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See the copyright notice Conditions of use .
In accordance with the decision of the Council of State for the presentation of the Ministry of the Environment, the Act of 30 December 2004 on the organisation of (1299/2004) Articles 10, 20 and 26 Pursuant to:
This Regulation provides for studies to be included in the river basin management plan, the assessment and monitoring of water status and the preparation of a river basin management plan.
Law on the organisation of water management (1299/2004) , the river basin management plan referred to in Article 11 shall be drawn up for a period of six years. The first river basin management plans shall be prepared so that they are adopted by 21 December 2009 at the latest.
The Centre for Food, Transport and the Environment defines the location and boundaries of surface water and groundwater areas in its territory, as well as groundwater, of which surface water ecosystems and terrestrial ecosystems are directly dependent. (7 OCTOBER 2010/869)
The characteristics of the sampling, the assessment of the water status and the monitoring and monitoring of similar surface waters and groundwater can be considered as a group.
The Centre for Enterprise, Transport and the Environment shall compile the information on the following areas within its territory:
(1) an area which is or is to be taken into account for more than 10 cubic metres per day or more than the needs of more than 50 people;
(2) an area defined as a bathing water under European Union law;
(3) A Natura 2000 network area where maintenance or improvement of water status is important for the protection of the environment or species.
(7 OCTOBER 2010/869)In addition, the areas identified for the protection of economically significant aquatic species are laid down in the Council Decision (192/1999) On the quality of inland waters needing protection and improvement, in order to safeguard the living conditions of fish and, in addition, the nutrient-sensitive areas of the Council Regulation (1999) Restricting access to waters of nitrates from agricultural sources. (7 OCTOBER 2010/869)
On the quality of inland waters needing protection and improvement in order to safeguard the living conditions of fish 1172/1999 Has been repealed with A 1281/2014 . Limitation of access to waters of nitrates from agricultural sources 931/2000 Has been repealed by Vnato on the limitation of emissions from certain agricultural and horticultural products 1250/2014 , which is valid from 1 April 2015.
In accordance with Article 22 of the Water Management Act, an artificial surface water body may be designated in the river basin management plan to designate a reservoir and a canal built on a land, and by means of the construction, regulation or otherwise of a highly modified surface water body. The modified surface water body, the original hydrologic-morphological conditions are no longer dominant.
The Centre for Food, Transport and the Environment, in its territory, gathers information on the human activity of the state of surface and groundwater significantly. These include:
(1) for installation, industry, agriculture, forestry and other industrial activities, including in the Council Regulation on hazardous and harmful substances (1022/2006) Emissions of substances intended for use;
(2) the number of settlements, industry, agriculture, forestry and other water needs, as well as the formation of artificial groundwater including seasonal variations, the total annual need and the loss of water;
(3) the construction of surface water and the water rationing;
(4) other activities affecting the status of water, including Directive 2000 /60/EC of the European Parliament and of the Council establishing a framework for Community action in the field of water policy, hereinafter referred to as: Water Framework Directive The activities referred to in Annex II.
On the basis of the information referred to in Article 6 and the information on the state of the water, the Centre for Food, Transport and the Environment shall determine surface and groundwater bodies which may not achieve the environmental objectives referred to in Article 21 of the Water Management Act. If it is estimated that the environmental objectives may not be met, the industry, transport and the Environment Agency should submit further reports for the preparation of monitoring and operational programmes for surface water and groundwater. (7 OCTOBER 2010/869)
This information shall be compiled on the basis of the monitoring by the various authorities and bodies of the State and local authorities and the bodies providing public services, as well as monitoring and surveys carried out by operators under other legislation.
For the purposes of this chapter, the financial statement of the use of water shall be:
(1) Use of water Water services and other activities within the meaning of Article 6;
(2) Water services Surface and groundwater extraction, damping, storage, processing and distribution, as well as the collection and treatment of waste water, which are provided as services.
The economic report of the water use shows, at least in industry, households and agriculture, the assessment of the economic importance of water uses, water supply and long-term forecasts, water services Economic analysis and the most cost-effective combinations of water use for operational programmes.
The financial statement of the water services includes calculations of the calculation of the cost recovery principle in water services.
The Ministry of the Environment, in cooperation with the Ministry of Agriculture and Forestry, directs the industry, transport and environmental centres and the Finnish Environment Agency to draw up a financial report on the use of water.
For the purposes of this Chapter, the classification of the ecological status of surface water is:
(1) Biological factors Phytoplankton, coating, macroalgae, other aquatic vegetation, demersal species and fisheries;
(2) Hydrologic morphological factors The flow conditions, the delay, the height of the water, the depth ratios, the base and the structure of the beach zone, and the connection to groundwater;
(3) Physico-chemical agents The substances referred to in point D of Annex 1D to the Council Regulation on visual depth, temperature, oxygen conditions, salinity, acidification, nutrient conditions and nationally selected hazardous and harmful substances; (7 OCTOBER 2010/869)
(4) Reference conditions The values of the elements referred to in paragraphs 1 to 3, which correspond to the total or almost completely undisturbed ecological conditions;
(5) The ecological quality ratio A deviation from the comparative conditions of biological factors indicating the ecological status.
The factors referred to in paragraphs 1 to 3 in the river, lake and coastal waters are given in more detail in Annex 1 and Annex V to the Water Framework Directive. (7 OCTOBER 2010/869)
For the purposes of this Chapter, the classification of groundwater status:
(1) On a quantitative holding The extent to which direct and indirect water abstraction affects the body of groundwater;
(2) Available aquifers available The long-term average values of the quantity of water forming part of the groundwater body, taking into account the impact on surface water and terrestrial ecosystems in relation to groundwater.
(7 OCTOBER 2010/869)For the purpose of classifying surface water for the purpose of classifying the ecological status of surface water, the centre of life, transport and the environment shall allocate surface waters of the same nature to river, lake and coastal waters as well as to the river-changing areas as set out in Annex 2 Based on. In addition to Annex 2, the breakdown shall apply as set out in Annex II to the Water Framework Directive. (7 OCTOBER 2010/869)
Artificial and highly modified surface water bodies are to be broken down by characteristic predominantly of the corresponding surface water type.
