聚合氯化铝铁絮凝剂的性能研究

煤矸石是采煤过程之废料。本文利用煤矸石制备出了聚合氯化铝铁（ＰＡＦＣ）：一种新型无机高分子絮凝剂，探讨了Ｆｅ＾３＋的稳定性与溶液离子强度之间的关系，发现溶液的离子强度越大，则产生Ｆｅ（ＯＨ）３沉淀时的ＰＨ越高。研究了ＰＡＦＣ水解产物的ζ电位及絮凝效果随ＰＨ的变化情况，比较了ＰＡＦＣ、ＰＡＣ和ＰＦＳ的除浊性能，ＰＡＦＣ在ＰＨ为７．０－８．２范围内除浊效果最佳，ＰＡＦＣ的除浊效果优于ＰＡＣ。     

沸石对降雨径流中氨氮的吸附特性

城市面源污染是重要水体污染源之一,降雨发生时,雨水径流会携带累积在路面、屋面的含有机物、氮磷、重金属等污染物质进入水体,其中氮磷是造成水体富营养化的重要因素。针对这一情况,采用不同种类沸石,对雨水径流中的氮磷进行了吸附研究,着重考察了沸石对氨氮的吸附动力学,吸附等温线特征,并考察了pH、共存阳离子以及COD对吸附能力的影响。结果表明,Na型改性沸石吸附性能优于其他2种,饱和吸附量达到9.09 mg/g,沸石的吸附过程符合准二级动力学模型。Mg2+、Ca2+对Na型改性沸石的影响较大,Na型改性沸石吸附氨氮的适宜pH为5~8。本研究为探索用物化方法来处理雨水提供了依据,Na型改性沸石可以作为吸附雨水中氨氮的优选吸附剂。     

Fe3O4-TiO2Al吸附剂去除水中氟离子

以实验室制备的Fe3O4-TiO2·nH2O·Al吸附剂处理模拟和实际含氟废水,探讨了吸附剂用量、体系pH、吸附温度和吸附时间等因素对F-吸附效果的影响。结果表明:在初始F-浓度16.1 mg/L,起始pH 8.0,吸附剂投加量5 g/L,室温(约25 ℃)下吸附15 min时,模拟和实际废水的出水F-均可达到3O4-TiO2·nH2O·Al具有一定的实际应用价值。含氟水溶液初始pH对Fe3O4-TiO2·nH2O·Al吸附F-性能影响较大。在pH 介于3.0~5.0 时,吸附容量较大,过高或过低都会导致吸附容量降低。Fe3O4-TiO2·nH2O·Al吸附F-的过程为放热反应,升温不利于F-的吸附。该吸附剂吸附F- 的过程为化学吸附,符合准二级动力学模型,等温线拟合接近Freundlich吸附等温线。     

城市生活垃圾渗透系数测试研究

采用常水头测渗实验，对不同压实密度和水力梯度下的新鲜垃圾与陈垃圾的渗透系数进行测试，根据达西定律求得渗透系数值。由于垃圾的不均匀性、小颗粒的运动和大孔隙沟道流的形成和改变，实验初始阶段渗透系数值先增大至峰值，然后缓慢降低直至趋于稳定。实验稳定后，新鲜垃圾压实密度为0．75—0．95t／m^3时，渗透系数值约为1．26E-03～1．43E-03cm／s。陈垃圾在压实密度分别为1．2和1．4t／m^3时，渗透系数为8．29E-04和1．35E-04cm／s。     

溶胶-凝胶法制备磁载光催化剂

悬浮态的光催化反应器相比固载的光催化反应器有更高的光催化效率。但是如何在光催化反应完成后使催化剂与水溶液的分离 ,成为了一个关键的问题。本研究采用溶胶 凝胶法将二氧化钛直接沉积在磁性颗粒的表面 ,制备出了磁载的光催化剂。这种催化剂在保留了磁性能具有可磁分离的基础上又具有很好的光催化降解效果。     

排水管道内湍动能分布特性及影响因素

污水中的污染物在管道输送过程中由于管道壁生物膜的微生物作用而发生降解,生化反应过程取决于物质从水相到生物膜之间的传质过程,传质过程受管道中流态特别是湍流作用的影响较大。采用PIV技术和FLUENT软件模拟下水道流态,重点研究充满度为0.1、0.2、0.3、0.4、0.5和坡度为0.003、0.005、0.008、0.01、0.03时水相中湍动能和湍动耗散率的沿程变化。结果表明,在充满度一定时管壁处的湍动能及湍动耗散率最大,且其随着坡度的增大而逐渐增大;坡度一定时,充满度越大管壁处湍动能及湍动耗散率越大。     

