Abstract
17
The green seaw eed Ul va depends on its associated bact eria for morphogenesis and is an 18
important model to study algal-bacterial interactions. Ul va -associated bact eria exhibit 19
high turnover across environmental gradients, leading t o the h ypothesis that bacteria 20
contribute to the acclimation potential of the host. Y et little is known about the variation 21
in the functional profile of Ulva-associat ed bacteria in relation to environmental 22
changes. T o test which microbial fu nctions shift alongside a strong en vironmental 23
gradient, w e analysed microbial communities of 91 Ul va samples across a 2,000 km 24
Atlantic–Baltic Sea salinity gr adient using metagenomic sequencing. Metabolic 25
reconstruction of 639 metagenome-assembled genomes rev ealed widespread potential 26
for carbon, sulphur , nitrogen, and vitamin metabolism, including amino acid and vitamin 27
B bios ynthesis. While salinity explained 70% of taxonomic variation, it only accounted 28
for 17% of functional v ariation, indicating extensiv e fun ctional stability . The limit ed 29
variation was attributed to typical high-salin ity bacteria exhibiting enrichment in genes 30
for thiamine, pyridoxal, and betaine biosynthesis. These metabolic modules likely 31
contribute to oxidativ e stress mitigation, cellular osmotic homeostasis, and membrane 32
stabilization in r esponse to salinity variations. Our results emphasise the importance of 33
functional profiling to understand the seaw eed holobiont and its collecti ve r esponse to 34
environmental change. 35
36
37
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3
Introduction
38
Microbial communities interact with eukaryotic hosts in e very ecosystem, yet our 39
understanding of how (variation in) microbial metabolisms impact host performance is 40
very l imited. Seaweeds, or macroalg ae, are a group of important coastal inhabitants. As 41
ecosystem engineers and primary p roducers, they are an essential sour ce of food and 42
they provid e shelt er and habitat f or di verse marine organisms 1 . Health, reproduction, 43
and dev elopment of the macroalgal host — and indirectl y their ecosystem functioning 44
— are strongly dependent on the associat ed symbionts. Beyond the ex change of ke y 45
nutrients, vitamins, and secondary metabolites, the microbial biofilm forms a physical 46
and chemical barrier acting as a “second skin ” that prot ects the host and modulat es its 47
int eractions with the en vironment 2–4 . Beneficial bacteria can, f or ex ample, shield the 48
host against pathogens 5 , stimulate algal growth 6 , or mitigate the ad verse effects of 49
environmental pollution 7 . 50
Species of the gr een seaweed Ulva are particularl y w ell-studied and ar e considered a 51
model system t o study algal-bact erial interactions 8 . The r elation between Ulv a an d its 52
symbionts, t ogether often referred to as a holobiont, is so indisp ensable that the 53
seaw eed fails to develop its typical leaf- or tube-lik e morphology in the absence of 54
particular bacteria 9,10 . Morphological de velopment is induced b y chemical compounds 55
produced by bacteria that trigger cell wall de v elopment, rhizoid formation, and cell 56
division 11 . Initial studies id entified a combination of two complementary strains (a 57
Roseo varius and a Maribacter strain) that were necessary for full morphogenesis in Ulva 58
mutabilis . Since then, multiple strains ha ve been identified that ha ve the same capacity 59
12 . This functional r edundancy across taxa is important for the host in relation to shifts 60
in bacterial communities. 61
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Seaweed-associated bacterial communities are f ar from static. Although a small core 62
community can sometimes be identified, the bacteria form a highl y d ynamic community 63
tha t fluctuates through time and space 13,14 . Abiotic f act ors, such as temperatur e, light, 64
and salinity influence the community composition, as does the host itself 15–17 . P rior 65
research has mainly focused on dyn amics in the tax onomic composition of the 66
communities r ather than the functional potential that the community harbours. 67
T axonomic profiling is based on 16S rRNA amplicon sequencing that in recent y ears has 68
become wid el y accessible due to increased speed and reduced costs. Genome-wide 69
studies or metagenomic sequencing that gi ve information on the functional potential of 70
the bact erial communities in comparison are more expensi v e and the sample size in 71
those studies is oft en limit ed. Metagenomic functional profiling in, for e xample, 72
Sargassum spp. 18,19 , P yropia haitanensis 20 , and Nereocystis luetkeana 21 highlighted the 73
importance of the bacterial biofilm in t erms of vitamin production, poly saccharide 74
degr adation, and nutrient cy cling. Howev er , these studies w er e based o n a relati v ely 75
small number of replicat es (between 3–7 samples) and theref ore do not capture 76
differences across en vironments. T o understand how the functional potential of a 77
bacterial community r esponds to en vironmental change and t o ev aluate the potential 78
consequences for the seaw eed host, it is essential to expand functional profiling on a 79
broader scale across di v erse environmental gradients 22 . 80
Ulva species are known for their broad salinity tolerance, thriving in en vironments 81
ranging from fresh w ater habitats t o highly saline conditions. The Baltic Sea is a 82
particularly interesting area to study Ulva , as it hos ts more than 15 species distributed 83
across its distincti ve salinity gradient 23 . This r elati v ely stable gradient stretches across 84
more than 2,000 km of distance, transitioning from near fresh water conditions in the 85
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innermost parts t owards fully marine conditions on the North Sea side 24 . While the 86
distribution of certain Ulva speci es is confined to higher salinity le vels, other species lik e 87
