PMID-sentid	Pub_year	Sent_text		comp_official_name	comp_offsetprotein_name	organism	prot_offset
33940423-7	2021	It is found that pH plays a significant role in the reaction, and ammonium sulfate has significant impacts on the enhancement of aqueous phase sulfate production through regulating the pH of solution.	Sulfates	75-82	phenylalanine hydroxylase	Homo sapiens	185-187	
33934496-0	2021	Influences of pH and substrate supply on the ratio of iron to sulfate reduction.	Sulfates	62-69	phenylalanine hydroxylase	Homo sapiens	14-16	
33934496-6	2021	In acidic reactors (pH 6.0 media), the ratio of iron to sulfate reduction decreased from 3:1 to 2:1 as acetate supply increased (0-1 mM).	Sulfates	56-63	phenylalanine hydroxylase	Homo sapiens	20-22	
33934496-9	2021	Thus, the influence of sulfate supply on iron reduction extent also depended on pH and suggests that iron reduction grows more dependent on sulfate reduction as pH increases.	Sulfates	23-30	phenylalanine hydroxylase	Homo sapiens	80-82	
33934496-9	2021	Thus, the influence of sulfate supply on iron reduction extent also depended on pH and suggests that iron reduction grows more dependent on sulfate reduction as pH increases.	Sulfates	23-30	phenylalanine hydroxylase	Homo sapiens	161-163	
33934496-9	2021	Thus, the influence of sulfate supply on iron reduction extent also depended on pH and suggests that iron reduction grows more dependent on sulfate reduction as pH increases.	Sulfates	140-147	phenylalanine hydroxylase	Homo sapiens	161-163	
33934496-10	2021	Our results compare well to trends in groundwater geochemistry and provide further evidence that pH is a major control on iron and sulfate reduction in systems with crystalline (oxyhydr)oxides.	Sulfates	131-138	phenylalanine hydroxylase	Homo sapiens	97-99	
31655738-2	2019	In cases where zero-valent (elemental) sulfur, sulfate and other oxidized forms are used as electron acceptor in (primarily) anaerobic microbial metabolisms, the end product is hydrogen sulfide (HS- or H2S, dependent on pH).	Sulfates	47-54	phenylalanine hydroxylase	Homo sapiens	220-222	
31655738-4	2019	This review outlines the background and current status of the biodiversity and metabolisms of sulfate- and sulfur-reducing prokaryotes that are metabolically active in low pH environments, and describes the developing technologies in which they are being used to remediate acidic waste waters (which are often metal-contaminated) and to recover metal resources.	Sulfates	94-101	phenylalanine hydroxylase	Homo sapiens	172-174	
24171660-7	2013	The composition of PAH/CD-S sprayed films determined by X-ray photoelectron spectroscopy is independent of the spraying rate ratio of the two constituents and corresponds to one allylamine for one sulfate group.	Sulfates	197-204	phenylalanine hydroxylase	Homo sapiens	19-22	
17162569-4	2007	Comparison of the PAH degradation rates under three reducing conditions showed the following order: sulfate-reducing conditions > methanogenic conditions > nitrate-reducing conditions.	Sulfates	100-107	phenylalanine hydroxylase	Homo sapiens	18-21	
17162569-5	2007	The addition of electron donors (acetate, lactate and pyruvate) enhanced PAH degradation under methanogenic and sulfate-reducing conditions.	Sulfates	112-119	phenylalanine hydroxylase	Homo sapiens	73-76	
17162569-8	2007	Our results show that sulfate-reducing bacteria, methanogen and eubacteria are involved in the degradation of PAH; sulfate-reducing bacteria constitute a major microbial component in PAH degradation.	Sulfates	22-29	phenylalanine hydroxylase	Homo sapiens	110-113	
17162569-8	2007	Our results show that sulfate-reducing bacteria, methanogen and eubacteria are involved in the degradation of PAH; sulfate-reducing bacteria constitute a major microbial component in PAH degradation.	Sulfates	22-29	phenylalanine hydroxylase	Homo sapiens	183-186	
17162569-8	2007	Our results show that sulfate-reducing bacteria, methanogen and eubacteria are involved in the degradation of PAH; sulfate-reducing bacteria constitute a major microbial component in PAH degradation.	Sulfates	115-122	phenylalanine hydroxylase	Homo sapiens	110-113	
17162569-8	2007	Our results show that sulfate-reducing bacteria, methanogen and eubacteria are involved in the degradation of PAH; sulfate-reducing bacteria constitute a major microbial component in PAH degradation.	Sulfates	115-122	phenylalanine hydroxylase	Homo sapiens	183-186	
31655738-0	2019	Dissimilatory reduction of sulfate and zero-valent sulfur at low pH and its significance for bioremediation and metal recovery.	Sulfates	27-34	phenylalanine hydroxylase	Homo sapiens	65-67	
16535261-2	1996	Sulfate reduction was necessary for PAH oxidation.	Sulfates	0-7	phenylalanine hydroxylase	Homo sapiens	36-39	
16535261-3	1996	These results suggest that the self-purification capacity of PAH-contaminated sulfate-reducing environments may be greater than previously recognized.	Sulfates	78-85	phenylalanine hydroxylase	Homo sapiens	61-64	
8305846-3	1993	There is a partially overlapping substrate specificity between the PAH, dicarboxylate, and sulfate transport systems but also between the PAH and organic cation transport system.	Sulfates	91-98	phenylalanine hydroxylase	Homo sapiens	67-70	
8305846-3	1993	There is a partially overlapping substrate specificity between the PAH, dicarboxylate, and sulfate transport systems but also between the PAH and organic cation transport system.	Sulfates	91-98	phenylalanine hydroxylase	Homo sapiens	138-141