全文获取类型
收费全文 | 122篇 |
免费 | 11篇 |
国内免费 | 31篇 |
专业分类
安全科学 | 12篇 |
废物处理 | 1篇 |
环保管理 | 11篇 |
综合类 | 80篇 |
基础理论 | 27篇 |
污染及防治 | 15篇 |
评价与监测 | 10篇 |
社会与环境 | 4篇 |
灾害及防治 | 4篇 |
出版年
2024年 | 1篇 |
2023年 | 1篇 |
2022年 | 2篇 |
2021年 | 8篇 |
2020年 | 2篇 |
2019年 | 1篇 |
2018年 | 4篇 |
2017年 | 3篇 |
2016年 | 6篇 |
2015年 | 3篇 |
2014年 | 3篇 |
2013年 | 15篇 |
2012年 | 14篇 |
2011年 | 17篇 |
2010年 | 14篇 |
2009年 | 9篇 |
2008年 | 12篇 |
2007年 | 7篇 |
2006年 | 10篇 |
2005年 | 4篇 |
2004年 | 4篇 |
2003年 | 2篇 |
2002年 | 6篇 |
2001年 | 2篇 |
2000年 | 2篇 |
1999年 | 2篇 |
1998年 | 1篇 |
1997年 | 3篇 |
1994年 | 1篇 |
1990年 | 2篇 |
1986年 | 1篇 |
1983年 | 1篇 |
1972年 | 1篇 |
排序方式: 共有164条查询结果,搜索用时 15 毫秒
1.
Longhurst J 《Environmental monitoring and assessment》2005,111(1-3):27-42
Denmark has a long tradition of monitoring the aquatic environment. Previous monitoring has mainly focused on loss of nutrients
and subsequent impacts on the biological structure in lakes and coastal areas. However, as part of the third Action Plan for
the Aquatic Environment more emphasis has been put on stream ecology. The present paper describes background, strategy and
content of the new NOVANA stream programme, which will run for the period 2004–2009. The new programme will encompass more
than 800 stations covering all stream types in Denmark and monitoring will include three biological quality elements (macrophytes,
macroinvertebrates and fish) as well as physico-chemical features and hydromorphological elements. In addition, the new programme
integrates monitoring of elements both in the stream itself and in the riparian zone. Compliance with important European Commission
Directives such as the Water Framework Directive and the Habitat Directive is discussed. 相似文献
2.
Andrew D. Kennedy 《Environmental monitoring and assessment》1997,48(2):173-192
Identifying process from pattern is one of the most vexing tasks inenvironmental monitoring. Given information on the distribution of speciesin a pre-defined area, together with comprehensive data on how environmentalconditions in that area have altered through time, is it possible toidentify the factors controlling the species‘ layout? Here, the practicalsignificance of this quandary is demonstrated using a series ofenvironmentally-degraded coastal lagoons in New South Wales. The TuggerahLakes (33°17′S,151°30′E) have over the last 50 yearsexperienced significant changes in species‘ distributions. Seagrasses,macroalgae, phytoplankton, molluscs, prawns and the jellyfish Catostylus mosaicus have altered in spatial pattern. Two human activitieshave been blamed for these perturbations: (1) agricultural clearance ofnative vegetation from the catchment, with associated input of top-soil andnutrients; (2) the commissioning of a coal-fired power station in 1967, withmassive uptake and recirculation of lake water for cooling purposes. In thispaper, spatial changes in macrophyte distributions over the last 50 yearsare reviewed in an attempt to identify the true source(s) of perturbation.The model adopted assumes that the power station is a point source of impactwhile nutrient inputs from the catchment are a diffuse source of impact;changes in species distributions can hypothetically be related back to thesesources according to whether they are localised or widespread. However,after a comprehensive analysis of available macrophyte data derived frominterviews, aerial photography and line transect methodologyies theconclusion is reached that changes in biogeographical pattern around theTuggerah Lakes cannot be attributed to specific anthropogenic pressures atanything beyond the coarsest of levels. This is considered to be the normfor most coastal management situations where natural background variation(’noise‘) and the complexity of linkages between physical, chemical andbiological components confounds the identification of causal relationships.The practical implications of this conclusion are discussed in the contextof litigation and remedial management design. Emphasis is placed on theneed to adopt an adaptive approach to estuarine management, incorporatingexplicit recognition of the limitations of available data, and to developnew techniques for identifying cause-effect relationships. 相似文献
3.
