PMID-sentid	Pub_year	Sent_text		comp_official_name	comp_offsetprotein_name	organism	prot_offset
31158641-3	2019	In the reaction lacking PDS, phenol in aqueous solution was removed from the initial 10 mg L-1 to 4.75 mg L-1 (by 52.5%), whereas the addition of 1770 mg L-1 PDS increased the overall removal to 78.7%, as indicated by a one-fold increase in the pseudo-first-order kinetic constant.	Phenol	29-35	immunoglobulin kappa variable 1-16	Homo sapiens	91-94	
31158641-3	2019	In the reaction lacking PDS, phenol in aqueous solution was removed from the initial 10 mg L-1 to 4.75 mg L-1 (by 52.5%), whereas the addition of 1770 mg L-1 PDS increased the overall removal to 78.7%, as indicated by a one-fold increase in the pseudo-first-order kinetic constant.	Phenol	29-35	immunoglobulin kappa variable 1-16	Homo sapiens	106-109	
31158641-3	2019	In the reaction lacking PDS, phenol in aqueous solution was removed from the initial 10 mg L-1 to 4.75 mg L-1 (by 52.5%), whereas the addition of 1770 mg L-1 PDS increased the overall removal to 78.7%, as indicated by a one-fold increase in the pseudo-first-order kinetic constant.	Phenol	29-35	immunoglobulin kappa variable 1-16	Homo sapiens	106-109	
30620558-5	2019	It was seen that the activity reached 400 U L-1 when phenol was used as an inducer.	Phenol	53-59	immunoglobulin kappa variable 1-16	Homo sapiens	44-47	
29992415-7	2018	In addition, 95% of phenol removal was attained within 96 h (although 85% was removed after 4 h), thus reaching below the maximum authorized concentration allowed by Quebec"s discharge criteria (0.05 mg L-1).	Phenol	20-26	immunoglobulin kappa variable 1-16	Homo sapiens	203-206	
29998704-7	2018	When the concentration of phenol was low (50-100 mg L-1), there was little effect on ANAMMOX-MFC denitrification electrogenesis performance.	Phenol	26-32	immunoglobulin kappa variable 1-16	Homo sapiens	52-55	
29998704-8	2018	When the concentration of phenol exceeded 200 mg L-1, ANAMMOX-MFC denitrification performance was gradually inhibited.	Phenol	26-32	immunoglobulin kappa variable 1-16	Homo sapiens	49-52	
28165517-6	2017	Interestingly, phenol in aqueous solution (10 mg L-1) can also be completely degraded within 60 min, even under the direct exposure of sunlight irradiation.	Phenol	15-21	immunoglobulin kappa variable 1-16	Homo sapiens	49-52	
32086677-10	2020	As a result of our study, total phenol content and the free radical scavenging activity increased with 100 mg l-1 of salicylic acid.	Phenol	32-38	immunoglobulin kappa variable 1-16	Homo sapiens	110-113	
31194060-5	2019	Maximum adsorption efficiency was calculated 98.5% at optimized parameters: concentration of phenol 25 mg L-1, Iron impregnated activated carbon dose 75 mg, pH 7.0 and agitation time 90 min.	Phenol	93-99	immunoglobulin kappa variable 1-16	Homo sapiens	106-109	
30245272-1	2018	In this work, the capability of the ionic liquid, 1-ethyl-3-methylimidazolium bis(fluorosulfonyl)imide, [C2mim]FSI, to extract o-cresol, 2-chlorophenol, resorcinol and phenol from water, reaching the legal limit of 1 mg L-1 was analyzed.	Phenol	145-151	immunoglobulin kappa variable 1-16	Homo sapiens	220-223	
29998686-2	2018	The results showed that when the phenol concentration was no higher than 50 mg L-1, the removal efficiencies of COD and PO43--P were above 85%.	Phenol	33-39	immunoglobulin kappa variable 1-16	Homo sapiens	79-82	
29998686-4	2018	However, when phenol was higher than 100 mg L-1, phosphorus removal performance of the reactor decreased drastically.	Phenol	14-20	immunoglobulin kappa variable 1-16	Homo sapiens	44-47	
29998686-5	2018	When phenol concentration was 200 mg L-1, the system lost phosphorus removal performance after only 22 cycles.	Phenol	5-11	immunoglobulin kappa variable 1-16	Homo sapiens	37-40	
29998686-9	2018	In addition, the limited sludge bulking disappeared gradually owing to acclimation of the sludge to toxicity with a low phenol concentration (<= 50 mg L-1).	Phenol	120-126	immunoglobulin kappa variable 1-16	Homo sapiens	154-157	
28946001-1	2017	Phenol-production wastewater is difficult to treat biologically by aerobic processes to meet the effluent standard COD of 120 mg L-1 because it contains several highly refractory aromatic pollutants, particularly dimethyl phenyl carbinol.	Phenol	0-6	immunoglobulin kappa variable 1-16	Homo sapiens	129-132	
28944420-3	2017	In this study, the anaerobic digestion of phenol (500 mg L-1) and quinoline (50 mg L-1) was investigated using an anaerobic baffled ceramic membrane bioreactor (ABCMBR).	Phenol	42-48	immunoglobulin kappa variable 1-16	Homo sapiens	57-60	
11005921-11	2000	In order to maximize the flow through the reactor, the liquid flow was increased stepwise while the feed concentrations were reduced correspondingly, keeping the volumetric conversion rates of phenol (0.24 g L(-1) h(-1)) and benzoic acid (0.17 g L(-1) h(-1)) constant.	Phenol	193-199	immunoglobulin kappa variable 1-16	Homo sapiens	208-213	
31274385-9	2021	A considerable amount of phenol degradation was observed even at low catalyst dose (i.e. 0.5 g L-1).	Phenol	25-31	immunoglobulin kappa variable 1-16	Homo sapiens	95-98