化学活化法制备麻疯树果壳活性炭的实验研究

以麻疯树果壳为原料,KOH为活化剂,通过化学活化法制备活性炭。考察了反应温度、反应时间和碱炭比（KOH与麻疯树果壳炭化料的质量比）等因素对活化结果的影响,并利用N2吸附和BET等现代分析测试方法来表征活性炭的结构特征。结果表明,化学活化法制备的活性炭吸附剂性能较好,且当活化温度为850℃,活化时间为240min,碱炭比R=4时制得活性炭产品的质量最好;化学活化法制备的活性炭为微孔吸附剂,在最佳条件下得到最大的碘吸附值和比表面积分别为2218．44mg／g和1890m^2／g。     

氧浓度对煤低温氧化热效应影响规律研究

为了准确掌握氧浓度对煤低温氧化热效应的影响,采用C80微量量热仪研究低温阶段煤氧化的自热过程,根据单升温速率的非等温动力学分析方法,得到不同氧浓度下煤样的活化能。研究结果表明:氧浓度对实验初始阶段的热流曲线和放热量的影响较小,随着温度的升高,氧浓度对热流曲线和放热量影响逐渐变得明显,放热趋势随着氧浓度的增大而增强;煤样的初始放热温度随着氧浓度的增大而降低;活化能随着氧气浓度的降低呈阶梯式上升;总放热量和氧浓度服从线性方程y=ax+b;与21%（空气气氛）氧浓度相比,15%,10%和5%氧浓度下煤的放热量分别降低了约19%,33%和46%,表明降低氧浓度对煤样的氧化放热具有明显的减缓作用。因此可以加强采空区的密闭性检测、注入惰性气体,使采空区的氧浓度尽可能地低,对采空区煤自热升温的防治有着理论指导意义。     

长柄扁桃核壳活性炭的制备及表征

以长柄扁桃核壳为原料采用磷酸活化法制备活性炭,分别研究了温度、时间、浸渍比和磷酸浓度对活性炭吸附性能的影响;进而采用氮气吸附曲线和SEM对最佳工艺条件下的活性炭进行了表征。结果表明,长柄扁桃核壳是一种优质的活性炭原料;当温度为400℃,活化时间2 h,浸渍比2：1,磷酸浓度60%时,得到产率为46.46%,碘吸附值和亚甲基蓝吸附值分别为1 073 mg/g、255 mg/g,比表面积高达1 740 m²/g,中孔率为73.12%的孔隙发达的高中孔率活性炭。     

石墨烯电极电活化过硫酸盐降解含酚废水研究

以苯酚为目标污染物,利用石墨烯电极自身性质及电活化共同作用下活化过硫酸盐(PDS)产生氧化性自由基降解苯酚,对影响苯酚降解的因素(包括电流密度、初始pH值、PDS浓度及影响反应的主导自由基)进行探讨。通过系统中加入一定量的甲醇和叔丁醇作为自由基猝灭剂的猝灭试验确定降解过程中的主导自由基。结果表明,在未通电情况下石墨烯电极对苯酚也具有去除作用,可以吸附苯酚。在通电情况下,由于电活化和石墨烯活化的双重作用,相比于单一石墨烯体系和单一PDS体系,石墨烯/PDS体系对苯酚的降解率显著提高,在n(PDS)∶n (phenol)为50∶1、苯酚初始质量浓度为25mg/L、pH值为11、电流密度为30 mA/cm²的条件下,在90 min内苯酚的降解率可达98.91%。通过淬灭试验确定在石墨烯/PDS降解苯酚体系中以硫酸根自由基为主(SO₄^-·)、羟基自由基(·OH)为辅。综上所述,在未通电情况下,石墨烯可以利用自身吸附作用去除苯酚,在通电情况下,石墨烯电极利用自身性质以及电活化活化过硫酸盐,与单一PDS体系和单一石墨烯体系相比,有效提高了过硫酸盐的活化程度,提高了苯酚的降解率。     

废利乐包资源化回收铝及制备活性炭研究

将废利乐包热解并对获得的热解炭和铝箔进行分拣,再以热解炭为原料,K₂CO₃为活化剂制备活性炭。通过热重/差热-傅里叶变换红外光谱(TG/DTA-FTIR)联用对废利乐包的热解特性进行分析,采用自动气体吸附仪测定活性炭的氮气吸附/脱附曲线,采用FTIR对活性炭的表面官能团进行表征,利用TG-FTIR联用研究了活性炭的活化机理。结果表明,废利乐包中的纸和聚乙烯分别在365和490 ℃发生热解,铝箔则在664 ℃时熔化,填充剂CaCO₃在720 ℃发生分解。活性炭的比表面积和总孔体积分别为1 215 m ²/g和0.768 cm ³/g,其表面官能团主要为C=O、C—O—C和脂肪族C—H。热解炭本身含有的CaCO₃在740 ℃分解生成CO₂,CO₂会氧化刻蚀炭基体进行造孔;820 ℃之后熔融的K₂CO₃也会与炭基体反应生成CO并造成炭的损耗,上述2个过程均参与了活性炭的活化造孔。     

Reactions of the amine-containing drugs fluoxetine and metoprolol during chlorination and dechlorination processes used in wastewater treatment

