Institute of Environmental and Occupational Health Sciences, National Yang Ming University, Taipei 112, Taiwan.
Environ Sci Technol. 2012 Mar 6;46(5):2839-46. doi: 10.1021/es204230p. Epub 2012 Feb 27.
Polychlorinated dibenzo-p-dioxins and dibenzofurans (PCDD/Fs) are a group of compounds of major environmental concern. Once emitted into the atmosphere, PCDD/Fs undergo photochemical reactions and enter other environmental compartments via wet and dry deposition. In this study, atmospheric PCDD/F depositions were collected via an automated PCDD/F deposition sampler and traditional cylindrical vessels, respectively, in northern, central, and southern Taiwan from 2008 to 2010. The automated PCDD/F precipitation sampler used in this study can prevent both resuspension and photodegradation of the PCDD/Fs collected and also effectively separates the PCDD/F samples into dry and wet contributions. The results indicate that the average atmospheric PCDD/F concentrations collected by the high-volume sampling trains were 13.6 ± 10 (n = 10), 15.6 ± 5.2 (n = 7), and 10.9 ± 6.3 (n = 6) fg I-TEQ/m(3) in northern, central, and southern Taiwan, respectively. In addition, the results also indicate that the PCDD/F deposition flux collected with an automated PCDD/F sampler (1.84 ± 0.90-8.68 ± 5.1 pg I-TEQ/m(2)/day, n = 23) is significantly higher than that sampled with cylindrical vessels (1.11 ± 0.69-5.64 ± 5.2 pg I-TEQ/m(2)/day, n = 23). Based on the Mann-Whitney statistical analysis, the p value (0.037) of PCDD/F deposition flux between those two samplers measurement is lower than 0.05. The difference is attributed to the fact that part of the PCDD/F depositions collected by traditional cylindrical vessels is photodegraded and revolatilized. In addition, the wet deposition flux of PCDD/Fs (3.66 to 470 pg I-TEQ/m(2)/rainy day, n = 23) observed in Taiwan is significantly higher than the dry deposition flux (0.38 to 4.55 pg I-TEQ/m(2)/sunny day, n = 23). The results demonstrate that the wet deposition is the major PCDD/F removal mechanism in the atmosphere. Furthermore, the overall PCDD/Fs deposition velocity and scavenging (rainout) coefficient in Taiwan are calculated as 0.20 ± 0.07 cm/s and 6.5 ± 0.2 × 10(4), respectively.
多氯二苯并对二恶英和多氯二苯并呋喃(PCDD/Fs)是一组主要的环境关注化合物。一旦排放到大气中,PCDD/Fs 会经历光化学反应,并通过湿沉降和干沉降进入其他环境介质。在这项研究中,我们分别使用自动 PCDD/F 沉降采样器和传统的圆柱形容器,在 2008 年至 2010 年期间在台湾北部、中部和南部收集大气 PCDD/F 沉降物。本研究中使用的自动 PCDD/F 降水采样器可以防止收集的 PCDD/F 发生再悬浮和光降解,并能有效地将 PCDD/F 样品分为干沉降和湿沉降两部分。结果表明,使用大容量采样器采集的大气 PCDD/F 浓度分别为北部、中部和南部台湾的 13.6 ± 10(n = 10)、15.6 ± 5.2(n = 7)和 10.9 ± 6.3(n = 6) fg I-TEQ/m3。此外,结果还表明,使用自动 PCDD/F 采样器采集的 PCDD/F 沉降通量(1.84 ± 0.90-8.68 ± 5.1 pg I-TEQ/m2/天,n = 23)显著高于使用圆柱形容器采集的沉降通量(1.11 ± 0.69-5.64 ± 5.2 pg I-TEQ/m2/天,n = 23)。基于曼-惠特尼统计分析,两个采样器测量的 PCDD/F 沉降通量之间的 p 值(0.037)低于 0.05。这种差异归因于传统圆柱形容器采集的部分 PCDD/F 沉降物发生光降解和再挥发。此外,在台湾观测到的 PCDD/F 湿沉降通量(3.66 至 470 pg I-TEQ/m2/rainy day,n = 23)显著高于干沉降通量(0.38 至 4.55 pg I-TEQ/m2/sunny day,n = 23)。结果表明,湿沉降是大气中 PCDD/F 的主要去除机制。此外,台湾的 PCDD/F 总沉降速度和清除(雨除)系数分别计算为 0.20 ± 0.07 cm/s 和 6.5 ± 0.2×104。