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1 the test mixture contained both anisole and fluoranthene.
2 n this case, a nitrogen-containing adduct of fluoranthene.
3 9.8% dibenzo[ah]anthracene and 69.0% benzo[b]fluoranthene.
4 roducts are benzo[k]fluoranthene and benzo[j]fluoranthene.
5 leading to prototype PAHs: triphenylene and fluoranthene.
6 um (5:95 ratio), and also converts slowly to fluoranthene.
7 media containing fluorene, phenanthrene, and fluoranthene.
8 enzo(a)anthracene to 10.8 mug/kg for benzo(b)fluoranthene.
9 ncentrations of phenanthrene and benzo(g,h,i)fluoranthene.
10 tal organic carbon and the anthropogenic PAH fluoranthene.
11 nthrene and from 0.006 to 90.0 mug L(-1) for fluoranthene.
12 clic aromatic hydrocarbons (PAHs), including fluoranthene.
13 and proposed pathways for the degradation of fluoranthene.
14 ugh study on b- and l,j-expanded and N-doped fluoranthenes.
15 r chrysene, 3.51 +/- 1.23 mg m(-2) d(-1) for fluoranthene, 0.23 +/- 0.08 mg m(-2) d(-1) for naphthale
17 pyrene (22%), followed by perylene (21%) and fluoranthene (16%), but the fingerprint (in contrast to
20 -1,6,7,10-tetramethylfluoranthene 3, benzo[k]fluoranthene 6, and 3,6-dimethyldibenzo[j,l]fluoranthene
25 ng NPAH, which sustained 2-nitrofluoranthene/fluoranthene and 2-nitropyrene/pyrene yields of (3.7 +/-
26 ing of benzo(a)anthracene, chrysene, benzo(b)fluoranthene and benzo(a)pyrene (PAH4) that have been ch
30 benzo[a]pyrene, benzo[a]anthracene, benzo[b]fluoranthene and chrysene in chocolate by high performan
32 estigate ion/ion reaction mechanisms between fluoranthene and divalent, metal-adducted carbohydrates
33 died the conversion of the semivolatile PAHs fluoranthene and pyrene into the 2-nitro derivatives 2-n
37 organic (the polycyclic aromatic hydrocarbon fluoranthene), and agrochemical (the herbicide atrazine)
38 dical- and OH radical-initiated reactions of fluoranthene, and 2-nitropyrene (2-NP) is formed from th
40 arbons; benz[a]anthracene, chrysene, benzo[b]fluoranthene, and benzo[a]pyrene) in roasted cocoa beans
41 cene, and fluorene, and the HMW PAHs pyrene, fluoranthene, and benzo[a]pyrene, with the highest enzym
42 ne, benzo[a]pyrene, anthracene, naphthalene, fluoranthene, and benzo[ghi]perylene) were identified in
43 Thus, FVP of benzo[kl]thioxanthene (1) gives fluoranthene, and naphtho[2,1,8,7-klmn]thioxanthene (6)
44 elta2x(13)C values) of the PAHs naphthalene, fluoranthene, and pyrene are 9 to 51 per mille higher th
45 ions were <30% for phenanthrene, anthracene, fluoranthene, and pyrene implying excellent reproducibil
46 Greatest concentrations of phenanthrene, fluoranthene, and pyrene were typically from the same si
48 artitioning constants for semivolatile PAHs, fluoranthene, and pyrene, within 1 order of magnitude ac
50 ubjected to electron transfer reactions with fluoranthene anions to produce singly charged, radical s
51 Electron transfer from gaseous Cs atoms and fluoranthene anions triggered backbone dissociations of
52 C (1000 m), where the aromatic hydrocarbons fluoranthene, anthracene, and Dibenzothiophene showed no
53 Anions generated by chemical ionization of fluoranthene are often used for both ETD and PTR reactio
54 benzo[c]phenanthrene gives 1-phenylbenzo[ghi]fluoranthene as the major product by homolysis of the C-
56 ns (PAHs), benzo(a)anthracene (BaA), benzo(b)fluoranthene (BbF), and benzo(a)pyrene (BaP) in tea samp
57 a)anthracene (BaA), chrysene (Chry), benzo(b)fluoranthene (BbF), and benzo(a)pyrene (BaP) were chosen
58 [a]anthracene (BaA), chrysene (Chr), benzo[b]fluoranthene (BbF), and benzo[a]pyrene (BaP), were detec
59 e clastogenicity and mutagenicity of benzo[b]fluoranthene (BbF), one of 16 priority PAHs, in MutaMous
60 acene, chrysene, benz[b]fluoranthene, benz[k]fluoranthene, benz[a]pyrene, dibenz[a,h]anthracene, benz
61 pyrene, benz[a]anthracene, chrysene, benz[b]fluoranthene, benz[k]fluoranthene, benz[a]pyrene, dibenz
63 a]anthracene, benzo[k]-fluoranthene, benzo[b]fluoranthene, benzo[a]pyrene, chrysene, dibenz[a,h]anthr
64 samples, namely, benz[a]anthracene, benzo[k]-fluoranthene, benzo[b]fluoranthene, benzo[a]pyrene, chry
65 er PAHs including benz[a]anthracene, benzo[k]fluoranthene, benzo[e]pyrene, benzo[a]pyrene, benzo[ghi]
