Shiroudi Abolfazl, Kurtén Theo, Czub Jacek
Department of Physical Chemistry, Gdańsk University of Technology, Narutowicza 11/12, Gdańsk, 80-233, Poland.
Department of Chemistry, University of Helsinki, Helsinki, 00014, Finland.
Sci Rep. 2025 Jan 7;15(1):1038. doi: 10.1038/s41598-024-84982-0.
The study investigated the degradation of 3-methoxy-1-propanol (3M1P) by OH using the M06-2X/6-311++G(d, p) level, with CCSD(T) single-point corrections. We focused on hydrogen atom abstraction from various alkyl groups within the molecule. The rate coefficient for 3M1P degradation was calculated from the sum of the rate coefficients corresponding to the removal of H-atoms from primary (-CH), secondary (-CH-), tertiary (-CH< ), and alcohol (-ΟH) groups. The primary attack by hydroxyl radicals occurs at the hydrogen atom bonded to carbon atoms adjacent to the oxygen atom in the ether group, leading to the formation of alkyl radicals. The computed overall rate constant is 1.85 × 10 cm molecule sec at atmospheric pressure and room temperature, which is consistent with the experimental value of (2.15 ± 0.28)×10 cm molecule sec. This strong agreement confirms the reliability of the computational approach, which provides insights into the atmospheric reactivity and degradation pathways of 3M1P. The tropospheric lifetime of 3M1P is around 15 h, indicating rapid degradation in the atmosphere, potentially contributing to photochemical smog formation. The average ozone production from 3M1P emissions is ~ 2.1 ppb, with estimated photochemical ozone creation potential (POCP) values of 44 and 43 for north-west European and USA-urban conditions, respectively. These values indicate a moderate risk of photochemical smog production and potential harm to human health and the environment due to 3M1P emissions. Successive pathways involve the addition of molecular oxygen to the energized adducts [3M1P], forming [3M1P-O] peroxy radicals, which primarily react with nitric oxide to produce nitrogen dioxide and the [3M1P-O] alkoxy radicals. The major degradation products include methyl formate, 3-hydroxypropyl formate, glycolaldehyde, and 3-methoxypropanal.
该研究使用M06 - 2X/6 - 311++G(d, p)水平并进行CCSD(T)单点校正,研究了羟基(OH)对3 - 甲氧基 - 1 - 丙醇(3M1P)的降解作用。我们重点关注从分子内各种烷基夺取氢原子的过程。3M1P降解的速率系数是根据从伯(-CH)、仲(-CH-)、叔(-CH< )和醇(-ΟH)基团去除氢原子对应的速率系数之和计算得出的。羟基自由基的主要攻击发生在与醚基中氧原子相邻的碳原子所键合的氢原子上,从而导致烷基自由基的形成。在大气压力和室温下计算得到的总速率常数为1.85×10 cm³分子⁻¹秒⁻¹,这与实验值(2.15 ± 0.2)×10 cm³分子⁻¹秒⁻¹一致。这种高度吻合证实了计算方法的可靠性,该方法为3M1P的大气反应性和降解途径提供了深入见解。3M1P在对流层的寿命约为15小时,表明其在大气中快速降解,可能对光化学烟雾的形成有贡献。3M1P排放产生的平均臭氧生成量约为2.1 ppb,在西北欧和美国城市条件下,估计的光化学臭氧生成潜力(POCP)值分别为44和43。这些值表明3M1P排放存在中等程度的光化学烟雾产生风险以及对人类健康和环境的潜在危害。后续途径包括分子氧加成到激发的加合物[3M1P]上,形成[3M1P - O]过氧自由基,其主要与一氧化氮反应生成二氧化氮和[3M1P - O]烷氧基自由基。主要降解产物包括甲酸甲酯、3 - 羟基丙基甲酸酯、乙醇醛和3 - 甲氧基丙醛。