EC Number | Application | Comment | Organism |
---|---|---|---|
1.3.7.8 | analysis | the detection of benzoyl-CoA reductase genes from bacterial pure cultures and environmental samples can be used to determine the genetic capability for anaerobic degradation of aromatic compounds and to monitor the anaerobic degradation of many different aromatic compounds in the environment. Sequence divergence of benzoyl-CoA reductase genes could be used to identify and distinguish among different bacterial populations degrading aromatic compounds in various environments. Microarray or real-time PCR amplification with specific primers for different types of benzoyl-CoA reductase genes could be applicable in environmental studies to determine which types are dominant and activated in particular environmental conditions and to evaluate the population response to variation in environmental factors. The first step in this approach is described | Acidovorax sp. |
1.3.7.8 | analysis | the detection of benzoyl-CoA reductase genes from bacterial pure cultures and environmental samples can be used to determine the genetic capability for anaerobic degradation of aromatic compounds and to monitor the anaerobic degradation of many different aromatic compounds in the environment. Sequence divergence of benzoyl-CoA reductase genes could be used to identify and distinguish among different bacterial populations degrading aromatic compounds in various environments. Microarray or real-time PCR amplification with specific primers for different types of benzoyl-CoA reductase genes could be applicable in environmental studies to determine which types are dominant and activated in particular environmental conditions and to evaluate the population response to variation in environmental factors. The first step in this approach is described | Magnetospirillum magnetotacticum |
1.3.7.8 | analysis | the detection of benzoyl-CoA reductase genes from bacterial pure cultures and environmental samples can be used to determine the genetic capability for anaerobic degradation of aromatic compounds and to monitor the anaerobic degradation of many different aromatic compounds in the environment. Sequence divergence of benzoyl-CoA reductase genes could be used to identify and distinguish among different bacterial populations degrading aromatic compounds in various environments. Microarray or real-time PCR amplification with specific primers for different types of benzoyl-CoA reductase genes could be applicable in environmental studies to determine which types are dominant and activated in particular environmental conditions and to evaluate the population response to variation in environmental factors. The first step in this approach is described | Thauera selenatis |
1.3.7.8 | analysis | the detection of benzoyl-CoA reductase genes from bacterial pure cultures and environmental samples can be used to determine the genetic capability for anaerobic degradation of aromatic compounds and to monitor the anaerobic degradation of many different aromatic compounds in the environment. Sequence divergence of benzoyl-CoA reductase genes could be used to identify and distinguish among different bacterial populations degrading aromatic compounds in various environments. Microarray or real-time PCR amplification with specific primers for different types of benzoyl-CoA reductase genes could be applicable in environmental studies to determine which types are dominant and activated in particular environmental conditions and to evaluate the population response to variation in environmental factors. The first step in this approach is described | Thauera aromatica |
1.3.7.8 | analysis | the detection of benzoyl-CoA reductase genes from bacterial pure cultures and environmental samples can be used to determine the genetic capability for anaerobic degradation of aromatic compounds and to monitor the anaerobic degradation of many different aromatic compounds in the environment. Sequence divergence of benzoyl-CoA reductase genes could be used to identify and distinguish among different bacterial populations degrading aromatic compounds in various environments. Microarray or real-time PCR amplification with specific primers for different types of benzoyl-CoA reductase genes could be applicable in environmental studies to determine which types are dominant and activated in particular environmental conditions and to evaluate the population response to variation in environmental factors. The first step in this approach is described | Aromatoleum evansii |
