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    Rational design of a microbial consortium of mucosal sugar utilizers reduces Clostridiodes difficile colonization

    Ethics statement
    All animal experiments were performed at the Max F. Perutz Laboratories of the University of Vienna, Austria. All experiments were discussed and approved by the University of Veterinary Medicine, Vienna, Austria, and conducted in accordance with protocols approved by the Federal Ministry for Education, Science and Research of the Republic of Austria under the license number BMWF-66.006/0001-WF/V/3b/2016. Animals were randomized for interventions but researchers processing the samples and analyzing the data were aware which intervention group corresponded to which cohort of animals.
    Mouse colon incubations
    Three adult (6-8 weeks old) C57BL/6N mice bred at the Max F. Perutz Laboratories, University of Vienna, under SPF conditions were sacrificed per experiment, and their colon was harvested anaerobically (85% N2, 10% CO2, 5% H2) in an anaerobic tent (Coy Laboratory Products, USA). Contents from each colon were suspended in 7.8 mL of 50% D2O-containing PBS and homogenized by vortexing. Similar conditions have been successfully applied in the past to monitor activity of individual cells in gut communities without causing major changes in the activity of individual community members34. The homogenate was left to settle for 10 min, and the supernatant was then distributed into glass vials and supplemented with different concentrations of mucosal sugar monosaccharides, glucose, mucin or nothing (no-amendment control) (all amendment chemicals were from Sigma-Aldrich, except D(+)-galactose which was purchased from Carl Roth GmbH) (Fig. 1a,c). After incubation for 6 h at 37 °C, glycerol was added (to achieve a final concentration of 20% (v/v) of glycerol in the microcosms) and the vials were crimp-sealed with rubber stoppers and stored at −80 °C until further processing. Prior to glycerol addition, subsamples of the biomass were collected, pelleted and supernatants stored at −80 °C for HILIC LC-MS/MS measurements. Pellets were washed with PBS to remove D2O and were fixed in 3% formaldehyde for 2 h at 4 °C and stored in 50% PBS/50% ethanol solution at −20 °C until further use. A total of three biological replicates were established using starting material pooled from three animals each (experiments MonoA, MonoB and MonoC). For the MonoA and MonoB experiments, microcosms were established for all the different concentrations of monosaccharides tested (Fig. 1c), while for MonoC only the highest concentrations of monosaccharides tested in incubations MonoA and MonoB were supplemented. Note that analysis of mucin-amended sorted fractions has been published elsewhere35. Since mucin contains all the monosaccharides included in this study, it constitutes an important control, and therefore we processed the sequencing data from mucin sorts in parallel with our samples and included it in our analyses (Fig. 2).
    Mass spectrometric analysis of mucosal monossaccharides
    Hydrophilic interaction chromatography (HILIC) LC-MS/MS was used for the measurement of mucosal monosaccharides in microcosm supernatants. Frozen samples were thawed at room temperature and centrifuged for 10 min at 18.000 × g and 4 °C. Supernatants were then diluted 1:50 with acetonitrile:water (1:1; v/v) and a volume of 3 µl was injected onto the chromatographic column. The UHPLC system (UltiMate 3000, Thermo Scientific) was coupled to a triple quadrupole mass spectrometer (TSQ Vantage, Thermo Scientific) by an electrospray ionization interface. Hydrophilic interaction chromatographic separation was realized on a Luna aminopropyl column (3 µm, 150 × 2 mm; Phenomenex, Torrance, CA) at a flow rate of 0.25 ml/min. Eluent A consisted of 95% water and 5% acetonitrile with 20 mM ammonium acetate and 40 mM ammonium hydroxide as additives and eluent B of 95% acetonitrile and 5% water. A multi-step gradient was optimized as follows: 100% B until minute 2, then linearly decreased to 80% B until minute 20 and further to 0% B until minute 25. The column was kept at 0% B for 4 min before it was equilibrated for 5 min at the initial conditions. The column temperature was maintained at 40 °C. The mass spectrometer was operated in multiple reaction monitoring (MRM) mode. Electrospray ionization (ESI) was optimized as follows: spray voltage 2800 V (positive mode) and 3000 V (negative mode); vaporizer temperature 250 °C; sheath gas pressure 30 Arb; ion sweep gas pressure 2 Arb; auxiliary gas pressure 10 Arb; capillary gas temperature 260 °C. Mass spectrometric parameters were optimized by direct injection and are reported together with the retention times of individual sugars in Supplementary Table 6. Spiking experiments and regular quality control checks were conducted to evaluate and ensure the systems’ proper performance.
    Confocal Raman microspectroscopy and spectral processing of fixed samples
    Formaldehyde-fixed samples were spotted on aluminum-coated slides (Al136; EMF Corporation) and washed by dipping into ice-cold Milli-Q (MQ) water (Millipore) to remove traces of buffer components. Individual cells were observed under a 100×/0.75 NA microscope objective. Single microbial cell spectra were acquired using a LabRAM HR800 confocal Raman microscope (Horiba Jobin-Yvon) equipped with a 532-nm neodymium-yttrium aluminum garnet (Nd:YAG) laser and either 300 grooves/mm diffraction grating. Spectra were acquired in the range of 400–3200 cm−1 for 30 s with 2.18 mW laser power. Raman spectra were background-corrected using the sensitive nonlinear iterative peak algorithm, and afterwards normalized to the sum of its absolute spectral intensity34. For quantification of the degree of D substitution in CH bonds (%CD), the bands assigned to C–D (2040–2,300 cm−1) and C–H (2,800–3,100 cm−1) were calculated using integration of the specified region34.
    Raman-activated cell sorting
    For RACS of D-labeled cells, 100 μl of glycerol-preserved microcosms containing non-fixed cells were pelleted, washed once with MQ water containing 0.3 M glycerol and finally resuspended in 0.5 ml of 0.3 M glycerol in MQ water. Cell sorting was performed in a fully automated manner using a Raman microspectroscope (LabRAM HR800, Horiba Scientific, France) combined with optical tweezers and a polydimethylsiloxane (PDMS) microfluidic sorter. The optical tweezers (1,064 nm Nd:YAG laser at 500 mW) and Raman (532 nm Nd:YAG laser at 45 mW or 80 mW; see below) laser were focused at the same position of the interface between the sample and sheath streams using a single objective (63x, 1.2 NA water-immersion, Zeiss). The in-house software based on the graphical user interface (GUI; written in MATLAB) detected the single-cell capture and its deuterium labeling status by calculating the cell index (PC = I1,620-1,670/Ifluid,1,620-1,670; where I is the integrated intensity between the indicated wavenumbers) and the labeling index (PL = I2040-2300/I1850-1900), respectively. We did not detect a significant change in the C–D peak region (2040–2300 cm−1) due the presence of 0.3 M of glycerol in the sorting fluid (added to minimize the osmotic stress when the sample was re-suspended for the RACS) (Supplementary Fig. 2a). Other spectral regions (e.g., 2700 cm−1) were slightly affected, but the sorting algorithm employed and the parameters described above take these small changes into account: the cell index PC (I1620–1670/Ifluid,1620–1670) used to detect single-cell capture was calculated by comparing the Raman intensity of cells measured in real-time to that of the working fluid measured in the calibration (conducted before the actual sorting). The threshold value for PL (I2040–2300/I1850–1900) was chosen based on the measurement of the control sample (i.e., sample incubated in non-D2O-containing medium). We used two software versions, each of which uses 45 mW (version 1) and 80 mW (version 2) Raman laser powers, respectively. The second version operates with higher power based on the addition of a laser shutter that blocks the Raman laser while the cells are being translocated, reducing the laser-induced damage on the cell. This version allows shorter acquisition times to be employed, and therefore higher throughput of the platform. The laser power for each version was chosen based on visual inspection of captured cells as described35. For the NeuAc and GlcNAc-amendment sorts (version 1, since version 2 was not yet available), PC value was calculated from cell spectra acquired for 2 s at the “capture location”, while the PL value was calculated from spectra obtained with a 5 s exposure time at the “evaluation location”. Fucose, GalNAc, and galactose-supplemented sorts were performed with version 2 of the platform, which in the meantime became available, significantly reducing sorting times. For these sorts both PC and PL values were simultaneously measured at the “capture location” with a 0.3 s exposure time. Only the D-labeled cells were translocated to the ‘evaluation location’ and immediately released. In order to determine the threshold PL above which a cell from the microcosms should be considered D-labeled (and therefore selected and sorted), cells from glucose-supplemented microcosms incubated in the absence or presence of D (0% versus 50% D2O in the microcosms) were run on the platform prior to sorting. The threshold PL number can vary across microcosms due to different microbial compositions and/or physiological status of cells present in the starting material, as well as due to different laser powers employed. Therefore we determined the PL threshold separately for both MonoA and MonoB incubations using both 45 and 80 mW laser power. Nevertheless, we reached a PL threshold of 6.19 for all sets of conditions and incubations tested (Supplementary Fig. 2b). We speculate this was due to the identical conditions used in both incubations and the fact that both communities have a similar microbial composition (Fig. 1e). To test the sorting accuracy of the platform on our samples, the negative control (H2O, glucose-supplemented microcosm) was re-run in the platform and sorted using the adopted threshold (PL = 6.19) (Supplementary Table 1). As expected, no cells were considered labeled by the platform under these conditions. Sorted fractions were nevertheless collected and sequenced as controls.
    Preparation of 16S rRNA gene amplicon libraries and 16S rRNA gene sequence analyses
    DNA extracted from the mouse colon microcosms or from mouse fecal pellets using a phenol-chloroform bead-beating protocol52 was used as a template for PCR. PCR amplification was performed with a two-step barcoding approach53. In the first-step PCR, the 16S rRNA gene of most bacteria was targeted using oligonucleotide primers (Supplementary Table 7) containing head adaptors (5′-GCTATGCGCGAGCTGC-3′) in order to be barcoded in a second step PCR53. Barcode primers consisted of the 16 bp head sequence and a sample-specific 8 bp barcode from a previously published list at the 5′ end. The barcoded amplicons were purified with the ZR-96 DNA Clean-up Kit (Zymo Research, USA) and quantified using the Quant-iT PicoGreen dsDNA Assay (Invitrogen, USA). An equimolar library was constructed by pooling samples, and the resulting library was sent for sequencing on an Illumina MiSeq platform at Microsynth AG (Balgach, Switzerland). Paired-end reads were quality-filtered and processed using QIIME 153,54. Reads were then clustered into operational taxonomic units (OTUs) of 97% sequence identity and screened for chimeras using UPARSE implemented in USEARCH v8.1.186155. OTUs were classified using the RDPclassifier v2.1256 as implemented in Mothur v1.39.557 using the Silva database v13258. Sequencing libraries were rarefied and analyzed using the vegan package (v2.4-3) of the software R (https://www.r-project.org/, R 3.4.0).
    Sequencing of mouse gut isolates
    Bacteroides sp. Isolate FP24 was isolated from YCFA agar plates (DSMZ medium 1611- YCFA MEDIUM (modified)) by plating ten-fold dilution series of a microcosms supplemented with 2 mg/ml of NeuAc (experiment MonoB)). Escherichia sp. isolate FP11 and Anaerotruncus sp. isolate FP23 were isolated from C. difficile minimal medium17 agar plates supplemented with 0.25% NeuAc or 0.25% GlcNAc by plating ten-fold dilution series of a microcosms supplemented with 2 mg/ml of NeuAc (experiment MonoB) or of a microcosms supplemented with 5 mg/ml of GlcNAc (experiment MonoA), respectively. Colonies were re-streak on the same medium plates until complete purity. Pure colonies were grown overnight in 10 mL of BHI medium (Brain heart infusion at 37 g per liter of medium) supplemented with: yeast extract, 5 g; Na2CO3, 42 mg; cysteine, 50 mg; vitamin K1, 1 mg; hemin, 10 µg. DNA was extracted from pelleted biomass using the QIAGEN DNAeasy Tissue and Blood kit (Qiagen, Austin, TX, USA) according to the manufacturer´s instructions. Sequencing libraries were prepared using the NEBNext® Ultra™ II FS DNA kit (Illumina) and sequenced in an Illumina MiSeq platform with 300-bp paired-end sequencing chemistry (Joint Microbiome Facility, University of Vienna and Medical University of Vienna, Austria). Reads were quality trimmed with the bbduk option of BBmap (v 34.00) at phrad score 15. Quality-trimmed reads were assembled with SPAdes (v 3.11.1)59. For isolate FP11, assembled reads were subsequently, iteratively (n = 6) reassembled with SPAdes using contigs of >1 kb from the previous assembly as “trusted contigs” for input and iterating kmers from 11 to 121 in steps of 10. CheckM (v1.0.6) assessment60 of these genomes is summarized in Supplementary Data 1.
    Mini-metagenome sequencing and genomic analyses
    Labeled RACS cells were collected into PCR tubes, lysed and subjected to whole-genome amplification using the Repli-g Single Cell Kit (QIAGEN), according to the manufacturer’s instructions. Shotgun libraries were generated using the amplified DNA from WGA reactions (sorted fractions) or DNA isolated using the phenol-chloroform method (initial microcosms) as a template and Nextera XT (Illumina) reagents. Libraries were sequenced with a HiSeq 3000 (Illumina) in 2 × 150 bp mode at the Biomedical Sequencing Facility, Medical University of Vienna, Austria. The sequence reads were quality trimmed and filtered using BBMap v34.00 (https://sourceforge.net/projects/bbmap/). The remaining reads were assembled de novo using SPAdes 3.11.159 in single-cell mode (k-mer sizes: 21, 35, 55). Binning of the assembled reads into metagenome-assembled genomes (MAGs) was performed with MetaBAT 2 (v2.12.1)61 using the following parameters: minContig 2000, minCV 1.0, minCVSum 1.0, maxP 95%, minS 60, and maxEdges 200. The quality and contamination of all MAGs were checked with CheckM 1.0.660 (Supplementary Data 1). MAGs >200 kb obtained from all samples were compared and de-replicated using dRep 1.4.362. Automatic genome annotation of contigs >2 kb within each de-replicated MAG was performed with RAST 2.063. Taxonomic classification of each MAG was obtained using GTDB-Tk64 (v0.1.3, gtdb.ecogenomic.org/).
    The relative abundance of each MAG on the initial microcosms was calculated based on metagenomic coverage. Filtered reads from each sequenced microcosm were mapped competitively against all retrieved MAGs using BBMap (https://sourceforge.net/projects/bbmap/). Read coverage was normalized by genome size and relative abundances of each genome in each sample were calculated based on the formula: covA = (bpA/gA)/(bpT/gT), where covA is the relative abundance of MAG A on a particular sample, bpA is the number of base pairs from reads matching MAG A, gA is the genome length of MAG A, bpT is the total number of base pairs from reads matching all MAGs recovered from that particular sample and gT is the sum of all MAGs genome lengths.
    For determination of the presence of encoded enzymes for catabolism of mucin monosaccharides among MAGs, predicted protein sequences from recovered MAGs were subject to local BLASTP analyses65, against a custom database. The database was composed of all enzymes involved initial hydrolysis and catabolism of mucosal sugar monosaccharides (Supplementary Data 2), which were previously curated from a total of 395 human gut bacteria15. A strict e-value threshold of 10−50 was used for all BLASTP analyses. During initial setup of the analysis pipeline, functional assignments of proteins that gave positive BLASTP hits were manually verified by examining annotations from RAST 2.0 and by performing BLASTP analyses against the NCBI-nr database (NCBIBlast 2.2.26).