M.E.Soltan 《环境科学学报(英文版)》2002,14(4):464-473
IntroductionAswangovernorate ,Egypt ,isfamousforbymonuments (Ancient,CopticandIslamic) .Thefoundationareofthefirstimportanceandcareshouldbetakentoseethattheyareconsolidatedandprotectedasforaspossiblefromtheinfiltrationofwater.Waterisamajorcauseofdamage ,no… 相似文献
4.
5.
关于防范环境突发事件的探索和思考 总被引:2,自引:0,他引:2
从环保工作实际出发,阐述了防范环境突发事件的3个长效机制,即排查潜在事故隐患,建立信息系统;依据信息指标,建立预警系统;控制污染事态,构建应急处理系统. 相似文献
6.
基于2009年-2015年重庆市突发环境事件统计数据,研究了重庆市近7年突发环境事件的动态变化趋势、空间分布格局及污染影响特征,讨论了引发突发环境事件内外部因素之间的关系.结果表明:重庆市7年内共发生突发环境事件134起,且呈波动下降趋势,春季和夏季为交通事故和自然灾害高发期;突发环境事件空间上主要集中在主城九区及相邻的区县,渝西、渝东南及渝东北各区县发生次数较少.道路交通事故、设备故障和操作不当是导致突发环境事件的主要因素,主要发生形式为泄漏.污染类型主要为水污染和水气复合污染,污染物出现频率大小为:油类>酸碱类>液氨>苯及其化合物>减水剂>其他各种污染物. 相似文献
7.
淀山湖沉水植物死亡分解过程中营养物质的释放 总被引:8,自引:0,他引:8
测定了上海淀山湖5种常见沉水植物的营养成分含量及其死亡后在好氧(DO>3.5 mg/L)或低氧(DO<3.5 mg/L)状态下分解释放TN、TP和有机物(以高锰酸盐指数计,下同)等营养物质的动态过程,并对营养物质释放强度与营养成分含量的相关性进行了分析.结果表明, 5种沉水植物中,金鱼藻的TN和TP含量最高,质量分数分别为(4.07±0.22)%和(0.99±0.09)%;好氧状态下TN和有机物的释放强度大于低氧状态,两种状态下TP的释放强度没有显著差异;TP的释放比TN快,一般需10 d左右,而TN和有机物的释放分别需要29 d和20 d左右;在好氧状态下,NO-2-N、NO-3-N和可溶性总磷酸盐的平均释放强度与植物TN含量呈显著正相关(p<0.05),NH 4-N的平均释放强度与植物TP含量呈显著正相关(p<0.05);在低氧状态下,NO-2-N的平均释放强度与植物TN含量、NO-3-N的平均释放强度与植物TP含量分别呈显著正相关(p<0.05);有机物的平均释放强度与植物TP含量呈极显著负相关(p<0.01). 相似文献
8.
Küster A Pohl K Altenburger R 《Environmental science and pollution research international》2007,14(6):377-383
Background, Goals and Scope During the last years the miniaturization of toxicity test systems for rapid and parallel measurements of large quantities
of samples has often been discussed. For unicellular algae as well as for aquatic macrophytes, fluorescence-based miniaturized
test systems have been introduced to analyze photosystem II (PSII) inhibitors. Nevertheless, high-throughput screening should
also guarantee the effect detection of a broad range of toxicants in order to ensure routinely applicable, high-throughput
measuring device experiments which can cover a broad range of toxicants and modes of action others than PSII inhibition. Thus,
the aim of this study was to establish a fast and reproducible measuring system for non-PSII inhibitors for aquatic macrophyte
species to overcome major limitations for use.
