Effects of copper on chemical kinetics and brown carbon formation in the aqueous ˙OH oxidation of phenolic compounds†

IF 4.3 3区 环境科学与生态学 Q1 CHEMISTRY, ANALYTICAL
Junwei Yang, Tianye Zhou, Yuting Lyu, Beatrix Rosette Go Mabato, Jason Chun-Ho Lam, Chak K. Chan and Theodora Nah
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引用次数: 0

Abstract

Many phenolic compounds (PhCs) in biomass burning and fossil fuel combustion emissions can partition into atmospheric aqueous phases (e.g., cloud/fog water and aqueous aerosols) and undergo reactions to form secondary organic aerosols (SOAs) and brown carbon (BrC). Redox-active transition metals, particularly Fe and Cu, are ubiquitous species in atmospheric aqueous phases known to participate in Fenton/Fenton-like chemistry as a source of aqueous ˙OH. However, even though the concentrations of water-soluble Cu are close to those of water-soluble Fe in atmospheric aqueous phases in some areas, unlike Fe, the effects that Cu have on SOA and BrC formation in atmospheric aqueous phases have scarcely been studied and remain poorly understood. We investigated the effects of Cu(II) on PhC reaction rates and BrC formation during the aqueous oxidation of four PhCs (guaiacol, catechol, syringol, and vanillin) by ˙OH generated from Fenton-like chemistry under different pH conditions. While the PhCs reacted when both H2O2 and Cu(II) were present in the absence (i.e., dark oxidation) and presence (i.e., photooxidation) of light, the reaction rates were at least one order of magnitude higher during photooxidation. Higher PhC reaction rates were measured at higher pH during both dark oxidation and photooxidation as a result of higher ˙OH concentrations produced by Fenton-like chemistry. Only water-soluble BrC was formed during dark oxidation and photooxidation when Cu(II) was present. Mass absorption coefficients (103 to 104 cm2 g−1) comparable to those of biomass burning BrC were measured during dark oxidation and photooxidation when Cu(II) was present. Light absorption was enhanced at higher pH during dark oxidation and photooxidation, which indicated that higher quantities and/or more absorbing BrC chromophores were formed at higher pH. The effects that Cu(II) had on the PhC reaction rates and the composition of SOAs and BrC formed depended on the PhC base structure (i.e., benzenediol vs. methoxyphenol). Overall, these results show how aqueous reactions involving Cu(II), H2O2, and PhCs can be an efficient source of daytime and nighttime water-soluble BrC and SOAs, which can have significant implications for how the atmospheric fates of PhCs are modeled for areas with substantial concentrations of water-soluble Cu in highly to moderately acidic cloud/fog water and aqueous aerosols.

Abstract Image

铜对酚类化合物水溶液 ∙OH 氧化过程中的化学动力学和褐碳形成的影响
生物质燃烧和化石燃料燃烧排放物中的许多酚类化合物(PhCs)会进入大气水相并发生反应,形成二次有机气溶胶(SOA)和褐碳(BrC)。具有氧化还原活性的过渡金属(铁和铜)是大气水相中无处不在的物种,它们参与类似芬顿/芬顿的化学反应,成为 ∙OH 的来源。然而,尽管在某些地区大气水相中水溶性铜的浓度与水溶性铁的浓度接近,但与铁不同的是,铜对大气水相中 SOA 和 BrC 形成的影响却鲜有研究,人们对这一问题的了解仍然不够深入。我们研究了在不同 pH 值条件下,芬顿类化学反应产生的 ∙OH 对四种 PhC(愈创木酚、邻苯二酚、丁香酚和香草醛)的水氧化过程中,Cu(II)对 PhC 反应速率和 BrC 形成的影响。在没有光(即暗氧化)和有光(即光氧化)的情况下,当 H2O2 和 Cu(II)同时存在时,PhCs 都会发生反应,而在光氧化过程中,反应速率至少要高出一个数量级。在暗氧化和光氧化过程中,pH 值越高,PhC 反应速率越高,这是因为芬顿化学反应产生的 ∙OH 浓度越高。有 Cu(II)存在时,暗氧化和光氧化过程中只形成水溶性 BrC。在有 Cu(II)存在的暗氧化和光氧化过程中,测得的质量吸收系数(103 至 104 cm2 g-1)与生物质燃烧的 BrC 的质量吸收系数相当。在暗氧化和光氧化过程中,pH 值越高,光吸收越强,这表明 pH 值越高,形成的 BrC 发色团数量越多和/或吸收能力越强。Cu(II) 对 PhC 反应速率以及所形成的 SOA 和 BrC 成分的影响取决于 PhC 碱结构(即苯二酚与甲氧基苯酚)。总之,这些结果表明了涉及 Cu(II)、H2O2 和 PhCs 的水反应如何成为白天和夜间水溶性 BrC 和 SOA 的有效来源,这对如何模拟 PhCs 在高度至中度酸性云/雾水和水气溶胶中具有大量水溶性 Cu 的地区的大气命运具有重要意义。
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来源期刊
Environmental Science: Processes & Impacts
Environmental Science: Processes & Impacts CHEMISTRY, ANALYTICAL-ENVIRONMENTAL SCIENCES
CiteScore
9.50
自引率
3.60%
发文量
202
审稿时长
1 months
期刊介绍: Environmental Science: Processes & Impacts publishes high quality papers in all areas of the environmental chemical sciences, including chemistry of the air, water, soil and sediment. We welcome studies on the environmental fate and effects of anthropogenic and naturally occurring contaminants, both chemical and microbiological, as well as related natural element cycling processes.
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