    To verify the enrichment of a selected dataset of mucin-degrading enzymes35 in the assemblies derived from sorted fractions, BLASTX analyses of scaffolds from each fraction as well as from the initial microcosms metagenomes (unsorted) were performed against the selected mucin-degrading enzyme sequences15 (Supplementary Table 3). An e-value threshold of 10−50 was also used for all BLASTX analyses.
    Phylogenomic analyses
    A concatenated marker alignment of 34 single-copy genes was generated for all MAGs using CheckM 1.0.660 and the resulting alignment was used to calculate a tree with the approximate maximum-likelihood algorithm of FastTree 2.1.1066. Phylogenomic trees were visualized and formatted using iTOL v4 (https://itol.embl.de/). In order to identify the closest relative for each MAG, the query MAG and close reference genomes (based on the generated phylogenomic tree) were compared using dRep 1.4.362. Compared genomes with a whole-genome-based average nucleotide identity (ANIm) >99%39 were considered to be the same population genome.
    High-resolution mass spectrometric analyses
    Glycerol-preserved biomass (150 μL) from microcosm incubations was pelleted and suspended in 50 μL of lysis buffer (1% sodium dodecyl sulfate (SDS), 10 mM TRIS base, pH 7.5). Protein lysates were subjected to SDS polyacrylamide gel electrophoresis followed by in-gel tryptic digestion. Proteins were stained with colloidal Coomassie Brilliant Blue G-250 (Roth, Kassel, Germany) and detained with Aqua dest. Whole protein bands were cut into gel pieces and in-gel-digestion with trypsin 30 µL (0.005 µg/µL) was performed overnight. Extracted peptides where dried and resolved in 0.1% formic acid and purified by ZipTip® treatment (EMD Millipore, Billerica, MA, USA).
    In total, 5 µg of peptides were injected into nanoHPLC (UltiMate 3000 RSLCnano, Dionex, Thermo Fisher Scientific), followed by separation on a C18-reverse phase trapping column (C18 PepMap100, 300 µm × 5 mm, particle size 5 µm, nano viper, Thermo Fischer Scientific), followed by separation on a C18-reverse phase analytical column (Acclaim PepMap® 100, 75 µm × 25 cm, particle size 3 µm, nanoViper, Thermo Fischer Scientific). Mass spectrometric analysis of eluted peptides where performed on a Q Exactive HF mass spectrometer (Thermo Fisher Scientific, Waltham, MA, USA) coupled with a TriVersa NanoMate (Advion, Ltd., Harlow, UK) source in LC chip coupling mode. LC Gradient, ionization mode and mass spectrometry mode were performed as described before67. Briefly, peptide lysate were injected into a Nano-HPLC and trapped in a C18-reverse phase column (Acclaim PepMap® 100, 75 µm × 2 cm, particle size 3 µM, nanoViper, Thermo Fisher) for 5 min. Peptide separation was followed by a two-step gradient in 90 min from 4 to 30% of B (B: 80% acetonitrile, 0.1% formic acid in MS-grade water) and then 30 min from 30 to 55% of B. The temperature of the separation column was set to 35 °C and the flow rate was 0.3 µL/min. The eluted peptides were ionized and measured. The MS was set to a full MS/dd-MS2 mode scan with positive polarity. The full MS scan was adjusted to 120,000 resolution, the automatic gain control (AGC) target of 3 × 106 ions, maximum injection time for MS of 80 s and a scan range of 350 to 1550 m/z. The dd-MS2 scan was set to a resolution of 15,000 with the AGC target of 2 × 105 ions, a maximum injection time for 120 ms, TopN 20, isolation window of 1.6 m/z, scan range of 200 to 2000 m/z and a dynamic exclusion of 30 s.
    Raw data files were converted into mzML files and searched with MS-GF + against a database obtained from microcosm metagenomes composed of 276,284 predicted protein-encoding sequences. The following parameters were used for peptide identification: enzyme specificity was set to trypsin with one missed cleavage allowed using 10 ppm peptide ion tolerance and 0.05 Da MS/MS tolerance. Oxidation (methionine) and carbamidomethylation (cysteine) were selected as modifications. False discovery rates (FDR) were determined with the node Percolator68. Proteins were considered as identified when at least one unique peptide passed a FDR of 5%.
    The MetaProSIP toolshed69 embedded in the Galaxy framework70 (v2.3.2, http://galaxyproject.org/) was used to identify the incorporation of stable isotopes into peptides. MetaProSIP calculates the relative isotope abundance (RIA) on detected isotopic mass traces (m/z tolerance of ±10 ppm, intensity threshold of 1000, and an isotopic trace correlation threshold of 0.7).
    In vitro growth experiments
    A. muciniphila strain Muc (DSM 22959), Ruthenibacterium lactatiformans strain 585-1 (DSM 100348) and Alistipes timonensis strain JC136 (DSM 25383) were obtained from DSMZ. Muribaculum intestinale strain YL27 (DSM 28989) was kindly provided by Prof. Bärbel Stecher (Max-von-Pettenkofer Institute, LMU Munich, Germany). Bacteroides sp. FP24 was isolated from YCFA agar plates (DSMZ medium 1611-YCFA MEDIUM (modified)). All strains were grown in reduced A II medium71 consisting of (per liter of medium): BHI, 18.5 g; yeast extract, 5 g; trypticase soy broth, 15 g; K2HPO4, 2.5 g; hemin, 10 µg; glucose, 0.5 g; Na2CO3, 42 mg; cysteine, 50 mg; menadione, 5 µg; fetal calf serum (complement-inactivated), 3% (vol/vol). For A. muciniphila cultivation, the growth medium was supplemented with 0.025% (w/v) of mucin. C. difficile was grown in BHI medium (37 g per liter of medium) supplemented with: yeast extract, 5 g; Na2CO3, 42 mg; cysteine, 50 mg; vitamin K1, 1 mg; hemin, 10 µg. All strains were grown at 37 °C under anaerobic conditions until stationary phase, and then serially diluted and plated into media agar plates in order to determine the number of viable cells present in 1 ml of stationary phase-culture. For mixed-growth experiments, the culture volume equivalent to 1 × 106 CFU of each strain was pelleted, cells were washed with PBS, mixed in equal proportions and finally resuspended in 100 μl of PBS. This bacterial mixture containing a total of 5 × 106 BacMix cells was then used to inoculate 2.5 ml of A II medium (diluted two fold in 2× PBS) supplemented or not with 0.25% (10 mM) carbon source (0.125% or 4 mM of NeuAc and 0.125% or 6 mM of GlcNAc). After 12 h, the same tube was inoculated with 1 × 106 C. difficile CFU and bacterial growth was followed by measuring the OD at 600 nm every hour until stationary phase. At three distinct points of the C. difficile growth curve—lag (t12, right after C. difficile addition), mid-exponential (t18) and early stationary phase (t21)—a sample aliquot was collected and ten-fold dilutions were plated in a C. difficile selective medium72. This selective medium (CCFA) includes antibiotics such as cycloserine and cefoxitn at concentrations that are inhibitory to most gut organisms, except for C. difficile, allowing to determine total C. difficile counts. A second aliquot was immediately pelleted and the pellet was stored at −80 °C for RNA extraction.
    Quantitative PCR of C. difficile 16S rRNA gene copy number density
    DNA was extracted from 100 mg of mouse fecal pellet using the QIAGEN DNAeasy Tissue and Blood kit (Qiagen, Austin, TX, USA) according to the manufacturer´s instructions, with an additional step of mechanical cell disruption by bead beating (30 s at 6.5 m/s) right after addition of kit lysis buffer AL. Extracted DNA (2 μl) was subjected to quantitative PCR using 0.2 μM of primers specifically targeting the C. difficile 16S rRNA gene73 (Supplementary Table 7) and 1× SYBR green Master Mix (Bio-Rad) in a total reaction volume of 20 μl. Standard curves were generated from DNAs extracted from fecal pellets of SPF (uninfected) mice spiked in with different known numbers of C. difficile cells (102, 103, 104, 105, 106, 107, and 108) as described in Kubota et al., 2014. Amplification and detection were performed using a CFX96™ Real-Time PCR Detection System (Bio-Rad) using the following cycling conditions: 95 °C for 5 min, followed by 40 cycles of 95 °C for 15 s, 56 °C for 20 s, and 72 °C for 30 s. To determine the specificity of PCR reactions, melt curve analysis was carried out after amplification by slow cooling from 95 to 60 °C, with fluorescence collection at 0.3 °C intervals and a hold of 10 s at each decrement. Only assays with amplification efficiencies above 80% were considered for analysis.
    RNA extraction and quantitative real-time PCR
    Total nucleic acids (TNA) were extracted from mouse fecal pellets or from in vitro cultures using a phenol-chloroform bead-beating protocol52. RNA was purified from DNAse-treated TNA fractions using the GeneJET Cleanup and Concentration micro kit (Thermo Fisher Scientific). cDNA was synthesized from 0.5 μg of total RNA with 1 μl of random hexamer oligonucleotide primers. Samples were heated for 5 min at 70 °C. After a slow cooling, 2 μl of deoxynucleoside triphosphates (dNTP; 2.5 mM each), 40 units of recombinant ribonuclease inhibitor (RNaseOUT) and 4 μl of reverse transcription (RT) buffer were added and cDNAs were synthesized for 2 h at 50 °C using 200 units SuperScript™ III Reverse Transcriptase (all reagents used in cDNA synthesis were from Thermo Fisher Scientific). Real-time quantitative PCR was performed in a 20-μl reaction volume containing 2 μl of cDNA, 1x SYBR green Master Mix (Bio-Rad) and 0.2 μM of gene-specific C. difficile primers targeting the following genes: DNA polymerase III PolC-type dnaF74, nanA, nanT17 and nagB (this work; Supplementary Table 7). Amplification and detection were performed as described above. In each sample, the quantity of cDNAs of a gene was normalized to the quantity of cDNAs of the C. difficile DNA polymerase lII gene74 (dnaF). The relative change in gene expression was recorded as the ratio of normalized target concentrations (threshold cycle [ΔΔCT] method75). Fold changes were normalized to in vitro growths in C. difficile minimal medium containing 0.5% glucose17. To determine the specificity of PCR reactions, melt curve analysis was carried out after amplification by slow cooling from 95 to 60 °C, with fluorescence collection at 0.3 °C intervals and a hold of 10 s at each decrement. Only assays with amplification efficiencies above 80% were considered for analysis.
    Murine in vivo adoptive transfer experiments
    Female C57BL/6N 6-8 weeks old mice (n = 33 total) were purchase from Janvier Labs. Animals were kept in isolated, ventilated cages under specific pathogen-free conditions at the animal facility of the Max F. Perutz Laboratories, University of Vienna, Austria, with controlled temperature of 21 ± 1 °C and humidity of 50 ± 10%, in a 12-h light/dark cycle. Mice received a standard diet (V1124-300; Ssniff, Soest, Germany) and autoclaved water ad libitum. Mice were administered antibiotics (0.25 mg/ml clindamycin (Sigma-Aldrich) for six days in drinking water) and subsequently assigned randomly to one of two groups. One day following antibiotic cessation, mice from each group were split into 3 cages (to minimize the cage effect) and each mouse received either 5,000,000 CFU of a 5-bacteria suspension (BacMix, containing equal numbers of A. muciniphila strain Muc (DSM 22959), Ruthenibacterium lactatiformans strain 585-1 (DSM 100348), Alistipes timonensis strain JC136 (DSM 25383), Muribaculum intestinale strain YL27 (DSM 28989), and Bacteroides sp. isolate FP24) or vehicle (PBS) by gavage (Fig. 5a). At the time of BacMix and BacMixC administration, the mouse diet was switched from a standard diet (V1124-300; Ssniff, Soest, Germany) to a isocaloric polysaccharide-deficient chow76 with sucrose but no cellulose or starch (Ssniff, Soest, Germany). For the BacMixC adoptive transfer, each mouse (n = 10 per group) received 5,000,000 CFU of a 3-bacteria suspension (BacMixC, containing equal numbers of Anaerotruncus sp. isolate FP23; Lactobacillus hominis strain DSM 23910 and of Escherichia sp. isolate FP11) or vehicle (PBS) by gavage (Supplementary Fig. 7). One day after BacMix or BacMixC administration, mice were challenged with 1,000,000 CFU of C. difficile strain 630 deltaErm77. A. muciniphila, R. lactatiformans and M. intestinale were grown in reduced A II medium (supplemented with 0.025% mucin for A. muciniphila). Anaerotruncus sp. isolate FP23, A. timonensis and Bacteroides sp. isolate FP24 were grown in PYG (DSMZ medium 104). Lactobacillus hominis and Escherichia sp. isolate FP11 were grown in YCFA medium (DSMZ medium 1611). C. difficile was grown in BHI medium (37 g per liter of medium). All bacteria were grown under anaerobic conditions (5% H2, 10% CO2, rest N2) at 37 °C and resuspended in anaerobic PBS prior to administration to animals. C. difficile titers were quantified in fecal samples obtained from mice 24, 48, 72, and 120 h after infection by overnight cultivation in C. difficile selective agar plates72. Animals were monitored throughout the entire experiment and weight loss was recorded.
    Measurement of mucus thickness and goblet cell volume
    Segments of mouse colon (approximately 10 mm long) were fixed in 2% PFA in phosphate-buffered saline (PBS) for 12 h at 4 °C. Samples were washed with 1× PBS and then stored in 70% ethanol at 4 °C until embedding. For embedding, samples were immersed in 3 changes of xylene for 1 h each, then immersed in 3 changes of molten paraffin wax (Paraplast, Electron Microscopy Sciences) at 56–58 °C for one hour each. Blocks were allowed to harden at room temperature. Sections were cut to 4 μm thickness using a Leica microtome (Leica Microsystems) and were floated on a water bath at 40–45 °C, then transferred to slides, dried, and stored at room temperature. In preparation for staining, slides were de-paraffinized by heating at 60 °C for 30 min followed by immersion in 2 changes of xylene for 5 min each, then in 2 changes of 100% ethanol for 1 minute each, then rehydrated through 80%, and 70% ethanol for 1 minute each. Slides were then dipped in water, drained, air-dried and a drop of Alcian Blue stain (Sigma Aldrich) applied on top. Samples were incubated with Alcian Blue for 20 min at room temperature and then washed in water to remove the excess of stain. Samples were mounted in Vectashield Hardset™ Antifade Mounting Medium (Vector Laboratories) and visualized using a Leica Confocal scanning laser microscope (Leica TCS SP8X, Germany). For measurements of the width of the mucus layer and determination of goblet cell volume per crypt, ImageJ software (https://imagej.nih.gov/ij/, 1.48 v) was used.
    Histology and histopathological scoring
    Mouse colons were flushed with cold PBS to remove all contents, and the entire colon was rolled into Swiss rolls. The tissues were fixed in 2% PFA for 12 h at 4 °C and then washed in 1x PBS and transferred to 70% ethanol until embedding. Swiss rolls were embedded in the same manner as described above for segments of mouse colon. Paraffin-embedded, PFA fixed tissues were sectioned at 4.5 μm. Tissue sections were de-paraffinized and hematoxylin and eosin stained (Mayer’s Hematoxylin, Thermo Scientific; Eosin 1%, Morphisto, Germany). Histopathological analyses were performed using a semi-quantitative scoring system78 that evaluated the severity of crypt damage and cellular infiltration, epithelial erosion and tissue thickening using a severity score from 0 to 3 (0 = intact, 1 = mild, 2 = moderate, 3 = severe), and those scores were multiplied by a score for percent involvement (0 = 0%, 1 = 1–25%, 2 = 26–50%, 3 = 50–100%). A trained and blinded scientist performed the scoring. Representative images were acquired using an Olympus CKX53 microscope and Olympus SC50 camera.
    Quantification of C. difficile toxin TcdB
    Levels of TcdB in mouse colon contents were quantified relative to a standard curve of purified TcdB using an ELISA assay kit (“Separate detection of C. difficile toxins A and B”, TGC Biomics) according to the manufacturer’s instructions. For each mouse, approximately 10 mg of colon content were used in the assay. The limit of detection for the assay in our conditions was determined to be 5.14 ng of TcdB per gram of colon content (Supplementary Fig. 8c). One of the mice from the BacMix group had toxin levels below the detection limit and was therefore excluded from analysis.
    Reporting summary
    Further information on research design is available in the Nature Research Reporting Summary linked to this article. More

