固定化小球藻对海水养殖废水氮磷的处理

本研究利用海藻酸钠（SA）作为载体、以氯化钙（CaCl₂）为交联剂,探究小球藻最佳固定化条件及其对海水养殖废水氨氮和磷酸盐的处理效果.通过对比不同浓度SA和CaCl₂对小球藻生长的影响及不同固定化条件的藻球对氨氮、磷酸盐处理效果,确定最佳固定化条件为2.0% SA和2.0% CaCl₂.对比固定化藻球和悬浮小球藻对模拟海水养殖废水氨氮、磷酸盐去除效果,结果表明固定化藻球比悬浮藻液对氮、磷处理效果更好.其中低接种率（1：10）固定化藻球的最大氨氮、磷酸盐去除率分别为63.26%和62.76%.固定化小球藻浓度越高,其净化能力越强,高接种率（1：1）固定化藻球的最大氨氮、磷酸盐去除率分别是85.16%和75.94%.连续流运行下固定化藻球对海水养殖废水氨氮、磷酸盐的平均去除率分别为84.49%和72.17%.小球藻固定化态保留并延长了悬浮态生长活性,提高了对海水养殖废水脱氮除磷效果.     

菌藻复合体系氮代谢性能及菌群特征

为了城市尾水深度脱氮,控制地表水体富营养化,利用分子生物学等方法,分别对脱氮复合菌群和藻菌共生系统的氮代谢性能进行研究.结果表明,氮代谢复合菌群具有较高氨化和反硝化性能.JZ组对城市尾水中氨氮的去除效果最好,降解率高达95%以上,在实验室模拟污水中JZ组系统总氮去除效果优于J组.高通量测序显示,J组主要优势菌群及占比分别为：厚壁菌门44.53%,变形菌门43.41%,放线菌门5.37%,类杆菌门3.04%,绿弯菌门1.35%;JZ组丰度主要优势菌群和占比分别为：蓝藻门33.89%,绿弯菌门25.34%,变形菌门19.38%,厚壁菌门10.02%,酸杆菌门4.20%;各优势物种在J组和JZ组比例不同,厚壁菌门分别为82%和18%,变形菌门为69%和31%,蓝藻门为1%和99%,绿弯菌门为5.1%和95%,放线菌门分别为73%和27%.表明JZ组在城市尾水中去除氨氮效果较好,J组氮代谢菌群随着微球藻加入和生长,JZ组氮代谢菌群构成随之发生变化,以适应优势藻类形成的环境,与微球藻构成新的菌藻氮代谢体系.研究结果为藻菌共代谢体系应用提供了理论和数据基础.     

外源稀土La在沉积物中的形态及其生物可利用性

将沉积物中的外源稀土La分为可溶解态、酸可提取态、有机质及硫化物结合态,研究了小球藻(Chlorella Vulgaris Beijerinck)对这三种形态La的生物可利用性.研究结果表明:这三种形态的La在沉积物中的含量与其在藻中的含量有很好的相关关系.其中可溶解态La的生物可利用性最大,这说明,沉积物中La的释放对其生物可利用性至关重要.     

Changes in the Biochemical Composition of Tetraselmis Suecia and Isochrysis Galbana During Growth and Decay

The variations of the biochemical composition of Tetraselmis suecica and Isochrysis galbana during growth and decay were determined. the content of chlorophyll a (Chl-a) of the cultures, as expected, slowly degraded into phaeopigments during decay, confirming that chlorophyll measurements do not always provide an accurate estimate of phytoplanktonic biomass and, consequently, may fail if used to measure the food availability of particulate matter for consumers. Measurements of total amounts of proteins, carbohydrates and lipids, related to the nutritional value of particles in terms of caloric content, are shown to provide information on the readily available food for consumers, particularly during the blooms. the protein/carbohydrate, C/N and POC/Chl-a ratios were used to evaluate the differences between these two species during the growth and the decomposition processes. A comparison between experimental and field conditions was undertaken to implement our understanding of the growth and degradation processes of particulate organic matter of phytoplanktonic origin in the sea and its role on natural systems, during and after phytoplankton blooms.     

Ecotoxic Effect of Photocatalytic Active Nanoparticles (TiO2) on Algae and Daphnids (8 pp)

