PMID-sentid	Pub_year	Sent_text		comp_official_name	comp_offsetprotein_name	organism	prot_offset
22872375-2	2012	Significant highest metal concentration in water (0.45 mg L(-1) Cd and 3.94 mg L(-1) Pb) and sediment (2.83 mg kg(-1) Cd and 6.61 mg kg(-1) Pb) were found at the mouth of the Tigre River, where the fishing town of El Moron is located.	Metals	20-25	immunoglobulin kappa variable 1-16	Homo sapiens	79-87	
27619373-2	2016	Total heavy metal concentrations ranged from 34.88 to 4201.23 mug L-1 in water (as the sum of the water dissolved phase and suspended particulate matter) and from 42.81 to 1686.84 mg kg-1 in sediment samples.	Metals	12-17	immunoglobulin kappa variable 1-16	Homo sapiens	66-69	
26687098-3	2016	L1 and D1 possess efficient Cu(2+) cation ON-OFF selective signaling behavior based on ligand-to-metal binding mechanism at physiological pH condition.	Metals	97-102	immunoglobulin kappa variable 1-16	Homo sapiens	0-9	
24362996-2	2013	The metal ions on Chromosorb-105 resin column were eluted with 3.0 mL of 2.0 mol L-1 HNO3 and determined by microsample injection system coupled flame atomic spectrometry (MIS-FAAS) using 75.0 microL of sample solution for single element determination.	Metals	4-9	immunoglobulin kappa variable 1-16	Homo sapiens	81-84	
23494165-7	2013	L 1 exhibited high selectivity and sensitivity towards Cu(2+) in both the medium over other common metal ions like Ni(2+), Co(2+), Mn(2+), Mg(2+), Zn(2+), Pb(2+) and Hg(2+).	Metals	99-104	immunoglobulin kappa variable 1-16	Homo sapiens	0-3	
30303004-4	2018	Due to the fact that about 58.16% of the Cu(I)/Cu(II) is occupied in molecular structure and most of the metal active sites are fully utilized, this ICPQS can accelerate the photocatalytic degradation of methylene blue (MB) (K = 2.5 mg L-1 min-1 at pH 3) and organic compounds in coking wastewater and biotreated coking wastewater.	Metals	105-110	immunoglobulin kappa variable 1-16	Homo sapiens	236-245	
15252572-10	2004	Moreover, L(1) is able to electrochemically and selectively sense Cu(2+) in the presence of a large excess of the other transition metal cations studied.	Metals	131-136	immunoglobulin kappa variable 1-16	Homo sapiens	10-14	
31009815-6	2019	Metal(loid) leaching from the bauxite residue, examined using ICP-OES, indicated that aluminium and iron were the dominant metals present in the treated effluent, both of which were above the EPA parametric values (0.2 mg L-1 for both Al and Fe) for drinking water.	Metals	0-5	immunoglobulin kappa variable 1-16	Homo sapiens	222-225	
30218331-3	2018	Results indicated that Zn was the most abundant metal with a concentration of 16.92 mug L-1 in fall and 19.91 mug L-1 in winter and flux of 4.71 mg m-2 in fall, while Cd was the least with a monthly mean concentration of 0.02-0.37 mug L-1.	Metals	48-53	immunoglobulin kappa variable 1-16	Homo sapiens	88-91	
28971675-6	2017	In the end, after one filtration process, the heavy metal concentration can be significantly decreased from 1.0 mg L-1 to below the drinking water standard recommended by the World Health Organization (e.g., less than 0.01 mg L-1 for Pb).	Metals	52-57	immunoglobulin kappa variable 1-16	Homo sapiens	115-118	
28971675-6	2017	In the end, after one filtration process, the heavy metal concentration can be significantly decreased from 1.0 mg L-1 to below the drinking water standard recommended by the World Health Organization (e.g., less than 0.01 mg L-1 for Pb).	Metals	52-57	immunoglobulin kappa variable 1-16	Homo sapiens	226-229