  • in

    Mechanisms of possible self-limitation in the invasive Asian shore crab Hemigrapsus sanguineus

    1.
    Bowman, W.D., Hacker, S.D., Cain, M.L. Ecology, 4th Edn. (Sinauer Press, 2017).
    2.
    Eggleston, D. B., Lipcius, R. N. & Hines, A. H. Density-dependent predation by blue crabs upon infaunal clam species with contrasting distribution and abundance patterns. Mar. Ecol. Progr. Ser. 85, 55–68 (1992).
    ADS  Article  Google Scholar 

    3.
    Boström-Einarsson, L., Bonin, M. C., Munday, P. L. & Jones, G. P. Strong intraspecific competition and habitat selectivity influence abundance of a coral-dwelling damselfish. J. Exp. Mar. Biol. Ecol. 448, 85–92 (2013).
    Article  Google Scholar 

    4.
    Ruggerone, G.T., Zimmermann, M., Myers, K.W., Nielsen, J.L., & Rogers, D.E. Competition between Asian pink salmon (Oncorhynchus gorbuscha) and Alaskan sockeye salmon (O. nerka) in the North Pacific Ocean. Fish. Oceanogr. 12, 209–219 (2003).

    5.
    Greer, A. L., Briggs, C. J. & Collins, J. P. Testing a key assumption of host-pathogen theory: Density and disease transmission. Oikos 117, 1667–1673 (2008).
    Article  Google Scholar 

    6.
    Turchin, P. Does population ecology have general laws?. Oikos 94, 17–26 (2001).
    Article  Google Scholar 

    7.
    Yenni, G., Adler, P. B. & Ernest, S. M. Strong self-limitation promotes the persistence of rare species. Ecology 93, 456–461 (2012).
    PubMed  Article  Google Scholar 

    8.
    Weis, A. E., Simms, E. L. & Hochberg, M. E. Will plant vigor and tolerance be genetically correlated? Effects of intrinsic growth rate and self-limitation on regrowth. Evol. Ecol. 14, 331–352 (2000).
    Article  Google Scholar 

    9.
    Marino, A., Rodríguez, V. & Pazos, G. Resource-defense polygyny and self-limitation of population density in free-ranging guanacos. Behav. Ecol. 27, 757–765 (2016).
    Article  Google Scholar 

    10.
    Chamaillé-Jammes, S., Fritz, H., Valeix, M., Murindagomo, F. & Clobert, J. Resource variability, aggregation and direct density dependence in an open context: The local regulation of an African elephant population. J. Anim. Ecol. 77, 135–144 (2008).
    PubMed  Article  Google Scholar 

    11.
    Westoby, M. The self-thinning rule. Adv. Ecol. Res. 14, 167–225 (1984).
    Article  Google Scholar 

    12.
    Sedinger, J. S., Herzog, M. P., Person, B. T., Kirk, M. T., Obritchkewitch, T., Martin, P. P., & Bosque, C. Large-scale variation in growth of Black Brant goslings related to food availability. Auk 118, 1088–1095 (2001).

    13.
    Marschall, E. A. & Crowder, L. B. Density-dependent survival as a function of size in juvenile salmonids in streams. Can. J. Fish. Aquat. Sci. 52, 136–140 (1995).
    Article  Google Scholar 

    14.
    Zheng, X., Huang, L., Huang, B. & Lin, Y. Factors regulating population dynamics of the amphipod Ampithoe valida in a eutrophic subtropical coastal lagoon. Acta Oceanol. Sin. 32, 56–65 (2013).
    ADS  CAS  Article  Google Scholar 

    15.
    Li, G. Y., & Zhang, Z. Q. Does size matter? Fecundity and longevity of spider mites (Tetranychus urticae) in relation to mating and food availability. Syst. Appl. Acarol.-UK 23, 1796–1808 (2018).

    16.
    Niu, H., Zhao, L. & Sun, J. Phenotypic plasticity of reproductive traits in response to food availability in invasive and native species of nematode. Biol. Inv. 15, 1407–1415 (2013).
    Article  Google Scholar 

    17.
    Cannizzo, Z. J., Lang, S. Q., Benitez-Nelson, B. & Griffen, B. D. An artificial habitat increases the reproductive fitness of a range-shifting species within a newly colonized ecosystem. Sci. Rep. 10, 1–13 (2020).
    Article  CAS  Google Scholar 

    18.
    Zera, A. J. & Harshman, L. G. The physiology of life history trade-offs in animals. Annu. Rev. Ecol. Evol. Syst. 32, 95–126 (2001).
    Article  Google Scholar 

    19.
    Strayer, D. L., D’Antonio, C. M., Essl, F., Fowler, M. S., Geist, J., Hilt, S., & Latzka, A. W. Boom‐bust dynamics in biological invasions: Towards an improved application of the concept. Ecol. Lett. 20, 1337–1350 (2017).

    20.
    Jaćimović, M. et al. Boom-bust like dynamics of invasive black bullhead (Ameiurus melas) in Lake Sava (Serbia). Fish. Manag. Ecol. 26, 153–164 (2019).
    Article  Google Scholar 

    21.
    Alcorlo, P., Geiger, W., & Otero, M. Reproductive biology and life cycle of the invasive crayfish Procambarus clarkii (Crustacea: Decapoda) in diverse aquatic habitats of South-Western Spain: Implications for population control. Fund. Appl. Limnol./Arch. Hydrobiol. 173, 197–212 (2008).

    22.
    Melero, Y., Robinson, E., & Lambin, X. Density-and age-dependent reproduction partially compensates culling efforts of invasive non-native American mink. Biol. Invasions 17, 2645–2657.

    23.
    Yoshida, K., Hoshikawa, K., Wada, T. & Yusa, Y. Patterns of density dependence in growth, reproduction and survival in the invasive freshwater snail Pomacea canaliculata in Japanese rice fields. Freshw. Biol. 58, 2065–2073 (2013).
    Article  Google Scholar 

    24.
    Williams, A. B. & McDermott, J. J. An eastern United States record for the western Indo-Pacific crab, Hemigrapsus sanguineus (Crustacea: Decapoda: Grapsidae). Proc. Biol. Soc. Wash. 103, 108–109 (1990).
    Google Scholar 

    25.
    Breton, G., Faasse, M., Noël, P. & Vincent, T. A new alien crab in Europe: Hemigrapsus sanguineus (Decapoda: Brachyura: Grapsidae). J. Crustacean Biol. 22, 184–189 (2002).
    Article  Google Scholar 

    26.
    Blakeslee, A. M., Kamakura, Y., Onufrey, J., Makino, W., Urabe, J., Park, S., & Miura, O. Reconstructing the invasion history of the Asian shorecrab, Hemigrapsus sanguineus (De Haan 1835) in the Western Atlantic. Mar. Biol. 164, 47 (2017).

    27.
    Lohrer, A. M. & Whitlatch, R. B. Interactions among aliens: Apparent replacement of one exotic species by another. Ecology 83, 719–732 (2002).
    Article  Google Scholar 

    28.
    Kraemer, G. P., Sellberg, M., Gordon, A. & Main, J. Eight-year record of Hemigrapsus sanguineus (Asian shore crab) invasion in western Long Island Sound estuary. Northeast. Nat. 14, 207–224 (2007).
    Article  Google Scholar 

    29.
    Epifanio, C. E. Invasion biology of the Asian shore crab Hemigrapsus sanguineus: A review. J. Exp. Mar. Biol. Ecol. 441, 33–49 (2013).
    Article  Google Scholar 

    30.
    Lord, J. P. & Williams, L. M. Increase in density of genetically diverse invasive Asian shore crab (Hemigrapsus sanguineus) populations in the Gulf of Maine. Biol. Invasions 19, 1153–1168 (2017).
    PubMed  PubMed Central  Article  Google Scholar 

    31.
    Brousseau, D. J., Kriksciun, K. & Baglivo, J. A. Fiddler crab burrow usage by the Asian crab, Hemigrapsus sanguineus, in a Long Island Sound salt marsh. Northeast. Nat. 10, 415–420 (2003).
    Article  Google Scholar 

    32.
    O’Connor, N. J. Invasion dynamics on a temperate rocky shore: from early invasion to establishment of a marine invader. Biol. Invasions 16, 73–87 (2014).
    Article  Google Scholar 

    33.
    O’Connor, N. J. Changes in population sizes of Hemigrapsus sanguineus (Asian Shore Crab) and resident crab species in southeastern New England (2010–2016). Northeast. Nat. 25, 197–201 (2018).
    Article  Google Scholar 

    34.
    Schab, C. M., Park, S., Waidner, L. A. & Epifanio, C. E. Return of the native: Historical comparison of invasive and indigenous crab populations near the mouth of Delaware Bay. J. Shellfish Res. 32, 751–758 (2013).
    Article  Google Scholar 

    35.
    Bloch, C. P., Curry, K. D., Fisher-Reid, M. C. & Surasinghe, T. D. Population Decline of the Invasive Asian Shore Crab (Hemigrapsus sanguineus) and Dynamics of Associated Intertidal Invertebrates on Cape Cod, Massachusetts. Northeast. Nat. 26, 772–784 (2019).
    Article  Google Scholar 

    36.
    Kraemer, G. P. Changes in population demography and reproductive output of the invasive Hemigrapsus sanguineus (Asian Shore Crab) in the Long Island Sound from 2005 to 2017. Northeast. Nat. 26, 81–94 (2019).
    Article  Google Scholar 

    37.
    Stentiford, G. D., Bateman, K. S., Dubuffet, A., Chambers, E., & Stone, D. M. Hepatospora eriocheir (Wang and Chen, 2007) gen. et comb. nov. infecting invasive Chinese mitten crabs (Eriocheir sinensis) in Europe. J. Invertebr. Pathol. 108, 156–166 (2011).

    38.
    Bateman, A. W., Buttenschön, A., Erickson, K. D. & Marculis, N. G. Barnacles vs bullies: Modelling biocontrol of the invasive European green crab using a castrating barnacle parasite. Theor. Ecol. 10, 305–318 (2017).
    Article  Google Scholar 

    39.
    Bojko, J., Stebbing, P. D., Dunn, A. M., Bateman, K. S., Clark, F., Kerr, Stewart-Clark, S., Johannesen, Á., & Stentiford, G. D. Green crab Carcinus maenas symbiont profiles along a North Atlantic invasion route. Dis. Aquat. Organ. 128, 147–168 (2018).

