472 resultados para Gentiana tibetica


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采用高效液相色谱法测定了野生与栽培藏药麻花秦艽(Gentiana straminea)根中龙胆苦苷、落干酸、獐牙菜苦苷和獐牙菜苷四种环烯醚萜苷类化学成分的含量及其在不同生长季节的变化趋势。结果表明,4种环烯醚萜苷类成分的含量随植物的生长季节而波动,其活性成分含量在野生种与栽培种之间发生了一定的差异。但是,栽培根中的龙胆苦甙已达到药典的标准,可供药用。

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选用西宁地区人工栽培的高山植物唐古特大黄(Rheum tanguticum)、山莨菪(Anisodus tanguticus)和麻花艽(Gentiana straminea),比较了3种高山植物之间光合作用的光响应和CO2响应特性,叶片光合色素以及UV—B吸收物质的差异;并以低海拔植物菘蓝(Isatis indigotica)为对比,分析了高山植物与低海拔植物的差异。结果表明:与低海拔植物菘蓝相比,3种高山植物光合作用的表观量子效率(AQY)都偏低;唐古特大黄叶片的AQY、羧化效率(CE)和光呼吸速率(Rp)都很低,净光合速率(Pn)的光响应曲线在全日照光辐射范围内并没有达到完全饱和,这与单位面积叶片具有较高的光合色素以及UV—B吸收物质有关;麻花艽植物与唐古特大黄一样,具有较高的UV-B吸收物质和光合色素含量,但其Rp较高,加之Pn受气孔限制较为明显,故其光合作用的饱和光强很低,Pn相对于其它3种植物也较低;山莨菪与低海拔植物菘蓝的光合特性很相似,都具有较高的AQY和CE。这些结果表明,3种高山植物的光合特性有较大差异,但并没有一致的相对于低海拔植物的共性。4种植物Pn的胞间CO2浓度(G)响应曲线在CO2饱和点以后都表现为无机磷(Pi)再生限制,其吃的变化与CO2饱和点以后的最大Pn的变化基本一致。

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麻花秦艽(Gentiana straminea Maxim.)具有清热利胆、舒筋止痛之功效,是一种治疗风湿性关节炎、肺结核、低热盗汗、黄疸型肝炎等的珍稀藏药草本植物。笔者系统阐述了近年来该植物的研究进展,并对其研究方向进行了展望,为该物种资源的进一步有效开发利用提供参考。

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运用核糖体DNA内转录间隔区ITS序列对狭蕊龙胆属Metagentiana10种及其近缘属22种植物进行了系统发育分析.ITS分析结果表明狭蕊龙胆属是一个多系群:在系统发育树上,双蝴蝶属Tripterospermum和蔓龙胆属Crawfurdia的种类位于狭蕊龙胆属各分支中,而且双蝴蝶属和蔓龙胆属的种类也相互交叉;这一结果不支持将3个属各自独立为属.但是,在所有分析中,3个属共同形成一单系分支,是龙胆属Gentiana的姊妹群;这一结果与形态学、花部解剖学、细胞学、孢粉学和胚胎学等证据基本一致,狭蕊龙胆属应该从龙胆属中分离出来,它与双蝴蝶属和蔓龙胆属有更为密切的亲缘关系.根据分支图,在狭蕊龙胆属、双蝴蝶属和蔓龙胆属组成的复合群中,现已知的染色体基数x=17、21和23可能存在网状和平行进化.

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以人工种植的多年生高山植物麻花艽( Gentiana straminea )为材料,在3个不同强度的UV-B辐射处理下,定时测定处理和对照叶片的净光合速率、表观量子效率和暗呼吸的变化.结果显示:UV-B处理对麻花艽叶片的光合作用在短期内有一定的抑制作用,但随着处理时间的增加,该高山植物能很快地适应强UV-B辐射的处理.表明麻花艽这种青藏高原常见的高山植物在长期的自然选择过程中可能已经形成了适应UV-B辐射的特有生理机制.暗呼吸的实验结果亦表明:在3种强度的UV-B辐射处理下,麻花艽叶片的呼吸作用从一开始就未受到抑制;随着UV-B辐射时间的增加,UV-B辐射强度越高,呼吸强度越强;这可能是 UV-B辐射并未引起麻花艽呼吸机构的破坏所致.

