高铁氧化去除饮用水中邻氯苯酚的研究

采用自制的固体高铁酸钾作为氧化剂，研究高铁对水中微量邻氯苯酚的去除效果及主要影响因素。结果表明，当水中邻氯苯酚的含量为4mg/L时，加入60mg/L的K2FeO4氧化处理10min，对邻氯苯酚的去除率可达99．3％。取得高铁酸钾对邻氯苯酚的最佳氧化去除效果的pH范围为9－10，高铁氧化邻氯苯酚近似的二级动力学反应。     

Transformation and migration of phosphorus in excess sludge reduction pretreatment by alkaline ferrate oxidation combined with anaerobic digestion

Recently,more and more attention has been paid to the strong oxidation ability of newly prepared potassium ferrate(NAPF) in sludge reduction process,but less attention has been paid to the change of phosphorus in this process.The feasibility of phosphorus migration and transformation during excess sludge reduction pretre atment using NAPF pre-oxidation combined with anaerobic digestion was investigated.After 70 mg/g suspended solids NAPF pretreatment and 16 days anaerobic digestion,the solid-phase volatile suspended solids decreased by 44.2%,and much organic matter had been released into the liquid-phase and then degraded during digestion by indigenous microorganisms.As the sludge pre-oxidation process was performed,solid-phase organic phosphorus and chemically combined phosphorus also released into the liquid-phase as PO_4~(3-),peaking at 100 mg/L.During anaerobic digestion,the Fe~(3+)in the liquid-phase was gradually reduced to Fe~(2+),and then formed Fe~(2+)-PO_4~(3-) compound crystals and re-migrated to the solid-phase.The concentration of PO_4~(3-) decreased to 17.08± 1.1 mg/L in the liquid-phase after anaerobic digestion.Finally,the phosphorus in the Fe~(2+)-PO_4~(3-) compound accounts for 80% of the total phosphorus in the solid-phase.A large number of vivianite crystals in sludge were observed.Therefore,this technology not only effectively reduces sludge,but also increases the proportion of PO_4~(3-)in the sludge in the form of Vivianite.     

K2FeO4氧化降解3,4－二甲基苯胺的机理研究

以3,4－二甲基苯胺为目标污染物,高铁酸钾（K₂FeO₄）为氧化剂,考察催化氧化过程中的表观动力学及反应机制,确定高铁酸钾降解3,4 －二甲基苯胺的表观动力学方程为：r=0.0043C_A^0.486C_B^1.2477,反应级数为1.7337,符合准二级动力学方程.同时通过GC/MS技术,分析降解过程的中间产物,推测在高铁酸钾的作用下,3,4－二甲基苯胺先转变成2,4－二甲基苯胺,然后苯环上的氨基及甲基先后被氧化,生成4－硝基间苯二甲酸,再发生脱羧反应,生成硝基苯,硝基苯被高铁酸钾进一步攻击,生成苯环正离子,其后开环生成一系列小分子烃类物质,这些物质继续被氧化,最终生成二氧化碳与水.推测该氧化还原过程的控制反应为两步：第一步,高铁酸钾攻击3,4－二甲基苯胺苯环上的侧链;第二步为苯环的开环反应.此降解过程主要包括表面络合催化与界面催化两种反应机制.     

两种国标方法测定大气中二氧化硫的比较研究

国标方法中环境空气中二氧化硫的测定方法主要有甲醛吸收-副玫瑰苯胺分光光度法和四氯汞盐吸收-副玫瑰苯胺分光光度法.对国标方法中两种副玫瑰苯胺分光光度法测定环境空气中二氧化硫所用的两种吸收液(四氯汞钾、甲醛)的吸收效果及方法的准确性、精密度等条件作了比较试验.结果表明,采用甲醛溶液作吸收液与四氯汞钾溶液作吸收液相比,吸收效果、精密度和准确度更好,测定的检出限低.用甲醛溶液做吸收液,除了上述优点外,还可避免使用大量的汞盐,有利于环境保护.     

