洁净环境样本低浓度微生物高效富集检测及应用

为了研究对洁净环境样本的低浓度微生物监测方法,制备了低浓度的革兰氏阳性菌和阴性菌各3种,使用修饰后的新型磁珠对模拟样本中的微生物进行富集评价实验.革兰氏染色和菌落计数结果表明,磁珠对3种革兰氏阳性菌和3种阴性菌均具有显著富集浓缩作用,与大肠杆菌相比,磁珠对金黄色葡萄菌的富集浓缩比更高.使用磁珠富集液对自来水、桶装水和瓶装矿泉水中的微生物进行非特异性吸附后,比较上清和磁珠-微生物复合物的细菌16S rDNA基因拷贝数和菌落总数指标,结果表明磁珠对自来水和桶装水中的微生物均具有显著的吸附效果（P<0.01,P<0.001）.通过比较,抽滤法和磁珠法对自来水中的微生物富集效果有差异（P=0.002）,2种方法对桶装水和矿泉水的富集效果无显著差异（P=0.362）.采集实际空气样本进行磁珠富集微生物的菌落计数及细菌16S rDNA基因拷贝数进行分析,磁珠-微生物复合物中的绝对基因拷贝数和菌落总数均显著高于磁分离后上清液中基因拷贝数和菌落计数（P=0.0001）.此方法对微生物具有一定的高效富集作用.     

固定化条件对苯系物细胞传感器检测效果的影响

利用海藻酸钠作为包埋剂对苯系物细胞传感器Pseudomonas fluorescens A506(pTS)进行固定化处理,并对细胞浓度、固定化时间、投加量等检测因素进行了优化.固定化后的细胞与游离细胞对苯系污染物的检测效果进行对比.经过2 h固定化处理的细胞传感器,在检测时间1.5～6.0 h内,信号上升速度为游离细胞的2.26倍,信号最大值为游离细胞的2.23倍.固定化处理后的细胞生长缓慢,且浓度远低于游离细胞,说明了固定化处理后的单位细胞信号强度增加.同时,细胞浓度随着固定化时间的延长而降低.在影响因素方面,细胞浓度和固定化时间对于检测信号的影响较大.固定化后,对高浓度的苯系污染物有着更快的信号响应.     

Combined effects of adsorption and photocatalysis by hybrid TiO2/ZnO-calcium alginate beads for the removal of copper

The use of nanosized titanium dioxide(TiO_2) and zinc oxide(ZnO) in the suspension form during treatment makes the recovering and recycling of photocatalysts difficult.Hence,supported photocatalysts are preferred for practical water treatment applications.This study was conducted to investigate the efficiency of calcium alginate(CaAlg) beads that were immobilized with hybrid photocatalysts,TiO_2/ZnO to form TiO_2/ZnO-CaAlg.These immobilized beads,with three different mass ratios of TiO_2:ZnO(1:1,1:2,and 2:1) were used to remove Cu(Ⅱ) in aqueous solutions in the presence of ultraviolet light.These beads were subjected to three cycles of photocatalytic treatment with different initial Cu(Ⅱ) concentrations(10-80 ppm).EDX spectra have confirmed the inclusion of Ti and Zn on the surface of the CaAlg beads.Meanwhile,the surface morphology of the beads as determined using SEM,has indicated differences of before and after the photocatalytic treatment of Cu(Ⅱ).Among all three,the equivalent mass ratio TiO_2/ZnO-CaAlg beads have shown the best performance in removing Cu(Ⅱ) during all three recycling experiments.Those TiO_2/ZnO-CaAlg beads have also shown consistent removal of Cu,ranging from 7.14-52.0 ppm(first cycle) for initial concentrations of10-80 ppm.In comparison,bare CaAlg was only able to remove 6.9-48 ppm of similar initial Cu concentrations.Thus,the potential use of TiO_2/ZnO-CaAlg beads as environmentally friendly composite material can be further extended for heavy metal removal from contaminated water.     

基于高通量测序的流化床生物滤器细菌群落结构分析

为了解流化床生物滤器内部细菌群落组成及其净水机制,通过高通量测序方法,研究了不同时期滤器中表层和底层滤料的细菌群落结构,分析了滤器不同床层的营养盐变化情况及水处理性能.结果表明,滤器的硝化作用主要发生于床层下部,表层对其的贡献率不显著.稳定工况下,流化床生物滤器对NH_4~+-N、TN、BOD_5和SS的去除率达到(68.3±2.24)%、(49.54±3.56)%、(60.35±4.98)%和(45.21±2.11)%,对氨氮的去除负荷达到(343.28±75.5)g·(m~3·d)~(-1),其硝化性能优于常规生物滤器.试验共筛选31个门,490个细菌属,其生物多样性显著高于常规生物滤器.自清洗装置的启停对滤器中不同区域载体表面细菌的多样性没有影响,对各样品的优势菌群略有影响.在滤器稳定运行时,表层区域的优势细菌基本维持不变,主要包括厌氧绳菌科、黄杆菌科、红杆菌科、硝化螺菌属、暖绳菌科.而底层区域的优势细菌随着时间的推移有所变化,主要包括硝化螺菌属、微丝菌属、Muricauda、Defluviimonas、红杆菌科.     

