全文获取类型
收费全文 | 429篇 |
免费 | 107篇 |
国内免费 | 105篇 |
专业分类
测绘学 | 66篇 |
大气科学 | 63篇 |
地球物理 | 142篇 |
地质学 | 225篇 |
海洋学 | 44篇 |
天文学 | 4篇 |
综合类 | 61篇 |
自然地理 | 36篇 |
出版年
2024年 | 4篇 |
2023年 | 12篇 |
2022年 | 35篇 |
2021年 | 39篇 |
2020年 | 31篇 |
2019年 | 33篇 |
2018年 | 27篇 |
2017年 | 26篇 |
2016年 | 26篇 |
2015年 | 30篇 |
2014年 | 25篇 |
2013年 | 27篇 |
2012年 | 31篇 |
2011年 | 43篇 |
2010年 | 26篇 |
2009年 | 19篇 |
2008年 | 42篇 |
2007年 | 37篇 |
2006年 | 21篇 |
2005年 | 13篇 |
2004年 | 7篇 |
2003年 | 5篇 |
2002年 | 6篇 |
2001年 | 6篇 |
2000年 | 3篇 |
1999年 | 16篇 |
1998年 | 9篇 |
1997年 | 9篇 |
1996年 | 8篇 |
1994年 | 8篇 |
1993年 | 6篇 |
1992年 | 2篇 |
1991年 | 3篇 |
1989年 | 1篇 |
1988年 | 2篇 |
1986年 | 2篇 |
1985年 | 1篇 |
排序方式: 共有641条查询结果,搜索用时 46 毫秒
1.
为了满足大行星卫星的高精度CCD位置观测与运动理论研究工作的需要 ,采用天王星 5颗主要卫星摄动理论模型 (Gust86 )作为核心 ,设计了一个天王星视位置可视化软件。该软件具有卫星证认 ,最佳观测时段选取 ,精确模拟卫星视运动和实时引导CCD精密定位观测等功能。 相似文献
2.
3.
本文通过对1982年磁扰期间琼中、北京两站地磁X分量变化的分析,证实了磁层-电离层电动耦合对中纬电离层电流的影响.分析发现:磁静、磁扰条件下的平均日变化中,两站X分量变化在白天有反向的趋势.这表明它们分处于与动力效应对应的电离层发电机电流圈中心之南北两侧.在磁暴主相期间,X分量变化形态与之明显不同,两站地磁南北分量有同向变化,且变幅相近,甚至有时北京站△X更大.对环电流能量增长指数R小于-25nT/h的21次事件所作的时序叠加分析(以R最负时为零时)进一步证明,这种同向变化是普遍存在的.两站零时之△X大小相近,相关系数高达0.98.该同向变化与R指数突然变负密切相关. 以上对比表明,与发电机电流造成两站X分量反向变化不同,同向变化是磁层源高纬扰动电流向中低纬直接穿透的结果.本文对动力和电动耦合两种过程的不同进行了初步讨论. 相似文献
4.
5.
滇西兰坪盆地北部发育了一类受逆冲推覆构造控制的浅成热液Cu—Ag—Pb-Zn矿化,形成了白秧坪、富隆厂、吴底厂、麻栗坪及金满、科登涧等大-中型矿床和矿点,并存在矿化分带。文章利用这些矿化脉体的流体包裹体和热液方解石的碳氧同位素组成资料,研究成矿流体与矿化分带的关系。结果表明,成矿流体主要属于NaCl-H2O成分体系,盐度ω(NaCleq)为2%~11%,形成温度为170~300℃,形成于1.8~3.8km深度内,这些相似性说明这类矿化的发生具有相似的流体性质和沉淀机制。热液方解石在δ^13C-δ^18O图解中呈近水平线展布的型式,指示流体源自地壳浅部的地下水系统,与海相灰岩等围岩作用形成了溶解碳以[HCO3^]-为主的成矿流体,流体与岩石的相互作用可能是成矿流体沉淀的主要机理。从西到东,流体包裹体的盐度-温度由高到低变化与矿化分带和逆冲推覆构造的根带→中带→锋带相配套,显示重力驱动流动可能是主要的流体流动机制。成矿流体在不同构造部位流动的通畅及流体.岩石系统的封闭-开放程度等流体流动性质与矿化发生的强度和规模有关,兰坪北部逆冲推覆构造中带的流体通畅地流动及沉淀时处于相对开放状态,有利于该区形成较大规模的浅成热液多金属矿化。 相似文献
6.
7.
煤田地震勘探一直探寻着对小断层的自动检测方法,因受各种因素的影响,至今尚无良策。本文介绍了多元地震参数的模式识别方法,并通过模型及实测资料成功地检测到10m以下小断层。 相似文献
8.
