野生植物甜菜树嫩茎叶的营养成分分析

甜菜树[Yunnanopilia longistaminea(W.Z.Li)C.Y.Wuet D.Z.Li]为山柚子科(Opiliaceae)甜菜树属(YunnanopiliaC.Y.Wu et D.Z.Li)植物,小乔木,主要分布于云南红河谷地区海拔1 000～1 400 m的河谷密林中,邻近的云南东南部和广西西南部也有分布[1].每年3-8月间当地民众主要采食其嫩茎叶,炒食、做汤或腌制都鲜甜爽口,一直是当地非常受欢迎的特色野菜,鲜菜市场价格远高于一般栽培蔬菜和野生蔬菜的价格,且供不应求,具有广阔的市场开发前景.本文对甜菜树可食部分嫩茎叶的水分、灰分、总酸、总糖、碳水化合物、粗蛋白质、粗脂肪、Vc、氨基酸及矿物质含量进行了分析,为甜菜树的开发利用提供科学依据.     

虎杖不同部位白藜芦醇含量的分析

白藜芦醇(反-3,4,5-三羟基二苯乙烯,resveratrol)是一种活性多酚物质,也称芪三酚,1940年从毛叶藜芦(Veratrum puberulum Loes. f.)的根中最先得到.有研究认为,白藜芦醇及其苷是植物体在恶劣环境下或遇到病原侵害时自身分泌的一种抗毒素,因此有“植物杀菌素”之称[1].     

海菜花（水鳖科）-新变种-嵩明海菜花

报道了海菜花-新变种-嵩明海菜花（Ottelia acuminata var．songmingensis Z．T．Jiang,H．Li et Z．L．Dao）。该变种与原变种的区别在于叶片带状厚纸质,不透明,叶尖钝圆或具短尖。     

绿绒蒿属一新变种

报道了绿绒蒿属一新变种,即椭圆叶红花绿绒蒿(MeconopsispuniceaMaxim.var.ellipticaZ.J.Cui etY.Sh.Lian)。     

野生软枣猕猴桃总黄酮含量的测定

利用分光光度法,测定了软枣猕猴桃中总黄酮的含量,建立了芦丁浓度-吸光度关系的回归方程.     

Recruitment and growth of herb‐layer species with different colonizing capacities in ancient and recent forests

Abstract. Forest herbs differ greatly in their capacity to recolonize secondary forests established on former agricultural land. We investigated whether interspecific differences in recruitment or growth can account for differences in colonization success. Seeds and adults of two species with limited colonization capacities (Anemone nemorosa and Primula elatior) and two species with high colonization capacities (Ranunculus ficaria and Geum urbanum) were introduced in ancient and recent forest sites within the Muizen forest (Belgium). At all sites, half of the plots were also cleared of above‐ground vegetation. Seedling establishment was similar in recent and ancient forest sites. However, both the number and subsequent survival of seedlings of the two hemicryptophytes (G. urbanum and P. elatior) were significantly lower when vegetation cover was present, while seedling number and survival of the two geophytes (A. nemorosa and R. ficaria) were less influenced by vegetation cover. Adult performance of P. elatior and G. urbanum was significantly better in the nutrient enriched recent forest stands and in the absence of vegetation cover. Performance of A. nemorosa and R. ficaria was not affected by any of these factors. We conclude that the extent of seed limitation is probably the main cause for the different colonization capacities of the species investigated.     