66 ic hydrocarbons: benzo[a]anthracene, benzo[b]fluoranthene, benzo[k]fluoranthene and benzo[a]pyrene in
68 This is demonstrated for the example of the fluoranthene cation, C(16)H(10)(+*), which is reacted wi
70 benzo[a]anthracene, benzo[a]pyrene, benzo[b]fluoranthene, chrysene, and fluorene) and eight oxygenat
72 nated anthracenes/phenanthrenes, and pyrenes/fluoranthenes (Cl-PAHs and X-PAHs, X = Br and Cl), as we
73 w covalent organic polymers (COPs) made with fluoranthene-containing monomers and hexahydroxytripheny
74 cyclopenta ring-fused PAHs (CP-PAHs) such as fluoranthene/corannulene appeared as a preferred route o
75 While each of the monomers contains the same fluoranthene core, the resultant pore sizes range from m
76 ons of benzo[a]pyrene-d12 (BaP-d12), benzo[k]fluoranthene-d12 (BkF-d12), benzo[ghi]perylene-d12 (Bghi
80 lecular-weight PAHs [2- and 3-ring PAHs plus fluoranthene (FLA) and pyrene (PYR)] in contrast to high
81 hingomonas paucimobilis var. EPA505 utilizes fluoranthene (FLA), naphthalene (NAP), and phenanthrene
82 tives, which serve as substrates for the key fluoranthene-forming step, were prepared via selective m
83 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
84 s follows: TCDD>dibenz[ah]anthracene>benzo[k]fluoranthene>indeno[1,2,3-cd]pyrene>benzo[a]pyr ene>chry
87 used to interpret the effects of cadmium and fluoranthene, in both single and mixed exposure, on the
90 ccording to our hypothesis, the oxidation of fluoranthene is initiated by dioxygenation at the C-1,2,
92 d phenanthrene (L4), C14H10; pyrene (L5) and fluoranthene (L6), C16H10; a series of isomers of the C1
93 ETD and PTR reactions; the radical anion of fluoranthene (m/z 202) for ETD and the closed-shell anio
94 ge-reduced species shows that in the case of fluoranthene-mediated NETD, proton transfer only account
100 st substrate oxidation rate of 110 min-1 for fluoranthene oxidation by the R47L/Y51F/A264G mutant.
101 mples of persistent oxidation dications from fluoranthene-PAHs namely 1,3,4,6,7,10-hexamethyl- 2 and
102 iphenylanthracene, anthracene, anthanthrene, fluoranthene, perylene, and benzo[ghi]fluoranthene at pp
103 phthene, fluorene, phenanthrene, anthracene, fluoranthene, pyrene, benz[a]anthracene, chrysene, benz[
104 mpounds: fluorene, phenanthrene, anthracene, fluoranthene, pyrene, benzo(a)anthracene and chrysene.
105 mpounds: fluorene, phenanthrene, anthracene, fluoranthene, pyrene, benzo(a)anthracene and chrysene.
106 e environment in Africa toward phenanthrene, fluoranthene, pyrene, benzo(a)pyrene, 2,3,7,8-tetrachlor
108 e achieved using the substrates p-terphenyl, fluoranthene, pyrene, triphenylene, and corannulene.
111 sis represents a new approach to the benzo[j]fluoranthene ring system and specifically provides a met
113 ry in their position of pai-expansion on the fluoranthene scaffold and the location of the pyridinic
114 ficient method for the rapid construction of fluoranthene skeleton to access a variety of substituted
115 ion of the impact of such alterations in the fluoranthene structure on their overall properties.
116 nd for probing the structures of the crowded fluoranthene substrates and their bifluoranthenyls.
117 all parent PAHs (PPAHs), except fluorene and fluoranthene], suggesting that PS debris is a source and
118 investigations have sought to understand how fluoranthene-the primary, commercially available anion r
119 ntrations ranged from 1.2 mug/kg for benzo(b)fluoranthene to 125.0 mug/kg for benzo(a)anthracene in s
121 from exposure of filter-adsorbed deuterated fluoranthene to N2O5/NO3/NO2 and that collected from the
122 lated PAH varied from 83.3 +/- 2.4 (benzo[ k]fluoranthene) to 95.7 +/- 4.1% (benzo[ g,h,i]perylene).
123 The results reported here for pyrene and fluoranthene, two PAHs with different structures but the
125 C-1,2 and C-2,3 dioxygenation routes degrade fluoranthene via fluorene-type metabolites, whereas the
128 ne, chrysene, benzo[a]anthracene and benzo[b]fluoranthene) were between 3 and 12 mug kg(-1) wet weigh
129 energy of the electron transfer process for fluoranthene, which is estimated at 2.5-4.5 eV, compared
130 vents to produce 1-(o-chlorophenyl)benzo[ghi]fluoranthene, which then suffers a second radical cycliz