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Potentilla fruticosa scrub, Kobresia humilis meadow and Kobresia tibetica meadow are widely distributed on the Qinghai-Tibet Plateau. During the grass exuberance period from 3 July to 4September, based on close chamber-GC method, a study on CO2 emissions from different treatments was conducted in these meadows at Haibei research station, CAS. Results indicated that mean CO2emission rates from various treatments were 672.09+152.37 mgm-2h-1 for FC (grass treatment); 425.41+191.99 mgrn-2h-1 for FJ (grass exclusion treatment); 280.36+174.83 mgrn-2h-1 for FL (grass and roots exclusion treatment); 838.95+237.02 mgm-2h-1 for GG (scrub+grass treatment); 528.48+205.67 mgm-2h-1for GC (grass treatment); 268.97 ±99.72 mgm-2h-1 for GL (grass and roots exclusion treatment); and 659.20±94.83 mgm-2h-1 for LC (grass treatment), respectively (FC, FJ, FL, GG, GC, GL, LC were the Chinese abbreviation for various treatments). Furthermore, Kobresia humilis meadow, Potentilla fruticosa scrub meadow and Kobresia tibetica meadow differed greatly in average CO2 emission rate of soil-plant system, in the order of GG>FC>LC>GC. Moreover, in Kobresia humilis meadow,heterotrophic and autotrophic respiration accounted for 42% and 58% of the total respiration of soil-plant system respectively, whereas, in Potentilla fruticosa scrub meadow, heterotrophic and autotrophic respiration accounted for 32% and 68% of total system respiration from G-G; 49% and 51%from GC. In addition, root respiration from Kobresia humilis meadow approximated 145 mgCO2m-2h-1,contributed 34% to soil respiration. During the experiment period, Kobresia humilis meadow and Potentilla fruticosa scrub meadow had a net carbon fixation of 111.11 grn-2 and 243.89 grn-2,respectively. Results also showed that soil temperature was the main factor which influenced CO2 emission from alpine meadow ecosystem, significant correlations were found between soil temperature at 5 cm depth and CO2 emission from GG, GC, FC and FJ treatments. In addition, soil moisture may be the inhibitory factor of CO2 emission from Kobresia tibetica meadow, and more detailed analyses should be done in further research.

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对青藏高原东部麻花艽(Gentiana straminea)海北居群的传粉生态学进行了3a连续的观察和实验。试验表明自然去雄、人工自交和杂交处理均结实,而人工去雄套袋和自然套袋不结实。麻花艽自交亲合,但必须依赖传粉媒介才能完成授粉过程,不存在无融合生殖。野外捕捉到14种访花昆虫,它们分别属于2个纲,7个目,8个科。观察和分析了各种昆虫的访花行为后,认为苏氏熊蜂(Bombus sushikini)是麻花艽有效而稳定的传粉者。测量表明麻花艽花蜜通道的深度和苏氏熊蜂的舌长基本吻合。苏氏熊蜂的访花频率在lO:00~12:00,13:00~15:00和16:00~18:OO时间段没有差别,单花的访花频率为0.005次/(花·rain)。和其它高山植物相比,青藏高原高山植物麻花艽的访花频率较高。熊蜂传粉和高频率的访花维持了麻花艽在极端寒旱的青藏高原环境下的有性生殖。此外,高频率的访花对于维持该地区高山植物的生殖保障具有重要的现实意义,但是否具有普遍性,还有待研究更多的高山代表类群。

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就青藏高原高寒嵩草草甸生态系统中主要3种植物群落类型:矮生嵩草Kobresia humilis草甸、小嵩草K.pygmaea草甸和藏嵩草K.tibetica沼泽化草甸的环境特征、种类的组成及数量特征、生物量的分布及季节的动态等进行阐述,并对其初级生产力的提高和可持续利用及发展进行分析,提出应对措施.

