Ferri Priscila, Ramil María, Rodríguez Isaac, Bergamasco Rosângela, Vieira Angélica Marquetotti Salcedo, Cela Rafael
Departamento de Química Analítica, Nutrición y Bromatología, Instituto de Investigación y Análisis Alimentario (IIAA), Universidad de Santiago de Compostela, Santiago de Compostela, 15782, Spain.
Postgraduate Program in Chemical Engineering, Universidade Estadual de Maringá, Maringá, Paraná, 87020-900, Brazil.
Anal Bioanal Chem. 2017 Apr;409(11):2981-2991. doi: 10.1007/s00216-017-0241-x. Epub 2017 Feb 16.
Quinoxyfen has been recently identified as a priority hazardous substance in the field of the European water policy. In this work, its fate in aqueous samples and solid supports under UV and solar radiation is investigated. Diverse degradation experiments were carried out, at lab scale, using spiked aliquots of different aqueous matrices (ultrapure, treated wastewater and river water) irradiated at different wavelengths (λ = 254 nm, λ = 365 nm and solar light). Half-lives of quinoxyfen (2-26 min) depended on the wavelength and the intensity of radiation whilst the nature of the aqueous matrix did not play an important role in degradation kinetics. Moreover, experiments under solar radiation of doped silicone tubes were performed to simulate degradation when quinoxyfen is adsorbed on plant leaves or soil. As the compound is not completely mineralized, the identification of quinoxyfen transformation products (TPs) was performed by liquid chromatography quadrupole time-of-flight mass spectrometry (LC-QTOF-MS) injection of different irradiated time aliquots. The full-fragment ion spectra, at different collision energies, allowed the elucidation of the chemical structure of TPs formed by hydroxylation, cyclization or cleavage reactions. Five out of seven identified TPs have not been reported previously. The ecotoxicity simulation by software (TEST and ECOSAR) for TPs revealed that some of them could cause harmful effects to organisms such as Daphnia magna or Fathead minnow in a similar extent to the precursor; moreover, the time course profiles of major TPs (TP1 and TP2) revealed a much higher resistance to further photodegradation than quinoxyfen. Graphical abstract Quinoxyfen phototransformation pathways.
喹氧灵最近被确定为欧洲水政策领域的一种优先有害物质。在这项工作中,研究了其在紫外线和太阳辐射下在水样和固体载体中的归宿。在实验室规模下,使用不同水基质(超纯水、处理后的废水和河水)的加标等分试样在不同波长(λ = 254 nm、λ = 365 nm和太阳光)下进行了各种降解实验。喹氧灵的半衰期(2 - 26分钟)取决于波长和辐射强度,而水基质的性质在降解动力学中不起重要作用。此外,进行了掺杂硅管在太阳辐射下的实验,以模拟喹氧灵吸附在植物叶片或土壤上时的降解情况。由于该化合物没有完全矿化,通过液相色谱四极杆飞行时间质谱(LC - QTOF - MS)对不同辐照时间等分试样进样来鉴定喹氧灵的转化产物(TPs)。在不同碰撞能量下的全碎片离子光谱有助于阐明通过羟基化、环化或裂解反应形成的TPs的化学结构。七个已鉴定的TPs中有五个以前未被报道过。通过软件(TEST和ECOSAR)对TPs进行的生态毒性模拟表明,其中一些可能对大型溞或黑头呆鱼等生物造成与前体类似程度的有害影响;此外,主要TPs(TP1和TP2)的时间进程曲线显示,它们比喹氧灵对进一步光降解具有更高的抗性。图形摘要 喹氧灵的光转化途径。