Dihydroferulate
Formula: C10H12O4 (196.0736)
Chinese Name: 3-(4-羟基-3-甲氧苯基)丙酸, 二氢阿魏酸, 磷酸异丙酯(单双酯混合物)
BioDeep ID: BioDeep_00000017611
( View LC/MS Profile)
SMILES: COC1=C(C=CC(=C1)CCC(=O)O)O
Found 57 Sample Hits
m/z | Adducts | Species | Organ | Scanning | Sample | |
---|---|---|---|---|---|---|
161.0599 | [M+H-2H2O]+PPM:1.2 |
Marker Pen | NA | DESI (None) |
3ul_0.8Mpa_RAW_20241016-PAPER PNMK - MEMI_testResolution: 30μm, 315x42
By writing the four English letters “PNMK” on white paper with a marker pen, and then scanning with a DESI ion source to obtain the scanning result. The signal of the chemical substances on the marker pen used appears on the channel with an m/z value of |
|
197.0787 | [M+H]+PPM:10.8 |
Marker Pen | NA | DESI (None) |
3ul_0.8Mpa_RAW_20241016-PAPER PNMK - MEMI_testResolution: 30μm, 315x42
By writing the four English letters “PNMK” on white paper with a marker pen, and then scanning with a DESI ion source to obtain the scanning result. The signal of the chemical substances on the marker pen used appears on the channel with an m/z value of |
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196.094 | [M-H2O+NH4]+PPM:14.4 |
Mus musculus | Kidney | MALDI (CHCA) |
FULL_MS_centriod_CHCA_20210819 - FULL_MS_centriod_CHCA_20210819Resolution: 17μm, 638x437
AP-MALDI instrument demo test, mass spectrum scan in centroid mode. |
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161.0601 | [M+H-2H2O]+PPM:2.5 |
Plant | Root | MALDI (DHB) |
MPIMM_035_QE_P_PO_6pm - MPIMM_035_QE_P_PO_6pmResolution: 30μm, 165x170
|
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179.0693 | [M+H-H2O]+PPM:5.4 |
Rattus norvegicus | Epididymis | MALDI (DHB) |
epik_dhb_head_ito03_17 - MTBLS58Resolution: 17μm, 208x108
1 male adult wild-type rat was obtained from Inserm U1085 - Irset Research Institute (University of Rennes1, France). Animals were age 60 days and were reared under ad-lib conditions. Care and handling of all animals complied with EU directive 2010/63/EU on the protection of animals used for scientific purposes. The whole epididymis was excised from each animal immediately post-mortem, loosely wrapped rapidly in an aluminum foil and a 2.5% (w/v) carboxymethylcellulose (CMC) solution was poured to embed the epididymis to preserve their morphology. To remove air bubbles, the filled aluminum molds was gently freezed by depositing it on isopentane or dry ice, then on the nitrogen vapors and finally by progressively dipping the CMC/sample coated with aluminum foil into liquid nitrogen (or only flush with liquid nitrogen). Frozen tissues were stored at -80 °C until use to avoid degradation. |
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179.0693 | [M+H-H2O]+PPM:5.4 |
Rattus norvegicus | Epididymis | MALDI (DHB) |
epik_dhb_head_ito03_18 - MTBLS58Resolution: 17μm, 208x104
|
|
179.0694 | [M+H-H2O]+PPM:4.8 |
Rattus norvegicus | Epididymis | MALDI (DHB) |
epik_dhb_head_ito08_43 - MTBLS58Resolution: 17μm, 298x106
|
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179.0695 | [M+H-H2O]+PPM:4.3 |
Rattus norvegicus | Epididymis | MALDI (DHB) |
epik_dhb_head_ito08_44 - MTBLS58Resolution: 17μm, 299x111
|
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179.0695 | [M+H-H2O]+PPM:4.3 |
Rattus norvegicus | Epididymis | MALDI (DHB) |
epik_dhb_head_ito08_46 - MTBLS58Resolution: 17μm, 298x106
|
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196.0951 | [M-H2O+NH4]+PPM:8.7 |
Vitis vinifera | Fruit | MALDI (DHB) |
grape_dhb_164_1 - Grape DatabaseResolution: 17μm, 136x122
Grape berries fruit, condition: Late |
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179.0695 | [M+H-H2O]+PPM:4.3 |
Rattus norvegicus | Epididymis | MALDI (DHB) |
epik_dhb_head_ito08_47 - MTBLS58Resolution: 17μm, 301x111
|
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179.0696 | [M+H-H2O]+PPM:3.7 |
Rattus norvegicus | Epididymis | MALDI (DHB) |
epik_dhb_head_ito08_48 - MTBLS58Resolution: 17μm, 294x107
|
|
179.0695 | [M+H-H2O]+PPM:4.3 |
Rattus norvegicus | Epididymis | MALDI (DHB) |
epik_dhb_head_ito01_04 - MTBLS58Resolution: 17μm, 178x91
|
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179.0694 | [M+H-H2O]+PPM:4.8 |
Rattus norvegicus | Epididymis | MALDI (DHB) |
