ABSTRACT

Bacterial biofilms have a complex and heterogeneous three-dimensional architecture that is characterized by chemically and structurally distinct microenvironments. Confocal microscopy-based pH ratiometry and fluorescence lectin-binding analysis (FLBA) are well-established methods to characterize pH developments and the carbohydrate matrix architecture of biofilms at the microscale. Here, we developed a combined analysis, pH-FLBA, to concomitantly map biofilm pH and the distribution of matrix carbohydrates in bacterial biofilms while preserving the biofilm microarchitecture. As a proof of principle, the relationship between pH and the presence of galactose- and fucose-containing matrix components was investigated in dental biofilms grown with and without sucrose. The pH response to a sucrose challenge was monitored in different areas at the biofilm base using the ratiometric pH-sensitive dye C-SNARF-4. Thereafter, the fucose- and galactose-specific fluorescently labeled lectins Aleuria aurantia lectin (AAL) and Morus nigra agglutinin G (MNA-G) were used to visualize carbohydrate matrix components in the same biofilm areas and their immediate surroundings. Sucrose during growth significantly decreased biofilm pH (P < 0.05) and increased the amounts of both MNA-G- and AAL-targeted matrix carbohydrates (P < 0.05). Moreover, it modulated the biofilm composition towards a less diverse community dominated by streptococci, as determined by 16S rRNA gene sequencing. Altogether, these results suggest that the production of galactose- and fucose-containing matrix carbohydrates is related to streptococcal metabolism and, thereby, pH profiles in dental biofilms. In conclusion, pH-FLBA using lectins with different carbohydrate specificities is a useful method to investigate the association between biofilm pH and the complex carbohydrate architecture of bacterial biofilms.

IMPORTANCE

Biofilm pH is a key regulating factor in several biological and biochemical processes in environmental, industrial, and medical biofilms. At the microscale, microbial biofilms are characterized by steep pH gradients and an extracellular matrix rich in carbohydrate components with diffusion-modifying properties that contribute to bacterial acid–base metabolism. Here, we propose a combined analysis of pH ratiometry and fluorescence lectin-binding analysis, pH-FLBA, to concomitantly investigate the matrix architecture and pH developments in microbial biofilms, using complex saliva-derived biofilms as an example. Spatiotemporal changes in biofilm pH are monitored non-invasively over time by pH ratiometry, while FLBA with lectins of different carbohydrate specificities allows mapping the distribution of multiple relevant matrix components in the same biofilm areas. As the biofilm structure is preserved, pH-FLBA can be used to investigate the in situ relationship between the biofilm matrix architecture and biofilm pH in complex multispecies biofilms.

INTRODUCTION

Confocal microscopy-based pH ratiometry is a valuable method for the study of microscale pH developments in biofilms (13). Biofilm pH is a key metabolic factor that modulates a variety of biological and biochemical processes in microbial biofilms. Optimizing the pH is important for electricity generation in microbial fuel cells (4), as well as for the productivity of industrial fungal fermentation (5). Light-dependent pH changes in photosynthetic biofilms affect different biogeochemical processes, such as the biologically induced precipitation of minerals (6, 7). In the medical field, biofilm pH has been identified as a crucial factor for wound healing of the skin (8), biofilm formation in otitis media infections (9), and the establishment of Pseudomonas aeruginosa biofilms in cystic fibrosis (10). Likewise, acid production in dental biofilms is of central importance for the development of caries lesions. Bacterial fermentation of dietary carbohydrates, in particular, sucrose, lowers the pH at the tooth surface, which leads to a gradual dental mineral loss that, over time, may result in the formation of a cavity (11). Importantly, pH in dental biofilms is spatially heterogeneous, and areas of high and low acidogenicity may be found in close proximity. Localized acidic niches may be regarded as hotspots of demineralization that promote the progression of disease (12, 13). Such spatiotemporal variations in biofilm pH at the microscale can be adequately monitored with pH ratiometry (2).
Fluorescence-lectin binding analysis (FLBA) is a well-established method that allows mapping the spatial distribution of biofilm matrix carbohydrates with the help of fluorescently labeled proteins that bind specific sugar motifs with high affinity (14). Matrix carbohydrates, such as glycoconjugates and polysaccharides, play a vital role for microbial adhesion and co-adhesion, as well as for the mechanical stability of biofilms (15, 16). They serve as a nutrient source and hamper the free diffusion of solutes, including protons, through the biofilm (16, 17). In dental biofilms, matrix carbohydrates are strongly associated with virulence. Polysaccharides, such as dextrans and mutans, have been identified as essential for biofilm rigidity and also for the creation and maintenance of acidic niches (18). Recently, it has been shown by FLBA that dental biofilms also exhibit a surprisingly high abundance of carbohydrate structures containing galactose, fucose, and mannose, the production of which seems to be triggered by sucrose metabolism (19, 20). The combined use of suitable fluorescently labeled lectins and ratiometric pH-sensitive dyes could help elucidate the interplay between the biofilm matrix carbohydrate architecture and bacterial acid metabolism.
The aim of the present study was to establish a method for the combined application of pH ratiometry and FLBA, pH-FLBA, in complex multispecies biofilms. A protocol was developed to concomitantly map the biofilm pH and the distribution of carbohydrate matrix components at the microscale without compromising the biofilm architecture. As a proof of principle, the relationship between biofilm pH and the abundance and distribution of galactose- and fucose-containing matrix carbohydrates was studied in dental biofilms grown from salivary inocula in the presence and absence of sucrose.

