College of Earth and Environmental Sciences, University of the Punjab, Lahore 54590, Pakistan.
Queensland Alliance for Environmental Health Science, The University of Queensland, Brisbane 4102, Australia; Guangdong-Hong Kong-Macao Joint Laboratory for Contaminants Exposure and Health, Guangdong Key Laboratory of Environmental Catalysis and Health Risk Control, Institute of Environmental Health and Pollution Control, Guangdong University of Technology, Guangzhou 510006, PR China; Guangzhou Key Laboratory of Environmental Catalysis and Pollution Control, Key Laboratory for City Cluster Environmental Safety and Green Development of the Ministry of Education, School of Environmental Science and Engineering, Guangdong University of Technology, Guangzhou 510006, PR China.
Sci Total Environ. 2024 Nov 25;953:176054. doi: 10.1016/j.scitotenv.2024.176054. Epub 2024 Sep 6.
This study provides the first systematic data on the distribution of short- (SCCPs) and medium chlorinated paraffins (MCCPs) in the atmosphere and surface soils of Lahore, Pakistan. The spatial distribution of SCCPs and MCCPs in air (n = 12) and soil (n = 15) was investigated from industrial, residential, commercial, conventional e-waste burning and background areas of Lahore. The concentrations ranged from below the limit of detection (<LOD)-130 and <LOD-74 ng/g dw for SCCPs and MCCPs, respectively in soil while in air their corresponding concentrations were <LOD-2.9 and <LOD-1.1 ng/m. Higher CPs contaminated soil and air were observed in industrial and commercial areas likely due to the use of CPs as flame retardants/plasticizers in products and metalworking. Total organic carbon (TOC), SCCPs and MCCPs in soil were not correlated with each other however, a significant association between SCCPs and MCCPs was observed in air samples. Among all the samples of soil and air C Cl and CCl were the predominant congeners for SCCPs and MCCPs, respectively. The comprehensive investigation of soil-air exchange for SCCPs and MCCPs revealed approximately 67 % of fugacity fractions (ffs) above 0.7, indicating net volatilization for most of the congeners. This study also revealed a notably high emission flux for SCCPs and MCCPs compared to their deposition flux, indicating that soil acted as a major source of CPs. Additionally, the emission flux for SCCPs was higher than for MCCPs, owing to their greater volatility and transport potential. A preliminary risk assessment suggested limited risks (Risk quotient <0.02) to the soil community while, the adult and toddler community had daily intakes of 5.7 and 7.2 ng/kg/day of CPs, respectively via different pathways highlighting the hotspots with high risk areas.
本研究首次提供了巴基斯坦拉合尔市大气和表层土壤中短链氯化石蜡(SCCPs)和中链氯化石蜡(MCCPs)分布的系统数据。本研究调查了拉合尔市工业区、居民区、商业区、传统电子废物焚烧区和背景区空气中(n=12)和土壤中(n=15)SCCPs 和 MCCPs 的空间分布。土壤中 SCCPs 和 MCCPs 的浓度范围分别为低于检出限(<LOD)-130 和 <LOD-74 ng/g dw,而空气中 SCCPs 和 MCCPs 的浓度相应地分别为 <LOD-2.9 和 <LOD-1.1 ng/m。在工业区和商业区,发现受污染程度较高的土壤和空气,这可能是由于 CP 作为阻燃剂/增塑剂用于产品和金属加工。土壤中的总有机碳(TOC)、SCCPs 和 MCCPs 彼此之间没有相关性,但在空气样本中观察到 SCCPs 和 MCCPs 之间存在显著关联。在所有土壤和空气样本中,C Cl 和 CCl 分别是 SCCPs 和 MCCPs 的主要同系物。SCCPs 和 MCCPs 的土壤-空气交换的综合调查显示,约 67%的逸度分数(ffs)大于 0.7,表明大多数同系物处于净挥发状态。本研究还表明,SCCPs 和 MCCPs 的排放通量明显高于其沉积通量,表明土壤是 CP 的主要来源。此外,由于 SCCPs 具有更大的挥发性和传输潜力,其排放通量高于 MCCPs。初步风险评估表明,土壤群落面临的风险有限(风险商数<0.02),而成人和幼儿通过不同途径每天摄入的 SCCPs 和 MCCPs 分别为 5.7 和 7.2 ng/kg/天,突出了高风险地区的热点。