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41.
本文探讨了在草业科学研究中,建立基于GIS空间定位数据的多类型数据框架,以及基于服务的数据共享系统的必要性和可行性,并进行了系统框架设计。提出基于服务概念的数据服务平台应该是一个主动的数据存储、加工、分析和提供者,是一个基于主动服务的管理信息系统,它需要一个综合观测平台作为搭载主动服务理念的物质服务系统平台;数据开放实验室是数据综合观测和共享服务系统的实现平台,系统的服务功能通过开放实验室得以实现。  相似文献   
42.
中国农业技术推广机构设置与运行机制的战略思考   总被引:1,自引:0,他引:1  
简要回顾了中国农业技术推广体系的历史和现状,分析了现行农技推广机构的利弊,提出了农业科研、教育和推广紧密结合的新型农技推广机构的设置思路及其运行机制,并探讨了该体系实现的措施。新型农技推广机构是以农业部为最高管理机构,加设专家顾问团,负责研究全国各地重大农业问题,从而为其决策提供参考;以农业大学、农科院和农校组成的教研联合体为实施机构,上直对农业部,下直面农业生产第一线,并组建和依托各级农业科技园,重组原地、县、乡镇各级推广机构,开展科研、教学及推广工作。  相似文献   
43.
  1. The Asian clam Corbicula fluminea is an invasive freshwater species that can cause adverse ecological and economic impacts. Information on its dispersal abilities, ecological preferences and impacts may contribute towards the improvement of management strategies, including those relating to regulatory demands such as the European Water Framework Directive (WFD).
  2. Both the above perspectives were addressed through inspection of environmental constraints to C. fluminea dispersal and impacts in a semi‐natural drainage catchment (interconnected system of ditches). Forty sites were surveyed in 2014 to describe the species distribution and to characterize benthic macroinvertebrate communities, water column and sediment physico‐chemistry, as well as the hydromorphological conditions.
  3. Clams were unevenly distributed in the study area and artificial barriers (dikes) did not prevent downstream dispersal of juveniles. Large variation in clam density (0–3077 clams m?2) could not be explained by physico‐chemical or hydromorphological gradients. Although typical clam preference ranges reported in the literature were often exceeded, dense populations were nevertheless observed.
  4. Macroinvertebrate community structure suggested associations between the Asian clam and some functional feeding groups. However, the impacts of clams on macroinvertebrate assemblages and ecological quality were negligible, suggesting that contemporary methods designed to comply with the WFD bioassessment scheme may fail to detect important drivers of ecological change in freshwater ecosystems.
  5. This study demonstrated the reduced ecological impacts and broad ecological competence of the Asian clam, but also that its spread depends on human vectors. These findings highlight the need to rethink prediction tools supporting preventive measures against the introduction and spread of this invasive bivalve.
  相似文献   
44.
  • 1. A method has been developed for assessing the degree of human alteration of river flow regimes relative to near‐natural or reference conditions.
  • 2. The Dundee Hydrological Regime Alteration Method (DHRAM) utilizes the Indicators of Hydrologic Alteration approach of the US Nature Conservancy to classify the risk of damage to in‐stream ecology using a five‐class scheme compatible with the requirements of the EC Water Framework Directive.
  • 3. Separate methods have been developed for rivers and lakes, though only the former are considered in this paper.
  • 4. DHRAM uses daily mean flow time‐series data, representing un‐impacted and impacted situations for the site of interest, in relation to any type of anthropogenic hydrological impact such as impoundments, abstractions or flow augmentation.
  • 5. Procedures for coping with different levels of data availability are outlined, utilizing the Micro Low Flows computer package to generate synthetic series of daily mean flows, supplemented by flow alteration data as appropriate.
  • 6. The utility of DHRAM is demonstrated through a pair of Scottish case studies illustrating its ability in classifying regime alteration and supporting mapping, which will be of value to river basin managers.
  • 7. Finally, present and future issues relating to the calibration of DHRAM scores to levels of ecological damage are discussed.
Copyright © 2005 John Wiley & Sons, Ltd.  相似文献   
45.
  • 1. In the absence of a standard procedure for characterizing the physical habitat of lakes in Europe, this paper describes the development of a multi‐purpose Lake Habitat Survey (LHS). The technique has been designed to meet the hydromorphological assessment needs of the Water Framework Directive (WFD), as well as to assist in monitoring the condition of designated sites in the UK and for wider application in environmental impact assessments and restoration programmes.