In the river basins, surface waters can be examined as a whole, taking into account the lake characteristics of the rivers and the river characteristics of the lakes.
For each surface water type, the reference conditions shall be determined according to the specifications of the excellent condition set out in Annex 1.
In accordance with Article 8 of the Water Management Act, the Centre for Enterprise, Transport and the Environment classifies surface water and groundwater in its territory for a river basin management plan.
In the field of fisheries related tasks, the Centre for Life, Transport and the Environment and the Natural Resources Centre shall provide the information necessary for the classification of the industry, transport and the environment referred to in paragraph 1.
The ecological status of surface water is classified as excellent, good, satisfactory, avoided or degraded by comparing the state of water with the reference conditions and using the definitions set out in Annex 1. The status of artificial and highly modified surface water shall be classified as satisfactory, satisfactory, avoided or poor in proportion to the best achievable ecological status.
Classification is made with the help of biological agents, taking into account the hydrological and morphological and physico-chemical factors supporting them. Classification is an excellent indicator of an ecological quality ratio of 1 to 0.
The ecological status of surface water shall be classified as satisfactory if the environmental quality standard for the substance referred to in point D of Annex 1D of the Council Regulation on hazardous and harmful substances is exceeded. (7 OCTOBER 2010/869)
The classification of the ecological status of surface water and the presentation of results shall also apply to the provisions of Annex V to the Water Framework Directive. (7 OCTOBER 2010/869)
The chemical status of surface water in the water body is classified in favour, unless the environmental quality standard for the substance listed in point C2 of Annex 1 to the Council Regulation on hazardous and harmful substances has been exceeded. In the case of Brominated diphenyl ether, dicofol, perfluorooctane sulfonic acid, dioxins, hexabromyclododecane, heptachloor, heptachloro-epoxide, mercury, hexachlorobenzene and hexachlorobutadiene, Environmental quality standards for fish set out in point C2 of Annex 1 to the Regulation and the environmental quality standards for molluscs provided for in that paragraph for fluoranthene and PAH. (17,11/1309)
With A 13,09/2015 (1) shall enter into force on 22 December 2015. The previous wording reads:
The chemical status of surface water in the water body is classified in favour, unless the environmental quality standard for the substance referred to in point C of the Annex to the Council Regulation on hazardous and harmful substances has been exceeded. For mercury, hexachlorobenzene and hexachlorobutadiene, the environmental quality standards set out in point C of Annex 1 to that Regulation shall apply.
The classification of the chemical status of surface water and the presentation of results shall also apply to the provisions of Annex V to the Water Framework Directive.
Groundwater is classified in good or bad conditions based on quantitative and chemical status, whichever is worse. The classification and presentation of results shall also apply to the provisions of Annex V to the Water Framework Directive.
A quantitative status shall be classified if:
(1) the average annual water abstraction does not exceed the amount of groundwater, taking particular account of the effects of the abstraction on surface water and terrestrial ecosystems associated with groundwater; and
2) the height of the ground water level is not continuously reduced as a result of human activity.
The classification of groundwater chemical status is made to bodies of groundwater which, on the basis of the impact assessment and further reports, may not reach a good chemical status.
Classification shall take into account the concentrations of the groundwater pollutants listed in Annex 7 A (pollutant) Which may reduce the chemical status of the body of groundwater in the groundwater concerned.
The chemical status of groundwater shall be classified, taking into account the provisions of Article 14b, in favour of:
(1) the concentration of the pollutant in the monitoring cases of the body of groundwater, calculated as an annual average, does not exceed the environmental quality standard referred to in Annex 7a in any of the monitoring cases; and
(2) on the basis of the monitoring results, it may be assessed that the conditions for other adverse factors referred to in Annex 7 B are met.
(7 OCTOBER 2010/869)The chemical status of the groundwater body may be classified, irrespective of paragraph 1, even if the environmental quality standard referred to in Annex 7a is exceeded in one or more monitoring cases, provided that:
(1) the concentration of the pollutant in the body of groundwater does not pose a significant environmental risk;
(2) the concentration of the pollutant has not significantly impaired the suitability of groundwater for the purpose for which it could be used; and
(3) the other conditions laid down in paragraph 1 (2) are met.
The Finnish Environment Agency shall prepare amendments to Annex 7 A, provided that new information on pollutants, groups of substances or indicators of pollution indicates that the protection of human health or the environment must be established An environmental quality standard for a substance other than the substance or group of substances listed in Annex 7 A, the existing EQS shall be amended or deleted or the eqs shall be returned to the list.
When drawing up the proposal, the Finnish Environment Agency shall make a proposal to the relevant authorities and to the parties with an interest or right to be heard.
Where appropriate, the Agency shall assess the relevance of the exceptional nature of the natural or accident situation referred to in Article 21 (3) of the water management law to the environmental objectives From an angle.
In assessing whether the state of water can be considered to be compatible with environmental objectives, the following conditions shall be considered by the means of life, transport and the Agency:
(1) all practical measures have been taken to prevent further deterioration of the holding;
(2) the achievement of environmental objectives shall not be adversely affected by other bodies of water which are not affected by exceptional circumstances;
(3) Whereas the measures set out in the operational programme referred to in Article 12 of the Water Management Act for exceptional circumstances do not prevent the restoration of water status where circumstances can no longer be regarded as exceptional;
(4) take practical steps to restore the status of water as soon as possible.
Where the river basin management plan sets out the exceptions referred to in Article 21 (3) or Articles 22 to 25 of the Water Management Law, the environmental objectives referred to in Article 21 (1) of the Law, shall be ensured by the means of life, transport and the environment of the Agency that: Shall not prevent or jeopardise the achievement of environmental objectives in other water bodies of the same water management area or run counter to the requirements or objectives laid down in other environmental legislation.
The Centre for Food, Transport and the Environment shall define the needs for the monitoring of surface water and groundwater in its territory, taking into account the provisions of Articles 16 to 20. It shall establish a monitoring programme within its territory, which shall, where appropriate, combine monitoring organised by the authorities and the monitoring carried out by the operator under other law. The monitoring programme shall include the necessary monitoring points and areas, the following factors and the frequency of monitoring.
The Centre for the Environment, Transport and the Environment, in cooperation with the competent industry, transport and the Environment Agency, is defined by the Centre for Transport and the Environment.
