Summary of Study ST004347
This data is available at the NIH Common Fund's National Metabolomics Data Repository (NMDR) website, the Metabolomics Workbench, https://www.metabolomicsworkbench.org, where it has been assigned Project ID PR002738. The data can be accessed directly via it's Project DOI: 10.21228/M8R54Z This work is supported by NIH grant, U2C- DK119886. See: https://www.metabolomicsworkbench.org/about/howtocite.php
| Study ID | ST004347 |
| Study Title | Homarine Catabolism: In situ metabolomics from KM1906, surface samples along a transect in the North Pacific |
| Study Summary | Across stations in the North Pacific, homarine concentrations (sum of dissolved and particulate measurements) were significantly correlated with hom gene transcript abundance (R² = 0.518, p = 0.0052, Spearman’s correlation), supporting coupling between substrate availability and gene expression. |
| Institute | University of Washington |
| Department | Oceanography |
| Last Name | Carlson |
| First Name | Laura |
| Address | 1501 NE Boat Street |
| truxal@uw.edu | |
| Phone | 2062216732 |
| Submit Date | 2025-11-03 |
| Study Comments | Part 3 of 6 datasets in project |
| Raw Data Available | Yes |
| Raw Data File Type(s) | mzML |
| Analysis Type Detail | LC-MS |
| Release Date | 2026-01-02 |
| Release Version | 1 |
Select appropriate tab below to view additional metadata details:
Project:
| Project ID: | PR002738 |
| Project DOI: | doi: 10.21228/M8R54Z |
| Project Title: | Conserved pathway for homarine catabolism in environmental bacteria |
| Project Summary: | Homarine (N-methylpicolinic acid) is a ubiquitous marine metabolite produced by phytoplankton and noted for its bioactivity in marine animals, yet its microbial degradation pathways are uncharacterized. Here, we identify a conserved operon (homABCDER) that mediates homarine catabolism in bacteria using comparative transcriptomics, mutagenesis, and targeted knockouts. Phylogenetic and genomic analyses show this operon distributed across abundant bacterial clades, including coastal copiotrophs (e.g., Rhodobacterales) and open-ocean oligotrophs (e.g., SAR11, SAR116). High-resolution mass spectrometry revealed N-methylglutamic acid and glutamic acid as key metabolic products of homarine in both model and natural systems, with N-methylglutamate dehydrogenase catalyzing their conversion. Metatranscriptomics showed responsive and in situ expression of hom genes aligned with homarine availability. These findings uncover the genetic and metabolic basis of homarine degradation, establish its ecological relevance, and highlight homarine as a versatile growth substrate that feeds into central metabolism via glutamic acid in diverse marine bacteria. |
| Institute: | University of Washington, School of Oceanography |
| Last Name: | Heal |
| First Name: | Katherine |
| Address: | 1501 NE Boat Street, Marine Science Building, Room G, Seattle |
| Email: | katherine.heal@pnnl.gov |
| Phone: | 612-616-4840 |
Subject:
| Subject ID: | SU004506 |
| Subject Type: | Water sample |
Factors:
Subject type: Water sample; Subject species: - (Factor headings shown in green)
| mb_sample_id | local_sample_id | Sample source | Lat | Long |
|---|---|---|---|---|
| SA516084 | 220623_Smp_MQBlk_5 | Dissolved_Blank | NA | NA |
| SA516085 | 220623_Smp_MQBlk_1 | Dissolved_Blank | NA | NA |
| SA516086 | 220623_Smp_MQBlk_2 | Dissolved_Blank | NA | NA |
| SA516087 | 220623_Smp_MQBlk_4 | Dissolved_Blank | NA | NA |
