城市生活污水中志贺氏菌ipaH毒力基因的定量PCR检测

基于ipaH毒力基因的实时荧光定量PCR检测,建立适合城市污水中志贺氏菌的定量检测方法。使用从临床分离出的志贺氏菌构建重组质粒作为实时荧光定量PCR的标准品。在ipaH基因模板量2.58×100～2.58×106copy范围内具有良好的线性关系,每100 mL水样中含有2.58×101copy以上的ipaH基因即可被检出。从西安市生活污水分离得到2株野生型志贺氏菌,分析ipaH基因数量和菌体数量的关系,从而确定ipaH基因定量检测志贺氏菌的可行性。该方法灵敏、快速、特异性好,适用于城市生活污水中志贺氏菌的检测。     

水泥、粉煤灰及DTCR固化/稳定化重金属污染底泥

采用水泥、粉煤灰及有机硫稳定剂DTCR固化/稳定化处理重金属污染的底泥,考察固化体的抗压强度及重金属浸出毒性,确定了底泥固化/稳定化的最佳工艺条件。结果表明:仅用水泥固化/稳定化重金属污染底泥,固化体抗压强度随水泥用量的增加而上升,重金属浸出浓度则下降,当水泥∶干底泥质量比为0.6∶1.0时,固化体7 d抗压强度能达到0.99 MPa的标准值;进一步研究发现,水泥∶粉煤灰∶干底泥质量比为0.54∶0.06∶1.0时,重金属浸出浓度有所上升,但7 d及28 d抗压强度仍能分别达到1.2 MPa和2.8 MPa;加入DTCR后,当水泥∶粉煤灰∶DTCR∶干底泥质量比为0.54∶0.06∶0.012∶1.0时,固化体7 d及28 d抗压强度分别为1.1 MPa和2.1 MPa,醋酸缓冲溶液法浸出的Cd、Pb、Zn和Cu浓度分别为0.102、0.189、0.180和0.032 mg/L。     

The short-term effect of cadmium on low molecular weight organic acid and amino acid exudation from mangrove (Kandelia obovata (S., L.) Yong) roots

The aim of this study was to evaluate short-term concentration and time effects of cadmium on Kandelia obovata (S., L.) Yong root exudation, thereby evaluating and predicting the ecophysiological effects of mangrove to heavy metals at the root level. Mature K. obovata propagules were cultivated in a sandy medium for 3 months, and then six concentrations of Cd (0, 2.5, 5, 10, 20, and 40 mg L^?1) were applied. After exposure time of 24 h and 7 days, respectively, the root exudates of K. obovata were collected and low molecular weight organic acids (LMWOAs) and amino acids of which were analyzed. In addition, we measured glutathione, soluble protein content, and Cd concentration in the plant. We found 10 and 15 types of LMWOAs and amino acids in root exudates of K. obovata with total concentrations ranging from 29.54 to 43.08 mg g^?1 dry weight (DW) roots and from 737.35 to 1,452.46 ng g^?1 DW roots, respectively. Both of them varied in quality and quantity under different Cd treatment strengths and exposure times. Oxalic, acetic, l-malic, tartaric acid, tyrosine, methionine, cysteine, isoleucine, and arginine were dominant. Both LMWOAs and amino acids excreted from K. obovata roots play a key role in Cd toxicity resistance. The responsiveness of amino acids was less than that of LMWOAs. We suggest that the ecological effect of root-excreted free amino acids in the rhizosphere is mainly based on the role of nutrients, supplemented with detoxification to heavy metals.     

紫外光促进盐酸聚苯胺催化H_2O_2氧化处理罗丹明B废水

以苯胺和过硫酸铵为主要原料合成了盐酸聚苯胺（HClPANI）催化剂,并通过FTIR、XRD、SEM和EDS对催化剂进行了表征。研究了在紫外光照下、HClPANI催化H2O2氧化处理罗丹明B染料废水工艺参数,探讨了各种因素对废水脱色效果的影响,并对催化氧化机理进行了初步探讨。结果表明,催化剂HClPANI对催化H2O2氧化处理罗丹明B具有较好的催化活性、稳定性和重复使用性能。UV-H2O2-HClPANI体系产生了明显的协同效应,在pH=3、200 mg/L的罗丹明B废水中,30%H2O2用量为1.2 mL/L、HClPANI用量1 g/L、反应温度25℃、紫外灯功率500 W、光照70 min,罗丹明B脱色率达到了98.2%。     

Influence of tetracycline exposure on the growth of wheat seedlings and the rhizosphere microbial community structure in hydroponic culture

