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91.
Many smallholder farmers in vulnerable areas continue to face complex challenges in adoption and adaptation of resource management and conservation strategies. Although much has been learned from diverse experiences in sustainable resource management, there is still inadequate understanding of the market, policy and institutional failures that shape and structure farmer incentives and investment decisions. The policy and institutional failures exacerbate market failures, locking smallholder resource users into a low level equilibrium that perpetuates poverty and land degradation. Improved market access that raises the returns to land and labor is often the driving force for adoption of new practices in agriculture. Market linkages, access to credit and availability of pro-poor options for beneficial conservation are critical factors in stimulating livelihood and sustainability-enhancing investments. Future interventions need to promote joint innovations that ensure farmer experimentation and adaptation of new technologies and careful consideration of market, policy and institutional factors that stimulate widespread smallholder investments. Future projects should act as ‘toolboxes’, giving essential support to farmers to devise complementary solutions based on available options. Addressing the externalities and institutional failures that prevent private and joint investments for management of agricultural landscapes will require new kinds of institutional mechanisms for empowering communities through local collective action that would ensure broad participation and equitable distributions of the gains from joint conservation investments. Readers should send their comments on this paper to: BhaskarNath@aol.com within 3 months of publication of this issue.  相似文献   
92.
This article aims to highlight the current status of compliance to Machinery Directive 98/37/EC (transposed to Spanish regulation as RD 56/1995, of 20th January) (a new directive numbered as 2006/42/EC [Directive 2006/42/EC of the European Parliament and of the Council of 17 may 2006 on machinery, and amending Directive 95/16/EC (recast). OJ L157/24-86, 9.6.2006.], that recasts and replaced 98/37/ED directive and its amendments, came into force on 29 June 2006; it will not be applied until 29th December 2009. European Member States have a lead-time of two years to adopt and publish the national laws and regulations transposing the provisions of the new Directive into national law. Latest 10th October, Spain transposed Machinery Directive 2006/42/EC to national regulation as Real Decreto 1644/2008 [Real Decreto 1644/2008, de 10 de octubre, por el que se establecen las normas para la comercialización y puesta en servicio de las máquinas. BOE 246/2008, de 11 octubre 2008. Páginas 40995–41030]) of a particular family of machinery (hand-held, medium and small-size, deeply introduced in the market, of low-medium cost), that any user, professional or non-professional, can acquire as first-hand in any of the sales points (whether or not experts in these kind of products).At the same time, it emphasises the most significant shortcomings and non-conformities found, after analyzing the results of five consecutive Campaigns of Control of Industrial Products performed by one of the labs (placed in Spain) involved in the market surveillance European Program.  相似文献   
93.
Transformation toward a sustainable future requires an earth stewardship approach to shift society from its current goal of increasing material wealth to a vision of sustaining built, natural, human, and social capital—equitably distributed across society, within and among nations. Widespread concern about earth’s current trajectory and support for actions that would foster more sustainable pathways suggests potential social tipping points in public demand for an earth stewardship vision. Here, we draw on empirical studies and theory to show that movement toward a stewardship vision can be facilitated by changes in either policy incentives or social norms. Our novel contribution is to point out that both norms and incentives must change and can do so interactively. This can be facilitated through leverage points and complementarities across policy areas, based on values, system design, and agency. Potential catalysts include novel democratic institutions and engagement of non-governmental actors, such as businesses, civic leaders, and social movements as agents for redistribution of power. Because no single intervention will transform the world, a key challenge is to align actions to be synergistic, persistent, and scalable.  相似文献   
94.
A FS-830型双道原子荧光光度计常见故障及排除方法   总被引:1,自引:0,他引:1  
以吉天AFS-830型双道原子荧光光度计为例,介绍了仪器使用过程中出现的联机失败、管路不畅、自动进样器停止工作等常见故障,分析了故障产生的原因,并提出了排除方法。  相似文献   
95.
选取我国废弃电器电子产品中回收处理数量最多、获得政策基金补贴最多的电视机产品,通过对其销量、最长使用年限、报废高峰期、报废系数的分析,采用市场供给A模型测算其报废产生量,并进一步对废弃电视机产生量测算结果与实际处理量做对比分析,提出废电视机产生量的修正方法。最终测算得到废电视机产生量为4 213万台,与同年电视机的实际处理量持平。  相似文献   
96.
冷宇祥 《四川环境》2001,20(2):74-76
本文就当前个别地方排污收费中存在的问题进行了阐述,并提出在市场经济体制下如何依法征收排污费的一些建议。  相似文献   
97.