| SA516088 | 220623_Smp_MQBlk_3 | Dissolved_Blank | NA | NA |
| SA516089 | 220623_Smp_MQBlk_6 | Dissolved_Blank | NA | NA |
| SA516097 | 220623_Smp_MU1_A | Dissolved | 22.24 | -158 |
| SA516098 | 220623_Smp_MU1_C | Dissolved | 22.24 | -158 |
| SA516099 | 220623_Smp_MU1_B | Dissolved | 22.24 | -158 |
| SA516100 | 220623_Smp_MU2_C | Dissolved | 24.1 | -158 |
| SA516101 | 220623_Smp_MU2_A | Dissolved | 24.1 | -158 |
| SA516102 | 220623_Smp_MU2_B | Dissolved | 24.1 | -158 |
| SA516103 | 220623_Smp_MU3_C | Dissolved | 25.55 | -158 |
| SA516104 | 220623_Smp_MU3_B | Dissolved | 25.55 | -158 |
| SA516105 | 220623_Smp_MU3_A | Dissolved | 25.55 | -158 |
| SA516106 | 220623_Smp_MU4_A | Dissolved | 27.47 | -158 |
| SA516107 | 220623_Smp_MU4_B | Dissolved | 27.47 | -158 |
| SA516108 | 220623_Smp_MU4_C | Dissolved | 27.47 | -158 |
| SA516109 | 220623_Smp_MU5_A | Dissolved | 29.28 | -158 |
| SA516110 | 220623_Smp_MU5_B | Dissolved | 29.28 | -158 |
| SA516111 | 220623_Smp_MU5_C | Dissolved | 29.28 | -158 |
| SA516112 | 220623_Smp_MU6_A | Dissolved | 31.1 | -158 |
| SA516113 | 220623_Smp_MU6_B | Dissolved | 31.1 | -158 |
| SA516114 | 220623_Smp_MU6_C | Dissolved | 31.1 | -158 |
| SA516115 | 220623_Smp_MU7_C | Dissolved | 32.18 | -158 |
| SA516116 | 220623_Smp_MU7_A | Dissolved | 32.18 | -158 |
| SA516117 | 220623_Smp_MU7_B | Dissolved | 32.18 | -158 |
| SA516118 | 220623_Smp_MU13_C | Dissolved | 33 | -158 |
| SA516119 | 220623_Smp_MU13_B | Dissolved | 33 | -158 |
| SA516120 | 220623_Smp_MU13_A | Dissolved | 33 | -158 |
| SA516121 | 220623_Smp_MU8_C | Dissolved | 34.16 | -158 |
| SA516122 | 220623_Smp_MU8_A | Dissolved | 34.16 | -158 |
| SA516123 | 220623_Smp_MU8_B | Dissolved | 34.16 | -158 |
| SA516124 | 220623_Smp_MU9_C | Dissolved | 35.59 | -158 |
| SA516125 | 220623_Smp_MU9_B | Dissolved | 35.59 | -158 |
| SA516126 | 220623_Smp_MU9_A | Dissolved | 35.59 | -158 |
| SA516127 | 220623_Smp_MU10_C | Dissolved | 36.57 | -158 |
| SA516128 | 220623_Smp_MU10_B | Dissolved | 36.57 | -158 |
| SA516129 | 220623_Smp_MU10_A | Dissolved | 36.57 | -158 |
| SA516130 | 220623_Smp_MU14_B | Dissolved | 37.38 | -158 |
| SA516131 | 220623_Smp_MU14_A | Dissolved | 37.38 | -158 |
| SA516132 | 220623_Smp_MU14_C | Dissolved | 37.38 | -158 |
| SA516133 | 220623_Smp_MU12_A | Dissolved | 37 | -158 |
| SA516134 | 220623_Smp_MU12_B | Dissolved | 37 | -158 |
| SA516135 | 220623_Smp_MU12_C | Dissolved | 37 | -158 |
| SA516136 | 220623_Smp_MU15_B | Dissolved | 38.45 | -158 |
| SA516137 | 220623_Smp_MU15_A | Dissolved | 38.45 | -158 |
| SA516138 | 220623_Smp_MU15_C | Dissolved | 38.45 | -158 |
| SA516139 | 220623_Smp_MU11_B | Dissolved | 38.58 | -158 |
| SA516140 | 220623_Smp_MU11_A | Dissolved | 38.58 | -158 |
| SA516141 | 220623_Smp_MU11_C | Dissolved | 38.58 | -158 |
| SA516142 | 220623_Smp_MU16_A | Dissolved | 40.53 | -158 |
| SA516143 | 220623_Smp_MU16_B | Dissolved | 40.53 | -158 |
| SA516144 | 220623_Smp_MU16_C | Dissolved | 40.53 | -158 |
| SA516145 | 220623_Smp_MU17_B | Dissolved | 42.334 | -158 |
| SA516146 | 220623_Smp_MU17_A | Dissolved | 42.334 | -158 |
| SA516090 | 220623_Poo_TruePooG3-CXSPE_Full3 | Dissolved_QC | NA | NA |
| SA516091 | 220623_Poo_TruePooG3-CXSPE_Full2 | Dissolved_QC | NA | NA |
| SA516092 | 220623_Poo_TruePooG3-CXSPE_Full1 | Dissolved_QC | NA | NA |
| SA516093 | 220623_Std_4uMStdsMix1InH2O_1 | Dissolved_Standard | NA | NA |
| SA516094 | 220623_Std_4uMStdsMix1InH2O_2 | Dissolved_Standard | NA | NA |
