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施用城市生物固体后土壤中全氟化学品的出现和归宿。

Occurrence and fate of perfluorochemicals in soil following the land application of municipal biosolids.

机构信息

Colorado School of Mines , Golden, Colorado 80401, United States.

出版信息

Environ Sci Technol. 2011 Oct 1;45(19):8106-12. doi: 10.1021/es103903d. Epub 2011 Mar 29.

Abstract

The recent implementation of soil and drinking water screening guidance values for two perfluorochemicals (PFCs), perfluorooctanoate (PFOA) and perfluorooctane sulfonate (PFOS) by the U.S. Environmental Protection Agency (EPA), reflects the growing concerns regarding the presence of these persistent and bioaccumulative chemicals in the natural environment. Previous work has established the potential risk to the environment from the land application of industrially contaminated biosolids, but studies focusing on environmental risk from land application of typical municipal biosolids are lacking. Thus, the present study investigated the occurrence and fate of PFCs from land-applied municipal biosolids by evaluating the levels, mass balance, desorption, and transport of PFCs in soils receiving application of municipal biosolids at various loading rates. This study is the first to report levels of PFCs in agricultural soils amended with typical municipal biosolids. PFOS was the dominant PFC in both biosolids (80-219 ng/g) and biosolids-amended soil (2-483 ng/g). Concentrations of all PFCs in soil increased linearly with increasing biosolids loading rate. These data were used to develop a model for predicting PFC soil concentrations in soils amended with typical municipal biosolids using cumulative biosolids loading rates. Mass balance calculations comparing PFCs applied vs those recovered in the surface soil interval indicated the potential transformation of PFC precursors. Laboratory desorption experiments indicated that the leaching potential of PFCs decreases with increasing chain length and that previously derived organic-carbon normalized partition coefficients may not be accurate predictors of the desorption of long-chain PFCs from biosolids-amended soils. Trace levels of PFCs were also detected in soil cores from biosolids-amended soils to depths of 120 cm, suggesting potential movement of these compounds within the soil profile over time and confirming the higher transport potential for short-chain PFCs in soils amended with municipal biosolids.

摘要

美国环境保护署(EPA)最近实施了两项全氟化学品(PFCs)——全氟辛酸(PFOA)和全氟辛烷磺酸(PFOS)的土壤和饮用水筛选指导值,这反映出人们对这些持久性和生物累积性化学物质在自然环境中存在的日益关注。先前的工作已经确定了土地应用工业污染生物固体对环境的潜在风险,但缺乏针对土地应用典型城市生物固体的环境风险研究。因此,本研究通过评估接收不同施用量的城市生物固体的土壤中 PFCs 的水平、质量平衡、解吸和迁移,来研究 PFCs 从土地应用城市生物固体中的出现和归宿。本研究首次报道了用典型城市生物固体改良的农业土壤中 PFCs 的水平。在生物固体(80-219ng/g)和生物固体改良土壤(2-483ng/g)中,PFOS 都是主要的 PFC。所有 PFCs 在土壤中的浓度都随生物固体施用量的增加呈线性增加。这些数据用于开发一个模型,以便使用累积生物固体施用量率来预测用典型城市生物固体改良的土壤中的 PFC 土壤浓度。比较施入与表层土壤间隔中回收的 PFCs 的质量平衡计算表明,PFC 前体可能发生了转化。实验室解吸实验表明,PFCs 的淋溶潜力随链长的增加而降低,先前推导的有机碳归一化分配系数可能无法准确预测长链 PFCs 从生物固体改良土壤中的解吸。在生物固体改良土壤的土壤芯中还检测到痕量的 PFCs,深度达 120cm,这表明这些化合物在土壤剖面中的潜在迁移,并证实了短链 PFCs 在施用城市生物固体的土壤中的更高迁移潜力。

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