to
study bacterial colonization of submerged steel (53), to
examine growth at oil-water interfaces (20), and to probe cell membrane elasticity (1, 59) and the adhesive properties of artificial bacterial lawns (47, 48). Here, we extend the use of bacterial AFM through our studies of the morphology and surface
characteristics of native unsaturated biofilms that have been cultured
and treated using conditions that commonly occur in unsaturated
environments. By studying unsaturated biofilms directly and at high
resolution, we strengthen our hypothesis that biofilms are
morphologically different in unsaturated systems and thus merit further
study and description.
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MATERIALS AND METHODS |
Biofilm culturing.
P. putida mt-2 (Gary Sayler,
University of Tennessee) was sampled from
80°C stock cultures (in
70% Luria broth [LB]-30% glycerol) and inoculated directly onto
Nuclepore 0.1-µm-pore-diameter polycarbonate filters (Corning, Acton,
Mass.) overlaying LB agar. By visual observation, the amount of biomass
inoculated onto the membrane was insignificantly small compared to the
fully mature biofilms used in our studies. Biofilms were cultured at
27°C and harvested at various time intervals in order to study the
effects of biofilm age on biofilm surface properties and morphology.
Sample preparation.
Biofilms on filters were handled under
sterile conditions until just prior to imaging and were prepared
according to one of four treatment combinations: fresh and unwashed,
dried and unwashed, fresh and washed, or fresh and dried. These
treatments were selected because they mimic the environmental
conditions that biofilms in unsaturated environments experience during
transient cycles of wetting and drying. Fresh biofilms on filters were
imaged without any alteration to the sample. Biofilms were dried on
filters by equilibrating with a 75.5% relative humidity (RH) air
atmosphere. This RH is equivalent to a water potential of approximately
38 MPa (41), which is on the lower end of water stress
tolerable by any bacteria (27). Washed biofilms on filters
were rinsed with 100 µl of sterile MilliQ water (Millipore,
Burlington, Mass.). Following preparation, filters with biofilms were
transferred onto freshly cleaved mica disks (33) for
imaging. Adhesion of unwashed biofilms on filters to the mica disk was
facilitated by placing either a 10-µl drop of MilliQ water underneath
the filter or a piece of double-stick Scotch tape (3M Corp., St. Paul, Minn.) between the mica and filter. The difference in method of adhesion did not appear to affect the data, but the double-stick tape
provided a more stable substrate for AFM imaging.
AFM operation.
The biofilms were imaged in either contact
mode or tapping mode, using a Nanoscope III MultiMode AFM (Digital
Instruments, Santa Barbara, Calif.). The contact mode is the imaging
mode used to provide morphological data in conjunction with force
mapping (33). Contact mode images were obtained using
V-shaped silicon nitride (Si3N4) Nanoprobe
cantilevers (Digital Instruments). In tapping mode, the tip oscillates,
touching the sample surface at the bottom of each oscillation (22,
26), and both height and phase images are captured. Tapping mode
images were obtained using silicon cantilevers with resonance
frequencies of ca. 200 to 350 kHz (Digital Instruments). New
cantilevers were used for each experiment to prevent sample
cross-contamination.
Force mapping.
The AFM was operated in force mode to analyze
the adhesion forces across the biofilm surface. The Nanoscope force
mapping was performed as previously described (33). Force
mapping was conducted in contact mode, using short, wide, V-shaped
silicon nitride cantilevers with spring constants of ca. 0.6 N/m. Force maps were captured in the relative trigger mode, using trigger thresholds, or maximum cantilever deflections, of 10 and 50 nm. The
force maps included 64 × 64 force plots containing 64 data points
per force plot. A Z-scan speed of 13.0 Hz was used, allowing a force
map to be completed every 10 min. Before force plots were acquired,
each sample was imaged in contact mode to ensure initial stability.
Force maps were captured using X-Y scan sizes of 4,000 nm or smaller.
This provides spacing between force plots of 62 nm or less. Force maps
were analyzed graphically to determine the median adhesion force for
each force map, i.e., the adhesion force such that half the points on
the force map had a lower adhesion force and half the points had a
higher adhesion force. This analysis of force maps represents a new
approach to systematize the data and to use the data to comparatively
analyze biofilm treatment effects.
Roughness analysis.
We used Nanoscope software (Digital
Instruments) to calculate the surface roughness parameters for the
height images. The images were flattened and plane fitted prior to
analysis. The surface roughness parameters calculated included the
Z range (the difference between the highest and lowest
points within a given area), the mean (the average of all the
Z values), the root mean square (RMS; the standard deviation
of the Z values), and the mean roughness (Ra; mean value of
the surface relative to the center plane) (50). In addition
to the roughness analysis of the entire biofilm image, the surface
roughness parameters were also calculated for a 200- to 300-nm × 200- to 300-nm box on all 2,000-nm or lower scan sizes to provide a
local roughness analysis of the extracellular polymers.
Estimating molecular masses of extracellular polymers.
For
molecules of known molecular mass, molecular volumes measured by AFM
correlate well with calculated molecular volumes (18, 45,
51). We measured diameters of extracellular structures but not
volumes, because the height of these crowded structures is unknown.
