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Impact of process temperature and organic loading rate on cellulolytic/hydrolytic biofilm microbiomes during biomethanation of ryegrass silage revealed by genome-centered metagenomics and metatranscriptomics

Maus, Irena,Klocke, Michael,Derenkó, Jaqueline,Stolze, Yvonne,Beckstette, Michael,Jost, Carsten,Wibberg, Daniel,Blom, Jochen,Henke, Christian,Willenbücher, Katharina,Rumming, Madis,Rademacher, Antje,Pühler, Alfred,Sczyrba, Alexander,Schlüter, Andreas

Abstract

Background: Anaerobic digestion (AD) of protein-rich grass silage was performed in experimental two-stage twophase biogas reactor systems at low vs. increased organic loading rates (OLRs) under mesophilic (37 °C) and thermophilic (55 °C) temperatures. To follow the adaptive response of the biomass-attached cellulolytic/hydrolytic biofilms at increasing ammonium/ammonia contents, genome-centered metagenomics and transcriptional profiling based on metagenome assembled genomes (MAGs) were conducted. Results: In total, 78 bacterial and archaeal MAGs representing the most abundant members of the communities, and featuring defined quality criteria were selected and characterized in detail. Determination of MAG abundances under the tested conditions by mapping of the obtained metagenome sequence reads to the MAGs revealed that MAG abundance profiles were mainly shaped by the temperature but also by the OLR. However, the OLR effect was more pronounced for the mesophilic systems as compared to the thermophilic ones. In contrast, metatranscriptome mapping to MAGs subsequently normalized to MAG abundances showed that under thermophilic conditions, MAGs respond to increased OLRs by shifting their transcriptional activities mainly without adjusting their proliferation rates. This is a clear difference compared to the behavior of the microbiome under mesophilic conditions. Here, the response to increased OLRs involved adjusting of proliferation rates and corresponding transcriptional activities. The analysis led to the identification of MAGs positively responding to increased OLRs. The most outstanding MAGs in this regard, obviously well adapted to higher OLRs and/or associated conditions, were assigned to the order Clostridiales (Acetivibrio sp.) for the mesophilic biofilm and the orders Bacteroidales (Prevotella sp. and an unknown species), Lachnospirales (Herbinix sp. and Kineothrix sp.) and Clostridiales (Clostridium sp.) for the thermophilic biofilm. Genome-based metabolic reconstruction and transcriptional profiling revealed that positively responding MAGs mainly are involved in hydrolysis of grass silage, acidogenesis and / or acetogenesis. Conclusions: An integrated -omics approach enabled the identification of new AD biofilm keystone species featuring outstanding performance under stress conditions such as increased OLRs. Genome-based knowledge on the metabolic potential and transcriptional activity of responsive microbiome members will contribute to the development of improved microbiological AD management strategies for biomethanation of renewable biomass. Keywords: Metagenome assembled genomes, Integrated -omics, Polyomics, Anaerobic digestion, Biogas, Bioconversion, Microbial community structure, Methane, Metabolic activity

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RESEARCH ARTICLE Open Access Impac o p ocess empe a u e and o ganic loading a e on celluloly ic / hyd oly ic bio ilm mic obiomes du ing biome hana ion o yeg ass silage e ealed by genome-cen e ed me agenomics and me a ansc ip omics I ena Maus 1† , Michael Klocke 2† , Jaqueline De enkó 2 , Y onne S olze 1 , Michael Becks e e 3 , Ca s en Jos 2 , Daniel Wibbe g 1 , Jochen Blom 4 , Ch is ian Henke 5 , Ka ha ina Willenbüche 2 , Madis Rumming 5 , An je Rademache 2 , Al ed Pühle 1 , Alexande Sczy ba 1,5† and And eas Schlü e 1*† Abs ac Backg ound: Anae obic diges ion (AD) o p o ein- ich g ass silage was pe o med in expe imen al wo-s age wo- phase biogas eac o sys ems a low s. inc eased o ganic loading a es (OLRs) unde mesophilic (37 °C) and he mophilic (55 °C) empe a u es. To ollow he adap i e esponse o he biomass-a ached celluloly ic/hyd oly ic bio ilms a inc easing ammonium/ammonia con en s, genome-cen e ed me agenomics and ansc ip ional p o iling based on me agenome assembled genomes (MAGs) we e conduc ed. (Con inued on nex page) © The Au ho (s). 2020 Open Access This a icle is dis ibu ed unde he e ms o he C ea i e Commons A ibu ion 4.0 In e na ional License (h p://c ea i ecommons.o g/licenses/by/4.0/), which pe mi s un es ic ed use, dis ibu ion, and ep oduc ion in any medium, p o ided you gi e app op ia e c edi o he o iginal au ho (s) and he sou ce, p o ide a link o he C ea i e Commons license, and indica e i changes we e made. The C ea i e Commons Public Domain Dedica ion wai e (h p://c ea i ecommons.o g/publicdomain/ze o/1.0/) applies o he da a made a ailable in his a icle, unless o he wise s a ed. * Co espondence: aschlue @cebi ec.uni-biele eld.de † I.M. and M.K. con ibu ed equally o his wo k. † A.Scz. and A.Schl. con ibu ed equally o his wo k. 1 Biele eld Uni e si y, Cen e o Bio echnology (CeBiTec), Genome Resea ch o Indus ial Mic oo ganisms, Uni e si ä ss . 27, 33615 Biele eld, Ge many Full lis o au ho in o ma ion is a ailable a he end o he a icle En i o nm e n a l Mi c ob i o m e Maus e al. En i onmen al Mic obiome (2020) 15:7 h ps://doi.o g/10.1186/s40793-020-00354-x (Con inued om p e ious page) Resul s: In o al, 78 bac e ial and a chaeal MAGs ep esen ing he mos abundan membe s o he communi ies, and ea u ing de ined quali y c i e ia we e selec ed and cha ac e ized in de ail. De e mina ion o MAG abundances unde he es ed condi ions by mapping o he ob ained me agenome sequence eads o he MAGs e ealed ha MAG abundance p o iles we e mainly shaped by he empe a u e bu also by he OLR. Howe e , he OLR e ec was mo e p onounced o he mesophilic sys ems as compa ed o he he mophilic ones. In con as , me a ansc ip ome mapping o MAGs subsequen ly no malized o MAG abundances showed ha unde he mophilic condi ions, MAGs espond o inc eased OLRs by shi ing hei ansc ip ional ac i i ies mainly wi hou adjus ing hei p oli e a ion a es. This is a clea di e ence compa ed o he beha io o he mic obiome unde mesophilic condi ions. He e, he esponse o inc eased OLRs in ol ed adjus ing o p oli e a ion a es and co esponding ansc ip ional ac i i ies. The analysis led o he iden i ica ion o MAGs posi i ely esponding o inc eased OLRs. The mos ou s anding MAGs in his ega d, ob iously well adap ed o highe OLRs and/o associa ed condi ions, we e assigned o he o de Clos idiales(Ace i ib io sp.) o he mesophilic bio ilm and he o de s Bac e oidales (P e o ella sp. and an unknown species), Lachnospi ales (He binix sp. and Kineo h ix sp.) and Clos idiales (Clos idium sp.) o he he mophilic bio ilm. Genome-based me abolic econs uc ion and ansc ip ional p o iling e ealed ha posi i ely esponding MAGs mainly a e in ol ed in hyd olysis o g ass silage, acidogenesis and / o ace ogenesis. Conclusions: An in eg a ed -omics app oach enabled he iden i ica ion o new AD bio ilm keys one species ea u ing ou s anding pe o mance unde s ess condi ions such as inc eased OLRs. Genome-based knowledge on he me abolic po en ial and ansc ip ional ac i i y o esponsi e mic obiome membe s will con ibu e o he de elopmen o imp o ed mic obiological AD managemen s a egies o biome hana ion o enewable biomass. Keywo ds: Me agenome assembled genomes, In eg a ed -omics, Polyomics, Anae obic diges ion, Biogas, Biocon e sion, Mic obial communi y s uc u e, Me hane, Me abolic ac i i y Backg ound Impo an pa o bioeconomical s a egies o sus ain- able