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	
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	
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	
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	
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	
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	
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	
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	
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	
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