MATERIALS AND METHODS

In vitro biofilm growth

Stimulated saliva was collected and pooled from 38 healthy volunteers after written informed consent was obtained. The collection of pooled saliva was considered exempt from ethical review by the Ethical Committee of Region Midtjylland (1-10-72-109-23). All donors refrained from eating or drinking for at least 30 min before saliva collection. The volunteers were asked to chew on a paraffin tablet (Sigma-Aldrich, Brøndby, Denmark) to stimulate saliva flow, and the produced saliva was collected in centrifuge tubes (Corning Life Sciences, Corning, NY, USA). Half of the collected saliva was centrifuged for 5 min at room temperature (RT) at 1,150 × g and pooled and stored at −80°C in a 1:1:1 mix of saliva:glycerol:phosphate-buffered saline (PBS). The remaining saliva was centrifuged for 1 min (RT) at 1,150 × g and used for the preparation of sterile saliva, as detailed elsewhere (21). Briefly, the saliva samples were pooled, diluted 1:1 with demineralized sterile water, and mixed with dithiothreitol (BDH Biochemicals, Poole, UK) to a final concentration of 2.5 mmol. Subsequently, the samples were centrifuged at 48,000 × g for 10 min (4°C), sterilized by ultrafiltration using 0.45 µm pre-filters (Jet Biofil, Guangzhou, China) and 0.22 µm filters (Jet Biofil), and stored at −20°C.
For in vitro biofilm growth, the channels of flow cells with a non-fluorescent polymer coverslip bottom (uncoated μ-slide VI, Ibidi, Munich, Germany) were inoculated with 10 µL of whole saliva in 90 µL of medium that contained 80% sterile saliva, 20% fetal bovine serum, and either 1% sucrose (SUC) or no sucrose (NoSUC). Each channel had the following dimensions: 0.4 mm (height), 17 mm (length), and 3.8 mm (width). Biofilms were grown anaerobically under static conditions at 37°C. After 24 h of growth, SUC biofilms were too thick for confocal microscopy examination and FLBA. Therefore, SUC biofilms were grown for 16 h and NoSUC biofilms for 24 h, which resulted in similar biofilm thicknesses for both growth conditions. After biofilm growth, the flow cells were immediately subjected to confocal microscopy analysis. All experiments were performed in biological triplicates. The experimental procedures are illustrated in Fig. S1.

Calibration of C-SNARF-4

The extracellular pH in the biofilms was monitored using the ratiometric pH-sensitive dye C-SNARF-4 (Thermo Fisher Scientific, Roskilde, Denmark) (2). The calibration of the dye was performed using MES buffer solutions (50 mM; Sigma-Aldrich) titrated to pH 4.0–8.0 in steps of 0.2 pH units. Buffer solutions were mixed with C-SNARF-4 in the wells of a 96-well plate to a final dye concentration of 30 µM and allowed to equilibrate for 5 min at 35°C. An inverted confocal microscope (Zeiss LSM 700 Axio Observer, Jena, Germany) coupled with a 63×/1.40 oil-immersion objective (alpha Plan-Apochromat, Zeiss) was used for image acquisition. The microscope was set to a pinhole size of 1.76 AU (1.3 µm optical slice thickness), an image size of 512 × 512 pixels (101.61 × 101.61 µm), a pixel dwell time of 12.61 µs, zoom of 1×, and an 8-bit intensity resolution. Images of the buffer solutions were acquired at a 5 µm distance from the bottom of the wells in three randomly chosen fields of view (FOVs) using an excitation wavelength of 555 nm and simultaneous detection from 300 to 618 nm (green channel) and 618 to 800 nm (red channel). The detector gain for both channels was kept constant throughout the experiments. Additionally, images with the laser turned off were acquired for each pH value to correct for detector offset (background). All red and green channel images were exported to ImageJ (22) as TIF files, the background was subtracted, and the fluorescence intensity ratios between the two channels (green/red) were calculated. Finally, the intensity ratios (r) were plotted against the respective pH values and fitted to a symmetrical sigmoidal curve (R2 = 0.9998) using online software (www.mycurvefit.com) (Fig. S2). The resulting equation (1) allowed the conversion of fluorescence emission ratios to pH values:
pH=(((2.249r0.171)1)×136977785393)114.53178
(1)

Ratiometric pH measurements

The flow cell was mounted onto the microscope sample holder (universal mounting frame K, Zeiss), and the medium was carefully removed by inserting filter paper strips (8 × 1.2 mm; Melitta, Minden, Germany) in the outlet of each channel. Thereafter, the biofilms were washed with 100 µL of sterile saline (pH 7.0). The biofilm pH response to sucrose was monitored in 100 µL of saline (pH 7.0) containing 0.4% (wt/vol) sucrose and C-SNARF-4 (30 µM). For each biofilm, five FOVs, at least 1,000 µm apart from each other, were selected at random and marked in the microscope software (Zen 2012 SP5, Zeiss). Images were acquired at the bottom of the biofilms, 5 min (T1) and 15 min (T2) after the addition of sucrose, with the same microscope settings as during pH calibration.

