DHA高产菌Schizochytrium sp.FJU-512的分离及其18S rRNA基因序列比较分析

采用松花粉垂钓法分离到一株Docosahexaenoicacid(DHA)高产菌FJU 512.该菌株DHA含量高(占总脂肪酸的56. 24 % ),其它长链杂酸含量少(仅有docosapentaenoicacid, DPA),极具开发应用价值.高密度培养可获得33gL-1生物量.该菌株行二分裂生长,没有分生胞子.对其18SrRNA基因进行了克隆测序并登录GenBank(AY758384).依据18SrRNA基因建立的系统进化树表明:该菌与Schizochytriumlimacinum具有紧密的亲源关系. 图7表2参29     

生活垃圾堆肥工艺条件及其反应动力学研究

为了改善堆肥微环境 ,提高生活垃圾堆肥速率 ,研究堆肥工艺条件及其反应动力学是非常必要的。通过控制堆肥工艺条件 ,如初始温度、含水率、C/N比及堆料颗粒大小 ,研究生活垃圾堆肥过程中生物、化学及物理因素的变化。试验结果表明 ,生活垃圾堆肥反应符合一级反应动力学 ;合理控制堆肥初始反应条件 ,能明显提高堆肥效率。     

湖泊富营养化模型的研究进展

湖泊的富营养化是全球普遍关注的环境问题之一.湖泊的富营养化模型是防治、修复和治理湖泊富营养化的重要决策工具.按研究的侧重点不同,将湖泊富营养化模型分为简单回归模型、水质模型、生态模型和生态-水动力水质模型,并分别回顾了四类模型的研究进展.最后指出湖泊富营养化模型的发展趋势,强调不确定理论、3S技术、耦合模型是今后湖泊富营养化模型研究的重点,应在此基础上建立通用的模拟、预测、评价和优化模型,为湖泊富营养化管理提供科学依据.     

黑藻对铅离子的生物吸附

研究了黑藻对Pb^2＋的生物吸附作用,考察了溶液pH、Pb^2＋初始质量浓度、黑藻加入量和吸附时间对吸附效果的影响。实验结果表明,溶液pH在2．5～5．0时吸附效果最好,吸附20min基本达到平衡。在溶液pH为4．0、黑藻加入量为2g／L、吸附时间为60min、Pb^2＋初始质量浓度为100mg／L的条件下,黑藻对Pb^2＋的吸附量为47．5mg／g。通过元素分析和等温吸附模型对黑藻吸附Pb^2＋的机理进行了研究,发现黑藻吸附Pb“是阳离子交换过程,吸附符合Langmuir、Freundlich和D—R等温吸附模型。考察了Cd^2＋、Cu^2＋和Ni^2＋对黑藻吸附Pb^2＋的影响,结果表明,Cd^2＋、Cu^2＋和Ni^2＋的存在不干扰黑藻对Pb^2＋的吸附。     

二氧化氯的发生技术

本文对国内外ＣｌＯ２的发生技术进行了综合评述，详尽地介绍了作者自行研制的ＣｌＯ２发生技术和装置，认为我国推广应用ＣｌＯ２消毒处理饮用水的时机已经成熟。     

A/O-MBR中硝化活性污泥的富集及其对氧氟沙星的降解作用

采用A/O-MBR系统,逐步提高进水氨氮浓度富集了硝化活性污泥(NAS),在此基础上,考察了COD、烯丙基硫脲(ATU)、氨氮初始浓度及氨氧化速率对NAS降解氧氟沙星(OFL)的影响。结果表明:富集的NAS的氨氧化速率达到了20 mg/(g SS·h)以上,对OFL具有明显降解作用;ATU存在条件下,COD对OFL的去除作用没有影响;提高初始氨氮浓度和NAS氨氧化速率均可以提高OFL降解量;初始氨氮浓度由50 mg/提升至150 mg/L时,OFL降解量由67.26 μg/g提高到82.11 μg/g;氨氧化速率由小于2.5 mg/(g SS·h)提升至大于20 mg/(g SS·h)时,OFL降解量由30.71 μg/g提高到75.16 μg/g。     

Zinc tolerance and accumulation in Pteris vittata L. and its potential for phytoremediation of Zn- and As-contaminated soil

