This chapter considers Ukraine’s ambitions and outlook for its water sector including water-related obligations under the Association Agreement with the European Union and targets under multilateral environmental agreements including the Sustainable Development Goals. Obligations under the EU Water Framework Directive and associated directives are discussed, including time-bound commitments concerning the identification of river basin districts and preparation of river basin plans. The chapter considers Ukraine’s current state of play with regard to water resources and pressures facing the sector. Finally, the chapter considers the existing policy and legislative framework and considers scenarios for possible future reforms.
Developing a Water Policy Outlook for Georgia, the Republic of Moldova and Ukraine
4. Options for Ukraine’s water policy reform journey – challenges in developing a water policy outlook
Copy link to 4. Options for Ukraine’s water policy reform journey – challenges in developing a water policy outlookAbstract
Ukraine’s relationship with the European Union provides a framework for water policy reform
Copy link to Ukraine’s relationship with the European Union provides a framework for water policy reformOver the past few decades, the European Union has intensified its co‑operation with the countries of Eastern Europe and the Caucasus, including Ukraine. This co‑operation has developed notably within the framework of the Eastern Partnership (EaP), which was launched in 2009. Closer bilateral ties culminated in the signing of the EU-Ukraine Association Agreement (AA) including a Deep and Comprehensive Free Trade Area (DCFTA) in 2014. After provisional application, the AA and DCFTA came into force in September 2017. The AA commits Ukraine to bring its legislative and regulatory frameworks into line with those of the European Union in several areas, including environment and water resources management.
The AA defines timeframes in which Ukraine is expected to align national practices with the EU directives related to water quality and resource management, including the marine environment. All provisions should be implemented by 2027, which will mark ten years of the AA’s entry into force. Of these directives, the Water Framework Directive (WFD) is the most crucial legal act concerning water protection and regulation. It aims to ensure the viable, socio-economic management of resources; to protect the quantity and quality of water; and to promote sustainable water use.
The EU-Ukraine AA transcends the WFD, extending to commitments more broadly related to the water sector. Table 4.1 summarises the water-related EU directives, including provisions, timeframes for implementation as defined by the AA and status as of 2021. This assessment covers all water-related EU directives except the Floods Directive and the Marine Strategy Framework Directive.
Ukraine has assigned responsibility for implementation of EU directives to relevant institutions, but some problems persist. Institutional issues remain unresolved in management of both maritime protection and underground waters according to the basin principle. In terms of legislation, Ukraine has partially completed the approximation required by Ukraine’s AA, notably through the 2017 amendment of the 2002 Water Code. However, legislative shortcomings persist, including a lack of definition for “ecological river flow” in water legislation. Pollution is insufficiently monitored and controlled. Sources include diffuse pollution of groundwater with nitrates and phosphorous compounds, as well as pesticides and persistent organic pollutants, discharge of polluted wastewater from municipal treatment facilities and pollution linked to the mining industry. In addition, there are persistent risks of inadequate access to drinking water and sanitation related to floods, droughts and health impacts. Water supply and sanitation (WSS) service delivery varies widely and is particularly inadequate in rural areas. Finally, ageing irrigation and drainage infrastructure leads to reduced agricultural yields and increases risk of desertification.
Table 4.1. EU directives on water quality and resource management and timeframes for their implementation in Ukraine
Copy link to Table 4.1. EU directives on water quality and resource management and timeframes for their implementation in Ukraine|
Directive |
Provision |
Timeframe (from entry into force in 2017) |
Status (2021) |
|---|---|---|---|
|
Water Framework Directive (Directive 2000/60/EC establishing a framework for Community action in the field of water policy as amended by Decision No 2455/2001/EC and Directive 2009/31/EC) |
Adoption of national legislation and designation of competent authority/authorities |
Within three years (i.e. 2020) |
2002 Water Code updated in 2017. Ministry of Environmental Protection and Natural Resources responsible for implementation. |
|
Establishment of legislative definition of the country's territory hydrographic zoning unit |
Within three years (i.e. 2020) |
||
|
Development of appropriate national legislation (Regulation on Basin Directorate) making the "Basin Directorate" responsible for functions provided by art. 3 of Directive 2000/60/EC |
Within three years (i.e. 2020) |
||
|
Identification of river basin districts and establishment of administrative arrangements for international rivers, lakes and coastal waters |
Within three years (i.e. 2020) |
River basin districts have been established and basin councils have been introduced. |
|
|
Analysis of the characteristics of river basin districts |
Within six years (i.e. 2023) |
||
|
Establishment of programmes for monitoring water quality |
Within six years (i.e. 2023) |
||
|
Preparation of river basin management plans, consultations with the public and publication of these plans |
Within ten years (i.e. 2027) |
In development. |
|
|
Floods Directive (Directive 2007/60/EC of the European Parliament and of the Council of 23 October 2007 on the assessment and management of flood risks) |
Adoption of national legislation and designation of competent authority/ies |
Within two years (i.e. 2019) |
Ministry of Internal Affairs and the State Service for Extraordinary Situations responsible for implementation. |
|
Undertaking preliminary flood assessment |
Within four years (i.e. 2021) |
||
|
Preparation of flood hazard maps and flood risk maps |
Within six years (i.e. 2023) |
||
|
Establishment of flood risk management |
Within eight years (i.e. 2025) |
||
|
Urban Waste Water Directive (Directive 91/271/EEC of 21 May 1991 concerning urban waste water treatment as amended by Directive 98/15/EC and Regulation (EC) No 1882/2003) |
Adoption of national legislation and designation of competent authority/ies |
Within three years (i.e. 2020) |
Ministry of Development of Communities and Territories responsible for implementation. |
|
Assessment of the status of urban wastewater collection and treatment |
Within five years (i.e. 2022) |
||
|
Identification of sensitive areas and agglomerations |
Within six years (i.e. 2023) |
||
|
Preparation of technical and investment programme for the urban wastewater collection and treatment |
Within eight years (i.e. 2025) |
||
|
Drinking Water Directive (Directive 98/83/EC of 3 November 1998 on quality of water intended for human consumption as amended by Regulation (EC) No 1882/2003) |
Adoption of national legislation and designation of competent authority/ies |
Within five years (i.e. 2022) |
Ministry of Health Care responsible for implementation. |
|
Establishment of standards for drinking water |
Within five years (i.e. 2022) |
||
|
Establishment of a monitoring system |
Within five years (i.e. 2022) |
||
|
Establishment of a mechanism to provide information to consumers |
Within five years (i.e. 2022) |
||
|
Nitrates Directive (Directive 91/676/EC of 12 December 1991 concerning the protection of waters against pollution caused by nitrates from agricultural sources as amended by Regulation (EC) No 1882/2003) |
Adoption of national legislation and designation of competent authority/ies |
Within three years (i.e. 2020) |
Ministry of Economic, Trade and Agrarian Development and Ministry of Environmental Protection and Natural Resources responsible for implementation. |
|
Establishment of monitoring programmes |
Within four years (i.e. 2021) |
||
|
Identification of nitrate vulnerable zones |
Within three years (i.e. 2020) |
||
|
Establishment of action plans for nitrate vulnerable zones |
Within four years (i.e. 2021) |
||
|
Marine Strategy Framework Directive (Directive 2008/56/EC of the European Parliament and of the Council of 17 June 2008 establishing a framework for Community action in the field of marine environmental policy) |
Adoption of national legislation and designation of competent authority/ies |
Within two years (i.e. 2019) |
Ministry of Environmental Protection and Natural Resources responsible for implementation. |
|
Development of a marine strategy in co‑operation with relevant EU member state(s) |
Within four years (i.e. 2021) |
||
|
Initial assessment of marine waters, determination of good environmental status and establishment of environmental targets and indicators |
Within four years (i.e. 2021) |
||
|
Establishment of a monitoring programme for ongoing assessment and regular updating of targets |
Within six years (i.e. 2023) |
||
|
Preparation of a programme of measures to achieve good environmental status |
Within seven years (i.e. 2024) |
Source: Author’s own elaboration based on European Union (2014[1]), “Association Agreement between the European Union and its Member States, of the one part, and Ukraine, of the other part”, Official Journal of the European Union, I. 161/4, 29 May 2014, https://eur-lex.europa.eu/legal-content/EN/TXT/PDF/?uri=CELEX:22014A0529(01)&from=EN
In addition to these directives, Ukraine is striving to implement environmental and water-related national legislation. It is also aiming to achieve the Sustainable Development Goals (SDGs) adopted at the 2015 UN Summit (6, 14 and 15). In addition, it wants to ratify the UN Economic Commission for Europe (UNECE) Convention on protection and use of transboundary water courses and international lakes (1999). Finally, it wants to implement the UNECE Convention on access to information to improve public participation in decision making and environmental justice.
