ライフサイエンスコーパス: polycyclic aromatic hydrocarbon

1 e to degrade substituted and non-substituted polycyclic aromatic hydrocarbons.

2 eral population and occupational exposure to polycyclic aromatic hydrocarbons.

3 thod for assessing the aromatic character of polycyclic aromatic hydrocarbons.

4 hase microextraction of seven representative polycyclic aromatic hydrocarbons.

5 of Environmental Protection Agency-priority polycyclic aromatic hydrocarbons.

6 osol (51 mg kg-fuel(-1)), and particle-bound polycyclic aromatic hydrocarbons (0.7 mg kg-fuel(-1)).

7 imitations during slow biodegradation of the polycyclic aromatic hydrocarbon 2-methylnaphthalene (2-M

8 Although concentrations of alkylated polycyclic aromatic hydrocarbons (alkyl-PAHs) in oil-con

9 Polycyclic aromatic hydrocarbons and diamondoids, which

10 ly monitored aromatics (parent and alkylated-polycyclic aromatic hydrocarbons and dibenzothiophenes)

11 he highest incidence, while those exposed to polycyclic aromatic hydrocarbons and heavy metals have t

12 Organic semiconductors are usually polycyclic aromatic hydrocarbons and their analogs conta

13 nthesis of a wide variety of angularly fused polycyclic aromatic hydrocarbons and their putative meta

14 predicted mixture effects were dominated by polycyclic aromatic hydrocarbons, and among the chemical

15 ospheric concentrations of flame retardants, polycyclic aromatic hydrocarbons, and pesticides were me

16 ge hydrophobic guests, including fullerenes, polycyclic aromatic hydrocarbons, and steroids, with sub

17 environmental pollutants (e.g., bisphenols, polycyclic aromatic hydrocarbons, and synthetic progesti

18 lusters resemble the resonance structures of polycyclic aromatic hydrocarbons, and water-ice analogue

19 Standards of polycyclic aromatic hydrocarbons, angiotensin I, lidocai

20 reduction potential and capacity of various polycyclic aromatic hydrocarbons are correlated with the

21 The complexity and range of asphaltene polycyclic aromatic hydrocarbons are established in deta

22 Polycyclic aromatic hydrocarbons are important structura

23 In this study, polycyclic aromatic hydrocarbons are introduced within a

24 rse class of extended periacenes and related polycyclic aromatic hydrocarbons as advanced materials f

25 The obtained mass spectra of five pure polycyclic aromatic hydrocarbons as well as complex petr

26 ted that OP(AO) was strongly correlated with polycyclic aromatic hydrocarbons at the traffic site whi

27 High exposures to several polycyclic aromatic hydrocarbons before conception and d

28 Therefore, PAH4 (sum of four different polycyclic aromatic hydrocarbons; benz[a]anthracene, chr

29 for simultaneous trace determination of four polycyclic aromatic hydrocarbons: benzo[a]anthracene, be

30 tormwater transports substantial mixtures of polycyclic aromatic hydrocarbons, bioactive contaminants

31 Second, for many alkanes and polycyclic aromatic hydrocarbons biodegradation occurred

32 occupied molecular orbital (LUMO) gap in the polycyclic aromatic hydrocarbons comprising the CNPs.

33 As an extended polycyclic aromatic hydrocarbon containing a defined cav

34 of these emerging nanomaterials in removing polycyclic aromatic hydrocarbon contaminants from water.

