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31.
INTENTION, GOAL, SCOPE, BACKGROUND: Cyanobacteria have the natural ability to degrade moderate amounts of organic pollutants. However, when pollutant concentration exceeds the level of tolerance, bleaching of the cells and death occur within 24 hours. Under stress conditions, cyanobacterial response includes the short-term adaptation of the photosynthetic apparatus to light quality, named state transitions. Moreover, prolonged stresses produce changes in the functional organization of phycobilisomes and in the core-complexes of both photosystems, which can result in large changes in the PS II fluorescence yield. The localization of ferredoxin-NADP+ reductase (FNR) at the ends of some peripheral rods of the cyanobacterial phycobilisomes, makes this protein a useful marker to check phycobilisome integrity. OBJECTIVE: The goal of this work is to improve the knowledge of the mechanism of action of a very potent pesticide, lindane (gamma-hexaclorociclohexane), in the cyanobacterium Anabaena sp., which can be considered a potential candidate for bioremediation of pesticides. We have studied the effect of lindane on the photosynthetic apparatus of Anabaena using fluorescence induction studies. As ferredoxin-NADP+ reductase plays a key role in the response to oxidative stress in several systems, changes in synthesis, degradation and activity of FNR were analyzed. Immunolocalization of this enzyme was used as a marker of phycobilisome integrity. The knowledge of the changes caused by lindane in the photosynthetic apparatus is essential for rational further design of genetically-modified cyanobacteria with improved biorremediation abilities. METHODS: Polyphasic chlorophyll a fluorescence rise measurements (OJIP) have been used to evaluate the vitality and stress adaptation of the nitrogen-fixing cyanobacterium Anabaena PCC 7119 in the presence of increasing concentrations of lindane. Effects of the pesticide on the ultrastructure have been investigated by electron microscopy, and FNR has been used as a marker of phycobilisome integrity. RESULTS AND DISCUSSION: Cultures of Anabaena sp. treated with moderate amounts of lindane showed a decrease in growth rate followed by a recovery after 72 hours of pesticide treatment. Concentrations of lindane below 5 ppm increased the photosynthetic performance and activity of the cells. Higher amounts of pesticide caused a decrease in these activities which seems to be due to a non-competitive inhibition of PS II. Active PS II units are converted into non-QA reducing, so called heat sink centers. Specific activity and amount of FNR in lindane-treated cells were similar to the values measured in control cultures. Release of FNR from the thylakoid after 48 hours of exposure to 5 ppm of lindane towards the cytoplasm was detected by immunogold labeling and electron microscopy. CONCLUSIONS: From these results, we conclude that the photosynthetic performance and activity of the cells are slightly increased in the presence of lindane up to 5 ppm. Moreover, in those conditions, lindane did not produce significant changes in the synthesis, degradation or activity of FNR. The high capability of Anabaena to tolerate lindane makes this cyanobacterium a good candidate for phytoremediation of polluted areas. RECOMMENDATION AND OUTLOOK: The results of this study show that cultures of Anabaena PCC 7119 tolerate lindane up to 5 ppm, without significant changes in the photosynthetic vitality index of the cells. However, a slight increase in phycobiliprotein synthesis is observed, which is related to total protein content. This change might be due to degradation of proteins less stable than phycobiliproteins. An identification of the proteins with altered expression pattern in the presence of the pesticide remains the subject of further work and will provide valuable information for the preparation of strains which are highly tolerant to lindane.  相似文献   
32.
同源四倍体与二倍体水稻Wx基因位点的遗传差异   总被引:2,自引:3,他引:2  
测定了中国科学院成都生物所培育出的14种同源四倍体水稻及8种大面积推广的二倍体水稻的直链淀粉含量,并利用微卫星标记484/485,Wxup2/485及PCR—AceⅠ分子标记对同源四倍体及二倍体水稻进行扩增.发现直链淀粉含量发生变化的部分同源四倍体水稻队基因位点发生变异,表明微卫星标记与同源四倍体水稻直链淀粉含量之间存在相关性,并初步探讨了同源四倍体水稻Wx基因位点遗传变异的原因.图2表1参13  相似文献   
33.
北京市轻型汽车尾气排放检测结果分析   总被引:2,自引:0,他引:2  
对北京市566辆在用轻型车排放尾气进行了BASM检测,对不同厂牌的化油器车、化油器改造车和电喷车排放的HC、CO和NO平均浓度进行了比较,结果表明,化油器改造车3种污染物平均浓度比化油器车低50%左右,电喷车3种污染物平均浓度可比化油器车低80%左右。同时对几种车型的劣化规律进行了分析,发现化油器车的劣化关系离散性大,而另外两种技术的车辆的劣化关系呈收敛性,说明化油器车的污染物排放和保养关系密切,电喷车劣化规律明显优于化油器车和化油器改造车。实验结果为I/M实施提供了科学依据。  相似文献   
34.
Investigationsonsimultaneousdeterminationofsilverandmercuryincatalytic-ligandsubstitutionreactionwithstopped-flowtechniquecal...  相似文献   
35.
In recent years, the ability of microorganisms to decolorize textile wastewater has received great attention due to the environmental persistence and toxicity of these pollutants. In this paper biological decolorization of triphenylmethane dye, C.I. Basic Green 4 (BG 4), by Chlorella species was investigated. The effect of operational parameters (temperature, pH, initial dye concentration and algal concentration) on decolorization efficiency was examined. Results indicated that the desired initial pH was 9. The stability and efficiency of the algae in long-term repetitive operations were also examined. Michaelis-Menten kinetics was employed to describe the apparent correlation between the decolorization rate and dye concentration. The optimal kinetic parameters, Vmax (specific decolorization rate) and Km (maximum specific decolorization rate) were 4.6 mg dye g cell-1 h-1and 151.0 mg L-1, respectively. Fig 10, Tab 2, Ref24  相似文献   
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38.
水蕹菜对啤酒及饮食废水净化与资源化研究   总被引:35,自引:2,他引:35  
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39.
以8W黑光灯为光源,γ-FeOOH为催化剂,加入草酸构成光化学Fenton体系,研究了这一体系中橙黄I的光化学脱色动力学;考察了橙黄I的初始浓度、初始pH值和草酸初始浓度对橙黄I光化学脱色降解的影响.结果表明,草酸能显著促进橙黄I的脱色与降解,橙黄I光化学脱色一级动力学常数随草酸浓度的增大呈先升后降的趋势,最佳草酸初始浓度为1·8mmol·L-1;溶液pH值的变化也显著影响橙黄I的脱色.光化学反应过程中Fe2+和总Fe的浓度也随草酸浓度与反应时间的变化而变化.  相似文献   
40.
研究了厌氧折流板反应器(ABR)活性厌氧污泥对偶氮染料酸性大红GR的吸附与生物降解性能,并与失活污泥进行了对比。试验结果表明,35℃时厌氧活性污泥2h、12h、6d的脱色率分别为78.2%、86.0%、98.9%。无论在反应初始阶段还是稳定阶段,ABR活性厌氧污泥对染料的去除效果都明显优于失活污泥。而且在初始COD为1152mg/L的,由于非有效吸附位置染料脱落等原因,反应期间,失活污泥混合液中染料浓度还会升高。情况下,活性厌氧污泥混合液出水COD为86.0mg/L,去除率约为92.5%。这说明ABR厌氧污泥微生物在短时间内便可以得到驯化,一旦厌氧微生物适应生长环境,生物降解便开始对染料发挥作用。  相似文献   
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