PMID-sentid	Pub_year	Sent_text		comp_official_name	comp_offsetprotein_name	organism	prot_offset
30865563-5	2020	With the initial concentration of Cr(VI) increased from 10 to 50 mg L-1, the Cr(VI) removal efficiencies of Nano-FeS and CMC-FeS decreased.	Chromium	34-36	immunoglobulin kappa variable 1-16	Homo sapiens	68-71	
30865563-5	2020	With the initial concentration of Cr(VI) increased from 10 to 50 mg L-1, the Cr(VI) removal efficiencies of Nano-FeS and CMC-FeS decreased.	Chromium	77-79	immunoglobulin kappa variable 1-16	Homo sapiens	68-71	
29550888-2	2018	The planktonic community from a coastal site was exposed to a chromium increase of 80 mug L-1 for 72 h in laboratory conditions.	Chromium	62-70	immunoglobulin kappa variable 1-16	Homo sapiens	90-93	
30910194-4	2019	RESEARCH PROBLEM: In the case of cobalt and chromium, a blood level exceeding 7 mug L-1 indicates potential for local toxicity, and a failing implant.	Chromium	44-52	immunoglobulin kappa variable 1-16	Homo sapiens	84-87	
30684773-9	2019	Large-scale operation using 100 L of packed-bed reactor showed the breakthrough time of adsorption for mixed waste tea of 30 min in 100 mg L-1 Cr(VI) concentration.	Chromium	143-145	immunoglobulin kappa variable 1-16	Homo sapiens	139-142	
29414334-6	2018	For metals, Fe, Cr, and Rb were dominant in the raw leachate, detected at 7.55, 2.82, and 4.50 mg L-1, respectively.	Chromium	16-18	immunoglobulin kappa variable 1-16	Homo sapiens	98-101	
30963426-3	2019	It was also verified that the most favorable conditions for chromium removal were the following: pH 5.0, Cr(VI) concentration of 130 mg L-1, adsorbent mass of 5 mg, and Fe(II) content of 45% (w/w) in the CT-Fe beads.	Chromium	60-68	immunoglobulin kappa variable 1-16	Homo sapiens	136-139	
30262104-4	2019	This method resulted in detection limits of 0.85 ng L-1 for Cr(VI) and 1.82 ng L-1 for Cr(total), as well as enrichment factors around 77.	Chromium	60-62	immunoglobulin kappa variable 1-16	Homo sapiens	52-55	
30262104-4	2019	This method resulted in detection limits of 0.85 ng L-1 for Cr(VI) and 1.82 ng L-1 for Cr(total), as well as enrichment factors around 77.	Chromium	87-89	immunoglobulin kappa variable 1-16	Homo sapiens	79-82	
30101887-4	2018	The method detection limits measured at m/z 53 were 0.66 mug of Cr L-1 for Cr(III) and 0.74 mug L-1 for Cr(VI) with a sample injection volume of 20 muL under a no gas mode.	Chromium	64-66	immunoglobulin kappa variable 1-16	Homo sapiens	67-70	
30101887-4	2018	The method detection limits measured at m/z 53 were 0.66 mug of Cr L-1 for Cr(III) and 0.74 mug L-1 for Cr(VI) with a sample injection volume of 20 muL under a no gas mode.	Chromium	75-77	immunoglobulin kappa variable 1-16	Homo sapiens	67-70	
28762145-7	2017	A gradational variation in Cr accumulation was observed in the three villages from contaminated wastewater having the least contamination level (2.02-4.40 mg L-1), to soil (25.16-37.67 mg kg-1), and ultimately in the seasonal vegetable crops (156.67-248.33 mg kg-1) cultivated in the region, having the highest level of Cr contamination above the permissible limit.	Chromium	27-29	immunoglobulin kappa variable 1-16	Homo sapiens	158-161	
28192915-7	2017	The instrument is applicable for multielement analysis, and the LODs ranged from 0.16 to 11.65 mug L-1 for Zn, Pb, Ag, Cd, Au, Cu, Mn, Fe, Cr, and As.	Chromium	139-141	immunoglobulin kappa variable 1-16	Homo sapiens	99-102	
28111723-5	2017	We were able to reduce chromium concentration in the samples from 0.295 mg L-1 to a tolerable amount of 0.144 mg L-1.	Chromium	23-31	immunoglobulin kappa variable 1-16	Homo sapiens	75-78	
28111723-5	2017	We were able to reduce chromium concentration in the samples from 0.295 mg L-1 to a tolerable amount of 0.144 mg L-1.	Chromium	23-31	immunoglobulin kappa variable 1-16	Homo sapiens	113-116	