福建省毛竹混交林群落结构特征的比较

通过设置临时标准地对龙栖山、武夷山和天宝岩3个国家级自然保护区的3种毛竹混交林群落类型结构进行调查与统计分析.结果表明,在物种数量上从多到少依次为:武夷山国家级自然保护区的毛竹 少叶黄杞(Phyllostachys pubescences Mazel ex H. Delehaie Engelhardtia fenzelii Merr.)混交林(68科125属230种),龙栖山国家级自然保护区的毛竹 南方红豆杉[Taxus chinensis (Pilger) Rehd. var. mairei (Lemee et Lévl.) Cheng et L. K. Fu]混交林(69科135属194种)和天宝岩国家级自然保护区的毛竹 长苞铁杉(Tsuga longibracteata Cheng)混交林(41科71属105种).3个毛竹混交林群落结构分明,毛竹在混交林群落乔木层中占绝对优势的地位.乔木层、灌木层和草本层层次清晰,还具有层间层.毛竹 南方红豆杉群落和毛竹 长苞铁杉群落乔木层可分为3个亚层,而毛竹 少叶黄杞群落乔木层可分为2个亚层.毛竹 少叶黄杞群落的灌木层物种数和草本层盖度均比其他2个群落高.     

亚贡叶中营养成分和功能性化学成分分析

亚贡[Smallanthus sonchifolius (Poepp. et Endl.) H. Robinson]为多年生草本植物[1],原产南美洲安第斯山脉,是当地印第安人的传统根茎食品, 在我国海南、台湾等地有种植.亚贡生长在亚热带气候、无霜冻、湿度大、常年云雾缭绕且海拔1 000 m以上的高山中.亚贡可生长至2～3 m,根茎在生长7～12个月后成熟.根茎中果寡糖含量丰富[2],其低热量、高甜度的特性适合糖尿病人及减肥者食用[3].     

Herbaceous vegetation change in variable rangeland environments: The relative contribution of grazing and climatic variability

Abstract. A 44‐yr record of herbaceous vegetation change was analysed for three contrasting grazing regimes within a semi‐arid savanna to evaluate the relative contribution of confined livestock grazing and climatic variability as agents of vegetation change. Grazing intensity had a significant, directional effect on the relative composition of short‐ and mid‐grass response groups; their composition was significantly correlated with time since the grazing regimes were established. Interannual precipitation was not significantly correlated with response group composition. However, interannual precipitation was significantly correlated with total plant basal area while time since imposition of grazing regimes was not, but both interannual precipitation and time since the grazing regimes were established were significantly correlated with total plant density. Vegetation change was reversible even though the herbaceous community had been maintained in an altered state for ca. 60 yr by intensive livestock grazing. However, ca. 25 yr were required for the mid‐grass response group to recover following the elimination of grazing and recovery occurred intermittently. The increase in mid‐grass composition was associated with a significant decrease in total plant density and an increase in mean individual plant basal area. Therefore, we failed to reject the hypotheses based on the proportional change in relative response group composition with grazing intensity and the distinct effects of grazing and climatic variability on response group composition, total basal area and plant density. Long‐term vegetation change indicates that grazing intensity established the long‐term directional change in response group composition, but that episodic climate events defined the short‐term rate and trajectory of this change and determines the upper limit on total basal area. The occurrence of both directional and non‐directional vegetation responses were largely a function of (1) the unique responses of the various community attributes monitored and (2) the distinct temporal responses of these community attributes to grazing and climatic variation. This interpretation supports previous conclusions that individual ecosystems may exist in equilibrial and non‐equilibrial states at various temporal and spatial scales.     

Effect of time on the natural regeneration of salt marsh

Abstract. The effect of time on natural regeneration of two salt marshes was studied in relation to plant and edaphic factors. The study was carried out in two naturally restoring salt marshes, differing in restoration time, in Txingudi (Bay of Biscay). After 20 yr, the younger salt marsh had the same plant species richness and high species similarity as a 35 yr old salt marsh (17 and 16, respectively, similarity index = 0.9), but both sites had lower species richness and similarity than a nearby natural salt marsh (36 plant species and similarity indices of 0.45 with the 35 yr old marsh and 0.46 with the 20 yr old marsh). Plant species present in the two recovering salt marshes followed a similar distribution pattern in relation to organic matter, conductivity and moisture content although this zonation differed from the natural salt marsh. The range of edaphic factors measured was also similar, but differed from those in the natural salt marsh. The process of plant species recolonization and spatial distribution might be delayed by a low probability of species arrival and by the time need for the restoration of hydrologic and edaphic factors. This study supports the necessity of long‐term monitoring in measuring coastal salt marsh restoration.