Department of Chemistry, Faculty of Science, Dayalbagh Educational Institute, Dayalbagh, Agra (UP), Agra, India.
Environ Sci Pollut Res Int. 2019 Jul;26(19):19749-19762. doi: 10.1007/s11356-019-05144-8. Epub 2019 May 14.
In the present study, the distribution and chemical fractionation of heavy metals (Cd, Cr, Cu, Fe, Mn, Ni, Pb, and Zn) in PM collected at Sikandarpur in Agra from September 2015 to February 2016 were carried out to evaluate their mobility potential, environmental, and human health risk through inhalation. Sequential extraction procedure was applied to partition the heavy metals into four fractions (soluble and exchangeable fraction (F1); carbonates, oxides, and reducible fraction (F2); bound to organic matter, oxidizable, and sulphidic fraction (F3); and residual fraction (F4)) in PM samples. The metals in each fraction were analyzed by inductively coupled plasma-atomic emission spectroscopy (ICP-AES). Daily PM concentration ranged between 13 and 238 μg m during the study period. For more than 92% of the days, the mass concentrations were greater than the National Ambient Air Quality Standard (NAAQS) set at 60 μg m. The total mass concentration of the eight metals was 3.3 μg m that accounted for 2.5% of the PM mass concentration and followed the order Fe > Zn > Cu > Mn > Pb > Ni > Cd > Cr in dominance. The carcinogenic metals (Cd, Cr, Ni, and Pb) comprised 10% of the total metal determined. Almost all the metals had the highest proportion in the residual fraction (F4) except Ni, which had the highest proportion in the reducible fraction (F2). Chemical fractionation and contamination factor (CF) showed that Pb and Ni are readily mobilized and more bioavailable. Risk assessment code (RAC) showed that Cd, Cu, Mn, Ni, Pb, and Zn had medium environmental risk, while Cr and Fe had low risk. When the bioavailable (F1 + F2) concentrations were applied to calculate non-carcinogenic and carcinogenic risk, the results showed that the value of hazard index (HI) for toxic metals was 1.7 for both children and adults through inhalation. The integrated carcinogenic risk was 1.8 × 10 for children and 7.3 × 10 for adults, with both values being higher than the precautionary criterion (1 × 10). Enrichment factor (EF) calculations showed that Cd, Pb, Zn, and Ni were enriched being contributed by anthropogenic activities carried out in the industrial sectors of the city.
在本研究中,我们对 2015 年 9 月至 2016 年 2 月在阿格拉的锡坎达尔布尔采集的 PM 中重金属(Cd、Cr、Cu、Fe、Mn、Ni、Pb 和 Zn)的分布和化学形态进行了研究,以评估它们通过吸入的迁移潜力、环境和对人类健康的风险。采用连续提取程序将重金属分为 PM 样品中的四个部分(可溶和可交换部分(F1);碳酸盐、氧化物和可还原部分(F2);与有机物、可氧化和硫化物部分结合(F3);以及残余部分(F4))。通过电感耦合等离子体原子发射光谱法(ICP-AES)分析各部分的金属。在研究期间,每日 PM 浓度在 13 至 238μg/m 之间。超过 92%的天数,质量浓度大于国家环境空气质量标准(NAAQS)设定的 60μg/m。八种金属的总质量浓度为 3.3μg/m,占 PM 质量浓度的 2.5%,其优势顺序为 Fe>Zn>Cu>Mn>Pb>Ni>Cd>Cr。致癌金属(Cd、Cr、Ni 和 Pb)占总金属的 10%。除 Ni 外,几乎所有金属在残余部分(F4)中的比例最高,而 Ni 在可还原部分(F2)中的比例最高。化学形态和污染因子(CF)表明,Pb 和 Ni 易于迁移且更具生物利用性。风险评估代码(RAC)表明,Cd、Cu、Mn、Ni、Pb 和 Zn 具有中等环境风险,而 Cr 和 Fe 具有低风险。当应用可利用部分(F1+F2)浓度计算非致癌和致癌风险时,结果表明,通过吸入,儿童和成人的有毒金属危害指数(HI)值均为 1.7。综合致癌风险分别为儿童 1.8×10 和成人 7.3×10,均高于预防标准(1×10)。富集因子(EF)计算表明,Cd、Pb、Zn 和 Ni 是由城市工业部门人为活动造成的富集。