U. int estinalis and U . linza can be found throughout the entire range. Pre vious studies 88
showed that salinity also strongl y structur es the taxonomic composition of Ul va -89
associat ed bacterial communities 25 . The question remains , however , whether these 90
taxonomic shifts in r esponse to salinity ar e reflect ed by corresponding changes in 91
functional profile of the same bacterial communities, or if functional traits are 92
conserv ed across the environmental gradient 26 . 93
T o address these knowledge gaps and enhance our understanding of the Ulva holobiont 94
model s ystem, we investigated the taxonomic and functional composition of Ulva -95
associat ed bacteria across the Balti c–Atlantic salinity gradient using metagenomic 96
sequencing. Th e aim of this stud y w as tw ofold: (i) t o provide a compreh ensi ve ov erview 97
of the functional potential within th e Ulva bacteriome based on a large number of 98
samples (n=91), and (ii ) to assess if the functional potential of the microbial community 99
was stable across an en vironmental gradient. W e expected that the functional repertoire 100
of Ulva-asso ciat ed bacteria would be rich in carbon utilisation and nutrient cycling 101
path way s, as these functions ar e traditionally associated with sea weed microbiomes 102
20,21 . Gi ven that salinity has been identified as a major dri ving force of global bact erial 103
di versity and community structure 27 , we also h ypothesized pronounced ch anges in the 104
functional profile of the Ul va -ass ociated bac ter ial community , partic ularly in functions 105
related to osmopro tection. 106
107
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Results
and discussion 108
Ulva -associ ated bacteria utilize host-deri v ed carbon and sulphur 109
Rich in organ ic carbon, oxygen, and nutrients, the algal surf ace provides an ideal habitat 110
for the growth of microbes 28,29 . The microbial community r eciprocat es by supplying the 111
algal host with phosphate, nitrogen, and vitamins in r eturn 2,30 . Such an exchange of k ey 112
nutrients is an essential f eatur e of the Ulva holobiont. W e used metagenomic sequencing 113
to comprehensi vely describe the functional profile of Ul va -associated bacteria, obtaining 114
a large dataset of metagenome-assembled genomes (MAGs) that were annotat ed with 115
the Car bohydrate-Active EnZ ymes database (CAZy) 31 and K yoto Encyclopedia of Genes 116
and Genomes (KEGG) 32,33 . Across 91 Ulva microbiome samples (T able S1) and 639 117
MAGs (T able S2 ), we identified a total of 6,525 K O (KEGG Orthology) terms and 399 118
KEGG modules (T able S3). MAGs with an estimated completeness of >90% contained on 119
av erage 59 KEGG modules (ranging from 33-94 modules). Apart from basic cellular 120
metabolic pathw ays (e.g., fatty acid biosynthesis, RNA polymerases, DN A polymerases, 121
ribosome, F-type ATP ases, cyt ochro me C oxidase, etc.), the Ul va -as sociated bac ter ial 122
communities contained a range of functions that ar e clearly linked t o the association 123
with its host. This included the wid espread potential of bacteria t o utili ze host-deriv ed 124
carbon and sulphur . 125
All 639 MA Gs were able t o utilize organic carbon as th eir primary energy source 126
through, e.g., complex carbon degradation, gl y colysi s (KEGG modules 127
M00001+M00002), and the tricarboxylic acid (TCA) cy cle (M00009) (Fig. 1a). Likewise, 128
many bact eria were capable of utilizing sulphur compounds produced by the host. 129
Sulphur metabolism r elated gen es in Ulva-associated communities wer e predominantly 130
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invol ved with assimilatory sulphat e reduction (M00176), leading t o the formation of 131
sulphite and, ultimately , sulphide (Fig. 1a). In addition, 137 MAGs were able to oxidize 132
thiosulphate (the r esult of the incomplet e oxidation of sulphides) through sulphur-133
oxidizing prot eins Sox AB and SoxXYZ that together f orm the Sox complex (M00595) (Fig. 134
1a). Due to the presence of sulphate esters in cell w all polysaccharides, Ulva species 135
ha ve a relativ el y h igh sulphur content 34,35 and our findings support the hypothesis that 136
the widespread pre v alence of sulphonates in marine algae contribut es to the high 137
abundance of sulphonate-degr ading bacteria in marine h abitats 36 . 138
Other pre valent sulphur cy cling enzymes in Ulva -as sociated bac ter ia were related to 139
dimethylsulfoniopropionat e (DMSP) metabolism, an organosulphur compound 140
produced by Ulva 37,38 . DMSP has a wide range of ecophy siological functions and in the 141
model species Ulva mutabilis it is known to mediat e the int eraction with the symbiont 142
Roseov ar ius sp. MS2. This symbiont releases morphogenetic compounds that stimulate 143
algal morphogenesis and growth 39 . Interestingly , although the bacterial strain is 144
attracted by the release of DMSP and rapidly takes up the compound, its growth is not 145
affected b y DMSP . Instead, DMSP is conv erted int o dimethylsulphide (DMS) and 146
methanethiol (MeSH). In our dataset, the capacity t o conv ert DMSP to DMS was almost 147
exclusi vely restricted to a few gener a within the Rhizobiaceae (the undescribed genus 148
JAALLB01) and Rhodobacteraceae (predominantly Jannaschia , Ros e ov ari u s , S ulfitobacter , 149
and Ta t e y a m a r i a ). Thi s observ ation aligns with previous find ings that another well-150
known morphogenesis-inducing symbiont of Ulva , Maribacter sp. MS6 (belonging to the 151
Flavobacteriaceae ), is not attracted by DMSP 39 . 152
Apart from examining carbon and sulphur metabolic functions organized in KEGG 153
modules, we also screened the Ul va -associated bacterial MAGs for the presence of 154
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carbohydrate-acti ve enzymes using the CAZ y database. Th e CAZ y database categorizes 155
