首页 | 本学科首页   官方微博 | 高级检索  
文章检索
  按 检索   检索词:      
出版年份:   被引次数:   他引次数: 提示:输入*表示无穷大
  收费全文   472篇
  免费   51篇
  国内免费   86篇
测绘学   4篇
大气科学   24篇
地球物理   23篇
地质学   11篇
海洋学   445篇
综合类   75篇
自然地理   27篇
  2024年   1篇
  2023年   9篇
  2022年   4篇
  2021年   11篇
  2020年   19篇
  2019年   3篇
  2018年   15篇
  2017年   10篇
  2016年   14篇
  2015年   14篇
  2014年   18篇
  2013年   49篇
  2012年   18篇
  2011年   29篇
  2010年   20篇
  2009年   23篇
  2008年   19篇
  2007年   33篇
  2006年   36篇
  2005年   30篇
  2004年   26篇
  2003年   18篇
  2002年   21篇
  2001年   26篇
  2000年   19篇
  1999年   13篇
  1998年   24篇
  1997年   13篇
  1996年   12篇
  1995年   14篇
  1994年   9篇
  1993年   5篇
  1992年   11篇
  1991年   5篇
  1990年   3篇
  1989年   3篇
  1988年   2篇
  1986年   2篇
  1985年   2篇
  1984年   2篇
  1983年   1篇
  1982年   3篇
排序方式: 共有609条查询结果,搜索用时 31 毫秒
91.
92.
厦门文昌鱼人工繁殖和幼虫发育及其变态的研究   总被引:6,自引:0,他引:6  
用组织学和胚胎学方法对厦门国家级自然保护区文昌鱼的生殖季节、胚胎发育和幼虫培育进行详细研究,结果表明,自然保护区文昌鱼生殖季节可分为两个繁殖时期,从6月初开始至7月初为繁殖高峰期,8和9月为繁殖小产期.观察人工繁殖得出,文昌鱼(Branchiostoma belcheri)产卵时间在傍晚19:00前后,可以观察到雌、雄文昌鱼的产卵和排精行为:雄性文昌鱼先离开沙,并跃出水面快速游动和排精,接着雌鱼也跃出水面,所有的卵通过破裂的性腺壁进入到围鳃腔并通过围鳃孔到水中受精,受精率在98.5%以上,还观察了文昌鱼幼虫发育并变态为幼鱼(长度为1.05~13.5mm)的全过程.  相似文献   
93.
通过对鸟蛤(Cardium sp.)的生物学研究,进行了苗种培育、稚贝中间培育、养成、增殖技术的综合系统研究,探明了鸟蛤的生态分布、食性、繁殖习性、生长发育、埋栖及移动生态等生物学特性,报道了鸟蛤人工苗种培育及增养殖技术措施,系统地提出了鸟蛤苗种控温培育及增养殖技术工艺流程与操作规范。  相似文献   
94.
星斑裸颊鲷胚胎及卵黄囊期仔鱼发育研究   总被引:5,自引:0,他引:5  
对星斑裸颊鲷(Lethrinus nebulosusForska.l)的胚胎发育过程做了详细的观察和描述,并跟踪了孵化仔鱼的生长情况。结果表明,星斑裸颊鲷受精卵为浮性卵,卵径0.761 mm±0.019 mm,在水温27℃±1℃,盐度30~32的条件下,受精后约16.5 h孵化;在水温25℃±1℃,盐度30~32的条件下,受精后约17.83 h孵化。初孵仔鱼全长1.739~1.772 mm,仔鱼孵出2 d后开口,卵黄囊与油球已基本消耗完毕,大部分仔鱼开始摄食L-S型轮虫,开始由内源营养期向外源营养期过渡。同时发现在不同温度下,胚胎发育的时间、初孵仔鱼的大小、生长速度及卵黄囊的大小均不同。  相似文献   
95.
Accidental oil spills from ships or rigs and inputs of effluent such as production formation water (PFW) are key perceived threats to tropical biota from industry activities. Scleractinian corals are an important functional component of tropical reefs and the abundance, diversity and resilience of coral communities can be used as an indicator of ecosystem health. In this paper, we report the effects of petroleum products, including water accommodated fractions (WAF) of crude oil, PFW and dispersant (Corexit 9527), on fertilization and larval metamorphosis of the widespread scleractinian coral, Acropora millepora (Ehrenberg, 1834) in laboratory-based assays. At 20% v/v PFW fertilization was inhibited by 25%. This concentration was equivalent 0.0721 mg l−1 total hydrocarbon (THC). In contrast, larval metamorphosis was more sensitive to this effluent, with 98% metamorphosis inhibited at the same concentration. Crude oil WAF did not inhibit fertilization of gametes until dispersant was introduced. Dispersed oil was slightly more toxic to fertilization than dispersant alone, suggesting toxicity to that event may be additive. The minimum concentration of dispersed oil which inhibited fertilization was 0.0325 mg l−1 THC. Larval metamorphosis was more sensitive than fertilization to crude oil. Although crude oil and dispersant inhibited larval metamorphosis individually, this toxicity was magnified when larvae were exposed to combinations of both. Crude oil inhibited metamorphosis at 0.0824 mg l−1 THC and at 0.0325 mg l−1 THC when dispersed in 10% v/v (dispersant/oil). Management of petroleum-related risks to spawning corals should consider not only the occurrence of the annual coral spawning event, but also the subsequent 1–3-week period during which most larval metamorphosis and recruitment occur.  相似文献   
96.