Molecular masses were estimated from these diameters by assuming
densities for the globular extracellular structures of 1 to 1.3 g/ml.
Statistical analysis.
Statistics were performed using the
Wilcoxon signed-rank test (34) to find any differences in
the surface roughness based on the effect of preparation.
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RESULTS |
Over 40 separate P. putida biofilms were analyzed by
AFM, with approximately equivalent representation of the various
treatments. The method of biofilm preparation affected the stability of
AFM imaging. Stabler, higher-quality AFM images were obtained with dried biofilms than with fresh biofilms. Also, stabler AFM images were
obtained with washed biofilms than with unwashed biofilms. When
biofilms grown on filters were washed with water, the upper layers of
the biofilm were usually removed, leaving a single layer of bacterial
cells on the filter. These washed biofilms offered an opportunity to
study bacterial cells at the base of the biofilm, rather than the top
layer of the biofilm with its many layers underneath. Age also affected
the image quality, causing the older specimens to become thick with
clumps of bacteria and, therefore, more unstable during imaging.
Individual bacteria varied around the expected dimensions of 1 by 2 µm (Fig. 1). Height images in Fig. 1
show the topographic profile of the biofilm surface, while phase images
show the substructural features in more detail. Bacterial flagella were
readily seen in some images (Fig. 1A and B), especially in areas devoid
of cells. The flagella were most easily seen on the filter where biofilms had flaked off the filter after drying. Flagella were also
seen in single-cell layer images at the edges of washed biofilms, as in
Fig. 1A, which shows a single cell thickness of the biofilm on the
edge. The flagella in Fig. 1B are nestled between two bacteria in the
biofilm; other images show elongated bacteria that appear to be in the
process of dividing (Fig. 1C and D,
arrows). These dividing cells were seen
in both the top and bottom cell layers in biofilms that had been
growing for 2 to 4 days.

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FIG. 1.
Bacterial flagella (A and B) and bacteria during cell
division (C and D, arrows). Flagella were seen both on the filter
adjacent to biofilm bacteria (A) and nestled between bacteria (B,
arrows). Shown are height (left) and phase (right) AFM images of
unsaturated P. putida mt-2 biofilms. Before AFM imaging,
biofilms were 1 day old, unwashed and undesiccated (A), 3 days old,
unwashed and desiccated (B), 2 days old, washed and desiccated (C), and
4 days old, unwashed and desiccated (D).
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FIG. 2.
Biofilm bacteria with crevasses (A) and ridges (B)
between cells. Surface plots of AFM height images emphasized surface
corrugations. Z (height) scales are 250 (A) and 150 (B)
nm/division. Unsaturated P. putida mt-2 biofilms were
unwashed, desiccated, and 4 (A) or 3 (B) days old before AFM imaging.
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In most biofilms there were valleys between the individual bacteria
(Fig. 1 and 2A). The valleys between bacteria were typically 40 to 120 nm deep, measured from the highest point on the adjacent bacteria. The
depth of these valleys may be even greater because the width of the AFM
tip makes it impossible to measure the depth of valleys that are too
deep and narrow for the tip to reach the bottom. Bacteria such as those
in Fig. 1 and 2A typically also showed indentations on their surfaces,
with depths of ~10 to 60 nm. These indentations are broad enough that
their depth can be measured accurately by AFM.
Instead of valleys, some biofilms exhibited ridges surrounding the
individual bacteria (Fig. 2B); these ridges were typically 20 to 70 nm
above the lowest point in the adjacent bacteria. Ridges were seen only
on the top layer of biofilm bacteria. Valleys, not ridges, were
observed in basal cell layers following washing. The ridges may be due
to variable production of EPS, such that EPS is sometimes produced in
such great quantity that it protrudes around the edges of the bacteria
and is more pronounced after the bacterial cytoplasm has shrunk
following biofilm drying (Fig. 2B). In other biofilms (Fig. 2A), there
may be much less EPS, so that the bacteria shrink and separate from one
another upon drying.
Extracellular mesostructures.
The EPS exhibited mesostructures
on the cells. Mesostructures were typically 40 to 70 nm in diameter
(Fig. 3), although some as small as 10 to
20 nm were occasionally observed (Fig. 3B). EPS mesostructures were
arranged in arrays that showed differences in appearance, varying from
rounded, spheroid structures (Fig. 3A and B) to worm-like structures
(Fig. 3C). Sometimes adjacent cells or adjacent regions on the same
cell showed both worm-like and spheroid structures (Fig. 3D). Some of
the mesostructures appeared in a hexagonal array (data not shown). In
general, the morphologies of mesostructures appeared to be independent
of the conditions used to prepare the biofilm for AFM imaging.

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FIG. 3.
EPS by AFM on unsaturated P. putida mt-2
biofilms according to sample preparation treatment and age. Before AFM
imaging, biofilms were 1 day old, unwashed and desiccated (A), 3 days
old, unwashed and desiccated (B), 2 days old, washed and desiccated
(C), and 2 days old, washed and undesiccated (D).