Ukraine’s international relations in the water sector relate to transboundary co‑operation on water use and protection. Ukraine joined the Water Convention in 1999 and ratified the Water Protocol in 2003. International water co‑operation under these treaties is carried out through basin agreements (for the Black Sea, and Danube and Dniester rivers). This is a new co‑operation approach in Ukraine and co-exists with Soviet-era bilateral agreements on transboundary water co‑operation with neighbours.
4.1. State of play
Copy link to 4.1. State of play4.1.1. Water resources in Ukraine
4.1.1.1. Water use and main pressures on water resources
Ukraine is a relatively water-abundant country, but water use is intensive. Ukraine is the most populous country in the EaP by a wide margin with an economy heavily dependent on agriculture. Following a decrease in freshwater abstraction in Ukraine between 2000 and 2015, abstraction has begun to trend upwards in recent years [Figure 4.1(a)].
Only a fraction of Ukraine’s water resources is formed locally. Most water flows into the country from Belarus, Romania and the Russian Federation (hereafter “Russia”). As such, water stress (defined as the ratio of abstracted water to renewable water resources) in 2018 was 18.8% (locally formed resources only) and 5.2% (all water resources). Per capita freshwater abstraction in 2018 was 253 cubic metres (m3).
Ukraine faces water quality challenges caused by the discharge of untreated and insufficiently treated wastewater into water bodies [Figure 4.1(c)]. Urban treatment plants, which lack tertiary treatment facilities, have inadequate capacity and poor working conditions. In addition, rural areas have low access to sewerage (European Environment Agency, 2020[2]).
While Ukraine has consistently increased access to WSS services, access is still far from universal [Figure 4.1 (d)]. By 2030, Ukraine aims to overcome inequalities in access to water and sanitation. It aims to guarantee a social minimum of water (a certain number of litres per person per day) for drinking and sanitation purposes regardless of place of residence (rural or urban).
In accordance with international norms, Ukraine is required to pass legislation by 2025 that guarantees equal rights to water and sanitation. Water policy measures would follow to implement the legislation. By 2025, ensuring the right to drinking water and sanitation is likely to be considered as a priority for financing in the budgets of all levels (national-regional-local). Co-financing and attracting investment in the development of the water supply and sewerage sector and wastewater treatment will be required.
Figure 4.1. Water use in Ukraine
Copy link to Figure 4.1. Water use in Ukraine
Source: State Statistics of Ukraine (2020[3]), Environment of Ukraine 2019, State Statistics of Ukraine, https://ukrstat.org/uk/druk/publicat/kat_u/2020/zb/11/Dovk_19.pdf; State Statistics of Ukraine (State Statistics of Ukraine, 2017[4]), Enviroment of Ukraine 2016, State Statistics of Ukraine, https://ukrstat.org/uk/druk/publicat/Arhiv_u/07/Arch_dov_zb.htm.
4.1.1.2. Ukraine’s water resources and river basins
According to multi-year observations, the potential water resources of Ukrainian rivers amount to over 209.8 cubic kilometres (km3), only 25% (52.4 km3) of which are formed on the territory of Ukraine. The remainder (157.4 km3) enters Ukraine from neighbouring countries, particularly Belarus and Russia. Projected resources of underground waters not connected to surface waters are 61.7 million m3 per day, and their extraction volume is about 3.3 million m3/day. Additionally, some sectors of the Ukrainian economy use about 1 km3/day of marine water.
Ukraine’s water resources are unevenly distributed across the country's territory due to climate conditions, topography and the geological structure of nine individual river basin districts. Five empty into the Black Sea (the Dnieper River Basin, the Dniester River Basin, the Danube River Basin, the area of the Southern Bug River Basin, the Black Sea River Basin). Two empty into the Sea of Azov (the Don River Basin, the Priazovya River Basin). One empties into the Baltic Sea (the Vistula River Basin). Finally, one enters into both the Black Sea and Sea of Azov (the Crimean River Basin District).
The southern regions of Ukraine, where most agricultural and industrial water users are concentrated, suffer from water stress and insecurity. These regions rely on the Dnieper River for all their water resources. The Dnieper makes up 80% of all water resources in Ukraine, supplying drinking water to two-thirds of the country’s population.
Ukraine has built more than 1 160 reservoirs with a cumulative volume of about 55 km3 to improve water supply. These include the Kremenchukske and Kahovske reservoirs (part of the cascade of Dnieper reservoirs), which rank among the largest in the world with surface areas of 2.23 thousand km2 and 2.15 thousand km2 respectively. Ukraine also has an extensive network of canals (over 1 000 km) and water supply systems (over 2 000 km). This makes it possible to redistribute annually 3‑12 km3 of fresh water, respectively.
The long-term change in the hydrological regime has been pronounced in Ukraine over the last 20 years, leading to the shallowing and further disappearance of small rivers and streams. This problem is especially urgent for small rivers. Due to intensive agricultural activity, their run-off in the forest-steppe zone and in Polissya (a region in the country’s north, primarily in the Pripyat River Basin, a sub-basin of the Dnieper River Basin District – see below) has decreased by 5% and in the steppe by 10%.
In some parts of the steppe zone, the volume of run-off decreased by 40%; in Polissya, it decreased by 15-20%. A considerable number of small rivers has been lost over the decades following independence. Although lack of data prevents exact quantification of these losses, evidence from the Dnieper River suggests the cumulative impact of decreased run-off from small rivers is considerable. Over the past three years, the Dnieper’s run-off decreased by 11 km3 according to measurements taken at the city of Kherson, on the Black Sea at the mouth of the Dnieper River.
Along with the significant climate change impact, other root causes of the negative impact on the hydrological regime include the following:
high agricultural use of lands, especially in southern regions, and improper agricultural practices, including violations of water protection zones, ploughing of agricultural lands near the water edge of small rivers, burning and cutting of reeds and other coastal vegetation, and so on
high water capacity of industrial and agricultural production
systematic violations and failures in complying with legislation on water protection strips
lack of clarity in the definition and application of the ecological water flow
artificial modification of hydromorphological characteristics, which is straightening riverbeds, silting, shallowing and further disappearing water streams
lack of funds and works, as well as lack of political will on the appropriate restoration of hydromorphological characteristics, including repair and restoration of hydraulic constructions that are important in the hydrological regime regulation (e.g. a flood in Western Ukraine in 2020 destroyed water dams everywhere).
4.1.1.2.1. River basin management plans
River basin management plans (RBMPs) in Ukraine are being developed to achieve specific environmental objectives for each of the nine river basin districts. The Ministry of Environmental Protection and Natural Resources and the State Water Agency are carrying out measures for the development of the plans and their implementation. Updates are foreseen every six years. All basins seek to achieve and maintain “good” ecological status of surface water and groundwater bodies, and “good” ecological potential of artificial or significantly altered surface water bodies. The plans are developed by the State Water Agency together with the State Agency for Geodesy, central and local executive bodies, local governments and other stakeholders; they also consider decisions of the relevant basin councils. To date, RBMP implementation has begun only on the Dnieper River Basin.
The Dnieper River Basin Management Plan
The Dnieper Basin is the largest in Ukraine, covering twice the total land area covered by the other eight basins. It is thus divided into four smaller sub-basins, each with its own RBMP. Input at the local level helped determine how the ecosystems interact with human activities in each sub-basin and measures needed to develop each one sustainably. The plan was prepared in accordance with European requirements and developed based on best practice for implementation of the WFD. Plans contain a general description of the river basin, analysis of anthropogenic impacts and protected areas, environmental objectives and an economic analysis of water use within the basin. The plan’s next cycle is expected to be supplemented by assessments of water monitoring results, further building a Programme of Measures (PoM) to achieve the relevant environmental objectives of the basin. The plan will serve as the basis for other RBMPs in Ukraine that are in development.
