液氮泡沫发生器内流动特性研究

低温液氮与泡沫混合液直接接触产生氮气泡沫是一种新型的掺混形式,利用液氮高汽化比的特点,搭建液氮泡沫可视化实验装置,进行氮气-水两相流及液氮泡沫流动特性的研究。结果表明,液氮相变产生大量氮气,其与泡沫液混合产生泡沫,温度有所回升,最终趋于泡沫混合液温度;管路沿程压降较小;液氮射流破碎及流动过程可分为6个区域:低温液氮区、向上循环翻滚区、滞留区、泡沫与泡沫混合液混合区、致密泡沫区、泡沫混合液区。流体向下游流动过程中持续发泡;为防止管路结冰,需合理控制泡沫混合液与液氮流量。     

基于GM-SVR的小样本条件下化工设备可靠性预测

为了准确预测化工设备可靠性趋势，针对化工设备失效寿命数据为小样本的情形，基于灰色估计法与支持向量回归机在小样本数据处理中的优势，建立了失效寿命时间服从三参数威布尔分布的化工设备可靠性模型；结合GM（1，1）和SVR对模型进行参数估计，在压缩机可靠性分析中进行了实例应用，对比分析了最小二乘法、灰色估计法和GM-SVR的估计效果。研究结果表明:GM-SVR对威布尔分布参数的估计精度明显优于最小二乘法和灰色估计法，可以有效地应用于化工设备失效数据为小样本时的可靠性预测。     

水质氨氮在线监测仪对污染源低浓度样品测定的研究

水质氨氮在线监测仪广泛用于各类水体中氨氮的在线监测,随着我国水质氨氮减排工作的开展,污染源废水中氨氮浓度逐渐降低,目前市场上的水质氨氮在线监测仪是否适用于低浓度氨氮样品的在线监测成为广大环保工作者关心的问题。选取3种不同类型的水质氨氮在线监测仪分别进行低浓度标样和实际水样测试,并对结果进行了讨论。     

An LC-MS/MS method for creatine and creatinine analysis in paraquat-intoxicated patients

Abstract

A sudden increase in serum creatinine after paraquat intoxication has been reported in several clinical studies. However, this dramatic change of creatinine may be possibly due to an interconversion of creatine-creatinine in relation to paraquat toxicity. In order to investigate the creatine-creatinine relationship, a liquid chromatography tandem mass spectrometry in combination with electrospray ionization was developed and validated for simultaneous determination of creatine and creatinine in the serum. The chromatographic separation was achieved on a Gemini® C₆-Phenyl column with a gradient elution consisting of 0.1% formic acid in ultrapure water and methanol as the mobile phase. The method yielded suitable levels of specificity and selectivity, and calibration curves of creatine and creatinine in serum were linear over the concentration range of 0.5–200?µg mL^?1. The limit of quantification of both compounds was 0.5?µg mL^?1, and the method was accurate within the recovery range of 96.23–102.75%, indicating the robustness of the method. The method was successfully applied to toxicological samples from paraquat-intoxicated patients, and the concentrations of creatine and creatinine were quantified. High creatine concentrations in serum samples were observed which may lead to high serum creatinine despite normal kidney function as creatine is converted to creatinine in proportion to its concentration.     

高锰酸盐指数测定中影响因素的探讨

通过对酸性法测定高锰酸盐指数全过程的分析,结果表明水样静置时间、水样浓度、水浴时间、反应温度等因素影响测定结果。文章总结了测定过程中需要注意的几个关键环节,确保获得准确数据。     

沈阳地区水环境和生物样品中全氟化合物的污染分布特征

采用高效液相色谱/电喷雾负电离源串联质谱法对沈阳市各类水环境和生物样品中全氟化合物(PFCs)进行测定,研究了PFCs的河流分布及季节分布特征.同时,对通过饮用水及家禽和鱼摄入全氟辛烷磺酸(PFOS)和全氟辛酸(PFOA)的人体健康风险进行了评价.结果表明,沈阳市各类水环境样品中总PFCs浓度范围为nd～6.01ng·L-1,平均浓度为5.23ng·L-1.PFOS和PFOA是沈阳地区所有水环境样品中最主要的PFCs污染物,浓度范围分别为nd～2.83ng·L-1和nd～5.71ng·L-1,平均浓度分别为1.11和2.13ng·L-1.细河的PFOS含量最高,约为浑河PFOS含量的2倍,蒲河PFOS含量的3倍.一些PFCs化合物之间呈正相关关系,说明其可能具有相同的来源.PFOS与PFOA之间无相关关系,由此推断沈阳水体中二者具有不同来源.浑河流经沈阳市时,PFOS和PFOA浓度升高.流经沈阳市区后,PFOS和全氟己烷磺酸钾(PFHxS)浓度明显升高.细河中PFHxS也有检出,表明沈阳市是周边水体中PFOS及PFHxS的主要污染来源.丰水期地表水中PFOS和PFOA浓度与枯水期相比没有明显差异,但丰水期水中PFCs组成更为丰富,出现了大量全氟庚酸(PFHpA).沈阳地区自来水中PFOS和PFOA浓度平均值分别为0.39和0.85ng·L-1,最高浓度分别为1.16和2.55ng·L-1,均低于美国饮用水健康参考值.沈阳生物样品中PFOS和全氟十一酸(PFUnDA)是最普遍的化合物.总PFCs平均含量在鱼样品中为6.59ng.g-1(以干重计),鸡和鸭血清样品中分别为1.65和0.69ng·mL-1,鸡和鸭肝脏样品中分别为0.41和1.68ng.g-1(以干重计),与文献报道相比处于较低水平.     

固相微萃取技术及其在环境样品分析中的应用

在介绍SPME技术装置、工作原理及影响因素的基础上,阐述了近年来SPME技术在环境样品分析中的应用。     

Airsolution液体在净化有机废气方面的应用

Airsoluton是一系列植物提取液复配而成的,这些植物提取液是含有气味的有机物,它们是从树、草和花等植物中提取的。这些有味的液体含有大量复杂的化合物,它们是绝大多数植物油的主要成分。本文根据Airsolution液体的氧化性,对处理含苯、甲苯和二甲苯的有机工业废气进行了净化研究,结果表明:Airsolution液体用于处理有机废气是可行的,处理后的苯、甲苯和二甲苯可实现达标排放。且该工艺具有运行费用低,投资少的特点。     

降水中甲酸、乙酸和草酸的离子色谱法测定及样品保存研究

甲酸、乙酸和草酸是降水中有机酸的主要成分。研究选用离子色谱法同时测定降水中的甲酸、乙酸和草酸,并对降水样品中3种有机酸的保存条件进行了研究。优化后的色谱条件为4. 0 mmol/L Na_2CO_3和1. 2 mmol/L NaHCO_3混合淋洗液,淋洗液流速为1. 0 m L/min,进样体积为200μL,电导池温度为30℃,柱温为室温。甲酸、乙酸和草酸的检出限分别为0. 002、0. 005、0. 005 mg/L,实际降水样品测定时平行样的相对标准偏差为1. 4%～12%,加标回收率为95%～118%。样品采集后需尽快用0. 45μm聚醚砜微孔滤膜过滤,4℃以下冷藏密封保存,2 d内测定。若用氢氧化钠溶液调节p H至8～10,样品可保存7 d。     

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.