Dihydroxyacetone phosphate
Formula: C3H7O6P (169.998)
Chinese Name: 磷酸二氢丙酮, 磷酸二羟丙酮, 二羟丙酮磷酸
BioDeep ID: BioDeep_00000003224
( View LC/MS Profile)
SMILES: C(C(=O)COP(=O)(O)O)O
Found 68 Sample Hits
m/z | Adducts | Species | Organ | Scanning | Sample | |
---|---|---|---|---|---|---|
192.99 | [M+Na]+PPM:14.3 |
Plant | Root | MALDI (DHB) |
MPIMM_035_QE_P_PO_6pm - MPIMM_035_QE_P_PO_6pmResolution: 30μm, 165x170
|
|
192.9898 | [M+Na]+PPM:13.2 |
Vitis vinifera | Fruit | MALDI (DHB) |
grape_dhb_91_1 - Grape DatabaseResolution: 50μm, 120x114
Grape berries fruit, condition: Ripe |
|
192.9897 | [M+Na]+PPM:12.7 |
Vitis vinifera | Fruit | MALDI (DHB) |
grape_dhb_164_1 - Grape DatabaseResolution: 17μm, 136x122
Grape berries fruit, condition: Late |
|
192.9897 | [M+Na]+PPM:12.7 |
Vitis vinifera | Fruit | MALDI (DHB) |
grape_dhb_163_1 - Grape DatabaseResolution: 17μm, 132x115
Grape berries fruit, condition: Late |
|
152.9922 | [M+H-H2O]+PPM:16.6 |
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. |
|
170.0207 | [M-H2O+NH4]+PPM:3.4 |
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. |
|
171.0026 | [M+H]+PPM:15.8 |
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. |
|
192.9886 | [M+Na]+PPM:7 |
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. |
|
171.0027 | [M+H]+PPM:15.2 |
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. |
|
192.9893 | [M+Na]+PPM:10.6 |
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. |
|
170.021 | [M-H2O+NH4]+PPM:1.7 |
Posidonia oceanica | root | MALDI (CHCA) |
20190613_MS1_A19r-18 - MTBLS1746Resolution: 17μm, 246x264
|
|
171.0029 | [M+H]+PPM:14 |
Posidonia oceanica | root | MALDI (CHCA) |
20190613_MS1_A19r-18 - MTBLS1746Resolution: 17μm, 246x264
|
|
192.9895 | [M+Na]+PPM:11.7 |
Posidonia oceanica | root | MALDI (CHCA) |
20190613_MS1_A19r-18 - MTBLS1746Resolution: 17μm, 246x264
|
|
152.9922 | [M+H-H2O]+PPM:16.6 |
Posidonia oceanica | root | MALDI (CHCA) |
MS1_20180404_PO_1200 - MTBLS1746Resolution: 17μm, 193x208
|
|
171.0027 | [M+H]+PPM:15.2 |
Posidonia oceanica | root | MALDI (CHCA) |
MS1_20180404_PO_1200 - MTBLS1746Resolution: 17μm, 193x208
|
|
192.9888 | [M+Na]+PPM:8.1 |
Posidonia oceanica | root | MALDI (CHCA) |
MS1_20180404_PO_1200 - MTBLS1746Resolution: 17μm, 193x208
|
|
152.9952 | [M+H-H2O]+PPM:3 |
Homo sapiens | esophagus | DESI () |
LNTO22_1_3 - MTBLS385Resolution: 75μm, 121x68
|
|
171.006 | [M+H]+PPM:4.1 |
Homo sapiens | esophagus | DESI () |
LNTO22_1_3 - MTBLS385Resolution: 75μm, 121x68
|
|
152.9952 | [M+H-H2O]+PPM:3 |
Homo sapiens | esophagus | DESI () |
LNTO22_1_4 - MTBLS385Resolution: 17μm, 82x80
|
|
171.0059 | [M+H]+PPM:3.5 |
Homo sapiens | esophagus | DESI () |
LNTO22_1_4 - MTBLS385Resolution: 17μm, 82x80
|
|
192.9901 | [M+Na]+PPM:14.8 |
Homo sapiens | esophagus | DESI () |
LNTO22_1_4 - MTBLS385Resolution: 17μm, 82x80
|
|
152.9951 | [M+H-H2O]+PPM:2.4 |
Homo sapiens | esophagus | DESI () |
LNTO29_16_2 - MTBLS385Resolution: 17μm, 95x101
|
|
171.0069 | [M+H]+PPM:9.3 |
Homo sapiens | esophagus | DESI () |
LNTO29_16_2 - MTBLS385Resolution: 17μm, 95x101
|
|
152.9955 | [M+H-H2O]+PPM:5 |
Homo sapiens | esophagus | DESI () |
TO42T - MTBLS385Resolution: 17μm, 69x81
|
|
152.9954 | [M+H-H2O]+PPM:4.3 |
Homo sapiens | esophagus | DESI () |
LNTO22_1_9 - MTBLS385Resolution: 75μm, 89x74
|
|
171.0063 | [M+H]+PPM:5.8 |