4.1.1.2.2. Water management issues and pressures in Ukraine’s river basin districts
Key water management issues within the Dnieper River Basin relate principally to problems with pollution. They require management interventions to align with the WFD in the following areas:
insufficient or absent wastewater treatment resulting in organic and nutrient pollution
pollution from hazardous substances, particularly from the wastewaters of industrial and municipal enterprises, and pesticides, among others
hydromorphological changes throughout the basin, which influence flood protection, hydropower, flow regulation and riverbed straightening
insufficient data to determine the ecological status of water bodies, which means experts designate risk (EUWI+, 2020[5]).
Aligning with the WFD’s environmental objectives means achieving “good” rating for ecological/chemical status of surface water bodies; ecological potential and chemical status of heavily modified and artificial water bodies; and chemical or quantitative status of groundwater bodies. Based on these objectives, the Dnieper RBMP identified more specific environmental objectives drawing on the delineation categories for water bodies within the basin (see Table 4.2).
Table 4.2. Environmental objectives of the Dnieper RBMP
Copy link to Table 4.2. Environmental objectives of the Dnieper RBMP|
Status of the water body in 2015 |
Environmental objective |
|---|---|
|
Water bodies deemed as “high” or “good” status. |
Maintaining the water status across all planning cycles up to 2032 and beyond. |
|
Water bodies that are either at risk of failing the environmental objectives in 2015 or in moderate status in 2015. |
By 2021, having Water Framework Directive compliant status assessment in place or achieving a “good” status by 2021. |
|
Water bodies that are either at risk of failing the environmental objectives in 2015 or in poor status in 2015. |
By 2021, having Water Framework Directive compliant status assessment in place or achieving a “good” status by 2027. |
|
Water bodies that are either at risk of failing the environmental objectives in 2015 or in bad status in 2015. |
By 2021, having Water Framework Directive compliant status assessment in place or achieving a “moderate” status by 2021, achieving a “moderate” or “good” status by 2027, or certainly achieving a “good status” by 2033. |
Source: Information in this table was obtained from UNENGO ‘MAMA-86’ (2015[6]), Draft River Basin Management Plan for the Upper Dnieper Pilot Basin of Ukraine, http://blacksea-riverbasins.net/sites/default/files/RBMP_Upper%20Dnieper_UA_EN_final_1.pdf
4.1.1.2.3. Programme of measures
The PoM identifies actions that will help meet the environmental objectives set in the RBMP. Table 4.3 describes the major issues in the Dnieper River Basin and the aligned measures that contribute to overcoming them.
Table 4.3. Programme of measures in the Dnieper RBMP: Achieving the environmental objectives
Copy link to Table 4.3. Programme of measures in the Dnieper RBMP: Achieving the environmental objectives|
Environmental issues |
Programme of measures |
|---|---|
|
Untreated wastewater causes organic and chemical pollution. |
|
|
Mineral fertilisers from agriculture result in nutrient pollution. |
|
|
Hydromorphological changes from engineering projects can disrupt natural flow regimes and ecosystems. |
|
|
Agricultural run-off can contain dangerous industrial substances and pesticides contaminating surface waters. |
|
|
Improperly sealed cesspools and septic tanks in areas where municipal sanitation services are lacking. Leaking contaminates surface water and groundwater, leading to health hazards. |
|
Source: Information in this table was obtained from the Regional Environmental Centre for Central and Eastern Europe (2016[7]), Upper Dnieper River Basin: Draft River Management Plan, http://documents.rec.org/publications/4_UpperDnieper_Eng.pdf
4.1.2. Ukraine’s policy, legal and institutional framework
The legal, regulatory, policy and institutional environment in Ukraine is becoming more robust in terms of alignment with the WFD. However, major pieces of legislation delegate responsibilities to sub-legal and normative-legal acts, creating inefficiencies in the legal system. Further, issues with corruption can obstruct effective management across regulations, policies and institutions. Streamlining and clarifying roles and responsibilities of water management actors and establishing long-term policy objectives would help align and strengthen water management direction within Ukraine and in relation to the WFD.
4.1.2.1. Policy framework
Broadly, Ukrainian water policy can be seen through two interconnected “policy avenues”. The first revolves around the rational use of water resources and quantitative restoration. The second focuses on quality aspects combating and preventing pollution.
Until 2020, the Law of Ukraine "On basic principles (strategy) of the environmental policy of Ukraine till to 2020" served as the main prerequisite for obtaining EU Sectoral Budget Support. The strategy proposed strategic objectives including: introducing integrated water resource management (IWRM) according to river basin principles; reconstructing existing and constructing new municipal treatment plants; developing and implementing a PoM to reduce pollution of inland waters and the territorial seas; and ensuring compliance with regulatory requirements.
In 2020, the Ministry of Ecology and Natural Resources developed the Law of Ukraine "On basic principles (strategy) of the state environmental policy of Ukraine till to 2030". This stipulates water management objectives, including the following:
ensuring the clear division of responsibilities in the field of environmental protection at the state, regional and local levels
implementing principles of good environmental governance
maintaining a permanent dialogue with stakeholders in strategic decision making
strengthening institutional capacity for planning, monitoring and evaluating the effectiveness of environmental policy implementation
strengthening capacity of environmental governance in conducting comprehensive environmental monitoring and state control in the field of environmental protection, rational use, reproduction and protection of natural resources
defining functions on environmental protection and economic activity related to the use of natural resources.
These objectives more closely align Ukrainian and EU policy objectives. They have been further specified and reformulated in the draft Strategy for the Development of Water Policy of Ukraine till 2050. The Cabinet of Ministers is reviewing the draft strategy. In 2022, it will also review a draft Strategy of Maritime Environmental Policy of Ukraine till 2032.
Besides these draft strategies, Ukraine has developed the Concept of Water Sector Reform. This aims chiefly to establish a national water market. However, it also separates the economic functions of water service supply from state water governance. In addition, it establishes the National Water Council to undertake both guidance and supervision on the preparation and implementation of RBMPs and to regulate water tariffs for irrigation. Long term, it aims to do the following:
Ensure equal access of the population to safe water and proper sanitation.
Achieve and maintain the “good” ecological status of surface water bodies; ecological potential of artificial or significantly altered surface water bodies; quantitative and qualitative groundwater conditions; and ecological status of coastal and sea waters.
Ensure water efficiency and the required amount of quality water resources for restoration of aquatic ecosystems and achieving sustainable abstraction and supply of fresh water for the needs of the population.
Manage and minimise growing water risks of extreme floods, floods and droughts, as well as risks to human health related to lack of adequate access to safe water and sanitation.
Introduce IWRM according to basin principles and achieve proper environmental governance in the districts of river basins, coastal and sea waters.
The uptake of the draft strategy and the Concept of Water Sector Reforming depends on the stability of the Ministry of Environmental Protection and Natural Resources, and funding.
Another key policy document is the National Action Plan for 2020-25. The plan was adopted in January 2020 and supports the preparation process for implementing the Strategy of the State Environmental Policy of Ukraine till to 2030. Its two stages (2020-25 and 2026-30) will be evaluated against indicators outlined in the strategy. An assessment of its predecessor is in preparation.
4.1.2.2. Legal framework
Ukraine’s natural resources are public property, with the rights of Ukrainian people being exercised by state bodies and local governments within limits defined by the Constitution and other laws. The Water Code of Ukraine (2002) is the main piece of legislation driving Ukrainian water management. Updates to the Code in 2017 aligned large parts of legislation with EU directives.
Ukraine’s Water Code legislates all types of water bodies including surface, underground and marine waters. In 2017, changes to the Code, in accordance with the WFD, defined legal provisions for moving towards IWRM. They also further established basin principles for water resource management. The main improvements relate to defining river basin districts and establishing river basin councils and procedures for RBMP development.