曝气深度对河道底泥特性及水质的影响

采用室内模拟实验方法对受污河道底泥和上覆水进行研究,对比分析静置状态X0和不同曝气深度条件下(分别为水体曝气泥水界面上方10 cm,底泥曝气下方5和15 cm处,依次记为X+10、X-5和X-15)河道底泥特性及水质的影响情况。结果表明:底泥曝气较水体曝气而言,能促进水体DO更快恢复;停止曝气,DO浓度也会维持在较高的状态,有利于有机物和氨氮的进一步去除。在相同曝气量下,底泥曝气比水体曝气能更好地去除底泥中污染物,并减少再次释放,且底泥曝气深度越深,处理效果越好,至实验结束时,X-15组上覆水中COD、NH4+-N、TN及TP浓度分别为16.25、3.03、13.39及0.09 mg/L,去除率分别为69.73%、78.36%、45.98%及84.21%;停止曝气后,经曝气处理的底泥对磷的吸附容量显著增加,并且不会再向上覆水中释放污染物,避免引起水体的二次污染。     

Effect of cadmium on nodulation and N2-fixation of soybean in contaminated soils

The effects of cadmium stress on nodulation, N2-fixation capabilities of the root nodule, the change in ultrastructure of the root nodule, soybean growth, and the distribution of cadmium in plants were studied. The results obtained show that the nodulation of soybean roots was greatly inhibited by the addition of Cd, especially at the addition level of 10 and 20 mg kg(-1) soil. The inhibition of plant growth, especially the root growth, increased as the cadmium concentration increased, with deleterious effects observed for the roots. The weight ratio of soybean root/leaf decreased as the Cd concentration increased, which might explain the reason for nodulation decreases. The results also indicate that N2-fixation of root nodule was stimulated to some extent at the low levels of Cd addition, but decreased sharply with further increase of the Cd concentration. High Cd levels were also associated with changes in the ultrastructure of root nodule, in which the effective N2-fixing area was reduced and the N2-fixing cells in the area also reduced. In addition, the results also reveal that the content of Cd in different parts of the plants was as follows: roots > stems > seeds, indicating that the accumulation of Cd by roots is much larger than that by any other part of the soybean plant, and might cause deleterious effects to root systems.     

Comparison of phosphorus forms in wet and dried animal manures by solution phosphorus-31 nuclear magnetic resonance spectroscopy and enzymatic hydrolysis

Both enzymatic hydrolysis and solution (31)P nuclear magnetic resonance (NMR) spectroscopy have been used to characterize P compounds in animal manures. In this study, we comparatively investigated P forms in 0.25 M NaOH/0.05 M EDTA extracts of dairy and poultry manures by the two methods. For the dairy manure, enzymatic hydrolysis revealed that the majority of extracted P was inorganic P (56%), with 10% phytate-like P, 9% simple monoester P, 6% polynucleotide-like P, and 18% non-hydrolyzable P. Similar results were obtained by NMR spectroscopy, which showed that inorganic P was the major P fraction (64-73%), followed by 6% phytic acid, 14 to 22% other monoesters, and 7% phosphodiesters. In the poultry manure, enzymatic hydrolysis showed that inorganic P was the largest fraction (71%), followed by 15% phytate-like P and 1% other monoesters, and 3% polynucleotide-like P. NMR spectroscopy revealed that orthophosphate was 51 to 63% of extracted P, phytic acid 24 to 33%, other phosphomonoesters 6 to 12%, and phospholipids and DNA 2% each. Drying process increased orthophosphate (8.4% of total P) in dairy manure, but decreased orthophosphate (13.3% of total P) in poultry manure, suggesting that drying treatment caused the hydrolysis of some organic P to orthophosphate in dairy manure, but less recovery of orthophosphate in poultry manure. Comparison of these data indicates that the distribution patterns of major P forms in animal manure determined by the two methods were similar. Researchers can utilize the method that best fits their specific research goals or use both methods to obtain a full spectrum of manure P characterization.     

Treatment and desalination of domestic wastewater for water reuse in a four-chamber microbial desalination cell

Environmental Science and Pollution Research - Microbial desalination cells (MDCs) have been studied for contaminant removal from wastewater and salinity reduction in saline water. However, in an...