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91.
稀植大穗型玉米品种的品比试验 总被引:1,自引:1,他引:1
通过对13个稀植大穗品种的品比试验研究,得出了在山西北中部不同生态区如何选择、推广稀植大穗品种的结论:山西北中部平川区高水肥地宜推广种植忻玉106、晋单48号、新45、天塔1号;丘陵旱作区宜推广种植晋单48号、大丰2号、农大364、强盛12号、泽玉4号;在利用秸秆贮青的养殖区宜选用天塔1号、新45,可以粮饲兼顾,收益更高;生产玉米用于加工淀粉可选用晋单48号;连续种植玉米的地块慎选沈单16号、大丰2号、强盛17号、晋单45号、泽玉4号,避免感染丝黑穗病而造成减产。 相似文献
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Y-M. Chang D. Gianola B. Heringstad & G. Klemetsdal 《Zeitschrift für Tierzüchtung und Züchtungsbiologie》2006,123(5):290-300
Robust threshold models with multivariate Student's t or multivariate Slash link functions were employed to infer genetic parameters of clinical mastitis at different stages of lactation, with each cow defining a cluster of records. The robust fits were compared with that from a multivariate probit model via a pseudo‐Bayes factor and an analysis of residuals. Clinical mastitis records on 36 178 first‐lactation Norwegian Red cows from 5286 herds, daughters of 245 sires, were analysed. The opportunity for infection interval, going from 30 days pre‐calving to 300 days postpartum, was divided into four periods: (i) ?30 to 0 days pre‐calving; (ii) 1–30 days; (iii) 31–120 days; and (iv) 121–300 days of lactation. Within each period, absence or presence of clinical mastitis was scored as 0 or 1 respectively. Markov chain Monte Carlo methods were used to draw samples from posterior distributions of interest. Pseudo‐Bayes factors strongly favoured the multivariate Slash and Student's t models over the probit model. The posterior mean of the degrees of freedom parameter for the Slash model was 2.2, indicating heavy tails of the liability distribution. The posterior mean of the degrees of freedom for the Student's t model was 8.5, also pointing away from a normal liability for clinical mastitis. A residual was the observed phenotype (0 or 1) minus the posterior mean of the probability of mastitis. The Slash and Student's t models tended to have smaller residuals than the probit model in cows that contracted mastitis. Heritability of liability to clinical mastitis was 0.13–0.14 before calving, and ranged from 0.05 to 0.08 after calving in the robust models. Genetic correlations were between 0.50 and 0.73, suggesting that clinical mastitis resistance is not the same trait across periods, corroborating earlier findings with probit models. 相似文献
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商丘地区彩色马铃薯引种试验 总被引:2,自引:0,他引:2
通过对9个彩色马铃薯品种进行品种比较试验,筛选出适合商丘地区种植的彩色马铃薯品种。结果表明,紫罗兰、诺兰、中薯6号和黑美人4个品种薯形好,品质优,产量高,较抗病,适宜商丘地区种植。特别是紫罗兰、诺兰产量分别比对照增产10.30%和2.65%,均达极显著水平,可作为主推品种。中联红、花云2号、紫云1号、云3458和夏LX-70不适宜商丘地区种植。 相似文献
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Goal, Scope and Background
In the nineteen nineties most European countries issued legislation on soil protection, including soil contamination. In the case of a presumed contamination, soil investigation mostly follows a stepwise approach starting with a preliminary investigation, then an in-depth investigation and, finally, remediation. Soil clean-up standards are often foreseen as trigger criteria to determine the need for an in-depth soil investigation or for remediation. There are however large differences in soil clean-up standards. This is partly because of the different roles of soil clean-up standards in each legislative framework and partly because of differences in the soil clean-up standard (SCS) derivation procedures. Despites these differences there are large similarities in the concepts of the derivation procedures for clean-up standards. A better understanding of the differences in clean-up standards is needed. In order to clarify the variation, the background of the clean-up standards for a selected number of countries was investigated. The objective of this paper is to investigate the underlying reason why country-wide generic soil and groundwater clean-up standards of eight trace elements (cadmium, chromium (III), copper, mercury, lead, nickel, zinc and arsenic) differ between the selected countries.Main Features
To avoid misinterpretation of the differences in application of the clean-up standards, a short overview of the legislative role of clean-up standards is given first. Differences in model concepts and parameter values are discussed, followed by a comparison of the generic soil and groundwater clean-up standards for trace elements and a discussion on the sources of variation. The influence of the use of ecotoxicological criteria and data for the derivation of soil clean-up standards will be discussed in more detail. Selected countries were Canada, the Flemish Region (Belgium), France, Germany, Great-Britain, the Netherlands, Norway, Sweden, Switzerland and United States of America (USA).Results and Discussion
When soil clean-up standards for eight trace elements (cadmium, chromium (III), copper, mercury, lead, nickel, zinc and arsenic) were compared between the selected countries differences of more than a factor 1000 arose. Notwithstanding the use of similar derivation procedures, differences were caused by the use of different software models with their specific input data, boundary conditions and applied protection criteria for humans and the ecology. Ecotoxicological criteria tend to lower the soil clean-up standard for the selected trace elements.Conclusions
In the countries that are included in this study, clean-up standards are used is different ways, this is for the determination of the necessity for remediation or for the need for further soil investigation. This paper shows a wide variation in the clean-up standards, which has further implication on the decision for remediation or further investigation and, hence, the financial costs of soil management. All the clean-up standards have as primary goal the protection of human health. A number of countries also include the protection of the ecological function of the soil. Differences in selected software model, (standard) parameters values, selected human toxicological and ecotoxicological criteria, are reason for a substantial variation in the clean-up standards for trace elements.Recommendations and Perspective
. Is this variation justified? The derivation of soil clean-up standards involves - besides scientific elements - political elements, like differentiation in landuse types (agricultural, residential, recreational, industrial), receptor at risk or protection level. It is obvious that harmonization of these elements will be complicated. However, a European action programme, like the thematic strategy for soil protection, could initiate this process of harmonization. Nevertheless, soil-clean-up standards could never be uniform over the whole of Europe because they include country specific elements (geographical, ethnological) and political decisions. 相似文献100.
熊健 《安徽农业大学学报》2001,(1):23-24
海峡两岸尽管政治制度和经济发展模式不同,但由于粮食问题在国计民生中所处的特殊地位,几十年来两岸始终将粮食问题置于社会与经济发展的首位。大陆地区的粮食政策与制度在近半个世纪的历程中走过了艰难曲折的发展道路,取得了显著的成绩,也有明显的失误。同样,台湾地区的粮食政策与制度也经历了反复的波折与探索,有丰富的经验和教训。两者在一些方面有很大的相似性,而在某些方面却有很大的差异,有许多做法是可以相互学习和借鉴的。 相似文献