Table 4.4. Key legislation for water management in Ukraine
Copy link to Table 4.4. Key legislation for water management in Ukraine|
Legislation and relevant information |
Stipulations |
|---|---|
|
Water Code of Ukraine No.213/95-VR (1995) |
|
|
Law of Ukraine “on drinking water, drinking water supply, and wastewater drainage” (2017) |
|
|
Law of Ukraine No. 1264-XII on environmental protection (1991) |
The law is supported by Land, Water, Subsoil, Forest Codes of Ukraine, the Tax Code containing economic instruments of natural resources regulation, Laws on the Protection of atmospheric air and Protection of Lands, Laws of Ukraine on the plant world and the animal world, Law on Natural Reserved Fund of Ukraine, Law on Wastes and other legal acts. Shortcomings include:
|
|
Subsoil Code (No.132/94-VR of 1994) |
The Code is under revision. |
|
Law of Ukraine "on Environmental Impact Assessment" No. 2059-VIII (2017) |
|
|
The Law of Ukraine “About the statement of the National target program of development of water management and ecological improvement of the basin of the river Dnieper for the period till 2021” (2013) |
|
|
The Law of Ukraine "On Organisations of Water Users and Stimulation of Hydraulic Land Reclamation" (in preparation) |
|
|
The Law of Ukraine "On main principles (strategy) of the state environmental policy of Ukraine till 2030" |
|
Source: Author’s own elaboration.
Because Ukrainian legislation was developed according to former Soviet practices, it does not generally include specifics on action. These are typically delegated to lower legislative levels such as sub-legal and normative legal acts. Although high-level legislation may outline effective water management, subsequent lower-level legislation may thus distort or counteract its effectiveness.
4.1.2.3. Regulatory framework
The following table considers the major regulatory acts that govern water sector management.
Table 4.5. Key water management regulation in Ukraine
Copy link to Table 4.5. Key water management regulation in Ukraine|
Regulation |
Stipulations and shortcomings |
|---|---|
|
Decision of the Cabinet of Ministers of Ukraine # 413 "On adoption of the Guidelines for development of normative on limit permissible discharge of pollutants into water bodies and a list of pollutants discharged into water bodies is regulated" (1996) |
|
|
Decision of the Cabinet of Ministers of Ukraine # 336 "On adoption of the Guidelines for development of the river basin management plan" (2017) |
|
|
Decision of the Cabinet of Ministers of Ukraine # 758 "On adoption of the Guidelines for carrying out the state water monitoring" (2018) |
|
|
Decision of the Cabinet of Ministers of Ukraine # 321 "On adoption of the Guidelines for issuing the permit for special water use" (2002) |
|
|
Decision of the Cabinet of Ministers of Ukraine # 247 "On adoption of the Guidelines for development of the flooding risks management plan" (2018) |
|
|
Decision of the Cabinet of Ministers of Ukraine # 1107 "On approval of Guidelines for development and adoption of standards for drinking water supply (2004). |
|
There are opportunities for strengthening Ukrainian regulation both in terms of its implementation. The effectiveness of Ukrainian water regulation is hindered by the wording of the regulation with multiple possible interpretations. This causes misunderstandings between central and local approaches to regulation implementation and impedes the overall effectiveness of the regulation.
4.1.2.4. Institutional framework
Table 4.6. Water institutional bodies and arrangements in Ukraine
Copy link to Table 4.6. Water institutional bodies and arrangements in Ukraine|
Institution |
Sub-bodies and agencies |
Water-related functions |
|---|---|---|
|
Ministry of Environment Protection and Natural Resources |
|
The Natural Reserve Fund does not relate to water management directly, although it provides protection over land and water regions. There is some crossover between the Fund’s objectives and those of RBMPs. |
|
State Agency of Water Resources
Interagency co‑ordination body led by SAWR: Interagency commission on the regulation of work regimes of reservoirs of Dnieper and Dniester rivers. |
|
|
|
State Ecological Inspection (SEI) In the process of reform. |
|
|
|
Public Service on Geology and Subsoil (PSGS) In the process of reform. |
|
|
|
State Agency of Forest Resources |
|
|
|
National Commission regulating in the sphere of Energy and Communal Services |
|
|
|
Ministry of Development of Communities and Territories |
|
|
|
Ministry of Economic, Trade and Agrarian Development |
|
|
|
Ministry of Internal Affairs |
|
|
|
State Service on Emergency Situations |
|
|
|
Ministry of Health Care |
|
|
Source: Author’s own elaboration
Shortcomings hindering robust water management from an institutional standpoint include the following:
Imposing clear roles and responsibilities in practice: Roles and responsibilities are clearly defined but tend to shift, particularly regarding RBMPs and environmental objectives.
Lack of data exchange between authorities, particularly those responsible for water monitoring: Monitoring issues were once resolved by signing “regalements” dictating exchanges of information between monitoring institutions. However, regalements were inefficient as they had no continuity or longevity. Regalements have now ceased.
4.2. Next steps: Scenarios for reform
Copy link to 4.2. Next steps: Scenarios for reformThree scenarios reflect the possibilities for alignment to the WFD. The baseline scenario reflects the current situation and efforts; the business-as-usual scenario envisages minimal alignment efforts; and the future scenario foresees a consolidated effort for achieving alignment.
Unsurprisingly, the future scenario yields the best results in relation to alignment. However, there are risks and challenges associated with each scenario. In all cases, corruption poses challenges to the transparent and efficient implementation and functioning of measures. The socio-economic situation underpinning each scenario will strongly depend on the war in the East of Ukraine. Table 4.7 provides an overview of each scenario and their alignment possibilities, while Table 4.8 compares scenarios and their activities.
4.2.1. Scenarios
4.2.1.1. The baseline scenario
The baseline scenario is developed based on the current proceedings and alignment efforts with the EU directives. In this sense, foundations for alignment exist, although there are various issues that hinder and delay alignment beyond 2030.
Issues with the baseline scenario include the following:
changing and unstable roles and responsibilities within the Ministry of Environmental Protection and Natural Resources,
lack of specific responsibilities assigned to agencies implementing RBMPs and lack of laws to govern procedure,
unstable and weak financing for RBMPs and tariffs for water use, and low appetite for increasing water tariffs,
delays in implementation due to low prioritisation of water and environmentally related issues.
4.2.1.2. The future scenario
In the future scenario, Ukraine will ensure efficient water resource and environmental management nationally by 2030 by developing and implementing institutional and legal reforms in 2024. However, the development of the scenario depends on the availability of strategic policy documents. In this scenario, amendments to the Water Code will provide a solid base for the WFD’s provisions. Further, it will develop an appropriate organisational structure for integrated water resources management at both central and basin levels.
The future scenario is generally well aligned with the WFD. However, risks and challenges may slow down or impede full alignment. These include the following:
lack of specific responsibilities assigned to agencies implementing RBMPs and lack of laws to govern procedure,
failure to identify an agency as competent for achieving or maintaining the “good” ecological status of surface bodies and “good” chemical status of groundwater bodies,
lack of full cost-recovery mechanisms for water and ecosystem services,
lack of definition for financial mechanisms for RBMP implementation,
lack of a system for managing growing risks, including floods, droughts and human health risks related to inadequate access to safe water and sanitation,
risks that the ecological consciousness of Ukrainian citizens and territorial communities are insufficiently developed for addressing water management issues.
4.2.1.3. The business-as-usual scenario
The business-as-usual scenario presumes only marginal alignment with the WFD. The scenario foresees relatively long periods of political uncertainty in the post-election period. This is projected to obstruct robust water management. Within the scenario, gross domestic product is predicted to increase two-fold by increasing state budgets for water management and the environment. Although financing for water protection measures will approximately double in this scenario, this funding will not be enough to establish the nine RBMPs.
Potential risks in this scenario include the following:
the required co‑operation with Russia and Belarus due to agreements of the State Water Agency on protection and use of transboundary watercourses, which makes progress more difficult,
likely political instability leading to the absence of environmental ministers and political decisions oriented towards environmental and water resource protection between 2000-21 and 2024-25,
alignment with EU directives dependent on elected politicians and not on the system’s functioning,
priorities within the federal budget leading to spending cuts on environmental protection,
integration of some strategies depending on others, hindering full implementation of some EU directives
low priority for government of the National Water Council,
control of basin councils by the State Agency of Water Resources, which prevents them from organising funds independently and implementing RBMPs,
conflict zones preventing nation-wide implementation of EU directives,
weak funding mechanisms for RBMPs that may possibly hamper success.