35 ons of individual saturated hydrocarbons and polycyclic aromatic hydrocarbons continued to decrease o

36 i-conjugated oligomers featuring a nonplanar polycyclic aromatic hydrocarbon, corannulene, and a plan

37 antum interference patterns in the hearts of polycyclic aromatic hydrocarbons could be isolated and m

38 ility, and dermal absorption of carcinogenic polycyclic aromatic hydrocarbons (cPAHs) in soil by huma

39 teobacteria populations were enriched in the polycyclic-aromatic-hydrocarbon-degrading communities an

40 between global NER and TCR in repairing the polycyclic aromatic hydrocarbon-derived DNA adducts (+)-

41 ters of the spill that assimilate alkane and polycyclic aromatic hydrocarbons during stable-isotope p

42 tudy investigated accumulation of petrogenic polycyclic aromatic hydrocarbons (E(39)PAHs) in the live

43 nontraditional synthesis of cyclopentafused-polycyclic aromatic hydrocarbon embedded ladder polymers

44 nts the largest three-dimensional conjugated polycyclic aromatic hydrocarbons ever prepared using sca

45 Vehicular traffic-related polycyclic aromatic hydrocarbon exposure and breast canc

46 oxypyrene (HP) is a widely used biomarker of polycyclic aromatic hydrocarbon exposure relevant for bi

47 gamma radiation (GR) in combination with the polycyclic aromatic hydrocarbon fluoranthene (FA).

48 idation of soot, which led to consumption of polycyclic aromatic hydrocarbons, formation of oxygen-co

49 g thermal injury (from hot tea), exposure to polycyclic aromatic hydrocarbons (from opium and indoor

50 Synthetic routes for heteroatom-containing polycyclic aromatic hydrocarbons (H-PAHs) with alkyl and

51 Nanographenes, or extended polycyclic aromatic hydrocarbons, have been attracting r

52 ing the degradation of high molecular weight-polycyclic aromatic hydrocarbons (HMW-PAHs) in sediments

53 Heavy polycyclic aromatic hydrocarbons (HPAHs) are known to ca

54 he convenient and efficient determination of polycyclic aromatic hydrocarbons in environmental water

55 thin a factor of 2 for parent- and alkylated-polycyclic aromatic hydrocarbons in petroleum-impacted s

56 hat mediates the toxicity of halogenated and polycyclic aromatic hydrocarbons in vertebrates.

57 Polycyclic aromatic hydrocarbons, in various charge and

58 nmental Health to determine whether prenatal polycyclic aromatic hydrocarbons interacts with DNA meth

59 The uptake of 16 polycyclic aromatic hydrocarbons into polyethylene passi

60 ng the hexagonal lattice of graphene-derived polycyclic aromatic hydrocarbons is a critical tool in t

61 otion that pai-extension of heteroatom-doped polycyclic aromatic hydrocarbons is an attractive approa

62 Benzo[a]pyrene (BaP), an archetypical polycyclic aromatic hydrocarbon, is classified as "carci

63 Benzo[a]pyrene (BaP), a polycyclic aromatic hydrocarbon, is the major cause of l

64 ves as a core upon which up to nine mono- or polycyclic aromatic hydrocarbon ligands are exohedrally

65 DNA adducts derived from carcinogenic polycyclic aromatic hydrocarbons like benzo[a]pyrene (B[

66 tal-free general method for the synthesis of polycyclic aromatic hydrocarbons like phenanthrenes and

67 Polycyclic aromatic hydrocarbons, major constituents of

68 envelopes, including the important role that polycyclic aromatic hydrocarbons might play in this, it

69 as evaluated by separating a three-component polycyclic aromatic hydrocarbon mixture on a commercial

70 g to a divergent set of ionic nitrogen-doped polycyclic aromatic hydrocarbons (N-doped PAHs), is pres

71 lyzed pot and step economic synthesis of aza-polycyclic aromatic hydrocarbons (N-PAHs) from readily a

72 at to cancer, including heterocyclic amines, polycyclic aromatic hydrocarbons, N-nitroso compounds, a

73 ker compounds (levoglucosan and resin acids, polycyclic aromatic hydrocarbons, nicotine) in the mass

74 Among the nitrated and oxygenated polycyclic aromatic hydrocarbons (NPAHs and OPAHs) are s

75 transformation products, including nitrated polycyclic aromatic hydrocarbons (NPAHs) and oxygenated

76 the spatial distribution of several nitrated polycyclic aromatic hydrocarbons (NPAHs) to identify fin

77 centrations of CYP1A1 phase I metabolites of polycyclic aromatic hydrocarbons (OH-PAHs) in liver and

