123 resultados para 412


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用聚丙烯酰胺凝胶电泳技术分析了蜂猴(N. coucang)和倭蜂猴(N. pygmaeus) 的血红蛋白(Hb)、乳酸脱氢酶、酯酶、苹果酸脱氢酶同功酶。用醋酸薄膜电泳分 析了蜂猴和倭蜂猴的血清 蛋白成分, 并进行了比较。懒猴的LDH-B含量明显低 于高等灵长类。

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<正>目前又到了鱼塘容易发生翻塘的季节,在此介绍一些有关池塘中氧气循环的知识,以便更好地认识翻塘发生的机理和发生规律,便于积极地防止翻塘现象的发生。一、冬天的氧循环在冬天,由绿色植物和藻类的光合作用产生的氧减少,这是因为从秋天开始这些植物和藻类会正常地相继死亡,数量就会减少,

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国家十五重大科技专项(2002AA601021); 淡水生态与生物技术国家重点实验室开放课题; 河南省科技攻关项目(0624440039)资助

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以18种细胞系为材料,研究微囊藻毒素LR(20μg/mL和50μg/mL)所诱导的细胞毒性。形态观察表明,在经过30h以上的微囊藻毒素处理后,PC-3,J82,786-0,5637,VERO-E6等5种细胞出现了明显的细胞形态改变,毒素浓度越高,形态改变越厉害。微囊藻毒素LR的细胞毒性用LDH泄漏来表示。结果显示,5种毒素处理细胞的LDH泄漏呈剂量依赖性增加,其中5637和PC-3的LDH泄漏在同样的处理后较为厉害;同对照比较,SOD活力在20μg/mL MCLR处理下呈增加趋势,但在50μg/mL浓度下

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水生植物组织内氮和磷(N和P)含量受到水体营养状况和植物生长状况影响。对长江中游江汉湖群不同营养水平湖泊中大型水生植物的N和P含量3个季度的研究表明,在不同生活型水生植物中,沉水植物主要分布在中营养到中富营养湖泊中,在富营养湖泊均无分布,浮叶和挺水植物在不同营养类型湖泊的沿岸带均有分布。N和P含量以沉水植物最高,浮叶植物次之,挺水植物最低。水生植物的N和P含量都达到或超过生长所需最低N和P阈值,代表性浮叶植物和沉水植物的N和P含量随着湖泊营养水平提高呈现规律性变化。湖泊5种常见的水生植物N和P含量与水柱中

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分别在拥挤胁迫后第3、10、20、30天对鲫鱼(Carassiusauratus)血液皮质醇水平和血液溶菌酶水平进行了检测,并在每次采集血样后用嗜水气单胞菌(Aeromonashydrophila)进行人工感染以评估鱼体抵抗力。结果显示,血液皮质醇水平在胁迫后几天内显著升高(P<0.005),随后虽有所下降,但至第30天高密度组仍保持较高水平(216.32±11.91)ng/mL。实验初期,血液溶菌酶水平小幅升高,但经过长时间的拥挤后,高密度组血液溶菌酶活性受到极大抑制,显著低于同期对照组(P<0.01)

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中国科学院知识创新工程项目资助 ( 2 2 0 3 16); 国家自然科学基金项目资助 ( 3 0 0 70 15 4)

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以F4代转hGH基因红鲤体细胞 (肾脏和尾鳍 )及培养 18代的F4代转hGH基因红鲤尾鳍细胞为核供体 ,泥鳅或黄河鲤成熟卵为受体 ,进行了核移植 ,以探讨外源F4代转基因鱼体外源基因的分布与存在形式、稳定性和克隆转基因鱼的可能性。F4代红鲤肾脏细胞核与泥鳅卵配合的核移植胚胎有 12 4 %发育到囊胚 ,0 33%发育到神经胚 ;F4代尾鳍细胞核移入泥鳅卵后的重组胚发育到囊胚、神经胚、肌节期和肌肉效应期的胚胎分别为 2 4 5 %、0 3%、0 2 %和 0 1% ;对照卵无发育。F4代红鲤尾鳍培养细胞与

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将大珠母贝精子经不同脉冲循环数、脉冲数和不同脉冲幅度处理后,与卵子受精,然后观察受精和发育情况并进行统计分析,根据受精率确定最佳参数组合为:脉冲循环数 6、脉冲数 28和脉冲幅度 6kV。此前用电击参数为脉冲循环数6、脉冲数27和脉冲幅度 10kV进行了大珠母贝转基因实验,获得转基因阳性贝。

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用地质统计学中的半方差和双对数半方差图对保安湖—湖湾(黄风口)的大型水生植物群落格局进行了研究,在不同的尺度上对群落及其主要组成种类的空间异质性进行了定量的描述。结果表明:保安湖黄风口大型水生植物群落的双对数半方差图存在线性区域,群落具有分形特征(自相似性)。在不同的尺度下,群落和各组成种类空间格局具有不同的分形维数值,异质性程度存在差异。但其异质性程度不高,建议进行群落调查时,样方尺度应取520m;单一种群调查时的样方尺度取380m。