In this study, the effects of tetracycline exposure on wheat growth and the microbial community structure in the rhizosphere were investigated under hydroponic culture conditions. Exposure to various concentrations of tetracycline resulted in significant suppression of the growth of wheat roots and shoots, with minimum doses of 0.8 mg L^?1 and 4 mg L^?1 resulting in inhibition rates of 32% and 15.4%, respectively. Complete inhibition of the growth of these two parts of wheat plants was observed in response to treatment with tetracycline at 20 mg L^?1 and 100 mg L^?1, respectively. However, the germination of wheat seeds was not sensitive to exposure to tetracycline. The effects of tetracycline exposure on the microbial community in the wheat rhizosphere were evaluated through traditional cultivation and molecular biological analyses. The cultivation results indicated that bacteria were the dominant population, being present in concentrations of 1× 10⁸–2.45× 10⁹CFUs mL^?1, although 39% to 87% inhibition occurred in response to tetracycline. The concentration of fungi increased in all tetracycline treated samples to 2.5 to 15.8 times that of the control. The highest concentration of fungi (4.27× 10⁸ CFU mL^?1) was observed in response to 60 mg L^?1 tetracycline after 15 days of cultivation. In this stage, a large amount of fungal colonies was observed on the surface of the culture solution, the wheat roots became rotted and the plants became atrophic or even died. Molecular biological analysis indicated that the bacterial community structure was significantly different in samples that were exposed to high levels of tetracycline (over 20 mg L^?1) than in samples that were exposed to lower concentrations. As the concentration of tetracycline increased, the diversity of the bacteria decreased. Additionally, several dominant sensitive species such as Sphingobacterium multivorum were suppressed by tetracycline, while some resistant species such as Acinetobacter sp. appeared or were conserved. The bacteria population tended to stabilize when the drug concentration exceeded 40 mg L^?1.     

不同热处理温度对污泥厌氧发酵产氢的影响

污水处理厂污泥产生量日益增加,对环境的影响倍受关注。污泥除了含有大量的葡萄糖、蛋白质等有机物外,还包括大量的微生物,具有厌氧发酵产氢的潜能。通过批式实验系统研究了热处理污泥厌氧发酵产氢情况。研究结果表明,经过适当热处理,可以抑制耗氢菌,同时能保持产氢菌的活性,另外,对污泥还有一定的融胞作用,使污泥中溶解性的糖和蛋白质的含量增加,提高预处理污泥的产氢效率;最佳的热处理温度为75℃,处理后污泥进行厌氧发酵产氢的最大累积产氢量为18.32 mL,比产氢率3.49 mL/g VS。     

硅藻土强化混凝处理线路板含络合铜废水

采用硅藻土对聚合硫酸铁（PFS）、聚合氯化铝（PAC）的混凝能力进行强化,并用于线路板含络合铜废水中铜的去除。考察了硅藻土加入量、混凝剂加入量、pH、快速搅拌速率和沉淀时间等因素对除铜效果的影响,并与目前常用的硫化钠破络方法进行了对比。实验结果表明：硅藻土强化混凝的除铜效果明显好于单独投加PAC或PFS;PFS-硅藻土除铜效果好于PAC-硅藻土;在pH为8.0~9.0、硅藻土加入量为120 mg/L、PFS加入量为60 mg/L、快速搅拌速率为250 r/min的条件下,沉淀40 min后可使出水铜质量浓度低于0.30 mg/L,比传统破络工艺出水水质更稳定,成本更低。     

粉煤灰两步水热法制备人工沸石

以粉煤灰为原料,采用两步水热法制备人工沸石。SEM、XRD、X射线荧光光谱分析结果表明:制得的人工沸石纯度较高,主要为Na-A型沸石和少量13X型沸石,主要化学成分为SiO2和Al2O3。说明采用两步法制备人工沸石克服了传统水热法杂质含量高的缺陷。采用人工沸石处理初始Mn2+质量浓度为50.00mg/L的模拟含锰废水,吸附125min后,Mn2+去除率达98.19%,模拟废水中剩余Mn2+质量浓度为0.90mg/L。     

数学规划在水网络优化设计中的应用进展

综述了数学规划在连续过程水网络优化设计中的应用进展。分析了树搜索、线性规划、非线性规划、混合整数非线性规划、基于数学规划的复合方法等方法设计水网络的特点、求解策略及应用情况,探讨了模型求解的优化算法。     

电动力学作用下多溴联苯醚在土壤中的迁移特性

以4,4′-二溴联苯醚(BDE-15)为研究对象,探讨了电极电压、初始土壤pH、β-环糊精加入量、NaCl加入量等工艺条件对多溴联苯醚在土壤中迁移效果的影响。实验结果表明:在电极电压为5~15V范围内,随着电极电压的升高,土壤中BDE-15的迁移效果增强;初始土壤为酸性时、加入β-环糊精或NaCl后,土壤中BDE-15的迁移效果均增强。本实验选择的最佳工作条件为:电极电压15V,初始土壤pH3,β-环糊精的加入量3g,NaCl加入量5g。