1.3.7.8 | analysis | the detection of benzoyl-CoA reductase genes from bacterial pure cultures and environmental samples can be used to determine the genetic capability for anaerobic degradation of aromatic compounds and to monitor the anaerobic degradation of many different aromatic compounds in the environment. Sequence divergence of benzoyl-CoA reductase genes could be used to identify and distinguish among different bacterial populations degrading aromatic compounds in various environments. Microarray or real-time PCR amplification with specific primers for different types of benzoyl-CoA reductase genes could be applicable in environmental studies to determine which types are dominant and activated in particular environmental conditions and to evaluate the population response to variation in environmental factors. The first step in this approach is described | Aromatoleum tolulyticum |
1.3.7.8 | analysis | the detection of benzoyl-CoA reductase genes from bacterial pure cultures and environmental samples can be used to determine the genetic capability for anaerobic degradation of aromatic compounds and to monitor the anaerobic degradation of many different aromatic compounds in the environment. Sequence divergence of benzoyl-CoA reductase genes could be used to identify and distinguish among different bacterial populations degrading aromatic compounds in various environments. Microarray or real-time PCR amplification with specific primers for different types of benzoyl-CoA reductase genes could be applicable in environmental studies to determine which types are dominant and activated in particular environmental conditions and to evaluate the population response to variation in environmental factors. The first step in this approach is described | Thauera chlorobenzoica |
1.3.7.8 | analysis | the detection of benzoyl-CoA reductase genes from bacterial pure cultures and environmental samples can be used to determine the genetic capability for anaerobic degradation of aromatic compounds and to monitor the anaerobic degradation of many different aromatic compounds in the environment. Sequence divergence of benzoyl-CoA reductase genes could be used to identify and distinguish among different bacterial populations degrading aromatic compounds in various environments. Microarray or real-time PCR amplification with specific primers for different types of benzoyl-CoA reductase genes could be applicable in environmental studies to determine which types are dominant and activated in particular environmental conditions and to evaluate the population response to variation in environmental factors. The first step in this approach is described | Aromatoleum toluvorans |
1.3.7.8 | analysis | the detection of benzoyl-CoA reductase genes from bacterial pure cultures and environmental samples can be used to determine the genetic capability for anaerobic degradation of aromatic compounds and to monitor the anaerobic degradation of many different aromatic compounds in the environment. Sequence divergence of benzoyl-CoA reductase genes could be used to identify and distinguish among different bacterial populations degrading aromatic compounds in various environments. Microarray or real-time PCR amplification with specific primers for different types of benzoyl-CoA reductase genes could be applicable in environmental studies to determine which types are dominant and activated in particular environmental conditions and to evaluate the population response to variation in environmental factors. The first step in this approach is described | Aromatoleum toluclasticum |
1.3.7.8 | analysis | the detection of benzoyl-CoA reductase genes from bacterial pure cultures and environmental samples can be used to determine the genetic capability for anaerobic degradation of aromatic compounds and to monitor the anaerobic degradation of many different aromatic compounds in the environment. Sequence divergence of benzoyl-CoA reductase genes could be used to identify and distinguish among different bacterial populations degrading aromatic compounds in various environments. Microarray or real-time PCR amplification with specific primers for different types of benzoyl-CoA reductase genes could be applicable in environmental studies to determine which types are dominant and activated in particular environmental conditions and to evaluate the population response to variation in environmental factors. The first step in this approach is described | Rhodopseudomonas palustris |