In order to assess the impact of the activities referred to in Article 6, periodic monitoring shall be carried out to assess the impact of the activities referred to in Article 6, in order to design monitoring programmes and of natural and horizontal human activities. To determine the long-term effect ( Basic monitoring ).
Where it is possible that environmental objectives are not achieved, monitoring of surface water and groundwater shall be organised in such a way as to identify the status of the waters and the impact of the measures of the operational programme ( Operational monitoring ).
If the reason for the failure to achieve the environmental objectives is not known or is due to a sudden cause, the number of surface water status deterioration and the impact on the preparation of the operational programme ( Examined Monitoring ).
The monitoring programme shall contain sufficient monitoring sites or areas in order to assess the status of surface waters as a whole and their classification is possible.
On the basis of an assessment by the Business, Transport and Environment Agency, the monitoring sites or areas of the basic monitoring shall be located in the surface water referred to in point A of the Annex. (7 OCTOBER 2010/869)
Functional monitoring sites or areas shall be located in the surface water referred to in point B of the Annex.
The basic monitoring of surface water shall be directed at biological, hydrological and morphological and physico-chemical agents and the chemical status variables. The functional monitoring of surface water shall be applied to the biological, hydrological or morphological or physico-chemical agents, as well as to the chemical status of the detectable variables, which show a pollutant or change effect.
The frequency and timing of the monitoring shall be chosen in such a way as to achieve acceptable reliability and precision.
The basic monitoring shall be organised for at least one year in each river basin management plan. The parameters for biological and hydrologic morphological factors shall be monitored at least once. The physico-chemical parameters shall be monitored in accordance with Annex 4, subject to technical knowledge and expert judgement.
The basic monitoring may be reduced in every third river basin management plan if:
(1) previous monitoring has shown that the state of surface water is at least good and is likely to be maintained or improved; and
2. In the impact of the action referred to in Article 6, no material changes have been made to the state of surface water.
Functional monitoring shall be carried out for biological, hydrological and morphological or physico-chemical agents as laid down in Annex 4. In the course of the river basin management plan, monitoring may be carried out in the course of the river basin management plan if the cessation of the operation of the surface water or the harmful or harmful effect on the state of the water may no longer be considered as significant.
In addition, the monitoring of hazardous and noxious substances is provided for in Articles 9 and 9a of the Council Regulation on hazardous and harmful substances. (7 OCTOBER 2010/869)
The monitoring programme shall provide sufficient monitoring facilities in order to permit a reliable assessment of the state of groundwater and of the natural or anthropogenic nature of the holding or of human activity.
Where it is possible that the good status of the groundwater is not achieved, the monitoring sites, factors and frequency shall be chosen in such a way as to determine how the water abstraction, other human activities and the discharge of groundwater have an impact on the state of groundwater.
Operational monitoring shall be organised in a body of groundwater, for which, on the basis of the basic monitoring and the impact assessment provided for in Article 7, it is possible that groundwater environmental objectives will not be achieved. Monitoring cases shall be selected in such a way as to best demonstrate the quantitative and chemical status of the body of groundwater.
The monitoring of a body of groundwater outside the border of Finland is set out in Annex 4 C.
The initial and functional monitoring of the quantitative space shall monitor the height of the groundwater level. Operational monitoring shall also monitor the amount of groundwater to be taken.
The basic monitoring of groundwater chemical status shall be applied to the factors listed in Annex 4B. In addition, factors which demonstrate the potential risk to a body of groundwater shall be selected.
The functional monitoring of the chemical status shall at least monitor the concentrations of the pollutants specified in Annex 7 A in groundwater, which may pose a risk to groundwater contamination in the groundwater area.
The basic monitoring frequency of the quantitative space shall be sufficient to determine the short and long-term variations in the formation of groundwater.
In a body of groundwater where environmental objectives may not be achieved, adequate monitoring frequency shall be ensured in order to assess the effects of water abstraction and water discharge at the height of the groundwater level.
The basic monitoring of chemical status should be adequately organised. Functional monitoring is organised outside the basic monitoring period at a sufficient frequency and at least once a year in order to detect the effects of human activity in the body of groundwater.
When monitoring the state of water, sediment and biota, the requirements set out in Annex 3 to the Council Regulation on hazardous and harmful substances shall be applied to the performance of analytical methods, the quality of the analytical results And the interpretation of the results.
The Centre for Business, Transport and the Environment shall ensure that the necessary studies are drawn up for the river basin management plan and the operational programmes referred to in Article 12 of the Water Management Act. The preparation of the management plan referred to in Article 13 of the Water Management Act and the work programme and the proposals and opinions of the group of cooperation referred to in Article 14 of the Water Management Act shall be taken into account.
The Centre for Enterprise, Transport and the Environment shall compile a proposal for a management plan for water management prepared in the water management area, the summary of operational programmes and the monitoring programmes, and shall submit it to the Water Management Code. The steering group referred to in Article 14.
In addition to Article 11 of the Water Management Act, the river basin management plan shall set out the elements listed in Annex 5.
In addition, the water management plan should indicate how the (1303/2004) The proposals submitted by the group of cooperation referred to in paragraph 1 and the contributions referred to in paragraph 3 have affected the content of the river basin management plan.
The basic water management measures referred to in Article 12 of the Water Management Act include:
(1) emission management and water protection measures, including ex ante control of point and diffuse pollution; (7 OCTOBER 2010/869)
(2) ex ante control of ground and surface water abstraction, artificial groundwater formation and surface water damping;
(3) a report on the involvement of water users in the cost of water use;
(4) the ex ante control of water rationing and the construction of water affected by the objective of the ecological status of the waters; (7 OCTOBER 2010/869)
(5) measures concerning the management of hazardous and noxious substances in the aquatic environment;
(6) measures to ensure the quality of water used for drinking water abstraction; (7 OCTOBER 2010/869)
(7) measures to prevent pollution and to reduce the risk of pollution incidents and other exceptional situations, as well as to prevent the relevant loss of polluting substances from technical equipment; (18/12/2011)
(8) measures to promote efficient and sustainable water use; (7 OCTOBER 2010/869)
(9) restrictions and conditions for the use of specific areas for the use of the regions. (7 OCTOBER 2010/869)
As part of the review of the operational programme referred to in Article 19 of the Water Management Act, the Agency shall also review the ex ante control measures referred to in points 1, 2, 4 and 5 of Article 19 of the Water Management Act and, where appropriate, propose measures to: In order to update them. The amendments to the ex ante control measures and the monitoring provisions shall be laid down in the Environmental Protection Act (177/2014) And the water (197/2011) . (18/12/2011)
The complementary measures referred to in Article 12 of the Water Management Act are listed in Annex 6b.