Fluorescence lectin-binding analysis

Glycoconjugates and polysaccharides in the biofilms were visualized by fluorescence lectin binding analysis (FLBA using Aleuria aurantia lectin (AAL; SMS Gruppen, Rungsted Kyst, Denmark) and Morus nigra agglutinin G (Morniga-G/MNA-G; SMS Gruppen), both labeled with fluorescein isothiocyanate (FITC). AAL specifically binds fucose-containing carbohydrate components, whereas MNA-G targets galactose in the biofilm matrix (Table S1). After pH measurements, the ratiometric dye C-SNARF-4 was gently removed from the flow cell channels using absorbing filter paper strips. The biofilms were then washed two times with 100 µL of PBS (pH 7.4) to remove the remaining dye and minimize background fluorescence signals. Thereafter, the biofilms were incubated with 100 µL of the respective FITC-labeled lectin (100 µM) for 30 min (RT), washed once with PBS, and counterstained for 10 min with SYTO 60 (10 µM; Molecular Probes, Thermo Fisher, Carlsbad, CA, USA) to visualize microbial cells. To investigate the relationship between the biofilm pH profiles and the abundance and spatial distribution of matrix carbohydrate components at the microscale, FLBA images were acquired in the same FOVs previously imaged during pH ratiometry. In each FOV, six-sliced z-stacks spanning the height of the biofilms were acquired, both with zoom 1× (512 × 512 pixels; 101.61 × 101.61 µm) and zoom 0.5× (512 × 512 pixels; 203.23 × 203.23 µm). Therefore, carbohydrate components could be quantified within the biofilm areas investigated with pH ratiometry and also in the immediate surroundings. Images were acquired with a pixel dwell time of 2.5 µs, and the pinhole size was set to 1.6 AU (1.3 µm optical slice). FITC-labeled lectins were excited at 488 nm and detected from 300 to 628 nm. SYTO 60 was excited at 639 nm and detected from 644 to 800 nm. Laser power (488 nm) and detector gain were kept constant for each fluorescently labeled lectin and across all biofilm samples. Experiments were carried out in biological triplicates.

Digital image analysis

Extracellular pH in the biofilms was determined as described previously (23). Briefly, the C-SNARF-4 images were imported into the software daime (digital image analysis in microbial ecology, v. 2.2) (24) and segmented to remove microbial cells. In ImageJ (22), the green and red channel images were divided by each other to obtain the fluorescence intensity ratios for all extracellular areas. The average ratios (±SD) were calculated for each FOV and converted to pH values according to equation (1).
The biovolumes of microbial cells and lectin-targeted carbohydrates in the biofilms were estimated in each six-sliced z-stack using the software daime (19). First, all green- and red-channel images were imported into daime as TIF files, and the areas covered by microorganisms (red) and carbohydrates (green) were identified using intensity threshold-based segmentation. The microbial and carbohydrate biovolumes in the bottom layer (slices one and two), in the middle layer (slices three and four), and at the top of the biofilms (slices five and six), as well as the total biovolumes (all six slices), were determined for each FOV using the Cavalieri principle (25), by multiplying the interslice distance with the respective areas covered by microbial cells or lectin-targeted carbohydrates. The carbohydrate biovolumes in each z-stack were quantified as a percentage of the total number of voxels and as normalized biovolumes (% of the microbial biovolumes). The digital image analysis procedures are illustrated in Fig. S3 and S4.

Bacterial 16S rRNA gene sequencing and analysis

For bacterial 16S rRNA sequencing, biofilms were grown in flow cells as previously described and then removed by sonication for 10 min at 37°C in an ultrasonic cleaner (Branson 5510, Branson Ultrasonics Co., Danbury, CT, USA). The collected material from technical duplicates was pooled, and DNA extraction was performed using the DNeasy PowerLyzer PowerSoil DNA Isolation Kit (Qiagen, Hilden, Germany) according to the manufacturer’s instructions. The V3–V4 region of bacterial 16S ribosomal RNA genes was amplified using primers Bac 314F and Bac 805R (26), as described previously (20). Paired-end sequencing (2 × 300 bp) was done on an Illumina MiSeq sequencer using the V3 sequencing kit (Illumina, Inc., San Diego, CA, USA). Experiments were performed in biological triplicates.
All sequence analyses were performed in R v. 4.3.0 (27). Sequences were trimmed to remove barcodes and primers using cutadapt v. 0.2.0 (28). Error correction, amplicon sequence variant (ASV) calling, chimera removal, and taxonomic classification were performed with the R package “DADA2” v. 1.27.1 (29). The classification was done according to the Silva SSU reference database nr. 138 (30). ASVs were filtered to only include those classified as bacteria. Nucleic acid extraction blanks and PCR negatives were used for decontaminating the data using the R package Decontam v. 1.19.0 (31). Contaminants were found using the prevalence method with a threshold of 0.1 and subsequently removed from the data.
Differentially abundant genera between the SUC and NoSUC treatments were identified using the R package ANCOM-BC2 v2.1.4 (32). The R packages Phyloseq v. 1.43.0 (33), Microbiome v1.21.0 (34), vegan v2.6.4 (35), ggplot2 v3.4.2 (36), and custom R scripts were used for all further analyses. For calculating alpha diversity (Shannon index), the number of reads was subsampled to a common read depth of 33,555 reads. All other analyses were performed without subsampling. Relevant ASVs were blasted against the extended Human Oral Microbiome Database (http://www.homd.org) to obtain a species-level classification, and only sequences with 100% identity were retained (Table S2). ASV tables with read counts, relative abundances, and relevant metadata can be found in Table S3. Raw sequences were submitted to NCBI under the BioProject PRJNA1004439.

Statistical analysis

Differences in average biofilm pH after 5 and 15 min of sucrose challenge were compared using paired t-tests, while differences in pH, cell density, and biofilm thickness between SUC and NoSUC biofilms were assessed using unpaired t-tests. pH variances at the FOV level were compared between groups using the F-test. The lectin-stained biovolumes in SUC and NoSUC biofilms were compared using paired t-tests. Correlations between biofilm pH and biofilm thickness were assessed using Pearson or Spearman correlation coefficients. Data were checked for normal distribution and homogeneity of variance using the Shapiro–Wilk and Levene tests, respectively. Statistical analyses were performed with the software R v. 4.3.0 (27) and GraphPad Prism v. 10 (GraphPad Software Inc., San Diego, CA, USA) with the level of significance set at α = 0.05.

