spatial distribution analyses of natural phyllosphere-colonizing bacteria on a rabidopsis thaliana...
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Remus-Emsermann et al.
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Spatial distribution analyses of natural phyllosphere-colonizing bacteria 1
on Arabidopsis thaliana revealed by fluorescence in situ hybridization1 2
3
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Mitja N.P. Remus-Emsermann1*, Sebastian Lücker2, Daniel B. Müller1, Eva 5
Potthoff1, Holger Daims2, and Julia A. Vorholt1* 6
7
1Institute of Microbiology, ETH Zurich, Switzerland 8
2Division of Microbial Ecology, Department of Microbiology and Ecosystem 9
Science, University of Vienna, Altanstrasse 14, 1090 Vienna, Austria 10
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*Corresponding authors 12
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Running title: Bacterial distribution on Arabidopsis phylloplanes 14
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Subject Category: Microbial population and community ecology 16
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18 19 20 21 22
Keywords: environmental heterogeneity/ fluorescence in situ hybridization/ 23
phyllosphere/ single-cell microbiology/ community composition 24
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This article has been accepted for publication and undergone full peer review but has not been through the
copyediting, typesetting, pagination and proofreading process, which may lead to differences between this version
and the Version of Record. Please cite this article as doi: 10.1111/1462-2920.12482
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26 Abstract 27
Bacterial colonizers of the aerial parts of plants, or phyllosphere, have been 28
identified on a number of different plants using cultivation-dependent and 29
independent methods. However, the spatial distribution at the micrometer scale 30
of different main phylogenetic lineages is not well documented and mostly based 31
on fluorescence-tagged model strains. In this study we developed and applied a 32
spatial explicit approach that allowed the use of fluorescence in situ 33
hybridization (FISH) to study bacterial phylloplane communities of 34
environmentally grown Arabidopsis thaliana. We found on average 5.4×106 35
bacteria per cm2 leaf surface and 1.5×108 bacteria per gram fresh weight. 36
Furthermore we found that the total biomass in the phylloplane was normally 37
distributed. About 31% of the bacteria found in the phylloplane did not hybridize 38
to FISH probes but exhibited infrared autofluorescence indicative for aerobic 39
anoxygenic phototrophs. Four sets of FISH probes targeting Alphaproteobacteria, 40
Betaproteobacteria, Actinobacteria, and Bacteroidetes were sufficient to identify 41
all other major contributors of the phylloplane community based on general 42
bacterial probing. Spatial aggregation patterns were observed for all probe-43
targeted populations at distances up to 7 µm, with stronger tendencies to co-44
aggregate for members of the same phylogenetic group. Our findings contribute 45
to a bottom-up description of leaf surface community composition. 46
47
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48 Introduction 49
The above ground organs of plants, or phyllosphere, represent a large global 50
habitat for microorganisms. The habitat is dominated by leaves, which were 51
estimated to encompass as much as 109 km2 world-wide and the total number of 52
inhabitants in the phyllosphere is believed to be as high as 1026 bacteria (Morris 53
and Kinkel, 2002). Microorganisms that are living on the surface of leaves, also 54
known as the phylloplane, are generally referred to as epiphytes. Many of these 55
epiphytes are not harmful to the host plants (Vorholt, 2012), but instead are 56
commensals or are even beneficial to the plant host by preventing the growth of 57
secondary colonizers that might be pathogens (Stockwell et al., 2010; Innerebner 58
et al., 2011). 59
Cultivation-dependent and more recently independent methods were used to 60
describe natural community compositions on leaves of various plants (Yang et 61
al., 2001; Delmotte et al., 2009; Knief et al., 2010b; Knief et al., 2012); for reviews 62
see Vorholt (2012); Rastogi et al. (2013), and for the model plant Arabidopsis 63
thaliana in particular see Delmotte et al. (2009); Vorholt (2012); Bodenhausen et 64
al. (2013). Next generation sequencing approaches showed that the bacterial 65
communities found on different plant species are plant-host dependent, stable 66
and have a high degree of reproducibility at the genus level or higher (Knief et al., 67
2010b; Redford et al., 2010; Vorholt, 2012). These findings suggest that the plant 68
host and colonizers might select for each other. However, the underlying 69
processes of community assembly remain to be elucidated. 70
Current knowledge of bacterial colonization of the phylloplane at a micrometer 71
or single-cell scale is mostly based on studies that investigated phylloplane 72 Acc
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colonization using fluorescently tagged model strains (Leveau and Lindow, 2001; 73
Brandl and Mandrell, 2002; Monier and Lindow, 2004, 2005b, a; Zhang et al., 74
