4.7 Article

Optimized Derivation of Predicted No-Effect Concentrations (PNECs) for Eight Polycyclic Aromatic Hydrocarbons (PAHs) Using HC10 Based on Acute Toxicity Data

Journal

TOXICS
Volume 11, Issue 7, Pages -

Publisher

MDPI
DOI: 10.3390/toxics11070563

Keywords

two-parameter nonlinear functions; cumulative probability; toxicity on multi-species; median effect concentration; no observed effect concentration; aquatic organisms

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In this study, the application of the species sensitivity distribution (SSD) for ecological risk assessment of persistent organic pollutants (POPs), specifically polycyclic aromatic hydrocarbons (PAHs), is improved by exploring the use of acute SSD curves to derive chronic predicted no-effect concentrations (PNECs) and calculating PNECs using HC10 instead of HC5. The results show that the chronic PNEC for PAHs can be estimated by multiplying the acute PNEC by 0.1 and the assessment factor for HC10 is 10. The obtained chronic PNECs based on acute HC10 values for specific PAHs are reported.
For persistent organic pollutants, a concern of environmental supervision, predicted no-effect concentrations (PNECs) are often used in ecological risk assessment, which is commonly derived from the hazardous concentration of 5% (HC5) of the species sensitivity distribution (SSD). To address the problem of a lack of toxicity data, the objectives of this study are to propose and apply two improvement ideas for SSD application, taking polycyclic aromatic hydrocarbons (PAHs) as an example: whether the chronic PNEC can be derived from the acute SSD curve; whether the PNEC may be calculated by HC10 to avoid solely statistical extrapolation. In this study, the acute SSD curves for eight PAHs and the chronic SSD curves for three PAHs were constructed. The quantity relationship of HC(5)s between the acute and chronic SSD curves was explored, and the value of the assessment factor when using HC10 to calculate PNEC was derived. The results showed that, for PAHs, the chronic PNEC can be estimated by multiplying the acute PNEC by 0.1, and the value of the assessment factor corresponding to HC10 is 10. For acenaphthene, anthracene, benzo[a]pyrene, fluoranthene, fluorene, naphthalene, phenanthrene, and pyrene, the chronic PNECs based on the acute HC(10)s were 0.8120, 0.008925, 0.005202, 0.07602, 2.328, 12.75, 0.5731, and 0.05360 & mu;g/L, respectively.

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