RESULTS

Biofilm growth and composition

Biofilm formation in both the presence and absence of sucrose was robust. The biofilms exhibited areas of high and low cell density, and thick protruding cell clusters were often present. Sixteen-hour SUC and twenty-four-hour NoSUC biofilms were similar in thickness (P = 0.11) and cell density (P = 0.49), with average thicknesses (±SD) of 31.76 (±3.66) µm and 26.46 (±6.22) µm and average cell densities (% pixels) of 15.13 (±9.2) and 13.61 (±7.8), respectively. If grown for 24 h, SUC biofilms increased in thickness to 157.37 (±53.22) µm, which prevented FLBA imaging of the biofilms due to the limited lectin penetration (data not shown).
Biofilm composition for both treatment groups was highly reproducible across biological replicates (Fig. 1). SUC biofilms were dominated by Streptococcus spp. (mean relative abundance of 96%); all other bacterial genera had mean relative abundances below 0.6%. NoSUC biofilms were more diverse than SUC biofilms (Shannon indices of 3.3 ±0.09 SD and 1.6 ±0.05 SD, respectively). The most abundant genera in NoSUC biofilms were Streptococcus spp. (mean relative abundance of 32%) and Porphyromonas spp. (mean relative abundance of 28%), with lower contributions from Fusobacterium spp., Haemophilus spp., and Gemella spp. (mean relative abundances of 5%–10%). The microbial composition differed markedly between groups, with the genera Rothia and Streptococcus being significantly more abundant in SUC biofilms (P < 0.05) (Fig. 2). Interestingly, the presence of sucrose during growth also shifted the dominant streptococcal ASV in the biofilms from the Streptococcus mitis/oralis group to the Streptococcus salivarius group (Fig. 1; Table S2).
Fig 1
Fig 1 Bacterial community composition of the biofilms grown in the presence (SUC) or absence (NoSUC) of 1% sucrose. (A) Heatmap of the relative abundance of the 23 most abundant bacterial genera (mean relative abundance above 0.1%) for each biological replicate (R1-R3) of SUC and NoSUC biofilms. (B) Heatmap showing the relative abundance of all Streptococcus ASVs. The dominating streptococcal ASV in SUC biofilms (ASV1) belongs to the salivarius group, while the dominating ASV in NoSUC biofilms (ASV2) belongs to the mitis/oralis group (B).
Fig 2
Fig 2 Differentially abundant genera between biofilms grown in the presence (SUC) and absence (NoSUC) of sucrose. Only genera with an overall mean relative abundance above 0.1% are represented (false discovery rate-adjusted P < 0.05). (A) Positive values indicate genera that were significantly more abundant in SUC biofilms; negative values show genera that were more abundant in NoSUC biofilms. (B) Mean relative abundances (+SD) of the differentially abundant genera between NoSUC and SUC biofilms.

pH-FLBA

The washing of the flow cells with PBS after pH recordings successfully removed C-SNARF-4 from the microbial cells and the extracellular matrix, and no remaining background fluorescence signals interfered with the subsequent FLBA (Fig. S5). The carefully executed washing procedures and the protective geometry of the flow cell preserved the biofilm structure through the sequential staining and washing steps, such that identical FOVs could be re-identified and re-imaged (Fig. 3).
Fig 3
Fig 3 Representative images illustrating the sequential execution of pH ratiometry and fluorescence lectin-binding analysis in a biofilm grown without sucrose. (A) Biofilm imaged with the ratiometric dye C-SNARF-4 after 15 min of sucrose challenge. (B) The extracellular green/red fluorescence intensity ratios in the image were quantified by digital image analysis and converted to pH values. False coloring was applied for the graphic representation of biofilm pH. (C) After washing, the biofilm was stained with FITC-labeled MNA-G (green), the bacterial cells were counterstained with SYTO 60 (red), and the same field of view was re-imaged. (D) Additional images were obtained using 0.5× zoom to visualize matrix carbohydrates in the immediate surroundings. Bars = 20 µm.

Biofilm pH

The extracellular pH of both SUC and NoSUC biofilms dropped significantly after 5 and 15 min of sucrose challenge (P < 0.001) (Fig. 4A). The average pH (±SD) for NoSUC biofilms was 6.56 (±0.15) after 5 min and 6.38 (±0.15) after 15 min. Biofilm pH drops were more pronounced for SUC compared to NoSUC biofilms at both time points, with pH values dropping to 6.28 (±0.14) (P = 0.01) and 6.15 (±0.13) (P = 0.02) after 5 and 15 min, respectively. pH varied moderately between different FOVs inside the biofilms, with differences ranging from 0.05 to 0.54 pH units between the least and most acidogenic FOVs. In NoSUC biofilms, pH variance was significantly more pronounced than in SUC biofilms (0.017 ±0.011 SD vs 0.007 ±0.002 SD; P = 0.004). In both groups, biofilm pH did not correlate with biofilm thickness (NoSUC: r = −0.16, P = 0.41; SUC: r = −0.9; P = 0.65). Figure 4B shows the pH developments over time in two FOVs representative of SUC and NoSUC biofilms.
Fig 4
Fig 4 Extracellular pH in biofilms grown in the presence (SUC) and absence (NoSUC) of sucrose. (A) The biofilm pH, as determined by pH ratiometry, dropped significantly for both groups from 5 to 15 min after the sucrose challenge. At both time points, SUC biofilms exhibited a lower mean extracellular pH compared with NoSUC biofilms. Different letters indicate statistically significant differences between groups; small and capital letters indicate significant differences between time points for each group (P < 0.05). Line and box = median, Q1, and Q3; “x”= mean; error bars = minimum and maximum. (B) Representative images of NoSUC and SUC biofilms imaged with the ratiometric dye C-SNARF-4 (left panels). Following digital image analysis, false coloring was applied to illustrate the pH drops after 5 min (middle panels) and 15 min (right panels) of sucrose exposure. Bars = 20 µm.

