全文获取类型
收费全文 | 2384篇 |
免费 | 266篇 |
国内免费 | 224篇 |
专业分类
化学 | 533篇 |
晶体学 | 4篇 |
力学 | 202篇 |
综合类 | 47篇 |
数学 | 1359篇 |
物理学 | 729篇 |
出版年
2024年 | 6篇 |
2023年 | 15篇 |
2022年 | 95篇 |
2021年 | 112篇 |
2020年 | 108篇 |
2019年 | 75篇 |
2018年 | 70篇 |
2017年 | 81篇 |
2016年 | 60篇 |
2015年 | 75篇 |
2014年 | 113篇 |
2013年 | 167篇 |
2012年 | 124篇 |
2011年 | 159篇 |
2010年 | 112篇 |
2009年 | 177篇 |
2008年 | 153篇 |
2007年 | 135篇 |
2006年 | 130篇 |
2005年 | 116篇 |
2004年 | 111篇 |
2003年 | 105篇 |
2002年 | 75篇 |
2001年 | 59篇 |
2000年 | 62篇 |
1999年 | 61篇 |
1998年 | 68篇 |
1997年 | 58篇 |
1996年 | 43篇 |
1995年 | 30篇 |
1994年 | 28篇 |
1993年 | 14篇 |
1992年 | 16篇 |
1991年 | 11篇 |
1990年 | 10篇 |
1989年 | 6篇 |
1988年 | 6篇 |
1987年 | 4篇 |
1986年 | 2篇 |
1985年 | 3篇 |
1984年 | 4篇 |
1983年 | 3篇 |
1982年 | 1篇 |
1981年 | 4篇 |
1979年 | 2篇 |
1977年 | 1篇 |
1974年 | 1篇 |
1973年 | 2篇 |
1957年 | 1篇 |
排序方式: 共有2874条查询结果,搜索用时 927 毫秒
961.
962.
任意循环的卡诺循环分解 总被引:3,自引:0,他引:3
指出任意循环的两种卡诺循环分解的极限都趋于原来的循环,一些献中关于其中一种分解不趋于原循环的证明是欠妥的。 相似文献
963.
一类Holling功能性反应模型极限环的唯一性 总被引:10,自引:0,他引:10
考虑捕食者无密度制约,食饵具有非线性密度制约的第三类Holling功能性反应捕食者-食饵系统.对该系统给出了完整的定性分析,证明了该系统至多有一个极限环,存在极限环的充要条件是正平衡点不稳定. 相似文献
964.
Thomas F. Lytle Charles S. Manning William W. Walker Julia S. Lytle David S. Page 《应用有机金属化学》2003,17(9):653-661
Dibutyltin (DBT) is used in the plastics polymerization process as a catalyst in polyvinyl chloride (PVC) products and is the primary degradation product of tributyltin (TBT), an antifoulant in marine paint. DBT and other organotin compounds make their way into the environment through antifoulants, PVC processing plants, and PVC products maintained in water and water‐handling systems. A flow‐through saltwater life‐cycle toxicity test was conducted to determine the chronic effect of DBT to the sheepshead minnow (Cyprinodon variegatus Lacepede), an estuarine species. Embryos were monitored through hatch, maturation, growth, and reproduction in DBT concentrations of 158, 286, 453, 887, and 1510 µg l?1. Progeny were monitored for survival as embryos and fry/juveniles, and growth for 30 days post‐isolation. Mean length of parental generation fish was significantly reduced on day 30 at DBT concentrations ≥887 µg l?1, setting the lowest observable effect concentration (LOEC) at 887 µg l?1 and the no observable effect concentration (NOEC) at 453 µg l?1. Fecundity, as egg viability, was significantly reduced at the LOEC. Survival of parental and progeny generation embryos and mean length, wet weight and dry weight of progeny generation juveniles were not significantly affected at concentrations ≤LOEC. TBT, a toxic impurity in DBT reversibly produced in DBT by the process of comproportionation, was also monitored throughout this study. Comparing measured levels of TBT in this study with levels exerting toxic effects in an earlier TBT life‐cycle study with C. variegatus suggests biological responses in this study were likely due to the TBT impurity and not to DBT alone. Results indicate that TBT impurity as low as 0.1% may have a significant influence on the perceived toxicity of DBT and that spontaneous production of TBT in DBT may be the major source of biological toxicity of DBT. Copyright © 2003 John Wiley & Sons, Ltd. 相似文献
965.