78 aromatic hydrocarbons (NPAHs) and oxygenated polycyclic aromatic hydrocarbons (OPAHs) was then linked

79 Particulate polycyclic aromatic hydrocarbons (p-PAHs) emitted from d

80 hlorinated dibenzo-p-dioxins/furan (PCDD/F), polycyclic aromatic hydrocarbon (PAH) and polychlorinate

81 eport the first synthesis of a persulfurated polycyclic aromatic hydrocarbon (PAH) as a next-generati

82 Soil polycyclic aromatic hydrocarbon (PAH) bioavailability is

83 Aerobic and anaerobic polycyclic aromatic hydrocarbon (PAH) biodegradation was

84 We show that polycyclic aromatic hydrocarbon (PAH) chromophores that

85 ants) to Northern Hemisphere (NH) and Arctic polycyclic aromatic hydrocarbon (PAH) concentrations, us

86 from 359 locations and evaluated for biliary polycyclic aromatic hydrocarbon (PAH) concentrations.

87 ctor of lethality and pericardial edema than polycyclic aromatic hydrocarbon (PAH) content.

88 Mycobacterium gilvum VM552 served as a model polycyclic aromatic hydrocarbon (PAH) degrading bacteriu

89 Gulf of Mexico (GoM) in 2011-2013, to assess polycyclic aromatic hydrocarbon (PAH) exposure.

90 dy, arable soils of broad pH (4.26-8.43) and polycyclic aromatic hydrocarbon (PAH) gradients (0.18-20

91 frequently abundant, and sometimes the only polycyclic aromatic hydrocarbon (PAH) in aquatic sedimen

92 e thermodynamically most stable isomer - the polycyclic aromatic hydrocarbon (PAH) indene - is not fo

93 iad allows the formation of heteroatom-doped polycyclic aromatic hydrocarbon (PAH) isosteres, which e

94 Polycyclic aromatic hydrocarbon (PAH) measurements were

95 Interaction between polycyclic aromatic hydrocarbon (PAH) molecule and energ

96 MS) is a powerful method for the analysis of polycyclic aromatic hydrocarbon (PAH) molecules, which a

97 PM and benzo[a]pyrene B[a]P, a carcinogenic polycyclic aromatic hydrocarbon (PAH) of MW > 228 amu.

98 Benzo[a]pyrene (BaP), a key polycyclic aromatic hydrocarbon (PAH) often associated w

99 Benzo[a]pyrene (B[a]P) is a polycyclic aromatic hydrocarbon (PAH) that can be metabo

100 The formation of more polar and toxic polycyclic aromatic hydrocarbon (PAH) transformation pro

101 high-flow (3-30 L/min) for the collection of polycyclic aromatic hydrocarbon (PAH) vapor is described

102 g conditions and report effects on particle, polycyclic aromatic hydrocarbon (PAH), and alkyl- and ni

103 r-desorption of the near-planar, fluorinated polycyclic aromatic hydrocarbon (PAH), C60H21F9 (s).

104 ound both murine and human AHR and inhibited polycyclic aromatic hydrocarbon (PAH)- and TCDD-induced

105 k assessment approach currently employed for polycyclic aromatic hydrocarbon (PAH)-contaminated media

106 a biological vector, and, respectively, the polycyclic aromatic hydrocarbon (PAH)-degrading bacteria

107 , followed by oxidation with DDQ, afforded a polycyclic aromatic hydrocarbon (PAH)-porphyrin hybrid i

108 cts of diesel aftertreatment on emissions of polycyclic aromatic hydrocarbons (PAH) and their nitrate

109 Polycyclic aromatic hydrocarbons (PAH) are major primary

110 ottom-up strategy toward a novel bowl-shaped polycyclic aromatic hydrocarbons (PAH) C34 with two pent

111 ging to find a possibility of elimination of polycyclic aromatic hydrocarbons (PAH) from smoked sausa

112 Polycyclic aromatic hydrocarbons (PAH) indicate possible

113 e predictions of the total concentrations of polycyclic aromatic hydrocarbons (PAH), PHC, and alkanes

114 tion of resistance to a ubiquitous pollutant-polycyclic aromatic hydrocarbons (PAH).

