State Key Laboratory of Urban and Regional Ecology, Research Center for Eco-Environmental Sciences, Chinese Academy of Sciences, Beijing, 100085, China; Department of Environmental and Conservation Sciences, University of Swat, Swat, 19130, Pakistan.
Department of Environmental and Conservation Sciences, University of Swat, Swat, 19130, Pakistan.
Environ Res. 2022 Aug;211:113113. doi: 10.1016/j.envres.2022.113113. Epub 2022 Mar 11.
Perfluoroalkyl acids (PFAAs) are of global interest due to their persistence in the aquatic environment. This study assessed the occurrence of PFAAs in the Indus Drainage System and discerned their potential sources and environmental risks for the first time in Pakistan. 13 perfluoroalkyl carboxylic acids (PFCAs) and 4 perfluoroalkyl sulfonates (PFSAs) were analyzed to verify the dominant prevalence of short-chain PFAAs in the environment since the phase-out of long-chain perfluorooctanoic acid (PFOA) and perfluorooctane sulfonate (PFOS). A significant variation (p ≤ 0.05) of individual PFAAs between the monitoring sites was confirmed by data normality tests Kolmogorov-Smirnov and Shapiro-Wilk, suggesting that different locations contribute differently to individual PFAAs concentrations. ΣPFAAs concentrations in riverine water and sediments ranged from 2.28 to 221.75 ng/L and 0.78-29.19 ng/g dw, respectively. PFBA, PFPeA, and PFHxA were the most abundant PFAAs, and on average accounted for 14.64, 13.75, and 12.97 ng/L of ∑PFAAs in riverine water and 0.34, 0.64, and 0.79 ng/g dw of ∑PFAAs in sediments. ΣPFAAs mean contamination in the drainage was significantly (p < 0.05) high in River Chenab followed by River Indus > Soan > Ravi > Kabul > Swat with more prevalence of short-chain (C4-C7) PFCAs followed by PFOA, PFBS, PFOS, PFNA, PFDA, PFHxS, PFUnDA, and PFDoDA. The correlation analysis determined the PFAAs' fate and distribution along the drainage, indicating that PFAAs with carbon chains C4-C12, except for PFSAs with carbon chains C6-C8, were most likely contaminated by the same source, the values of Kd and Koc increased linearly with the length of the perfluoroalkyl carbon chain, better understand the transport and partitioning of individual PFAAs between riverine water and sediments, where the HCA and PCA discerned industrial/municipal wastewater discharge, agricultural and surface runoff from nearby fields, and urban localities as potential sources of PFAAs contamination. The collective mass flux of short-chain (C4-C7) PFCAs was 5x higher than that of PFOS + PFOA, suggesting a continuous shift in the production and usage of fluorinated replacements for long-chain PFAAs with short-chain homologs. In terms of risk, individual PFAAs pollution in the drainage was within the world's risk thresholds for human health, with the exception of PFBA, PFPeA, PFHpA, PFHxA, PFOA, PFNA, and PFBS, whereas for ecology, the concentrations of individual PFAAs did not exceed the ecological risk thresholds of the United States of America, Canada, European Union (EU), Italy, Australia, and New Zealand, with the exception of PFSAs, whose detected individual concentrations were significantly higher than the EU, Australian and New Zealander PFSAs guidelines of 0.002 μg/L, 0.00047 μg/L, 0.00065 μg/L, 0.00013 μg/L, and 0.00023 μg/L, respectively, which may pose chronic risks to the regional ecosystem and population.
全氟烷基酸(PFAAs)因其在水生环境中的持久性而受到全球关注。本研究评估了 PFAAs 在印度河流域系统中的存在情况,并首次在巴基斯坦发现了其潜在来源和环境风险。分析了 13 种全氟烷基羧酸(PFCAs)和 4 种全氟烷基磺酸盐(PFSAs),以验证自长链全氟辛酸(PFOA)和全氟辛烷磺酸(PFOS)淘汰以来,短链 PFAAs 在环境中的占主导地位。通过数据正态性检验 Kolmogorov-Smirnov 和 Shapiro-Wilk 证实了监测点之间单个 PFAAs 的显著变化(p≤0.05),这表明不同地点对单个 PFAAs 浓度的贡献不同。河流水和沉积物中 ΣPFAAs 的浓度范围分别为 2.28-221.75ng/L 和 0.78-29.19ng/g dw。PFBA、PFPeA 和 PFHxA 是最丰富的 PFAAs,平均占河流水中∑PFAAs 的 14.64、13.75 和 12.97ng/L,以及沉积物中∑PFAAs 的 0.34、0.64 和 0.79ng/g dw。排水系统中的 ΣPFAAs 平均污染程度(p<0.05)以 Chenab 河最高,其次是 Indus 河>Soan 河>Ravi 河>Kabul 河>Swat 河,短链(C4-C7)PFCAs 的流行程度高于 PFOA、PFBS、PFOS、PFNA、PFDA、PFHxS、PFUnDA 和 PFDoDA。相关分析确定了 PFAAs 沿排水系统的命运和分布,表明碳链 C4-C12 的 PFAAs,除了碳链 C6-C8 的 PFSAs 外,最有可能受到同一来源的污染,Kd 和 Koc 值随全氟烷基碳链的长度线性增加,更好地了解了河流水和沉积物中单个 PFAAs 的迁移和分配,其中 HCA 和 PCA 将工业/城市污水排放、附近农田的农业和地表径流以及城市地区识别为 PFAAs 污染的潜在来源。短链(C4-C7)PFCAs 的集体质量通量比 PFOS+PFOA 高 5 倍,这表明长链 PFAAs 的生产和使用不断向短链同系物转变。就风险而言,除了 PFBA、PFPeA、PFHpA、PFHxA、PFOA、PFNA 和 PFBS 外,排水系统中单个 PFAAs 的污染都在人类健康的世界风险阈值内,而对于生态,单个 PFAAs 的浓度没有超过美国、加拿大、欧盟(EU)、意大利、澳大利亚和新西兰的生态风险阈值,除了 PFSAs,其检测到的单个浓度明显高于欧盟、澳大利亚和新西兰的 PFSAs 指南分别为 0.002μg/L、0.00047μg/L、0.00065μg/L、0.00013μg/L 和 0.00023μg/L,这可能对区域生态系统和人口造成慢性风险。