epik_dhb_head_ito01_03 - MTBLS58Resolution: 17μm, 159x110
|
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179.0695 | [M+H-H2O]+PPM:4.3 |
Rattus norvegicus | normal | MALDI (DHB) |
epik_dhb_head_ito01_05 - MTBLS58Resolution: 17μm, 183x105
|
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179.0694 | [M+H-H2O]+PPM:4.8 |
Rattus norvegicus | Epididymis | MALDI (DHB) |
epik_dhb_head_ito01_06 - MTBLS58Resolution: 17μm, 183x103
|
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179.0695 | [M+H-H2O]+PPM:4.3 |
Rattus norvegicus | Epididymis | MALDI (DHB) |
epik_dhb_head_ito03_14 - MTBLS58Resolution: 17μm, 205x103
|
|
161.0594 | [M+H-2H2O]+PPM:1.9 |
Posidonia oceanica | root | MALDI (CHCA) |
20190614_MS1_A19r-20 - MTBLS1746Resolution: 17μm, 262x276
Seagrasses are one of the most efficient natural sinks of carbon dioxide (CO2) on Earth. Despite covering less than 0.1% of coastal regions, they have the capacity to bury up to 10% of marine organic matter and can bury the same amount of carbon 35 times faster than tropical rainforests. On land, the soil’s ability to sequestrate carbon is intimately linked to microbial metabolism. Despite the growing attention to the link between plant production, microbial communities, and the carbon cycle in terrestrial ecosystems, these processes remain enigmatic in the sea. Here, we show that seagrasses excrete organic sugars, namely in the form of sucrose, into their rhizospheres. Surprisingly, the microbial communities living underneath meadows do not fully use this sugar stock in their metabolism. Instead, sucrose piles up in the sediments to mM concentrations underneath multiple types of seagrass meadows. Sediment incubation experiments show that microbial communities living underneath a meadow use sucrose at low metabolic rates. Our metagenomic analyses revealed that the distinct community of microorganisms occurring underneath meadows is limited in their ability to degrade simple sugars, which allows these compounds to persist in the environment over relatively long periods of time. Our findings reveal how seagrasses form blue carbon stocks despite the relatively small area they occupy. Unfortunately, anthropogenic disturbances are threatening the long-term persistence of seagrass meadows. Given that these sediments contain a large stock of sugars that heterotopic bacteria can degrade, it is even more important to protect these ecosystems from degradation. |
|
179.0689 | [M+H-H2O]+PPM:7.6 |
Posidonia oceanica | root | MALDI (CHCA) |
20190614_MS1_A19r-20 - MTBLS1746Resolution: 17μm, 262x276
Seagrasses are one of the most efficient natural sinks of carbon dioxide (CO2) on Earth. Despite covering less than 0.1% of coastal regions, they have the capacity to bury up to 10% of marine organic matter and can bury the same amount of carbon 35 times faster than tropical rainforests. On land, the soil’s ability to sequestrate carbon is intimately linked to microbial metabolism. Despite the growing attention to the link between plant production, microbial communities, and the carbon cycle in terrestrial ecosystems, these processes remain enigmatic in the sea. Here, we show that seagrasses excrete organic sugars, namely in the form of sucrose, into their rhizospheres. Surprisingly, the microbial communities living underneath meadows do not fully use this sugar stock in their metabolism. Instead, sucrose piles up in the sediments to mM concentrations underneath multiple types of seagrass meadows. Sediment incubation experiments show that microbial communities living underneath a meadow use sucrose at low metabolic rates. Our metagenomic analyses revealed that the distinct community of microorganisms occurring underneath meadows is limited in their ability to degrade simple sugars, which allows these compounds to persist in the environment over relatively long periods of time. Our findings reveal how seagrasses form blue carbon stocks despite the relatively small area they occupy. Unfortunately, anthropogenic disturbances are threatening the long-term persistence of seagrass meadows. Given that these sediments contain a large stock of sugars that heterotopic bacteria can degrade, it is even more important to protect these ecosystems from degradation. |