2009; Tecon and Leveau, 2012). From these and other studies it became 75
apparent that the phylloplane is not uniformly colonized, but that bacterial 76
colonization takes place in hotspots (Kinkel et al., 1995; Monier and Lindow, 77
2004, 2005b; Sy et al., 2005; Remus-Emsermann et al., 2012). Environmental 78
studies using general DNA dyes and scanning electron microscopy, as well as 79
fluorescent bioreporter-based studies, have shown that bacteria prevalently 80
colonize trichomes, stomates, hydatodes and other prominent leaf features as 81
well as grooves formed by epidermis cells (Beattie and Lindow, 1999; Lindow 82
and Brandl, 2003; Monier and Lindow, 2004). To date, studies investigating 83
natural phylloplane communities at a micrometer scale have been scarce (Morris 84
et al., 1997; Fett and Cooke, 2003; Warner et al., 2008), and efforts to 85
taxonomically identify individual epiphytes at a micrometer scale have been 86
made even less frequently (Li et al., 1997; Bisha and Brehm-Stecher, 2009). In 87
particular, no information on natural epiphytic communities has been obtained 88
by using a multi-labeled combinatorial FISH approach. In this study, we aimed at 89
analyzing natural communities on leaves of Arabidopsis thaliana, which is the 90
best-studied plant model system and one of the current models for microbiota 91
colonization both above- and below ground (Innerebner et al., 2011; Bulgarelli et 92
al., 2012; Lundberg et al., 2012; Vogel et al., 2012). We set out to address the 93
following issues: Firstly, we wanted to understand whether and how the overall 94
bacterial community composition which was described at a low spatial 95
resolution, i.e. the level of individual plants (Knief et al., 2010b; Redford et al., 96
2010), is reflected at micrometer-scale resolution; secondly, if phylloplane 97 Acc
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colonization patterns are predictable, e.g., if the different phylloplane colonizers 98
have non-random spatial relationships, as it was shown for dual species 99
phyllosphere colonization by Monier and Lindow (2005b); and thirdly, if the 100
preferential colonization of specific leaf organs as observed for single-strain 101
inoculations can also be seen in bacterial communities of environmentally grown 102
Arabidopsis. 103
To achieve these goals we tested several methods and established a protocol that 104
allowed us to investigate the distribution of bacterial groups on leaf surfaces at a 105
micrometer scale without introducing a spatial bias. Bacteria were recovered 106
from plant leaves using adhesive tape before fluorescence in situ hybridization 107
(FISH) was used to visualize the distribution of the phylloplane community at the 108
single-cell level. Analysis of the obtained patterns was performed using 109
computer assisted image analysis, and spatial statistical tools provided a 110
systematic microscale investigation of representative parts of the phylloplane of 111
environmentally grown, naturally colonized Arabidopsis leaves. 112
113
Materials and methods: 114
Sampling of environmentally grown Arabidopsis thaliana and isolation of 115
the epiphytic community by cuticle tape lift 116
Arabidopsis plants from a wild population were sampled by digging out whole 117
plants including roots and soil (July 2013, Windisch AG, Switzerland; GPS 118
coordinates 47° 28.898’, 8° 13.054’). Plants were transported to the lab on wet 119
tissue. Weather conditions were hot and dry during sampling, i.e. the minimal 120
night temperature was 15 °C and the maximal day temperatures 32 °C. 121 Acc
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Cuticle tape lifts were performed while the plants were still turgescent. To this 122
end, double-sided adhesive tapes (Yamori 50, 3M double sided adhesive tape 123
9086, X-Film Montex DXP 12, Tesa double sided adhesive tape, two Neschen 124
double sided tape “strong/strong”, and “strong/removable”, all tapes were 125
acquired at Modulor, Berlin, Germany) were glued onto microscopical slides with 126
the protective sheath still intact on the backside of the tape. The protective 127
sheath of the tape was removed and the leaf was carefully flattened onto the 128
sticky layer of the tape using an ethanol wiped, clean glass stick with 1 mm 129
diameter. Spring steel tweezers were used to rip off the leaf from the sticky tape, 130
which resulted consistently in an imprint of the leaf on the adhesive tape, which 131
was checked by phase contrast microscopy. If the leaf remained intact, its still 132
untreated side was then applied to another adhesive tape, which resulted in 133
combined adaxial and abaxial samples of the same leaf. 134
Transferred microorganisms on the adhesive tapes were fixed using a modified 135
protocol of Daims et al. (Daims et al., 2005) by application of 4% 136
paraformaldehyde solution (PFA, 4% PFA in 1 x phosphate buffered saline, pH 7) 137
on top of the adhesive tape harboring the recovered bacteria and incubation for 138
3 hours at room temperature in sealed incubation chambers. After incubation, 139
the slides were dipped for 10 seconds into sterile double distilled H2O to wash 140
off the PFA solution. The slides were then dehydrated by incubations for three 141
