废旧硬质聚氨酯泡沫塑料的木质素改性及再生

采用含有二乙二醇(DEG)和乙醇胺(ETA)的双组分解交联剂降解废旧硬质聚氨酯泡沫塑料(PU硬泡),并利用降解得到的低聚物多元醇与木质素复合制备出性能增强的再生PU硬泡。通过对制备的再生PU硬泡的红外光谱、密度、吸水率、抗压强度、热稳定性、导热系数、热重曲线等进行分析测试,考察m(DEG)∶m(ETA)对再生PU硬泡性能的影响。实验结果表明:m(DEG)∶m(ETA)=1∶3时废旧PU硬泡的降解效果最好;木质素加入量为2.0%(w)时再生PU硬泡的密度低、抗压强度高、保温性能良好,达到国家标准《建筑绝热用硬质聚氨酯泡沫塑料》(GB/T 21558—2008)的品质要求。     

有机垃圾厌氧消化泡沫产生机理及控制方法

为了分析厌氧消化泡沫的产生机理和控制方法有助于解决有机垃圾厌氧消化起泡问题,本文调研了近年来报道的厌氧消化系统起泡现象,并从底物特性、反应器构造及运行条件和消化过程相关特性3方面分析了不同底物、工艺和环境条件下厌氧消化反应器的起泡机理;讨论了丝状菌指数、表面张力、粘度、有机负荷、起泡趋势和泡沫稳定性等参数作为起泡风险评价指标的合理性;介绍和比较了4类消泡方法（物理法、机械法、生物法和化学法）的消泡原理及优缺点.目前,除污泥厌氧消化系统外,其他有机垃圾厌氧消化系统起泡的主要因素尚不明确,而这也限制了泡沫控制方法的开发.后期探索关键起泡微生物或研究生物表面活性物质与起泡的相关性,将有助于从新的角度揭示起泡机理,并开发出针对性更强的泡沫控制方法.     

船舶涂料海洋大气暴露与室内加速试验模拟性研究

通过两年海洋大气环境暴露试验、盐雾／紫外冷凝老化交替试验和氙灯老化试验。对比聚氨酯涂料、丙烯酸涂料涂层的色差和失光率，研究了3种试验对涂层表观性能的影响。发现紫外／冷凝老化加速试验对海洋大气暴露试验有很好的模拟性。     

废旧冰箱拆解聚氨酯泡沫塑料制备PU/PP复合材料

利用废旧冰箱拆解的聚氨酯泡沫塑料(PU)和聚丙烯(PP)、聚丙烯接枝马来酸酐(PP-g-MAH)为原料,采用物理化学回收技术制备PU/PP复合材料。用正交实验法分析PU填充量、PU粒径和PP-g-MAH 3个因素对PU/PP复合材料力学性能影响的显著性。结果表明,PU填充量对PU/PP复合材料拉伸性能有显著影响,对冲击性能和弯曲性能没有显著影响;在本文的实验范围内,PU粒径对PU/PP复合材料的力学性能影响不大;而PP-g-MAH投加量对PU/PP复合材料具有一定的影响。确定的优化工艺配方为:PU 40%;PU粒径选择2.00 mm;PP-g-MAH投加量10%。采用优化工艺制备的PU/PP复合材料的密度为1 042.88 kg/m3;冲击强度为2.9 kJ/m2;拉伸强度为10.30 MPa;拉伸模量为1 100 MPa;弯曲强度为18.5 MPa;弯曲模量为733 MPa。     

Prediction of future disposal of end-of-life refrigerators containing CFC-11

The objective of this study was to predict the number of refrigerators containing CFC-11 blown isolation foam and the amount of CFC-11 banked in these refrigerators. By using a Weibull-based survival function, the number of CFC-11 containing and still-functioning refrigerators was estimated to be approximately 1.6 million in 2013 in Turkey. In order to determine the amount of CFC-11 in the isolation foam of these refrigerators, polyurethane (PU) foam samples were taken from a refrigerator manufactured in 1993 and the quantity of CFC-11 was analyzed by a GC-MS. It was determined that 113–195 mg CFC-11/g PU remains in the PU foam depending on the location such as door, sides, top and bottom. Knowing that a mid-sized refrigerator contains 4 kg PU on average, the total amount of PU foam to be disposed of is 6344 tons when the CFC-11 containing refrigerators in Turkey become obsolete in the near future. Furthermore, 717–1237 tons of CFC-11 are expected to be banked in the PU foam of these refrigerators which will exert an equivalent amount of ozone depleting potential (ODP). In addition, the global warming potential will vary between 3.4 and 5.9 million tons of CO₂.     

