PMID-sentid	Pub_year	Sent_text		comp_official_name	comp_offsetprotein_name	organism	prot_offset
24077263-4	2013	PAHs are reactive towards a number of atmospheric oxidants, most notably the hydroxyl radical, ozone, the nitrate radical (NO3) and nitrogen dioxide.	Polycyclic Aromatic Hydrocarbons	0-4	NBL1, DAN family BMP antagonist	Homo sapiens	123-126	
9148793-5	1997	In addition, OH, NO3, and O3 are shown to play a central role in the formation and fate of airborne toxic chemicals, mutagenic polycyclic aromatic hydrocarbons, and fine particles.	Polycyclic Aromatic Hydrocarbons	127-159	NBL1, DAN family BMP antagonist	Homo sapiens	17-20	
28675851-2	2017	Sequential addition of co-substrate (acetate) and electron acceptor (NO3-) in a two-phase treatment was capable of effectively removing polycyclic aromatic hydrocarbons (PAHs) in river sediment.	Polycyclic Aromatic Hydrocarbons	136-168	NBL1, DAN family BMP antagonist	Homo sapiens	69-72	
28675851-2	2017	Sequential addition of co-substrate (acetate) and electron acceptor (NO3-) in a two-phase treatment was capable of effectively removing polycyclic aromatic hydrocarbons (PAHs) in river sediment.	Polycyclic Aromatic Hydrocarbons	170-174	NBL1, DAN family BMP antagonist	Homo sapiens	69-72	
25329713-3	2014	In previous studies, these two products were observed in the gas-phase reaction between N2O5/NO3/NO2 and their parent polycyclic aromatic hydrocarbons (PAHs), while the heterogeneous reaction generated other nitro-PAH isomers (1, 3, 7, 8-NFL and 1-NPY) (Atkinson et al.	Polycyclic Aromatic Hydrocarbons	118-150	NBL1, DAN family BMP antagonist	Homo sapiens	93-96	
25329713-3	2014	In previous studies, these two products were observed in the gas-phase reaction between N2O5/NO3/NO2 and their parent polycyclic aromatic hydrocarbons (PAHs), while the heterogeneous reaction generated other nitro-PAH isomers (1, 3, 7, 8-NFL and 1-NPY) (Atkinson et al.	Polycyclic Aromatic Hydrocarbons	152-156	NBL1, DAN family BMP antagonist	Homo sapiens	93-96	
25329713-3	2014	In previous studies, these two products were observed in the gas-phase reaction between N2O5/NO3/NO2 and their parent polycyclic aromatic hydrocarbons (PAHs), while the heterogeneous reaction generated other nitro-PAH isomers (1, 3, 7, 8-NFL and 1-NPY) (Atkinson et al.	Polycyclic Aromatic Hydrocarbons	152-155	NBL1, DAN family BMP antagonist	Homo sapiens	93-96	
22747347-0	2012	Kinetic studies of heterogeneous reactions of polycyclic aromatic hydrocarbon aerosols with NO3 radicals.	Polycyclic Aromatic Hydrocarbons	46-77	NBL1, DAN family BMP antagonist	Homo sapiens	92-95	
23865889-0	2013	Formation of nitro-PAHs from the heterogeneous reaction of ambient particle-bound PAHs with N2O5/NO3/NO2.	Polycyclic Aromatic Hydrocarbons	19-23	NBL1, DAN family BMP antagonist	Homo sapiens	97-100	
18311955-0	2008	Reactive uptake of NO3, N2O5, NO2, HNO3, and O3 on three types of polycyclic aromatic hydrocarbon surfaces.	Polycyclic Aromatic Hydrocarbons	66-97	NBL1, DAN family BMP antagonist	Homo sapiens	19-22	
18311955-1	2008	We investigated the reactive uptake of NO3, N2O5, NO2, HNO3, and O3 on three types of solid polycyclic aromatic hydrocarbons (PAHs) using a coated wall flow tube reactor coupled to a chemical ionization mass spectrometer.	Polycyclic Aromatic Hydrocarbons	92-124	NBL1, DAN family BMP antagonist	Homo sapiens	39-42	
18311955-1	2008	We investigated the reactive uptake of NO3, N2O5, NO2, HNO3, and O3 on three types of solid polycyclic aromatic hydrocarbons (PAHs) using a coated wall flow tube reactor coupled to a chemical ionization mass spectrometer.	Polycyclic Aromatic Hydrocarbons	126-130	NBL1, DAN family BMP antagonist	Homo sapiens	39-42	
18311955-3	2008	Reaction of NO3 radicals with all three PAHs was observed to be very fast with the reactive uptake coefficient, gamma, ranging from 0.059 (+0.11/-0.049) for benz[a]anthracene at 273 K to 0.79 (+0.21/-0.67) for pyrene at room temperature.	Polycyclic Aromatic Hydrocarbons	40-44	NBL1, DAN family BMP antagonist	Homo sapiens	12-15	
18311955-6	2008	Reaction of NO3 on all three PAH surfaces slowed down at 263 K after long NO3 exposure times, suggesting that the PAH molecules were reactants.	Polycyclic Aromatic Hydrocarbons	29-32	NBL1, DAN family BMP antagonist	Homo sapiens	12-15	
18311955-6	2008	Reaction of NO3 on all three PAH surfaces slowed down at 263 K after long NO3 exposure times, suggesting that the PAH molecules were reactants.	Polycyclic Aromatic Hydrocarbons	29-32	NBL1, DAN family BMP antagonist	Homo sapiens	74-77	
18311955-6	2008	Reaction of NO3 on all three PAH surfaces slowed down at 263 K after long NO3 exposure times, suggesting that the PAH molecules were reactants.	Polycyclic Aromatic Hydrocarbons	114-117	NBL1, DAN family BMP antagonist	Homo sapiens	12-15	
18311955-8	2008	Our results show that under certain atmospheric conditions, NO3 radicals can be a more important sink for PAHs than NO2, HNO3, N2O5, or O3 and impact tropospheric lifetimes of surface-bound PAHs.	Polycyclic Aromatic Hydrocarbons	106-110	NBL1, DAN family BMP antagonist	Homo sapiens	60-63	
18311955-8	2008	Our results show that under certain atmospheric conditions, NO3 radicals can be a more important sink for PAHs than NO2, HNO3, N2O5, or O3 and impact tropospheric lifetimes of surface-bound PAHs.	Polycyclic Aromatic Hydrocarbons	190-194	NBL1, DAN family BMP antagonist	Homo sapiens	60-63