LC-MS based plant metabolic profiles of thirteen grassland species grown in diverse neighbourhoods

In plants, secondary metabolite profiles provide a unique opportunity to explore seasonal variation and responses to the environment. These include both abiotic and biotic factors. In field experiments, such stress factors occur in combination. This variation alters the plant metabolic profiles in yet uninvestigated ways. This data set contains trait and mass spectrometry data of thirteen grassland species collected at four time points in the growing season in 2017. We collected above-ground vegetative material of seven grass and six herb species that were grown in plant communities with different levels of diversity in the Jena Experiment. For each sample, we recorded visible traits and acquired shoot metabolic profiles on a UPLC-ESI-Qq-TOF-MS. We performed the raw data pre-processing in Galaxy-W4M and prepared the data for statistical analysis in R by applying missing data imputation, batch correction, and validity checks on the features. This comprehensive data set provides the opportunity to investigate environmental dynamics across diverse neighbourhoods that are reflected in the metabolomic profile. Measurement(s) plant metabolite Technology Type(s) liquid chromatography-mass spectrometry Factor Type(s) Season • Diversity Level Sample Characteristic - Organism Anthoxanthum odoratum • Avenula pubescens • Centaurea jacea • Dactylis glomerata • Festuca rubra • Geranium pratense • Holcus lanatus • Knautia arvensis • Leucanthemum vulgare • Phleum pratense • Plantago lanceolata • Poa pratensis • Ranunculus acris Sample Characteristic - Environment grassland biome Sample Characteristic - Location Jena Measurement(s) plant metabolite Technology Type(s) liquid chromatography-mass spectrometry Factor Type(s) Season • Diversity Level Sample Characteristic - Organism Anthoxanthum odoratum • Avenula pubescens • Centaurea jacea • Dactylis glomerata • Festuca rubra • Geranium pratense • Holcus lanatus • Knautia arvensis • Leucanthemum vulgare • Phleum pratense • Plantago lanceolata • Poa pratensis • Ranunculus acris Sample Characteristic - Environment grassland biome Sample Characteristic - Location Jena Machine-accessible metadata file describing the reported data: https://doi.org/10.6084/m9.figshare.13288721

. Steps of analysis performed on the thirteen target species and the quality controls. Species belonging to the functional groups (FG) grass and herb were assembled in two groups of eight species (Pool). The Pools included four species per FG. Three of the species were represented in both pools (*). Shoots were collected at four time points (seasons: A, B, C, D) in four diversity levels (DL1, DL2, DL4, DL8). A detailed list of the study samples can be found in the associated Metadata Record (MTBLS679 33 ). For details of the experimental setup, see Fig. 1, and Ebeling et al. 30 for a plot overview. Study samples are processed in the respective analysis step (+). One sample was excluded from the analysis due to the loss of the sampled material, and some samples did not pass the final validation check (±; see section "Cryo Sample Preparation" and "Sample Validity Check"). This overview also indicates where the quality controls were used for the analysis.
Traits & sampling. Prior to plant biomass collection in each season, we surveyed each plot to record the actual number of present species (species richness), both sown (target) and weed (not deliberately cultivated) species. We also estimated the abundance of each species (Shannon diversity) in relation to the plot size.
In each season, we collected the above-ground tissue of two replicates per plot and species (Fig. 2b). In each plot, we randomly chose two plant individuals as replicates from specimens with a similar phenological stage according to the BBCH 35 scale. We recorded the following traits of these plant individuals: phenological stage (BBCH 35 ), the number of leaves and inflorescences, plant height, and the proportional damage inflicted by either pathogen or mechanically.
The plants were cut 3 cm above the ground ( Fig. 1 ⑤). An aliquot of shoot (leaf and stem) tissues was collected in plastic vials, snap-frozen on dry ice and stored for LC-MS analysis (referred to as study sample). The remaining biomass, including the inflorescences, was stored in plastic bags for biomass measurements. We collected the samples following the order of plots in the TBE (randomised DLs and Pools across the experimental site), starting at the southern end of the TBE 30 . We also recorded the exact time of the sampling for each sample to account for possible time-related shifts in the metabolic profile (sampling between 1 pm and 8 pm). We collected the samples within a single day to reduce the environmental influences to a minimum (for the exact dates see the MTBLS679 33 data repository).
We applied the following labelling scheme to ensure the randomisation for sample extraction and LC-MS data acquisition. For each season, we assigned a number between 001 and 128 to each sample. These Lab-IDs were chosen randomly for each sample while collecting the biomass. For example, the Lab-ID 013_2017_A refers to the sample 2017_A_PHLPRA_A002_a: collected in season 2017_A; Phleum pratense, in plot A002, which is referring to DL2 in P1, replicate a; and 013_2017_C refers to the sample 2017_C_FESRUB_B067_b: collected in season 2017_C; Festuca rubra; in plot B067, which is referring to DL4 in P1; replicate b. The plot numbers (e.g. A002 and B067) and the corresponding DLs (e.g. DL2 and DL4) are specified in the sample metadata in the data records MTBLS679 33 . The sample preparation and extraction for the LC-MS data acquisition were conducted in the order of the respective Lab-IDs to ensure the equal distribution of seasons and full randomisation across the species, DL and replicates. Details on the randomisation can be found in the section "Sequence of LC-MS Measurements". All details concerning the sampling strategy are included in the sample table in the MTBLS679 33 data repository.