Table 4.7. Alignment of each scenario to the EU framework directives
Copy link to Table 4.7. Alignment of each scenario to the EU framework directives|
Main policy issues |
Description of characteristic features and differences |
||
|---|---|---|---|
|
Baseline scenario |
Business-as-usual scenario |
Future state scenario |
|
|
Adoption and implementation of Water Strategy and Marine Strategy |
Both prepared by 2019 but not adopted due to unsustainable situation in the Ministry of Environmental Protection and Natural Resources. The Marine Strategy still requires the definition of Good Environmental Status descriptors. |
Envisages Water Strategy adoption in 2022. A sustainable institutional basis will not be implemented due to lack of continuity in ministerial teams and lack of government understanding around the importance of water and environmental issues. |
Envisages Water Strategy adoption in 2021. It will be reflected in RBMPs and relatively successfully implemented thanks to the growing global importance of water resources in combating climate change and the government's awareness of this situation. |
|
There are no differences between two scenarios concerning the Marine Strategy. This is due to the uncertainty around the status of the territorial Black Sea in connection with the annexation of the Autonomous Republic of Crimea by Russia and the consequential unpredictable policy and behaviour in the Sea of Azov region. It is expected that Good Environmental Statuses will be defined in the framework of the EMBLAS III project until 2023. It is envisaged the Marine Strategy will be adopted in 2024, and the Marine National Action Plan (NAP) prepared and adopted in 2025. However, NAP implementation will be complicated due to the unclear juridical status of the Black and Azov Seas. The Marine Strategy Framework Directive doesn't consider the Azov Sea within EU jurisdiction. It is unclear whether Ukraine’s National Marine Strategy will consider both Black and Azov Seas or pay attention to the Black Sea only. |
|||
|
Implementation of the Strategy on irrigation and drainage in Ukraine on the period till 2030 |
Adopted by the Cabinet of Ministers of Ukraine’s decisions #688 in 2019. The NAP, as the main implementation instrument, is in the final stages of preparation and acceptance. |
Envisages NAP's adoption in 2021. The World Bank and the European Bank for Reconstruction and Development (EBRD) will not invest money until 2030 in the irrigation and drainage sector due to the unclear tariff situation. Implementation of the strategy will begin, thanks to national investments. However, it will be unstable and only partial. |
Envisages NAP's adoption in 2021. The World Bank and the EBRD will consider the tariff situation as an acceptable risk thanks to land reforms. They may propose an investment portfolio for Ukraine in 2023/24. National investors will join the process, improving the investment environment. |
|
Development of Organisations of Water Users |
The draft Law "On organisations of water users (OWU)" is in the final stage of development. It should be proposed to stakeholders for discussion soon. |
Envisages adoption in 2023/24. Will improve investment conditions for national investors. Inter-farm and internal farm irrigation and drainage structures and networks will be partly restored by 2030. |
Envisages adoption in 2022. Will improve investment conditions for national investors. Inter-farm and internal farm irrigation, and drainage structures and networks will be restored by 2026. |
|
Approximation to the Drinking Water Directive (98/83/EC) and its implementation, and implementation of SDG 6 (clean water and sanitation), SDG 14 (life below water) and SDG 15 (life on land). |
The National Report "SDG: Ukraine" was prepared in 2015 and jointly adopted by the Cabinet of Ministers of Ukraine and the UNDP. Presidential Order #722 from 2019 envisages its implementation. |
By 2030 implementation of:
With respect to SDG 15, (reducing share of arable land), land will be reduced to 55%, falling short of required 47%. |
By 2030 implementation of
With respect to SDG 15 (reducing the share of arable land), land will be reduced to the required 47%. |
|
Approximation to the Water Framework Directive (2000/60/EC) and its implementation |
Despite successful approximation and implementation of most of the WFD, article 9 is still under question. Currently, cost recovery of water resources and services is not achievable. |
Changes in social attitudes towards environment and water resources due to water shortages will lead to significant increases in water prices and prices for water pollution. |
Environmental and economic revisions of water recourses and service pricing in alignment with the framework of National Water Policy Dialogue by 2024 will lead to a real increase of costs for first generation RBMP implementation. |
|
Approximation to the Urban Wastewater Directive (91/271/EC) and its implementation |
Delays due to the unpreparedness of the Ministry of Development of Communities and Territories and Vodokanals in meeting basic requirements. |
No implementation by 2030. Potential partial and inconsistent implementation due to lack of financing for tertiary wastewater treatment initiatives and remaining problems with use of post-treatment sludge. These problems may be partially addressed in 2028-30. |
Relative implementation success by 2030 thanks to establishment of a flexible finance policy for building tertiary wastewater treatment facilities, smart implementation of local treatments by enterprises, and proper regulation of post-treatment sludge use in the construction and agricultural sectors. |
|
Approximation to the Nitrates Directive (91/676/EC) and its implementation |
Delays due to lack of action of the Ministry of Economic, Trade and Agrarian Development. |
Expected adoption by 2024 with developed definitions of zones vulnerable to the accumulation of nitrate compounds and the Code of the best agricultural practice. First generation RBMPs will use vulnerable zones as recommendations, though they are not legally defined. |
Expected adoption by 2021-22 with developed definitions of zones vulnerable to the accumulation of nitrate compounds and the Code of the best agricultural practice. Vulnerable zones will be included in first generation RBMPs as the regulatory norms for implementation in agriculture production between 2025-30. |
|
Approximation to the Floods Directive (2007/60/EC) and its implementation |
Relative success under the auspices of the State Service on Extraordinary Situations. Guidance on the development of the Flood Risk Management Plan was adopted by the Cabinet of Ministers of Ukraine in decision #247 in 2018. |
Envisages development and adoption of Flood Risk Management Plans for every river basin district by 2024. Due to delays in development and adoption of these plans, they will not be reflected in RBMPs (final plans should be prepared and adopted in August 2024). |
Envisages the development and adoption of River Basin Flood Risk Management Plans by 2022. In June 2021, draft plans should be published on the State Service on Extraordinary Situations’ website and be reflected in every RBMP. |
Source: Author’s own elaboration
Table 4.8. Comparative analysis of the proposed scenarios’ activities: Baseline scenario (BS), future scenario (FS) and business-as-usual scenario (BAU)
Copy link to Table 4.8. Comparative analysis of the proposed scenarios’ activities: Baseline scenario (BS), future scenario (FS) and business-as-usual scenario (BAU)|
Objectives & measures |
Responsible agencies, organisations |
Scenarios |
|---|---|---|
|
A. Formulation and implementation of policies, RBMPs and NAPs |
||
|
Preparation and adoption of the Water Strategy |
MEPNR, MDCT, METAD, Ministry of Internal Affairs, SAWR, PSGS, State Service on Emergency Situations, Oblast State Administrations |
BS: financed through MEPRN's annual budget (under the budget line of “staff wages”). |
|
Preparation and adoption of the Marine Environmental Strategy |
MEPNR, Oblast State Administrations bordering seas |
BS: financed through MEPRN's annual budget (under the budget line of “staff wages”). |
|
Preparation of RBMPs |
MEPNR, SAWR and its territorial bodies, RBCs |
BS: financed through SAWR and its territorial bodies' annual budgets (under the budget line of “staff wages”). |
|
Preparation and implementation of the NAP for the Marine Environmental Strategy |
MENR, USCME, Oblast State Administrations bordering seas |
BS: financed through MEPRN's annual budget (under the budget line of “staff wages”). |
|
Preparation and adoption of Flood Risk Management Plans for each RBD |
MIA, MEPNR, State Service on Emergency Situations, SAWR |
BS: financed through SSES and its territorial bodies' annual budgets (under the budget line of “staff wages”). |
|
Preparation of the national concept on drought risk management and respective NAPs for each RBD |
MEPNR, METAD, Ministry of Internal Affairs, State Service on Emergency Situations, SAWR |
BS: financed through MEPRN's annual budget (under the budget line of “staff wages”). |
|
B. Finalisation of public water management institutional reforms |
||
|
Establishment of the National Water Council |
Cabinet of Ministers of Ukraine, MEPNR, Ministry of Finance |
FS: biannual meetings (EUR 1 000 each) BAU: irregular meetings. |
|
Strengthening the role of RBCs in decision making on RBMP preparation and implementation |
FS: successful power transfers decrease the state budget and increases local governments' annual budgets. BAU: foresees delays power transfers and the continuation of the predominant funding of meetings by SAWR. |
|
|
Establishing the National Joint Stock Company (NJSC) providing irrigation and drainage services |
MEPNR, METAD, SAWR, Oblast State Administrations dealing with irrigation and drainage |