115 etrahydrophenanthrene (PheT), a biomarker of polycyclic aromatic hydrocarbons (PAH).

116 es) was associated with prenatal exposure to polycyclic aromatic hydrocarbons (PAHs combined: OR = 1.

117 as demonstrated in the extraction of several polycyclic aromatic hydrocarbons (PAHs) (acenaphthylene,

118 vironmental Protection Agency (EPA)-priority polycyclic aromatic hydrocarbons (PAHs) adsorbed on LCPM

119 d water dissolved phase concentrations of 33 polycyclic aromatic hydrocarbons (PAHs) and 22 oxygenate

120 d water dissolved phase concentrations of 33 polycyclic aromatic hydrocarbons (PAHs) and 22 oxygenate

121 hod for the simultaneous determination of 18 polycyclic aromatic hydrocarbons (PAHs) and 26 n-alkanes

122 By investigating the uptake of 16 priority polycyclic aromatic hydrocarbons (PAHs) and five heavy m

123 for hydrogen shifts in radicals derived from polycyclic aromatic hydrocarbons (PAHs) and for rearrang

124 Syntheses of large polycyclic aromatic hydrocarbons (PAHs) and graphene nan

125 studies have suggested associations between polycyclic aromatic hydrocarbons (PAHs) and heart rate v

126 udies between exposure to pollutants such as polycyclic aromatic hydrocarbons (PAHs) and human health

127 ace carcinogenic organic pollutants, such as polycyclic aromatic hydrocarbons (PAHs) and ionic dyes,

128 t in higher concentrations of particle-phase polycyclic aromatic hydrocarbons (PAHs) and n-alkanes, h

129 ased (CT) sealcoated pavement is a source of polycyclic aromatic hydrocarbons (PAHs) and N-heterocycl

130 Exposures to polycyclic aromatic hydrocarbons (PAHs) and other organi

131 nge atmospheric transport (LRAT) modeling of polycyclic aromatic hydrocarbons (PAHs) and PAH oxidatio

132 Polycyclic aromatic hydrocarbons (PAHs) and polybrominat

133 ydrophobic organic chemicals (HOCs), such as polycyclic aromatic hydrocarbons (PAHs) and polychlorina

134 Polycyclic aromatic hydrocarbons (PAHs) and some of thei

135 Polycyclic aromatic hydrocarbons (PAHs) are a diverse gr

136 Polycyclic aromatic hydrocarbons (PAHs) are common atmos

137 Complex mixtures of polycyclic aromatic hydrocarbons (PAHs) are common envir

138 Mixtures of metals and polycyclic aromatic hydrocarbons (PAHs) are commonly fou

139 Polycyclic aromatic hydrocarbons (PAHs) are considered t

140 Polycyclic aromatic hydrocarbons (PAHs) are hazardous ai

141 Polycyclic aromatic hydrocarbons (PAHs) are of significa

142 Polycyclic aromatic hydrocarbons (PAHs) are omnipresent

143 Polycyclic aromatic hydrocarbons (PAHs) are persistent e

144 their formation mechanism and interplay with polycyclic aromatic hydrocarbons (PAHs) are poorly under

145 Polycyclic aromatic hydrocarbons (PAHs) are potentially

146 ion, hydrogenation, and covalent coupling of polycyclic aromatic hydrocarbons (PAHs) are processes of

147 Polycyclic aromatic hydrocarbons (PAHs) are routinely sc

148 ion (WSF) from crude oil have concluded that polycyclic aromatic hydrocarbons (PAHs) are the primary

149 Polycyclic aromatic hydrocarbons (PAHs) are toxic organi

150 Polycyclic aromatic hydrocarbons (PAHs) are ubiquitous a

151 Polycyclic aromatic hydrocarbons (PAHs) are widely distr

152 Polycyclic aromatic hydrocarbons (PAHs) are widespread e

153 rances, as novel personal care products, and polycyclic aromatic hydrocarbons (PAHs) as combustion an