LC-MS data dacquisition. Cryo sample preparation.
We prepared the 511 study samples of frozen shoot material, collected in 20 mL vials, by adding two steel balls (7 mm) to the tubes. One sample tube (2017_B: FESRUB (P1): DL1_b) broke prior to analysis and was, therefore, excluded from further analysis. We used a cryo ball mill equipped with an autosampler (Labman IPB Cryogrinder Ball Mill, Labman Automation, Middlesbrough, UK) to grind the material at −75 °C for 150 s (5 cycles: 30 s grinding, 30 s pausing). We ground the samples according to their Lab-IDs and the season they were collected in (Fig. 1 ⑥).
Methanolic extraction. We transferred aliquots (100 mg ± 50 mg) of the fine frozen powder to extraction tubes and added extraction beads (Rimax/Zircosil, 1.2-1.7 mm). For the extraction, we used methanol/water (80/20 v/v; HPLC-grade, Honeywell, Seelze, Germany) as the extraction solvent. We added the following internal standards at a 5 mM concentration to the extraction solvent: Kinetin (Roth, Karlsruhe, Germany), IAA-Val (Sigma-Aldrich, St. Louis, USA) and Biochanin A (Sigma-Aldrich, St. Louis, USA). The extraction solvent was added in a weight-specific five-fold surplus (Fig. 1 ⑦) to the frozen powder (e.g. 500 µL added to 100 mg powder), which we kept on liquid nitrogen. We thawed the prepared samples for 3 minutes at room temperature before extracting them in a homogeniser (Precellys ® 24 Tissue Homogenizer, Bertin Technologies, Montigny-le-Bretonneux, France) for 90 s (2 cycles: 45 s run, 15 s pausing) at 6500 rpm. We centrifuged the extracts at 16168 g for 15 min and collected the supernatants in fresh extraction tubes (Fig. 3a). After an additional extraction of the remaining pellet, 160 µL of the combined supernatants were added to 40 µL of water/formic acid (99.9/0.1 v/v) (formic acid: VWR International, Radnor, USA) and stored at −20 °C for at least 48 hours (Fig. 3a).
To prepare the samples for mass spectrometry, we centrifuged the sample extracts at 16168 g for 15 minutes to remove particles. We transferred 160 µL of the resulting supernatant to vials equipped with 300 µL glass inserts www.nature.com/scientificdata www.nature.com/scientificdata/  Quality controls. We used two types of blanks to account for possible contamination or inconsistency during extraction. The field blanks (plastic vials used for sampling) were included in the sampling, transportation and grinding steps. After the sampling in season 2017_A, we used a new shipment of plastic vials. We, therefore, labelled the field blanks "old" and "new" for the vials either used in 2017_A or 2017_B to 2017_D, respectively. We used the extraction blanks (eX01-03) to capture contaminations introduced in the methanolic extraction steps. For each replacement of extraction solvent, a new extraction blank was used. Both field blanks and extraction blanks were processed according to the extraction protocol applied to the study samples.
Sequence of LC-MS measurements. We measured the 511 analytical samples in 12 analytical batches. Each batch was composed of an acetonitrile aliquot, a blank, a QC aliquot and 44 analytical samples (Fig. 1 ⑨, Fig. 3c). We distributed the analytical samples equally across the batches in the order of their Lab-IDs, and the season they were collected in (Lab-IDs were assigned to the samples randomly while sampling; see "Traits & Sampling"). For example, the analytical samples 2017_A_001 to 011, 2017_B_001 to 011, 2017_C_001 to 011, and 2017_D_001 to 011 were measured in batch "pos01". We started the batch measurement sequence with three acetonitrile runs followed by the QC. After this run-in sequence, we measured the QC again, to equilibrate both the LC-column and MS-system, followed by one blank and a block of 11 analytical samples (Fig. 3c). We used the different blanks to detect potential systematic contaminations that were either introduced during sampling, extraction or the LC-MS measurements. After each block of analytical samples, we measured the QC again. The samples measured within one block were chosen randomly from the 44 samples assigned to the batch. After each batch, the MS ion source was cleaned, and the MS was recalibrated.
We pre-processed the raw LC-MS spectra of the analytical samples and the quality controls (blanks and QC) on the Galaxy-W4M infrastructure 31 (based on XCMS 3.0). The workflow (https://doi.org/10.15454/1.56404977 89529167E12) includes the following analytical and processing steps: feature detection, grouping and retention time correction (Fig. 1 ⑫). A detailed description of parameter settings and tool versions used in the workflow is also shown in Table 2.
The initial step in the workflow is feature detection. The parameters were set in order to separate measured peaks from background noise ( Table 2). We then grouped the features across samples and corrected them for retention time shifts. We grouped the corrected spectra again and annotated adducts and isotopes of the measured features.
After these pre-processing steps, we filtered the detected features for the region of interest (ROI). We cut features with retention times between 0 s to 80 s (injection peak and very polar compounds) and from 840 s to 1080 s (very nonpolar compounds). We exported the pre-processed data as separate data tables for sample metadata (sampleMetadata), variable metadata (variableMetadata) and the data matrix (dataMatrix), containing the measured intensities. These data matrices are also available in the associated metadata records MTBLS679 33 . The number of detected features per species is shown in Table 3.

