重金属对藻类的毒性作用研究进展

从四方面分析了藻类与重金属的相互作用,提示重金属污染对水体危害十分严重,而利用藻类净化重金属废水具有重要的意义。     

不同温度下滇池蓝藻沼气发酵的实验研究

以滇池蓝藻为发酵原料,改变发酵温度,采用批量式发酵工艺进行沼气发酵实验。实验结果表明:在常温、20℃、25℃、30℃和35℃下,滇池蓝藻的发酵时间、产气量及产气潜力有明显的差异性。随发酵温度的升高,实验启动越快、发酵时间越短、产气量越高、产气潜力越高。35℃下,产气效果最好,发酵时间29d,产气潜力为255mL/g.TS、285mL/g.VS.     

水中藻毒素降解的影响因素及其净水工艺控制

藻毒素污染已成为普遍关注的水质问题，在水环境中，藻毒素的迁移转化受光照、温度、有机物、溶解氧、水生生物等因素的共同影响。单元净水工艺（混凝、沉淀、砂滤、氯化等）和常规组合工艺对藻毒素的去除率较低，常规工艺＋活性炭过滤、臭氧＋常规工艺的去除率可达100％，不破坏藻细胞而能够大量降低其数量的预处理＋臭氧＋常规工艺＋ 性炭工艺应能够取得最佳的解毒效果。     

基于模糊最近邻聚类学习算法的海水藻类繁殖状态预测

为了预报海洋赤潮等灾害的发生,需要监测海水中藻类的繁殖状况.通过建立针对海水中叶绿素a浓度状态的预测模型间接预测海水中藻类的繁殖生长状况.运用基于数据的模糊最近邻聚类学习算法对采样数据进行聚类处理,基于最优模糊逻辑系统建立了针对海水叶绿素a浓度状态的预测模型.根据采样数据的特点和降低模型阶次的实际需求,设计了改进的模糊...     

藻类强化光降解去除水中双酚A的动力学研究

为提高污染水体中双酚A光降解效率,采用铜绿微囊藻进行强化,研究该藻强化光降解去除水中双酚A的效能和动力学规律,并讨论了藻质量浓度、pH值及光源等因素对降解速率的影响.研究表明,藻类质量浓度相对较大时,光降解反应符合假一级反应动力学规律,提高反应液中藻类质量浓度可提高双酚A的降解率;pH值对光降解速率有显著影响,当pH值为5时,反应速率达到最大值;光源对反应速率也存在影响,光源采用紫外灯时,光降解反应速率是同条件下高压汞灯作为光源时的9倍,其原因是后者不能使反应液中产生大量的羟基自由基.     

应用浮游藻类评价桂湖水质的研究

于2004年应用浮游藻类对桂林旅游景点——桂湖水质进行监测评价，初步探讨了桂湖浮游藻类与水质的相互关系．研究内容：浮游藻类的组成、生物种类、生物数量、指示生物、均匀度指数、多样性指数及理化对照监测等．结果表明：桂湖含有浮游藻类7门69属138种，主要种类为硅藻和绿藻；水质评价指数大多数样点达到清洁水质标准，少数有轻度污染，桂湖水质整体为清洁。     

河北秦皇岛仙菜科Ceramiaceae红藻的分类研究

仙菜科Ceramiaceae是重要的海洋大型红藻类群,具有重要的研究价值和经济价值,但因其个体微小脆弱、形态多变等,分类上还存在许多不足。本研究利用生物冷冻切片及显微拍照等技术,通过形态解剖方法,对2019-2021年采自我国秦皇岛沿岸海域的仙菜科红藻进行分类学研究。经鉴定,样品中包括仙菜属Ceramium 3种,即波登仙菜Ceramium boydenii Gepp、三叉仙菜C.kondoi Yendo和孙氏仙菜(新拟名)C.sungminbooi J.R.Hughey et G.H.Boo,其中孙氏仙菜为我国新纪录种;对丝藻属Antithamnion 1种,即多姿对丝藻Antithamnion defectum Kylin;绢丝藻属Callithamnion 1种,即绢丝藻Callithamnion corymbosum(Smith)Lyngbye。本文对新纪录种及其他物种进行详细的形态特征描述,提供了解剖学特征图片及生物地理分布信息等内容。研究结果丰富了中国仙菜科的物种多样性。     

Growth ofNostoc muscorum mutants in the presence of diuron (DCMU) and L-methionine-DL-sulfoximine

Summary Diuron (DCMU) is inhibitory to the photoautotrophic and photoheterotrophic growth of the N₂-fixing blue-green algaNostoc muscorum at concentrations of 1.0×10^–5 M and 2.0×10^–5 M, respectively. A mutant of this organism resistant to 5.0×10^–5 M DCMU under its photoheterotrophic growth conditions, with the ability to utilize DCMU as a carbon and nitrogen source for growth, and complete inability to grow photoautotrophically has been isolated. With the apparent defect in its photosynthetic ability, it is suggested that theDCMU ^r mutant lacks the step inhibited by 1.0×10^–5 M DCMU, and metabolizes DCMU by an existing enzyme system in the absence of such inhibition. That this enzyme may be glutamine synthetase (GS) is explained with the help of a L-methionine-DL-sulfoximine (MSO)-resistant mutant ofN. muscorum which is able to grow faster with 2.0×10^–5 DCMU and is known to contain an altered GS.Thanks are due to the Council of Scientific and Industrial Research, CSIR Complex, Govt. of India, New Delhi-110012, for appointing the author to the Scientists' Pool for undertaking researches on the physiological and genetic controls of nitrogen metabolism in blue-green algae, a part of which is presented in this literature.     

Experimental study of gold distribution in the algae-organic matter-fluid system

Conclusion Gold distribution and transformation in algae-organic matter-fluid system is very complicated. Gold is first concentrated in kerogen after algae died. With the increase of dissolved organic matter owing to the increase of temperature and pressure, part of gold simultaneously emigrates from kerogen to DOM. When DOM forms organic fluid and emigrates from the strata, gold is simultaneously carried away by organic fluid in acidic condition, but by water in alkali condition. When the auriferous fluid flows through carbonaceous strata, gold in fluid is unloaded by kerogen. Gold migration in the system, accompanied by the evolution of algae-organic matter-fluid, provides the basic information of biometallogenetic evolution of gold.