PMID-sentid	Pub_year	Sent_text		comp_official_name	comp_offsetprotein_name	organism	prot_offset
2335085-3	1990	Nickel contents in 8 different domestic tap waters and another underground water sample were also measured by plasma scan.	Nickel	0-6	nuclear RNA export factor 1	Homo sapiens	40-43	
18968797-9	2002	The method was applied for the determination of nickel in samples of tap and mineral water.	Nickel	48-54	nuclear RNA export factor 1	Homo sapiens	69-72	
9874038-0	1998	Nickel in tap water in Warsaw.	Nickel	0-6	nuclear RNA export factor 1	Homo sapiens	10-13	
2335085-4	1990	Nickel contents in the patient"s underground water were 9 times higher on average than those in domestic tap water.	Nickel	0-6	nuclear RNA export factor 1	Homo sapiens	105-108	
6851522-0	1983	Nickel in tap water.	Nickel	0-6	nuclear RNA export factor 1	Homo sapiens	10-13	
3987257-0	1985	Nickel in tap water.	Nickel	0-6	nuclear RNA export factor 1	Homo sapiens	10-13	
6851522-1	1983	Nickel analyses of tap water from several sources in Copenhagen gave up to 490 X 10(-6) g X 1(-1) in the first 250 ml portions.	Nickel	0-6	nuclear RNA export factor 1	Homo sapiens	19-22	
32064409-0	2020	Using Smartphone APP To Determine the CN- Concentration Quantitatively in Tap Water: Synthesis of the Naked-Eye Colorimetric Chemosensor for CN- and Ni2+ Based on Benzothiazole.	Nickel	149-153	nuclear RNA export factor 1	Homo sapiens	74-77	
26810082-7	2016	Significant reductions in concentrations of aluminium, cadmium, copper, lead and/or nickel were found in tap waters where households were successfully treating low-pH groundwaters, and similar adventitious results were found for arsenic and nickel where treatment was installed for iron and/or manganese removal, and successful treatment specifically to decrease tap water arsenic concentrations was observed at two properties where it was installed.	Nickel	84-90	nuclear RNA export factor 1	Homo sapiens	105-108	
19118932-1	2009	A natural experiment indicated that a link between the presence and concentration of four elements, copper, lead, nickel, and zinc in the influent to two wastewater reclamation plants to the presence and concentrations of the same four elements in the tap water of residential properties.	Nickel	114-120	nuclear RNA export factor 1	Homo sapiens	252-255	
22928956-8	2012	Bivariate analyses pointed to significantly increased nickel excretion with increasing age, ingestion of dietary supplements, drinking of stagnant tap water, and consumption of nickel-rich food.	Nickel	54-60	nuclear RNA export factor 1	Homo sapiens	147-150	
22285091-9	2012	Nickel exposure via drinking water was derived from databases on Ni tap water quality.	Nickel	0-6	nuclear RNA export factor 1	Homo sapiens	68-71	
19124200-0	2009	Octadecyl bonded silica membrane disk modified with Cyanex302 for separation and flame atomic absorption spectrometric determination of nickel from tap water and industrial effluent.	Nickel	136-142	nuclear RNA export factor 1	Homo sapiens	148-151	
19124200-4	2009	The method applied for detection of nickel in tap water and effluent sample had a relative standard deviation (R.S.D.)	Nickel	36-42	nuclear RNA export factor 1	Homo sapiens	46-49	
16724222-6	2006	The proposed methodology showed a high tolerance to the commonly encountered alkaline earth matrix elements in environmental waters, that is, calcium and magnesium, and was successfully applied for the determination of nickel in an NIST standard reference material (NIST 1640-Trace elements in natural water), household tap water of high hardness and local seawater.	Nickel	219-225	nuclear RNA export factor 1	Homo sapiens	320-323