    40.
    Jensen, G. C., McDonald, P. S. & Armstrong, D. A. East meets west: competitive interactions between green crab Carcinus maenas, and native and introduced shore crab Hemigrapsus spp. Mar. Ecol. Progr. Ser. 225, 251–262 (2002).
    ADS  Article  Google Scholar 

    41.
    DeRivera, C. E., Ruiz, G. M., Hines, A. H. & Jivoff, P. Biotic resistance to invasion: Native predator limits abundance and distribution of an introduced crab. Ecology 86, 3364–3376 (2005).
    Article  Google Scholar 

    42.
    Kim, A. K. & O’Connor, N. J. Early stages of the Asian shore crab Hemigrapsus sanguineus as potential prey for the striped killifish Fundulus majalis. J. Exp. Mar. Biol. Ecol. 346, 28–35 (2007).
    Article  Google Scholar 

    43.
    Brousseau, D. J., Murphy, A. E., Enriquez, N. P. & Gibbons, K. Foraging by two estuarine fishes, Fundulus heteroclitus and Fundulus majalis, on juvenile Asian shore crabs (Hemigrapsus sanguineus) in Western Long Island Sound. Estuar. Coast. 31, 144–151 (2008).
    Article  Google Scholar 

    44.
    Savaria, M. C. & O’Connor, N. J. Predation of the non-native Asian shore crab Hemigrapsus sanguineus by a native fish species, the cunner (Tautogolabrus adspersus). J. Exp. Mar. Biol. Ecol. 449, 335–339 (2013).
    Article  Google Scholar 

    45.
    Griffen, B. D. & Delaney, D. G. Species invasion shifts the importance of predator dependence. Ecology 88, 3012–3021 (2007).
    PubMed  Article  Google Scholar 

    46.
    Keogh, C. L., Miura, O., Nishimura, T. & Byers, J. E. The double edge to parasite escape: invasive host is less infected but more infectable. Ecology 98, 2241–2247 (2017).
    PubMed  Article  Google Scholar 

    47.
    Kroft, K. L. & Blakeslee, A. M. Comparison of parasite diversity in native panopeid mud crabs and the invasive Asian shore crab in estuaries of northeast North America. Aquat. Invasions 11, 287–301 (2016).
    Article  Google Scholar 

    48.
    Blakeslee, A. M., Keogh, C. L., Byers, J. E., Lafferty, A. M. K. K. D. & Torchin, M. E. Differential escape from parasites by two competing introduced crabs. Mar. Ecol. Progr. Ser. 393, 83–96 (2009).
    ADS  Article  Google Scholar 

    49.
    Lohrer, A. M., Fukui, Y., Wada, K. & Whitlatch, R. B. Structural complexity and vertical zonation of intertidal crabs, with focus on habitat requirements of the invasive Asian shore crab, Hemigrapsus sanguineus (de Haan). J. Exp. Mar. Biol. Ecol. 244, 203–217 (2000).
    Article  Google Scholar 

    50.
    Ledesma, M. E. & O’Connor, N. J. Habitat and diet of the non-native crab Hemigrapsus sanguineus in southeastern New England. Northeast. Nat. 8, 63–78 (2001).
    Article  Google Scholar 

    51.
    Brousseau, D. J. & Goldberg, R. Effect of predation by the invasive crab Hemigrapsus sanguineus on recruiting barnacles Semibalanus balanoides in western Long Island Sound, USA. Mar. Ecol. Progr. Ser. 339, 221–228 (2007).
    ADS  Article  Google Scholar 

    52.
    Brousseau, D. J. & Baglivo, J. A. Laboratory investigations of food selection by the Asian shore crab, Hemigrapsus sanguineus: Algal versus animal preference. J. Crustacean Biol. 25, 130–134 (2005).
    Article  Google Scholar 

    53.
    Griffen, B. D. Linking individual diet variation and fecundity in an omnivorous marine consumer. Oecologia 174, 121–130 (2014).
    ADS  PubMed  Article  Google Scholar 

    54.
    Riley, M. E., Vogel, M. & Griffen, B. D. Fitness-associated consequences of an omnivorous diet for the mangrove tree crab Aratus pisonii. Aquat. Biol. 20, 35–43 (2014).
    Article  Google Scholar 

    55.
    Griffen, B. D. & Norelli, A. P. Spatially variable habitat quality contributes to within-population variation in reproductive success. Ecol. Evol. 5, 1474–1483 (2015).
    PubMed  PubMed Central  Article  Google Scholar 

    56.
    Griffen, B. D. & Riley, M. E. Potential impacts of invasive crabs on one life history strategy of native rock crabs in the Gulf of Maine. Biol. Invasions 17, 2533–2544 (2015).
    Article  Google Scholar 

    57.
    Belgrad, B. A. & Griffen, B. D. The influence of diet composition on fitness of the blue crab, Callinectes sapidus. PLoS ONE 11, e0145481 (2016).
    PubMed  PubMed Central  Article  CAS  Google Scholar 

    58.
    Griffen, B. D., Vogel, M., Goulding, L. & Hartman, R. Energetic effects of diet choice by invasive Asian shore crabs: Implications for persistence when prey are scarce. Mar. Ecol. Progr. Ser. 522, 181–192 (2015).
    ADS  Article  Google Scholar 

    59.
    Griffen, B. D. The timing of energy allocation to reproduction in an important group of marine consumers. PLoS ONE 13, e0199043 (2018).
    PubMed  PubMed Central  Article  CAS  Google Scholar 

    60.
    Guiñez, R., Petraitis, P. S. & Castilla, J. C. Layering, the effective density of mussels and mass-boundary curves. Oikos 110, 186–190 (2005).
    Article  Google Scholar 

    61.
    Bertness, M. D., Gaines, S. D. & Yeh, S. M. Making mountains out of barnacles: The dynamics of acorn barnacle hummocking. Ecology 79, 1382–1394 (1998).
    Article  Google Scholar 

    62.
    Guiñez, R. & Castilla, J. C. An allometric tridimensional model of self-thinning for a gregarious tunicate. Ecology 82, 2331–2341 (2001).
    Article  Google Scholar 

    63.
    Alunno-Bruscia, M., Petraitis, P. S., Bourget, E. & Fréchette, M. Body size–density relationship for Mytilus edulis in an experimental food-regulated situation. Oikos 90, 28–42 (2000).
    Article  Google Scholar 

    64.
    Weller, D. E. A reevaluation of the‐3/2 power rule of plant self‐thinning. Ecol. Monogr. 57, 23–43 (1987).

    65.
    Griffen, B. D. & Byers, J. E. Community impacts of two invasive crabs: the interactive roles of density, prey recruitment, and indirect effects. Biol. Invasions 11, 927–940 (2009).
    Article  Google Scholar 

    66.
    Lohrer, A. M. & Whitlatch, R. B. Relative impacts of two exotic brachyuran species on blue mussel populations in Long Island Sound. Mar. Ecol. Progr. Ser. 227, 135–144 (2002).
    ADS  Article  Google Scholar 

    67.
    Nelson, K. Scheduling of reproduction in relation to molting and growth in malacostracan crustaceans. Crustacean Egg Product. 7, 77–116 (1991).
    Google Scholar 

    68.
    Kibria, G. Studies on molting, molting frequency and growth of shrimp Penaeus monodon fed on natural and compounded diets. Asian Fish. Sci. 6, 203–211 (1993).
    Google Scholar 

    69.
    Petit, H., Nègre-Sadargues, G., Castillo, R. & Trilles, J. P. The effects of dietary astaxanthin on growth and moulting cycle of postlarval stages of the prawn, Penaeus japonicus (Crustacea, Decapoda). Comp. Biochem. Physiol. A Physiol. 117, 539–544 (1997).
    Article  Google Scholar 

    70.
    Clark, R. M., Zera, A. J. & Behmer, S. T. Nutritional physiology of life-history trade-offs: How food protein–carbohydrate content influences life-history traits in the wing-polymorphic cricket Gryllus firmus. J. Exp. Biol. 218, 298–308 (2015).
    PubMed  Article  Google Scholar 

    71.
    Rosa, R., Calado, R., Narciso, L. & Nunes, M. L. Embryogenesis of decapod crustaceans with different life history traits, feeding ecologies and habitats: A fatty acid approach. Mar. Biol. 151, 935–947 (2007).
    Article  Google Scholar 

    72.
    Hines, A. H. Allometric constraints and variables of reproductive effort in brachyuran crabs. Mar. Biol. 69, 309–320 (1982).
    Article  Google Scholar 

    73.
    Sorte, C. J., Davidson, V. E., Franklin, M. C., Benes, K. M., Doellman, M. M., Etter, R. J., & Menge, B. A. Long‐term declines in an intertidal foundation species parallel shifts in community composition. Global Change Biol.23, 341–352 (2017).

    74.
    Goedknegt, M. A., Havermans, J., Waser, A. M., Luttikhuizen, P. C., Velilla, E., Camphuysen, K. C., & Thieltges, D. W. Cross-species comparison of parasite richness, prevalence, and intensity in a native compared to two invasive brachyuran crabs. Aquat. Invasions12, 201–212 (2017).

    75.
    Latham, A. & Poulin, R. Field evidence of the impact of two acanthocephalan parasites on the mortality of three species of New Zealand shore crabs (Brachyura). Mar. Biol. 141, 1131–1139 (2002).
    Article  Google Scholar 

    76.
    Latham, A. D. M. & Poulin, R. Effect of acanthocephalan parasites on hiding behaviour in two species of shore crabs. J. Helminthol. 76, 323–326 (2002).
    CAS  PubMed  Article  Google Scholar 

    77.
    Griffen, B. D., van den Akker, D., NiNuzzo, E. R., Anderson, L. III, & Vernier, A. Comparing methods for predicting the impacts of invasive species (in press).

    78.
    Tyrrell, M.C., & Harris, L.G. Potential impact of the introduced Asian shore crab, Hemigrapsus sanguineus, in northern New England: Diet, feeding preferences, and overlap with the green crab, Carcinus maenas. in Marine Bioinvasions: Proceedings of the First National Conference, Cambridge, MA, 24–27 January 1999 (pp. 208–220). (MIT Sea Grant College Program, 2000).

    79.
    Spilmont, N., Gothland, M. & Seuront, L. Exogenous control of the feeding activity in the invasive Asian shore crab Hemigrapsus sanguineus (De Haan, 1835). Aquat. Invasions 10, 327–332 (2015).
    Article  Google Scholar 

    80.
    McDermott, J. J. The western Pacific brachyuran Hemigrapsus sanguineus (Grapsidae) in its new habitat along the Atlantic coast of the United States: reproduction. J. Crustacean Biol. 18, 308–316 (1998).
    Article  Google Scholar 

    81.
    R Core Team. R: A Language and Environment for Statistical Computing. (R Foundation for Statistical Computing, Vienna, 2019). https://www.R-project.org/.

    82.
    Griffen, B. D. & Mosblack, H. Predicting diet and consumption rate differences between and within species using gut ecomorphology. J. Anim. Ecol. 80, 854–863 (2011).
    PubMed  Article  Google Scholar 

    83.
    Wolcott, D. L. & O’Connor, N. J. Herbivory in crabs: Adaptations and ecological considerations. Am. Zool. 32, 370–381 (1992).
    Article  Google Scholar 

    84.
    Mattson, W. J. Jr. Herbivory in relation to plant nitrogen content. Annu. Rev. Ecol. Evol. Syst. 11, 119–161 (1980).
    Article  Google Scholar 

    85.
    Griffen, B. D., Cannizzo, Z. J. & Gül, M. R. Ecological and evolutionary implications of allometric growth in stomach size of brachyuran crabs. PLoS ONE 13, e0207416 (2018).
    PubMed  PubMed Central  Article  CAS  Google Scholar 

    86.
    Gül, M. R. & Griffen, B. D. Diet, energy storage, and reproductive condition in a bioindicator species across beaches with different levels of human disturbance. Ecol. Indic. 117, 106636 (2020).
    Article  Google Scholar 

    87.
    Vogt, G. Functional cytology of the hepatopancreas of decapod crustaceans. J. Morphol. 280, 1405–1444 (2019).
    CAS  PubMed  Google Scholar 

    88.
    Kyomo, J. Analysis of the relationship between gonads and hepatopancreas in males and females of the crab Sesarma intermedia, with reference to resource use and reproduction. Mar. Biol. 97, 87–93 (1988).
    Article  Google Scholar 

    89.
    Zuur, A. F., Ieno, E. N., Walker, N. J., Saveliev, A. A., Smith, G. M. Zero-truncated and zero-inflated models for count data. in Mixed Effects Models and Extensions in Ecology with R 261–293. (Springer, New York, 2009).

    90.
    Mente, E. Effect of ration level on individual food consumption, growth and protein synthesis in the shore crab Carcinus maenas. In Nutrition, Physiology and Metabolism of Crustaceans 53–67 (Science Publishers, Enfield, 2003).
    Google Scholar  More

  • in

    Extracellular heme recycling and sharing across species by novel mycomembrane vesicles of a Gram-positive bacterium

    1.
    Faust K, Raes J, Faust K, Raes J. Microbial interactions: from networks to models. Nat Rev Microbiol. 2012;10:538–50.
    CAS  PubMed  Article  Google Scholar 
    2.
    Phelan VV, Liu WT, Pogliano K, Dorrestein PC. Microbial metabolic exchange—the chemotype-to-phenotype link. Nat Chem Biol. 2011;8:26–35.
    PubMed  Article  CAS  Google Scholar 

    3.
    Natale P, Brüser T, Driessen AJM. Sec- and Tat-mediated protein secretion across the bacterial cytoplasmic membrane: Distinct translocases and mechanisms. Biochim Biophys Acta. 2007;1778:1735–56.
    PubMed  Article  CAS  Google Scholar 

    4.
    Holland IB. The extraordinary diversity of bacterial protein secretion mechanisms. Meth Mol Biol. 2010;619:1–20.
    CAS  Article  Google Scholar 

    5.
    Guerrero-Mandujano A, Hernández-Cortez C, Ibarra JA, Castro-Escarpulli G. The outer membrane vesicles: Secretion system type zero. Traffic. 2017;18:425–32.
    CAS  PubMed  Article  Google Scholar 

    6.
    Orench‐Rivera N, Kuehn MJ. Environmentally controlled bacterial vesicle‐mediated export. Cell Microbiol. 2016;18:1525–36.
    PubMed  PubMed Central  Article  CAS  Google Scholar 

    7.
    Kim JH, Lee J, Park J, Gho YS, editors. Gram-negative and Gram-positive bacterial extracellular vesicles. Semin Cell Dev Biol. 2015;40:97–104.

