Abstract:Polymers are increasingly applied for the enrichment of hydrophobic organic chemicals (HOCs) from various types of samples and media in many analytical partitioning-based measuring techniques. We propose using polymers as a reference partitioning phase and introduce polymer-polymer partitioning as the basis for a deeper insight into partitioning differences of HOCs between polymers, calibrating analytical methods, and consistency checking of existing and calculation of new partition coefficients. Polymer-polym… Show more
“…In general, these silicone rubber-water partition coefficients are not very high but in agreement with reported/calculated logK p values of 3.71 ‡ . In general, lower logK pw have been reported for SSP silicone rubber than for AlteSil™ (Gilbert et al 2016). This is also the case for TDBrPP.…”
Section: Polymer-water Partition Coefficient Kpw For Tdbrppmentioning
The flame-retardant tris(2,3-dibromopropyl) phosphate (TDBrPP) was in the 1970s banned for uses in textiles that may be in contact with the skin, owing to strong suspicions that the substance was a human carcinogen. The substance is looked for but rarely detected in samples from the built and natural environments, but there are indications that TDBrPP is still in use. Here, we report the measurement of a polymer-water partition coefficient (K) for two types of silicone rubber (SR), allowing quantitative estimation of freely dissolved concentrations of TDBrPP by passive sampling in water. We found levels of 100 to 200 pg/L in two Arctic rivers that were sampled during a 2014-2015 survey of contamination using passive samplers in Norwegian and Russian rivers draining into the Barents Sea. We also report the widespread presence of other organophosphorus flame retardants in this survey of eight rivers that drain into the Barents Sea.
“…In general, these silicone rubber-water partition coefficients are not very high but in agreement with reported/calculated logK p values of 3.71 ‡ . In general, lower logK pw have been reported for SSP silicone rubber than for AlteSil™ (Gilbert et al 2016). This is also the case for TDBrPP.…”
Section: Polymer-water Partition Coefficient Kpw For Tdbrppmentioning
The flame-retardant tris(2,3-dibromopropyl) phosphate (TDBrPP) was in the 1970s banned for uses in textiles that may be in contact with the skin, owing to strong suspicions that the substance was a human carcinogen. The substance is looked for but rarely detected in samples from the built and natural environments, but there are indications that TDBrPP is still in use. Here, we report the measurement of a polymer-water partition coefficient (K) for two types of silicone rubber (SR), allowing quantitative estimation of freely dissolved concentrations of TDBrPP by passive sampling in water. We found levels of 100 to 200 pg/L in two Arctic rivers that were sampled during a 2014-2015 survey of contamination using passive samplers in Norwegian and Russian rivers draining into the Barents Sea. We also report the widespread presence of other organophosphorus flame retardants in this survey of eight rivers that drain into the Barents Sea.
“…Loading methods based on solvent evaporation have previously been used for passive dosing with halogenated and non-halogenated aromatic chemicals. 42,43 Also, recently Gilbert et al 44 loaded silicone polymers with PCBs using isooctane, which was thereaer allowed to evaporate. To conrm that all loading solvent had evaporated, the weight of dosing vials (n ¼ 9) containing 0.03 g of polymer was determined before loading and aer evaporation of the solvent.…”
Section: Chemical Analysismentioning
confidence: 99%
“…Hence, partition coefficients are polymer-specic as the content of different additives and llers (e.g. diatomaceous earth 44 ) may vary between suppliers and thus cause differences in partitioning properties. In an extensive review by DiFilippo et al, 56 it was concluded that improper measuring techniques were a main source of error for the K p-w and as opposed to Smedes et al, no signicant effect associated with the supplier of the polymers was found.…”
Environmental mixtures of chemicals consist of a countless number of compounds with unknown identity and quantity. Yet, chemical regulation is mainly built around the assessment of single chemicals. Existing frameworks for assessing the toxicity of mixtures require that both the chemical composition and quantity are known. Quantitative analyses of the chemical composition of environmental mixtures are however extremely challenging and resource-demanding. Bioassays may therefore serve as a useful approach for investigating the combined toxicity of environmental mixtures of chemicals in a cost-efficient and holistic manner. In this study, an unknown environmental mixture of bioavailable semi-hydrophobic to hydrophobic chemicals was sampled from a contaminated sediment in a coastal Baltic Sea area using silicone polydimethylsiloxane (PDMS) as an equilibrium passive sampler. The chemical mixture was transferred to a PDMS-based passive dosing system, and its applicability was demonstrated using green algae Tetraselmis suecica in a cell viability assay. The proportion of dead cells increased significantly with increasing exposure level and in a dose-response manner. At an ambient concentration, the proportion of dead cells in the population was nearly doubled compared to the control; however, the difference was non-significant due to high inter-replicate variability and a low number of replicates. The validation of the test system regarding equilibrium sampling, loading efficiency into the passive dosing polymer, stability of the mixture composition, and low algal mortality in control treatments demonstrates that combining equilibrium passive sampling and passive dosing is a promising tool for investigating the toxicity of bioavailable semi-hydrophobic and hydrophobic chemicals in complex environmental mixtures.
“…The accuracy of Kpw might explain a large fraction of the uncertainty in PSMs (Lydy et al, 2014) because accurate determination of high Kpw values for HOCs is challenging. Recently, Gilbert et al (2016) proposed to measure and use polymer-polymer partition coefficients for calibration, property evaluation, and data consistency tests of multiple passive samplers. This is a promising approach for the consistency test of sediment passive samplers because polymer-polymer partition coefficients can be much more accurately measured than polymer-water partition coefficients (Gilbert et al, 2016), primarily due to the fact that the error-prone measurement of low aqueous phase concentrations can be avoided.…”
Two sediment passive samplers, polyethylene (PE) and polyoxymethylene (POM), were compared and mutually validated for measuring freely dissolved concentrations (C) of polychlorinated biphenyls (PCBs) in sediment porewater. PE and POM strips in commonly used dimensions (30 and 76 μm in thickness, respectively) were exposed to sediment slurries for 28 d. The C values calculated using literature polymer-water partition coefficients were consistently higher for PE than for POM by a factor of 2 on average. Time series experiments over 96 d show that 28 d are sufficient for attaining partition equilibrium of PCBs for PE, whereas even 96 d may not be enough for POM. To gain additional insight, POM and PE strips were co-exposed to bovine serum albumin suspension spiked with PCBs. The POM/PE concentration ratios increased over 56 d, and the ratios at 28 d were in agreement with the POM-to-PE ratios of PCB concentrations from the 28-d sediment slurry experiments. This agreement suggests that the use of apparent POM-water partition coefficients (i.e., non-equilibrium concentration ratios) suitable for a 28-d exposure to sediment slurries may correct the non-attainment of equilibrium and could provide more accurate C values.
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