Vantelon Delphine, Lanzirotti Antonio, Scheinost Andreas C, Kretzschmar Ruben
Institute of Terrestrial Ecology, Swiss Federal Institute of Technology (ETH) Zurich, CH-8952 Schlieren, Switzerland.
Environ Sci Technol. 2005 Jul 1;39(13):4808-15. doi: 10.1021/es0482740.
We investigated the spatial distribution and speciation of Pb in the weathering crust and soil surrounding corroding metallic Pb bullets in a shooting range soil. The soil had a neutral pH, loamy texture, and was highly contaminated with Pb, with total Pb concentrations in the surface soil up to 68 000 mg kg(-1). Undisturbed soil samples containing corroding bullets were collected and embedded in resin, and polished sections were prepared for micro-X-ray fluorescence (micro-XRF) elemental mapping and micro-X-ray absorption near edge structure (micro-XANES) spectroscopy. Bullet weathering crust material was separated from the metallic Pb cores and analyzed by powder X-ray diffraction analysis. Our results show a steep decrease in total Pb concentrations from the bullet weathering crust into the surrounding soil matrix. The weathering crust consisted of a mixture of litharge [alpha-PbO], hydrocerussite [Pb3(CO3)2-(OH)2], and cerussite [PbCO3], with litharge dominating near the metallic Pb core and cerussite dominating in the outer crust, which is in contact with the soil matrix. On the basis of these results and thermodynamic considerations, we propose that the transition of Pb species after oxidation of Pb(O) to Pb(II) follows the sequence litharge --> hydrocerussite --> cerussite. Consequently, the solubility of cerussite limits the activity of Pb2+ in the soil solution in contact with weathering bullets to < or =1.28 x 10(-6) at pH 7, assuming that the CO2 partial pressure (PCO2) in the soil is equal or larger than in the atmosphere (PCO2 > or = 0.000 35 atm).
我们研究了射击场土壤中,腐蚀的金属铅弹周围风化壳和土壤中铅的空间分布及形态。该土壤pH值呈中性,质地为壤土,且铅污染严重,表层土壤中总铅浓度高达68000 mg·kg⁻¹。采集含有腐蚀子弹的原状土样并嵌入树脂,制备抛光切片用于微X射线荧光(micro-XRF)元素绘图和微X射线吸收近边结构(micro-XANES)光谱分析。将子弹风化壳物质与金属铅芯分离,并通过粉末X射线衍射分析进行检测。我们的研究结果表明,从子弹风化壳到周围土壤基质,总铅浓度急剧下降。风化壳由密陀僧[α-PbO]、白铅矿[Pb₃(CO₃)₂(OH)₂]和碳酸铅矿[PbCO₃]混合而成,密陀僧在金属铅芯附近占主导,碳酸铅矿在外层风化壳中占主导,外层风化壳与土壤基质接触。基于这些结果和热力学考虑,我们提出铅(0)氧化为铅(II)后,铅形态的转变顺序为密陀僧→白铅矿→碳酸铅矿。因此,假设土壤中二氧化碳分压(PCO₂)等于或大于大气中的二氧化碳分压(PCO₂≥0.00035 atm),在pH值为7时,碳酸铅矿的溶解度将与风化子弹接触的土壤溶液中Pb²⁺的活性限制在≤1.28×10⁻⁶。