    8.
    Schwechheimer C, Kuehn MJ. Outer-membrane vesicles from Gram-negative bacteria: biogenesis and functions. Nat Rev Microbiol. 2015;13:605–19.
    CAS  PubMed  PubMed Central  Article  Google Scholar 

    9.
    McBroom AJ, Kuehn MJ. Release of outer membrane vesicles by Gram‐negative bacteria is a novel envelope stress response. Mol Microbiol. 2007;63:545–58.
    CAS  PubMed  PubMed Central  Article  Google Scholar 

    10.
    Arntzen MO, Varnai A, Mackie RI, Eijsink VGH, Pope PB. Outer membrane vesicles from Fibrobacter succinogenes S85 contain an array of carbohydrate-active enzymes with versatile polysaccharide-degrading capacity. Environ Microbiol. 2017;19:2701–14.
    CAS  PubMed  Article  Google Scholar 

    11.
    Nordstrom T, Blom AM, Tan TT, Forsgren A, Riesbeck K. Ionic binding of C3 to the human pathogen Moraxella catarrhalis is a unique mechanism for combating innate immunity. J Immunol. 2005;175:3628–36.
    PubMed  Article  Google Scholar 

    12.
    Fulsundar S, Harms K, Flaten GE, Johnsen PJ, Chopade B, Nielsen KM. Gene transfer potential of outer membrane vesicles of Acinetobacter baylyi and effects of stress on vesiculation. Appl Environ Microb. 2014;80:3469–83.
    Article  CAS  Google Scholar 

    13.
    Mashburn LM, Whiteley M. Membrane vesicles traffic signals and facilitate group activities in a prokaryote. Nature. 2005;437:422–5.
    CAS  PubMed  Article  Google Scholar 

    14.
    Toyofuku M, Morinaga K, Hashimoto Y, Uhl J, Shimamura H, Inaba H, et al. Membrane vesicle-mediated bacterial communication. ISME J. 2017;11:1504–9.
    PubMed  PubMed Central  Article  Google Scholar 

    15.
    Lee EY, Choi DY, Kim DK, Kim JW, Park JO, Kim S, et al. Gram‐positive bacteria produce membrane vesicles: proteomics‐based characterization of Staphylococcus aureus‐derived membrane vesicles. Proteomics. 2009;9:5425–36.
    CAS  PubMed  Article  Google Scholar 

    16.
    Prados-Rosales R, Baena A, Martinez LR, Luque-Garcia J, Kalscheuer R, Veeraraghavan U, et al. Mycobacteria release active membrane vesicles that modulate immune responses in a TLR2-dependent manner in mice. J Clin Investig. 2011;121:1471–83.
    PubMed  Article  CAS  Google Scholar 

    17.
    Prados-Rosales R, Brown L, Casadevall A, Montalvo-Quiros S, Luque-Garcia JL. Isolation and identification of membrane vesicle-associated proteins in Gram-positive bacteria and mycobacteria. MethodsX. 2014;1:124–9.
    PubMed  PubMed Central  Article  Google Scholar 

    18.
    White DW, Elliott SR, Odean E, Bemis LT, Tischler AD. Mycobacterium tuberculosis Pst/SenX3-RegX3 regulates membrane vesicle production independently of ESX-5 activity. mBio. 2018;9:e00778–18.
    CAS  PubMed  PubMed Central  Google Scholar 

    19.
    Hoffmann C, Leis A, Niederweis M, Plitzko JM, Engelhardt H. Disclosure of the mycobacterial outer membrane: cryo-electron tomography and vitreous sections reveal the lipid bilayer structure. PNAS. 2008;105:3963–7.
    CAS  PubMed  Article  Google Scholar 

    20.
    Ganz T, Nemeth E. Iron homeostasis in host defence and inflammation. Nat Rev Immunol. 2015;15:500–10.
    CAS  PubMed  PubMed Central  Article  Google Scholar 

    21.
    Huber DL. Synthesis, properties, and applications of iron nanoparticles. Small. 2005;1:482–501.
    CAS  PubMed  Article  Google Scholar 

    22.
    Wandersman C, Delepelaire P. Bacterial iron sources: from siderophores to hemophores. Annu Rev Microbiol. 2004;58:611–47.
    CAS  PubMed  Article  Google Scholar 

    23.
    Morel FM, Price N. The biogeochemical cycles of trace metals in the oceans. Science. 2003;300:944–7.
    CAS  PubMed  Article  PubMed Central  Google Scholar 

    24.
    Ram RJ, VerBerkmoes NC, Thelen MP, Tyson GW, Baker BJ, Blake RC, et al. Community proteomics of a natural microbial biofilm. Science. 2005;308:1915–20.
    CAS  PubMed  Article  Google Scholar 

    25.
    Cao B, Shi L, Brown RN, Xiong Y, Fredrickson JK, Romine MF, et al. Extracellular polymeric substances from Shewanella sp. HRCR‐1 biofilms: characterization by infrared spectroscopy and proteomics. Environ Microbiol. 2011;13:1018–31.
    CAS  PubMed  Article  Google Scholar 

    26.
    Vong L, Laës A, Blain S. Determination of iron–porphyrin-like complexes at nanomolar levels in seawater. Anal Chim Acta. 2007;588:237–44.
    CAS  PubMed  Article  Google Scholar 

    27.
    Létoffé S, Nato F, Goldberg ME, Wandersman C. Interactions of HasA, a bacterial haemophore, with haemoglobin and with its outer membrane receptor HasR. Mol Microbiol. 1999;33:546–55.
    PubMed  Article  Google Scholar 

    28.
    Tong Y, Guo M. Bacterial heme-transport proteins and their heme-coordination modes. Arch Biochem Biophys. 2009;481:1–15.
    CAS  PubMed  Article  Google Scholar 

    29.
    Pilpa RM, Robson SA, Villareal VA, Wong ML, Phillips M, Clubb RT. Functionally distinct NEAT (NEAr Transporter) domains within the Staphylococcus aureus IsdH/HarA protein extract heme from methemoglobin. J Biol Chem. 2009;284:1166–76.
    CAS  PubMed  PubMed Central  Article  Google Scholar 

    30.
    Gat O, Zaide G, Inbar I, Grosfeld H, Chitlaru T, Levy H, et al. Characterization of Bacillus anthracis iron‐regulated surface determinant (Isd) proteins containing NEAT domains. Mol Microbiol. 2008;70:983–99.
    CAS  PubMed  PubMed Central  Google Scholar 

    31.
    Choby JE, Skaar EP. Heme synthesis and acquisition in bacterial pathogens. J Mol Biol. 2016;428:3408–28.
    CAS  PubMed  PubMed Central  Article  Google Scholar 

    32.
    Allen CE, Schmitt MP. HtaA is an iron-regulated hemin binding protein involved in the utilization of heme iron in Corynebacterium diphtheriae. J Bacteriol. 2009;191:2638–48.
    CAS  PubMed  PubMed Central  Article  Google Scholar 

    33.
    Allen CE, Schmitt MP. Novel hemin binding domains in the Corynebacterium diphtheriae HtaA protein interact with hemoglobin and are critical for heme iron utilization by HtaA. J Bacteriol. 2011;193:5374–85.
    CAS  PubMed  PubMed Central  Article  Google Scholar 

    34.
    Duckworth AW, Grant S, Grant WD, Jones BE, Meijer D. Dietzia natronolimnaios sp. nov., a new member of the genus Dietzia isolated from an East African soda lake. Extremophiles. 1998;2:359–66.
    CAS  PubMed  Article  PubMed Central  Google Scholar 

    35.
    Mayilraj S, Suresh K, Kroppenstedt R, Saini H. Dietzia kunjamensis sp. nov., isolated from the Indian Himalayas. Int J Syst Evol Microbiol. 2006;56:1667–71.
    CAS  PubMed  Article  PubMed Central  Google Scholar 

    36.
    Li J, Chen C, Zhao G-Z, Klenk H-P, Pukall R, Zhang Y-Q, et al. Description of Dietzia lutea sp. nov., isolated from a desert soil in Egypt. Syst Appl Microbiol. 2009;32:118–23.
    CAS  PubMed  Article  PubMed Central  Google Scholar 

    37.
    Fang H, Qin X-Y, Zhang K-D, Nie Y, Wu X-L. Role of the Group 2 Mrp sodium/proton antiporter in rapid response to high alkaline shock in the alkaline-and salt-tolerant Dietzia sp. DQ12-45-1b. Appl Microbiol Biotechnol. 2018;102:3765–77.
    CAS  PubMed  Article  PubMed Central  Google Scholar 

    38.
    Wang X-B, Chi C-Q, Nie Y, Tang Y-Q, Tan Y, Wu G, et al. Degradation of petroleum hydrocarbons (C6–C40) and crude oil by a novel Dietzia strain. Bioresour Technol. 2011;102:7755–61.
    CAS  PubMed  Article  PubMed Central  Google Scholar 

    39.
    Rédei GP M9 Bacterial Minimal Medium. In: Rédei GP, editors. Encyclopedia of genetics, genomics, proteomics and informatics, 3rd edn. Dordrecht: Springer Group; 2008. pp. 484–6.

    40.
    Van Kessel JC, Hatfull GF. Recombineering in Mycobacterium tuberculosis. Nat Methods. 2007;4:147–52.
    PubMed  Article  CAS  Google Scholar 

    41.
    Liang J, Jiangyang J, Nie Y, Wu X. Regulation of the alkane hydroxylase CYP153 gene in a Gram-positive alkane-degrading bacterium, Dietzia sp. strain DQ12-45-1b. Appl Environ Microbiol. 2016;82:608–19.
    CAS  PubMed  PubMed Central  Article  Google Scholar 

    42.
    Lu S, Nie Y, Tang Y-Q, Xiong G, Wu X-L. A critical combination of operating parameters can significantly increase the electrotransformation efficiency of a Gram-positive Dietzia strain. J Microbiol Methods. 2014;103:144–51.
    CAS  PubMed  Article  Google Scholar 

    43.
    Szvetnik A, Bihari Z, Szabo Z, Kelemen O, Kiss I. Genetic manipulation tools for Dietzia spp. J Appl Microbiol. 2010;109:1845–52.
    CAS  PubMed  Google Scholar 

    44.
    Deininger PL. Molecular cloning: a laboratory manual. Anal Biochem. 1990;186:182–3.
    Article  Google Scholar 

    45.
    McBroom AJ, Johnson AP, Vemulapalli S, Kuehn MJ. Outer membrane vesicle production by Escherichia coli is independent of membrane instability. J Bacteriol. 2006;188:5385–92.
    CAS  PubMed  PubMed Central  Article  Google Scholar 

    46.
    Prados-Rosales R, Weinrick BC, Pique DG, Jacobs WR Jr, Casadevall A, Rodriguez GM. Role for Mycobacterium tuberculosis membrane vesicles in iron acquisition. J Bacteriol. 2014;196:1250–6.
    PubMed  PubMed Central  Article  CAS  Google Scholar 

    47.
    Bligh EG, Dyer WJ. A rapid method of total lipid extraction and purification. Biochem Cell Biol. 1959;37:911–7.
    CAS  Google Scholar 

    48.
    Keddie RM, Cure GL. The cell wall composition and distribution of free mycolic acids in named strains of coryneform bacteria and in isolates from various natural sources. J Appl Microbiol. 1977;42:229–52.
    CAS  Google Scholar 

    49.
    Liu Y, Zhang Q, Hu M, Yu K, Fu J, Zhou F, et al. Proteomic analyses of intracellular Salmonella enterica serovar Typhimurium reveal extensive bacterial adaptations to infected host epithelial cells. Infect Immun. 2015;83:2897–906.
    CAS  PubMed  PubMed Central  Article  Google Scholar 

    50.
    Calderoncelis F, Encinar JR, Sanzmedel A. Standardization approaches in absolute quantitative proteomics with mass spectrometry. Mass Spectrom Rev. 2018;37:715–37.
    CAS  Article  Google Scholar 

    51.
    Liang J-L, Gao Y, He Z, Nie Y, Wang M, JiangYang J-H, et al. Crystal structure of TetR family repressor AlkX from Dietzia sp. strain DQ12-45-1b implicated in biodegradation of n-alkanes. Appl Environ Microbiol. 2017;83:e01447–17.
    CAS  PubMed  PubMed Central  Article  Google Scholar 

    52.
    Tashiro Y, Hasegawa Y, Shintani M, Takaki K, Ohkuma M, Kimbara K, et al. Interaction of bacterial membrane vesicles with specific species and their potential for delivery to target cells. Front Microbiol. 2017;8:571.
    PubMed  PubMed Central  Article  Google Scholar 

    53.
    Marchler-Bauer A, Derbyshire MK, Gonzales NR, Lu S, Chitsaz F, Geer LY, et al. CDD: NCBI’s conserved domain database. Nucleic Acids Res. 2014;43:D222–D6.
    PubMed  PubMed Central  Article  CAS  Google Scholar 

    54.
    Tamura K, Stecher G, Peterson D, Filipski A, Kumar S. MEGA6: molecular evolutionary genetics analysis version 6.0. Mol Biol Evol. 2013;30:2725–9.
    CAS  PubMed  PubMed Central  Article  Google Scholar 

    55.
    Yu NY, Wagner JR, Laird MR, Melli G, Rey S, Lo R, et al. PSORTb 3.0: improved protein subcellular localization prediction with refined localization subcategories and predictive capabilities for all prokaryotes. Bioinformatics. 2010;26:1608–15.
    CAS  PubMed  PubMed Central  Article  Google Scholar 

    56.
    Song H, Sandie R, Wang Y, Andrade-Navarro MA, Niederweis M. Identification of outer membrane proteins of Mycobacterium tuberculosis. Tuberculosis. 2008;88:526–44.
    CAS  PubMed  Article  Google Scholar 

    57.
    Daffé M, Quémard A, Marrakchi H. Mycolic acids: from chemistry to biology. In: Geiger O, editors. Biogenesis of fatty acids, lipids and membranes. Cham: Springer; 2017. p. 1–36.

    58.
    Choi D, Kim D, Choi SJ, Lee J, Choi J, Rho S, et al. Proteomic analysis of outer membrane vesicles derived from Pseudomonas aeruginosa. Proteomics. 2011;11:3424–9.
    CAS  PubMed  Article  Google Scholar 

    59.
    Marchand CH, Salmeron C, Bou Raad R, Meniche X, Chami M, Masi M, et al. Biochemical disclosure of the mycolate outer membrane of Corynebacterium glutamicum. J Bacteriol. 2012;194:587–97.
    CAS  PubMed  PubMed Central  Article  Google Scholar 

    60.
    Daffe M, Marrakchi H. Unraveling the structure of the mycobacterial envelope. Microbiol Spectr. 2019;7:1087–95.
    Article  Google Scholar 

    61.
    Nishiuchi Y, Baba T, Yano I. Mycolic acids from Rhodococcus, Gordonia, and Dietzia. J Microbiol Methods. 2000;40:1–9.
    CAS  PubMed  Article  Google Scholar 

    62.
    Collins M, Goodfellow M, Minnikin D. A survey of the structures of mycolic acids in Corynebacterium and related taxa. Microbiology. 1982;128:129–49.
    CAS  Article  Google Scholar 

    63.
    Rath P, Saurel O, Czaplicki G, Tropis M, Daffé M, Ghazi A, et al. Cord factor (trehalose 6, 6′-dimycolate) forms fully stable and non-permeable lipid bilayers required for a functional outer membrane. Biochim Biophys Acta-Biomemb. 2013;1828:2173–81.
    CAS  Article  Google Scholar 

    64.
    Caruana JC, Walper SA. Bacterial membrane vesicles as mediators of microbe – microbe and microbe – host community interactions. Front Microbiol. 2020;11:432.
    PubMed  PubMed Central  Article  Google Scholar 

    65.
    Rich PR, Maréchal A 8.5 electron transfer chains: structures, mechanisms and energy coupling. In: Egelman EH, editor. Comprehensive biophysics. Amsterdam: Elsevier; 2012. p. 72–93.

