Abstract
13
14
A plant parasite associated with the white haze disease in apples, the Basidiomycota 15
Gjaerumia minor, has been found in most samples of the global bathypelagic ocean. An 16
analysis of environmental 18S rDNA sequences on 12 vertical profiles of the Malaspina 17
2010 expedition shows that the relative abundance of this cultured species actually 18
increases with depth while its distribution is remarkably different between the deep 19
waters of the Pacific and Atlantic oceans, being present in higher concentrations in the 20
former. This is evident from sequence analysis and a microscopic survey with a species-21
specific newly designed TSA-FISH probe. Several hints point to the hypothesis that G. 22
minor is transported to the deep ocean attached to particles, and the absence of G. minor 23
in bathypelagic Atlantic waters could then be explained by the absence of this organism 24
in surface waters of the equatorial Atlantic. The good correlation of G. minor biomass 25
with recalcitrant carbon and free-living prokaryotic biomass in South Pacific waters, 26
together with the identification of the observed cells as yeast and not as a resting spore 27
(teliospore), point to the possibility that once arrived at deep layer this species keeps on 28
growing and thriving. 29
30
31
32
33
34
35
36
37
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38
Introduction
39
The bathypelagic ocean is one of the largest reservoirs of carbon on the planet, both 40
particulate and dissolved. The bioavailable part of this deep carbon pool, also known as 41
labile carbon, decreases along the conveyor belt, following the aging of the water 42
masses, being higher in the Atlantic Ocean compared to the Pacific Ocean1. Despite this 43
general decrease, fast-sinking episodes, such as the collapse of a bloom, could inject 44
fresh organic carbon into the deep sea2 . The remanent part, known as refractory carbon, 45
has been operationally defined as the organic carbon that cannot be degraded at in situ 46
conditions3 and increases towards Pacific waters. This increase of refractory carbon 47
along the conveyor belt is mainly explained by the fact that microbial communities act 48
on the total bathypelagic carbon pool reshaping its composition. Among these active 49
microbes, fungi have been proposed to play an important role as decomposers of 50
organic matter, both labile and refractory 4, with a specialized skillset for the second 51
pool. Despite their importance for the microbial carbon pump, the study of bathypelagic 52
fungal community and marine fungi in general has long been overlooked. 53
54
Pelagic fungi, which are consistently detected in seawater samples, belong mainly to 55
two taxonomic divisions, Ascomycota and Basidiomycota5. Species affiliated with these 56
groups, including G. minor, survive thanks to two main trophic strategies: saprotrophy 57
and parasitism. Saprotrophic fungi degrade and recycle organic matter with extracellular 58
enzymes6, in particular, it has been reported that the abundance of CAZymes 59
(Carbohydrate Active enZymes) increases toward mesopelagic waters 7 pointing to the 60
central role of fungal catabolism in aphotic environments. A similar pattern was also 61
detected for genes related to protein degradation 8. The utilization of extracellular 62
enzymes is a more effective digestion strategy if associated with a particulate-attached 63
lifestyle and, actually, in bathypelagic waters fungi are main colonizers of marine snow, 64
exceeding in some cases the biomass of bacteria 9. As parasites, pelagic fungi are 65
associated with different hosts, including animals, macroalgae, and microplankton 10–12. 66
Several environmental variables have been proposed to shape fungi abundance in photic 67
waters, including temperature, particulate organic matter 13, salinity, depth, oxygen and 68
nitrate14,15 whereas less information is available about the drivers of their distribution in 69
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the bathypelagic realm. It has been suggested that they increase in diversity with depth, 70
mirroring what happens with prokaryotes5. 71
72
During the Malaspina 2010 expedition, Basidiomycota were found to be one of the most 73
important microbial eukaryotic groups in the Bathypelagic Ocean 16. Their relative 74
abundance, based on 454-pyrosequencing, peaked at equatorial Pacific waters, being the 75
most abundant 18S rDNA sequence virtually identical to Gjaerumia minor. A further 76
Illumina sequencing17 confirmed that one of the ASVs (Amplicon Sequence Variants) 77
retrieved (ASV-363) has 100% similarity with Gjaerumia minor (NG_063045). A G. 78
