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Applied and Environmental Microbiology, February 2008, p. 731-737, Vol. 74, No. 3
0099-2240/08/$08.00+0 doi:10.1128/AEM.01725-07
Copyright © 2008, American Society for Microbiology. All Rights Reserved.

Department of Food Science, University of Otago, P.O. Box 56, Dunedin, New Zealand,1 Institute of Food Nutrition and Human Health, Massey University, Private Bag 11 222, Palmerston North, New Zealand,2 Department of Chemistry, University of Otago, P.O. Box 56, Dunedin, New Zealand3
Received 26 July 2007/ Accepted 27 November 2007
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107 spores ml–1; spores were purified using a two-phase system created with polyethylene glycol 4000 and 3 M phosphate buffer. The zeta potentials of the spores from the four isolates ranged from –10 to –20 mV at neutral pH, with an isoelectric point between pH 3 and 4. Through contact angle measurements, spores were found to be hydrophilic and had relative hydrophobicity values of 10 to 40%, as measured by the microbial adhesion to hexadecane assay. The most hydrophilic spore isolate with the smallest negative charge attached in the highest numbers to Thermanox and stainless steel (1 x 104 spores cm–2), with fewer spores attaching to glass (3 x 103 spores cm–2). However, spores produced by the other three strains attached in similar numbers (P > 0.05) to all substrata (
1 x 103 spores cm–2), indicating that there was no simple relationship between individual physicochemical interactions and spore adherence. Therefore, surface modifications which limit the attachment of one strain may not be effective for all stains, and control regimens need to be devised with reference to the characteristics of the particular strains of concern. |
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Several studies have used electron microscopy and atomic force microscopy to examine the physical structure of the spore's surface (7, 18, 28). However there have been few studies of the surface chemistry of spores, and it is likely that what little information is known may not be broadly applicable across spores of all the species. It is known that the physical structure of the outer surfaces of spores varies dramatically. For example, the outer layer of a Bacillus subtilis spore consists of protein and carbohydrates (57), while in species such as Bacillus cereus and Bacillus anthracis, the spores exhibit pili (46) and an additional layer, known as an exosporium (16), comprising proteins, carbohydrates, and lipids (30). Little is known of the outer layer of thermophilic spores found in dairy plants.
The physicochemical characterization of the surface properties of microorganisms has also received extensive interest (49). However, there have only been a few studies on the surface characterization of spores, and these have been confined to mesophilic species (11, 37). Surface characterization techniques have involved measuring surface charge through zeta potential and relative hydrophobicity through the microbial adhesion to solvents assay and the determination of contact angles (52).
A large number of studies (3) have assessed the role of the physicochemical properties in the attachment of vegetative cells. However, it has remained unclear how much of this information is relevant to spore adhesion to surfaces. Spores differ from vegetative cells in that they are not metabolically active (44), and unlike vegetative cells they are clearly nonmotile (34).
Before the surface of a spore can be characterized, large quantities of free endospores must be obtained. Previous spore isolation methods have focused on harvesting spores from mesophilic bacilli such as B. subtilis and B. cereus (9, 12, 15), with only a few published papers on spore production from the thermophile Geobacillus stearothermophilus (24, 25, 59) and even fewer on recovering spores from dairy microorganisms (36, 40). For characterization purposes it is important that the spore suspensions do not contain debris, which may influence the results. Researchers have used detergents, enzymes, and ultrasonication to purify spores and disrupt them in order to recover proteins or DNA (41). However, these techniques have been shown to alter the spore's surface (10). To overcome this problem, density gradient centrifugation using either sodium bromide (27, 33), urografin (47), or a two-phase separation technique with polyethylene glycol (PEG) has been used (42).
The aims of this study were to develop a method to produce large quantities of endospores from thermophilic bacilli dairy isolates, to determine the surface physicochemical characteristics of the endospores, and to show how these characteristics impact the ability of the endospores to attach to a variety of substrata. Such information could be used to develop strategies to prevent or reduce the number of spores attaching to stainless steel and thereby reduce fouling within a milk powder production plant.
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Spore production.