and ca bon dioxide (CO 2 ) - neu al ene gy p oduc- ion is he anae obic diges ion (AD) and biome hana ion o enewable aw ma e ials. Beside manu e and slu ies om ag icul u al husband y, also ag icul u ally p oduced biomass such as maize silage (‘ene gy c ops’) o ma e ial om landscape managemen we e u ilized [1,2]. C op biomass is ich in long-chained ca bohyd a es such as cellulose, hemicellulose, and xylan and addi ionally con- ains conside able amoun s o p o eins depending on he pa icula c op. To diges c op biomass as sole subs a e and a high o ganic loading a es (OLRs), specially designed bio- gas eac o s a e ad an ageous such as s aged deg ada ion s ep (‘phase’) sepa a ed eac o sys ems consis ing o a cellu- lolysis / hyd olysis e men e and a downs eam me hano- genesis eac o . Compa ed o single phase eac o s, hese wo-s age wo-phase eac o s possess se e al ad an ages, o example, he mo e s able ope a ion (unde pa icula p ocess condi ions) combined wi h highe bioene gy yields [2–6]. The deg ada ion o high-molecula compounds e- qui es he di ec access o mic obial specialis s. Acco d- ingly, c op biomass is colonized by a celluloly ic bio ilm which composi ion a ies wi h he abio ic en i onmen al condi ions, as example, he p ocess empe a u e, bu also elies on he physico-chemical cha ac e is ics o c op ma e ial and p ocess liquids [7]. Once he bio ilm is es ablished, i unc ions as a coope a i e conso ium leading o enhanced biomass deg ada ion and, in conse- quence, o biogas p oduc ion [8,9]. Comp ehensi e mic obiome analyses by means o me a- genome sequencing e ealed ha many biogas mic o- biome membe s could no be classi ied down o he species le el and hence a e cu en ly unknown (‘mic obial da k ma e ’)[10,11]. As example published p e iously, in he me agenome da ase de e mined o a biogas plan op- e a ed unde he mophilic empe a u e egime, only 18% o he included 16S RNA gene sequences we e assignable o a axonomically es ablished genus [10]. In addi ion, in- o ma ion on he me abolic ac i i y o biogas bio ilm mi- c obial communi ies is only udimen a ily a ailable. Mos o he co esponding s udies ocus on he me hanogenic sub-communi y, while he me abolic po en ial o he en- i e biogas bio ilm mic obiome emains poo ly cha ac e - ized [12,13]. Fo his p opose, he in eg a ion o di e en -omics app oaches (in eg a ed o poly-omics), as example, he combina ion o me agenome wi h me a ansc ip ome da ase s, is indispensable o dis inguish be ween me abol- ically ac i e and less ac i e mic obial species. Genome- cen e ed biogas mic obiome analyses al eady disclosed and p ospec i ely will disclose u he unc ionali ies and in e ac ions o keys one mic obiome membe s [14–21]. The deg ada ion o plan biomass by hyd oly ic enzymes o su ace a ached celluloly ic and hyd oly ic bac e ia and he subsequen seconda y e men a ion s ill ep esen bo - lenecks in he enginee ed op imiza ion o biogas p ocesses. Maus e al. En i onmen al Mic obiome (2020) 15:7 Page 2 o 21 Fo economically op imal AD p ocess ope a ion, celluloly ic / hyd oly ic bio ilms adap ed o maximal OLRs and, wi h special espec o he e men a ion o subs a es wi h high con en s o ni ogen-con aining compounds such as p o- eins and pep ides (e.g., g ass silage), mic obiomes ea u ing ole ance o high ammonium / ammonia con en s a e es- sen ially equi ed. I was hypo hesized ha such bio ilm membe s, in pa icula unc ional keys one species, will become ecognizable by hei inc easing abundances and ansc ip ional ac i i ies unde demanding p ocess condi ions. To un a el he s uc u e, unc ionali y, and me abolic ac- i i y o such celluloly ic / hyd oly ic bio ilm mic obiomes, in his s udy, an in eg a ed -omics app oach was applied consis ing o pa allel mic obial me agenome and me a an- sc ip ome analyses. To ob ain di ec access o hese mic o- biomes, bio ilm samples g own on he su ace o yeg ass silage diges ed in he hyd olysis eac o s (HR) o wo-s age wo-phase biogas eac o sys ems (Fig. 1)ope a edunde mesophilic (37 °C) and he mophilic (55 °C) empe a u e e- gime and a wo (low and inc eased) OLRs we e analyzed. Me abolic econs uc ion o candida e me agenome- assembled genomes (MAGs) and co esponding genome- cen e ed ansc ip ome analyses p o ided insigh s in o li e- s yles and ac i i ies o adap ed species. Resul s Biogas eac o pe o mance and long- e m mic obial dynamics Fou biogas eac o sys ems we e ope a ed in pa allel o e a pe iod o longe han 750 days esul ing in wo (biological) eplica es o mesophilic (M1, M2) and wo eplica es o he mophilic condi ions (T1, T2) (Fig. 1). Sampling o subs a e su ace a ached bio ilms was con- duc ed o wo di e en OLRs, i.e., 500 g (low OLR) and 1500 g (inc eased OLR) o pe ennial yeg ass silage. The summa ized a e age biogas yields om hyd oly ic eac o s (HR) and anae obic il e s (AF) we e cons an ly 601 ± 18 l no malized o s anda d empe a u e and p essu e (L N ) pe kg ola ile subs ances (VS) (M1) and 599 ± 26 L N kg VS −1 (M2) o he eac o sys ems ope - a ed unde mesophilic empe a u e egime wi h an a e - age me hane con en o 56 ± 2% ( / ) (Fig. 2). Unde he he mophilic empe a u e egime, he summa ized sys- ems’biogas yields we e sligh ly highe wi h a e age alues o 645 ± 27 L N kg VS −1 (T1) and 644 ± 19 L N kg VS −1 (T2) wi h a sligh ly lowe a e age me hane con- en o 54 ± 2% ( / ) each. The a e age me hane yields anged om 337 ± 20 L N kg VS −1 (M2) o 348 ± 19 L N kg VS −1 (T2) which is less han 5% lowe han he e e - ence alue o , on a e age, 353 L N kg VS −1 as de e mined by s anda d ba ch e men a ion es s acco ding o he Ge man echnical s anda d VDI 4630. E en i , in gen- e al, he me hane con en in he biogas was highe in he AF han in he HR (mesophilic, 71 ± 3% s. 51 ± 2%; he mophilic, 70 ± 2% s. 50 ± 2%), mos o he biogas and me hane was p oduced in he HR (mesophilic, 74 ± 6% and 67 ± 6% on a e age; he mophilic, 79 ± 4% o 81 ± 4% and 73 ± 4% o 76 ± 4% depending on he e- spec i e p ocess s a us). The main p oduc o bac e ial e men a ion in he HR was ace ic acid. Highes concen a ions we e de e mined o e men a ion day 2 wi h alues anging om 0.80 g L −1 Fig. 1 Flow scheme (a) and pic u e (b) o he wo-s age wo-phase biogas eac o sys em Maus e al. En i onmen al Mic obiome (2020) 15:7 Page 3 o 21 (s a -up phase) o 5.30 g L −1 (OLR 1500 g silage) and unde he he mophilic condi ions, om 0.91 g L −1 (s a - up phase) o 4.21 g L −1 (OLR 1500 g silage). P opionic acid was p oduced only in mino amoun s o up o 0.58 g L −1 (mesophilic) and 0.43 g L −1 ( he mophilic). The ola ile a y acids (VFA) accumula ion h oughou he ongoing e - men a ion p ocess was no obse ed. Due o he ni ogen con en o he silage o 7.6 g kg FM −1 ,a NH 4+ accumula ion o up o 2.3 g L −1 (mesophilic) and 2.7 g L −1 ( he mophilic) was obse ed in he p ocess luids du ing he e men a ion and wi hin he en i e biogas eac o sys em (Fig. 2). In con as o he e men a ions a mesophilic em- pe a u es, unde he mophilic empe a u e egime also an accumula ion o cy o oxic NH 3 o up o 1.3 g L −1 occu ed. Fig. 2 Biogas and me hane yields, and NH 4+ - and NH 3 -con en s in he biogas eac o e luen s. Bac e ial 16S RNA gene a ge ing TRFLP analyses esul s a e shown exempla y o di e en ime poin s a di e en p ocess condi ions. Do ed lines indica e ime poin s o sampling o NGS. ▲,△, hyd olysis eac o (HR) o eac o sys em M1 (mesophil) esp. T1 ( he mophil);▼,▽, downs eam AF o eac o sys em M1 (mesophil) esp. T1 ( he mophil); ■,□, HR o eac o sys em M2 (mesophil) esp. T2 ( he mophil); ◆,◇, AF o eac o sys em M2 (mesophil) esp. T2 ( he mophil); L N , li e s no malized o 0 °C and 1013 hPa; VS, ola ile subs ances; OLR, o ganic loading a e Maus e al. En i onmen al Mic obiome (2020) 15:7 Page 4 o 21 As e ealed by bac e ial 