华南西部晚二叠世碳同位素地层学研究 总被引:1,自引:1,他引:1
对黔桂地区7条晚二叠世碳酸盐岩型煤系剖面进行了碳酸盐岩碳氧同位素测定,发现晚二叠世吴家坪阶与长兴阶碳酸盐岩的δ13C值有明显差异,前者δ13C多大于3.0‰,后者多小于3.0‰,进一步对晚二叠世δ13C的变化原因的分析表明,δ13C的变化可能与晚古生代末期聚煤作用的减弱密切相关,后者造成自然界碳库中的12C的富集,从而使得海水以及在其中沉淀出的碳酸盐岩中的δ13C值降低。此外,植物光合作用从大气中吸收CO2的量也随陆地植被减少而减少,结果造成大气中的CO2的大量富集,从而进一步产生温室效应,制约生物界的发展。联系到这一阶段生物界的衰亡灭绝,可以认为温室效应是晚二叠世生物逐渐衰亡及晚二叠世末群体灭绝的主要原因之一。 相似文献
9.
Jianwei Wang 《Earth and Planetary Science Letters》2004,222(2):517-527
Molecular dynamics (MD) modeling of the 10-Å phase, Mg3Si4O10(OH)2·xH2O, with x=2/3, 1.0 and 2.0 shows complex structural changes with pressure, temperature and water content and provides new insight into the structures and stabilization of these phases under subduction zone conditions. The structure(s) of this phase and its role as a reservoir of water in the mantle have been controversial, and these calculations provide specific predictions that can be tested by in situ diffraction studies. At ambient conditions, the computed structures of talc (x=0) and the 10-Å phases with x=2/3 and 1.0 are stable over the 350-ps period of the MD simulations. Under these conditions, the 10-Å phases show phlogopite-like layer stacking in good agreement with previously published structures based on powder X-ray diffraction data for samples quenched from high-pressure and high-temperature experiments. The calculations show that the 10-Å phase with x=2.0 is unstable at ambient conditions. The computed structures at P=5.5 GPa and T=750 K, well within the known stability field of the 10-Å phase, change significantly with water content, reflecting changing H-bonding configurations. For x=2/3, the layer stacking is talc-like, and for x=1.0, it is phlogopite-like. The calculations show that transformation between these two stackings occurs readily, and that the talc-like stacking for the x=2/3 composition is unlikely to be quenchable to ambient conditions. For x=2.0, the layer stacking at P=5.5 GPa and T=750 K is different than any previously proposed structure for a 10-Å phase. In this structure, the neighboring basal oxygens of adjacent magnesium silicate layers are displaced by b/3 (about 3 Å) resulting in the Si atoms of one siloxane sheet being located above the center of the six-member ring across the interlayer. The water molecules are located 1.2 Å above the center of all six-member rings and accept H-bonds from the OH groups located below the rings. The b/3-displaced structure does not readily transform to either the talc-like or phlogopite-like structure, because neither of these stackings can accommodate two water molecules per formula unit. There is likely to be a compositional discontinuity and phase transition between the b/3-displaced phase and the phase with phlogopite-like stacking. The simulations reported here are the first to use the recently developed CLAYFF force field to calculate mineral structures at elevated pressures and temperatures. 相似文献
10.
SHA Liqing ZHENG Zheng TANG Jianwei Wang Yinghong ZHANG Yiping CAO Min WANG Rui Liu Guangren WANG Yuesi SUN Yang 《中国科学D辑(英文版)》2005,48(Z1)
With the static opaque chamber and gas chromatography technique, from January 2003 to January 2004 soil respiration was investigated in a tropical seasonal rain forest in Xishuangbanna, SW China. In this study three treatments were applied, each with three replicates: A (bare soil), B (soil+litter), and C (soil+litter+seedling). The results showed that soil respiration varied seasonally, low from December 2003 to February 2004, and high from June to July 2004. The annual average values of CO2 efflux from soil respiration differed among the treatments at 1% level, with the rank of C (14642 mgCO2· m-2. h-1)>B (12807 mgCO2· m-2. h-1)>A (9532 mgCO2· m-2. h-1). Diurnal variation in soil respiration was not apparent due to little diurnal temperate change in Xishuangbanna. There was a parabola relationship between soil respiration and soil moisture at 1% level. Soil respiration rates were higher when soil moisture ranged from 35% to 45%. There was an exponential relationship between soil respiration and soil temperature (at a depth of 5cm in mineral soil) at 1% level. The calculated Q1o values in this study,ranging from 2.03 to 2.36, were very near to those of tropical soil reported. The CO2 efflux in 2003was 5.34 kgCO2· m-2. a-1 from soil plus litter plus seedling, of them 3.48 kgCO2· m-2. a-1 from soil (accounting for 62.5%), 1.19 kgCO2· m-2. a-1 from litter (22.3%) and 0.67 kgCO2·m-2. a-1 from seedling (12.5%). 相似文献