全文获取类型
收费全文 | 926篇 |
免费 | 71篇 |
国内免费 | 1篇 |
出版年
2023年 | 3篇 |
2022年 | 7篇 |
2021年 | 17篇 |
2020年 | 7篇 |
2019年 | 11篇 |
2018年 | 7篇 |
2017年 | 9篇 |
2016年 | 24篇 |
2015年 | 45篇 |
2014年 | 45篇 |
2013年 | 51篇 |
2012年 | 74篇 |
2011年 | 95篇 |
2010年 | 32篇 |
2009年 | 34篇 |
2008年 | 40篇 |
2007年 | 44篇 |
2006年 | 50篇 |
2005年 | 49篇 |
2004年 | 30篇 |
2003年 | 34篇 |
2002年 | 28篇 |
2001年 | 20篇 |
2000年 | 22篇 |
1999年 | 21篇 |
1998年 | 4篇 |
1997年 | 9篇 |
1996年 | 8篇 |
1995年 | 10篇 |
1994年 | 4篇 |
1993年 | 6篇 |
1992年 | 14篇 |
1991年 | 17篇 |
1990年 | 23篇 |
1989年 | 6篇 |
1988年 | 17篇 |
1987年 | 11篇 |
1986年 | 5篇 |
1985年 | 7篇 |
1984年 | 4篇 |
1983年 | 4篇 |
1982年 | 7篇 |
1981年 | 3篇 |
1980年 | 3篇 |
1979年 | 7篇 |
1975年 | 3篇 |
1974年 | 4篇 |
1973年 | 3篇 |
1972年 | 3篇 |
1935年 | 2篇 |
排序方式: 共有998条查询结果,搜索用时 15 毫秒
171.
A tumor promoter enhances the phosphorylation of polyphosphoinositides while decreasing phosphatidylinositol labelling in lymphocytes 总被引:1,自引:0,他引:1
A M Boon B J Beresford A Mellors 《Biochemical and biophysical research communications》1985,129(2):431-438
12-O-Tetradecanoyl-phorbol-13-acetate, a comitogen for lymphocytes, suppresses the concanavalin A-induced accumulation of 3 2P-phosphatidyl-inositol, in mouse spleen lymphocytes incubated with 3 2P-orthophosphate. The comitogenic tumor promoter does not affect the rate of de novo synthesis of phosphatidylinositol, as measured by [3H]-glycerol incorporation. Mitogen stimulates the incorporation of [3 2P]-phosphate into phosphatidylinositol, phosphatidylinositol-4-phosphate and phosphatidylinositol-4,5-bisphosphate, but the tumor promoter suppresses only the increased labelling of the phosphatidylinositol, while it enhances phosphorylation of the polyphosphoinositides. 相似文献
172.
Matilda E. Boon 《The Histochemical journal》1990,22(6-7):311-312
Conclusion The introduction of microwave technology in the laboratory is a slow process, but we are sure that the point of no return will be passed in 1990. Forced by environmental defence groups, we start to realize that minimalization of reagent usage in the laboratory is urgently needed. This is especially the case with reagents which are unpleasant or dangerous for laboratory personnel (such as formalin), or which are harmful to the environment (heavy metals). Perhaps administration and laboratory management will see their responsibilities and take steps to make it possible for the laboratory personnel to achieve this. It is clear to us that microwave technology can play a key role here.From whom information regarding the Boerhaave Course on Microwaves, 15–19 October, can be obtained. 相似文献
173.
A study was made of decomposition ofCeratophyllum demersum litter over a 17-day period under controlled conditions of temperature and oxygen (5, 10 and 18 °C; aerobic and anaerobic) and over a 169-day period in the field (Lake Vechten, The Netherlands). Litter, water and sediment were sampled on the 0, 2, 4, 7 and 17th day under controlled conditions and on the 0, 17, 49, 127 and 169th day in the field. The litter was analyzed quantitatively for dry mass, ash, carbon, nitrogen, phosphorus and qualitatively of organic composition by pyrolysis mass spectrometry. The water was analyzed for the elemental concentrations of organic carbon (total and dissolved), nitrogen (total, ammonia and particulate) and phosphorus (total and orthophosphate) and for the concentrations of photosynthetic pigments and bacteria. The sediment was analyzed for the elemental concentrations of nitrogen, carbon and phosphorus, and for bacterial numbers.The pattern of litter mass loss fitted an exponential model fairly well. Mass decreased faster under controlled aerobic than under anaerobic conditions and the decrease was stimulated by increasing temperature, relatively more in the range of 5 to 10 °C (by 20%) than in the range of 10 of 18 °C (by 2%). The residual mass ranged from 73 to 43% of initial under controlled aerobic conditions and from 84 to 65% under anaerobic conditions after 17 days. It decreased far less in the field, to 38% of initial mass in the field after 169 days.The litter initially lost a carbohydrate fraction by leaching in all treatments. The protein content decreased initially as well but increased subsequently at increasing temperature stimulated under anaerobic conditions. The changes in organic composition were correlated with those in nitrogen but not with those in carbon and phosphorus contents. The organic composition of litter incubated in the field differed from that of litter incubated in the laboratory. The field residues contained less proteinaceous material than the laboratory