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The toxicity of oil sands process-affected water (OSPW) has been primarily attributed to polar organic constituents, including naphthenic acid fraction components (NAFCs). Our objective was to assess the toxicity of NAFCs derived from fresh and aged OSPW, as well as commercial naphthenic acid (NA) mixtures. Exposures were conducted with three aquatic species: Hyalella azteca (freshwater amphipod), Vibrio fischeri (marine bacterium, Microtox ® assay), and Lampsilis cardium (freshwater mussel larvae (glochidia)). Commercial NAs were more toxic than NAFCs, with differences of up to 30-, 4-, and 120-fold for H. azteca , V. fischeri , and L. cardium , respectively, demonstrating that commercial NAs are not reliable surrogates for assessing the toxicity of NAFCs. Differences in toxicity between species were striking for both commercial NAs and NAFCs. Overall, V. fischeri was the least sensitive and H. azteca was the most sensitive organism. Responses of V. fischeri and H. azteca to NAFC exposures were consistent (< 2-fold difference) regardless of source and age of OSPW; however, effects on L. cardium ranged 17-fold between NAFCs. NAFCs derived from fresh OSPW sources were similarly or less toxic to those from aged OSPW. Our results support the need to better characterize the complex mixtures associated with bitumen-influenced waters, both chemically and toxicologically. [ABSTRACT FROM AUTHOR]

The prodrug droxidopa increases blood pressure (BP) in patients with neurogenic orthostatic hypotension. The BP profile of droxidopa in neurogenic orthostatic hypotension patients (n = 18) was investigated using ambulatory BP monitoring. Following dose optimization and a washout period, 24-hour “off-drug” data were collected. “On-drug” assessment was conducted after 4–5 weeks of droxidopa treatment (mean dose, 444 mg, three times daily). Ambulatory monitoring off drug revealed that 90% of patients already had abnormalities in the circadian BP profile and did not meet criteria for normal nocturnal BP dipping. On treatment, both overall mean 24-hour systolic and diastolic BPs were higher compared to off drug (137/81 mm Hg vs. 129/76 mm Hg; P = .017/.002). Mean daytime systolic BP was significantly higher with droxidopa (8.4 ± 3.1 mm Hg; P = .014). Although nocturnal BP was not significantly higher on droxidopa versus off treatment ( P = .122), increases in nocturnal (supine) BP ≥10 mm Hg were observed in four cases (22%). Severe supine systolic hypertensive readings at night (>200 mm Hg) were captured in one case and only while on treatment. These data demonstrate that ambulatory BP monitoring is useful to evaluate the circadian BP profile after initiating treatment with a pressor agent. [ABSTRACT FROM AUTHOR]

Unconventional oil production in Alberta's oil sands generates oil sands process-affected water (OSPW), which contains toxic constituents such as naphthenic acid fraction components (NAFCs). There have been few studies examining effects of NAFC exposure over long periods of early-life stage development in fish. Here we examined the effects of NAFCs extracted from OSPW to embryo-larval fathead minnow, exposed for 21 days. We compared the sensitivity of fathead minnow to walleye reared to 7 days post-hatch (18–20 days total). EC50s for hatch success, including deformities, and total survival were lower for walleye (10–11 mg/L) than fathead minnow (22–25 mg/L), with little post-hatch mortality observed in either species. NAFC exposure affected larval growth at concentrations below the EC50 in fathead minnow (total mass IC10 14–17 mg/L). These data contribute to an understanding of the developmental stages targeted by oil sands NAFCs, as well as their toxicity in a greater range of relevant taxa. [ABSTRACT FROM AUTHOR]

Polycyclic aromatic compounds (PACs) are ubiquitous across environmental media in Canada, including surface water, soil, sediment and snowpack. Information is presented according to pan-Canadian sources, and key geographical areas including the Great Lakes, the Alberta Oil Sands Region (AOSR) and the Canadian Arctic. Significant PAC releases result from exploitation of fossil fuels containing naturally-derived PACs, with anthropogenic sources related to production, upgrading and transport which also release alkylated PACs. Continued expansion of the oil and gas industry indicates contamination by PACs may increase. Monitoring networks should be expanded, and include petrogenic PACs in their analytical schema, particularly near fuel transportation routes. National-scale roll-ups of emission budgets may not expose important details for localized areas, and on local scales emissions can be substantial without significantly contributing to total Canadian emissions. Burning organic matter produces mainly parent or pyrogenic PACs, with forest fires and coal combustion to produce iron and steel being major sources of pyrogenic PACs in Canada. Another major source is the use of carbon electrodes at aluminum smelters in British Columbia and Quebec. Temporal trends in PAC levels across the Great Lakes basin have remained relatively consistent over the past four decades. Management actions to reduce PAC loadings have been countered by increased urbanization, vehicular emissions and areas of impervious surfaces. Major cities within the Great Lakes watershed act as diffuse sources of PACs, and result in coronas of contamination emanating from urban centres, highlighting the need for non-point source controls to reduce loadings. • Urban centres within the Great Lakes watershed act as diffuse sources of PACs. • National roll-ups of emission budgets may not expose details for localized areas. • Expansion of the oil and gas industry indicates contamination by PACs may increase. • Coal combustion to produce aluminum and steel is a large source of pyrogenic PACs. • Oil recovery produces mainly alkylated PACs, while burning organic matter produces parent PACs. [ABSTRACT FROM AUTHOR]

