Примеры использования Nitrates directive на Английском языке и их переводы на Русский язык
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The EU Nitrates Directive was also referred to.
This is largely driven by stricter environmental legislation such as the Nitrates Directive.
Emissions reduction effects of the NECD and Nitrates Directive after the year 2000 were small.
Implementation of the Nitrates Directive is likely to result in further improvements in the quality of both surfaces waters and groundwater.
An expert from the Czech Republic reported on nitrogen management in Czech agriculture with particular reference to the EU Nitrates Directive.
Legislation such as the Nitrates Directive(EC 91/676) seeks to limit nutrient losses from farming to freshwater bodies.
Furthermore, Finland referred to the current revision process for its Nitrate Decree(931/2000) which implements the EU Nitrates Directive.
Some 1,235 km2 has been designated as vulnerable according to the Nitrates Directive in the Czech part of the Oder/Odra Basin, 9,713 km2 in the German part, and 3,437 km2 in the Polish part.
The Nitrates Directive(91/676/EEC) requires the identification of groundwater sites/bodies where the annual average nitrate concentration exceeds or could exceed 50 mg NO3/l.
For many intensively-farmed areas,the programmes of measures developed under the Nitrates Directive will not, by themselves, necessarily be enough to restore water quality.
The Nitrates Directive which caps the total application of N from animal manures to 170 kg N/ha and restricts application of manure and inorganic fertilizer in situations with high risk of N loss.
Lack of secondary legislation concerning the implementation of WFD, Nitrates Directive and the Urban Waste Water Directive, which should be developed in both countries similarly to Romania.
For Serbia and Romania, it was helpful not only in implementation of the EU WFD, butalso of other water-related directives such as the Floods Directive, the Nitrates Directive and the Groundwater Directive.
EU water-related legislation, such as the Nitrates Directive and the Water Framework Directive, EU Common Agricultural Policy and agri-environmental measures.
The system is gradually being extended toincorporate reporting of the Bathing Water Directive(2006/7/EC), the Urban Wastewater Directive(91/271/EEC), the Nitrates Directive(91/676/EEC) and the Drinking Water Directive 98/83/EC.
Fulfilling the requirements of the Nitrates Directive and the Urban Wastewater Treatment Directive are for EU countries the fundamental measures for reducing nutrient load at basin level.
Based on review work in the European Nitrogen Assessment(ENA), a threshold for nitrogen effects in fresh water bodies had been identified of 2 mg per litre,which was much more stringent than the limit established by the EU Nitrates Directive.
The implementation of the Urban Wastewater Treatment Directive and the implementation of the EU Nitrates Directive are decisive steps to significantly improve the status of the Tisza in Hungary and its tributaries in Slovakia and Romania.
In the context of groundwater these areas may include Natura 2000 sites established under the Habitats Directive(92/43/EC) orthe Birds Directive(79/409/EC), Nitrate Vulnerable Zones established under the Nitrates Directive(91/676/EC);
For reduction of nutrient pollution, implementation of basic measures according to the EU Nitrates Directive and the Urban Wastewater Directive are central, and in the case of groundwater vulnerability, so is mapping for land use planning.
The Ministry of Agriculture has developed a codex of good agricultural practice ensuring the protection of water against nitrates through the implementation of Council Directive 91/676/EEC concerning the protection of water against pollution caused by nitrates from agricultural sources(the Nitrates Directive), and is responsible for its implementation.
For urban wastewater and the Nitrates Directive, the reporting is slightly out of phase, with the Urban Wastewater Directive foreseeing reporting every two years, and the Nitrates Directive reporting every four years.
Considering the increase in springtime NH3 emissions that had occurred in implementing some policies such as the EU Nitrates Directive, further research was recommended to quantify the seasonal dependence of environmental impacts of NH3.
The fact that current Nr emission reduction policies in agriculture(e.g., EU Nitrates Directive, OSPAR Commission for the Protection of the Marine Environment of the North-East Atlantic, ECE Gothenburg Protocol and EU National Emissions Ceilings Directive) have only made limited progress can be linked in part to the large number of diverse actors(including many small farms), the diffuse nature of the Nr emission sources, and the challenge of passing any perceived costs onto consumers 4.5.
In the context of the European Union, these include the Habitats Directive, the Birds Directive, the Water Framework Directive, the Marine Strategy Framework Directive, the Nitrates Directive, the Common Agricultural Policy and the Common Fisheries Policy.
The reporting regimes which exist for the Urban Waste Water Treatment Directive, Nitrates Directive, Bathing Water Directive, and Drinking Water Directive also include data and information relevant for implementation of the Water Convenrtion.
These include the introduction of three-way catalysts in vehicles, which increased NH3 and N2O emissions(although overall Nr emissions were still greatly reduced),and the implementation of the Nitrates Directive, prohibiting wintertime manure spreading, which has led to a new peak in springtime NH3 emissions 9.2.
On the basin-wide level, basic measures(fulfilling the UWWTD and EU Nitrates Directive) for EU member States and the implementation of the ICPDR Best Agricultural Practices Recommendation for non-EU countries are the main measures contributing to nutrient reduction.
The main pressures on water resources are documented as a result of the implementation of the Urban Waste Water Treatment Directive(1991), the Integrated Pollution Prevention andControl Directive(1996) and the Nitrates Directive(1991- on nitrates for agricultural sources), as well as the Directive on Pollution Caused by Certain Dangerous Substances Discharged into the Aquatic Environment of the Community 1976.
The Task Force noted that this work should:(a) identify information requirement of various policy processes dealing with nitrogen,e.g. the European Union(EU) Nitrates Directive, to avoid pollution swapping and enable integrated assessment modelling;(b) make full use of existing work of the Convention; and(c) advise how various policy targets could be met in a cost-effective way.