minutes each in 50%, 80%, and 100% ethanol. After drying the slides with 142
compressed air and an additional drying for 5 minutes in the dark, the slides 143
were stored in tightly closed plastic tubes at -20 °C in the dark until they were 144
processed for microscopy. 145
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Fluorescence in situ hybridization 147
Ribosomal RNA-targeted oligonucleotide probes designed and evaluated for 148
different phylogenetic groups were chosen from the ProbeBase database (Loy et 149
al., 2007) (for a general discussion on limitations of probes see Amann and Fuchs 150
2008) based on available data for Arabidopsis phyllosphere communities 151
(Delmotte et al., 2009; Knief et al., 2010b; Vorholt, 2012). Probes were 5'-tagged 152
with the fluorochromes Cy3, Cy5, 5’FAM, or ATTO488 (Table 1). Hybridization 153
conditions were chosen according to ProbeBase and the hybridization protocol 154
was adapted from Daims et al. 2005 (Daims et al., 2005). In short, frozen samples 155
were allowed to warm to room temperature in the dark to prevent precipitation 156
of air humidity before they were removed from their plastic containers. Samples 157
were once more dehydrated in an ethanol series as described above to remove 158
any residual water. Remaining ethanol was blown off using compressed air and 159
the slides were allowed to dry in the dark for 10 minutes. Depending on the size 160
of the leaf imprints, the samples were subsequently overlaid by 10 to 40 µL 161
hybridization buffer. Stringent hybridization conditions were ensured by adding 162
formamide to the final concentrations indicated by ProbeBase (see Table 1). All 163
Cy3, Cy5 and ATTO488 labeled probes except HGC69A were added to a final 164
concentration of 1.5 ng/µL, 5’FAM labeled probes to a concentration of 2.5 165
ng/µL. Probe HGC69A was used at a concentration of 2.25 ng/µL. If necessary, 166
unlabeled competitor oligonucleotides were added at the same concentrations as 167
the respective labeled probes. Samples were then transferred to a hybridization 168
chamber filled with tissue paper soaked in hybridization buffer and hybridized at 169
46 °C for three hours. To remove any non-specifically bound probes, samples 170
were then washed for 10 minutes in the appropriate washing buffer (Daims et 171 Acc
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al., 2005). Slides were then dipped into ice-cold water, dried using compressed 172
air and additionally kept for 10 minutes in the dark to allow water residuals to 173
evaporate. In total we hybridized 14 leaves from 4 plants with the general 174
bacterial probe EUB338 and two group-specific probes each. At least 5 175
hybridization experiments per phylogentic group were performed. 176
Even though only the probe EUB338 instead of the probe mix EUB338 I-III 177
(Daims et al., 1999) was used for general bacterial probing, phase contrast 178
microscopy indicated that all microorganisms present on the tape lift (except for 179
infrared autofluorescent bacteria, see below) were detected. 180
181
Microscopy 182
Microscopy was performed using an AxioObserver D2 epifluorescence 183
microscope (Carl Zeiss GmbH, Oberkochen, Germany) with attached light source 184
X-Cite 120Q (Lumen Dynamics Group Inc., Mississauga, Canada). FAM and 185
ATTO488 emission were visualized using Zeiss filterset 38 HE (BP 470/40 186
nm/FT 495 nm/ BP 525/50 nm), Cy3 emission was visualized using Zeiss 187
filterset 43 HE (BP 550/25 nm/FT 570 nm/ BP 605/70 nm), Cy5 emission was 188
visualized using Zeiss filterset 50 (BP 640/30 nm/FT 660 nm/BP 690/50 nm), 189
and emission of infrared fluorescent bacteria was visualized using a custom filter 190
set with a 320-650 nm excitation filter (BG39, Schott AG, Mainz, Germany), 650 191
nm dichroic mirror (5650dcxru, Chroma, Bellows Falls, VT, USA), and a 850 nm 192
longpass emission filter (RG840, Schott AG). Samples were mounted in Citifluor 193
AF1 antifade (Citifluor Ltd., London, UK) and covered with a coverslip prior to 194
observation with a Zeiss 100 x EC Plan-Neofluar oil-objective (1.3 NA, Phaco 3). 195
Images were acquired using an AxioCam Mrm (Carl Zeiss GmbH) and the 196 Acc
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program AxioVision 4.8 (Carl Zeiss GmbH). For every sample, between 20 and 60 197
random fields of view (FOV) with a size of 83 x 62 µm were recorded with up to 5 198
channels assigned to phase contrast, different fluorescent labels, and infrared 199
autofluorescence. 200
201
Image processing and analysis 202
Images were exported from the AxioVision software to 8-bit greyscale TIFF 203
images. Images of green probe signals generally required more processing due to 204
a low signal to noise ratio. These images were processed using the program Fiji 205
(Schindelin et al., 2012) to reduce the background by performing a rolling ball 206
subtraction and applying a median filter before they were imported into the 207
image analysis software DAIME 2.0 (Daims et al., 2006). Images of infrared 208
fluorescent bacteria likely engaged in aerobic anoxygenic photosynthesis were 209
deconvolved using the Huygens remote manager v.2.1 implementation of the 210
Huygens deconvolution software package (Scientific Volume Imaging, Hilversum, 211
