离子膜辅助电催化氧化法预处理焦化废水的研究

焦化废水是属有毒有害、难降解的有机废水,常规的生物处理工艺对其去除效果不甚理想,从而导致出水中难降解污染物含量较高,COD和NH3-N不能达标。论文针对焦化废水的水质特点,采用离子膜电解技术进行预处理。对焦化废水中主要污染物苯酚降解效果的几种因素进行了研究,得出了苯酚降解的最佳工艺条件并在此工艺参数下,对模拟焦化废水电解2.5h,苯酚、COD的去除率分别为84%,45%,氨氮去除率和回收率别为99.5%和96.5%,总能耗27kwh/m3,可以为后续生化处理大大减轻负担,采用该方法作为焦化废水的预处理手段比较经济合理。     

蛭石吸附及解吸锌离子特性研究

用蛭石对锌离子的吸附解吸进行了实验研究,初步探讨了其对锌离子吸附解吸的机理。研究结果表明：蛭石对Zn^2＋具有较强的吸附能力,吸附在8h左右接近平衡。随着锌离子浓度的增加,蛭石的吸附量也在逐渐增加,当锌离子浓度达到400mg／L时,吸附量趋于平稳。在完成吸附实验的基础上,分别采用过滤和取上清液的方法解吸,实验证明静置平衡后,取出上清液50ml,再加入50ml解吸剂的方法解吸效果较好;解吸时间在0h到12h,蛭石的解吸量呈现递增的趋势,且达到1．070mg／g;在12h到48h内,解吸量基本没有增加,其中在24h时达到最大解吸量1．074mg／g。不同的解吸剂对蛭石解吸锌离子影响效果不同：蒸馏水不能使锌离子解吸;K^＋的影响作用相对于Na^＋更明显,随着两种阳离子浓度的增加,蛭石的解吸量逐渐增加。     

腐殖酸以及共存阳离子对膨润土吸附废水中铅离子的影响

研究了钠基膨润土的理化性质及其对水中铅离子的吸附作用,考查了pH值、共存阳离子浓度、腐殖酸浓度对铅离子吸附的影响,结果表明,钠基膨润土对水中铅离子有较好的吸附效果.铅离子在膨润土上的吸附量随pH值的升高而增加,随共存阳离子浓度的升高而减少,随腐殖酸浓度的升高而增加.从热力学角度探讨了吸附机理,发现钠基膨润土对铅离子的吸附量随温度升高而增大,并且吸附等温线符合Freundlich模型.计算了相关的吸附热力学函数:△H=0.9594kJ/mol, △S=16.611 3kJ/(mol·K).     

地方传真

上海：对能耗超标的企业实行惩罚性价格上海市日前取消电价目录表中离子膜烧碱等3类高耗能企业用电价格每年0．05元／千瓦时的优惠。继续对电解铝、铁合金、钢铁、电石、烧碱、水泥、黄磷、锌冶炼8个高耗能行业实施差别电价政策,并将限制类企业执行的电价加价标准由每千瓦时0．05元提高到0．15元,淘汰类企业执行的电价加价标准由每千瓦时0．20元提高到0．40元。对制革、印染、规划保留的工业园区之外的零星化工生产和危化生产企业,     

壳寡／聚糖系列衍生物对铅离子的吸附研究

比较了9种壳寡/聚糖系列衍生物作为吸附剂对同一浓度铅离子的吸附,结果为交联香草醛壳聚糖（CTSV-G）〉香草醛壳聚糖（CTSV）〉羧甲基壳聚糖（CM-CTS）〉巯基化壳寡糖（O-CTS-SH）〉壳寡糖（O-CTS）〉香草醛壳寡糖（O-CTSV）〉壳聚糖（CTS）〉壳寡糖硫酸酯（O-CTSS）〉羧甲基壳寡糖（CM-O-CTS）;比较了同一吸附剂对不同浓度的铅离子的吸附率,其吸附率随着溶液浓度的升高而降低。研究了各吸附剂在铅、镉、铬金属离子竞争中对铅吸附的影响,结果表明各吸附剂对镉和铅离子的吸附效果最好,可达80%,对铬离子吸附较少,在40%左右。     

Effect of ionic strength on adsorption of As（Ⅲ） and As（Ⅴ） on variable charge soils

The study was to investigate the adsorption behavior of arsenite (As(Ⅲ)) and arsenate (As(Ⅴ)) on two variable charge soils, i.e., Haplic Acrisol and Rhodic Ferralsol at different ionic strengths and pH with batch methods. Results indicated that the amount of As(Ⅲ) adsorbed by these two soils increased with increasing solution pH, whereas it decreased with increasing ionic strength under the acidic condition. This suggested that As(Ⅲ) was mainly adsorbed on soil positive charge sites through electrostatic attraction under the acidic condition. Moreover, intersects of As(Ⅴ) adsorption-pH curves at different ionic strengths (a characteristic pH) are obtained for both soils. It was noted that above this pH, the adsorption of As(Ⅴ) was increased with increasing ionic strength, whereas below it the reverse trend was true. Precisely the intersect pH was 3.6 for Haplic Acrisol and 4.5 for Rhodic Ferralsol, which was near the values of PZSE (soil point of zero salt effect) of these soils. The effects of ionic strength and pH on arsenate adsorption by these soils were interpreted by the adsorption model. The results of zeta potential suggested that the potential in adsorption plane becomes less negative with increasing ionic strength above soil PZSE and decreases with increasing ionic strength below soil PZSE. These results further supported the hypothesis of the adsorption model that the potential in the adsorption plane changes with ionic strength with an opposite trend to surface charge of the soils. Therefore, the change of the potential in the adsorption plane was mainly responsible for the change of arsenate adsorption induced by ionic strength on variable charge soils.     

