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

1 stitution at the central position of a model polycyclic aromatic hydrocarbon.

2 is described and applied to the synthesis of polycyclic aromatic hydrocarbons.

3 or chlorinated compounds as well as for some polycyclic aromatic hydrocarbons.

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

5 ldehyde, acetaldehyde, acrolein, and several polycyclic aromatic hydrocarbons.

6 erated derivatives of both common and exotic polycyclic aromatic hydrocarbons.

7 eral population and occupational exposure to polycyclic aromatic hydrocarbons.

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

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

10 ded in the columns was reduced by 95-99% for polycyclic aromatic hydrocarbons and 93-97% for polychlo

11 Polycyclic aromatic hydrocarbons and diamondoids, which

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

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

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

15 hemicals monitored, pesticides, tributyltin, polycyclic aromatic hydrocarbons, and brominated flame r

16 rge hydrophobic guests including fullerenes, polycyclic aromatic hydrocarbons, and large, structurall

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

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

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

20 Standards of polycyclic aromatic hydrocarbons, angiotensin I, lidocai

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

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

23 Polycyclic aromatic hydrocarbons are important structura

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

25 tion, gas-phase reactions of fullerenes with polycyclic aromatic hydrocarbons are investigated to pro

26 Polycyclic aromatic hydrocarbons are suspected developme

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

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

29 ed in multiple sorbate experiments with four polycyclic aromatic hydrocarbons at small concentration.

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

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

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

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 nontraditional synthesis of cyclopentafused-polycyclic aromatic hydrocarbon embedded ladder polymers

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

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

45 form for developing ribbon-like nitrogenated polycyclic aromatic hydrocarbons for a broad spectrum of

46 The majority of these are halogenated polycyclic aromatic hydrocarbons (halo-PAHs), including

47 Exposure to polycyclic aromatic hydrocarbons has often been quantifi

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

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

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

51 y introduced method was applied to determine polycyclic aromatic hydrocarbons in Iranian smoked fish.

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

53 Polycyclic aromatic hydrocarbons, in various charge and

54 The uptake of 16 polycyclic aromatic hydrocarbons into polyethylene passi

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

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

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

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

59 Polycyclic aromatic hydrocarbons, major constituents of

60 , neurodevelopmental effects attributable to polycyclic aromatic hydrocarbons may be quite different

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

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

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

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

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

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

67 The level of polycyclic aromatic hydrocarbons occurrence and the poss

68 Subsequently, mixtures containing polycyclic aromatic hydrocarbons, of which some are bioa

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

70 Concentrations of 12 hydroxylated polycyclic aromatic hydrocarbons (OH-PAHs) were determin

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

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

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

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

75 Soil polycyclic aromatic hydrocarbon (PAH) bioavailability is

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

77 dictive models between time-weighted average polycyclic aromatic hydrocarbon (PAH) concentrations in

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

79 Polycyclic aromatic hydrocarbon (PAH) contamination in t

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

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

82 en lung cancer mortality rates, carcinogenic polycyclic aromatic hydrocarbon (PAH) emissions, and smo

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

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

85 n water using a family of highly hydrophobic polycyclic aromatic hydrocarbon (PAH) luminophores and b

86 Polycyclic aromatic hydrocarbon (PAH) measurements were

87 dge of bacterial high-molecular-weight (HMW) polycyclic aromatic hydrocarbon (PAH) metabolism, the ke

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

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

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

91 converted catalytically into PAH-MOF-1 with polycyclic aromatic hydrocarbon (PAH) pillars.

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

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

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

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

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

97 Benzo[a]pyrene (BaP), a polycyclic aromatic hydrocarbon (PAH), is one of the maj

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

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

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

101 We report that polycyclic aromatic hydrocarbon (PAH)-inducible CYP1B1 i

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

103 GC/MS data for the quantitative analysis of polycyclic aromatic hydrocarbons (PAH) and polycyclic ar

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

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

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

107 as used to trace and identify the sources of polycyclic aromatic hydrocarbons (PAH) in sediments of L

108 ve been recently shown to actively transport polycyclic aromatic hydrocarbons (PAH) in water-unsatura

109 m of our study was to evaluate LUR models of polycyclic aromatic hydrocarbons (PAH), hopanes/steranes