Androgens originating from pulp mill processing, sewage treatment facilities and agricultural activities have the potential for discharge into aquatic receiving environments. To assess androgen effects on reproductive endocrine status in fish in estuarine environments, male and female adult northern mummichog ( Fundulus heteroclitus macrolepidotus ) were exposed to an aromatizable androgen (17α-methyltestosterone; MT) and a non-aromatizable androgen (5α-dihydrotestosterone; DHT) in a short-term reproductive endocrine bioassay. Fish were nominally exposed to 10 μg/L or 100 μg/L DHT, or 0.1 μg/L or 1 μg/L MT for 14 days during gonadal recrudescence. Actual concentrations of androgens, as measured by enzyme immunoassay (EIA), were 10–49% of nominal MT 0.1, 3–6% of nominal MT 1, 5–10% of nominal DHT 10 and 3–25% of nominal DHT 100. Female mummichog were impacted to a greater degree by androgen exposure, with increased plasma testosterone (T) at 100 μg/L DHT, depressed plasma 17β-estradiol (E 2 ) at both DHT concentrations and at 1 μg/L MT, as well as depressed in vitro E 2 at both MT concentrations and 100 μg/L DHT. Males had depressed plasma T in the 10 μg/L DHT treatment and depressed in vitro 11-ketotestosterone production for both MT concentrations and 10 μg/L DHT. Ovarian aromatase gene expression was induced in females exposed to 1 μg/L MT. DHT at 100 μg/L increased hepatic vitellogenin-1 (VTG1) expression in males and depressed VTG1 expression in females. The range of responses between sexes and among species provides evidence for modes of actions and potential impacts of androgens in aquatic receiving environments. [ABSTRACT FROM AUTHOR]

Abstract: Fertilized mummichog eggs retrieved from 17α-ethynylestradiol (EE2) exposed adult fish were raised in concentrations of EE2 ranging from 0 to 100ng/L (100ng/L EE2 estimated to have actual average exposure concentrations of 30% of nominal; 0.1–10ng/L were below detect throughout 24-h exposure period) for 61weeks post-hatch. Eggs exposed at 100ng/L hatched sooner, the larvae were longer, and survival of juvenile fish from hatch to study termination was greater than all other treatments, though fewer hatched at this treatment. Sex ratios were skewed (>80% female phenotype) at 100ng/L EE2, and some gonadal male fish displayed female secondary sex characteristics. Condition factor, gonadosomatic index (GSI), and liver somatic index (LSI) were found to decrease in both sexes between 52 and 61weeks post-hatch. Female fish had increased hepatic vitellogenin (VTG) at 52weeks post-hatch. When exposed to 1, 10 and 100ng/L EE2, female fish had a higher proportion of vitellogenic follicles in the ovarian tissue. Males exposed at 100ng/L may have had disruption at some endpoints (GSI, VTG) that is masked due to reduced sample size compared to other treatments. Fish exposed to concentrations of EE2 at or below 10ng/L showed inconsistent effects on development and reproductive potential. This study indicates the potential for population-level effects at the high range of environmental EE2 at concentrations equivalent to those at which consistent effects in fecundity in the adult mummichog reproductive test have been measured. This work demonstrates that chronic EE2 exposure causes developmental effects at concentrations similar to those which cause effects in the shorter-term adult mummichog reproductive test. Effects are at higher concentrations than have been noted for freshwater model species. Whether this is because of species sensitivity or due to differences between freshwater and saltwater availability of EE2 or its uptake requires further study. [Copyright &y& Elsevier]

The acid-extractable organic compounds (AEOs), including naphthenic acids (NAs), present within oil sands process-affected water (OSPW) receive great attention due to their known toxicity. While recent progress in advanced separation and analytical methodologies for AEOs has improved our understanding of the composition of these mixtures, little is known regarding any variability (i.e., spatial, temporal) inherent within, or between, tailings ponds. In this study, 5 samples were collected from the same location of one tailings pond over a 2-week period. In addition, 5 samples were collected simultaneously from different locations within a tailings pond from a different mine site, as well as its associated recycling pond. In both cases, the AEOs were analyzed using SFS, ESI-MS, HRMS, GC×GC-ToF/MS, and GC- & LC-QToF/MS (GC analyses following conversion to methyl esters). Principal component analysis of HRMS data was able to distinguish the ponds from each other, while data from GC×GC-ToF/MS, and LC- and GC-QToF/MS were used to differentiate samples from within the temporal and spatial sample sets, with the greater variability associated with the latter. Spatial differences could be attributed to pond dynamics, including differences in inputs of tailings and surface run-off. Application of novel chemometric data analyses of unknown compounds detected by LC- and GC-QToF/MS allowed further differentiation of samples both within and between data sets, providing an innovative approach for future fingerprinting studies. [ABSTRACT FROM AUTHOR]