  • 2. LHS involves detailed recording of shoreline features at a number of plots (Hab‐Plots), complemented by a meso‐scale survey of the entire lake, including shoreline characteristics and pressures, and modifications to the hydrological regime. A temperature and dissolved oxygen profile is also compiled at the deepest point of the lake (Index Site). Existing databases are exploited where possible, and remote sensing data (e.g. aerial photographs) are used to assist field‐based observations.
  • 3. Initial field trials demonstrated that the consistency of the method, whether conducted by boat or on foot, was high. More than 250 surveys were carried out across the UK in 2004 through collaboration with the statutory environment and conservation agencies.
  • 4. Two levels of complexity were tested — a full version requiring 10 Hab‐Plots and an abridged version, LHScore, involving four plots and omitting the Index Site. While 8–10 plots were required to capture the full diversity of features at complex sites, LHScore data were sufficient to generate metrics for classification purposes.
  • 5. A Lake Habitat Modification Score (LHMS) may be calculated from LHS data. This synthesizes a wide array of hydromorphological and human pressures and has direct applications for assessment of ecological status under the WFD. Preliminary analysis illustrates a spectrum of hydromorphological alteration of 82 lakes in the UK.
  • 6. Further considerations are discussed, including the prospect that the LHS protocol might form the basis of a European standard developed through CEN (Comité Européen de Normalisation).
Copyright © 2006 John Wiley & Sons, Ltd.  相似文献   
46.
  • 1. Macroalgae are one of the biological parameters considered in the European Water Framework Directive (WFD) for establishing the ecological status of coastal water bodies. In order to test the metric used to assess this element in the Cantabrian coast, the quality of rocky bottoms (CFR) index was applied to 164 transects at 28 sites on the coast of Asturias (northern Spain) in the summers of 2007 and 2008.
  • 2. At each sampling point, three variables were measured: species richness, cover of characteristic and opportunistic macroalgae, and in 2008 the percentage of the area occupied by each characteristic species was also estimated.
  • 3. Application of the Shapiro–Wilk test to the variables ‘cover of characteristic macroalgae’ and ‘cover of opportunistic algae’ revealed that the data were not normally distributed (P<0.001). A Kolmogorov–Smirnov test revealed: (a) significant differences (P<0.01) between the exposed and semi‐exposed sites, for the three variables studied; (b) significant differences in cover, for six species depending on the type of exposure; and (c) significant differences (P<0.01) in opportunistic macroalgal cover in relation to the two subtypes of water bodies in the study area. However, no significant differences were observed for overall macroalgal cover or species richness.
  • 4. According to the results obtained, new reference conditions and class boundaries are proposed for the implementation of the CFR index in Asturian coastal waters. The ranges proposed for the CFR index in the present study provide better discrimination for evaluating the ecological status of the studied area.
  • 5. The results of SIMPER and MDS analyses reinforced the conclusion that the type of exposure and the degree of human impact are the factors that best explain the degree of similarity between the sites sampled. Copyright © 2010 John Wiley & Sons, Ltd.
  相似文献   
47.
  • 1. The assessment of links between ecology and physical habitat has become a major issue in river research and management. Key drivers include concerns about the conservation implications of human modifications (e.g. abstraction, climate change) and the explicit need to understand the ecological importance of hydromorphology as prescribed by the EU's Water Framework Directive. Efforts are focusing on the need to develop ‘eco‐hydromorphology’ at the interface between ecology, hydrology and fluvial geomorphology. Here, the scope of this emerging field is defined, some research and development issues are suggested, and a path for development is sketched out.
  • 2. In the short term, major research priorities are to use existing literature or data better to identify patterns among organisms, ecological functions and river hydromorphological character. Another early priority is to identify model systems or organisms to act as research foci. In the medium term, the investigation of pattern–processes linkages, spatial structuring, scaling relationships and system dynamics will advance mechanistic understanding. The effects of climate change, abstraction and river regulation, eco‐hydromorphic resistance/resilience, and responses to environmental disturbances are likely to be management priorities. Large‐scale catchment projects, in both rural and urban locations, should be promoted to concentrate collaborative efforts, to attract financial support and to raise the profile of eco‐hydromorphology.
  • 3. Eco‐hydromorphological expertise is currently fragmented across the main contributory disciplines (ecology, hydrology, geomorphology, flood risk management, civil engineering), potentially restricting research and development. This is paradoxical given the shared vision across these fields for effective river management based on good science with social impact. A range of approaches is advocated to build sufficient, integrated capacity that will deliver science of real management value over the coming decades.
Copyright © 2007 John Wiley & Sons, Ltd.  相似文献   
48.
