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光化学老化对源自于实际燃烧事件(如木材和稻草燃烧)的 PM 中多环芳烃的半衰期和固有诊断比的影响。

Impacts of photochemical ageing on the half-lives and diagnostic ratio of polycyclic aromatic hydrocarbons intrinsic to PM collected from 'real-world' like combustion events of wood and rice straw burning.

机构信息

Environmental Sciences Section, Bose Institute, P 1/12 CIT Scheme VII-M, Kolkata, 700054, India.

Centre for Astroparticle Physics and Space Science, Block-EN, Sector-V, Salt Lake, Kolkata, 700091, India; Department of Physics, Bose Institute, 93/1, A.P.C Road, Kolkata, 700009, India.

出版信息

J Hazard Mater. 2019 Mar 15;366:10-15. doi: 10.1016/j.jhazmat.2018.11.079. Epub 2018 Nov 22.

DOI:10.1016/j.jhazmat.2018.11.079
PMID:30500693
Abstract

The present experimental study describes the characteristics of polycyclic aromatic hydrocarbons (PAHs) emitted with PM particles during wood and rice straw burning as well as impacts of photochemical ageing on the half lives of particulate PAHs and their diagnostic ratio values. The photochemical degradation kinetics experiments were carried out by exposing the PM to light and synthetic air flow. Pseudo first order rate constants were calculated based on PAH loss as a function of exposure time. Relatively quick degradation of lighter PAHs (3-rings) [(0.2-0.5)h] than heavier PAHs (4-6 rings) [(0.0005-0.03)h] indicates substantial impact of PAH-substrate interaction through π-π stacking with the carbonaceous substrates. Moreover, our results showed distinct PAH diagnostic ratios (DR) for wood and rice straw burnings which, however, change with time due to photochemical degradation. The later may add uncertainties in the applications of DR values for source apportionment. Furthermore, considerably large half lives (100-3000 h) of the carcinogenic PAHs as estimated under ambient solar radiation may cause poor and adverse air quality in long range and therefore demands immediate regulations against uncontrolled biomass burning.

摘要

本实验研究描述了木质和稻草燃烧过程中 PM 颗粒排放的多环芳烃(PAHs)的特性,以及光化学老化对颗粒物 PAHs 的半衰期及其诊断比值的影响。通过将 PM 暴露在光照和合成气流下进行光化学降解动力学实验。基于 PAH 损失随暴露时间的函数,计算了拟一级速率常数。较轻的 PAHs(三环)(0.2-0.5 h)比较重的 PAHs(四环-六环)(0.0005-0.03 h)的降解速度更快,这表明 PAH-基质相互作用通过π-π堆积与碳质基质的相互作用有很大的影响。此外,我们的结果显示了木质和稻草燃烧的明显的 PAH 诊断比值(DR),然而,由于光化学降解,这些比值会随时间发生变化。这可能会给 DR 值在源解析中的应用带来不确定性。此外,在环境太阳辐射下估计的致癌 PAHs 的半衰期(100-3000 h)相当长,可能会导致长距离空气质量较差和不利,因此需要立即对不受控制的生物质燃烧进行监管。

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