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1 lipoferum) and denitrifying bacteria (i.e., Pseudomonas stutzeri).
2 ratory chains, and the gamma-proteobacterium Pseudomonas stutzeri.
3 y oxidized nitric oxide reductase (NOR) from Pseudomonas stutzeri.
4 ration (N = 20) showed a higher abundance of Pseudomonas stutzeri (2.1% versus 1.0%, p = 0.024) and P
6 aminoacid was carried out with a lipase from Pseudomonas stutzeri and a protease from Bacillus subtil
7 5, the transfer of an inducible cluster from Pseudomonas stutzeri and Azotobacter vinelandii yields a
8 H NMR spectra of the CuA center of N2OR from Pseudomonas stutzeri, and a mutant enzyme that contains
10 igands for the CuA centre of the enzyme from Pseudomonas stutzeri ATCC14405 were substituted by evolu
11 ulations with a mix of Bacillus subtilis and Pseudomonas stutzeri, bacteria species isolated from the
13 osphodiesterases, GlpQI and GlpQII, found in Pseudomonas stutzeri DSM4166 and Pseudomonas fluorescens
14 (BIRD-1), Pseudomonas fluorescens SBW25 and Pseudomonas stutzeri DSM4166 was performed in unison wit
16 der the optimal conditions it was found that Pseudomonas stutzeri lipase and Chromobacterium viscosum
18 eport cryo-electron microscopy structures of Pseudomonas stutzeri NosDFY and its complexes with NosL
19 HBSS bottle and from pericardial tissue grew Pseudomonas stutzeri of the same genotype; however, no P
20 Here we report that the wastewater bacterium Pseudomonas stutzeri OX1 degrades aerobically 0.56 micro
21 t toluene/o-xylene monooxygenase (ToMO) from Pseudomonas stutzeri OX1 is capable of oxidizing arenes,
22 us (Bath), toluene monooxygenase (ToMO) from Pseudomonas stutzeri OX1, and phenol hydroxylase (PH) fr
23 us (Bath), toluene monooxygenase (ToMO) from Pseudomonas stutzeri OX1, and phenol hydroxylase (PH) fr
26 n adaptation to oxygen-limited conditions in Pseudomonas stutzeri (P. stutzeri), a model for the clin
28 o particular residues, Glu175 and Ala176, in Pseudomonas stutzeri phosphite dehydrogenase (PTDH) as t
30 on of streaked Shewanella oneidensis MR1 and Pseudomonas stutzeri RCH2 colonies and further resolve c
31 ) from a metal tolerant groundwater isolate, Pseudomonas stutzeri RCH2 to assess the impact of host-d
32 quencing of an 8182-bp chromosomal region in Pseudomonas stutzeri revealed the major portion of an ap
34 (SMX) contamination, and a laboratory-grown Pseudomonas stutzeri strain, were exposed to 240-520 mug
35 We address this question using consortia of Pseudomonas stutzeri strains, where one is an antibiotic
36 encoding for bacterial cytochrome c-551 from Pseudomonas stutzeri substrain ZoBell has been mutated t
37 red harboring the gene cluster nirFDLGH from Pseudomonas stutzeri substrain ZoBell on a high copy pla
38 he gene nirM, coding for cytochrome c-551 in Pseudomonas stutzeri substrain ZoBell, was engineered to
39 ors diazotrophic (N(2)-fixing) endobacteria (Pseudomonas stutzeri) that allow JGTA-S1 to fix N(2) and
40 TCA16, Pseudomonas putida TCA23 and N7, and Pseudomonas stutzeri TRA27a were able to produce branche
49 osomal RNA operon from the marine bacterium, Pseudomonas stutzeri Zobell, was cloned and characterize
50 shown that, in the oxidized state, heme c of Pseudomonas stutzeri (ZoBell strain) cytochrome cd1 has