戻る
「早戻しボタン」を押すと検索画面に戻ります。 [閉じる]

コーパス検索結果 (１語後でソート)

通し番号をクリックするとPubMedの該当ページを表示します
1                                              Assimilatory 3'-phosphoadenosine 5'-phosphosulfate (PAPS
2                          DOS originates from assimilatory and bacterial dissimilatory S reduction (BD
3                                              Assimilatory and dissimilatory biomass utilisation was i
4 g genes involved in anammox, ammonification, assimilatory and dissimilatory N reduction, denitrificat
5 uman health, taxonomy of nitrate reductases, assimilatory and dissimilatory nitrate reduction, cellul
6 ruvate is located at a metabolic junction of assimilatory and dissimilatory pathways and represents a
7  bacteria metabolize nitrogen oxides through assimilatory and dissimilatory pathways.
8 ite reductases (NiRs) are key enzymes in the assimilatory and dissimilatory reduction of nitrite (NO(
9 inked formaldehyde oxidation pathway and the assimilatory and dissimilatory ribulose monophosphate cy
10 cluded gene transcripts associated with both assimilatory and dissimilatory single-carbon compound ut
11 owth, hydrogen sulphide is a product of both assimilatory and dissimilatory sulphate reduction.
12                                              Assimilatory and dissimilatory utilisation of autotroph
13  net 80% higher protein abundance for carbon assimilatory and glycolytic pathways leading to fatty ac
14 s was confirmed by demonstrating the loss of assimilatory and respiratory nitrate reductase activity
15 e results suggest that the dissimilatory and assimilatory APS reductases evolved convergently.
16                            However, only the assimilatory branch of the denitrification pathway was e
17 sR-type regulator, is the major regulator of assimilatory C1 metabolism in Methylobacterium extorquen
18                                              Assimilatory carbon enters the ethylmalonyl-CoA pathway
19 icture of the flhDC master operon as a major assimilatory checkpoint in Proteus mirabilis and other G
20     The binding of GS, the principal ammonia assimilatory enzyme, to the conserved C-terminal domain
21 ulfur (S), we examined the activity of key S assimilatory enzymes ATP sulfurylase (ATPS), APS reducta
22 pulating the expression levels of key sulfur assimilatory enzymes could be exploited to improve the n
23 ammonium or dinitrogen through the action of assimilatory enzymes.
24 ssimilation, despite having normal levels of assimilatory enzymes.
25 nd (18)epsilon) for nitrate reduction by two assimilatory eukaryotic nitrate reductase (eukNR) enzyme
26 m previously characterized dissimilatory and assimilatory Fe(III) reductases in its molecular composi
27 erates as a linear pathway carrying the full assimilatory flux to produce glyoxylate, malate, and suc
28  synthesis pathway through formate dominates assimilatory flux.
29 g that the levels of mRNA for plant nitrogen assimilatory genes such as glutamine synthetase (GLN) an
30            Fungal transcripts for putative S assimilatory genes were identified, indicating the prese
31 and NLP7, which act as activators of nitrate assimilatory genes, bind to adjacent sites in the upstre
32 te in turn regulates the expression of key N-assimilatory genes.
33 with increased expression of several nitrate assimilatory genes.
34 e biomass pathways, MtdA plays a key role in assimilatory metabolism.
35 ns to convert formate to methylene H(4)F for assimilatory metabolism.
36  in methylotrophy-specific dissimilatory and assimilatory modules suggested that methylamine use via
37 regressions were in agreement with predicted assimilatory N-uptake based on additional metabolic data
38                                              Assimilatory NADPH-sulfite reductase (SiR) from Escheric
39 he capacity to express respiratory (Nar) and assimilatory (Nas) nitrate reductases to utilize this ab
40  is converted through nitrite to ammonium by assimilatory nitrate and nitrite reductase, respectively
41 tion pathways were absent, as were genes for assimilatory nitrate and sulfate reduction and vitamin B
42                  It is well established that assimilatory nitrate reductase (ANR) activity in soil is
43  the inhibitory effect of ammonium (NH4+) on assimilatory nitrate reductase (ANR) activity in soil is
44 ap), respiratory nitrate reductase (Nar) and assimilatory nitrate reductase (Nas), they are defined b
45 respiratory nitrate reductase (NarG) and the assimilatory nitrate reductase (NasC), the latter of whi
46                                   Eukaryotic assimilatory nitrate reductase (NR) is a multi-domain pr
47 es the oxidized sites in sulfite oxidase and assimilatory nitrate reductase as deduced from crystallo
48 e catalytic subunits, which evolved from the assimilatory nitrate reductase lineage.