minor MAG retrieved from the deep ocean featured an ITS rRNA sequence identical to 79
a strain isolated from a pleural effusion of a child with pneumonia (KT149771). This 80
species, previously known as Tilletiopsis minor, was recently renamed since the entire 81
taxonomy of Exobasidiomycetes has been redefined based on their phylogenetic 82
relations18. Although the most frequently reported habitat of G. minor is plant material 83
(dead or alive), through propagules in the air, this yeast is capable of colonizing other 84
niches19 , including the deep ocean. This ability to adapt to different environments is 85
well exemplified by the fact that this fungus has been found to be a pathogen both for 86
plants and humans. G. minor is one of the causes of the “white haze” in apple trees 20, a 87
post-harvest disease that flourishes with humidity, cold (4ºC) and low oxygen levels 19 88
while in literature three cases are reported of G. minor as a human pathogen, finding 89
this yeast involved in subcutaneous mycosis 21, severe pneumonia 22 and corneal 90
abscess23. The unusual plasticity of G. minor, coupled with its uneven distribution in 91
the Bathypelagic Ocean, makes this interesting species worth of deeper analyses. 92
93
Here we reanalyze published sequencing datasets from the Malaspina expedition to 94
report the distribution of the Gjaerumia minor along the vertical profiles of several 95
oceanic stations. In addition, taking advantage of the fact that a strain of Gjaerumia 96
minor is commercially available, we were able to develop and test a new TSA-FISH 97
probe with the aim of confirming the presence of this fungus in marine pelagic samples, 98
describing its morphology, quantifying its abundance and investigating a possible role 99
in the labile and refractory carbon degradation process. Finally, we aim to highlight 100
which abiotic and biotic parameters may explain this organism's uneven distribution 101
with the final goal of better characterizing the trophic dynamics of the Bathypelagic 102
Ocean. 103
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104
Methods
105
Information about the studied stations and sampling of Malaspina 2010 expedition 106
could be found in previously published works. In particular, the methodology for 107
bacterial abundance with flow-cytometry and prokaryotic biomass calculation is 108
described in Pernice et al. (2015) 24; DNA extraction, 454-pyrosequencing, and 109
bioinformatic pipeline for samples belonging to the deep ocean are in Pernice et al. 110
(2016)16; DNA extraction and Illumina sequencing for 12 vertical profiles (5 to 4000 m) 111
are in Giner et al. (2020) 17; Illumina sequencing from samples belonging to surface of 112
the entire cruise are in Logares et al. (2020) 25; and data for Illumina sequencing in 113
bathypelagic samples are in Junger et al. (2023)26. All the Illumina raw data (12 vertical 114
profiles, global surface and global bathypelagic) has been newly analyzed here with 115
DADA227 to define the distribution of the ASV of interest (363) in the different 116
datasets. Data for fluorescence Dissolved Organic Matter (FDOM) were obtained using 117
parallel factor analyses (PARAFAC) as described in Catalá et al. (2016) 28 and DOM 118
data and AOU values are from Catalá et al. (2015)29. 119
For TSA-FISH analyses, a seawater sample of 475 mL was fixed with 25 mL of 37% 120
formaldehyde (final concentration 1.85%, at least 1h at 4ºC) and filtered on board on a 121
0.6 µm pore size polycarbonate filter (25 mm diameter). The filters were stored at -80 122
ºC until processing. The TSA-FISH probe (Gmin01, CGACCACCATGTGCCCTT 5'-123
3') to count Gjaerumia minor cells at the microscope was designed based on the target 124
sequence ASV-363 as well as sequences belonging to G. minor from NCBI. The probe 125
was checked in silico against the SILVA 138 database and results to be species-specific 126
(the closer non-target sequence had 3 mismatches). The optimization of the 127
hybridization condition was done using a commercial strain of G. minor (Tilletiopsis 128
minor Nyland fungal strain, JCM No. 8361). A first attempt with a standard TSA-FISH 129
protocol, as described in Pernice et al. (2015) 24,30 adapted from Pernthaler et al. 130
(2001)30, gave poor results (less than 25% of positive cells in the culture). The addition 131
of helpers to contiguous regions of the probe ( HelperA-Gmin1 5’-132
GCGGGCTCGCGGCGATCAAT-3’; HelperB-Gmin1 5’-ACCAAGTTTGCCCAAGTTTT-3’ ) 133
increased the results to 65% of positive cells. The use of Wheat Germ Agglutinin 134
conjugated with Alexa Fluor 594 (Thermofisher; WGA 0.01mg mL -1, 30 min at RT), a 135
fluorescent marker staining chitin, confirmed the presence of a thick wall in cells 136