|
197.0782 | [M+H]+PPM:13.4 |
Posidonia oceanica | root | MALDI (CHCA) |
20190614_MS1_A19r-20 - MTBLS1746Resolution: 17μm, 262x276
Seagrasses are one of the most efficient natural sinks of carbon dioxide (CO2) on Earth. Despite covering less than 0.1% of coastal regions, they have the capacity to bury up to 10% of marine organic matter and can bury the same amount of carbon 35 times faster than tropical rainforests. On land, the soil’s ability to sequestrate carbon is intimately linked to microbial metabolism. Despite the growing attention to the link between plant production, microbial communities, and the carbon cycle in terrestrial ecosystems, these processes remain enigmatic in the sea. Here, we show that seagrasses excrete organic sugars, namely in the form of sucrose, into their rhizospheres. Surprisingly, the microbial communities living underneath meadows do not fully use this sugar stock in their metabolism. Instead, sucrose piles up in the sediments to mM concentrations underneath multiple types of seagrass meadows. Sediment incubation experiments show that microbial communities living underneath a meadow use sucrose at low metabolic rates. Our metagenomic analyses revealed that the distinct community of microorganisms occurring underneath meadows is limited in their ability to degrade simple sugars, which allows these compounds to persist in the environment over relatively long periods of time. Our findings reveal how seagrasses form blue carbon stocks despite the relatively small area they occupy. Unfortunately, anthropogenic disturbances are threatening the long-term persistence of seagrass meadows. Given that these sediments contain a large stock of sugars that heterotopic bacteria can degrade, it is even more important to protect these ecosystems from degradation. |
|
161.0593 | [M+H-2H2O]+PPM:2.5 |
Posidonia oceanica | root | MALDI (CHCA) |
20190822_MS1_A19r-19 - MTBLS1746Resolution: 17μm, 303x309
Seagrasses are among the most efficient sinks of carbon dioxide on Earth. While carbon sequestration in terrestrial plants is linked to the microorganisms living in their soils, the interactions of seagrasses with their rhizospheres are poorly understood. Here, we show that the seagrass, Posidonia oceanica excretes sugars, mainly sucrose, into its rhizosphere. These sugars accumulate to µM concentrations—nearly 80 times higher than previously observed in marine environments. This finding is unexpected as sugars are readily consumed by microorganisms. Our experiments indicated that under low oxygen conditions, phenolic compounds from P. oceanica inhibited microbial consumption of sucrose. Analyses of the rhizosphere community revealed that many microbes had the genes for degrading sucrose but these were only expressed by a few taxa that also expressed genes for degrading phenolics. Given that we observed high sucrose concentrations underneath three other species of marine plants, we predict that the presence of plant-produced phenolics under low oxygen conditions allows the accumulation of labile molecules across aquatic rhizospheres. |
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161.0597 | [M+H-2H2O]+PPM:0 |
Posidonia oceanica | root | MALDI (CHCA) |
20190613_MS1_A19r-18 - MTBLS1746Resolution: 17μm, 246x264
|
|
179.07 | [M+H-H2O]+PPM:1.5 |
Posidonia oceanica | root | MALDI (CHCA) |
20190613_MS1_A19r-18 - MTBLS1746Resolution: 17μm, 246x264
|
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196.0955 | [M-H2O+NH4]+PPM:6.7 |
Posidonia oceanica | root | MALDI (CHCA) |
20190613_MS1_A19r-18 - MTBLS1746Resolution: 17μm, 246x264
|
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161.0594 | [M+H-2H2O]+PPM:1.9 |
Posidonia oceanica | root | MALDI (CHCA) |
20190828_MS1_A19r-22 - MTBLS1746Resolution: 17μm, 292x279
|
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161.0596 | [M+H-2H2O]+PPM:0.6 |
Posidonia oceanica | root | MALDI (CHCA) |
MS1_20180404_PO_1200 - MTBLS1746Resolution: 17μm, 193x208
|
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179.0699 | [M+H-H2O]+PPM:2 |
Posidonia oceanica | root | MALDI (CHCA) |
MS1_20180404_PO_1200 - MTBLS1746Resolution: 17μm, 193x208
|
|
197.0789 | [M+H]+PPM:9.8 |