Guo Y  Zhang J  Yu R  Zhu KY  Guo Y  Ma E 《Chemosphere》2012,86(7):709-717
Composite samples of Australian farmed Yellowtail Kingfish (Seriola lalandi) (YTKF) (n = 27), Mulloway (Argyrosomus hololepidotus) (n = 6) and manufactured feed (n = 5) were analysed to benchmark levels of a broad range of residues and contaminants of potential public health and trade significance. A subset of these samples [YTKF (n = 5), Mulloway (n = 2) and feed (n = 5)] was analysed for dioxins and polychlorinated biphenyls (PCBs). The mean concentration of dioxins in YTKF was 0.6 pg TEQ g−1 (range 0.22-0.8) and in Mulloway was 0.16 pg TEQ g−1 (range 0.16-0.16). The mean concentration of dioxins and dioxin-like PCBs in YTKF was 2.6 pg TEQ g−1 (range 1.4-3.5), while Mulloway had a mean concentration of 0.67 pg TEQ g−1 (range 0.57-0.76). The mean concentration of PCBs in YTKF was 21 μg kg−1 (range 8.6-29) and in Mulloway was 5.4 μg kg−1 (mean 4.7-6). The mean concentration of dioxin-like PCBs in YTKF was 2.1 pg TEQ g−1 (range 1.2-2.8) and in Mulloway was 0.51 pg TEQ g−1 (range 0.41-0.61). The mean mercury concentration in YTKF was 0.03 mg kg−1 (range 0.02-0.05) and in Mulloway it was 0.02 mg kg−1 (range 0.02-0.04). There were no detectable levels of any pesticide or antimicrobial compounds in any sample of YTKF or Mulloway. Attention is drawn to technical differences in port of entry testing programs such as sampling strategies, portion tested, laboratory methodology, residue definitions and reporting conventions that exporters’ products may be subject to. All residues and contaminants were either undetectable or present at very low levels when judged against Australian, Japanese and European Union regulatory standards (where set).  相似文献   
98.
In this paper, we present a simple theoretical extension from the Economic Geography literature to characterize the main features of pollution havens (lax environmental regulation, good market access to high-income countries and corruption opportunities). Using structural and reduced-form estimations, we find that pollution havens are not a “popular myth” for European firms, laxer environmental standards significantly explain the location choice of polluting affiliates. We analyze in depth the role of trade costs (using various bilateral and multilateral measures), a 1% increase in access to the European market from a pollution haven fosters relocation there by 0.1%. We also find that corruption lowers environmental standards, which strongly attract polluting firms: a 1% increase of corruption fuels relocation by 0.28%. We test the economic significance of these empirical findings via simulations. The protection of the European market (e.g., a carbon tax on imports) to stop relocations to pollution havens must be high (a decrease of the European market for Morocco and Tunisia equivalent to 13%) not to say prohibitive (31% for China).  相似文献   
99.
Fresh and pasteurized milk samples from Kampala markets were analyzed for organochlorine pesticides using a gas chromatograph equipped with an electron capture detector. Five organochlorine pesticides, namely; aldrin, dieldrin, endosulfan, lindane, DDT and its metabolites were detected in the milk samples and confirmed with a gas chromatograph equipped with a mass spectrometer [GC-MS]. The mean values are expressed in mg kg−1 milk fat (mf) basis. The mean concentration in the fresh milk (= 54) were: 0.026 ± 0.003 mg kg−1 mf; 0.002 ± 0.0003 mg kg−1, below the detection limit; 0.007 ± 0.003 mg kg−1, 0.009 ± 0.002 mg kg−1 milk fat for lindane, endosulfan dieldrin and aldrin, respectively. The mean concentrations of p,p′-DDE; p,p′-DDT and o,p′-DDT were 0.009 ± 0.002 mg kg−1; 0.033 ± 0.007 mg kg−1 and 0.008 ± 0.001 mg kg−1 mf, respectively in the fresh milk samples.In the pasteurized milk samples (= 47), the mean concentrations recorded were: 0.008 ± 0.003 mg kg−1, 0.025 ± 0.004 mg kg−1, and 0.007 ± 0.001 mg kg−1, respectively for p,p′-DDE; p,p′-DDT and o,p′-DDT.Alpha and beta-endosulfan recorded the concentration below the detection limit and the mean of 0.022 ± 0.001 mg kg−1 mf, 0.005 ± 0.002 mg kg−1 mf, and 0.006 ± 0.0002 mg kg−1 mf, respectively for lindane, dieldrin and aldrin. Although, most of the residues detected were above the residue limits set by the FAO/WHO (2008), bioaccumulation of these residues is likely to pose health risks to the consumers of milk in Uganda.  相似文献   
100.
作为一种新型环境政策,排污权交易在美国已经成功地演进为总量控制型排污权交易,这被认为是最接近市场经济的环境管理手段。在国内,排污权交易也日益受到政府的重视。自1988年以来,中国的许多地方都先后试点了排污权交易,但多停留在补偿政策,很少有关于总量控制型排污权交易的尝试。在政策设计的技术层面,造成这种状况的一个主要原因是缺乏有效的排污权初始分配结构设计框架。为此,在区域清洁激励市场计划排污权初始分配结构的基础上,针对渐进式减排战略指导下的总量控制型排污权交易计划,分纵向结构设计和横向结构设计两部分,提出了一种具有通用性的排污权初始分配结构设计框架。这有助于合理进行排污权初始分配。  相似文献   
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