Ewen Caroline, Anagnostopoulou Maria A, Ward Neil I
Department of Chemical Sciences, Faculty of Science, University of Surrey, Guildford, GU2 7XH, UK.
Environ Monit Assess. 2009 Oct;157(1-4):483-98. doi: 10.1007/s10661-008-0550-9. Epub 2008 Oct 9.
In recent years, the level of heavy metal pollution in urban areas has been of considerable concern. The principal source has been attributed to the motor vehicle and increasing inner city congestion, which has lead to a change and enlargement of transport stop-start zones. These areas of high traffic density are associated with an increased release of heavy metals into the adjacent residential or commercial areas. Seventy-five roadside dust samples were collected throughout the inner city and by-pass motorway areas of Thessaloniki, Northern Greece. Samples were taken from arterial, major and minor roads, as well as the ring road, to compare and contrast the levels of heavy metals, namely Cu, Zn, Cd, Mn and Pb. Flame Atomic Absorption Spectroscopy (FAAS) was developed to quantitatively determine concentrations of both total element and geochemical fractionation, within the two dust particulate fraction sizes <75 microm and 75-125 microm. Acid digestion using Aqua Regia (3:1 conc. HCl:HNO(3)) was employed for the total elemental analysis, a method that was validated through the use of certified reference materials (CRM). Fractionation studies involved a three-step sequential extraction method performed on five selected samples (representatives of high, mid and low total elemental concentrations). The resultant solutions were analysed for lead and zinc levels to ascertain fractionation throughout the different geochemical fractions, thus assessing bioavailability.It was found that congestion/stop-start traffic patterns did influence and have led to increased levels of heavy metal deposition along inner city roads compared to levels observed on the new relief ring road. Dust particulate fraction sizes were only found to show statistically significant differences in cadmium and manganese, at the probability P < 0.001 or 99.9% confidence limit. Both Cd and Mn showed higher total levels in the smaller fraction sizes (<75 microm), implying that their major release source is exhaust emissions. There were no significant differences in the other elements, at the P > 0.05 or 95% confidence limit. Road type was seen to have little affect on cadmium and manganese, though lead, copper and zinc were all found to show higher levels on the inner city routes. This can be related back to the wear-and-tear of vehicle components as a result of the stop-start traffic patterns (brake pads etc). Both Pb and Zn have shown to be in chemical forms that are bio available to ecosystems.
近年来,城市地区的重金属污染程度备受关注。主要污染源被认为是机动车以及城市中心日益拥堵的交通,这导致了交通启停区域的变化和扩大。这些交通密度高的区域与重金属向相邻居民区或商业区的释放增加有关。在希腊北部塞萨洛尼基的市中心和绕城高速公路区域采集了75个路边灰尘样本。样本取自主干道、主要道路和次要道路以及环路,以比较和对比铜、锌、镉、锰和铅等重金属的含量。采用火焰原子吸收光谱法(FAAS)定量测定两种灰尘颗粒粒径(<75微米和75 - 125微米)内的总元素浓度和地球化学分馏情况。采用王水(3:1浓盐酸:硝酸)进行酸消解以进行总元素分析,该方法通过使用有证标准物质(CRM)进行了验证。分馏研究涉及对五个选定样本(代表总元素浓度高、中、低的样本)进行三步连续萃取法。对所得溶液分析铅和锌含量,以确定不同地球化学分馏中的分馏情况,从而评估生物有效性。研究发现,与新的绕城环路相比,拥堵/启停交通模式确实影响并导致市中心道路沿线的重金属沉积水平增加。仅发现灰尘颗粒粒径在镉和锰方面存在统计学显著差异,概率P < 0.001或置信限为99.9%。镉和锰在较小粒径(<75微米)中的总含量均较高,这意味着它们的主要释放源是尾气排放。在P > 0.05或置信限为95%时,其他元素没有显著差异。道路类型对镉和锰影响不大,不过在市中心道路上发现铅、铜和锌的含量都较高。这可能与启停交通模式导致的车辆部件磨损(如刹车片等)有关。铅和锌均呈现出对生态系统具有生物有效性的化学形态。