enzymes invol ved in d egrading, modifying, or creating gl ycosidic bonds into f amilies, 156
including gl y cosid e h ydrolases (GHs) and poly saccharid e l yases (PLs). A total of 121 157
different GH families and 26 differ ent PL families w ere id entified within Ul va -associated 158
MAGs. Our results d emonstrated that a substantial majority [97%] of the bact eria in 159
Ulva -associated communities are capable of breaking down complex polysaccharides 160
constituting the Ulva cell w all. The Ulva cell wall is mainl y composed of cellulose, 161
glucuronan, ulv an, and xyloglucan, which together mak e up 45% of the dry-w eight 162
biomass 40 . Ul van, a key component, is composed of sulph ated rhamnose, xylose, and 163
uronic acids (D-glucuronate and iduronic acid) 40 . The initial steps in the breakdown of 164
ulv an can be catalysed by ulv an l yases (sulfatases) 41 , but additional gl y coside 165
hydrolases ar e needed to obtain monomeric sugars 42 . Ulvan lyases [amongst other s 166
CAZ y family PL24, PL25, and PL37] were found in 146 MAGs (Fig. 1a), man y of which 167
were typical Ulva- a ssoc iat ed b a ct eri a, s uch a s Lewinella , Nonlabens, A lgibacter , 168
Glaciecola , and P olaribacter 12 . Pre v alent glycoside h ydrolase famili es included GH3 [553 169
MAGs], GH16 [305 MAGs], and GH5 [299 MAGs]. F amily GH3 includes, amongst others, 170
xyloglucan-sp ecific exo-β-1,4- glucosidase (EC 3.2.1 .-), xylan β-1,4-xylosidase (EC 171
3.2.1.37) , several glucanases , and several other glucosidases. Enzymes of family GH16 172
are acti ve on β-1,4 or β-1 ,3 gly cosidic bonds in v arious glucans and galactans and 173
includes xyloglu can:xyloglucosyl transferase (EC 2.4.1 .207). Members of the GH5 family 174
are mainl y acti ve on cellulose, but this family also includes high specificity 175
xyloglucanases. 176
177
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Nitrogen metabolism and amino acid biosynthesis 178
Unlik e animals, seaw eeds can synth esise essential amino acid s themsel ves and relati vel y 179
little is known about the uptake of dissol ved organic nitrogen compounds by seaw eed s 180
43 . It is lik ely , howe ver , that seaw eeds and bacteria do e xchange amino acids, especially 181
when dis solved inor ganic nitrogen availab ility is low 44 . The biosynthesis of multiple 182
amino acids w as part of the core modules of the Ulva - assoc iat ed b a ct eri a ( with 0 .6 5-183
1.42% relati ve abundan ce in at least 99% of samples). Thi s in cluded the biosynthesis of 184
proline (KEGG module M00015), threonine (M00018), l ysine (M00016, M00526, 185
M00527), valine/isoleucine (M00019), serine (M00020), cy steine (M00021), 186
tryptophan (M00023), hi stidine (M00026), ornithine (M00028), leucin e (M00432), and 187
arginine (M00844). Of these core m odules, cystein e biosynthesis was d et ected in the 188
fewest number of MAGs (222 MAGs), while histidine biosynthesis was found in the 189
highest number of MAGs (443 MAGs). Lik ewise, genes necessary for gl y cine biosynthesis 190
(from threonine or serin e), alanine biosynthesis (from pyru vate) and glutamine 191
biosynthesis (from glutamate), as w ell as the conv ersion between aspartate and 192
asparagine were pre valent in the majority of the MAGs. 193
Nitrogen metabolism pot ential largely centred on the conv ersion from nitrat e and 194
nitrit e to ammonia (F ig. 1a). A large number of 174 MAGs contained the nr fAH or nirBD 195
genes that ar e essential for nitrite r eduction to ammonia, which is the final st ep in 196
dissimilat ory nitr ate reduction to ammonia. A total of 30 MAGs exhibited the genes for 197
the full dissimilatory nitrat e redu ction to ammonia, utilizing nitrate r espiration for 198
energy production (M00530). Onl y sev en MAGs, all belonging t o the Cy anobact eriia, 199
demonstrat ed complet e assimilat ory nitrate reduction capability , in volving the 200
reduction of nitrate to ammonia for biosynthesis pur poses (M00531). Never theless , the 201
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first step in this process (nitrat e t o nitrite reduction mediat ed by the narB gene) was 202
identified in 53 MAGs, and the subsequent st ep (nitrite to ammonia reduction facilitated 203
by the nir A gen e) w as detected in 4 5 MAGs. The narB gene was predominantly observ ed 204
in Flavobact eriaceae and Saprospiraceae , while the nirA gene w as pre valent in 205
Akkermansiaceae and Pirellulaceae . T wo MAGs harboured all the genes necessary for the 206
denitrification process in volving the reduction of nitrate and nitrite t o nitrogen 207
(M00529), while none of the MAGs carried genes associat ed with nitrification (the 208
oxidation of ammonia to nitrate; M00528). Finally , t en MAGs from div erse families 209
showed the capacity to fix nitrogen (M00175). 210
Previous studies demonstrat ed that observ ed amino acid uptake rates in Ulva w er e 211
highest f or gl ycine and alanine and that while Ulva prefers inorganic nitrogen, the 212
organic c ompounds may als o play a significant role 45,46 . A transcriptomic stud y in 213
Laurencia dendroidea show ed that t he associated bact eria had a higher relativ e 214
contribution to amino acid metabolism than the host itself, indicating a symbiotic 215
relation 47 . Similarly , in P yropia haitanen sis , co- culti vation with a Bac illus sp. did not only 216
Result
in an increased growth rate, but also in a downregulation of genes relat ed to the 217
biosynthesis of sev er al amino acids and other metabolit es 48 . As free amino acids are 218
known to increase primary production of algae 49,50 , it is h ypothesised that the release of 219
amino acids by bact eria serv es as one mechanism through w hich they may facilitate 220
algal growth. 221
222
223
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224
Fig. 1 | Fu n ct ion al p r ofil e of the Ulva mic r obiome . ( a ) O v er v i ew o f th e m et abolic p ot ent ial of th e Ulva 225