Photocatalytic degradation of methyl orange over ITO/CdS/ZnO interface composite films

ITO/CdS/ZnO interface composite films were successfully prepared by subsequent electrodeposition of CdS and ZnO onto indium tin oxide (ITO) glass substrates. The obtained ITO/CdS/ZnO composite films were characterized with X-ray diffraction (XRD), scanning electron microscopy (SEM), and UV-Vis spectroscopy. The photocatalytic activity of ITO/CdS/ZnO composite films were investigated using methyl orange (MO) as a model organic compound under UV light irradiation. The influence of operating parameters on MO degradation including initial concentration of MO, pH value of solution, and inorganic anion species over the composite films were examined. A blue shift of absorption threshold was observed for the ITO/CdS/ZnO film in comparison with ITO/ZnO film. ITO/CdS/ZnO composite films prepared under specific conditions showed a higher photocatalytic activity than that of ITO/ZnO films. It was also found that the photocatalytic degradation of MO on the composite filing followed pseudo-first order kinetics.     

Synthesis, characterization, and adsorption performance of Pb（Ⅱ）-imprinted polymer in nano-TiO2 matrix

Surface ion-imprinted in combination with sol-gel process was applied to synthesis a new Pb(II)-imprinted polymer for selective separation and enrichment of trace Pb(II) from aqueous solution. The prepared material was characterized by using the infrared spectra, X-ray di ractometer, and scanning electron microscopy. The batch experiments were conducted to study the optimal adsorption condition of adsorption trace Pb(II) from aqueous solutions on Pb(II)-imprinted polymer. The equilibrium was achieved in approximately 4.0 h, and the experimental kinetic data were fitted the pseudo second-order model better. The maximum adsorption capacity was 22.7 mg/g, and the Langmuir equation fitted the adsorption isotherm data. The results of selectivity experiment showed that selectively adsorbed rate of Pb(II) on Pb(II)-imprinted polymer was higher than all other studied ions. Desorption conditions of the adsorbed Pb(II) from the Pb(II)-imprinted polymer were also studied in batch experiments. The prepared Pb(II)-imprinted polymer was shown to be promising for the separation and enrichment of trace Pb(II) from water samples. The adsorption and desorption mechanisms were proposed.     

风浪作用下太湖改性沉积物对藻体絮凝去除效果研究

以壳聚糖改性的太湖原位沉积物为分散介质,应用Y-型再悬浮发生装置,通过定量模拟太湖常见的中等级别风情,研究再悬浮作用下,改性沉积物对蓝藻水华的絮凝去除作用.结果表明,在黏土加入量为0.2　g·L^-1,壳聚糖分别为0.100和0.150　g·L^-1,其蓝藻的去除率分别为93.55%和99.19%;在静止30 min后,壳聚糖加入量为0.15 　g·L^-1时,水体的浊度去除率达到78.60%;静止8 h后,水体的浊度去除率达到93.88%.同时,短期内壳聚糖的加入对水体中PO^3-₄-P有一定的去除作用.初步结果表明,在中风风情下,壳聚糖的加入量为0.15　g·L^-1时,能更有效地去除蓝藻.表明利用壳聚糖改性沉积物来絮凝沉降太湖水华藻体,具有较好的应用前景.对比研究表明,引入水动力强度和水柱高度定量模拟方法,在确定壳聚糖投加量絮凝除藻中,具有明显的方法优势.     

pH和铜离子对微囊藻毒素-LR荧光免疫检测的影响与消除

研究了pH和铜离子对倏逝波全光纤免疫传感器检测微囊藻毒素-LR（MC-LR）的影响及其消除措施.研究表明,过酸或过碱条件对MC-LR免疫检测均有较强烈的影响,当pH<6或pH>8时,系统检测的信号随pH的降低或增大明显下降;而当pH在6～8之间时,检测标准曲线的IC₅₀为1.01～1.04 μg/L,检测区间在0.12～10.5 μg/L之间,较适合MC-LR的检测.低浓度铜离子对MC-LR免疫检测的影响不大,当CuSO₄浓度>5 mg/Ｌ时,系统检测荧光信号明显下降,而当CuSO₄浓度达到10 mg/Ｌ时,系统检测信号下降70％以上.在预反应混合物中添加1%的螯合剂EDTA,能有效抑制铜离子对免疫检测的影响.