†Air Quality Processes Research Section, Environment Canada, Toronto, ON M3H 5T4, Canada.
‡Universidade Federal do Rio Grande, Instituto de Oceanografia, Rio Grande, RS, Brazil.
Environ Sci Technol. 2015 Mar 17;49(6):3680-6. doi: 10.1021/es506071n. Epub 2015 Mar 2.
A passive air sampling network has been established to investigate polychlorinated dibenzo-p-dioxins (PCDDs) and polychlorinated dibenzofurans (PCDFs) at Global Atmospheric Passive Sampling (GAPS) sites and six additional sites in the Group of Latin American and Caribbean Countries (GRULAC) region. The air sampling network covers background, agricultural, rural, and urban sites. Samples have been collected over four consecutive periods of 6 months, which started in January 2011 [period 1 (January to June 2011), period 2 (July to December 2011), period 3 (January to June 2012), and period 4 (July 2012 to January 2013)]. Results show that (i) the GAPS passive samplers (PUF disk type) and analytical methodology are adequate for measuring PCDD/F burdens in air and (ii) PCDD/F concentrations in air across the GRULAC region are widely variable by almost 2 orders of magnitude. The highest concentrations in air of Σ4-8PCDD/Fs were found at the urban site São Luis (Brazil, UR) (i.e., 2560 fg/m3) followed by the sites in São Paulo (Brazil, UR), Mendoza (Argentina, RU), and Sonora (Mexico, AG) with values of 1690, 1660, and 1610 fg/m3, respectively. Very low concentrations of PCDD/Fs in air were observed at the background site Tapanti (Costa Rica, BA), 10.8 fg/m3. This variability is attributed to differences in site characteristics and potential local/regional sources as well as meteorological influences. The measurements of PCDD/Fs in air agree well with model-predicted concentrations performed using the Global EMEP Multimedia Modeling System (GLEMOS) and emission scenario constructed on the basis of the UNEP Stockholm Convention inventory of dioxin and furan emissions.
已建立被动空气采样网络,以在全球大气被动采样 (GAPS) 站点和拉丁美洲和加勒比国家集团 (GRULAC) 地区的其他六个站点调查多氯二苯并对二恶英 (PCDDs) 和多氯二苯并呋喃 (PCDFs)。该空气采样网络涵盖背景、农业、农村和城市站点。样品在四个连续的 6 个月时间段内收集,始于 2011 年 1 月[第 1 期 (2011 年 1 月至 6 月)、第 2 期 (2011 年 7 月至 12 月)、第 3 期 (2012 年 1 月至 6 月)和第 4 期 (2012 年 7 月至 2013 年 1 月)]。结果表明:(i) GAPS 被动采样器 (PUF 圆盘型) 和分析方法适用于测量空气中的 PCDD/F 负荷;(ii) GRULAC 地区空气中的 PCDD/F 浓度变化范围很广,相差近两个数量级。空气中 Σ4-8PCDD/Fs 的最高浓度出现在城市站点圣路易斯 (巴西,UR) (即 2560 fg/m3),其次是圣保罗 (巴西,UR)、门多萨 (阿根廷,RU) 和索诺拉 (墨西哥,AG) 站点,浓度分别为 1690、1660 和 1610 fg/m3。背景站点塔潘蒂 (哥斯达黎加,BA) 空气中 PCDD/F 的浓度非常低,为 10.8 fg/m3。这种变异性归因于站点特征和潜在的地方/区域来源以及气象影响的差异。使用全球 EMEP 多媒体建模系统 (GLEMOS) 进行的模型预测浓度与空气中 PCDD/F 的测量值吻合良好,该模型预测浓度是根据环境署斯德哥尔摩公约关于二恶英和呋喃排放的清单构建的排放情景得出的。