FS: NJSC is established and is properly financed. BAU: NJSC is established but insufficiently financed. |
|
Establishing Organisations of Water Users (OWU) |
Related enterprises and organisations |
FS: successful OWU formation involves an appropriate number of meetings. BAU: delays in OWU formation, thus, fewer meetings. |
|
Establishing government institutions for marine environment protection |
MEPNR, USCME, SEI, Oblast State Administrations bordering seas |
FS: establishment of two state enterprises providing public management for the Black and Azov Seas, including monitoring labs; adequate financing from the state budget and possible increased international technical assistance. BaU: delays in establishment and unclear management situations; slight increase in state funding and same level of international technical assistance so the USCME can undertake functions of MEPNR. |
|
Addressing groundwater management and monitoring issues Transferring functions from PSGS to SAWR |
MEPNR, SAWR, PSGS |
Possible redistribution of funds (between PSGS and SAWR) under existing budget programmes (at the expense of PSGS staff wages). FS: clear redistribution of responsibilities and transfer of groundwater management and monitoring to BDWR with appropriate transfer of financing from PSGS to SAWR BAU: delays in the transfer of functions and their duplication by territorial bodies without sufficient increase of financing. |
|
C. Implementation of RBMPs |
||
|
Building new and reconstructing existing municipal water treatment facilities |
MEPNR, SAWR, PSGS (Investments Stabilisation State Fund) Local government bodies (as a possible part of the Investments Stabilisation State Fund) |
BS: real (capital and current) expenditures of the sector. FS: UkrVodokanalEcology funding requirements for initial municipal reform BAU: state pressures on businesses lead to relative increase in finances derived from public investments. |
|
Addressing the issues of industrial pollution, including the mining industry |
Investments Stabilisation State Fund, local government bodies (as a possible part of Investments Stabilisation State Fund), related enterprises and organisations |
BS: current (2020) industry needs for environmental investments. FS: real needs of industry (particularly the mining industry) in initial environmental investments. BAU: slightly improved situation – investments caused by public pressure. |
|
Definition of zones vulnerable to nitrate compounds and application of best agricultural practices |
Investments Stabilisation State Fund, local government bodies (as a possible part of the Investments Stabilisation State Fund), related enterprises and organisations |
FS: requirements of agricultural businesses in initial environmental investments (not related to zones vulnerable to nitrate compounds). BAU: slight improvements from the current situation with investments resulting from public pressure. |
|
Implementation of the state water monitoring programmes |
MEPNR, SAWR, PSGS, State Service on Emergency Situations, State Agency on Exclusion Zone Management, local government bodies, other sources (investments), international donors |
BS: 2019 financing of water monitoring (accounting for creation of two laboratories for SAWR). FS: financing requirements for renovation of 13 laboratories for SAWR, 11 laboratories for SESS and 2 marine laboratories for monitoring at minimum 70% of delineated water bodies. BAU: partly improved water monitoring situation thanks to international technical assistance and increased state budget expenses. |
|
Implementation of the anti-flooding measures |
SAWR, local government bodies related enterprises and organisations |
BS: shows the current (2019) financing of the SAWR according to budgetary requests. FS: shows possible needs could arise in Flood Risk Management Plans by links with the National Target Program for the Protection of Population and Territories from Emergencies of Man-Made and Natural Character for 2013-17. BAU: shows slightly improved situation in addressing the problem. |
|
Costs required for flood prevention and management |
Hydromet Service of State Service on Emergency Situations, State Service on Emergency Situations |
BS: expenditures spent on prevention, management and consequences of floods FS: possible needs, derived from the National Target Program for the Protection of Population and Territories from Emergencies of Man-Made and Natural Characteristics for 2013-17. BAU: only marginal improvements in flood prevention and management. |
|
Protection of rural settlements and agricultural lands against harmful effects of water |
SAWR, local governments (through agreements) |
BS: real expenditures of the last two years (2019, 2020). FS: expected finances required wetlands drainage. BAU: worst-case scenario relative to FS due to delays in water strategy implementation. |
|
Costs required for irrigation and drainage |
SAWR and Investments Stabilisation Fund, related enterprises and organisations |
BS: real expenditure from the last two years (2019, 2020). FS: investment needs, requested by the Strategy on irrigation and drainage in Ukraine till 2030 (adopted by the CMU). BAU: slightly worse situation relative to the FS due to delays in strategy implementation. |
|
Costs required to minimise the effects of droughts |
Hydromet Service of State Service on Emergency Situations, State Service on Emergency Situations, private investments from impacted businesses |
BS: real expenditures spent on prevention and consequences of droughts (separate resolutions of the CMU on spending costs for dotation of agricultural business from the special reserve fund of CMU). FS: possible needs, with the National Action Plan for combating land degradation and desertification. BAU: only marginal improvements on the current situation. |
|
D. Integrated water resources and water basin management |
||
|
Scientific and applied research in integrated water resources management and staff training |
SAWR |
BS: real expenditure of the last two years (2019, 2020). FS: expected finances required for strengthening the water sector. BAU: worse-case scenario relative to the FS due to delays in water strategy implementation. |
|
Protected areas |
MEPNR |
BS: real expenditure on maintenance of existing protected areas and creation of new ones. FS: finances required for protecting the area of 6 276.9 ha (current 4 082.2 ha). BAU: only slight improvements on the current situation. |
|
Forestry |
MEPNR and State Agency of Forest Resources |
BS: real expenditures on maintenance of existing forests. FS: finances required increase the total area of forests from 16% to 20% of total land area. BAU: only slight improvements on the current situation. |
|
Land policy |
METAD and State GeoCadastr |
BS: real expenditures on land withdrawal from agricultural circulation. FS: finances required to reduce the area of arable land from 53.9% to 47%. State budgets will need to compensate current landowners. BAU: only slight improvements on the current situation. |
Note: MCTD = Ministry of Communities and Territorial Development; MEPNR = Ministry of Environment Protection and Natural Resources; METAD = Ministry of Economic, Trade and Agrarian Development; MIA = Ministry of Internal Affairs; SAWR = State Agency for Water Resources; SEI = State Environmental Inspectorate; USCME = Ukrainian Scientific Centre for Marine Environment.
Source: Author’s own elaboration
4.2.2. Financing each scenario
The following section offers an overview of the major costs associated with the scenarios and presents the respective additional costs. The business-as-usual and baseline scenarios do not differ significantly in terms of their required funding. However, the future scenario requires a significantly larger amount of funding, which corresponds with more thorough and timelier implementation. The future scenario also dedicates more resources to preparation and implementation of both RBMPs and IWRM.
Table 4.9 summarises the funding required to develop each scenario, as well as some costs related to forecasted natural disasters.
The State Fund for development of the water economy
The State Fund for development of the water economy was created by the Cabinet of Ministers of Ukraine in 2018. Funds support measures to develop and maintain water management and increase the efficiency of water use. The main administrator is the Ministry of Environmental Protection and Natural Resources with implementation by the State Agency of Water Resources.
The Fund for Environmental Protection
The Fund for Environmental Protection was created in the Law on Environmental Protection. The fund is derived from environmental taxes, and costs relating to recovered damages arising from the violation of environmental legislation. In 2014, the fund became a consolidated part of the state budget. In 2018, the fund of UAH 506 million was mainly used for the sustainable functioning of Exclusion Chornobyl Zone facilities. Other expenditures were directed towards environmental measures. Targeted use of the fund’s money is regulated by decisions of the Cabinet of Ministers of Ukraine in the resolution "on approval of the list of activities belonging to environmental ones". However, the resolution does not ensure proper use of the fund due to ambiguous wording and the possibility of multiple interpretations. Of the 85 environmental measures listed in the resolution, 17 relate to protection and rational use of water resources.
In addition to this fund, local governments have created a special fund out of environmental taxes for implementation of environmental measures. However, like the national fund, environmental measures are sometimes used for non-environmental purposes. This mars the efficacy and transparency of environmental protection, indicating the low priority of environmental issues for the current government.