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

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

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

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

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

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

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

117 Concentrations of total and freely dissolved polycyclic aromatic hydrocarbons (PAHs) and dissolved or

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

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

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

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

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

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

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

125 ons of ambient particulate matter (PM)-bound polycyclic aromatic hydrocarbons (PAHs) and nitro-PAHs (

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

127 Polycyclic aromatic hydrocarbons (PAHs) and polybrominat

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

129 Hydrophobic organic compounds (HOCs) like polycyclic aromatic hydrocarbons (PAHs) and polychlorina

130 Bs), polybrominated diphenyl ethers (PBDEs), polycyclic aromatic hydrocarbons (PAHs) and polycyclic m

131 Time-resolved emissions of particulate polycyclic aromatic hydrocarbons (PAHs) and total organi

132 The native PACs investigated were polycyclic aromatic hydrocarbons (PAHs) and, for the fir

133 Polycyclic aromatic hydrocarbons (PAHs) are abundant and

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

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

136 Polycyclic aromatic hydrocarbons (PAHs) are hazardous ai

137 Polycyclic aromatic hydrocarbons (PAHs) are known carcin

138 Polycyclic aromatic hydrocarbons (PAHs) are of significa

139 Polycyclic aromatic hydrocarbons (PAHs) are omnipresent

140 Polycyclic aromatic hydrocarbons (PAHs) are persistent e

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

142 Mutagenic Polycyclic aromatic hydrocarbons (PAHs) are present at v

143 to evaluate the hypothesis that atmospheric polycyclic aromatic hydrocarbons (PAHs) are trapped in s

144 Polycyclic aromatic hydrocarbons (PAHs) are ubiquitous a

145 Polycyclic aromatic hydrocarbons (PAHs) are ubiquitous o

146 Polycyclic aromatic hydrocarbons (PAHs) are widely distr

147 Polycyclic aromatic hydrocarbons (PAHs) are widespread e

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

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

150 tion of nonsubstituted and alkyl-substituted polycyclic aromatic hydrocarbons (PAHs) by the benthic i

151 BDEs), organochlorine pesticides (OCPs), and polycyclic aromatic hydrocarbons (PAHs) by up to 400% co

152 he environmental partitioning of atmospheric polycyclic aromatic hydrocarbons (PAHs) conditions their

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

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

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

156 Polycyclic aromatic hydrocarbons (PAHs) emerged as an im

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

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

159 ata for polychlorinated biphenyls (PCBs) and polycyclic aromatic hydrocarbons (PAHs) from a field cal

160 Exposure to polycyclic aromatic hydrocarbons (PAHs) from burning "sm

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

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

163 rdiac teratogenesis caused by high levels of polycyclic aromatic hydrocarbons (PAHs) from creosote.

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

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

166 new efficient three-step process to annulate polycyclic aromatic hydrocarbons (PAHs) has been develop

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

168 Sixteen polycyclic aromatic hydrocarbons (PAHs) have been identi

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

170 For almost half a century, polycyclic aromatic hydrocarbons (PAHs) have been propos

171 to measure time-integrated concentrations of polycyclic aromatic hydrocarbons (PAHs) in alpine stream

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

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

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

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

176 historical record of source apportionment of polycyclic aromatic hydrocarbons (PAHs) in dated sedimen

177 The determination of polycyclic aromatic hydrocarbons (PAHs) in fish oils is

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

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

180 ented significantly higher concentrations of polycyclic aromatic hydrocarbons (PAHs) in settled house

181 This study describes the occurrence of polycyclic aromatic hydrocarbons (PAHs) in smoked tea an

182 The concentrations of polycyclic aromatic hydrocarbons (PAHs) in smoked, grill

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

184 Although concentrations of polycyclic aromatic hydrocarbons (PAHs) in some environm

185 sure concentrations of gaseous and dissolved polycyclic aromatic hydrocarbons (PAHs) in the air and w

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

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

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

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

190 ed carbon (AC) to reduce the availability of polycyclic aromatic hydrocarbons (PAHs) including alkyla

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

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

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

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

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

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

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

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

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

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

201 Polycyclic aromatic hydrocarbons (PAHs) on virgin polyst

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

203 Polycyclic aromatic hydrocarbons (PAHs) represent a clas

204 human mammary carcinoma MCF-7 cells against polycyclic aromatic hydrocarbons (PAHs) such as benzo[a]

