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151.
小麦T型细胞质雄性不育系与相应保持系线粒体DNA的RAPD分析   总被引:13,自引:1,他引:13  
利用RAPD技术对小麦T型细胞质雄性不育系75-3369A和相应保持系75-336 9B 的线粒体DNA(mtDNA)进行了81个单引物和14组双引物的多态性研究。结果有73个单引物和全部的双引物有扩增结果,表现出多态性的有10个单引物和一组双引物。 Abstract:Using 81 single-primers and 14 double-primers,T-type CMS(cytoplasmic male sterile)line 75-3369 A and is maintainer 75-3369B were studied by means of RAPD.73 single-primers and all double-primers gave amplified products in the experiment,among them 10 single-primers and one double-primer presented polymorphism.  相似文献   
152.
本工作以钾离子透入引起大鼠甩尾反应作为痛反应指标,观察纳洛酮(NX)和抗阿片肽血清对大鼠中脑导水管周围灰质(PAG)内微量注射神经降压素(NT)增强电针镇痛作用的影响。结果显示:(1)PAG内微量注射NT后,大鼠电针镇痛效应明显提高;(2)PAG内注射大剂量NX,可以显著减弱NT增强电针镇痛效应;(3)PAG内微量注射抗甲脑啡肽血清和抗β内啡肽血清后,NT增强电针镇痛的作用明显降低;而PAG内微量注射抗强啡肽A113血清,对于NT增强电针镇痛的作用并无明显影响。提示:PAG内NT在针刺镇痛过程中发挥重要作用,NT增强电针镇痛的作用与甲脑啡肽和β内啡肽有较密切的关系。  相似文献   
153.
县域生态资产核算研究——以云南省屏边县为例   总被引:4,自引:0,他引:4  
生态资产(Eco-Assets)是生产与提供生态产品和服务的自然资源。以国家重点生态功能区县——屏边苗族自治县为例,研究了县域生态资产核算的指标和方法,以生态资产综合指数、负债表和损益表,开展屏边县生态资产实物量核算,以期能够切实反映出生态系统实物量的变化和生态补偿成效,结合生态补偿分析屏边县生态资产变化的原因和趋势,给生态补偿政策和离任干部审计提供技术支撑。结果表明:(1)屏边县生态资产核算可以分为森林、灌丛、草地、湿地自然生态系统和农田、城镇和荒漠人工生态系统实物量的核算。(2)2015年,屏边县生态资产指数为1.09,森林和灌丛占据主要位置,二者总和占当年生态资产的95.48%。15年来,屏边县生态资产综合指数降低了16.48%,其中森林和草地降低明显,分别减少了20.10%和6.67%,湿地指数增长了57.11%。(3)2000年以来,生态保护工程和城镇扩张是生态资产变化的主要原因,生态补偿投入持续增加为生态保护工程顺利建设实施提供了保障。本研究表明,现有的土地利用数据和生态环境监测数据基本可以支撑县域生态资产的核算,同时县域生态资产的变化能够体现出生态保护工程实行成效,并为实行领导干部自然资源资产离任审计提供重要依据,为生态补偿政策提供科学支撑。  相似文献   
154.
作为功能基因组学中重要的组成部分,基因表达谱在生物学、医学和药物研发等多个领域发挥着重要作用.特别是随着精准医疗概念的提出,整合多组学数据用于个性化医疗是未来的发展趋势.本文从基因表达谱的基本概念出发,重点介绍面向药物发现的基因表达谱分析方法,即基于关联图谱的方法、基于基因调控网络的方法和基于多组学数据整合的方法.系统整理了各种方法的研究进展,特别是在抗癌药物研发领域的最新进展,为利用基因表达谱数据进行药物研发提供方法借鉴.  相似文献   
155.
156.
Estimating total breeding populations (I) for species that exhibit biennial breeding is generally done from counts of individuals that breed in each year (N), but can be complicated by the fact that the proportion of individuals breeding varies from year to year. Partly, this reflects the proportion of individuals that re‐breed in successive years (re‐breeding rate, p), which is largely, although not exclusively, governed by reproductive failure. Here we show that variation in counts of breeding individuals not only reflects changes in total breeding population but can be sensitive to and powerfully driven by variation in p. A simulation of annual field counts of a bird exhibiting biennial breeding was constructed to explore the effect of re‐breeding attempts on estimations of the total breeding population. The model was used to simulate the consequences of adult mortality and different annual patterns of nesting failures on total breeding population estimates, and to explore the consequences of variation in p on N, when total breeding population remains constant. N is shown to be very sensitive to variations in p, so that even short‐term fluctuations in p can cause changes in N that oscillate for many years ahead. We compare our modelled results with real data for Grey‐headed Albatrosses Thalassarche chrysostoma and demonstrate that, when I is held constant in the model, actual counts may be simulated by variations in p only. Normally, I is unknown and is extrapolated from N on the assumption that N mirrors changes in the size of the total population. Consequently, applying average values of p can result in misleading estimates of total breeding population. We recommend that annual counts of breeding individuals are supplemented with annual estimates of p. Field protocols that aim to estimate annual breeding population size from counts of breeding individuals should be complemented by independent measures of rates of re‐breeding and nest failure.  相似文献   
157.