Reports on the water management area referred to in this Regulation, as well as estimates for the status and monitoring of surface water and groundwater, shall be reviewed two years before the publication of the revised water management plan. The reports are based on the previous year's data. The reports will be published in the revised water management plans. (7 OCTOBER 2010/869)
By way of derogation from paragraph 1, in the case of emissions of plant protection products referred to in point (C) of the Annex to the Council Regulation on hazardous and harmful substances, the emissions and rinds of plant protection products referred to in point (C) of the Annex to the Regulation may be used: The year average. (7 OCTOBER 2010/869)
The working documents referred to in Article 13 of the Water Management Act shall be accessible to the municipalities concerned and shall have the opportunity to give their opinion for a period of six months, including their contribution.
This Regulation shall enter into force on 1 December 2006.
Measures may be taken prior to the entry into force of the Regulation.
The first monitoring programmes referred to in Article 15 shall be drawn up by 22 December 2006.
Directive 2000 /60/EC of the European Parliament and of the Council (32000L0060); OJ L 327, 22.12.2000, p. 1 TO 73Annex 1
Definitions for the classification of surface water ecological status
1. Biological agents
| Excellent condition 1) | Good status 1) | Satisfactory status 1) | |
| Biological factor | Definition | Definition | Definition |
| Vegeplankton (lake and coastal water) | The composition and abundance ratios are entirely or almost entirely undisturbed. | Minor changes in phytoplankton taxonets and their abundance compared to the type specific to the type. | Plankton taxons and their abundance ratios are moderately different from those of the type. |
| The average biomass of phytoplankton corresponds fully to the physico-chemical conditions characteristic of the type and does not significantly alter the visual depth of the type. | There are minor changes in Biomass compared to circumstances specific to the type. | In the lake, biomass has been moderately altered and can lead to significant undesirable changes in other biological agents and physico-chemical quality of water or sediment. | |
| The frequency and intensity of plankton blooms correspond to the physico-chemical conditions characteristic of the type. | These changes do not indicate any increase in algae which would lead to unwanted changes in the lake in the aquatic organism or in the physico-chemical quality of water or sediment, in coastal waters, in aquatic organisms or in the quality of water. | In coastal waters, the biomass of algae exceeds the limits specific to the type and may affect other biological factors. | |
| There may be a slight increase in the frequency and intensity of the flowers compared to the type of situation. | A moderate increase may occur in the frequency and intensity of plankton blooms. Long term blooms may occur during the summer months. | ||
| Macrophytes and coating (river and lake) | The composition of the taxi is entirely or almost entirely undisturbed. | Minor changes in macrophytes and coating taxons and their abundance in relation to the type-specific entities. These changes do not indicate an increase in overhead or higher water growth which would lead to unwanted changes in aquatic organisms or in the physico-chemical quality of water and sediment. | The incidence of macrophyte and coating taxis differs from one specific to the type of Community and is significantly more disturbed than good space in similar circumstances. |
| No observable changes in the average abundance of macrophytes and coating. | Among the main algae, there are no harmful organisms caused by human activity. | Moderate changes in the average abundance of macrophytes and coating. | |
| The bacterial growth of human activity is harmful to the overhead or locally displaced. | |||
| Groundwater (river and lake) | Taxoniction and abundance ratios, as well as the relationship between taxon and insensitive taxons, are entirely or almost identical to the undisturbed circumstances of a type. | Taxoniction and abundance ratios, the relationship between taxonomic taxonis and insensitive taxones and diversity show minor changes compared to undisturbed conditions specific to the type. | The composition and abundance ratios are moderately different from those of the type. |
| The diversity of the wild fauna does not show any change in relation to undisturbed circumstances. | There are no major taxonomic groups that are specific to the type. | ||
| The relationship between taxonis and insensitive taxonis and the level of diversity are significantly lower than the type specific to the type and significantly lower than the good space in similar circumstances. | |||
| Groundwater (inshore water) | The diversity and abundance of fauna and flora vary within the limits which are normally associated with undisturbed circumstances. | The diversity and abundance ratios of fauna have changed slightly from the specific situation. | The diversity and abundance ratios of fauna have been moderately changed to the type of situation. |
| Typical changes in taxis typical of all undisturbed conditions. | Most of the types that are characteristic of the type of change occur. | Contamination taxons occur. | |
| There are many types of converter-sensitive taxonis missing. | |||
| Fish Stock (river and lake) | The species composition and abundance ratios are entirely or almost entirely undisturbed. | Minor changes in species composition and abundance in relation to the type specific to the type, due to the effects of human activity on physico-chemical and hydrologic morphological factors. | The composition and abundance ratios of the fleet are moderately different from those of the type, due to the effects of human activity on physico-chemical or hydrologic morphological factors. |
| All sensitive species specific to the type occur. | There are signs of changes in the age structure of the fleet due to the effects of human activity on physico-chemical and hydrological and morphological factors, and in some cases, there are signs of an increase in individual species or individual development. To the extent that some age categories can be completely absent. | There are sizeable changes in the age structure of the fleet due to the effects of human activity on physico-chemical or hydrologic morphological factors. A large proportion of the species specific to the type are missing or very limited. | |
| There are few changes in the age structure of the fleet, and there are no signs of disturbance in the reproduction or individual development of any species. | |||
| Macroalgae and Copper seed crops (coastal water) | All types of macrs and Copper seed taxons characteristic of a type of change are present. | Most sensitive types of macrs and Copper seed taxis are present. | There is a lack of macritic and Copper-seed taxis of a moderate number of transformations. |
| The camouflage and the abundance of Copper seed correspond fully or almost entirely to the undisturbed circumstances. | There are minor changes in the cover-up of the Makrit and the abundance of Copper seed. | The camouflage and the abundance of Copper seed have been moderately changed. This may result in unwanted changes in aquatic organisms | |