49 g the nitrate/proton symporter NasA from the assimilatory nitrate reductase pathway, support that Nar
50 e nasDE genes, together with nasBC (encoding assimilatory nitrate reductase) and nasF (required for n
51  catalytic subunit of R. solanacearum's sole assimilatory nitrate reductase, did not grow on nitrate
52 trate stimulated expression of some genes in assimilatory nitrate reduction and denitrification pathw
53 n in bacterioplankton toward N(2)-fixing and assimilatory nitrate reduction in certain cyanobacteria
54 ive abundance of functional genes related to assimilatory nitrate reduction in the emerged areas was
55 s the CBB is allied to sulfide oxidation and assimilatory nitrate reduction, suggesting distinctive y
56                                          The assimilatory nitrate transporter NasA of Bacillus subtil
57     Diverse species of bacteria that have an assimilatory nitrate/nitrite reductase system (NAS) can
58 e strongest evidence of adaptation, with the assimilatory nitrite reductase (nasD) and urease (ureG)
59 6 km2) revealed a strong correlation between assimilatory NO3- uptake and growth primary production (
60                             Percentage daily assimilatory NO3- uptake peaked at 47.4% of the daily NO
61                                  Mean yearly assimilatory NO3- uptake rates (Ua) were 7.4 times highe
62 multiparameter sensor measurements to relate assimilatory NO3- uptake to metabolic rates and calculat
63 ire watershed, whereas the percentage yearly assimilatory NO3- uptake was 9.0% of nitrogen loading to
64                        The percentage yearly assimilatory NO3- uptake was lower in the forest-dominat
65 APSK evolved after bifurcation of the sulfur assimilatory pathway in the green plant lineage and that
66 es, containing a blockage in the primary CO2 assimilatory pathway, derepress the synthesis of compone
67 by either an increased Se flux through the S assimilatory pathway, generated by the biosynthesis of t
68  coli dependent on the low-affinity ammonium-assimilatory pathway, we determined that biosynthetic gl
69 primary and secondary branches of the sulfur assimilatory pathway; however, the biochemical regulatio
70                                       Carbon assimilatory pathways in castor were compared with previ
71 imilatory pathways was higher than those for assimilatory pathways.
72 y provide a link between carbon and nitrogen assimilatory pathways.
73 eeds is directed toward transforming primary assimilatory products (sugars and amino acids) into seed
74 tant strains with lesions affecting ammonium-assimilatory proteins.
75 alent cations might serve other, potentially assimilatory, purposes.
76 r of NH4+ assimilation by microorganisms, on assimilatory reduction of nitrate (NO3-) in aerated soil
77 tion serves as an intermediate enzyme in the assimilatory reduction of sulfate.
78 bundance of functional genes associated with assimilatory sulfate reduction was higher than those inv
79 ic to the aerobic phase were responsible for assimilatory sulfate reduction, genetic information proc
80 enic S-bearing organic compounds produced by assimilatory sulfate reduction.
81             Escherichia coli NADPH-dependent assimilatory sulfite reductase (SiR) reduces sulfite by
82                                              Assimilatory sulfur metabolism, i.e. reactions used for
83  alphaproteobacterial clade are deficient in assimilatory sulphate reduction genes.
84 All aerobic marine bacteria are known to use assimilatory sulphate reduction to supply sulphur for bi
85 gh proportion of potential genes involved in assimilatory sulphate reduction, and cyanocobalamin synt
86 ously thought to occur only as a cofactor in assimilatory sulphite/nitrite reductases.
87 ates that the structural genes of the carbon assimilatory system are unusually arranged and possess a
88 ional analyses identify CTR1 and CTR2 as the assimilatory transporters of Chlamydomonas based on loca
89  no structural or sequence homology with the assimilatory-type APS reductase reported here.