PVC包装材料中酞酸酯增塑剂残留的ASE-GC-MS分析

针对PVC包装材料中酞酸酯（PAEs）增塑剂残留，采用加速溶剂萃取（ASE）和GC／MS联用技术分析5种PAEs（DMP，DEP，DBP，BBP，DEHP），结果表明加速溶剂萃取用于PVC包装材料中PAEs的提取，最佳温度条件为120℃，最佳循环次数为3次。方法检出限达到0．1mg／kg，回收率达到95．5％-99．8％；并且具有很好的重现性和精密度。     

Production of hydrogen by steam gasification of dehydrochlorinated poly(vinyl chloride) or activated carbon in the presence of various alkali compounds

Steam gasification of dehydrochlorinated poly(vinyl chloride) (PVC) or activated carbon was carried out in the presence of various alkali compounds at 3.0 MPa and 560°C–660°C in a batch reactor or in a semi-batch reactor with a flow of nitrogen and steam. Hydrogen and sodium carbonate were the main products, and methane and carbon dioxide were the minor products. Yields of hydrogen were high in the presence of sodium hydroxide and potassium hydroxide. The acceleration effect of the alkali compounds on the gasification reaction was as follows: KOH > NaOH > Ca(OH)₂ > Na₂CO₃. The rate of gasification increased with increasing partial steam pressure and NaOH/C molar ratio. However, the rate became saturated at a molar ratio of NaOH/C greater than 2.0.     

聚氯乙烯电缆料老化前后的火灾危险性研究

利用微型燃烧量热计（MCC）、热重分析（TGA）、实时红外光谱（RTFTIR）以及热重-红外联用技术（TG-FT-IR）研究了PVC电缆料老化前后火灾危险性的变化。MCC结果表明,老化后的PVC的最大热释放速率增加了56.3%,总热释放量从10.6kJ/g增加到16.8kJ/g,点燃温度也由302℃提前到282℃。TG-FTIR和RTFTIR的分析结果显示,PVC的主要降解产物有水、碳氢化合物、二氧化碳和一氧化碳。PVC达到最大降解速率的温度约为240℃,与MCC、TG的结果相符合。PVC的裂解气体中包含CO2和CO,还有剧毒气体HCl。这些实验数据说明PVC材料在使用过程中火灾危险性加大,为老城区电气线路和设备的改造提供了理论依据和实验基础。     

PVC附载TiO_2光催化剂的制备与评价

研究以PVC颗粒为载体、利用加热法制备附载型TiO2 光催化剂 ,并对其进行牢固性、附载率、使用寿命及活性等方面的评价     

循环水养殖系统（RAS）生物载体上微生物群落结构变化分析

为研究循环水养殖系统(recirculating aquaculture systems,RAS)生物滤池挂膜及运行过程中生物载体上微生物群落结构的变化及其脱氮机制,采用传统微生物培养方法,对不同时期生物载体上的异养细菌、氨氧化细菌及硝化菌进行堵养计数.并通过变性梯度凝胶电泳技术,对细菌的16S rDNA V3可变区的...     

阻燃PVC电工套管氧指数测定中的影响因素分析

通过对阻燃PVC电工套管氧指数测定中的影响因素分析,对现行的阻燃PVC电工套管的氧指数检验方法展开讨论,并为执法部门、建设单位和产品生产商提供数据参考。     

Dechlorination of polyvinyl chloride in NaOH/ethylene glycol solution by microwave heating

This study investigated the dehydrochlorination of flexible polyvinyl chloride (PVC) containing 59.2% PVC, 29.7% dioctyl phthalate (DOP), and approximately 12% stabilizers. Flexible PVC was treated with NaOH/ethylene glycol (NaOH/EG) solutions at NaOH concentrations in the range 0.5–4 mol/l and was heated in a microwave heater at a temperature between 100° and 160°C for 0–30 min. All chlorides were completely eliminated by internal heating at 160°C using microwaves for 10 min in a 1 mol/l NaOH/EG solution, and the residue was made up of hydrocarbons. The weight loss rate reached a maximum of 74.7% at a temperature of 160°C. It was discovered that the use of microwaves significantly shortened the reaction time compared to using conventional electric heaters or other external heating systems and also allowed the use of lower concentrations of NaOH. Chemical Feedstock Recycling & Other Innovative Recycling Techniques 6     

电石法生产聚氯乙烯行业危险废物判定要点分析

聚氯乙烯树脂是用途极广的热塑性高分子材料,然而,电石法生产聚氯乙烯树脂(PVC)的过程中会产生大量的危险废物,如处置不当会对环境造成严重污染。本文对电石法生产聚氯乙烯树脂(PVC)过程中产生危险废物的类型、环节和产生特性进行了分析,以供环保部门和相关企业作为针对危险废物环境管理的判定依据。     

臭氧氧化法降解聚氯乙烯离心母液废水中3种有机物

以聚氯乙烯离心母液废水中含量较高的3种有机物(聚乙烯醇、异辛醇和α-甲基苯乙烯)作为目标物,考察臭氧氧化工艺对3种有机物的去除效果,同时考察反应时间、臭氧投加量和初始pH对处理效果的影响。实验结果表明,臭氧氧化处理3种废水的最佳反应时间和臭氧投加量分别为:聚乙烯醇25 min,136 mg/L;异辛醇60min,312 mg/L;α-甲基苯乙烯60 min,32 mg/L。在此条件下,3种有机物的去除率分别为98%、85%和95%。此外,碱性条件有助于臭氧氧化工艺对3种有机物的降解。产物分析结果表明,经臭氧氧化,聚乙烯醇断链后进一步反应生成了草酸单乙酯,异辛醇和α-甲基苯乙烯分别生成了和苯乙酮。     

Biodegradation and bio-sorption of antibiotics and non-steroidal anti-inflammatory drugs using immobilized cell process

In the present study, the removal mechanisms of four antibiotics (sulfamethoxazole, sulfadimethoxine, sulfamethazine, and trimethoprim) and four non-steroidal anti-inflammatory drugs (acetaminophen, ibuprofen, ketoprofen, and naproxen) in immobilized cell process were investigated using batch reactors. This work principally explores the individual or collective roles of biodegradation and bio-sorption as removal routes of the target pharmaceuticals and the results were validated by various experimental and analytical tools. Biodegradation and bio-sorption were found as dominant mechanisms for the drug removal, while volatilization and hydrolysis were negligible for all target pharmaceuticals. The target pharmaceuticals responded to the two observed removal mechanisms in different ways, typically: (1) strong biodegradability and bio-sorption by acetaminophen, (2) strong biodegradability and weak bio-sorption by sulfamethoxazole, sulfadimethoxine, ibuprofen and naproxen, (3) low biodegradability and weak bio-sorption by sulfamethazine and ketoprofen, and (4) low biodegradability and medium bio-sorption by trimethoprim. In the sorption/desorption experiment, acetaminophen, sulfamethoxazole and sulfadimethoxine were characterized by strong sorption and weak desorption. A phenomenon of moderate sorption and well desorption was observed for sulfamethazine, trimethoprim and naproxen. Both ibuprofen and ketoprofen were weakly sorbed and strongly desorbed.