As the limit of time and budget etc, the control system of HL-2A just could be operated in programmed discharge when HL-2A was checked and accepted in 2002. Recent years, many subsystem of HL-2A have been improved in functions and performances. And the demand for experiment of HL-2A is becoming more and more higher in plasma discharge parameters. So it's necessary to develop a plasma feedback control system ( FBCS ) which has enough functions and good stability and reliability to satisfy the demand of experiment on HL-2A. 相似文献
966.
967.
We present an extension of the arrival theorem for the output process from a node in closed Markovian networks which we use
to obtain simple representations and explicit expressions for the throughput, the distribution of the cycle time, and the
joint distribution of interoutput times from a node in single class closed networks with exponential servers. Our approach
uses tools from Palm calculus to obtain a recursion on the number of customers in the system. The analysis relies on a non-overtake
condition and thus many of the results obtained here apply only to cyclic, single server networks. One of the surprising conclusions
of our analysis is that the interoutput times that comprise the cycle time of a customer are (finitely) exchangeable, i.e.,
that their joint distribution is invariant under permutations.
This revised version was published online in June 2006 with corrections to the Cover Date. 相似文献
968.
In this paper, we discuss the Poincare bifurcation of cubic Hamiltonian systems with double centers and prove that the systems may at least generate two limit cycles and at most generate three limit cycles outside the lemniscate after a small cubic perturbation. 相似文献
969.
In order to understand the distribution and the cycle of arsenic compounds in the marine environment, the horizontal distributions of arsenic(V) [As(V)], arsenic(III) [As(III)], monomethylarsonic acid (MMAA) and dimethylarsinic acid (DMAA) in the Indian Pacific Oceanic surface waters have been investigated. This took place during cruises of the boat Shirase from Tokyo to the Syowa Station (15 November–19 December 1990), of the tanker Japan Violet from Sakai to Fujayrah (28 July–17 August 1991) and of the boat Hakuho-maru from Tokyo to Auckland (19 September–27 October 1992). Vertical distributions of arsenic in the west Pacific Ocean have also been investigated. The concentration of As(V) was found to be relatively higher in the Antarctic than in the other areas. Its concentration varied from 340 ng dm?3 (China Sea) to 1045 ng dm?3 (Antarctic). On the other hand, the concentrations of the biologically produced species, MMAA and DMAA, were extremely low in the Antarctic and southwest Pacific waters. Their concentrations in Antarctic waters were 8 ng dm?3 and 22 ng dm?3 and those in the southwest Pacific were 12 ng dm?3 and 25 ng dm?3. In the other regions the concentration varied from 16 ng dm?3 (China Sea) to 36 ng dm?3 (north Indian Ocean) for MMAA and from 50 ng dm?3 (east Indian Ocean) to 172 ng dm?3 (north Indian Ocean) for DMAA. As a result, with the exception of Antarctic and southwest Pacific waters, the percentages of each arsenic species in the surface waters were very similar and varied from 52% (east Indian Ocean) to 63% (northwest Pacific Ocean) for As(V), from 22% (northwest Pacific Ocean) to 27% (east Indian Ocean) for As(III) and from 15% (northwest Pacific Ocean) to 21% (north and east Indian Oceans) for the methylated arsenics (MMAA+DMAA). These percentages in Antarctic waters were 97%, 0.2% and 2.8%, respectively, and those in the southwest Pacific Ocean were 97% for As(V)+As(III) and 3% for MMAA+DMAA. The very low concentrations of the biologically produced species in Antarctic waters and that of methylated arsenic in southwest Pacific waters indicated that the microorganism communities in these oceans was dominated by microorganisms having a low affinity towards arsenic. Furthermore, microorganism activity in the Antarctic was also limited due to the much lower temperature of the seawater there. The vertical profile of inorganic arsenic was 1350 ng dm?3 in surface waters, 1500 ng dm?3 in bottom waters with a maximum value of 1700 ng dm?3 at a depth of about 2000 m in west Pacific waters. This fact suggested the uptake of arsenic by microorganisms in the surface waters and the co-precipitation of arsenic with hydrated heavy-metal oxides in bottom waters. The suggested uptake of inorganic arsenic and subsequent methylation was also supported by the profile of DMAA, with a high concentration of about 26 ng dm?3 in surface water and a significant decrease to a value of 9 ng dm?3 at a depth of 1000 m. 相似文献
970.