micr ob io m e , h i ghli g h ti n g vit a mi n pr oduct i o n (p urple) , algal cell wa ll d egr ad ati on (gr e e n ) , a nd th e 226
m e t ab oli sm of car bo n (blu e ) , nitr og en (or a n g e) , an d sulph u r ( yello w ) . Th e nu mber of ide nti fi ed 227
m e t ag en o mic as se m bl e d ge n omes ( MAGs ) that ar e cap abl e p erfor m i ng t he r e a c ti ons a re di splay e d i n 228
br ackets . (b) Th e pr opor ti o n o f t he n um b er o f s e a wat er -is o l at ed (blu e) o r Ulva-i s o la te d ( g ree n ) ba c te r ia l 229
gen o m e s t ha n co nt ain e d a sp ecif ic CA Z Y f amil y ( p ol y sacc h a r ide l yas es = P L , glyc os id e h y dr o l as es = GH). 230
231
Large potential for vitamin B production by bacteria 232
Previous metagenomic studies in the red alga P yropia haitanensis 20 and brown alga 233
Nereocystis luetkeana 21 ha ve highlighted the potential of the bact erial symbionts to 234
produce vitamin B 12 (cobalamin). Our data show ed that the capacity of seaw eed-235
associat ed bacteria to biosynthesize vitamins is widespread within the Ul va microbiome 236
and extends beyond vitamin B 12 (Fig. 1a). Vitamins are essential to a w ell-functioning 237
central metabolism in both microbes and their hosts 51,52 . Algae require a combination of 238
different vitamins f or growth, but are lik el y unable to synthesise some of these organic 239
compounds themsel ves 53–55 . A stud y b y Croft et al. 56 , f or example, showed that more 240
than half of the algae studied by them required an exogenous suppl y of vitamin B 12 241
(cobalamin), 22% required vitamin B 1 ( thiamine) , and 5% required vitamin B 7 (biotin). 242
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In Ulva speci es, the addition of vitamin B 12 and particularly vitamin B 6 (p yridoxal) to 243
culture medium is necessary for growth and promot es nitrogen metabolism 57,58 . This 244
vitamin auxotroph y suggests that the host is dependent on the production by its 245
microbial symbionts. Within ou r dataset, the cap acity of bacteria to produce 246
tetrahydrofolate ( a derivative of vitamin B 9 ; KEGG module M00126) w as most 247
widespr ead and was identified in 1 10 MAGs from varying families, including the 248
Alteromonadaceae , Flavobacteriaceae , Granulosicoccac eae , Saprospiraceae , and 249
Spirosomaceae (Fig. 1a). This vitamin was the only vitamin that w as part of the core 250
functions of the Ulva microbiome, being consistently pr esent in all samples with a 251
minimum relati v e abundance of 0.1%. KEGG modules relat ed to the production of 252
vitamin B 1 ( thiamine; M00127) , vitamin B 2 (riboflavin; M00125), vitamin B 5 253
(pantothenate; M00119), vitamin B 6 (pyridoxal; M00124), vitamin B 7 (biotin; M00123), 254
and vitamin B 12 (cobalamin; M00122) w er e identified as w ell (F ig. 1a), although not as 255
core functions. This could be attribut ed to either the absence of MAGs with the capacity 256
to produce these vitamins in all samples or their pr esen ce in samples but not with high 257
abundance. 258
259
The Ulva microbiome is defined b y its ability t o degrade the host 260
Our metagenomic d ataset provided a thorough o verview of the functional profile of the 261
Ulva -associated microbiome. Next, we aimed to det ermine the functions contributing to 262
a "typical" Ulva microbiome, by contrasting taxa isolat ed from Ul va with those isolated 263
from sea water . In t otal, we selected 152 MAGs from our metagenomic dataset, 264
representing 33 different genera (T able S4). W e then searched for publicly a v ailable 265
genomes of bact eria from the same genera but isolated from sea water (71 genomes) 266
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(T able S4). Subsequently , w e conducted a comparativ e analy sis based on odds ratios to 267
identify pot ential enrichments of specific KEGG Orthology (K O) terms or Carboh ydr ate-268
Acti ve enZ ymes (CAZ ys) in bacteria from the same genus collected from Ulva ver sus 269
sea water . 270
Our results suggest that a def ining aspect of an Ulva microbiome is its ability to utilize 271
and break down the host organism, shown by the significant enrichmen t of CAZ ys (incl. 272
ulv an l yases, α-L-rhamnosidases, and rhamnogalacturonan α-L-rhamnoh ydrolase) that 273
specificall y target and break down Ulva’s polysaccharides and cell wall components 274
(e.g., ul van, iduronic acid, cellulose, xyloglucan) (Fig. 1b), as well as ABC transport ers 275
that facilitat e the extracellular uptake of small monosaccharides lik e fructose ( frcBCA ; 276
KEGG K O K10552, K10553 & K10554), α-glu coside ( aglEFGK ; K10232, K10233 & 277
K10234), and rhamnose ( rha SPQ T ; K1055 9 & K10560) r esulting from the degr adation 278
of the cell w all polysaccharides. It is clear that Ul va -associated bacteria do not only live 279
on the algal tissue, they li ve of i t a s w ell . 280
281
High tax onomic turnov er and fun ctional stability across salinity gradient 282
Subsequently , we examin ed the shifts in both the taxonomic and functional composition 283
of Ulva-asso ciat ed bacteria across a salinity gradient tra versing four distinct salinity 284
regions: sp anning from the horohalinicum (5–8 PSU), through the mesohaline (8–18 285
PSU) and the polyhaline (18 –30 PSU), to the euhaline (30–35 PSU) (Fig. 2a). The 286
Atlantic–Baltic salinity gradient exp lained more of the observ ed variation in the 287
taxonomic composition of Ul va -associated bacterial communities (p = 0.0001 , R 2 = 0.70) 288
than of the observed v ariation in the functional composition of the same communities (p 289
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= 0.0006, R 2 = 0.17) (Fig. 2b, 2c). Pairwise comparisons, for example, showed that the 290
taxonomic composition of Ulva -associated bacteri a d iffer ed between all salinity regions 291
(horohalinicum vs mesohaline vs polyhaline vs euhaline, p<0.01 for all comparisons; 292
pairwise Adonis t est). On the other hand, the functional gene profile of bact erial 293
