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141.
针对风城油田生产废水高盐、高温、高矿化度、可生化性差等水质特性,现场采用“混凝沉降+高级催化氧化”工艺,处理后出水达到《污水综合排放标准》GB8978中二级排放标准。混凝沉降阶段COD去除率为36~49%,挥发酚去除率为11~21%,石油类去除率为42~69%;催化氧化阶段COD去除率为20%~40%,挥发酚去除率为69%~73%,石油类去除率为16%~20%。 相似文献
142.
固体废物加工产物属于产品的条件 总被引:1,自引:0,他引:1
借鉴欧盟、经济合作与发展组织、美国提出的固体废物加工产物属于产品需要满足的条件,结合《固体废物鉴别导则(试行)》中鉴别固体废物加工产物不属于固体废物而属于产品时最常用的因素,提出固体废物加工产物属于产品需要同时满足的3个条件,即符合国家、地方或行业通用的产品质量标准,符合国家污染控制标准,以及生产工艺过程和相应设施通过环境影响评价及建设项目竣工环境保护验收,为固体废物加工产物的固体废物监管和鉴别提供参考。 相似文献
143.
为了实现装备制造业的生态化发展,必须同时在企业内部实施生态设计及生态化管理,从源头减少资源消耗;以骨干企业为支撑,逐渐完善与钢铁产业群、铸锻产业群及表面处理中心间的产品代谢链条,形成稳定的产品供应关系和产业群,扩展行业间的横向耦合,构建稳定的产品代谢和产业链。 相似文献
144.
Species interactions such as predation or competition can have notable implications for fish population dynamics. Stock status and associated biological reference points can be misrepresented if these interactions are not considered. Here we present a multispecies, biomass production model (MS-PROD) developed by incorporating modifications to the Schaefer production model. The modifications explicitly emphasize a functional group approach, highlighting the effects of species interactions that include competition between species within a group, competition between groups, and predation. The mathematical formulation also includes constraints on carrying capacity for both the entire system and for individual groups. We applied the model as initialized to the Northeast U.S. Large Marine Ecosystem finfish community. We then executed simulations designed to explore the behavior of the model with respect to fishery exploitation and ecological interactions. Collectively, the results demonstrated the utility, and the need, for incorporating ecological effects into fisheries models. 相似文献
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148.
Xiaojiang Tang Yang Bai Anh Duong Martyn T. Smith Laiyu Li Luoping Zhang 《Environment international》2009,35(8):1210-1224
Formaldehyde, an economically important chemical, is classified as a human carcinogen that causes nasopharyngeal cancer and probably leukemia. As China is the largest producer and consumer of formaldehyde in the world, the Chinese population is potentially at increased risk for cancer and other associated health effects. In this paper we review formaldehyde production, consumption, exposure, and health effects in China. We collected and analyzed over 200 Chinese and English documents from scientific journals, selected newspapers, government publications, and websites pertaining to formaldehyde and its subsequent health effects.Over the last 20 years, China's formaldehyde industry has experienced unprecedented growth, and now produces and consumes one-third of the world's formaldehyde. More than 65% of the Chinese formaldehyde output is used to produce resins mainly found in wood products — the major source of indoor pollution in China. Although the Chinese government has issued a series of standards to regulate formaldehyde exposure, concentrations in homes, office buildings, workshops, public places, and food often exceed the national standards. In addition, there have been numerous reports of formaldehyde-induced health problems, including poisoning and cancer. The lack of quality epidemiological studies and basic data on exposed populations emphasizes the need for more extensive studies on formaldehyde and its related health effects in China. 相似文献
149.
根据2007年原国家环境保护总局空气质量日报86个城市的空气污染指数资料,分析我国城市大气污染的时空分布特征。结果表明,我国城市大气污染时空分布特征明显,大气污染冬季最严重,其次为春秋季节,夏季最好;污染总体上北方重于南方。城市大气污染由人类活动及当地特殊的地理位置综合影响形成,沙尘天气加重了北方大气污染。 相似文献
150.
Diesel vehicles are responsible for most of the traffic-related nitrogen oxide (NOx) emissions, including nitric oxide (NO) and nitrogen dioxide (NO2). The use of after-treatment devices increases the risk of high NO2/NOx emissions from diesel engines. In order to investigate the factors influencing NO2/NOx emissions, an emission experiment was carried out on a high pressure common-rail, turbocharged diesel engine with a catalytic diesel particulate filter (CDPF). NO2 was measured by a non-dispersive ultraviolet analyzer with raw exhaust sampling. The experimental results show that the NO2/NOx ratios downstream of the CDPF range around 20%–83%, which are significantly higher than those upstream of the CDPF. The exhaust temperature is a decisive factor influencing the NO2/NOx emissions. The maximum NO2/NOx emission appears at the exhaust temperature of 350°C. The space velocity, engine-out PM/NOx ratio (mass based) and CO conversion ratio are secondary factors. At a constant exhaust temperature, the NO2/NOx emissions decreased with increasing space velocity and engine-out PM/NOx ratio. When the CO conversion ratios range from 80% to 90%, the NO2/NOx emissions remain at a high level. 相似文献