21 resultados para Lavandula viridis L’Hér

em Chinese Academy of Sciences Institutional Repositories Grid Portal


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Green-lipped mussels (Perna viridis) were collected from a site in Hong Kong which is relatively free from polycyclic aromatic hydrocarbon (PAH) contamination, and maintained in situ at this and three other sites with different degrees of PAH contamination. The transplanted mussels were retrieved after a 30-day field exposure. DNA adducts in the gill tissues were quantified, and tissue concentrations of benzo[a]pyrene as well as total PAHs (with potential carcinogenicity) determined for individual mussels. Results indicate that (1) tissue concentration of PAHs and adduct levels in mussels collected from a single site can be highly variable; and (2) adduct levels were related to tissue concentrations of benzo[a]pyrene as well as total PAHs of individual animals.

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外来生物入侵已经在世界范围内造成严重的危害,它不仅导致生物多样性的减少和丧失而且威胁着全球的生态环境和经济发展。入侵种在入侵区域的种群扩散是入侵种带来风险的最根本问题,也是其造成危害的重要原因。研究入侵物种的扩散规律可以了解其在入侵地的入侵状况和扩散趋势,这对制定合理的控制措施具有重要意义。本研究选取14种在我国具有较强威胁性的外来入侵植物,通过对其入侵历史动态的分析,判断其在我国的入侵与扩散阶段,进而预测其在我国的潜在分布区。这14种外来植物为紫茎泽兰(Ageratina adenophora)、土荆芥 (Chenopodium ambrosioides.)、喜旱莲子草(Alternanthera philoxeroides)、反枝苋(Amaranthus retroflexus)、刺苋(Amaranthus spinosus)、皱果苋(Amaranthus viridis)、北美独行菜(Lepidium virginicum)、藿香蓟(Ageratum conyzoides)、钻形紫菀(Aster subulatus)、小蓬草(Conyza canadensis)、一年蓬(Erigeron annuus)、牛膝菊(Galinsoga paviflora)、飞机草(Eupatorium odorata)和北美商陆(Phytolacca americana)。   紫茎泽兰最早于20世纪40年代入侵我国,经过1940—1960年长达20年的时滞期,紫茎泽兰开始在云南及其临近的省份如四川、贵州和广西迅速扩散。其中,紫茎泽兰在南亚热带和中亚热带气候条件下的扩散速度为20公里/年,而在垂直地带性北亚热带地区的扩散速度为6.8公里/年。紫茎泽兰仍没有入侵到垂直地带性暖温带地区。尽管1990年后,紫茎泽兰在云南基本停止扩散,但其在邻近省(市)的快速传播表明紫茎泽兰在我国仍处在扩散阶段,还没有达到饱和阶段。生态位模型预测结果和紫茎泽兰在已经入侵地区扩散的地理生态式样基本相符。我国南部及中南部地区的气候条件十分适合紫茎泽兰生长。而在华中地区,由于环境条件不太适宜,其扩散速度会相对较慢。我国北部和西北部的气候条件完全不适合紫茎泽兰生存。因此,我国南部和中南部广大未入侵地区将会受到紫茎泽兰入侵和快速扩散的严重威胁,对此应该立即采取紧急措施。   自从紫茎泽兰于1978年首次入侵四川省以来,已经在四川、重庆和湖北大面积扩散。紫茎泽兰在此新近入侵区域主要沿河流、公路、铁路扩散。其中沿安宁河、108国道和成昆铁路向北扩散的平均速度为19公里/年,而沿金沙江-长江向东北扩散的平均速度为33公里/年。特别是2000年以后,紫茎泽兰沿金沙江-长江的扩散速度达到了88公里/年。紫茎泽兰得以如此迅速扩散是其本身生物学特性和当地地理生态特点多种因素之间一系列耦合关系共同作用的结果。人类活动和1998年金沙江-长江特大洪水也促进了紫茎泽兰在该地区的扩散。另一方面,紫茎泽兰在新近入侵地区的垂直分布范围说明随海拔高度上升所引起的垂直地带性气候变冷是紫茎泽兰入侵和扩散的自然限制条件。   此外,通过对其余13种外来入侵植物入侵历史过程重建发现,除了牛膝菊、反枝苋和皱果苋最早入侵地位于内陆地区以外,其余10种外来入侵植物的最早入侵地都位于我国的东部、南部沿海和西南边境地区。这13种外来植物通常不是通过单一途径传入,而是通过两种或多种途径传入不同的地点。相应地,入侵后也呈现不同的扩散模式。这13种外来植物在我国大体上包括5种入侵和扩散式样即1)从南部沿海和西南边境分别向内陆扩散,如霍香蓟、飞机草,北美商陆;2)从东部沿海向内陆扩散,例如钻形紫菀,小蓬草、北美独行菜和喜旱莲子草;3)从东部沿海、南部沿海和西南边境分别向内陆扩散,如刺苋;4)从南部沿海向内陆扩散,如土荆芥;5)从最早入侵的内陆地区向周边地区扩散,如反枝苋、牛膝菊和皱果苋。分布区动态分析显示当前这13种外来入侵植物在我国都还处在扩散阶段,而且有些外来植物还处在快速扩散阶段,如飞机草。   在上述研究基础上,我们对这13种外来入侵植物开展了生态位模型适生区预测和比较分析。并且结合其扩散动态和当前分布现状,我们对其潜在的分布区及扩散趋势进行了系统分析和预测。飞机草、土荆芥、霍香蓟、牛膝菊和北美商陆,这5种外来植物的现有分布区明显小于其在我国的适生区,因此它们在我国的潜在分布区很广,应给予足够的重视。喜旱莲子草、反枝苋、皱果苋、北美独行菜、一年蓬、钻行紫菀和北美商陆在我国的入侵范围与其适生区域之间基本重合,但在其入侵范围内仍存在大面积的未入侵区域。这些未入侵地区通常被已入侵区域所包围,因此也应当给予足够的重视。刺苋和小蓬草在我国的潜在的分布区相对较小,这些植物已经基本上完全入侵了其适生区。因此,这些植物在我国向临近区域继续扩散的可能性不大。   