Enhancement of spore production was assessed by comparing four different media previously reported to be effective with other sporulating thermophilic bacilli (48, 59). Isolates were inoculated into 10 ml tryptic soy broth (TSB), which was incubated for 18 h at 55°C and used as a 1% inoculum for spore media. Spore media for Geobacillus sp. isolates D4, E7, E11, and CGT-8 contained either (per liter) 30 g Bacto tryptone (BD) or 30 g TSB (BD). These media were supplemented with the following salts (per liter): 0.125 g of CaCl2, 0.15 g of MnSO4, 0.155 g of FeSO4, and 0.55 g of MgCl2. All salts were analytical grade from BDH. Cultures were aerated by stirring for 72 h at 55°C. At intervals spore numbers were determined by the boiling of aliquots obtained from the culture, followed by serial dilution, and enumerated using the drop plate method (19). At the completion of sporulation, spores were harvested by centrifugation (10,000 x g, 8 min at 4°C) and washed three times in sterile 18-M
cm–1 water (Barnstead). Crude spore suspensions consisting of
1 x 107 spores ml–1 were stored at 4°C in water until needed.
Purification of spores.
Spores were purified using a PEG two-phase system as described by Sacks and Alderton (42). The system was created by dissolving 5.6 g of PEG 4000 in 17 ml of 3 M phosphate buffer (pH 7.4). After phase separation, the crude spore suspension was carefully layered on the gradient, creating a total volume of 50 ml. The sample was centrifuged at 1,500 x g for 3 min at 20°C. Debris migrated to the lower phase, while spores were concentrated in a layer above the PEG phase. Spores were carefully recovered and washed five times at 20°C in water. The effectiveness of the separation procedure was determined by visual examination of the recovered fractions using phase-contrast microscopy.
Characterization.
The surface hydrophobicities of the four spore isolates were determined using the microorganism adhesion to hexadecane (MATH) assay (39). Purified spores were suspended in 0.1 M KCl at either pH 3 or 6.8 to an optical density at 600 nm of 0.6 to 1.0. Spore suspensions (2 ml) were added to 1 ml of hexadecane and mixed on a vortex mixer for 1 min, incubated at 37°C for 10 min, and vortexed again for 2 min. After the suspensions settled at 20°C for 30 min, the absorbance of the aqueous phase was measured at 600 nm. The mean of five measurements was taken. The percent hydrophobicity (%h) was determined from the absorbance of the original spore suspension (Ai) and absorbance of the aqueous phase after mixing with hexadecane (A
) according to the following equation: %h = (Ai – Af/Ai) x 100.
The zeta potentials of spores from the four isolates were determined (Zetasizer Nano ZS90; Malvern Instruments Ltd., United Kingdom) between pH 3 and 11 at 25°C. The mean of three separate measurements from the same sample was recorded. Purified spores were suspended in 0.1 M KCl to an optical density of 0.01 at 600 nm. The pH was adjusted using HCl or NaOH. The zeta potential was calculated from the electrophoretic mobility using the Smoluchowski equation (21).
Spore lawn preparation and contact angle measurements of surfaces.
Spore lawns were prepared as described by Busscher et al. (6) for bacteria. Suspensions of spores were collected on a cellulose triacetate filter (0.45 µm; Pall) to a density of 108 spores mm–2. The filters were placed on a gel surface containing 2% agar and 10% (wt/vol) glycerol in water to generate a uniform moisture content within the lawn before being cut into strips (1 cm in diameter) using a sterile scalpel blade. The strips were allowed to dry for 45 min at room temperature, and contact angles were measured, within a further 30 min, by the sessile-drop method using an FTA200 goniometer (First Ten Angstroms, Portsmouth, VA). To prepare surfaces for contact angle measurements, stainless steel 316 2B grade polish coupons (2 by 1 by 0.1 cm) were polished using 800 and 1200 grit sandpaper, washed in acetone at 20°C followed by 50% nitric acid at 80°C for 30 min to passivate the surface, rinsed in distilled water, and sterilized by autoclaving. Glass surfaces were cut from precleaned microscope slides into coupons (2.5 by 1 by 0.1 cm). Thermanox (Nalge Nunc International) coupons (2 by 1 by 0.05 cm) came precleaned, gamma irradiated, and ready to use. Contact angles of two polar solutions (water and formamide) and one nonpolar solution (
-bromonaphthalene) were obtained by depositing a drop of each test liquid on the surface of either glass, Thermanox, stainless steel (316 2B grade polish), or the filter strips containing the spore lawns. A series of 10 contact angle measurements were recorded, each within 2 seconds of the drop contacting the surface. Surface Gibbs energies were determined using the FTA32, version 2.0, software (First Ten Angstroms). Energetic properties of the materials were obtained from the Young-van Oss equation (55), (1 + cos
)
TOT = 2[(
svLW
lvLW)1/2 + (
sv+
lv–)1/2 + (
sv–
lv+)1/2], where
TOT is the total surface energy;
LW,
+, and
– are the van der Waals, electron acceptor, and electron donor components of the surface Gibbs energy, respectively; and
is the contact angle. The subscripts sv and lv correspond to the solid-vapor and liquid-vapor interfaces, respectively. The hydrophobicity of microbial cell surfaces can be thermodynamically expressed as a Gibbs energy of aggregation (
Gsls) (54) according to the following equation:
Gsls = –2[(
svLW)1/2 – (
lvLW)1/2]2 – 4[(
sv+
sv–)1/2 + (
lv+
lv–)1/2 – (
sv+
lv–)1/2 – (
sv–
lv+)1/2]. Organisms with hydrophilic surfaces prefer the aqueous phase and display a
Gsls >0, while hydrophobic organisms tend to aggregate and therefore have a
Gsls <0.
