白龙江上游地区森林植物群落物种多样性的研究

 白龙江上游地区属长江防护林工程重点地区之一。根据36个样地的调查资料,分析了该地区森林植物群落物种多样性的特征：群落内各层物种丰富度指数的大小顺序为“灌木层>草本层>乔木层”;均匀度指数变化比较复杂,在杜鹃巴山冷杉（Rhododendron fastigiatum-Abies fargesii）林中为“草本层>灌木层>乔木层”,在苔藓巴山冷杉林中为“乔木层>灌木层>草本层”,其余群落中为“灌木层>草本层>乔木层”;多样性指数的大小顺序为“乔木层<灌木层和草本层”,而灌木层与草本层的多样性指数随林分郁闭度变化而变化,在郁闭度30%的杜鹃巴山冷杉林中,草本层大于灌木层,在郁闭度47%的箭竹巴山冷杉林中,草本层和灌木层相当,在郁闭度55%以上的各个群落内,灌木层大于草本层。同一海拔不同坡向群落的物种多样性表现为分布于阳坡的油松（Pinus tabulaeformis）林大于分布于阴坡的草类云杉（Picea asperata）林。物种多样性沿海拔梯度的变化表现为随海拔升高先降低后增加,从海拔2 400 m的栎类阔叶林,2 600 m的草类云杉林,2 800 m的箭竹(Sinarundinaria nitida)巴山冷杉林,到3 000 m的苔藓巴山冷杉林和3 200 m的杜鹃巴山冷杉林,物种多样性依次下降,到海拔3 400 m的高山杜鹃（Rhododendron fastigiatum）灌丛,物种多样性增加。物种多样性在紫果云杉(Picea purpurea)林的演替系列中表现为随群落演替发展而增加,后降低,在针阔混交林阶段达到最大。     

北京松山自然保护区森林群落物种多样性及其神经网络预测

物种多样性是群落结构和功能复杂性的一种度量,物种多样性的空间分布格局受许多环境因子的影响.运用多样性指数,多层感知器网络,分析了松山保护区森林群落物种多样性与群落类型、结构和生境之间的关系.结果表明:(1)大果榆+山杨混交林、油松+青杨混交林物种丰富度、多样性和均匀度均较高,而大果榆林、华北落叶松林的各项指数值均较低.Patrick指数和Shannon-Weiner指数在森林群落中均表现为草本层＞灌木层＞乔木层;Pielou指数在榆林中表现为草本层＞乔木层＞灌木层,而在其他森林群落中表现为灌木层＞草本层＞乔木层.(2)功能层物种多样性在海拔梯度上的变化趋势不同,在乔木层,丰富度、多样性和均匀度随海拔的升高逐渐降低;在灌木层,丰富度、多样性和均匀度均呈比较明显的单峰曲线变化趋势;在草本层,丰富度和多样性随海拔的升高都呈下降趋势,而在草本层,均匀度变化不大.(3)用多层感知器网络预测功能层多样性效果很好,结果发现坡向对乔木层和灌木层物种多样性的影响最大,而海拔高度对草本层物种多样性的影响最大.     

大兴安岭呼中地区白卡鲁山植物群落结构及其多样性研究

通过沿海拔梯度系统调查,运用TWINSPAN分类方法,划分出大兴安岭地区白卡鲁山的主要植物群落类型并分析了其结构特征。利用物种丰富度和α多样性等指标,研究了乔木层、灌木层和草本层植物的多样性特征及其随海拔的变化趋势。结果显示：(1)白卡鲁山乔木层在海拔。700-1290m范围内,可分为4种主要群落类型：兴安落叶松疏林、兴安落叶松-白桦混交林、兴安落叶松-白桦-樟子松混交林、兴安落叶松纯林群落;(2)同一植物群落的结构特征比较相似,除兴安落叶松疏林外,其他三种森林类型的平均胸径和平均树高随海拔升高有逐渐增大的趋势;(3)乔木层的直径和树高分布清晰地反映了群落的水平和垂直结构。直径分布均呈现倒“J”型,表明森林的自我更新状况良好;而树高分布主要以双峰分布和近似对称分布为主;(4)乔木层的物种丰富度和α多样性在兴安落叶松纯林中最小,在兴安落叶松-白桦混交林和兴安落叶松-白桦-樟子松混交林群落次之,而在兴安落叶松疏林群落相对较高。各群落类型的灌木层和草本层植物多样性没有明显的差异。乔木层、灌木层和草本层的物种多样性随海拔梯度均没有表现出明显的变化趋势。     

