Tengda Ding*, Zhangming Hou, Hongfeng Zhou and Ling Liu,
{"title":"微塑料改变典型药物在水溶液中的分布和毒性:机理和理论计算","authors":"Tengda Ding*, Zhangming Hou, Hongfeng Zhou and Ling Liu, ","doi":"10.1021/acsestwater.5c00636","DOIUrl":null,"url":null,"abstract":"<p >The aquatic risks associated with various pharmaceuticals can be significantly influenced by the ubiquitous presence of microplastics (MPs), leading to unforeseen environmental effects. Uncovering the interactions between MPs and pharmaceuticals with diverse functional groups is of crucial importance for accurate risk assessment. Here, the sorption behaviors and underlying mechanisms by which polystyrene (PS) MPs interact with pharmaceuticals having different functional groups were explored through experimental methods, site energy distribution theory, and density functional theory (DFT) calculations. Results indicated that PS MPs exhibited a notable sorption capacity for pharmaceuticals, with the order of sorption being naproxen (NAP), bezafibrate (BZF), norfloxacin (NOR), ibuprofen (IBU), sulfamethoxazole (SMX), and carbamazepine (CAB). A deeper analysis revealed that multiple factors, including hydrophobicity, electrostatic repulsion, π–π interactions, and hydrogen bonding, regulate the sorption process. Furthermore, the Dubinin–Astakhov (DA) model was employed to calculate the energy distribution. The adsorption affinity (<i>E</i><sub>m</sub> = 2.88–8.36 kJ/mol) and energy heterogeneity (σ<sub>e</sub>* = 1.59–2.25) of PS MPs for different pharmaceuticals followed the order SMX > NOR > NAP > CAB > IBU > BZF. DFT calculations confirmed that the formation of n−π bonds between PS MPs and pharmaceuticals was also a primary sorption mechanism. The different sorption mechanisms of PS MPs for various pharmaceuticals can eventually alter their toxicity, such as increased toxicity of pharmaceuticals with carboxyl groups. Overall, this study offers a more comprehensive understanding of the interactions between MPs and pharmaceuticals, which can contribute significantly to the risk assessment of pharmaceuticals in the presence of MPs.</p>","PeriodicalId":93847,"journal":{"name":"ACS ES&T water","volume":"5 9","pages":"5605–5613"},"PeriodicalIF":4.3000,"publicationDate":"2025-08-06","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"","citationCount":"0","resultStr":"{\"title\":\"Microplastics Alter the Distribution and Toxic Potential of Typical Pharmaceuticals in Aqueous Solutions: Mechanisms and Theory Calculations\",\"authors\":\"Tengda Ding*, Zhangming Hou, Hongfeng Zhou and Ling Liu, \",\"doi\":\"10.1021/acsestwater.5c00636\",\"DOIUrl\":null,\"url\":null,\"abstract\":\"<p >The aquatic risks associated with various pharmaceuticals can be significantly influenced by the ubiquitous presence of microplastics (MPs), leading to unforeseen environmental effects. Uncovering the interactions between MPs and pharmaceuticals with diverse functional groups is of crucial importance for accurate risk assessment. Here, the sorption behaviors and underlying mechanisms by which polystyrene (PS) MPs interact with pharmaceuticals having different functional groups were explored through experimental methods, site energy distribution theory, and density functional theory (DFT) calculations. Results indicated that PS MPs exhibited a notable sorption capacity for pharmaceuticals, with the order of sorption being naproxen (NAP), bezafibrate (BZF), norfloxacin (NOR), ibuprofen (IBU), sulfamethoxazole (SMX), and carbamazepine (CAB). A deeper analysis revealed that multiple factors, including hydrophobicity, electrostatic repulsion, π–π interactions, and hydrogen bonding, regulate the sorption process. Furthermore, the Dubinin–Astakhov (DA) model was employed to calculate the energy distribution. The adsorption affinity (<i>E</i><sub>m</sub> = 2.88–8.36 kJ/mol) and energy heterogeneity (σ<sub>e</sub>* = 1.59–2.25) of PS MPs for different pharmaceuticals followed the order SMX > NOR > NAP > CAB > IBU > BZF. DFT calculations confirmed that the formation of n−π bonds between PS MPs and pharmaceuticals was also a primary sorption mechanism. The different sorption mechanisms of PS MPs for various pharmaceuticals can eventually alter their toxicity, such as increased toxicity of pharmaceuticals with carboxyl groups. 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引用次数: 0
摘要
与各种药物相关的水生风险可能受到无处不在的微塑料(MPs)的显著影响,从而导致不可预见的环境影响。揭示MPs与具有不同功能基团的药物之间的相互作用对于准确的风险评估至关重要。本文通过实验方法、位能分布理论和密度泛函理论(DFT)计算,探讨了聚苯乙烯(PS) MPs与具有不同官能团的药物相互作用的吸附行为和潜在机制。结果表明,PS MPs对药物具有较强的吸附能力,吸附顺序依次为萘普生(NAP)、贝扎贝特(BZF)、诺氟沙星(NOR)、布洛芬(IBU)、磺胺甲恶唑(SMX)、卡马西平(CAB)。进一步分析表明,疏水性、静电斥力、π -π相互作用和氢键等多种因素调节了吸附过程。采用Dubinin-Astakhov (DA)模型计算能量分布。PS MPs对不同药物的吸附亲和度(Em = 2.88 ~ 8.36 kJ/mol)和能量异质性(σe* = 1.59 ~ 2.25)依次为SMX >; NOR > NAP > CAB > IBU >; BZF。DFT计算证实了PS - MPs与药物之间形成n−π键也是主要的吸附机制。PS - MPs对各种药物的不同吸附机制最终会改变其毒性,例如含有羧基的药物毒性增加。总的来说,本研究提供了对MPs与药物之间相互作用的更全面的了解,这可以为存在MPs的药物的风险评估做出重大贡献。
Microplastics Alter the Distribution and Toxic Potential of Typical Pharmaceuticals in Aqueous Solutions: Mechanisms and Theory Calculations
The aquatic risks associated with various pharmaceuticals can be significantly influenced by the ubiquitous presence of microplastics (MPs), leading to unforeseen environmental effects. Uncovering the interactions between MPs and pharmaceuticals with diverse functional groups is of crucial importance for accurate risk assessment. Here, the sorption behaviors and underlying mechanisms by which polystyrene (PS) MPs interact with pharmaceuticals having different functional groups were explored through experimental methods, site energy distribution theory, and density functional theory (DFT) calculations. Results indicated that PS MPs exhibited a notable sorption capacity for pharmaceuticals, with the order of sorption being naproxen (NAP), bezafibrate (BZF), norfloxacin (NOR), ibuprofen (IBU), sulfamethoxazole (SMX), and carbamazepine (CAB). A deeper analysis revealed that multiple factors, including hydrophobicity, electrostatic repulsion, π–π interactions, and hydrogen bonding, regulate the sorption process. Furthermore, the Dubinin–Astakhov (DA) model was employed to calculate the energy distribution. The adsorption affinity (Em = 2.88–8.36 kJ/mol) and energy heterogeneity (σe* = 1.59–2.25) of PS MPs for different pharmaceuticals followed the order SMX > NOR > NAP > CAB > IBU > BZF. DFT calculations confirmed that the formation of n−π bonds between PS MPs and pharmaceuticals was also a primary sorption mechanism. The different sorption mechanisms of PS MPs for various pharmaceuticals can eventually alter their toxicity, such as increased toxicity of pharmaceuticals with carboxyl groups. Overall, this study offers a more comprehensive understanding of the interactions between MPs and pharmaceuticals, which can contribute significantly to the risk assessment of pharmaceuticals in the presence of MPs.