Biofilm matrix carbohydrates

The biovolumes visualized by fluorescently labeled lectins were quantified and normalized against microbial biovolumes in the biofilms (Fig. 5A). Overall, both lectins stained high biovolumes, particularly in sucrose-grown biofilms, where they clearly exceeded the microbial biovolume. Both AAL and MNA-G stained significantly larger biovolumes (±SD) in SUC biofilms compared with NoSUC biofilms (206.1% ±82.0 vs 70.0% ±44.8 and 453.2% ±56.0 vs 153.4% ±133.8, respectively; P < 0.05). The biovolumes stained by MNA-G were significantly larger than those visualized by AAL in SUC (P = 0.02), but not in NoSUC biofilms (P = 0.40).
Fig 5
Fig 5 Abundance and distribution of MNA-G- and AAL-targeted matrix carbohydrates in biofilms grown in the presence (SUC) and absence (NoSUC) of sucrose. (A) Amount of lectin-stained biovolume normalized to the bacterial biovolume. Both lectins targeted significantly higher biovolumes in SUC than in NoSUC biofilms (*P < 0.05). (B) Distribution of the biovolume across the layers of the biofilms (pie charts) and proportion of lectin-stained (green) and bacterial (red) biovolumes in the bottom, middle, and top layers of the biofilms (bar charts). Here, 100% denotes the total biovolume occupied by bacteria + the biovolume occupied by lectin-stained carbohydrates. The proportion of lectin-stained biovolumes was increased in SUC biofilms compared to NoSUC biofilms for both MNA-G and AAL. In SUC biofilms, MNA-G was distributed evenly across the layers of the biofilms, whereas AAL was most abundant in the middle and top layers.
In addition, we evaluated the distribution of biovolumes (microbial cells and matrix carbohydrates) across biofilm layers (Fig. 5B). The proportion of lectin-stained biovolumes compared to microbial biovolumes was increased in SUC biofilms compared to NoSUC biofilms for both MNA-G and AAL. In SUC biofilms, MNA-G was distributed evenly across the layers of the biofilms, whereas AAL was more abundant in the middle and top layers. In NoSUC biofilms, both AAL and MNA-G were progressively more abundant towards the bottom of the biofilms.
The relationship between biofilm pH and the amount of lectin-stained carbohydrates in SUC and NoSUC biofilms at the FOV level for each biological replicate is shown in Fig. S6.

DISCUSSION

The present work developed a protocol for the combined application of pH ratiometry and FLBA in microbial biofilms. pH-FLBA allows for the concomitant mapping of local biofilm pH developments and the spatial distribution of extracellular carbohydrate compounds in the biofilm matrix. The method is, therefore, a useful tool to investigate the interplay between the biofilm matrix carbohydrate architecture and the occurrence of local acidic microenvironments in complex biofilms. As a proof of concept, biofilm pH and the presence of MNA-G- and AAL-targeted matrix components were investigated in multispecies biofilms grown from saliva inoculum in the presence and absence of sucrose.
Biofilms grown with sucrose exhibited significantly lower pH levels and higher abundances of both galactose- and fucose-containing matrix carbohydrates, which indicates that the production of those components might be related to the metabolism of acidogenic bacteria. A previous study that investigated the abundance of 10 different lectins in biofilms grown in situ in the presence and absence of sucrose reported that fucose-containing, but not galactose-containing carbohydrates were more abundant in biofilms exposed to sucrose. Due to the considerable biological variation in the biofilm matrix composition between participants, however, the differences were not statistically significant (19).
In the present work, the presence of sucrose during growth modulated the bacterial composition of the biofilms towards a less diverse community dominated by Streptococcus spp. that belonged to the S. salivarius group, which suggests that they are the principal producers of galactose- and fucose-containing matrix components in the employed model. This finding supports the results of Dige et al., who found a significant negative correlation between galactose-containing carbohydrates and the alpha diversity of in situ-grown biofilms (19).
pH-FLBA requires the careful handling of the biofilms after pH ratiometry to preserve the delicate biofilm architecture through the subsequent washing and staining steps. Only if the biofilm structure remains intact, the fluorescence signals from pH ratiometry and FLBA can be correlated at the FOV level. Biofilms were, therefore, washed by gently removing liquids with absorbing filter papers instead of pipets. Moreover, the protective geometry of the employed flow cell channels contributed to shielding the biofilms from excessive shear. For the current study, pH-FLBA was optimized for a complex in vitro model of dental biofilm, but it can likely be extended to in situ- or in vivo-grown biofilms, which are typically more robust. As the sensitive pH range of C-SNARF-4 stretches from pH 4.5 to 7.0, the applicability of the method is limited to moderately acidogenic biofilms.
The emission spectrum of C-SNARF overlaps with most fluorophores available for FLBA. Therefore, the removal of the ratiometric dye after pH analysis was an essential step to allow for the reliable quantification of lectin-targeted matrix biovolumes. At neutral or alkaline pH values, the phenolic group of C-SNARF-4 is deprotonated (37), which facilitates its removal from microbial cells and the biofilm matrix. Double rinses with PBS at pH 7.4 proved to be sufficient to eliminate any background signal from C-SNARF-4 in the detection window employed for the FITC-labeled lectins (Fig. S5).
The thickness and composition of the investigated biofilms can limit the application of pH-FLBA. While C-SNARF-4 penetrates easily through microbial biofilms, the lectins with molecular weights of approximately 70 kDa failed to fully penetrate thick (>100 µm) biofilms grown in the presence of sucrose. Interestingly, fixed biofilm samples have been stained successfully by fluorescently labeled lectins regardless of biofilm thickness (19, 20), indicating that unfixed biofilms are less penetrable. However, the use of standard fixatives (e.g., cross-linking agents) typically causes dimensional alterations in the biofilm structure that may render the re-imaging of identical FOVs impossible (38). As pH ratiometry has to be performed on metabolically active biofilm samples, its combination with FLBA was only possible without fixation.
In summary, pH-FLBA is a useful method to investigate the relationship between pH and carbohydrate matrix architecture in bacterial biofilms at the microscale. Biofilm matrix components have diffusion-modifying properties that interfere with the distribution of acids inside biofilms (17, 18), which in turn affects various biological and biochemical processes in environmental, industrial, and medical biofilms. Spatiotemporal changes in biofilm pH can be accurately monitored by pH ratiometry, while the use of lectins with different carbohydrate specificities allows mapping of distinct carbohydrate matrix compounds in the biofilm matrix. Careful removal of C-SNARF-4 ensures that no remaining background fluorescence interferes with the subsequent lectin imaging. Preservation of the biofilm structure is essential for re-imaging the same areas of the biofilm, and it can be achieved by minimizing the shear forces generated during the multiple staining and washing procedures. Future studies may aim to combine pH-FLBA with other in situ analyses, such as mapping the spatial distribution of target bacteria, to investigate the relationship between acid metabolism, matrix architecture, and microbial composition of biofilms at the microscale.

