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11.
建立了湖北省分地区水灾损失灾度等级的划分标准。基于模糊模式识别理论,按最大隶属原则和择近原则对灾度等级进行了模糊综合评判。 相似文献
12.
绵阳官司河流域水土流失综合报告 总被引:1,自引:0,他引:1
报告简述域地质地貌水文气象土壤,植被等地理因素的概况及其与土壤侵蚀的关系,指出本流域由于长防林的建立,发挥了保持水土作用,水土流失不严重,属轻度-中度侵蚀,最大侵蚀模数小于7400[t/(km^2.年],全区平均侵蚀模数1754.42[t/km^2.年];确定了水土流失类型,即片蚀,沟蚀,母质侵蚀三大类;分析了水土流失的原因:以泥岩和灰白砂岩,第四纪冰碛物堆积土侵蚀最高测定不同精植被类型的土壤质地 相似文献
13.
夏大豆亩产262.1kg生理指标研究 总被引:4,自引:1,他引:3
研究了夏大豆中油-89D亩产262.1kg各项生理指标:叶面积系数,开花期、结荚期、鼓粒期分别为3.98、5.80、4.91;总光合势18.2万m^2·日,平均净光合生产率4.81g/m^2·日,氮磷总积累量分别为22.28kg和3.13kg,每生产100kg籽粒需吸收氮8.50kg,磷1.19kg,总干物质积累876.47kg,粒茎比0.51,经济系数0.30。 相似文献
14.
本文从分析同步发电机原动系统基本数学模型入手,提出了一种实现同步发电机原动系统仿真的专用可控硅直流调速系统及其实用装置。该控制系统采用有差调节的模拟调速器,水汽管道特性模拟、自平衡特性模拟和集成块模拟触发器,以及过流与超速保护,并可实现有差-无差调节的转换。 相似文献
15.
我国小型渔船(船长20~35米)捕鱼作业信号灯至今未能达到《1972年国际海上避碰规则(1989年修订本)》的要求。本文根据光学原理,对号灯间距分辨率进行了多次测试和研究,并根据我国渔船客观实际提出了小型渔船号灯设置最佳配置方案。 相似文献
16.
应激性急性肾上腺皮质功能不全症的病理机制十分复杂,目前人医的各类文献中大都以“垂体—肾上腺轴”功能不全、功能衰竭、或发生广泛性出血坏死性病演作解释。本病在奶牛分娩难产过程中并不少见,病牛的症状表现以心衰和失钠性低血症为主征。但在兽医临床上由于认识不足,曾有不少中外学者将奶牛产后卧地不起的各类疾病,含糊地统称为“母牛睡倒爬不起来综合征”;更由于救治不当,病牛常以淘汰或死亡告终。本文通过对一具体典型病例辨析,着重讨论了本病的基本病理反应和确立诊断依据,强调对本病救护施治时应遵循的基本原则,供同道们在分析和解决这一实际问题时参考。 相似文献
17.
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. 相似文献
18.
Z. Ngoko K.F. Cardwell W.F.O. Marasas M.J. Wingfield R. Ndemah F. Schulthess 《European journal of plant pathology / European Foundation for Plant Pathology》2002,108(9):893-902
The aim was to identify biological and physical factors responsible for reducing maize yield in Cameroon. Two surveys were conducted in 137 fields in two agroecological zones in 1995–1997. In the Humid Forest (HF), Bipolaris maydis, Stenocarpella macrospora, Puccinia polysora, Rhizoctonia solani and soil fertility were factors that reduced maize production in 1995 and 1996. In the Western Highlands (WHL), Cercospora zeae-maydis, and the interaction between soil fertility and maize variety were the most important constraints to maize production in 1996. In 1997, C. zeae-maydis, S. macrospora, physiological spot and stem borer damage (Busseola fusca) were negatively related to ear weight. The combination of these biological factors (diseases and insects), and the physical parameter of soil fertility were responsible for reducing maize yield in these selected benchmarks of Cameroon. Maximum potential yield reductions were estimated at 68% due to B. maydis and 46% due to S. macrospora, respectively, in the HF in 1995. In 1996, maximum potential yield reductions in the HF were estimated at 34%, 41% and 30% due to S. macrospora, P. polysora and R. solani, respectively. In the WHL, C. zeae-maydis had the potential to cause a yield reduction of 79% in 1996. In the WHL in 1997, the interaction between C. zeae-maydis and B. fusca, stem diseases and the physiological spot caused potential reductions of 52%, 34% and 39%, respectively. 相似文献
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