Table 4.9. Financial requirements for each scenario, in thousands of euros per year
Copy link to Table 4.9. Financial requirements for each scenario, in thousands of euros per year|
Objectives & measures |
Financing sources |
Responsible agencies, organisations |
Scenarios (thousand EUR/year) |
||
|---|---|---|---|---|---|
|
Baseline |
Future |
Business-as-usual |
|||
|
TOTAL ANNUAL SPENDING FOR EACH SCENARIO (EUR 1 000) |
2 087 474 |
23 121 867.6 |
4 130 207.5 |
||
|
A. Formulation and implementation of policies, RBMPs, and NAPs |
94 275 |
123 720 |
95 400 |
||
|
Preparation and adoption of the Water Strategy |
State budget |
MEPNR, MDCT, METAD, Ministry of Internal Affairs, SAWR, PSGS, State Service on Emergency Situations, Oblast State Administrations (OSAs) |
2 025 |
2 959 |
2 500 |
|
Preparation and adoption of the Marine Environmental Strategy |
State budget |
MEPNR, OSAs bordering seas |
To be financed in MEPRN’s routine annual budget (as staff time) |
||
|
Preparation of RBMPs |
State budget |
MEPNR, SAWR and its territorial bodies, RBCs |
850 |
1 161 |
900 |
|
Preparation and implementation of the NAP for Marine Environmental Strategy |
State budget |
MENR, USCME, OSAs having access to seas |
To be financed in MEPRN ‘s routine annual budget (at the expense of staff wages) |
||
|
Preparation and adoption of Flood Risk Management Plans for each RBD |
State budget |
Ministry of Internal Affairs, MENPR, State Service on Emergency Situations, SAWR |
91 400 |
119 600 |
92 000 |
|
Preparation of the National concept on drought risk management and respective NAPs for each RBD |
State budget |
MEPNR, METAD, Ministry of Internal Affairs, State Service on Emergency Situations, SAWR |
Financed through MEPRN's annual budget (at the expense of staff wages) |
||
|
B. Finalisation of institutional reforms in public water management |
0 |
1 223.6 |
745.5 |
||
|
Establishment of the NWC |
State budget |
Cabinet of Ministers of Ukraine, MEPNR, Ministry of Finance |
N/A |
2 |
0.5 |
|
Strengthening the role of RBCs in decision making on RBMPs preparation and implementation |
State budget |
SAWR |
Not yet possible |
3 |
20 |
|
Local budget |
Local water management bodies |
18 |
25 |
||
|
Total |
MEPNR, SAWR, PSGS and local water management bodies |
N/A |
21 |
25 |
|
|
Establishing the National Joint Stock Company (NJSC) providing irrigation and drainage services |
State budget |
MEPNR, METAD, SAWR, OSAs dealing with irrigation and drainage |
Not yet established |
250 |
200 |
|
Establishing Organisations of Water Users (OWU) |
Related enterprises |
Related enterprises and organisations |
0 |
48 |
20 |
|
Establishing government institutions for marine environment protection |
State budget |
MEPNR, METAD, Ministry of Finance |
159 |
543 |
250 |
|
Possible international technical assistance |
EU, GEF, UNDP |
70 |
150 |
100 |
|
|
Total |
MEPNR, USCME, SEI, OSAs bordering seas |
229 |
693 |
350 |
|
|
Addressing groundwater management and monitoring issues. Transferring functions from PSGS to SAWR |
State budget |
MEPNR, SAWR, PSGS |
149 |
209.6 |
150 |
|
C. Implementation of RBMPs |
1 974 325 |
15 555 151 |
4 012 705 |
||
|
C-1. Total expected costs required for liquidation of consequences of floods and droughts |
151 000 |
70 400 |
109 500 |
||
|
C-2. Total expected losses caused by floods and droughts |
242 100 |
85 700 |
252 750 |
||
|
Building new and reconstructing existing municipal water treatment facilities |
State budget |
MEPNR, SAWR, PSGS (Investments Stabilisation State Fund) |
18 900 |
250 000 |
37 800 |
|
Local budget |
Local government bodies (as a possible part of the Investments Stabilisation State Fund) |
56 700 |
750 000 |
114 000 |
|
|
Related enterprises |
Related enterprises and organisations |
302 000 |
4 000 000 |
622 850 |
|
|
Total |
|
377 600 |
5 000 000 |
774 650 |
|
|
Addressing the issues of industrial pollution, including the mining industry |
State budget |
Investments Stabilisation State Fund |
44 640 |
212 700 |
89 300 |
|
Local budget |
Local government bodies (as a possible part of Investments Stabilisation State Fund) |
96 400 |
459 650 |
193 000 |
|
|
Related enterprises |
Related enterprises and organisations |
1 287 480 |
6 135 000 |
2 580 000 |
|
|
Total |
|
1 428 520 |
6 807 350 |
2 862 300 |
|
|
Definition of zones vulnerable to nitrate compounds and application of best agricultural practices |
State budget |
Investments Stabilisation State Fund |
N/A |
15 000 |
500 |
|
Local budget |
Local government bodies (as a possible part of the Investments Stabilisation State Fund) |
|
459 358 |
4 800 |
|
|
Related enterprises |
Related enterprises and organisations |
|
2 884 643 |
96 155 |
|
|
Total |
|
0 |
3 359 000 |
101 455 |
|
|
Implementation of the state water monitoring programmes |
State budget |
MEPNR, SAWR, PSGS, State Service on Emergency Situations, State Agency for Exclusion Zone Management |
490 |
5 600 |
1 200 |
|
Local budget |
Local government bodies |
0 |
0 |
0 |
|
|
Related enterprises |
Other sources (investments) |
0 |
0 |
0 |
|
|
International technical assistance |
International donors |
400 |
800 |
400 |
|
|
Total |
|
890 |
6 400 |
1 600 |
|
|
Implementation of anti-flooding measures |
State budget |
SAWR |
1 730 |
6 260 |
1 900 |
|
Local budget |
Local government bodies |
Data n/a |
Data n/a |
Data n/a |
|
|
Related enterprises |
Related enterprises and organisations |
Data n/a |
Data n/a |
Data n/a |
|
|
Total |
|
1 730 |
6 260 |
1 900 |
|
|
Costs required for flood prevention and management |
State budget |
Hydromet Service of State Service on Emergency Situations |
3 500 |
9 500 |
3 700 |
|
Total expected losses |
Losses caused by floods |
17 100 |
5 700 |
42 750 |
|
|
State budget - Special reserve fund of Cabinet of Ministers of Ukraine |
State Service on Emergency Situations |
11 000 |
4 100 |
27 100 |
|
|
Total |
|
14 500 |
13 600 |
30 800 |
|
|
Protection of rural settlements and agricultural lands against harmful effects of water |
State budget |
SAWR |
8 840 |
5 400 |
7 100 |
|
Local budget |
Local governments (through agreements) |
5 390 |
3 290 |
4 200 |
|
|
Total |
|
14 230 |
8 690 |
11 300 |
|
|
Costs required for irrigation and drainage |
State budget |
SAWR and Investments Stabilisation Fund |
70 |
3 050 |
3 000 |
|
Local budget |
As sources to Investments Stabilisation Fund |
50 |
14 000 |
7 000 |
|
|
Related enterprises |
Related enterprises and organisations |
235 |
280 000 |
140 000 |
|
|
Total |
|
355 |
297 050 |
150 000 |
|
|
Costs required to minimise the effects of droughts |
State budget |
Prevention: Hydromet Service of State Service on Emergency Situations |
3 500 |
9 500 |
3 700 |
|
Total expected losses |
Losses caused by droughts |
225 000 |
80 000 |
210 000 |
|
|
State budget: the special reserve fund of CMU |
State Service on Emergency Situations, private investments from impacted businesses |
133 000 |
47 300 |
75 000 |
|
|
Total |
|
136 500 |
56 800 |
78 700 |
|
|
D. Integrated water resources and water basin management |
18 874 |
7 441 773 |
21 357 |
||
|
Scientific and applied research in integrated water resources management and staff training |
State budget |
SAWR |
237 |
1 040 |
340 |
|
Protected areas |
State budget |
MEPNR |
16.7 |
33 |
17 |
|
Forestry |
State budget |
MEPNR and State Agency on Forestry Resources |
17 800 |
28 000 |
20 000 |
|
Land policy |
State budget |
METAD and State GeoCadastr |
820 |
7 412 700 |
1 000 |
Note: GEF = Global Environment Facility; METAD = Ministry of Economic, Trade and Agrarian Development; MEPNR = Ministry of Environment Protection and Natural Resources; PSGS =Public Service on Geology and Subsoil; RBD = river basin district; SAWR = State Agency for Water Resources; SEI = State Environmental Inspection USCME = Ukrainian Scientific Centre for Marine Environment; UNDP = United Nations Development Programme.