Dye removal by eco-friendly physically cross-linked double network polymer hydrogel beads and their functionalized composites

Hydrogels have attracted large attention in wastewater treatment fields due to their low-cost and good interaction with pollutants, among which novel double network hydrogel is an outstanding class. To expand the application of double network hydrogel in water treatment, in this study, eco-friendly physically cross-linked double network polymer hydrogel beads (DAP) are prepared and studied in depth on the mechanism of Methylene Blue (MB) adsorption; and then the polymer hydrogels are further functionalized by inorganic materials. MB adsorption on DAP favors alkaline condition which is due to the increase of electrostatic attraction and adsorption site, and it reaches equilibrium within 10?hr, which is faster than that of the single network hydrogel beads (SAP). Through thermodynamics study, the process shows to be an exothermic and spontaneous process. The adsorption isotherms are well fitted by Langmuir model, with a maximum monolayer adsorption capacity of 1437.48?mg/g, which is larger than SAP (1255.75?mg/g). After being functionalized with common inorganic materials including activated carbon, Fe₃O₄ and graphene oxide (GO), the composites show to have larger pore sizes and have obvious increases in adsorption capacity especially the one contains GO. Then the composites contains Fe₃O₄ are used as heterogeneous Fenton catalyst which shows to have excellent performance in MB degradation. The results indicate the potential of polymer double network to be functionalized in environmental areas.     

硫酸盐还原菌(SRB)污泥固定化小球还原硫酸盐的动力学研究

通过研究硫酸盐还原菌(SRB)污泥固定化小球还原硫酸盐过程硫酸盐浓度的变化规律,建立了反应动力学方程,确定了pH值和球液配比量对反应速率常数的影响,计算了相应的反应表观活化能.结果表明: SRB还原硫酸盐的反应为一级反应,反应动力学方程为:V=-dC/dt=0.080 56C.pH值为6-7时,SRB还原硫酸盐的反应速率常数相差不大,pH＜4和pH＞10时,反应速率常数逐渐减小.球液配比量减少,反应速率常数也随之减小,反应表观活化能增大.在实验条件下,SRB还原硫酸盐属化学控制.并由此确定了SRB污泥固定化小球还原硫酸盐的最佳工艺条件为温度35 ℃、pH值6-7、球液配比量1∶10(g/mL).     

高分子凝胶球去除废水中重金属离子的研究

用海藻酸钠（SA）、海藻酸钠-聚乙烯醇（SA—PVA）、海藻酸钠-聚氧化乙烯（SA—PEO）凝胶球作为吸附剂吸附溶液中的Pb^2＋。探讨了凝胶球固定化时间、吸附时间、溶液pH值、溶液初始浓度对Pb^2＋去除率的影响,并对吸附动力学方程进行了分析。结果表明：固定化时间对去除率的影响较小;反应速率较快,吸附时间在10min时,三种凝胶球对Pb^2＋的去除率就分剐达到了80％、82％和88％,吸附时间在2h后基本达到吸附平衡,三种凝胶球对Pb^2＋的吸附能力为：SA—PGE〉SA—PVA〉SA;三种凝胶球吸附铅离子的行为均符合一级反应动力学方程;溶液的pH在4～6时有较高的去除率;三种凝胶球对不同金属的吸附能力为Pb^2＋〉Cu^2＋〉Cd^2＋;饱和吸附后的三种凝胶球均可以再生利用。     

空心微珠的开发及应用研究进展

为促进资源利用和环境改善,拓展空心微珠的开发空间,文章概述了其种类、组成和理化性能.空心微珠的生产工艺主要有干选和湿选两大类.粉煤灰空心微珠在建筑材料、化学工业、温控材料、功能材料等方面有较多的开发应用.空心微珠经化学镀、化学气相沉积等手段进行表面改性后,性能更加优越,可用于环境保护、制药行业,还可用作发泡材料、示踪粒子等特殊功能乃至航空、航天等高科技领域.空心微珠质轻、稳定、耐磨、耐热、强度高、耐腐蚀,用途广泛、前景广阔.建议加大政策支持和研究投入;开发新材料,增大附加值;探讨治理水体污染的可能性.     

高分子凝胶球用于城市污水深度处理的研究

制备海藻酸钠-钙(SA-Ca)、海藻酸钠-铁(SA-Fe)、包埋活性炭海藻酸钠-铁(SA-Fe-AC)凝胶球,对城市污水处理厂二级出水的COD和无机磷进行深度处理。结果表明:SA-Ca凝胶球对COD的去除率为10%,SA-Fe凝胶球对COD及无机磷的去除率分别为42%和93%。SA-Fe-AC凝胶球对COD及无机磷的去除率分别为75%和87%。SA-Fe及SA-Fe-AC对COD的吸附符合Langmuir型,均属于单分子层吸附,其饱和吸附量分别为416.7mg/g、909mg/g。     

聚乙烯醇-海藻酸钠凝胶球去除废水中无机磷的研究

研究了聚乙烯醇-海藻酸钠(PVA-SA)凝胶球对废水中无机磷的去除效率及吸附特性。研究结果表明:交联剂质量分数0.5%、pH=2为最佳实验条件;PVA-SA-Fe凝胶球和PVA-SA-Ca凝胶球吸附无机磷的吸附平衡时间为120min;PVA-SA-Ca-Fe凝胶球吸附平衡时间为240min,去除率高,超过90%;模拟污水pH值为9时,PVA-SA-Ca-Fe凝胶球的去除效果最好,可达到97.5%;PVA-SA-Ca-Fe凝胶球可以很好的再生利用,主要影响因素是盐酸和Fe3+。准二级动力学方程可以很好的描述PVA-SA-Ca-Fe凝胶球的吸附过程,主要受颗粒内扩散控制;Langmuir型吸附等温线可以较好的描述PVA-SA-Ca-Fe凝胶球对无机磷的吸附行为。