全文获取类型
收费全文 | 4805篇 |
免费 | 990篇 |
国内免费 | 1292篇 |
专业分类
测绘学 | 488篇 |
大气科学 | 812篇 |
地球物理 | 992篇 |
地质学 | 2872篇 |
海洋学 | 685篇 |
天文学 | 148篇 |
综合类 | 458篇 |
自然地理 | 632篇 |
出版年
2024年 | 50篇 |
2023年 | 150篇 |
2022年 | 337篇 |
2021年 | 356篇 |
2020年 | 288篇 |
2019年 | 296篇 |
2018年 | 332篇 |
2017年 | 287篇 |
2016年 | 314篇 |
2015年 | 289篇 |
2014年 | 297篇 |
2013年 | 283篇 |
2012年 | 232篇 |
2011年 | 272篇 |
2010年 | 273篇 |
2009年 | 240篇 |
2008年 | 225篇 |
2007年 | 212篇 |
2006年 | 151篇 |
2005年 | 165篇 |
2004年 | 158篇 |
2003年 | 182篇 |
2002年 | 310篇 |
2001年 | 239篇 |
2000年 | 210篇 |
1999年 | 202篇 |
1998年 | 121篇 |
1997年 | 88篇 |
1996年 | 82篇 |
1995年 | 78篇 |
1994年 | 75篇 |
1993年 | 59篇 |
1992年 | 60篇 |
1991年 | 29篇 |
1990年 | 31篇 |
1989年 | 18篇 |
1988年 | 18篇 |
1987年 | 13篇 |
1986年 | 13篇 |
1985年 | 12篇 |
1984年 | 9篇 |
1983年 | 2篇 |
1982年 | 8篇 |
1981年 | 6篇 |
1980年 | 3篇 |
1978年 | 1篇 |
1977年 | 1篇 |
1958年 | 4篇 |
1957年 | 1篇 |
1954年 | 5篇 |
排序方式: 共有7087条查询结果,搜索用时 0 毫秒
41.
42.
南黄海绿潮暴发与紫菜养殖的关系 总被引:2,自引:0,他引:2
采用现场调查、社会调查和卫星遥感多种手段相结合,调查了南黄海绿潮早期零星漂浮到大面积暴发的时空变化过程,分析了紫菜养殖工艺对绿潮暴发的影响,估算了南黄海不同紫菜养殖区输入海洋的绿潮藻初始生物量,并探讨了主要海域紫菜养殖面积的增长与绿潮暴发的关系。结果表明,受紫菜养殖生产工艺的影响,数以千吨的绿潮藻在短期内被刮落集中输入至海洋,为绿潮的暴发提供了最为直接和充足的绿潮藻初始生物量,其主要来源为竹根沙、蒋家沙和东沙紫菜养殖区。2005年以来,上述3个养殖区的紫菜养殖面积持续扩大,是2007年以来南黄海绿潮持续暴发的主要原因。水温是影响绿潮形成的关键环境因素,4~6月份大量被刮落入海的绿潮藻在适宜环境条件下漂浮和快速生长,并最终形成绿潮。 相似文献
43.
为了将图像处理技术应用于智能客流检测,准确及时地获取运动信息,对视频图像中运动物体的分割与跟踪技术进行研究,将图像分割与跟踪技术有机地结合在一起。采用帧间与帧内相结合的分割算法,将图像填充技术应用于图像分割,消除了背景区域的干扰以及图像处理过程中造成的失真,达到了准确获取视频流中运动物体的目的。在图像跟踪过程,引入了边缘衍生点的概念,在此基础上,提出基于部分轮廓线特征点集的多线程跟踪算法,把运动物体跟踪转变为连续帧间特征点集匹配的问题,极大地减少了运算量,解决了图像跟踪处理领域中目标物体自遮挡与不完全遮挡的难题。经客流测试证明,文中方法能够对上下车客流数量进行准确统计。 相似文献
44.
45.
46.
47.