ACKNOWLEDGMENTS

The authors would like to thank Anette Aakjær Thomsen for the excellent technical support and Eero Juhani Raittio for fruitful discussions.
This work was not supported by any specific funding.

SUPPLEMENTAL MATERIAL

Figure S1 - aem.02007-23-s0001.tif
Experimental setup. Saliva-derived biofilms were grown in the channels (height: 0.4 mm; length: 17 mm; width 3.8 mm) of flow cells in the presence or absence of sucrose for 16 or 24 h. After biofilm growth, pH was monitored over time in five fields of view (FOVs) at the bottom of the biofilms by pH ratiometry. Thereafter, matrix components were visualized in the same FOVs by fluorescence lectin-binding analysis (FLBA). Biofilm pH and biovolumes of the targeted biofilm matrix components were quantified by digital image analysis.
Figure S2 - aem.02007-23-s0002.tiff
Calibration curve for the pH-sensitive dye C-SNARF-4. Green/red fluorescence emission intensity ratios were plotted against the respective pH of MES buffer solutions and fitted to a sigmoidal curve.
Figure S3 - aem.02007-23-s0003.tiff
Digital image analysis procedures to quantify the biofilm extracellular pH. A) For pH quantification, biofilms were imaged with C-SNARF-4 after a sucrose challenge. B) The microbial cells were identified by intensity-thresholding. C) After removal of the cells, the resulting green and red channel images were divided by each other to obtain the fluorescence intensity ratios for the extracellular areas. D) False coloring was applied for graphic representation of the ratios converted to pH values. Bars = 20 µm.
Figure S4 - aem.02007-23-s0004.tiff
Digital image analysis procedures to quantify the lectin-targeted carbohydrates in the biofilms. A) After pH imaging, the biofilms were washed, targeted matrix carbohydrates were stained with FITC-labelled lectins (green) and bacteria were counterstained with SYTO 60 (red). Using intensity threshold-based segmentation, lectin-stained areas (B) and microbial cells (C) were identified for biovolume quantification in the middle, bottom and top of the biofilms. D) The same procedure was performed for 0.5x zoomed-out images of the fields of view. Bars = 20 µm.
Figure S5 - aem.02007-23-s0005.tiff
Removal of C-SNARF-4 for subsequent matrix visualization by fluorescence lectin-binding analysis. A) Biofilms were initially stained with C-SNARF-4 for pH ratiometry. After pH image acquisition, biofilms were washed twice with phosphate-buffered saline (PBS) and the fields of view were reimaged. Images B1-2 show no background fluorescence signals after the washing steps using the image acquisition parameters for visualizing FITC-labeled lectins AAL (B1) and MNA-G (B2). Bars = 20 µm.
Figure S6 - aem.02007-23-s0006.tif
Relationship between biofilm pH and the amount of AAL- or MNA-G-stained carbohydrate matrix components. The top row shows the lectin-stained biovolumes quantified in the same field of view (FOV) imaged for pH analysis (biofilm bottom). The bottom row shows the total lectin-stained biovolume quantified in 6-sliced z-stacks spanning the height of the biofilm acquired in the same FOVs using 0.5x zoom. Data from three biological replicates (R1-3) of the biofilms grown in the presence and absence of sucrose. Each symbol represents one FOV.
Table S1 - aem.02007-23-s0007.docx
Employed fluorescently labeled lectins.
Table S2 - aem.02007-23-s0008.docx
Reference 16S rRNA sequences that exhibited 100% alignment (427/427 nucleotide bases) with Streptococcus ASV1 and ASV2, identified using the Basic Local Alignment Search Tool (BLAST) of the expanded Human Oral Microbiome Database (eHOMD, http://www.homd.org).
Table S3 - aem.02007-23-s0009.xlsx
ASV read counts, relative abundances and associated sample metadata.
ASM does not own the copyrights to Supplemental Material that may be linked to, or accessed through, an article. The authors have granted ASM a non-exclusive, world-wide license to publish the Supplemental Material files. Please contact the corresponding author directly for reuse.