154 n attempting to rationalize the formation of polycyclic aromatic hydrocarbons (PAHs) as detected in c

155 (PM) and the associated low molecular weight polycyclic aromatic hydrocarbons (PAHs) as key mediators

156 This review summarizes recent knowledge of polycyclic aromatic hydrocarbons (PAHs) biotransformatio

157 This study aimed at evaluating the polycyclic aromatic hydrocarbons (PAHs) contamination of

158 gas chromatography (GC) to characterize the polycyclic aromatic hydrocarbons (PAHs) content of soot.

159 tigates the concentration and composition of polycyclic aromatic hydrocarbons (PAHs) dispersed in LSM

160 EGR resulted in an accumulation of polycyclic aromatic hydrocarbons (PAHs) during combustio

161 dy was to evaluate the formation kinetics of polycyclic aromatic hydrocarbons (PAHs) during drying of

162 Polycyclic aromatic hydrocarbons (PAHs) emerged as an im

163 c structure calculations suggest these large polycyclic aromatic hydrocarbons (PAHs) exhibit excellen

164 of tetrachlorodibenzo-p-dioxin (TCDD) and 18 polycyclic aromatic hydrocarbons (PAHs) for induction of

165 n methods for concentrations of elements and polycyclic aromatic hydrocarbons (PAHs) for the PM(2.5)

166 Specifically, polycyclic aromatic hydrocarbons (PAHs) found in ultrafi

167 Of particular relevance are polycyclic aromatic hydrocarbons (PAHs) from combustion

168 orescence detection for the determination of polycyclic aromatic hydrocarbons (PAHs) from contaminate

169 diation technique used to remove and recover polycyclic aromatic hydrocarbons (PAHs) from contaminate

170 egy for the selective separation of specific polycyclic aromatic hydrocarbons (PAHs) from mixtures.

171 let (UV) radiation is one mechanism by which polycyclic aromatic hydrocarbons (PAHs) from oil spills

172 iously shown to enhance the mass transfer of polycyclic aromatic hydrocarbons (PAHs) from sediment in

173 al reactions that make new covalent bonds to polycyclic aromatic hydrocarbons (PAHs) have been confin

174 Sixteen polycyclic aromatic hydrocarbons (PAHs) have been identi

175 The atmospheric dry deposition fluxes of 16 polycyclic aromatic hydrocarbons (PAHs) have been measur

176 n of heterocyclic aromatic amines (HCAs) and polycyclic aromatic hydrocarbons (PAHs) in beef steak we

177 Levels of polycyclic aromatic hydrocarbons (PAHs) in cocoa beans o

178 ed as a key route to aromatic ring growth of polycyclic aromatic hydrocarbons (PAHs) in combustion sy

179 Analysis of polycyclic aromatic hydrocarbons (PAHs) in complex foods

180 c polyaromatic pollutants that co-occur with polycyclic aromatic hydrocarbons (PAHs) in contaminated

181 al studies have shown high concentrations of polycyclic aromatic hydrocarbons (PAHs) in living spaces

182 Benthic organisms may be exposed to polycyclic aromatic hydrocarbons (PAHs) in marine sedime

183 eloping a method for the determination of 16 polycyclic aromatic hydrocarbons (PAHs) in rice grain sa

184 developed for the determination of selected polycyclic aromatic hydrocarbons (PAHs) in rice samples

185 The bioavailability of polycyclic aromatic hydrocarbons (PAHs) in soils can be

186 nked to increasing atmospheric deposition of polycyclic aromatic hydrocarbons (PAHs) in the Athabasca

187 Characteristics of polycyclic aromatic hydrocarbons (PAHs) in the Chicxulub

188 the production process, biochars can contain polycyclic aromatic hydrocarbons (PAHs) in the high mg/k