Adhesion experiment.
A flow loop reactor system was used to experimentally determine the initial attachment of thermophilic spores to glass, stainless steel, and Thermanox. The system consisted of a reservoir and loop (total volume was 200 ml) containing coupons of different materials (Fig. 1). Coupons were inserted into silicon tubing (1 cm in diameter) and placed along the loop in triplicate groups. The spores of the different isolates were suspended in 0.1 M KCl at a concentration of
1 x 107 spores ml–1. The suspending medium containing 0.1 M KCl was chosen, as this resembles the ionic strength found in milk (0.08 M). Spore suspensions were circulated at a speed of 1 m s–1 (Reynolds number, 5,600) through the recirculating loop to model the velocity in a dairy plant. The entire system was held in a water bath at 20°C to prevent spore germination. Coupons were removed after 30 min and rinsed in water three times to remove loosely adherent spores. The number of spores attached to the coupons was estimated by swabbing the coupons in 0.1% peptone containing three glass beads (5 mm in diameter). The coupon, swab, and media were vortexed for 15 seconds. The number of viable spores recovered from the surface was determined using the drop plate method after the suspension had been boiled for 30 min to activate the spores. There was little difference in the numbers of spores estimated to be present on the surface by the swabbing and plating method compared to epifluorescence direct counts (data not shown).
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FIG. 1. Schematic of the flow reactor used to expose the different substrata to spores.
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99% phase-bright endospores and were used for subsequent characterization studies.
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FIG. 2. Numbers of spores recovered from Geobacillus sp. isolates D4 (a) and CGT-8 (b) over 72 h in TSB with ( ) or without ( ) salt or in tryptone with () or without ( ) salt. Values represent the mean of three replicates and standard deviations of the means.
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FIG. 3. Zeta potentials of spores from Geobacillus sp. isolates D4 ( ), E7 ( ), E11 ( ), and CGT-8 (x) in 0.1 M KCl between pH 3 and 12. Values represent the means of three replicates and standard deviations of the means.
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FIG. 4. Relative hydrophobicities of spores from Geobacillus sp. isolates at pH 3 (black bars) and 6.8 (gray bars) in 0.1 M KCl, as determined by the MATH assay. Error bars represent the means of five replicates and the standard deviations of the means.
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TOT values, ranging from 49.4 to 58.3 mJ m–2. Purification of the spores using the two-phase system reduced the apolar (
LW) component while increasing the total polar (
AB) component. The most prominent feature for all spore isolates was the electron-donating (
–) component. All spore isolates had similar
Gsls values, and all were >0, indicating that they were all hydrophilic. In contrast to the results shown for the MATH assay, CGT-8 appeared to be the most hydrophilic, with a
Gsls of 31.4 mJ m–2 and E7 the most hydrophobic at 20.1 mJ m–2. |
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TABLE 1. Mean contact angle measurements, surface Gibbs energies, and energy of interaction for crude and purified suspensions of spores from Geobacillus sp. isolates and inert surfaces
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Gsls of 29.2 mJ m–2 (
Gsls > 0) (Table 1). Thermanox and stainless steel surfaces had larger water contact angles of 63° ± 5° and 54° ± 10°, respectively, and
-bromonapthalene had contact angles of 8° ± 1° and 15° ± 3°, respectively. This resulted in greater
LW values for Thermanox and stainless steel of 43.9 and 42.9 mJ m–2, respectively, than for glass (34.8 mJ m–2). This translated into Thermanox and stainless steel being hydrophobic, with
Gsls values <0: –40.2 and –21.7 mJ m–2, respectively. A larger difference was seen for the
– component, with glass having the highest value of 54.4 mJ m–2 and Thermanox and stainless steel having lower values of 6.3 and 16.5 mJ m–2, respectively.