The Netherlands) since the focus layer of the used filterset was different from all 212
other images. All other images were directly imported into DAIME 2.0 where a 213
“blur and subtract” background correction was performed and histogram 214
stretching was applied to improve the results of subsequent image segmentation. 215
Images were segmented in DAIME using the automatic threshold algorithms 216
“isodata” or “local” depending on the individual dataset. Automatically 217
segmented images were manually validated. To exclude non-microbial 218
fluorescent particles from further analysis, the phase contrast images of the 219
affected FOVs were used to check dubious fluorescence signals. False negative 220
results (i.e., cells overlooked during the automated segmentation procedure) 221 Acc
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occurred in case of large differences in fluorescence intensity between cells in 222
the same FOV and were included by using manual segmentation tools provided 223
in DAIME. The image area occupied by bacteria was used as a proxy for bacterial 224
population density. 225
Total bacterial population density was estimated by cumulating the areas 226
occupied by bacterial cells hybridized to EUB338 and by bacteria exhibiting 227
infrared autofluorescence, which did not hybridize to FISH probes. 228
The relative abundance per FOV of a bacterial group under study was estimated 229
by quantifying the area fraction relative to all bacterial cells. To estimate 230
absolute cell numbers of each bacterial group per cm2 leaf surface, the median 231
object area of each probe-target group was measured assuming that the cells 232
formed a monolayer. Subsequently, the corresponding total area was divided by 233
the median object area. 234
To quantify the spatial arrangement patterns of the different phyla and classes 235
under study, we performed a stereological analysis using the linear dipole 236
algorithm implemented in DAIME, which yields pair correlation and pair cross-237
correlation plots with 95% confidence intervals (Daims and Wagner, 2011). 238
Spatial arrangement patterns within the same probe-target group were 239
quantified by taking into account also co-aggregation signals within the same 240
objects to appropriately analyze microcolonies of densely packed cells that could 241
not be further resolved by the segmentation algorithms. To mark the length of an 242
individual cell and thus distances from which pair correlations become 243
meaningful, a vertical line was added to the resulting pair correlation plots to 244
depict the determined average length of the bacteria under study. Pair (cross) 245
correlation values that are not significantly different from one indicate that the 246 Acc
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spatial arrangement of the tested groups is random at the respective distance. 247
Values significantly greater than one indicate co-aggregation, whereas values 248
significantly smaller than one indicate a negative spatial correlation. 249
250
Results 251
Establishment of cuticle tape lifts to observe phylloplane microbial 252
communities 253
To analyze spatial relations of phylloplane bacteria we established a protocol, 254
which consists of applying double-sided adhesive tape to Arabidopsis leaves. A 255
similar approach was previously reported by Bisha and Brehm-Stecher for 256
tomato fruits (Bisha and Brehm-Stecher, 2009). The protocol allowed to readily 257
detect the presence of bacteria by phase contrast microscopy and projected the 258
three-dimensional leaf surface onto a two-dimensional plane, thereby also 259
facilitating image acquisition. In total we screened six different adhesive tapes 260
(see Materials and Methods). Cuticle tape lifts to remove phylloplane bacteria 261
were first applied to Arabidopsis plants cultivated in growth chambers as 262
described before (Innerebner et al., 2011) that were inoculated with red-263
fluorescent mCherry-protein expressing Sphingomonas Fr1 (unpublished). All 264
adhesive tapes tested were able to quantitatively remove the phylloplane 265
community from Arabidopsis leaves resulting in leaves that were almost devoid 266
of fluorescent bacteria (exemplarily shown in Supplemental Figure 1). The 267
bacterial patterns that were observed on the tape lifts matched those 268
colonization patterns that were visible during direct in planta observations of the 269
same fluorescent bacteria (Supplemental Figure 1). The tape “Yamori 50” had the 270
best properties for the study. The autofluorescent background of this tape was 271 Acc
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low and even, in contrast to most other tapes that exhibited high background 272
fluorescence or contained a mesh of fibers that produced an uneven background 273
and severely hampered validation by phase contrast microscopy. 274
As alternative approaches we also tested a 3D-FISH protocol where entire 275
samples were embedded in polyacrylamide pads (Daims et al., 2006) and an 276
analogous technique using agar (Brandl et al., 2006). However, these approaches 277
did not yield satisfactory results as they produced obvious artifacts in the 278
distribution of phylloplane bacteria under study, or the protective gel cover 279
