全文获取类型
收费全文 | 151篇 |
免费 | 12篇 |
国内免费 | 46篇 |
专业分类
安全科学 | 9篇 |
废物处理 | 1篇 |
环保管理 | 19篇 |
综合类 | 96篇 |
基础理论 | 29篇 |
污染及防治 | 25篇 |
评价与监测 | 5篇 |
社会与环境 | 23篇 |
灾害及防治 | 2篇 |
出版年
2023年 | 5篇 |
2022年 | 4篇 |
2021年 | 7篇 |
2020年 | 9篇 |
2019年 | 6篇 |
2018年 | 8篇 |
2017年 | 9篇 |
2016年 | 14篇 |
2015年 | 9篇 |
2014年 | 6篇 |
2013年 | 13篇 |
2012年 | 13篇 |
2011年 | 18篇 |
2010年 | 13篇 |
2009年 | 9篇 |
2008年 | 9篇 |
2007年 | 3篇 |
2006年 | 10篇 |
2005年 | 8篇 |
2004年 | 8篇 |
2002年 | 6篇 |
2001年 | 2篇 |
2000年 | 6篇 |
1999年 | 2篇 |
1998年 | 3篇 |
1996年 | 1篇 |
1995年 | 2篇 |
1994年 | 1篇 |
1991年 | 2篇 |
1987年 | 1篇 |
1982年 | 1篇 |
1979年 | 1篇 |
排序方式: 共有209条查询结果,搜索用时 15 毫秒
1.
Gałuszka A 《Environmental monitoring and assessment》2005,110(1-3):55-70
In June of 2000, biogeochemical study was carried out in three ecosystems of the Holy Cross Mountains (south-central Poland).
This paper presents element concentrations and stable sulfur (and in one site lead) isotope ratios in rocks, detailed soil
profiles, and plant bioindicators including epiphytic lichen Hypogymnia physodes (L.) Nyl., mosses (Pleurozium schreberi (Brid.) Mitt., Hypnum cupressiforme Hedw. S. Str., Hylocomium splendens (Hedw.) B.S.G.), Scots pine (Pinus sylvestris L.), common birch (Betula pendula Roth.), aspen (Populus tremula L.) and English oak (Quercus robur L.). Chemical analyses were performed with ICP-AES and AAS methods in the accredited laboratory (Central Chemical Laboratory
of the Polish Geological Institute in Warsaw). The principal objective of this study was to compare the chemical composition
of rocks, soils and selected plant bioindicators between investigation sites using the same methods of sample collection,
preparation and analyses. The results of this study have shown that there is a high variability in concentrations of elements
in plant bioindicators from the same sites that can not be explained only by soil properties or anthropogenic influence. This
conclusion indicates that for biomonitoring purposes (especially with vascular plants) we cannot neglect individual features
of the species examined. 相似文献
2.
为探明不同宽度沟垄集雨种植下土壤呼吸对土壤水热因子的响应机制,对比研究了沟垄比分别为20 cm∶40 cm(P40)、30 cm∶30 cm(P30)、40 cm∶20 cm(P20)的沟垄集雨种植和平作种植(CP)下冬小麦的土壤呼吸动态变化,及其与土壤温度和水分的关系.结果表明,4个处理的土壤呼吸速率在越冬期最低,返青期开始升高,扬花期前后达到峰值,之后逐渐降低.沟垄集雨处理土壤呼吸速率表现为P40P30P20,垄宽增加使呼吸速率提高1.2%~18.4%;苗期和越冬期,沟垄集雨种植提高了土壤呼吸速率,表现为P40P30P20CP,其中苗期3个沟垄集雨处理均显著高于CP(P0.05),越冬期P40处理显著高于CP;苗期和越冬期沟垄集雨种植提高了土壤温度,拔节期至成熟期CP土壤温度高于沟垄集雨处理;沟垄集雨种植能有效蓄水保墒,随着垄宽的增加集雨效果越好,苗期至拔节期降雨稀少,7.6 cm和12 cm土层土壤含水量均表现为P40P30P20CP.相关分析表明,土壤呼吸与温度的相关系数达极显著水平(P0.01),P40和P30的土壤呼吸与水分的相关系数小于P20和CP;水热双因子二次方程模型能解释呼吸变化的61.7%~74.1%,温度指数模型能解释50.3%~68.2%.本研究结果为沟垄集雨种植的生态效益评估提供理论依据. 相似文献
3.
