School of Resources and Environmental Engineering, Hefei University of Technology, 193 Tunxi Road, Hefei, 230009, China.
School of Environmental Science and Engineering, Shanghai Jiao Tong University, 800 Dongchuan Road, Shanghai, 200240, China.
Environ Sci Pollut Res Int. 2022 Jan;29(5):6449-6462. doi: 10.1007/s11356-021-16142-0. Epub 2021 Aug 27.
The resource, environment, and ecological value of drinking reservoirs have received widespread concerns due to the pollution of persistent organic pollutants such as polycyclic aromatic hydrocarbons (PAHs). Therefore, we comprehensively studied the occurrence, source, distribution, and risk assessment of representative PAHs in Fengshuba Reservoir (FSBR) (large drinking reservoir, China). The total concentrations of 16 USEPA PAHs in the water phase, porewater phase, sediment phase, and soil phase were in ranges of 109.72-393.19 ng/L, 5.75-35.15 μg/L, 364.4-743.71 μg/kg, and 367.81-639.89 μg/kg, respectively. The naphthalene (Nap) was the dominant PAHs in the water phase, while it was Nap and phenanthrene (Phe) in porewater, sediment, and soil phase. The main sources of PAHs in FSBR were biomass combustion. Redundancy analysis indicated that the NTU, NO, NH, Chl-α, and IC were the dominant factors influencing the PAH distribution in water phase, and the PAHs in sediment phase was affected by T and NO. Pseudo-partitioning coefficients indicated that the PAHs in the porewater phase were more likely to migrate to the sediment phase. Risk assessment indicated that the PAHs both in the water and sediment phases were generally in a low-risk state, while the PAHs in the soil phase were in a moderate-risk state, and the Nap was in a high-risk state, and exposure to the PAHs in FSBR through drinking and skin exposure had little impact on consumers' health. In summary, Nap could be used as a key indicator to evaluate the existence and potential risk of PAHs in FSBR.
由于多环芳烃(PAHs)等持久性有机污染物的污染,饮用水库的资源、环境和生态价值受到了广泛关注。因此,我们综合研究了丰水坝(FSBR)(中国大型饮用水库)中代表性 PAHs 的发生、来源、分布和风险评估。水相、孔隙水相、沉积物相和土壤相中的 16 种 USEPA PAHs 的总浓度范围分别为 109.72-393.19ng/L、5.75-35.15μg/L、364.4-743.71μg/kg 和 367.81-639.89μg/kg。萘(Nap)是水相中的主要 PAHs,而在孔隙水、沉积物和土壤相中则是 Nap 和菲(Phe)。FSBR 中 PAHs 的主要来源是生物质燃烧。冗余分析表明,NTU、NO、NH、Chl-α 和 IC 是影响水相 PAH 分布的主要因素,而沉积物相中 PAHs 受 T 和 NO 的影响。拟分配系数表明,孔隙水相中 PAHs 更有可能迁移到沉积物相中。风险评估表明,水相和沉积物相中的 PAHs 总体处于低风险状态,而土壤相中的 PAHs 处于中风险状态,Nap 处于高风险状态,通过饮用和皮肤接触 FSBR 中的 PAHs 对消费者健康的影响较小。综上所述,Nap 可作为评价 FSBR 中 PAHs 存在和潜在风险的关键指标。