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Partial cDNA sequences of TCR gamma and CD3 gamma/delta were isolated from the thymus of common carp (Cyprinus carpio L.) by the method of suppression subtractive hybridization (SSH). Subsequently the full length cDNAs of carp TCR gamma and CD3 gamma/delta were obtained by means of 3' RACE and 5' RACE, respectively. The full length of carp TCR gamma chain is 1368 bp and encodes 326 amino acids including a signal peptide region of 19 amino acids and a transmembrane region of 23 amino acids at the C-terminal region from aa 291 to 313. The V region of carp TCR gamma contains 109 amino acids, the core motif FGXG in J segment was also found in carp TCR gamma. The C region of carp TCR gamma contains the characteristic CX6PX6WX45C motif. The CP region of carp TCR C gamma contains 37 amino acids. The full length of carp CD3 gamma/delta is 790 bp and encodes 175 amino acids including a signal peptide region of 17 amino acids and a transmembrane region of 23 amino acids from aa 93 to 115. Similar to other known CD3 gamma/delta s, four cysteine residues in the extracellular domain and an immunoreceptor tyrosine-based activation motif ITAM (YxxL/Ix6-8YxxL/I) in the intracellular domain are also included in carp CD3 gamma/delta. Differing from other known CD3 gamma/delta s, carp CD3 gamma/delta tacks the CXXCXE motif in the extracellular domain. RTPCR analysis demonstrated that the expression of TCR gamma gene was mainly in the thymus and gill of 6-month carp, but in 18-month carp, TCR gamma gene was detected in all the examined tissues. The expression of CD3 gamma/delta gene was detected in all examined tissues of 6 and 18-month carp; among them, the highest expression level was in the thymus of 6-month carp. In situ hybridization showed that CD3 gamma/delta-expressing cells were widely distributed in the head kidney, spleen and kidney of carp, whereas in the thymus, they were densely distributed in the lymphoid outer zone and scattered in the epithelioid inner zone. (c) 2007 Published by Etsevier Ltd.

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Experimental sediments and water from shallow, eutrophic Dianchi Lakes were treated in a controlled laboratory microcosm using different chemicals under different anoxic levels. This study revealed that the polyaluminum chloride (PAC) was able to inhibit the phosphorus release and decrease the UV254 value at any anoxic level. When the DO concentrations were between 0.76-0.95 mg(.) L-1, the UV(254)value, total phosphorus (TP), and total dissolved phosphorus (TDP) in the water column were decreased by 71.93%, 87.12% and 64.24% respectively. The UV254, TP, and TDP were also decreased by 72.94%, 70.87% and 50.76% respectively at the levels of 4.56-5.32mg(.)L(-1) of DO concentrations. The treatment effects of TP and TDP in the water column using copper sulfate however were not as efficient as the PAC treatment. The UV254 value was increased with the addition of copper sulfate at every anoxic level tested but the chlorophyll-a (Chl-a) content was decreased rapidly and efficiently by copper sulfate more than the treatment by PAC. When the DO concentrations were 0.76-0.86mg(.)L(-1) and 4.75-5.14mg(.)L(-1), the Chl-a concentrations were decreased by 84.87% and 75.07% respectively through copper sulfate treatment. With additions of PAC and copper sulfate, the phosphorus fractions in sediments were shifted forward to the favorable shapes that have little ability of release. The TP concentrations in sediments were increased after treatment via PAC and copper sulfate. Under anoxic conditions, most of the BD-P (Fe-P) to NaOH-P (Al-P) was converted using the recommended PAC dose in BD-P rich sediment. Similar to the PAC, the copper sulfate also could flocculate the exchange phosphorus from sediment to overlying water. Overall though, the effects of copper sulfate treatment were not better than that of the PAC.

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The sequencing analysis of the mitochondrial DNA control region (mtCR DNA) was performed to assess the genetic divergence and population structure of the Chinese sucker Myxocyprinus asiaticus (Cypriniformes Catostomidae) using four sample lots from natural populations of the Yangtze River. The mtCR DNA sequences of approximately 920 base pairs were obtained. A total of 223 nucleotide positions were polymorphic, and these defined 39 haplotypes. Of the 39 haplotypes, 37 (90%) were not shared, and among the populations as a whole there was little sharing of haplotypes. The average haplotype diversity (0.958) and the average nucleotide diversity (0.052) indicated a higher level of genetic diversity of Chinese sucker through the river. Analysis of molecular variation (AMOVA) of data revealed significant partitioning of variance (P<0.001) among populations (60.29%), and within populations (39.71%). The topology according to the neighbor joining and maximum parsimony methods showed mosaic composition of the 39 haplotypes, suggesting that the populations wore not completely divergent. The pairwise F statistic values, however, indicated that the population structuring existed to some extent among the geographic populations. There was a positive relationship between the aquatic distance and the genetic distance (Fst) among the populations (P<0.05). Based on our data, it is suggested that genetic drift, gene flow, and stochastic events are the possible factors influencing the population structure and genetic variation.