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1 n this case, a nitrogen-containing adduct of fluoranthene.
2 9.8% dibenzo[ah]anthracene and 69.0% benzo[b]fluoranthene.
3 roducts are benzo[k]fluoranthene and benzo[j]fluoranthene.
4 um (5:95 ratio), and also converts slowly to fluoranthene.
5 media containing fluorene, phenanthrene, and fluoranthene.
6 enzo(a)anthracene to 10.8 mug/kg for benzo(b)fluoranthene.
7 ncentrations of phenanthrene and benzo(g,h,i)fluoranthene.
8 nthrene and from 0.006 to 90.0 mug L(-1) for fluoranthene.
9 clic aromatic hydrocarbons (PAHs), including fluoranthene.
10 and proposed pathways for the degradation of fluoranthene.
11 the test mixture contained both anisole and fluoranthene.
12 r chrysene, 3.51 +/- 1.23 mg m(-2) d(-1) for fluoranthene, 0.23 +/- 0.08 mg m(-2) d(-1) for naphthale
14 pyrene (22%), followed by perylene (21%) and fluoranthene (16%), but the fingerprint (in contrast to
17 -1,6,7,10-tetramethylfluoranthene 3, benzo[k]fluoranthene 6, and 3,6-dimethyldibenzo[j,l]fluoranthene
22 ing of benzo(a)anthracene, chrysene, benzo(b)fluoranthene and benzo(a)pyrene (PAH4) that have been ch
30 organic (the polycyclic aromatic hydrocarbon fluoranthene), and agrochemical (the herbicide atrazine)
31 dical- and OH radical-initiated reactions of fluoranthene, and 2-nitropyrene (2-NP) is formed from th
33 cene, and fluorene, and the HMW PAHs pyrene, fluoranthene, and benzo[a]pyrene, with the highest enzym
34 Thus, FVP of benzo[kl]thioxanthene (1) gives fluoranthene, and naphtho[2,1,8,7-klmn]thioxanthene (6)
35 ions were <30% for phenanthrene, anthracene, fluoranthene, and pyrene implying excellent reproducibil
37 artitioning constants for semivolatile PAHs, fluoranthene, and pyrene, within 1 order of magnitude ac
39 ubjected to electron transfer reactions with fluoranthene anions to produce singly charged, radical s
40 Electron transfer from gaseous Cs atoms and fluoranthene anions triggered backbone dissociations of
41 C (1000 m), where the aromatic hydrocarbons fluoranthene, anthracene, and Dibenzothiophene showed no
42 Anions generated by chemical ionization of fluoranthene are often used for both ETD and PTR reactio
43 benzo[c]phenanthrene gives 1-phenylbenzo[ghi]fluoranthene as the major product by homolysis of the C-
45 [a]anthracene (BaA), chrysene (Chr), benzo[b]fluoranthene (BbF), and benzo[a]pyrene (BaP), were detec
46 acene, chrysene, benz[b]fluoranthene, benz[k]fluoranthene, benz[a]pyrene, dibenz[a,h]anthracene, benz
47 pyrene, benz[a]anthracene, chrysene, benz[b]fluoranthene, benz[k]fluoranthene, benz[a]pyrene, dibenz
49 a]anthracene, benzo[k]-fluoranthene, benzo[b]fluoranthene, benzo[a]pyrene, chrysene, dibenz[a,h]anthr
50 samples, namely, benz[a]anthracene, benzo[k]-fluoranthene, benzo[b]fluoranthene, benzo[a]pyrene, chry
51 er PAHs including benz[a]anthracene, benzo[k]fluoranthene, benzo[e]pyrene, benzo[a]pyrene, benzo[ghi]
52 ic hydrocarbons: benzo[a]anthracene, benzo[b]fluoranthene, benzo[k]fluoranthene and benzo[a]pyrene in
54 This is demonstrated for the example of the fluoranthene cation, C(16)H(10)(+*), which is reacted wi
57 nated anthracenes/phenanthrenes, and pyrenes/fluoranthenes (Cl-PAHs and X-PAHs, X = Br and Cl), as we