溞对中国对虾早期幼体的循环系统及血液流向进行了活体观察 ,描述了中国对虾早期幼体发育阶段中幼体循环系统血管的走向与分布、血液的流向及循环路径等 ,比较各期幼体循环系统的形态 ,并探讨对虾早期幼体循环系统的发育过程。  相似文献   
97.
长牡蛎 (Crassostrea gigas) 是我国重要的海水养殖贝类,近年其大规模死亡现象频繁发生。为了解长牡蛎的免疫基因在季节上的表达模式变化规律及死亡爆发高峰期的水环境情况,在其主养区山东乳山进行了相关研究。分别在 2018 年 1、 3、5—9 月对该地区牡蛎鳃样品做了免疫基因定量分析,在 6、7、9 月对养殖海域的环境因子 (水温、盐度、pH、溶解氧)、各时间点水体里的浮游植物数量及各采样点牡蛎条件指数的变化进行了研究。结果显示,HSP70 在 7 月份高表达,其余 5 个抗性相关基因在 8 月表达水平达到峰值。在测量的三个月中,7 月水温最高,6 月和 9 月水温略低于 7 月,这一结果和表达模式相关。研究表明近岸的藻类丰度更大。因此,温度是影响长牡蛎存活的各环境因子中的主要因素,温度显著影响到体内抗性基因的表达情况并且间接影响到夏季牡蛎的条件指数。  相似文献   
98.
This study showed lethal concentrations (LC) of copper forPeneaus penicillatus at various stages of its life cycle were 1000 μg/L for nauplii, 1000 μg/L for Zoea I, 2000 vg/L for Zoea II, 2500 μg/L for Zoea III, 3000 μg/L for Mysis I, II and III and that for almost 100% mortality for postlarvae was 3000 μg/L. For cadmium LC were 100 μg/L for nauplii, 500 μg/L for Zoea I, 1000 μg/L for Zoea II, 2000 μg/L for Zoea III, 2500 μg/L for Mysis I and 3500 μg/L for Mysis II, III and postlarvae. For mixture of both metals, LC were 400 μg/L for nauplii, 1000 μg/L for Zoea I, 2000 μg/L for Zoea II and 3000 μg/L for Mysis I, II, III and post larvae.  相似文献   
99.
The experimental results showed that: 1) The embryonic development of bay scallop is inhibited at a dissolved oxygen range of 1.38–3.64×10−3 at 23°C, and completely blocked below the lower limit. 2) The tolerance of larvae to anoxia increased with larval sizes and was related to their oxygen debt. 3) The scallop larvae exhibited specific behavioral responses to oxygen deficiency, which finally led to velum disintegration and larval death. The possible relationship between environmental oxygen deficiency and the disease of disintegration of the larval velum is also discussed. In this study, considerable oxygen debt was found in bay scallop larvae, which was greater in small animals. Based on the works of previous authors, a new concept is proposed for the estimation of oxygen debt, namely, the compensatory rate of oxygen debt (CROD). This can be used in intra—or interspecific comparison of oxygen debt. The results can be helpful in the management of water quality and for the prevention of larval diseases encountered in scallop culture. Contribution No. 2167 from the Institute of Oceanology, Chinese Academy of Sciences.  相似文献   
100.
This study showed Iethal concentrations (LC) of copper for Peneaus penicillatus at various stages ofits Iife cycle were 1000μg/L for nauplii, 1000μg/L for Zoea I, 2000μg/L for Zoea Il, 2500μg/Lfor Zoea III, 3000μg/L for Mysis I, II and III and that for almost 100% mortality for postlarvae was3000μg/L. For cadmium LC were 100μg/L for nauplii, 500μg/L for Zoea l, 1000μg/L forZoea II, 2000μg/L for Zoea III, 2500μg/L for Mysis I and 3500μg/L for Mysis II, III andpostlarvae. For tmixture of both metals, LC were 400μg/L for nauplii, 1000 μg/L for nauplii, 1000μg/L for Zoea I,2000μg/L for Zoea II and 3000μg/L for Mysis I, II, III and post larvae.  相似文献   
设为首页 | 免责声明 | 关于勤云 | 加入收藏

Copyright©北京勤云科技发展有限公司  京ICP备09084417号