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labeled with the probe so it was decided to include an additional permeabilization step. 137
After trying several protocols, the best results were obtained using an incubation step 138
for 1 h at 30ºC in a permeabilization buffer (pH 6.5) consisting of 1x PBS, 1% SDS, 1 139
mg mL −1 chitinase and 6 mg mL −1 Glucanex (a cocktail of enzymes isolated from 140
Trichoderma harzianum that contains β -glucanase, cellulase, protease and chitinase as 141
in Priest et al. 2021) 31. With this permeabilization step we reached more than 90% of 142
positive cells (Fig. 1). Finally, the optimal hybridization stringency was determined by 143
keeping the temperature constant at 35ºC and varying formamide concentrations (0% – 144
70%) in the hybridization buffer. The optimal value was 20% formamide, the highest 145
possible concentration before probe signal intensity decreased. We then applied the 146
developed TSA-FISH protocol to a subset of 34 environmental samples from the 147
deepest layer of the Malaspina 2010 expedition. 148
Target cells (two morphotypes, rounded and elongated) were counted by inspecting a 149
transect between 30 and 80 mm (average of 54 mm/sample equivalent to 540 fields). 150
Microscopic analyses were performed on an Olympus BX61 epifluorescence 151
microscope (Olympus America Inc.) at 1000× magnification under UV for DAPI, blue 152
light for A488 (TSA-FISH) and green light for WGA. Pictures were taken on an 153
Olympus DP72 camera connected to the microscope. Biovolume for the rounded 154
morphotype was calculated by assuming a spherical cell based on the average radio 155
(100 cells measured). The biovolume of the elongated morphotype was calculated 156
assuming a prolate spheroid shape (Hillebrand et al., 1999) 32 based on the following 157
formula: V=pi/6*d2*h, where h is the largest cell dimension and d is the largest cross-158
section of h, average h and d are based on 40 measured cell. We then used the equation 159
of Menden-Deuer and Lessard (2000) 33 to convert cell biovolume to cell biomass: pgC 160
cell-1 = 0.216*(Biovolume 0.939). Within each sample, average cell biomass times cell 161
abundance counted by TSA-FISH for each morphotype was calculated and then 162
summed to obtain the total biomass of the G. minor population. 163
Statistical analyses (Regression analyses and Pearson correlation) were performed with 164
Rstudio (package Hmisc). 165
166
Results
167
Morphotypes 168
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Two different morphotypes have been identified as Gjaerumia minor by the TSA-FISH 169
probe (Fig. 2), one rounded with an average diameter size of 1.5 µm (panels a and b), 170
and one elongated (panels c and d) with an average h (larger cell axis) of 5.2 µm and an 171
average d (smaller cell axis) of 1.5. The rounded morphotype, which represents the 172
majority of cells retrieved, shows a single nucleus per cell, evidenced in the figure by 173
DAPI stain. This cell type never appears in culture and was not stained by WGA, as it is 174
clearly visible when comparing to the elongated shape in Figs 2g, 2h and 2i. So, it was 175
assumed that the rounded morphotype has low chitin content. Although a rounded shape 176
is often associated in congenera species with teliospore (resting spore, ticker chitin wall, 177
dikarya), our observations (cell size, lack of thick chitin, and the presence of only one 178
nucleus) lead us to consider the rounded morphotype not a resting spore but an active 179
yeast cell. The elongated morphotypes, present only in Pacific waters, are probably 180
hyphae, sometimes found in chains (Figs. 2c, 2d) but more often as single units (Figs 181
2g, 2h and 2i) with a visible nucleus in the middle as observed also in cultured cells. 182
183
Vertical distribution of the target 18S rDNA sequence 184
In order to have a general view of the distribution of G. minor in the global ocean, we 185
used already published sequencing data of 18S rDNA genes from the 0.2-3 µm size 186
fraction (Illumina tags grouped in ASVs). The relative abundance of the G. minor ASV 187
(ASV-363) was available for 12 vertical profiles from the surface till 4,000 m and for 188
124 surface samples of the entire cruise (Fig. 3). G. minor ASV tends to increase with 189
depth, as shown by the median of its relative abundance (excluding zero values), which 190
is higher in the bathypelagic ocean (median of 0.02% of tags). Sequences belonging to 191
G. minor were not found in 29% of the samples of the Bathypelagic realm, while this 192
number was 53% for Mesopelagic and 67% for Epipelagic samples, further stressing its 193