| Biological agents (artificial or highly modified surface water) | The values of the biological agents in question correspond as far as possible to the values of the corresponding surface water type, taking into account the physical conditions resulting from artificial or highly modified characteristics of the water body. | Minor changes in the values of the biological agents concerned compared to the best achievable ecological status. | Moderately, changes in the values of the relevant factors compared to the best achievable ecological status. |
| These values have changed significantly more than the values observed in good ecological conditions. |
2. Hydrological-morphological factors
| Excellent condition 1) | Good status 1) | Satisfactory status 1) | |
| Hydrologis morphological factor | Definition | Definition | Definition |
| Hydrological system (river and lake) | The amount and dynamics of the flow, in addition to the lake, the level of the surface and the delay, and the resulting link to groundwater, are entirely or almost completely undisturbed. | The status quo is not detrimental to the achievement of the values set out in paragraph 1 above in the definitions given to biological agents. | The status quo is not detrimental to the achievement of the values set out in paragraph 1 above in the definitions given to biological agents. |
| Accessibility (river) | Human activity has not changed the accessibility of the river, which allows the free movement of aquatic organisms and the sediment introduction. | The status quo is not detrimental to the achievement of the values set out in paragraph 1 above in the definitions given to biological agents. | The status quo is not detrimental to the achievement of the values set out in paragraph 1 above in the definitions given to biological agents. |
| Morphological factors (river, lake and coastal water) | The design, width and depth of the river basin, the flow rates, the quality of the bottom and the structure and conditions of the coastal zone are fully or almost completely undisturbed. | The status quo is not detrimental to the achievement of the values set out in paragraph 1 above in the definitions given to biological agents. | The status quo is not detrimental to the achievement of the values set out in paragraph 1 above in the definitions given to biological agents. |
| The variation in the depth of the lake, the number of dregs and the structure and conditions of the lake are fully or almost entirely undisturbed. | |||
| The variation in the depth of the coastal water, as well as the structure and quality of the bottom, are fully or almost completely undisturbed. | |||
| Hydrologis morphological factor (artificial or highly modified surface water) | In the case of hydrological and morphological conditions, only those effects on surface water are detectable as a result of artificial or highly altered characteristics of water after all The mitigation measures have been taken in order to ensure that as close as possible to the best practicable ecological continuity, in particular the migration of fauna and the appropriate breeding areas. | The status quo is not detrimental to the achievement of the values set out in paragraph 1 above in the definitions given to biological agents. | The status quo is not detrimental to the achievement of the values set out in paragraph 1 above in the definitions given to biological agents. |
3. Physical-chemical agents
| Excellent condition 1) | Good status 1) | Satisfactory status 1) | |
| Physico-chemical | Definition | Definition | Definition |
| General conditions of water (river, lake, coastal water, artificial or heavily modified and surface water) | Nutrition concentrations vary within the limits normally associated with undisturbed circumstances. | Nutrition concentrations do not exceed the levels determined to ensure the functioning of the type specific to the type of ecosystem and the attainment of the values set out in paragraph 1 above for biological agents. | The status quo is not detrimental to the achievement of the values set out in paragraph 1 above in the definitions given to biological agents. |
| In the river, lake and coastal water, physico-chemical agents are fully or almost completely undisturbed. | In the river and lake, temperature, oxygen conditions, pH, alkalinity and salinity, in addition to the lake, visual depth, inshore water temperature, oxygen conditions and visual acuity, do not indicate changes in human activity and vary within the limits of: Normally associated with undisturbed circumstances. | ||
| In the river and lake, temperature, oxygen conditions, pH, alkalinity and salinity, in addition to the lake, visual depth, coastal water temperature, oxygen conditions and visual acuity, and artificial or highly modified surface water temperature and pH do not exceed the limits, Which are defined to ensure the functioning of the type specific to the type of ecosystem and the achievement of the values set out in paragraph 1 above for biological agents. | |||
| In the case of artificial and highly modified surface water, physico-chemical agents are fully or almost completely undisturbed, associated with the type of water that is closest to the corresponding surface water type. | |||
| In an artificial or highly modified surface water temperature, oxygen conditions and pH are not deviated from the characteristic values characteristic of the type of surface water type. | |||
| Water identified synthetic pollutants (river, lake, coastal water, artificial or heavily modified surface water) | The concentrations are close to zero and at least less than the most advanced, commonly used analysis techniques can be detected. | The concentrations do not exceed the environmental quality standards for substances harmful to the nationally selected aquatic environment. | The status quo is not detrimental to the achievement of the values set out in paragraph 1 above in the definitions given to biological agents. |
| Water-identified non-synthetic pollutants (river, lake, coastal water, artificial or highly modified surface water) | Concentrations remain within the limits normally associated with undisturbed circumstances. | The concentrations do not exceed the environmental quality standards for substances harmful to the nationally selected aquatic environment. | The status quo is not detrimental to the achievement of the values set out in paragraph 1 above in the definitions given to biological agents. |
| Concentrated or heavily modified surface water concentrations remain within the limits normally associated with the undisturbed conditions of the corresponding surface water type. |
It is necessary to classify the waters where there are significant changes in the values of biological agents and where the biogradients differ significantly from those normally associated with the undisturbed conditions of that type of surface water.
They are classified as bad waters, which show serious changes in the values of biological agents and are missing a large part of the organisms which are normally associated with the undisturbed circumstances of the type of surface water concerned.
1) Similarly, the best achievable ecological status, a good achievable ecological status and a satisfactory ecological status can be found for the artificial and heavily modified body of water.
