TiO2镀膜电极光电催化降解酸性紫红

采用溶胶-凝胶法在钛片上涂覆TiO2薄膜为电极,自行设计组装光电催化反应器,对酸性紫红染料废水进行光电脱色处理,探讨了光电反应的协同性并研究了初始染料浓度、电压、pH和电解质浓度对脱色反应的影响。结果表明,光化学催化和电化学氧化具有协同效应,单一紫外光催化和单一电催化酸性紫红的脱色率分别为44.27%和13.12%,而光电催化(紫外、外加电压10 V)的脱色率达到77.18%。初始浓度较低、电压适中、pH偏碱性时,酸性紫红废水脱色率较高;电解质对脱色反应有促进作用,且浓度越高,酸性紫红脱色率越高。     

免烧结粉煤灰陶粒BAF对乙烯化工废水的深度处理效果

以粉煤灰为主要原料制备了免烧结粉煤灰陶粒,并将其作为曝气生物滤池(BAF)的填料用于深度处理乙烯化工厂二级生化出水。实验结果表明,在平均进水COD为54.62mg/L、平均SS为33.93mg/L、平均ρ(NH3-N)为1.33mg/L的条件下,自制免烧结粉煤灰陶粒BAF平均COD去除率为57.14%,平均SS去除率为68.64%,平均NH3-N去除率为74.89%,均略高于普通商业陶粒BAF。自制免烧结粉煤灰陶粒BAF最佳反冲洗周期为2d,并具有反冲洗耗水量小、反冲洗效果好的优势。     

乙二醇生产废水中特征污染物含量的测定

建立了气相色谱(氢火焰离子化检测器)检测乙二醇生产废水中乙二醇、二乙二醇、三乙二醇含量的新方法。该方法采用HP-FFAP型毛细管色谱柱,优化的色谱条件为:进样口温度230℃,初始柱温50℃,载气流量1.0mL/min,分流比1∶1。在质量浓度为1.0~150.0mg/L范围内,废水中各组分色谱峰面积与浓度呈良好的线性关系,相关系数均在0.9989~0.9996之间;相对标准偏差均小于2.0％;乙二醇、二乙二醇、三乙二醇的最低检出限分别为0.63,0.21,0.25mg/L,加标回收率为97.72％~103.52％。     

电絮凝处理牛仔布印染废水

用铁分别作为电絮凝反应系统的阴极和阳极,研究电絮凝法对牛仔布印染废水的处理效果。考察了电极电压、反应时间和pH等因素对电絮凝法去除实验所用废水中COD和色度效果的影响。结果表明,电极电压和反应时间是主要的影响因素,pH次之。电极电压24 V,反应时间35 min,pH为7.4时,脱色率可达99%,COD去除率在70%左右,处理效果最佳。因此,电絮凝法可以作为印染废水的预处理工艺,有效降低废水COD和色度。     

酸化油渣与膨胀型阻燃剂协效阻燃环氧树脂

餐厨垃圾生产柴油中产生酸化油渣固废(AR)。采用红外光谱(FTIR)法对AR进行分析,认为AR具有较好的阻燃成炭性能。将AR与多聚磷酸铵/三聚氰胺/季戊四醇(APP/MEL/PER)膨胀阻燃体系(IFR)复配,协效阻燃环氧树脂(EP),用极限氧指数法(LOI)、垂直燃烧法(UL94)对其阻燃性能进行了检测,并通过对燃烧残渣的分析讨论了阻燃机理。结果表明,当APP/MEL/PER/AR质量分数为25%,其中AR的质量分数为2%~6%时,阻燃EP的LOI达到30%,具有良好的阻燃性能,并降低了阻燃剂及阻燃材料总体成本。研究成果对餐厨垃圾能源化起到积极推动作用。     