Source: Author’s calculations.
4.2.3. Progress monitoring indicators
The progress monitoring indicators in water resource management and alignment with EU water directives show potential for improvement. In 2011, Ukraine developed and adopted indicators measuring the implementation of the Water Protocol of the Water Convention. According to international obligations, the Water Protocol indicators were revised in 2019; this work was performed under the auspices of UNECE in the framework of the EUWI+ Project. The indicators are waiting for approval. Some of the proposed indicators in encompass the SMART elements required for successful monitoring and evaluation (i.e. Specific, Measurable, Achievable, Realistic and Timely). However, in other cases, indicators such as “the degree of implementation of integrated water resources management” lack specificity, are difficult to measure and are not time-bound. Notably, there are no specific timeframes accompanying each indicator. In this sense, there are opportunities for strengthening the indicators to monitor and evaluate the success and impacts of aligning with EU directives more thoroughly. Table 4.10 presents the relevant progress monitoring indicators with their units of measurement.
The adoption of the Water Strategy is the first performance indicator in the framework of the future state scenario. Subsequently, evidence of incorporating Water Strategy provisions into RBMPs is considered a performance indicator.
Table 4.10. Progress monitoring indicators
Copy link to Table 4.10. Progress monitoring indicators|
Indicators |
Unit of measurement |
|---|---|
|
Indicators assessing the effectiveness of the water institutional framework and water governance mechanisms (baseline vs. future scenario) |
|
|
Degree of implementation of integrated water resources management (legal, institutional, regulatory and financial aspects) |
Percentage |
|
Awareness and accessibility of water information |
According to the results of online surveys |
|
Percentage of transboundary river basin districts for which appropriate (river basin-oriented) water co‑operation mechanisms have been introduced |
Percentage |
|
Revenue for state and local budgets from rental fees for Special Water Users |
Million UAH |
|
Revenue for state and local budgets from environmental taxes for discharging pollutants into water bodies |
Million UAH |
|
Number of detected unauthorised water users |
Physical or juridical entities |
|
Monetary amount of recovered damages for violations of water protection legislation |
Million UAH |
|
Number of laboratories in the optimised system of ecological (water) monitoring that meet the Water Framework Directive requirements |
Number of units |
|
Evidence of practical use of automated information systems in making management decisions |
Automated information system protocols |
|
Budget allocated to the RBMPs at the national, oblast and local levels |
Million UAH |
|
Indicators assessing water quantity management effectiveness (baseline vs. future scenario) |
|
|
Introduction into Ukrainian legislation of the definition of “ecological river flow” and its application in the water permitting procedure |
Inclusion of “ecological river flow” definition and examples of practical application in the water permitting procedure |
|
Water stress level: the share of the volume of fresh water taken in relation to the volume of available freshwater resources |
Percentage |
|
Water volume used for all economic activities, particularly agriculture, industry and the service sectors |
Million cubic metres |
|
The share of arable land in the total territory of the country |
Percentage |
|
Number of restored riverbeds of small rivers and swamps of Ukraine |
Kilometres or hectares |
|
Water capacity of GDP (per UAH 1 000 of GDP in real prices) |
Cubic metres |
|
Annual value added per volume (cubic metre) of water taken economic activities |
USD |
|
The amount of annual water losses during transportation |
Million cubic metres |
|
Number of annual violations of the legislation on water protection zones and coastal protection strips |
Units |
|
Indicators for water quality effectiveness and pollution prevention (baseline vs. future scenario) |
|
|
Share of treated wastewater discharges of total discharges to water bodies |
Percentage |
|
Share of polluted wastewater discharges in the total amount of discharges to water bodies (separately to for marine environments) |
Percentage |
|
Additional capacity of constructed or reconstructed wastewater treatment facilities in urban and rural areas |
Thousand cubic metres/year |
|
Number of enterprises that have introduced preliminary (local) wastewater treatment facilities |
Units |
|
Detection cases of water pollution |
Units/year |
|
Percentage of surface water bodies deemed in “good” ecological condition in relation to the total number |
Percentage |
|
Percentage of artificial or significantly modified surface water bodies deemed in “good” condition in relation to the total number |
Percentage |
|
Percentage of groundwater bodies deemed in “good” quantitative and qualitative status in relation to the total number |
Percentage |
|
Economic value of damage to aquatic ecosystems (particularly fisheries) due to thermal water pollution |
UAH million/year |
|
Damage to aquatic ecosystems, in particular fisheries, due to biological pollution of water |
UAH million/year |
|
Total area of zones vulnerable to the accumulation of nitrate compounds identified for each area of the river basin district |
Thousand hectares |
|
Share of the area of zones vulnerable to the accumulation of nitrate compounds (defined for each river basin district) in the total area of the river basin district |
Percentage |
|
Mass of dehydrated and utilized post-treatment sludge |
Thousand tonnes |
|
Volume of detergents sold in Ukraine that does not contain orthophosphate compounds |
Thousand tonnes |
|
Amount of funds received by the State Budget of Ukraine as part of the environmental tax for water pollution |
UAH million/year |
|
Facts (evidence) of BAT introduction in industrial and agricultural production |
Facts (evidence) of BAT availability |
|
Indicators for assessing the availability of appropriate (quantity and quality) drinking water (baseline vs. future scenario) |
|
|
Volume of daily water used by one urban resident (per capita water use) |
Cubic metres/day |
|
Proportion of the rural population with access to safe and affordable drinking water from the total |
Percentage |
|
Proportion of urban population with access to safe and affordable drinking water |
Percentage |
|
Share of the rural population connected to the centralised water supply |
Percentage |
|
Share of the urban population connected to the centralised water supply |
Percentage |
|
Length of urban water supply networks that have been repaired or replaced |
Kilometre |
|
Share of the rural population with access to improved sanitation |
Percentage |
|
Share of the urban population with access to improved sanitation |
Percentage |
|
Length of urban sewage systems that have been repaired or replaced |
Kilometre |
|
Tariffs for water supply and sewerage |
UAH/cubic metre |
|
Existence of water supply, sewerage network and urban treatment facilities optimisation schemes in Master plans for development of cities or settlements |
Fact of availability |
Source: Author’s own elaboration
References
[2] European Environment Agency (2020), Water availability, surface water quality and water use in Eastern Partnership countries: An indicator-based assessment, https://www.eea.europa.eu/publications/regional-water-report.
[1] European Union (2014), “Association Agreement between the European Union and its Member States, of the one part, and Ukraine, of the other part”, Official Journal of the European Union I. 161/3, https://eur-lex.europa.eu/legal-content/EN/TXT/PDF/?uri=CELEX:22014A0529(01)&from=EN.
[5] EUWI+ (2020), Dnipro River Basin Management Plan: Significant Water Management Issues, https://www.euwipluseast.eu/en/component/k2/item/1180-ukraine-summary-of-the-dnipro-rbmp-for-the-1st-consultation-main-issues-full-dnipro-basin-eng?fromsearch=1.
[7] Regional Environmental Centre for Central and Eastern Europe (2016), Upper Dnieper River Basin: Draft River Management Plan, http://documents.rec.org/publications/4_UpperDnieper_Eng.pdf.
[4] State Statistics of Ukraine (2017), Environment of Ukraine 2016, https://ukrstat.org/uk/druk/publicat/Arhiv_u/07/Arch_dov_zb.htm.
[3] State Statistics Service of Ukraine (2020), Environment of Ukraine 2019, https://ukrstat.org/uk/druk/publicat/kat_u/2020/zb/11/Dovk_19.pdf.
[6] UNENGO ’MAMA-86’ (2015), River Basin Management Plan for the Upper Dnieper Pilot Basin of Ukraine: Draft, http://blacksea-riverbasins.net/sites/default/files/RBMP_Upper%20Dnieper_UA_EN_final_1.pdf.