16S RNA gene a ge ing TRFLP analysis, he bac e ial communi y s uc u e had adap ed du ing he ongoing biome hana ion expe imen (Fig. 2). I is assumed ha adap a ion o he communi y p ima ily occu ed as esponse o he inc ease in OLR. Likewise, also he inc ease in NH 4+ concen a ions and, in pa icula du ing he he mophilic e men a ions, he inc ease in NH 3 concen a ions may had a ec ed he communi y composi ion. Celluloly ic / hyd oly ic bio ilm communi y s uc u e To cha ac e ize he s uc u e o he bac e ial bio ilms es ablished on he su ace o yeg ass silage diges a e in he mesophilic and he mophilic HRs, nex gene a ion sequencing (NGS) o he 16S RNA gene was pe o med. Due o he used p ime se s, p ima ily 16S RNA genes o he domain Bac e ia we e de ec ed. 16S RNA gene sequences o me hanogenic A chaea we e only de ec ed o mesophilic bio ilm samples (in maximum, wi h an abundance o 1.2% in case o he HR bio ilm sample M1 OLR1500 ) and assigned o genus Me hanosae a, i.e., Me hano h ix. O e all, 66% o he 16S RNA gene sequences we e classi ied in o ope a ional axonomic uni s (OTUs) ha could be assigned o known gene a. 34% emained un- assigned a genus ank (Addi ional ile 1). In gene al, he he mophilic bio ilms exhibi ed a sligh ly lowe di e si y han he mesophilic bio ilms (Shannon indices in a e - age 2.9 s. 3.2). In hemesophilicbio ilms,anumbe o gene awe e exclusi ely de ec ed belonging o he classes Clos- idia (i.e., Cellulosily icum,Lachnospi a,Anae ospo o- bac e ,Bu y i ib io,andEpulopiscium), Bac e oidia (i.e., Bac e oides,andPe imonas), Tissie ellia (i.e., Sedimen ibac e )(Fig.3, Addi ional ile 2). In gene al, he abundance o pa icula OTUs a ied be ween he biological eplica es and OLRs indica ing a ying mic obiome s uc u e. Fig. 3 Taxonomic p o iling o he hyd olysis eac o (HR) bio ilm mic obiome. Rela i e abundances a e shown o he mos abundan gene a o mic obial sub-communi ies as de e mined by 16S RNA gene amplicon NGS. M1, M2, mesophilic eplica es; T1, T2, he mophilic eplica es; OLR500, OLR1500, o ganic loading a es o 500 o 1500 g yeg ass silage. Fo u he de ails on sample denomina ion, e e o Fig. 2 Maus e al. En i onmen al Mic obiome (2020) 15:7 Page 5 o 21 In he he mophilic bio ilms, membe s o he gene a Ruminiclos idium and Halocella (phylum Fi micu es, class Clos idia), and Tepidimic obium (class Tissie ellia) we e ound, which we e no o only de ec ed in mino amoun s in he mesophilic bio ilms. Also in hese bio- ilms, he abundance o OTUs a ied be ween biological eplica es and OLRs. Some gene a we e p esen in all bio ilms, such as Ruminococcus,De lu ii alea, and Mobi- li alea (class Clos idia), bu all showing subs an ial di e ences in abundance in mesophilic and he mophilic bio ilms (Fig. 3, Addi ional ile 2). Unde mesophilic empe a u e egime, he inc ease in OLR had a posi i e e ec on he abundance o some membe s, e.g., o he gene a P o einiphilum (OLR 500 g: 0.7 esp. 0.4% s. OLR 1500 g: 3.7 esp. 1.3%) and De lu- ii alea (OLR 500 g: 0.1 esp. 0.9% s. OLR 1500 g: 1.8 esp. 4.8%). O he bio ilm membe s dec eased in abun- dance a e inc ease o OLR, such as membe s o gene a Anae ospo obac e (OLR 500 g: 5.0 esp. 6.0% s. OLR 1500 g: 0.8 esp. 0.9%) and Cellulosily icum (OLR 500 g: 15.2 esp. 12.4% s. OLR 1500 g: 7.8 esp. 5.7%) (Add- i ional ile 2). A he mophilic empe a u es, only he genus Mobili- alea bene i ed om he inc eased OLR (OLR 500 g: 8.8 esp. 9.6% s. OLR 1500 g: 17.2 esp. 11.9%) (Addi ional ile 2). All o he gene a emained a mo e o less simila abundances. Thus, i can be assumed ha Mobili alea species a e mo e ole an owa ds inc eased NH 3 con- cen a ions compa ed o o he species. MAG abundance in he celluloly ic/hyd oly ic bio ilms depending on he empe a u e and he OLR To de e mine and cha ac e ize di e en ial abundances o species ep esen ed by me agenomically assembled genomes (MAGs) in he celluloly ic/hyd oly ic bio ilms es ablished on he su ace o yeg ass silage, mic obial me agenome sequencing ollowed by a combined assem- bly o sequence da a and genome binning we e applied (Addi ional ile 3). In o al, 157 MAGs we e compiled and axonomically classi ied (Addi ional ile 4). 74 MAGs we e assigned o he domain Bac e ia, i e MAGs o A chaea, and 78 emained unclassi ied a domain le el. A he phylum le el, he MAGs we e alloca ed o he Fi micu es (55), Bac e oido a (12), Eu ya chaeo a (5), Spi ochae o a (2), Fib obac e o a (1), and Cloacimo- nado a (1). A he amily le el, only 53 MAGs we e clas- si iable among o he s o he Lachnospi aceae (19), Bac e oidaceae (4), Ruminoclos idiaceae (3), Clos idia- ceae (3), indica ing occu ence o so a unknown mic obial species and/o insu icien ep esen a ion o adequa e e e ence genomes in da abases ha a e a ail- able o compa a i e analyses. To unco e he ela i e abundances o he compiled MAGs in he HRs analyzed, me agenome sequences ob ained om he mesophilic and he mophilic mic o- bial communi ies we e mapped on o he MAG se- quences. Only 78 MAGs ea u ing con amina ion a es below 10% we e conside ed o his app oach. Deepe me agenome sequencing would ce ainly ha e imp o ed he comple eness and numbe o compiled MAGs. How- e e , sequencing dep h always is a ade-o be ween in- cu ed cos s and expec ed esul s. P incipal componen (PCA) analysis o MAG abun- dance p o iles e ealed close clus e ing o eplica es con- i ming ep oducibili y o he ea men s ca ied ou (Fig. 4a). Mo eo e , empe a u es (mesophilic s. he mophilic) led o a clea sepa a ion o MAG abun- dance p o iles in he PC plo s. Likewise, he OLRs (OLR500 s. OLR1500) di e en ia e MAG abundances. Howe e , his e ec is a mo e p onounced o he mesophilic sys ems as compa ed o he he mophilic ones (Fig. 4a). MAG abundance p o iles a e isualized o all condi- ions es ed ( wo empe a u es and wo OLRs in epli- ca es) in hea -maps o he 78 MAGs es ed (Fig. 4b). Clus e analysis e ealed ha he empe a u e is he mos impo an ac o ha d i es shaping o he com- muni y ollowed by he OLR. Replica es a e e y simila o each o he ega ding MAG abundance p o iles unde he condi ions es ed. Rela i e abundances o he ollowing MAGs signi i- can ly inc eased (log 2 old-change o > 2 and –log 10 (p- alue) o > 0.05) unde mesophilic condi ions when he OLR was aised o 1500 g: MAG 13, 40, 48, 84, 85, 107, 109, 111, 132, 145 and 146 as shown by olcano plo analysis (Fig. 4c). Rela i e abundances o se e al mo e MAGs dec eased unde high OLRs. Unde he mophilic condi ions, he MAGs 50, 68, 106 and 146 inc eased in abundance upon OLR aise (Fig. 4d). Responsi e MAGs ea u ing comple eness alue o mo e han 50% and con- amina ion less han 10% we e u he analyzed ega ding hei gene ic po en ial and ansc ip ional ac i i y. These a e MAGs 40, 50, 85, 107, 109, 111 and 145 (see below). Func ional po en ial o MAGs posi i ely esponding o inc eased OLR To gain insigh s in o he unc ional po en ial o MAGs posi i ely esponding o inc eased OLRs, gene ic de e - minan s o u iliza ion o ca bohyd a es (Fig. 5) as well as he key enzymes o AD pa hways we e analyzed (Add- i ional ile 5). The gene ic de e minan s we e ca ego ized acco ding o he ou s ages o he AD p ocess, namely hyd olysis, acidogenesis, ace ogenesis and me hanogen- esis as desc ibed p e iously [23]. Rega ding he unc ional con ex ‘hyd olysis’, he gene ic po en ial o u iliza ion o ca bohyd a es was cha ac e ized in he selec ed bac e ial MAGs. Genes en- coding ca bohyd a e-ac i e enzymes we e de e mined by Maus e al. En i onmen al Mic obiome (2020) 15:7 Page 6 o 21 applying he HMM-based Ca bohyd a e-ac i e enzyme anno a ion da abase dbCAN 7 [24] (Fig. 5). Be ween 45 and 236 genes encoding cellulosomal p o eins o en- zymes wi h p edic ed ac i i ies on ca bohyd a es we e iden i ied in each o he bac e ial MAGs analyzed. Ob