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The extracellular mesostructures that we observed were not artifacts
from the scanning of the AFM tip, as have been seen on the surface of
polymer films (35). Such tip artifacts are readily detected
because, upon zooming out, one sees a characteristic square pattern in
the center of the larger scan that clearly shows the tip-induced
changes during scanning of the smaller square area. In contrast, the
mesostructures on the surface of these biofilms are extremely stable
and resistant to damage or distortion by repeated scanning.
Biofilm roughness.
The surface roughness of the biofilms was
analyzed from over 450 AFM images on length scales ranging from 0.5 to
10 µm. These different length scales are visually depicted in the
diagram at the top of Fig. 4 and the AFM
images of Fig. 4A to C. Figure 4, top, depicts a conceptual model of
three scales of surface roughness: across the extracellular polymers on
a single bacterium (A), across one or a few bacteria (B), and across
many bacteria on the biofilm surface (C). Images of small scan size
(Fig. 4A) reveal the organization of the mesostructures on the surface
of an individual bacterium in detail. Medium scan sizes (Fig. 4B)
depict the individual bacteria, the crevices between the bacteria, and
pores or pits on the surface of the bacteria. Large scan sizes (Fig.
4C) reveal the packing of bacteria at the biofilm surface, with
bacteria grouped next to each other in random organization. Unwashed,
multilayer biofilms also reveal bacteria emerging out from underneath
other bacteria, giving an impression of considerable crowding and
variation in cell size (e.g., Fig. 1C).

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FIG. 4.
Three scales of roughness on biofilms. (Top) Conceptual
diagram. (Bottom) AFM height images of unsaturated P. putida
mt-2 biofilms. Each of the three length scales provides different
values for roughness, which probably vary due to the predominating
surface feature at that scale: (A) within cells (0.5-µm scale),
mesoscale structures of EPS determine roughness; (B) across 1 or 2 cells (2-µm scale), roughness is from EPS and boundaries between
bacteria; (C) roughness averaged over many cells (5-µm and greater
scale) is likely dominated by fluctuations in biofilm thickness and
boundaries between bacteria.
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Roughness showed a direct correlation with scan size, as measured by
both RMS roughness (Fig. 5) and Ra. There
were no clear effects of biofilm preparation on biofilm roughness (data
not shown), but older biofilms were slightly rougher than younger biofilms at scan sizes of 5 µm and smaller (Fig. 5).

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FIG. 5.
Surface roughness (RMS) of unwashed, unsaturated
P. putida mt-2 biofilms as a function of AFM scan size. The
RMS roughness for similar biofilm age groups is displayed. Within each
age group, n > 3; standard errors of the means are
shown. Within each age group, roughness did not vary with sample
preparation treatment.
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Biofilm force maps.
Force maps of biofilms generally showed
median lift-off forces of ~30 to 60 nN. There was no consistent trend
for differences in this median adhesion force between washed versus
unwashed biofilms, dry versus fresh biofilms, or new versus older biofilms.
In the force map of Fig. 6, each pixel
contains the information for a pair of force-versus-distance curves (a
force plot), such as those in Fig. 6A and at the bottom of Fig. 6B.
Force plots display the tip-sample interaction forces as the AFM tip
moves toward and away from the sample surface. Each force plot contains one force-versus-distance curve for the approach of the cantilever toward and into the sample and a second force-versus-distance curve for
the retraction of the cantilever from the sample. Force plots show
whether the tip-sample interactions are primarily attractive, as in
Fig. 6, or repulsive. Attractive force plots typically show some
hysteresis between the approach and retract curves. This hysteresis is
typically of the type shown in Fig. 6A, where the tip is slightly
attracted to the surface upon approaching and then adheres more
strongly to the surface as it retracts from the surface. Force plots
also show whether the sample surface is hard or elastic (33,
46). The biofilm surface in Fig. 6 shows no elasticity that can
be detected with the cantilever of 0.6-N/m spring constant that was
used.

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FIG. 6.
Biofilm force map. (A) Diagram of the tip-sample
interactions occurring as the AFM tip approaches and retracts from an
adhesive surface. The force plot consists of two curves: one for the
tip approaching the sample and one for the tip retracting from the
sample. During the approach, the cantilever moves from right to left in
the diagram, and the cantilever deflects as it presses into the
biofilm. In the retract curve, the cantilever deflects sharply before
separating from the biofilm as it moves from left to right in the
diagram. The horizontal region of the curve represents the tip not in
contact with the biofilm, and the sloped region of the curve represents
the tip in contact with the biofilm. The slope for a hard surface is
approximately 1 nm of deflection/nm of z distance, while
softer surfaces show a more gradual deflection (33). (B)
Force map analysis of unsaturated P. putida mt-2 biofilm.
Biofilm was 2 days old, unwashed, and desiccated at 75.5% RH. Height
image arrows show where example force plots were acquired. Lighter
regions are higher than darker regions. Force map (force-volume image)
shows patterns of adhesion on surface of biofilm. Darker regions are
more adhesive than lighter regions. Arrowheads indicate pixels on force
map where force plots were acquired. Scale bar indicates the
x-y scales of the force map and height image.
Force-versus-distance curves on cell surface (left) and between cells
(right) show the large adhesion on the bacterial surface and small
adhesion between bacteria. Vertical bars on force plots show the
z position represented in the force map (= 50 nm above the
position of maximum cantilever deflection into surface). Scale bars
give x and y dimensions of force plots.
