共查询到17条相似文献,搜索用时 93 毫秒
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以水华鱼腥藻的乙酰乳酸合成酶(ALS)比活力作为研究对象,通过在离体和活体条件下比较其对甲磺隆的敏感性,探讨了甲磺隆对水华鱼腥藻的作用机理.结果表明:离体条件下,甲磺隆对水华鱼腥藻ALS抑制强烈,且浓度越高抑制作用越强,其IC50=0.026mg/L;活体条件下,当甲磺隆的浓度为0.001mg/L时,甲磺隆对水华鱼腥藻ALS几乎没有抑制作用,这可能是甲磺隆在水华鱼腥藻体内被降解失活的缘故.当甲磺隆的浓度为0.01~10mg/L时,甲磺隆对水华鱼腥藻ALS抑制与离体条件下的抑制作用基本一样,其IC50=0.714mg/L. 相似文献
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该文针对滦河源水进行了杀藻的试验研究。研究结果表明:对引滦水而言,硫酸铜、高锰酸钾和过氧化氢三种杀藻剂的藻类去除率均随药剂投量的增加而升高;在原水含藻量较高(高于1000万个/L)情况下,硫酸铜较佳投量1.0mg/L,藻类去除率为70%~80%;过氧化氢投量4mg/L,藻类去除率为60%左右;高锰酸钾投量0.6mg/L,藻类去除率为85%;通过杀藻效果、经济性以及安全性等方面的综合比较,对于以有毒蓝藻为优势藻的引滦水,三种杀藻剂的优劣排序为:高锰酸钾〉硫酸铜〉过氧化氢。 相似文献
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壳聚糖凝聚去除景观水中微囊藻的研究 总被引:2,自引:0,他引:2
考察了壳聚糖原位除藻的效果及可行性。对pH范围为5.5-7.0,藻浓度大于5.0×10^5cells/mL的模拟含藻水,壳聚糖投加量与藻浓度比大于0.5mg:(106cells/mL)、壳聚糖投加量〉0.5g/m3时,0D650去除率可以达到90%以上。而对相同藻浓度的实际景观水,当壳聚糖投加量与藻浓度比大于0.8mg:(10^6cells/mL)、壳聚糖投加量〉0.8g/m3时,OD650去除率可以达到80%以上。通过现场围隔实验.研究了壳聚糖凝聚除藻与遮光工艺相结合的处理效果,即投加壳聚糖凝聚沉淀藻细胞后进行遮光处理,使沉入水底的藻类由于失去光源而不再上浮,逐渐死亡。与无遮光处理围隔组对照,发现除藻效果有明显提升,显示了该工艺的可行性。 相似文献
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在高光强为160μE/(m2·s)、低光强为16μE/(m2·s)、葡萄糖浓度0~30g/L范围内,、进行了鱼腥藻Anabaenasp.PCC7120的摇瓶光自养和混合营养培养.在高光强下最大藻细胞密度(0.92~3.1g/L)明显高于低光强(0.11~0.58g/L),而且高光强使混合营养培养的对数期缩短.在不同光强下,葡萄糖浓度在0~18g/L范围内提高显著促进了细胞的生长,在18~30g/L范围内变化对细胞生长不再有更大的影响.高光强促进了藻细胞对葡萄糖的利用.在高光强下随着葡萄糖浓度的提高,细胞得率逐渐变小. 相似文献
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杜邦开发的以磺酰脲为基质,用于与草甘膦桶混在耐草甘膦玉米中进行应用的两个除草剂已在美国获得批准。它们是①Require Q(砜嘧磺隆6.3%+麦草畏52.9%)和②Resolve Q(砜嘧磺隆18.4%+噻吩磺隆4%)。它们对多种禾木科杂草和阔叶杂草可提供触杀和残留防治效果,对耐草甘膦杂草也提供可靠的管理效果。由于上述两种除草剂中均含有安全剂双苯嗯唑酸,从而使得它能在多种玉米杂交品种虫应用。Resolve Q的推荐用量为0.9公斤/公顷,而Require Q的用量为4盎司/英亩。 相似文献
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本文生要研究了甲嘧磺隆对鲈鱼、蛏两种主要的滩涂养殖生物进行了急性毒性研究,为甲嘧磺隆用于滩涂防治互花米草提供科学依据。结果表明:处理96h后对于鲈鱼和蛏的半致死浓度(LC50)分别为151.322和374.450mg/L,甲嘧磺隆对两种实验动物急性毒性属于低毒,对于两种滩涂养殖动物在急性毒性方面没有明显影响。 相似文献
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[目的]单嘧磺隆是我国创制的谷子田内吸型磺酰脲类除草剂,在谷子田应用前景广阔。采用超高效液相色谱串联质谱法(UPLC-MS/MS)建立了谷子、植株和土壤中单嘧磺隆的残留检测方法,并测定了收获期的残留量,为单嘧磺隆的安全使用提供技术支撑。[方法]谷子、植株和土壤中的单嘧磺隆残留采用纯乙腈振荡提取,C18和GCB净化,UPLC-MS/MS检测,外标法定量。[结果]在0.0025~0.1 mg/L质量浓度范围内,单嘧磺隆质量浓度与其峰面积之间呈现出良好线性关系,R2≥0.9984。在0.005、0.01、0.1 mg/kg添加水平,单嘧磺隆在谷子、植株和土壤中的回收率在69%~96%范围内,相对标准偏差低于12.1%,符合农药残留分析的要求。田间条件下,按照推荐剂量施用10%单嘧磺隆可湿性粉剂,收获期谷子、植株和土壤中单嘧磺隆残留均低于方法的定量限(LOQ,0.005 mg/kg)。[结论]10%单嘧磺隆可湿性粉剂按照推荐剂量施用收获期安全。本试验可以为单嘧磺隆的安全使用和最大残留限量(MRL)的制定提供基础数据。 相似文献
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Jignasha G. Patel J. I. Nirmal Kumar Rita N. Kumar Shamiyan R. Khan 《Polycyclic Aromatic Compounds》2016,36(1):72-87
This study encompasses the biodegradation capacity of Anabaena fertilissima to model PAH (Polycyclic Aromatic Hydrocarbon) compounds namely Anthracene (ANT) and Pyrene (PYR) at different LC50 concentrations viz., 5.0 mg/L and 3.0 mg/L, respectively, on growth in terms of Chlorophyll-a and protein. Depletion in chlorophyll-a and protein content was registered with rise in PAHs concentration while the inhibition of nitrogen fixing enzymes such as nitrate reductase and glutamine synthetase activity was also concentration dependent and showed more sensitivity for high molecular weight aromatic compound PYR as compared to ANT. GC/MS analysis explained the degradation of ANT by 46% and PYR by 33%, at 5.0 mg/L and 3.0 mg/L, respectively. Moreover, the common degraded product for ANT was 2, 4-Dimethyl-1-heptene and for PYR it was 2, 3, 4-Trimethylhexane. Results indicate that PYR was more stable and recalcitrant compared to ANT. This study suggests that Anabaena fertilissima could be used for bioremediation of ANT and PYR pollution in surface waters and terrestrial environments. 相似文献