A field investigation and pot experiments were conducted to determine the potential of arsenic (As) hyperaccumulator, Pteris vittata L., to remediate sites co-contaminated with zinc (Zn) and As. We found that P. vittata L. had a very high tolerance to Zn and grew normally at sites with high Zn concentrations. In addition, P. vittata L. could effectively take up Zn into its fronds, with a maximum of 737 mg kg(-1) under field conditions. In pot experiments, the accumulated Zn concentration increased significantly as the Zn treatment was raised from 0 to 2000 mg kg(-1), with a maximum Zn accumulation of 0.22 mg pot(-1). Although the concentration of As in P. vittata L. was reduced by the addition of Zn, total frond accumulation of As was elevated when the Zn treatment was increased from 0 to 1000 mg kg(-1), with a maximum As accumulation of 8.3 mg pot(-1) in the presence of 1000 mg kg(-1) Zn. The high Zn tolerance, relatively high ability to accumulate Zn, and great capacity to accumulate As under conditions of suppression by high Zn suggest that P. vittata L. could be useful for the remediation of sites co-contaminated with Zn and As.     

Toxicity of copper on rice growth and accumulation of copper in rice grain in copper contaminated soil

Pot soil experiments showed that copper (Cu) is highly toxic to rice. Rice grain yields decreased exponentially and significantly with the increase of soil Cu levels. Rice grain yield was reduced about 10% by soil Cu level of 100 mg kg(-1), about 50% by soil Cu level of 300-500 mg kg(-1) and about 90% by soil Cu concentration of 1,000 mg kg(-1). Root was more sensitive to soil Cu toxicity than other parts of rice plant at relatively lower soil Cu levels (less than 300-500 mg kg(-1)), but the growth of whole rice plant was severely inhibited at high soil Cu levels (300-500 mg kg(-1) or above). Cu concentrations in rice grain increased with soil Cu levels below 150-200 mg kg(-1), but decreased with soil Cu levels above 150-200 mg kg(-1), with peak Cu concentration at soil Cu level of 150-20 mg kg(-1). Cu was not distributed evenly in different parts of rice grain. Cu concentration in cortex (embryo) was more than 2-fold that in chaff and polished rice. More than 60% of the Cu in grain was accumulated in polished rice, about 24% in cortex (embryo), and about 12% in chaff. So, about 1/3 of the Cu in rice grain was eliminated after grain processing (chaff, cortex and embryo was removed).     

Kinetics of heat-assisted persulfate oxidation of methyl tert-butyl ether (MTBE)

The kinetics of heat-assisted persulfate oxidation of methyl tert-butyl ether (MTBE) in aqueous solutions at various pH, temperature, oxidant concentration and ionic strength levels was studied. The MTBE degradation was found to follow a pseudo-first-order decay model. The pseudo-first-order rate constants of MTBE degradation by persulfate (31.5 mM) at pH 7.0 and ionic strength 0.11 M are approximately 0.13 x 10(-4), 0.48 x 10(-4), 2.4 x 10(-4) and 5.8 x 10(-4) S(-1) at 20, 30, 40 and 50 degrees C, respectively. Under the above reaction conditions, the reaction has an activation energy of 24.5 +/- 1.6 kcal/ mol and is influenced by temperature, oxidant concentration, pH and ionic strength. Raising the reaction temperature and persulfate concentration may significantly accelerate the MTBE degradation. However, increasing both pH (over the range of 2.5-11) and ionic strength (over the range of 0.11-0.53 M) will decrease the reaction rate. Reaction intermediates including tert-butyl formate, tert-butyl alcohol, acetone and methyl acetate were observed. These intermediate compounds were also degraded by persulfate under the experimental conditions. Additionally, MTBE degradation by persulfate in a groundwater was much slower than in phosphate-buffer solutions, most likely due to the presence of bicarbonate ions (radical scavengers) in the groundwater.     

溶胶-凝胶法制备磁载光催化剂

悬浮态的光催化反应器相比固载的光催化反应器有更高的光催化效率。但是如何在光催化反应完成后使催化剂与水溶液的分离 ,成为了一个关键的问题。本研究采用溶胶 凝胶法将二氧化钛直接沉积在磁性颗粒的表面 ,制备出了磁载的光催化剂。这种催化剂在保留了磁性能具有可磁分离的基础上又具有很好的光催化降解效果。