PMID-sentid Pub_year Sent_text comp_official_name comp_offsetprotein_name organism prot_offset 23376598-2 2013 The highest PAH concentrations recovered in foodstuffs corresponded to the following contributors: chrysene (25.7%), benzo[b]fluoranthene (15.0%) and benz[a]anthracene (9.0%) whereas the lowest concentrations were those of dibenz[a,h]anthracene, 5 methylchrysene and dibenzo[a,h]pyrene (below 2.0%). anthracene 157-167 phenylalanine hydroxylase Homo sapiens 12-15 22869394-3 2012 The following PAH were found in bioavailable form: acenaphthylene, acenaphthene, fluorene, phenanthrene, anthracene, fluoranthene, pyrene, with C(free) varying between 2.38 and 62.35 ng/L. anthracene 105-115 phenylalanine hydroxylase Homo sapiens 14-17 23295026-4 2013 In this paper, optimized mats of ZnO nanofibers with an average fiber diameter of 60 nm are shown to be highly effective in the photocatalytic degradation of the PAH dyes--naphthalene and anthracene. anthracene 188-198 phenylalanine hydroxylase Homo sapiens 162-165 23837345-2 2013 Pyrene was continuously the most abundant PAH, whereas anthracene was the PAH with the lowest concentrations. anthracene 55-65 phenylalanine hydroxylase Homo sapiens 74-77 20973527-3 2010 We examine the effects of the PAH-substrate interaction on the oxidation of surface-adsorbed anthracene, pyrene, and benzo[a]pyrene by ozone (O(3)) using density functional theory. anthracene 93-103 phenylalanine hydroxylase Homo sapiens 30-33 21255289-2 2009 To evaluate the thermodynamic constraints on methanogenic PAH degradation we have estimated the Gibbs free energy values for naphthalene, phenanthrene, anthracene, pyrene and chrysene in the aqueous phase, and used these values to evaluate several possible routes whereby PAHs may be converted to methane. anthracene 152-162 phenylalanine hydroxylase Homo sapiens 58-61 20346485-11 2010 The anthracene/phenanthrene and benzo[a]anthracene/chrysene ratios in the winter were significantly lower than those in the summer, which indicate that there might be long-range transported PAH input to Guangzhou in the winter. anthracene 4-14 phenylalanine hydroxylase Homo sapiens 190-193 20346485-11 2010 The anthracene/phenanthrene and benzo[a]anthracene/chrysene ratios in the winter were significantly lower than those in the summer, which indicate that there might be long-range transported PAH input to Guangzhou in the winter. anthracene 40-50 phenylalanine hydroxylase Homo sapiens 190-193 19302510-5 2009 The median concentration of PAH ranged from 0.14 (lowest, anthracene) to 31.18 microg g(-1) [dibenz(a,h)anthracene] in kajal sample and from not detectable concentration (naphthalene) to 197.47 microg g(-1) of benzo(a)pyrene in surma sample. anthracene 58-68 phenylalanine hydroxylase Homo sapiens 28-31 17162569-2 2007 The degradation rates of PAH were in the order: acenaphthene > fluorene > phenanthrene > anthracene > pyrene. anthracene 98-108 phenylalanine hydroxylase Homo sapiens 25-28 17570467-5 2007 Two- and 3-ring PAHs (methylnaphthalene, fluorene, phenanthrene and anthracene) were the main compounds found in most sites, although total PAH concentrations showed relatively low levels compared with other human-impacted areas in Antarctica. anthracene 68-78 phenylalanine hydroxylase Homo sapiens 16-19 18688457-11 2008 The best reflection of the PAH losses was observed in the case of fluoranthene, anthracene and indeno[1,2,3-cd]pyrene. anthracene 80-90 phenylalanine hydroxylase Homo sapiens 27-30 16613835-6 2006 We exposed mouse (NMRI) E18 mandibular first and second molar explants to 7,12-dimethylbenz[a]anthracene (DMBA), a toxic PAH compound, in organ culture for 7 or 12 days. anthracene 94-104 phenylalanine hydroxylase Homo sapiens 121-124