Homo sapiens | esophagus | DESI () |
LNTO22_1_9 - MTBLS385Resolution: 75μm, 89x74
|
|
152.995 | [M+H-H2O]+PPM:1.7 |
Homo sapiens | esophagus | DESI () |
LNTO30_8M_1 - MTBLS385Resolution: 17μm, 69x54
|
|
152.9954 | [M+H-H2O]+PPM:4.3 |
Homo sapiens | esophagus | DESI () |
TO39T - MTBLS385Resolution: 17μm, 69x81
|
|
152.995 | [M+H-H2O]+PPM:1.7 |
Homo sapiens | esophagus | DESI () |
LNTO29_16_3 - MTBLS385Resolution: 17μm, 108x107
|
|
171.0058 | [M+H]+PPM:2.9 |
Homo sapiens | esophagus | DESI () |
LNTO29_16_3 - MTBLS385Resolution: 17μm, 108x107
|
|
152.9952 | [M+H-H2O]+PPM:3 |
Homo sapiens | esophagus | DESI () |
LNTO26_7_1 - MTBLS385Resolution: 17μm, 75x74
|
|
171.0064 | [M+H]+PPM:6.4 |
Homo sapiens | esophagus | DESI () |
LNTO26_7_1 - MTBLS385Resolution: 17μm, 75x74
|
|
152.9954 | [M+H-H2O]+PPM:4.3 |
Homo sapiens | esophagus | DESI () |
LNTO26_7_2 - MTBLS385Resolution: 17μm, 135x101
|
|
152.9952 | [M+H-H2O]+PPM:3 |
Homo sapiens | esophagus | DESI () |
LNTO26_7_3 - MTBLS385Resolution: 75μm, 82x88
|
|
171.0064 | [M+H]+PPM:6.4 |
Homo sapiens | esophagus | DESI () |
LNTO26_7_3 - MTBLS385Resolution: 75μm, 82x88
|
|
152.9953 | [M+H-H2O]+PPM:3.7 |
Homo sapiens | esophagus | DESI () |
TO40T - MTBLS385Resolution: 17μm, 82x74
|
|
152.9951 | [M+H-H2O]+PPM:2.4 |
Homo sapiens | esophagus | DESI () |
TO31T - MTBLS385Resolution: 75μm, 56x54
|
|
171.0063 | [M+H]+PPM:5.8 |
Homo sapiens | esophagus | DESI () |
TO31T - MTBLS385Resolution: 75μm, 56x54
|
|
192.9891 | [M+Na]+PPM:9.6 |
Homo sapiens | esophagus | DESI () |
TO31T - MTBLS385Resolution: 75μm, 56x54
|
|
152.9953 | [M+H-H2O]+PPM:3.7 |
Homo sapiens | esophagus | DESI () |
TO29T - MTBLS385Resolution: 75μm, 56x48
|
|
171.0066 | [M+H]+PPM:7.6 |
Homo sapiens | esophagus | DESI () |
TO29T - MTBLS385Resolution: 75μm, 56x48
|
|
192.9897 | [M+Na]+PPM:12.7 |
Homo sapiens | esophagus | DESI () |
TO29T - MTBLS385Resolution: 75μm, 56x48
|
|
152.9956 | [M+H-H2O]+PPM:5.6 |
Homo sapiens | esophagus | DESI () |
TO41T - MTBLS385Resolution: 75μm, 69x43
|
|
171.0057 | [M+H]+PPM:2.3 |
Homo sapiens | esophagus | DESI () |
TO41T - MTBLS385Resolution: 75μm, 69x43
|
|
152.995 | [M+H-H2O]+PPM:1.7 |
Homo sapiens | esophagus | DESI () |
LNTO30_8M_2 - MTBLS385Resolution: 75μm, 108x68
|
|
152.995 | [M+H-H2O]+PPM:1.7 |
Homo sapiens | esophagus | DESI () |
LNTO30_8M_3 - MTBLS385Resolution: 75μm, 69x54
|
|
152.9951 | [M+H-H2O]+PPM:2.4 |
Homo sapiens | esophagus | DESI () |
LNTO30_8M_4 - MTBLS385Resolution: 75μm, 62x48
|
|
152.9951 | [M+H-H2O]+PPM:2.4 |
Homo sapiens | esophagus | DESI () |
LNTO30_8M_5 - MTBLS385Resolution: 75μm, 56x54
|
|
152.9951 | [M+H-H2O]+PPM:2.4 |
Homo sapiens | esophagus | DESI () |
LNTO30_17_2 - MTBLS385Resolution: 75μm, 82x54
|
|
171.0066 | [M+H]+PPM:7.6 |
Homo sapiens | esophagus | DESI () |
LNTO30_17_2 - MTBLS385Resolution: 75μm, 82x54
|
|
152.9953 | [M+H-H2O]+PPM:3.7 |
Homo sapiens | esophagus | DESI () |
LNTO22_1_5 - MTBLS385Resolution: 75μm, 135x94
|
|
171.0066 | [M+H]+PPM:7.6 |
Homo sapiens | esophagus | DESI () |
LNTO22_1_5 - MTBLS385Resolution: 75μm, 135x94
|
|
152.9953 | [M+H-H2O]+PPM:3.7 |
Homo sapiens | esophagus | DESI () |
LNTO22_1_7 - MTBLS385Resolution: 75μm, 69x54
|
|
171.0061 | [M+H]+PPM:4.7 |
Homo sapiens | esophagus | DESI () |
LNTO22_1_7 - MTBLS385Resolution: 75μm, 69x54
|
|
152.9952 | [M+H-H2O]+PPM:3 |