Data Records
A detailed description of the experimental setup, the performed analysis and the metadata of both study samples and the quality controls are available as MTBLS679 33 "From Field to Feature in Ecometabolomics -LC-MS Based Metabolite Profiles of Thirteen Grassland Plant Species Reflecting Environmental Dynamics". Raw data files of LC-MS analysis are also available in the repository. Furthermore, we provide data matrices of all stages of the processing steps (see Table 1). www.nature.com/scientificdata www.nature.com/scientificdata/ The W4M-Galaxy history (https://doi.org/10.15454/1.5640497789529167E12) that was used for data pre-processing is available at https://workflow4metabolomics.usegalaxy.fr/histories/list_published. All processing steps used for the data clean up are explained in the Supplementary File 1.

Technical Validation
Data processing. A detailed tutorial of the processing steps performed in R 32 and the complete code used for data processing are provided as PDF and as R script in the MTBLS679 33 repository. The tutorial PDF is also made available as supplemental material (Supplementary File 1).
Missing data imputation. In this study, the pre-processing of highly diverse LC-MS spectra lead to a data matrix with 90% zero values. This high number of zeros is a result of the data matrix containing all detected features, of which only small fractions belonged to a particular species (Table 3). Hence, features that are not part of the metabolic fingerprint in this species were not detected and are recognised as true zeros. Within a species, some features are only detected in a few specimens. These absences either occur due to variations in the technical performance or are indicators of actual biological adaptations to environmental changes. These are NA values, as the reason for their absence is uncertain at this stage of analysis. In the following, we refer to any missing values as missing data. In order to prepare the data matrix for further data cleaning and to make it accessible to processing and statistical analysis, we replaced the missing data with imputed values. Here, we imputed the missing data with random values (noise) by drawing absolute values from a normal distribution with mean 70 and a standard deviation of 20.

