Applied Chemistry Department, Federal University Dutsin-Ma, Katsina, Nigeria.
Chemistry Department, Ahmadu Bello University, Zaria, Kaduna, Nigeria.
Environ Geochem Health. 2023 Jul;45(7):5415-5439. doi: 10.1007/s10653-023-01542-7. Epub 2023 Mar 28.
The research aims to evaluate the seasonal differences in the distribution, source, and risks of water-contaminated PAHs. The PAHs were extracted by the liquid-liquid method and analyzed with GC-MS, and a total of eight PAHs were detected. There was a percentage increase in the average concentration of the PAHs from the wet to the dry season in the range of 20 (Anthracene)-350 (Pyrene)%. Total PAHs (∑PAHs) range from 0.31 to 1.23 mg/l in the wet period and from 0.42 to 1.96 mg/l in the dry period. The distribution of the average PAHs in mg/l showed that Fluoranthene ≤ Pyrene < Acenaphthene < Fluorene < Phenanthrene < Acenaphthylene < Anthracene < Naphthalene in wet period and while Fluoranthene < Acenaphthene < Pyrene < Fluorene < Phenanthrene < Acenaphthylene < Anthracene < Naphthalene in the dry period. The children were exposed to non-carcinogenic risk through non-dietary ingestion due to the accumulative effect (HI) of the PAHs in the dry period. Furthermore, the naphthalene was responsible for ecological and carcinogenic risk in the wet period, while the fluorene, phenanthrene, and anthracene were responsible for ecological and carcinogenic risk in the dry period. However, while adults and children are both susceptible to carcinogenic risk through the oral channel during the dry period, only children are susceptible to non-carcinogenic risk through this pathway. The multivariate statistical analysis revealed the influence of physicochemical parameters on the detected PAHs and also showed the PAHs' sources to be mainly combustion, pyrolysis, and vehicular emission.
本研究旨在评估受污染多环芳烃(PAHs)在分布、来源和风险方面的季节性差异。采用液液萃取法提取 PAHs,并用 GC-MS 进行分析,共检测到八种 PAHs。在干湿两季,PAHs 的平均浓度呈 20%(蒽)至 350%(芘)的递增趋势。湿季总多环芳烃(∑PAHs)浓度范围为 0.31 至 1.23mg/L,干季为 0.42 至 1.96mg/L。以毫克/升为单位的平均 PAHs 分布表明,在湿季,荧蒽≦芘<苊烯<芴<菲<蒽<苊<萘,而在干季,荧蒽<苊烯<芘<芴<菲<蒽<苊<萘。儿童在干季因 PAHs 的累积效应(HI),通过非饮食摄入途径受到非致癌风险的影响。此外,在湿季,萘导致生态和致癌风险,而在干季,芴、菲和蒽则导致生态和致癌风险。然而,在干季,成人和儿童都通过口服途径易受致癌风险影响,而只有儿童通过这一途径易受非致癌风险影响。多变量统计分析揭示了理化参数对所检测到的 PAHs 的影响,并表明 PAHs 的来源主要是燃烧、热解和车辆排放。