communities in the mesohaline, pol yhaline, and euhaline w ere not significantly different 294
from each other (p>0.05 f or all comparisons, pairwise Adonis t est), as only the 295
horohalinicum differed from the two high er salinity regions (horohalinicum vs 296
polyhaline, p=0.04; horohalinicum vs euhaline, p=0.04, pairwise Adonis test). 297
Nutrient concentrations, temperatu re and oxygen concentrations had little to no eff ect 298
on taxonomic turnov er (NO x , p = 0.04, R 2 =0.07; PO 4 , p = 0.08, R 2 =0.05; temperatu re, p = 299
0.01, R 2 =0.10; oxygen, p = 0.19, R 2 =0.04) and did not affect functional composition (NO x , 300
p = 0.90 , R 2 =0.002; PO 4 , p = 0.22, R 2 =0.03; temperature, p = 0.15, R 2 =0.04; oxygen, p = 301
0.84, R 2 =0.004). 302
Indicati ve of a high taxonomic turnover , 294 MAGs changed in relativ e abundance across 303
the salinity grad ient (p<0.01, LinDA linear regression) (F ig. 3a) (T able S2), of which 126 304
MAGs decreased with s alinity and 168 MAGs increased with salinity . Several MAGs 305
belonging to Dokdonia [MAG082, MAG518], Leucot hrix [MAG022, MAG360], and 306
Litor imonas [MAG193, MAG149] for example incr eased with salinity , while 307
Alteraurantiacibacter [MAG014, MAG020, MAG578], R ubripirellula [MAG422], and 308
Blastomonas [MAG197] decreased with salinity (Fig. 3b). 309
The taxonomic turnover was larger than the observed functional change, implying that 310
multiple taxa across the salinity gradient were able to perform similar functions. F ig. 4 311
gi ves a complete overview of the pr esence or absence of KEGG modules in the 312
metagenomic assembled genomes of 26 taxa that are characteristic to a specific salinity 313
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15
region ( horohalinicum 5–8 PSU, mesohaline 8–18 PSU , polyhaline 18–30 PSU, or 314
euhaline 30–36 PSU). P antothenate (vitamin B 5 ), for example, can be produced at low to 315
medium salinity (5–18 PSU) by an unknown Saprospirac eae (MAG591), but at medium 316
to high salinity (18–36 PSU) this function in the community was taken over b y 317
Robiginitomaculum and another unknown Saprospiraceae (MAG149) (Fig. 4). Similarly , 318
proline biosynthesis at low salinity can be conducted by Alteraurantiac ibac ter and 319
Rubripir ellula (5–8 PSU), at medium salinity by Litorimonas A (8–18 PSU), and w as 320
gradually taken over by Neomegalonema (18–30 PSU), and Le ucothr ix and Litorimonas 321
at high salinity (30–36 PSU). In addition, most MAGs shared a set of cor e genes that ar e 322
necessary for essential functions, in cluding nu cleotide metabolism, fatty acid 323
biosynthesis, energy metabolism (F-type ATPases, succinate deh ydrogenases, et c.), and 324
genes encoding structural modules (e.g., ribosomes, RNA polymerase, and DNA 325
polymerase) (Fig. 4). 326
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327
Fig. 2 | T axon om i c and fun cti onal patt e r ns a c r oss s al in ity. (a) Ge ogra phic d istri bu tio n of s ampl i n g 328
sit es ( n=63) al o n g t he Atl a n t ic –Ba l tic S e a g rad ie nt w h er e a t ot al of 9 1 Ulva sensu lato sa mples w e r e 329
c o l l e c t e d . T h e f o u r m aj o r s al i n i t y r e g i o n s ( h o r o h al i n i c u m , m e s o h a l i n e , p o l yh a l i n e , a n d eu h a l i n e ) h a v e 330
b e e n i n dic a t ed on t h e m ap a nd r i vers a r e p roj e c ted i n blue . P CA pl ots sh o w th e t axo nom ic (b ) a n d 331
fu nctio n al (c) co mpo s it ion o f Ulva -a ss o ci ate d ba c te ri a l communi t ie s a cr o s s s a lin i ty. Th e o r d ina ti o n in t h e 332
ta xo no m i c co mpo s it ion is M AG- b as ed (m et age n o me- ass em bled ge no m e ) a n d th e func tio nal co mpo s it ion 333
i s K O- ba se d ( K E G G O r t ho l og ie s ) . T he co n t ou r line s ( smo o th su r fa c e line s ) we r e fi t te d to t he o rd ina ti on 334
p l o t s b a se d o n t h e c o r re l a t i o n w i t h sa l i n i t y . C o l o u r r e p re se n t s s a l i n i t y i n a l l p l o t s. 335
336
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337
Fig. 3 | Abundance of metagenome-assembled genomes across salinity. (a) P h y lo g en et ic tr ee o f t h e 294 338
me ta ge nome - a ssem b le d gen o me s ( MA G s ) th at s ign i fi c ant l y di f fe r e d ( p <0 . 0 1 ) in r e la tive a b und an c e 339
acros s t he s a l i nit y gr adi en t. Th e out e r ri n g repr es e nts t h e l og 2F old Ch an g e (Li nD A li n ear r egr ess i o n 340
model) , wit h th e M AGs i n yello w-gr e en t ha t a r e e n r ich ed i n l ow s al i n i t y a n d t h e MA Gs th at a r e e nrich ed i n 341
high s ali n it y i n pu r ple- blu e . Th e c o l ours i n the p h yl o ge n et i c t r e e re p re sent th e ba cte ria l p hy la ( t he l eg en d 342
is ord er ed i n cloc kwis e or der of a pp e a r anc e ) . (b) Rea d a bun dan c e o f t he 2 8 m o s t di f fe r e n ti a l ly ab un dan t 343
MAGs acros s s al i nit y. Th e x- ax is d ispl a y s s a li n it y (P S U ) and t he y - axi s CL R-t ra n sfor m ed r ead a bu n danc e. 344
Col o ur s r epr es e nt s a li n it y . Cur v es wer e fit t ed wi th a g en er aliz ed l i ne a r mo d e l (GL M) usi n g th e R p acka ge 345
ggplot2 . Sh a d e d ar e as r epr es e nt t he 0 . 95 c o nfid enc e i nt e r val . 346
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347
Fig . 4 | T ax on om i c tur no v er a nd fu n ctio nal stab ility . H e at m a p d e pic t ing t he pr es e nce (d a r k-g r ee n) or 348
abs enc e (li ght - blu e ) of KEGG mod ules i n 2 6 m et age n ome - ass e mbl e d ge no mes ( MA Gs ) th a t ar e 349
char act eris tic t o a sp ecif ic s ali ni t y r e g i o n (hor o h al i n icum 5– 8 P S U , meso h alin e 8 – 1 8 PS U , po l y h a l i n e 18 –350
30 PSU , or eu h a li n e 30 – 35 P SU). 351
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Osm oregulation drives functional var iation 352
Despite low er functional turnover , we also identified 23 KEGG modules that differed in 353