| SA516095 | 220623_Std_4uMStdsMix2InH2O_1 | Dissolved_Standard | NA | NA |
| SA516096 | 220623_Std_4uMStdsMix2InH2O_2 | Dissolved_Standard | NA | NA |
| SA516147 | 220628_Smp_MMQBlk1_B | Particulate_Blank | NA | NA |
| SA516148 | 220628_Smp_MBlk1_B | Particulate_Blank | NA | NA |
| SA516149 | 220628_Smp_MBlk1_A | Particulate_Blank | NA | NA |
| SA516150 | 220628_Smp_MMQBlk1_A | Particulate_Blank | NA | NA |
| SA516158 | 220628_Smp_MU1_C | Particulate | 22.24 | -158 |
| SA516159 | 220628_Smp_MU1_A | Particulate | 22.24 | -158 |
| SA516160 | 220628_Smp_MU1_B | Particulate | 22.24 | -158 |
| SA516161 | 220628_Smp_MU2_A | Particulate | 24.1 | -158 |
| SA516162 | 220628_Smp_MU2_B | Particulate | 24.1 | -158 |
| SA516163 | 220628_Smp_MU2_C | Particulate | 24.1 | -158 |
| SA516164 | 220628_Smp_MU3_A | Particulate | 25.55 | -158 |
| SA516165 | 220628_Smp_MU3_B | Particulate | 25.55 | -158 |
| SA516166 | 220628_Smp_MU3_C | Particulate | 25.55 | -158 |
| SA516167 | 220628_Smp_MU4_A | Particulate | 27.47 | -158 |
| SA516168 | 220628_Smp_MU4_C | Particulate | 27.47 | -158 |
| SA516169 | 220628_Smp_MU4_B | Particulate | 27.47 | -158 |
| SA516170 | 220628_Smp_MU5_C | Particulate | 29.28 | -158 |
| SA516171 | 220628_Smp_MU5_B | Particulate | 29.28 | -158 |
| SA516172 | 220628_Smp_MU5_A | Particulate | 29.28 | -158 |
| SA516173 | 220628_Smp_MU6_A | Particulate | 31.1 | -158 |
| SA516174 | 220628_Smp_MU6_C | Particulate | 31.1 | -158 |
| SA516175 | 220628_Smp_MU6_B | Particulate | 31.1 | -158 |
| SA516176 | 220628_Smp_MU24_B | Particulate | 31.24 | -158 |
| SA516177 | 220628_Smp_MU24_C | Particulate | 31.24 | -158 |
| SA516178 | 220628_Smp_MU24_A | Particulate | 31.24 | -158 |
| SA516179 | 220628_Smp_MU7_C | Particulate | 32.18 | -158 |
| SA516180 | 220628_Smp_MU7_A | Particulate | 32.18 | -158 |
| SA516181 | 220628_Smp_MU7_B | Particulate | 32.18 | -158 |
| SA516182 | 220628_Smp_MU23_C | Particulate | 33.34 | -158 |
| SA516183 | 220628_Smp_MU23_B | Particulate | 33.34 | -158 |
| SA516184 | 220628_Smp_MU23_A | Particulate | 33.34 | -158 |
| SA516185 | 220628_Smp_MU8_C | Particulate | 34.16 | -158 |
| SA516186 | 220628_Smp_MU8_B | Particulate | 34.16 | -158 |
| SA516187 | 220628_Smp_MU8_A | Particulate | 34.16 | -158 |
| SA516188 | 220628_Smp_MU22_A | Particulate | 34.39 | -158 |
| SA516189 | 220628_Smp_MU22_C | Particulate | 34.39 | -158 |
| SA516190 | 220628_Smp_MU22_B | Particulate | 34.39 | -158 |
Collection:
| Collection ID: | CO004499 |
| Collection Summary: | Metabolite samples were collected during the Gradients 3 cruise (KM1906) in the North Pacific in 2019. Briefly, 10L of water was collected from the shipboard flow-through underway sampling system and particulate metabolites were sampled by filtering the seawater using peristaltic pumps onto 142 mm diameter, 0.2 um pore size PTFE Omnipore filters, flash frozen in liquid nitrogen, and stored at -80 C until analysis. Dissolved metabolites were sampled by collecting the filtrate in 50 mL acid washed polypropylene Falcon tubes. |
| Sample Type: | Marine particulate and dissolved matter |
| Storage Conditions: | -80℃ |
Treatment:
| Treatment ID: | TR004515 |
| Treatment Summary: | No treatment - this was a study of the natural marine microbial population of a transect in the North Pacific. |
Sample Preparation:
| Sampleprep ID: | SP004512 |
