澳门海岸防护林多树种配置造林效果分析

对澳门凼仔岛海岸山地防护林造林地 (8年生 )进行调查 ,分析了林分保存率、林分生长量、各树种平均胸径、平均树高、林分土壤肥力和林分植被变化情况。认为海岸山地防护林营造多树种阔叶混交林是一种值得研究推广的林分改造模式     

番茄对钾的吸收和分配的研究

对两个番茄品种，吸钾量的研究表明，“渝抗二号”番茄对Ｋ＾＋的吸收率较高，“早丰”番茄地上部分Ｋ＾＋的分配较多。当用ＮａＮＯ３代替营养液中的ＫＮＯ３后，Ｋ＾＋的分配比例与完全培养液中的植株相似，但分配到地上部的比例较小。加Ｎａ＾＋后，“渝抗二号”植株的叶和茎中的含Ｋ＾＋量比“早丰”更多，表明不同番茄品种在不同的Ｋ＾＋和Ｎａ＾＋环境中，有着明显不同的离子吸收和分配机制。     

落桦混交林幼龄期Ⅰ级木分布规律研究

利用３６块落叶松一样树混交林标准地调查资料，研究其幼龄期林分Ⅰ级木单位面积株数与林分密度之间的关系，结果表明：Ⅰ级木的株数并非随密度的增加而直线递增，而是趋向“二阶常数”分布，且在同一年龄阶段，在较低的密度范围（２３２５～４８００株／ｈｍ２）或较高的密度范围（４８０１～６７５０株／ｈｍ２）．Ⅰ级木的株数变动幅度不太大。     

猴头菌新菌株宁猴6号的选育初报

采用多孢分离技术产生多个新组合 ,经驯化筛选获得猴头新菌株宁猴 6号 ,宁猴 6号为适合用针叶林木屑物料栽培的新菌株。生物学特性表明 :猴头菌宁猴 6号菌丝生长适温 2 5～ 2 8℃ ,子实体生长适温 15～2 0℃ ,菌丝生长期短 ,36～ 4 0d长满瓶底 ,栽培袋在常温下培养 4 3～ 5 0d菌丝满袋。室内栽培生物学效率达5 6 .0 0 % ,室外栽培生物学效率达 6 1.4 0 % ,子实体中型匀称近球型 ,柄短或无柄 ,刺长 0 .9～ 2 .2cm。宁猴 6号不仅适于阔叶木屑栽培 ,最突出的是适应针叶林木屑栽培     

人工种植沙拐枣生长发育特性及营养动态的研究

沙拐枣属蓼科沙拐枣属多年生灌木，主要分布在我国的西北地区,本文就沙拐枣人工种植后的出苗状况，生长发育特性及不同生育期营养成分变化动态等进行了研究，为我国西部大开发生态治理工程中沙拐枣的大面积推广种植提供了指导。     

江西省古树资源系统研究报告

研究对象只限于散生于江西省山下及村落的30851株古树，不涉及自然保护区、森林公园中的古树。根据古树生长特征，分析其时间分布(古树级及树龄)、空间分布(设区市分布、县域分布)，借助于动态聚类统计分析方法从不同方向进行数量分类，并对数量分类成果用判别分析进行检验。最后对各县域每km^2和每万人负荷古树数进行核算，用数据资抖说明县域保护古树的重要性，增强县域保护古树的责任感。     

灭菌肥Ⅰ型涂治苹果树腐烂病效果

试验于１９９２～１９９４年在山东和北京的６个地区，１４个苹果园进行。田间试验表明，用灭菌肥Ⅰ型５０倍液涂治苹果树腐烂病患处，平均治愈率可达９０％以上，比对照２％福美砷当年平均治愈率提高７．２２─２９．５１％，周年平均治愈率提高１８．０５％～３２．３９％，愈伤组织宽度增加３．０３％～２９．２３％。室内试验表明，灭菌肥Ⅰ型最低抑菌剂量１０００倍，抑菌面积可达２２８９．０６ｍｍ２。     

柞树害虫栎粉舟蛾的初步研究

栎粉舟蛾Femtoma ocypete(Bremer)是柞树的重要害虫之一。此虫在辽宁一年发生一代,以蛹在土中越冬。翌年7月中旬开始羽化,持续到8月中旬。羽化后即可交配产卵。7月下旬到8月下旬均有幼虫孵出。幼虫经6个龄期,于9月中、下旬入土化蛹。防治方法:8月中旬往柞树上喷洒0.025％浓度的“杀虫灵”农药,能杀死各龄幼虫,防治效果为90％左右,七天后养蚕无害。     

Growth loss of Lebanon cedar (Cedrus libani) stands as related to periodic outbreaks of the cedar shoot moth (Dichelia cedricola)

An outbreak ofDichelia cedricola (Diakonoff) (Lep.: Tortricidae), the cedar shoot moth (CSM), began in spring 1998 and lasted 3 years. This was the first monitored outbreak of the CSM in Isparta, Turkey. Tree crowns recovered to near normal condition by the middle of each growing season (in early June) during the outbreak. Tree volume and volume element increments were examined throughout the outbreak cycle from 1954 to 2001. In the past, CSM activity in stands of Lebanon cedar (Cedrus libani A. Rich.) was assessed through radial increment analyses. Cedar tree ring chronologies were analyzed for evidence of the CSM. Tree-ring chronologies from nonhost cedar (nondefoliated sample trees) were used to estimate potential growth in the host cedar (defoliated sample trees) during current and past outbreaks; all trees selected were the same subspecies and varieties. Regional outbreaks of the CSM were identified by synchronous and sustained growth periods of the trees. In 2001, increment cores were collected from 17 host and 16 nonhost dominant or codominant trees and annual radial growth indices from 1954–2001 were calculated for each of two host and two nonhost sample plots. Growth functions were defined as the cumulative sum of radial, height, and volume increment, and were graphically compared between CSM host cedar and nonhost cedar trees. Tree ring evidence suggests that a large-scale outbreak occurred in 1955 (from 1955 to 1966) and a small outbreak occurred in 1985 (1985–1990) and in 1998 (1998-continued) in the study area. The average diameter growth reductions around 1955, 1985 and 1998 were 40%, 46% and 7% of potential, respectively. It was concluded that a narrow latewood band is significant indicator of defoliation by the CSM and the outbreaks appear to be associated with dry winter and spring weather prior to the autumn and winter in which wood feeding occurred. http://www.phytoparasitica.org posting Nov. 24, 2004.