ained esul s subdi ided he analyzed MAGs in o wo g oups. G oup I membe s we e p edic ed o en- code cellulosome s uc u es equi ed o e icien deg- ada ion o cellulose, comp ising docke in-con aining glycosyl hyd olases (GHs), co esponding cohesin- con aining sca oldins, and enzymes ac ing on la ge ca bohyd a e molecules. Some o he iden i ied en- zymes con ain ca bohyd a e-binding mo i s. MAG 50 ( amily De lu ii aleaceae), MAG 85 (phylum Fi mi- cu es) and 145 (a ilia ed o he genus Jeo galibaca) ep- esen g oup I membe s. In gene al, o celluloly ic/ hyd oly ic bio ilms, he MAGs belonging o g oup I a e o g ea impo ance, since hey ep esen bac e ial can- dida es ea u ing he po en ial o e icien decompos- i ion o complex ca bohyd a es such as cellulose, hemicellulose and xylan. The emaining MAGs we e classi ied o g oup II ep e- sen ing seconda y e men a i e bac e ia mainly u ilizing mono-, di- and oligosaccha ides o ene gy p oduc ion as supplied by g oup I bac e ia. G oup II comp ises MAGs lacking genes o p o eins in ol ed in cellulosome Fig. 4 Al e a ion o abundance o 157 me agenome-assembled genomes (MAGs) de ec ed in HR bio ilms a mesophilic (M) and he mophilic (T) p ocess empe a u e in esponse o he inc ease o o ganic loading a e (OLR) om 500 o 1500 g yeg ass silage as deduced om me agenome da a. PCA plo s a e shown o p inciple componen analyses o scaled and cen e ed log ans o med me agenome ead coun s mapped on MAGs (a). The hie a chical clus e ing o log ans o med abundance alues o 78 (con amina ion below 10%) selec ed MAGs de ec ed in HR bio ilms is isualized in (b). G een, mesophilic HR bio ilms; blue, he mophilic HR bio ilms. Fo u he de ails on sample denomina ion, e e o Figs. 2and 3. Al e a ion in abundance alues o 78 MAGs selec ed in esponse o he inc ease o OLR om 500 o 1500 g yeg ass silage a mesophilic (c) and he mophilic (d) p ocess empe a u e. Colo s o he MAGs indica e axonomic a ilia ion (g een, Fi micu es; blue, Bac e oido a; iole , A chaea; pink, Cloacimonado a; ligh g een, Fib obac e o a; da k ed, Spi ochae o a; ed, unknown a ilia ion). * indica e MAGs wi h comple eness abo e 50% and con amina ion a e less han 10% as lis ed in Table 1and in Addi ional ile 4 Maus e al. En i onmen al Mic obiome (2020) 15:7 Page 7 o 21 o ma ion and assembly. Howe e , due o he incomple e- ness o hese MAGs (Table 1), i canno be excluded ha cellulosome genes we e missed du ing he assembly and binning p ocesses. Fu he mo e, gene ic de e minan s encoding key en- zymes equi ed o u iliza ion o di e en o ganic mole- cules such as py u a e, lac a e, e hanol, ace a e, p opiona e and bu y a e ep esen ing impo an me abo- li es o he acidogenesis and ace ogenesis we e analyzed in he MAGs selec ed (Addi ional ile 5). As examples, he bac e ial MAGs 109 (P o einiphilum sp.) and 145 (Jeo galibaca sp.) encode high numbe s o key genes ea u ing p edic ed unc ions in py u a e me abolism (be ween 14 and 21), also ep esen ing he KEGG (map 00620) modules o u iliza ion o lac a e (be ween 5 and 7) and ace a e (8) only in case o he MAG 145. In MAG 145, essen ial genes encoding enzymes o he Wood- Ljungdahl pa hway (8) we e iden i ied, which plays an im- po an ole in ca bon ixa ion and ace a e u iliza ion. Du ing ace ogenesis, se e al bac e ial species u ilize p opionic acid employing he me hylmalonyl-CoA o he ac ylyl-CoA pa hway o he p opanoa e me abolism. The bac e ial MAGs 109 (P o einiphilum sp.) and 145 (Jeo ga- libaca sp.) possess se e al genes (be ween 5 and 9) o enzymes ha we e assigned o he me hylmalonyl-CoA b anch o he p opanoa e me abolism. Fu he mo e, MAGs 109 and 145 addi ionally encode he me hylmalonyl-CoA mu ase Mu (EC 5.4.99.2) and he me hylmalonyl-CoA/e hylmalonyl-CoA epime ase (EC 5.1.99.1) ep esen ing he key enzymes o his me abol- ism as desc ibed by Siko e e al. [23]. The e o e, hese MAGs we e p edic ed o be in ol ed in he p opionic acid me abolism in he analyzed celluloly ic/hyd oly ic bio ilms. Mo eo e , MAGs 50, 85, 109 and 145 mos p obably a e in ol ed in bu anoa e me abolism since hey possess be ween 2 and 6 o key genes classi ied o he bu anoa e pa hway (KEGG map00650). The bu a- noa e pa hway is no comple ely encoded in he MAGs analyzed. Howe e , genes encoding ele an key en- zymes desc ibed by Siko a e al. [23] we e iden i ied in he genomes o hese Bac e ia. The MAG 109 ha bo s a gene encoding PFL-py u a e o ma e lyase (EC 2.3.1.54), whe eas MAG 145 possesses he gene encoding bu y a e kinase (EC 2.7.2.7) indica ing he impo ance o hese bac e ia o AD a mesophilic empe a u es. The o ma ion o me hane, he las s ep o AD, is pe - o med by membe s o he phylum Eu ya chaeo a.In he analyzed bio ilms, MAG 111 (genus Me hanobac e - ium sp.) was de ec ed as mos abundan a chaeon posi- i ely esponding o he inc ease in OLRs. Twen y- wo genes encoding key enzymes o he hyd ogeno ophic me hanogenesis pa hway we e iden i ied in his MAG illus a ing he impo ance o his pa hway unde inc eased OLRs. T ansc ip ional ac i i y o MAGs in esponse o empe a u e and OLR To de e mine he ansc ip ional ac i i ies o he com- piled MAGs, he me a ansc ip omes om he di e en eac o sys ems we e sequenced cap u ing he p e ailing condi ions ( empe a u e: mesophilic s. he mophilic, OLRs o 500 g s. 1500 g). Mapping o he ansc ip ome sequences o each da ase o he assembled con igs allowed de e mina ion o he MAG’s ansc ip ional ac- i i ies unde he condi ions es ed. P incipal componen (PCA) analysis e ealed clea sepa a ion o he MAG’s ansc ip ional ac i i y pa e ns in ela ion o he empe a u e (mesophilic and he mo- philic) and he OLRs 500 g and 1500 g (Fig. 6a). How- e e , compa ed o he co esponding analysis based on Fig. 5 Genes encoding ca bohyd a e-ac i e enzymes p edic ed o bac e ial me agenome-assembled genomes (MAGs) mos abundan in hyd olysis eac o (HR) bio ilms. * These MAGs showed inc eased ansc ip ional ac i i y in esponse o he o ganic loading a e and we e he e o e addi ionally analyzed Maus e al. En i onmen al Mic obiome (2020) 15:7 Page 8 o 21 Table 1 Taxonomic a ilia ions and cha ac e is ics o selec ed me agenome-assembled genomes (MAGs) mos abundan in HR bio ilms MAG Taxonomic a ilia ion 1 MAG ea u es Phylum Class O de Family Genus Comle eness 2 [%] Con amina ion 2 [%] Size [bp] GC con en [%] No. o genes No. o n genes No. o RNA genes Bac e ia 13 Fi micu es Unknown Unknown Unknown Unknown 29.74 3.43 1,239,774 44.81 1159 3 31 17* Bac e oide es Bac e oidia Bac e oidales Bac e oidaceae P e o ella sp. 68.02 8.98 2,689,597 48.90 2294 2 39 18* Fi micu es Clos idia Lachnospi ales Lachnospi aceae Ace i ib io sp. 68.50 3.65 2,855,089 39.03 2917 n/d 3 15 40* Fi micu es Clos idia Lachnospi ales Lachnospi aceae He binix sp. 68.42 7.66 1,849,940 36.65 1755 n/d 8 48 Fi micu es Clos idia Lachnospi ales Lachnospi aceae He binix sp. 26.48 2.63 770,644 37.4 614 n/d 3 50 Fi micu es Clos idia Lachnospi ales De lu ii aleaceae Unknown 51.74 6.14 1,725,349 31.02 1775 n/d 31 68 Fi micu es Clos idia Lachnospi ales Lachnospi aceae He binix sp. 52.17 4.77 2,358,488 46.61 2310 2 27 84 Fi micu es Clos idia Lachnospi ales Unknown Unknown 35.22 5.14 1,970,476 38.81 1672 2 17 85 Fi micu es Unknown Unknown Unknown Unknown 80.11 3.08 2,011,311 47.98 2076 n/d 33 106 Fi micu es Clos idia Clos idiales Clos idiaceae Clos idium sp. 33.09 4.39 883,787 31.79 812 n/d 17 107* Fi micu es Clos idia Clos idiales Clos idiaceae Clos idium sp. 50.06 6.97 1,539,556 29.37 1648 n/d 17 108* Bac e oide es Bac e oidia Bac e oidales Unknown Unknown 79.01 8.21 2,032,215 47.60 2025 1 29 109 Bac e oide es Bac e oidia Bac e oidales Dysgonomonadaceae P o einiphilum sp. 63.52 7.19 2196,928 45.07 2196 1 27 132 Fi micu es Clos idia Unknown Unknown Unknown 26.26 2.37 