| Sampleprep Summary: | For particulate metabolites, cell pellets were extracted using a combination of mechanical and chemical disruption techniques as described in previous work (https://doi.org/10.1021/acs.analchem.7b04400). Dissolved metabolites were extracted using a cation-exchange-based solid phase extraction technique as described previously (https://doi.org/10.1002/lom3.10513). Following extraction, metabolites were dried down under N2 gas, reconstituted in water with isotope labeled internal standards, and analyzed using liquid chromatography mass spectrometry. Homarine concentrations were quantified by comparison to a 2H3-homarine internal standard. |
Combined analysis:
| Analysis ID | AN007257 |
|---|---|
| Chromatography ID | CH005508 |
| MS ID | MS006951 |
| Analysis type | MS |
| Chromatography type | HILIC |
| Chromatography system | Waters Acquity I-Class |
| Column | SeQuant ZIC- pHILIC (150 x 2.1mm,5um) |
| MS Type | ESI |
| MS instrument type | Orbitrap |
| MS instrument name | Thermo Q Exactive HF hybrid Orbitrap |
| Ion Mode | POSITIVE |
| Units | nM |
Chromatography:
| Chromatography ID: | CH005508 |
| Chromatography Summary: | For HILIC chromatography, a SeQuant ZIC-pHILIC column (5 um particle size, 2.1 mm x 150 mm, from Millipore) was used with 10 mM ammonium carbonate in 85:15 acetonitrile to water (Solvent A) and 10 mM ammonium carbonate in 85:15 water to acetonitrile (Solvent B) at a flow rate of 0.15 mL/min. This column was compared with a Waters UPLC BEH amide and a Millipore cHILIC column; the pHILIC showed superior reproducibility and peak shapes. The column was held at 100% A for 2 minutes, ramped to 64% B over 18 minutes, ramped to 100% B over 1 minute, held at 100% B for 5 minutes, and equilibrated at 100% A for 25 minutes (50 minutes total). The column was maintained at 30 C. The injection volume was 2 µL for samples and standard mixes. When starting a batch, the column was equilibrated at the starting conditions for at least 30 minutes. To improve the performance of the HILIC column, we maintained the same injection volume, kept the instrument running water blanks between samples as necessary, and injected standards in a representative matrix in addition to standards in water. After each batch, the column was flushed with 10 mM ammonium carbonate in 85:15 water to acetonitrile for 20 to 30 minutes. |
| Instrument Name: | Waters Acquity I-Class |
| Column Name: | SeQuant ZIC- pHILIC (150 x 2.1mm,5um) |
| Column Temperature: | 30 |
| Flow Gradient: | The column was held at 100% A for 2 minutes, ramped to 64% B over 18 minutes, ramped to 100% B over 1 minute, held at 100% B for 5 minutes, and equilibrated at 100% A for 25 minutes |
| Flow Rate: | 0.15 mL/min |
| Solvent A: | 85% acetonitrile/15% water; 10 mM ammonium carbonate |
| Solvent B: | 15% acetonitrile/85% water; 10 mM ammonium carbonate |
| Chromatography Type: | HILIC |
MS:
| MS ID: | MS006951 |
| Analysis ID: | AN007257 |
| Instrument Name: | Thermo Q Exactive HF hybrid Orbitrap |
| Instrument Type: | Orbitrap |
| MS Type: | ESI |
| MS Comments: | MS acquisition Comments: A full scan polarity switching method was used with a scan range of 60 to 900 m/z and a resolution of 60,000. MS parameters were as follows: capillary temperature was 320 ∞C, the H-ESI spray voltage was 3.5 kV, and the auxiliary gas heater temperature was 90 ∞C. The S-lens RF level was 65. Sheath gas, auxiliary gas, and sweep gas flow rates were maintained at 16, 3, and 1, respectively. |
| Ion Mode: | POSITIVE |