The numbers of spores from the four isolates which attached to either stainless steel, Thermanox, or glass were determined using a simple flow reactor (Fig. 5). Generally, more spores were recovered from Thermanox and stainless steel than from glass (fivefold increase for D4, twofold increase for other spore isolates). Spore attachment to substrata which had a low
TOT, such as stainless steel and Thermanox, was greater than attachment to substrata with a high
TOT. According to the Tukey grouping, the substrates were separated on the basis of the numbers of each spore isolate adhering to the different substrates. Glass and Thermanox were significantly different (P < 0.05). The test was unable to differentiate stainless steel from the other materials. There was no difference in the number of spores adhering to coupons based on their order in the series.
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FIG. 5. Numbers of Geobacillus sp. isolates D4, E7, E11, and CGT-8 recovered from different substrata (glass, Thermanox, and stainless steel). Values represent the means for three coupons ± standard deviations.
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Obtaining spores free from any cells or debris was crucial for the accurate determination of spore surface characteristics. While previous studies had used heat or enzymes to remove vegetative cells, it was desirable to avoid their approaches as such harsh treatments have been reported to alter the hydrophobicity of bacillus spores (10, 58). Previous studies have separated spores from cells and debris based on the density (33) difference between a spore (1.3 g ml–1) and a vegetative cell (1.1 g ml–1). In this project spore purification was initially attempted using simple density gradients made of solutions of sodium bromide (27, 33), urografin (47), or sucrose (58). However, these simple density gradients proved unable to reproducibly separate debris from lysed cells and to differentiate spores from partially sporulated cells. Using a two-phase separation technique Sacks and Alderton (42) found that spores of different mesophilic bacilli, such as B. cereus, accumulated in the PEG-rich phase while vegetative cells accumulated in the lower phosphate-rich phase. Interestingly, when this method was applied in the current study, Geobacillus sp. spores accumulated at the interface above the PEG-rich region while debris accumulated at the interface between the PEG- and phosphate-rich phases. This difference could be due to inherent structural differences between the surfaces of the spores of Geobacillus spp. and B. cereus. A potential drawback of the PEG separation method was that any residual PEG polymers remaining on the surfaces of the spores would alter their surface properties. To help reduce this possibility, the PEG was removed by washing the spores three times in water at room temperature with resting periods in between each centrifugation step to allow the polymers to be released from the surface. The contact water angle measurements (
W) of the spore lawns decreased after purification, suggesting that the two-phase method removed much of the hydrophobic material such as membranes and denatured protein from the crude spore extract.
Spores were negatively charged at neutral pH and at the pH of milk (pH 6.8). It has been shown previously that as the negative charge on the spore surface decreased the ability of spores to attach to glass increased due to reduced electrostatic repulsion (23). While the zeta potential values of the spores used in this study were similar to those found in other studies (22, 36), there was no clear relationship between surface charge and number of spores attaching to substrata. However, spores of isolate D4, which had the smallest negative charge, had the greatest propensity to attach to all the surfaces tested.
The MATH assay and water contact angle results indicated that the spores of the four Geobacillus sp. isolates were all hydrophilic, with isolate D4 being the most hydrophilic and having the lowest affinity for hexadecane and the smallest
W and spores of CGT-8 and E11 having the greatest affinity for hexadecane and the greatest
W. However, when the contact angles of the other solvents were taken into account and the
Gsls was calculated, there was no clear relationship between the MATH assay and
Gsls. From the
Gsls results purified spores of CGT-8 were the most hydrophilic and E7 spores were the most hydrophobic. Other studies have also found spores of G. stearothermophilus to be relatively hydrophilic through results obtained from hydrophobic interaction chromatography (HIC) (38) and MATH assays (36).