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本论文为国家自然科学基金重大项目“中国陆地生态系统对全球变化的反应模式研究”的部分研究内容。 本文对C02正常浓度(350ppm)和C02倍增(700ppm)条件下,小麦(Triticum, aestivum)、半野生小麦(Triticum aestivum spp.tibeticumShao)、大麦(Hordeum vulgare)、野大麦(Hordeum brevisubulalum)、水稻(Oryza sativa,)、野生稻(Or7za sativa ssp.)、谷子(Setaria italica)、狗尾草(Setaria viridis)、高粱(Sorghum vulgare)、玉米(Zea mays)、旱雀麦(Bromus tectorum)、旱麦草(Eremopyrum triticeum)等12种禾本科植物幼苗的叶片厚度、叶肉细胞密度、维管束鞘细胞中的叶绿体数、叶肉细胞中的叶绿体数、表皮细胞密度、气孔密度、气孔指数、气孔长度、气孔阻抗及平均株高、鲜重、茎秆直径、根的直径、种子的萌发率及叶绿体超微结构等进行了比较研究。 结果表明,C02倍增使不同种类、不同测试项目反应不一。总体上看,CO2浓度倍增,使10种禾本科植物(野大麦、玉米外)的吐片厚度普遍增加。除个别种类外,C4种类的平均株高、鲜重、根直径倍增组比对照组减小;气孔平均密度增加,而C3种类则呈相反趋势o C4种类比C3种类的叶片气孔开度对C02倍增反应更为敏感。在高浓度C02条件下,C4种类的叶绿体超微结构变化较明显,淀粉粒显著增加。野生种类的表皮细胞密度,叶肉细胞密度,维管束鞘细胞中的叶绿体数及茎秆直径,C02倍增组比对照组减少,栽培种类则显著增加。气孔密度与气孔指数基本呈正相关;而气孔长度与气孔密度则大体上呈负相关。 文中对高浓度C02条件下,供试植物形态结构的变化和规律,及全球大气变化对未来农业可能产生的影响进行了讨论。

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The genes encoding triosephosphate isomerase (TIM) in three species of Microcystis (M. aeruginosa, M. viridis and M. wesenbergii) were investigated. Reverse transcriptase-polymerase chain reaction indicated that they were transcribed in the cells. Analyses showed that their DNA and deduced amino acid sequences were highly conserved between all the three species, only a single nonsynonymous substitution was seen at position 31, from an Asp in M. aeruginosa and M. viridis to Glu in M. wesenbergii. Sequence alignment of these with 12 other known cyanobacterial TIM sequences showed that all the cyanobacterial TIMs had a very high level of amino acid identity (over 50% between each two). Comparison of the cyanobacterial TIMs with other reported TIMs (from diverse lineages of the three Domains) showed that they possessed common active-site residues and sequence motifs. All cyanobacterial TIMs have two common cysteine residues (Cys127 and Cys176), and the Cys176 is almost cyanobacteria-specific with only one exception in Streptomyces coelicolor. Both secondary structure alignment and comparative modelling of Synechocystis sp. TIM showed that Cys176 was located at the hinge region of the flexible loop-6 and might therefore be critical to the movement of TIM's loop-6, which is important to the function of the enzyme. Thus, the cyanobacterial TIM-specific Cys176 may be a potential site for the discovery of suitable drugs against cyanobacteria, and such drugs may have utility in controlling water blooms due to cyanobacteria.