205 tion of polychlorinated biphenyls (PCBs) and polycyclic aromatic hydrocarbons (PAHs) throughout a 12-

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

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

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

209 The level of 16 polycyclic aromatic hydrocarbons (PAHs) was determined i

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

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

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

213 The polycyclic aromatic hydrocarbons (PAHs) were predominant

214 Metals and polycyclic aromatic hydrocarbons (PAHs) were predominant

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

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

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

218 We show that polycyclic aromatic hydrocarbons (PAHs) within lake sedi

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

220 titioning coefficients (K(PE)) for 17 parent-polycyclic aromatic hydrocarbons (PAHs), 22 alkylated-PA

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

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

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

224 lic aromatic compounds (PACs), which include polycyclic aromatic hydrocarbons (PAHs), and heterocycli

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

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

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

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

229 Bs), polybrominated diphenyl ethers (PBDEs), polycyclic aromatic hydrocarbons (PAHs), and polycyclic

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

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

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

233 exposure to combustion byproducts, including polycyclic aromatic hydrocarbons (PAHs), can augment the

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

235 The enhancement of the degradation of polycyclic aromatic hydrocarbons (PAHs), exemplified by

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

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

238 ysiological deficits, likely attributable to polycyclic aromatic hydrocarbons (PAHs), occurred at env

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

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

241 Concentrations of polycyclic aromatic hydrocarbons (PAHs), polychlorinated

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

243 The transfer of HOCs including polycyclic aromatic hydrocarbons (PAHs), polychlorinated

244 rations and spatial distribution of selected polycyclic aromatic hydrocarbons (PAHs), polychlorinated

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

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

247 -affinity scavenger of an array of different polycyclic aromatic hydrocarbons (PAHs), ranging from tw

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

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

250 Besides polycyclic aromatic hydrocarbons (PAHs), these mixtures

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

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

253 e (PE) samplers were validated for measuring polycyclic aromatic hydrocarbons (PAHs), with a focus on

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

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

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

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

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

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

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

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

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

263 idespread environmental contaminants such as polycyclic aromatic hydrocarbons (PAHs).

264 ere potentially exposed to crude oil-derived polycyclic aromatic hydrocarbons (PAHs).

265 axis chamber to serve as sink and source for polycyclic aromatic hydrocarbons (PAHs).

266 e achievable sensitivity in the detection of polycyclic aromatic hydrocarbons (PAHs).

267 ntities to a landfill soil contaminated with polycyclic aromatic hydrocarbons (PAHs).

268 zo-p-dioxins and dibenzofurans (PCDD/Fs) and polycyclic aromatic hydrocarbons (PAHs).

269 R/V Endeavor in summer 2009 and analyzed for polycyclic aromatic hydrocarbons (PAHs).

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

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

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

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

274 hanges on the atmospheric transport of three polycyclic aromatic hydrocarbons (PAHs): phenanthrene (P

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

276 s of four key air pollutants, particle-bound polycyclic aromatic hydrocarbons (PB-PAH), particle numb

277 ntification: Diagnostic Ratios of n-alkanes, polycyclic aromatic hydrocarbons, pentacyclic triterpane

278 Bioaccumulation of the polycyclic aromatic hydrocarbon phenanthrene in the abse

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

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

281 sistent organic pollutants (POPs), including polycyclic aromatic hydrocarbons, polychlorinated dibenz

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

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

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

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

286 Both saturated and polycyclic aromatic hydrocarbon source indicators corrob

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

288 Linear and ribbon-like polycyclic aromatic hydrocarbons such as acenes and grap

289 molecules ranging from long pi-electron-rich polycyclic aromatic hydrocarbons, such as tetracene, tet

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

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

292 avily oiled based on concentrations of total polycyclic aromatic hydrocarbons ([TPAH]).

293 The repertoire of polycyclic aromatic hydrocarbon use varied among differe

294 f mercury, lead and its stable isotopes, and polycyclic aromatic hydrocarbons were determined in a da

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

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

297 rediction of the reactivity and stability of polycyclic aromatic hydrocarbons with a closed-shell ele

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

299 cenes are a type of nitrogenated ribbon-like polycyclic aromatic hydrocarbons with a very high stabil

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