辽宁省危险性林业有害生物风险分析指标体系的评价

本文采用专家依据《辽宁省林业危险性有害生物风险分析指标体系》对8种林业有害生物进行综合分析的数据作为研究对象,比较了各项因子对指标体系的影响度。针对其中有害生物风险分析指标体系的评价结果表明,指标层中设计的指标是相关的,但是仍有进一步完善的空间,并且"定殖和扩散的可能性"与"受害寄主经济重要性"两项指标的影响度最大;针对其中有害植物风险分析指标体系的评价结果表明,专家对影响有害植物风险程度因素的看法基本一致,并且"潜在经济危害性"与"辽宁地区分布情况"这两项指标对有害植物风险程度影响尤为明显。     

工业人工林发展研究——解决我国木材供需矛盾途径分析之一

从我国工业人工林的发展背景出发 ,论述我国工业人工林发展的意义 ;重点分析我国南方工业人工林经营的技术经济效益、发展中存在的问题以及工业人工林在我国的发展前景 ;找出影响我国工业人工林发展的关键因素 ,在此基础上提出进行制度创新和技术创新为我国工业人工林的发展提供必要的条件和相应技术支持的对策建议     

稀土元素对林木的生理效应

在适宜条件下,稀土对林木许多生理功能都有积极作用。稀土在促进林木生长发育,增强营养水平,提高抗性等方面效果显著。稀土可能主要通过调节有关酶和内源激素水平及活性而发挥作用,其作用机理还有待于进一步研究。     

森林可持续发展的动态优化模型

运用动态规划方法讨论森林可持续发展问题，建立了森林自然发展模型和森林可持续发展的优化开发模型，给出了相应的迭代公式，并选用青冈－夏蜡梅群落进行模拟计算。结果表明经过一段时间的自然发展，森林群落可达到稳定态，夏蜡梅群落必将过渡到青冈－夏蜡梅稳定群落。其后，各阶段各树种的数量有微小变化，但总体稳定，且算法快速收敛于稳定点。图3表2参4。     

旱泉沟流域次生林演替过程中种群格局动态

对旱泉沟流域的植被种类组成、物种多样性和物种重要值进行调查分析,采用TWINSPAN对旱泉沟流域次生植物群落进行数量分类,从植物群系组成、植物群落之间的生态关系方面,研究旱泉沟流域封山禁牧区植被群落的分布格局,初步探讨乔木树种的演替趋势。研究结果表明：1）采用TWINSPAN数量分类方法,将植被划分为7个群落类型;2）从群落Ⅰ到群落Ⅶ, 乔木、灌木、草本的Simpson优势度指数基本持平,Shannon Wiener多样性指数为乔木<灌木<草本,Pielou均匀度指数为乔木>草本>灌木,物种丰富度逐渐升高。群落的物种组成和空间结构逐渐复杂化,并趋于稳定;3）次生林的演替序列为山杨树Populus davidiana→桦树Betula platyphylla→青海云杉Pica crassifolia,其自然演替顶级为青海云杉。     

天山北坡中部林区天山云杉林小气候观测

从天山云杉林（ＰｉｃｅａｓｈｒｅｎｋｉａｎａＶａｒ．ｔｉａｎｓｃｈａｎｉｃａ）小气候观测结果了解到，森林小气候随林分的不同郁闭度、林内不同高度及林地不同深度，空气温度、空气相对湿度、太阳辐射强度，光照强度以及土壤温度等都将发生规律性的变化。     

浙江省平原农田林网化的研究

根据浙江省平原地区的特点,依照农作物对农田林网控制的要求,提出了平原农田林网化的规划设计原则、要求和浙江省的分区规划方案。     

安顺市环城林带绿化设计方案初步分析

阐述了安顺市环城林带绿化建设工程的绿化设计方案,对设计方案中的立地类型划分、树种选择、造林类型及混交设计、造林密度和配置方式等进行了初步分析,并对后期管理提出建议。     

Sprouting characteristics of a subtropical evergreen broad-leaved forest following clear-cutting in Okinawa,Japan

This study explores the sprouting characteristics of an evergreen broad-leaved forest after clear-cutting based on a survey of 1,893 stumps of 62 tree species in Okinawa, Japan. The sprouting capabilities of the stumps varied among tree species. The stumps of 60 species could produce sprouts, while those of the other two species could not. In 10 of the sprouting species, the mean sprout-stem number was higher than 4.0 stems per stump; nine sprouting species showed low sprouting capabilities. Additionally, Castanopsis sieboldii and Schima wallichii, the dominant species, exhibited high sprouting capabilities. Further, the sprouting capabilities varied with stump diameter at breast height (DBH). Stumps with a larger DBH tended to have a higher mean number of sprout stems per stump, higher DBH, and higher tree height than the smaller stumps. The forest stands regenerated by sprouting might recover into a tree community similar to that before clear-cutting.     

Occurrence and berry production of Rubus chamaemorus L., Vaccinium oxycoccus L. & Vaccinium microcarpum Turcz. and Vaccinium vitis‐idaea L. on Swedish peatlands

During three consecutive years, 1978–1980, cloudberries (Rubus chamaemorus L.), cranberries (Vaccinium oxycoccus L. & Vaccinium microcarpum Turcz.) and lingonberries Vaccinium vitis‐idaea L.) growing wild in Swedish forests and mires were inventoried in the annual National Forest Survey. Both the coverage and fertility of these were estimated. Observations from 42 000 test sites (314 m² each) were processed according to geographical region, composition of tree and field layer, altitude and occurrence of draining ditches. Cloudberries cover 425 000 hectares or 1.5 % of the total investigated area (28.6 million hectares). The corresponding values for cranberries and lingonberries are 136000 hectares (0.5 %) and 1362000 ha (4.8%) respectively. Open mires have a greater degree of coverage by cloudberry and cranberry than wet forests on peat. The reverse situation is true for lingonberry. The total berry yield on peatland was estimated to 116.6 million kg (freshweight), distributed as 75.7 million kg cloudberries, 20.8 million kg cranberries and 20.1 million kg lingonberries. The corresponding production of lingonberries on mineral soils was 188.8 million kg. Both in wet forests and on mires, drained areas show lower berry production for the three species, with one exception. Lingonberries yielded better on drained mires. Productive stands of cloudberries and cranberries ought not to be drained for economic reasons.