全文获取类型
收费全文 | 2538篇 |
免费 | 385篇 |
国内免费 | 1046篇 |
专业分类
安全科学 | 297篇 |
废物处理 | 63篇 |
环保管理 | 182篇 |
综合类 | 2303篇 |
基础理论 | 337篇 |
污染及防治 | 342篇 |
评价与监测 | 356篇 |
社会与环境 | 75篇 |
灾害及防治 | 14篇 |
出版年
2024年 | 6篇 |
2023年 | 39篇 |
2022年 | 113篇 |
2021年 | 189篇 |
2020年 | 164篇 |
2019年 | 143篇 |
2018年 | 143篇 |
2017年 | 167篇 |
2016年 | 198篇 |
2015年 | 244篇 |
2014年 | 241篇 |
2013年 | 264篇 |
2012年 | 251篇 |
2011年 | 250篇 |
2010年 | 177篇 |
2009年 | 193篇 |
2008年 | 164篇 |
2007年 | 193篇 |
2006年 | 185篇 |
2005年 | 96篇 |
2004年 | 86篇 |
2003年 | 91篇 |
2002年 | 80篇 |
2001年 | 50篇 |
2000年 | 42篇 |
1999年 | 56篇 |
1998年 | 33篇 |
1997年 | 26篇 |
1996年 | 18篇 |
1995年 | 11篇 |
1994年 | 13篇 |
1993年 | 11篇 |
1992年 | 7篇 |
1991年 | 7篇 |
1990年 | 2篇 |
1989年 | 2篇 |
1988年 | 1篇 |
1987年 | 1篇 |
1985年 | 3篇 |
1984年 | 2篇 |
1983年 | 1篇 |
1981年 | 1篇 |
1980年 | 1篇 |
1979年 | 1篇 |
1978年 | 1篇 |
1977年 | 1篇 |
1971年 | 1篇 |
排序方式: 共有3969条查询结果,搜索用时 843 毫秒
41.
42.
因子分析法解析北京市大气颗粒物PM10的来源 总被引:17,自引:3,他引:17
2004年10月份在北京市6个采样点采集了大气PM10样品,分析了大气颗粒物的质量浓度、元素组成、离子、有机碳(OC)和元素碳(EC)的浓度,并用因子分析模型对颗粒物的来源进行了研究。结果显示,北京市大气颗粒物的来源主要有6类:建筑水泥尘/机动车尾气尘/燃煤尘、土壤风沙尘、二次粒子尘、工业粉尘、生物质燃烧尘和燃油尘。用模型计算得到的各源对PM10的贡献率分别为建筑水泥尘/机动车尾气尘/燃煤尘占36.57%、土壤风沙尘占16.07%、二次粒子尘占12.33%、工业粉尘占10.29%、生物质燃烧尘占6.07%、燃油尘占3.84%、其它占14.84%。其中建筑水泥/机动车尾气尘/燃煤尘、土壤风沙尘、二次粒子尘、工业粉尘是大气颗粒物PM10的主要来源。实验表明,在缺少源成分谱时可以用因子分析模型来分析大气颗粒物的来源及其相对贡献。 相似文献
43.
活性炭法测量室内空气中氡浓度的影响因素研究 总被引:1,自引:0,他引:1
探讨了各种因素对活性炭法测量室内空气中氡浓度的影响,并提出既能保证检测质量,又能符合工程检测需要、提高检测效率的检测条件范围。 相似文献
44.
广州冬季霾天气大气PM2.5污染特征分析 总被引:8,自引:4,他引:8
收集了2005年12月至2006年2月的PM2.5浓度观测数据及同步气象数据,分析了冬季PM2.5质量浓度日变化趋势以及霾日期间PM2.5质量浓度日变化和小时变化趋势.结果发现,观测期间PM2.5日均值浓度为69μg/m3,霾日期间PM2.5日均值浓度为72μg/m3.冬季霾天气的发生频率为45%,霾天气过程最短持续2天,最长持续9天.较高的PM2.5浓度和较高的相对湿度及较小的风速是导致霾天气形成的主要原因.霾日期间PM2.5小时浓度变化趋势与人类活动周期和气象条件密切相关. 相似文献
45.