dissolved during the required washing and drying steps. Another obstacle of 280
these approaches was strong uneven autofluorescence from the plant tissue. 281
282
Establishment of FISH procedures 283
In a first step, we used pure culture isolates of typical phyllosphere colonizers to 284
test the FISH probe set (see Materials and Methods, Table 1). The tested strains 285
included the alphaproteobacteria Sphingomonas strain FR1 (Innerebner et al., 286
2011), S. phyllosphaere (Rivas et al., 2004), Methylobacterium extorquens PA1 287
(Knief et al., 2010a), Methylobacterium sp. L04, Methylobacterium sp. P01, and 288
Methylobacterium sp. Q12 (Stiefel et al., 2013), the gammaproteobacterium 289
Pseudomonas syrinage pv. tomato DC3000 (Cuppels, 1986), as well as recently 290
isolated strains including the betaproteobacterium Variovorax sp., the 291
actinobacterium Arthrobacter sp., and the Bacteroidetes member Pedobacter A03 292
(laboratory collection, unpublished). All probes were successfully tested for their 293
ability to detect the specific strains and to discriminate against members of non-294
target phylogenetic groups (examples of hybridizations are shown in 295
Supplemental Figure 2 and 3). 296 Acc
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In contrast to all other bacterial strains tested, we found that the 297
Methylobacterium strains exhibited an erratic hybridization pattern where some 298
cells of a population hybridized very well to FISH probes, while others did not 299
hybridize at all (even when two distinct FISH probes were applied that should 300
both target these cells, i.e. EUB338 and ALF698a; Supplemental Figure 3). 301
Notably, these bacterial strains exhibited infrared autofluorescence, which was 302
previously linked to aerobic anoxygenic phototrophs (AAnPs), after growth in 303
planta as well as on R2A media exposed to a diurnal cycle (Stiefel et al., 2013). 304
The cause of the failure to consistently hybridize to FISH probes is currently 305
unclear and it remains to be shown whether membrane compounds such as 306
hopanoids (Knani et al., 1994; Bradley et al., 2010; Muller et al., 2011), or the 307
expressed photosystems found in the membranes of Methylobacteria might 308
affect diffusibility of the probes or if the cellular ribosome content might be 309
strongly reduced in many, but not all, Methylobacterium individuals. At this time, 310
we can also not completely rule out that the bacterial photosystems are 311
quenching the fluorescent signal of the FISH probes. However, in our pure 312
culture hybridization we did not observe an inverse correlation between high 313
infrared autofluorescence and FISH signal. 314
315
General observation of cuticle tape lifts of the phylloplane 316
Upper and lower phylloplane samples of the same leaves were investigated and 317
the general bacterial cell density was estimated microscopically after hybridizing 318
the samples to the general bacterial probe EUB338. Images of random FOVs were 319
acquired with up to 5 color channels, and a total of more than 1100 FOVs were 320
analyzed. We found that on average, approximately 5% of the abaxial 321 Acc
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phylloplane, i.e. the lower leaf surface, were covered with bacteria (Figure 1), 322
while we hardly detected bacterial cells on the adaxial phylloplane. We therefore 323
focused on the abaxial leaf side for stereological analyses. The bacteria on the 324
abaxial phylloplane were organized in clusters and individual cells (Figure 2). In 325
general, most detected bacteria of the same phylogenetic probe-target group 326
exhibited similar morphologies. Three-dimensional assemblages were observed 327
occasionally (e.g., ball-shaped colonies of Bacteroidetes, Figure 2 C), possibly 328
leading to an underestimation of the total bacterial abundance as measured here 329
from areas in two-dimensional images. We found that bacteria regularly 330
accumulated close to imprints of stomatal openings (Figure 2 A and B) and 331
bacteria of the same phylogenetic group often formed small microcolonies of five 332
or more cells (Figure 2). However, it was common to find cells of different 333
phylogenetic groups to co-aggregate. Bacterial densities increased towards the 334
leave edges and high densities of AAnPs could be found here often (data not 335
shown). 336
The area covered by bacteria per FOV was found to be normally distributed 337
(Figure 1). The standard deviation, as indicated by the slope of the plots, was 338
almost identical between samples (Figure 1). 339
Members of the Alphaproteobacteria, Betaproteobacteria, and Actinobacteria 340
constituted the major parts of biomass on the leaves studied (Figure 3); however 341
a significant proportion of bacteria in the phylloplane did not hybridize to any 342
FISH probe. Coincidentally, these bacteria also exhibited detectable infrared 343
autofluorescence indicative of AAnP (Figures 3) (Atamna-Ismaeel et al., 2012), as 344
which they will be referred to in the following. We found that 2.5% of the 345
autofluorescent bacteria also hybridized to the Alphaproteobacteria-directed 346 Acc
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probe ALF968 and the general probe EUB338. 347
