A rapidly equilibrating, thin film, passive water sampler for organic contaminants; characterization and field testing

Improving methods for assessing the spatial and temporal resolution of organic compound concentrations in marine environments is important to the sustainable management of our coastal systems. Here we evaluate the use of ethylene vinyl acetate (EVA) as a candidate polymer for thin-film passive sampling in waters of marine environments. Log K_EVA−W partition coefficients correlate well (r² = 0.87) with Log K_OW values for selected pesticides and polychlorinated biphenyls (PCBs) where Log K_EVA−W = 1.04 Log K_OW + 0.22. EVA is a suitable polymer for passive sampling due to both its high affinity for organic compounds and its ease of coating at sub-micron film thicknesses on various substrates. Twelve-day field deployments were effective in detecting target compounds with good precision making EVA a potential multi-media fugacity meter.     

Numerical simulation of flame acceleration and deflagration-to-detonation transition of ethylene in channels

Ethylene (C₂H₄) is a hydrocarbon fuel and widely used in chemical industry, however, ethylene is highly flammable and therefore presents a serious fire and explosion hazard. This work is initiated by addressing the hazard assessment of ethylene mixtures in different scale channels (d = 5 mm, 10 mm and 20 mm) from the aspect of flame acceleration (FA) and deflagration-to-detonation transition (DDT) by using large eddy simulation (LES) method coupled with the artificially thickened flame (ATF) approach. The fifth order local characteristics based weighted essentially non-oscillatory (WENO) conservative finite difference scheme is employed to solve the governing equations. The numerical results confirm that flame velocity increase rapidly at the beginning stage in three channels, and the flame acceleration rate is slower in the subsequent stage, afterwards, the flame velocity has an abrupt increase, and the onset of detonation occurs. Due to the fact that wall effect is significant in the narrow channel (e.g.,5 mm), especially in the ignition stage of the flame, flames have different shapes in wider channels (10 mm and 20 mm) and narrow channel (5 mm). Both the pressure and temperature profiles confirm DDT run-up distances are 0.251 m, 0.203 m and 0.161 m in 20 mm, 10 mm and 5 mm channels, respectively, which indicates that a shorter run-up distance is required in narrower channel. The cellular detonation structures for the ethylene-air mixture in different channels indicate that multi-headed detonation structures can be found in 20 mm channel, as the channel width decreases to 10 mm, detonation has a single-headed spinning structure, as the width is further reduced to 5 mm, only large longitudinal oscillation of the pressure can be observed.     

乙烯排海废水深度处理及回用研究

茂名石化乙烯公司排海废水水质较好，远低于国家排放标准。经过深度处理后，水质可达到回用水要求。再进一步通过挂片腐蚀试验、杀菌试验和动态模拟试验，证明了乙烯排海废水能回用做循环水补充水。     

Genotoxic consequences of occupational exposure to ethylene oxide and formaldehyde ‐ a pilot study

The study evaluates chromosome damage caused by simultaneous occupational exposure to ethylene oxide (EtO) and formaldehyde (FA). To determine the extent of chromosome damage, eleven workers were analyzed using chromosome aberration (CA) assay, sister chromatid exchange (SCE) frequencies, micronucleus (MN) assay, and mitotic activity (MA). The results show significant deviations in subjects exposed to EtO and FA from control values in all four assays. The study shows a complex mode of action of EtO and FA on human genome and confirms the need for further research of cytogenetic risk which should be obtained through several assays.     

ETU mineralization in soil under influence of organic carbon content,temperature, concentration,and depth

The mineralization of ¹⁴C‐ETU was measured by the evolution of ¹⁴CO₂ and described with a mathematical model consisting of two terms — one term describing the immediate mineralization of ¹⁴C‐ETU and another term describing the first order degradation of humus and/or biomass, where ¹⁴C had been built in. The influence of pesticide concentration, depth of soil, and incubation temperature showed combined interaction effects on the amount of ¹⁴CO₂ formed during the process and on the degradation rate of the pesticide. With the addition of soil extract, a combined effect between concentration and addition of organic extract was seen for the degradation rate, while a three‐way interaction between depth, concentration and organic extract was seen for the formation of ¹⁴CO₂. Degradation of ¹⁴C‐ETU can thus not be described only through investigations of one single of the mentioned parameters.