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Mixotrophic growth is one potential mode for mass culture of microalgae and cyanobacteria particularly suitable for the production of high value bioactive compounds and fine chemicals.The typical heterocystous cyanobacterium Anabaena sp.PCC 7120 was grown in the presence of exogenous glucose in light.Glucose improved the cell growth evidently,the maximal specific growth rate under mixotrophic condition(0.38 d1)being 1.6-fold of that of photoautotrophic growth.Mixotrophy caused a variation in cellular pigment composition,increasing the content of chlorophyll a and decreasing the contents of carotenoid and phycobiliprotein relative to chlorophyll a.Fluorescence emission from photosystem II(PSII)relative to photosystem I was enhanced in mixotrophic cells,implying an increased energy distribution in PSII.Glucokinase(EC 2.7.1.2)activity was further induced in the presence of glucose.The mixotrophic culture was scaled up in a 15 L airlift photobioreactor equipped with an inner and an outer light source.A modified Monod model incorporating the specific growth rate and the average light intensity in the reactor was developed to describe cell growth appropriately.The understanding of mixotrophic growth and relevant physiological features of Anabaena sp.PCC 7120 would be meaningful for cultivation and exploitation of this important cyanobacterial strain. 相似文献
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Spence E Dunlap WC Shick JM Long PF 《Chembiochem : a European journal of chemical biology》2012,13(4):531-533
Route of the sun block: according to empirical evidence, sun-screening mycosporine-like amino acids (MAAs) in Eukarya originate from the shikimic acid pathway, whereas in cyanobacteria, biosynthesis of the MAA shinorine reportedly occurs through the pentose phosphate pathway. However, gene deletion shows that the cyanobacterium Anabaena variabilis ATCC 29143 does not biosynthesise shinorine exclusively by this route. 相似文献
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Amparo Ramos F.Gabriel Acién José M. Fernández‐Sevilla Cynthia V. González Ruperto Bermejo 《Journal of chemical technology and biotechnology (Oxford, Oxfordshire : 1986)》2010,85(6):783-792
BACKGROUND: Phycobiliproteins are water soluble proteins useful as fluorescent markers of cells and macromolecules, and as natural colorants, and are anticarcinogenic. Although phycobiliproteins have many applications, their use is limited by the high cost of the purified macromolecules, mainly related with the cost of extraction and purification. In this study a fast and scalable method for preparative extraction and purification of C‐phycocyanin (C‐PC) from Anabaena marina is developed. RESULTS: The method developed consists in the extraction of phycobiliproteins using repeated single contact strategy, separation being performed by expanded bed adsorption (EBA) chromatography using Streamline‐DEAE. Optimal conditions for EBA were obtained at small scale, using a 15 mm internal diameter column, these being a sample load of 0.9 mg C‐PC mL?1 adsorbent, an expanded bed volume twice the settled bed volume and a sample viscosity of 1.109 mP. The process was then scaled up 36 times, the success of the scale‐up process being verified. Finally, to obtain pure C‐PC conventional ion‐exchange chromatography was utilized. CONCLUSION: Small diameter columns was shown to be useful to simulate the behavior of larger diameter columns for use in scaled up systems. Expanded bed adsorption was demonstrated to be a scalable technology allowing large quantities of C‐PC to be obtained, maintaining high protein recovery while reducing both processing cost and time. The proposed methodology allows recovery of more than 62% of the C‐PC contained in the biomass in the form of pure C‐PC concentrates. Copyright © 2010 Society of Chemical Industry 相似文献