While Alphaproteo-, Betaproteo-, Actinobacteria, and AAnPs were evenly 348
distributed, i.e. they could be found in every FOV of a sample to similar degrees 349
(Figure 3), Bacteroidetes appeared only in some FOVs as cell clusters or 350
individual cells (Figure 2). Gammaproteobacteria were detected rarely and 351
occurred as single cells. 352
353
Bacterial diversity and abundance in the phylloplane of Arabidopsis 354
In general, FISH probes targeting four phylogenetic groups, in combination with 355
the detection of infrared autofluorescence, were sufficient to cover the total 356
bacterial communities. Specific phylogenetic groups covered the phylloplane to 357
different degrees. On average, 1.4% of the phylloplane was covered by 358
Alphaproteobacteria, 2.7% by AAnPs, 0.8% by Betaproteobacteria, 0.4% by 359
Actinobacteria, and 0.2% by Bacteroidetes (Figure 4 A). By adding up the average 360
areas covered by different bacterial groups, i.e. the groups detected by specific 361
FISH and infrared autofluorescence, and comparing the result to the average 362
total phylloplane area covered by bacteria, we found that no major bacterial 363
contributor remained undetected (Figure 4 B). Note, bacteria with an infrared 364
fluorescence that also stained with FISH probes represented a minor fraction 365
and were counted only once. 366
Cell numbers for the analyzed bacterial groups per cm2 leaf surface were 367
estimated by using their median object size (extracted from the segmented 368
images in DAIME and exemplarily validated manually). This approach predicted 369
median areas covered per a cell of 0.5 µm2 for Alphaproteobacteria; 1.4 µm2 for 370
Betaproteobacteria; 0.3 µm2 for Actinobacteria; 1.4 µm2 for Bacteroidetes; and 1.6 371 Acc
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µm2 for AAnPs. The estimated cell densities were between 105 and 2.5 x 106 cm-2 372
per phylogenetic group (Figure 4 C). This conversion from areas to cell numbers 373
shifted the relative abundances of the phylogenetic groups (Figure 4 D and E), as 374
the median cell sizes of the phylogenetic groups differed. Adding up all bacteria 375
we estimate an average bacterial abundance of 5.42 x 106 bacteria per cm2 leaf 376
surface and 1.46 x 108 bacteria per gram fresh weight (leaf fresh weight was 377
estimated from surface area / weight correction factors found in Schmitz 2010). 378
379
Spatial arrangement patterns of phylogenetic groups in the phylloplane of 380
Arabidopsis 381
Based on specific FISH labeling and digital image analysis, it was possible to 382
analyze spatial relationships among the dominating members of the phylloplane 383
community (all images passed the DAIME suitability tests for spatial 384
arrangement analyses). Most analyses indicated co-aggregation of bacteria 385
belonging to different phylogenetic groups at distances below 6 µm (Figure 5). At 386
distances larger than 6 µm, cells were randomly distributed, i.e, pair cross-387
correlation values were not significantly different from 1. Bacteroidetes showed a 388
lower tendency to co-aggregate with members of other groups. Notably, much 389
higher pair correlation values indicated that co-aggregation within phylogenetic 390
groups was much stronger than co-aggregation between groups (Figure 5). 391
Moreover, for bacteria of the same group co-aggregation was in general observed 392
for longer distances (up to 8 µm) than for members of different groups. This 393
indicates that bacteria of the same group preferentially clustered in 394
microcolonies. The tendency of AAnPs to co-aggregate with each other was 395
rather weak as indicated by low pair correlation values at distances beyond the 396 Acc
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median cell size of AAnPs (Figure 5). 397
398
Discussion: 399
FISH approaches have occasionally been used in studies of bacteria colonizing 400
plants (Li et al., 1997; Bisha and Brehm-Stecher, 2009; Bulgarelli et al., 2012) but 401
so far a combinatorial FISH approach that allows uncovering the phylogenetic 402
identity of several phylogenetic groups naturally colonizing the phyllosphere or 403
phylloplane was not performed to our knowledge. 404
It is noteworthy that the bacterial phylogenetic groups identified and their 405
relative abundances at the single-cell level roughly reflect the community 406
structure determined by next generation sequencing approaches (Vorholt, 2012; 407
Bodenhausen et al., 2013), although at lower phylogenetic resolution. Three 408
major phylogenetic groups, namely Alphaproteobacteria, Betaproteobacteria, and 409
Actinobacteria, dominated the phylloplane samples and were evenly distributed. 410
Furthermore, Bacteroidetes were consistently found in every Arabidopsis 411
phylloplane sample observed but appeared only in some FOVs. 412
Gammaproteobacteria were only rarely detected in this study. Since they are 413
nevertheless readily detectable in sizeable proportions in metagenomic studies 414
(Vorholt, 2012) and by 16S rDNA amplicon sequencing (Bodenhausen et al., 415
2013). However, these studies did not distinguish epiphytic from endophytic 416
bacterial populations. It is noteworthy, that the weather had been hot for several 417
weeks prior to sampling, possibly selecting against the fast growing epiphytic 418