residues.The changes in carbon, nitrogen and phosphorus concentrations in the litter showed different patterns. The carbon concentration generally increased, the nitrogen concentration initially dropped and increased subsequently, and the phosphorus concentration initially dropped and remained relatively constant subsequently. Chemical immobilization of the decomposition process may have occurred in the laboratory, but was unlikely in the field.Carbon, nitrogen and phosphorus left the litter initially largely in particulate form and were recovered in the water. The ratio dissolved: total nutrient concentration was lower under controlled aerobic than under anaerobic conditions. Increasing temperature stimulated bacterial use of dissolved organic carbon and nitrogen. A rapid nutrient flow occurred from macrophyte litter, via water to sediment.The phytoplankton biomass in the water was greatly stimulated by substances freed from the decomposing litter. Diatoms increased generally relatively more than green algae, predominating alternatively with green algae under aerobic conditions and continuously under anaerobic conditions. Bacterial numbers in the water initially increased, partly due to transgression of bacteria from the sediment-water interface to the water and partly due to an actual increase in community biomass. The bacteria returned largely to the sediment-water interface, stimulated by increasing temperature, as most of the substrate readily usable by them had left the litter in the litter-bag and was associated with the upper sediment layers.It is feasible that the annual die-off of theC. demersum population of Lake Vechten barely affects nutrient cycling in the lake, because the contribution to the nutrient pools of the lake when fully mixed is only small. However, small particles originating from decomposingC. demersum litter may influence the lake considerably by decreasing water transparency and serving as a food source for filter-feeders and detritivorous macrofauna. 相似文献
174.
Oriane Viale P. van der Bruggen Eva Meuer Regina Kunzmann Hubertus Kohler Roland Mertelsmann T. Boon Paul Fisch 《Immunogenetics》1996,45(1):27-34
Daudi Burkitt’s lymphoma cells, unlike other tumor cell lines, stimulate human T cells coexpressing the variable (V) region genes TCRG-V9 and V TCRD-V2 to proliferate and secrete lymphokines. Hybrids, derived by the fusion of Daudi cells with the human melanoma cell line MZ2-MEL
2.2, retain the morphology of melanoma cells. Unlike the parental melanoma cell line, these Daudi × MZ2-MEL 2.2 hybrids stimulate
secretion of tumor necrosis factor (TNF) and granulocyte/macrophage colony stimulating factor (GM-CSF) by CD4-positive Vγ9/Vδ2
T-cell clones. Whereas the stimulator phenotype of Daudi cells behaves as a dominant trait in Daudi × melanoma hybrids, the
expression of B-cell differentiation markers is suppressed. Thus, the γ/δ T-cell ligand expressed by Daudi cells behaves as
a dominant tumor antigen in Daudi × melanoma hybrids and is unrelated to the differentiated B-cell phenotype. Dominant expression
of the Daudi ligand for human Vγ9/Vδ2 T cells in these hybrids may provide a basis for defining the stimulatory principle
at the molecular level.
Received: 2 May 1996 / Revised: 15 July 1996 相似文献
175.
Jean Herman Pierre van der Bruggen Immanuel F Luescher Susanna Mandruzzato Pedro Romero Joëlle Thonnard Katharina Fleischhauer Thierry Boon Pierre G. Coulie 《Immunogenetics》1996,43(6):377-383
The humanMAGE3 gene is expressed in a significant proportion of tumors of various histological types, but is silent in normal adult tissues other than testis and placenta. Antigens encoded byMAGE3 may therefore be useful targets for specific antitumor immunization. Two antigenic peptides encoded by theMAGE3 gene have been reported previously. One is presented to cytolytic T lymphocytes (CTL) by HLA-A1, the other by HLA-A2 molecules. Here we show that MAGE3 also codes for a peptide that is presented to CTL by HLA-1344.MAGE3 peptides containing the HLA-1344 peptide binding motif were synthesized. Peptide MEVDPIGHLY, which showed the strongest binding to HLA-1344, was used to stimulate blood T lymphocytes from normal HLA-1344 donors. CTL clones were obtained that recognized not only HLA-B44 cells sensitized with the peptide, but also HLA-B44 tumor cell lines expressingMAGE3. The proportion of metastatic melanomas expressing theMAGE3/HLA-1344 antigen should amount to approximately 17% in the Caucasian population, since 24% of individuals carry theHLA-B44 allele and 76% of these tumors express MAGE3. 相似文献
176.