REFERENCES

1.
Schlafer S, Kamp A, Garcia JE. 2018. A confocal microscopy based method to monitor extracellular pH in fungal biofilms. FEMS Yeast Res 18.
2.
Schlafer S, Garcia JE, Greve M, Raarup MK, Nyvad B, Dige I. 2015. Ratiometric imaging of extracellular pH in bacterial biofilms with C-SNARF-4. Appl Environ Microbiol 81:1267–1273.
3.
Koo H, Yamada KM. 2016. Dynamic cell-matrix interactions modulate microbial biofilm and tissue 3D microenvironments. Curr Opin Cell Biol 42:102–112.
4.
Oliveira VB, Simões M, Melo LF, Pinto A. 2013. Overview on the developments of microbial fuel cells. Biochem Eng J 73:53–64.
5.
Mohd Azhar SH, Abdulla R, Jambo SA, Marbawi H, Gansau JA, Mohd Faik AA, Rodrigues KF. 2017. Yeasts in sustainable bioethanol production: a review. Biochem Biophys Rep 10:52–61.
6.
Bissett A, Reimer A, de Beer D, Shiraishi F, Arp G. 2008. Metabolic microenvironmental control by photosynthetic biofilms under changing macroenvironmental temperature and pH conditions. Appl Environ Microbiol 74:6306–6312.
7.
Roeselers G, Loosdrecht M van, Muyzer G. 2008. Phototrophic biofilms and their potential applications. J Appl Phycol 20:227–235.
8.
Percival SL, McCarty S, Hunt JA, Woods EJ. 2014. The effects of pH on wound healing, biofilms, and antimicrobial efficacy. Wound Repair Regen 22:174–186.
9.
Osgood R, Salamone F, Diaz A, Casey JR, Bajorski P, Pichichero ME. 2015. Effect of pH and oxygen on biofilm formation in acute otitis media associated NTHi clinical isolates. Laryngoscope 125:2204–2208.
10.
Lin Q, Pilewski JM, Di YP. 2020. Cystic fibrosis acidic microenvironment determines antibiotic susceptibility and biofilm formation of Pseudomonas aeruginosa. Microbiology.
11.
Takahashi N, Nyvad B. 2008. Caries ecology revisited: microbial dynamics and the caries process. Caries Res 42:409–418.
12.
Kim D, Barraza JP, Arthur RA, Hara A, Lewis K, Liu Y, Scisci EL, Hajishengallis E, Whiteley M, Koo H. 2020. Spatial mapping of polymicrobial communities reveals a precise biogeography associated with human dental caries. Proc Natl Acad Sci U S A 117:12375–12386.
13.
Schlafer S, Baelum V, Dige I. 2018. Improved pH-ratiometry for the three-dimensional mapping of pH microenvironments in biofilms under flow conditions. J Microbiol Methods 152:194–200.
14.
Neu TR, Lawrence JR. 2014. Investigation of microbial biofilm structure by laser scanning microscopy. Adv Biochem Eng Biotechnol 146:1–51.
15.
Kolenbrander PE, Ganeshkumar N, Cassels FJ, Hughes CV. 1993. Coaggregation: specific adherence among human oral plaque bacteria. FASEB J 7:406–413.
16.
Flemming H-C, Wingender J. 2010. The biofilm matrix. Nat Rev Microbiol 8:623–633.
17.
Stewart PS. 2003. Diffusion in biofilms. J Bacteriol 185:1485–1491.
18.
Xiao J, Klein MI, Falsetta ML, Lu B, Delahunty CM, Yates JR, Heydorn A, Koo H, Mitchell AP. 2012. The exopolysaccharide matrix modulates the interaction between 3D architecture and virulence of a mixed-species oral biofilm. PLoS Pathog 8:e1002623.
19.
Dige I, Paqué PN, Del Rey YC, Lund MB, Schramm A, Schlafer S. 2022. Fluorescence lectin binding analysis of carbohydrate components in dental biofilms grown in situ in the presence or absence of sucrose. Mol Oral Microbiol 37:196–205.
20.
Tawakoli PN, Neu TR, Busck MM, Kuhlicke U, Schramm A, Attin T, Wiedemeier DB, Schlafer S. 2017. Visualizing the dental biofilm matrix by means of fluorescence lectin-binding analysis. J Oral Microbiol 9:1345581.
21.
de Jong MH, van der Hoeven JS, van OS JH, Olijve JH. 1984. Growth of oral Streptococcus species and Actinomyces viscosus in human saliva. Appl Environ Microbiol 47:901–904.
22.
Schneider CA, Rasband WS, Eliceiri KW. 2012. NIH Image to imageJ: 25 years of image analysis. Nat Methods 9:671–675.
23.
Schlafer S, Dige I. 2016. Ratiometric imaging of extracellular pH in dental biofilms. J Vis Exp 109:53622.
24.
Daims H, Lücker S, Wagner M. 2006. Daime, a novel image analysis program for microbial ecology and biofilm research. Environ Microbiol 8:200–213.
25.
Gundersen HJ, Jensen EB. 1987. The efficiency of systematic sampling in stereology and its prediction. J Microsc 147:229–263.
26.
Herlemann DP, Labrenz M, Jürgens K, Bertilsson S, Waniek JJ, Andersson AF. 2011. Transitions in bacterial communities along the 2000 km salinity gradient of the Baltic Sea. ISME J 5:1571–1579.
27.
Team RC. 2022. R: a language and environment for statistical computing. R Foundation for Statistical Computing, Vienna, Austria. Available from: https://www.R-project.org
28.
Martin M. 2011. Cutadapt removes adapter sequences from high-throughput sequencing reads. EMBnet j 17:10.
29.
Callahan BJ, McMurdie PJ, Rosen MJ, Han AW, Johnson AJA, Holmes SP. 2016. DADA2: high-resolution sample inference from illumina amplicon data. Nat Methods 13:581–583.
30.
Quast C, Pruesse E, Yilmaz P, Gerken J, Schweer T, Yarza P, Peplies J, Glöckner FO. 2013. The SILVA ribosomal RNA gene database project: improved data processing and web-based tools. Nucleic Acids Res 41:D590–6.
31.
Davis NM, Proctor DM, Holmes SP, Relman DA, Callahan BJ. 2018. Simple statistical identification and removal of contaminant sequences in marker-gene and metagenomics data. Microbiome 6:226.
32.
Lin H, Peddada SD. 2020. Analysis of compositions of microbiomes with bias correction. Nat Commun 11:3514.
33.
McMurdie PJ, Holmes S. 2013. phyloseq: an R package for reproducible interactive analysis and graphics of microbiome census data. PLoS One 8:e61217.
34.
Salojarvi L, Lahti S, Shetty J. 2017. Microbiome. Bioconductor.
35.
Jari OFGB, Friendly M, Kindt R, Legendre P, McGlinn D, Peter R, Minchin RBOH, Simpson GL, Peter SM, Henry HS, Eduard S, Helene W. 2020. Vegan: community ecology package., R. package editor.
36.
Wickham H. 2016. ggplot2. In ggplot2: elegant graphics for data analysis. Springer-Verlag New York, Cham.
37.
Hunter RC, Beveridge TJ. 2005. Application of a pH-sensitive fluoroprobe (C-SNARF-4) for pH microenvironment analysis in Pseudomonas aeruginosa biofilms. Appl Environ Microbiol 71:2501–2510.
38.
Azeredo J, Azevedo NF, Briandet R, Cerca N, Coenye T, Costa AR, Desvaux M, Di Bonaventura G, Hébraud M, Jaglic Z, Kačániová M, Knøchel S, Lourenço A, Mergulhão F, Meyer RL, Nychas G, Simões M, Tresse O, Sternberg C. 2017. Critical review on biofilm methods. Crit Rev Microbiol 43:313–351.