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对不同类型草地功能群多样性和组成与植物群落生产力之间的关系进行了探讨.结果表明:(1)在矮嵩草(Kobresia humlis)草甸和金露梅(Potentilla froticosa)灌丛中,豆科植物的作用比较明显,而其他功能群植物的作用较弱.(2)在藏嵩草(Kobresia tibetica)沼泽化草甸和小嵩草(K. pygmaca)草甸中,虽然杂类草、C3植物和莎草科植物功能群的生产力占群落初级生产力的比例较大,但二者在统计上没有显著性差异,这表明群落生产力除受物种多样性的影响外,也受物种本身特征和环境资源的影响,更主要的是受到功能群内物种密度和均匀度的影响,即功能群组成比功能群多样性更能说明对生态系统过程的影响.(3)不同类型草地群落植物功能群盖度与群落初级生产力呈显著的线性相关.(4)不同类型草地群落生产力与功能群内物种数的变化均表现为单峰曲线关系,即功能群内物种数处于中间水平时,群落生产力最高。

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在高寒矮嵩草 (K obresia humilis)草甸地区以太阳短波辐射为背景 ,建立了人工增强 U V- B辐射的实验装置 ,每天增补 15 .8k J· m- 2 的辐射剂量 ,模拟平流层臭氧破坏约 5 %时近地表面太阳 UV- B辐射的增强。观测表明 :UV- B辐射的增强对麻花艽 (Gentiana straminea)植物的光合作用无明显的抑制或伤害作用。相反 ,在早晨补充UV- B辐射的短时间内 ,叶片的 Pn 随 Gs的增大而有所提高。随 UV- B辐射时间的延长 ,约在 11∶ 30~ 12∶ 30 ,Pn和Gs有所降低。U V- B辐射时间进一步延长后 (约 14∶ 0 0以后 ) ,处理和对照组叶片 Pn和 Gs的差异趋向不明显。增强太阳 UV- B辐射后 ,麻花艽叶片的光合色素并无明显变化 ,U V-B 吸收物质的含量也无明显变化。麻花艽叶片厚度的直接测量表明: 增强UV -B 辐射能明显提高叶片的厚度。叶片厚度的增加可补偿增强UV -B 辐射后引起的光合色素的光降解, 改善单位叶面积为基础的光合速率, 是高原植物对强UV-B 辐射的一种适应方式。

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本文提出了龙胆属两个种的新名称 (GentianamembranuliferaT .N .Ho,G .nudicaulis Kurz var.as samensisT .N .Ho )和 5个变种的新组合 [(Gentianalateriflora Hemsl.var.uncifolia (H.J.Lam)T.N.Ho,G.sumatranaRidl.var.humifusa (S .Moore)T .N .Ho ,G .quadrifariaBl.var.wightii(Kusnez.)T .N .Ho,G .loerzingiiRidl.var.timida (Kerr)T .N .Ho ,G .membranuliferaT .N .Hovar.recurvata (Kusnez.)T .N .Ho) ]。

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首次报道了条纹龙胆(Gentiana striata Maxim.) 的胚胎学特征, 研究结果用以讨论龙胆属狭蕊组(Gentiana Sect.Stenogyne) 的系统演化关系。主要研究结果如下: 花药四室; 药壁发育为双子叶型; 绒毡层细胞仅来源于初生壁细胞, 故绒毡层起源属单型起源, 细胞具单核,原位退化, 属腺质型绒毡层, 药隔处的绒毡层细胞经多次平周分裂形成2 层至多层的绒毡层细胞, 其余部位的绒毡层细胞仍为1 层细胞; 中层细胞1 层;在花药成熟时, 花药的表皮细胞和药室内壁均部分纤维状加厚且柱状伸长。小孢子母细胞减数分裂为同时型, 四分体的排列主要为四面体形;成熟花粉为32细胞型。子房为2心皮, 1室, 侧膜胎座。胚珠4列。薄珠心,单珠被, 珠心基部产生珠被原基, 进而形成珠被, 条纹龙胆仅有1 层珠被。珠被沿珠心向上生长并将珠心包围, 于胚珠顶部形成珠孔。胚珠在发育过程中, 整个胚珠的本体倒转, 而且珠柄继续生长并弯曲, 使珠孔与合点端的连线与珠柄垂直, 形成Hypertropous 胚珠。大孢子母细胞减数分裂形成的4 个大孢子呈直列式排列, 合点端的大孢子具功能。胚囊发育为蓼型。极核在受精前融合为次生核, 反足细胞3 个、多宿存。雄蕊先熟。珠孔受精。胚乳发育为核型。胚胎发育为茄型酸浆Ⅱ变型。通过比较龙胆属狭蕊组与龙胆属其它组和双蝴蝶属的胚胎学特征表明, 龙胆属狭蕊组在一些重要的胚胎学特征上与双蝴蝶属较相似, 而与龙胆属其它组存在较大差异, 故建议应将龙胆属狭蕊组从龙胆属中移出。

