Department of Earth Sciences, Faculty of Sciences, Shiraz University, Shiraz, 71454, Iran.
School of Environmental Sciences, University of Guelph, Guelph, ON, N1G 2W1, Canada.
Environ Geochem Health. 2018 Jun;40(3):1155-1174. doi: 10.1007/s10653-017-9994-6. Epub 2017 Jun 9.
When the hazard quotient for ingestion (HQI) of a trace element in soil and dust particles is adjusted for the element's bioaccessibility, the HQI is typically reduced as compared to its calculation using pseudo-total element concentration. However, those studies have mostly used bulk particles (<2 mm or <250 µm), and the reduction in HQI when expressed as bioaccessible metal may not be similar among particle size fractions, the possibility probed by the present study of street dusts and soils collected in Tehran. The highest Cu, Pb and Zn near-total concentrations occurred in the finest particles of dusts and soils. Bioaccessible concentrations of Cu, Pb and Zn in the particles (mg kg) were obtained using simple bioaccessibility extraction test (SBET). The bioaccessibility (%) did not vary much among near-total concentrations. In the bulk (<250 µm) sample, the bioaccessible concentration of Cu and Pb increased as the pH of sample increased, while Zn bioaccessibility (%) in the bulk particles was influenced by organic matter and cation exchange capacity. X-ray diffraction identified sulfide and sulfate minerals in all of the size-fractionated particles, which are insoluble to slightly soluble in acidic conditions and included most of the Cu and Pb in the samples. The only Zn-bearing mineral identified was hemimorphite, which would be highly soluble in the SBET conditions. The calculated HQI suggested potential non-carcinogenic health risk to children and adults from ingestions of soils and dusts regardless of particle size consideration, in the order of Zn > Pb ≥ Cu. The HQI calculated from near-total metal was not much different for particle size classes relative to bulk particles; however, the bioaccessibility percent-adjusted HQI for Pb was higher for the smaller particles than the bulk. This work is novel in its approach to compare HQI for a bulk sample of particles with its composite particle size fractions.
当调整土壤和粉尘颗粒中微量元素的摄入(HQI)的危害商时,与使用假总元素浓度计算相比,HQI 通常会降低。然而,这些研究大多使用散装颗粒(<2 毫米或<250 微米),并且以生物可利用金属表示的 HQI 减少量在粒径分数之间可能不相似,本研究对德黑兰收集的街道灰尘和土壤进行了探讨。在尘埃和土壤中,Cu、Pb 和 Zn 的近全浓度最高的颗粒最细。使用简单生物可利用性提取试验(SBET)获得颗粒中 Cu、Pb 和 Zn 的生物可利用浓度(mg/kg)。近全浓度之间的生物可利用度(%)差异不大。在大块(<250 微米)样品中,Cu 和 Pb 的生物可利用浓度随着样品 pH 值的增加而增加,而大块颗粒中 Zn 的生物可利用性(%)受有机物和阳离子交换容量的影响。X 射线衍射在所有分级颗粒中都确定了硫化物和硫酸盐矿物,这些矿物在酸性条件下不溶或略溶,包含了样品中的大部分 Cu 和 Pb。唯一确定的含 Zn 矿物是纤锌矿,在 SBET 条件下溶解度很高。计算出的 HQI 表明,无论考虑粒径如何,儿童和成人因摄入土壤和灰尘而产生的潜在非致癌健康风险为 Zn>Pb>Cu。相对于大块颗粒,粒径类别的近全金属计算的 HQI 没有太大差异;然而,对于较小的颗粒,Pb 的生物利用度调整后的 HQI 高于大块。本工作的新颖之处在于,将大块颗粒的 HQI 与其复合粒径分数进行比较。