Information & Contributors

Information

Published In

cover image Applied and Environmental Microbiology
Applied and Environmental Microbiology
Volume 90Number 221 February 2024
eLocator: e02007-23
Editor: Jeremy D. Semrau, University of Michigan, Ann Arbor, Michigan, USA
PubMed: 38265212

History

Received: 6 November 2023
Accepted: 8 December 2023
Published online: 24 January 2024

Permissions

Request permissions for this article.

Keywords

  1. dental biofilms
  2. biofilm matrix
  3. confocal microscopy
  4. pH ratiometry
  5. fluorescence lectin-binding analysis

Contributors

Authors

Section for Oral Ecology, Cariology, Department of Dentistry and Oral Health, Aarhus University, Aarhus, Denmark
Author Contributions: Conceptualization, Formal analysis, Funding acquisition, Investigation, Methodology, Visualization, and Writing – original draft.
Andreas Schramm
Section for Microbiology, Department of Biology, Aarhus University, Aarhus, Denmark
Author Contributions: Funding acquisition, Methodology, Resources, Supervision, and Writing – review and editing.
Interdisciplinary Nanoscience Center, Aarhus University, Aarhus, Denmark
Author Contributions: Funding acquisition, Methodology, Resources, Supervision, and Writing – review and editing.
Marie Braad Lund
Section for Microbiology, Department of Biology, Aarhus University, Aarhus, Denmark
Author Contributions: Data curation, Formal analysis, Investigation, Visualization, and Writing – review and editing.
Section for Oral Ecology, Cariology, Department of Dentistry and Oral Health, Aarhus University, Aarhus, Denmark
Author Contributions: Conceptualization, Formal analysis, Funding acquisition, Investigation, Methodology, Supervision, Visualization, and Writing – original draft.

Editor

Jeremy D. Semrau
Editor
University of Michigan, Ann Arbor, Michigan, USA

Notes

The authors declare no conflict of interest.

Metrics & Citations

Metrics

Note:

  • For recently published articles, the TOTAL download count will appear as zero until a new month starts.
  • There is a 3- to 4-day delay in article usage, so article usage will not appear immediately after publication.
  • Citation counts come from the Crossref Cited by service.

Citations

If you have the appropriate software installed, you can download article citation data to the citation manager of your choice. For an editable text file, please select Medlars format which will download as a .txt file. Simply select your manager software from the list below and click Download.

View Options

Figures and Media

Figures

Media

Tables

Share

Share

Share the article link

Share with email

Email a colleague

Share on social media

American Society for Microbiology ("ASM") is committed to maintaining your confidence and trust with respect to the information we collect from you on websites owned and operated by ASM ("ASM Web Sites") and other sources. This Privacy Policy sets forth the information we collect about you, how we use this information and the choices you have about how we use such information.
FIND OUT MORE about the privacy policy