1,284,977 37.03 1286 n/d 16 134* Fi micu es Clos idia Lachnospi ales Lachnospi aceae Kineo h ix sp. 78.46 9.27 2,788,291 40.86 2946 n/d 31 145 Fi micu es Bacilli Lac obacillales Ae ococcaceae Jeo galibaca sp. 63.37 9.48 2,346,037 46.04 2647 n/d 14 146 Fi micu es Bacilli Unknown Unknown Unknown 33.22 0.00 861,844 38.49 705 1 13 A chaea 111 Eu ya chaeo a Me hanobac e ia Me hanobac e iales Me hanobac e iaceae Me hanobac e ium sp. 73.74 8.57 2,134,563 37.98 2406 2 51 1 GTDB-Tk based classi ica ion 2 Fo de ails, e e o [22] and Addi ional ile 4 3 n/d = no de ec ed * MAGs which showed inc eased ansc ip ional ac i i y in esponce o he o ganic loading a e (OLR) Maus e al. En i onmen al Mic obiome (2020) 15:7 Page 9 o 21 Table 2 Mos ac i ely ansc ibed genes o enzymes in ol ed in ca bohyd a e o p o ein u iliza ion o selec ed HR bio ilm MAGs (Con inued) Me agenome assembled genome (MAG) 1 Assumed axonomic a ilia ion Analyzed HR 2 bio ilm sample Gene ansc ip s in ol ed in ca bohyd a e o p o ein u iliza ion P edic ed unc ional ole in AD 4 GenID Gene leng h Pu a i e gene p oduc Gene EC numbe T ansc ip s mapped No malized numbe o ansc ip s [TPM] 3 Bin_108_01184 441 50S ibosomal p o ein L15 plO n/s 14 0.2 134 Lachnospi ales (Kineo h ix sp.) T2 OLR1500 Bin_134_02838 177 T ansi ion s a e egula o y p o ein ab B n/s 1527 181 Hyd olysis Bin_134_00038 555 Hypo he ical p o ein n/s n/s 491 7 Bin_134_00185 291 ATP-dependen Clp p o ease, p o eoly ic subuni clpP n/s 81 3 Bin_134_00184 1278 ATP-dependen Clp p o ease, ATP-binding subuni clpX n/s 622 3 Bin_134_00305 906 HTH- ype ansc ip ional egula o yo A n/s 324 2 Bin_134_02093 1110 T ehalose impo ATP-binding p o ein acm 3.2.1.17 234 1 Bin_134_00012 570 Amylopullulanase pulA 3.2.1.41 74 1 Bin_134_00958 3558 Py u a e- la odoxin oxido educ ase ydbK 1.2.7.1 623 1 1 The i s i e ansc ip s o each MAG ep esen he op ansc ip s o he co esponding MAG 2 Hyd olysis eac o 3 T ansc ip s pe million a e aged o da ase s om wo echnical eplica es 4 Anae obic diges ion n/s No speci ied Maus e al. En i onmen al Mic obiome (2020) 15:7 Page 16 o 21 p ocess de ails we e as p e iously published by [3]. S a -up o all e men e s we e pe o med using liquid e men e ma e ial om a biogas plan con e ing ca le manu e in co-diges ion wi h g ass and maize silage and o he biomass a a ying concen a ions and a mesophi- lic empe a u es. Silage o pe ennial yeg ass (Lolium pe enne L.) was diges ed as sole subs a e in ba ches o a ying amoun s wi h e en ion imes o 28 d (s o age o bale silage a −20 °C, cu ing leng h 3 cm), ola ile subs ances (VS) 32% o esh mass (FM), o al Kjeldahl ni ogen 7.6 g kg FM −1 ,NH 4+ -N 0.7 g kg FM −1 , ace ic acid 2.6 g kg FM −1 , p opionic acid < 0.04 g kg FM −1 , lac ic acid 2.6 g kg FM −1 , e hanol 2.2 g kg FM −1 , C/N a io 19.3, chemical oxygen demand (COD) 357.7 g kg FM −1 , analysis o chemical p ope ies acco ding o [6]. The o al Kjeldahl ni ogen is an app oxima ion o a p o ein con en in he sample. The a e age pH had a alue be ween 7 (a he beginning o e e y expe imen ) and 8 (a he end o e e y expe i- men a e 28 days). No spoilage was obse ed in he sil- age. Biogas yields we e calcula ed as li e s no malized o 0 °C and 1013 hPa (L N ) pe kilog am ola ile subs ances (kg VS ). Fo chemical analysis, samples we e aken om he e luen s o HR and AF. Fo sequencing o 16S RNA gene amplicon lib a ies, mic obial me agenomes, and mic obial me a ansc ip- omes, samples we e aken om he silage diges a e in he HR diges ed o 2 d. A his ime poin , high AD a es we e de ec ed as indica ed by he as inc ease o ola ile a y acids (VFA), e.g., ace ic acid. Sampling was pe o med a wo di e en o ganic loading a es (OLRs), i.e.,ba ch- e men a ion o 500 g (denomina ed as “low OLR”, samples M OLR500 and T OLR500 ) and 1500 g silage (denomina ed as “inc eased OLR”, samples M OLR1500 and T OLR1500 ) (Fig. 2). Excess ai was emo ed and he bo le wi h app oxima ely 200 mg o silage diges a e was igh ly closed wi h a sc ew cap. The bio ilm on plan ma e ial su aces o igina ing om he diges a e sample was de ached using a s e ile scalpel in an anae obic chambe . Fu he de ails we e desc ibed by [12]. All samples we e s o ed a −20 °C un il u he analysis ex- cep samples o RNA isola ion, which we e p ocessed immedia ely a e sampling. Ex ac ion o o al mic obial genomic DNA To al mic obial communi y DNA was ex ac ed om su - ace a ached bio ilms by using he Fas DNA™Spin Ki o Soil (MP Biomedicals, USA) wi h Lysing Ma ix E Tubes acco ding o he manu ac u e ’s ins uc ions. Mechanical cell dis up ion was pe o med using he Fas P ep®-24 In- s umen (MP Biomedicals, USA) o wo imes a 6500 pm (speed 5) o 20 s. Fu he , wo washing s eps using SEWS-M we e accomplished. Finally, he DNA was elu ed in 100 μl DES. Two independen echnical eplica es o each HR we e p epa ed, and subsequen ly pooled in equi- mola amoun s oge he o collec su icien DNA ma e ial o sequencing pu poses (Addi ional ile 7). Quali y and quan i y o ex ac ed DNA we e e alua ed by gel elec o- pho esis and pho ome ic analysis (NanoPho ome e , Implen). All DNA samples we e s o ed a −20 °C un il u he p ocessing. Te minal es ic ion agmen leng h polymo phism (TRFLP) inge p in ing The mic obial communi y dynamics du ing he ope - a ion o he biogas eac o sys ems we e moni o ed by DNA-based TRFLP analysis a ge ing he bac e ial 16S RNA gene acco ding o he p o ocol p e iously pub- lished by [12] wi h he modi ica ions as published by [45]. TRFLP p o iles we e de e mined in iplica es o mic obial DNA samples pu i ied om he HR e luen a e 28 d ba ch e men a ion. TRFLP inge p in p o- cessing and subsequen analysis we e pe o med acco d- ing o [46] using BioNume ics 7.1 so wa e (Applied Ma hs, Belgium). Simila i ies o inge p in p o iles we e calcula ed using Pea son co ela ion wi h 0.5% op imiza ion, clus e analysis was pe o med applying he unweigh ed pai g oup me hod wi h a i hme ic mean (UPGMA) algo i hm. Nex -gene a ion-sequencing (NGS) o 16S RNA gene amplicon lib a ies The mic obial communi y s uc u es we e axonomically cha ac e ized by high- h oughpu nex gene a ion sequen- cing (NGS) o 16S RNA gene amplicon lib a ies as de- sc ibed p e iously [47]. The lib a ies we e cons uc ed using he p ime s 515F (5′- CTACGGGNGGCWGCAG - 3′) and 806R (5′- GACTACHVGGGTATCTAATCC - 3′) ampli ying he V3 and V4 egions o he bac e ial 16S RNA gene [48]. Two biological eplica es pe sample we e analyzed (Addi ional ile 7). Ob ained sequence eads we e used o i e a i e ead pai me ging applying he FLASH so wa e [49]. Subsequen ly, he QIIME NGS analysis pipe- line was applied o amplicon da a p ocessing as desc ibed p e iously [29]. Ob ained OTUs we e clus e ed a he 97% sequence iden i y le el applying he QIIME NGS analysis pipeline. Mic obial me agenome lib a y p epa a ion, NGS, and assembly o genomes om me agenome da ase s Fo lib a y p epa a ion, mic obial DNA samples we e pu i- ied using he Genomic DNA Clean & Concen a o Ki (Zymo Resea ch, USA). Fo each sample, DNA om wo subsamples (i.e., echnical eplica es) we e ex ac ed. Fo se- quencing, 1 μg o o al DNA was shea ed o app oxima ely 430 bp agmen s using a ocused-ul asonica o (Co a is M220,Wobu n,MA,USA).Finally, he Illumina T uSeq® Maus e al. En i onmen al Mic obiome (2020) 15:7 Page 17 o 21 DNA PCR- ee sample p epa a ion ki (Illumina, Eindho- en, Ne he lands) was used o cons uc he sequencing li- b a ies, which we e sequenced on he Illumina HiSeq 1500 sequence using he Illumina HiSeq Rapid SBS Ki 2 (Illu- mina, Eindho en, Ne he lands), ollowing a 2 × 250 indexed high ou pu un p o ocol. Fu he mo e, Megahi ool ( 1.0.2) [50](command line se ings: --p ese s me a --min-con ig-len 1000) was used o assembly o he pooled sequencing da a o all