用超滤法处理回用生活污水

研究了用超滤法处理山西铝厂生活污水站出水的阻力特性及清洗可恢复性,通过试验对比了颗粒活性炭、微滤 颗粒活性炭和混凝进行处理污水后的超滤效果.试验结果表明,污水经微滤 颗粒活性炭预处理后,可以得到较好的过滤效果,过滤阻力低;用质量浓度为500mg/L的NaClO溶液反洗浸泡后可以得到较好的清洗效果;混凝可以去除悬浮物、胶体及污水中的部分有机物,明显降低了膜过滤阻力;超滤的产水水质符合生活杂用水标准GB JXX—2001的要求.     

Inactivation Removal for Excess Propagation of Copepod of Zooplankton in Ozone-Granular Activated Carbon Filter in Southern China

Comparative experiments on the inactivation of Copepod were investigated in southern China.The 100% of inactivation effect may be attained by 3.0 mg/L of ozone for contacting time of 25 min,whereas 0.5 mg/L of dosage resulted in only 30% of inactivation rate.Copepod may not be completely inactivated by ozone oxidation for feasible dosage limited by higher bromide in raw water.The favorable environment of granular activated carbon(GAC)filter provided Copepod with conditions for excess propagation.The disinfe...     

活性炭对2，4-二氯苯酚的催化臭氧化降解

研究了粒状活性炭（GAC）对2，4-二氯苯酚（2，4-DCP）臭氧化降解的催化性能。由于活性炭的吸附和催化作用，提高了2，4-DCP的分解。在酸性条件下具有较高的催化臭氧化效率，而酸性和碱性的强弱对2，4-DCP的分解几乎没有影响。活性炭的重复使用实验表明活性炭在臭氧化处理过程中可以得到原位再生，多次使用后其催化活性几乎没有降低。     

Pilot Study on Nanofiltration Combined with Ozonation and GAC for Advanced Drinking Water Treatment

IntroductionThe conventional process for surface water treatment,which consists of flocculation, sedimentation and filtrationcurrently, had been applied inproducingdrinkingwater formany years. Although this process can remove turbidityand bacteria in surface water effectively, only about from20% to 30% of natural organic matter ( NOM) can beeliminated. When the purified water is disinfected bychlorination, these NOMs may react with chlorine. As aresult some dis…     

Pt/GAC催化剂的制备及催化氧化冷凝废水研究

以H2PtCl6·6H2O为前驱体,颗粒活性炭为载体,采用乙二醇还原法制备Pt/GAC催化剂,并用于催化氧化冷凝废水.实验结果表明,当催化剂活性组分Pt负载量为1.5%、焙烧温度为350 ℃、NaOH与Pt的物质的量的比为6∶ 1条件下制备的催化剂具有较高的催化活性,在反应温度40 ℃和常压条件下,催化剂投加量为13.33 g/L和反应时间为2 h,冷凝废水中85%以上的乙醇被氧化,而且催化剂重复使用6次后,冷凝废水中80%以上的乙醇可被氧化,其催化活性仍然达到80%以上.该种条件下制备的催化剂粒径约为5～15 nm,活性组分Pt以Pt0的形式在载体表面均匀分布.     

微波辅助催化氧化高浓度含醛废水应用研究

考查了活性炭（GAC）固定床反应器在微波辅助催化氧化作用下对某石化公司高浓度含醛废水的连续处理情况,在消除活性炭吸附作用后,在微波功率400W、废水流量6．0mL／min、空气流量0．085m^3／h和45gGAC条件下对含醛废水（初始CODCr浓度为33494mg／L）进行了处理．实验结果表明,含醛废水的CODCr去除率为94％,TOC去除率为99％;在没有GAC的条件下,微波对含醛废水则几乎没有效果．     

TiO_2/GAC光催化剂对中水杀菌效果的研究

探讨了利用太阳光作光源,固定在颗粒活性炭上的二氧化钛光催化剂(T iO2/GAC)对中水除菌效果的影响因素.实验表明细菌的浓度范围在5.7×107~5.7×102cfu/mL时,光催化除菌率为86.1%~99.5%.光照强度在1.35 mW/cm2时,除菌率达96.6%.光照加T iO2/GAC 3 h时,99%以上的菌体死亡.仅光照无T iO2/GAC时除菌效果甚微,只有15.4%的菌体失活;仅有T iO2/GAC无光照,除菌率为42.3%.     

基于水平集运动目标检测与跟踪方法

针对目前常采用的运动分析检测方法存在的缺点,提出了基于水平集理论的测地线活动轮廓模型与背景差分相结合的运动目标检测方法.该方法使水平集函数免重新初始化,大大减少了曲线演化迭代的次数和运行时间,得到准确的运动目标轮廓.通过与粒子滤波和mean shift跟踪方法的比较,最终采用效率最高、最优的Kalman滤波预测物体的运动轨迹.实验结果表明,该方法对刚性和非刚性两类目标都具有较好的检测与跟踪效果.     

颗粒活性炭对SBR反应器中好氧颗粒污泥培养的影响研究

好氧颗粒污泥培养耗时长已经成为限制其广泛应用的重要因素之一,依据"晶核假说"原理,在反应器中投加惰性核可以加快污泥好氧颗粒化进程.为了研究颗粒活性炭对于污泥好氧颗粒化进程的影响,在SBR反应器启动初期投加颗粒活性炭(SBR有效体积的1%,平均粒径为0.1—0.3mm)作为诱导核,采用扫描电镜和细菌凋亡荧光染色来表征好氧颗粒污泥.结果表明,颗粒活性炭有利于好氧颗粒污泥的形成,运行20d即获得了成熟的好氧颗粒污泥.扫描电镜结果显示,成熟的好氧颗粒污泥结构密实,微生物种类较为丰富.好氧颗粒污泥细菌凋亡荧光染色结果表明死细菌分布较为均匀,但活细菌多位于外层;胞外多聚物多重荧光染色表明蛋白质和多糖(α-吡喃葡萄糖、α-甘露糖和β-D-吡喃葡萄糖)等物质在好氧颗粒污泥内部分布较为均匀,虽然含量接近,但β-D-吡喃葡萄糖含量最多.本研究表明,在反应器中投加颗粒活性炭可以促进好氧颗粒污泥的形成.     

Treatment of Organic Compounds in Reclaimed Wastewater for Groundwater Recharge

To study water quality problems associated with groundwater recharge, a tertiary treatment process, consisting of coagulation, sand filtration, and granular activated carbon (GAC) adsorption, was used in combination with a simulated soil aquifer treatment. The process significantly improved secondary effluent quality. GAC adsorption reduced organic substances expressed by UV-254, dissolved organic carbon as well as partially adsorbable organic halogens. The results of the Ames test show that the secondary effluent contains a high concentration of mutagens. GAC filtration removed adsorbable organic bromine slightly whereas GAC adsorption removed mutagens effectively. The simulated soil aquifer treatment was able to further reduce UV-254, dissolved organic carbon, and adsorbable organic halogens through biodegradation. Adsorbable organic bromine levels were also reduced by the soil aquifer treatment process. The given reclamation technology used for groundwater recharge is of benefit to the removal of dissolved organic carbon, UV-254, adsorbable organic halogens, and rnutagenicity.