189 The downstream accumulation of polycyclic aromatic hydrocarbons (PAHs) in the Peace-Ath

190 ased pavement sealants are a major source of polycyclic aromatic hydrocarbons (PAHs) in urban setting

191 ine particulate matter (PM(2.5)), species of polycyclic aromatic hydrocarbons (PAHs) including naphth

192 Evidence suggests that exposure to polycyclic aromatic hydrocarbons (PAHs) increases atopy;

193 icant discharges of particulate matter-bound polycyclic aromatic hydrocarbons (PAHs) into aquatic env

194 The blowout released complex mixtures of polycyclic aromatic hydrocarbons (PAHs) into critical pe

195 ediation uses soil microorganisms to degrade polycyclic aromatic hydrocarbons (PAHs) into less toxic

196 r synthesis of regiospecifically fluorinated polycyclic aromatic hydrocarbons (PAHs) is described.

197 detection of aromatic hydrocarbons (AHs) and polycyclic aromatic hydrocarbons (PAHs) is of high impor

198 Environmental exposure to polycyclic aromatic hydrocarbons (PAHs) is prevalent and

199 To assess the exposure to polycyclic aromatic hydrocarbons (PAHs) it is important

200 In the absence of dopants, polycyclic aromatic hydrocarbons (PAHs) mostly form [M +

201 Mixtures of metals and polycyclic aromatic hydrocarbons (PAHs) occur ubiquitous

202 tion isotherms were generated for a suite of polycyclic aromatic hydrocarbons (PAHs) on multiwalled c

203 ke, penetration, and distribution of sixteen polycyclic aromatic hydrocarbons (PAHs) on the morpholog

204 ted in this work is a 9 s separation of four polycyclic aromatic hydrocarbons (PAHs) over a 2.2 s sep

205 Architectures of the polycyclic aromatic hydrocarbons (PAHs) play a crucial r

206 Polycyclic aromatic hydrocarbons (PAHs) present in crude

207 Polycyclic aromatic hydrocarbons (PAHs) represent key mo

208 Polycyclic aromatic hydrocarbons (PAHs) represent the li

209 inogen exposure biomarkers (heavy metals and polycyclic aromatic hydrocarbons (PAHs) represented by 1

210 ng conventional hypotheses that synthesis of polycyclic aromatic hydrocarbons (PAHs) solely proceeds

211 t a high structural complexity, comprised of polycyclic aromatic hydrocarbons (PAHs) that are a mixtu

212 rmation of acenes, phenacenes, and helicenes-polycyclic aromatic hydrocarbons (PAHs) that are distinc

213 Polycyclic aromatic hydrocarbons (PAHs) undergo transfor

214 e examined the efficacy of passive dosing of polycyclic aromatic hydrocarbons (PAHs) using silicone O

215 lth risks among seafood consumers exposed to polycyclic aromatic hydrocarbons (PAHs) via consumption

216 trial environments leads to the formation of polycyclic aromatic hydrocarbons (PAHs) via gas phase ra

217 A model for gas-particle partitioning of polycyclic aromatic hydrocarbons (PAHs) was evaluated us

218 nosulfates (OSs) from the photo-oxidation of polycyclic aromatic hydrocarbons (PAHs) was investigated

219 Formation of polycyclic aromatic hydrocarbons (PAHs) was not observed

220 organic material, such as wood, can generate polycyclic aromatic hydrocarbons (PAHs) which are known

221 capable of forming inclusion complexes with polycyclic aromatic hydrocarbons (PAHs) with high bindin

222 by the cigarette-related compounds nicotine, polycyclic aromatic hydrocarbons (PAHs) with one to five

223 Polycyclic aromatic hydrocarbons (PAHs) with six and sev

224 , and xylene (BTEX); carbonyl compounds; and polycyclic aromatic hydrocarbons (PAHs)) were measured w

225 alkenes, alkynes, aromatics, carbonyls, and polycyclic aromatic hydrocarbons (PAHs))-were measured i

226 nd fats are important sources of exposure to polycyclic aromatic hydrocarbons (PAHs), a group of orga

227 Samples were analyzed for polycyclic aromatic hydrocarbons (PAHs), alkylated PAHs,

228 es for 5 polychlorinated biphenyls (PCBs), 7 polycyclic aromatic hydrocarbons (PAHs), and 15 pesticid

229 rmined for polychlorinated biphenyls (PCBs), polycyclic aromatic hydrocarbons (PAHs), and organochlor

230 s (PBDEs), polychlorinated biphenyls (PCBs), polycyclic aromatic hydrocarbons (PAHs), and pesticides.

