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Ultrasonic degradation, mineralization and detoxification of diclofenac in water: Optimization of operating parameters

机译:水中双氯芬酸的超声波降解,矿化和解毒:操作参数的优化

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The 20 kHz ultrasound-induced degradation of non-steroidal, anti-inflammatory drug diclofenac (DCF)was investigated. Several operating conditions, such as power density (25–100 W/L), substrate concentration (2.5–80 mg/L), initial solution pH (3.5–11), liquid bulk temperature and the type of sparging gas (air, oxygen, argon), were tested concerning their effect on DCF degradation (as assessed measuring absorbance at 276 nm) and hydroxyl radicals generation (as assessed measuring H2O2 concentration).Sample mineralization (in terms of TOC and COD removal), aerobic biodegradability (as assessed by the BOD5/COD ratio) and ecotoxicity to Daphnia magna and Artemia salina were followed too.DCF conversion is enhanced at increased applied power densities and liquid bulk temperatures, acidic conditions and in the presence of dissolved air or oxygen. The reaction rate increases with increasing DCF concentration in the range 2.5–5 mg/L but it remains constant in the range 40–80 mg/L, indicating different kinetic regimes (i.e. first and zero order, respectively). H2O2 production rates in pure water are higher than those in DCF solutions, implying that decomposition basically proceeds through hydroxyl radical reactions. Mineralization is a slow process as reaction by-products are more stable than DCF to total oxidation;nonetheless, they are also more readily biodegradable. Toxicity to D. magna increases during the early stages of the reaction and then decreases progressively upon degradation of reaction by-products;nevertheless, complete toxicity elimination cannot be achieved at the conditions in question. Neither the original nor the treated DCF samples are toxic to A. salina.
机译:研究了20 kHz超声诱导的非甾体抗炎药双氯芬酸(DCF)的降解。几种操作条件,例如功率密度(25–100 W / L),底物浓度(2.5–80 mg / L),初始溶液pH(3.5–11),液体体积温度和喷射气体的类型(空气,氧气)测试了其对DCF降解(在276 nm处的吸光度进行评估)和羟基自由基生成(以H2O2浓度进行评估)的影响样品的矿化作用(根据TOC和COD的去除),好氧生物降解性(经评估)通过BOD5 / COD比率)以及对水蚤(Daphnia magna)和卤虫(Artemia salina)的生态毒性也得到了证实.DCF转化率在增加的施加功率密度和液体体积温度,酸性条件下以及存在溶解的空气或氧气的情况下得到了增强。反应速率随DCF浓度在2.5-5 mg / L范围内增加而增加,但在40-80 mg / L范围内保持恒定,表明存在不同的动力学机制(分别为一阶和零阶)。纯水中H2O2的生产率高于DCF溶液,这表明分解基本上是通过羟基自由基反应进行的。矿化是一个缓慢的过程,因为反应副产物对总氧化的稳定性比DCF稳定;尽管如此,它们也更易于生物降解。在反应的早期阶段,对D. magna的毒性增加,然后在反应副产物降解时逐渐降低;然而,在上述条件下无法完全消除毒性。原始DCF样品和处理过的DCF样品均无毒。

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