Matrix solid-phase microextraction for measuring freely dissolved concentrations and chemical activities of PAHs in sediment cores from the western Baltic Sea
“…Immediately after the POM strips were removed, 50:10:40 ml heptane:acetone:water was added to the samples along with an internal standard of five 13 C-PCBs and six d-PAHs. Sediments were reflux extracted, and the extract was reduced and purified by successive solvent exchange with dimethylformamide followed by cyclohexane and eluted over a deactivated silica column [32].…”
Section: Sediment Concentration Of Pahs and Pcbsmentioning
confidence: 99%
“…However, for organic contaminants, it has been shown that freely dissolved sediment porewater concentrations, C pw (mol/L pw ), are more appropriate for such assessments than C sed , because C pw is more closely linked with toxic endpoints and bioaccumulation [9][10][11][12]. To date, however, sediment core studies measuring C pw are only just emerging [13], most likely because methods needed for determining C pw in thin sediment layers have only recently been developed [14,15]. One implication of this is that, even if C sed levels are found to be decreasing with time as a result of burial by cleaner, recent sediments, this does not by itself imply that environmental recovery is occurring, insofar as there may be no change or an increase in C pw .…”
Contaminant levels in urban harbor sediments vary with contaminant emission levels, sedimentation rates, and sediment resuspension processes such as propeller wash. Levels of polycyclic aromatic hydrocarbons (PAHs) and polychlorinated biphenyls (PCBs) are decreasing in many urban harbors, as heavily contaminated sediments that accumulated during past decades are being buried by less-contaminated sediments. However, PAHs and PCBs remain a concern in areas where burial is slow or resuspension processes re-expose heavily contaminated older layers. Chronostratigraphic sediment core studies typically characterize contaminant level histories by using total sediment concentrations, C(sed) , and do not determine the freely dissolved porewater concentrations, C(pw) , which provide a better measure of bioavailability. Here both C(sed) and C(pw) profiles were established for PAHs and PCBs in dated sediment cores from diverse areas of Oslo Harbor, Norway. Sediment-porewater partitioning profiles were established alongside profiles of various sorbing carbonaceous phases, including total organic carbon (TOC), black carbon, and diverse carbonaceous geosorbents identified by petrographic analysis. Stratigraphic trends in carbonaceous phases and C(sed) could be associated with different industrial epochs: hydropower (post-1960, approximately), manufactured gas (∼1925-1960), coal (∼1910-1925), and early industry (∼1860-1910). Partitioning was highly variable and correlated best with the TOC. Hydropower-epoch sediments exhibit decreasing C(sed) with time and a relatively strong sorption capacity compared with the manufactured-gas epoch. Sediments from the manufactured-gas epoch exhibit substantial PAH and metal contamination, large amounts of coke and char, and a low sorption capacity. Reexposure of sediments of this epoch increases risks to local benthic species. Implications on natural recovery as a sediment management strategy are discussed.
“…Immediately after the POM strips were removed, 50:10:40 ml heptane:acetone:water was added to the samples along with an internal standard of five 13 C-PCBs and six d-PAHs. Sediments were reflux extracted, and the extract was reduced and purified by successive solvent exchange with dimethylformamide followed by cyclohexane and eluted over a deactivated silica column [32].…”
Section: Sediment Concentration Of Pahs and Pcbsmentioning
confidence: 99%
“…However, for organic contaminants, it has been shown that freely dissolved sediment porewater concentrations, C pw (mol/L pw ), are more appropriate for such assessments than C sed , because C pw is more closely linked with toxic endpoints and bioaccumulation [9][10][11][12]. To date, however, sediment core studies measuring C pw are only just emerging [13], most likely because methods needed for determining C pw in thin sediment layers have only recently been developed [14,15]. One implication of this is that, even if C sed levels are found to be decreasing with time as a result of burial by cleaner, recent sediments, this does not by itself imply that environmental recovery is occurring, insofar as there may be no change or an increase in C pw .…”
Contaminant levels in urban harbor sediments vary with contaminant emission levels, sedimentation rates, and sediment resuspension processes such as propeller wash. Levels of polycyclic aromatic hydrocarbons (PAHs) and polychlorinated biphenyls (PCBs) are decreasing in many urban harbors, as heavily contaminated sediments that accumulated during past decades are being buried by less-contaminated sediments. However, PAHs and PCBs remain a concern in areas where burial is slow or resuspension processes re-expose heavily contaminated older layers. Chronostratigraphic sediment core studies typically characterize contaminant level histories by using total sediment concentrations, C(sed) , and do not determine the freely dissolved porewater concentrations, C(pw) , which provide a better measure of bioavailability. Here both C(sed) and C(pw) profiles were established for PAHs and PCBs in dated sediment cores from diverse areas of Oslo Harbor, Norway. Sediment-porewater partitioning profiles were established alongside profiles of various sorbing carbonaceous phases, including total organic carbon (TOC), black carbon, and diverse carbonaceous geosorbents identified by petrographic analysis. Stratigraphic trends in carbonaceous phases and C(sed) could be associated with different industrial epochs: hydropower (post-1960, approximately), manufactured gas (∼1925-1960), coal (∼1910-1925), and early industry (∼1860-1910). Partitioning was highly variable and correlated best with the TOC. Hydropower-epoch sediments exhibit decreasing C(sed) with time and a relatively strong sorption capacity compared with the manufactured-gas epoch. Sediments from the manufactured-gas epoch exhibit substantial PAH and metal contamination, large amounts of coke and char, and a low sorption capacity. Reexposure of sediments of this epoch increases risks to local benthic species. Implications on natural recovery as a sediment management strategy are discussed.
“…Horstmann and McLachlan (1992) developed a ''fugacity meter'' for vegetation samples. Mayer and colleagues have pioneered the use of solid-phase microextraction techniques or equilibrium sampling methods for measuring chemical activities in sediments and soils (Reichenberg et al 2010;Witt et al 2009). The fundamental differences between accessible quantity of chemical and chemical activity has been discussed by Reichenberg and Mayer (2006), especially with respect to bioavailability and the potential for toxic effects.…”
Section: Direct Measurement Of Environmental Activitiesmentioning
confidence: 99%
“…This degree of accuracy obtained using activity is often sufficient for screening level assessments and for identifying the need for more detailed analysis. Witt et al (2009) have used chemical activity to assess the toxic potential of PAH mixtures in marine sediments. A test of the Ferguson Principle for a number of chemicals is to plot log LC50 versus log liquid or subcooled liquid solubility in water or in air.…”
It is suggested that chemical activity in environmental media can serve as an integrating concept for holistic evaluations of contaminants, including their fate and effects. In support of this assertion, information underlying the thermodynamic principles and the relationships between monitored and modeled concentrations and activities are presented. The toxicological significance of activity is discussed, with emphasis on substances that exert baseline narcosis. Illustrations are given of the application of activity using models and monitoring data for chemical risk assessment and management. It is argued that the proximity of prevailing multimedia environmental activities to activities causing toxic effects is a particularly insightful metric of environmental contamination for both narcotics and reactive toxic substances.
“…It has frequently been applied to marine sediments (Yang et al ., 2007;Trimble et al ., 2008;Witt et al ., 2009) and provides a matrix-and chemical-independent estimation of bioaccumulation for hydrophobic contaminants without extensive biotransformation (You et al ., 2006). For heavy metals, modelling approaches are of increasing interest when predicting potential risk due to metal concentration in the environment, the most accepted being the biotic ligand model.…”
Section: Organisms Can Render Contaminants Bioavailablementioning
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