| نویسندگان | حیدر رئیسی,افسانه قهاری,سجاد اخضری |
| نشریه | Npj clean water |
| شماره صفحات | 1-15 |
| شماره سریال | ۷ |
| شماره مجلد | ۳۱ |
| نوع مقاله | Full Paper |
| تاریخ انتشار | ۲۰۲۴ |
| نوع نشریه | چاپی |
| کشور محل چاپ | ایران |
| نمایه نشریه | ISI،JCR،Scopus |
چکیده مقاله
Macrolide antibiotics, including erythromycin, clarithromycin, and azithromycin, are frequently
misused for human treatment globally. Therefore, they were considered high-risk substances on the
Union-wide monitoring Watch list under Regulation 2018/840/EU. The present work investigates the
adsorption behavior of the pharmaceutical pollutants on the 1,3,5-tris (4-aminophenyl) benzene/2,5
dimethoxyterephthalaldehyde (TAPB-DMTP) covalent organic frameworks (COFs). In this study, we
employ molecular dynamics simulations and well-tempered metadynamics to evaluate the adsorption
affinity of pristine covalent organic frameworks and their functionalized form (F-COFs) for the removal
of four distinct pharmaceutical pollutant molecules (PPMs): erythromycin (EMC), dexamethasone
(DEG), azithromycin (AZM), and clarithromycin (CMC). We utilized MD simulations to examine the
impact of two different temperatures (298 and 310 K) on enhancing the adsorption of the
pharmaceutical contaminants from wastewater by COFs/F-COFs. To evaluate this process, several
descriptors are calculated from the simulation trajectories, including interaction energies, root-meansquare deviation, radial distribution function, solvent-accessible surface area, mean square
displacement, and the number of hydrogen bonds (HB). It is determined that HB and X–H⋯π (X = C, N,
O; π = aromatic system) interactions are the most critical factors contributing to system stability. In
addition, it is shown that COFs with a pore-based structure have a higher capacity for removing
pollutants. The free energy landscapes confirm that the global minimum is typically associated with the
formation of hydrogen bonds. At 298 K, their global minima are DEG/F-COFs = −665.81, AZM/FCOFs = −638.53, EMC/F-COFs = −566.31, and CMC/F-COFs = −326.75 KJ mol−1
.
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