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41.
为了探讨东方蝾螈在人工养殖效果评估方面 ,在确定屠宰或捕捞的大小与时间的适宜度方面 ,在生理、病理分析时 ,在治疗时间和用药量等诸方面 ,都达到取材时期的合理性问题 ,测定了东方蝾螈的身型指数 ,并初步建立了回归方程Y =- 2 5 0 +0 .6 2X1 ,并对相关数据的处理方法进行了探讨。 相似文献
42.
近年来,我国的景观植物产业得到了很大发展,但仍存在很多问题,为了解决这些问题,我们开发了景观植物信息查询系统(简称LPIIS)。LPIIS的构建包括后台数据库和管理系统2部分,以Microsoft Access开发后台景观植物数据库,实现各种零散的景观植物数据资料的数字化;采用面向对象的开发语言VB进行信息系统的界面设计和系统集成,实现了人性化的界面,操作更为方便。LPIIS的出现改变了过去景观植物信息管理的手工方式,具有可视化人性化的界面、提供多媒体信息、数据的维护和更新具有继承性、后台数据库可方便的移植于网络等特点。 相似文献
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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
46.
选择3周龄健康、无病、体重无显著差异的肉仔鸡96只,随机分为3组,每组设4 个重复,每个重复8只。分别饲喂蛋白质水平(19.5%)相同而能量水平不同(3.0 Mcal/kg、 3.08 Mcal/kg、3.16Mcal/kg)的3种饲粮。试验结果表明:前两周饲料转化(采食/增重)均以 中能量组(3.08 Mcal/kg)最好,为1.4416±0.1199,但三种不同能量水平对肉仔鸡平均日增 重、平均日耗料、饲料转化率均差异不显著(P>0.05);后两周饲料转化仍以中能量组最好,为 1.6362±0.1346,且显著优于高能量组(P<0.05),而与低能组和中能组之间差异不显著,各 能量处理组蛋白质、粗纤维、钙的代谢率均差异不显著(P>0.05),而磷的代谢率却存在显著 差异(P<0.05),其中,以中等能量组的磷代谢率最高,平均为90.73%;3种能量水平下肉仔鸡 半净膛率、全净膛率均差异不显著(P>0.05),表明能量水平并不影响肉仔鸡屠宰性能。 相似文献
47.
试验将槐花蜂花粉进行振动磨超微粉碎破壁,分别按1 g/kg、5 g/kg、10 g/kg三个不同剂量混到蛋鸡饲料中,从7日龄开始饲喂至50日龄,每个剂量分两个试验,试验一用新城疫Ⅳ系疫苗免疫雏鸡,利用β-微量法监测血清中的血凝抑制抗体效价的动态变化;试验二用大肠杆菌油乳苗免疫雏鸡,利用间接血凝法监测血清中大肠杆菌抗体效价的动态变化。分别定期称重捕杀取脾、胸腺、法氏囊,计算免疫器官指数,取肠道内容物计数大肠杆菌和乳酸菌,测定肠道内pH值。结果表明,不同剂量的破壁蜂花粉均能不同程度地提高病毒抗原性抗体效价和菌体抗原性抗体效价,对雏鸡免疫器官的发育以及肠道内环境、菌群的平衡也有一定影响。 相似文献
48.
The influence of sampling scheme and interpolation method on the power to detect spatial effects of forest birds in Ontario (Canada) 总被引:1,自引:0,他引:1
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
49.
Verbeylen Goedele De Bruyn Luc Adriaensen Frank Matthysen Erik 《Landscape Ecology》2003,18(8):791-805
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
50.
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