abundance across the salinity en vir onment (p<0.05, LinDA linear regr ession) (F ig. 5). 354
These modules are lik ely in volv ed in the osmoregulation of bacterial cells, but may also 355
affect the osmoregulation and acclimation potential of the host. One of the best-known 356
strategies in bacteria and eukaryotes alike is the accumulation of low molecular w eight 357
compounds, su ch as sugars and amino acids, that act as osmoprotectants t o maintain 358
osmotic homeostasis and turgor pressure. Oth er strategies included the stabilization of 359
cell membranes and mitigating oxidativ e stress. 360
Salinity-induced osmotic changes trigger the o verproduction of r eacti ve oxygen species 361
(ROS), causing oxidati ve stress 59 and damaging membrane lipids, proteins, nu cleic 362
acids, and chloroplasts 60 . Bact eria t hat were abundant in high salinity areas more often 363
contained the genes needed t o produce factor F 420 (KEGG module M00378, p=0.0004), 364
thiamine (vitamin B 1 ; KEGG module M00127, p<0 .0001) and p yridoxal-5P (the acti ve 365
form of B 6 ; M00124, p=0.001). Se veral antioxidant mech anisms ar e F 420 -dependent 61 366
and cofactor F 420 is known to help bact eria combat oxidati ve str ess 62 . In t errestrial 367
plants, both vitamin B 1 and B 6 are known to alleviat e salinity stress, for example in 368
Arabidopsis t haliana 63 and in milk thistle 64 , due to the stimulation of antioxidant 369
enzyme activity and proline cont ent . Similarly , gene exp ression of vitamin B 1 is 370
upregulated in phytoplankton during salt str ess and oxid ati ve stress is t hought to 371
function as a stress signalling molecule 65,66 . In addition to pro tection from oxidative 372
stress, pyridoxal-5P also incr eases photosynthetic pigment in wheat 67 , and it facilitates 373
growth through the reduction of eth ylene accumulation that usually occurs under 374
salinity stress in rice 68 . As algae are likely not always able to produce their own 375
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vitamins 53 , it is possible that thiamine and p yrodixal-5P produced by bacteri a also aid 376
the Ulva cells against oxidativ e rad icals that are more pre valent under high salinity 377
levels. 378
Bacteria that were abundant at high salinity also more oft en contained the genes needed 379
to produce betaine (M00555, p = 0.03), an osmolyte that acts as one of the pref err ed 380
compatible solutes in the majority of prokaryotes 69,70 . It is known to accumulat e in 381
bacterial cells with incr easing salinity 71 , and betaine transport ers are enriched in 382
bacterial communities originating from marine habitats compared to fr esh water 383
environments 72 . Although betaine plays a more important role in higher plants than in 384
algae as osmoprotectant 73 , a transcript omic study show ed that three choline 385
deh ydrogenase genes (in vol ved in the conv ersion from choline to betaine) w ere 386
upregulated in Ulva compr essa during a reco very period after hyposaline stress 74 . W e 387
also found an enri chment at high salinity of bact erial genes necessary for the produ ction 388
of the es sential amino acid phenylalanine, which is known to accumulate in plants and 389
algae under high salinity conditions 75,76 and increases salinity tolerance in maize 77 . 390
Genes associated with other well-known osmolytes and osmoprot ectants, such as 391
ectoine and tr ehalose, were compar ativ el y less pre valent in our d ataset. How ever , it is 392
important to k eep in mind that these findings are solel y deriv ed from gene cont ent 393
analyses and do not reflect gene expression patterns. Future transcriptomic studies 394
could shed more light on the up- or downregulation of specific genes b y Ulva and its 395
associat ed bacteria in response to changing salinity conditions. 396
Another w ell-known strategy of bacteria to cope with cell turgor pressu re is to alter the 397
membrane composition through changes in fatty acids or phospholipid s 78 . The cell 398
membrane separates the cell’s interior from the external en vironment and is therefor e 399
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the first structure to encounter the effects of fluctuating salinity and osmotic stress. The 400
disruption of membranes aff ects man y processes such as transport of compounds, 401
enzyme activities and si gnal transduction. It is therefore important t o maintain the 402
correct fluidity of the lipid bila yer 79 . W e found that many typ ical h igh-salinity MAGs 403
wer e associated with the ability to synthesize ubiquinone (M00117, p= 0.02), wh ich 404
agrees with the findings by Dupont et al. 72 on pelagic bact erial communities. 405
Ubiquinone (also called coenzyme Q) is a membrane-stabilizing isopr enoid and the 406
accumulation of this compound increases salt t olerance in bact eria, especiall y in the 407
thin-walled gr am-negativ e bacteria 80,81 . Ubiquinone alters the phy sicochemical 408
properties of the membrane by incr easing the lipid packing and density . This results in 409
reduced membrane permeability (i.e., a slower r elease of small solutes) and in cr eases 410
the strength of the membrane (i.e., resistance to cell rupture) 82 . Con versely , we found 411
that the module for phosphatid ylcholine biosynthesis was enriched in low salinity 412
conditions (M00091, p=0.002). Phosphatidylcholin e (PC) is a membrane-forming 413
phospholipid that is synthesized from Phosphatid yl ethanolamine (PE) and studies 414
found that PE levels increased in salt-adapted cells 83 . It has been not ed before that 415
while PE is the more common phospholipid in bacteria, gram-negativ e bacteria with 416
high proportions of unsatu rated fatty acids often contain add itional PC to maintain 417
stable bilayers 84 . Indeed, in our dataset, th e ability to con vert PE to PC w as mainl y 418
found in low salinity enrich ed Sphingomonadales (e.g., Alteraurantiacibacter , 419