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对高山草甸主要植物群落结构特征及其分布格局的研究结果表明, 矮嵩草草甸植物群落的丰富度最大, 隶属18科, 43属45种, 呈多优势种植物群落; 小嵩草草甸居中, 隶属11科, 30属35种, 小嵩草(K obresia py gm aea) 为优势种; 藏嵩草沼泽化草甸最小, 隶属9科, 21属23种, 藏嵩草(K. tibetica) 为优势种。其中, 有9个种群为3个群落中的共有种, 分别占矮嵩草草甸、小嵩草草甸和藏嵩草沼泽化草甸总种数的20100%、25171% 和39113%。它们在水分资源位上的生态位宽度较大。3个植物群落类型的种2面积关系呈对数曲线分布, 群落的最小样方面积为0125m 2或015m 2较适宜。种2多度分布呈对数正态分布, 其分布模型的表达式如下: S (R ) = S 0e- (a2R 2)

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对青海海北地区高山草甸主要植物群落小嵩草(K obresia pygmaea) 草甸、矮嵩草(K. humilis) 草甸、藏嵩草(K. tibetica) 沼泽化草甸地上生物量动态和能量分配的研究结果表明, 不同植物群落年地上净生产量及其年际动态和主要植物类群生物量季节动态具明显的差异, 其生物量季节动态可由如下模型表示: W i = Ki/(1 + exp (A i - B it) )   植物群落地上、地下生物量的垂直分布呈典型的金字塔和倒金字塔模式。小嵩草草甸、矮嵩草草甸和藏嵩草沼泽化草甸的地上净生产量依次为368.4g·m – 2·a- 1、418.5 g·m – 2·a- 1和518.4 g·m – 2·a- 1, 所固定的太阳能值依次为6655.16kJ·m – 2·a- 1、7610.09 kJ·m – 2·a- 1、9488.77 kJ·m – 2·a- 1。光能利用率分别为0.1097%、0.1256%、0.1568%。

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Alpine Kobresia meadows are major vegetation types on the Qinghai-Tibetan Plateau. There is growing concern over their relationships among biodiversity, productivity and environments. Despite the importance of species composition, species richness, the type of different growth forms, and plant biomass structure for Kobresia meadow ecosystems, few studies have been focused on the relationship between biomass and environmental gradient in the Kobresia meadow plant communities, particularly in relation to soil moisture and edaphic gradients. We measured the plant species composition, herbaceous litter, aboveground and belowground biomass in three Kobresia meadow plant communities in Haibei Alpine Meadow Ecosystem Research Station from 2001 to 2004. Community differences in plant species composition were reflected in biomass distribution. The total biomass showed a decrease from 13196.96 +/- 719.69 g/m(2) in the sedge-dominated K. tibetica swamp to 2869.58 +/- 147.52 g/m(2) in the forb and sedge dominated K. pygmaea meadow, and to 2153.08 +/- 141.95 g/m(2) in the forbs and grasses dominated K. humilis along with the increase of altitude. The vertical distribution of belowground biomass is distinct in the three meadow communities, and the belowground biomass at the depth of 0-10 cm in K. tibetica swamp meadow was significantly higher than that in K. humilis and K. pygmaea meadows (P < 0.01). The herbaceous litter in K. tibetica swamp was significantly higher than those in K. pygnaeca and K. humilis meadows. The effects of plant litter are enhanced when ground water and soil moisture levels are raised. The relative importance of litter and vegetation may vary with soil water availability. In the K. tibetica swamp, total biomass was negatively correlated to species richness (P < 0.05); aboveground biomass was positively correlated to soil organic matter, soil moisture, and plant cover (P < 0.05); belowground biomass was positively correlated with soil moisture (P < 0.05). However, in the K. pygnaeca and K. humilis meadow communities, aboveground biomass was positively correlated to soil organic matter and soil total nitrogen (P < 0.05). This suggests that the distribution of biomass coincided with soil moisture and edaphic gradient in alpine meadows.