8 research outputs found

    Impact of Simulated California Rice-Growing Conditions on Chlorantraniliprole Partitioning

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    Chlorantraniliprole (3-bromo-<i>N</i>-[4-chloro-2-methyl-6-(methylcarbamoyl)­phenyl]-1-(3-chloro-2-pyridine-2-yl)-1<i>H</i>-pyrazole-5-carboxamide, CAP; water solubility 1.023 mg·L<sup>–1</sup>) was recently registered for application on California rice fields. Air– and soil–water partitioning of CAP were investigated under simulated California rice field conditions through calculation of <i>K</i><sub>H</sub> and Δ<sub>aw</sub><i>H</i> and a batch equilibrium method following OECD 106 guidelines, respectively. <i>K</i><sub>H</sub> and Δ<sub>aw</sub><i>H</i> were determined to be 1.69 × 10<sup>–16</sup> – 2.81 × 10<sup>–15</sup> atm·m<sup>3</sup>·mol<sup>–1</sup> (15–35 °C) and 103.68 kJ·mol<sup>–1</sup>, respectively. Log­(<i>K</i><sub>oc</sub>) ranged from 2.59 to 2.96 across all soil and temperature treatments. Log­(<i>K</i><sub><i>F</i></sub>) ranged from 0.61 to 1.14 across all soil, temperature, and salinity treatments. Temperature and salinity increased sorption significantly at 35 °C (<i>P</i> < 0.05) and 0.2 M (<i>P</i> < 0.0001), respectively, while soil properties impacted sorption across all treatments. Overall results, corroborated using the Pesticides in Flooded Applications Model, indicate that volatilization of CAP is not a major route of dissipation and sorption of CAP to California rice field soils is moderately weak and reversible

    A light touch: solar photocatalysis detoxifies oil sands process-affected waters prior to significant treatment of naphthenic acids or acid extractable organics

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    The toxicity of oil sands process-affected water (OSPW) has been associated to its dissolved organics, a complex mixture of naphthenic acid fraction components (NAFCs). Here, we evaluated solar treatment with buoyant photocatalysts (BPCs) as a candidate passive advanced oxidation process (P-AOP) for OSPW remediation, according to both analytical chemistry and standard rainbow trout (Oncorhynchus mykiss) and fathead minnow (Pimephales promelas) whole effluent toxicity (WET) bioassays. Solar photocatalysis with BPCs fully degraded naphthenic acids (NAs) and acid extractable organics (AEO) in 3 different OSPW samples, however fish toxicity was eliminated well before concentrations of dissolved organics had significantly diminished, within <2 days of sunlight exposure for all OSPWs. Classical NAs and AEO, traditionally considered among the principal toxicants in OSPW, were not correlated with OSPW toxicity herein. Instead, petroleomic mass spectrometry (MS) analysis revealed low polarity organosulfur NAFCs – O2S− and OS+ (putatively naphthenic sulfoxides), together composing <10% of the total AEO – were correlated with WET outcomes, and apparently accounted for the majority of waters’ toxicity, as described by a physiologically-based model (PBM) of tissue partitioning. These results demonstrate that complete elimination of OSPW toxicity per standard WET bioassays is achievable without significant changes to overall concentrations of dissolved organics, suggesting that most AEO are toxicologically benign, and toxicity may instead be driven by only a small subset of NAFCs, which are preferentially photocatalytically treated. These findings have implications for OSPW release, for which a less extensive but more selective treatment may be required than previously expected

    Leukocyte driven-decidual angiogenesis in early pregnancy

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