[17-13C,3H]Gibberellin A4 (GA4) was injected into the shoots of tall (W23/L317), dwarf-1 (d1), and dwarf-5 (d5) Zea mays L. (maize); tall (cv Nipponbare), dwarf-x (dx), and dwarf-y (dy) Oryza sativa L. (rice); and tall (ecotype Landsberg erecta), ga4, and ga5 Arabidopsis thaliana (L.) Heynh. [13C]GA4 and its metabolites were identified from the shoots by full-scan gas chromatography-mass spectrometry and Kovats retention indices. GA4 was metabolized to GA1 in all nine genotypes. GA4 was also metabolized in some of the genotypes to 3-epi-GA1, GA2, 2[beta]-OH-GA2, 3-epi-GA2, endo-GA4, 16[alpha], 17-H2-16, 17-(OH)2-GA4, GA34, endo-GA34, GA58, 15-epi-GA63, GA71, and 16-epi-GA82. No evidence was found for the metabolism of GA4 to GA7 or of GA4 to GA3. The bioactivities of GA4 and GA1 were determined using the six dwarf mutants for assay. GA4 and GA1 had similar activities for the maize and rice mutants. For the Arabidopsis mutants, GA4 was more active than GA1 at low dosages; GA4 was less active than GA1 at higher dosages.  相似文献   
158.
A mass balance has been performed on trace metals concentrations and hydrology observed between 1994 and 1996 at the Sacramento Demonstration Constructed Wetlands using a first-order areal plug flow model. Water losses to infiltration and evapotranspiration from a typical cell are estimated to average 35 and 7% of influent flow, respectively. The wetlands effluent metals concentrations consistently meet proposed discharge criteria. Annual total mass loadings for all trace metals average 14.0 kg ha−1 yr−1, 88% of which consists of zinc, copper, and nickel. Effluent metals leaving the wetland average 3.1 kg ha−1 yr−1, 79% of which consists of the same three metals. Annual vegetation harvest events do not appear to account for more than 5% of annual trace metals mass removal, although harvest does appear to represent a significant loss pathway for some metals like mercury, lead, nickel, and chromium. Metals mass removals resulting from first-order removal interactions within the wetland range from 27 to 81%, with the exception of arsenic and nickel which display poor mass removals in part due to their high dissolved concentrations. An average of 7.6 kg ha−1 yr−1, or 54% of influent metals loadings, is sequestered within the internal wetland compartments.  相似文献   
159.
The stepwise metabolism of gibberellin A12-aldehyde (GA12-aldehyde) to GA20 is demonstrated from seedling shoots of maize (Zea mays L.). The labeled substrates [13C,3H]GA12-aldehyde, [13C,3H]GA12, [14C4]GA53, [14C4/2H2]GA44, and [14C4/2H2]GA19 were fed individually to dwarf-5 vegetative shoots. Both [13C,3H]GA12-aldehyde and [13C,3H]GA12 were also added individually to normal shoots. The labeled metabolites were identified by full-scan gas chromatography-mass spectrometry and Kovats retention indices. GA12-aldehyde was metabolized to GA53-aldehyde, GA12, GA53, GA44, and GA19; GA12 was metabolized to 2[beta]-hydroxy-GA12, GA53, 2[beta]-hydroxyGA53, GA44, 2[beta]-hydroxyGA44, and GA19; GA53 was metabolized to GA44, GA19, GA20, and GA1; GA44 was metabolized to GA19; and GA19 was metabolized to GA20. These results, together with previously published data from this laboratory, document the most completely defined gibberellin pathway for the vegetative tissues of higher plants.  相似文献   
160.
Young shoots of normal maize (Zea mays L.) were used to determine both the stepwise metabolism of ent-kaurene to gibberellin A12-aldehyde and the endogenous presence of the members in this series. Each of the five steps in the sequence was established by feeds of 17-13C, 3H-labeled kauranoids to cubes from the cortex of elongating internodes, to homogenates from the cortex of elongating internodes, and/or to homogenates from dark-grown seedlings. The 13C-metabolites were identified by Kovats retention indices (KRI) and full-scan capillary gas chromatography-mass spectrometry (GC-MS). Five substrates and the final product in this sequence were shown to be native by the isotopic dilution of 17-13C, 3H-labeled substrates added as internal standards to extracts obtained from elongating internodes. Evidence for the isotopic dilution was obtained by KRI and full-scan capillary GC-MS. Thus, we document the presence in young maize shoots of the metabolic steps, ent-kaurene → ent-kaurenol → ent-kaurenal → ent-kaurenoic acid → ent-7 α-hydroxykaurenoic acid → gibberellin A12-aldehyde.  相似文献   
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