Passive sampling to quantify net partitioning of hydrophobic organic contaminants between the porewater and solid phase has advanced risk management for contaminated sediments. Direct porewater () measures represent the best way to predict adverse effects to biota. However, when the need arises to convert between solid-phase concentration () and , a wide variation in observed sediment-porewater partition coefficients () is observed due to intractable complexities in binding phases. We propose a stochastic framework in which a given is mapped to an estimated range of through variability in passive sampling-derived relationships. This mapping can be used to pair estimated with biological effects data or inversely to translate a measured or assumed to an estimated . We apply the framework to both an effects threshold for polycyclic aromatic hydrocarbon (PAH) toxicity and an aggregate adverse impact on an assemblage of species. The stochastic framework is based on a "bioavailability ratio" (BR), which reflects the extent to which potency-weighted, aggregate PAH partitioning to the solid-phase is greater than that predicted by default, -based values. Along a continuum of , we use the BR to derive an estimate for the probability that will exceed a threshold. By explicitly describing the variability of K and BR, estimates of risk posed by sediment-associated contaminants can be more transparent and nuanced.

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http://www.ncbi.nlm.nih.gov/pmc/articles/PMC11137493PMC
http://dx.doi.org/10.1021/acs.est.1c01537DOI Listing

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