samples applying a k-me sizes o 21, 41, 61, 81 and 99 (i e a i e assembly). Pai ed-end me agenome eads om indi idual da ase s we e mapped e sus all assembled me a- genome con igs wi h Bow ie 2 ( 2.2.4) [51]inend- o-end mode applying he op ion ‘sensi i e’. To con e SAM o BAM, so he alignmen ile and calcula e ead mapping s a is ics SAM ools ( 1.0) [52] was used. Fu he mo e, o p edic genes on assembled con igs la ge han 1 kb, he gene p edic ion ool P odigal .2.6.0 [53] was applied. P e- dic ed p o ein sequences we e compa ed o NCBI’sda a- base using he BLASTP mode o DIAMOND [54]. The esul ing ou pu ile was loaded in o MEGAN5 [55] o axonomic classi ica ion o each gene sequence. In he ol- lowing binning s ep, he abundance p o ile and he e anu- cleo ide equencies we e used o bin con igs in o me agenome-assembled genomes (MAGs) wi h Me aBAT ( 0.21.3) [56]. Mapping o he eads was always pe o med on all con igs, including he con igs o he MAGs and he con igs which we e no binned. Subsequen ly, comple e- ness, con amina ion, and s ain he e ogenei y o he MAGs we e es ima ed wi h CheckM ( 1.0.4) [22], using se s o clade-speci ic single-copy ma ke genes. Mic obial me a ansc ip ome lib a y p epa a ion and NGS The o al mic obial RNA om wo sub-samples ( om he same silage bio ilm as o he DNA ex ac ion) was ex ac ed applying he RNeasy Mini Ki (Qiagen, Hilden, Ge many) acco ding o he manu ac u e ’s guidelines. In o al, wo echnical eplica es we e p ocessed o each o wo pa allel hyd oly ic eac o communi ies yielding eigh samples o he mesophilic sys em and eigh samples o he he mophilic sys em (Addi ional ile 7). Subsequen ly, he RNA was pu i ied using he Ambion® Tu bo DNA- ee Ki (The moFishe , Ge many). Ribosomal RNA was deple ed using he Ribo-Ze o™ RNA Remo al Ki o Bac e ia (Illumina, Madison, USA) acco ding o he manu ac u e ’sin- s uc ions. The emaining mRNA ansc ip s we e agmen ed o app oxima ely 550 bp agmen s using a ocused-ul asonica o (Co a is M220, Wobu n, USA). cDNA lib a ies o Illumina sequencing we e cons uc edusing heT uSeqRNALib a yP epKi 2 (Illumina, Eindho en, Ne he lands). The esul ing cDNA lib a ies we e sequenced on he Illumina HiSeq 1500 machine using he Illumina HiSeq Rapid SBS Ki 2 (Illumina, Eindho en, Ne he lands) o gene a e 2 × 100 bp pai ed-end eads. Me agenome and me a ansc ip ome sequence analysis Pai ed end me agenome and me a ansc ip ome eads we e mapped e sus all assembled me agenome con igs wi h Bow ie2 [51] in end- o-end mode wi h op ion sen- si i e. A e ead mapping SAM ools [52] was used o il- e he esul ing BAM iles o uniquely mapped eads. Reads we e classi ied as uniquely mapped eads wi h a unique genomic loca ion i and only i hey could no be aligned o ano he loca ion wi h a highe o same map- ping quali y. Me agenome as well as me a ansc ip ome eads ha could be aligned o assembled MAG’s we e quan i ied wi h he HTSeq-coun p og am [57] o ge an es ima e o MAG abundance and o e all MAG exp es- sion, espec i ely. To accoun o di e en MAG abun- dance, aw me a ansc ip ome ead coun s o each MAG plus one (pseudocoun ) we e di ided by he MAG’s aw me agenome ead coun plus one and ounded o in ege alues. The esul ing coun s o each MAG se ed as inpu o DESeq2 [58] o pai wise de- ec ion and quan i ica ion o di e en ially abundan and ansc ip ionally ac i e MAGs, espec i ely. Fo DESeq2 pa ame iza ion, a be a p io and disabled Cook dis ance cu o il e ing was used. All o he pa ame e s emained unchanged. Fold change es ima es, p- alues, and egula - ized log- ans o med ( log) coun s OF (1) me agenome ead coun s and (2) me a ansc ip ome ead coun s no - malized o di e en MAG abundances as desc ibed abo e we e emplyed o assess p ope sample esp. epli- ca e clus e ing wi h (PCA, mul idimensional scaling (MDS)), and hie a chical clus e ing. In addi ion, olcano plo s we e used o iden i y signi ican ly di e en ially exp essed MAGs. Simila compa a i e analyses we e pe o med assuming equal MAG abundances. Phylogene ic and unc ional analysis o he me agenome- assembled genomes The Genome Taxonomy Da abase oolki [59] was used o assign objec i e axonomic classi ica ions o bac e ial and a chaeal genomes. Each MAG was de ined as single ope a ional axonomic uni (OTU). Fo MAGs wi h comple eness alues o mo e han 50% and a con amin- a ion a e less han 10% (Addi ional ile 4), analysis o he gene ic po en ial was pe o med using he EMGB [60] anno a ion sys em including KEGG pa hway map- ping and DIAMOND ool [54]. MAGs ha mee he c i- e ia men ioned abo e we e subsequen ly analyzed ega ding hei ansc ip ional ac i i ies using he EMGB anno a ion sys em again. To p edic genes encoding ca bohyd a e-ac i e en- zymes, he ca bohyd a e-ac i e enzyme da abase (CAZy) Maus e al. En i onmen al Mic obiome (2020) 15:7 Page 18 o 21 anno a ion web se e dbCAN 7 [24] was used. The genes encoding enzymes ac ing di ec on cellulose we e iden i ied by he p esence o coding egions o ype one o wo docke in o cohesin modules, among o he s. Supplemen a y in o ma ion Supplemen a y in o ma ion accompanies his pape a h ps://doi.o g/10. 1186/s40793-020-00354-x. Addi ional ile 1. S a is ics o 16S RNA gene sequence analysis. Addi ional ile 2. Rela i e abundances o mos abundan 16S RNA gene sequences. Addi ional ile 3. S a is ics o he ob ained and p ocessed me agenome and me a ansc ip ome sequences. Addi ional ile 4. Taxonomic a ilia ions o me agenome-assembled ge- nomes (MAGs) o his s udy o igina ing om HR bio ilms. Addi ional ile 5. Analysis o he key enzymes o AD pa hways in me agenome-assembled genomes (MAGs). The gene ic de e minan s we e ca ego ized acco ding o he ou s ages o he AD p ocess, namely hyd olysis, acidogenesis, ace ogenesis and me hanogenesis as desc ibed p e iously [23]. Addi ional ile 6. Hie a chical clus e ing o abundance alues o 78 selec ed me agenome-assembled genomes (MAGs) de ec ed in HR bio- ilms a mesophilic and he mophilic p ocess empe a u e a o ganic loading a e (OLR) o 500 g esp. 1500 g yeg ass silage as deduced om ansc ip ome da a. Addi ional ile 7. Expe imen al se up and sampling scheme. Abb e ia ions AD: Anae obic diges ion; AF: Anae obic il e ; ANI: A e age nucleo ide sequence iden i y; CAZymes: Ca bohyd a e-ac i e enzymes; CO 2 : Ca bon dioxide; COD: Chemical oxygen demand; d: day; FM: F esh mass; GH: Glycosyl hyd olase; HR: Hyd olysis eac o ; HT: High- h oughpu ; kg: kilog am; kg VS : kilog ams ola ile subs ances; L: Li e ; L N : Li e no malized; M: Mesophilic; MAG: Me agenome assembled genomes; MG: Mic obial me agenome da ase ; MT: Mic obial me a ansc ip ome da ase ; OLR: O ganic loading a es; OTU: Ope a ional axonomic uni ; SAOB: Syn ophic ace a e- oxidizing bac e ia; T: The mophilic; TPM: T ansc ip s pe million; TRFLP: Te minal es ic ion agmen leng h polymo ophism; VFA: Vola ile a y acids; VS: Vola ile subs ances Acknowledgemen s The au ho s g a e ully acknowledge he highly aluable echnical suppo o M. Felgen eu, M. Jäkel, K. Mund , and G. Rehde. The bioin o ma ics suppo o he BMBF- unded p ojec ‘Biele eld-Gießen Cen e o Mic obial Bioin o - ma ics - BiGi (g an no. 031A533)’wi hin he Ge man Ne wo k o Bioin o - ma ics In as uc u e (de.NBI) is also g a e ully acknowledged. ASz and A.S. acknowledge unding om he Eu opean Union’s Ho izon 2020 esea ch and inno a ion p og am unde g an ag eemen No. 818431 (SIMBA). This ou pu e lec s only he au ho ’s iew and he Resea ch Execu i e Agency (REA) can- no be held esponsible o any use ha may be made o he in o ma ion con ained he ein. Au ho s’con ibu ions IM p epa ed he 16S RNA gene amplicon lib a ies o sequencing, analyzed he axonomic p o iles o bio ilm communi ies, analyzed and in e p e ed me agenome and me a ansc ip ome da a, pe o med he compa a i e MAG