A positive correlation has been established between increased levels of airborne particulate pollution and adverse health effects, the toxicological mechanisms of which are poorly understood. For toxicologists to unambiguously determine thesemechanisms, truly representative samples of ambient PM10 are required. This presents problems, as PM10 collecting equipment commonly employed, such as the Tapered Element Oscillating Microbalance (TEOM®), heat the inflow toexclude moisture or use fibrous filters, resulting in a PM10sample that may have undergone significant chemical change on thefilter surface or is contaminated by filter fibres. Other systems(i.e. Negretti and Partisol) can successfully collect PM10 without chemical alteration or filter contamination. Comparativecollections from Port Talbot, S. Wales suggest that TEOMs and Negretti/Partisol systems collect different PM10's; the principle difference arising from the TEOM's heating chamber, which precipitates water-soluble ions and volatilises some organic components. This results in both the mass and compositionof the PM10's being altered. Particle size distributionsfor Negretti and Partisol collections highlighted differences mainly attributed to different flow rates. The results of thiswork demonstrate that simple correlations between PM10 massand adverse health effects are problematic. Furthermore, elucidation of the complex fractionation and chemical changes indifferent collectors is necessary. 相似文献
46.
47.
Ports can generate large quantity of pollutants in the atmosphere due to various activities like loading and unloading,transportation, and construction operations. Determination of the character and quantity of emissions from individual sources is an essential step in any project to control and minimize the emissions.In this study a detailed emission inventory of total suspendedparticulate matter (TSP), particulate matter less than 10 m(PM10), sulfur dioxide (SO2) and nitrogen oxides (NOx) for a port and harbour project near Mumbai is compiled. Results show that the total annual average contributions of TSP and PM10 from all the port activitieswere 872 and 221 t yr-1, respectively. Annual average emissions of gaseous pollutants SO2 and NOxwere 56 and 397 t yr-1, respectively, calculatedby using emission factors for different port activities. The maximum TSP emission (419 t yr -1) was from paved roads, while the least (0.4 t yr-1) was from bulk handling activity. The maximum PM10 emission (123 t yr-1) was from unpaved roads and minimum (0.2 t yr-1) from bulk handling operations. Similarly the ratio of TSP and PM10 emission was highest (5.18) from paved roads and least (2.17) from bulk handling operations. Regression relation was derivedfrom existing emission data of TSP and PM10 from variousport activities. Good correlation was observed between TSP andPM10 having regression coefficient >0.8. 相似文献
48.
对悬浮颗粒物室外人体暴露的测定一直受到可用资源的限制。设计有效的网络就要求对测定方法的选择、采样点的数量、采样时间、采样频率等进行调整。采样位置要求能表征因周围污染源对附近地区和城市最小影响的空间数值。虽然大多数判定PM是否达标的测定方法是每第3天至第6天的24h监测,但是室外人体暴露的评价要求连续监测一整天。最好有1h或更短时间的监测时段。更详细的粒径大小和化学性质数据也很有必要,因为较小的颗粒及其特殊的化学物质要比总的样品质量更有助于反映对健康的不良影响。 相似文献
49.
对悬浮颗粒物室外人体暴露的测定一直受到可用资源的限制,设计有效的网络就要求对测定方法的选择、采样点的数量、采样时间、采样频率等进行调整。采样位置要求能表征因周围污染源对附近地区和城市最小影响的空间数值。虽然大多数判定PM是否达标的测定方法是每第3天至第6天的24h监测,但是室外人体暴露的评价要求连续监测一整天,最好有1h或更短时间的监测时段。更详细的粒径大小和化学性质数据也很有必要,因为较小的颗粒及其特殊的化学物质要比总的样品质量更有助于反映对缝康的不良影响。 相似文献
50.
J. Franzaring 《Environmental monitoring and assessment》1997,46(3):209-220
Up to now only very few studies in biomonitoring of organic air pollutants have been published taking into account the strong influence mean temperatures have on the accumulation process into plants during the course of the exposition. Temperature governed sorption as well as the plants vitality pose a major source of uncertainty making inter-study comparisons difficult. Different surface-to-volume ratios of plant foliage lead to strongly varying concentration effects in different plant species. Moreover a plants content of waxes and lipids must be considered in order to relate xenobiotic concentrations to the compounds being most efficient in the bioaccumulation process. Some of these factors are evaluated in regard to the use of plants as biomonitors for organic air pollutants. Another aim is to deduce the mean ambient gas phase concentrations from PAH concentrations determined in the biomonitor plants using vegetation-air partitioning coefficients which have been corrected for temperature dependent sorption as well as the plants lipid content. Restrictions of such approaches and methods of biomonitoring in general are discussed. 相似文献