3.5.4.43: hydroxydechloroatrazine ethylaminohydrolase
This is an abbreviated version!
For detailed information about hydroxydechloroatrazine ethylaminohydrolase, go to the full flat file.
Reaction
Synonyms
adenosine aminohydrolase 3, artB, AtzB, EC 3.5.99.3, FRAAL1473, FraEuI1c_5875, HAEA, hydroxyatrazine ethylaminohydrolase, Hydroxyatrazine hydrolase, hydroxyatrazine N-ethylaminohydrolase, More
ECTree
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Application
Application on EC 3.5.4.43 - hydroxydechloroatrazine ethylaminohydrolase
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agriculture
degradation
agriculture
expression of the atrazine degradation-related gene atzB in coculture treatments (of Arthrobacter sp. DNS10 and Enterobacter sp. P1 is a phosphorus-solubilizing bacterium that releases various kinds of organic acids but lacks the ability to degrade atrazine) is 1.8 times that of the single strain DNS10 culture treatment. This phenomenon is due to metabolite exchange between the two strains. Culturing these two strains together is a biostimulation strategy to enhance the biodegradation of atrazine and the level of available phosphorus in soil by culturing these two strains together
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strain ADP, use of atrazine as sole nitrogen source, but not as sole carbon source. Comparison of degradation products with those from Pseudoaminobacter sp. and Nocardiodes sp.
degradation
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use of atrazine as sole nitrogen source and as sole carbon source. Comparison of degradation products with those from Pseudomonas sp. and Nocardiodes sp.
degradation
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use of atrazine as sole nitrogen source and as sole carbon source. End product of atrazine metabolism is N-ethylammelide. Comparison of degradation products with those from Pseudomonas sp. and Nocardiodes sp.
degradation
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mineralization of low concentrations of atrazine in the groundwater zone at low temperatures is possible by bioremediation treatments. In combined biostimulation treatment using citrate or molasses and augmentation with Pseudomonas citronellolis ADP or Arthrobacter aurescens strain TC1, up to 76% of atrazine is mineralized at 30°C, and the atrazine degradation gene numbers increase up to 10 million copies/g soil
degradation
mineralization of low concentrations of atrazine in the groundwater zone at low temperatures is possible by bioremediation treatments. In combined biostimulation treatment using citrate or molasses and augmentation with Pseudomonas citronellolis ADP or Arthrobacter aurescens strain TC1, up to 76%of atrazine is mineralized at 30°C, and the atrazine degradation gene numbers increase up to 10 million copies/g soil
degradation
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strain HB-6 is capable of utilizing atrazine and cyanuric acid as a sole nitrogen source for growth and even cleaves the s-triazine ring and mineralizes atrazine. The strain demonstrate a very high efficiency of atrazine biodegradation with a broad optimum pH and temperature ranges and can be enhanced by cooperating with other bacteria
degradation
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mineralization of low concentrations of atrazine in the groundwater zone at low temperatures is possible by bioremediation treatments. In combined biostimulation treatment using citrate or molasses and augmentation with Pseudomonas citronellolis ADP or Arthrobacter aurescens strain TC1, up to 76% of atrazine is mineralized at 30°C, and the atrazine degradation gene numbers increase up to 10 million copies/g soil
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degradation
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mineralization of low concentrations of atrazine in the groundwater zone at low temperatures is possible by bioremediation treatments. In combined biostimulation treatment using citrate or molasses and augmentation with Pseudomonas citronellolis ADP or Arthrobacter aurescens strain TC1, up to 76%of atrazine is mineralized at 30°C, and the atrazine degradation gene numbers increase up to 10 million copies/g soil
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degradation
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strain HB-6 is capable of utilizing atrazine and cyanuric acid as a sole nitrogen source for growth and even cleaves the s-triazine ring and mineralizes atrazine. The strain demonstrate a very high efficiency of atrazine biodegradation with a broad optimum pH and temperature ranges and can be enhanced by cooperating with other bacteria
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