Posidonia oceanica | root | MALDI (CHCA) |
MS1_20180404_PO_1200 - MTBLS1746Resolution: 17μm, 193x208
|
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161.0621 | [M+H-2H2O]+PPM:14.9 |
Homo sapiens | esophagus | DESI () |
LNTO22_1_3 - MTBLS385Resolution: 75μm, 121x68
|
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179.071 | [M+H-H2O]+PPM:4.1 |
Homo sapiens | esophagus | DESI () |
LNTO22_1_3 - MTBLS385Resolution: 75μm, 121x68
|
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197.0806 | [M+H]+PPM:1.2 |
Homo sapiens | esophagus | DESI () |
LNTO22_1_3 - MTBLS385Resolution: 75μm, 121x68
|
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179.07 | [M+H-H2O]+PPM:1.5 |
Homo sapiens | esophagus | DESI () |
LNTO22_1_4 - MTBLS385Resolution: 17μm, 82x80
|
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161.0592 | [M+H-2H2O]+PPM:3.1 |
Homo sapiens | esophagus | DESI () |
LNTO29_16_2 - MTBLS385Resolution: 17μm, 95x101
|
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179.0698 | [M+H-H2O]+PPM:2.6 |
Homo sapiens | esophagus | DESI () |
LNTO29_16_2 - MTBLS385Resolution: 17μm, 95x101
|
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197.0797 | [M+H]+PPM:5.7 |
Homo sapiens | esophagus | DESI () |
LNTO29_16_2 - MTBLS385Resolution: 17μm, 95x101
|
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214.1082 | [M+NH4]+PPM:3.8 |
Homo sapiens | esophagus | DESI () |
LNTO29_16_2 - MTBLS385Resolution: 17μm, 95x101
|
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196.0902 | [M-H2O+NH4]+PPM:6.2 |
Mus musculus | Liver | MALDI (CHCA) |
Salmonella_final_pos_recal - MTBLS2671Resolution: 17μm, 691x430
A more complete and holistic view on host–microbe interactions is needed to understand the physiological and cellular barriers that affect the efficacy of drug treatments and allow the discovery and development of new therapeutics. Here, we developed a multimodal imaging approach combining histopathology with mass spectrometry imaging (MSI) and same section imaging mass cytometry (IMC) to study the effects of Salmonella Typhimurium infection in the liver of a mouse model using the S. Typhimurium strains SL3261 and SL1344. This approach enables correlation of tissue morphology and specific cell phenotypes with molecular images of tissue metabolism. IMC revealed a marked increase in immune cell markers and localization in immune aggregates in infected tissues. A correlative computational method (network analysis) was deployed to find metabolic features associated with infection and revealed metabolic clusters of acetyl carnitines, as well as phosphatidylcholine and phosphatidylethanolamine plasmalogen species, which could be associated with pro-inflammatory immune cell types. By developing an IMC marker for the detection of Salmonella LPS, we were further able to identify and characterize those cell types which contained S. Typhimurium.
[dataset] Nicole Strittmatter. Holistic Characterization of a Salmonella Typhimurium Infection Model Using Integrated Molecular Imaging, metabolights_dataset, V1; 2022. https://www.ebi.ac.uk/metabolights/MTBLS2671. |
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161.0622 | [M+H-2H2O]+PPM:15.5 |
Homo sapiens | esophagus | DESI () |
LNTO22_1_9 - MTBLS385Resolution: 75μm, 89x74
|
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179.0707 | [M+H-H2O]+PPM:2.4 |
Homo sapiens | esophagus | DESI () |
LNTO22_1_9 - MTBLS385Resolution: 75μm, 89x74
|
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197.0796 | [M+H]+PPM:6.2 |
Homo sapiens | esophagus | DESI () |
LNTO22_1_9 - MTBLS385Resolution: 75μm, 89x74
|
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179.0691 | [M+H-H2O]+PPM:6.5 |
Homo sapiens | esophagus | DESI () |
LNTO29_16_3 - MTBLS385Resolution: 17μm, 108x107
|
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197.0797 | [M+H]+PPM:5.7 |
Homo sapiens | esophagus | DESI () |
LNTO29_16_3 - MTBLS385Resolution: 17μm, 108x107
|
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214.1081 | [M+NH4]+PPM:3.4 |
Homo sapiens | esophagus | DESI () |
LNTO29_16_3 - MTBLS385Resolution: 17μm, 108x107
|
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161.0613 | [M+H-2H2O]+PPM:9.9 |
Homo sapiens | esophagus | DESI () |