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Many of the force maps showed an unexpected feature (Fig. 6): the
spaces between cells were less adhesive than the surfaces of the cells.
This can be seen from the two force plots in Fig. 6, which show the
large adhesion on the top of the cell (left) and the small adhesion in
the crack between the cells (right). Similarly, the force map or force
volume image on the right shows a pattern of light pixels (less
adhesive force plots) following the spaces between the cells, with most
of the top of the cell surface covered by dark pixels (more adhesive
force plots). There are at least two possible explanations for this
observation. One possibility is that the bacterial surfaces differ from
the spaces between bacteria in properties such as moisture content or
quantity of EPS. An alternate possibility is that the AFM tip makes
less contact with the biofilm in the spaces between the cells, so that the reduced adhesion is due to the smaller tip-sample contact area
between the bacteria. Further research will be needed to distinguish
between these two explanations.
Another unexpected feature of the biofilm force maps is that the
adhesion forces between the tip and the biofilm surface were not
strongly dependent on the maximum force that was applied to the biofilm
surface during each force plot. The maximum force applied to the
biofilm during each force plot is set by the trigger threshold. The
trigger threshold is the maximum cantilever deflection that can occur
as the cantilever advances into the biofilm surface. Trigger thresholds
were set at 10 to 50 nm, which corresponds to ~6- to 30-nN applied
force for cantilevers with a spring constant of 0.6 N/m.
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DISCUSSION |
This study of surface characteristics of P. putida
unsaturated biofilms is part of an ongoing investigation into why these biofilms have appeared to be highly resistant to mass transfer (31). Generally biofilms are studied as part of an aqueous, fluid flowing system; in contrast, biofilms grown in air have been
studied less. Because biofilm is an important growth habit in
unsaturated systems, the factors that limit the transfer of nutrients
and waste to unsaturated biofilms should be understood. We relied on
AFM, a high-resolution tool in surface imaging and probing, to make our investigations.
AFM has been a useful tool in furthering many areas of biological
research, including the imaging of DNA (6, 24), proteins (39, 52), and cells (1, 14, 28, 29, 56). The
biofilms that have been imaged previously by AFM were all grown in
fluid (2, 4, 55) or, in the case of P. putida, at
an oil-water interface (20). Many of our AFM images of
unsaturated P. putida are reminiscent of the published AFM
images of P. putida in fluid (20, 53), although
the prior methods were quite different from ours.
Our work offers three significant new contributions that have not been
addressed previously. First, we studied specifically the air-biofilm
interface using a range of preparation conditions representative of
those that unsaturated biofilms could be exposed to in the natural
environment (e.g., wet to dry, unwashed to washed). Second, we measured
the roughness of unsaturated biofilms and showed that, in contrast to
roughness measures of biofilms in saturated, fluid flowing
environments, unsaturated biofilms are very smooth. Third, we measured
the adhesive properties of the biofilms and developed an approach for
analyzing the force mapping data so that we could demonstrate how
adhesive the biofilms were as a function of treatment. In this
discussion, we address these three contributions to biofilm science and
provide additional interpretation of our morphological observations.
Reproducing the unsaturated biofilm environment.
We observed
that our biofilms had similar morphologies under all conditions used
for growth and imaging
desiccated versus fresh; older versus younger;
top versus bottom layer of bacterial cells. Such comparisons,
particularly dry versus wet, can provide a sense of how biofilm
morphologies in unsaturated environments are stable with the changing
environmental conditions that commonly occur in soils subject to
seasonal wetting and drying. Through washing, we also found that
extracellular mesostructures, presumably clumped exopolymers, were
present in both the top and basal cell layers of the biofilm.
Smooth biofilms.
Biofilm roughness has previously been
reported either as RMS (3) or as Ra* (40, 44),
where Ra* is calculated by dividing Ra by the biofilm thickness
(40). We reported only RMS as our index of biofilm roughness
because Ra was numerically similar in all cases. Although aquatic
biofilms shrink when dried such that the hydrated parts of EPS condense
to 1% of the original volume (55), drying did not increase
the surface roughness of our biofilms. This may imply that shrinkage or
condensation of the polymers was uniform.
Age may indirectly relate to roughness: older aquatic biofilms are
generally thicker and rougher (40, 42). Consistently, the
surface structures of biofilms growing in water become continuously more complex as they age, over a period of weeks and months
(44). In our studies of unsaturated biofilm, we found a
slight increase in surface roughness at smaller scan sizes (below 10 µm) for biofilms over 2 days old versus younger biofilms. Overall,
however, our biofilms are less than 0.2% as rough at all scan sizes
compared to biofilms cultivated in aqueous fluid flowing systems. Thus, the smoothness of our biofilms, measured here by surface roughness, generally confirms our previous observations by transmission electron microscopy that the air-biofilm interface of P. putida
biofilms cultured under unsaturated conditions was uniformly flat over distances ranging from one cell to tens of cells (31).