58 w covalent organic polymers (COPs) made with fluoranthene-containing monomers and hexahydroxytripheny
59 cyclopenta ring-fused PAHs (CP-PAHs) such as fluoranthene/corannulene appeared as a preferred route o
60 While each of the monomers contains the same fluoranthene core, the resultant pore sizes range from m
61 ons of benzo[a]pyrene-d12 (BaP-d12), benzo[k]fluoranthene-d12 (BkF-d12), benzo[ghi]perylene-d12 (Bghi
65 lecular-weight PAHs [2- and 3-ring PAHs plus fluoranthene (FLA) and pyrene (PYR)] in contrast to high
66 hingomonas paucimobilis var. EPA505 utilizes fluoranthene (FLA), naphthalene (NAP), and phenanthrene
67 kg, chrysene from 9.4 to 1.9 mug/kg, benzo[b]fluoranthene from 5.3 to 0.6 mug/kg and benzo[a]pyrene f
68 s follows: TCDD>dibenz[ah]anthracene>benzo[k]fluoranthene>indeno[1,2,3-cd]pyrene>benzo[a]pyr ene>chry
70 used to interpret the effects of cadmium and fluoranthene, in both single and mixed exposure, on the
72 ccording to our hypothesis, the oxidation of fluoranthene is initiated by dioxygenation at the C-1,2,
74 d phenanthrene (L4), C14H10; pyrene (L5) and fluoranthene (L6), C16H10; a series of isomers of the C1
75 ETD and PTR reactions; the radical anion of fluoranthene (m/z 202) for ETD and the closed-shell anio
76 ge-reduced species shows that in the case of fluoranthene-mediated NETD, proton transfer only account
82 st substrate oxidation rate of 110 min-1 for fluoranthene oxidation by the R47L/Y51F/A264G mutant.
83 mples of persistent oxidation dications from fluoranthene-PAHs namely 1,3,4,6,7,10-hexamethyl- 2 and
84 iphenylanthracene, anthracene, anthanthrene, fluoranthene, perylene, and benzo[ghi]fluoranthene at pp
85 phthene, fluorene, phenanthrene, anthracene, fluoranthene, pyrene, benz[a]anthracene, chrysene, benz[
86 mpounds: fluorene, phenanthrene, anthracene, fluoranthene, pyrene, benzo(a)anthracene and chrysene.
87 mpounds: fluorene, phenanthrene, anthracene, fluoranthene, pyrene, benzo(a)anthracene and chrysene.
88 e environment in Africa toward phenanthrene, fluoranthene, pyrene, benzo(a)pyrene, 2,3,7,8-tetrachlor
90 e achieved using the substrates p-terphenyl, fluoranthene, pyrene, triphenylene, and corannulene.
92 sis represents a new approach to the benzo[j]fluoranthene ring system and specifically provides a met
95 all parent PAHs (PPAHs), except fluorene and fluoranthene], suggesting that PS debris is a source and
96 ntrations ranged from 1.2 mug/kg for benzo(b)fluoranthene to 125.0 mug/kg for benzo(a)anthracene in s
98 from exposure of filter-adsorbed deuterated fluoranthene to N2O5/NO3/NO2 and that collected from the
99 lated PAH varied from 83.3 +/- 2.4 (benzo[ k]fluoranthene) to 95.7 +/- 4.1% (benzo[ g,h,i]perylene).
100 The results reported here for pyrene and fluoranthene, two PAHs with different structures but the
102 C-1,2 and C-2,3 dioxygenation routes degrade fluoranthene via fluorene-type metabolites, whereas the
103 ne, chrysene, benzo[a]anthracene and benzo[b]fluoranthene) were between 3 and 12 mug kg(-1) wet weigh
104 energy of the electron transfer process for fluoranthene, which is estimated at 2.5-4.5 eV, compared
105 vents to produce 1-(o-chlorophenyl)benzo[ghi]fluoranthene, which then suffers a second radical cycliz
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