Quantitative risk assessment of the polycyclic aromatic hydrocarbons dietary exposure from edible fats and oils in China.
- Author:
Mengsi CAO
1
;
Jun WANG
;
Lishi ZHANG
;
Weixing YAN
Author Information
- Publication Type:Journal Article
- MeSH: Adolescent; Adult; Child; Child, Preschool; China; Chromatography, High Pressure Liquid; Diet; Environmental Exposure; Fats; chemistry; Female; Food Safety; Humans; Male; Plant Oils; chemistry; Polycyclic Aromatic Hydrocarbons; analysis; Risk Assessment; Tandem Mass Spectrometry; Young Adult
- From: Chinese Journal of Preventive Medicine 2016;50(2):163-167
- CountryChina
- Language:Chinese
-
Abstract:
OBJECTIVETo assess the quantitative risk of the polycyclic aromatic hydrocarbons (PAHs) dietary exposure from edible fats and oils in China.
METHODSOne hundred samples of edible fats and oils were collected from the supermarkets and the farmers markets in 11 provinces of China from December in 2013 to May in 2014. Then they were tested for EU15+1 PAHs (16 PAHs were controlled in priority by European Food Safety Authority) by two test methods which were QuECHERS-GC-MS-MS and GPC-HPLC-FLD. Data of PAHs concentration and edible fats and oils consumption which were from Chinese National Nutrition and Health Survey in 2002 were combined to evaluate carcinogenic risk of PAHs in edible fats and oils by the method of margin of exposure (MOE). In this process, we divided the population into 6 groups, namely male adults (older than 18 years old), female adults (older than 18), male youths (13-17), female youths (13-17), school-agers (6-12) and preschoolers (2-5), and thought carcinogenicity as the critical toxicity end point of PAHs. Two quantitative risk assessment methods, i.e. point assessment and probability assessment, were used to evaluate the dietary exposure and MOEs.
RESULTSEU15+1 PAHs in one of 100 samples were not detected, other samples were polluted in different degrees; the detection rates were 3%-98% and the average contents were 0.26-3.26 μg/kg. The results of PAHs dietary exposure from both of point assessment and probability assessment were the same. The average exposures of PAH8 were as the following: male adults were 10.03 and (9.34 ± 12.61) ng·kg(-1)·d(-1)(The former was from point assessment and the latter from probability assessment, the same below), female adults were 9.95 and (9.60 ± 15.04) ng · kg(-1)·d (-1), male youths were 11.09 and (10.84 ± 16.54) ng·kg(-1)·d(-1), female youths were 10.06 and (9.58 ± 12.87) ng·kg(-1)·d(-1),school-agers were 15.29 and (15.62 ± 25.54) ng·kg(-1)·d(-1), preschoolers were 19.27 and (19.22 ± 28.91) ng·kg(-1)·d(-1). MOEs of mean and 50% exposure levels in different group of people were more than 10,000, while MOEs of 95% exposure levels in school-agers and preschoolers were less than 10,000.
CONCLUSIONFor general consumers, the health risk of PAHs exposure is very low. However, for high-end consumers (95% exposure level) from the sensitive groups (school-ager and preschooler) has a potential health risk.