higher presence in the deeper ocean. Illumina sequencing was also performed in 22 194
bathypelagic samples belonging to a different size fraction (0.8-20 µm). This set of 195
samples shows higher values with a median of 1.73% and a maximal value of 25%. The 196
vertical distribution clearly points to the bathypelagic ocean as a preferred environment 197
for this fungus and we decided to focus on the deepest sampling point for the TSA-198
FISH analysis. 199
200
Cell abundance in the Bathypelagic region and fit with sequencing data 201
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TSA-FISH analysis targeting G. minor was performed on the deepest sample (between 202
2600 and 4000 m) of 34 stations. Figure 4a shows the cell abundance of the two 203
morphotypes retrieved along the cruise track crossing the Atlantic, Indian, and Pacific 204
Oceans. Cells were observed in all 34 bathypelagic samples inspected, with the rounded 205
morphotype being always more abundant than the elongated one. G. minor rounded 206
cells had low abundances (less than 10 cells mL -1) both in Atlantic and Indian oceans 207
whereas they were more abundant in Pacific waters, peaking at station 91 with 107 cells 208
mL-1. Elongated cells were also more abundant (3-6 cells mL -1) where rounded cells 209
were abundant (stations 88-91-92). 210
211
We then compared the cell counts with the relative abundance of the corresponding 212
phylotype in the same samples, analyzed in the 0.8-20 µm size fraction where G. minor 213
had a larger representation, this fraction includes 20 samples of the Illumina survey 214
reported before for the vertical profile (Fig. 4b) and 26 samples from a previous report16 215
in which the same DNA extracts and the same 18S DNA region were analyzed and 454-216
pyrosequenced (Fig. 4c). As expected, since the two sequencing analyses are based on 217
the same DNA extract, the relative abundance of the specific OTU (by pyrosequencing) 218
and the specific ASV (by Illumina) have a very strong direct relationship (n=19, 219
R=0.84, p<0.001). Both sequencing datasets found an almost absence of G. minor in 220
Atlantic Ocean, an intermediate presence in the Indian ocean and maximal values in the 221
Pacific Ocean. There was a statistically significant moderate direct relationship both for 222
the specific ASV (n=18, R=0.54, p=0.02) and the specific OTU (n=26, R=0.51, 223
p=0.008) with the counts of rounded cells. These moderate fits could be explained by 224
the typical errors of each approach and the huge difference in filtered volume which was 225
~120 L for the DNA analysis and only 500 mL for the TSA-FISH. Sequencing data also 226
allowed us to put the abundance of G. minor (in green in Figs. 4b and c) in the context 227
of other fungi, like the rest of Basidiomycota (in blue) and Ascomycota (in light 228
yellow). In the Indian and Pacific Oceans, where G. minor is abundant, this single 229
species represents almost the totality (median of 87%) of Basidiomycota. Ascomycota 230
is generally less abundant than Basidiomycota along the cruise track, but follow a 231
similar global distribution, being functionally absent in the Atlantic Ocean and abundant 232
in Pacific waters. Ascomycota maximal abundance is shifted to station 103 respect to 233
the peak of the Basidiomycota in station 88. 234
235
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Biomass and its relation with AOU and FDOM 236
The biomass of the two morphotypes combined (Total Biomass) ranged between 237
1.74·10-5 and 2.05·10-2 µg C L -1, being globally the rounded morphotype the dominant 238
contributor to the species biomass. The distribution of biomass along the entire cruise is 239
shown in Fig. 5 (bar plot), with the highest values found in equatorial Pacific waters. 240
The points on the graph correspond to AOU (Apparent Oxygen Utilization), which is a 241
proxy for the age of the water mass, higher AOU values imply older waters. 242
Considering the entire cruise track, G.minor biomass is higher in aged waters. A similar 243
picture is obtained observing the relationship between G. minor biomass and the 244
Fluorescent Dissolved Organic Matter (FDOM) (Fig. 6). The FDOM profile for each 245
sampling point was obtained through a PARAFAC analysis28 and it is composed by four 246
peaks, two belonging to Humic-like matter (C1 and C2) that are proxies for the 247
refractory carbon, and two associated with protein-like matter (C3 and C4) that 248
represent the labile carbon. Among the four FDOM components, C2 and C4 did not 249
show a significant relationship with G. minor biomass nor bacteria (both in total 250
Bathypelagic and considering only Pacific samples) and were not considered in this 251
