PMID-sentid	Pub_year	Sent_text		comp_official_name	comp_offsetprotein_name	organism	prot_offset
33257072-14	2021	To conclude, soil pH was a key factor affecting the contribution of ammonia oxidizers to nitrification-related N2O emissions.	Ammonia	68-75	phenylalanine hydroxylase	Homo sapiens	18-20	
32917041-5	2020	At the same pH value, the absolute values of the zeta potentials with different pH agents were: ethanolamine < ammonia < morpholine.	Ammonia	111-118	phenylalanine hydroxylase	Homo sapiens	80-82	
33861488-7	2021	The reaction involves hydrolysis of urea by urease and production of ammonia which increases the pH.	Ammonia	69-76	phenylalanine hydroxylase	Homo sapiens	97-99	
34403844-2	2021	The ammonia removal in the stripping process depends on the pH, temperature, and air supply, and in general, 10.5, 60  C, 5 L/min or more are recommended as near-optimal.	Ammonia	4-11	phenylalanine hydroxylase	Homo sapiens	60-62	
34364243-5	2021	Based on the results of this study, it was observed that the effectiveness of ammonia removal depends on the pH and air flow rate.	Ammonia	78-85	phenylalanine hydroxylase	Homo sapiens	109-111	
34464086-4	2021	The baseline pH adjustment was successfully done with an ammonia permeation device without solution mixing, which may cause analyte dilution, dispersion, and mixing noise.	Ammonia	57-64	phenylalanine hydroxylase	Homo sapiens	13-15	
34464086-5	2021	After pH adjustment, the pH response was universal to the equivalent of introduced analyte acids because the pH response was obtained by the titration of the permeant ammonia by the analytes.	Ammonia	167-174	phenylalanine hydroxylase	Homo sapiens	6-8	
34464086-5	2021	After pH adjustment, the pH response was universal to the equivalent of introduced analyte acids because the pH response was obtained by the titration of the permeant ammonia by the analytes.	Ammonia	167-174	phenylalanine hydroxylase	Homo sapiens	25-27	
34464086-5	2021	After pH adjustment, the pH response was universal to the equivalent of introduced analyte acids because the pH response was obtained by the titration of the permeant ammonia by the analytes.	Ammonia	167-174	phenylalanine hydroxylase	Homo sapiens	109-111	
16584268-9	2006	X-ray photoelectron spectroscopy revealed that, in this case, excess negative charges generated on the manganese oxide layers upon reduction can be balanced by the protons being released from the -NH3(+) Cl- sites in the interlayer PAH; the Cl- anions becoming unnecessary are inevitably excluded from the interlayer, and vice versa upon oxidation.	Ammonia	197-200	phenylalanine hydroxylase	Homo sapiens	232-235	
34403844-9	2021	The electric field improved the ammonia removal more as the pH, temperature, and air supply conditions were far from optimal.	Ammonia	32-39	phenylalanine hydroxylase	Homo sapiens	60-62	
34260224-2	2021	In this study, we present a calculation method to more intuitively quantify the relationship between aerosol pH and its influencing factors, including gaseous NH3 concentration, particle properties, relative humidity, temperature, and nonvolatile cations, based on the NHx phase-partitioning equilibrium used in the E-AIM thermodynamic model.	Ammonia	159-162	phenylalanine hydroxylase	Homo sapiens	109-111	
35351554-3	2022	The results showed that thermophilic denitrification could adapt to pH 5-11, but suffered from obvious nitrite and ammonia accumulation at pH 3.	Ammonia	115-122	phenylalanine hydroxylase	Homo sapiens	139-141	
35351554-5	2022	Besides, the potential selecting advantage of nitrate reducing bacteria over nitrite reducing bacteria and the enrichment of dissimilatory nitrate reduction to ammonium (DNRA) bacteria could be responsible for the nitrite and ammonia accumulation at pH 3.	Ammonia	226-233	phenylalanine hydroxylase	Homo sapiens	250-252