Annex 2
Factors for the breakdown of surface water types
| Surface water type | Breakdown by division | ||
| River | 1. All | ||
| 2. Terrestrial and bedrock: organic, quartz-rich, high-nutrient or high-calcine | |||
| 3. Height above sea level | |||
| 4. Share of water in the catchment area | |||
| 5. Geographical location | |||
| Lake | 1. All | ||
| 2. Terrestrial and bedrock: organic, quartz-rich, high-nutrient or high-calcine | |||
| 3. Height above sea level | |||
| 4. Average water depth | |||
| 5. The delay | |||
| 6. Geographical location | |||
| Inshore water | 1. Salinity | ||
| 2. The impact of the wave | |||
| 3. Geographical location | |||
| 4. Ice-covered time |
Annex 2a (20.5.2009)
If necessary, a further explanation of the characteristics of groundwater
1. Geological characteristics of the body of groundwater, including the extent and type of geological formation;
2. Hydrogeological characteristics of a body of groundwater, including hydraulic conductivity, porosity and weight;
3. Soil characteristics in the area of groundwater, including the thickness of strata and soil thickness, porosity, hydraulic conductivity and absorption characteristics;
4. The characteristics of groundwater in the body of groundwater;
5. The listing of terrestrial ecosystems and surface waters in a dynamic context;
6. Estimates for the direction and quantity of water exchange between the body of groundwater and the related terrestrial ecosystem and surface water;
7. Sufficient data for the calculation of the average annual average amount of time;
8. Examination of the characteristics of the chemical composition of groundwater, including the definition of human activity.
Additional explanation of the effects of human activity in bodies of groundwater where good status may not be achieved
The following reports shall be drawn up where appropriate, if the body of groundwater reaches the territory of two or more Member States, or where it is possible that the good status of the groundwater may not be achieved:
1. Location of surface water abstracts;
2. Average annual water abstraction from groundwater abstractions;
3. The chemical composition of the water taken and taken from the body of groundwater;
4. The location of the places where water is discharged directly into the body of groundwater and the quantity of water discharged;
5. The chemical composition of the water discharged into groundwater;
6. Land use in groundwater, including pollution and changes in bodies of groundwater as a result of human activity, such as the introduction of rain and drainage water for other water impermeable structures, immersion in soil, damping Or drying.
Annex 3
Monitoring sites and areas in surface waters
A) Surface water monitoring sites or areas for the assessment of surface waters as a whole:
1. The parts of the large rivers where the catchment area exceeds 2 500 km 2 And water flow shall be significant for the whole of the water management area.
2. Large lakes and reservoir lakes whose water capacity is important for the water management area.
3. Significant watercourses which extend beyond the state boundary.
4. Places defined in Council Decision 77 /795/EEC on the exchange of information.
5. The places needed for the assessment of the load of pollutants across the state line and in the marine environment.
B) Surface water monitoring cases where it is possible that the environmental objectives are not achieved:
1. In surface waters where the point load is significantly affected, sufficient monitoring sites or areas are placed in order to assess the size and impact of the score. In the case of multiple scoring, the monitoring sites shall be selected in such a way as to permit a review of these magnitude and impact as a whole.
2. In surface waters where the diffuse load is significantly affected, sufficient monitoring sites or areas are placed in order to assess the size and impact of diffuse pollution. Places must be chosen in such a way as to represent the relative share of diffuse pollution and the risk of not achieving good surface water status.
3. In order to assess the extent and impact of the changes, sufficient number of monitoring sites or areas shall be placed in the surface waters which may be affected by significant surface water. Places or areas shall be selected in such a way as to demonstrate the overall effect of hydrologic morphological changes on surface water.
Annex 4
(A) (20.5.2009)
Surface water monitoring frequency
| Author | Joes | Lakes | Inshore waters |
| Biological | |||
| Vegeplankton | 2 times /v | 2 times per year | 2 times per year |
| Other aquatic vegetation | 3 years | 3 years | 3 years |
| Groundwater | 3 years | 3 years | 3 years |
| Fish Stock | 3 years | 3 years | |
| Hydrologis morphology | |||
| Accessibility | 6 years | ||
| Hydrology | Continuous | 1 month | |
| Morphology | 6 years | 6 years | 6 years |
| Physico-chemical | |||
| Temperature | 4 times per year | 4 times per year | 4 times per year |
| Oxygen conditions | 4 times per year | 4 times per year | 4 times per year |
| Salinity | 4 times per year | 4 times per year | 4 times per year |
| Nutrition conditions | 4 times / | 4 times per year | 4 times per year |
| Acidification situation | 4 times per year | 4 times per year | |
| Nationally selected substance harmful to aquatic environment | 4 times per year | 4 times per year | 4 times per year |
| Hazardous and harmful to the aquatic environment selected at Community level | 12 times per year | 12 times per year | 12 times per year |
(B) (20.5.2009)
Factors for basic monitoring of the chemical status of the groundwater body
1. Oxygen content;
2. PH reading;
3. Electricity conductivity;
4. Nitrate;
5. Ammonium;
6. Other parameter describing the risk of human activity to a body of groundwater. In particular, the pollutants referred to in Annex 7a shall be taken into account.
(C) (20.5.2009)
Monitoring of the body of groundwater beyond the border of the Finnish State
The groundwater body, which extends beyond the territory of the Finnish State, is in the territory of the Finnish State:
1) provide sufficient provision for monitoring and basic monitoring of quantitative and chemical status. In addition, there must be sufficient monitoring of the direction and the amount of groundwater flowing; and
(2) monitor the determinants of quantitative and chemical status relevant for the protection of the use of that body of groundwater.
Annex 5
Information to be presented in the water management plan:
1. Summary of the characteristics of surface and groundwater characteristics of the water management area, the definition of the reference conditions for surface water and the justification for the exclusion of the biological factor in the assessment of the ecological status of the surface water type.
2. Summary of the significant load and alteration of surface and groundwater status and of other human activities and a summary of the annual impact of the exceptional circumstances referred to in Article 14e Including the criteria used in the assessment of exceptional circumstances. (7 OCTOBER 2010/869)
2. (a) Environmental quality standards for groundwater and a summary of the essential information on the procedure for setting them. (20.5.2009)
(2b) Information on how the exceedances of groundwater quality standards found in individual monitoring cases in the water management area have been taken into account in the final assessment of groundwater quality. (20.5.2009)
2 (c) Reports of emissions, leaching and presence of hazardous and noxious substances in the aquatic environment. (7 OCTOBER 2010/869)
3. The specific areas referred to in Article 4 and a report on the legislation on the basis of which the regions are defined.
