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111.
112.
New radiological routine methods for detecting sediment deposits and for absolute dating of sediment layers were developed and tested on the banks of a river of the Ruhr district (Lippe). The remarkably simple methods improve the well-known excess-210Pb-dating for the use to rivers in industrial regions and allow the preparation of load histories (chronologies) for the years since 1900 with a mean standard deviation less than 3 years. The chronologies of load with radionuclides of thorium, radium, lead and cesium are shown; preliminary chemical measurements for lead, zinc, arsenic, mercury, cadmium, barium, dioxins, PCB and EOX are reported. The new methods of dating are especially suitable for rivers with radioactivity from mines e.g. Mulde, Elbe and Oder. 相似文献
113.
The concentration of trace elements within cephalopod statoliths can provide a record of the environmental characteristics at the time of calcification. To reconstruct accurately the environmental characteristics at the time of calcification, it is important to understand the influence of as many factors as possible. To test the hypothesis that the elemental composition of cuttlefish statoliths could be influenced by diet, juvenile Sepia officinalis were fed either shrimp Crangon sp. or fish Clupea harengus under equal temperature and salinity regimes in laboratory experiments. Element concentrations in different regions of the statoliths (core–lateral dome–rostrum) were determined using laser ablation inductively coupled plasma mass spectrometry (LA- ICPMS). The ratios of Sr/Ca, Ba/Ca, Mn/Ca and Y/Ca in the statolith’s lateral dome of shrimp-fed cuttlefish were significantly higher than in the statolith’s lateral dome of fish-fed cuttlefish. Moreover, significant differences between statolith regions were found for all analysed elements. The fact that diet adds a considerable variation especially to Sr/Ca and Ba/Ca must be taken into account in future micro-chemical statolith studies targeting cephalopod’s life history. 相似文献
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The basic idea of LCA is that all environmental burdens connected with a product or service have to be assessed, back to the
raw materials and down to waste removal. Therefore, the term “Life Cycle Assessment” is more precise than the German “?kobilanz”
or the French “écobilan”. This basic idea is undoubtedly true, and LCA is the only environmental assessment tool which avoids
positive ratings for measurements which only consists in the shifting of burdens.
In the years from 1990 to 1993, SETAC and SETAC-Europe shaped the development of LCA in a series of important workshops culminating
in the “Code of Practice” of 1993. The results of these workshops can be illustrated by the famous SETAC-triangle. It shows
the basic structure which is now underlying the standardizing activities of ISO: 1. Goal definition and scoping, 2. Inventory
analysis, 3. Impact assessment, 4. Improvement assessment.
The structure recently defined by ISO differs from the SETAC structure only in the last element which is called “Interpretation”
in the international standard 14040. According to ISO, “Improvement Assessment” is only one of the many activities which may
follow LCA but is not part of the true analysis.
The components of an LCA are described and interpreted in detail, SETAC vs. ISO. Recent developments and activities initiated
by ISO, SPOLD and other organisations complete the review. 相似文献
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Environmental Science and Pollution Research - 相似文献
118.
B. Kløve J. Kettunen O. Varis P. Vakkilainen H. Sirviö 《Environmental monitoring and assessment》1993,24(2):167-180
The hygienic quality of the water of the Kerava river, southern Finland, deteriorates occasionally. The purpose of the study was to design a real-time monitoring system that would inform the public using the river for recreational purposes about the changes in water quality. The system was constrained to consist of on-line sensing of water quality and quantity, and adjacent forecasting models. Four different system alternatives were analyzed and compared. The first alternative observes river flow in real-time; the second alternative also monitors water temperature, turbidity, pH, conductivity and dissolved oxygen. The data collected in this way are used to forecast Streptococcus and E. coli concentrations, using canonical correlation and regression analysis. The third configuration is a two-step procedure, where river flow is first predicted by an ARMAX model and the hygienic state is then based on the flow estimate, as in the first assemblage. The most expensive monitoring system, which at present is the least well-known, is to apply the Lidar system, where the hygienic status of the river quality is observed directly using laser technology, placing less emphasis on modeling. In this paper, the alternatives are formulated and a preliminary comparison is made, using the criteria of operational feasibility, prediction uncertainty, investment and maintenance costs, and suitability for in-situ monitoring. 相似文献
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