analysis. The correlation between fungi biomass (green dots) and FDOM other two 252
peaks (C1-C3) as well as the relationship between bacteria biomass (blue dots) and the 253
same parameters it is shown in Fig. 6, samples belonging to Pacific waters are in bold. 254
G. minor in Pacific waters has a very strong inverse relationship with the Humic-like C1 255
peak (n=11, R=-0.83, p=0.001). So, despite the presence of G. minor being higher in 256
Pacific compared to Atlantic waters, considering only the Pacific region that is richer in 257
recalcitrant carbon (C1 peak), the abundance of this fungus is higher where the C1 258
concentration is lower suggesting a possible consumption of recalcitrant carbon by 259
G.minor. It is important to note that, despite the biomass of bacteria is much higher than 260
that of G. minor , the relationship between total bacteria biomass and C1 is not 261
significant (p=0.22) in Pacific waters. Considering also the Pacific samples, G. minor 262
biomass presents also a strong inverse relationship with the protein-like C3 peak (n=9, 263
R=-0.72, p=0.027), which in this case is resembled by the prokaryotic biomass (n=9, 264
R=-0.74, p=0.023). 265
266
Abiotic and Biotic parameters 267
Abiotic parameters (temperature, salinity, conductivity and oxygen) did not have a 268
significant correlation with G. minor biomass both for the global bathypelagic ocean 269
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and considering only Pacific samples. Higher values of biomass are within a narrow 270
range of values both for salinity (around 34.7 psu) and oxygen (3.23-3.58 mL L -1), 271
which is expected considering that they all belong to the same water mass. The values 272
of G.minor biomass are extremely low compared with the total prokaryotic biomass 273
which range between 0.12 to 4.49 µg C L -1. Nevertheless, the biomass of G.minor and 274
prokaryotes are strongly correlated (n=26, R=0.8, p<0.001). In particular, in Pacific 275
waters, the Low Nucleic Acid content bacteria (LNA) better correlated with the G. 276
minor biomass than total bacterial biomass (R2=0.86 versus R2=0.59). 277
278
Discussion
279
The presence of a clear hotspot for G. minor in the bathypelagic region of the Equatorial 280
Pacific has been shown in consensus by two different sequencing analyses and a 281
species-specific TSA-FISH probe. Since the ASV retrieved from the sequencing 282
analyses was 100% similar to a cultured strain of G. minor it was possible to test the 283
probe before its application to environmental samples. The TSA-FISH technique 284
allowed us to visualize the morphotype (life-stage) of the targeted fungi, showing that 285
the majority of the G. minor cells were rounded, with a single nucleus and unstained 286
with WGA (Fig. 2). Larger elongated cells were also observed but at much lower 287
abundance. 288
289
G. minor belongs to the class ustilaginomycetes, which are usually dimorphic, 290
producing a saprobic haploid yeast phase and a parasitic dikaryotic phase 34, so 291
particular attention was given to the identification of the proper life-stage of the rounded 292
cells. If they corresponded to a resting stage (teliospore) this would mean that G. minor 293
is not thriving in the bathypelagic environment, whereas a yeast phase opens the 294
possibility that G. minor is alive and active in those waters. Three hints suggest us to 295
exclude the teliospore hypothesis: i) their size is too small; although teliospores from 296
the sister species Gjaerumia ossifragi (Bauer 2005, figs 5-14) 35 show a rounded shape, 297
they are ten times larger than the ones retrieved here, and in proportion G. minor 298
rounded cells seem too little for the size of the hyphae to be a teliospore, ii) they are not 299
dikaryotic, as a teliospore is expected to be; we did not observe two nuclei in DAPI 300
stained samples, iii) last and most relevant, rounded cells are not stained by WGA, a 301
specific stain for chitin; teliospores, on the other hand, are expected to have a very tick 302
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chitin wall (Figs. 2 g-i). The lack of WGA staining is probably due to the fact that yeast 303
merging and budding are favored by a thinner chitin wall. There is still the possibility 304
that the rounded morphotype is a reproductive spore, such as basidiospore (sexual) or 305
basidioconidia (asexual), but although the pressure of the bathypelagic environment 306
could force a more globose shape, both of them are expected to be fusiform 35,36, 307
therefore, we also tend to exclude this hypothesis. 308
309
G. minor is known to have a strong plasticity being retrieved both as plant parasites 19,20 310