高铁酸盐氧化絮凝去除含油污水中的油

油田产出的油、水经分离后会产生大量的含油污水,选用高铁酸钾对污水进行处理已成为人们关注的一个问题。用荧光比色法测定非均相固-液悬浮体系中油含量的实验证明:(1)高铁酸盐在含油污水中的初始反应速度快,可将大部分有机物氧化;(2)氧化法处理含油污水受多种因素的影响;(3)高铁直接氧化和芬顿氧化法均可比较彻底地处理油田含油污水。用高铁氧化法处理含油污水技术上很有发展前景,各种浓度的污水经处理后都可达到国家排放标准。     

用过硫酸钾氧化—紫外分光光度法测定地表水中总氮的几个问题

通过对过硫酸钾溶解方式及储存时间的条件实验，表明，用过硫酸钾氧化一紫外分光光度法测定地表水中的总氮时，过硫酸钾氧化剂以自然溶解为好，存放时间以不超过３ｄ为为宜，还对影响总氮测定的准确度、精密度的实验因素进行了探讨。     

南京市机动车尾气污染现状调查及其对人群健康的影响

机动车尾气排是影响城市大气环境质量的重要因素，监测表明：南京市道路环境污染来重，尤其是隧道及交通繁忙的路段。通过对２２０人作问卷调查，发现机动车尾气污染已对经常接触的人群产生很大的影响。     

高铁酸钾预处理强化污泥破解及厌氧产酸

在序批式污泥厌氧反应器中探究了高铁酸钾对污泥破解及厌氧产酸的影响。实验结果表明高铁酸钾对污泥具有较强的破解性,当高铁酸钾的质量浓度由0 mg/L增加至16 mg/L时,溶解性COD与总COD的比值由6.2%升至35.6%。同时污泥液相中溶解性蛋白质的质量浓度由561 mg/L增加至1 365 mg/L。高铁酸钾的浓度与挥发性悬浮固体(VSS)的减量具有一定的线性关系。当高铁酸钾的质量浓度为8 mg/L时,污泥厌氧产挥发性脂肪酸最大,并且最大值为895 mg/L,其浓度是空白组2.56倍。     

海水中总氮的测定方法比较研究

通过标准曲线、检出限和测定范围、方法精密度、方法准确度、实际海水样品测定结果、加标回收率、分析效率和物料消耗这几方面比较了过硫酸钾氧化法、流动注射分析法和高温氧化-化学发光检测法这3种测定海水中总氮(TN)方法的优缺点。结果表明,流动注射分析法和高温氧化-化学发光检测法的测定范围更宽,精密度、准确度更好,3种样品的加标回收率达到96.2%~101%;高温氧化-化学发光检测法分析效率高、物料消耗少、节能环保,适用于一般海水样品的批量分析,且由于测定范围大,该法也适用于TN浓度较高的海水样品的批量分析,流动注射分析法因其较低的检出限更适用于TN浓度较低的海水样品的批量分析。     

Plant uptake of radiocaesium from artificially contaminated soil monoliths covering major European soil types

Uptake of ¹³⁷Cs was measured in different agricultural plant species (beans, lettuce, barley and ryegrass) grown in 5 undisturbed soil monoliths covering major European soil types. The first cultivation was made three years after soil contamination and plants were grown during 3 successive years. The plant–soil ¹³⁷Cs transfer factors varied maximally 12-fold among soils and 35-fold among species when grown on the same soil. Single correlations between transfer factors and soil properties were found, but they varied widely with plant type and can hardly be used as a predictive tool because of the few soils used. The variation of ¹³⁷Cs concentrations in plants among soils was related to differences in soil solution ¹³⁷Cs and K concentrations, consistent with previous observations in hydroponics and pot trials. Absolute values of transfer factors could not be predicted based on a model validated for pot trials. The ¹³⁷Cs activity concentration in soil solution decreased significantly (11- to 250-fold) for most soils in the 1997–1999 period and is partly explained by decreasing K in soil solution. Transfer factors of lettuce showed both increasing and decreasing trends between 2 consecutive years depending on soil type. The trends could be explained by the variation in ¹³⁷Cs and K concentrations in soil solution. It is concluded that differences in ¹³⁷Cs transfer factors among soils and trends in transfer factors as a function of time can be explained from soil solution composition, as shown previously for pot trials, although absolute values of transfer factors could not be predicted.