LNTO22_1_5 - MTBLS385Resolution: 75μm, 135x94
|
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179.0707 | [M+H-H2O]+PPM:2.4 |
Homo sapiens | esophagus | DESI () |
LNTO22_1_5 - MTBLS385Resolution: 75μm, 135x94
|
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161.0621 | [M+H-2H2O]+PPM:14.9 |
Homo sapiens | esophagus | DESI () |
LNTO22_1_7 - MTBLS385Resolution: 75μm, 69x54
|
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179.0706 | [M+H-H2O]+PPM:1.9 |
Homo sapiens | esophagus | DESI () |
LNTO22_1_7 - MTBLS385Resolution: 75μm, 69x54
|
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197.0795 | [M+H]+PPM:6.8 |
Homo sapiens | esophagus | DESI () |
LNTO22_1_7 - MTBLS385Resolution: 75μm, 69x54
|
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161.0619 | [M+H-2H2O]+PPM:13.6 |
Homo sapiens | esophagus | DESI () |
LNTO22_1_8 - MTBLS385Resolution: 75μm, 69x61
|
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179.0709 | [M+H-H2O]+PPM:3.5 |
Homo sapiens | esophagus | DESI () |
LNTO22_1_8 - MTBLS385Resolution: 75μm, 69x61
|
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197.0796 | [M+H]+PPM:6.2 |
Homo sapiens | esophagus | DESI () |
LNTO22_1_8 - MTBLS385Resolution: 75μm, 69x61
|
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161.062 | [M+H-2H2O]+PPM:14.3 |
Homo sapiens | esophagus | DESI () |
LNTO22_2_1 - MTBLS385Resolution: 75μm, 89x88
|
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161.0623 | [M+H-2H2O]+PPM:16.1 |
Homo sapiens | esophagus | DESI () |
LNTO22_2_2 - MTBLS385Resolution: 75μm, 135x94
|
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179.0704 | [M+H-H2O]+PPM:0.7 |
Homo sapiens | esophagus | DESI () |
LNTO22_2_2 - MTBLS385Resolution: 75μm, 135x94
|
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179.0702 | [M+H-H2O]+PPM:0.4 |
Homo sapiens | esophagus | DESI () |
LNTO29_18_2 - MTBLS385Resolution: 75μm, 62x68
|
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214.1081 | [M+NH4]+PPM:3.4 |
Homo sapiens | esophagus | DESI () |
LNTO29_18_2 - MTBLS385Resolution: 75μm, 62x68
|
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197.0809 | [M+H]+PPM:0.3 |
Homo sapiens | esophagus | DESI () |
LNTO30_7_2 - MTBLS385Resolution: 75μm, 82x68
|
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Dihydroferulic acid is a monocarboxylic acid that is propanoic acid in which one of the hydrogens at position 3 has been replaced by a 4-hydroxy-3-methoxyphenyl group. It has a role as a human xenobiotic metabolite, a plant metabolite, a mouse metabolite and an antioxidant. It is a monocarboxylic acid, a phenylpropanoid and a member of guaiacols. It is functionally related to a propionic acid. It is a conjugate acid of a dihydroferulate. 3-(4-Hydroxy-3-methoxyphenyl)propionic acid is a natural product found in Colchicum kotschyi, Bulbophyllum vaginatum, and other organisms with data available. Dihydroferulic acid, also known as 3-(4-hydroxy-3-methoxyphenyl)propionic acid or dihydroconiferylate, is classified as a member of the phenylpropanoic acids. Phenylpropanoic acids are compounds with a structure containing a benzene ring conjugated to a propanoic acid. Dihydroferulic acid is considered to be slightly soluble (in water) and acidic. Dihydroferulic acid is a phenolic acid metabolite and was found to be significantly elevated in serum after whole grain consumption which makes this compound a potential serum biomarker of whole grain intake (PMID: 25646321). A monocarboxylic acid that is propanoic acid in which one of the hydrogens at position 3 has been replaced by a 4-hydroxy-3-methoxyphenyl group. A polyphenol metabolite detected in biological fluids [PhenolExplorer] Dihydroferulic acid (Hydroferulic acid) is one of the main metabolites of curcumin and antioxidant/radical-scavenging properties with an IC50 value of 19.5 μM. Dihydroferulic acid is a metabolite of human gut microflora as well as a precursor of vanillic acid[1][2]. Dihydroferulic acid (Hydroferulic acid) is one of the main metabolites of curcumin and antioxidant/radical-scavenging properties with an IC50 value of 19.5 μM. Dihydroferulic acid is a metabolite of human gut microflora as well as a precursor of vanillic acid[1][2].