    66.
    Butaitė E, Baumgartner M, Wyder S, Kümmerli R. Siderophore cheating and cheating resistance shape competition for iron in soil and freshwater Pseudomonas communities. Nat Commun. 2017;8:1–12.
    Article  CAS  Google Scholar 

    67.
    Zuber B, Chami M, Houssin C, Dubochet J, Griffiths G, Daffé M. Direct visualization of the outer membrane of mycobacteria and corynebacteria in their native state. J Bacteriol. 2008;190:5672–80.
    CAS  PubMed  PubMed Central  Article  Google Scholar 

    68.
    Sani M, Houben ENG, Geurtsen J, Pierson J, De Punder K, Van Zon M, et al. Direct visualization by cryo-EM of the mycobacterial capsular layer: a labile structure containing ESX-1-secreted proteins. PLoS Pathog. 2010;6:e1000794.
    PubMed  PubMed Central  Article  CAS  Google Scholar 

    69.
    Kramer J, Özkaya Ö, Kümmerli R. Bacterial siderophores in community and host interactions. Nat Rev Microbiol. 2020;18:152–63.
    CAS  PubMed  Article  Google Scholar 

    70.
    Rakoff-Nahoum S, Coyne MJ, Comstock LE. An ecological network of polysaccharide utilization among human intestinal symbionts. Curr Biol. 2014;24:40–9.
    CAS  PubMed  Article  PubMed Central  Google Scholar  More

  • in

    Crop microbiome and sustainable agriculture

    1.
    Food and Agriculture Authority. Microbiome the Missing Link. http://www.fao.org/3/ca6767en/CA6767EN.pdf (2020).
    2.
    Singh, B. K. & Trivedi, P. Microbiome and the future for food and nutrient security. Microbial. Biotechnol. 10, 50–53 (2017).
    Article  Google Scholar 

    3.
    National Academies of Science, Engineering and Medicine. New Report Identifies Five Breakthroughs to Address Urgent Challenges and Advance Food and Agricultural Sciences by 2030. http://www8.nationalacademies.org/onpinews/newsitem.aspx?RecordID=25059 (2018).

    4.
    Stratistics Market Research Consulting. Agricultural Microbials – Global Market Outlook (2017–2026). https://www.researchandmarkets.com/research/vdth4t/global?w=4 (2020).

    5.
    European Commission. Farm to fork fact sheet https://ec.europa.eu/commission/presscorner/api/files/attachment/865559/factsheet-farm-fork_en.pdf.pdf (2020).

    6.
    Trivedi, P., Leach, J. E. & Tringe, S. G. et al. Plant–microbiome interactions: from community assembly to plant health. Nat. Rev. Microbiol. https://doi.org/10.1038/s41579-020-0412-1 (2020).
    Article  PubMed  Google Scholar 

    7.
    Qiu, Z. et al. New frontiers in agriculture productivity: optimised microbial inoculants and in situ microbiome engineering. Biotechnol. Adv. 37, 107371 (2019).
    CAS  Article  Google Scholar 

    8.
    Kaminsky, L. M. et al. The inherent conflicts in developing soil microbial noculants. Trends Biotechnol. 37, 140–151 (2019).
    CAS  Article  Google Scholar 

    9.
    Busby, P. E. et al. Research priorities for harnessing plant microbiomes in sustainable agriculture. PLOS Biol. 15, e2001793 (2017).
    Article  Google Scholar  More

  • in

    Health risk indices and zooplankton-based assessment of a tropical rainforest river contaminated with iron, lead, cadmium, and chromium

    The study area
    The study was carried out on Egbokodo River (longitude 5° 38′ and 5° 41′ and latitude 5° 36′ and 5° 33′) in Warri South Local Government Area of Delta State, Southern Nigeria (Fig. 1), between the periods of September 2008–May 2009. The river is a brackish and tidal River that serves as a source of water for drinking, washing, and fishing to the communities in the catchment area. Three (3) Stations (tagged Stations A, B, and C) were selected about 150 m apart, based on distinct anthropogenic activities. Station A was located at a vandalized oil pipeline, while Stations B and C were located downstream at points of dredging and municipal waste disposal respectively. Station A was 6.3–9.3 m in depth, Station B was 11.4–16.1, and Station C was 7.5–19.5 m during the study duration.
    Figure 1

    Map of the study area showing sampled stations. Map designed using QGIS software version 3.10.1 ‘A Coruña’ (QGIS Development Team29). https://qgis.org/en/site/forusers/download.html#.

    Full size image

    The study area comprises of coarse and interspersed soil with lignite and patches of laterite and sandy clay soil. The climate of the study area is typically tropical. It is characterized by the humid tropical wet and dry climate which is primarily regulated by rainfall. The wet season lasts a period of 7 months (April to October). Rainfall ranged from 15 to 91 mm during this period. The driest months are December to January; with a mean monthly rainfall of 15 mm. The bank of the river was densely shaded by a thick canopy of vegetation, dominated by mangrove plants, Nypa palm, and Rhizophora sp.
    Collection of samples (water and zooplankton)
    Water samples were collected from the 3 stations using a 1 L sampling bottle which was pre-cleaned with the deionized water at each station. This sampling procedure was repeated monthly from September 2008 to May 2009. The samples were preserved in a cooler and transported to the laboratory where they were refrigerated at − 10 °C before the physiochemical analysis. Preservation and analysis of water samples were according to standard methods of the American Public Health Association (APHA).
    Samples of zooplankton were collected at the 3 stations between 0800 and 1100 h by towing a hydrobios plankton net (mesh size 25 µm) with a speed boat at 2 knots, just below the water surface for 5 min at every station. At each station, the filtered zooplankton samples were condensed in a 25 mL plankton bottle and preserved using buffered 4% formalin. Each plankton bottle was properly labeled indicating the stations and dates of collection. This procedure was repeated for 9 months (September 2008–May 2009).
    Analysis of water
    Determination of pH
    The pH was estimated using a PH meter—Orion Model 290A (ASTM D 1293B) and recorded accordingly every month.
    Measurement of temperature (°C)
    A mercury-in-glass thermometer was used to measure surface water temperature. A stable initial reading was ensured by shaking it the thermometer carefully. Afterward, the thermometer was left inside the water for about 3 min till a stable reading was observed and recorded.
    Determination of phosphate
    Five (5) mL antimony molybdate was added to 40 mL of water sample was in a 50 mL measuring cylinder. Afterward, 2 mL of Ascorbic acid was added to the mixture. It was left to stand for 30 min for full colour formation2. The absorbance was measured with a UV–visible spectrophotometer at 680 nm.
    Phosphate was then calculated thus;

    $${text{Phosphate}},({text{mg}}/{text{l}}) = frac{{{text{Y}} – {text{C}}}}{{text{M}}}$$
    (1)

    In Eq. (1) above, Y = absorbance of the sample.
    C = absorbance of blank

    $${text{M}} = {text{Gradient}}frac{{({text{B}} – {text{A}})}}{{text{X}}}$$
    (2)

    B = absorbance of standard (Eq. 2)
    A = absorbance of blank
    X = concentration of the standard.
    Determination of nitrate
    Nitrate was tested using the diazotization method—Alpha 419 C/ASTM D3867. 0.5 mL of (0.1% W/V) NaN3 was added to the water sample to remove any NO2 present. 3.0 mL of (2.6% W/V) NH4Cl solution was added. One (1) mL of (2.1% W/V) Borax solution was added. 0.5–0.6 g of spongy cadmium was added. It was then covered and shaken for some 15 to 20 min. Afterward, 7 mL of the solution was transferred to a 25 mL measuring cylinder. 1 mL of (1.0% W/V in 10% HCl) sulphanilamide reagent and was mixed by swirling. After about 3 min, 1.0 mL N-1—naphthalene diamine dihydrochloride (0.1% W/V) was added and mixed thoroughly2. The mark was made-up with distilled water. The blank solution was also subjected to the same treatment as the sample. After about 10–20 min, the absorbance of both the water sample and the blank solutions were measured with a UV–visible spectrophotometer at a wavelength of 543 nm.
    Analysis of total petroleum hydrocarbons (TPH)
    HP-5 capillary column coated with 5% phenyl methyl siloxane (30 m length × 0.32 mm diameter × 0.25 µm film thickness) (Agilent Technologies) was used as a stationary phase of separation of hydrocarbons from water samples. 1µL of the samples was injected in splitless mode at an injection temperature of 300 °C, and pressure of 13.74psi and a total flow of 21.364 mL/min. Purge flow to split vent was set at 15 mL/min at 0.75 min. The oven was initially programmed at 40 °C (1 min) then ramped at 12 °C/min to 300 °C for 10 min. The temperature of the flame ionization detector was regulated to 300 °C using hydrogen gas. Airflow was at 30 mL/min while nitrogen was used as makeup gas at a flow of 22 mL/min. Agilent 7890B gas chromatography coupled to flame ionization detector (GC-FID) was used for the determination of TPH at 254 nm. After calibration, water samples were analyzed and corresponding TPH concentrations were obtained3,10.
    Analysis of oil and grease (OG)
    One (1) L separating funnels with retort stand, 100 mL volumetric flask, glass jar, xylene, and anhydrous sodium sulfate were used in determining the concentrations of oil and grease (OG) in the water.
    Extraction
    Twenty (20) mL xylene was put in a glass jar containing a water sample. The content of the jar was shaken, poured into the separating funnel and shaken again. It was allowed for phase separation and the bottom layer xylene was drained into a 100 mL volumetric flask through a funnel with a plug of glass wool and about 2/3 full with anhydrous Na2SO4.
    Another 20 mL xylene was added to the content in the separating funnel, agitated thoroughly and xylene layer was again drained into the same flask. Water was drained into a measuring cylinder and the volume was noted. Separating funnel was rinsed with 20 mL xylene into the same flask as done earlier. It was made up to mark of the extract in the 100 mL volumetric flask with pure xylene.
    The oil and grease (OG) was calculated thus:
    The concentration of oil reported as OG (mg/L)

    $$= frac{{{text{Conc}}. , left( {{text{mg}}/{text{L}},{text{extract}}} right) times {text{DF}} times {text{EV}},{text{(mL)}}}}{{{text{The}},{text{volume}},{text{of}},{text{water}},,{text{(mL)}}}}$$
    (3)

    In Eq. (3), DF = Dilution factor
    CF = Conversion factor from absorbance to mg/L extract
    EV = Extraction volume of solvent in (mL).
    Analysis of trace metals
    Ten (10) mL of water sample was put in a beaker and 2 mL concentrated nitric acid was added to the sample. The mixture was then heated to evaporation and allowed to cool afterward and then transferred into a volumetric flask. It was then allowed to stand for 24 h, after when it was centrifuged at 3000 rpm until clear. The sample was screened for suspended solids which were filtered off before further analysis. The trace metals in the mixture were then read using an atomic absorption spectrophotometer (AAS, Philips model PU 9100) at a wavelength range of 250–350 V using the ABS knob10.
    The experimental procedures were conducted as described by Estefan et al.30 and modified by Jones Jr.31.
    Quality control and quality assurance
    Validation of trace metals
    The precision of the AAS was validated by repeating every experimental procedure 3 times. Certified reference materials (CRM) and standard reference materials (SRM) published by the Federal Environmental Protection Agency32 were employed as a guide. The recovery rates ranged from 87 to 95%. The calculated relative standard deviation (SD) was  More

  • in

    Comparison of soil microbial community between reseeding grassland and natural grassland in Songnen Meadow

    1.
    Zhang, Y. et al. Variation of soil microbial community along elevation in the Shennongjia Mountain. For. Sci. 50, 161–166 (2014).
    ADS  CAS  Google Scholar 
    2.
    Davidson, E. A. & Janssens, I. A. Temperature sensitivity of soil carbon decomposition and feedbacks to climate change. Nature 440, 165–173 (2006).
    ADS  CAS  PubMed  Article  Google Scholar 

    3.
    Mariotte, P. et al. Plant-soil feedback: bridging natural and agricultural sciences. Trends Ecol. Evol. 33, 129–136 (2018).
    PubMed  Article  Google Scholar 

    4.
    Mommer, L. et al. Lost in diversity: The interactions between soil-borne fungi, biodiversity and plant productivity. New Phytol. 218, 542–553 (2018).
    PubMed  PubMed Central  Article  Google Scholar 

    5.
    Seneviratne, S. I. et al. Land radiative management as contributor to regional-scale climate adaptation and mitigation. Nat. Geosci. 11, 88–96 (2018).
    ADS  CAS  Article  Google Scholar 

    6.
    Song, X. P. et al. Global land change from 1982 to 2016. Nature 560, 639 (2018).
    ADS  CAS  PubMed  PubMed Central  Article  Google Scholar 

    7.
    Tripathi, B. M. et al. Soil pH mediates the balance between stochastic and deterministic assembly of bacteria. ISME J. 12, 1072–1083 (2018).
    CAS  PubMed  PubMed Central  Article  Google Scholar 

    8.
    Zhang, Y. G. et al. Soil bacterial endemism and potential functional redundancy in natural broadleaf forest along a latitudinal gradient. Sci. Rep. 6, 28–39 (2016).
    ADS  Article  CAS  Google Scholar 

    9.
    Yang, Y. F. et al. The microbial gene diversity along an elevation gradient of the Tibetan grassland. ISME J. 8, 430–440 (2014).
    CAS  PubMed  Article  Google Scholar 

    10.
    Zhang, Y. G. et al. Soil bacterial diversity patterns and drivers along an elevational gradient on Shennongjia Mountain, China. Microb. Biotechnol. 8, 739–746 (2015).
    PubMed  PubMed Central  Article  Google Scholar 

    11.
    Shen, C. C. et al. Soil pH drives the spatial distribution of bacterial communities along elevation on Changbai Mountain. Soil Biol. Biochem. 57, 204–211 (2013).
    CAS  Article  Google Scholar 

    12.
    Zhang, Y. G. et al. The microbially mediated soil organic carbon loss under degenerative succession in an alpine meadow. Mol. Ecol. 26, 3676–3686 (2017).
    CAS  PubMed  Article  Google Scholar 

    13.
    Davidson, E. A., Janssens, I. A. & Luo, Y. Q. On the variability of respiration in terrestrial ecosystems: moving beyond Q10. Glob. Change Biol. 12, 154–164 (2006).
    ADS  Article  Google Scholar 

    14.
    Walther, G. R. et al. Ecological responses to recent climate change. Nature 416, 389–395 (2002).
    ADS  CAS  PubMed  Article  Google Scholar 

    15.
    Zhang, Q. et al. Effects of clipping frequency on the relationships between species diversity and productivity in temperate steppe. Int. J. Agric. Biol. 20, 2325–2328 (2018).
    Google Scholar 

    16.
    Guo, Z. G., Cheng, G. D. & Wang, G. X. Plant Diversity of Alpine Kobresia Meadow in the Northern Region of the Tibetan Plateau. J. Glaciol. Geocryol. 26, 95–100 (2004).
    Google Scholar 

    17.
    Fu, B. et al. Hydrogeomorphic ecosystem responses to natural and anthropogenic changes in the Loess Plateau of China. Annu. Rev. Earth Planet. Sci. 45, 223–243 (2017).
    ADS  CAS  Article  Google Scholar 

    18.
    Yang, Y., Dou, Y. & An, S. Testing association between soil bacterial diversity and soil carbon storage on the loess plateau. Sci. Total Environ. 626, 48–58 (2018).
    ADS  CAS  PubMed  Article  Google Scholar 