25268509-7	2014	Chromium in drinking water ranged from <0.5 to 90 mug L-1 in all samples but one (220 mug L-1), with a median concentration of 21.2 mug L-1.	Chromium	0-8	immunoglobulin kappa variable 1-16	Homo sapiens	57-60	
27638807-7	2016	At doses >=1 mg L-1, evolution of concentrations over time shows significant differences between these two metals: (i) chromium absorption from seawater is twice faster than lead; (ii) lead accumulates in considerable amount in sediments.	Chromium	122-130	immunoglobulin kappa variable 1-16	Homo sapiens	19-22	
27541153-5	2016	The average concentrations of Cr, Cu, Ni, Pb, and Zn in surface pore water were 18.8, 23.4, 12.0, 13.5, and 42.5 mug L-1, respectively.	Chromium	30-32	immunoglobulin kappa variable 1-16	Homo sapiens	117-120	
28167882-3	2016	The use of SWNTs has increased sensitivity for Cr(VI) detection in aqueous solutions, providing a detection limit of 0.8 mug L-1.	Chromium	47-49	immunoglobulin kappa variable 1-16	Homo sapiens	125-128	
25268509-7	2014	Chromium in drinking water ranged from <0.5 to 90 mug L-1 in all samples but one (220 mug L-1), with a median concentration of 21.2 mug L-1.	Chromium	0-8	immunoglobulin kappa variable 1-16	Homo sapiens	93-96	
25268509-7	2014	Chromium in drinking water ranged from <0.5 to 90 mug L-1 in all samples but one (220 mug L-1), with a median concentration of 21.2 mug L-1.	Chromium	0-8	immunoglobulin kappa variable 1-16	Homo sapiens	93-96	
25268509-8	2014	Chromium levels in blood (median 0.32 mug L-1, range <0.18-0.92 mug L-1) and hair (median 0.22 mug g-1, range 0.03-1.26 mug g-1) were found within "normal range" according to the literature.	Chromium	0-8	immunoglobulin kappa variable 1-16	Homo sapiens	42-45	
25268509-8	2014	Chromium levels in blood (median 0.32 mug L-1, range <0.18-0.92 mug L-1) and hair (median 0.22 mug g-1, range 0.03-1.26 mug g-1) were found within "normal range" according to the literature.	Chromium	0-8	immunoglobulin kappa variable 1-16	Homo sapiens	71-74	
12938382-4	2002	The linear range of this method was 0.08-0.40 mg.L-1 and the relative standard deviation was found to be 1.1% for Cr(VI) (11 replicates).	Chromium	114-116	immunoglobulin kappa variable 1-16	Homo sapiens	49-52	
20935379-5	2010	The removal efficiency of some variables was insufficient, leading to high final mean concentrations of metals [e.g. aluminium (0.29 mg L-1), chromium (0.02 mg L-1) and iron (1.1 mg L-1)] as well as nitrogen-ammonia (25.8 mg L-1) and total suspended solids (18 mg L-1) in the treated water.	Chromium	142-150	immunoglobulin kappa variable 1-16	Homo sapiens	160-163	
20935379-5	2010	The removal efficiency of some variables was insufficient, leading to high final mean concentrations of metals [e.g. aluminium (0.29 mg L-1), chromium (0.02 mg L-1) and iron (1.1 mg L-1)] as well as nitrogen-ammonia (25.8 mg L-1) and total suspended solids (18 mg L-1) in the treated water.	Chromium	142-150	immunoglobulin kappa variable 1-16	Homo sapiens	160-163	
20935379-5	2010	The removal efficiency of some variables was insufficient, leading to high final mean concentrations of metals [e.g. aluminium (0.29 mg L-1), chromium (0.02 mg L-1) and iron (1.1 mg L-1)] as well as nitrogen-ammonia (25.8 mg L-1) and total suspended solids (18 mg L-1) in the treated water.	Chromium	142-150	immunoglobulin kappa variable 1-16	Homo sapiens	160-163	
20935379-5	2010	The removal efficiency of some variables was insufficient, leading to high final mean concentrations of metals [e.g. aluminium (0.29 mg L-1), chromium (0.02 mg L-1) and iron (1.1 mg L-1)] as well as nitrogen-ammonia (25.8 mg L-1) and total suspended solids (18 mg L-1) in the treated water.	Chromium	142-150	immunoglobulin kappa variable 1-16	Homo sapiens	160-163	
25026425-2	1993	The results indicated that the direction of the CR of the whole lumbar spine (ie between L1 and S1) was significantly different between the flexed and extended lumbar spine position.	Chromium	48-50	immunoglobulin kappa variable 1-16	Homo sapiens	89-98