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11.
白长财  马志刚 《园艺学报》2005,32(1):155-158
 在对甘肃荚蒾属植物资源调查的基础上, 整理并描述了27个分类群的生境、分布以及观赏性状, 包括叶、花、果实等, 并结合该属植物的资源现状, 提出了可持续开发利用的建议。  相似文献   
12.
‘过山香’香蕉多芽体的诱导及其体细胞胚的发生   总被引:7,自引:2,他引:7  
 以我国重要香蕉种质‘过山香’ (AAB) 为材料, 研究了香蕉多芽体诱导、多芽体茎尖薄切片即分生组织性的表层结构物( scalp) 愈伤组织诱导和体细胞胚发生的合适条件。结果表明, 该品种单个不定芽茎尖在P4培养基(含BAP 100 μmol·L - 1和IAA 1 μmol·L - 1 ) 中继代5个周期后可诱导获得类似花椰菜结构的多芽体。从30 μmol· m - 2 ·s- 1光强, 光/暗周期(16 h /8 h) 培养的多芽体所获得的scalp在添加2,4-D 5μmol·L - 1和Zeatin 1 μmol·L - 1的愈伤组织诱导培养基中黑暗培养, 45 d后愈伤组织诱导率可达97.6%。诱导20 d后黄色分生小球体类结节状愈伤组织开始发生, 90~120 d后在分生小球体局部可获得白色或浅黄色松散的胚性愈伤组织(诱导率为17.5% ) 。从胚性愈伤组织诱导的体细胞胚在成熟培养基上培养60 d后体胚萌发率和植株转化率分别为14.5%和11.1%。  相似文献   
13.
红千层的离体培养及快速繁殖   总被引:3,自引:0,他引:3  
 研究了红千层离体快繁的若干影响因素。结果表明: 叶片在MS + 6-BA 115 mg·L - 1+NAA015 mg·L - 1中的愈伤组织诱导率43% , 并可直接从愈伤组织表面分化出不定芽, 分化率为69.2%; 腋芽启动培养基为MS + 6-BA 1~1.5 mg·L - 1 + NAA 0.5 mg·L - 1 , 萌动率为77%; 继代和增殖培养基为MS + 6-BA 1 mg·L - 1 +NAA 0.25 mg·L - 1 , 平均增殖系数为16.7; 生根壮苗培养基为1 /2MS +NAA 0.25 mg·L - 1 , 生根率96.1%; 试管苗生根培养30~35 d移栽, 成活率最高可达90%以上。  相似文献   
14.
绵阳城市广场建设中的特色分析   总被引:1,自引:0,他引:1  
苏军 《西南园艺》2005,33(1):26-28
在调查的基础上,介绍了四川绵阳市的广场,并以铁牛广场为例分析其特色和不足。  相似文献   
15.
重庆地区色叶植物资源及其在园林中的应用   总被引:5,自引:0,他引:5  
色叶植物是未来园林应用的主要造景植物之一,本文就重庆地区色叶植物资源作了详细调查.按植物色彩分成常色叶类、春色叶类、秋色叶类和两季色类,并对其在园林中的应用途径和前景作了详尽介绍.  相似文献   
16.
桂花在园林景观设计中的应用   总被引:2,自引:0,他引:2  
对桂花植物造景的配置原则、园林应用进行概述和研究,提出因地制宜、层次错落、季相变化、背景烘托、民族传统的配置原则,并就园林应用上桂花的独立造景,桂花与其他植物的配置,桂花与山石、建筑物的配置作了分述。  相似文献   
17.
 选用四川省地方品种‘竹根姜’的茎尖组织建立了体细胞胚性细胞悬浮系, 并通过悬浮培养获得了姜再生植株。结果表明悬浮细胞干质量受pH影响。接种量和AgNO3 对悬浮细胞的生长都有影响:最佳接种量为1.0% , 最适AgNO3浓度为6.0 mg·L - 1。胚性细胞悬浮系增殖后, 接种到前期筛选的成熟分化培养基上获得了再生植株。  相似文献   
18.
Spatial ecology is becoming an increasingly important component of resource management, and the general monitoring of how human activities affect the distribution and abundance of wildlife. Yet most work on the reliability of sampling strategies is based on a non-spatial analysis of variance paradigm, and little work has been done assessing the power of alternative spatial methods for creating reliable maps of animal abundance. Such a map forms a critical response variable for multiple scale studies relating landscape structure to biotic function. The power to reconstruct patterns of distribution and abundance is influenced by sample placement strategy and density, the nature of spatial auto-correlation among points, and by the technique used to extrapolate points into an animal abundance map. Faced with uncertainty concerning the influence of these factors, we chose to first synthesize a model reference system of known properties and then evaluate the relative performance of alternative sampling and mapping procedures using it. We used published habitat associations of tree nesting boreal neo-tropical birds, a classified habitat map from the Manitou Lakes area of northwestern Ontario, and point count means and variances determined from field studies in boreal Canada to create 4 simulated models of avian abundance to function as reference maps. Four point sampling strategies were evaluated by 4 spatial mapping methods. We found mixed-cluster sampling to be an effective point sampling strategy, particularly when high habitat fragmentation was avoided by restricting samples to habitat patches >10 ha in size. We also found that of the 4 mapping methods, only stratified ordinary point kriging (OPK) was able to generate maps that reproduced an embedded landscape-scale spatial effect that reduced nesting bird abundance in areas of higher forest age-class fragmentation. Global OPK was effective only for detecting broader, regional-scale differences. This revised version was published online in July 2006 with corrections to the Cover Date.  相似文献   
19.
In determining isolation effects in fragmented populations, the landscape matrix is not often considered. Usually simple distance measures are used to quantify degree of isolation. We tested the effect of the matrix on the presence of red squirrels in 354 wooded patches in the Brussels Region, by comparing several isolation measures. These were 1) distance to the nearest source patch, 2) the Hanski-measure (a combination of distance to and size of all possible sources), 3) effective distances calculated from different least cost models using the ArcView grid extension ‘Cost Distance’ (a combination of distance and resistance of the landscape, with different resistances for different landscape types) and 4) some combinations of the Hanski-measure and the effective distances. Size and quality of the target patches were always included in the tests of the predictive power of different isolation measures on squirrel presence/absence. All variables examined (patch size, quality and isolation) significantly influenced squirrel presence. Models using the effective distances gave the best results. Models including the Hanski-measure improved significantly when Euclidean distance was replaced by effective distance, showing that parameterisation of matrix resistance added significant additional explanatory power when modelling squirrel presence. This revised version was published online in July 2006 with corrections to the Cover Date.  相似文献   
20.
Agee  James K. 《Landscape Ecology》2003,18(8):725-740
The historical range of variability (HRV) has been suggested as a coarse filter approach to maintain ecosystem sustainability and resiliency. The historical range of variability in forest age structure for the central eastern Cascade Range in Washington State, USA was developed from historical fire return intervals and the manner in which fire acted as both cyclic and stochastic processes. The proportions of seven forest structural stages calculated through these processes were applied to the area of each forest series within the central eastern Cascades landscape. Early successional forest stages were more common in high elevation forest than low elevation forest. The historical proportion of old growth and late successional forest varied from 38 to 63 percent of the forested landscape. These process-based estimates are consistent with those developed from forest structural information. HRV is a valuable planning tool for ecosystem conservation purposes, but must be applied to real landscapes with consideration of both temporal and spatial scale. This revised version was published online in July 2006 with corrections to the Cover Date.  相似文献   
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