南京冬季市区和郊区气溶胶中PAHs浓度的昼夜特征及粒径分布 总被引:4,自引:4,他引:0
为了研究南京市区与郊区气溶胶中多环芳烃(PAHs)污染状况和分布特征,利用气-质联用仪(GC-MS)分析了2010年1月1~10日日间和夜间分别在南京大学和南京信息工程大学采集的气溶胶样品,得到南京市区与郊区17种PAHs浓度,总浓度分别为41.36~220.35 ng.m-3和45.10~200.86 ng.m-3,其中约66%~67%分布于细粒子(Dp≤2.1μm)中.研究发现,南京市区和郊区气溶胶中PAH总浓度均处于较高的水平;但两者昼夜变化趋势不同,即市区PAH总浓度日间高于夜间,郊区PAH总浓度日间低于夜间.主导风向的改变和高压天气系统对PAH浓度变化影响较大;在市区其影响主要表现在细粒子部分,而郊区主要表现在粗粒子部分.市区和郊区不同环数的PAHs粒径分布不同;2~3环PAHs,郊区含量高于市区;而4~6环PAHs,市区含量高于郊区.高环数(4~6环)PAHs在粗模态出现较大浓度峰可能是由于南京地区粗模态气溶胶中碳含量较高.市区和郊区相似的特征比值说明两者的PAHs具有相同污染来源,主要为生物质及煤的燃烧和汽车尾气,表明南京市区PAHs受到郊区工业源排放影响较大. 相似文献
4.
青藏高原淡水湖泊水化学组成特征及其演化 总被引:19,自引:12,他引:7
青藏高原淡水湖具有高生态价值和高脆弱性并存的特点.以海拔5 080 m±10 m的打加芒错湖水为研究对象,测试及分析了湖水化学组分,探讨了其主要离子来源、控制因子和湖泊水化学演化趋势.结果表明,湖水阳离子以Ca2+和Na+为主,阴离子以HCO3-为主,为HCO3-Ca型水;TDS为71.2~199.8 mg·L-1,矿化度低;受地表径流的稀释作用和富铝贫钙的地质背景约束湖区东南部水体的EC、Ca2+和HCO3-浓度均较低.湖水的Na+/(Na++Ca2+)为0.08~0.75,Cl-/(Cl-+HCO3-)为0.11~0.35,Ca/Na值为0.58,Mg/Ca值为0.12,HCO3/Na值为1.46,据Gibbs模型和元素化学计量分析表明,其化学组成主要受硅酸盐岩风化控制.湖区流域参与风化的矿物岩石包括斜长石(钙长石、钠长石)、钾长石、云母、石膏、盐岩等,但以斜长石风化为主,湖水的K/Na值平均为0.059,表明流域钾长石风化程度较低.湖水中方解石、白云石、石英、石膏等矿物饱和指数(SI)大于0,石盐的SI则小于0,揭示了青藏高原上淡水湖泊演变成咸水湖的变化趋势. 相似文献
5.
潮白河周丛生物群落元素组成与水质变化的生态计量学关系研究 总被引:2,自引:0,他引:2
研究了潮白河流域中污染水体对周丛生物群落的碳(C)、氮(N)、磷(P)元素含量以及生态计量组成的影响.结果表明,下游潮白河NH4+-N、NOx--N分别占TN的52%和28%;上游白河则分别占1.6%和38%.潮白河TP含量(0.104 mg.L-1)为白河TP含量(0.005 mg.L-1)的21倍.白河和潮白河周丛生物C、N、P元素的变异系数分别为0.55、0.41、0.62和0.24、0.13、0.18,表明生长于白河周丛生物的元素结构变化更大.无周丛生物的水体NH4+-N和TP的浓度分别为有周丛生物的21倍和11倍.通过对TOC、TN、NOx--N、NH4+-N、TP、pH、氧化还原电位(ORP)和电导率(conductivity)等水质指标进行二元Logistic回归分析得知,水体TP为影响潮白河周丛生物生存的主要因素,其预测正确率为87.3%.周丛生物C、N、P元素间有强相关性,其中N起了"桥梁"作用.生态计量学分析进一步显示周丛生物的N∶P的比值追随水体TN∶TP的变化;并且该比值主要受水体TP浓度影响.周丛生物N∶P可用于水体TN∶TP变化的生态计量学的指示因子.本研究为进一步探究周丛生物群落结构变化,以及对高一级营养级生物群落结构和元素循环的影响奠定了基础. 相似文献
6.