and human pathogens 21–23. In the frame of Malaspina 2010 cruise, it is often present 311
also in surface waters (51 of 136 stations), although in a lower percentage. It is clear 312
that G. minor is not an endemic species of the Bathypelagic environment but is 313
transported there from land through the surface global ocean. For prokaryotic 314
communities, based on samples from the same cruise, it has been reported a direct 315
connectivity through fast-sinking particles between surface and the bathypelagic 316
layer37,38. We hypothesized a similar mechanism of transport for G. minor, as previously 317
suggested by Bochadansky and colleagues in 2017 9. This idea is also reinforced by the 318
fact that the osmotrophic food acquisition in fungi, based on the secretion of 319
extracellular enzymes, better suits a particle-attached life-style 6. These particles could 320
be represented by sinking G. minor hosts (phytoplankton) or by fragments of them 321
(animals or macroalgae). Species taxonomically close to G. minor have been found 322
associated with sea-animals 10,11, macroalgae12 and even dinoflagellates 39,40. Related to 323
this, data of the same cruise 41 reported highest concentrations of large phytoplankton in 324
the deep sea, represented by living fast-sinking cells (81.5% of diatoms followed by 325
dinoflagellates) in the Equatorial Pacific, opening the hypothesis of undiscovered 326
microbial interactions. Interestingly, the sequencing analyses shows an absence of G. 327
minor in a large surface area of the equatorial Atlantic Ocean, from 14º N to 24º S 328
(stations 17 to 26) so, the lower presence of this species in Atlantic bathypelagic waters 329
could be explained by its absence at the surface, as the snowfall of particles at the 330
equator is similar between the two oceans42. 331
332
Despite several hints pointing to the fact that fungi arrive to the deep ocean attached to 333
particles, we have only been able to observe this phenomenon once (Fig. 2e, f, which 334
shows a large particle colonized by rounded cells), while most observed rounded cells 335
appear to be free-living. There are possible methodological reasons to explain the lack 336
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of particles observed in our TSA-FISH filters (low volume, high filtering pressure); 337
nevertheless, even in an environment full of particles, yeasts are expected to look for 338
new resources once the ones of their transport-particle are exhausted. We propose that, 339
although the manipulation of the samples could separate some cells from particles, part 340
of the community live temporarily in a free-living state as evidenced by past results of 341
flow cytometry16, sequencing of the 0.2-0.8 µm size fraction (often used as the free-342
living size fraction for bacteria, supplementary table 1) and the TSA-FISH itself. 343
344
The biomass of G. minor yeast cells correlates very well with the biomass of free-living 345
bacteria, although fungal biomass was 3 orders of magnitude lower than the bacterial 346
one. This contrasts Bochadansky et al. (2017) 9, who found similar values for the two 347
groups. The prokaryotic free-living pool represents the endemic part of the community 348
and, in contrast with the particle attached assemblage, does not correlate with surface 349
biotic variables but with bathypelagic environmental conditions 38. This leads us to 350
propose that the good correlation between the biomass of fungi and free-living bacteria 351
is due either to a parallel response to the bathypelagic conditions and resources or to the 352
utilization by fungi of carbon processed by bacteria. In fact, both cases point to an 353
active free-living fungal community. In culture conditions, G. minor does not grow 354
without some vitamins36 ,and in particular, it needs thiamine to thrive. It is possible that 355
the prokaryotic community could be the source of these vitamins and a reliable scenario 356
is that vitamin availability coupled with recalcitrant carbon (C1 peak) created optimal 357
conditions for G. minor, which could grow and reproduce in marine deep waters. 358
359
The idea that once passively transported to the Bathypelagic layer of the Pacific, G. 360
minor is capable of establishing an actively thriving population is supported by several 361
hints. First, we know from experimental evidence in Saccharomyces cerevisiae that 362
fungi can alter their membrane composition to tolerate high hydrostatic pressures 43, 363
which could make possible a rapid colonization of deep-sea habitats by surface strains44. 364
For G. minor this colonization could be supported by a great availability of resources, 365
