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171.
祁连山典型林区生态服务功能间接价值估算 总被引:2,自引:1,他引:1
采用常规和替代市场评估技术,对祁连山北坡东段哈溪林区有机质生产、水源涵养、水土保持、固定CO2和净化空气5种生态系统服务功能间接价值进行了估算,并对3种不同植被类型的生态服务功能价值进行了比较。结果表明,哈溪林区5种服务功能总价值为52061.00万元,其中森林、灌丛和草地分别为19510.34万元、25200.01万元和7350.65万元。按有林地面积推算,祁连山森林生态系统提供的服务功能间接经济价值是天祝县国民生产总值的3~5倍,森林生态系统所提供的生态服务功能价值远远超过了当地社会创造的经济价值。就水源涵养和水土保持服务功能而言,灌丛提供的总价值最大。 相似文献
172.
173.
人工鱼礁构建对海洋生态系统服务价值的影响——以深圳杨梅坑人工鱼礁区为例 总被引:6,自引:0,他引:6
基于深圳杨梅坑人工鱼礁区2008年的研究和统计数据,采用生态系统服务价值方法,系统分析了杨梅坑人工鱼礁建设对海洋生态系统的影响.结果表明:与深圳附近海域相比,杨梅坑人工鱼礁构建后旅游娱乐服务价值所占比例由87%降至42%,食品供给服务价值所占比例由7%升至27%,原材料供给、气候调节、空气质量调节、水质净化调节、有害生物和疾病的生物调节与控制、知识扩展服务价值所占比例少许提高;2008年,深圳杨梅坑人工鱼礁区单位面积服务价值为1714.7万元.km-2,远高于深圳市近海海洋生态系统的平均值和全球近海生态系统的平均值.人工鱼礁生态系统影响并改变了区域海洋生态系统服务价值结构,提高了区域生态系统服务价值,对于合理开发与利用海洋资源、修复受损的海洋生态环境和渔业资源有着重要意义.利用生态系统服务价值方法对人工鱼礁构建区进行评价,可以更好地反映人工鱼礁构建效益,能有效促进我国人工鱼礁建设的发展、提高海洋生态系统管理水平. 相似文献
174.
讨论了带一个参数的非线性四阶狄利克雷边值问题变号解的存在性.在非线性项满足一定条件时,通过利用一些新的概念如O-有界锥和O-正算子,我们得到该边值问题至少存在一个变号解. 相似文献
175.
疏勒河中游生态服务价值对土地利用变化的响应 总被引:1,自引:0,他引:1
利用ArcGIS 9.2和ERDAS 9.1软件平台和生态经济学方法,采用Costanza等生态系统服务价值计算公式,结合中国陆地生态系统服务单位面积价值,探讨了疏勒河中游1990-2010年土地利用和生态系统服务价值变化特征.结果表明:1990-2010年,疏勒河中游土地利用以未利用地、牧草地、耕地为主,三者面积占研究区总面积的98.2%,20年间土地利用整体特征并未发生重大变化;疏勒河中游主要土地利用变化发生在耕地、建设用地和牧草地,土地利用动态度分别为13.6%、8.0%和7.7%;生态系统服务价值总体呈上升趋势,从344.85亿元增加到485.11亿元,牧草地和水域对研究区总体生态系统服务价值的贡献率最大.研究区生态经济的发展已经处于低度协调水平的边缘,需要加强生态环境保护力度. 相似文献
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177.
Natural selection operates both directly, via the impact of a trait upon the individual's own fitness, and indirectly, via the impact of the trait upon the fitness of the individual's genetically related social partners. These effects are often framed in terms of Hamilton's rule, rb - c > 0, which provides the central result of social-evolution theory. However, a number of studies have questioned the generality of Hamilton's rule, suggesting that it requires restrictive assumptions. Here, we use Fisher's genetical paradigm to demonstrate the generality of Hamilton's rule and to clarify links between different studies. We show that confusion has arisen owing to researchers misidentifying model parameters with the b and c terms in Hamilton's rule, and misidentifying measures of genotypic similarity or genealogical relationship with the coefficient of genetic relatedness, r. More generally, we emphasize the need to distinguish between general kin-selection theory that forms the foundations of social evolution, and streamlined kin-selection methodology that is used to solve specific problems. 相似文献
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179.
Rhizosphere priming effect increases the temperature sensitivity of soil organic matter decomposition 总被引:3,自引:0,他引:3
The temperature sensitivity of soil organic matter (SOM) decomposition has been a crucial topic in global change research, yet remains highly uncertain. One of the contributing factors to this uncertainty is the lack of understanding about the role of rhizosphere priming effect (RPE) in shaping the temperature sensitivity. Using a novel continuous 13C‐labeling method, we investigated the temperature sensitivity of RPE and its impact on the temperature sensitivity of SOM decomposition. We observed an overall positive RPE. The SOM decomposition rates in the planted treatments increased 17–163% above the unplanted treatments in three growth chamber experiments including two plant species, two growth stages, and two warming methods. More importantly, warming by 5 °C increased RPE up to threefold, hence, the overall temperature sensitivity of SOM decomposition was consistently enhanced (Q10 values increased 0.3–0.9) by the presence of active rhizosphere. In addition, the proportional contribution of SOM decomposition to total soil respiration was increased by soil warming, implying a higher temperature sensitivity of SOM decomposition than that of autotrophic respiration. Our results, for the first time, clearly demonstrated that root–soil interactions play a crucial role in shaping the temperature sensitivity of SOM decomposition. Caution is required for interpretation of any previously determined temperature sensitivity of SOM decomposition that omitted rhizosphere effects using either soil incubation or field root‐exclusion. More attention should be paid to RPE in future experimental and modeling studies of SOM decomposition. 相似文献
180.
The evaluation of ecological field data can be done by an increasing number of quantitative methods. The application of these methods often is often blind against two kinds of problems: (i) the data often do not meet the requirements of a method, e.g., as an ultra-metric structure of the data in the case of hierarchical cluster analysis. In such cases, the result will be misleading because the presentation of results is ultra-metric independent on the structure of the data. (ii) Most of the animals are able to move actively or may drift passively by wind, etc. Therefore, species occurring by accident like vagrants have to be eliminated from the assemblage of animals at a particular site before a quantitative method is applied. In addition, the result of a quantitative analysis has to be checked for its ecological plausibility. This is a qualitative step, which can only be done by taking into account the known data on biology and ecology of the species.Some pitfalls of an exclusive application of quantitative methods will be demonstrated in this paper using a data set of salt marsh Carabidae. 相似文献