Determination of microbial surface hydrophobicity has been a focus of laboratories around the world for many years (11, 38, 51). However, a common concern is that it is difficult to directly compare results obtained from different laboratories using different or even similar tests (8). Surfaces of spores are heterogenous and contain a combination of functional groups such as carboxylate, amine, and phosphate groups, which may account for some of the variation between the different tests. Electrostatic interactions can also affect results from the MATH and HIC assays but not contact angle (1). Previous studies have found that negative ions, particularly phosphate, adsorb to the surfaces of hydrocarbon droplets, creating a negatively charged surface (5). In the current study, when the pH of the medium was reduced from 7 to 3, spore removal from the aqueous phase increased for isolates D4, E7, and CGT-8 but decreased for E11. The increase in hydrophobicity is believed to be due to the reduction in electrostatic repulsion since both spores and hexadecane are uncharged. These results reinforce the concept that the MATH assay is not solely a hydrophobicity assay but also measures the interplay of long-range van der Waals and electrostatic forces and various short-range interactions (50). Interestingly, these data also suggest that the relative change in the hydrophobicity of spores can differ as the conformation of the outer layers changes in response to external pH. We emphasize, however, that the MATH assay remains extremely useful as a simple assay for studying adhesion of microorganisms to a hydrophobic surface, and it is clearly different from being a hydrophobicity assay. It has been suggested that contact angles should be used as the universal measurement of hydrophobicity since they provide results in standard units rather than the relative results obtained from the MATH assay or HIC (49). However, contact angles are macroscopic measurement of the surface hydrophobicity of cells aggregated together in a lawn rather than of suspended single particles, as measured in the MATH assay. As all methods for measuring hydrophobicity have their advantages and disadvantages, it is now recognized that more than one method of measuring hydrophobicity should be used to obtain results. In this study, the results from both the MATH assay and contact angle measurements show that spores from the different Geobacillus spp. were predominately hydrophilic.
Factors such as hydrophobicity, surface charge, and cell density influence the attachment of microorganisms to surfaces (11, 23, 38). Previous research has shown that hydrophobic spores with zeta potentials close to zero attached to all surfaces in greater numbers than hydrophilic spores. In contrast, our research shows that the most hydrophilic spore (D4) adhered in the highest numbers to all the materials tested. Spores from this isolate also had the smallest zeta potential, thereby reducing the effect of electrostatic repulsion. One aspect that was not measured in the current study was the streaming zeta potential of the substrata. Previous studies have reported the streaming zeta potential for microscope slide glass to be –37 mV at 1 mM ionic strength, pH 7, and that for type 304 2B stainless steel to be –40 mV at 10 mM ionic strength, pH 7 (4, 29). Thermanox is made of a proprietary polyester, and, to the authors' knowledge, there has been no reports on its surface charge. However, streaming potential results have shown that certain polymer plastics exhibit a negative charge (56). Since the zeta potentials of glass and stainless steel are nearly the same, the Derjaguin, Landau, Verwey, and Overbeek theory predicts that the spores will attach in higher numbers to stainless steel since it has a lower Gibbs energy. This effect was seen for spores of isolate D4 but not for the other three isolates. Previous studies looked at a range of species of bacillus spores and, as mentioned earlier, the morphologies of those spores were dramatically different. Spores of B. cereus with pili had a greater propensity to attach to surfaces than those without pili (23, 26).
In the current study we were able to produce and characterize spores from thermophilic Geobacillus spp. isolated from a milk powder production line. Spores of the different isolates were hydrophilic, with a negative zeta potential. Similar numbers of spores were found attached to the three substrata tested for three of the four isolates. However, spores of isolate D4 attached in higher numbers to stainless steel and Thermanox than to glass. Therefore, it may be possible to reduce the adhesion of this particular strain by increasing both the
TOT and negative charge of the stainless steel surface. However, as spores produced by the other three strains tested did not show significant differences in attachment to the different substrates, these data also reinforce the fact that there is no simple relationship between individual physicochemical interactions and spore adhesion to surfaces. Rather, adhesion is dependent on complex and poorly defined relationships between a range of forces acting on both the spore and the substrate. The industrial significance of this is that surface treatments which limit the attachment of one strain may not be effective for all stains. Therefore, control regimens need to be devised with reference to the characteristics of the particular strains entering via the raw milk to the processing facility.
We thank Brian Niven (Department of Mathematics and Statistics, University of Otago, Dunedin, New Zealand) for statistical analysis of the data.
Published ahead of print on 14 December 2007. ![]()
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