Box-Behnken响应曲面法优化高聚复配絮凝剂制备条件

利用活性硅酸和聚合硫酸铁制备聚合硅酸硫酸铁,再采用二甲基二烯丙基氯化铵对其进行复配改性制备高聚复配絮凝剂。在单因素实验的基础上,以絮凝剂脱As性能为评价指标,采用Box-Behnken响应曲面法考察了Fe∶Si、改性剂量、改性温度对高聚复配絮凝剂制备的单独作用及交互影响作用,并建立了剩余c(As)的数学模型。结果显示,自变量对响应值的影响次序为:Fe∶Si改性温度改性剂量,改性剂量与改性温度及改性剂量与Fe∶Si交互影响显著;数学模型拟合度程度良好,模型显著,模型预测处理后最佳剩余c(As)=18.82μg/L,最佳工艺条件为Fe∶Si=2.1∶1,改性温度=79℃,改性剂量=0.56%(PFSS溶液质量),验证实验结果为剩余c(As)=19.21μg/L,预测值与测定值偏差率为2.07%。     

Application of Markov model to environmental fate of phenanthrene in Lanzhou Reach of Yellow River

The theory of Markov Chain is used scientifically to describe the transfer/transformation of phenanthrene in Lanzhou Reach of Yellow River. In Markov Model (MM), the states of phenanthrene in Lanzhou Reach are divided into six different states, namely being degraded, leaving the system with the addvective flow, being in air, being in water, being adsorbed on suspending substances (SS), and being in bottom sediment (BS). The MM is simulated by using Matlab6.5 to reveal the temporal changes and environmental fate of phenanthrene in Lanzhou Reach. It is shown that the environmental system will be steady in 30,000-35,000 h, the final distributions of phenanthrene in air, water, SS, and BS are 23,033 kg, 1961 kg, 800 kg, and 2824 kg respectively, with the corresponding percent of 80%, 7%, 3%, and 10%.The results of MM are approximate to the results of Fugacity Model (FM), so Markov Chain can be used to evaluate the environmental fate of pollutants in multimedia environment. The outputs of MM include the following aspects: (1) The residual time of pollutant in different environmental media and the transiting time of pollutant between different environmental media; (2) The response time of the environmental system; (3) The total mass of pollutant transferred or degraded during a given time interval; (4) The time needed for the environmental system to be steady and the final steady distributions of pollutant in the environmental system.     

Photocatalytic degradation of methyl orange in aqueous suspension of mesoporous titania nanoparticles

The photodegradation of methyl orange (MO) was investigated in aqueous suspension containing titania nanoparticles with mesostructures (m-TiO(2)) under UV irradiation. The experimental results show that 98% MO can be mineralized in the 1.0 g l(-1) m-TiO(2) suspension (pH 2.0) after 45 min illumination. Particular attention was devoted to the identification and the transformation of the fragments retaining the chromophoric group. The photodegradation mechanism of the quinonoid MO mainly involves three intermedial processes: demethylation, methylation and hydroxylation. Among those processes, demethylation is more favorable than the hydroxylation, but the hydroxylation results in the largest number of intermediates. The degradation pathway of quinonoid MO under the optimal conditions is also proposed.     

Removal of phenolic estrogen pollutants from different sources of water using molecularly imprinted polymeric microspheres

The efficiency and effects of using Bisphenol A-molecularly imprinted polymeric microspheres (MIPMs) to remove phenolic estrogens from different sources of water were evaluated. MIPMs prepared by precipitation polymerization removed a group of phenolic estrogens from different kinds of water selectively and effectively. The highest removal efficiency was observed at pH=5. Fifty millimoles per litre ions or 10mg/L humid acid improved removal efficiency. MIPMs were more suitable to remove trace estrogens in large volume than high concentration of estrogens in small volume. The removal efficiency of spiked tap water, lake water and river water were better than that of distilled water. Hundred milligrams of MIPMs had higher removal selectivity and efficiency than those of 100mg or 300mg activated carbons. Moreover, MIPMs can be re-used for at least 30 times without losing any removal efficiency. MIPMs provided a selective, simple, reliable and practicable solution to remove trace phenolic estrogens from different sources of water.