Source apportionment of polychlorinated biphenyls in the sediment of the Newtown Creek superfund site.

Polychlorinated biphenyls (PCBs) are a primary contaminant of potential concern at the Newtown Creek superfund site. Measurements of PCBs in hundreds of samples of sediment (surface and cores) within Newtown Creek and at nearby reference locations were obtained from the Remedial Investigation (RI) databases. This data set was analyzed using Positive Matrix Factorization (PMF). A weight-of-evidence approach was used to attribute the PMF-generated fingerprints to sources. The PMF analysis generated eight factors (fingerprints or sources) that represent primary sources, such as Aroclors, as well as secondary sources, including the East River and Combined Sewer Outfalls (CSOs). In addition to the high-production volume Aroclors (1016/1242, 1248, 1254, and 1260), some less-widely used Aroclors (1232 and 1268) were found in Newtown Creek sediment. Aroclor 1268 is disproportionately abundant in the deepest sediments, while PCBs likely from CSOs are relatively more abundant in surface sediment.

Sources of polychlorinated biphenyls to Upper Hudson River fish post-dredging.

Polychlorinated biphenyls (PCBs) are persistent, bioaccumulative, and toxic chemicals that are the dominant contaminant in the Upper Hudson River (UHR) in New York State where two General Electric (GE) plants historically discharged PCBs to the river. Portions of the UHR were dredged from 2009 to 2015 to address PCB contamination. In 2017, the first post-dredging survey of yearling feeder fish and sediment PCB contamination was conducted to establish a baseline for the recovery of the river. Prior analysis of the sediment data from the 2017 survey indicated that ∼2% of the PCBs in the surface sediment were higher in molecular weight than the formulation used by GE and therefore arose from non-GE sources. In this work, the fish PCB data from the 2017 survey were analyzed using Positive Matrix Factorization (PMF). Empirical Bayesian Kriging (EBK) was used to estimate PCB concentrations in the sediment at the locations where fish were collected. The results suggest that PCBs that are the products of microbial dechlorination bioaccumulate in the fish and represent 7% of the PCB mass in the fish data set. Further, the results suggest that about 13% of the PCBs in the fish may have come from non-GE sources. This is higher than the percentage of non-GE PCBs in the sediment, but can be explained by the higher molecular weight of the non-GE mixture which causes it to bioaccumulate more effectively than GE PCBs. Concentrations of the non-GE PCBs averaged about 240 ppb wet weight (whole body) in yearling feeder fish. The remedial goals range from 50 to 400 ppb ww in fillet for fish including piscivorous species that are likely to have higher PCB concentrations than feeder fish.

Comparison of a novel profile method to standard chamber methods for measurement of sediment oxygen demand.

A methodology is presented to determine the impact of flow rate upon sediment oxygen demand (SOD) based upon dissolved oxygen transport through the logarithmic boundary layer in stream systems. Previous work has used profile methodology to estimate atmospheric fluxes of pollutants from sediment, and similar principles are applied in this study. Chamber and profile SOD measurements were collected on July 21, 2009 in the Millstone River in Hillsborough, NJ and on July 22 and 28, 2009 in the Lawrence Brook in Milltown, NJ. The two systems were installed 2 meters apart laterally across the stream to measure SOD simultaneously. A total of 7 chamber measurements and 50 profile measurements were collected over 3 days. Chamber SOD measurements in the Lawrence Brook varied from 3.6 to 13.0 g/m(2)/day and had a mean of 5.0 g/m(2)/day. Concurrent profile SOD measurements varied from 1.3 to 13.5 g/m(2)/day and had a mean of 7.16 g/m(2)/day. In the Millstone River, the single chamber measurement was 4.6 g/m(2)/day while the profile measurements varied from 0.5 to 2.2 g/m(2)/day with a mean of 1.32 g/m(2)/day. The measurements made via the profile and chamber methods were found to be in relative agreement. A linear relationship between friction velocity and stream SOD was observed.

Temperature effects on tubificid worms and their relation to sediment oxygen demand.

Sediment samples were collected from the Dead River in New Jersey and tested in the laboratory under two temperature conditions, 4 degrees C and 20 degrees C. The study was conducted to determine the effect of worm density on the sediment oxygen demand (SOD) rate and if temperature affects the ability for tubificid worms to deplete dissolved oxygen (DO) from the overlying stream water. The study showed that the DO concentration was affected by tubificid worm density and that higher temperature increased the metabolic activity of the worms.