Erythrobacter ) and Rhodobact erales (e.g., Jannaschia, Pseudorhodobact er ). Membranes 420
lacking PC are more fluid, hav e a higher permeability for small molecules and ar e more 421
sensitiv e to osmotic ch anges 85 . Both quinone and phosphatid ylcholine seem to stabilize 422
the membrane to withstand changes in tu rgor pressur e and maintain osmotic balance. 423
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Bacteria-mediat ed acclimation 424
Our char acterization of the metabolic functions of a typical Ul va -microbiome, highlig hts 425
the large metabolic potential inherent to bacterial-algal symbiosis. The holobiont 426
concept, whi ch r egard s the seaw eed host and its associat ed microbes as an int egr ated 427
functional unit, is essential w hen studying the physiological response of sea weeds to 428
environmental change. This work demonstrat ed that both the taxonomic and functional 429
composition of Ulva-associated bacterial communities change across a 2,000 km salinity 430
gradient. While Ulva -associat ed bacterial taxa displa yed high taxonomic turnover across 431
salinity , se veral Ulva species were able to colonize the entire gr adient. This indicates 432
that Ul va -bacter ia have a smaller salinity-bas ed niche than the host and are les s tolerant 433
to changes in salinity conditions (i.e. limit ed acclimation potential). The high turnover of 434
microbial taxa is accompanied b y functional redundancy , wh ere guilds of taxa along the 435
entire environmental gr adient can perform crucial functions. These functions, includ ing 436
amino acid and vitamin B production, are pot entially important to the seaw eed host. 437
Alongside functional r edundan cy , w e identified distinct functional modules exhibiting 438
enrichment in either low or high salinity areas. These modules ar e likel y in vol ved in 439
mitigating oxidativ e stress, maintai ning cellular osmotic homeostasis, and stabilizing 440
cell membranes. Ulva depends on its microbiome for morphological de velopment and 441
growth — lik ewise, the forementioned bact erial acclimation mechanisms may play a 442
role in host metabolism and acclimation. In light of bacteria-mediated acclimation, 443
future laborator y experiments — involving the inoculation of s eaweed cultures with 444
targeted microbial communities — will be necessary to inv estigate whether bact eria can 445
indeed facilitate the acclimation of Ulva species to changes in salinity . 446
447
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448
Fig . 5 | F u n ct ion al c h ang es i n the Ulva -a ss o ci a t e d ba c t er ial c om mun itie s a c r o s s s ali nit y . (a ) 449
log 2 F oldCh a n ge v al ues ( ± s t and ar d e r r or) of th e KEGG m o d ules t h a t s i gni fic a ntl y (p< 0.05 ) d iff er e d i n 450
a b un dan c e wi t h sa l i ni ty . (b ) T a x o no m ic co mpos it io n (or d er l e v el) of th e me t age no me -a ss e m bl e d 451
gen o m e s ( M A G s) t h at h ar bour ed t h e id e nt i fi e d KEGG m o dul es . Th e r el a ti v e a b u nd a nce is b as ed on r e ad 452
coun ts of th e or d ers acr o s s th e e n tir e dat as et. 453
454
Methods
455
Sample collection 456
Samples of Ulva sensu lato individuals (n=91) w ere collected during June–August 2020 457
in the Baltic Sea area (T able S1). Of each indi vidual, a tissue sample w as collected t o 458
molecularly identify the host species and a sw ab sample for microbiome an alyses was 459
gener ated by rubbing f or 30 s on the tissue. Sterilized disposable glov es and st erilized 460
equipment wer e used throughout the sampling procedure to minimize contamination. 461
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All samples w er e stored in a portable fr eezer (-20 °C) until transferred to -80 °C in the 462
laboratory . 463
In total, 63 sampling sites w er e visited along a salinity gradi ent in the Baltic Sea and 464
adjacent areas such as the Kattegat, Skagerrak, and the east ern North Sea (Fig. 1a). Th e 465
salinity r anged from 5.1 to 34.3 PSU and is pr esented in the figur es in this study either 466
on a continuous scale (0–35 PSU) or in salinity zones defined according to the V enice 467
classification sy st em (5–8 = horohalinicum, 8–18 = mesohaline, 18–30 = polyhaline, and 468
30–35 = euhaline) 86 . In addition, w ater temperature (°C), oxygen le vels (mg L -1 ), and 469
nutrients concentrations (NO 3 - , NO 2 - , silicate, PO 4 3- in µmol L -1 ) were measured at eac h 470
site (T able S1). 471
Molecular identification, based on the tuf A marker , confirmed the samples in our dataset 472
represented sev en different species: Blidingia minima (Nägeli ex Kützing) K ylin (n=8), 473
Ulva compr essa Linnae us (n=10) , Ulva fenestrata Postels & Rup recht (n=8), Ul va 474
int estinalis Linnaeus ( n=29), Ulva lacinulata (Kützing) Wittrock (n=10), Ulv a linza 475
Linnaeus (n=20), and Ulva torta (Mert ens) T revisan (n=6) [see v an der Loos et al. 25 and 476
Steinhagen et al. 23 for detailed molecular methods and additional r esults concerning 477
Ulva d i versity in the Baltic r egion]. Throughout this stud y , “ Ulva ” r ef er s t o Ulva sensu 478
lato (including Blidingia ). 479
480
DNA extraction and metagenomic sequencing 481
T otal microbial DNA of the sw ab samples w as extracted with the Qiagen DNeasy mini kit 482
following the manufactur er’s protocol, with the addition of a bead beating step before 483
lysis using zirconium oxide beads (RETCH Mixer mill MM400; 5 minutes at 30 Hz). 484
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Quantity and quality of the DNA extracts were v erified with Qubit (Lif e T echnologies, 485
Grand Island, USA) and NanoDrop (Thermo Scientific, Wilmington, USA). DNA extracts 486
wer e sent to Novogene (Cambridge, United Kingdom) for libr ary pr epar ation and 487
metagenomic sequencing on an Illumina No vaSeq 6000 (150 bp paired-end). A neg ativ e 488
DNA extraction control and a positi ve control (A T CC microbial standard MSA-1002) 489