Juan Chen Fei-Hua Wu Qiang Xiao Zhang-Hua Yang Sheng-Kai Huang Jian Wang Yu-Guang Wu Xue-Jun Dong Zhen-Ming Pei Hai-Lei Zheng 《Estuarine, Coastal and Shelf Science》2010
The diurnal variation of nitric oxide (NO) emission fluxes from a Kandelia obovata and Avicennia marina mangrove wetland were studied in the Zhangjiang River Estuary Mangrove National Nature Reserve using a dynamic chamber-based technique and a chemiluminescent analyzer. Results from field experiments show that NO emission from K. obovata and A. marina sampling sites reached maximal values of 1.07 ng N m−2 s−1 and 1.23 ng N m−2 s−1, respectively after the night tide. Meanwhile NO emission maintained at a steady lower level in daytime for both wetland sites. In laboratory experiments, NO emission from the mangrove wetland soil samples treated with simulated tides in the darkness exhibited higher values than those in the light, therefore it seems that tides and darkness could increase NO emission from mangrove wetlands, while intensive light, high temperature, and dryness in the daytime decreased NO emission. Compared with K. obovata soil samples, the diurnal average NO emission rate of the A. marina site was significantly higher, which was closely related to relatively higher diurnal average CO2 emission rate, soil available nitrogen content and soil net nitrification rate of the A. marina site. Moreover, soil samples of the A. marina site were more responsive to simulated tides and the addition of nitrogen than those of the K. obovata site. 相似文献
48.
Biodegradation and oil mixing in Silurian sandstone reservoirs of the Tarim Basin, one of the largest composite basins in China, were investigated by analyzing the molecular characteristics and stable carbon isotopic signatures of low-molecular-weight (LMW) saturated hydrocarbons and high-molecular-weight (HMW) asphaltenes. Detection of 25-norhopanes and 17-nortricyclic terpanes in most Silurian tar sands from the Tabei Uplift in the Tarim Basin suggests a much greater degree of biodegradation here than in the Tazhong Uplift. This explains the relatively more abundant tricyclic terpanes, gammacerane, pregnane and diasteranes in tar sands from the Tabei Uplift than in those from the Tazhong Uplift. Hence, care must be taken when assigning oil source correlations using biomarkers in tar sands because of the biodegradation and mixing of oils derived from multiple sources in such an old composite basin. Asphaltenes in the tar sands seem to be part of the oil charge before biodegradation, depending on the relative anti-biodegradation characteristics of asphaltenes, the similarity in carbon isotopic signatures for asphaltenes and their pyrolysates, and the consistent product distribution for flash pyrolysis and for regular steranes in asphaltene pyrolysates, regardless of whether the tar sands were charged with fresh oil. According to the relative distributions of regular steranes and the relatively abundant 1,2,3,4-tetramethylbenzene significantly enriched in 13C, the oil sources for asphaltenes in the tar sands might be related to lower Paleozoic marine source rocks formed in euxinic conditions. Nevertheless, the relatively low abundance of gammacerane and C28 regular steranes observed in asphaltene pyrolysates and residual hydrocarbons, within limited samples investigated in this work, made a direct correlation of oils originally charged into Silurian tar sands with those Cambrian source rocks, reported so far, seem not to be possible. Comparison of carbon isotopic signatures of n-alkanes in asphaltene pyrolysates with those of LMW saturated hydrocarbons is helpful in determining if the abundant n-alkanes in tar sands are derived from fresh oil charges after biodegradation. The limited carbon isotopic data for n-alkanes in LMW saturated hydrocarbons from the tar sands can be used to classify oils charged after biodegradation in the composite basin into four distinct groups. 相似文献
50.
Control and eradication of the exotic and invasive plant Spartina alterniflora within the Chongming Dongtan nature reserve, Shanghai, China, is vital for the management and conservation of the saltmarshes. A demonstration project was established using waterlogging and cutting to control this invasive species. Results from 2007 to 2008 showed that, although the managed waterlogging significantly reduced biomass and seed production of S. alterniflora at an early stage, the species subsequently showed rapid adaptation to the long-term waterlogging stress. Thus, managed waterlogging alone was insufficient for the effective eradication of S. alterniflora. However, managed waterlogging for around 3 months, combined with cutting the above-ground part of S. alterniflora at a key stage (flowering period in July), controlled and eradicated the plant successfully. Both the above-ground and below-ground parts of S. alterniflora were killed and the plants began to decompose after 3 months. Furthermore, there was no re-growth of the emergent part of S. alterniflora in the following years. However, once the impounded water was released restoring the natural hydrodynamic regime of the saltmarshes, the seeds and seedlings of S. alterniflora reinvaded the controlled site from the neighboring areas and the S. alterniflora community was re-established. Thus, after eradication of S. alterniflora, control measures should be maintained to prevent the re-establishment of S. alterniflora. The results of this demonstration project indicate a potentially useful and effective approach for the control and management of large-scale invasion by S. alterniflora on saltmarshes in the Yangtze Estuary, China. 相似文献