PMID-sentid	Pub_year	Sent_text		comp_official_name	comp_offsetprotein_name	organism	prot_offset
32613501-10	2020	The greater n-pi EDA and complex efficiency of Cu with NOR resulted in the superior performance of Cu/SBA-15.	Copper	99-101	ectodysplasin A	Homo sapiens	17-20	
33304960-4	2020	On the other hand, the energy decomposition analysis based on absolutely localized molecular orbital (ALMO-EDA) describes the physical contributions that govern the interaction between ionic liquid and the copper nanoparticles.	Copper	206-212	ectodysplasin A	Homo sapiens	107-110	
20608701-5	2010	EDA-SAMMS and AC-CH(2)-EDA demonstrated rapid Cu(2+) sorption kinetics (minutes) and good sorption capacities (26 and 17 mg Cu/g sorbent, respectively) in seawater, whereas Phen-FMC had excellent selectivity for Cu(2+) over other metal ions (e.g., Ca(2+), Fe(2+), Ni(2+), and Zn(2+)) and was able to achieve Cu below the EPA recommended levels for river and sea waters.	Copper	46-48	ectodysplasin A	Homo sapiens	0-3	
29448754-2	2018	PAT-adsorbent and EDA-adsorbent were used and compared for adsorption of copper ions in a batch system due to the existence of amino group (-NH2) both on thioureido group and amine functional group.	Copper	73-79	ectodysplasin A	Homo sapiens	18-21	
25385159-1	2015	The metal-ligand, M-L, bonding situation in cyclic trinuclear complexes, CTCs, of copper(I), silver(I), and gold(I) was investigated in terms of the energy decomposition analysis (EDA-NOCV) and natural bond orbitals (NBOs).	Copper	82-88	ectodysplasin A	Homo sapiens	180-183	
25385159-3	2015	The EDA-NOCV results show that the M-L bonding is stronger in gold(I) than in copper(I) or silver(I) complexes.	Copper	78-84	ectodysplasin A	Homo sapiens	4-7	
25109645-5	2014	The order of increasing metal capacity for copper ions using magnetic nano-adsorbents was Fe3O4-SiO2-1,2-EDA < Fe3O4-SiO2-1,5-PDA < Fe3O4-SiO2-1,8-ODA at 5 s equilibrium time.	Copper	43-49	ectodysplasin A	Homo sapiens	105-108	
20608701-5	2010	EDA-SAMMS and AC-CH(2)-EDA demonstrated rapid Cu(2+) sorption kinetics (minutes) and good sorption capacities (26 and 17 mg Cu/g sorbent, respectively) in seawater, whereas Phen-FMC had excellent selectivity for Cu(2+) over other metal ions (e.g., Ca(2+), Fe(2+), Ni(2+), and Zn(2+)) and was able to achieve Cu below the EPA recommended levels for river and sea waters.	Copper	46-48	ectodysplasin A	Homo sapiens	23-26	
20608701-5	2010	EDA-SAMMS and AC-CH(2)-EDA demonstrated rapid Cu(2+) sorption kinetics (minutes) and good sorption capacities (26 and 17 mg Cu/g sorbent, respectively) in seawater, whereas Phen-FMC had excellent selectivity for Cu(2+) over other metal ions (e.g., Ca(2+), Fe(2+), Ni(2+), and Zn(2+)) and was able to achieve Cu below the EPA recommended levels for river and sea waters.	Copper	124-126	ectodysplasin A	Homo sapiens	0-3	
20608701-5	2010	EDA-SAMMS and AC-CH(2)-EDA demonstrated rapid Cu(2+) sorption kinetics (minutes) and good sorption capacities (26 and 17 mg Cu/g sorbent, respectively) in seawater, whereas Phen-FMC had excellent selectivity for Cu(2+) over other metal ions (e.g., Ca(2+), Fe(2+), Ni(2+), and Zn(2+)) and was able to achieve Cu below the EPA recommended levels for river and sea waters.	Copper	124-126	ectodysplasin A	Homo sapiens	23-26