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1 MOPS or a similar model could be integrated into the pip
2 d large decreases in k(cat) values in pH 7.5 MOPS buffer, but only exhibited small changes in k(cat)/
3 ity relative to wild-type activity in pH 7.5 MOPS buffer, suggesting that the original glutamate resi
4 relative to those of the wild type in pH 7.5 MOPS buffer, while other substitutions (E62A, -C, -H, -Q
5 addition of morpholinepropanesulfonic acid (MOPS) or Tris-HCl (pH 7.5) results in a dramatic increas
6 MES) and 3-N-morpholinopropanesulfonic acid (MOPS) did not bind copper and would be good choices for
7 0165 M 3-(N-morpholino)propanesulfonic acid (MOPS) and a 24-h incubation time, all of the isolates we
8 ses in 3-(N-morpholino)propanesulfonic acid (MOPS) buffer and characterize the hydrodynamic aspects o
10 buffer 3-(N-morpholino)propanesulfonic acid (MOPS), which has a very small temperature coefficient.
11 r with 3-(N-morpolino)propane sulfonic acid (MOPS) led to increased interparticle interference, consi
18 microM in Tris buffer or from 6.7 microM in MOPS buffer to 50 microM in phosphate buffer when tested
19 igh external osmolalities (1.02-2.17 Osm) in MOPS-buffered minimal medium (MBM) containing 1 mM betai
21 he broth macrodilution method with the lower MOPS concentration correlated with the results of the 24
24 esting in microdilution panels, the 0.0165 M MOPS concentration combined with 24 h of incubation appe
26 art I of this paper series; e.g., CHES, MES, MOPS, Tricine were used to demonstrate behavior of such
29 situ determination of the apparent pK(a) of MOPS (3-(N-morpholino)propanesulfonic acid) buffer at am
31 called the Multi Objective Pipeline Siting (MOPS) model, to incorporate habitat externalities into p
32 broth macrodilution method with the standard MOPS concentration did not correlate with any of the res