The reactivities of the amine-containing pharmaceuticals fluoxetine and metoprolol with hypochlorite were studied using conditions that simulate wastewater disinfection including neutral pH (7.0), a range of reaction times (2–60 min), and a molar excess of hypochlorite relative to the pharmaceutical concentration (5.7 times). The reactions were monitored using liquid chromatography (LC) with several detection modes including ultraviolet absorbance (UV), mass spectrometry (MS), and post-column reaction/reductive electrochemistry (EC) for determining active chlorine products. At levels of 10 μM, both compounds reacted rapidly (<2 min) to form principally N-chloramine products that were stable in aqueous solution for at least 1 h. The reaction was also studied in wastewater, and similar reactivity was noted. These results demonstrate that the cations fluoxetine and metoprolol are likely to be rapidly transformed into neutral N-chloramines during wastewater disinfection. The reactivity of the N-chloramines was also studied with sulfite to simulate dechlorination, which is often employed in wastewater treatment. Both N-chloramines reacted slowly with sulfite. In the pure water dechlorination experiments, it was estimated that 70% and 10% of the peak areas remained after 2 min reaction time for fluoxetine and metoprolol, respectively. At longer reaction times both N-chloramines had been completely reduced by sulfite, and the product of the sulfite reduction reaction was the parent pharmaceutical amine. Since typical dechlorination times in wastewater treatment are on the order of seconds, this suggests the chloramines formed from these two basic drugs might evade dechlorination and be released into the environment. The implications of chloramine release are discussed.     

零价铁活化过硫酸钠体系降解污染土壤中的多环芳烃

采用Fe0活化Na2S2O8体系降解污染土壤中的PAHs,其代表化学物为NAP、PHE、FLA和BAP。分别研究了Na2S2O8的添加量、Na2S2O8与Fe0的物质的量比、水土比和温度对降解效果的影响,同时探讨了PAHs的降解动力学;并利用电子顺磁共振法(EPR)验证了Fe0活化Na2S2O8的自由基产生情况。结果表明,当1 mol·L-1的Na2S2O8添加量为10 mL、Na2S2O8与Fe0物质量之比为200∶1、水土比为2∶1、温度为60 ℃时反应36 h后,NAP、PHE、FLA、BAP的降解率分别为98.15%、78.41%、93.47%和97.64%。PAHs的降解符合一级反应动力学,且BAP的反应速率常数最大为0.030 5 h-1。EPR谱图表明,Fe0活化Na2S2O8降解PAHs污染的土壤是SO4-·和·OH共存的反应体系。该研究可为Fe0活化Na2S2O8体系降解PAHs污染土壤的机理提供一定的依据。     

程序升温脱附法测定活性炭上酯类有机物的脱附活化能

采用程序升温脱附(TPD)法,测定了5个不同升温速率下乙酸甲酯、乙酸乙酯、乙酸异丙酯、乙酸丁酯的程序升温脱附曲线,研究了其脱附活化能、及其与汽化潜热及偶极距之间的关系。4种酯类有机物在活性炭上的吸附过程是物理吸附,脱附活化能大小依次为:乙酸甲酯(20.17 kJ/mol)<乙酸异丙酯(27.4 kJ/mol)<乙酸乙酯(28.4 kJ/mol)<乙酸丁酯(51.9 kJ/mol);脱附活化能随物质沸点变化不明显,随汽化潜热的增大而增大,且与其极性大小有关,极性越大,越易被吸附。     

基于过碳酸钠的类Fenton体系对亚甲基蓝的降解动力学

采用改良低温结晶法制备过碳酸钠(sodium percarbonate,SPC),对其进行XRD表征,并用以作为氧化剂构建类Fenton体系(SPC/Fe2+)降解亚甲基蓝(MB),对其降解的影响因素及反应动力学进行了研究。结果表明,在该体系中,当溶液初始pH分别为2~10时,亚甲基蓝的去除率在1 min时均可达到97%以上,说明该体系可高效去除水体中的亚甲基蓝,反应速率快,且过碳酸钠的使用可以拓宽Fenton反应的pH范围。该反应的最佳工艺条件为0.75 g·L-1硫酸亚铁,300 mg·L-1过碳酸钠,亚甲基蓝去除率在反应10 min后可达99.0%。亚甲基蓝在该体系中的降解遵循二级反应动力学方程,反应速率常数分别为64.50×10-3 L·(mol·s)-1,快于Fenton体系的17.83×10-3 L·(mol·s)-1。该体系反应活化能为16.6 kJ·mol-1,远小于Fenton体系(46.234 kJ·mol-1),说明以过碳酸钠为氧化剂更有利于非均相类Fenton反应的发生。     

Retinue attraction and ovary activation: responses of wild type and anarchistic honey bees (Apis mellifera) to queen and brood pheromones

In most social insect colonies, workers do not attempt to lay eggs in the presence of a queen. However, in the honey bee (Apis mellifera), a rare phenotype occurs in which workers activate their ovaries and lay large numbers of male eggs despite the presence of a fecund queen. We examined the proximate mechanisms by which this ‘anarchistic’ behaviour is expressed. We tested the effects of brood and queen pheromones on retinue attraction and worker ovary activation using caged worker bees. We found no difference between the anarchistic and wild type queen pheromones in the retinue response elicited in either wild type or anarchistic workers. Further, we found that anarchistic queens produce a pheromone blend that is as effective at inhibiting ovary activation as the wild type queen pheromone. However, anarchistic workers are less inhibited by queen pheromones than their wild type counterparts, in a dose-dependent manner. These results show that the anarchistic phenomenon is not due to changes in the production of queen pheromones, but rather is due in part to a shift in the worker response to these queen-produced signals. In addition, we demonstrate the dose-dependent nature of the effect of queen pheromones on honey bee worker ovary activation.