长白山牛皮杜鹃群落物种多样性的海拔梯度变化及相似性

采用样地调查法,研究了牛皮杜鹃群落物种组成、群落结构特征、物种多样性及其沿海拔梯度的变化规律,对不同海拔牛皮杜鹃群落进行相似性分析。结果表明:(1)牛皮杜鹃群落相同海拔高度,草本层的物种多样性普遍高于灌木层的物种多样性。自海拔1926—1986m,灌木层α多样性指数先降低后升高,1986m后再次降低,到达海拔2010m处达到最低点,适应高山苔原带特殊生境条件的物种逐渐增多,多样性指数开始回升。海拔2250m,生物多样性指数的变化趋于平缓,物种组成相对较为稳定。海拔2528m以上,生物多样性再次呈降低趋势。草本层的α多样性指数中,物种多样性指数SW、丰富度指数D和均匀度指数R沿海拔梯度的变化趋势大致相同。海拔1986m处时出现最小值,海拔2350m时达最大值。牛皮杜鹃群落α多样性指数间呈P0.01水平极显著正相关性,物种丰富度指数对群落的物种多样性贡献率最大,表现为丰富度指数(D1、D2)种间机遇指数(H)生态优势度指数(SN)群落均匀度指数(R)。(2)牛皮杜鹃群落β多样性沿海拔梯度基本呈波形变化,草本层β多样性指数普遍高于灌木层β多样性指数。在牛皮杜鹃群落物种沿海拔梯度的替换速率上,草本植物高于灌木物种。Routledge指数的变化趋势不显著。海拔1986m处和海拔2250m处,草本层Cody指数出现两处极值,海拔2250m以上群落灌木层之间差异和变化较小,Whittaker多样性指数和Cody指数逐渐趋于平稳。(3)海拔梯度间生境及群落结构差异性越大,生物多样性变化越明显。海拔高度接近的群落间相似性系数较高,海拔是影响牛皮杜鹃群落差异的主要因素。     

幕阜山森林群落结构与物种多样性研究

幕阜山地处中亚热带-北亚热带过渡地带,物种资源丰富.通过对其典型样地的调查,分别采用Shannon-Wiener指数、Simpson指数和Pielou均匀度指数作为测度指标,研究了幕阜山地区森林群落结构及其物种多样性特征.结果表明,该地区主要有21个森林群落类型.其中常绿阔叶林中,物种丰富度指数与多样性指数在群落梯度上的总体趋势均为灌木层相对高于乔木层,乔木层相对高于草本层;在落叶阔叶林中,其丰富度指数的趋势为灌木层＞草本层和乔木层,而在草本层与乔木层间是波动的,多样性指数的趋势为灌木层＞草本层＞乔木层;在针叶林中,物种丰富度、多样性指数表现的总趋势基本一致,即灌木层的丰富度相对较高,其次为草本层,乔木层的相对较小.在其他群落类型中,多样性指数、均匀度指数在乔木层、灌木层和草本层则表现出多样化的趋势;另外,从总体上看,各种指数在海拔梯度上并未表现出明显的规律性.     

贡嘎山海螺沟冷杉群落物种多样性与群落结构随海拔的变化

冷杉(Abies fabri)是贡嘎山东坡亚高山暗针叶林主要的建群种和林线树种.在海螺沟沿海拔梯度调查了19个冷杉林样方,以此分析冷杉在其垂直分布范围内,物种多样性、群落结构及生物量沿海拔梯度的变化.结果表明(1)二元指示种分析(TWINSPAN)可将全部样方分为5个群落类型 a. 冷杉+麦吊云杉(Picea brachytyla)+云南铁杉(Tsuga dumosa)混交林群落; b. 冷杉+阔叶树-杂灌群落; c. 冷杉+阔叶树-冷箭竹(Bashania fangiana)群落; d. 冷杉-杂灌-苔藓群落; e. 冷杉-杜鹃(Rhododendron spp.)-苔藓群落.群落类型的空间分异主要受海拔和坡度、坡位等小地形因素控制.(2)群落乔木层、灌木层的物种丰富度和Shannon-Wiener指数随海拔上升而减小;但草本层没有明显的变化趋势.(3)各层的β多样性指数随海拔上升均有减小趋势;海拔3300 m以上的群落构成差异较小.(4)冷杉群落和冷杉种群的最大高度、平均高度、最大胸径、平均胸径都随海拔上升而逐渐减小;海拔3550 m以上,冷杉个体的高和直径生长因受到林线环境制约而明显减小,而DBH>5 cm的冷杉和全部种的密度随海拔上升而增大.(5)冷杉林材积随海拔上升而下降,平均值为846.4 m3/hm2.     

