用溴化容量法测定间甲酚的含量

探讨了间甲酚含量的容量分析方法。通过试验确定了利用溴化容量法测定间甲酚含量的最佳分析条件：反应温度为18～30℃、溴化反应时间为8～10min、溴化反应的酸度为1．0～1．5mol／L、溴过量50％～100％。此法简便快速,精密度好,准确度高,对高浓度和低浓度的试样均能获得满意的结果,检出下限为0.5％(5mg／L)。     

运用分子轨道理论考察甲酚的生物降解特性

运用分子轨道理论考察了甲酚同分异构体的生物降解特性。计算出最高占据轨道（HOMO）能量的大小，反映了甲酚同分异构体生物降解反应的难易程度，且结论与事实相符合。     

粉煤灰及改性粉煤灰对邻甲酚吸附性能的研究

研究了水溶液中粉煤灰(FA)和浸渍粉煤灰(IFA)吸附有害的邻甲酚,试验了颗粒大小、浸渍条件、pH值和温度等因素对吸附量的影响.结果表明,在稀溶液中进行吸附时,提高温度、减小粒径和pH值,可增加粉煤灰对邻甲酚的吸附量;用Al3+离子浸渍的粉煤灰具有较大的吸附量;吸附过程机理主要是多孔物质和静电作用的共同结果所致.     

甲酚异构体在活性炭上的吸附与解吸平衡特性

以邻、间、对甲酚为模拟废水,考察甲基的取代位置对吸附和解吸特性的影响,并以此评价活性炭吸附生物再生工艺处理甲酚废水的可行性.平衡数据经Freundlich模型拟合后表明,活性炭(AC)对3种甲酚的吸附能力由大到小的顺序为：对甲酚>邻甲酚>间甲酚,与pK_a呈正相关,与可溶性和氧化电极电位呈负相关;解吸能力由大到小的顺序为：邻甲酚>间甲酚>对甲酚,与沸点和黏度呈负相关.此外,对比吸附和解吸平衡曲线,发现吸附不可逆性是两曲线差异的重要原因,并结合数理统计的方法推导出理论不可逆吸附量的计算方法,得到AC对邻、间、对甲酚的不可逆吸附量Qi分别为27.9、 28.5、 33.4 mg/g.     

Determination of phenol,cresols and xylenols in workplace air using XAD‐2 sorbent cartridges

A method for sampling and analysis of phenolic compounds in workplace atmospheres using Amberlite XAD‐2 sorbent tubes has been laboratory and field tested. After extraction of the adsorbed phenols with methylene chloride, the concentrated extract was analyzed by capillary column gas chromatography coupled with a flame ionization detector or a mass spectrometer. For a 3L air sample, the method has a detection limit for phenol, cresols, alkyl‐substituted phenols and xylenols of 0.3 mg/m³ using gas chromatography with flame ionization detection (GC/FID) analysis and 0.07 mg/m³ using gas chromatography mass spectroscopy/selected ion monitoring GC‐MS/SIM. Evaluation tests conducted in the laboratory indicated recoveries >85% for a wide range of phenols, cresols, xylenols and other alkyl‐substituted phenols and resorcinol. Sampling conditions were established to ensure that no breakthrough occurred for a predetermined sample volume of three (3) liters even in humid atmospheres. Stability tests indicated that for storage of up to 2 weeks at 4°C, only resorcinol showed a significant reduction in sample recovery. The proposed method and NIOSH Method 3502 were compared for the determination of phenol concentrations in air samples collected at a plant processing phenolic resins. Phenol was positively identified in the XAD sample using GC‐MS/SIM and was detected at concentrations of 40–50% of the total phenols detected using NIOSH Method 3502. This difference is attributed to the airborne paniculate matter which is known to contain bisphenols that will contribute to the total phenolic content sampled in Method 3502, but not on the XAD sample.