4. Monitoring sites and regions in the form of a map. Monitoring results on the state of surface water, groundwater and protected areas in the form of a map and, if necessary, in the form of a map, information on the monitoring sites where the eqs have been exceeded, and on the aquatic environment dangerous and harmful The results of the monitoring of long-term trends within the meaning of Article 9a of the Council Regulation on substances. Assessment of the reliability and accuracy of the results of the monitoring. (7 OCTOBER 2010/869)
(4a) Information on the relevant and permanent upward trend of the pollutant observed in the individual monitoring case. In addition, information is provided on the concentration level of the pollutant in which measures have been taken to calculate the concentration level and data on the conversion of the concentration. (20.5.2009)
(4b) Summary of measures taken as a result of the consequences of cross-border pollution of the countries referred to in Article 6a of the Council Regulation on hazardous and harmful substances. (7 OCTOBER 2010/869)
(4c) Description of the approaches and methods applied to the definition of mixing zones referred to in Article 3 (5) of the Council Regulation on hazardous and harmful substances and the mixing zone Measures taken to limit the scope of the water management area, where one or more mixing zones are defined in accordance with Article 6b of the Regulation. (7 OCTOBER 2010/869)
5. List of environmental targets set for surface waters, groundwater and protected areas, justification for the application of Articles 22 to 25 of the Water Management Act and other information related to the setting of targets.
6. Summary of the financial statement of water use and water services.
7. Summary of the operational programme or programmes, including the means to achieve the objectives set, a summary of measures for exceptional situations and the relevant technical devices for technical equipment To prevent losses as well as an explanation of alternative measures and their choice. (18/12/2011)
8. List of programmes and management plans for the river basin district, certain sectors, certain aspects or surface water types, and a summary of their content.
9. Summary of actions to inform and consult citizens, as well as an explanation of the views expressed during the preparation and the negotiations between the Member States and how they have contributed to the content of the plan; and Choice of alternatives.
10. List of competent authorities with the following information:
(i) name and address of the competent authority;
(ii) the geographical area of the water management area,
(iii) the legal status of the competent authority;
(iv) an explanation of the legal and administrative responsibilities and functions of each competent authority in each water management area;
(v) where the competent authority acts as a coordinating body coordinating other competent authorities, a list of those authorities and a report on the relations established between the institutions to ensure cooperation; and
(vi) where the water management area is located in the territory of more than one Member State or includes regions that are not Member States, an explanation of the relationship between institutions established to ensure cooperation.
11. Information on where and how the background documents and data covered by the river basin management plan, the monitoring data of the Environmental Protection Act and the Water Code and the details of the monitoring data collected under the monitoring programmes are: Available. (18/12/2011)
12. Law on the assessment of the environmental impact of plans and programmes (2011) Information corresponding to the environmental report.
In accordance with Article 19 of the Water Management Act, the revised water management plan shall also include the following information:
13. Summary of any changes or updates made after the publication of the previous river basin management plan, including a summary of the checks carried out in accordance with Articles 22 to 25 of the Water Management Act.
14. Assessment of progress towards the achievement of the environmental objectives, including a map-shaped presentation of the results of the period covered by the previous plan, and an explanation of the environmental objectives that have not been achieved.
15. Summary of the measures taken.
16. Summary of provisional additional measures taken following the publication of the previous management plan for the water management area.
17. Summary and explanation of the previous operations in the river basin management plan which have not been implemented.
18. Changes in groundwater quality standards. (20.5.2009)
19. Table showing the limits of analysis of the analytical methods applied and information on the performance of those methods in relation to the provisions laid down in Annex 3 to the Regulation on hazardous and harmful substances And the justification for the monitoring frequency applicable in accordance with Article 9 (5) of that Regulation if the monitoring intervals are longer than one year. (17,11/1309)
With A 13,09/2015 Paragraph 19 shall enter into force on 22 December 2015.
20. The revised River Basin Management Plan may contain additional maps showing the chemical status of one or more of the substances referred to below separately from the information on other hazardous substances in the aquatic environment. Substances identified in point C2 of Annex 1 to the Council Regulation on undesirable substances:
(a) substances with numbers 5, 21, 28, 30, 35, 37, 43 and 44;
(b) substances whose numbers are 34 to 45,
(c) substances with numbers 2, 5, 15, 20, 22, 23 and 28.
In the case of numbered substances referred to in points (a) to (c), the extent to which the value of the environmental quality standard may be deviated in the river basin management plans may be indicated. Such additional maps shall be drawn up to ensure their mutual comparability at the level of the water management area and the European Union. (17,11/1309)
With A 13,09/2015 Paragraph 20 shall enter into force on 22 December 2015.
Annex 6
(a) Basic water management measures
The basic measures for water management are included in the following legislative acts:
(i) decision of the Ministry of Social Affairs and Health on the quality of bathing water quality and control surveys (SosTMp 292/1996);
(ii) the Nature Conservation Act (1096/1996)
(iii) Forest Law (1093/1996)
(iv) a regulation of the Ministry of Social Affairs and Health on the quality requirements for financial water and control studies; (1) OF THE
(v) Law on the safety of dangerous chemicals and explosives (390/2005)
(vi) Regulation concerning the industrial handling and storage of dangerous chemicals; (2003)
(vii) a law on the environmental impact assessment procedure (448/1994)
(viii) Decision of the Council of Ministers on the use of sewage sludge in agriculture (192,94)
Ix) Council Regulation on urban waste water (888/2006)
(x) pesticide law (327/1969)
Xi) Council Regulation restricting access to waters of nitrates from agricultural sources (1999)
Xii) environmental protection law (2006)
Xii) Council Regulation on hazardous and harmful substances in the aquatic environment (1022/2006)
(xiv) water law (264/1961)
Xv) Water supply law (19/2001)
Xvi) Land use and building law (132/1999)
Xvii) health protection law (763/1994)
Xviii) Maritime law (1415/1994) .
(b) Additional measures for water management
Additional measures for the management of water may include:
(i) legislative instruments
(ii) administrative means
(iii) economic or fiscal means;
(iv) environmental agreements
(v) guidelines on good environmental practice
(vi) restoring and restoring wetlands;
Vii) building projects;
Viii) environmental rehabilitation projects
Ix) training projects
(x) research, development and demonstration projects and
(xi) other relevant measures.