Gammaproteobacteria. Moreover, as plant colonizing Gammaproteobacteria are 419
mostly copiotrophs and grow fast when present in "ideal" environments, it is not 420
unlikely that they were clustered in rare hotspots containing high amounts of 421 Acc
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nutrients (Leveau and Lindow, 2001; Monier and Lindow, 2004; Remus-422
Emsermann et al., 2012). 423
The striking abundance of bacteria exhibiting anoxygenic photosystem-related 424
infrared autofluorescence was higher than the predicted relative abundances of 425
10-20% or 6% of the total community in the Arapidopsis phyllosphere based on 426
metagenomes or leaf-wash counts, respectively (Atamna-Ismaeel et al., 2012). 427
Also striking was that none of the applied FISH probes hybridized reliably to 428
these bacteria, and only probes ALF968 and EUB338 occasionally bound to these 429
organisms. We hypothesize that the majority of the AAnPs belonged to the class 430
Alphaproteobacteria (Atamna-Ismaeel et al., 2012). More specifically, they may 431
represent Methylobacterium strains, as it was recently found that all cultivable 432
bacteria exhibiting aerobic anoxygenic photosynthesis in the phyllosphere of 433
white clover were Methylobacteria (Stiefel et al., 2013). Moreover, the cells that 434
we found to exhibit infrared fluorescence were morphologically and 435
phenotypically similar to the pure culture strains shown in Supplemental Figure 436
2 since the observed cells were quite large in comparison to other morphotypes 437
found in the samples and the pure cultures also showed inconsistent 438
hybridization patterns to the aforementioned rRNA-targeted probes. The only 439
other cells that morphologically resembled AAnPs hybridized to the 440
Bacteroidetes-specific probes; however, to our knowledge no Bacteroidetes strain 441
has been described that belongs to the AAnPs. Consistently, none of the 442
Bacteroidetes-related cells exhibited infrared autofluorescence. 443
We observed higher bacterial cell numbers on the abaxial side of the leaves, 444
which is not surprising since the leaf offers more protection on this side. In 445
particular UV light and draught stress (Vorholt, 2012) will be much lower on the 446 Acc
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abaxial side since the leaf blocks much of the UV-fraction of the sunlight and 447
relative humidity can be expected to be higher under plant leaves. 448
We observed aggregation patterns for all probe combinations investigated, with 449
weak but significant cross correlation values at short distances between 450
members of most studied phylogenetic groups (Figure 5). This result indicates a 451
high probability to find bacteria belonging to different phylogenetic groups in 452
close vicinity of each other. However, we interpret this effect as dictated mainly 453
by the environment rather than by bacterial interactions. Bacteria seemed to 454
prevalently proliferate in similar sites like epidermal cell grooves, forcing 455
phylloplane colonizers to grow in close vicinity of each other. Any possible 456
interaction will thus be environmentally amplified due to geographical features 457
of the leaf. We observed significant co-aggregation only with a minimal distance, 458
(see Figure 5) which is in line with observations that multispecies aggregates are 459
not common (Monier and Lindow, 2005b). The much higher probability to find 460
bacteria of the same phylogenetic group to be co-aggregated reflects the growth 461
of microcolonies upon successful colonization. However, these spatial patterns 462
also appeared to be strongly influenced by the leaf environment, since the 463
distance until random distribution occurred was nearly identical for members of 464
the same and different phylogenetic groups (Figure 5). Thus, the habitability of 465
the phylloplane environment appears to shape the bacterial colonization pattern 466
and bacterial life seems to be concentrated at distinct sites in the phyllosphere, 467
where aggregation takes place. Similar effects have been observed previously in 468
bacterial dual species model systems (Monier and Lindow, 2005b). This 469
assumption is in line with a phyllosphere model in which many small sites with 470
intermediate resource availability are prevalent (Remus-Emsermann et al., 471 Acc
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2012). 472
The results presented in this study provide a first assessment of natural 473
community patterns in the phylloplane of the model plant Arabidopsis at a 474
micrometer level and can serve as a basis to investigate the dynamics of 475
phylloplane communities in the future. The methods presented will give us 476
better predictive power for questions on bacterial clustering behavior in situ and 477
may also help to analyze the mechanism of action of plant probiotic bacteria that 478
exhibit a protective effect against pathogenic bacteria (e.g. Innerebner et al., 479
2011; Vogel et al., 2012). It has been suggested that niche occupation is a critical 480
factor contributing to the protective effect known as preemptive colonization 481
(Lindow, 1987; Remus-Emsermann et al., 2013). Therefore, an in-depth spatial 482
description is crucial to understand and interpret such drivers of plant 483
