特稠油污水处理技术研究

采用自己研究的药剂对辽河油田稠油污水进行破乳和净水试验，找出了主要影响因素，确定了处理工艺的操作条件。结果表明，使用破乳剂DI，可使油的回收率大于99％；絮凝剂A中添加了收缩絮体的化学药剂和B之后作为净水剂，使积杂量小于5％（体积比）。同时，处理后的水完全达到辽河油田要求的指标，即油含量小于5mg/L，积杂量小于15mg/L。     

小康居住区的水环境与水质净化工程

分析了小康居住区水环境的含义，组成，并对居住区水质净化工程中3个热点问题（优质饮水，污水处理和中水回用等）进行了较深入的分析，建议小康居住区优质饮水供应以小区纯水站净化，管理输送至用户方式为主；不居住区的污水处理应分3种情况区别对待，在居住区污水处理达到排放标准的基础上，进一步处理回用，是经济合理的。     

废气污染控制高新技术的研究与应用

列举了大量的事实，重点介绍了几种高新技术在废气污染控制中的研究与应用，说明了向环保发展迟缓领挑战依赖于科学技术，而环保的发展又向科学技术提出了更高的要求。     

磷肥厂烘干磨高压静电除尘技术及应用

本文根据高压静电除尘的原理,磷肥厂烘干磨粉尘的特性分析,以及作者本人的工作实践,探讨了高压静电除尘技术在磷肥厂烘干磨粉尘治理中应用的可行性。     

王甫洲工程泄水闸围堰基础高喷防渗墙施工

王甫洲水利枢纽工程泄水闸施工围堰基础主要为砂卵石层，结构中密～密实，属较强～极强透水层。使用改制的ＢＺＫ—３Ａ 型喷灌机，大水量、大浆量、不分序连续施工，高压定喷构筑围堰基础防渗板墙。经围井开挖检查，钻孔及围井挖后抽水试验、泄水闸基坑开挖后的防渗效果分析表明，高喷防渗板墙厚度、墙体强度及墙体渗透系数均满足设计要求     

Food justice youth development: using Photovoice to study urban school food systems*

How do youth learn through participation in efforts to study and change the school food system? Through our participatory youth action research (YPAR) project, we move beyond the “youth as consumer” frame to a food justice youth development (FJYD) approach. We track how a group of youth learned about food and the public policy process through their efforts to transform their own school food systems by conducting a participatory evaluation of farm-to-school efforts in collaboration with university and community partners. We used the Photovoice research method, placing cameras in the hands of young people so that they themselves could document and discuss their concerns and perspectives. The research was designed to gain insight about youths’ knowledge of food, health, and community food systems. Drawing upon the youth group’s insights, we build a framework for building critical consciousness through FJYD.     

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.     

On the effect of Fe(III) on proliferation of Microcystis aeruginosa at high nitrate and low chlorophyll condition

The impact of Fe concentrations on the growth of Microcystisaeruginosa in aquatic systems under high nitrate and low chlorophyll conditions was studied. The responses of cell density, total and cell chlorophyll-a intracellular Fe content and organic elemental composition of M. aeruginosa to different concentration gradients of Fe(III) in the solutions were analysed. The results showed that the proliferation speeds of M. aeruginosa were: (1) decelerated when the Fe(III) concentration was lower than 50 μg/L in the solutions, (2) promoted and positively related to the increase of Fe(III) concentration from 100 to 500 μg/L in the solutions over the experimental period, and (3) promoted in the early stage but decelerated in later stages by excess adsorption of Fe by cells when the Fe(III) concentration was higher than 500 μg/L in the solutions. The maximum cell density, total and cell chlorophyll-a were all observed at 500 μg Fe(III)/L concentration. The organic elemental composition of M. aeruginosa was also affected by the concentration of Fe(III) in the solutions, and the molecular formula of M. aeruginosa should be expressed as C_7–7.5H₁₄O_0.8–1.3N_3.5–5 according to the functions for different Fe(III) concentrations. Cell carbon and oxygen content appeared to increase slightly, while cell nitrogen content appeared to decrease as Fe(III) concentrations increased from 100 to 500 μg/L in the solutions. This was attributed to the competition of photosynthesis and nitrogen adsorption under varying cell Fe content.     

菌渣中阿维菌素残留检测方法及其无害化工艺研究

文章建立了简单、快速的阿维菌素菌渣中阿维菌素残留量高校液相色谱检测方法以及利用水热法处理阿维菌素菌渣。采用固相萃取-高效液相色谱检测方法测定阿维菌素菌渣中阿维菌素残留量,提取剂为乙腈/水=4/1(V/V),采用HLB固相萃取柱进行净化。加标回收率90.3%~107.3%,相对标准偏差(RSD)为3.00%~5.69%,阿维2菌素标准曲线线性相关系数R~2=0.999 6,线性范围为1.0~1 000 mg/L。利用正交实验,水热法处理阿维菌素菌渣,在190℃的温度下处理2 h后,菌渣中阿维菌素残留量由991.30降至0.84 mg/kg,去除率达99.92%。处理前后的菌渣与有机肥标准作对比,除含水率外其余检测指标均达到有机肥标准要求。该项研究为阿维菌素菌渣的资源化利用提供了理论依据。     

厌氧氨氧化工艺脱氮及其污泥形态的研究

为研究厌氧氨氧化工艺对高浓度含氮废水的脱氮性能,在以聚乙烯海绵作为填料的上流式厌氧固定床反应器中利用人工配置高浓度含氮废水进行了实验研究.实验中通过添加充足无机碳源,实现了厌氧氨氧化反应器在总氮浓度900～1 210 mg/L长期稳定的运行,脱氮效率在80％以上,最高氮负荷为5.9 kg/m3·d.结果表明:充足的无机碳源在一定程度上可有效地降低高浓度亚硝氮对厌氧氨氧化菌的抑制作用.通过对污泥性状的研究,明确寻找出污泥上浮的原因所在.通过Stover-Kincannon模型确定系统动力学参数KB和Umax分别为30.2 g/L·d和2L2g/L·d,这将有助于对该厌氧氨氧化系统各控制条件的有效调节和准确设定,也为日后应用于实际工程中提供重要的理论依据.