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Determination of Arsenic Species in Ophiocordyceps sinensis from Major Habitats in China by HPLC-ICP-MS and the Edible Hazard Assessment

This study sought to determine the concentration and distribution of arsenic (As) species in Ophiocordyceps sinensis (O. sinensis), and to assess its edible hazard for long term consumption. The total arsenic concentrations, measured through inductively coupled plasma mass spectrometry (ICP-MS), ran...

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Detalles Bibliográficos
Autores principales: Guo, Lian-Xian, Zhang, Gui-Wei, Wang, Jia-Ting, Zhong, Yue-Ping, Huang, Zhi-Gang
Formato: Online Artículo Texto
Lenguaje:English
Publicado: MDPI 2018
Materias:
Acceso en línea:https://www.ncbi.nlm.nih.gov/pmc/articles/PMC6100492/
https://www.ncbi.nlm.nih.gov/pubmed/29701658
http://dx.doi.org/10.3390/molecules23051012
Descripción
Sumario:This study sought to determine the concentration and distribution of arsenic (As) species in Ophiocordyceps sinensis (O. sinensis), and to assess its edible hazard for long term consumption. The total arsenic concentrations, measured through inductively coupled plasma mass spectrometry (ICP-MS), ranged from 4.00 mg/kg to 5.25 mg/kg. As determined by HPLC-ICP-MS, the most concerning arsenic species—AsB, MMA(V), DMA(V), As(V), and As(Ш)—were either not detected (MMA(V) and DMA(V)) or were detected as minor As species (AsB: 1.4–2.9%; As(V): 1.3–3.2%, and As(Ш): 4.1–6.0%). The major components were a cluster of unknown organic As (uAs) compounds with As(Ш), which accounted for 91.7–94.0% of the As content. Based on the H(2)O(2) test and the chromatography behavior, it can be inferred that, the uAs might not be toxic organic As. Estimated daily intake (EDI), hazard quotient (HQ), and cancer risk (CR) caused by the total As content; the sum of inorganic As (iAs) and uAs, namely i+uAs; and iAs exposure from long term O. sinensis consumption were calculated and evaluated through equations from the US Environmental Protection Agency and the uncertainties were analyzed by Monte-Carlo Simulation (MCS). EDI(total As) and EDI(i+uAs) are approximately ten times more than EDI(iAs); HQ(total) (As) and HQ(i+u)(As) > 1 while HQ(i)(As) < 1; and CR(total As) and CR(i+uAs) > 1 × 10(−4) while CR(iAs) < 1 × 10(−4). Thus, if the uAs is non-toxic, there is no particular risk to local consumers and the carcinogenic risk is acceptable for consumption of O. sinensis because the concentration of toxic iAs is very low.