Background, Aim and Scope Due to their large potential for manifold applications, the use of nanoparticles is of increasing importance. As large amounts of nanoparticles may reach the environment voluntarily or by accident, attention should be paid on the potential impacts on the environment. First studies on potential environmental effects of photocatalytic TiO2 nanoparticles have been performed on the basis of widely accepted, standardized test systems which originally had been developed for the characterization of chemicals. The methods were adapted to the special requirements of testing photocatalytic nanoparticles. Materials and Methods: Suspensions of two different nanoparticles were illuminated to induce their photocatalytic activity. For testing, the growth inhibition test with the green alga Desmodesmus subspicatus and the immobilization test with the daphnid Daphnia magna were selected and performed following the relevant guidelines (algae: ISO 8692, OECD 201, DIN 38412-33; daphnids: ISO 6341, OECD 202, DIN 38412-30). The guidelines were adapted to meet the special requirements for testing photocatalytic nanoparticles. Results: The results indicate that it is principally possible to determine the ecotoxicity of nanoparticles. It was shown that nanoparticles may have ecotoxicological effects which depend on the nature of the particles. Both products tested differ in their toxicity. Product 1 shows a clear concentration-effect curve in the test with algae (EC50: 44 mg/L). It could be proven that the observed toxicity was not caused by accompanying contaminants, since the toxic effect was comparable for the cleaned and the commercially available product. For product 2, no toxic effects were determined (maximum concentration: 50 mg/L). In the tests with daphnids, toxicity was observed for both products, although the concentration effect-curves were less pronounced. The two products differed in their toxicity; moreover, there was a difference in the toxicity of illuminated and non-illuminated products. Discussion: Both products differ in size and crystalline form, so that these parameters are assumed to contribute to the different toxicities. The concentration-effect curves for daphnids, which are less-pronounced than the curves obtained for algae, may be due to the different test organisms and/or the differing test designs. The increased toxicity of pre-illuminated particles in the tests with daphnids demonstrates that the photocatalytic activity of nanoparticles lasts for a period of time. Conclusions: The following conclusions can be drawn from the test results: (I) It is principally possible to determine the ecotoxicity of (photocatalytic) nanoparticles. Therefore, they can be assessed using methods comparable to the procedures applied for assessing soluble chemicals. - (II) Nanoparticles may exert ecotoxicological effects, which depend on the specific nanoparticle. - (III) Comparable to traditional chemicals, the ecotoxicity depends on the test organisms and their physiology. - (IV) The photocatalytic activity of nanoparticles lasts for a relevant period of time. Therefore, pre-illumination may be sufficient to detect a photocatalytic activity even by using test organisms which are not suitable for application in the pre-illumination-phase. Recommendations and Perspectives: First results are presented which indicate that the topic 'ecotoxicity and environmental effects of nanoparticles' should not be neglected. In testing photocatalytic nanoparticles, there are still many topics that need clarification or improvement, such as the cause for an observed toxicity, the improvement of the test design, the elaboration of a test battery and an assessment strategy. On the basis of optimized test systems, it will be possible to test nanoparticles systematically. If a potential risk by specific photocatalytic particles is known, a risk-benefit analysis can be performed and, if required, risk reducing measures can be taken.     

滇池水体除藻材料的除藻作用试验研究

利用昆明地区的粘土矿制作新型轻质除藻材料,试验研究该材料对滇池湖水中藻类的除藻及净化作用.实验室小试(20 L)结果表明,该除藻材料放入滇池水样实验70 d后,水质明显好转,藻类去除率可达95.8%,CODMn、TN及TP的去除率分别为34.4%、81.5%、28.2%.在滇池湖边300 m2水面围栏扩大试验结果显示,除藻材料放入试验区水体10 d后,水体中藻类含量明显减少,水体透光率从55%增加到80%,水质状况也有很大改善.研究结果表明,该材料具有良好的湖泊水体除藻及净化作用,有必要对其开展进一步的深入研究.     

藻类对壬基酚微生物降解的影响

壬基酚(NP)为在水环境中广泛存在的一种典型环境内分泌干扰物质。为了探讨NP在自然水体中的归趋,研究了水体中藻类对微生物降解NP的影响。结果表明,本研究筛选的耗氧混合菌可以有效降解NP,在暗环境下半衰期为1.16d,光照不利于NP的微生物降解,半衰期增加到5.19d;藻类和藻胞外分泌物可以提高光照条件下NP的微生物降解,这是藻类和菌加和作用的结果;而破碎的藻对降解作用改善不大。藻类和微生物相互作用对于有机污染物降解的影响还鲜见报道,本研究为全面理解NP在水环境中的归驱提供了重要的数据。     

藻类与有机污染物间的相互作用研究

本文就若干有机污染物对藻类的毒性效应及藻类对这些污染物的富集降解作用进行了系列研究。结果表明，不同污染物对藻类的毒性有很大差别，其中三有机锡的毒性最大。此外，不同藻类对毒物具有不同的敏感性，其中扁藻Platymonas sp.和斜生栅藻S．obliquus最敏感。藻类通过生物富集和生物降解两种途径去除水中污染物，其中，邻苯二甲酸二丁酯最容易被去除。藻类固定化能够在一定程度上增加藻类对污染物的降解。     

单甲脒农药对模型池塘生态系统藻类群落结构的影响

在１．５－５０．０ｍｇ／Ｌ的浓度范围内，单甲脒农药对模型池塘生态系统中的浮游植物群落结构有明显影响。尤其在加药的头４ｄ内，藻类种类、数量、多样性指数、种类数比及增长率明显下降，优势比显著上升，敏感种及清洁种减少甚至消失，高浓度（５０．０ｍｇ／Ｌ）的单甲脒在２ｄ内可把藻类全部杀灭。随试验时间的延长，药物不断降解，６ｄ后藻类种类、数量、多样性指数又不断回升。随加药次数的增多，药物对藻类抑制作用明显减弱，藻类的种类、数量、多样性指数等指标不断上升，尤其是藻类数量增加明显，试验后期，藻类数量高低主要受Ｎ、Ｐ浓度大小的影响。     

三种海藻凝集素细胞凝集活性的比较

比较了3种经纯化的海藻凝集素即铁钉菜凝集素（IOL），鹿角沙菜凝集素（HCL0和脆江蓠凝集素（GBL）对红细胞，微藻，细菌，酵母及肿瘤细胞的凝集活性，IOL对供试的动物红细胞均有凝集作用，而HCL和GBL只对部分红细胞产生凝集作用，3种凝集素都不能凝集人的A，O，B型血红细胞。在12种供试的微藻中，有6种单细胞藻类分别被海藻凝集素所凝集，海洋微藻比淡水微藻敏感，盐生杜氏藻均可被3种海藻凝集素所凝集，3种海藻凝集素都能凝集枯草杆菌，但不能凝集胃癌细胞，3种凝集素中，IOL对细胞的凝集作用最好，表3参13