    19.
    Yang, Y., Cheng, H., Liu, L. X., Dou, Y. X. & An, S. S. Comparison of soil microbial community between planted woodland and natural grass vegetation on the Loess Plateau. For. Ecol. Manage. 460, 117–128 (2020).
    Article  Google Scholar 

    20.
    Tong, X. W. et al. Rasmus Fensholt. Increased vegetation growth and carbon stock in China karst via ecological engineering. Nat. Sustain. 1, 44–50 (2018).
    Article  Google Scholar 

    21.
    Liu, Y. et al. Temporal and spatial succession and dynamics of soil fungal communities in restored grassland on the Loess Plateau in China. Land Degrad. Dev. 30, 1273–1287 (2019).
    Article  Google Scholar 

    22.
    Bardgett, R. D. et al. Below-ground microbial community development in a high temperature world. Oikos 85, 193–203 (1999).
    Article  Google Scholar 

    23.
    Nave, L. E. et al. Reforestation can sequester two petagrams of carbon in us top soils in a century. Proc. Natl. Acad. Sci. USA https://doi.org/10.1073/pnas.1719685115 (2018).
    Article  PubMed  Google Scholar 

    24.
    Chen, J. S., Zhu, R. F. & Zhang, Y. X. The effect of nitrogen addition on seed yield and yield components of Leymus chinensis. J. Soil Sci. Plant Nutr. 13, 329–339 (2013).
    Google Scholar 

    25.
    Lange, M. et al. Plant diversity increases soil microbial activity and soil carbon storage. Nat. Commun. 6, 6707 (2015).
    ADS  CAS  PubMed  Article  Google Scholar 

    26.
    Lal, R. Digging deeper: a holistic perspective of factors affecting soil organic carbon sequestration in agroecosystems. Glob. Change Biol. 24, 3285–3301 (2018).
    ADS  Article  Google Scholar 

    27.
    Gao, Q. Z. et al. Alpine grassland degradation index and its response to recent climate variability in Northern Tibet, China. Quatern. Int. 226, 143–150 (2010).
    Article  Google Scholar 

    28.
    Li, N. et al. Short-term effects of temperature enhancement on community structure and biomass of alpine meadow in the Qinghai-Tibet Plateau. Acta Ecol. Sin. 31, 0895–0905 (2011).
    CAS  Google Scholar 

    29.
    Gao, Y. H. et al. Vegetation net primary productivity and its response to climate change during 2001–2008 in the Tibetan Plateau. Sci. Total Environ. 444, 356–362 (2013).
    ADS  CAS  PubMed  Article  Google Scholar 

    30.
    Chen, J. S. et al. Effects of clipping and fertilizing n on the relationship between diversity and productivity of Leymus Chinensis Meadow. Acta Agrestia Sin. 24, 910–914 (2016).
    Google Scholar 

    31.
    Peng, F. et al. Intensified plant N and C pool with more available nitrogen under experimental warming in an alpine meadow ecosystem. Ecol. Evol. 6, 8546–8555 (2016).
    PubMed  PubMed Central  Article  Google Scholar 

    32.
    Li, L. et al. Precipitation overrides warming in mediating soil nitrogen pools in an alpine grassland ecosystem on the Tibetan Plateau. Sci. Rep. 6, 31–38 (2016).
    Google Scholar 

    33.
    Niu, S. Q. et al. Microbial diversity in saline alkali soil from Hexi Corridor analyzed by Illumina MiSeq high-throughput sequencing system. Microbiology China 9, 66–72 (2017).
    Google Scholar 

    34.
    Chaffron, S. et al. A global network of coexisting microbes from environmental and whole-genome sequence data. Genome Res. 20, 947–959 (2010).
    CAS  PubMed  PubMed Central  Article  Google Scholar 

    35.
    Steele, J. A. et al. Marine bacterial, archaeal and protest an association networks reveal ecological linkages. ISME J. 5, 1414–1425 (2011).
    PubMed  PubMed Central  Article  Google Scholar 

    36.
    Kreimer, A. et al. NetCmpt: a network-based tool for calculating the metabolic competition between bacterial species. Bioinformatics 28, 2195–2197 (2012).
    CAS  PubMed  Article  Google Scholar 

    37.
    O’Brien, J. D. et al. A Bayesian approach to inferring the phylogenetic structure of communities from metagenomic data. Genetics 197, 925–937 (2014).
    PubMed  PubMed Central  Article  Google Scholar 

    38.
    Deng, Y. et al. Elevated carbon dioxide accelerates the spatial turnover of soil microbial communities. Glob. Change Biol. 22, 957–964 (2016).
    ADS  Article  Google Scholar 

    39.
    Zhou, J. Z. et al. Functional molecular ecological networks. mBio 1, e00169-10 (2010).
    PubMed  PubMed Central  Article  CAS  Google Scholar 

    40.
    Zhou, J. Z. et al. Phylogenetic molecular ecological network of soil microbial communities in response to elevated CO2. mBio 2, e00122-e211 (2011).
    PubMed  PubMed Central  Article  Google Scholar 

    41.
    Deng, Y. et al. Molecular ecological network analyses. BMC Bioinformatics 13, 113 (2012).
    PubMed  PubMed Central  Article  Google Scholar 

    42.
    Wang, J. F. & Wu, Q. B. Influences of the vegetaion degradation on the shallow cryic soil environment in the wet meadow areas on the Qinghai-Tibetan plateau. J. Lanzhou Univ. 47, 39–45 (2011).
    Google Scholar 

    43.
    Wang, Y. et al. Artificial reforestation produces less diverse soil nitrogen-cycling genes than natural restoration. Ecosphere 10, e02562 (2019).
    Google Scholar 

    44.
    Bao, S. D. Soil and Agricultural Chemical Analysis (China Agriculture Press, Beijing, 2000).
    Google Scholar 

    45.
    Zhou, J. Z., Bruns, M. A. & Tiedje, J. M. DNA recovery from soils of diverse composition. Appl. Environ. Microbiol. 62, 316–322 (1996).
    CAS  PubMed  PubMed Central  Article  Google Scholar 

    46.
    Shen, C. C. et al. Dramatic increases of soil microbial functional gene diversity at the treeline ecotone of Changbai Mountain. Front. Microbiol. 7, 1184 (2016).
    PubMed  PubMed Central  Google Scholar 

    47.
    Chen, W., Koide, R. T. & Eissenstat, D. M. Nutrient foraging by mycorrhizas: From species functional traits to ecosystem processes. Funct. Ecol. 32, 858–869 (2018).
    Article  Google Scholar 

    48.
    Guo, X. et al. Climate warming leads to divergent succession of grassland microbial communities. Nat. Glob. Change 8, 813–818 (2018).
    ADS  Article  Google Scholar 

    49.
    Jiao, S., Xu, Y., Zhang, J. & Lu, Y. Soil bacterial community dynamics reflect changes in plant community and soil properties during the secondary succession of abandoned farmland in the Loess Plateau. Microbiome 6, 146–156 (2018).
    PubMed  PubMed Central  Article  Google Scholar 

    50.
    Brabcová, V., Štursová, M. & Baldrian, P. Nutrient content affects the turnover of fungal biomass in forest topsoil and the composition of associated microbial communities. Soil Biol. Biochem. 118, 187–198 (2018).
    Article  CAS  Google Scholar 

    51.
    He, J. Z. & Ge, Y. Recent advances in soil microbial biogeography. Acta Ecol. Sin. 28, 5571–5582 (2008).
    CAS  Google Scholar 

    52.
    Horner-Devine, M. C., Lage, M., Hughes, J. B. & Bohannan, B. J. M. A taxa-area relationship for bacteria. Nature 432, 750–753 (2004).
    ADS  CAS  PubMed  Article  Google Scholar 

    53.
    McCann, K., Hastings, A. & Huxel, G. R. Weak trophic interactions and the balance of nature. Nature 395, 794–798 (1998).
    ADS  CAS  Article  Google Scholar 

    54.
    Pimm, S. L., Lawton, J. H. & Cohen, J. E. Food web patterns and their consequences. Nature 350, 669–674 (1991).
    ADS  Article  Google Scholar 

    55.
    Fuhrman, J. A. Microbial community structure and its functional implications. Nature 459, 193–199 (2009).
    ADS  CAS  PubMed  Article  Google Scholar 

    56.
    Sun, X., Gao, Y. & Yang, Y. F. Recent advancement in environmental research with metagenomics tools. Biodivers. Sci. 21, 393–400 (2013).
    CAS  Google Scholar 

    57.
    Barabási, A. L. & Oltvai, Z. N. Network biology: understan Mommer the cell’s functional organization. Nat. Rev. Genet. 5, 101–113 (2004).
    PubMed  Article  CAS  Google Scholar 

    58.
    Ding, J. J. et al. Integrated metagenomics and network analysis of soil microbial community of the forest timberline. Sci. Rep. 5, 7994 (2015).
    CAS  PubMed  PubMed Central  Article  Google Scholar 

    59.
    Brundrett, M. C. & Tedersoo, L. Evolutionary history of mycorrhizal symbioses and global host plant diversity. New Phytol. 220, 55–61 (2018).
    Article  Google Scholar 

    60.
    Xiong, J. B. et al. Geographic distance and pH drive bacterial distribution in alkaline lake sediments across Tibetan Plateau. Environ. Microbiol. 14, 2457–2466 (2012).
    CAS  PubMed  PubMed Central  Article  Google Scholar  More

  • in

    Habitat segregation and migration in tropical anguillid eels, Anguilla bengalensis bengalensis and A. bicolor bicolor

    1.
    Ege, V. A revision of the Genus Anguilla Shaw. Dana Rep. 16, 8–256 (1939).
    Google Scholar 
    2.
    Arai, T. Taxonomy and distribution. In Biology and Ecology of Anguillid Eels (ed. Arai, T.) 1–20 (CRC Press, Boca Raton, 2016).
    Google Scholar 

    3.
    Arai, T. & Chino, N. Diverse migration strategy between freshwater and seawater habitats in the freshwater eels genus Anguilla. J. Fish Biol. 81, 442–455 (2012).
    CAS  PubMed  Article  PubMed Central  Google Scholar 

    4.
    Arai, T., Limbong, D., Otake, T. & Tsukamoto, K. Recruitment mechanisms of tropical eels, Anguilla spp., and implications for the evolution of oceanic migration in the genus Anguilla. Mar. Ecol. Prog. Ser. 216, 253–264 (2001).
    ADS  CAS  Article  Google Scholar 

    5.
    Shiao, J. C., Tzeng, W. N., Collins, A. & Iizuka, Y. Role of marine larval duration and growth rate of glass eels in determining the distribution of Anguilla reinhardtii and A. australis on Australian eastern coasts. Mar. Freshw. Res. 53, 1–10 (2002).
    Article  Google Scholar 

    6.
    Arai, T., Abdul Kadir, S. R. & Chino, N. Year-round spawning by a tropical catadromous eel Anguilla bicolor bicolor. BMar. Biol. 163, 37 (2016).
    Google Scholar 

    7.
    Arai, T. & Abdul Kadir, S. R. Opportunistic spawning of tropical anguillid eels Anguilla bicolor bicolor and A. bengalensis bengalensis. Sci. Rep. 7, 41649 (2017).
    ADS  CAS  PubMed  PubMed Central  Article  Google Scholar 

    8.
    Beumer, J. & Sloane, R. Distribution and abundance of glass-eels Anguilla spp. in east Australian waters. Int. Rev. Hydrobiol. 75, 721–736 (1990).
    Article  Google Scholar 

    9.
    Arai, T., Aoyama, J., Limbong, D. & Tsukamoto, K. Species composition and inshore migration of the tropical eels Anguilla spp. recruiting to the estuary of the Poigar River, Sulawesi Island. Mar. Ecol. Prog. Ser. 188, 299–303 (1999).
    ADS  Article  Google Scholar 

    10.
    Sugeha, H., Arai, T., Miller, M. J., Limbong, D. & Tsukamoto, K. Inshore migration of the tropical eels Anguilla spp. recruiting to the Poigar River estuary on North Sulawesi Island. Mar. Ecol. Prog. Ser. 221, 233–243 (2001).
    ADS  Article  Google Scholar 

    11.
    Hewavitharane, C.A., Pickering, T.D., Ciro, R., Mochioka. N. Species composition, abundance and seasonal recruitment patterns of freshwater eels (Anguilla spp.) to Viti Levu, Fiji Islands, in the western South Pacific. Mar. Freshw. Res. 69,1704–1711 (2018).
    Article  Google Scholar 

    12.
    Leander, N. J., Shen, K. N., Chen, R. T. & Tzeng, W. N. Species composition and seasonal occurrence of recruiting glass eels (Anguilla spp.) in the Hsiukuluan Rive, River Eastern Taiwan. Zool. Stud. 51, 59–71 (2012).
    CAS  Google Scholar 

    13.
    Arai, T., Chino, N., Zulkifli, S. Z. & Ismail, A. Notes on the occurrence of the tropical eel Anguilla bicolor bicolor in Peninsular Malaysia, Malaysia. J. Fish Biol. 80, 692–697 (2012).
    CAS  PubMed  Article  Google Scholar 

    14.
    Arai, T. First record of a tropical mottled eel, Anguilla bengalensis bengalensis (Actinopterygii: Anguillidae) from the Langkawi Islands, Peninsular Malaysia, Malaysia. Mar. Biodivers. Rec. 7, e38 (2014).
    Article  Google Scholar 

    15.
    Arai, T., Chin, T. C., Kwong, K. O. & Siti Azizah, M. N. Occurrence of the tropical eels, Anguilla bengalensis bengalensis and A. bicolor bicolor in Peninsular Malaysia, Malaysia and implications for the eel taxonomy. Mar. Biodivers. Rec. 8, e28 (2015).
    Article  Google Scholar 

    16.
    Arai, T. & Wong, L. L. Validation of the occurrence of the tropical eels, Anguilla bengalensis bengalensis and A. bicolor bicolor at Langkawi Island in Peninsular Malaysia, Malaysia. Tropic. Ecol. 57, 23–31 (2016).
    Google Scholar 

    17.
    Abdul Kadir, S. R., Abdul Rasid, M. H. F., Kwong, K. O., Wong, L. & Arai, T. Occurrence and the ecological implication of a tropical anguillid eel Anguilla marmorata from peninsular Malaysia. Zookeys 695, 103–110 (2017).
    Article  Google Scholar 

    18.
    Arai, T. & Abdul Kadir, S. R. Diversity, distribution and different habitat use among the tropical freshwater eels of genus Anguilla. Sci. Rep. 7, 7593 (2017).
    ADS  PubMed  PubMed Central  Article  CAS  Google Scholar 

    19.
    Arai, T. Evidence of local short-distance spawning migration of tropical freshwater eels, and implications for the evolution of freshwater eel migration. Ecol. Evol. 4, 3812–3819 (2014).
    PubMed  PubMed Central  Article  Google Scholar 

