福州市古树名木资源的保护与利用

通过对福州市现有古树名木分析,总结了5大特点并结合多年的古树保护经验,探讨了福州市古树景观保护和利用问题。古树景观开发应在保护好古树的前提下进行。古树景观利用切忌异地移植,重点是解救散落于民居中或饱受围困的古树,通过改良环境和复壮,再造宜人景观。文章还涉及古树景观的设计原则、价值评测、指标体系和枯树景观利用以及物种竞争、开发与保护的矛盾等问题。     

改善城市绿化生态效益的途径探讨

从国情和生态角度出发,针对当前城市绿化中存在的问题,以国内外城市改善生态环境成功经验为例,并通过树木和草坪的综合比较,提出城市绿化应因地制宜,以栽树为主,乔灌草结合,注重生态系统的完整性和效益最大化,发展生态园林,改善城市生态环境。     

莆田城市行道树特征分析

用统计学的方法,对莆田市建成区行道路进行全面的调查分析,结果表明:九里香等5种灌木占较大优势,观花灌木较少;与灌木相比,乔木树种占有明显优势,观花、观叶、观果树种较为多样;人行道多为乔木单层结构,树体多为10 m以下低矮乔木;近郊树种分布单一。针对分析结果提出设想和建议。     

模糊数学在适地适树决策方法中的应用

以小兴安岭带岭林区为研究对象,利用模糊数学原理,并通过对主要造林树种、立地类型及隶属度的确定,进行适地适树决策方法的探讨,得出各种立地条件下的适地适树方案.     

浅谈平原绿化管护措施

根据平原绿化的质量要求及特点,关键是做好管护工作.具体介绍了平原绿化可行措施,主要从意识、行政、经济、法制、科技等方面来抓,形成严密、合理、科学地管护系统.     

石梓栽培技术的研究

本文报道了石梓栽培技术研究结果：23°N以南为石梓适生地区，其年均温20．5－24．5℃，极端低温＞－1．5℃，年降雨量1200－2000mm，年平均风速＜2．5m/s。适宜立地为地形开阔，阳光充足，土壤疏松，表土层含有机质＞2％，全氮＞0．1％，速效磷＞0．025mg/100g土，PH4．5－6．9，土壤含水率10％－24％，种子贮存以干燥器最好，贮存一芽率87．4％，催芽用浸晒和浸沤处理，比不处理提前10天发芽，发芽率提高9％－12％，不同子叶类型的芽苗分别移植，较混合移植的苗木合格率提高20．6％；评定了种子主要质量指标和效果良好的育苗，造林方法。技术综合指标；材积年均生长量＞12m^3/ha。     

对东北野生树木资源的引种栽培及在北方城市绿化开发利用上的研究

通过引种,从东北野生树木资源中筛选出适宜于北方地区栽培的绿化树种,丰富了北方地区绿化树木的种类。     

厦门白蚁种类名录与常见白蚁的防治

记载厦门白蚁种类4科12属21种，其中9种为厦门新记录种。为害林木的主要有家白蚁、黑翅土白蚁、黄翅大白蚁，介绍了此3种白蚁常见寄主及防治方法。     

河南省古树名木的保护意义与保护对策

阐述了保护古树名木的重要意义,通过对河南省古树名木的现状分析,提出了今后在保护古树名木方面应采取的措施。     

Hollows in jarrah (Eucalyptus marginata) and marri (Corymbia calophylla) trees: I. Hollow sizes, tree attributes and ages

One hundred and fifty-four jarrah (Eucalyptus marginata) and 85 marri (Corymbia calophylla) trees were measured and assessed, and the numbers and sizes of hollows in these trees were determined by destructive sampling; 665 hollows were located and measured. The relationship between tree diameter and tree age was determined from counts of annual growth rings on 162 of these trees. Large trees and trees with moderately senescent crowns individually bear the most hollows. Although the number of hollows found in individual trees increased with tree diameter, the distribution of tree diameters in the forest is skewed and the large number of small trees with diameters between 40 and 80 cm contribute approximately 50% of all hollows in the jarrah forest. The distributions of entry size, and of hollow depth, are highly skewed, with small hollows occurring more frequently than large hollows. Although jarrah trees bear more hollows than marri trees and the distribution of entry sizes is similar for both tree species, the hollows in jarrah are significantly smaller than the hollows in marri. Most hollows are cylindrical in shape, vertically oriented and occur in dead wood in the tree crown. Relatively few hollows (14%) occur in the tree bole or at crown break. Counts of hollows made from ground level are inaccurate as estimates of the actual number of hollows in trees.