In aquatic systems, rough biofilms facilitate external (boundary layer)
mass transport to biofilms (7, 10) and improve the rate of
nutrient resupply into biofilms (16). Improved mass transfer
of nutrients will tend to improve biofilm growth rate (32,
42). In aquatic systems, there may be a sequence of
roughness-mass transfer relationships that begins with rough biofilms
whose texture is a consequence of nutrient deprivation; then, with
rapid fluid flow, rough biofilms improve boundary layer mass transfer
of nutrients to the end that the biofilms grow and become smooth
(43). We interpreted a previously defined (43)
ratio of growth rate to mass transfer, G, for the case of
unsaturated biofilms. In our biofilms, G = µ(L2/D), where µ is the first-order growth rate
constant for exponentially growing cells, L is a
characteristic length for external mass transfer, and D is
the molecular diffusivity for the diffusing substrate. We assumed the
limiting mass transfer process external to unsaturated biofilms to be
gas-phase substrate (e.g., oxygen) diffusion (as opposed to flowing
air). Our calculations using a molecular diffusivity for oxygen
(ambient temperature) of 0.175 cm2/s (57), a
first-order growth rate constant for P. putida mt-2 of
approximately 0.5/h (30), and a characteristic length
L of 1 µm result in a value for G that is very
low, i.e., on the order of 10
11. One interpretation of
this calculation is that diffusive transport of oxygen to the biofilm
should not limit growth; another interpretation is that the biofilm
should be smooth given the high external mass transfer rate relative to
cellular growth rate (43). Thus the smoothness of P. putida air-biofilm interfaces reported here and previously by
transmission electron microscopy (31) is indicative of
relatively low mass transfer resistance across the air-biofilm interfacial boundary layer.
Biofilm adhesiveness.
AFM force mapping reveals properties of
a sample that are not revealed in the AFM height images
(46). For example, force mapping of cholinergic synaptic
vesicles has revealed that the centers of these vesicles are harder or
stiffer than the peripheries of the vesicles (33). Force
maps combine force plot data with the visual images and thus enable one
to correlate specific tip-sample interactions with specific features on
the sample surface.
Our biofilm force maps showed that the spaces between biofilm bacteria
were less adhesive than the bacterial surfaces and that the median
adhesion forces were 30 to 60 nN. These median adhesion forces can be
compared to what one would expect for the surface tension of an aqueous
solution, such as the thin water layer on the surface of the biofilm.
Surface tensions of aqueous Triton X detergent solutions range from 70 (dilute) to 30 (concentrated) mN/m, as measured with a liquid
tensiometer. A biofilm adhesion force of 30 nN corresponds to an
air-liquid surface tension of 30 mN/m if the circumference of contact
between the tip and the biofilm is 1 µm.
AFM images, depending on the mode of acquisition, lend themselves to
physical interpretations not available through other high-resolution
imaging approaches such as electron microscopy. For example, phase
images in tapping AFM, such as those in Fig. 1 and 3, show the phase
difference between the oscillation driving the cantilever and the
oscillation of the cantilever as it interacts with the sample surface
(36) (http://www.di.com/appnotes/Phase/PhaseMain.html). Phase images are a map of the energy dissipated by the tip-sample interaction at each point on the sample surface (9). Changes in energy dissipation over the sample surface are related to changes in
such surface properties as adhesiveness and stiffness. Phase images of
lysed synpatic vesicles (15), wood pulp fiber, and DNA
(23) show distinctively varying patterns of energy
dissipation. In contrast to these biomaterials, the biofilm phase
images in Fig. 1 and 3 are relatively uniform.
Extracellular mesostructures.
Although the overall morphology
of the biofilms is smooth, the surface morphology of individual biofilm
bacteria indicated the presence of extracellular structures larger than
the glycolipids and glycoproteins reported previously, which generally
range in size from ~1 kDa for glycolipids to 100 kDa for
glycoproteins (13, 49)
(http://www.cmdr.ubc.ca/bobh/genomics.htm). The extracellular mesostructures in our images resembled the "orange peel" appearance previously reported for P. putida grown at an oil-water
interface (20). The smallest mesostructures in Fig. 3 have
diameters of 10 nm, which gives them a molecular mass of >100 kDa if
they are globular. Typical mesostructures of 40 nm or larger may have
masses of at least 10,000 kDa. Therefore, either there are larger
macromolecules on the surface of these biofilm bacteria than have been
identified previously or the observed mesostructures are actually
aggregates of much smaller molecules.
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ACKNOWLEDGMENTS |
We thank the reviewers for their valuable suggestions.
This work was supported by NSF grant MCB9604566 (H.G.H., C.S., and
I.D.A.), the UCSB Donald Bren School of Environmental Science and
Management (I.D.A.), and U.S. EPA grant R827133-01.
 |
FOOTNOTES |
*
Corresponding author. Mailing address: 4670 Physical
Sciences Building North, University of California, Santa Barbara, CA 93106. Phone: (805) 893-3195. Fax: (805) 893-7612. E-mail:
holden{at}bren.ucsb.edu.
 |
REFERENCES |
| 1.
|
Arnoldi, M.,
C. M. Kacher,
E. Baeuerlein,
M. Radmacher, and M. Fritz.
1998.
Elastic properties of the cell wall of Magnetospirillum gryphiswaldense investigated by atomic force microscopy.
Appl. Phys. A
66:S613-S617[CrossRef].
|
| 2.
|
Beech, I. B.