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We investigated the relationships of Asian bufonids using partial sequences of mitochondrial DNA genes. Twenty-six samples representing 14 species of Bufo from China and Vietnam and 2 species of Torrentophryne from China were examined. Three samples of Bufo viridis from Armenia and Georgia were also sequenced to make a comparison to its sibling tetraploid species B. danatensis. Bufo americanus, from Canada, was used as the outgroup. Sequences from the 12S ribosomal RNA, 16S ribosomal RNA, cytochrome b, and the control region were analyzed using parsimony. East Asian bufonids were grouped into two major clades. One clade included B. andrewsi, B. bankorensis, B. gargarizans, B. tibetanus, B. tuberculatus, its sister clade B. cryptotympanicus, and the 2 species of Torrentophryne. The second clade consisted of B. galeatus, B. himalayanus, B. melanostictus, and a new species from Vietnam. The placement of three taxa (B. raddei B. viridis, and its sister species, B. danatensis) was problematic. The genus Torrentophryne should be synonymized with Bufo to remove paraphyly. Because B. raddei does not belong to the clade that includes B. viridis and B. danatensis, it was removed from the viridis species group. The species status of B bankorensis from Taiwan is evaluated. (C) 2000 Academic Press.

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根据中国云南滇池藻类样品的观察结果,对中国分布的淡水微囊藻属Microcystis10个常见种的形态特征进行了描述,同时对它们的分类学进行了讨论,并整理出分类检索表。这10种微囊藻是铜绿微囊藻M.aeruginosa、放射微囊藻M.botrys、坚实微囊藻M.firma、水华微囊藻M.flos-aquae、鱼害微囊藻M.ichthyoblabe、挪氏微囊藻M.novacekii、假丝微囊藻M.pseudofilamentosa、史密斯微囊藻M.smithii、绿色微囊藻M.viridis、惠氏微囊藻M.w

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测定了3种微囊藻水华中的优势种类,即铜锈微囊藻(Microcystis aeruginosaK櫣tz .) ,绿色微囊藻(Microcystis viridis(A. Br .)Lemm) ,惠氏微囊藻(Microcystis wesenbergii(Kom.)Kom.) ,以及微囊藻573(Microcystissp.573)的碳酸酐酶活性;研究了无机碳、pH、温度、光强、N/P比等环境因素和外源葡萄糖对铜锈微囊藻碳酸酐酶活性的影响,发现微囊藻碳酸酐酶活性受环境中碳酸氢根浓度的调节,故推断碳酸氢根是铜锈

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应用RAPD-PCR的方法,选用24个随机引物,分析来自不同地区的7株微囊藻的基因组多态性.结果显示,Microcystis.viridis及M.wesenbergii明显与M.aeruginosa区分开.M.aeruginosa分为两个可视为不同种的异源分类单位.作为对照的Anabaenasp.7120与其他微囊藻株表现出完全不同的基因型及更远的遗传距离.此项研究表明,以基因型而不是表现型为基础,分析蓝藻种内及种间区别是可能的.因此,为解决蓝藻分类问题,特别是在种和属的水平上,提供了重要的线索.结合正在

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应用RAPD-PCR的方法,选用24个随机引物,分析来自不同地区的7株微囊藻的基因组多态性。结果显示,Microcystis.viridis及M.wesenbergii明显与M.aeruginosa区分开。M.aeruginosa分为两个可视为不同种的异源分类单位。作为对照的Anabaena sp.7120与其他微囊藻株表现出完全不同的基因型及更远的遗传距离。 此项研究表明,以基因型而不是表现型为基础,分析蓝藻种内及种间区别是可能的。因此,为解决蓝藻分类问题,特别是在种和属的水平上,提供了重要的线索。结合

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<正> 蓝藻植物中的微囊藻属(Microcystis),是存在于湖泊、池塘、水库等环境中普生性藻类,其中一些种类能产生毒素。到目前为止,对铜绿微囊藻(Microcystis aeruginosa)及其它的毒性研究国内外都进行了大量的工作;但对绿色微囊藻(Microcystis viridis)的形态描述、生态特性及

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It is well known that several morphospecies of Microcystis, such as Microcystis aeruginosa (Kutzing) Lemmermann and Microcystis viridis (A. Brown) Lemmermann can produce hepatotoxic microcystins. However, previous studies gave contradictory conclusions about microcystin production of Microcystis wesenbergii (Komarek) Komarek. In the present study, ten Microcystis morphospecies were identified in waterblooms of seven Chinese waterbodies, and Microcystis wesenbergii was shown as the dominant species in these waters. More than 250 single colonies of M. wesenbergii were chosen, under morphological identification, to examine whether M. wesenbergii produce hepatotoxic microcystin by using multiplex PCR for molecular detection of a region (mcyA) of microcystin synthesis genes, and chemical analyses of microcystin content by ELISA and HPLC for 21 isolated strains of M. wesenbergii from these waters were also performed. Both molecular and chemical methods demonstrated that M. wesenbergii from Chinese waters did not produce microcystin. (C) 2007 Elsevier Ltd. All rights reserved.

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Ten common species of Microcystis, based on the examination of water samples from the Dianchi Lake, Yunnan, China, were morphologically described, and their taxonomy was also discussed. They are Microcystis aeruginosa, M botrys, M firma, M flos-aquae, M ichthyoblabe, M novacekii, M pseudofilamentosa, M smithii, M viridis and M wesenbergii. Taxonomic status of other Microcystis species reported in China was also evaluated.