  • 1. The EC Water Framework Directive requires that Member States assess the ecological quality of their water bodies on the basis of a wide set of variables, including benthic invertebrates.
  • 2. The aim of the study was to find one or more faunistic indices that could be related to ecological status of shallow lakes, independent of different macrophyte types.
  • 3. Six invertebrate indices were calculated from abundance and biomass data in 10 Spanish shallow lakes: total abundance and biomass, Shannon's index, percentage of predators, percentage of Ephemeroptera, Plecoptera and Trichoptera, Orthocladiinae as a percentage of the total Chironomidae, and Chironominae as a percentage of the whole macroinvertebrate community. Taxon richness was also calculated.
  • 4. Differences in the values of indices across different macrophyte types were explored by means of a one‐way analysis of variance. Significant differences were occasionally found when indices were calculated from biomass data. Total abundance was also significantly different across some architecture types.
  • 5. No significant correlations were found between the overall values of the indices for each lake and the environmental variables measured (ecological status, total nitrogen, total phosphorus, chlorophyll a concentrations, dynamics of the water flow, and naturalness of the shore), except in the case of total biomass.
  • 6. Values of indices were plotted (box plots) to detect potential differences between lakes of different ecological status. None of the index values was clearly related to ecological status. Thus, the approach used here, requiring relatively little sampling effort and taxonomic expertise, was of little use as a quality indicator for shallow lakes. The implementation of the Directive will therefore require different approaches to be developed and tested.
Copyright © 2004 John Wiley & Sons, Ltd.  相似文献   
49.
  • 1. The ecological status of shallow lakes is highly dependent on the abundance and composition of macrophytes. However, large‐scale surveys are often confined to a small number of water bodies and undertaken only infrequently owing to logistical and financial constraints.
  • 2. Data acquired by the Compact Airborne Spectrographic Imager‐2 (CASI‐2) was used to map the distribution of macrophytes in the Upper Thurne region of the Norfolk Broads, UK. Three different approaches to image classification were evaluated: (i) Euclidean minimum distance, (ii) Gaussian maximum likelihood, and (iii) support vector machines.
  • 3. The results show macrophyte growth‐habits (i.e. submerged, floating‐leaved, partially‐emergent, emergent) and submerged species could be mapped with a maximum overall classification accuracy of 78% and 87%, respectively. The Gaussian maximum likelihood algorithm and support vector machine returned the highest classification accuracies in each instance.
  • 4. This study suggests that remote sensing is a potentially powerful tool for large‐scale assessment of the cover and distribution of aquatic vegetation in clear water shallow lakes, particularly with respect to upscaling field survey data to a functionally relevant form, and supporting site‐condition monitoring under the European Union Habitats (92/43/EEC) and Water Framework (2000/60/EC) directives. Copyright © 2010 John Wiley & Sons, Ltd.
  相似文献   
50.
  • 1. The Water Framework Directive (WFD) requires member states to establish ‘type‐specific biological reference conditions’ for the assessment of surface waters and describes a method for establishing such biological targets. The methodology described in the Directive is based on geographic and physical characteristics and similar to the ‘multimetric’ approach used widely in North America, but contrasts with the biological classification of the ‘multivariate’ approach which is commonly used in Europe.
  • 2. An investigation was made of the relative efficiency of the multimetric and multivariate classification approaches in partitioning the observed biological variation of the macroinvertebrate communities of 22 minimally disturbed lakes in Northern Ireland. Furthermore, the accuracy of predictive models based on the two approaches was compared.
  • 3. The WFD environmental typologies partitioned the observed biological variation poorly with a maximum ANOSIM R‐value of 0.216 compared with 0.609 for a multivariate biological site classification. The WFD System B approach partitioned more variation than the System A approach.
  • 4. The use of a predictive model, based on any of the site classification approaches, resulted in more accurate faunal predictions than a null model. However, the biological model produced the most accurate predictions.
  • 5. Canonical correspondence analysis showed that the environmental variables used in the biological classification model explained more variation (28%) than the best‐performing environmental classification model (24%). The most important variable was pH, followed by surface area and altitude. The variables used in all approaches explained more variation when used as continuous rather than categorized parameters.
  • 6. The results of this work, the first such comparative study of predictive models in lakes, concur with similar studies in streams. It may be concluded that large‐scale environmental classifications are unreliable as a method for setting type‐specific reference targets for the ecological assessment of fresh waters.
Copyright © 2007 John Wiley & Sons, Ltd.  相似文献   
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