PMID-sentid	Pub_year	Sent_text		comp_official_name	comp_offsetprotein_name	organism	prot_offset
21707270-7	2011	Atrazine was the predominant triazine, detectable in many spring water locations, tap and bottled water, ranging (mean) from 0-57 (9), 0-44 (4), and 0-4 (1) ng l(-1), respectively.	Atrazine	0-8	nuclear RNA export factor 1	Homo sapiens	82-85	
24246238-10	2014	Urinary metabolites of both atrazine and dealkylated triazine were correlated with tap water consumption (OR=2.94, 1.09-7.90, and OR=1.82, 1.10-3.03, respectively); hydroxylated triazine metabolites were correlated with fish intake (OR=1.48, 1.09-1.99).	Atrazine	28-36	nuclear RNA export factor 1	Homo sapiens	83-86	
22000761-8	2011	Estimated "dose" of atrazine and chlorotriazine from tap water was inversely related to mean mid-luteal estradiol metabolite.	Atrazine	20-28	nuclear RNA export factor 1	Homo sapiens	53-56	
32217410-0	2020	A nationwide study of the occurrence and distribution of atrazine and its degradates in tap water and groundwater in China: Assessment of human exposure potential.	Atrazine	57-65	nuclear RNA export factor 1	Homo sapiens	88-91	
32217410-5	2020	The predominant compounds of ATZs in tap water were ATZ and DEA, with a detection frequency of 99.5% and 98.0%, respectively, followed by ATZ-OH (87.3%), DACT (84.0%), and DIA (78.1%).	Atrazine	29-32	nuclear RNA export factor 1	Homo sapiens	37-40