1996.
The potential use of atomic force microscopy for studying corrosion of metals in the presence of bacterial biofilms an overview.
Int. Biodeterior. Biodegrad.
37:141-149[CrossRef].
|
| 3.
|
Bishop, P. L.,
J. T. Gibbs, and B. E. Cunningham.
1997.
Relationship between concentration and hydrodynamic boundary layers over biofilms.
Environ. Technol.
18:375-386.
|
| 4.
|
Bremer, P. J.,
G. G. Geesey, and B. Drake.
1992.
Atomic force microscopy examination of the topography of a hydrated bacterial biofilm on a copper surface.
Curr. Microbiol.
24:223-230[CrossRef].
|
| 5.
|
Bustamante, C., and D. Keller.
1995.
Scanning force microscopy in biology.
Phys. Today
48:32-38.
|
| 6.
|
Bustamante, C., and C. Rivetti.
1996.
Visualizing protein-nucleic acid interactions on a large scale with the scanning force microscope.
Annu. Rev. Biophys. Biomol. Struct.
25:395-429[Medline].
|
| 7.
|
Characklis, W. G., and K. C. Marshall.
1990.
Biofilms: a basis for an interdisciplinary approach, p. 3-15.
In
W. G. Characklis, and K. C. Marshall (ed.), Biofilms. John Wiley & Sons, Inc., New York, N.Y.
|
| 8.
|
Chenu, C.
1995.
Extracellular polysaccharides: an interface between microorganisms and soil constituents, p. 217-233.
In
P. M. Huang, J. Berthelin, J.-M. Bollag, W. B. McGill, and A. L. Page (ed.), Environmental impact of soil component interactions, vol. 1. Natural and anthropogenic organics. CRC Press, Inc., Boca Raton, Fla.
|
| 9.
|
Cleveland, J. P.,
B. Anczykowski,
A. E. Schmid, and V. B. Elings.
1998.
Energy dissipation with a tapping-mode atomic force microscope.
Appl. Phys. Lett.
72:2613-2615[CrossRef].
|
| 10.
|
Costerton, J. W., and H. M. Lappin-Scott.
1995.
Introduction to microbial biofilms, p. 1-11.
In
H. M. Lappin-Scott, and J. W. Costerton (ed.), Microbial biofilms. Cambridge University Press, Cambridge, England.
|
| 11.
|
Costerton, J. W.,
Z. Lewandowski,
D. De Beer,
D. Caldwell,
D. Korber, and G. James.
1994.
Biofilms, the customized microniche.
J. Bacteriol.
176:2137-2142[Free Full Text].
|
| 12.
|
Davies, D. G.,
M. R. Parsek,
J. P. Pearson,
B. H. Iglewski,
J. W. Costerton, and E. P. Greenberg.
1998.
The involvement of cell-to-cell signals in the development of a bacterial biofilm.
Science
280:295-298[Abstract/Free Full Text].
|
| 13.
|
Desai, J. D., and I. M. Banat.
1997.
Microbial production of surfactants and their commercial potential.
Microbiol. Mol. Biol. Rev.
61:47-64[Abstract].
|
| 14.
|
Fritz, M.,
M. Radmacher, and H. E. Gaub.
1994.
Granula motion and membrane spreading during activation of human platelets imaged by atomic force microscopy.
Biophys. J.
66:1328-1334[Abstract/Free Full Text].
|
| 15.
|
Garcia, R. A.,
D. E. Laney,
S. M. Parsons, and H. G. Hansma.
1998.
Substructure and responses of cholinergic synaptic vesicles in the atomic force microscope.
J. Neurosci. Res.
52:350-355[CrossRef][Medline].
|
| 16.
|
Gibbs, J. T., and P. L. Bishop.
1995.
A method for describing biofilm surface roughness using geostatistical techniques.
Water Sci. Technol.
32:91-98.
|
| 17.
|
Gilbert, P., and M. R. W. Brown.
1995.
Mechanisms of the protection of bacterial biofilms from antimicrobial agents, p. 118-130.
In
H. M. Lappin-Scott, and J. W. Costerton (ed.), Microbial biofilms. Cambridge University Press, Cambridge, England.
|
| 18.
|
Golan, R.,
L. I. Pietrasanta,
W. Hsieh, and H. G. Hansma.
1999.
DNA toroids: stages in condensation.
Biochemistry
38:14069-14076[CrossRef][Medline].
|
| 19.
|
Gray, T. R. G.,
P. Baxby,
I. R. Hill, and M. Goodfellow.
1968.
Direct observation of bacteria in soil, p. 171-192.
In
T. R. G. Gray, and D. Parkinson (ed.), The ecology of soil bacteria. University of Toronto Press, Toronto, Canada.
|
| 20.
|
Gunning, P. A.,
A. R. Kirby,
M. L. Parker,
A. P. Gunning, and V. J. Morris.
1996.
Comparative imaging of Pseudomonas putida bacterial biofilms by scanning electron microscopy and both DC contact and AC non-contact atomic force microscopy.
J. Appl. Bacteriol.
81:276-282.
|
| 21.
|
Hamilton, W. A.
1995.
Biofilms and microbially influenced corrosion, p. 171-182.