wer e included. A t otal of 4,297,091,260 reads were generated (35,622,356–78,544,930 490
reads per sample). The sequences are archiv ed at SRA (BioProject PRJNA1040445). 491
492
Bioinformatics and statistical anal yses 493
The metagenomic sequen cing data was processed with the ATLA S Snakemake workflow 494
87 , which integrates quality control, assembly , genomic binning, and annotation. In short, 495
quality control w as perf ormed using the B BT ools suite 88 . This includes removal of PCR 496
duplicates and adapters, trimming and filtering of r eads based on qualit y and length, 497
and compressing the raw data files. Host sequences were remov ed based on an a v ailable 498
Ulva r efer ence genome (B ioProject PR JEB25750) 89 . The de novo metagenome assembly 499
was done using MEGAHIT v1.0 90 . Next, metagenome-assembled genomes (MAGs) were 500
predicted with binning tools MetaBAT 2 91 and MaxBin 2.0 92 . Binning results w er e 501
aggregat ed with D AS T ool 93 . Quality assessment of the r esulting MAGs was performed 502
with CheckM 94 . MAGs were der eplicated across samples with dR ep 95 , and taxonomic 503
classification was performed with G TDB-Tk 96 . Finally , genes w er e predicted with 504
Prodigal 97 , red undant genes w ere clustered with lin clust 98 , and annotat ed with 505
eggNOG-mapper 99 . This resulted in a classification of the genes following the 506
Carbohydrate-Activ e EnZ ymes database (CAZ y) 31 and K yoto Encyclopedia of Genes and 507
Genomes (KEGG) 32,33 databases. 508
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The effect of salinity , NO x , and PO 4 on bacterial community composition at both MAG 509
(taxonomic profile) and K O (KEGG Orthology; functional p rofile) le vels was assessed 510
using the en vfit function from the v egan package with 9999 permutations 100 . 511
Multivari ate comparisons with 9999 permutations w er e subsequently conduct ed with 512
pairwise Adonis among the d iffer ent salinity zones 101 . Functional differ ences across 513
salinity w ere visualised with a PCA and smooth surface lines were fitted to the 514
ordination with the ordisurf function (v egan package) based on the correlation with 515
salinity 100 . A LinD A linear regression was used to identify which MAGs and which KEGG 516
modules (a set of genes with a specific reaction within a metabolic p athwa y) 517
significantly changed across salinity and nutrient concentrations 102 . P-values were 518
Benjamini & Hochberg corr ect ed. Gi ven the compositional natur e of the data, r ead 519
abundance v alues w er e tr ansformed with the centric log-ratios (CLR) prior t o the 520
analyses 103 . 521
T o gain a deeper understanding of what defines the metabolic potential of Ulva 522
microbiomes, we compared the genomes of bacterial taxa isolated from Ulva to those 523
isolated from seaw ater . In total, we selected 152 MAGs from our metagenomic dataset, 524
representing 33 different genera. W e then searched for publicl y available genomes of 525
bacteria from the same genera that wer e isolated from sea w ater (resulting in a set of 71 526
genomes) (T able S4 ). These originated from a v ariety of geographical locations and 527
habitats (e.g., surface w ater , deep sea, hydrothermal sy st ems, and oceanic gyr es). 528
Subsequently , we conducted a comparativ e analy sis based on odds ratios t o identify 529
pot ential enrichments of specific K O t erms or CAZ y f amilies within bacteria of the same 530
genus collected from Ulva versus seawat er . F or each K O term and CAZ y family , the odds 531
ratio was calculat ed as the number of discordant genome pairs in f avour of the Ulva 532
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27
(ter m/family present in the Ulva bacterial genome, but not present in the sea water 533
bacterial genome) di vided by the number of discordant pairs in f avour of sea water 534
(term/family present in the sea wat er bacterial genome, but not present in the Ul va 535
bacterial genome). An offset of 0.5 was added to the number of discordant pairs to 536
prev ent dividing by zero. As multiple genomes were a vailable per genus, pairs were 537
randomly assigned 1000 times (permutations) and odds ratios w ere calculated for each 538
permutation. The median odds ratio was r etained. A t erm/family more frequent in Ulva 539
bacterial genomes results in an odds r atio larger than one. The opposite results in an 540
odds ratio smaller than one. 541
All statistical tests were performed in R 104 and data wer e visualised using the ggplot2 542
105 and phyloseq 106 packages. 543
544
Data availability statement 545
Raw whole-genome sequ ence r eads and r elated metadata are deposited in the SRA 546
(BioProject PR JNA1040445). 547
548
Acknowledgements
549
The research leading t o the results present ed in this publication w as carried out with 550
infrastructur e funded by the FW O P hD F ellowsh ip fundamental r esearch (3F020119), 551
the EMBR C Belgium (F WO project I001621N), and the F ormas-funded ‘ A manual for the 552
use of sustainable marine resources’ project (Grant no. 2022-00331). W e would like to 553
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28
thank Samanta Hoffmann for her assistan ce during field work and Nadja Stär ck f or 554
assistance with nutri ent analy ses. WS is funded through the FW O grant nr 1252821N. 555
556
Author contributions 557
L.M.L .: Conceptualization, Methodology , F ormal analy sis, Data Cu ration, Writing - 558
Original Draft, V isu alization. S.ST .: Investigation, W riting, F unding acquisition - Re view 559
& Editing. W. S . : Resources, W riting - R eview & Editing. F. W . : W riting - R e view & Editing. 560
S.D.: Methodology , R esources, Writing - Review & Editing. A.W .: W riting - Review & 561
Editing, Supervision. O .D.C.: Writin g - Review & Editing, Supervision, F unding 562
acquisition. 563
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29
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