Polycyclic aromatic hydrocarbons are enriched but bioaccessibility reduced in brownfield soils adhered to human hands

被引:44
|
作者
Siciliano, Steven D. [1 ,2 ]
Laird, B. D. [1 ,3 ]
Lemieux, C. L. [4 ]
机构
[1] Univ Saskatchewan, Dept Soil Sci, Saskatoon, SK S7N 5A8, Canada
[2] Univ Saskatchewan, Toxicol Grp, Saskatoon, SK S7N 5B3, Canada
[3] Univ Saskatchewan, Interdisciplinary Grad Program Toxicol, Saskatoon, SK S7N 5A8, Canada
[4] Hlth Canada, Mech Studies Div, Res & Radiat Directorate, Ottawa, ON K1A 0K9, Canada
基金
加拿大自然科学与工程研究理事会;
关键词
Polycyclic aromatic hydrocarbon; Arctic brownfields; Ingestion; Humans; Risk assessment; PERSISTENT ORGANIC POLLUTANTS; INTESTINAL MICROBIAL ECOSYSTEM; PARTICLE-SIZE; ORAL BIOACCESSIBILITY; CONTAMINATED SITES; SORPTION STRENGTH; CURRENT STANDARDS; HUMAN EXPOSURE; CANADA MEASURE; URBAN SOILS;
D O I
10.1016/j.chemosphere.2010.04.061
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
The health risk associated with exposure to urban brownfields is often driven by the incidental ingestion of soil by humans. Recent evidence found that humans likely ingest the fraction of soil that passes a 45-mu m sieve, which is the particle size adhered to the hands. We evaluated if PAH concentrations were enriched in this soil fraction compared to the bulk soil and if this enrichment lead to an increase in bio-accessability and thus an increase in incremental lifetime cancer risk for exposed persons. Soils (n = 18) with PAH concentrations below the current Canadian soil quality guidelines for human health were collected from an Arctic urban site and were sieved to pass a 45-mu m sieve. Soil PAH profiles were measured and bioaccessibility was assessed using the Simulator of the Human Intestinal Microbial Ecosystem (SHIME). PAHs were significantly enriched in the <45 mu m size fraction (3.7-fold) and this enrichment could be predicted according to the fugacity capacity of soil (Enrichment = 2.18-0.055Z(soil), r(2) = 0.65, p < 0.001). PAH release in the stomach and small intestine compartments of the SHIME was low (8%) and could not be predicted by PAH concentrations in 45-mu m sieved soil. In fact, PAH release in the SHIME was lower from the <45 mu m size fraction despite the fact that this fraction had higher levels of PAHs than the bulk soil. We postulate that this occurs because PAHs adsorbed to soil did not reach equilibrium with the small intestinal fluid. In contrast, PAH release in the colonic compartment of the SHIME reached equilibrium and was linked to soil concentration. Bioaccessibility in the SHIME colon could be predicted by the ratio of fugacity capacity of soil to water for a PAH (Bioaccessibilty = 0.15e((-6.4 x 10E-7) (Z-soil/Zwater)), r(2) = 0.53, p < 0.01). The estimated incremental lifetime cancer risk was significantly greater for the <45 mu m soil fraction compared to the bulk fraction: however, when bioaccessible PAH concentrations in a simulated small intestine were used in the risk assessment calculations, cancer risk was slightly lower in the <45 mu m soil fraction for these soils. Our results highlight the importance of using a small soil size fraction, e.g. 45 mu m, for contaminated site human health risk assessment. However, further work is needed to estimate the bioavailability of this size fraction in an in vivo model and to assess the correlation between in vitro and in vivo gastrointestinal models. (C) 2010 Elsevier Ltd. All rights reserved.
引用
收藏
页码:1101 / 1108
页数:8
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