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首页> 外文期刊>Environmental Science: Water Research & Technology >Formation of bioactive transformation products during glucocorticoid chlorination
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Formation of bioactive transformation products during glucocorticoid chlorination

机译:糖皮质激素氯化过程中生物活性转化产物的形成

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Glucocorticoid (GC) release into the environment has led to widespread detection of glucocorticoid receptor (GR) activity in water resources that has been shown to persist throughout conventional and some advanced wastewater treatment processes. Here, we used high performance liquid chromatography, high resolution mass spectrometry and nuclear magnetic resonance spectroscopy to explore the reaction of natural (cortisone, cortisol) and synthetic (prednisone, prednisolone, dexamethasone) GCs with free chlorine (HOCl) to simulate their fate during chemical disinfection of water and wastewater. Generally, GCs react slowly (t(1/2) similar to 7-200 h) with HOCl when compared to other steroid classes, but they yield complex mixtures of transformation products, with at times the majority of product mass comprising structurally identifiable and likely bioactive steroids. For example, we frequently observed chlorination at the C-9 position (e.g., 9-chloro-prednisone), a reaction known to increase GC activity 4-fold. We also identified reaction products in the adrenosterone family of androgens produced via cleavage of the C-17 side-chain on many GCs. Another common transformation pathway was the conversion of endogenous GCs to their more potent synthetic analogs via oxidation at the C-1/C-2 positions, with unsaturation reported to increase GR activity 4-fold (e.g., cortisol to prednisolone). Despite identification of such products, in vitro assays generally suggest GR activity decreases with extent of parent decay during chlorination. Cortisol was the exception, with GR activity only decreasing 2-fold in product mixtures (based on measured EC50 values) despite a 95% reduction in parent concentration, a result attributable to formation of the more potent prednisolone during chlorination. Furthermore, our assay likely underestimates product bioactivity as it did not account for the activity of several identified GC byproducts that first require in vivo activation via C-11 reduction, nor did it consider androgen receptor (AR) activity associated with byproducts from the adrenosterone family. To avoid formation of product mixtures with conserved bioactivity, advanced chemical oxidation processes may represent a more promising approach; we show that GCs react much more rapidly with ozone (t(1/2) similar to 0.4-1.3 min) and produce no observable UV-active products. This suggests disruption of the GC conjugated p-electron and ring systems, thereby likely mitigating biological activity.
机译:糖皮质激素(GC)释放到环境中导致了对水资源中糖皮质激素受体(GR)活性的广泛检测,事实表明,糖皮质激素受体(GR)活性在整个常规和某些先进的废水处理过程中都将持续存在。在这里,我们使用高效液相色谱,高分辨率质谱和核磁共振波谱研究了天然(可的松,氢化可的松)和合成(强的松,泼尼松龙,地塞米松)气相色谱与游离氯(HOCl)的反应,以模拟它们在过程中的命运。对水和废水进行化学消毒。通常,与其他类固醇类化合物相比,GC与HOCl反应缓慢(t(1/2)类似于7-200 h),但它们会生成转化产物的复杂混合物,有时大部分产物质量在结构上可识别且很可能具有生物活性的类固醇。例如,我们经常观察到C-9位置的氯化反应(例如9-氯泼尼松),该反应可将GC活性提高4倍。我们还鉴定了通过在许多GC上裂解C-17侧链产生的雄激素肾上腺素家族的反应产物。另一个常见的转化途径是内源性GC通过C-1 / C-2位置的氧化转化为更有效的合成类似物,据报道,不饱和度将GR活性提高了4倍(例如,皮质醇变为泼尼松龙)。尽管已鉴定出此类产物,但体外测定通常表明,在氯化过程中,GR活性随母体衰变程度而降低。皮质醇是例外,尽管母体浓度降低了95%,但GR活性在产品混合物中仅降低了2倍(基于测得的EC50值),这是由于氯化过程中形成了更强的泼尼松龙。此外,我们的测定法可能低估了产品的生物活性,因为它没有考虑到几种首先通过C-11还原需要体内激活的已鉴定GC副产物的活性,也没有考虑与肾上腺素家族的副产物相关的雄激素受体(AR)活性。 。为了避免形成具有保守生物活性的产物混合物,先进的化学氧化工艺可能代表一种更有希望的方法。我们显示,气相色谱仪与臭氧的反应速度更快(t(1/2)类似于0.4-1.3分钟),并且没有可观察到的紫外线活性产物。这表明GC偶联的p-电子和环系统的破坏,从而可能减轻生物活性。

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