Review of root dynamics in forest ecosystems grouped by climate,climatic forest type and species 总被引:17,自引:0,他引:17
Kristiina A. Vogt Daniel J. Vogt Peter A. Palmiotto Paul Boon Jennifer O'Hara Heidi Asbjornsen 《Plant and Soil》1995,187(2):159-219
Patterns of both above- and belowground biomass and production were evaluated using published information from 200 individual data-sets. Data sets were comprised of the following types of information: organic matter storage in living and dead biomass (e.g. surface organic horizons and soil organic matter accumulations), above- and belowground net primary production (NPP) and biomass, litter transfers, climatic data (i.e. precipitation and temperature), and nutrient storage (N, P, Ca, K) in above- and belowground biomass, soil organic matter and litter transfers. Forests were grouped by climate, foliage life-span, species and soil order. Several climatic and nutrient variables were regressed against fine root biomass or net primary production to determine what variables were most useful in predicting their dynamics. There were no significant or consistent patterns for above- and belowground biomass accumulation or NPP change across the different climatic forest types and by soil order. Similarly, there were no consistent patterns of soil organic matter (SOM) accumulation by climatic forest type but SOM varied significantly by soil order—the chemistry of the soil was more important in determining the amount of organic matter accumulation than climate. Soil orders which were high in aluminum, iron, and clay (e.g. Ultisols, Oxisols) had high total living and dead organic matter accumulations-especially in the cold temperate zone and in the tropics. Climatic variables and nutrient storage pools (i.e. in the forest floor) successfully predicted fine root NPP but not fine root biomass which was better predicted by nutrients in litterfall. The importance of grouping information by species based on their adaptive strategies for water and nutrient-use is suggested by the data. Some species groups did not appear to be sensitive to large changes in either climatic or nutrient variables while for others these variables explained a large proportion of the variation in fine root biomass and/or NPP. 相似文献
177.
Effect of an 18-wk weight-training program on energy expenditure and physical activity 总被引:1,自引:0,他引:1
Van Etten Ludo M.L.A.; Westerterp Klaas R.; Verstappen Frans T.J.; Boon Bart J.B.; Saris Wim H.M. 《Journal of applied physiology》1997,82(1):298-304
Van Etten, Ludo M. L. A., Klaas R. Westerterp, Frans T. J. Verstappen, Bart J. B. Boon, and Wim H. M. Saris. Effect of an18-wk weight-training program on energy expenditure and physicalactivity. J. Appl. Physiol. 82(1):298-304, 1997.The purpose of this study was to examine theeffect of an 18-wk weight-training program on average daily metabolicrate (ADMR). Before the intervention and in weeks8 and 18 (T0,T8, andT18, respectively) data on bodycomposition, sleeping metabolic rate (SMR), food intake, energy cost ofthe weight-training program(EEex), and nontraining physicalactivity (accelerometer) were collected in the exercise group (EXER,n = 18 males). ADMR was determined ina subgroup (EX12, n = 12) by usingdoubly labeled water. At T0 andT18, data (except ADMR) were alsocollected in a control group (Con, n = 8). Body mass did not change in EXER or Con. Fat-free mass increased only in EXER with 2.1 ± 1.2 kg, whereas fat mass decreased in EXERas well as Con (2.0 ± 1.8 and 1.4 ± 1.0 kg, respectively). Initial ADMR (12.4 ± 1.2 MJ/day) increased atT8 (13.5 ± 1.3 MJ/day, P < 0.001) with no further increaseat T18 (13.5 ± 1.9 MJ/day). SMR did not change in EXER (4.8 ± 0.5, 4.9 ± 0.5, 4.8 ± 0.5 kJ/min) or Con (4.7 ± 0.4, 4.8 ± 0.4 kJ/min). Energy intake didnot change in EXER (10.1 ± 1.8, 9.7 ± 1.8, 9.2 ± 1.9 MJ/day) or Con (10.2 ± 2.6, 9.4 ± 1.8, 10.1 ± 1.5 MJ/day)and was systematically underreported in EX12 (21 ± 14, 28 ± 18, 34 ± 14%,P < 0.001).EEex (0.47 ± 0.20, 0.50 ± 0.18 MJ/day) could only explain 40% of the increase in ADMR.Nontraining physical activity did not change in both groups. Inconclusion, although of modest energy cost, weight-training induces asignificant increase in ADMR. 相似文献
178.
The original article to which this Erratum refers was published in Biotechnology and Bioengineering (2004) 85 (2)202–213 相似文献
179.
A frequent observation in plant–animal mutualistic networks is that abundant species tend to be more generalised, interacting with a broader range of interaction partners than rare species. Uncovering the causal relationship between abundance and generalisation has been hindered by a chicken‐and‐egg dilemma: is generalisation a by‐product of being abundant, or does high abundance result from generalisation? Here, we analyse a database of plant–pollinator and plant–seed disperser networks, and provide strong evidence that the causal link between abundance and generalisation is uni‐directional. Specifically, species appear to be generalists because they are more abundant, but the converse, that is that species become more abundant because they are generalists, is not supported by our analysis. Furthermore, null model analyses suggest that abundant species interact with many other species simply because they are more likely to encounter potential interaction partners. 相似文献
180.