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中国半山区工业园多环芳烃的分布、输入途径和土壤-空气交换。

Distribution, input pathway and soil-air exchange of polycyclic aromatic hydrocarbons in Banshan Industry Park, China.

机构信息

Department of Environmental Science, Zhejiang University, Hangzhou, Zhejiang 310058, China.

出版信息

Sci Total Environ. 2013 Feb 1;444:177-82. doi: 10.1016/j.scitotenv.2012.11.091. Epub 2012 Dec 23.

Abstract

Given the steel industry park-city paired structure commonly found across China and it associated environmental pollution, the objective of this study was to examine the spatial-temporal distributions of polycyclic aromatic hydrocarbons (PAHs) as well as the relative contributions of the main influx pathways in Banshan steel industry park, China. We analyzed the concentrations of 16 PAHs in soil, air, water and dry/wet deposition samples using gas chromatography-mass spectrometry (GC-MS). The concentrations of ∑(16)-PAHs ranged from 572 to 4,654 μg/kg in April 2010; and the average concentration is 12.7% and 26.1% higher than that of April 2009 and April 2008, respectively, mainly due to the rapid increase of highly toxic high molecular weight (MW) PAHs. The principal input pathway for high and low MW PAHs was determined to be dry deposition (e.g., 69.73% for Benzo[a]pyrene) and wet deposition (e.g., 78.87% for Naphthalene), respectively. Together, 54.79% of total PAHs found in this region are via dry deposition, whereas wet deposition and river water irrigation contribute to 25.46% and 19.76% (corrected with toxic equivalency factors). The approach to the soil-air equilibrium was assessed by calculating fugacity quotients between soil and air samples, and the results indicate that the soil acted as a secondary source for light MW atmospheric PAHs and a sink for higher MW PAHs. It was also determined that the soil acted as a source for median MW PAHs, particularly PY.

摘要

鉴于中国普遍存在钢铁产业园区与城市相匹配的结构以及由此产生的环境污染问题,本研究旨在检测中国半山区钢铁产业园区多环芳烃(PAHs)的时空分布特征,以及主要输入途径的相对贡献。我们采用气相色谱-质谱法(GC-MS)分析了土壤、空气、水和干湿沉降样品中 16 种 PAHs 的浓度。2010 年 4 月,∑(16)-PAHs 的浓度范围为 572-4654μg/kg;与 2009 年 4 月和 2008 年 4 月相比,平均浓度分别升高了 12.7%和 26.1%,主要是由于高毒性高分子量(MW)PAHs 的快速增加。高 MW 和低 MW PAHs 的主要输入途径分别为干沉降(如苯并[a]芘的 69.73%)和湿沉降(如萘的 78.87%)。该地区发现的总 PAHs 中有 54.79%是通过干沉降输入的,而湿沉降和河水灌溉分别贡献了 25.46%和 19.76%(经毒性等效因子校正)。通过计算土壤和空气样品之间的逸度比来评估土壤-空气平衡的方法表明,土壤是轻 MW 大气 PAHs 的二次源,也是高 MW PAHs 的汇。此外,研究还确定土壤是中 MW PAHs(特别是芘)的源。

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