Tool name Description Version Parameter Value
MSnbase readMSData Import mass-spectrometry data files 2.  www.nature.com/scientificdata www.nature.com/scientificdata/ We chose these values as they are below the threshold initially set for our data set, which equals 100 ( Fig. 1 ⑬, see Table 2: feature detection). This choice is instrument specific and based on the prefilter parameters used in the pre-processing steps.
Batch correction. We performed a batch correction on the imputed data matrix. Splitting the 511 analytical samples into 12 analytical batches enhanced the chance of technical performance variability due to cleaning, recalibration and solvent replacements. These batch effects are mostly reflected in changes of intensities of the features across different batches. To account for these intensity shifts, the QC, which was measured multiple times across all batches (see "Sequence of LC-MS Measurements"), was used to determine the unwanted variation within (intra-batch distance) and between (inter-batch distance) batches. Ideally, the intensity profiles of the QC in all batches are identical. However, systematic variation between and within batches was present. Here, we used the RUVs function in the RUVSeq package (version 1.20.0) 37 , which is based on a principal component analysis (PCA), and applied it to the QC measurements (referred to as pool in dataMatrix). RUVs creates a PCA model of the systematic part of the variation of the QC. This PCA model describes unwanted systematic variation. In the next step, it substracts the PCA model from the study samples; thereby eliminating any unwanted systematic variation. A detailed description of the underlying calculations can be found in Risso et al. 37 .
The performance of the batch correction mainly depends on the number of components used for the analysis. We determined the optimal number of components to be used for the correction with a scree plot. In this scree plot, we compared the remaining inter-batch distances (Supplementary File 1 Fig. 1) after correction for different numbers of components. In this data set, the knee (or elbow) in the plot was reached after 6 components, as the inter-batch distances did not decrease anymore after 6 components (see Supplementary File 1 Table 3.2). After the batch correction, the calculated inter-batch distances for the QC measurements showed a strong decline (Table 4; Fig. 1 ⑭). The score plots before the batch correction show apparent batch effects in PC 1 and PC 2 ( Fig. 1 ⑭). This shows that the batches, in which the QC has been measured, are the largest systematic source of variation for the QC measurements. After correction, the pattern in the PCs related to the different batches was no longer distinguishable. This shows that the huge variation of the feature intensities present in the original measurements related to the batches is removed and does not influence any consequent (statistical) analysis.
After performing the batch correction, the QC measurements are removed from both the metadata and data matrix (Table 1).  www.nature.com/scientificdata www.nature.com/scientificdata/ Blank removal. We checked the validity of the features before using them in the statistical analysis. We assigned a feature as valid when it was derived from an analytical sample. Here, we used the blanks as a reference for the validity check. Blanks did not contain a biological sample but were handled and processed like the analytical samples. Hence, we considered all features that were detected in blanks to be systematic contaminations introduced during sampling, extraction or the LC-MS analytical process. We removed all features that were detected in at least one blank from the data matrix and excluded them from any further analysis (Fig. 1 ⑮; see Table 3 for the number of features before and after the blank removal). Following this feature validity check, we also removed the blank samples from the sample metadata (Table 1).
Sample validity check. The amount of biological variation in the metabolomic profiles within a species differed across the species. This intra-species variation was found to be lower than the inter-species variation. To check the validity of each sample and, thereby, ensuring that the sample was not contaminated, we compared their metabolomic profiles to the average composition of their species. Here, we defined a feature as belonging to a species when it was detected in at least 8 of the samples (25%) in that species (Table 3). Note that for assigning a feature to the respective species, we used the data matrix without the imputed values (see "Missing Data Imputation"). As a quality measure, for each sample, we calculated Mahalanobis distances (Fig. 1 ⑯). We compared the distance of each sample to the average distance of the remaining samples in the respective species. For example, we calculated distances for the 32 samples in the species Holcus lanatus and compared the distance of the sample "HOLLAN (P2): 2017_A (DL4_b)" to the average distance of the other 31 samples. We kept only those samples that were closer than three times the average distance and shared over 25% of their features with their species (Table 1). Consequently, we excluded the following samples from further analysis as they did not pass the validity check: Preparation for statistical analysis. After performing validity checks on the data, we prepared the cleaned and processed data matrix to be used for statistical analysis. The data matrix can be accessed in three different stages, with (1) imputed values or (2) zeros or (3) NAs for missing values (see "Missing Data Imputation"). Depending on the nature of the planned analysis, either one of the matrices can be used for statistical analysis and conclusion drawing.

Usage Notes
This comprehensive data set provides the opportunity to investigate the metabolomic profiles on the feature level of thirteen grassland species grown in diverse neighbourhoods. The profiles were acquired from plants collected at different time point across the growing season. Therefore, relevant features and seasonality can be investigated within this eco-metabolomic dataset. Additionally, the mass spectrometry raw data are available in an open file format (mzML) and provide the opportunity to be re-processed with common metabolomics tools, such as xcms, OpenMS and MS-Dial.

Code availability
The raw data files and processed data matrices are available in the online repository MTBLS679 33 . The complete history of the used workflow for the raw LC-MS data pre-processing is available in Galaxy-W4M 31 from https:// doi.workflow4metabolomics.org/W4M00008. We provide the complete R 32 script used to process the data along with a detailed tutorial in the supplemental material (Supplementary File 1).