Development of heat transfer and evaporation model of LNG covered by Hi-Ex foam

Natural gas is a kind of clean, efficient green energy source, which is used widely. Liquefied natural gas (LNG) is produced by cooling natural gas to −161 °C, at which it becomes the liquid. Once LNG was released, fire or explosion would happen when ignition source existed nearby. The high expansion foam (Hi-Ex foam) is believed to quickly blanket on the top of LNG spillage pool and warm the LNG vapor to lower the vapor cloud density at the ground level and raising vapor buoyancy. To identify the physical structure after it contacted with LN₂ and to develop heat transfer model, the small-scale field test with liquid nitrogen (LN₂) was designed. In experiment, three layers including frozen ice layer, frozen Hi-Ex layer and soft layer of Hi-Ex foam were observed at the steady state. By characterizing physical structure of the foam, formulas for calculating the surface of single foam bubble and counting foam film thickness were deduced. The micro heat transfer and evaporation model between cryogenic liquid and Hi-Ex foam was established. Indicating the physical structure of the frozen ice layer, there were a certain number of icicles below it. The heat transfer and evaporation mathematical model between the frozen ice layer and LNG was derived. Combining models above with the heat transfer between LNG, ground and cofferdam, the heat transfer and evaporation mathematical model of LNG covered by Hi-Ex foam was developed eventually. Finally, LN₂ evaporation rate calculated by this model was compared with the measured evaporation rate. The calculated results are 1.2–2.1 times of experimental results, which were acceptable in engineering and proved the model was reliable.     

改性聚氨酯载体用于高氨氮废水处理的研究

利用聚丁二酰亚胺对聚氨酯泡沫体进行化学改性处理,研究改性载体固定化微生物处理高氨氮模拟废水的效果。结果表明:当聚氨酯单元与聚丁二酰亚胺单元摩尔比为10∶1时,对泡沫进行改性后聚氨酯泡沫载体亲水性能良好,且具有较高的微生物负载量。改性后泡沫体上具有化学活性的官能团增加,有利于通过载体结合法固定化微生物细胞;,改性后的聚氨酯泡沫体作为微生物固定化载体用于模拟废水处理时,对主要污染指标呈现良好的污染物去除效果。     

重质油储罐固定式泡沫灭火系统设计优化研究

通过重质油储罐的实体火灭火试验,获得了氟蛋白泡沫液和水成膜泡沫液的供给强度与灭火时间对应关系数据,确定了每种泡沫液扑救重质油储罐火灾的最低泡沫供给强度;以10 000 m3固定顶重质油储罐为例进行了泡沫系统设计计算,将优化设计方案与原有设计方案进行了对比,主要变化是泡沫发生器数量从4只提高至6~8只,泡沫主管线管径从DN200提高至DN250,泡沫消防泵流量也相应提高。优化后的储罐泡沫灭火系统提高了泡沫灭火能力,提升了系统的可靠性,降低了储罐火灾风险。     

大孔网状聚氨酯载体MBBR工艺处理低浓度硝基苯废水实验研究

利用大孔网状聚氨酯载体在MBBR工艺条件下,研究了系统挂膜与启动过程,同时利用挂膜成熟稳定的载体进行低浓度硝基苯废水处理实验。研究结果表明,在20℃条件下培养的活性污泥生长状况良好,挂膜速度快,生物膜厚度大,耐冲击负荷。在MBBR反应时间24 h、材料投加量为1/4、硝基苯初始浓度为2.095mg/L的条件下,处理低浓度硝基苯废水的效果最好,CODcr去除率为92.58%,硝基苯去除率为49.82%。     

The structure of the fire fighting foam surfactant Forafac®1157 and its biological and photolytic transformation products

For several decades, perfluorooctane sulfonate (PFOS) has widely been used as a fluorinated surfactant in aqueous film forming foams used as hydrocarbon fuel fire extinguishers. Due to concerns regarding its environmental persistence and toxicological effects, PFOS has recently been replaced by novel fluorinated surfactants such as Forafac®1157, developed by the DuPont company. The major component of Forafac®1157 is a 6:2 fluorotelomer sulfonamide alkylbetaine (6:2 FTAB), and a link between the trade name and the exact chemical structure is presented here to the scientific community for the first time. In the present work, the structure of the 6:2 FTAB was elucidated by ¹H, ¹³C and ¹⁹F nuclear magnetic resonance spectroscopy and high-resolution mass spectrometry. Moreover, its major metabolites from blue mussel (Mytilus edulis) and turbot (Scophthalmus maximus) and its photolytic transformation products were identified. Contrary to what has earlier been observed for PFOS, the 6:2 FTAB was extensively metabolized by blue mussel and turbot exposed to Forafac®1157. The major metabolite was a deacetylated betaine species, from which mono- and di-demethylated metabolites also were formed. Another abundant metabolite was the 6:2 fluorotelomer sulfonamide. In another experiment, Forafac®1157 was subjected to UV-light induced photolysis. The experimental conditions aimed to simulate Arctic conditions and the deacetylated species was again the primary transformation product of 6:2 FTAB. A 6:2 fluorotelomer sulfonamide was also formed along with a non-identified transformation product. The environmental presence of most of the metabolites and transformation products was qualitatively demonstrated by analysis of soil samples taken in close proximity to an airport fire training facility.