人尿中痕量铜的分光光度测定

本文采用自己合成的水溶性卟啉Ｔ（４－ＴＡＰ）Ｐ作试剂，在ｐＨ４５，盐酸羟胺存在下，建立了一种测定人尿中痕量铜的分光光度法，操作简便，结果准确，令人满意。     

CuAPO-5分子筛催化氧化水溶液中苯酚的性能

以水热晶化法合成了铜磷铝分子筛CuAPO-5，并用XRD、SEM，FT—IR，UV—Vis等对样品进行了表征，结果表明Cu^2＋进入到了AlPO4-5分子筛骨架中。研究了以CuAPO-5为催化剂，H2O2为氧化剂对水溶液中苯酚的催化氧化性能。在苯酚初始浓度200mg／L、H2O2添加量1200mg／L、pH值5．0、处理温度80℃时，处理240min时苯酚去除率达到100％，TOC去除率达81．76％，析出到溶液中Cu^2＋浓度仅为0．527mg／L。温度从40℃上升到80℃时，苯酚的去除率及TOC去除率明显增大，表明温度对催化剂的活性影响显著，相比于均相催化剂骨架Cu催化过氧化氢分解需要更多的能量。重复性实验表明，催化剂性能稳定。     

邻异丙基酚残渣的回收利用

邻异丙基酚残渣的回收利用湖南省临湘氨基化学品厂赵达邻异丙基酚生产过程中，歧化液蒸馏后的残渣就是邻异丙基酚残渣，主要成份有苯酚、多烷基酚、高沸物和酚铝等、年产１５００ｔ邻异丙基酚装置产渣量约３００ｔ，渣热值为４０６１４ｋＪ／ｋｇ，对残渣可观的热值，把它...     

苯酚在土壤中吸附的试验研究

采用动态法研究苯酚在不同土壤中的有吸附过程，试验结果表明，土壤的腐殖质含量，ＰＨ值，目数，含水率都对吸附过程产生影响。     

土壤中苯酚迁移转化的研究进展

近年来,由于污水灌溉和运输事故等原因造成土壤苯酚污染的事件多有发生,处理土壤苯酚污染已成为目前亟待解决的环境问题.本文根据土壤中苯酚的水运移,土壤颗粒对苯酚的吸附、土壤微生物对苯酚的降解、植物的吸收、苯酚的挥发等特性以及各种治理方法,提出土壤中苯酚污染的净化与修复措施.     

光电催化降解2,4-二氯苯酚的研究

采用Sol-Gel法制备了纳米TiO2／导电玻璃薄膜电极，应用XRD表征了TiO2薄膜的物相和粒度，以上述电极为工作电极和光催化剂，研究了2，4－二氯苯酚溶液的光催化和光电催化降解行为，结果表明，外加阳极偏压为0．7V，时间100min时，光电催化降解率为85％，高出光催化降解25％，2，4－DCP初始浓度（C0）与反应速率（r0)的关系符合Langmuir-Hinshelwood方程，当C0≤0．50mmol.L^-1时，光电催化降解速率可用一级动力学模式来描述。     

微生物降解苯酚废水的特性研究

通过对驯化微生物处理苯酚模拟废水的研究,考察了苯酚初始浓度、菌种投加量、葡萄糖添加量、废水pH值、反应温度等因素对苯酚降解效果的影响.结果表明,当苯酚浓度大于500mg/L时开始表现出对微生物的抑制作用,浓度高于700mg/L以后微生物降解效果不理想;当苯酚浓度为500mg/L时,微生物接种量大于400mg/L可获得最大降解速率;适量添加葡萄糖可促进微生物对苯酚的降解,但浓度超过0.2g/L以后由于底物竞争会对苯酚的降解形成抑制;生物降解苯酚的适宜pH值和温度范围分别为5.5～6.5和30～35℃.     

Degradation of 2,6-di-tert-butylphenol by an isolated high-efficiency bacterium strain

An aerobic bacterium strain, F-3-4, capable of effectively degrading 2,6-di-tert-butylphenol(2,6-DTBP), was isolated and screened out from an acrylic fiber wastewater and the biofilm in the wastewater treatment facilities. This strain was identified as Alcaligenes sp. through morphological, physiological and biochemical examinations. After cultivation, the strain was enhanced by 26.3% in its degradation capacity for 2,6-DTBP. Results indicated that the strain was able to utilize 2,6-DTBP, lysine, lactamine, citrate, n-utenedioic acid and malic acid as the sole carbon and energy source, alkalinize acetamide, asparagine, L-histidine, acetate, citrate and propionate,but failed to utilize glucose, D-fructose, D-seminose, D-xylose, sedne and phenylalanine as the sole carbon and energy source. The optimal growth conditions were determined to be: temperature 37℃, pH 7.0, inoculum size 0.1% and shaker rotary speed 250 r/min. Under the optimal conditions, the degradation kinetics of 2,6-DTBP with an initial concentration of 100 mg/L was studied. Results indicated that 62.4% of 2,6-DTBP was removed after 11 d. The degradation kinetics could be expressed by Eckenfelder equation with a half life of 9.38 d. In addition, the initial concentration of 2,6-DTBP played an important role on the degradation ability of the strain. The maximum initial concentration of 2,6-DTBP was determined to be 200 mg/L. Above this level, the strain was overloaded and exhibited significant inhibition.