In
H. M. Lappin-Scott, and J. W. Costerton (ed.), Microbial biofilms. Cambridge University Press, Cambridge, England.
|
| 22.
|
Hansma, H. G., and J. Hoh.
1994.
Biomolecular imaging with the atomic force microscope.
Annu. Rev. Biophys. Biomol. Struct.
23:115-139[Medline].
|
| 23.
|
Hansma, H. G.,
K. J. Kim,
D. E. Laney,
R. A. Garcia,
M. Argaman, and S. M. Parsons.
1997.
Properties of biomolecules measured from atomic force microscope images: a review.
J. Struct. Biol.
119:99-108[CrossRef][Medline].
|
| 24.
|
Hansma, H. G., and L. Pietrasanta.
1998.
Atomic force microscopy and other scanning probe microscopies.
Curr. Opin. Chem. Biol.
2:579-584[CrossRef][Medline].
|
| 25.
| Hansma, H. G., L. I. Pietransanta, I. D. Auerbach, C. Sorenson, R. Golan, and P. A. Holden. Probing
biopolymers with the atomic force microscope: a review. J. Biomater. Sci. Polym. Ed., in press.
|
| 26.
|
Hansma, P. K.,
J. P. Cleveland,
M. Radmacher,
D. A. Walters,
P. Hillner,
M. Bezanilla,
M. Fritz,
D. Vie,
H. G. Hansma,
C. B. Prater,
J. Massie,
L. Fukunaga,
J. Gurley, and V. Elings.
1994.
Tapping mode atomic force microscopy in liquids.
Appl. Phys. Lett.
64:1738-1740[CrossRef].
|
| 27.
|
Harris, R. F.
1981.
Effect of water potential on microbial growth and activity, p. 23-95.
In
J. F. Parr, W. R. Gardner, and L. F. Elliott (ed.), Water potential relations in soil microbiology. SSSA Special Publication no. 9. Soil Science Society of America, Madison, Wis.
|
| 28.
|
Henderson, E.,
P. G. Haydon, and D. S. Sakaguchi.
1992.
Actin filament dynamics in living glial cells imaged by atomic force microscopy.
Science
257:1944-1946[Abstract/Free Full Text].
|
| 29.
|
Hoh, J. H., and C.-A. Schoenenberger.
1994.
Surface morphology and mechanical properties of MDCK monolayers by atomic force microscopy.
J. Cell Sci.
107:1105-1114[Abstract].
|
| 30.
|
Holden, P. A.,
L. J. Halverson, and M. K. Firestone.
1997.
Water stress effects on toluene biodegradation by Pseudomonas putida.
Biodegradation
8:143-151[CrossRef][Medline].
|
| 31.
|
Holden, P. A.,
J. R. Hunt, and M. K. Firestone.
1997.
Toluene diffusion and reaction in unsaturated Pseudomonas putida biofilms.
Biotechnol. Bioeng.
56:656-670[CrossRef].
|
| 32.
|
Korber, D. R.,
A. Choi,
G. M. Wolfaardt,
S. C. Ingham, and D. E. Caldwell.
1997.
Substratum topography influences susceptibility of Salmonella enteritidis biofilms to trisodium phosphate.
Appl. Environ. Microbiol.
63:3352-3358[Abstract].
|
| 33.
|
Laney, D. E.,
R. A. Garcia,
S. M. Parsons, and H. G. Hansma.
1997.
Changes in the elastic properties of cholinergic synaptic vesicles as measured by atomic force microscopy.
Biophys. J.
72:806-813.
|
| 34.
|
Lapin, L. L.
1975.
Statistics: meaning and method.
Harcourt Brace Jovanovich, Inc., San Francisco, Calif.
|
| 35.
|
Leung, O. M., and M. C. Goh.
1992.
Orientational ordering of polymers by atomic force microscope tip-surface interaction.
Science
255:64-66[Abstract/Free Full Text].
|
| 36.
|
Magonov, S. N.,
V. Elings, and M. H. Whangbo.
1997.
Phase imaging and stiffness in tapping-mode atomic force microscopy.
Surf. Sci.
375:L385-L391[CrossRef].
|
| 37.
|
Marsh, P. D.
1995.
Dental plaque, p. 282-300.
In
H. M. Lappin-Scott, and J. W. Costerton (ed.), Microbial biofilms. Cambridge University Press, Cambridge, England.
|
| 38.
|
Morris, C. E.,
J.-M. Monier, and M.-A. Jacques.
1997.
Methods for observing microbial biofilms directly on leaf surfaces and recovering them for isolation of culturable organisms.
Appl. Environ. Microbiol.
63:1570-1576[Abstract].
|
| 39.
|
Muller, D. J.,
M. Amrein, and A. Engel.
1997.
Adsorption of biological molecules to a solid support for scanning probe microscopy.
J. Struct. Biol.
119:172-188[CrossRef][Medline].
|
| 40.
|
Murga, R.,
P. S. Stewart, and D. Daly.
1995.
Quantitative analysis of biofilm thickness variability.
Biotechnol. Bioeng.
45:503-510[CrossRef].
|
| 41.
|
Papendick, R. I., and G. S. Campbell.
1981.
Theory and measurement of water potential, p. 1-22.
