LEESU, École des Ponts ParisTech, University of Paris-Est Créteil. 6-8 avenue Blaise Pascal, Cité Descartes, 77455 Marne-la-Vallée cedex 2, France; DEEP (Laboratory of Wastes, Water, Environment & Pollutions), University of Lyon, INSA Lyon, 11 rue de la Physique, 69621 Villeurbanne cedex, France.
LEESU, École des Ponts ParisTech, University of Paris-Est Créteil. 6-8 avenue Blaise Pascal, Cité Descartes, 77455 Marne-la-Vallée cedex 2, France; IEM (European Institute of Membranes), University of Montpellier, ENSCM, CNRS, UMR5635, 300 avenue du Professeur Emile Jeanbrau, 34090 Montpellier, France.
Sci Total Environ. 2021 May 15;769:144862. doi: 10.1016/j.scitotenv.2020.144862. Epub 2020 Dec 31.
This study addresses soil contamination in vegetated road shoulders with diffuse inflow of runoff. It aims (i) to characterize the spatial distribution of three metals (copper, lead, zinc) and PAHs, and (ii) to identify influencing factors for the inter-site differences. An extensive sampling campaign was carried out on forty road segments in the Paris region, targeting various distances and soil depths. Copper and zinc contamination was found to be mainly restricted to the first 30 cm from the road, where their concentrations ranged respectively between 40 and 270 mg.kg, and between 150 and 950 mg.kg (with a few additional extreme values related to the presence of a galvanized steel guardrail). Lead contamination was moderate (< 100 mg.kg in more than 75% of the sites) and relatively uniform across the width of the shoulders. Conversely, highest PAH concentrations were found further from the road. These differences between contaminants were likely due to the varying importance of wet weather-related processes and atmospheric transport in their dispersion mechanisms. Copper and zinc concentrations correlated well with the traffic density, which alone explained ≥ 69% of the inter-site variability, whereas lead and PAHs did not exhibit such dependence. Soil organic matter was found to control the "ceiling" concentration of metals, thus limiting the maximum amounts that can be intercepted from road runoff. These results illustrate the feasibility of estimating contamination levels on road shoulders, and thus offer interesting perspectives for better consideration of the infrastructures' maintenance needs and improved routine operations.
本研究针对植被路肩土壤污染和漫流径流下的污染扩散问题展开。其目的为:(i) 描述三种金属(铜、铅、锌)和多环芳烃的空间分布,(ii) 识别造成站点间差异的影响因素。在巴黎地区,对四十个路段开展了广泛的采样工作,涵盖不同距离和土壤深度。研究发现,铜和锌污染主要集中在距道路 30 厘米以内,其浓度分别在 40 至 270 毫克/千克和 150 至 950 毫克/千克之间(另有少数极值与镀锌钢护栏的存在有关)。铅污染程度适中(超过 75%的站点中含量低于 100 毫克/千克),且在路肩宽度上较为均匀。相比之下,多环芳烃的最高浓度出现在离道路更远的地方。这些污染物之间的差异可能是由于其扩散机制中与湿天气相关的过程和大气传输的重要性不同所致。铜和锌浓度与交通密度相关性良好,交通密度可单独解释 69%以上的站点间变异性,而铅和多环芳烃则没有这种相关性。土壤有机质控制着金属的“上限”浓度,从而限制了从道路径流下拦截的最大金属量。这些结果表明,在路肩上估算污染水平是可行的,为更好地考虑基础设施的维护需求和改进日常作业提供了有趣的前景。