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211.
本文提出用快速法测定出COD_(Cr)值后,按稀释倍数通式c_n=COD_(Cr)/6.5×2~(n-1))(n=1,2,3)计算出三个适当的稀释倍数.与其他方法相比,本方法简便、可靠,普遍适用,可保证样品BOD_5分析一次成功.在BOD_5分析监测中具有实际意义和推广价值. 相似文献
212.
A good estimate of the design effect is critical for calculating the most efficient sample size for cluster surveys. We reviewed the design effects for seven nutrition and health outcomes from nine population-based cluster surveys conducted in emergency settings. Most of the design effects for outcomes in children, and one-half of the design effects for crude mortality, were below two. A reassessment of mortality data from Kosovo and Badghis, Afghanistan revealed that, given the same number of clusters, changing sample size had a relatively small impact on the precision of the estimate of mortality. We concluded that, in most surveys, assuming a design effect of 1.5 for acute malnutrition in children and two or less for crude mortality would produce a more efficient sample size. In addition, enhancing the sample size in cluster surveys without increasing the number of clusters may not result in substantial improvements in precision. 相似文献
213.
Griffith DA 《Environmental geochemistry and health》2008,30(6):495-509
Properly sampling soils and mapping soil contamination in urban environments requires that impacts of spatial autocorrelation
be taken into account. As spatial autocorrelation increases in an urban landscape, the amount of duplicate information contained
in georeferenced data also increases, whether an entire population or some type of random sample drawn from that population
is being analyzed, resulting in conventional power and sample size calculation formulae yielding incorrect sample size numbers
vis-à-vis model-based inference. Griffith (in Annals, Association of American Geographers, 95, 740–760, 2005) exploits spatial statistical model specifications to formulate equations for estimating the necessary sample
size needed to obtain some predetermined level of precision for an analysis of georeferenced data when implementing a tessellation
stratified random sampling design, labeling this approach model-informed, since a model of latent spatial autocorrelation
is required. This paper addresses issues of efficiency associated with these model-based results. It summarizes findings from
a data collection exercise (soil samples collected from across Syracuse, NY), as well as from a set of resampling and from
a set of simulation experiments following experimental design principles spelled out by Overton and Stehman (in Communications in Statistics: Theory and Methods, 22, 2641–2660). Guidelines are suggested concerning appropriate sample size (i.e., how many) and sampling network (i.e., where).
相似文献
Daniel A. GriffithEmail: |
214.
三氟乙酸是HFC-134a等氯氟烃替代品的降解产物,对植物和土壤微生物群落的生长有一定抑制作用。笔者建立了测定TFA质量浓度的实验方法:将样品中的三氟乙酸与硫酸二甲酯在浓硫酸介质中衍生为三氟乙酸甲酯(MTFA),利用MTFA的易挥发性,以顶空进样和气相色谱-质谱联用的方法检测样品中MTFA的质量浓度,进而得到环境水样中TFA的质量浓度。并应用该方法测定了北京部分地表水体中三氟乙酸的质量浓度。测定结果:北京青年湖水样和北海水样中的ρ(三氟乙酸)分别为78和93ng L,而北京大学自来水水样中ρ(三氟乙酸)低于方法检测限10ng L。 相似文献
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A More Cost-Effective Emap Benthic Macrofaunal Sampling Protocol 总被引:1,自引:0,他引:1
Benthic macrofaunal sampling protocols in the U.S. Environmental Protection Agency's Environmental Monitoring and Assessment
Program (EMAP) are to collect 30 to 50 random benthic macrofauna [defined as animals retained on a 0.5 mm (East and Gulf Coasts,
USA) or a 1.0 mm mesh sieve (West Coast, USA)] samples per reporting unit using a 0.044 m2 (East and Gulf Coasts) or 0.1 m2 (West Coast) grab. Benthic macrofaunal community conditions in the reporting unit are characterized by cumulative distribution
functions (CDFs) on end points of interest, such as number of species (S), abundance (A), and Shannon--Wiener diversity (H′). An EMAP and a companion field study were conducted concurrently in Tillamook Bay (Oregon, USA) to compare the cost effectiveness
of benthic macrofauna samples collected using the EMAP West Coast (0.1 m2 × ≥7 cm deep, 1.0 mm mesh), a 0.01 m2 × 5 cm deep, 1.0 mm mesh, and a 0.01 m2 × 5 cm deep, 0.5 mm mesh sampling protocol. Cost was estimated in relative laboratory sample-processing time. Sampling protocols
were judged equally effective for EMAP purposes if, after linear transformation to adjust for scale changes in end point distributions,
their S, A, and H′ CDFs were not significantly different. The 0.01 m2 × 5 cm deep, 1.0 mm mesh sampling protocol was the most cost effective. 相似文献
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