Annex 7 (20.5.2009)
A) Groundwater pollutants and their eqs 1
| Substance | Environmental quality standards for groundwater | Unit | |
| 1. | Nitrates | 50 | Mg/l |
| 2. | Pesticide active substances and their (relevant) metabolites, breakdown or reaction products | 0,1 | µ g/l |
| 0,5 in total 2 2 | µ g/l | ||
| 3. | Benzene | 0.5 | µ g/l |
| 4. | Toluene | 12 | µ g/l |
| 5. | Ethylbenzene | 1 | µ g/l |
| 6. | Clovenes (high-level, meta-and paraxylene) | 10 | µ g/l |
| 7. | Anthracene | 60 | µ g/l |
| 8. | Naphthalene | 1.3 | µ g/l |
| 9. | Benzo (a) pyrene | 0.005 | µ g/l |
| 10. | Benzo (b) fluoranthene, benzo (k) fluoranthene, benzo (g, h, i) perylene and indeno - (1,2,3-cd) pyrene | 0.05 | µ g/l |
| 11. | PCBs (??? kongeners 28, 52, 101, 118, 138, 153 and 180) | 0.015 | µ g/l |
| 12. | Trichloroethylene and tetrachloroethylene | 5 | µ g/l |
| 13. | 1,2-dichloroethylene | 25 | µ g/l |
| 14. | 1,2-dichloroethane | 1.5 | µ g/l |
| 15. | Dichloromethane (methylene chloride) | 10 | µ g/l |
| 16. | Vinyl chloride (chloroethylene) | 0.15 | µ g/l |
| 17. | Carbon tetrachloride | 2 | µ g/l |
| 18. | Chloroform (trichloromethane) | 100 | µ g/l |
| 19. | Chlorobenzene | 3 | µ g/l |
| 20. | 1,2-dichlorobenzene | 0.3 | µ g/l |
| 21. | 1,4-dichlorobenzene | 0.1 | µ g/l |
| 22. | Trichlorobenzene (1,2,3 -, 1,2,4-and 1,3,5-trichlorobenzene) | 2.5 | µ g/l |
| 23. | Pentachlorobenzene | 1.2 | µ g/l |
| 24. | Hexachlorobenzene | 0.024 | µ g/l |
| 25. | Monochlorophenols | 0.05 | µ g/l |
| 26. | Dichlorophenols | 2.7 | µ g/l |
| 27. | Tri, tetra and pentachlorophenol | 5 | µ g/l |
| 28. | MTBE (methyl tert-butyl ether) | 7.5 | µ g/l |
| 29. | TAME (tert-amyl methyl ether) | 60 | µ g/l |
| 30. | Oil fractions (C10-40) | 50 | µ g/l |
| 31. | Mercury | 0.06 | µ g/l |
| 32. | Cadmium | 0.4 | µ g/l |
| 33. | Cobalt | 2 | µ g/l |
| 34. | Chromium | 10 | µ g/l |
| 35. | Copper | 20 | µ g/l |
| 36. | Lead Lead | 5 | µ g/l |
| 37. | Nickel | 10 | µ g/l |
| 38. | Zinc | 60 | µ g/l |
| 39. | Antimony | 2.5 | µ g/l |
| 40. | Arsenic | 5 | µ g/l |
| 41. | Ammonium NH4 + | 0,25 (NH4 +) | Mg/l |
| Or Ammonium nitrogen NH4N | 0,20 (NH4N) | Mg/l | |
| 42. | Chloride | 25 | Mg/l |
| 43. | Sulphate | 150 | Mg/l |
1 Environmental quality standards for groundwater Referred to in this Regulation and at Community level, the concentration of the pollutant, the group of pollutants or the indicator of pollution in groundwater, expressed in groundwater, as a quality standard for the protection of human health or the environment Exceeds the limit value referred to in Article 2 (2) of Directive 2006 /118/EC as well as nationally established.
2 Total means the sum of all individual pesticides detected and measured in the monitoring, including their relevant metabolites, breakdown or reaction products.
(B)
Other elements to be used in the classification of the chemical status of the groundwater body and their impact assessment
(1) The concentration of the pollutant listed in point A of this Annex in the body of groundwater does not indicate any adverse effects on groundwater. For the pollutant, the impact of the substance on the body of groundwater shall be assessed;
(2) the concentration of the pollutant in the body of groundwater does not lead to the presence of a surface water body in the context of a body of groundwater:
(2a) non-compliance with environmental objectives;
2b) the essential deterioration of the ecological or chemical quality;
Estimate the amount, concentration and probable impact of the passing pollutant;
(3) the concentration of the pollutant in the body of groundwater does not cause any material injury to the terrestrial ecosystem. The quantity and concentration of the pollutant coming into the terrestrial ecosystem and the likely effect where it is possible that the substance may be discharged from a groundwater body to the terrestrial ecosystem;
(4) salinisation or access to a body of groundwater for the purpose of access to an aquifer if it is possible to access groundwater;
(5) an assessment of whether the potentially polluting substance in the body of groundwater would jeopardise the quality of the drinking water.
This Regulation shall enter into force on 1 June 2009.
Before the entry into force of the Regulation, measures may be taken to implement it.
Directive 2006 /118/EC of the European Parliament and of the Council (32006L0118); OJ L 372, 27.12.2006, p. 19
This Regulation shall enter into force on 15 November 2009.
Directive 2000 /60/EC of the European Parliament and of the Council (32000L0060); OJ L 327, 22.12.2000, p. 1-73
This Regulation shall enter into force on 1 November 2010.
Directive 2008 /105/EC of the European Parliament and of the Council (32008L0105); OJ L 348, 24.12.2008, p. Directive 2000 /60/EC of the European Parliament and of the Council (32000L0060); OJ L 327, 22.12.2000, p. 1-73, Commission Directive 2009 /90/EC (32009L0090); OJ L 201, 1.8.2009, p. 36-38
This Regulation shall enter into force on 1 January 2015.
This Regulation shall enter into force on 1 January 2015.
Directive 2000 /60/EC of the European Parliament and of the Council (32000L0060); OJ L 327, 22.12.2000, p. 1
This Regulation shall enter into force on 22 December 2015.
Directive 2013 /39/EU of the European Parliament and of the Council (32013L0039); OJ L 226, 24.8.2013, p. 1