EC Number | Natural Substrates | Organism | Comment (Nat. Sub.) | Natural Products | Comment (Nat. Pro.) | Rev. | Reac. |
---|---|---|---|---|---|---|---|
1.3.7.8 | benzoyl-CoA + reduced acceptor + ATP + H2O | Acidovorax sp. | central enzyme in the anaerobic degradation of organic carbon | cyclohexa-1,5-diene-1-carbonyl-CoA + acceptor + ADP + phosphate | - |
? | |
1.3.7.8 | benzoyl-CoA + reduced acceptor + ATP + H2O | Magnetospirillum magnetotacticum | central enzyme in the anaerobic degradation of organic carbon | cyclohexa-1,5-diene-1-carbonyl-CoA + acceptor + ADP + phosphate | - |
? | |
1.3.7.8 | benzoyl-CoA + reduced acceptor + ATP + H2O | Thauera selenatis | central enzyme in the anaerobic degradation of organic carbon | cyclohexa-1,5-diene-1-carbonyl-CoA + acceptor + ADP + phosphate | - |
? | |
1.3.7.8 | benzoyl-CoA + reduced acceptor + ATP + H2O | Thauera aromatica | central enzyme in the anaerobic degradation of organic carbon | cyclohexa-1,5-diene-1-carbonyl-CoA + acceptor + ADP + phosphate | - |
? | |
1.3.7.8 | benzoyl-CoA + reduced acceptor + ATP + H2O | Aromatoleum evansii | central enzyme in the anaerobic degradation of organic carbon | cyclohexa-1,5-diene-1-carbonyl-CoA + acceptor + ADP + phosphate | - |
? | |
1.3.7.8 | benzoyl-CoA + reduced acceptor + ATP + H2O | Aromatoleum tolulyticum | central enzyme in the anaerobic degradation of organic carbon | cyclohexa-1,5-diene-1-carbonyl-CoA + acceptor + ADP + phosphate | - |
? | |
1.3.7.8 | benzoyl-CoA + reduced acceptor + ATP + H2O | Thauera chlorobenzoica | central enzyme in the anaerobic degradation of organic carbon | cyclohexa-1,5-diene-1-carbonyl-CoA + acceptor + ADP + phosphate | - |
? | |
1.3.7.8 | benzoyl-CoA + reduced acceptor + ATP + H2O | Aromatoleum toluvorans | central enzyme in the anaerobic degradation of organic carbon | cyclohexa-1,5-diene-1-carbonyl-CoA + acceptor + ADP + phosphate | - |
? | |
1.3.7.8 | benzoyl-CoA + reduced acceptor + ATP + H2O | Aromatoleum toluclasticum | central enzyme in the anaerobic degradation of organic carbon | cyclohexa-1,5-diene-1-carbonyl-CoA + acceptor + ADP + phosphate | - |
? | |
1.3.7.8 | benzoyl-CoA + reduced acceptor + ATP + H2O | Rhodopseudomonas palustris | central enzyme in the anaerobic degradation of organic carbon | cyclohexa-1,5-diene-1-carbonyl-CoA + acceptor + ADP + phosphate | - |
? | |
1.3.7.8 | benzoyl-CoA + reduced acceptor + ATP + H2O | Thauera selenatis 3CB-1 | central enzyme in the anaerobic degradation of organic carbon | cyclohexa-1,5-diene-1-carbonyl-CoA + acceptor + ADP + phosphate | - |
? | |
1.3.7.8 | benzoyl-CoA + reduced acceptor + ATP + H2O | Acidovorax sp. 2FB7 | central enzyme in the anaerobic degradation of organic carbon | cyclohexa-1,5-diene-1-carbonyl-CoA + acceptor + ADP + phosphate | - |
? | |
1.3.7.8 | benzoyl-CoA + reduced acceptor + ATP + H2O | Thauera chlorobenzoica 3CB-1 | central enzyme in the anaerobic degradation of organic carbon | cyclohexa-1,5-diene-1-carbonyl-CoA + acceptor + ADP + phosphate | - |
? |
EC Number | Organism | UniProt | Comment | Textmining |
---|---|---|---|---|
1.3.7.8 | Acidovorax sp. | - |
- |
- |
1.3.7.8 | Acidovorax sp. 2FB7 | - |
- |
- |
1.3.7.8 | Aromatoleum evansii | Q8VUG0 | subunit of benzoyl-CoA reductase, gene name: bzdQ | - |
1.3.7.8 | Aromatoleum evansii | Q8VUG1 | subunit of benzoyl-CoA reductase, gene name: bzdP | - |
1.3.7.8 | Aromatoleum evansii | Q8VUG2 | subunit of benzoyl-CoA reductase, gene name: bzdO | - |
1.3.7.8 | Aromatoleum evansii | Q8VUG3 | subunit of benzoyl-CoA reductase, gene name: bzdN | - |
1.3.7.8 | Aromatoleum toluclasticum | - |
- |
- |
1.3.7.8 | Aromatoleum tolulyticum | Q4Z8X5 | putative benzoyl-CoA reductase, gene name: bzdQ | - |
1.3.7.8 | Aromatoleum toluvorans | - |
- |
- |
1.3.7.8 | Magnetospirillum magnetotacticum | - |
- |
- |
1.3.7.8 | Rhodopseudomonas palustris | O07460 | subunit of benzoyl-CoA reductase, gene name badD | - |
1.3.7.8 | Rhodopseudomonas palustris | O07461 | subunit of benzoyl-CoA reductase, gene name badE | - |
1.3.7.8 | Rhodopseudomonas palustris | O07462 | subunit of benzoyl-CoA reductase, gene name badF | - |