231 drin, chlordane- and DDT-related pesticides, polycyclic aromatic hydrocarbons (PAHs), and polybromina

232 for polybrominated diphenyl ethers (PBDEs), polycyclic aromatic hydrocarbons (PAHs), and polychlorin

233 rom four other classes of human carcinogens: polycyclic aromatic hydrocarbons (PAHs), aromatic amines

234 nology for cleanup of soil contaminated with polycyclic aromatic hydrocarbons (PAHs), but it can incr

235 ium into which organic contaminants, such as polycyclic aromatic hydrocarbons (PAHs), can accumulate,

236 mpassed a diverse set of compounds including polycyclic aromatic hydrocarbons (PAHs), consumer produc

237 ations of SPR in the detection of pesticide, polycyclic aromatic hydrocarbons (PAHs), heavy metals an

238 The toxic nature of polycyclic aromatic hydrocarbons (PAHs), in particular b

239 blowout resulted in the deposition of toxic polycyclic aromatic hydrocarbons (PAHs), in the coastal

240 The concentration of twelve polycyclic aromatic hydrocarbons (PAHs), included in the

241 ere, we present a record of the abundance of polycyclic aromatic hydrocarbons (PAHs), organic compoun

242 The PACs investigated were polycyclic aromatic hydrocarbons (PAHs), oxygenated-PAHs

243 eric transport on measured concentrations of polycyclic aromatic hydrocarbons (PAHs), PAH derivatives

244 Ps), polybrominated diphenyl-ethers (PBDEs), polycyclic aromatic hydrocarbons (PAHs), phthalates, ins

245 hemicals (SVOCs) to the atmosphere including polycyclic aromatic hydrocarbons (PAHs), polychlorinated

246 Concentrations of polycyclic aromatic hydrocarbons (PAHs), polychlorinated

247 al persistent organic pollutants (POPs) like polycyclic aromatic hydrocarbons (PAHs), polychlorinated

248 rs, benzene polycarboxylic acids (BPCAs) and polycyclic aromatic hydrocarbons (PAHs), preserved in aq

249 ompounds, including methoxyphenols (MPs) and polycyclic aromatic hydrocarbons (PAHs), some of which a

250 gradation of substituted and non-substituted polycyclic aromatic hydrocarbons (PAHs), thereby suggest

251 Besides polycyclic aromatic hydrocarbons (PAHs), these mixtures

252 even polychlorinated biphenyls (PCBs), seven polycyclic aromatic hydrocarbons (PAHs), three chlorinat

253 fish to varying concentrations of dissolved polycyclic aromatic hydrocarbons (PAHs), which can have

254 assessment study, which included methylated polycyclic aromatic hydrocarbons (PAHs), which have neve

255 t monocyclic aromatic hydrocarbons (MAHs) or polycyclic aromatic hydrocarbons (PAHs).

256 ed in petroleum-derived compounds, including polycyclic aromatic hydrocarbons (PAHs).

257 o more profound toxic effects from uptake of polycyclic aromatic hydrocarbons (PAHs).

258 n that has enabled the syntheses of numerous polycyclic aromatic hydrocarbons (PAHs).

259 ghways and other impervious surfaces include polycyclic aromatic hydrocarbons (PAHs).

260 nd were measured for 50 parent and alkylated polycyclic aromatic hydrocarbons (PAHs).

261 Samplers were analyzed for 62 polycyclic aromatic hydrocarbons (PAHs).

262 erns about emissions of contaminants such as polycyclic aromatic hydrocarbons (PAHs).