the pool of recalcitrant carbon. Second, considering the entire dataset, not only 366
Basidiomycota but also Ascomycota are more abundant in the aged waters. Moreover, 367
Ascomycota peak is displaced spatially forward compared to the Basidiomycota peak, 368
pointing to a different target substrate and reinforcing the hypothesis of an active fungal 369
deep community. Third and more importantly, our analysis showed a strong and 370
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significant correlation between G. minor biomass and recalcitrant carbon (C1 peak of 371
FDOM) in Pacific waters suggesting a possible consumption of the recalcitrant pool by 372
G. minor (Fig. 6); the same relation is not significant for bacterial biomass. This 373
possibility is in accordance with Clipson et al. (2006) 45 who state that fungi are often 374
better than bacteria at breaking down recalcitrant organic material. Although the 375
biomass of G. minor is much lower than the biomass of bacteria, it is still possible that 376
they both contribute to the degradation in a mutualistic rather than antagonistic way9,46. 377
378
G. minor also relates significantly to labile carbon (C3 peak of FDOM). In fact, the 379
slope of the correlation line between the labile C3 peak and G. minor is steeper than in 380
the C1 relationship in Pacific waters, which could point to faster utilization of labile 381
than recalcitrant carbon by fungi. It has been proposed that labile matter could act as a 382
primer for the digestion of more refractory components in a dynamic known as 383
priming7,47–49 . Although this topic is still controversial for the aquatic environment 50, 384
our results could suggest a parallel consumption of Humic-like and Labile-like matter 385
operated by G. minor. 386
387
The presence of the cultured plant-parasite G. minor has been highlighted in 388
bathypelagic waters, especially in the Equatorial Pacific where its biomass peaks, both 389
by species-specific TSA-FISH probe and by high-throughput sequencing. Our data 390
suggests that in these waters G. minor feeds osmotrophically on the recalcitrant carbon 391
pool, a resource with which it correlates better than free-living bacteria. Our results 392
show, in accordance to previous works 38,51, that the Bathypelagic Ocean is not an 393
isolated environment but it is in continue connection with surface waters and with the 394
land. In this regard the fungus G. minor shows an enormous potential to be an important 395
active part of the global carbon cycle, pointing at the same time to the importance and 396
necessity of more studies both on the Bathypelagic Ocean and on its fungal diversity. 397
398
Acknowledgements
399
This project was supported by the Spanish Ministry of Economy and Competitiveness 400
through projects Consolider-Ingenio Malaspina-2010 (CSD2008–00077), ALLFLAGS 401
(CTM2016-75083-R, MINECO) and MINIME (PID2019-105775RB-I00, AEI, Spain). 402
We thank our fellow scientists, the crew of the R/V BIO-Hesperides and chief scientists 403
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of the different cruise legs for collaboration, a special thank goes to J.M. Gasol and 404
X.A.G. Moran for sharing the bacterial abundance data. 405
406
Competing interests 407
The authors declare no competing interests. 408
409
Data Availability 410
The sequencing dataset analysed in this present work are all belonging to Malaspina 411
expedition and they are already published and publicly available at the European 412
Nucleotide Archive (ENA). Amplicon sequences from 454-pyrosequencing of the deep 413
ocean are available at www.ebi.ac.uk/ena/data/view/PRJEB9943; Illumina sequences 414
from vertical profiles are available at www.ebi.ac.uk/ena/data/view/ PRJEB23771; 415
Illumina sequences from surface samples are available at 416
www.ebi.ac.uk/ena/PRJEB23913 and Illumina sequenc es from the deep ocean are 417
available at www.ebi.ac.uk/ena/data/view/PRJEB45014. 418
419
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556
Authors contribution 557
MCP, RM, and RL ideate the paper, IF developed the protocol and counted the samples 558
at the microscope, MCP developed the figures and wrote the first draft. MCP, RM, RL 559
and IF edited the final version of the paper. 560
561
Figure Legends 562
Figure 1: Epifluorescence pictures of cultured cells of Gjaerumia minor with triple 563
staining protocols. Panels above show a single elongated cell, possible an hypha, stained 564
with a) DAPI, b) TSA-FISH (Gmin01 probe conjugated with Alexa-488), and c) WGA. 565
The panels below show an entire hyphal structure stained with d) DAPI, e) TSA-FISH, 566
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and f) WGA. Nuclei are visible in blue in a and d, the ribosome-containing cytoplasm in 567