protection. Moreover, the herein developed technique to fix and observe spatial 484
patterns will help to study phylum distributions in the phyllosphere at scales 485
relevant to microbial life with a phylogenetic resolution down to the genus level 486
in the future. 487
488
Acknowledgements: 489
Funding was provided by ETH Zurich and Austrian Science Fund (FWF, grant no. 490
P24101-B22). 491
492
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493 494
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673
Table 1: FISH probes applied in this study 674
*competitor probe required 675
676
Figure legends: 677
678
Figure 1: Relative area per FOV covered by bacteria of different samples shown as a 679
normal probability plot. Each point represents the bacterial coverage in one FOV; different 680
symbols correspond to the different samples. No significant differences could be detected 681
between the samples. Horizontal stippled line = average biomass. Vertical stippled line = 682
median and average of the distributions. 683
684
Figure 2: Representative rRNA-targeted FISH micrographs of phylloplane communities 685
sampled by employing the cuticle tape lift technique. A) Green = Actinobacteria; Purple = 686
Betaproteobacteria; Blue = general bacterial probe; AAnPs not shown. Betaproteobacteria 687
are enclosing an imprint of a stomate. B) Purple = Alphaproteobacteria; Green = 688
Betaproteobacteria; Blue = general bacterial probe; AAnPs not shown. Betaproteobacteria 689
are clustering close to a stomate imprint. C) Green = Alphaproteobacteria; Purple = 690
Bacteroidetes; Blue = general bacterial probe; White = AAnPs. Alphaproteobacteria formed 691
Target group Probe name Probe sequence
**competitor probe sequence
Labels Formamide % Reference
Alphaproteobacteria ALF968 GGTAAGGTTCTGCGCGTT Cy3;
Cy5
30 (Neef, 1997)
Betaproteobacteria* Bet42a GCCTTCCCACTTCGTTT **GCCTTCCCACATCGTTT
Cy3;
Cy5
30 (Manz et al., 1992)
Gammaproteobacteria* Gam42a GCCTTCCCACATCGTTT **GCCTTCCCACTTCGTTT
Cy3 30 (Manz et al., 1992)
Bacteroidetes CFB319a TGGTCCGTGTCTCAGTAC Cy3,
Cy5
30 (Manz et al., 1996)
Bacteroidetes CFB719 AGCTGCCTTCGCAATCGG Cy3,
Cy5
30 (Weller et al.,
2000)
Actinobacteria* HGC69A (HGC)
TATAGTTACCACCGCCGT **TATAGTTACCGGCGCCGT
Cy3 30 (Roller et al.,
1994)
Most Bacteria EUB388 GCTGCCTCCCGTAGGAGT Atto488;
5’FAM
20-50 (Amann et al.,
1990)
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many small single layered aggregates. Bacteroidetes formed a small, possibly ball-shaped 692
multilayered microcolony. D) Green = Alphaproteobacteria; Purple = Bacteroidetes; Blue = 693
general bacterial probe; White = AAnPs. Arrows point to stomatal imprints. Scale bars = 10 694
µm 695
696
Figure 3: Relative coverage of leaf samples by different bacterial phylogenetic groups and 697
AAnPs. A = Bacteroidetes; B = Alphaproteobacteria; C = AAnPs; D = Betaproteobacteria; E = 698
Actinobacteria. Every box represents the bacterial coverage in one leaf sample and the 699
recorded FOVs. Box boundaries and middle line represent the 25 percentile, median, and 700
75 percentile; whiskers represent 10 and 90 percentiles, respectively. 701
702
Figure 4: A) Average relative area covered by bacteria B) Average total area covered by 703
bacteria per FOV compared to the average area covered by the specific phylogenetic 704
groups analyzed. Adding up the average occurrence of bacterial groups, we could not 705
detect any differences between the total area covered by bacteria and cumulative 706
abundance of all groups. C) Estimated cell counts of the different groups and AAnPs per 707
cm2 D) Relative area contribution of different groups and E) relative contributions of 708
different groups normalized by cell size. All error bars represent the standard deviation of 709
the mean. 710
711
Figure 5: Analyses of spatial arrangement patterns observed for different phylogenetic 712
groups in the phylloplane and members of the same probe target group. Solid curves show 713
the average pair correlation or cross-correlation values averaged over all images, dotted 714
curves indicate upper and lower 95% confidence limits. The horizontal stippled line 715
indicates values 1, which represents a random spatial distribution. Pair correlation values 716
greater than 1 indicate spatial co-aggregation of the populations analyzed. Values below 1 717
indicate a negative spatial correlation, possibly due to repulsion or niche segregation. The 718
vertical stipple-dashed line represents the intercept of the lower 95% confidence interval 719
with the random distribution line; this point marks the end of a co-aggregation signal and 720 Acc
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the beginning of random spatial distribution. Solid vertical lines in self-correlation plots 721
depict the determined average cell size; pair correlation values >1 at distances larger than 722
the average cell size indicate microcolony formation of bacteria of the same phylogenetic 723
group. 724
725
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31%
8%2%
10%
49%
53%
12% 3%
7%
25%
Actinobacteria
Bacteriodetes
Betaprotebacteria
AlphaproteobacteriaAAnP
total biomass
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4
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