Homo sapiens | esophagus | DESI () |
LNTO22_1_8 - MTBLS385Resolution: 75μm, 69x61
|
|
171.0066 | [M+H]+PPM:7.6 |
Homo sapiens | esophagus | DESI () |
LNTO22_1_8 - MTBLS385Resolution: 75μm, 69x61
|
|
192.9891 | [M+Na]+PPM:9.6 |
Homo sapiens | esophagus | DESI () |
LNTO22_1_8 - MTBLS385Resolution: 75μm, 69x61
|
|
152.9952 | [M+H-H2O]+PPM:3 |
Homo sapiens | esophagus | DESI () |
LNTO22_2_1 - MTBLS385Resolution: 75μm, 89x88
|
|
171.0062 | [M+H]+PPM:5.3 |
Homo sapiens | esophagus | DESI () |
LNTO22_2_1 - MTBLS385Resolution: 75μm, 89x88
|
|
152.9954 | [M+H-H2O]+PPM:4.3 |
Homo sapiens | esophagus | DESI () |
LNTO22_2_2 - MTBLS385Resolution: 75μm, 135x94
|
|
171.0071 | [M+H]+PPM:10.5 |
Homo sapiens | esophagus | DESI () |
LNTO22_2_2 - MTBLS385Resolution: 75μm, 135x94
|
|
152.9953 | [M+H-H2O]+PPM:3.7 |
Homo sapiens | esophagus | DESI () |
LNTO26_16_1 - MTBLS385Resolution: 75μm, 95x88
|
|
171.0063 | [M+H]+PPM:5.8 |
Homo sapiens | esophagus | DESI () |
LNTO26_16_1 - MTBLS385Resolution: 75μm, 95x88
|
|
152.9949 | [M+H-H2O]+PPM:1.1 |
Homo sapiens | esophagus | DESI () |
LNTO29_18_2 - MTBLS385Resolution: 75μm, 62x68
|
|
171.0056 | [M+H]+PPM:1.7 |
Homo sapiens | esophagus | DESI () |
LNTO29_18_2 - MTBLS385Resolution: 75μm, 62x68
|
|
152.9951 | [M+H-H2O]+PPM:2.4 |
Homo sapiens | esophagus | DESI () |
LNTO30_7_1 - MTBLS385Resolution: 75μm, 69x68
|
|
152.9957 | [M+H-H2O]+PPM:6.3 |
Homo sapiens | esophagus | DESI () |
LNTO30_7_2 - MTBLS385Resolution: 75μm, 82x68
|
|
171.0067 | [M+H]+PPM:8.2 |
Homo sapiens | esophagus | DESI () |
LNTO30_7_2 - MTBLS385Resolution: 75μm, 82x68
|
|
An important intermediate in lipid biosynthesis and in glycolysis.; Dihydroxyacetone phosphate (DHAP) is a biochemical compound involved in many reactions, from the Calvin cycle in plants to the ether-lipid biosynthesis process in Leishmania mexicana. Its major biochemical role is in the glycolysis metabolic pathway. DHAP may be referred to as glycerone phosphate in older texts.; Dihydroxyacetone phosphate lies in the glycolysis metabolic pathway, and is one of the two products of breakdown of fructose 1,6-phosphate, along with glyceraldehyde 3-phosphate. It is rapidly and reversibly isomerised to glyceraldehyde 3-phosphate.; In the Calvin cycle, DHAP is one of the products of the sixfold reduction of 1,3-bisphosphoglycerate by NADPH. It is also used in the synthesis of sedoheptulose 1,7-bisphosphate and fructose 1,6-bisphosphate which are both used to reform ribulose 5-phosphate, the key carbohydrate of the Calvin cycle. Dihydroxyacetone phosphate is found in many foods, some of which are sesame, mexican groundcherry, parsley, and common wheat. [Spectral] Glycerone phosphate (exact mass = 169.99802) and beta-D-Fructose 1,6-bisphosphate (exact mass = 339.99605) and NADP+ (exact mass = 743.07545) were not completely separated on HPLC under the present analytical conditions as described in AC$XXX. Additionally some of the peaks in this data contains dimers and other unidentified ions. Dihydroxyacetone phosphate is an important intermediate in lipid biosynthesis and in glycolysis. Dihydroxyacetone phosphate is found to be associated with transaldolase deficiency, which is an inborn error of metabolism. Dihydroxyacetone phosphate has been identified in the human placenta (PMID: 32033212). KEIO_ID D014