In
J. F. Parr, W. R. Gardner, and L. F. Elliot (ed.), Water potential relations in soil microbiology. SSSA Special Publication no. 9. Soil Science Society of America, Madison, Wis.
|
| 42.
|
Peyton, B. M.
1996.
Effects of shear stress and substrate loading rate on Pseudomonas aeruginosa biofilm thickness and density.
Water Res.
30:29-36.
|
| 43.
|
Picioreanu, C.,
M. C. M. van Loosdrecht, and J. J. Heijnen.
1999.
Discrete-differential modelling of biofilm structure.
Water Sci. Technol.
39:115-122.
|
| 44.
|
Picioreanu, C.,
M. C. M. van Loosdrecht, and J. J. Heijnen.
1998.
Mathematical modeling of biofilm structure with a hybrid differential-discrete cellular automation approach.
Biotechnol. Bioeng.
58:101-116[CrossRef][Medline].
|
| 45.
|
Pietrasanta, L. I.,
D. Thrower,
W. Hsieh,
S. Rao,
O. Stemmann,
J. Lechner,
J. Carbon, and H. G. Hansma.
1999.
Probing the Saccharomyces cerevisiae CBF3-CEN DNA kinetochore complex using atomic force microscopy.
Proc. Natl. Acad. Sci. USA
96:3757-3762[Abstract/Free Full Text].
|
| 46.
|
Radmacher, M.,
J. P. Cleveland,
M. Fritz,
H. G. Hansma, and P. K. Hansma.
1994.
Mapping interaction forces with the atomic force microscope.
Biophys. J.
66:2159-2165[Abstract/Free Full Text].
|
| 47.
|
Razatos, A.,
Y.-L. Ong,
M. M. Sharma, and G. Georgiou.
1998.
Evaluating the interaction of bacteria with biomaterials using atomic force microscopy.
J. Biomater. Sci. Polym. Ed.
9:1361-1373[Medline].
|
| 48.
|
Razatos, A.,
Y.-L. Ong,
M. M. Sharma, and G. Georgiou.
1998.
Molecular determinants of bacterial adhesion monitored by atomic force microscopy.
Proc. Natl. Acad. Sci. USA
95:11059-11064[Abstract/Free Full Text].
|
| 49.
|
Russel, M.
1998.
Macromolecular assembly and secretion across the bacterial cell envelope: type II protein secretion systems.
J. Mol. Biol.
279:485-499[CrossRef][Medline].
|
| 50.
|
Sayles, R. S.
1982.
The profile as a random process, p. 91-118.
In
T. R. Thomas (ed.), Rough surfaces. Longman, London, England.
|
| 51.
|
Schneider, S. W.,
J. Larmer,
R. M. Henderson, and H. Oberleithner.
1998.
Molecular weights of individual proteins correlate with molecular volumes measured by atomic force microscopy.
Pflugers Arch.
435:362-367[CrossRef][Medline].
|
| 52.
|
Shao, Z.,
J. Mou,
D. M. Czaijkowsky,
J. Yang, and J.-Y. Yuan.
1996.
Biological atomic force microscopy: what is achieved and what is needed.
Adv. Phys.
45:1-86.
|
| 53.
|
Steele, A.,
D. T. Goddard, and I. B. Beech.
1994.
An atomic force microscopy study of the biodeterioration of stainless steel in the presence of bacterial biofilms.
Int. Biodeterior. Biodegrad.
34:35-46.
|
| 54.
|
Stoodley, P.,
D. DeBeer, and Z. Lewandowski.
1994.
Liquid flow in biofilm systems.
Appl. Environ. Microbiol.
60:2711-2716[Abstract/Free Full Text].
|
| 55.
|
Surman, S. B.,
J. T. Walker,
D. T. Goddard,
L. H. G. Morton,
C. W. Keevil,
W. Weaver,
A. Skinner,
K. Hanson,
D. Caldwell, and J. Kurtz.
1996.
Comparison of microscope techniques for the examination of biofilms.
J. Microbiol. Methods
25:57-70[CrossRef].
|
| 56.
|
Ushiki, T.,
J. Hitomi,
S. Ogura,
T. Umemoto, and M. Shigeno.
1996.
Atomic force microscopy in histology and cytology.
Arch. Histol. Cytol.
59:421-431[Medline].
|
| 57.
|
Welty, J. R.,
C. E. Wicks, and R. E. Wilson.
1984.
Fundamentals of momentum, heat and mass transfer, 3rd ed.
John Wiley & Sons, New York, N.Y.
|
| 58.
|
Wyndham, R. C., and K. J. Kennedy.
1995.
Microbial consortia in industrial wastewater treatment, p. 183-195.
In
H. M. Lappin-Scott, and J. W. Costerton (ed.), Microbial biofilms. Cambridge University Press, Cambridge, England.
|
| 59.
|
Xu, W.,
P. J. Mulhern,
B. L. Blackford,
M. H. Jericho,
M. Firtel, and T. J. Beveridge.
1996.
Modeling and measuring the elastic properties of an archaeal surface, the sheath of Methanospirillum hungatei, and the implication for methane production.
J. Bacteriol.
178:3106-3112[Abstract/Free Full Text].
|
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