福建梅花山常绿阔叶林植物物种多样性及其海拔梯度格局

常绿阔叶林是福建梅花山国家级自然保护区地带性植被。采用样带与典型群落调查法对区内的常绿阔叶林14400m2样地展开调查,并对植物多样性海拔梯度格局进行分析,结果表明：（1） 群落植物物种丰富度、Gleason丰富度指数、Simpson指数、Shannon Wiener指数和Pielou均匀度指数的均值分别为64.42、10.75、5.75、3.50、0.58,且这5种指数在各样带间差异极为显著,并随海拔的升高均呈单峰曲线变化,峰值出现在海拔700m~900m。（2） 群落各层次的植物物种丰富度、Shannon Wiener指数均呈现灌木层（包括幼树和层间植物）〉乔木层〉草本层的特征。乔木、灌木层物种丰富度与乔木层Shannon Wiener指数在海拔梯度上的样带间差异极显著,变化趋势与群落相似;灌木层与草本层Shannon Wiener指数以及草本层物种丰富度随海拔梯度变化不明显。因此,梅花山自然保护区常绿阔叶林植物物种多样性的海拔梯度格局呈现单峰分布,并支持中间高度膨胀模式（mid domain model）。     

安徽皇甫山黄檀群落物种多样性初步研究

分析了安徽皇甫山黄檀（Dalbergia hupeana）群落乔木层、灌木层、草本层物种多样性指数,表明群落物种多样性较低.乔木层物种多样性指数最低,灌木层、草本层物种多样性指数较高.黄檀在群落中优势度明显.     

浙江天台山甜槠群落物种多样性研究

对浙江省天台山甜槠群落的不同样地、不同层次的物种丰富度、物种多样性指数和群落均匀度进行了分析。结果表明:木本植物的物种丰富度、物种多样性指数明显大于草本植物,而群落均匀度两者无显著差异。在群落垂直结构中,乔木层第二亚层的物种丰富度、物种多样性指数均显著大于第一亚层,它们之间的群落均匀度差异不显著。灌木层的物种丰富度、多样性指数最大,乔木层次之,草本层最小。灌木层的群落均匀度明显大于乔木层,而乔木层、灌木层的群落均匀度与草本层差异不显著。乔木层、灌木层、草本层的多样性各项指标在群落各样地间均有一定的差异,相对而言,灌木层、乔木层的差异较小,草本层的差异较大。     

太行山南段森林群落物种多样性研究

分别用多样性指数、丰富度指数、均匀度指数对山西太行山南段森林群落的物种多样性及其与环境的关系进行了分析.结果表明:(1)3个植被型的物种多样性指数的顺序为:落叶阔叶林>温性针阔叶混交林>温性针叶林.(2)落叶阔叶林中各群系的物种多样性指数的顺序为:漆树 青麸杨林>鹅耳枥 青榨槭林>青檀林>辽东栎林>栓皮栎林>白桦林>红桦林>山杨 白桦林.(3)温性针叶林中各群系的物种多样性指数的顺序为南方红豆杉林>油松林>白皮松林>侧柏林.(4)物种丰富度指数在群落梯度上的总体趋势表现为草本层>灌木层>乔木层;多样性指数的趋势则为灌木层>乔木层>草本层;各群落灌木层物种均匀度指数大于乔木层和草本层,乔木层均匀度与草本层相差不明显.(5)各群落多样性指数在海拔梯度上表现出明显的规律,呈单峰曲线变化,即中等海拔高度上的群落物种多样性较高,而高海拔和低海拔多样性较低,这主要是由于在中海拔(大约1 500 m)地段水热条件组合较好、人类活动干扰较少所致.     

Uniform hypothesis of cell behavior--movement, contact inhibition of movement, adhesion, chemotaxis, phagocytosis, pinocytosis, division, contact inhibition of division, fusion.

The cell has been represented as a charged liquid drop. Contrary to the DLVO-theory, the effect of the surface potential upon the value of the interfacial tension of the cell membrane has also been taken into consideration. The cell membrane has visco-elastic properties and its constituents may move against each other. Cell movement is caused by the appearance of a small number of the electrically charged constituents of the cell membrane on the leading edge of the cell. This produces a local decrease in the surface tension and the cell membrane expansion. At the moment of contact between two cells proton transfers occur between the strongly negatively charged microvilli of one cell and the body of the other, analogous to a condenser breakdown. This, through the effect on the surface tension, causes contact inhibition of movement. The distribution of the proton dissociable groups modifies the interaction between the cells (differentiation) and between the cell and the substratum (adhesion). Adsorption of the charged compounds at the surface of the cell membrane, decreasing the surface potential and increasing the surface tension, causes the phenomena of chemotaxis, phagocytosis and pinocytosis. Cell division, considered in the terms of the surface energy, requires an adequate supply of considerable quantities of energy inversely proportional to the surface potential value. In case of a reduction of the distance between the cells, their surface potential and the energetic barrier of the cell division processes increases, and causes contact inhibition of cell division. Due to their high charge, division of neoplastic cells is inhibited much later than division of normal cells, or is completely ininhibited due to geometric conditions. Fusion of the cell membrane in the intra-cellular and intercellular processes is a reverse process in relation to the cell division.     