Methods A newly developed imaging pulse-amplitude-modulated chlorophyll fluorometer (I-PAM) was applied as an effect detector in short-term
bioassays with the aquatic macrophyte species Lemna minor. This multiwell-plate based measuring device enabled the incubation and measurement of up to 24 samples in parallel. The
chemicals paraquat-dichloride, alizarine and triclosan were chosen as representatives for the toxicant groups of non-PSII
herbicides, polycyclic aromatic hydrocarbons (PAHs) and pharmaceuticals and personal care products (PPCPs), which are often
detected in the aquatic environment. The I-PAM was used (i) to establish and validate the sensitivity of the test system to
the three non-PSII inhibitors, (ii) to compare the test systems with standardized and established biotests for aquatic macrophytes,
and (iii) to define necessary time scales in aquatic macrophyte testing. For validation of the fluorescence-based assay, the
standard growth test with L. minor (ISO/DIS 20079) was performed in parallel for each chemical.
Results The results revealed that fluorescence-based measurements with the I-PAM allow rapid and parallel analysis of large amounts
of aquatic macrophyte samples. The I-PAM enabled the recording of concentration-effect-curves with L. minor samples on a 24-well plate with single measurements. Fluorescence-based concentration-effect-curves could be detected for
all three chemicals after only 1 h of incubation. After 4–5 h incubation time, the maximum inhibition of fluorescence showed
an 80–100% effect for the chemicals tested. The EC50 after 24 h incubation were estimated to be 0.06 mg/L, 0.84 mg/L and 1.69
mg/L for paraquatdichloride, alizarine and triclosan, respectively.
Discussion The results obtained with the I-PAM after 24 h for the herbicide paraquat-dichloride and the polycyclic aromatic hydrocarbon
alizarine were in good accordance with median effective concentrations (EC50s) obtained by the standardized growth test for
L. minor after 7 d incubation (0.09 mg/L and 0.79 mg/L for paraquat-dichloride and alizarine, respectively). Those results were in
accordance with literature findings for the two chemicals. In contrast, fluorescence-based EC50 of the antimicrobial agent
triclosan proved to be two orders of magnitude greater when compared to the standard growth test with 7 d incubation time
(0.026 mg/L) as well as with literature findings.
Conclusion Typically, aquatic macrophyte testing is very time consuming and relies on laborious experimental set-ups. The I-PAM measuring
device enabled fast effect screening for the three chemicals tested. While established test systems for aquatic macrophytes
need incubation times of ≥ 7 d, the I-PAM can detect inhibitory effects much earlier (24 h), even if inhibition of chemicals
is not specifically associated with PSII. Thus, the fluorescence-based bioassay with the I-PAM offers a promising approach
for the miniaturization and high-throughput testing of chemicals with aquatic macrophytes. For the chemical triclosan, however,
the short-term effect prediction with the I-PAM has been shown to be less sensitive than with long-term bioassays, which might
be due to physicochemical substance properties such as lipophilicity.
Recommendations and Perspectives The results of this study show that the I-PAM represents a promising tool for decreasing the incubation times of aquatic macrophyte
toxicity testing to about 24 h as a supplement to existing test batteries. The applicability of this I-PAM bioassay on emergent
and submerged aquatic macrophyte species should be investigated in further studies. Regarding considerations that physicochemical
properties of the tested substances might play an important role in microplate bioassays, the I-PAM bioassay should either
be accompanied by evaluating physicochemical properties modeled from structural information prior to an experimental investigation,
or by intensified chemical analyses to identify and determine nominal concentrations of the toxicants tested. The chemicals
paraquat-dichloride, alizarine and triclosan were chosen as representatives for the toxicant groups of non-PSII herbicides,
PAHs and PPCPs which are often detected in the aquatic environment. Nevertheless, in order to ensure a routinely applicable
measuring device, experiments with a broader range of toxicants and samples of surface and/or waste waters are necessary.
ESS-Submission Editor: Dr. Markus Hecker (MHecker@Entrix.com) 相似文献
9.
将突发事件应对能力分为一般应对能力和特殊应对能力,以大学生为样本编制量表,在社会居民中验证其适用性,量表有良好的信效度和适用性。对浙江省11个地区的居民抽样调查表明,积极行为能力强于情绪管理能力,传染疾病和火灾应对能力比较强,食物中毒应对能力比较弱;城市居民强于农村居民,男性比女性强;社会居民强于大学生,50岁以下的比较强;机关干部最强,农民最弱;受训者强于未受训者,受训者太少。突发事件应对训练竭待加强。 相似文献
10.