4.5 Article

Characteristics of PAHs in farmland soil and rainfall runoff in Tianjin, China

Journal

ENVIRONMENTAL MONITORING AND ASSESSMENT
Volume 189, Issue 11, Pages -

Publisher

SPRINGER
DOI: 10.1007/s10661-017-6290-y

Keywords

Polycyclic aromatic hydrocarbons (PAHs); Rainfall runoff; Farmland; Leaching

Funding

  1. National Natural Science Foundation of China [21477138]
  2. State Key Laboratory Environmental Chemistry and Ecotoxicology, Research Center for Eco-Environmental Sciences, Chinese Academy of Sciences [KF2016-12]
  3. China Postdoctoral Science Foundation [2016 M602210]

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Rainfall runoff can remove certain amounts of pollutants from contaminated farmland soil and result in a decline in water quality. However, the leaching behaviors of polycyclic aromatic hydrocarbons (PAHs) with rainfall have been rarely reported due to wide variations in the soil compositions, rainfall conditions, and sources of soil PAHs in complex farmland ecosystems. In this paper, the levels, spatial distributions, and composition profiles of PAHs in 30 farmland soil samples and 49 rainfall-runoff samples from the Tianjin region in 2012 were studied to investigate their leaching behaviors caused by rainfall runoff. The contents of the Sigma(16)PAHs ranged from 58.53 to 3137.90 mu g/kg in the soil and 146.58 to 3636.59 mu g/L in the runoff. In total, most of the soil sampling sites (23 of 30) were contaminated, and biomass and petroleum combustion were proposed as the main sources of the soil PAHs. Both the spatial distributions of the soil and the runoff PAHs show a decreasing trend moving away from the downtown, which suggested that the leaching behaviors of PAHs in a larger region during rainfall may be mainly affected by the compounds themselves. In addition, 4- and 5-ring PAHs are the dominant components in farmland soil and 3- and 4-ring PAHs dominate the runoff. Comparisons of the PAH pairs and enrichment ratios showed that acenaphthylene, acenaphthene, benzo[a]anthracene, chrysene, and fluoranthene were more easily transferred into water systems from soil than benzo[b]fluoranthene, benzo[k]fluoranthene, benzo[ghi]perylene, and indeno[123-cd]pyrene, which indicated that PAHs with low molecular weight are preferentially dissolved due to their higher solubility compared to those with high molecular weight.

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