analyses, coo dina ed d a ing and d a ed co esponding pa s o he manusc ip . MK pa icipa ed in da a analysis and isualiza ion, and d a ed pa s o he in oduc ion, esul s, discussion, and conclusions sec ions. JD conduc ed all AD expe imen s, he sampling o diges a es and p ocess liquids, DNA and RNA ex ac ion om bio ilm samples, and TRFLP analysis. JD con ibu ed also o AD da a analysis and e ised he manusc ip . YS also pe o med DNA and RNA ex ac ion om bio ilm samples, p epa ed he me agenome and me a ansc ip ome sequencing lib a ies, and e ised he manusc ip . DW and JB de e mined he phylogene ic ela ionship be ween he MAGs, con ibu ed o he esul s and discussion sec ion, and e ised he manusc ip . MB pe o med he compa a i e me agenome and me a ansc ip ome analysis, con ibu ed o he ma e ial and me hods sec ion, and e ised he manusc ip . CJ pa icipa ed in AD expe imen s and co esponding da a analysis, and e ised he manusc ip . KW pa icipa ed in me a ansc ip ome da a analysis, and e ised he manusc ip . MR ca ied ou he axonomic classi ica ion o he mic obial communi ies, con ibu ed o he esul s sec ion, and e ised he manusc ip . AR pa icipa ed in AD expe imen s and TRFLP analysis and co esponding da a analysis, and e ised he manusc ip . AP pa icipa ed in he design o his s udy, con ibu ed o he esul s and discussion sec ions, and e ised he manusc ip . ASz and CH ca ied ou he axonomic classi ica ion o he mic obial communi ies based on me agenome and me a ansc ip ome da a, pe o med he me agenome assembly and binning, pa icipa ed in he compa a i e me agenome and me a ansc ip ome analysis, con ibu ed o he esul s and discussion sec ion, and e ised he manusc ip . ASz, AS, and MK concei ed he s udy, pa icipa ed in manusc ip coo dina ion, o ganized hi d-pa y unding, su- pe ised all biological and bioin o ma ic da a analyses, con ibu ed o d a - ing o he manusc ip and e ised he manusc ip . All au ho s ead and app o ed he inal manusc ip . Funding This wo k was pa o he join p ojec BIOGAS-MARKER suppo ed by he Ge man Fede al Minis y o Educa ion and Resea ch (BMBF), g an nos. 03SF0440A and 03SF0440C. A ailabili y o da a and ma e ials Sequence da ase s we e deposi ed in he Eu opean Nucleo ide A chi e (ENA) unde he Biop ojec accession numbe s PRJEB27769 (me agenome da ase s), E-MTAB-7533 (me a ansc ip ome da ase s), PRJEB30260 (16S RNA gene amplicon sequences). E hics app o al and consen o pa icipa e No applicable. Consen o publica ion No applicable. Compe ing in e es s The au ho s decla e ha hey ha e no compe ing in e es s. Au ho de ails 1 Biele eld Uni e si y, Cen e o Bio echnology (CeBiTec), Genome Resea ch o Indus ial Mic oo ganisms, Uni e si ä ss . 27, 33615 Biele eld, Ge many. 2 Depa men Bioenginee ing, Leibniz Ins i u e o Ag icul u al Enginee ing and Bioeconomy (ATB), Max-Ey h-Allee 100, 14469 Po sdam, Ge many. 3 Helmhol z Cen e o In ec ion Resea ch, Mic obial In ec ion Biology / Expe imen al Immunology, Inho ens asse 7, 38124 B aunschweig, Ge many. 4 Depa men Bioin o ma ics and Sys ems Biology, Jus us-Liebig Uni e si y Gießen, Hein ich-Bu -Ring 58, 35392 Giessen, Ge many. 5 Facul y o Technology, Biele eld Uni e si y, Uni e si ä ss . 25, 33615 Biele eld, Ge many. Recei ed: 20 Sep embe 2019 Accep ed: 14 Feb ua y 2020 Re e ences 1. Weiland P. Biogas p oduc ion: cu en s a e and pe spec i es. Appl Mic obiol Bio echnol. 2010;85:849–60. 2. Nizami AS, Ko es NE, Mu phy JD. Re iew o he in eg a ed p ocess o he p oduc ion o g ass biome hane. En i on Sci Technol. 2009;43:8496–508. 3. Schönbe g M, Linke B. The in luence o he empe a u e egime on he o ma ion o me hane in a wo-phase anae obic diges ion p ocess. Eng Li e Sci. 2012;12:279–86. 4. Pohl M, Heeg K, Mumme J. Anae obic diges ion o whea s aw – pe o mance o con inuous solid-s a e diges ion. Bio esou Technol. 2013; 146:408–15. 5. Shen F, Yuan H, Pang Y, Chen S, Zhu B, Zou D, e al. Pe o mances o anae obic co-diges ion o ui & ege able was e (FVW) and ood was e (FW): single-phase s. wo-phase. Bio esou Technol. 2013;144:80–5. Maus e al. En i onmen al Mic obiome (2020) 15:7 Page 19 o 21 6. Linke B, Rod íguez-Abalde Á, Jos C, K ieg A. Pe o mance o a no el wo- phase con inuously ed leach bed eac o o demand-based biogas p oduc ion om maize silage. Bio esou Technol. 2015;177:34–40. 7. Habouzi F, Hamelin J, San a-Ca alina G, S eye J-P, Be ne N. Bio ilm de elopmen du ing he s a -up pe iod o anae obic bio ilm eac o s: he bio ilm A chaea communi y is highly dependen on he suppo ma e ial. Mic ob Bio echnol. 2014;7:257–64. 8. Zak zewski M, Goesmann A, Jaenicke S, Jünemann S, Eikmeye F, Szczepanowski R, e al. P o iling o he me abolically ac i e communi y om a p oduc ion-scale biogas plan by means o high- h oughpu me a ansc ip ome sequencing. J Bio echnol. 2012;158:248–58. 9. Lange S, Sch opp D, Bengelsdo FR, O hman M, Kazda M. Dynamics o bio ilm o ma ion du ing anae obic diges ion o o ganic was e. Anae obe. 2014;29:44–51. 10. Maus I, Koeck DE, Cibis KG, Hahnke S, Kim YS, Lange T, e al. Un a eling he mic obiome o a he mophilic biogas plan by me agenome and me a ansc ip ome analysis complemen ed by cha ac e iza ion o bac e ial and a chaeal isola es. Bio echnol Bio uels. 2016;9:171. 11. Maus I, Rumming M, Be gmann I, Heeg K, Pohl M, Ne mann E, e al. Cha ac e iza ion o Ba hya chaeo a genomes assembled om me agenomes o bio ilms esiding in mesophilic and he mophilic biogas eac o s. Bio echnol Bio uels. 2018;11:167. 12. Rademache A, Nol e C, Schönbe g M, Klocke M. Tempe a u e inc eases om 55 o 75 °C in a wo-phase biogas eac o esul in undamen al al e a ions wi hin he bac e ial and a chaeal communi y s uc u e. Appl Mic obiol Bio echnol. 2012;96:565–76. 13. Kouzuma A, Tsu sumi M, Ishii S, Ueno Y, Abe T, Wa anabe K. Non- au o ophic me hanogens domina e in anae obic diges e s. Sci Rep. 2017;7: 1510. 14. B emges A, Maus I, Belmann P, Eikmeye F, Winkle A, Albe smeie A, e al. Deeply sequenced me agenome and me a ansc ip ome o a biogas- p oducing mic obial communi y om an ag icul u al p oduc ion-scale biogas plan . Gigascience. 2015;4:33. 15. Hassa J, Maus I, O S, Pühle A, Sche e P, Klocke M, e al. Me agenome, me a ansc ip ome, and me ap o eome app oaches un a eled composi ions and unc ional ela ionships o mic obial communi ies esiding in biogas plan s. Appl Mic obiol Bio echnol. 2018;102:5045–63. 16. Heye R, Koh s F, Reichl U, Benndo D. Me ap o eomics o complex mic obial communi ies in biogas plan s. Mic ob Bio echnol. 2015;8:749–63. 17. Campana o S, T eu L, Kougias PG, De F ancisci D, Valle G, Angelidaki I. Me agenomic analysis and unc ional cha ac e iza ion o he biogas mic obiome using high h oughpu sho gun sequencing and a no el binning s a egy. Bio echnol Bio uels. 2016;9:26. 18. Kougias PG, Campana o S, T eu L, Zhu X, Angelidaki I. A no el a chaeal species belonging o Me hanoculleus genus iden i ied ia de-no o assembly and me agenomic binning p ocess in biogas eac o s. Anae obe. 2017;46:23–32. 19. Maus I, B emges A, S olze Y, Hahnke S, Cibis KG, Koeck DE, e al. Genomics and p e alence o bac e ial and a chaeal isola es om biogas-p oducing mic obiomes. Bio echnol Bio uels. 2017;10:264. 20. Maus I, Cibis KG, B emges A, S olze Y, Wibbe g D, Tomaze o G, e al. Genomic cha ac e iza ion o De lu ii oga unisiensis L3, a key hyd oly ic bac e ium in a he mophilic biogas plan and i s abundance as de e mined by me agenome agmen ec ui men . J Bio echnol. 2016; 232:50–60. 21. Campana o S, T eu L, Rod iguez-R L, Ko alöo szki A, Ziels R, Maus I, e al. The anae obic diges ion mic obiome: a collec ion o 1600 me agenome- assembled genomes shows high species di e si y ela ed o me hane p oduc ion. Bio echnol Bio uels. 2019; h ps://doi.o g/10.1101/680553. 