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1.
A continuous flow reactor was operated at atmospheric pressure and feed rate of 0–1.5 kg h−1 for degradation of PE, PP and PS in presence of 1–2 wt% PVC. The degradation temperatures were between 360 and 440 °C depending on the feeding material. The influence of PVC, temperature and silica-alumina catalysts on degradation behavior and on the properties of the products was studied and discussed. Different effects were observed for binary PE/PVC, PP/PVC, PS/PVC and complex PE/PP/PS/PVC mixtures due to specific interactions between PVC and each hydrocarbon polyolefin. Silica-alumina catalysts decreased the Cl concentration in oils but it seems to generate high amounts of Cl-containing organic compounds in gases.  相似文献   

2.
The oxidative and thermo-mechanical degradation of HDPE was studied during processing in an internal mixer under two conditions: totally and partially filled chambers, which provides lower and higher concentrations of oxygen, respectively. Two types of HDPEs, Phillips and Ziegler-Natta, having different levels of terminal vinyl unsaturations were analyzed. Materials were processed at 160, 200, and 240 °C. Standard rheograms using a partially filled chamber showed that the torque is much more unstable in comparison to a totally filled chamber which provides an environment depleted of oxygen. Carbonyl and transvinylene group concentrations increased, whereas vinyl group concentration decreased with temperature and oxygen availability. Average number of chain scission and branching (ns) was calculated from MWD curves and its plotting versus functional groups' concentration showed that chain scission or branching takes place depending upon oxygen content and vinyl groups' consumption. Chain scission and branching distribution function (CSBDF) values showed that longer chains undergo chain scission easier than shorter ones due to their higher probability of entanglements. This yields macroradicals that react with the vinyl terminal unsaturations of other chains producing chain branching. Shorter chains are more mobile, not suffering scission but instead are used for grafting the macroradicals, increasing the molecular weight. Increase in the oxygen concentration, temperature, and vinyl end groups' content facilitates the thermo-mechanical degradation reducing the amount of both, longer chains via chain scission and shorter chains via chain branching, narrowing the polydispersity. Phillips HDPE produces a higher level of chain branching than the Ziegler-Natta's type at the same processing condition.  相似文献   

3.
Regulatory agencies from all over the world have set up stringent guidelines with regard to drug degradation products due to their toxic effects or carcinogenicity. Lansoprazole, a proton‐pump inhibitor, was subjected to forced degradation studies as per ICH guidelines Q1A (R2). The drug was found to degrade under acidic, basic, neutral hydrolysis and oxidative stress conditions, whereas it was found to be stable under thermal and photolytic conditions. The chromatographic separation of the drug and its degradation products were achieved on a Hiber Purospher, C18 (250 × 4.6 mm, 5 μ) column using 10 mM ammonium acetate and acetonitrile as a mobile phase in a gradient elution mode at a flow rate of 1.0 ml/min. The eight degradation products (DP1–8) were identified and characterized by UPLC/ESI/HRMS with in‐source CID experiments combined with accurate mass measurements. DP‐1, DP‐2 and DP‐3 were formed in acidic, DP‐4 in basic, DP‐5 in neutral and DP‐1, DP‐6, DP‐7 and DP‐8 were in oxidation stress condition Among eight degradation products, five were hitherto unknown degradation products. In addition, one of the major degradation products, DP‐2, was isolated by using semi preparative HPLC and other two, DP‐6 and DP‐7 were synthesized. The cytotoxic effect of these degradation products (DP‐2, DP‐6 and DP‐7) were tested on normal human cells such as HEK 293 (embryonic kidney cells) and RWPE‐1(normal prostate epithelial cells) by MTT assay. From the results of cytotoxicity, it was found that lansoprazole as well as its degradation products (DP‐2, DP‐6 and DP‐7) were nontoxic up to 50‐μM concentrations, and the latter showed slightly higher cytotoxicity when compared with that of lansoprazole. DNA binding studies using spectroscopic techniques indicate that DP‐2, DP‐6 and DP‐7 molecules interact with ctDNA and may bind to its surface. Copyright © 2017 John Wiley & Sons, Ltd.  相似文献   

4.
A methodical design-of-experiments were performed by applying quality-by-design concepts to establish a design-space for simultaneous and rapid quantification of Carvedilol and Ivabradine by UPLC in the presence of degradation products. Response-surface, central-composite design, and quadratic model were employed for statistical assessment of experimental data using the Design-Expert software. Response variables such as resolution and retention time were analyzed statistically for chromatographic screening. During DoE study, various plots such as perturbation, contour, 3D and design-space plots were considered for method optimization. The method was developed using C8 [100?×?2.1?mm, 1.8?µ] UPLC column, mobile phase comprising 0.5% triethylamine buffer [pH 6.4] and acetonitrile in the ratio of 50:50 v/v, the flow rate of 0.4?mL minute?1 and UV detection at 285?nm for both Carvedilol and Ivabradine. The method was developed with a short run time of two minutes. The method was found to be linear in the range of 25.0–199.9?µg?mL?1 and 8.9–21.3?µg?mL?1 for Carvedilol and Ivabradine, respectively with a correlation coefficient of 0.9998 in each case. The recovery values were found in the range of 99.7–100.8% and 98.9–100.9% for Carvedilol and Ivabradine, respectively. The method was validated according to ICH Q2 (R1) guidelines.  相似文献   

5.
Omeprazole is one of the most consumed pharmaceuticals around the world. However, this compound is scarcely detected in urban wastewater and surface water. The absence of this pharmaceutical in the aquatic ecosystem might be due to its degradation in wastewater treatment plants, as well as in receiving water. In this work, different laboratory‐controlled degradation experiments have been carried out on surface water in order to elucidate generated omeprazole transformation products (TPs). Surface water spiked with omeprazole was subjected to hydrolysis, photo‐degradation under both sunlight and ultraviolet radiation and chlorination. Analyses by liquid chromatography coupled to quadrupole time‐of‐flight mass spectrometry (LC–QTOF MS) permitted identification of up to 17 omeprazole TPs. In a subsequent step, the TPs identified were sought in surface water and urban wastewater by LC–QTOF MS and by LC coupled to tandem mass spectrometry with triple quadrupole. The parent omeprazole was not detected in any of the samples, but four TPs were found in several water samples. The most frequently detected compound was OTP 5 (omeprazole sulfide), which might be a reasonable candidate to be included in monitoring programs rather than the parent omeprazole. Copyright © 2013 John Wiley & Sons, Ltd.  相似文献   

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