green in b and e, and the outer chitin cover in red in c and f. Scale bar is 5 µm. 568
569
Figure 2: Examples of cells from environmental samples. A rounded morphotype (1.06 570
µm on average, probably a yeast) from ST83 stained with DAPI (a) and the Gmin01 571
probe (b). A hyphal structure (h= 6.9 µm, d=1.16 on average) from ST88 stained with 572
DAPI (c) and the Gmin01 probe (d). A group of rounded morphotypes embedded in a 573
gel particle from ST97 stained with DAPI (e) and the Gmin01 probe (f). A field 574
including the two morphotypes from ST92, an hyphae in the low-left corner and a 575
rounded cell in the up-right corner stained with DAPI (g), the Gmin01 probe (h) and 576
WGA (i). Note that the chitin staining applies to the hypha but not to the rounded cell. 577
Scale bar is 5 µm. 578
579
580
Figure 3: Vertical distribution of Gjaerumia minor based on the relative abundance of 581
ASV-363 that is 100% similar to cultured G. minor (strain AB7-11). Sequences derive 582
from previously published Illumina datasets 17, 25 . Samples from 0.2-3 µm size-fraction 583
were grouped in three layers: Epipelagic (3-200 m), including 149 samples, 584
Mesopelagic (200-1000 m), including 32 samples, and Bathypelagic (1000-4000), 585
including 31 samples (zero values are not shown in the graph). The last boxplot (in 586
blue) shows the relative abundance in 22 Bathypelagic samples belonging to the 0.8-20 587
µm fraction (no zero values found in this dataset). 588
589
Figure 4: Distribution of Gjaerumia minor in bathypelagic waters (deepest sample in 590
each station) along the entire track of Malaspina cruise. Oceanic boundaries are 591
depicted as a red dotted line for the three graphs. a) Cell abundance of rounded cells 592
(probably yeasts, violet) and elongated cells (hyphae, yellow) stained with TSA-FISH in 593
the deepest point of 34 stations spread across Atlantic, Indian and Pacific Oceans; b) In 594
green it is shown the relative abundance of G. minor illumina tags (ASV_363), 595
abundance of tags belonging to other Basidiomycota is shown in blue whereas tags 596
belonging to Ascomycota are shown in light yellow; c) relative abundance of 454-597
pyrosequenced tags (in 26 of the 34 previous stations) published in Pernice et al. 598
(2016)16 (size fraction 0.8-20 µm), tags belonging to OTU-6359 (99.7 similar to G. 599
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minor) are shown in green, other Basidiomycota in blue and Ascomycota in yellow. 600
Illumina and 454 sequencing were done from the same DNA extraction, asterisks show 601
stations where no sequencing data was available. 602
603
Figure 5: Distribution of Gjaerumia minor biomass and Apparent Oxygen Utilization 604
(AOU, µmol O 2 Kg-1) across the Malaspina track. The biomass (expressed as µg C l -1) 605
is visualized as a barplot (left y axis) whereas the AOU, corrected by the real value of 606
measured oxygen, is represented by the blue dot (right y axis). AOU is a measure of the 607
amount of oxygen respired in the deep ocean, higher values of AOU are typical of aged 608
waters. 609
610
Figure 6: Microbial biomass relationship with C1 peak of FDOM (Humic-like, on the 611
left) and C3 peak of FDOM (Labile-like, on the right). G. minor biomass is in green 612
whereas bacterial biomass is in blue; dots belonging to Pacific samples are darker than 613
the rest. Red lines indicate the linear relationships between biomass and FDOM values 614
using only the darker dots. 615
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Bathypelagic
0.8-20 µm
Bathypelagic
0.2-3 µm
Mesopelagic
0.2-3 µm
Epipelagic
0.2-3 µm
10-3 10−2 10−1 100 101
Relative abundance of itags (%)
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0
20
40
60
st17st20st23st26st30st32st35st41st43st44st49st50st53st59st62st63st65st67st74st77st81st82st83st88st91st92st97st103st109st110st112st118st121st131
abundance % pyrotags
0
30
60
90
abundance cells ml-1
Atlantic PacificIndian
abundance % itags
a. TSA-FISH
c. 454 pyroseq-OTUs
0
20
40
60
b. Illumina seq-ASV
* * * * * * * * * * * * * *
* * * * * * * *
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0.000
0.005
0.010
0.015
0.020
0
50
100
150
200
st17st20st23st26st30st32st35st41st43st44st49st50st53st59st62st63st65st67st74st77st81st82st83st88st91st92st97st103st109st110st112st118st121st131
AOU µmol O2 Kg-1
G. minor biomass µg C L-1
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10-2
10-3
10-4
G. minor biomass (µg C l-1)
100.5
10-1
10-0.5
100
Bacteria biomass (µg C l-1)
10-1.7510-1.8010-1.8510-1.90
C1(RU) Humic-like
10-2.0010-2.2510-2.50
C3 (RU) Labile-like
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