1.3.7.8 | Rhodopseudomonas palustris | O07463 | subunit of benzoyl-CoA reductase, gene name badG | - |
1.3.7.8 | Thauera aromatica | O87876 | A-subunit of benzoyl-CoA reductase; all the Thauera strains and the isolates from the genera Acidovorax, Bradyrhizobium, Paracoccus, Ensifer, and Pseudomonas have bcr-type benzoyl-CoA reductases with amino acid sequence similarities of more than 97% | - |
1.3.7.8 | Thauera chlorobenzoica | - |
all the Thauera strains and the isolates from the genera Acidovorax, Bradyrhizobium, Paracoccus, Ensifer, and Pseudomonas have bcr-type benzoyl-CoA reductases with amino acid sequence similarities of more than 97% | - |
1.3.7.8 | Thauera chlorobenzoica 3CB-1 | - |
all the Thauera strains and the isolates from the genera Acidovorax, Bradyrhizobium, Paracoccus, Ensifer, and Pseudomonas have bcr-type benzoyl-CoA reductases with amino acid sequence similarities of more than 97% | - |
1.3.7.8 | Thauera selenatis | - |
all the Thauera strains and the isolates from the genera Acidovorax, Bradyrhizobium, Paracoccus, Ensifer, and Pseudomonas have bcr-type benzoyl-CoA reductases with amino acid sequence similarities of more than 97% | - |
1.3.7.8 | Thauera selenatis 3CB-1 | - |
all the Thauera strains and the isolates from the genera Acidovorax, Bradyrhizobium, Paracoccus, Ensifer, and Pseudomonas have bcr-type benzoyl-CoA reductases with amino acid sequence similarities of more than 97% | - |
EC Number | Substrates | Comment Substrates | Organism | Products | Comment (Products) | Rev. | Reac. |
---|---|---|---|---|---|---|---|
1.3.7.8 | benzoyl-CoA + reduced acceptor + ATP + H2O | central enzyme in the anaerobic degradation of organic carbon | Acidovorax sp. | cyclohexa-1,5-diene-1-carbonyl-CoA + acceptor + ADP + phosphate | - |
? | |
1.3.7.8 | benzoyl-CoA + reduced acceptor + ATP + H2O | central enzyme in the anaerobic degradation of organic carbon | Magnetospirillum magnetotacticum | cyclohexa-1,5-diene-1-carbonyl-CoA + acceptor + ADP + phosphate | - |
? | |
1.3.7.8 | benzoyl-CoA + reduced acceptor + ATP + H2O | central enzyme in the anaerobic degradation of organic carbon | Thauera selenatis | cyclohexa-1,5-diene-1-carbonyl-CoA + acceptor + ADP + phosphate | - |
? | |
1.3.7.8 | benzoyl-CoA + reduced acceptor + ATP + H2O | central enzyme in the anaerobic degradation of organic carbon | Thauera aromatica | cyclohexa-1,5-diene-1-carbonyl-CoA + acceptor + ADP + phosphate | - |
? | |
1.3.7.8 | benzoyl-CoA + reduced acceptor + ATP + H2O | central enzyme in the anaerobic degradation of organic carbon | Aromatoleum evansii | cyclohexa-1,5-diene-1-carbonyl-CoA + acceptor + ADP + phosphate | - |
? | |
1.3.7.8 | benzoyl-CoA + reduced acceptor + ATP + H2O | central enzyme in the anaerobic degradation of organic carbon | Aromatoleum tolulyticum | cyclohexa-1,5-diene-1-carbonyl-CoA + acceptor + ADP + phosphate | - |
? | |
1.3.7.8 | benzoyl-CoA + reduced acceptor + ATP + H2O | central enzyme in the anaerobic degradation of organic carbon | Thauera chlorobenzoica | cyclohexa-1,5-diene-1-carbonyl-CoA + acceptor + ADP + phosphate | - |
? | |
1.3.7.8 | benzoyl-CoA + reduced acceptor + ATP + H2O | central enzyme in the anaerobic degradation of organic carbon | Aromatoleum toluvorans | cyclohexa-1,5-diene-1-carbonyl-CoA + acceptor + ADP + phosphate | - |
? | |
1.3.7.8 | benzoyl-CoA + reduced acceptor + ATP + H2O | central enzyme in the anaerobic degradation of organic carbon | Aromatoleum toluclasticum | cyclohexa-1,5-diene-1-carbonyl-CoA + acceptor + ADP + phosphate | - |
? | |
1.3.7.8 | benzoyl-CoA + reduced acceptor + ATP + H2O | central enzyme in the anaerobic degradation of organic carbon | Rhodopseudomonas palustris | cyclohexa-1,5-diene-1-carbonyl-CoA + acceptor + ADP + phosphate | - |
? | |
1.3.7.8 | benzoyl-CoA + reduced acceptor + ATP + H2O | central enzyme in the anaerobic degradation of organic carbon | Thauera selenatis 3CB-1 | cyclohexa-1,5-diene-1-carbonyl-CoA + acceptor + ADP + phosphate | - |
? | |
1.3.7.8 | benzoyl-CoA + reduced acceptor + ATP + H2O | central enzyme in the anaerobic degradation of organic carbon | Acidovorax sp. 2FB7 | cyclohexa-1,5-diene-1-carbonyl-CoA + acceptor + ADP + phosphate | - |
? | |
1.3.7.8 | benzoyl-CoA + reduced acceptor + ATP + H2O | central enzyme in the anaerobic degradation of organic carbon | Thauera chlorobenzoica 3CB-1 | cyclohexa-1,5-diene-1-carbonyl-CoA + acceptor + ADP + phosphate | - |
? |