22. Pa ks DH, Imel o M, Skenne on CT, Hugenhol z P, Tyson GW. CheckM: assessing he quali y o mic obial genomes eco e ed om isola es, single cells, and me agenomes. Genome Res. 2015;25:1043–55. 23. Siko a A, De man A, Mielecki D, Chojnacka A, Błaszczyk M. Sea ching o me abolic pa hways o anae obic diges ion: a use ul lis o he key enzymes. Biogas. 2018. h ps://doi.o g/10.5772/in echopen.81256. 24. Yin Y, Mao X, Yang J, Chen X, Mao F, Xu Y. dbCAN: a web esou ce o au oma ed ca bohyd a e-ac i e enzyme anno a ion. Nucleic Acids Res. 2012; 40:W445–51. 25. Sundbe g C, Al-Soud WA, La sson M, Alm E, Yek a SE, S ensson BH, e al. 454 py osequencing analyses o bac e ial and a chaeal ichness in 21 ull- scale biogas diges e s. FEMS Mic obial Ecol. 2013;85:612–26. 26. L Z, Wu X, Zhou B, Wang Y, Sun Y, Wang Y, e al. E ec o one s ep empe a u e inc emen om mesophilic o he mophilic anae obic diges ion on he linked pa e n be ween bac e ial and me hanogenic communi ies. Bio esou Technol. 2019;292:121968. 27. Munk B, Guebi z GM, Lebuhn M. In luence o ni ogen- ich subs a es on biogas p oduc ion and on he me hanogenic communi y unde mesophilic and he mophilic condi ions. Anae obe. 2017;46:146–54. 28. Shin SG, Han G, Lee J, Shin J, Hwang S. A snapsho o mic obial communi y s uc u es in 20 di e en ield-scale anae obic bio eac o s ea ing ood was e. J En i on Manag. 2019;248:109297. 29. S olze Y, B emges A, Rumming M, Henke C, Maus I, Pühle A, e al. Iden i ica ion and genome econs uc ion o abundan dis inc axa in mic obiomes om one he mophilic and h ee mesophilic p oduc ion-scale biogas plan s. Bio echnol Bio uels. 2016;9:156. 30. Bassini JP, Diass N, Caoe SMS, .Sen a E, La anjei a Y, Dezo i M. E ec o inc easing o ganic loading a es on he pe o mance o mo ing-bed bio ilm eac o s illed wi h di e en suppo media: assessing he ac i i y o suspended and a ached biomass ac ions. P oc Sa En i on P o ec 2016; 100:131–141. 31. Liu C, Wang W, Anwa N, Ma Z, Liu G, Zhang R. E ec o o ganic loading a e on anae obic diges ion o ood was e unde mesophilic and he mophilic condi ions. Ene gy Fuel. 2017;31:2976–84. 32. Ko ács E, Wi h R, Ma ó i G, Bagi Z, Rákhely G, Ko ács KL. Biogas p oduc ion om p o ein- ich biomass: ed-ba ch anae obic e men a ion o casein and o pig blood and associa ed changes in mic obial communi y composi ion. PLoS One. 2013;16:e77265. 33. Wes e holm M, Schnü e A. Mic obial esponses o di e en ope a ing p ac ices o biogas p oduc ion sys ems. Anae obic Diges ion. 2019. h ps:// doi.o g/10.5772/in echopen.82815. 34. Zhang L, Ban Q, Li J. Mic obial communi y dynamics a high o ganic loading a es e ealed by py osequencing du ing suga e ine y was ewa e ea men in a UASB eac o . F on En i on Sci Eng. 2018;12:4. 35. Lei e AF, Janke L, L Z, Ha ms H, Richnow HH, Nikolausz M. Imp o ed moni o ing o semi-con inuous anae obic diges ion o suga cane was e: e ec s o inc easing o ganic loading a e on me hanogenic communi y dynamics. In J Mol Sci. 2015;25:23210–26. 36. Xu R, Yang ZH, Zheng Y, Liu JB, Xiong WP, Zhang YR, e al. O ganic loading a e and hyd aulic e en ion ime shape dis inc ecological ne wo ks o anae obic diges ion ela ed mic obiome. Bio esou Technol. 2018;262:184– 93. 37. Ben Hania W, Godbane R, Pos ec A, Hamdi M, Olli ie B, Fa deau ML. De lu ii oga unisiensis gen. No ., sp. no ., a he mophilic bac e ium isola ed om a meso he mic and anae obic whey diges e . In J Sys E ol Mic obiol. 2012;62:1377–82. 38. Zhang L, Loh KC, Sa anan ha ajah S, Tong YW, Wang CH, Dai Y. Mesophilic and he mophilic anae obic diges ion o soybean cu d esidue o me hane p oduc ion: cha ac e izing bac e ial and me hanogen communi ies and hei co ela ions wi h o ganic loading a e and ope a ing empe a u e. Bio esou Technol. 2018;288:121597. 39. T eu L, Kougias PG, Campana o S, Bassani I, Angelidaki I. Deepe insigh in o he s uc u e o he anae obic diges ion mic obial communi y; he biogas mic obiome da abase is expanded wi h 157 new genomes. Bio esou Technol. 2016;2016:260266. 40. Zhou J, Deng Y, Luo F, He Z, Tu Q, Zhi X. Func ional molecula ecological ne wo ks. MBio. 2010;2010;1. 41. Zhou J, Deng Y, Luo F, He Z, Yang Y. Phylogene ic molecula ecological ne wo k o soil mic obial communi ies in esponse o ele a ed CO2. mBio. 2011;2:e00122–11. 42. Yang J, Li G, Qian Y, Yang Y, Zhang F. Mic obial unc ional gene pa e ns ela ed o soil g eenhouse gas emissions in oil con amina ed a eas. Sci To al En i on. 2018;628–629:94–102. 43. Louca S, Polz MF, Mazel F, Alb igh MBN, Hube JA, O’Conno MI, e al. Func ion and unc ional edundancy in mic obial sys ems. Na u e Ecol E ol. 2018;2:936. 44. Bilen M, Du ou J-C, Lagie J-C, Cado e F, Daoud Z, Dubou g G, e al. The con ibu ion o cul u omics o he epe oi e o isola ed human bac e ial and a chaeal species. Mic obiome. 2018;6:94. 45. Theue l S, Koh s F, Benndo D, Maus I, Wibbe g D, Schlü e A, e al. Communi y shi s in a well-ope a ing ag icul u al biogas plan : how p ocess a ia ions a e handled by he mic obiome. Appl Mic obiol Bio echnol. 2015; 99:7791–803. Maus e al. En i onmen al Mic obiome (2020) 15:7 Page 20 o 21 46. Klang J, Theue l S, Szewzyk U, Hu h M, Tölle R, Klocke M. Dynamic a ia ion o he mic obial communi y s uc u e du ing he long- ime mono- e men a ion o maize and suga bee silage. Mic ob Bio echnol. 2015;8: 764–75. 47. Maus I, Kim YS, Wibbe g D, S olze Y, O S, An onczyk S, e al. Biphasic s udy o cha ac e ize ag icul u al biogas plan s by high- h oughpu 16S RNA gene amplicon sequencing and mic oscopic analysis. J Mic obiol Bio echnol. 2017;27:321–34. 48. Klindwo h A, P uesse E, Schwee T, Peplies J, Quas C, Ho n M, e al. E alua ion o gene al 16S ibosomal RNA gene PCR p ime s o classical and nex -gene a ion sequencing-based di e si y s udies. Nucleic Acids Res. 2013; 41:e1. 49. MagočT, Salzbe g SL. FLASH: as leng h adjus men o sho eads o imp o e genome assemblies. Bioin o ma ics. 2011;27:2957–63. 50. Li D, Liu CM, Luo R, Sadakane K, Lam TW. MEGAHIT: an ul a- as single- node solu ion o la ge and complex me agenomics assembly ia succinc de B uijn g aph. Bioin o ma ics. 2015;31:1674–6. 51. Langmead B, Salzbe g SL. Fas gapped- ead alignmen wi h bow ie 2. Na Me hods. 2012;9:357–9. 52. Li H, Handsake B, Wysoke A, Fennell T, Ruan J, Home N, e al. The sequence alignmen /map o ma and SAM ools. Bioin o ma ics. 2009;25: 2078–9. 53. Hya D, LoCascio PF, Hause LJ, Ube bache EC. Gene and ansla ion ini ia ion si e p edic ion in me agenomic sequences. Bioin o ma ics. 2012;28: 2223–30. 54. Buch ink B, Xie C, Huson DH. Fas and sensi i e p o ein alignmen using DIAMOND. Na Me hods. 2015;12:59–60. 55. Huson DH, Mi a S, Ruscheweyh H-J, Webe N, Schus e SC. In eg a i e analysis o en i onmen al sequences using MEGAN4. Genome Res. 2011;21: 1552–60. 56. Kang DD, F oula J, Egan R, Wang Z. Me aBAT, an e icien ool o accu a ely econs uc ing single genomes om complex mic obial communi ies. Pee J. 2015;3:e1165. 57. Ande s S, Pyl P, Hube W. HTSeq--a Py hon amewo k o wo k wi h high- h oughpu sequencing da a. Bioin o ma ics. 2015;15:166–9. 58. Lo e MI, Hube W, Ande s S. Mode a ed es ima ion o old change and dispe sion o RNA-seq da a wi h DESeq2. Genome Biol. 2014;15:550. 59. A oolki o assigning objec i e axonomic classi ica ions o bac e ial and a chaeal genomes.: Ecogenomics/GTDBTk. Py hon. Aus alian Cen e o Ecogenomics; 2018. h ps://gi hub.com/Ecogenomics/GTDBTk. Accessed 6 No 2018. 60. Jünemann S, Kleinböl ing N, Jaenicke S, Henke C, Hassa J, Nelkne J, e al. Bioin o ma ics o NGS-based me agenomics and he applica ion o biogas esea ch. J Bio echnol. 2017;261:10–23. Publishe ’sNo e Sp inge Na u e emains neu al wi h ega d o ju isdic ional claims in published maps and ins i u ional a ilia ions. Maus e al. En i onmen al Mic obiome (2020) 15:7 Page 21 o 21