The Effect of Age and Gender on Al, B, Ba, Ca, Cu, Fe, K, Li, Mg, Mn, Na, P, S, Sr, V, and Zn Contents in Rib Bone of Healthy Humans

The effect of age and gender on major, minor, and trace element contents in the intact rib bone of 80 relatively healthy 15–55-year-old women and men was investigated. Contents or upper limit of contents of 16 chemical elements in the rib bone were determined by inductively coupled plasma atomic emission spectrometry (ICP-AES). Mean values (M?±?SΕΜ) for the mass fraction of Ba, Ca, Cu, Fe, K, Li, Mg, Na, P, S, Sr, and Zn (milligram per kilogram of dry bone) were as follows: 2.54?±?0.16, 171,400?±?4,050, 1.35?±?0.22, 140?±?11, 1,874?±?71, 0.049?±?0.011, 2,139?±?38, 5,378?±?88, 75,140?±?1,660, 1,881?±?51, 291?±?20, and 92.8?±?1.5, respectively. The upper limits of contents of Al, B, Mn, and V were <7.20, <0.65, <0.36, and <0.03, respectively. Statistically significant tendency for the Ca, Mg, and P content to decrease with age was found in the human rib bone, regardless of gender. The mass fraction of Fe in the male rib bone increases with age. It was shown that higher Ca, Mg, Na, P, and Sr mass fractions as well as lower Fe content were typical of female ribs as compared to those in male ribs.     

Distribution of N,P, K,Ca, Mg,S, Zn,Fe, Mn and Cu in groundnut

Summary Concentration of N, P, K, Ca, Mg and S in summer groundnut crop was higher than in kharif while Zn, Fe, Mn and Cu contents were higher in summer crop. Kernel's N, P and Zn; Leaflet's Ca and Mn; Stem's K and Fe; Root's S and Cu and Petiole's Mg contents were highest. Shell's N, P, K, Mg, S, Zn and Cu; Kernel's Ca, Fe and Mn contents were the least. N, P, K, S, Zn and Cu concentrations decreased linearly as the crop grew. Ca, Mg, Fe and Mn concentrations did not display any distinct pattern. Ca concentration was positively correlated with pod yield in both the seasons.     

Synthesis,tautomerism, and antimicrobial,anti-HCV,anti-SSPE,antioxidant, and antitumor activities of arylazobenzosuberones

2-Dimethylaminomethylene-1-benzosuberone 1 was coupled with diazotized aniline derivatives to afford a series of the hitherto unreported 2-arylazo-1-benzosuberones 3a–i. The tautomeric structure and the effect of substituents on the tautomeric form (s) of the products 3a–i were discussed. Similar coupling of the enaminone 1 with diazonium salts of heterocyclic amines gave the respective fused azolotriazino-benzosuberones. Some of the newly synthesized compounds showed potent antimicrobial, anti-HCV, antioxidant, antitumor (as topoisomerase I inhibitors), and antimicrobial activities.     

The effect of malathion,diazinon, and various concentrations of zinc,copper, nickel,lead, iron,and mercury on fish

Acute and chronic toxicity tests for malathion, diazinon, copper (Cu), mercury (Hg), lead (Pb), zinc (Zn), nickel (Ni), and iron (Fe) were conducted. Mortalities ofBarilius vagra andCyprinus carpio (common carp) were variable but LC50-96 hr were similar for pesticides. AdultB. vagra seem to be more sensitive to malathion than juvenile carp. Both juvenile carp and adultB. vagra were extremely sensitive to diazinon. Long-term exposure to pesticides modified morphology and behavior. The LC50-96 values for Cu, Hg, and Pb were 0.3, 0.16, and 0.44, respectively, for smaller fish and 1.0, 0.77, and 1.33, respectively, for larger fish. Replicate LC50 values for Zn, Ni, and Fe were somewhat variable, and for these metals, the size of the fish seemed to affect response because LC50 values increased as fish size increased. Cooper, Pb, Zn, and Fe residues following exposure to sublethal concentrations of these metals for 15 d were significantly greater in whole juvenile common carp than in controls.