    20.
    Arai, T., Kotake, A. & McCarthy, T. K. Habitat use by the European eel Anguilla auguilla in Irish waters. Estuar. Coast. Shelf Sci. 67, 569–578 (2006).
    ADS  Article  Google Scholar 

    21.
    Shiao, J. C., Ložys, L., Iizuka, Y. & Tzeng, W. N. Migratory patterns and contribution of stocking to the population of European eel in Lithuanian waters as indicated by otolith Sr:Ca ratios. J. Fish Biol. 69, 749–769 (2006).
    CAS  Article  Google Scholar 

    22.
    Lin, Y. J., Yalçin-Özdilek, S., Iizuka, Y., Gümüş, A. & Tzeng, W. N. Migratory life history of European eel Anguilla anguilla from freshwater regions of the River Asi, southern Turkey and their high otolith Sr:Ca ratios. J. Fish Biol. 78, 860–868 (2011).
    PubMed  Article  Google Scholar 

    23.
    Arai, T., Kotake, A., Harrod, C., Morrissey, M. & Mccarthy, T. K. Ecological plasticity of the European eel Anguilla anguilla in a tidal Atlantic lake system in Ireland. J. Mar. Biol. Assoc. UK 99, 1189–1195 (2019).
    CAS  Article  Google Scholar 

    24.
    Thibault, I. et al. Facultative catadromy in American eels: testing the conditional strategy hypothesis. Mar. Ecol. Prog. Ser. 344, 219–229 (2007).
    ADS  Article  Google Scholar 

    25.
    Jessop, B. M. et al. Otolith Sr:Ca and Ba:Ca may give inconsistent indications of estuarine habitat use for American eels (Anguilla rostrata). Environ. Biol. Fish. 93, 193–207 (2012).
    Article  Google Scholar 

    26.
    Tsukamoto, K. & Arai, T. Facultative catadromy of the eel, Anguilla japonica, between freshwater and seawater habitats. Mar. Ecol. Prog. Ser. 220, 365–376 (2001).
    Article  Google Scholar 

    27.
    Tzeng, W. N., Shiao, J. C. & Iizuka, Y. Use of otolith Sr:Ca ratios to study the riverine migratory behaviors of the Japanese eel Anguilla japonica. Mar. Ecol. Prog. Ser. 245, 213–221 (2002).
    ADS  Article  Google Scholar 

    28.
    Shiao, J. C., Iizuka, Y., Chang, C. W. & Tzeng, W. N. Disparities in habitat use and migratory behaviour between tropical eel Anguilla marmorata and temperate eel A. japonica in four Taiwanese rivers. Mar. Ecol. Prog. Ser. 261, 233–242 (2003).
    ADS  Article  Google Scholar 

    29.
    Chino, N. & Arai, T. Relative contribution of migratory type on the reproduction of migrating silver eels, Anguilla japonica, collected off Shikoku Island, Japan. Mar. Biol. 156, 661–668 (2009).
    CAS  Article  Google Scholar 

    30.
    Arai, T., Kotake, A., Lokman, P. M., Miller, M. J. & Tsukamoto, K. Evidence of different habitat use by New Zealand freshwater eels, Anguilla australis and A. dieffenbachii, as revealed by otolith microchemistry. Mar. Ecol. Prog. Ser. 266, 213–225 (2004).
    ADS  Article  Google Scholar 

    31.
    Briones, A. A., Yambot, A. V., Shiao, J. C., Iizuka, Y. & Tzeng, W. N. Migratory pattern and habitat use of tropical eels Anguilla spp. (teleostei: Anguilliformes: Anguillidae) in the Philippines, as revealed by otolith microchemistry. Raffl. Bull. Zool. 14, 141–149 (2007).
    Google Scholar 

    32.
    Chino, N. & Arai, T. Migratory history of the giant mottled eel (Anguilla marmorata) in the Bonin Islands of Japan. Ecol. Freshw. Fish. 19, 19–25 (2010).
    Article  Google Scholar 

    33.
    Lin, Y. J. et al. Regional variation in otolith Sr:Ca ratios of African longfinned eel Anguilla mossambica and mottled eel Anguilla marmorata: a challenge to the classic tool for reconstructing migratory histories of fishes. J. Fish Biol. 81, 427–441 (2012).
    PubMed  Article  PubMed Central  Google Scholar 

    34.
    Arai, T., Chino, N. & Le, D. Q. Migration and habitat use of the tropical eels Anguilla marmorata and A. bicolor pacifica in Vietnam. Aquat. Ecol. 47, 57–65 (2013).
    Article  Google Scholar 

    35.
    Arai, T. & Chino, N. Opportunistic migration and habitat use of the giant mottled eel Anguilla marmorata (Teleostei: Elopomorpha). Sci. Rep. 8, 5666 (2018).
    ADS  PubMed  PubMed Central  Article  CAS  Google Scholar 

    36.
    Arai, T. & Chino, N. Variations in the migratory history of the tropical catadromous eels Anguilla bicolor bicolor and A. bicolor pacifica in south-east Asian waters. J. Fish Biol. 94, 752–758 (2019).
    CAS  PubMed  Article  PubMed Central  Google Scholar 

    37.
    Chino, N. & Arai, T. Occurrence of marine resident tropical eel Anguilla bicolor bicolor in Indonesia. Mar. Biol. 157, 1075–1081 (2010).
    Article  Google Scholar 

    38.
    Chino, N. & Arai, T. Habitat use and habitat transitions in the tropical eel Anguilla bicolor bicolor. Environ. Biol. Fish. 89, 571–578 (2010).
    Article  Google Scholar 

    39.
    Tzeng, W. N. Effects of salinity and ontogenetic movements on strontium:calcium ratios in the otoliths of the Japanese Eel, Anguilla japonica Temminck and Schlegel. J. Exp. Mar. Biol. Ecol. 199, 111–122 (1996).
    CAS  Article  Google Scholar 

    40.
    Lin, S. H., Chang, C. W., Iizuka, Y. & Tzeng, W. N. Salinities, not diets, affect strontium/calcium ratios in otoliths of Anguilla japonica. J. Exp. Mar. Biol. Ecol. 34, 254–263 (2007).
    Article  CAS  Google Scholar 

    41.
    Arai, T. & Chino, N. Influence of water salinity on the strontium:calcium ratios in otoliths of the giant mottled eel Anguilla marmorata. Environ. Biol. Fish. 100, 281–286 (2017).
    Article  Google Scholar 

    42.
    Jellyman, D. J. & Todd, P. R. Why are migrating male shortfinned eels (Anguilla australis) in Lake Ellesmere, New Zealand, getting smaller but not younger?. Bull. Fr. Peche. Piscic. 349, 141–152 (1998).
    Article  Google Scholar 

    43.
    Jellyman, D. J., Glova, G. J., Sagar, P. M. & Sykes, J. R. E. Spatiotemporal distribution of fish in the Kakanui River estuary, South Island, New Zealand. NZ J. Mar. Freshw. Res. 30, 103–118 (2001).
    Google Scholar 

    44.
    McDowall, R. M. New Zealand Freshwater Fishes: A Natural History and Guide (Heinemann Reed, Auckland, 1990).
    Google Scholar 

    45.
    Jowett, I. G. & Richardson, J. Habitat preferences of common, riverine New Zealand native fishes and implication for flow management. NZ J. Mar. Freshw. Res. 29, 13–23 (1995).
    Article  Google Scholar 

    46.
    Glova, G. J., Jellyman, D. J. & Bonnett, M. L. Factors associated with the distribution and habitat of eels (Anguilla spp.) in three New Zealand lowland streams. NZ J. Mar. Freshw. Res. 32, 255–269 (1998).
    Article  Google Scholar 

    47.
    Bozeman, E. K., Helfman, G. S. & Richardson, T. Population size and home range of American eels in a Georgia tidal creek. Trans. Am. Fish. Soc. 114, 821–825 (1985).
    Article  Google Scholar 

    48.
    Ford, T. E. & Mercer, E. Density, size distribution and home range of American eels, Anguilla rostrata, in a Massachusetts salt marsh. Environ. Biol. Fish. 17, 309–314 (1986).
    Article  Google Scholar 

    49.
    Chisnall, B. L. & Kalish, J. M. Age validation and movement of freshwater eels (Anguilla dieffenbachii and A. australis) in a New Zealand pastoral stream. NZ J. Mar. Freshw. Res. 27, 333–338 (1993).
    Article  Google Scholar 

    50.
    Oliveira, K. Movement and growth rates of yellow phase American eels in the Annaquatucket River, Rhode Island. Trans. Am. Fish. Soc. 126, 638–646 (1997).
    Article  Google Scholar 

    51.
    Jellyman, D. J. & Sykes, J. R. E. Diel and seasonal movements of radio-tagged freshwater eels, Anguilla spp., in two New Zealand streams. Environ. Biol. Fish. 66, 143–154 (2003).
    Article  Google Scholar 

    52.
    Poole, W. R. & Reynolds, J. D. Variability in growth rate in European eel Anguilla anguilla (L.) in a Western Irish catchment. Proc. R. Irish Acad. 98B, 141–145 (1998).
    Google Scholar 

    53.
    Jessop, B. M. Geographic effects on American eel (Anguilla rostrata) life history characteristics and strategies. Can. J. Fish. Aquat. Sci. 2010(67), 326–346 (2010).
    Article  Google Scholar 

    54.
    Kotake, A. et al. Ecological aspects of Japanese eels, Anguilla japonica, collected from coastal areas of Japan. Zool. Sci. 24, 1213–1221 (2007).
    PubMed  Article  Google Scholar 

    55.
    Jellyman, D. J. Status of New Zealand fresh-water eel stocks and management initiatives. ICES J. Mar. Sci. 64, 1379–1386 (2007).
    Article  Google Scholar 

    56.
    Chisnall, B. L. & Hicks, B. J. Age and growth of longfinned eels (Anguilla dieffenbachii) in pastoral and forested streams in the Waikato River basin, and in two hydro-electric lakes in the North Island, New Zealand. NZ J. Mar. Freshw. Res. 27, 317–332 (1993).
    Article  Google Scholar 

    57.
    Iizuka, Y. Electron microprobe study of otolith: Migratory behavior and habitat of three major temperate species of eels. JEOL News 47, 33–50 (2012).
    Google Scholar 

    58.
    Arai, T., Otake, T. & Tsukamoto, K. Drastic changes in otolith microstructure and microchemistry accompanying the onset of metamorphosis in the Japanese eel Anguilla japonica. Mar. Ecol. Prog. Ser. 161, 17–22 (1997).
    ADS  CAS  Article  Google Scholar 

    59.
    Oliveira, K. Field validation of annular growth rings in the American eel Anguilla rostrata, using tetracycline-marked otolith. Fish. Bull. 94, 186–189 (1996).
    Google Scholar 

    60.
    Graynoth, E. Improved otolith preparation, ageing and back-calculation techniques for New Zealand freshwater eels. Fish. Res. 42, 137–146 (1999).
    Article  Google Scholar 

    61.
    Arkhipkin, A. I., Schuchert, P. C. & Danyushevsky, L. Otolith chemistry reveals fine population structure and close affinity to the Pacific and Atlantic oceanic spawning grounds in the migratory southern blue whiting (Micromesistius australis australis). Fish. Res. 96, 188–194 (2009).
    Article  Google Scholar 

    62.
    Schuchert, P. C., Arkhipkin, A. I. & Koenig, A. E. Traveling around Cape Horn: Otolith chemistry reveals a mixed stock of Patagonian hoki with separate Atlantic and Pacific spawning grounds. Fish. Res. 102, 80–86 (2010).
    Article  Google Scholar  More

  • in

    Accommodating individual travel history and unsampled diversity in Bayesian phylogeographic inference of SARS-CoV-2

    SARS-CoV-2 genome data sets and associated travel history
    To focus on the early stage of COVID-19 spread, we analyzed SARS-CoV-2 genome sequences and metadata available in GISAID on March 10th8. We curated a data set of 305 genomes by removing error-prone sequences, keeping only genomes with appropriate metadata, and a single genome from patients with multiple genomes available. We assigned each genome a global lineage designation based on the nomenclature scheme outlined in Rambaut et al.28 using pangolin v1.1.14 (https://github.com/hCoV-2019/pangolin), lineages data release 2020-05-19 (https://github.com/hCoV-2019/lineages). We aligned the remaining genomes using MAFFT v.7.45329 and partially trimmed the 5′ and 3′ ends. All sequences were associated with exact sampling dates in their meta-information, except for one genome from Anhui with known month of sampling. Upon visualizing root-to-tip divergence as a function of sampling time, using TempEst v.1.5.330 based on an ML tree inferred with IQ-TREE v.2.0-rc131, we removed one potential outlier. The root-to-tip plots without the outlier are shown in Supplementary Fig. S3. We formally tested for temporal signal using BETS32. The final 282 genomes were sampled from 28 different countries, with Chinese samples originating from 13 provinces, one municipality (Beijing), and one special administrative area (Hong Kong), which we considered as separate locations in our (discrete) phylogeographic analyses. Phylogenetic signal in the data set was explored through likelihood mapping analysis33 (Supplementary Fig. S4).
    We searched for travel history data associated with the genomes in the GISAID records, media reports, and publications and retrieved recent travel locations for 64 genomes (22.5%, Supplementary Table 2): 43 traveled/returned from Hubei (Wuhan), 1 from Beijing, 3 from China without further detail (which we associated with an appropriate ambiguity code in our phylogeographic analysis that represents all sampled Chinese locations), 2 from Singapore, 1 from Southeast Asia (which we also associated with an ambiguity code that represents all sampled Southeast Asian locations), 7 from Italy, and 7 from Iran. In this data set, Italy is better represented by recent travel locations than actual samples (n = 4) and Iran is exclusively represented by travelers returning from this country. For 46 out of the 64 genomes, we retrieved the date of travel, which represents the most recent time point at which the ancestral lineage circulated in the travel location.
    In order to examine (i) to what extent our reconstructions could be updated by the genome data that has become available retrospectively for the same locations and the same time period before March 10 ~4 months after this date, and (ii) how sampling bias can be mitigated by downsampling from the larger collection of available genomes, we assembled an additional data set of 500 genomes. For this purpose, SARS-CoV-2 genomes were downloaded from GISAID on June 23, 2020 and processed according to the COG-UK pre-analysis pipeline (https://github.com/COG-UK/grapevine). Briefly, sequences were aligned to the reference sequence Wuhan-Hu-1 (Genbank accession number NC_045512) using Minimap2 v.2.1734. Problematic sites were masked (https://virological.org/t/issues-with-sars-cov-2-sequencing-data/473), and sequences with More