基于多目标决策的水污染负荷分配方法 总被引:3,自引:2,他引:1
为科学、合理地配置汇流区域的水污染负荷,从经济最优性、公平性综合决策角度,构建了一个以区域环境经济收益最大化、水污染负荷削减费用和加权综合基尼系数等最小化为目标的水污染负荷分配多目标决策优化模型,并将该模型应用于巢湖流域COD削减负荷分摊中.计算得到合肥市、肥东县、肥西县、巢湖市、庐江县、无为县、含山县、和县和舒城县等... 相似文献
7.
中国地区经济差距及其演化的产业变动因素 总被引:9,自引:0,他引:9
敖荣军 《长江流域资源与环境》2007,16(4):420-420
20世纪90年代以来中国地区经济差距扩大具有深刻的产业变动原因。以人均GDP为基本指标,通过对基尼系数进行产业分解和对泰尔指数进行地区分解,深刻分析了1990~2004年中国地区经济差距的动态变化、地区构成和产业构成,揭示了中国地区经济差距及其演变的产业结构变动与产业地区集中因素。结果表明,1990年以来中国地区经济差距的决定性因素是第二产业发展水平的地区差距,而非农产业向东部沿海地区的集中又是推动中国地区经济差距扩大的主导性因素。20世纪90年代以来,随着以制造业为主的非农产业向东部沿海地区集中,中西部地区逐渐沦落为以农业与采掘业为主的外围区域,中国的地区经济差距也由此持续扩大。基于此,认为缩小地区差距的关键是推进中西部地区制造业发展,缓解非农产业地区分布的不平衡状况。 相似文献
8.
Monitoring of eutrophication and nutrient limitation in the Izmir Bay (Turkey) before and after Wastewater Treatment Plant 总被引:3,自引:0,他引:3
The distribution of inorganic nutrients and phytoplankton chlorophyll-a was investigated and N/P ratios were determined in Izmir Bay during 1996-2001. The average concentrations showed ranges of 0.01-0.19 and 0.01-10 microM for phosphate-phosphorus; 0.11-1.8 and 0.13-27 microM for (nitrate+nitrite)-nitrogen, 0.30-4.1 and 0.50-39 microM for silicate and 0.02-4.3 and 0.10-26 microg l(-1) for chlorophyll-a in the outer and middle-inner bays, respectively. The results are compared with the values obtained from the relatively unpolluted waters of the Aegean Sea. The N/P ratio is significantly lower than the assimilatory optimal (N/P=15:1) in conformity with Redfield's ratio N/P=16:1. Nitrogen is the limiting element in the Izmir Bay. Phosphate, which originates from detergents, is an important source for eutrophication in the bay, especially in the inner bay. In early 2000, a Wastewater Treatment Plant (WTP) began to treat domestic and industrial wastes. This plant treats the wastes about 60% capacity between 2000 and 2001. The sampling periods cover before and after treatment plant. Although the capacity of wastewater plant is sufficient for removal of nitrogen from the wastes, it is inadequate for removal of phosphate. This is also in accordance with the decreasing N/P ratios observed during 2000-2001 (after WTP) in the middle-inner bays. 相似文献
9.
E. Susan Boydstun Terry Nelson Roger B. Long 《Journal of the American Water Resources Association》1979,15(4):1086-1095
ABSTRACT: Public investments in water resource development projects are continually under scrutiny in terms of economic, environmental, and social impacts. Results of an analysis of a water development project that supplies irrigation water in Idaho are discussed in terms of the impact on income distribution and income growth 44 to 64 years after the project was initiated. Gini ratios for the rural farm population of these counties were consistently lower than they were for the United States as a whole and for the state of Idaho. In addition, income distributions tended to become more equitable over time in the water project counties. Rural farm population income growth rates were found to be similar to those for the nation as a whole. Some of the reasons for these results may be related to the tendency for income distribution to become more equitable as income increases, and the fact that average farm size is relatively small. 相似文献
10.
The relationship between diversity profiles,evenness and species richness based on partial ordering 总被引:4,自引:0,他引:4
Rousseau Ronald Van Hecke Piet NIjssen David Bogaert Jan 《Environmental and Ecological Statistics》1999,6(2):211-223
Problems with the notion of evenness, such as ambiguity, proliferation of indices, choice of indices, etc. can be overcome by a more fundamental, mathematical approach. We show that the Lorenz curve is an adequate representation of evenness. The corresponding Lorenz order induces a partial order in the set of equivalent abundance vectors. Also diversity can adequately be studied through a partial order and represented by a curve derived from the classical Lorenz curve. This curve is known as the intrinsic diversity profile (or k-dominance curve) and was introduced by Patil and Taillie (1979) and Lambshead et al. (1981). 相似文献