263 vity, which makes it a powerful receptor for polycyclic aromatic hydrocarbons (PAHs).

264 isotope approach for source apportionment of polycyclic aromatic hydrocarbons (PAHs).

265 ures, may be susceptible to contamination by polycyclic aromatic hydrocarbons (PAHs).

266 ion rate, such as phthalate plasticizers and polycyclic aromatic hydrocarbons (PAHs).

267 ompounds, including acrolein, acrylamide and polycyclic aromatic hydrocarbons (PAHs).

268 lic cores to yield expanded difunctionalized polycyclic aromatic hydrocarbons (PAHs).

269 formation of non-desirable compounds such as polycyclic aromatic hydrocarbons (PAHs).

270 owering modification of graphene and related polycyclic aromatic hydrocarbons (PAHs).

271 strategy for accessing heteroatom-containing polycyclic aromatic hydrocarbons (PAHs).

272 y, however, contain a considerable amount of polycyclic aromatic hydrocarbons (PAHs).

273 n and are known for their ability to degrade polycyclic aromatic hydrocarbons (PAHs).

274 emical and electronic properties of extended polycyclic aromatic hydrocarbons (PAHs, or namely nanogr

275 ollutants (black carbon (BC), particle-bound polycyclic aromatic hydrocarbons (PB-PAH), benzene, and

276 Bioaccumulation of the polycyclic aromatic hydrocarbon phenanthrene in the abse

277 nds originating from shale formations (e.g., polycyclic aromatic hydrocarbons, phthalates), fracturin

278 lack carbon, methane, total hydrocarbons, 32 polycyclic aromatic hydrocarbons, PM2.5, levoglucosan (a

279 Interestingly, retene, a polycyclic aromatic hydrocarbon present in PM10, is a po

280 Zn and/or polycyclic aromatic hydrocarbons (pyrene, phenanthrene,

281 Seven species of reef fish were tested for polycyclic aromatic hydrocarbons, several metals, and a

282 The resulting BN-substituted contorted polycyclic aromatic hydrocarbons show large bathochromic

283 A class of methacrylate polymers based on a polycyclic aromatic hydrocarbon side moiety, pyrene, was

284 Both saturated and polycyclic aromatic hydrocarbon source indicators corrob

285 physical phenomena surrounding this class of polycyclic aromatic hydrocarbons, specifically emphasizi

286 tile mechanism to build up even more complex polycyclic aromatic hydrocarbons such as [5]- and [6]-he

287 -1) dry fuel, gas + particle-associated) for polycyclic aromatic hydrocarbons ( summation operator13

288 re, we introduce nanographenes, namely large polycyclic aromatic hydrocarbons that can also be regard

289 Deepwater Horizon crude oil is comprised of polycyclic aromatic hydrocarbons that cause a number of

290 and useful intermediates in the synthesis of polycyclic aromatic hydrocarbons, they can be difficult

291 eversible dearomative coupling reaction with polycyclic aromatic hydrocarbons to afford diboration pr

292 ntrations, and compositions of oil and total polycyclic aromatic hydrocarbons (TPAH) in the Gulf of M

293 The repertoire of polycyclic aromatic hydrocarbon use varied among differe

294 in all participants include urinary hydroxy-polycyclic aromatic hydrocarbons, volatile organic chemi

295 ed biphenyls, organochlorine pesticides, and polycyclic aromatic hydrocarbons were measured in mangro

296 This is especially true for polycyclic aromatic hydrocarbons, which represent an imp

297 ]aceanthrylene (B[j]A) is a cyclopenta-fused polycyclic aromatic hydrocarbon with strong mutagenic an

298 ries of contorted, yet noncentrosymmetrical, polycyclic aromatic hydrocarbons with a pentabenzo-fused

299 Polycyclic aromatic hydrocarbons with less than seven ri

300 of a well-studied reaction of surface-bound polycyclic aromatic hydrocarbons with ozone are presente